HomeMy WebLinkAbout2660018 - F.I. Received Doc. - EIAR - Appendices to Environmental Impact Assessment Report
August 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
Stream BioEnergy Ireland Limited
PROPOSED RENEWABLE BIOGAS PLANT
IN THE TOWNLANDS OF
MAGHERNAKELLY AND DRUMCALL,
DRUM, CO. MONAGHAN. RECEIVED: 28/08/2026
Volume III – Appendices
Table of Contents
Chapter
No.
Chapter Title Appendices
1. Introduction 1.1 Cumulative Project List
1.2 Economic Impact Assessment
2. Project Description 2.1 Outline Construction Environmental
Management Plan
3. Alternatives 3.1 Site Selection Environmental Analysis
4. Population & Human Health - -
5. Landscape & Visual - -
6. Material Assets: Traffic &
Transport
6.1 Traffic Counts
6.2 Network Flow Diagrams
7. Material Assets: Built Services 7.1 Electrical Connection Feasibility
8. Material Assets: Waste 8.1 Resource & Waste Management Plan
8.2 Operational Waste Management Plan
9. Land & Soils 9.1 NRA/TII Rating Criteria: Soils & Geological
9.2 Monaghan – County Geological Site Report
10. Water (Hydrology &
Hydrogeology)
10.1 NRA/TII Rating Criteria: Hydrological &
Hydrogeological
10.2 Flood Risk Assessment
10.3 Water Framework Directive Assessment
10.4 Groundwater Abstraction Feasibility Assessment
11. Biodiversity 11.1 Arboriculture Survey Report
11.2 Additional Walkover Survey
11.3 Mammal Report
11.4 Bat Survey Report
11.5 Wintering Bird Survey Report
11.6 Breeding Bird Report
12. Noise & Vibration 12.1 Glossary of Acoustic Terminology
12.2 Baseline Noise Survey Data
12.3 Noise Modelling Details
13. Air Quality 13.1 Air Quality Technical Information
14. Climate - -
15. Cultural Heritage: Built Heritage
& Archaeology
15.1 Summary of relevant legislation
15.2 Excerpts of County Development Plan
15.3 Glossary of Impacts
15.4 Geophysical Survey Report
15.5 Testing Report
15.6 Archaeological Testing Report
16. Major Accidents and Disasters - -
17. Summary of Mitigation &
Monitoring Measures
- -
18. Interactions of the Foregoing - -
RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 1.1
CUMULATIVE PROJECT LIST
Stream BioEnergy Ireland Limited RECEIVED: 28/08/2026
RECEIVED: 28/08/2026
PlanRef Applicant Address Decision Date Description Comments
16203 Richard
Carelton
Maghernakelly, Drum, Co.
Monaghan Granted 08/07/2016
permission to 1. change existing finish, 2. carry out elevational alterations, 3. construct a two
storey extension to rear (incorporating car-port with living accommodation over), all to existing
dwelling, with associated ancillary site works
Developer to pay €620 (indexed) development contribution before works; retain and
reinforce site hedgerows with native species; match extension finishes to existing
dwelling; build per submitted plans.
14207 Richard
Carleton
Maghernakelly, Drum, Co.
Monaghan Granted 11/02/2015 change existing finish and carry out elevational alterations to existing dwelling
07585 Wilfred
Carleton Tullyard, Co. Monaghan Granted 16/08/2007
1) replacing a wind damage, dormant slatted cubicle shed with a loose house and handling
facility. 2) a silo pit with retaining walls, working aprons and all ancillary site works
Use dark roof/cladding; retain northern boundary vegetation; plant native mix (≤30%
conifers) along silage pit; control livestock per approved waste plan; ensure compliant
effluent, storage, and drainage; construct per revised plans.RECEIVED: 28/08/2026
PlanRef Applicant Address
Type of
permission Decision Date Description Notes
2660140 Cavan and Monaghan Education and
Training Board
Tonnagh, Rockcorry, Co.
Monaghan Retention Granted with Conditions 07/07/2026 retention of the existing single storey sports hall and associated site works at Tonnagh Rd., Rockcorry, Co.
Monaghan Education
2460274 Carney Dairy Farms Limited Dernamoyle, Dartrey,
Cootehill Co. Monaghan Permission Granted with Conditions 16/12/2024
permission to construct a calf rearing livestock unit complete with concrete apron and drains. Significant Further
Information received relates to a revised Site Layout Plan, a Nutrient Management Plan, Nitrogen Loading Details and other
documents.
livestock
20354 James Carleton & Victoria Hendon Dernamoyle, Dartrey, Co
Monaghan Permission Granted with Conditions 10/03/2021
Permission to construct a two storey dwelling house, with proprietary waste water treatment system along with other
associated ancillary site works (using existing site entrance & access lane)dwelling
20263 Percival Browne Drumanny, Drum, Co.
Monaghan Permission Granted with Conditions 30/09/2020
permission for a development consisting of (1) construction of an agricultural slatted shed to incorporate slatted area,
external feed passage and underground slurry storage tank, (2) completion of all associated and ancillary site works agri shed
2039 Harry Carney & Pauric Carney Dernamoyle, Dartrey,
Cootehill Permission Granted with Conditions 19/06/2020 permission to construct a slatted livestock shed with underground waste storage tanks, concrete apron and drains agri shed
19180 David and Glen Carleton Tattygare, Rockcorry, Co.
Monaghan Permission Granted with Conditions 07/02/2020
permission to construct a broiler type poultry house, together with all ancillary structures including vertical meal bin and
underground washings tank, together with all ancillary site works, using existing site access.poultry
19123 David Carleton Cordressigo, Rockcorry, Co.
Monaghan Permission Granted with Conditions 04/06/2019 Permission to construct a silage base, along with associated ancillary site works. silage base
177 Carleton Poultry Ltd.Dernamoyle, Dartrey (via
Cootehill), Co. Monaghan Permission Granted with Conditions 11/04/2017
permission to construct 1 No. poultry house together with all ancillary structures (to include meal bin(s) and soiled water
tank(s) and site works associated with the above development on an existing poultry farm. This application relates to a
developme
poultry
16476 Kieran & Grainne O'Connor Drumanny, Drum, Co.
Monaghan Permission Granted with Conditions 17/02/2017
permission to demolish derelict house and erect a two storey dwelling with attached sun-room, carport and domestic
garage, sewerage treatment unit, percolation area, new entrance and all associated site works dwelling
16308 Andrew Browne & Carol Kissane Drumanny, Drum, Co.
Monaghan Permission Granted with Conditions 16/12/2016
permission for the construction of a two storey style dwelling house and domestic garage, with access via existing field
entrance, the construction of a sewerage treatment unit and percolation area and all associated site works dwellingRECEIVED: 28/08/2026
Plan Auth PlanRef Applicant Address Type of permission Decision Date Description
Monaghan 239013 Patrick Greenan Kilmore East , Rockcurry , Co. Monaghan Extension of Duration Granted with Conditions -
Permission to revise the proposed development granted permission Planning Ref: 18/57, by providing for: a)
extensions to the 2 No. Proposed poultry houses, and, b) a supplementary extension to the existing poultry house (in
addition to the extension prev
Monaghan 21362 James Stewart Aghareagh East, Drum, Co. Monaghan Permission Refused 21 January 2022
permission to construct 2 no. poultry houses together with all ancillary structures (to include meal storage bin(s) and
soiled water tank(s)) and site works (to include new/relocated site entrance) associated with the above
development. This application
Monaghan 219031 James Tierney Drumskelt, Newbliss, Co. Monaghan Extension of Duration Refused 31 January 2022
Permission- to construct 2 No. Poultry Houses, together with all ancillary structures (to include meal storage bin(s),
etc.) and all associated site works (to include upgraded site entrance)
Monaghan 219033 AK Agricultural Ltd Drumborisk , Drum , Co. Monaghan Extension of Duration Granted with Conditions -
permission to construct 2 No. poultry units together with underground washings tanks, vertical meal bins, use
existing agricultural entrance and all ancillary site works. An EIS has been submitted with this application
Monaghan 2367 S.Wilkin & Sons Ltd Boyher , Rockcorry , Co.Monaghan Permission Granted with Conditions 28 February 2024
permission for development consisting of 1) Removal of existing 2 no. office buildings, 2) Construction of detached
single storey office building incorporating office, sanitary canteen and storage areas, 3) Installation of proprietary
wastewater treatmen
Monaghan 2366 Sammy Wilkin Boyher , Rockcorry , Co. Monaghan Retention Granted with Conditions 11 December 2023
permission & retention permission consisting of (1) Installation of agricultural effluent collection tank, (2)
Completion of all ancillary site works and associated site structures together with the retention of agricultural shed
incorporating bedded are
Monaghan 2460274 Carney Dairy Farms Limited Dernamoyle , Dartrey , Cootehill Co. Monaghan Permission Granted with Conditions 16 December 2024
permission to construct a calf rearing livestock unit complete with concrete apron and drains. Significant Further
Information received relates to a revised Site Layout Plan, a Nutrient Management Plan, Nitrogen Loading Details and
other documents.
Monaghan 22497 Abbott Ireland Dromore West, Cootehill, Co.Monaghan Permission Granted with Conditions 01 February 2023
permission for development consisting of: Expansion to existing facility to provide additional warehouse capacity of
443.50sqm, laboratory area of 327.2sqm, ancillary office & staff facilities of 951.10sqm over 4 storeys, with an
overall height of 15.8m
Monaghan 22312
Carleton Cake Company
Limited Dyan, Cootehill, Co.Monaghan Permission Granted with Conditions 22 September 2022
permission consisting of erection of 1,300m2 or 250.24kWP of photovoltaic panels on the roofs of our existing
manufacturing buildings, in the factory; with all associated site works
Monaghan 21424
Gordon and Mervyn
McConkey magherashaghry, Drum, Co. Monaghan Permission Refused 08 February 2022
permission for development consisting of amendments and alterations to a previously granted poultry unit
development under planning reference number 19/565 which consisted of (1) construction of free range poultry unit
(2) construction of manure storage
Monaghan 2491 Keltec Farms Ltd Tomany Td. , Rockcorry , Co. Monaghan Permission Granted with Conditions 07 March 2025
permission to construct a new poultry unit together with new agricultural entrance, hardened areas, vertical meal
bins, underground washings tanks and all ancillary site works
Monaghan 2360285 Drumlins Park Limited Cornawall Td , Newbliss , Co Monaghan Permission Granted with Conditions 11 April 2024
permission for the installation of a Turbine Service Base Compound consisting of an Office/Canteen unit, 2 no.
storage containers, a 2-person toilet block unit with an associated underground alarmed effluent tank, and all
ancillary site works on an area
Monaghan 21506 Noel Hall Doohat, Newbliss, Co Monaghan Permission Granted with Conditions 23 November 2021
permission that consists of construction of a slatted cubicle house with underground slurry storage tank together
with all ancillary site development works
Monaghan 2498 Nigel Norris Correvan Td. , Newbliss , Co. Monaghan Permission Granted with Conditions 06 January 2025 permission to construct new milking parlour with underground slatted tank with all ancillary site works
Monaghan 22436
Gordon & Mervyn
McConkey Magherashagry, Drum, Co. Monaghan Permission Granted with Conditions 05 September 2023
permission to construct 1 no. poultry house and 1 no. manure storage shed (in lieu of 1 no. poultry house and 1 no.
manure storage shed previously approved under planning permission ref: 19/565), together with A) all ancillary
structures (to include meal
Monaghan 23126 William McGuigan Drumate, Newbliss, Co. Monaghan Permission Granted with Conditions 19 October 2023
Permission to construct 1 No. poultry house together with all ancillary structures (to include meal storage bin(s) and
soiled water tank(s)) and site works associated with the development (to be completed in lieu of similar
development previously approve
Monaghan 21471 Sammy Wilkin Cornawall, Rockcorry, Co. Monaghan Permission Granted with Conditions 23 May 2022
permission to construct 2 no. poultry houses together with all ancillary structures (to include meal bins and soiled
water/ancillary storage tanks) and site works (to include new/upgraded site entrance, and re-contouring (incl. with
imported soil and sto
Cavan 2460613
JJ McCauley Construction
Ltd Drumman , Cootehill , Co.Cavan Permission Granted with Conditions 25 March 2025
of: i) Works to facilitate infill and re-contouring of the subject lands to facilitate use for agricultural purposes. ii) All
associated works and services. The application relates to an activity requiring a Waste Facility Permit/Certificate of
Registrat
Cavan 23295 Leszek Keauszowski Old Cavan Street , Magheranure , Cootehill Co. Cavan Retention Granted with Conditions 21 June 2024
to retain change of use from disused poultry hatchery to vehicle maintenance garage together with all ancillary site
works
Cavan 2373 Cootehill Pastoral Council Station Road , Magheranure , Cootehill Permission Granted with Conditions 23 August 2023
for the erection of a fully serviced single storey pastoral centre incorporating meeting room/hall, offices,
reception/coffee dock, toilet facilities, connection to existing services and all ancillary site works. (The works are to
be carried out within t
Cavan 21143 Aldi Stores (Ireland) Ltd Station Road & Market Street , Cootehill , Co Cavan Permission Granted with Conditions 02 February 2022
for A) Site clearance and demolition of all existing structures on the site of c. 313 sq. m; B) Construction of a single
storey discount foodstore (to include off licence use) with a gross floor area of c. 1,824 sq. m (net retail area 1,333
sq. m); C) Ne
Cavan ACP312878-23
Aldi Stores (Ireland) Ltd.
(Applicant)
RGDATA (3rd Party
Appellant) (Active)
Station Road & Market Street , Cootehill , Co Cavan Permission
Granted with Revised
Conditions Wednesday 15 November 2023
Site clearance and demolition. Construction of supermarket (including off-licence) with associated signage and site
development works. Removal of the boundary wall relating to the Court House building, a protected structure (no.
CV17027).
Cavan 21510
Renewable Energy Systems
(RES) Ltd Errigal Drumman and Lislea , Cootehill , Co Cavan Permission Granted with Conditions 09 November 2021
to amend the approved development (Planning Reference: 16/507) of a temporary (25 years) solar farm to include
photovoltaic panels with mounting frames on screw pile foundations, inverters, transformers, substation, DNO
building, communications building,RECEIVED: 28/08/2026
Plan Auth PlanRef Applicant Address
Type of
permission Decision Date Description Type Comments
Cavan County
Council 21510 Renewable Energy
Systems (RES) Ltd Errigal Drumman and Lislea , Cootehill , Co Cavan Permission
Granted with
Conditions 09/11/2021
to amend the approved development (Planning Reference: 16/507) of
a temporary (25 years) solar farm to include photovoltaic panels with
mounting frames on screw pile foundations, inverters, transformers,
substation, DNO building, communications build
Ammendment of ; 'for development which will consist of the installation and operation of a 5MW solar farm to
include photovoltaic panels with mounting frames on screw pile foundations, inverters, transformers, substation,
DNO building, communications building, security fencing, pole mounted security cameras, minor upgrades to
existing site entrance and all other associated development works. The proposed operational lifetime of the project
is 30 years. Significant further information and revised plans have been submitted '
Monaghan
County Council 21136 Drumlins Park Limited Killyleg & Lislongfield Co. Monaghan Permission
Granted with
Conditions 08/11/2021
Permission to consist of a minor amendment to the development
permitted under Monaghan County Council Planning Register
Reference 19/486 to revise the alignment of the permitted access
track between wind turbines T2 and T3. Significant further inform
Ammendment of below
Monaghan
County Council 19486 Drumlins Park Ltd.
Corlougharoe Correvan Drumlina Tullyard
Drumacreeve Drumanan Cornawall Drumgramph
Closdaw Killyleg Crossbane Lislongfield
Drumcrow Rakean Lismagonway Aghadrumkeen
and Newbliss Co. Monaghan. ,
Permission Granted with
Conditions 09/09/2020
A ten year permission for the development of 8 no. wind turbines,
each with a maximum tip height of up to 180 metres; and all
associated site development, reinstatement, temporary and ancillary
works including turbine foundations, crane hardstands, a
Wind Wind
An Commission
Pleanala ABP-309119-21 Drumlins Park Ltd.Drumanan and Cornawall, Newbliss, County
Monaghan Permission Granted with
Conditions 04/11/2021 110kV loop-in/loop-out substation including substation compound,
associated electrical plant and apparatus
Substation & Grid
Connection Windfarm - substation and undergroundRECEIVED: 28/08/2026
LPA PlanRef Applicant Address Decision Date Description Comments
Monaghan 19219
ABP-307617-20
Mr Paschal
Carvill
Tullycallick &
Rossarrell,
Glaslough, Co.
Monaghan
Granted 14/12/2020
permission for development of an on farm Anaerobic Digestion (AD) Plant, Combined Heat and Power (CHP) Plant, weighbridge, slurry
storage tank, slurry reception tank, gas flare, feed hopper, 3 no. silage clamps, electrical substation building, office building, perimeter
fencing, access and ancillary site works. Significant Further information relates to the submission of and Air & Noise Quality Assessment and
a Traffic and Transport Assessment report, a revised application form was submitted and the development description has been changed to
include a new waste water treatment plant.
MCC' Reason:
Unsuitable due to insufficient detail on scale, operations, grid connection, and landscaping—contrary to Policy ENP1; and inadequate info on nutrient runoff
and water impacts in a poor-status catchment—contrary to WPP1 and related policies.
ACP' Reason:
Having regard to national planning policy in respect of waste management and climate action, the location of the proposed development in a rural area, on
a site which is currently used for agricultural operations, the scale, siting and design of the proposed development, including the management and discharge
of surface water and digestate arising on site, it is considered that, subject to compliance with the conditions set out below, the proposed development
would not seriously injure the amenities of the area or of property in the vicinity, would not be prejudicial to public health or water quality, and would be
acceptable in terms of traffic safety and convenience. The proposed development would, therefore, be in accordance with the proper planning and
sustainable development of the area.
Cavan 16264
PL 02.248164 Andrew Fay
Lismagratty,
Cavan, Co.
Cavan
Refused 09/11/2017
For demolition of an existing derelict house. To construct an Anaerobic Digestion Facility comprising of 1 no. Reception Building, 2 no.
Digester Tanks, 4 no. Pre Storage Tanks, 2 no. Storage Tanks, Green Waste Storage, 1 no. Combined Heat and Power Unit, 1 no. Flare,
Biofilter, Office & Control room, Weighbridge, Wheel Wash Area, access road, parking spaces, and all associated site works and services. This
development requires a Waste Facility Permit under S.I. 821 of 2007 & S.I. 86 of 2008 in which application is also being made to Cavan
County Council. This development is also subject to a 3 stage validation process by the Department of Agriculture, Food and the Marine.
Significant further information has been received.
Cavan 10120 Biopower Ltd
Furnaceland,
Swanlinbar Refused 03/06/2010
develop a BioPark and its associated buildings; this BioPark will involve (a) new entrance, service road, carparking and associated site works,
(b) the construction of an Anaerobic Digestion Plant (20,000 t/a); the Anaerobic Digester and associated buildings is made up of a reception
building (30m x 24m - 12.5m to apex), a building (27m x 12.5m - 10m to apex) for the processing of compost digestate, two 13.2m radius
digestate storage tanks (6.28m high), two 10m radius digester tanks (6.28m high), two 7m radius reception tanks (3.24m high), one
control/boiler room (12m x 5m - 4.4m high), (c) an energy efficient site office (12.8m x 7.8m - 5.7m high) and a weighbridge will also be
constructed, (d) effluent treatment system and percolation area. The process of Anaerobic Digestion will require a Waste Licence. An EIS has
been submitted to the Planning Authority with the application
Unsuitable location in low agricultural area and inadequate EIS on water impacts; potential environmental harm, contrary to proper planning and
sustainable development.
Monaghan 03674
Silver Hill
Foods
Corlattallan,
Emyvale,
Co.Monaghan
Granted 22/10/2003
erect an effluent treatment plant and anaerobic digester plant consisting of a main processing and storage building , a chemical store and
polymer makeup building, 500 cubic metre effluent day tank, 100 cubic metre under ground anaerobic digester feed tank and ancillary
biogas handling facility , 100 cubic metre underground polymer mixing tank, process cooling tank, 145 cubic metre bunded digester
containment tank and permission to erect 1147 cubic metre balance tank and 517 cubic meter anoxic tank and ancillary site works
RECEIVED: 28/08/2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 1.2
ECONOMIC IMPACT ASSESSMENT
Stream BioEnergy Ireland Limited
AUGUST 2026 RECEIVED: 28/08/2026
Stream Bioenergy Monaghan
Renewable Biogas Plant
Policy, Business Community Alignment
and Economic Impact Assessment
November 2025
RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 2 - MC/GC, November 2025
Contents
1. Executive Summary .................................................................................................................. 3
2. Brief .......................................................................................................................................... 6
a. Summary of the Monaghan Biogas Plant Proposal ............................................................... 6
b. Comparison with Other Sources of Renewable Energy ........................................................ 7
3. Alignment with Policy............................................................................................................. 10
a. Monaghan County Development Plan 2025-2031 .............................................................. 10
b. Northern and Western Region ........................................................................................... 11
c. National Policy ................................................................................................................... 12
d. European Policy.................................................................................................................. 16
e. Food Industry Policy ........................................................................................................... 17
f. Other AD Plants and Exemplars ......................................................................................... 20
4. Regional Business and Project Partnership Potential ............................................................. 22
a. Food Chain Businesses ....................................................................................................... 22
b. Innovation Centres ............................................................................................................. 24
c. Road Transport, Industrial, Heating and Agricultural Fuel Transition ................................. 24
d. Sustainable Fertilisers and Soil Improvement .................................................................... 25
5. Economic Impact of the Monaghan Biogas Plant.................................................................... 27
a. Basis of Assessment ........................................................................................................... 27
b. Economic Baseline .............................................................................................................. 28
c. Baseline for the Monaghan Development Site ................................................................... 35
d. Construction ....................................................................................................................... 37
e. Operational ........................................................................................................................ 43
f. Total Economic Impact ....................................................................................................... 48
6. Positive Environmental and Social Impacts ............................................................................ 50
a. Circular Economy................................................................................................................ 50
b. Environmental Benefits for Agriculture and the Food Chain .............................................. 53
c. Positive Social Impacts for County Monaghan and the Borders ......................................... 54
7. Appendix ................................................................................................................................ 57
a. Waste Feedstock Baseline Use ........................................................................................... 57
b. Fertiliser Nutrient values .................................................................................................... 58
c. Broiler Litter Value ............................................................................................................. 58
d. Cattle Manure values ......................................................................................................... 59
e. Fertiliser values .................................................................................................................. 60
RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 3 - MC/GC, November 2025
1. Executive Summary
The Monaghan Renewable Biogas plant will use 99,000 tonnes of organic waste feedstocks
sourced from poultry and cattle farms, and food processing waste from the agri-food processing
industry in the surrounding area. The plant will use these waste streams to deliver multiple
products including biomethane for gas grid injection or sustainable transport fuels, sustainable
fertilisers for regional farmers, sustainable composts for the horticulture sector, and biogenic
CO₂, all of which have a use in the local, regional, and national economy.
The Plant directly supports one of the core aims of the Monaghan County Development Plan
2025-20311 of ‘To ensure the best use of the County’s resources to support the sustainable
development of infrastructure, amenities and economic investment in the area’ through the
transformation and valorisation of low value resources into valuable inputs for the local
economy and low carbon energy.
It will also support the development of the agri-food industry; Monaghan’s largest industry by
output and employment which is also Irelands ‘oldest and largest indigenous industry. In 2020,
the sector accounted for almost 7% of modified Gross National Income (GNI*) and 10% of exports
in value terms. It employs approximately 164,400 people, representing 7.1% of total
employment. At primary production level, some 137,500 farms, over 770,000 hectares of forest,
over 2,000 fishing vessels and some 180 aquaculture sites produced an estimated €8.5 billion in
output in 2019. The agri-food sector grew substantially over the past decade, with Irish food and
drink exports increasing from by 60% from €8.9 billion in 2010 to €14.2 billion in 2020.’2
The Monaghan Renewable Biogas plant is also able to provide wider benefits to the food chain,
Monaghan’s largest industry which provides most of its employment and output, with many
food plants, poultry, and cattle farms producing wastes which need treatment.
The development of the Monaghan Renewable Biogas plant is estimated to cost €120m of which
€35m is expected to be spent in County Monaghan and the north region; €45m throughout the
rest of the Republic of Ireland; and €40m spent on imported technology from abroad (including
Northern Ireland).
The construction process is expected to take 2 years and over this time the development will:
• Deliver a Gross Value Added (GVA) uplift per year of construction of €21.45m (2023 values),
of which €5.88m accrues to County Monaghan, rising to over €11m if the rest of the Border
region3 is included (€22m in total across the 2 years of construction).
• In total, at all spatial levels across the Republic of Ireland, the GVA uplift over the 2 years of
construction is expected to be €43m.
1 Written-Statement-Draft-Monaghan-County-Development-Plan-2025-2031.pdf
2 Food Vision 2030 – A World Leader in Sustainable Food Systems
3 NUTS-3 region, the Border, including Counties Donegal, Sligo, Leitrim, Cavan, and Monaghan. RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 4 - MC/GC, November 2025
• Including offsite jobs (e.g. aggregates, concrete, engineering etc.), this supports 58 net high
value jobs for 2 years in County Monaghan, with a further 42 jobs in the Border region and
72 jobs in the rest of Ireland, a total of 182 Irish jobs for 2 years.
Once operational the Biogas plant will create:
• 28 net jobs both directly on site and in the supply chain in Co. Monaghan and lead to an
annual growth in the economy worth €6.93m (2023 values).
• If the benefits for the rest of the Border region are included this positive impact rises to 54
net jobs and a GVA uplift of €13.57m.
• In total the plant’s operation will support 77 net jobs and €23.29m of GVA across the
Republic of Ireland.
The Biogas plant will also deliver social benefits to the local community:
• The biogas plant and the co-products produced will support high-quality long-term jobs in
County Monaghan, supporting growth of the sustainable green economy for the next 25
years+. This means that the plant can deliver lifetime careers for local people.
• The biogas plant is also important socially through helping to safeguard the future of County
Monaghan’s and the Border regions agri-food sector. Counties Monaghan and Cavan, the
traditional heart of the national poultry sector 4 face strong pressure to reduce pollution from
unprocessed poultry manure. The biogas plant will reduce this pressure, safeguarding the
primary production and processing of poultry throughout the wider region. Moreover, there
is pressure to decarbonise food production both from targets set by supermarkets and other
customers as well as government and EU policy. Food chain jobs, which are the majority of
employment within County Monaghan therefore depend on a transition to a circular
economy, move to renewable energy, development of sustainable fertilisers and access to
CO₂ for food processing.
Wider environmental benefits of the scheme include:
• The Biogas Plant will use food processing and agricultural wastes to create multiple higher
value products: biomethane for injection to the gas grid or transition to clean transport and
agricultural fuels; sustainable fertilisers; and food chain CO₂. These products:
o Displace the use of fossil fuels both directly e.g., biomethane as well as being a much
more sustainable way to produce fertilisers, which are currently an emissions hotspot for
the agricultural sector5.
4 Poultry Association - IBEC report that c.70% of the Irish poultry sector is within the Borders
5 Mitigating the impact of Irish grass-based systems - Teagasc | Agriculture and Food Development Authority RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 5 - MC/GC, November 2025
o Create the clean CO₂ needed by the large food processing cluster in County Monaghan
and the wider Border region6. The food chain needs a secure, sustainable source of high-
grade CO₂ as part of its journey to Net Zero and to protect the industry from shortages
and price surges, of up to 1,000% in recent years, which threatens the viability of food
processing. The plant is expected to provide 30% of current Irish industrial CO₂ demand.
• Anaerobic Digestion (AD) from waste uses a lot less farmland than alternatives such as solar
power or AD plants which use grown crops:
o Compared to the land area needed for the Monaghan Renewable Biogas Plant, a similar
energy output from a solar farm would require more than 20 times as much land and an
AD plant fuelled by maize would require an area over 295 times as large. If you lose a lot
more farmland this reduces the output of agriculture which can be processed, creating a
much larger impact on the wider economy and food chain.
o Compared to solar, which only produces intermittent electricity, biogas helps Ireland
deliver on the hard to decarbonise of sectors such as heating and HGV transport fuels
which electrification cannot easily resolve.
• Processing poultry and cattle manure, and agri-food organic waste to create a sustainable
fertiliser means:
o Farmers have access to sustainable fertilisers which means they, and the food chain they
supply, can meet the aspirations of the food chain to move towards Net Zero by 2050.
This will secure the future of Ireland’s large farming and food chain, which is its largest
indigenous industry.
o The sustainable fertiliser produced is also more stable than poultry or cattle manure,
meaning less of the nutrients are lost when applied to farmland. This means more of the
nutrients help the crops grow and less is lost through losses to the air or water
courses. This will also reduce emissions of methane, reducing both pollution and the
climate impact of fertilisers.
o The production of ammonium sulphate will also generate the first indigenous source of
non-organic fertiliser in more than 20 years. Helping to reduce the significant price
premium faced by Irish farmers for imported nitrogenous fertilisers.
6 NUTS-3 region the Border, includes Counties Donegal, Sligo, Leitrim, Cavan, and Monaghan. RECEIVED: 28/08/2026
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2. Brief
a. Summary of the Monaghan Renewable Biogas Plant Proposal
This report aims to provide:
• A strategic review of how the Monaghan Renewable Biogas Plant aligns with policy.
• An assessment of the economic and social impacts of the Biogas Plant development.
The Monaghan plant will be located on a 6.2-hectare site in Maghernakelly, Drum, County
Monaghan, 17.5 kilometres southwest of Monaghan Town. It is projected to generate up to
120 GWh of energy per annum, in the form of biomethane to inject into the national gas
grid.
Table 1 - Key Metrics for the Proposed Monaghan Renewable Biogas Plant7
Metric Estimated Value
Construction metrics:
Cost, of which: €120m
• Monaghan & Northern8 Region €35m
• Rest of Republic of Ireland €45m
• Outside of Ireland €40m
Period of construction 2 years
Construction jobs: 100 direct jobs+
140 indirect jobs
Floor area c.1ha (c.11,500m2)
Biogas Plant site area 6.2ha
Operational metrics:
Feedstock 99,000 tonnes
Outputs:
• Dried fertiliser/Pellets Up to 7,000 tonnes
• Fibre digestate Up to 60,000 tonnes
• Ammonium Sulphate Up to 9,000 tonnes
• Biogenic CO₂ Up to 15,000 tonnes
• Energy Up to 120 GWh / year
Jobs:
• Direct operational jobs 30
• Indirect jobs in supply chain (e.g. services, logistics) 75
Economics:
• Opex in Monaghan & Northern Region (exc. salaries) €3.5-4.5m/annum
• Opex in rest of Ireland €0.6-1.2m/annum
• Opex outside Ireland €0.6-1.2m/annum
Carbon savings: €13m/annum
• Carbon saving Up to 42,000
tCO₂eq/annum
7 Source: Stream Bioenergy
8 The ‘Northern’ region is coterminous with the (Nomenclature of territorial units for statistics) NUTS-3 region,
the ‘Border’ RECEIVED: 28/08/2026
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The plant will use 99,000 tonnes of locally sourced waste organic feedstocks. The current
indicative planned feedstock mix is outlined in Table 2.
Table 2 – Potential Feedstock Mix
Feedstock Type Potential Annual
Quantity (tonnes)
Source
Total Up to 99,000 Local Area
Poultry manure 80,000 – 99,000
tonnes
Material will be sourced from the significant
concentration of poultry farms in County
Monaghan and surrounding areas.
Cattle manure 2,000 – 10,000
tonnes
Material will be sourced from cattle farms in
the surrounding area.
Agri-food organic
waste
9,000 – 19,000
tonnes
This material will be sourced from food and
poultry processing plants in the surrounding
area.
Poultry and cattle manures will be sourced from farms in the surrounding region while other
locally sourced high energy agri-food organic wastes will be supplied by large scale local food
processors such as Carleton Cakes Bakery9, Lakeland Dairies10; Manor Farm11 and Silver Hill
Duck12.
Due to focusing on multiple waste streams the development can be considered a circular
economy project, with waste generating energy through the production of biomethane,
fertilisers, sustainable composts, digestate, and biogenic CO₂, all of which have a use in the
local and regional economy.
b. Comparison with Other Sources of Renewable Energy
The use of agricultural land to generate renewable energy is a contentious issue, with many
policymakers and commentators raising concerns about the impact of losing farmland and
the consequential impact on food security and the wider food and drink processing sector
and its support industries. As outlined in the Table 3, the proposed Monaghan Renewable
Biogas Plant is a much more efficient use of land for renewable energy generation than solar
farms or Anaerobic Digestion (AD) plants using purpose grown crops (table 3):
9 Carleton Cakes - Love the taste
10 Home | Lakeland Dairies
11 Manor Farm | Home of Irish Chicken
12 Silver Hill Duck RECEIVED: 28/08/2026
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• If solar is used instead a land use change more than 20 times greater is needed for the
same energy output. It should also be noted that the Monaghan Renewable Biogas
Plant will generate baseload biomethane capacity, whereas solar farms generate
intermittent supply, which is of lower value for Irish energy security. Solar power is also
seasonal with most supply during the summer when grid demand is the lowest13.
Table 3 – Comparison of Land Use Impact from Different Renewable Energy Plants
Site Details of output and farmland
needed
Intermittency Land Needed
per GWh
Monaghan
Renewable
Biogas Plant
The Monaghan Renewable Biogas
Plant will generate up to 120 GWh of
energy per annum, in the form of
biomethane which will be injected
into the national gas grid, from a 6.2-
hectare site. 100% of the feedstock is
waste.
24/7/365 supply
to national gas
grid, with ability
to store gas to
meet peak
demand
0.052ha
Gallanstown
Solar Farm in
Co. Meath14
198MWp solar farm across 500 acres
(c.200Ha) at Balleymacarney Co.
Meath, where specific photovoltaic
power output15 is 966.8MWH/MWp.
Intermittent
supply, with
major diurnal
and seasonal
variation
1.045ha
AD plants
using maize
(multiple
sites already
operating)
Fresh maize has an estimated biogas
output of 155m³/tonne16, at 30% dry
matter, with methane content of 50-
80% (65% on average). As such fresh
maize yields c.101m³ of biomethane.
‘Each cubic metre of methane will
equate to 10.0 kWh of energy’17.
Consequently, maize grown for AD
generates c.1MWht¯¹ of biomethane.
The 120 GWh of proposed Monaghan
Biomethane output would require
c.119,100 tonnes of fresh maize (30%
24/7/365
supply, which
can be used for
direct gas grid
injection or
power (then
only 50%
efficient unless
waste heat is
used)
15.27ha
13 Electricity
14 20 of the Biggest Solar Farm projects in Ireland - Energy Efficiency
15 Global Solar Atlas
16 Anaerobic Digestion - Teagasc | Agriculture and Food Development Authority
17 Farm Advisory Service (Scotland) | 2023 | Anaerobic Digestion (AD) – Farm Scale | Technical Note TN698 RECEIVED: 28/08/2026
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Site Details of output and farmland
needed
Intermittency Land Needed
per GWh
DM). At a yield of 19.5tDM/ha18,19,
this requires c.1,830 hectares of crop.
• Were the Monaghan plant to be dependent on energy crops, such as maize, instead of
using manures, an even larger area of farmland would be impacted, with more than 295
times as much land needed per GWh produced. It should also be noted that the area of
maize needed to fuel the Monaghan plant would be equivalent to more than 11% of the
16,200 hectares of maize grown in the Republic of Ireland on average between 2019 and
202320.
18 https://assets.gov.ie/215129/8fd0f544-fe5b-4728-a0e2-
26a35cd391e6.pdf#:~:text=The%20Recommended%20List%20shows%20the%20average%20dry%20matter,av
erage%20of%20the%20control%20varieties%20set%20at%20100.
19 This yield of 19.5 tonne of dry matter per hectare, or 65 tonne fresh, from the recommended list is 30%
better than the 50t/ha yield described by Agriland as achievable with good agronomic management. See
Forage maize - yields of 50t/ha achievable - Agriland.ie
20 AQA06 - Area Farmed in June RECEIVED: 28/08/2026
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3. Alignment with Policy
a. Monaghan County Development Plan 2025-2031
The Monaghan County Development Plan21 (2025-2031) was adopted on 26th May 2025 and
came into effect from 7th July 2025. The plan lays out how Monaghan can sustainably
develop over the next 6 years and has 7 main aims. Of these the proposed biogas plant
supports the following:
• ‘To provide for and support strong and sustainable development over the lifetime of the
Plan.
• To approach the overall development of the County in an inclusive and integrated way to
make sure all aspects of development occur in a consistent manner.
• To ensure the best use of the County’s resources to support the sustainable development
of infrastructure, amenities and economic investment in the area.
• To achieve a dynamic and vibrant living and working environment for the County’s
population by making the most of economic, social and physical development for the
benefit of communities and visitors alike.’
Regarding waste management the county development plan also notes that ‘Ireland is
moving away from the traditional linear ‘take-make-use-dispose’ model towards a circular
economy regenerative growth model where resources are reused or recycled as much as
possible, and the generation of waste is minimised. The transition to a circular economy is
essential to reduce pressure on natural resources, aid in achieving climate targets, support
Sustainable Development Goals and create sustainable growth and jobs. A circular economy
will support viable and sustainable enterprise opportunities, jobs and training, using the tools
of the modern economy in a new way, harnessing the potential of renewable energy, design
and the digital economy to create and recreate value.’
The Monaghan Renewable Biogas Plant directly supports this objective by transforming
organic wastes and by-products into higher value products and bioenergy, enabling the
industries from which the wastes originated to decarbonise and increase their value.
The plan also notes that ‘Monaghan County Council acknowledges the potential of bioenergy
to realise several objectives contained in this Development Plan in the areas of energy supply
and energy security, climate change, environmental quality and pollution and economic
development and rural development. In this context Monaghan County Council will promote
and support its development’ demonstrating the underlying policy support for the Monaghan
Renewable Biogas Plant.
21 Written-Statement-Draft-Monaghan-County-Development-Plan-2025-2031.pdf RECEIVED: 28/08/2026
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b. Northern and Western Region
The Northern and Western Region Regional Spatial and Economic Strategy 2020-2032
(RSES)22 states that the ‘regional economy has long-standing strengths in agri-food, life-
sciences, RTDI, engineering, retail, manufacturing, service sector, energy, creative sector,
tourism, marine and many more’.
The strategy also notes the strength of agri-food in County Monaghan, reporting that ‘The
Agri-Food sector is vital to the region and particularly to Counties Monaghan and Cavan. For
example, the agri-food industry alone accounts for over 60% of Monaghan’s employment and
90% of the food produced within the county is exported.’ The plant is therefore located in a
region with one of the densest concentrations of suitable waste feedstocks, and where the
outputs produced, e.g., biogenic CO₂; sustainable fertilisers; and bioenergy will be of most
use for the decarbonisation of this sector.
The RSES has a range of regional policy objectives on renewable energy, including the
following relevant to the Monaghan Renewable Biogas Plant development:
• RPO 4.17: ‘To position the region to avail of the emerging global market in renewable
energy by:
o Stimulating the development and deployment of the most advantageous renewable
energy systems.
o Raising awareness and public understanding of renewable energy and encourage
market opportunities for the renewable energy industry to promote the development
and growth of renewable energy businesses.
o Encourage the development of the transmission and distribution grids to facilitate
the development of renewable energy projects and the effective utilisation of the
energy generated from renewable sources having regard to the future potential of
the region over the lifetime of the Strategy and beyond.’
• RPO 4.18: ‘Support the development of secure, reliable and safe supplies of renewable
energy, to maximise their value, maintain the inward investment, support indigenous
industry and create jobs.’
• RPO 4.20: ‘Support and encourage the development of the bio-economy sector, and
facilitate its development for energy production, heat, and storage distribution, in
particular advocating Combined Heat and Power Units integrated into District Heating
networks, in combination with Pyrogenic Carbon Capture and Storage (PyCCS) or Bio-
Energy Carbon capture and storage (BECCS) all to be done in collaboration with EPA and
other regulators.’
22 REGIONAL SPATIAL AND ECONOMIC STRATEGY 2020-2032 RECEIVED: 28/08/2026
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The strategy includes three regional policy objectives related to the bioeconomy (page 173),
including:
• RPO 4.27: ‘It is an objective to support the National Policy Statement on the Bioeconomy
(2018), and the exploration of opportunities in the circular resource-efficient economy,
including undertaking a bioeconomy feasibility study for this region. This feasibility st udy
will aim to identify (and map) areas of potential growth to inform the National Transition
Agenda, enabling a Low Carbon, resilient nation.’
• RPO 4.28 ‘To support the potential creation of appropriately scaled local multi -feedstock
bio-refining hubs across the region as well as potential creation of bio -districts/clusters.’
• RPO 4.29 ‘The Assembly supports the future-proofing of infrastructure planning to allow
for the potential upgrading of existing industrial sites to bio -refining plants while also
supporting the use of bio-renewable energy for the sustainable production of bio-based
products.’
Both RPO 4.28 and 4.29 directly support the development of the proposed Monaghan
Renewable Biogas Plant which will act as an appropriately scaled biorefining hub, taking
wastes from the local agri-food clusters to produce renewable energy and biobased
products.
Other relevant RPOs include RPO 8.7: ‘Encourage and support innovative partnerships
extending the gas network in the region, including the potential for gas to grid injection
facilities along with anaerobic digestion facilities’, with the biogas plant directly delivering on
this policy objective.
c. National Policy
Ag Climatise
Nationally the focus on biomethane production, as well as sustainable fertilisers and CO₂
aligns with a range of government policies including the Ag Climatise, Roadmap Towards
Climate Neutrality23. This roadmap includes 2 actions which the Monaghan Renewable
Biogas Plant proposal respond to and are endorsed by addressing actions including:
• ‘Action 1: Reduce chemical nitrogen use to an absolute maximum of 325,000 tonnes
(annually) by 2030, with an interim target of 350,000 tonnes by 2025. Support the use of
non-chemical nutrients such as bio-based fertilisers and soil conditioners through greater
visibility of the fertiliser marketing regulations.’ Which the production of bio-based
fertilisers will directly support.
23 Ag Climatise - A Roadmap towards Climate Neutrality RECEIVED: 28/08/2026
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• ‘Action 20: Engage with stakeholders to maximise the potential opportunities from
Anaerobic Digestion for the agriculture sector, by:
o Work closely with DCCAE and other key stakeholders to set a target for the level of
energy to be supplied by indigenous biomethane injection and consider the necessary
supports including funding mechanisms.
o Work with DCCAE and other stakeholders to develop the necessary research, policies
and measures to provide policy certainty around the development of an Anaerobic
Digestion industry in Ireland. Work in partnership with co -operatives, farmers and
representative bodies to develop governance structures and business models to
ensure that the maximum benefit through Anaerobic Digestion is realised while also
contributing significantly to the decarbonisation of Ireland’s agriculture system.’
The Monaghan Renewable Biogas Plant proposal addresses these objectives by valorising
agri-food wastes in a region where these are low value. It turns these ‘wastes’ into products
of higher value, while producing biomethane for decarbonisation that will significantly
contribute to the decarbonisation of Ireland’s agriculture system.
National Waste Management Plan for a Circular Economy
The National Waste Management Plan for a Circular Economy 2024-203024 reports
Infrastructure constraints as its fifth key challenge to be resolved to foster the circular
economy. This notes in its chapter on infrastructure constraints that there is only ‘Circa
687,560 tonnes composting and anaerobic digestion capacity available within the State.’ This
means the proposal could increase the available infrastructure nationally for AD by one
seventh.
National Biomethane Strategy
The National Biomethane Strategy25 also states that ‘Government is committed to supporting
delivery of up to 5.7TWh of indigenously produced biomethane by 2030. A first key step to
delivering on this ambitious target is the publication of the National Biomethane Strategy.’
The strategy also noting that ‘Biogenic CO₂ is likely to be in high demand in Ireland as several
projects in Ireland and Europe assess the production of future fuels such as green methanol
and Sustainable Aviation Fuels (SAF), both of which will require significant volumes of
biogenic CO₂. Due to the abundance of offshore wind in Ireland, there is a vast potential for
developers of these fuels to assess projects in Ireland.’ The focus on both biomethane and
biogenic CO₂ therefore directly supports these policy objectives.
Agriculture is also important for emissions reduction in Ireland. Currently, approximately
37% of Irish emissions relate to the agricultural sector, of which 65% are estimated as being
24 National-Waste-Management-Plan-for-a-Circular-Economy-Volume-I-Current-Situation-and-Challenges.pdf
25 National Biomethane Strategy RECEIVED: 28/08/2026
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from methane (CH4) and 30% from nitrous oxide (N2O). Against the baseline year of 2018,
Ireland is committed to net zero agriculture by 2050 in line with the economy, with the
ambition to achieve a ‘22-30% - target reduction in agricultural emissions by 2030’26.
Food Vision 2030
This agricultural emissions reduction target is included in the sector wide Food Vision 2030 A
World Leader in Sustainable Food Systems strategy27. The Food Vision 2030 strategy has four
key missions which include a range of 22 sub goals with detailed actions to enable the Irish
agri-food industry to respond to the current megatrends and grow sustainably.
The Monaghan Renewable Biogas Plant responds directly to several of the overarching
mission statements and goals of Food Vision 2030.
‘MISSION 1 A Climate Smart, Environmentally Sustainable Agri -Food Sector:
GOAL 1: Develop a Climate Neutral Food System by 2050 and Improve Air Quality
• ‘ACTION 7 Scale up renewable energy (RE) sources, especially anaerobic digestion,’
• ‘ACTION 8 The food and beverage industry will continue to drive down GHG emissions
and develop zero waste approaches.’
The biogas plant will scale up anaerobic digestion production in Ireland; will process agri-
food wastes into higher value outputs supporting a zero-waste food chain; and the CO₂ will
be captured and recycled for the food processing industry. The plant will:
• Reduce emissions from the disposal of agri-food wastes;
• Produce renewable biomethane for bioenergy (which as noted in section 4.C have the
potential to decarbonise agricultural machinery);
• Produce sustainable fertilisers from poultry and cattle manure, decreasing N₂O
emissions associated with these unprocessed organic fertilisers, while also displacing
synthetic fertilisers and their associated manufacturing and use emissions.
GOAL 3: Protect High Status Sites and Contribute to Protection & Restoration of Good Water
Quality and Healthy Aquatic Ecosystems
• ‘ACTION 1 To protect waters from agricultural pollution, transition the agricultural
sector to a lower chemical nitrogen use system, and urgently in regions with identified
water quality problems, particularly from diffuse losses of nitrogen.’
• ACTION 2 To further protect waters, including surface waters, from agricultural, forestry
and urban/industry pollution (including microbiological pollution), land use activities
26 Understanding greenhouse gas emissions on Farms - Teagasc | Agriculture and Food Development Authority
27 Food Vision 2030 – A World Leader in Sustainable Food Systems RECEIVED: 28/08/2026
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need to manage and mitigate the losses of nitrogen, phosphorous and sediment to
water. Key elements in the realisation of this action include:
o c. Recover more nitrogen and phosphorus from livestock manures
The recovery of nitrogen and phosphorous from raw livestock manures will reduce the losses
of these nutrients to water courses. Moreover, the treatment of poultry and cattle manure
will reduce the microbial pollution of soils which is associated with the use of untreated
manures as organic fertilisers, reducing the risk of disease transmission to livestock. The
production of more stable biobased fertilisers will enable lower chemical nitrogen use
among both the grassland and tillage agricultural sectors.
• GOAL 6: Embed the Agri-Food Sector in the Circular, Regenerative Bioeconomy
o ACTION 2 Scale up resource-efficient, circular and low carbon solutions based on
principles of renewable energy, cascading and circular use of sustainable
biological resources. Examine biorefining, anaerobic digestion and other
technologies, including bioenergy, which can convert low-value material to
higher-value material and provide for treatment of waste, protection of the
environment, and the production of chemical building blocks, fuels, power and
heating (see also Goal 1). Cross-sector collaboration and investment, nationally
and internationally, should be pursued for the development of circular and
climate-neutral industries.
The biogas plant will embed the sector into a circular regenerative bioeconomy with
cascading uses of biogenic carbon and nutrients. Agri-food wastes from the primary
production of poultry and cattle products and processing of food stuffs will be used to
produce biomethane which will support the decarbonisation of the industry. Sustainable
fertilisers produced in the plant will support the primary production of both poultry and
cattle through their application to both feed crops and pasture. The biogenic CO₂ generated
in the process will be captured and provided to the food processing industry for abattoirs,
meat processing, and modified packaging.
MISSION 2 Viable & Resilient Primary Producers with Enhanced Wellbeing
• GOAL 1: Improve the Competitiveness and Productivity of Primary Producers
o ACTION 14 Under the auspices of the 2030 process, produce a detailed plan by
Q2 2022 to manage the sustainable environmental footprint of the dairy sector,
including minimising total emissions, while making a positive contribution to
improved water quality and biodiversity, in line with government policy. Further
details are included in Mission 1, Goal 1
o ACTION 22 Address specific environmental targets and actions for the sector,
encompassing GHG emissions reductions, including ammonia, and better energy RECEIVED: 28/08/2026
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efficiency, including renewables. Explore bioeconomy opportunities e.g. for the
use of pig manure
The upvaluing of wastes will also improve the competitiveness of primary producers in
Ireland’s agricultural sector, and the delivery of indigenous supplies of fertiliser and CO₂
which do not currently exist in Ireland, will improve sector resilience. Biogenic CO₂ for food
processing can also support the food industry to humanely slaughter livestock, and to modify
packaging for fresh produce. Improving the safety, and ethical nature of the agri-food supply
chain.
The strategy therefore notes that ‘The other strands of policy to achieve the sector’s climate
neutrality objective are measures to increase its role in carbon sequestration, especially
through forestry, and the scale-up of renewable energy sources, through anaerobic digestion,
solar energy and greater energy efficiency’.
The production of biobased sustainable fertilisers with superior use characteristics to
synthetic fertilisers will also support Irish agriculture to adapt to the changes to fertiliser use
regulations which have been introduced in 202528 with the Amendment to the Good
Agricultural Practices for the Protection of Water Regulations which will ban the use of
unprotected granulated Urea from September 2025.
d. European Policy
The EU, like Ireland, has written into law a climate neutrality target of 2050; as well as a
target of 55% emission reductions by 2030, compared to a 1990 baseline. In 2024 the
Commission published an additional intermediate target of 90% emissions reduction by
204029, in the Green Deal. The Renewable Energy Directive has set a legally binding target of
42% renewable energy generation across Europe by 203030.
Consequently, the EU is supportive of AD from waste projects to help achieve its climate
goals, as well as a wider range of policy objectives designed to support peace, and security in
Europe. RePower EU31 launched in 2022 aims to reduce EU dependence on Russian fossil
fuels to zero by 2027 and has already achieved a reduction in dependence on Russian natural
gas from 45% in 2021 to 19% in 2024, primarily by diversifying import sourcing and efficiency
driven demand reduction.
To achieve further reductions, the plan notes that ‘boosting sustainable biomethane
production to 35 bcm [circa 342TWh] by 2030 is a cost-efficient path to achieve our ambition
28 Technical note - Amendment to the Good Agricultural Practices for the Protection of Water Regulations
29 The European Green Deal
30 Renewable Energy Directive
31 REPowerEU RECEIVED: 28/08/2026
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to reduce imports of natural gas from Russia.’ This aim is equivalent to 3,420 plants of
equivalent scale to the proposed Monaghan plant to be completed across the EU by 2030.
The commission also notes that since 2024 under the Waste Framework Directive32, member
states must collect organic wastes separately, thereby supporting the availability of suitable
feedstocks for biogas production. Moreover, the accompanying working document33 on
RePower EU notes that the food and drink sector is the third largest industry user of natural
gas currently within Europe. As such, the generation of biomethane is essential for the
decarbonisation of this sector.
The accompanying Biomethane Fiche Ireland (2021)34 also reports that ‘About 4% (~15.8
bcm) of the total natural gas supply in EU was used for non -energy purposes, dominantly for
synthesizing nitrogen-based fertilizers, in addition to the energy input needed to support the
production process. Combining biomethane production with a strong support of using
digestate as a local source of nutrients would have multiple benefits for the reduction of
natural gas imports.’
e. Food Industry Policy
The Ibec Poultry Group, the sector group for Irish poultry in Food Drink Ireland35, published
in 2023 a Poultry Sustainability Roadmap 203036. This roadmap states that the sector
delivered around €700 million in output in 2022 and supports over 5,000 jobs. With ‘The
poultry sector (poultry meat & eggs) ha[ving] a multiplier effect of 1.8 which means that
every €10 million increase in the value of domestic output results in €18 million of additional
output in the wider economy.’
This roadmap lays out how the Irish poultry industry can respond to the strong demand
growth for poultry in Ireland and achieve sustainability improvements in line with national
policy and consumer demand. The sector is noted as the EU leader on sustainability already
as ‘The results of JRC analysis showed that Ireland had the lowest emissions intensity across
the EU at 3.3kgCO₂e per kg of poultry meat, a third lower than the EU average’.
However, despite this carbon advantage poultry meat imports have averaged 130,000
tonnes per year in recent years, representing a lost opportunity for growth of the domestic
sector, as consumer demand for poultry rises and is now 45% of total meat demand.
The report therefore sets out several challenges and opportunities for the sector which could
improve its economic competitiveness and enable it to grow further and displace more
carbon intensive imports. One of its priorities to 2030 is manure management, noting that
32 EUR-Lex - 02008L0098-20180705 - EN - EUR-Lex
33 eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:52022SC0230&from=EN
34 Circabc
35 Food Drink Ireland - IBEC
36 Poultry Association - IBEC RECEIVED: 28/08/2026
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‘There is real potential to turn litter from a product that costs more than €20 per tonne for
disposal to a situation where it delivers value to the sector by creating a circular economy
loop. There are a number of potential uses for poultry litter that the industry is committed to
exploring with relevant stakeholders. These include:
• The Climate Action Plan calls out the ambition to have 20037 AD plants of scale
operating in Ireland by 2030. Poultry litter could provide a valuable feedstock for such
plants to produce renewable energy while also producing a nutrient rich digestate for
land spreading.
• The nutrient rich nature of poultry litter makes it a potentially valuable organic fertiliser
for gardening. This would involve the litter being dried, sterilised and pelletised. There is
currently no infrastructure in Ireland to enable this development.’
On Ammonia, the roadmap states ‘Notwithstanding the decline recorded in 2020, the poultry
sector recognises the fact that ammonia emissions remain a challenge at a national level
[and] The potential for poultry litter to reduce the need for chemical fertilisers, which would
reduce overall ammonia emissions needs to be recognised.’
While further reporting on the processing end of the supply chain that:
‘Enabling the decarbonisation of poultry processing
There are a number of structural enablers required to incentivise the delivery of a
decarbonised processing sector. These include:
• Clearer framework to encourage the adoption of technologies such as Anaerobic
Digestion and biochar with incentives in place to deliver a co-ordinated infrastructure.
• Streamlined planning processes for wind, solar and anaerobic digestion.’
These challenges and priorities for sustainable growth of the poultry industry strongly align
with the proposed biogas plant, as the processing of poultry manure, currently a cost to the
industry, offers the potential to decrease sector costs and enable growth at the same time as
improving sustainability. The processing of this manure into higher value low emission
fertilisers will help to reduce ammonia emissions and the CO₂e equivalence of these
emissions.
The Food and Drink Manufacturing Report 2025, Appetite for Growth 38 reports that the Irish
agrifood sector is broadly positive about the future ‘with 58% of respondents rating the
manufacturing environment in Ireland as good or very good.’
37 N.B. since the publishing of the IBEC Poultry Roadmap, the Climate Action Plan 2023 has been updated with
the Climate Action Plan 2025 now stating in its Climate_Action_Plan_2025_-_Annex_of_Actions.pdf on page
50, ‘2025 KPI: -Production of 1 TWh of Biomethane by 2025 - Construction of up to 20 AD Plants of Scale’. This
change reflecting government acknowledgement that plants of scale, such as the Monaghan Renewable Biogas
Plant are necessary to meet national climate objectives.
38 Food Drink Ireland Manufacturing report - IBEC RECEIVED: 28/08/2026
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This report also sets out priorities for the programme for government including to ‘Reduce
Ireland’s high electricity costs by accelerating the roll -out of low-cost renewable generation
and storage technologies.’ As well as to ‘protect companies from rising costs’. Two key aims
which the biogas plant will help deliver through the generation of up to 120 GWh of
renewable energy, and up to 15,000 tonnes of domestically produced food grade CO₂
protecting the Irish agrifood industry from CO₂ price shocks. RECEIVED: 28/08/2026
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f. Other AD Plants and Exemplars
The National Waste Management Plan for a Circular Economy 2024-2030 notes that there
already exists: ‘Circa 687,560 tonnes composting and anaerobic digestion capacity available
within the State.’ While the 2024 biomethane strategy39 reported that: ‘According to the
European Biogas Association, there are also 43 facilities in Ireland producing 580 GWh of
biogas, in addition to the two biomethane facilities. This biogas is used in electricity
generation and is not upgraded to biomethane.’ As such the Stream Bioenergy proposals for
Monaghan are not unique within the Republic.
Map 1 - European Biogas Associations Biomethane Plant Map (2023)40
39 National Biomethane Strategy
40 GIE_EBA_BIO_2023_A0_FULL_202 RECEIVED: 28/08/2026
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Stream Bioenergy also already operates the successful 50,000 tonnes per annum Tully
anaerobic digestion plant at Ballymena41 in Northern Ireland which is run on up to 100%
chicken litter feedstock producing biogas and bio-fertilisers. Planning approved for a further
200,000 tonnes capacity expansion to Tully has been received and construction will begin in
2026. The proposed Monaghan plant will be a similar type of plant to Tully replicating an
already successful exemplar in a neighbouring region of the Island of Ireland.
The proposals are, however, more novel in the focus on the production of biomethane, with
the 2023 European Biogas Associations Biomethane (Map 1) identifying just 2 existing
biomethane plants in the Republic of Ireland, and just three in total across the Island of
Ireland.
Given that the same mapping42 reported a total of 1,322 biomethane-producing facilities in
April 2023 across Europe, the existence of just two plants within the Republic of Ireland
represents a significant underdevelopment of this key renewable infrastructure within the
country, which the proposal seeks to redress.
41IEA_Tully-biogas-Case-Story_end.pdf
42 Biomethane Map 2022-2023 | European Biogas Association RECEIVED: 28/08/2026
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4. Regional Business and Project Partnership Potential
The development of the Monaghan Renewable Biogas Plant can provide opportunities for
collaboration and partnership with other businesses and agri-food sector focused projects across
County Monaghan, the Border region, and the Republic of Ireland. Nationally the agri-food
‘sector is Ireland’s most important indigenous industry, with a turnover of almost €30 billion and
exports of over €16 billion.’43 Consequently it is essential, especially for rural development, to
support innovation and the improvement of competitiveness and efficiency within this keystone
industry.
a. Food Chain Businesses
Monaghan and the Northern and Western Region of Ireland is a predominantly rural area
with a strong production base in agriculture, which underpins the food and drink processing
sector as the key private sector and employment provider in the local economy. As already
noted, the North West RSES44 notes that ‘the agri-food industry alone accounts for over 60%
of Monaghan’s employment and 90% of the food produced within the county is exported.’
The Irish Farmers Association 2020 factsheet45 on Monaghan’s agriculture reported that
5,304 people were employed on the county’s farms across 4,544 farms with total farm area
of 103,511 Ha. This generates €341 million of agricultural output; and supporting €499
million of agri-food export value, with 2,400 jobs in food and drink processing within the
county in 2016. If the wider Borders region is included, this figure rises to more than 8,200.
Within Monaghan there are several significant and established food businesses which could
enjoy synergies with the proposed plant across a range of agri-food sub sectors.
Monaghan has a strong meat processing, and prepared meat sector. Key companies include
McCaughey Foods at Castleblaney46 who operate 2 facilities employing 130 staff producing a
range of prepared meat items; and which are currently investing 150 million euros in a new
facility at Castleblaney with ambition to generate 300 new jobs47. DMC Foods located at
Lough Egish Food Park, are Ireland’s leading ready meal manufacturer, with almost 1 in 5
ready meals in Ireland produced at their facility which employs more than 200 staff 48. Arthur
Mallons Foods49 trading as Mallons Sausages employs over 170 staff producing sausages and
pork products at Hilden, Monaghan, in a new facility finished in 2024.
43 Overview - IBEC
44 REGIONAL SPATIAL AND ECONOMIC STRATEGY 2020-2032
45 Monaghan.pdf
46 Home - McCaughey Foods
47 Brand-new €150 million McCaughey Foods production facility - Wastewater
48 DMC Foods - Home of Fit Foods
49 Mallon's Sausages – The site for everything Mallon's RECEIVED: 28/08/2026
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The county also has strong poultry clusters related to both meat and egg processing. Key
poultry meat producers include Silver Hill Ducks at Emyvale who are a vertically integrated
producer and processor of ducks, now producing more than 82,500 ducks per week50. Grove
Farm Turkeys51 is a producer of a range of turkey products and is ultimately a subsidiary of
the Boparan family office (the owner of 2 Sisters Food Group).
Rangeland Food Ltd at Lough Egish food park are a leading producer of quick service beef
burgers for the food service industry52.
Monaghan is also home to Ireland’s leading egg cluster, with Greenfield Foods53 based at
Smithboro employing circa 100 staff, with over 1.4 million birds on 74 local family-owned
farms, producing, packing and distributing 7 million eggs per week for the Irish market.
Golden Irish at Castleblaney employ 30 staff 54 producing a range of free-range eggs, in
partnership with farms across Monaghan, Cavan, Meath, and Louth 55.
Manor Farm’s chicken hatchery which supplies their farming partners across Monaghan, and
Cavan with poults56 is also located in County Monaghan.
Monaghan Mushrooms57 headquartered at Tyholland is a leading internationally operating
producer of mushrooms employing more than 3,000 staff. Monaghan Mushrooms also have
their own internal innovation arm, MBio, with which they have innovated a process of UV
lighting to produce vitamin D enriched mushrooms.
Bio Marine Ingredients Ireland58 located on the Lough Egish Food Park produce a range of
products including bio-fertilisers, aquaculture feeds, and pet and human nutrition solutions.
The wider Borders region is home to c.70%59 of Ireland’s poultry sector with around 3,500
jobs supported within the region by the sector, or approximately 2% of all jobs within the
region, primarily concentrated within Counties Monaghan and Cavan.
Abbott60 also produce a range of nutrition products, including for infants, located to the
north of Cootehill. The proposed biogas plant is therefore located in the heart of Ireland’s
agri-food sector, maximising the economic, sustainability, and social synergies which it will
provide.
50 Home - Silver Hill Duck
51 Leading manufacturers of quality poultry products | Grove Farm
52 Welcome | Rangelandfoods - Rangelandfoods
53 Home - Greenfield Foods Corporate Site
54 Golden Irish Eggs – Love Irish Food
55 Golden Irish Eggs. Free range, organic 100% Irish eggs.
56 Manor Farm | Home of Irish Chicken
57 Monaghan Mushrooms - A Natural Future
58 Home | Bio-marine Ingredients Ireland
59 Poultry Association - IBEC
60 Abbott In Ireland | Nutrition: Cootehill RECEIVED: 28/08/2026
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b. Innovation C entres
The Border region has a strong agri-food industry with nationally significant innovation
infrastructure within the sector. This includes the BioConnect project, a government
supported development project and innovation centre in Monaghan:
• ‘The BioConnect Project is anchored by a unique 1,639 square metre research and
development Innovation Centre located at Knockaconny in Monaghan – the beating
heart of Ireland’s agri-food industry…..With space for over 80 people the building is at
the heart of a major drive designed to support food and agri companies develop new
projects, whilst offering a creative environment for entrepreneurs, startup projects and
inward investing businesses and organisations.’ 61
Alongside these government supported initiatives, companies such as Monaghan
Mushrooms Group are also active in innovation, with the group having their own MBio62
innovation subsidiary. MBio is actively innovating to improve the nutritional quality of
Monaghan Mushrooms products, while also as a member of Origin Green working to
improve the sustainability of their production.
The proposed biogas plant will generate high quality biogenic CO₂; biomethane; and a range
of sustainable fertilisers including fibre digestate suitable for processing into compost is
therefore a natural addition to this existing ecosystem. A range of synergies can be created
for the innovation cluster, the biogas plant, and the regional agri-food sector through
collaboration to benefit the whole industry.
c. Road Transport, Industrial, Heating and Agricultural Fuel Transition
The biomethane strategy reports that the current production of biomethane in the Republic
is c. 75 GWh per annum, with most of this fuel used in the transport sector under the
renewable transport fuel obligation with c. 100 Irish heavy-duty vehicles capable of running
on this fuel. The Monaghan plant is capable of producing up to 120 GWh per annum, and if
used for this purpose could more than double the availability of biomethane for road fuel
use.
The recent consultation on the RTFO63 however noted that ‘Concerning biomethane, the
plans by Government to introduce a renewable heating obligation to incentivise renewable
gas into the heating sector are supported by analysis (SEAI Heating Study 2022) suggesting a
priority use of biomethane in heating rather than transport.’ This suggests a vision to use
biomethane to decarbonise the heating of homes, primarily in rural areas, where
alternatives are heavily constrained by electrical grid capacity and upgrade costs.
61 The BioConnect Project — BioConnect
62 mBio - Superfood ingredients from a single natural source, the mushroom
63 renewable-transport-fuel-policy-consultation-paper.pdf RECEIVED: 28/08/2026
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The Commission for Regulation of Utilities reported64 that in 2023 the typical natural gas
consumption value was 11,000 kWh (11 MWh). Consequently, the potential 120 GWh
(120,000 MWh) of biomethane which will be produced by the proposed plant, could provide
heating decarbonisation for up to 11,000 homes in Ireland.
Alternatively, biomethane could be used directly by the agricultural industry which as
already reported is responsible for 37% of Irish GHG emissions. Biomethane could be used
to fuel tractors, with New Holland producing the only production series 100% compressed
methane powered tractor at Basildon65 in Essex, UK, using a Fiat powertrain gas engine. The
T6.180 methane powertrain was developed with on farm trials and has, since 2022, offered
the potential for a fully closed fuel cycle on farms, utilising energy generated from capped
slurry pits, or anaerobic digestors run on farm wastes, or energy crops66.
In addition to the potential CO₂ savings from using biogenic methane; New Holland67 also
claim that ‘98% less particulate matter is produced when compared to European Stage V
emission limits’; and for farmers the ‘Same power, torque and durability as its diesel
counterpart, but with an estimated 30% reduction in running costs’.
Following the T6, New Holland developed the T7 liquid natural gas methane power tractor to
utilise LNG biomethane, with this tractor unveiled at the 2023 Agritechnica show68 as a
production prototype manufactured in Basildon, New Holland’s alternative fuels centre of
excellence.
d. Sustainable Fertilisers and Soil Improvement
The Monaghan Renewable Biogas Plant will produce large quantities of low carbon,
sustainable fertilisers for use on farms. It has been known for over a decade that in crops
such as cereals, circa 70%69 of the carbon footprint is from fertiliser’s manufacturing and N₂O
emissions. With Irish agriculture responsible for almost 40% of Ireland’s current emissions,
and N₂O primarily from chemical fertiliser use estimated as 25%70 of these emissions the
transition to more sustainable practices and fertilisers is essential to enable Net Zero in
agriculture.
Sustainable fertilisers with a higher carbon content and less volatile ammonia offer the
potential to improve soils across the Irish tillage sector by increasing soil organic carbon
matter. They also provide more steady release of nitrogen and other crop nutrients to crops
64 Typical gas consumption value 2023 - Commission for Regulation of Utilities
65 New Holland T6.180 methane tractor soon to be available - Future Farming
66 T6 Methane Tractor | New Holland UK
67 T6 Methane Tractor | New Holland UK
68 T7 Methane Power LNG pre-production prototype will take the stage on New Holland’s stand at Agritechnica
2023 | New Holland UK
69 PowerPoint Presentation
70 Reducing chemical fertiliser use for improved sustainability in agriculture | UCD Research RECEIVED: 28/08/2026
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as they grow, improving nutrient use efficiency and decreasing watercourse pollution, while
having lower N₂O emissions than those of conventional synthetic fertilisers.
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5. Economic Impact of the Monaghan Renewable Biogas Plant
a. Basis of Assessment
The Economic Impact Assessment of the Monaghan Renewable Biogas Plant looks at both
the jobs created and the increase in gross value added (GVA) resulting from the Biogas Plant
and the economic multipliers this creates in the wider economy. It also looks at the
economic benefits from both the construction and the operational phases of the project.
The economic analysis will account for:
• Multipliers (impacts from spending in the economy);
• Leakage (discounting impacts outside the area);
• Deadweight (what would have happened anyway);
• Displacement (discounting any decrease in economic activity elsewhere in the study
area as a result of the development);
• Substitution (replacing one economic activity with another).
The impact assessment uses these factors by:
• Estimating gross impact of the development, during construction and operation;
• Adjusting the gross impact for additionality created by leakage, displacement and
multiplier effects;
• Developing a reference case, based on keeping the land in agricultural production, and
the value of untreated poultry litter and cattle manure as organic fertilisers;
• Subtracting the reference case from the impacts envisaged to give the net additional
economic impact of the development.
The Economic Impact Assessment also allocates these impacts spatially to estimate where
these benefits will accrue. In this case the impacts are assessed for the local NUTS-371
region, the Border region (the smallest spatial level at which economic data is available); the
regional level; national level; as well as leakage overseas72 – these areas are:
• The Border73 region (including Co. Monaghan);
• Northern and Western Region;
71 Nomenclature of Territorial Units for Statistics (NUTS), the overarching framework for regional and
territorial statistics in the European Statistical System. CSO County and NUTS Regions classification - CSO -
Central Statistics Office
72 Including a split between leakage to Northern Ireland, and general overseas leakage.
73 IE041 Border NUTS-3: Counties Donegal; Sligo; Leitrim; Cavan; and Monaghan
CSO_Local_Authority_2019_and_NUTS_Classification.doc RECEIVED: 28/08/2026
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• Republic of Ireland;
• Leakage to Northern Ireland;
• Leakage to other international suppliers.
The assessment of the economic impact of the proposed development is supported by a
desk-based baseline assessment focused on the three selected impact areas of: (County
Monaghan and) the Border region (NUTS-3 region); Northern and Western Region (NUTS-2
region); and Republic of Ireland.
The economic impact assessment draws on the Department of Jobs, Enterprise, and
Innovation Evaluations of Business Development Programmes – Technical Annex 74(2015);
and the UK HCA Additionality Guide75 (2014). It also draws on a UK BIS research paper76
from 2009, which produced guidance on the values to use for multipliers, displacement, and
other economic impact factors.
b. Economic Baseline
The Central Statistics Office do not collect data on the residence and workplace of
employees by county, however the 2022 Census77 included information on the resident and
commuting workers of towns with more than 1,500 habitants. Monaghan town had a total
daytime working population of 4,198, of which 1,216 were resident in the town. Cootehill,
the nearest local town in County Cavan, recorded a daytime working population of 617 of
which 206 were resident in the town. As such the two closest local towns had leakage of jobs
to commuting workers of 71% and 66.6% respectively. Most of these commuters would
have originated from within the respective counties, and the wider Borders region, with
some workers originating from elsewhere in the Republic, and some from outside the
Republic of Ireland, chiefly from Northern Ireland.
The 2021 Northern Ireland Census78 reported a total of 1,314 people usually resident in the
six counties of Northern Ireland who gave their workplace address as in County Monaghan.
These workers were primarily resident in Fermanagh and Omagh; Armagh City, Banbridge
and Craigavon; Mid Ulster; and Newry, Mourne and Down. In 2021, 31,547 persons at work
were recorded in County Monaghan by the County Incomes and Regional Gross Domestic
Product (GDP) dataset79. This provides a leakage rate to Northern Ireland of 4.2% of jobs in
County Monaghan. By contrast 813 residents of Monaghan commuted to work into Northern
74 technical-annex-evaluation-methodology.pdf
75 HCA Policy Covers
76 Research to improve the assessment of additionality
77 F7069 - Population 15 Years of Age and Older, Usually Resident and Present in the State at Work
78 Census 2021 origin-destination place of work tables (ROI) | Northern Ireland Statistics and Research Agency
79 RAA02 - Estimates of Household Income RECEIVED: 28/08/2026
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Ireland in 202280, highlighting the net leakage of jobs from Monaghan into Northern Ireland.
It also noted that 813 residents of Monaghan commuted to work into Northern Ireland in
202281.
Across the wider Borders region, 174,393 persons were recorded at work in 2021, and 3,896
persons usually resident in Northern Ireland were recorded as working in the Borders
region82. Therefore, the leakage of employment from the Borders region as a whole to
Northern Ireland was 2.2%; and excluding Co. Monaghan was 1.8%.
The 2022 Census also recorded the travel times for workers by county 83. This data reveals
that the average journey time to work in Co. Monaghan was 26.9 minutes, while in
neighbouring Cavan it was 30.7 minutes. Nationally average journey times were 29.1
minutes, showing that Monaghan workers commute shorter travel times than the national
average, suggesting that leakage of workers from Monaghan to other counties is relatively
low compared to the national average.
This Census also has the following data on travel time by counties within the Borders region
(table 3), for those workers who reported their travel time.
Table 3: Travel to Work Journey Time by Area (2022)
Area Journey
time < 15
mins
Journey
time 15
mins - <
30 mins
Journey
time 30
mins - <
45 mins
Journey
time 45
mins - <
60 mins
Journey
time 60
mins - <
90 mins
Journey
time 90
mins and
over
State 23.8% 31.8% 23.6% 8.6% 8.8% 3.5%
Border
region
34.1% 31.4% 18.0% 5.8% 6.2% 4.5%
Cavan 30.4% 28.5% 18.0% 6.1% 9.5% 7.6%
Donegal 38.5% 30.2% 17.3% 5.9% 5.4% 2.7%
Leitrim 28.2% 29.8% 22.0% 7.1% 7.0% 6.0%
Monaghan 33.2% 31.9% 17.3% 5.6% 6.4% 5.6%
Sligo 32.8% 37.9% 18.2% 4.7% 3.8% 2.7%
80 Commuting to Work Census of Population 2022 Profile 7 - Employment, Occupations and Commuting -
Central Statistics Office
81 Commuting to Work Census of Population 2022 Profile 7 - Employment, Occupations and Commuting -
Central Statistics Office
82 Census 2021 origin-destination place of work tables (ROI) | Northern Ireland Statistics and Research Agency
83 F7068 - Travelling Time of Persons Usually Resident and Present in the State RECEIVED: 28/08/2026
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As seen above, 33.2% of workers in Monaghan had a journey time of less than 15 minutes,
significantly more workers than the state average, with a similar proportion of workers
journeying for between 15 and 30 minutes. A total of 65.1% of workers therefore journeyed
for less than 30 minutes. Given the location of the proposed development 2 kilometres from
the Monaghan and Cavan border, all workers journeying less than 30 minutes can be
expected to be captured within the Borders region, specifically within counties Monaghan
and Cavan.
Of those workers travelling between 30 and 45 minutes, these workers would be resident
either within the Borders region or Northern Ireland. While workers journeying more than
45 minutes would be split between Northern Ireland, the Border region, and elsewhere in
the Republic of Ireland (with most of these workers likely to be elsewhere in Ireland). For
those workers travelling over an hour, most of these workers could be expected to be from
elsewhere in Ireland, and Northern Ireland. Only those workers travelling over 90 minutes
are expected to be overwhelmingly from outside the border region or Northern Ireland
(0.2% of Monaghan’s workforce is from areas of Northern Ireland approximately more than
90 minutes from Co. Monaghan). It should be noted that overall, 4.2% of Monaghan’s
workforce originates from Northern Ireland, as per the 2021 NI Census.
The West region which is alongside the Border region, the other component of the Northern
and Western region, is located approximately 75 minutes or more from the site of the
proposed development. Therefore, of the leakage elsewhere in the Republic of Ireland, the
majority will be leakage to the Midlands, Mid East, and Dublin regions.
Therefore, the residence of employment generate by the proposed plant is estimated using
the above data as follows:
• County Monaghan: 45%
• The Border region: 40%
• West (Northern and Western region excl. the Border region): 3%
• Republic of Ireland: 8%
• Northern Ireland: 4%
Therefore, leakage of employment out of Co. Monaghan is projected to be 55% of
employment generated, primarily into adjacent Co. Cavan and the Borders region. There is
expected to be a further 11% leakage elsewhere across the Republic of Ireland (3% into the
West), and 4% internationally to Northern Ireland (UK).
In 2023, the most recent year for which persons at work data is available, the Central
Statistics Office report 29,025 persons at work in County Monaghan, or 1.08% of all persons
at work within the republic of Ireland. Including those employed across the wider Borders
region, the number of persons at work was 189,444 or 7.05% of the national total. RECEIVED: 28/08/2026
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GVA is a measure of economic value which assesses the value of goods and services
produced minus the cost of raw materials and other inputs used in production. The region
within which the biogas plant will be developed is disadvantaged and in 2023 had the lowest
GVA and GDP per capita figures within Ireland84.
Table 4 – GVA by Spatial Area85
Region GVA (€m) GVA per Capita (€) Trend (2018-‘23)
Border region €12,407 €29,074 +42%
Northern & Western €39,781 €43,115 +61%
Republic of Ireland €484,190 €91,428 +42%
Table 4 shows that in the Border region, including Monaghan, the average GVA per capita in
2023 was less than a third of the level nationally, and just under 33% lower than the figure
for the larger Northern and Western combined region. This demonstrates the relatively
underdeveloped nature of the local economy.
The trend in nominal GVA per capita between 2018 and 2023 was broadly identical between
the local and state level, with 42% nominal growth. However, this was significantly below
the 61% growth seen in the Northern and Western region, as per capita GVA growth in the
NUTS-3 Western region was more than 50% above that in the Border region. The Borders is
therefore being slowly left behind by the adjacent Western region, and thus needs more
investment in higher value jobs of the type the biogas plant can provide.
Table 5: GVA by Employment (2023)86
Region GVA (€m) (2023) GVA per Worker (€) Trend (2018-‘23)
Border region €12,407 €65,491 +29%
Northern & Western €39,781 €91,381 +40%
Republic of Ireland €484,190 €180,385 +30%
Table 5 shows that GVA per employee in 2023 was 28% lower in the Border region than in
the Northern and Western region, and 64% lower than the national average.
84 GVA by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office
85 RAA05 - Gross Value Added, Taxes and Subsidies and RAA07 - Gross Value Added, Taxes and Subsidies
86 RAA05 - Gross Value Added, Taxes and Subsidies and RAA07 - Gross Value Added, Taxes and Subsidies RECEIVED: 28/08/2026
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While this also shows that the region has a significant productivity challenge, it does reveal
that the lower GVA per capita in the region is partly due to a proportion of workers in the
population, because the gap compared to the state level is smaller for GVA per worker, than
for GVA per resident.
Table 6: 2022 Population Breakdown by Major Age Brackets87
Age Group Monaghan Border
region
Northern & Western Republic of
Ireland
Age 0-14 21.9% 20.7% 20.0% 19.7%
Age 15-64 62.1% 62.2% 62.9% 65.3%
Age 65+ 15.9% 17.2% 17.1% 15.1%
The lower employment level in the Border region is partly due to a smaller cohort in the core
working age groups amongst the population. With Ireland having a proportion of its
population between 15 and 64 years old which is 3.1% above the local level.
Table 7: GVA Split by Broad Industry Sector (2023)88
Broad Industry Sector Border
region
Northern &
Western
Republic
of Ireland
Agriculture Forestry and Fishing, A 3.9% 2.1% 0.9%
Industry (excluding Construction), Total BCDE 22.5% 35.4% 32.3%
… of which: Manufacturing, C 19.8% 33.6% 31.0%
Construction, F 6.7% 4.6% 2.6%
Distribution, Transport, Hotels & Restaurants, GHI 18.5% 15.1% 10.5%
Information and Communication, J 3.6% 4.4% 19.6%
Financial and Insurance Activities, K 3.6% 3.0% 4.9%
Real Estate Activities, L 5.8% 5.8% 6.3%
Professional, Admin & Support Services, MN 8.2% 9.0% 11.6%
Public Admin, Education & Health, OPQ 25.0% 19.0% 9.9%
Arts, Entertainment & Other Services, RST 2.2% 1.7% 1.3%
87 Based on SAP2022T1T1ACTY - Population and SAP2022T1T1ANUTS - Population
88 NA033 - Annual Gross Value Added (current prices and volumes) RECEIVED: 28/08/2026
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Table 7 shows that Ireland, and the wider Northern and Western region draw a higher
proportion of their economic output from advanced high output industries than in the
Border region, in industries such as financial and insurance activities, information and
communication technologies or industry and manufacturing. As shown below in table 8,
these disparities also present in the proportion of employment by broad industrial sectors.
Table 8: Proportion of Employment by Broad Industrial Group 202389
Broad Industry Sector Border
region
Northern &
Western
Republic
of Ireland
Agriculture forestry and fishing, A 9.6% 7.3% 4.0%
Industry (excluding Construction), Total BCDE 14.8% 15.3% 12.1%
… of which: Manufacturing, C 13.5% 14.2% 10.8%
Construction, F 8.2% 7.2% 6.2%
Distribution, Transport, Hotels & Restaurants, GHI 21.3% 23.1% 23.5%
Information and communication, J 2.7% 4.0% 6.5%
Financial and insurance activities, K 2.3% 2.6% 4.7%
Real Estate activities, L 0.3% 0.3% 0.4%
Professional, Admin & Support Services, MN 7.9% 8.0% 10.8%
Public Admin, Education & Health, OPQ 29.5% 28.3% 27.1%
Arts, Entertainment & Other Services, RST 3.6% 3.9% 4.6%
Table 8, however, also shows that in the Border region employment in construction is
significantly above the larger spatial areas. This higher level of employment in construction
was also reported by the 2022 census for Co. Monaghan, where 2,329 people were
employed in the sector in 2022, or just under 8.2% of all employment then in the county90.
89 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office
90 SAP2022T14T1CTY - Persons at Work RECEIVED: 28/08/2026
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Table 9: GVA per Worker by Industry (2023)91
Broad Industry/Region Border region Northern &
Western
Republic of
Ireland
Total A10 € 65,491 € 91,381 € 180,385
Agriculture Forestry and Fishing, A € 26,611 € 26,229 € 41,297
Industry (excluding Construction), Total
BCDE
€ 99,788 € 211,868 € 480,161
… of which: Manufacturing, C € 96,022 € 216,534 € 520,168
Construction, F € 54,003 € 58,373 € 75,813
Distribution, Transport, Hotels &
Restaurants, GHI
€ 56,652 € 59,841 € 80,401
Information and Communication, J € 87,958 € 100,026 € 544,699
Financial and Insurance Activities, K € 102,741 € 103,341 € 190,323
Real Estate Activities, L € 1,322,715 € 1,675,184 € 2,745,504
Professional, Admin & Support Services,
MN
€ 67,966 € 101,925 € 193,563
Public Admin, Education & Health, OPQ € 55,683 € 61,517 € 65,834
Arts, Entertainment & Other Services, RST € 40,535 € 39,453 € 50,060
Table 9 shows that across all sectors the Border region has a lower GVA per worker than the
national average, with this difference most stark among the highest GVA per worker
industries such as real estate activities, information and communication, or industry. The
Border region also has lower GVA, albeit by a much smaller differential, in most sectors as
compared to the wider Northern and Western region, however, GVA per worker is slightly
higher at the local level in industries, RST and agriculture than at the Northern and Western
region level.
Table 10 shows that the Border region has an unemployment rate slightly above the national
and regional levels. Similarly, it’s economic participation rate is lower than that regionally
and nationally. This suggests that the local labour market retains significant unutilised
potential and is not constricted.
91 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office RECEIVED: 28/08/2026
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Table 10: Labour Participation and Unemployment Q1 2025 92
Metric/Region Border
region
Northern &
Western
Republic of
Ireland
Persons aged 15 years and over in Labour
Force
217,400 489,700 2,918,300
Unemployed Persons aged 15 years and
over
10,500 22,300 124,200
ILO Unemployment Rate (15 - 74 years) 4.9% 4.6% 4.3%
ILO Participation Rate (15 years and over) 61.5% 63.0% 65.8%
In summary therefore, County Monaghan and the Border region has an economy with:
• Very low GVA per capita, and per job, due to structural differences in the sectors
present, a lower proportion of its population which is working age (16-64), lower labour
force participation, and a low level of employment relative to total population.
• A slack labour supply and a moderate unemployment rate, with a low labour
participation rate, suggesting that greater leakage of jobs outside of this area may be
lower than expected for similar developments where labour supply is more constrained.
• A higher proportion of employment within the construction industry than seen within
any of the other geographies, suggesting that leakage of construction jobs outside of the
district will be relatively low.
c. Baseline for the Monaghan Development Site
The development of the Biogas plant will lead to 2 current activities being displaced:
• Agricultural production on the site developed for the Biogas plant;
• The existing use of the ‘waste’ biomass used in the Biogas plant.
The current job and GVA value of these two activities is estimated to be:
Agricultural Output Displaced:
The biogas plant covers 6.2 hectares of land currently used for agriculture. This 6.2-hectare
site is composed of two fields of improved grassland divided by a tree/hedge line. Improved
grassland is used primarily for forage production and grazing to support cattle production, as
well as sheep and horse output.
92 QLF08 - Persons aged 15 years and over RECEIVED: 28/08/2026
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In 202393, Irish agriculture generated €3,545.9 million of GVA from €11,299.5 million of
agricultural output at basic prices; composed primarily of €10,670.5 million of goods output
at producer prices, alongside contractor services, subsidies, and taxes. Therefore, for every €
of crop or livestock output, just over 33 cents of GVA were generated.
The total output of cattle was €3,012.9 million and output of milk was €3,507.4 million; for a
combined beef and dairy output of €6,520.2 million, or 61% of all Irish livestock and crop
production in 2023. Sheep generated a further €344.7 million and horses a further €304.8
million. Grazed livestock therefore produced total output of €7,169.8 million.
In 2023, the total area farmed was 4,492,000 hectares, of which 4,119,700 hectares was
composed of pasture; hay; grass silage; and rough grazing in use. Given total grazed livestock
output of €7,169.8 million, the average value of grazed livestock output per hectare in 2023
was therefore €1,740/hectare, with estimated GVA of €578/hectare. The estimated output
of the biogas site is therefore €10,790 (2023) under agricultural production, with GVA of
€3,586 (2023 values).
In 2023, total GVA from agriculture, forestry, and fishing in the Borders94 was more than
€482 million. The estimated loss of GVA from the displacement of this 6.2-hectare site from
agriculture is therefore 0.00074% of agricultural GVA in the local region. With 18,130 people
employed in the industry in the Borders in 2023, the estimated employment loss is 0.13 jobs
based on the displacement of GVA.
Input Supplies:
• In 2023, farmers spent €7,753.6 million95 on ‘intermediate consumption’ to support
€10,670.5 million of livestock and crop output, or 72.7% of the value of this output.
• The estimated €10,790 of livestock output lost, can therefore be estimated to have
generated €7,841 of intermediate consumption spending in the supply chain.
• In addition to intermediate consumption, agricultural output also relies on the
consumption of fixed capital such as agricultural machinery or buildings. In 2023, this
consumption of fixed capital totalled €1,261.7 million, equivalent to 11.8% of the value
of crop and livestock output. Consumption of fixed capital (which requires replacement)
can therefore be estimated across the 6.2 hectares to be €1,276.
• This €9,117 of input spending supports jobs, with c.€300,000 of spending by livestock
farms on inputs or capital formation estimated to support 1 job (based on a broad mix of
inputs, capital and services bought by farms). The combined annual estimated
93 Output, Input and Income in Agriculture - Final Estimate 2023 - Central Statistics Office
94 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office
95 Output, Input and Income in Agriculture - Final Estimate 2023 - Central Statistics Office RECEIVED: 28/08/2026
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expenditure of €9,117 in the agricultural supply chain (inputs plus fixed capital) is
estimated to support 0.03 full time equivalent jobs in the agricultural supply chain.
• These input supply jobs are believed to broadly within the NACE broad industry group
BCDE which in 2023 in the Border region96 had GVA per worker of €99,788. As such this
input spending is estimated to support €3,032 of GVA (2023 values).
Food Processing, Logistics and Distribution:
• The Annual Review and Outlook for Agriculture, Food and the Marine 2024 97 notes that
‘estimates of economic multiplier coefficients, which measure the direct and indirect
effects of activity in the agri-food sector, range from 1.75 for seafood to as much as 2.0
for dairy and food processing and 2.5 for beef. Through its links to other sectors, in
purchasing and providing goods and services, the agri -food sector contributes strongly to
the Irish economy.’
• Noting that the land use is currently for cattle production, the average indirect jobs
multiplier for both dairy and beef production of 2.25 can be used to estimate the impact
on Irish GVA as €8,068.
• In 202398 industry BCDE in the Border region had GVA per worker of €99,788; and
Distribution, Transport, Hotels & Restaurants GHI €56,652. Assuming that these supply
chain jobs are equally split between these groups, then the GVA per worker displaced is
€78,220, meaning that the displaced food chain GVA supported 0.10 jobs.
Total impacted by this decline of agricultural production can therefore be estimated as:
• 0.27 FTE jobs lost across agricultural production; related input, capital and support
service industries, and the post-farm gate food chain;
• A €14,686reduction in GVA (2023 values).
d. Construction
The biogas plant construction will deliver up to a circa 120 GWh capable plant across a 6.2-
hectare site, with a 1.15-hectare floor area. The total build cost of this plant has been
estimated as €120 million, based on the materials and specialist equipment needed to
construct the plant. Of this €120 million, €35 million is projected to be spent within Co.
Monaghan and the Borders region; €45 million will be spent within the wider Republic of
Ireland; and €40 million will be spent outside of Ireland on the import of specialist
environmental equipment and services.
96 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office
97 annual-review-and-outlook-2024.pdf
98 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office RECEIVED: 28/08/2026
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Construction has been forecast to occur over a 24-month period. Estimated direct
employment on site and in project management is 100 workers for this 24-month period. A
further 140 jobs have been estimated to be indirectly supported by construction, through
the procurement of materials, equipment, machinery, and related services.
The jobs directly supported by the construction can be expected to be located mainly in Co.
Monaghan and the Border region with the impact of these jobs allocated based on the
estimated typical residence of workers whose workplace is in Co. Monaghan. The indirectly
supported jobs are likely to be located both locally and in the wider Republic of Ireland and
internationally.
A local spend of circa €35 million is projected for Co. Monaghan and the Border region
focused on the construction and installation of the project, with specialist equipment,
services, and materials sourced locally, regionally, nationally and from imports (including
from Northern Ireland). Ireland has several existing biogas plants (albeit most significantly
smaller and less complex than the proposed plant), and Stream Bioenergy already
constructed a similar plant in neighbouring Northern Ireland and are currently constructing a
plant in Cork; meaning existing specialist construction and installation expertise for the
general components of the site is available in the local and regional economy.
The 100 employees directly employed in the construction period will therefore be in
construction (41-43)99; installation of machinery and equipment (33); site landscaping and
excavation (services to buildings and landscape activities (81)) and architectural activities to
supervise construction (architectural and engineering activities; technical testing and
analysis (71)).
In 2023, the GVA per worker of construction (41-43) in the Border region was €54,003,
compared to an average state level of €75,813100. GVA per worker in industries 33, 71 and 81
is not available at the local spatial level, and as such the national figures will be used instead.
For consistency therefore the national figure for construction GVA will also be used. This
methodology is also defensible as construction GVA is lower in the Border region and other
rural areas of Ireland, due to the lower value of residential and some commercial property in
these areas, and as such labour productivity is lower. However, the plant developed will be
nationally leading, and its value once built will be based upon its productive capacity which is
independent of other economic factors and therefore labour productivity for this
construction project can be expected to be above the local average and instead in line with
the national average.
99 Throughout this report, numerical and letter codes are used to identify the specific industry classification
referred to. These classifications relate to the Statistical Classification of Economic Activities in the European
Community, Rev. 2 (NACE Rev. 2) and are used by the Central Statistics Office to monitor and report on
economic activity.
100 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office RECEIVED: 28/08/2026
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The GVA per worker in 2023101 for the industries was:
• Installation of machinery and equipment (33): €123,333
• Architectural and engineering activities; technical testing and analysis (71): €101,201
• Services to buildings and landscape activities (81): €62,457 102
Assuming that direct employment will be split between 80 jobs directly in construction; 10 in
the installation of the machinery and equipment in the plant; 5 in site preparation and
landscaping; and 5 in architectural services directing the construction, then the weighted
average GVA of these jobs in 2023 values was €81,167. Therefore, the annual GVA impact is
€8,116,660 (2023 values).
Adjusting for the baseline for the site, which supports 0.27 jobs, and €14,686 of GVA, the
gross jobs gain is 100 (99.73) jobs, and €8,103,394 of GVA. The GVA per gross job created is
therefore €81,238.
Taking the estimated distribution of Co. Monaghan worker’s residence into account, of the
100 gross jobs generated, 45 are expected to be in Co. Monaghan, 40 in the Border region, 3
in the West region (Northern and Western, excl. the Border region), 8 across Ireland, and 4
in Northern Ireland.
Regarding deadweight, no adjustment has been made as this development assessed here
would not occur without the employment and GVA examined here. Deadweight is therefore
considered to be zero in line with the sub-regional median value in the BIS (2009) paper103.
The assessment has allowed for leakage outside the 2 local impact areas, in line with the
proportion of the labour force in Co. Monaghan that originates from outside of the Border.
This reduces the gross jobs within the Border region by 15 jobs. Leakage of other spend has
already been included within the apportionment of construction spend elsewhere in Ireland
and overseas.
Displacement for construction projects is estimated at an average of 43.1% (+-9.7%) by BIS104
at the sub-regional level and 35.6% (+-9.2%) at the regional level, with a range of 0-70% and
0-95% respectively. For this development we expect displacement to be lower given the
significantly higher level of construction employment in Co. Monaghan and the Border
region itself, at the larger levels (i.e. state level) we expect displacement to be in line with
the average.
101 NA033 - Annual Gross Value Added (current prices and volumes) & QES01 - Persons aged 15 years and over
in Employment (ILO)
102 Average of industries 80-82.
103 BIS | 2009 | Research to improve the assessment of additionality | BIS OCCASIONAL PAPER NO. 1
104 BIS | 2009 | Research to improve the assessment of additionality | BIS OCCASIONAL PAPER NO. 1 RECEIVED: 28/08/2026
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We have therefore not split the spatial levels, and instead assumed a uniform displacement
level of 35% for the Border region, Northern and Western, and Ireland. This displacement
reduces the 100 gross direct jobs to 65 jobs, of which 55 are captured in the Border region.
Multipliers have been allowed for using the mean capital projects multiplier in the BIS
Occasional paper no.1, which assesses that for each direct job, the mean multiplier for
construction projects is 1.46 at the sub-regional level and 1.42 at the regional level (BIS,
2009). This increases the jobs created by 25 in the Border region (and a further 3 in the
wider Republic of Ireland). The net job creation by spatial level is therefore shown in the
table below.
Table 11: Net Direct Construction Job Creation by Spatial Level
Area Gross Jobs Displacement Multiplier Net Jobs
The Border region: of
which 85 35% 1.46 80
Co. Monaghan 45 43
Northern & Western
excluding the Border 3 35% 1.42 3
Republic of Ireland
excluding the Northern
and Western region 8 35% 1.42 7
Given the average GVA per job of these workers in 2023, the GVA uplift created per year by
the construction spend in the Border region is modelled below.
Table 12: GVA of Construction Direct Employment
Area Net Jobs GVA €m (2023)
The Border region: of
which
80 €6.54
Co. Monaghan 43 €3.46
Northern & Western
excluding the Border
3 €0.22
Republic of Ireland
excluding the Northern
and Western region
7 €0.60 RECEIVED: 28/08/2026
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The 140 indirect jobs supported will be split between the local region, Ireland, and imports.
The inputs purchased from overseas are expected to have the lowest employment per
€million spent, as these inputs and services are typically specialist equipment. Therefore, of
the 140 indirect jobs, 30 can be estimated as being supported overseas.
110 gross indirect jobs are thus forecast to be generated in Ireland based on the inputs and
services spend of the construction at the local and Irish level. Given that €35 million of the
€80 million of Irish spend will be spent locally, 48 gross jobs can be estimated as being
supported locally in the Border region via construction spend, and 62 gross jobs elsewhere in
Ireland. In the 2022 census year, the West region (forming the remainder of the Northern
and Western region) had 9.7% of employment in Ireland (excluding the Border region)105.
Given an estimated leakage rate of 3% of local gross jobs to the regional level, and 8% to the
state level (and 4% to NI workers), and that for the national spend, in line with the BIS paper,
leakage is zero106, as ‘The concept is not applied at the national level’; 41 gross jobs will be
generated within the Border region (including Co. Monaghan), 7 in the Northern and
Western region (excluding the Border region), and 60 gross jobs will be generated at the
state level (excluding the Northern and Western region).
These indirect jobs are expected to be composed of the manufacturing of building materials,
and equipment required to construct and fit out the AD plant; as well as in the logistics
industry delivering materials and equipment to the site. Consequently, the GVA per worker
of these jobs is expected to be composed of the weighted average GVA per worker (at the
Irish state level) of the manufacture of electrical equipment; manufacture of machinery and
equipment; manufacture of other non-metallic mineral products107; manufacture of
fabricated metal products; and land transport.
In 2023, the GVA per worker in these industries was:
• Manufacture of other non-metallic mineral products (23): €180,557;
• Manufacture of fabricated metal products (25): €93,069;
• Manufacture of machinery and equipment (28): € 223,804;
• Land transport (49): € 82,191.
105 RAA02 - Estimates of Household Income
106 N.B. the BIS technical paper is a UK paper, where this concept that leakage is zero is more defensible as
workers commuting daily to the mainland UK which accounts for c.98% of UK population and employment are
essentially 0% of UK workers given the commuting times involved means that rounded to the nearest 0.1%,
leakage is 0%. In the Republic of Ireland however in 2021 10,540 workers commuted daily into the State from
Northern Ireland. With 37% of these commuting into the border the leakage rate at the NUTS-3 region level is
2.2%, whereas the leakage rate across the wider state is less than 0.3%, and so can be proxied as zero.
107 E.g., cement, bricks, and other mineral based building products. RECEIVED: 28/08/2026
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The GVA per worker within the manufacture of electrical equipment (27) is not available at
this 2-digit industry level. However, the labour productivity per hour for this industry was
€94.8 per hour in Q2 2023108. The manufacturing sector (including sector 27) had average
weekly hours worked of 38 hours in the same quarter 109. As such, the annual total labour
productivity, (or GVA per worker), was €187,325 in 2023.
The average GVA of these jobs, assuming an even split across these five industries was
therefore €153,389 per annum in 2023. As with the gross jobs created by direct
employment, the jobs generated indirectly in the supply chain will cause a displacement
effect. As seen in the BIS (2009) paper, the larger the spatial level the lower the
displacement effect is, as more workers are available to undertake the economic activity
without it displacing them from alternative employment. Given that in the Border region, the
proportion of employment in manufacturing is significantly lower than the national average;
though in logistics is higher, we therefore should estimate that displacement in the Border
region is above the normal level. Whereas at the regional level employment in
manufacturing and logistics are similar to the state level. We have therefore modelled
displacement at the local level at 50%, and at the regional and state levels at 35%. The
multipliers are the same as for direct jobs, and therefore 1.46 locally, and 1.42 for national
jobs.
Therefore the 110 gross jobs generated indirectly in Ireland by spend on construction
materials, equipment and services can be expected to lead to the net jobs and total GVA
shown in Table 13, given a GVA per worker of €153,389 (2023).
Table 13 – Indirect Construction Jobs and GVA by Spatial Area (2023 values) per annum
Area Gross Jobs Displacement Multiplier Net Jobs GVA (€m)
Border region: 41 50% 1.46 30 €4.58
Of which: Co.
Monaghan
22 16 €2.42
Northern & Western
excluding the Border 7 35% 1.42 7 €1.05
Republic of Ireland
excluding the
Northern and
Western region 60 35% 1.42 55 €8.46
108 PIQ01 - Quarterly Productivity Indicators
109 EHQ03 - Average Earnings, Hours Worked, Employment and Labour Costs RECEIVED: 28/08/2026
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The total net impact of the construction period of the proposed biogas plant by spatial is
shown in table 14.
Table 14 – Total Construction Jobs and GVA by Spatial Area (2023 values)
Area Impact of Construction per
Annum
2023 GVA
Baseline €m
% Increase in
GVA due to
Construction Net Jobs GVA €m
The Border region 110 €11.12 €12,407 0.09%
Of which: Co.
Monaghan 58 €5.88 €1,901110 0.31%
Northern & Western
excluding the Border 10 €1.28 €27,374 0.00%
Republic of Ireland
excluding the
Northern and
Western region 62 €9.05 €444,409 0.00%
Total for Republic of
Ireland
182 €21.45 €484,190 0.00%
The 2-year construction period will therefore, as shown in table 14, support a total of 182
net jobs and €21.45 million of GVA uplift per year (2023 values) across Ireland as a whole,
with 58 of these jobs, and €5.88 million of the GVA uplift/year felt in County Monaghan, and
more than €11 million across the Border region as a whole.
This is equivalent to an estimated 0.31% increase in the GVA of County Monaghan during the
construction phase of the project.
e. Operational
Stream Bioenergy estimate that the biogas plant once operational will generate 30 direct
jobs for both energy production and the processing of by-products including organic
fertilisers, and biogenic CO₂. The estimated energy output of the AD plant is up to 120 GWh.
This analysis assumes that the operational impact will include 30 gross jobs involved in the
operation of the plant. With the plant producing biogenic CO₂, an industrial gas;
biomethane, an energy gas; and organic fertilisers; these 30 jobs will be split between
110 Estimated GVA in 2023 of Monaghan based on Monaghan’s share of persons in work in 2023 within the
Border NUTS-3 region. This estimate assumes that GVA per worker is uniform across the Border. RECEIVED: 28/08/2026
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electricity, gas, steam and air conditioning supply (35); and the manufacture of chemicals
and chemical products (20) (industrial gases and fertilisers).
In 2023, the average GVA per worker in industry 35 was €236,461, while data on the GVA of
industry 20 is not available at this 2-digit industry level. Industry 20 had hourly labour
productivity of €433.1 in Q2 2023111 with weekly average hours worked of 38112 for the
manufacturing sector. Therefore, estimated annual GVA per worker was €855,806 per
annum; or 65% higher than the average GVA per worker of all manufacturing113.
Assuming that of the 30 jobs created, 20 are in the production of biomethane, and 10 relate
to fertiliser and CO2 production (industry 20); then the average GVA per worker for these
jobs will be €442,909 per annum. This gives total GVA of €13,287,280 per annum (2023
values).
Subtracting the base case of the 6.2-hectare site of 0.27 jobs, and €14,686 of GVA, the gross
job generation and GVA generation is 30 (29.73) jobs, and €13,272,594 of GVA per annum.
The GVA per gross job generated is therefore €446,412 per annum.
Leakage, as with the assessment of the construction impacts, can be expected to be 15%,
with 85% of these jobs captured in the Border region, 3% elsewhere in the Northern &
Western region, and 8% elsewhere within the state.
The industries in which these jobs will be created are relatively specialist and therefore the
displacement impact of the job creation is likely to be above the average levels for
investment projects. Therefore, we assess this displacement as 50% at the sub regional level,
and 40% at the regional and state level. In line with the BIS (2009) paper we have assessed
multiplier effects as 1.46 at the local level, and 1.42 at the national level. The generation of
net jobs, resulting from the direct operational jobs at different spatial levels is therefore
shown in the table 15.
111 PIQ01 - Quarterly Productivity Indicators
112EHQ03 - Average Earnings, Hours Worked, Employment and Labour Costs
113 Economic Sectors by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office RECEIVED: 28/08/2026
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Table 15 – Direct Jobs Generated by Operation
Area Gross Jobs Displacement Multiplier Net Jobs
The Border region: of which 25 50% 1.46 18
Co. Monaghan 13 10
Northern & Western
excluding the Border 1 40% 1.42 1
Republic of Ireland excluding
the Northern and Western
region 2 40% 1.42 2
The GVA impact of these jobs is shown in the table 16.
Table 16 – Direct Operational GVA by Spatial Level (2023 values)
Area Net Jobs GVA (€m)
The Border region: of which 18 €8.24
Co. Monaghan 10 €4.36
Northern & Western
excluding the Border
1 €0.34
Republic of Ireland excluding
the Northern and Western
region
2 €0.90
Total for Republic of Ireland 21 €9.48
Total Jobs and GVA
In addition to the operational jobs from direct employment in the AD plant, an estimated 75
indirect jobs will also be created. These will include logistics jobs; engineering support jobs;
jobs related to the supply of consumables to the plant; and jobs in the sale and wholesaling
of the products generated.
The plant will use 99,000 tonnes of feedstocks per annum and produce circa 67,000 tonnes
of sustainable fertilisers (dried pellet and fibre fertilisers); 9,000 tonnes of ammonium
sulphate; as well as up to 15,000 tonnes of biogenic CO₂. These feedstocks and outputs will
be transported by covered bulker lorries, tanker lorries, and curtain sided lorries. This
logistics activity is project to support 25 jobs in industry 49, land transport, which will be
local to the site. RECEIVED: 28/08/2026
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Similarly, 25 jobs can be estimated as being generated in the repair and servicing of
machinery (industry 33); and wholesaling of the plant’s outputs (fertilisers and biogenic
CO₂). With these jobs also local to the biogas plant site.
The 50 jobs supported indirectly in the local region will be split between the following
industries which had in 2023 the following GVA per worker114:
• Land transport (49): €82,191;
• Repair and installation of machinery and equipment (33): €123,333; and
• Wholesale trade (46): €260,014.
The (weighted) average GVA of these jobs was €136,932 per annum. Leakage is assessed in
line with the previous assessments with 15% leakage, including 3% to the region, and 8% to
the state level. Displacement is assumed to be normal at all spatial levels and is therefore
estimated at 45% at the local level, and 35% for the larger region and national level.
Multipliers in line with the BIS (2009) paper are estimated at 1.46 at the sub-regional levels,
and 1.42 at the national level. The net jobs created by spatial level are shown in table 17.
Table 17 – Local Indirect Operational Job Creation
Area Gross Jobs Displacement Multiplier Net Jobs
The Border region: of
which
43 45% 1.46 34
Co. Monaghan 23 18
Northern & Western
excluding the Border
2 35% 1.42 1
Republic of Ireland
excluding the Northern
and Western region
4 35% 1.42 4
These jobs would generate the annual GVA (2023 values) as shown in the table 18.
114 Author’s calculation based on NA033 - Annual Gross Value Added (current prices and volumes) and QES01 -
Persons aged 15 years and over in Employment (ILO) RECEIVED: 28/08/2026
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Table 18 – Indirect Operational Jobs and GVA
Area Net Jobs GVA €m
The Border region: of which 34 €4.67
Co. Monaghan 18 €2.47
Northern & Western
excluding the Border
1 €0.19
Republic of Ireland excluding
the Northern and Western
region
4 €0.51
A further 25 jobs can also be estimated as being in the manufacturing of consumables and
repair parts for the plant. These jobs are likely to be supported nationally due to the
specialist nature of many of the consumable chemicals and wearable parts which will be
used by the plant.
In 2023 Ireland imported a total of €140,294 million115 of goods and had a state GVA of just
over €484,190 million. Goods imports therefore were equivalent to 29% of total GVA. As
such it can be estimated that 29% of jobs generated through spending on consumable inputs
to the plant will be lost to imports. This reduces the employment in manufacturing
supported by consumables and parts by 7.25 jobs to 17.75 gross jobs within the state. These
jobs can be estimated as being located by the regional breakdown of Irish manufacturing
employment, with 8.9% in the Border region and 12.5% in the Northern & Western region
(excl. the Border region). Therefore 2 gross jobs will be in the Border region, 2 elsewhere in
the Northern & Western region, and 14 elsewhere in Ireland.
The GVA per worker within the manufacture of the consumables and wearables which the
plant will consume is not available at 2-digit industry levels. However, the labour productivity
of industries NACE 10-18, 22-25, 27-30, 33 was €94.8 per hour in Q2 2023116, and in NACE
19-21, 26, 31-32 was €433.1 per hour. The manufacturing sector (including these sectors)
had average weekly hours worked of 38 hours in the same quarter117. As such, the annual
total labour productivity, (or GVA per worker) for these industries was €521,565 in 2023.
Assuming that displacement will be normal at each spatial level, and that within the Border
region, the proportion of employment generated will be assigned to County Monaghan in
115 Exports and Imports 2023 Ireland's Trade in Goods 2023 - Central Statistics Office
116 PIQ01 - Quarterly Productivity Indicators
117 EHQ03 - Average Earnings, Hours Worked, Employment and Labour Costs RECEIVED: 28/08/2026
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line with its proportion of total employment across all industries in the Border region; then
the following GVA and net jobs will be supported at each spatial level.
Table 19: Nationally Supported Indirect Manufacturing Jobs and GVA (2023 values)
Area Gross Jobs Displacement Multiplier Net
Jobs118
GVA €m
The Border region 2 45% 1.46 1 €0.66
Of which: Co.
Monaghan
0 0 €0.10
Northern & Western
excluding the Border
2 35% 1.42 2 €1.07
Republic of Ireland
excluding the
Northern and
Western region
14 35% 1.42 13 €6.72
f. Total Economic Impact
Once operational, the total net quantifiable economic impact of the indirect and direct
employment accounting for the operational jobs delivered, less the employment (0.27 FTE)
and GVA (€14,686) associated with the baseline use of the agricultural land currently, is
shown in table 21.
118 To the nearest whole number of jobs RECEIVED: 28/08/2026
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Table 20: Total net GVA and Net Jobs Generated (Operational) (2023 values)
Area Impact of Operation 2023 GVA
Baseline €m
% Increase in
GVA due to
Operation
Net Jobs GVA €m
The Border region: of
which
54 €13.57 €12,407 0.11%
Co. Monaghan 28 € 6.93 €1,901 0.36%
Northern & Western
excluding the Border
4 €1.60 €27,374 0.01%
Republic of Ireland
excluding the Northern
and Western region
19 €8.13 €444,409 0.00%
Total for Republic of
Ireland
77 €23.29 €484,190 0.00%
This table shows that the biogas plant, once operational, will provide a (2023 €value) annual
economic benefit of:
• GVA uplift of €23.29 million and 77 net jobs
of which:
• €6.93 million of additional GVA and 28 jobs will be within County Monaghan, equivalent
to a 0.36% growth in the economy;
• €13.57 million of additional GVA and 54 jobs will in the Border region (NUTS-3 region)
(including County Monaghan).
RECEIVED: 28/08/2026
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6. Positive Environmental and Social Impacts
a. Circular Economy
Fertilisers
The fertilisers derived are expected to have the nutritional composition, and annual
production figures shown in table 21.
Table 21: Nutritional Composition, and Output of Fertilisers
Fertiliser Annual Output
(tonnes)
Nitrogen
(%)
Phosphorus
(%)
Potassium (%)
Dried pellet fertiliser Up to 7,000 14.00% 0.60% 8.80%
Fibre digestate Up to 60,000 2.00% 1.00% 2.00%
Ammonium Sulphate Up to 9,000 8.30% <0.10% <0.10%
These fertilisers will be sold as bulk fertilisers to the agricultural industry, for which there is
unmet domestic demand119. For these markets these products would be sold on the value of
their nutritional composition in line with the assessment of the value of untreated poultry
litter.
Based on Teagasc and industry reported figures for nitrogen, phosphorus, potassium and
sulphur in spring 2025, the estimated values rounded to the nearest €5 per tonne for each
fertiliser product are:
• €305 per tonne for the dried pellet fertiliser;
• €75 per tonne for the fibre digestate; and
• €150 per tonne for the ammonium sulphate.
The total value of fertilisers produced would therefore be:
• €2.135 million of dried pellet fertiliser;
• €4.5 million of fibre digestate; and
• €1.35 million of ammonium sulphate.
Ireland currently imports 100% of its synthetic fertiliser requirements, primarily from other
European countries120 and Russia. This has significantly increased the cost of these fertilisers
for Irish farmers, with a report in 2024 noting that the price differential in 2022 between
Ireland and France was almost €200 per tonne121. Reliance on imports also increases the
119 Ireland imports 100% of it’s synthetic fertilisers Irish farmers face highest fertiliser import prices
120 Where the fertiliser we sell in Ireland is made | Yara Ireland
121 Irish farmers face highest fertiliser import prices RECEIVED: 28/08/2026
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environmental impact of these fertilisers due to the increased supply chain length and
therefore transport emissions.
In 2024122 the total nutrient composition of the key (NPK) fertilisers sold in Ireland was:
• Nitrogen content: 310,411 tonnes;123
• Phosphorous content: 28,736 tonnes; and
• Potassium content: 88,058 tonnes.
At the values for NPK used to calculate the value of feedstocks and fertilisers, the value of
the above nutrients used in Ireland in 2024 would be worth €620 million.
The value of available nutrients in the poultry manure which will be displaced by the
Monaghan Renewable Biogas Plant has been estimated at €4.32 million to €5.34 million for
the 80-99,000 tonnes of feedstock used; with the 2,000-10,000 tonnes of cattle manure
feedstock used valued at between €12,000 and €109,000.
However, as the AD process and subsequent processing creates more stable and higher
quality fertiliser the value of the available nutrients in the fertilisers generated by the AD
plant are estimated to be worth circa €8 million. Therefore, the plant will increase the
available value of fertilisers for Irish agriculture by circa €3 million per annum, equivalent to
approximately 0.5% of the estimated value of Irish fertiliser imports in 2024.
Biogenic CO₂ Production for the Food Chain
The biogas plant will also generate up to 15,000 tonnes of biogenic CO₂ per annum. CO₂ is
an essential input for a range of sectors in the food and beverage industries, including
carbonation of drinks, pub dispensing of beer, dry ice manufacture, modified atmosphere
packaging, meat processing, and abattoirs124.
In 2021 and 2022 CO₂ prices rose significantly, as plants producing CO₂ in the UK, from which
Ireland sources much of its CO₂, were closed due to spiking natural gas prices125, leaving food
processing within Ireland exposed as there are no domestic suppliers of CO₂. In 2022, Paul
Kelly, director of Ibec’s Food Drink Ireland group was quoted as noting that similar supply
shortage situations had deteriorated quickly in 2018 and 2021126.
Current total demand for CO₂ in Ireland is c.50,000 tonnes, according to the national
biomethane strategy127. However, this demand is likely to rise, as the strategy notes that
‘Biogenic CO₂ is likely to be in high demand in Ireland as several projects in Ireland and
122 Fertiliser Sales 2024 - Central Statistics Office
123 This nitrogen use is 11% above 2023, though still almost 100,000 tonnes (24%) below the 2018 level before
major price spikes occurred.
124 Risk for potential CO2 shortage
125 Explainer: How Ireland's food supply could be affected by gas price hikes in the UK - SundayWorld.com
126 Food sector alarm as gas prices shut vital CO₂ supplier – The Irish Times
127 National Biomethane Strategy RECEIVED: 28/08/2026
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Europe assess the production of future fuels such as green methanol and Sustainable
Aviation Fuels (SAF), both of which will require significant volumes of biogenic CO ₂. Due to
the abundance of offshore wind in Ireland, there is a vast potential for developers of these
fuels to assess projects in Ireland’.
The development of the biogas plant will therefore provide a domestic supply of food grade
CO₂, equivalent to circa 30% of current national demand, reducing reliance on imports and
the price uncertainty this imposes on the Irish agri-food and drinks sector. It will also
contribute to the long-term development of future fuels for both the aviation and
agricultural sectors.
Most of the UK and Irish market is controlled by BOC Gases128, part of the Linde Group. BOC
Gases currently sell food grade CO₂ in small volumes (34Kg) for €73.60129, and supply large
users in the agri-food, and water treatment industries with liquid bulk gases130 (via tanker).
Competitors such as CarbonDioxide.IE provide CO₂ refills of up to 45Kg for €70131. Prices for
food grade CO₂ are therefore in small quantities, approximately €2,000 per tonne, with
wholesale prices likely to be in the region of €1,000 per tonne. Consequently, the proposed
plant might provide up to €15 million of food grade CO₂ to the Irish agri-food industry.
Circular Economy
In addition to valorising waste streams and producing sustainable inputs for the Irish agri-
food chain, the biogas plant also provides a positive symbol for sustainable growth and the
circular economy in the heart of the Ireland’s poultry cluster. This demonstrates how
sustainable investment which reduces environmental harms, improves soil health, and
generates clean growth jobs in a deprived area, can improve profitability and resilience for
Ireland’s fastest growing meat segment.
The clear demonstration of sustainable development will help to encourage and unlock
further investment in the supply chain, by demonstrating state of the art technology to
transform negative environmental impacts into environmental gains.
128 Official BOC Gases | Gas, equipment & accessories | Services & industries - Ireland
129 Ireland BOC Online Shop: Carbon Dioxide Food Fresh
130 Bulk | Gas Supply Options | BOC Gases
131 Price List | Carbondioxide.ie RECEIVED: 28/08/2026
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b. Environmental Benefits for Agriculture and the Food Chain
Most supermarkets (Table 22) are targeting Net Zero for: scope 1 and 2 (their internal
operations and energy) for between 2035 and 2040, with Lidl having a partial target for
2030, and complete net zero by 2050. With scope 3 targeted (supply chain) by 2050 (though
most retailers have partial targets for their supply chains already by the early 2030s).
Table 22 – Retailer commitment on Net Zero Transition
Retailer Net Zero (Latest) Target Year
Scope 1 and 2 Scope 3
Musgrave
Group132
2040 2050
Tesco133 2035 2050
Aldi 2035134 2050 (52% reduction by 2030135)
Lidl136 2050 (46% by 2030) 2050 (42% for agricultural suppliers by 2034)
This means that a growing focus of the retailers is to address the carbon emissions in their
supply chain (scope 3 emissions). Some supermarkets have set ambitious targets for scope
3 as soon as 2030 such as Aldi, meaning the food chain is under real pressure to move
forward rapidly on carbon reduction. If Monaghan and Borders based food producers fail to
do this, they are likely to start to lose sales to other suppliers or potentially to imports within
the next 5-10 years if these competitors adopt net zero more rapidly.
The food industry therefore needs to both make rapid progress in decarbonisation and to be
able to demonstrate that it has achieved decarbonisation targets. Whilst soils are
recognised as the largest land-based carbon store, there are ongoing challenges with both
measuring soil carbon and in being able to demonstrate progress in soil carbon reserves.
This means that for agriculture the ‘heavy lifting’ will, in the early years of the road to Net
Zero, need to come primarily from areas in which it is easier to prove both the emissions and
the progress that is made. The two big agricultural emissions for which it is easier to show
progress is embracing low carbon fertilisers, and the transition to renewable energy and
fuels for tractors and for commercial vehicles in the supply chain.
Teagasc for instance note that the Irish tillage sector is one of the most sustainable in Europe
with an emissions intensity for wheat of 0.27-0.33KgCO₂e/KgDM, or more than 25% below
132 Caring for the planet - Musgrave Group
133 Climate change
134 Energy and Transport Efficiency | ALDI IE
135 ALDI sets targets for net-zero greenhouse gas emissions
136 Protecting Climate - Lidl RECEIVED: 28/08/2026
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UK levels. However, fertiliser (manufacture) and use accounts for 70% of these emissions137,
with fossil fuels and energy accounting for a significant proportion of the balance. Therefore,
action must be taken in these areas, if Irish agriculture is to reach its net zero targets.
The transformation of untreated poultry manure and cattle manure currently used as
fertiliser in the agricultural industry, into bioenergy and sustainable fertilisers will support
this transition. Excess use of poultry and cattle manures directly on soils is also associated
with eutrophication of watercourses, and ammonia and methane emissions to air138.
Teagasc also note that repeated poultry manure application can lead to phytotoxic effects on
crops due to accumulation of trace elements. The displacement of this organic fertiliser into
AD, was therefore recommended by Teagasc in their 2022 presentation 139 on the uses of
poultry manure, to recover useful fertilisers and bioenergy, and reduce fugitive methane
emissions and odours.
c. Positive Social Impacts for County Monaghan and the Borders
The Borders and Co. Monaghan is the most economically deprived NUTS-3 region within the
Republic of Ireland, with its economy heavily dependent on the agri-food sector. In 2023, it’s
GVA per capita was just 31.8% of the national average, and the region was bordered to its
south by the Midland which with a GVA per capita of 35.4% of the national average is the
second most deprived region140.
Table 23 – Borders and RoI GVA, Population, and Employment 2023 141
Metric/Region Border region Ireland
Gross Value Added (GVA) at Basic Prices (€m) €12,407 €484,190
Population (thousand) 427 5,296
Gross Value Added (GVA) per person at Basic Prices €29,074 €91,428
Persons at work (thousand) 189 2,684
GVA per Worker (€) €65,491 €180,385
Resident Population at work (%) 44.4% 50.7%
Percentage of Ireland Total Population 8.06% 100%
Percentage of Ireland Total Persons at work 7.06% 100%
137 Teagasc Broiler Manure Usage
138 Teagasc Broiler Manure Usage
139 Teagasc Broiler Manure Usage
140 GVA by Region County Incomes and Regional GDP 2022 - 2023 - Central Statistics Office
141 RAA05 - Gross Value Added, Taxes and Subsidies RECEIVED: 28/08/2026
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Table 24: Educational Attainment by Region (2022 Population 15 years and over)142
Educational Status/Region County
Monaghan
Border
region
Northern &
Western
Ireland
No formal education 3.5% 2.9% 2.6% 2.0%
Primary 7.9% 8.5% 7.4% 6.1%
Lower secondary 14.9% 13.2% 11.7% 10.8%
Upper secondary 15.0% 15.3% 15.4% 14.8%
Technical/vocational 7.0% 6.9% 6.5% 6.1%
Advanced certificate/completed
apprenticeship
5.2% 4.9% 4.8% 4.6%
Higher certificate 4.5% 4.9% 4.7% 4.5%
Ordinary bachelor
degree/professional qualification or
both
5.8% 6.3% 6.6% 6.6%
Honours bachelor
degree/professional qualification or
both
8.9% 9.2% 10.0% 10.9%
Postgraduate diploma or degree 5.3% 6.5% 7.8% 9.2%
Doctorate (Ph.D.) 0.3% 0.5% 0.8% 0.9%
Not stated 4.1% 4.4% 4.6% 5.3%
Economic status - total at school,
university, etc.
10.3% 10.4% 10.9% 11.1%
Economic status - other 7.2% 6.1% 6.2% 7.1%
Tables 23 and 24 shows that the Border region (including Co. Monaghan):
• Has a workforce participation rate (as a proportion of total population) which is
significantly (circa. one eighth) lower than the national average.
• Has GVA per worker of just 36.3% of the national average.
142 FY075A - Population Aged 15 Years and Over RECEIVED: 28/08/2026
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• Has a lower proportion of its population who are educated to degree level or equivalent
or above, and a higher proportion with no formal education.
The biogas plant will create higher paid, long-term careers with onsite employment
projected to generate an annual GVA of €9.48 million and support 30 jobs, or €316,000 per
job. This is almost 5 times higher than the average for the region of €65,491 and +75%
compared to the national average of €180,385. This development therefore provides high
value job opportunities for young professionals and will help to resolve the demographic
challenges in this rural part of Ireland.
RECEIVED: 28/08/2026
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7. Appendix
a. Waste Feedstock Baseline Use
The feedstocks which will be used for the biogas plant are projected to consist of 80,000 to
99,000 tonnes of poultry and cattle manure and 9,000 – 19,000 tonnes of agri-food organic
wastes.
Poultry manure is currently used by the agricultural industry, specifically the tillage sector as
an organic fertiliser; with Teagasc demonstrating its use in a 2015/16 trial as a partial
replacement for bagged fertilisers143. However, this trial did report significant challenges
associated with ammonia volatilisation and pollution, especially when poultry manure is
used for winter cereals. It cannot be used by the grassland and livestock sector as ’broiler
litter can transmit botulism to cattle on the home or neighbouring farms and for this reason
cannot be applied to grassland parcels’144. Estimated current values per tonne for this
organic manure are just under €54 (see sub-section C below), with total displaced value
therefore of c.€4.32 million to €5.34 million per annum145.
The 9,000 to 19,000 tonnes of agri-food organic wastes are not believed to have any current
economic value to the agri-food sector, with instead the cost of disposal to sewer or landfill
reducing the profitability and factor productivity of the agri-food sector in Monaghan and
the Border region.
Cattle manure is currently used by the agricultural industry, primarily on silage and tillage
land as an organic fertiliser. Due to its low nutrient density, it is mostly used internally on
farm holdings to reduce imported fertiliser requirements. In County Monaghan, this usage is
therefore primarily on grassland (e.g., silage) in line with the predominance of this
agricultural system in the county and region. Values of dairy slurry are currently estimated as
€6/tonne; while farmyard manure is worth approximately €11/tonne. The value displaced by
the cattle manure (c.2,000 to 10,000 tonnes) is therefore between €12,000 to €110,000 per
annum.
The maximum combined volume of organic fertilisers which will be displaced is 99,000
tonnes, with a minimum displacement of 80,000 tonnes per annum. The overall value of
organic fertilisers displaced is therefore between c.€4.32 million to c.€5.34 million.
143 GLAS
144 Pigs & Poultry - Broiler litter as a fertiliser in tillage systems - Teagasc | Agriculture and Food Development
Authority
145 Based on the poultry manure volume of 80,000 to 99,000 tonnes. RECEIVED: 28/08/2026
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b. Fertiliser Nutrient Values
The Irish Farmer Association reported in February 2025146 prices for Urea (46%N) as €490
per tonne; and the prices for 0-7-30147 as €500 per tonne (i.e. 70Kg of phosphorous and
300Kg of potassium). More recently, Urea prices of between €565 and €570 per tonne were
reported for the end of April 2025148. This would infer current price for nitrogen of €1,240
per tonne, or €1.24/Kg based on this more recent value of Urea.
Teagasc’s valuation of spent mushroom compost publicised in February 2025 149, provided
prices in February 2025 for the three key crop nutrients of €1.48 per kg for nitrogen (N),
€2.69 per kg for phosphorus (P), and €0.95 per kg for potassium (K). This suggests a spread
between the value of nitrogen as Urea, and the value of nitrogen in other fertilisers, with
Urea typically being the cheapest nitrogen source due to its higher volatility. Straight urea
is, however, set to be banned for use in Ireland from September 2025150 due to the higher
eutrophication risk it poses to watercourses and wildlife.
This analysis therefore uses the proposed values from Teagasc in February 2025, with the
proviso that fertiliser values vary significantly over time and are subject to large market
volatility151 driven by international market trends.
c. Broiler Litter Value
Assessed in terms of the value of broiler litter as a fertiliser, this is dependent on its
composition. Teagasc report that broiler litter has 14 kilos of available nitrogen (N); 6 kilos of
available phosphorus (P); and 18 kilos of available potassium (K) per tonne152.
Assessed on the estimated nutrient values of €1.48 per kg for nitrogen (N), €2.69 per kg for
phosphorus (P), and €0.95 per kg for potassium (K), broiler litter currently has an
approximate value based on its crop available nutrients of €20.72 of N; €16.14 of P; and
€17.10 of K per tonne, or €53.96 per tonne. Therefore, the estimated value of broiler litter to
the tillage sector is €53.96 per tonne, generating a displacement value of €4.32million to
€5.34million of organic fertiliser for the 80-99,000 tonnes of feedstock.
This value of poultry manure is not however received by the poultry industry in the Border
region, as the poultry sector is concentrated in Monaghan and Cavan, where the tillage
sector is significantly underrepresented153. Consequently, these untreated organic fertilisers
are exported from the region as they cannot be applied to grassland parcels, reducing their
146 Table: How are fertiliser prices looking this year? - Agriland.ie
147 Generic designation representing the nutrient ratio of phosphorus and potassium in the fertiliser
148 Fertiliser prices steady up - Free
149 €14 per ton of SMS- Teagasc - UMDIS Mushroom Agency
150 Straight urea to be banned from end of 2025 - Premium
151 Global conflicts drive uncertainty in fertiliser market - Premium
152 Available Nutrient Content of Organic Manures 2008/09*
153 Can poultry manure replace bag fertiliser on tillage farms? - Free RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 59 - MC/GC, November 2025
value to poultry producers due to transport costs. The Poultry Sustainability Roadmap154
notes that it is ‘a product that costs more than €20 per tonne for disposal’. Therefore, the
use of up to 99,000 tonnes of poultry manure in the proposed biogas plant could potentially
save the Monaghan and Cavan poultry cluster up to €1.98 million in disposal costs.
d. Cattle Manure values
Cattle manure for the plant is primarily expected to be dairy slurries from the surrounding
farm cluster which supplies the Lakeland155 Dairies cooperative.
These dairy slurries are currently typically spread on silage and tillage land as an organic
fertiliser, with farms utilising these fertilisers internally. Teagasc recently estimated in March
2025 that ‘Current fertiliser prices dictate organic manures offer savings in chemical fertiliser
costs. For example, an application of 25 m3/ha of cattle slurry can reduce costs by €150/ha in
N, P & K.’156 This is equivalent to estimated savings of €6/m³ or approximately €6/tonne.
Were the biogas plant to use the lower estimate of 2,000 tonnes of this feedstock per
annum, it would therefore displace €12,000 worth of fertiliser value; while at the higher
estimate of 10,000 tonnes, this would rise to €60,000 of displaced value to agriculture.
If this cattle manure is instead solid manures, such as cattle farmyard manure then the value
of fertiliser displace will be slightly higher reflecting the higher nutrient density of this form
of cattle manure. Teagasc report that farmyard manure has 1.35 kilos of available nitrogen
(N); 1.2 kilos of available Phosphorus (P); and 6 kilos of available potassium (K)157 per tonne.
Assessed on the estimated nutrient values of €1.48 per kg for nitrogen (N), €2.69 per kg for
phosphorus (P), and €0.95 per kg for potassium (K); this farmyard manure would have a
value of €2.00 of N; €3.23 of P; and €5.70 of K per tonne, or €10.93 in total value per tonne.
With an estimated value of €10.93 per tonne, the value of 2-10,000 tonnes of cattle
farmyard manure as fertiliser is therefore currently between c.€22,000 and €109,000 for
Irish agriculture.
These values for farmyard manure and slurry are however their gross value once applied,
and do not account for the significant infrastructure costs158 which farmers face to store
these manures over the late autumn and winter when their application to land is not
possible159. With their application during the growing season also requiring significant
investment in machinery, labour, and fuel. As such the true value of these manures to
farmers with an excess of availability can be negative, and therefore the plant is likely to
154 Poultry Association - IBEC
155 Home | Lakeland Dairies
156 Organic Manures
157 Available Nutrient Content of Organic Manures 2008/09*
158 Slurry storage and handling: How best to invest - Teagasc | Agriculture and Food Development Authority
159 Are slurry storage requirements likely to increase? - Agriland.ie RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 60 - MC/GC, November 2025
significantly reduce the slurry and manure management costs which surrounding farmers
face.
e. Fertiliser values
As shown in table 21, repeated below, the plant will produce a range of organic fertiliser
outputs with the following estimated production values and nutritional breakdown.
Table 21: Fertiliser Output and Nutrient Content
Fertiliser Annual Output
(tonnes)
Nitrogen
(%)
Phosphorus
(%)
Potassium (%)
Dried Pellet fertiliser Up to 7,000 14.00% 0.60% 8.80%
Fibre digestate Up to 60,000 2.00% 1.00% 2.00%
Ammonium Sulphate Up to 9,000 8.30% <0.10% <0.10%
The dried fertiliser will be produced by further processing of the liquid digestate through an
evaporator and drier to produce a dried pellet fertiliser which can be applied by traditional
granular fertiliser spreaders. With a nitrogen content of 14%, this fertiliser can be replaced
at a rate of approximately 2 tonnes for every tonne of Calcium Ammonium Nitrate (CAN)
fertiliser which growers currently use. CAN is typically a 27% nitrogen fertiliser. With CAN
prices quoted as €375160 in spring 2025, dried fertiliser pellets would have been valued at
c.€190 as a direct substitute for CAN use.
Alternatively, it can be valued using the NPK values provided by Teagasc in 2025, as shown
for all fertilisers in table 25.
Table 25: Value of Fertilisers Assessed on NPK Values
Fertiliser Tonnage Nitrogen
€1.48/Kg
Phosphorus
€2.69/Kg
Potassium
€0.95/Kg
Value per
tonne (€)
Total value
(€)
Dried pellet
fertiliser 7,000 € 207.20 € 16.14 € 83.60 € 306.94 € 2,148,580
Fibre
digestate 60,000 € 29.60 € 26.90 € 19.00 € 75.50 € 4,530,000
Ammonium
Sulphate 9,000 € 122.84 € 2.69 € 0.95 € 126.48 € 1,138,320
The ammonium sulphate would have further value beyond that shown above, with CAN plus
sulphur (which has 1kg of sulphur for every 7.5 kilos of nitrogen) being worth €10 per tonne
160 Table: How are fertiliser prices looking this year? - Agriland.ie RECEIVED: 28/08/2026
Collison
& Associates Limited
Stream Bioenergy Monaghan Renewable Biogas Plant
Policy and Economic Impact Assessment
November 2025
appendix 1.2 economic impact assessment.docx Page - 61 - MC/GC, November 2025
more than CAN without sulphur161. Providing a sulphur value of €10 per 36 kilos of available
sulphur, or circa €0.28 per kilo. Ammonium sulphate, with an 8.3% nitrogen content, has a
9.5% sulphur162 content based on its atomical weight. Each tonne of ammonium sulphate
will therefore have 95 kilos of sulphur worth circa €26.
The estimated values rounded to the nearest €5 per tonne for each fertiliser product are
therefore €305 per tonne for the dried pellet fertiliser; €75 per tonne for the fibre digestate;
and €150 per tonne for the ammonium sulphate fertiliser. Providing a total conservative
value output estimate of €7,985,000 of the fertiliser produced.
161 Table: How are fertiliser prices looking this year? - Agriland.ie
162 Nitrogen has an atomic weight of 28, sulphur has an atomic weight of 32, ammonium sulphate has 1
sulphur, and 1 nitrogen atom. Therefore, if nitrogen is 8.3% W.W. of the solution, then sulphur is 32/28 times
8.3% of the W.W. of the solution, i.e. 9.5% of the solution. RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 2.1
OUTLINE CONSTRUCTION
ENVIRONMENTAL MANGEMENT
PLAN
Stream BioEnergy Ireland Limited
AUGUST 2026 RECEIVED: 28/08/2026
P
OUTLINE CONSTRUCTION
ENVIRONMENTAL MANAGEMENT PLAN
(oCEMP)
August 2026
STREAM BIOENERGY IRELAND LIMITED
PROPOSED RENEWABLE BIOGAS PLANT
Maghernakelly, Drum, County Monaghan
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report
Outline Construction Environmental Management Plan (oCEMP)
Table of Contents
1. Introduction ................................................................................................................................. 1
1.1 Overview ............................................................................................................................. 1
1.2 Background ......................................................................................................................... 1
1.3 Objectives ........................................................................................................................... 3
2. Site Description ........................................................................................................................... 4
2.1 The Proposed Development Site........................................................................................ 4
2.2 Topography & Drainage ...................................................................................................... 5
2.3 Environmental Receptors ................................................................................................... 6
3. The Proposed Development ...................................................................................................... 7
3.1 Overview ............................................................................................................................. 7
3.2 The Proposed Development Description ............................................................................ 8
4. Construction .............................................................................................................................. 10
4.1 Construction Programme .................................................................................................. 10
4.2 Phasing of Works .............................................................................................................. 10
4.3 Working Hours .................................................................................................................. 11
4.4 Enabling & Site Preparation Works .................................................................................. 12
4.5 Site Compounds, Materials & Plant Storage Areas .......................................................... 12
4.6 Site Clearance .................................................................................................................. 14
4.7 Fencing ............................................................................................................................. 14
4.8 Earthworks (Borrow & Surplus Materials) ........................................................................ 15
5. Environmental Management .................................................................................................... 16
5.1 Roles & Responsibilities ................................................................................................... 16
5.2 Air Quality Management ................................................................................................... 17
5.3 Cultural Heritage ............................................................................................................... 18
5.4 Waste Management .......................................................................................................... 19
5.5 Water Management .......................................................................................................... 19
5.6 Noise and Vibration Management .................................................................................... 20
5.7 Landscape and Ecology Management ............................................................................. 21
5.8 Construction Traffic Management Plan ............................................................................ 22
6. Reporting, Monitoring and Auditing ....................................................................................... 24
6.1 Reporting and Record Keeping ........................................................................................ 24
6.2 Environmental Performance Monitoring ........................................................................... 24
6.3 Community Engagement & Liaison .................................................................................. 24
7. Conclusion ................................................................................................................................ 24
Appendix A - Resource & Waste Management Plan ........................................................................ 26
Appendix B - Summary of Environmental Mitigation Measures .................................................... 27
Appendix C - Soil and Surface Water Management Plan ................................................................ 28
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 1
1. Introduction
1.1 Overview
This outline Construction Environmental Management Plan (oCEMP) supports a planning application
to Monaghan County Council (MCC) by Stream BioEnergy Ireland Limited (‘the Applicant’) for the
development of a renewable biogas plant and associated works (hereafter referred to as the proposed
development) on a site situated in the townland of Maghernakelly and Drumcall Drum, County
Monaghan.
This oCEMP has been updated following the Further Information request issued by Monaghan County
Council in March 2026 and the subsequent refinement of the Proposed Development. In particular, the
Soil Relocation Area previously included within the planning application has been removed from the
Proposed Development. Suitable excavated material will continue to be reused within the Renewable
Biogas Plant site, with surplus excavated soil and stone managed off site in accordance with the
Resource and Waste Management Plan. The oCEMP has been reviewed and updated accordingly to
reflect the revised Proposed Development and the mitigation and monitoring measures identified in the
updated EIAR.
Stream’s proposal involves the use of anaerobic digestion (AD) technology to generate renewable
biogas from organic waste materials. Biogas generated by the proposed plant would be upgraded on
site to biomethane and exported to the gas network to replace fossil fuel derived natural gas.
This oCEMP relates to the construction of the Renewable Biogas Plant and associated works forming
the Proposed Development for which planning permission is sought. The associated Linear Gas Grid
Connection does not form part of the Proposed Development and will be delivered separately by Gas
Networks Ireland under the applicable statutory consenting process. The Renewable Biogas Plant and
Linear Gas Grid Connection have been considered collectively as the Proposed Project for the purposes
of the EIAR; however, the construction of the Linear Gas Grid Connection is not governed by this
oCEMP. Where Appendix B identifies mitigation or monitoring measures in respect of the Linear Gas
Grid Connection, these are recommendations for implementation by Gas Networks I reland and do not
constitute commitments by the Applicant.
1.2 Background
This oCEMP provides a framework for environmental management during construction of the proposed
development, with the primary aim of reducing any potential adverse impacts from construction on the
environment.
The oCEMP shall be adopted and expanded by the appointed Contractor into a Construction
Environmental Management Plan (CEMP) as more information becomes available (i.e. requirements of
planning conditions) and/or there is more certainty in terms of construction methods, programme, etc.
The Contractor’s CEMP will be a ‘live’ document, subject to ongoing review throughout the construction
phase, and would be agreed in writing with Stream. This will confirm the efficacy and implementation of
relevant mitigation measures and commitments identified throughout this oCEMP and will be prepared
in accordance with relevant best practice guidance.
The Contractor’s CEMP will also incorporate the following documents:
• Construction Health & Safety Management Plan;
• Resource & Waste Management Plan
• Soil & Surface Water Management Plan; and
• Construction Traffic Management Plan.
Towards the end of the construction phase, the CEMP shall be further refined by the Contractor as
necessary into a Handover Environmental Management Plan (HEMP) which shall contain essential
environmental information needed by those responsible for the future maintenance and operation of RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 2
the proposed development. This would also be subject to review and agreement with the Stream
development team.
The various stages of the document are summarised in Table 1.
Table 1 - Schedule of CEMP Updates
Project stage Iteration
Design First iteration of oCEMP produced during the design stage for the Project.
Construction Second iteration (CEMP) prepared by the appointed Contractor in advance of
construction commencing and then subsequently refined as required.
End of construction Third iteration of CEMP (the HEMP) building on the CEMP refined at the end of the
construction stage to support future management and operation of the asset.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 3
1.3 Objectives
The objectives of this oCEMP and subsequent iterations are therefore to:
• Act as a continuous link and main reference document for environmental aspects between the
design and construction phases;
• Demonstrate how construction activities and supporting design shall properly integrate the
requirements of environmental legislation, policy, good practice, and those of the environmental
regulatory authorities and third parties;
• Record environmental risks and identify how they will be managed during the construction
period;
• Record the objectives, commitments and mitigation measures to be implemented together with
programme and date of achievement;
• Identify the key responsibilities associated with the delivery of the project as necessary;
• Act as a vehicle for transferring key environmental information at handover to operational
management; and
• Provide a review, monitoring and audit mechanism to determine effectiveness of, and compliance
with, environmental control measures and how any necessary corrective action shall take place.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 4
2. Site Description
2.1 The Proposed Development Site
The proposed development is located at Maghernakelly, Drum, County Monaghan, centred at Irish
Transverse Mercator (ITM) coordinates X-658967, Y-818422.
Figure 2-1 Proposed Development Site Location
As shown on Figure 2-1, the proposed development site spans approximately 6.2 hectares (ha)
across two fields which are largely improved grassland.
The proposed development site is largely bordered by maintained hedgerow and ditches, with gated
field access from the adjacent public roads. These roads are:
• R189 which forms the eastern boundary;
• L2280 Drumcall Road which forms the northern boundary; and
• L22802 (McKeever’s Road) which forms the western boundary.
The site forms part of the agri-business unit associated with the adjacent farm and residential property
to the south, all forming part of the same overall land holding. An aerial photograph of the site is
presented in Figure 2-2. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 5
Figure 2-2 Site Aerial Photograph
2.2 Topography & Drainage
The topography of the proposed development site slopes gradually from the adjacent local roads to
the northeast and west, then rises steeply towards a high point to the south (close to the adjacent
farm property). The highest elevation is in the south-west at 111.75m Above Ordnance Datum
(mAOD) and lowest elevation in the north-east at 90.00 mAOD.
The topographical data indicates natural drainage towards the north-east. As shown on Figure 2-3, a
land drain along the northern field boundary of the proposed development site conveys surface water
runoff via a culvert under the R189 into another land drain along the Drumgole Road which is
hydrologically connected to the Coolkill Lough Stream, which rises to the northeast of the L2320
Drumgole Road.
A number of land drains are also aligned along the eastern and western field boundaries which
essentially separate the site from the adjacent local road network. A ditch also runs through the
central hedgerow on the proposed development site, connecting with the land drain aligned along the
eastern field boundary. As such, all land drains convey field drainage / surface run-off to the land drain
running to the north of the site. With the exception of these land drains, there are no watercourses on
the site. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 6
Figure 2-3 Land Drains & Flow Direction
2.3 Environmental Receptors
The following potential environmental receptors have been identified in the vicinity of the site:
• Residential receptors in the vicinity of the site; and
• Local drainage ditches, downstream surface waters and groundwater beneath the site.
• Hedgerows, trees and other ecological features;
• Archaeological and cultural heritage features; and
• the adjoining local and regional road network and its users.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 7
3. The Proposed Development
3.1 Overview
The proposed development will utilise AD technology to generate renewable biogas from up to 99,000
tonnes of poultry manure, cattle manure, and agri-food organic waste feedstocks sourced from County
Monaghan and surrounding areas. Biogas generated will be upgraded on site to biomethane and
injected to the national gas transmission network (approximately 3.5 km south of the site) to replace
fossil fuel derived natural gas. It will comprise a state-of-the-art AD facility designed to meet the highest
environmental and safety standards and shall be contained within a comprehensive scheme of new
landscape planting and engineered landscape features that provide visual screening, integration and
biodiversity enhancement.
Figure 3-1 Proposed Development Site Layout
As shown in Figure 3-1, the proposed development comprises a number of integrated elements
including:
• 1 - Administration Building (with associated surface level car parking);
• 2 - Main Process Building (with associated vehicle service areas);
• 3 - Odour Control System (with associated emission stack);
• 4 - Bunded Tank Farm (accommodating the vast majority of tanks that require containment);
• 5 - Digestate Treatment Plant (Evaporator);
• 6 - Digestate Drying Plant;
• 7 - Pellet Hall (for fertiliser storage);
• 8 - Combined Heat and Power (CHP) Building (accommodating two CHP Engines); RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 8
• 9 - Boiler Unit;
• 10 - Shared Emission Stack (Digestate Drying Plant, CHP engines and Boiler);
• 11 - CO2 Liquefaction Plant;
• 12 - Biogas Upgrade Plant (BUP);
• 13 - Biogas Treatment Plant (Biological De-sulphurisation Units);
• 14 - Gas (Holder) Buffer Dome;
• 15 - Weighbridges and Wheel Washes;
• 16 - Liquid Feedstock Storage Tanks (silos);
• 17 - Backup Gas Flare;
• 18 - Fuel Storage Tank;
• 19 - Gas Grid Entry Unit;
• 20 - Fire Water Storage Tank;
• 21 - Liquefied Petroleum Gas (LPG) Storage Tanks (propane);
• 22 - Process Water Buffer Storage Tank (underground);
• 23 - Staff and Visitor Parking;
• 24 - Control Building;
• 25 - Plant Room; and
• 26 - Back-Up generator.
Other integrated elements, though not numbered on Figure 3-1 include:
• Internal road and footway provision;
• Engineered stormwater drainage system;
• Landscaping and Earthworks;
• Lighting;
• Fencing and security gates; and
• Site entrance/exit off the L2280 Drumcall Road with gated frontage. This shall include localised
widening and realignment of this road and reconfiguration of the junction with the R189.
3.2 The Proposed Development Description
The proposed development comprises the following elements as detailed within Table 3-1able 3-1. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 9
Table 3-1 Proposed Development Description
Proposed Element Description
Administration Building Building incorporating a reception area, welfare and changing
facilities, canteen, offices etc.
Main Process Building Accommodating feedstock reception and pre-treatment areas and
processing areas.
Odour Control System Odour control system comprising air scrubbing, biofiltration and
carbon polishing. Treated air will be vented via a 40m high stack.
Bunded Tank Farm
Bunded structure containing digester tanks where AD process will
take place, as well as other storage tanks and digestate gas
treatment plant.
CHP Unit
Acoustically contained engine house accommodating the CHP
engines that will provide electricity and heat to the plant. Exhaust
gas emissions from the engines will be discharged to atmosphere via
a 20m high stack.
Boiler Boiler unit used to provide heat when CHP not running and hot
water required in processes on site.
Gas Holder Double membrane biogas storage unit for biogas to maintain system
pressure.
Biogas Upgrade Plant (BUP) Plant to upgrade biogas to biomethane by separating methane from
carbon dioxide.
Gas Grid Entry Unit Unit to facilitate the injection of biomethane into the national gas
grid.
CO2 Liquefaction Plant CO2 from the BUP is diverted to this plant where it is processed into
food grade liquid CO2.
Gas Flare System
Closed flare system for use during initial commissioning and as a
backup facility during routine engine maintenance and safety
protection to over biogas over pressure
Control and Plant Room Plant to allow for provision of back-up power to the plant from the
national grid in the event the CHP plant on site not operating.
Weighbridges & Wheelwash Facilities to record incoming and outgoing vehicles and clean
vehicles on exit.
Parking Parking spaces for vehicles and bicycles.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 10
4. Construction
4.1 Construction Programme
Construction works will commence on site following completion of the design and procurement
process. The construction phase is expected to last up to two years (in tandem with commissioning at
its later stages). Construction will follow procedures and good practices as outlined in this oCEMP
and subsequent iterations.
The appointed Contractor will manage the site on a day-to-day basis and will be required to comply
with the measures included herein, as well as the Resource & Waste Management Plan (RWMP)
prepared for the site (Appendix A).
The Contractor will provide an outline of construction activities associated with the proposed
development and sequence within the CEMP. These would then be further supported by the
Contractor through the development of Method Statements which will addres s specific work elements
and packages.
Once all the equipment and systems are installed, the biogas plant must be commissioned. This
involves testing all the equipment and systems to ensure they are functioning properly and meeting
the plant's design specifications. This typically entails a commissioning period of 3 months.
4.2 Phasing of Works
The phasing of the works will be undertaken in consultation with relevant stakeholders as required.
There may also be seasonal constraints that may affect timing of works, such as bird nesting and/or
landscape planting periods. It will be a requirement upon the Contractor to plan for these
appropriately within the programme.
Construction of the proposed development will be undertaken broadly in-line with the indicative key
activity phases outlined in Table 4-1:
Table 4-1 Summary of key construction activities and sequence
Activity Sequence / Description Indicative
Timeline
Enabling Works • Establishment of site compounds, contractor facilities (offices,
welfare units, storage, parking).
• Erection of construction fencing/hoarding and installation of
traffic management measures.
• Initial surveying, setting-out and pre-earthworks drainage and
pollution controls.
• Utility diversions – ESB 10kV overhead line and telecom
infrastructure.
• Licensed archaeological excavation and preservation by record
of Archaeological Area AA1 prior to commencement of the
relevant construction works.
• Archaeological monitoring of topsoil stripping and initial ground
disturbance across the remainder of the Renewable Biogas
Plant site in accordance with Chapter 15 of the EIAR.
• Enabling works may occur in advance of, or overlap with, site
preparation activities.
Month 0-3
Site Preparation • Clearance of vegetation, topsoil stripping, and initial grading to
achieve development plateaus and stable working areas.
• Formation of temporary access routes and delivery areas; new
site access from the L2280 Drumcall Road, including localised
widening and partial realignment.
Month 2-8 RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 11
Activity Sequence / Description Indicative
Timeline
• Construction of temporary haul roads and storage areas.
• Soil arising from cut-and-fill works used to construct screening
berms along the south-eastern and north-western boundaries
and landscaping of same.
Site Utilities &
Infrastructure
• Excavation and installation of service trenches for utilities,
including water, power, telecoms and drainage.
• Utility installation may commence during site preparation and
continue into subsequent construction phases.
Month 2-12
Foundations • Excavation for foundations across the building platforms, tank
farm, feed bunker reception area and any underground
stormwater storage/attenuation.
• Installation of reinforced concrete foundations, comprising pad
footings integrated into concrete floor slabs.
• Ground levels will vary across the site (approx. 101.5 mAOD to
94.5 mAOD), with foundations established at formation level.
Month 4-12
Structural Works
& Building
Envelope
• Construction of concrete slabs and erection of steel or concrete
structural frames.
• Installation of external walls, cladding, roofing and insulation to
complete the building envelopes.
• Construction of the full tank farm, including all digester and
storage tanks.
• Formation of internal access routes, footpaths, and
parking/yard areas.
Month 10-18
Installation of
Plant &
Equipment (MEP)
• Installation of plant and equipment associated with the
anaerobic digestion process, including tanks, mechanical units,
pipework, and ancillary systems.
• Mechanical, electrical and plumbing works including process
systems, ventilation, lighting, power, water supply, drainage
and control systems.
Month 14-21
Commissioning • Full testing and calibration of all equipment, plant, and control
systems.
• Verification that operational, environmental, and safety
performance meet design specifications.
• Commissioning activities will be completed within the overall
construction period.
Month 21-24
Site-Wide
Landscaping &
Reinstatement
• Final re-grading of berms with topsoil, reinstatement of
disturbed areas and completion of all hard and soft
landscaping.
• Final planting of trees, shrubs and vegetation in accordance
with the Landscaping Mitigation Plan.
Month 21-24
4.3 Working Hours
In general, it is envisaged that construction work will take place during the following working hours:
► Weekday Working Hours: 07:00 to 19:00hrs;
► Saturday Working Hours: 08:00 to 14:00hrs; and
► Sunday & Bank Holidays: No work.
The Contractor may need to work outside these hours, particularly for setting-up traffic management
arrangements associated with works to the L2280/R189 or for the likes of plant delivery (including
abnormal loads) and installation. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 12
Any civil works outside of these hours would be carried out with the prior agreement of the MCC (as
necessary).
4.4 Enabling & Site Preparation Works
Enabling works would primarily involve establishing the site (i.e. materials/plant compounds), site
clearance works, erection of fencing and hoarding, installation of pollution control/pre -earthworks
drainage, setting-up of traffic management measures and diversion of utilities.
The Contractor would be required to establish and maintain effective liaison with the local community
throughout the construction phase. This would include information about ongoing activities and
provision of contact details to report incidents or for fur ther information. These aspects would be
addressed as part of the CEMP.
There are a range of underground and overhead services and utilities that pass adjacent to and
through the Renewable Biogas Plant site that would require diversion/accommodation during the
construction phase, normally at the request of the statutory undertaker. Such works would typically
take place in order to protect public supply or if there is potential for the existing services/utilities to
delay or interfere with the construction process.
These works will be carried out in accordance with Statutory Undertaker requirements (or they may
appoint their own contractor to undertake the works). This will largely be limited to the diversion of the
overhead electricity lines that pass through the site and overhead telecoms lines that pass along the
boundary.
The existing land drain along the central hedgerow currently conveys surface water from the adjacent
agricultural fields. This minor drain will become redundant as surface water will be managed through
engineered drainage systems, including SuDS and site-wide attenuation features designed to
replicate the existing hydrological function, once the site becomes operational. This hedgerow and
associated land drain will be removed during the enabling works with any drainage requirements
managed in accordance with the SSWMP until connected to the operational site drainage system.
Crossings of land drains by entrance roads will be suitably designed to ensure the diameter of
pipework is sufficient to accommodate the required flows.
A full archaeological excavation of a burnt mound (fulachta fiadh) will also be carried out in advance of
construction, under licence to the National Monuments Service (NMS) (Department of Housing, Local
Government and Heritage (DHLGH)), subject to their approval of a licence application and method
statement. See Chapter 15 – Cultural Heritage for further information.
4.5 Site Compounds, Materials & Plant Storage Areas
The Contractor’s construction compound will be established during the initial stage. This will comprise
of project offices (modular anti-vandal containers), equipment and material storage areas, welfare
facilities and designated car parking areas. There is sufficient space within the site to allow for
construction offices, associated compound and working space, without compromising buildability of
the proposed development. No additional land is anticipated to be needed to accommodate the
works, other than for services / utilities diversions / connections, which shall be undertaken by
agreement with the relevant statutory undertakers.
As shown on Figure 4-1, it is a reasonable assumption that the compound would initially be located in
the vicinity of the administration building/parking area (see blue area) to allow for grading in order to
establish a stable foundation and levels across the site. This location is adjacent to the site entrance,
thus providing easy site access and good connectivity to the public road network, minimising the need
for traffic movements throughout the site, which can be hazardous and require additional
management/accommodation.
Once the platforms/levels are all established and foundations in place, a secondary compound would
likely be accommodated on the upper platform (see red area on Figure 4-1) for accessibility to
materials and to eventually move the construction offices to allow for the admin building, car park, and
other necessary works to take place.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 13
Figure 4-1 Proposed Construction Compound Locations
In general working areas will need to be clearly defined and managed in a sympathetic manner in
accordance with best practice to prevent adverse impacts. In general, the following compound
requirements shall apply:
• Be located in an area of the site that will minimise visual impact;
• Avoid where possible sensitive receptors for noisy equipment;
• Not be located in areas of ecological importance;
• Storage of hydrocarbons or any liquid chemicals within the compound will not be within 10 m of a
watercourse. All fuel storage areas shall be bunded to 110% of capacity to contain the effects of
any spills;
• Have an appropriate level of security to minimise the risk of damage, such as chemical spills
caused by vandalism;
• All loading and unloading of vehicles shall take place on site. To protect the amenity of the area,
no loading or unloading of vehicles shall take place on the public road;
• The carrying of dust, mud or debris from the site arising from construction activities onto or
deposited on the public road or footpath(s) shall be minimised and appropriately managed;
• Concrete required for construction will likely be mixed off-site and imported to the site. Wash
down and washout of concrete transporting vehicles will take place at an appropriate location;
• Materials including precast concrete sections, ready mix concrete, structural steelwork, glazing,
and a range of mechanical and electrical components will be brought onto the site using road
vehicles. In so far as is practicable, construction materials will be sourced locally to minimise
associated transportation. All construction materials will be stored in the area designated prior to RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 14
their usage. Materials will be securely stored to prevent disturbance by site activities and weather
conditions;
• During the course of construction, covered skips or other such receptacles will be provided onsite
for the deposit therein of all rubbish, litter, packaging, rubble, and other such materials arising
from the works. The Contractor shall ensure that the site and its environments are maintained at
all times in a clean and tidy condition. No burning of waste materials shall take place on site;
• Access to the site will be via a dedicated point from the L2280. The Contractor will be conscious
of the user and access requirements in the vicinity of the tie-in location. The number and type of
construction vehicles/plant that are likely to use the access point and internal haul routes to the
compound and working areas will be detailed in the Contractor’s CEMP. This will be an important
aspect when moving materials to and from the site;
• Appropriate maintenance of the public road in the vicinity of the site access on the L2280 and
R189. This will be kept free of detritus and debris associated with construction activities; and
• Works that will be lit at night shall be done with light standards fitted with cut off horizontal cowls
to minimise light spill and direct light downwards.
4.6 Site Clearance
Site clearance would primarily involve removal of grassland, hedgerow and trees to facilitate
construction of the site access. There would be a requirement placed upon the Contractor to
minimise vegetation removal as much as possible and implement measures to protect retained
vegetation.
No retained trees shall be cut down, uprooted or destroyed, or have roots damaged within the crown
spread, nor shall arboricultural work or tree surgery take place on any retained tree other than in
accordance with the approved plans and particulars without written approval. Any arboricultural work
or tree surgery will be carried out in accordance with British Standard 3998 2010 ‘Recommendations
for Tree Work’.
To minimise the potential for adverse impacts to soil structure and quality during site clearance, the
following is an outline of the general mitigation measures that will be in place:
• Spoil material will be stored temporarily within the site. Any stockpiled material will be managed
in accordance with best practice guidelines (such as the latest version of ‘Construction Code of
Practice for the Sustainable Use of Soils on Construction Sites ’). When required, pre-earthwork
drainage will be put in place to avoid sediment being washed off site as outlined in this oCEMP;
• If shallow groundwater is encountered during below ground construction, suitable best practice
de-watering methods will be used ;
• Although considered unlikely given the existing site use, construction works will be carried out in
such a way as to prevent, contain or limit, as far as reasonably practicable, any adverse effects
arising from the presence of contaminated land or materials. Should contamination be identified,
MCC will be notified;
• The Contractor will be required to prepare a Construction Traffic Management Plan (CTMP) to
minimise site traffic and damage to soil structure from smearing and compaction; and
• A RWMP has been prepared (Appendix A), with an aim to minimise waste arising at source and,
where such waste generation is unavoidable, to maximise its recycling and reuse potential.
Recycling of materials will primarily take place off-site where noise and dust are more easily
managed and less likely to impact on surrounding receptors.
4.7 Fencing
As deemed appropriate by the Contractor, fencing would be installed where necessary to provide
increased levels of security (i.e. at site compounds).
The erection of fencing for the protection of any retained tree shall be undertaken in accordance with
the approved plans and particulars before any equipment machinery or materials are brought on to RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 15
the site for the purposes of the scheme and shall be maintained until all equipment machinery and
surplus materials have been removed from the site.
4.8 Earthworks (Borrow & Surplus Materials)
The earthworks model identifies approximately 98,420 m³ of excavated material, of which approximately
79,900 m³ of suitable excavated soil and stone will be reused within the Renewable Biogas Plant site
for engineering fill, landscaping and screening berms. This results in a net surplus of approximately
18,520 m³. For the purposes of the environmental assessments, this has been conservatively rounded
to approximately 18,600 m³ of surplus excavated soil and stone requiring removal from the site.
The surplus material will be removed off site by suitably authorised contractors for appropriate reuse,
recovery or disposal at an appropriately authorised receiving facility or facilities, to be identified by the
appointed Contractor prior to commencement of the relevant excavation works.
The Contractor will be required to have a response and contingency plan in place during the
earthworks programme and works. These will comply with relevant guidelines such as:
• CIRIA C811 (2023). ‘Environmental good practice on site guide (fifth edition)’; and
• CIRIA C532 (2002). ‘Control of Water Pollution from Construction Sites - Guide to Good
Practice’.
During the works, the Contractor shall ensure that stockpiling areas, storage areas, fuel stores, waste
disposal points, and refuelling areas, for example, are located where they are least likely to affect
surface waters / drains. Pollution prevention measures shall be implemented to minimise the risk of
contamination to surface waters / drains including:
• Appropriately located wheel washes with dedicated drainage and pollution collection sumps and
interceptors should be installed;
• Surface waters / drains shall not be permitted to flow onto the public road from the site, to
prevent the flooding of the public road;
• Existing roadside drainage arrangements will be preserved, to maintain proper roadside drainage
and to prevent the flooding of the public road; and
• Temporary runoff from exposed soils during the earthworks programme shall be managed with
appropriate mitigation measures.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 16
5. Environmental Management
The Contractor will develop the CEMP prior to commencement of construction works, which will
define the responsibilities, practices and procedures provided for environmental management. It will
be developed to help prevent environmental incidents and pollution, to encourage reduced
consumption of resources, to restrict the production of waste, and to promote good relationships with
the relevant authorities/environmental bodies. Commitments made regarding mitigation; their
implementation and subsequent monitoring will be recorded.
The CEMP will include method statements for operations. These will show how the proposed methods
of construction will minimise potential impacts on the environment. Outline management and
mitigation measures are provided in this section. A summary of environmental mitigation measures
incorporated within the Environmental Impact Assessment Report (EIAR) submitted as part of the
planning application is provided in Chapter 17 of the EIAR, which is included as Appendix B herein.
All mitigation measures relevant to construction activities will be adopted into the CEMP.
5.1 Roles & Responsibilities
As listed in Table 5-1, the CEMP will outline the environmental management structure for all staff,
including key roles and responsibilities. This will describe the name of each team member, their role
and their responsibility.
Table 5-1: Key Contractor Team Roles and Responsibilities (Indicative)
Role Responsibilities
Contractor’s Director
• Assign specific environmental duties to competent members of the Contractor’s
team;
• Identify the environmental training needs of personnel under their control and
arrange appropriate training programmes and ensure records are being maintained;
• Ensure that environmental construction risks identified for the proposed
development are managed; and
• Promote the continual improvement of environmental performance.
CEMP Coordinator
(CEMPc)
• Will be the point of contact for dealing with environmental issues for Stream’s
development team, the Contractor’s employees, sub-contractors, relevant
authorities/environmental bodies, and members of the public;
• Develop, maintain and audit the CEMP (and supporting documents/plans) to ensure
all aspects, impacts and statutory requirements are reflected in the Plan;
• Develop and implement a programme of regular project environmental inspections,
monitoring, recording and reporting in accordance with procedures set out in the
CEMP;
• Ensure that the works are constructed in line with the CEMP, in liaison as necessary
with the Site Manager and Stream’s development team/environmental advisors
(where relevant);
• Attend construction meetings to ensure environmental issues are discussed and
addressed by the Contractor’s team;
• Liaise with relevant authorities/environmental bodies and the local community as
required;
• Comply with duties under relevant legislation and company procedures in relation to
environmental incident investigation and reporting;
• Oversee monitoring of the works in respect of environmental requirements;
• Provide support and training to the workforce with regard to understanding
environmental aspects, impacts, regulatory requirements, best practice, constraints
and methods of working;
• Appoint environmental specialists (as required) and ensure they are in attendance
on-site as required by the CEMP; and
• Report all identified non-conformances to Stream’s development team, review non-
conformance reports to identify any underlying issues or patterns and apply
corrective action (as required). RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 17
Role Responsibilities
Site Manager
• Ensure that all personnel undergo suitable and sufficient environmental induction
before starting work on the project;
• Monitor the performance of personnel and activities under their control and ensure
arrangements are in place so that all personnel will work in a manner which
minimises risks to them and to the environment;
• Undertake a programme of regular project environmental inspections in liaison with
the CEMPc;
• Notify the relevant third parties where required and liaise with them as necessary as
to the outcome of the non-compliance;
• Complete any corrective actions identified by the CEMPc and provide status reports
as required to Stream’s development team;
• Assist and support the CEMPc and statutory bodies in the investigation of any
incidents; and
• Notify the CEMPc of all environmental issues or incidents arising over the course of
operations.
• Maintain records of environmental issues, events and consultations with third parties
and of training/inductions delivered to site staff.
Environmental
Specialists – if
required (i.e.
Ecological Clerk of
Works (ECoW))
• Attend site as required to monitor the protection of the asset/feature in accordance
with the requirements of relevant legislation, the construction contract and the
CEMP;
• Identify potential risks from construction activities to the asset/feature and develop
suitable control measures outlined within the CEMP;
• Provide status reports and updates to the CEMPc in the completion of their
activities; and
• Liaise with the CEMPc as required to provide specific training to site staff.
5.2 Air Quality Management
The Contractor will be required to implement measures to minimise the amount of dust produced
during the construction phase and develop a Dust Management Plan (DMP), which will be
incorporated into the CEMP. This must reflect the requirements of best practicable means and level of
risk, such as those included in the Institute of Air Quality Management (IAQM) ‘Guidance on the
assessment of dust from demolition and construction’ (January 2024), relevant CIRIA guidance and
EPA best practice guidance.
There will be a duty of care on the Contractor to ensure that dust-raising activities are located away
from sensitive receptors as much as feasibly possible, and duration kept to a minimum when in
proximity to a receptor.
In order to minimise air quality impact and dust nuisance occurring at sensitive receptors, a series of
mitigation measures (including those identified in the EIAR) shall be incorporated in the DMP,
including those identified in 5-2.
Table 5-2: Air Quality Management & Mitigation Measures
Issue Control Measure
Dust management • Planning site layout so that machinery and dust causing activities are located
away from receptors, as far as is practicably possible;
• Ensuring an adequate water supply on the site for effective dust
suppression;
• Appropriately manage materials with the potential to generate dust, including
covering, dampening or prompt off-site removal where removal is required.;
• Movement of material will be minimised to reduce potential for dust
generation;
• Using cutting, grinding, or sawing equipment fitted or in conjunction with
suitable dust suppression techniques;
• Covering, seeding or fencing stockpiles to prevent wind whipping; RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 18
• Ensuring sand and other aggregates are stored in bunded areas and are not
allowed to dry out;
• Avoid scabbling (roughening of concrete surfaces) if possible;
• Ensure bulk cement and other fine powder materials are delivered in
enclosed tankers and stored in silos with suitable emission control systems
to prevent escape of material and overfilling during delivery ;
• For smaller supplies of fine powder materials, ensure bags are sealed after
use and stored appropriately to prevent dust;
• Used enclosed chutes and conveyors and covered skips;
• Minimise drop heights from conveyors, loading shovels, hoppers and other
loading or handling equipment and use fine water sprays on such equipment
wherever appropriate;
• Ensure equipment is readily available on site to clean any dry spillages and
clean up spillages as soon as reasonably practicable after the event using
wet cleaning methods;
• Burning of waste materials not permitted;
• Avoid site runoff of water or mud;
• Keep site fencing, barriers and scaffolding clean using wet methods;
• Carrying out regular site inspections / monitoring;
• Recording all dust and air quality complaints, identify cause(s), taking
appropriate measures to reduce emissions in a timely manner, and record
the measures taken;
• Make complaints log available to MCC as required; and
• Increase frequency of site inspections when activities with a high potential
for dust are being carried out or during prolonged dry or windy conditions.
Operating
vehicle/machinery and
sustainable travel
• On site traffic will be restricted to 15 km/hour;
• Ensure all vehicles switch off engines when stationary, no idling vehicles;
and
• Avoid the use of diesel or petrol powered generators and use mains
electricity or battery powered equipment where practicable.
• Detailed method statements, plans and assessments will be produced to
carry out compressed gas activities safely.
• A Site Emergency Response Plan will be developed prior to the
commencement of operations and will include detailed procedures in the
event of a major accident.
Earthworks • Re-vegetate earthworks and exposed areas/soil stockpiles to stabilise
surfaces as soon as practicable;
• Use Hessian, mulches or tackifiers where it is not possible to re-vegetate or
cover with topsoil, as soon as is practicable; and
• Only remove the cover in small areas during work and not all at once.
Track-out • Implement a wheel washing system at the site exit;
• Inspect on-site haul routes for integrity and instigate necessary repairs to the
surface as soon as reasonably practicable;
• Site roads will be regularly cleaned and maintained as appropriate;
• Unsurfaced roads will be restricted to essential site traffic only;
• Ensure vehicles entering and leaving sites are covered to prevent escape of
materials during transport;
• Use water-assisted dust sweepers on the access and local roads, to remove,
as necessary, any material tracked out of the site; and
• Avoid dry sweeping of large areas.
5.3 Cultural Heritage
Prior to commencement of the relevant construction works, Archaeological Area AA1 will be subject to
full licensed archaeological excavation and preservation by record in accordance with the requirements
of the National Monuments Service and Chapter 15 Cultural Heritage of the EIAR. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 19
Following completion of the licensed excavation of AA1, topsoil stripping and other initial ground
disturbance across the remainder of the Renewable Biogas Plant site will be subject to archaeological
monitoring by a suitably qualified archaeologist under the appropriate licence.
Should previously unidentified archaeological material be encountered, works in the affected area will
cease pending assessment by the project archaeologist and consultation with the National Monuments
Service. Any further measures required will be underta ken in accordance with the applicable statutory
requirements.
.
5.4 Waste Management
The Contractor will manage resources and waste on site in accordance with the RWMP, provided in
Appendix A, which will be included as part of the CEMP.
As a minimum, the Contractor will ensure the collection of wastes from the site will be undertaken by
suitably authorised waste hauliers and would only be recycled/recovered or disposed of at suitably
licenced waste facilities. The waste contractor(s) appointed for the works will have experience in
construction waste management and will be appropriately licenced, holding the relevant waste
collection permit and/or waste licences for the types of waste anticipated to be generated during
construction work.
5.5 Water Management
The CEMP will include surface water management measures to be implemented by the Contractor
during the construction stage to prevent run off onto the public road network and/or pollution of local
drains, surface water and/or groundwater. A standalone Soil and Surface Water Management Plan
has been included within Appendix C.
Measures to protect the water environment would be formulated in accordance with best practice
guidance, such as EPA best practice guidance and specific water related construction guidance
documentation such as CIRIA C741 ‘Environmental Good Practice Guide (5th Edition)’ and CIRIA
C532 ‘Control of water pollution from construction sites: guidance for consultants and contractors’
(Masters-Williams et al., 2001), including those outlined in Table -3.
Table 5-3: Water Management & Mitigation Measures
Issue Control Measure
General Water
management
• Identify potential pollution pathways and receptors on site;
• Define suitable controls to prevent pollution entering pathways and reaching
receptors;
• Identify temporary drainage patterns on site where interceptor channels and
site drainage towards settlement features should be;
• Protect local drains using appropriate measures (refer to Soil and Surface
Water Management Plan); and
• Gain any appropriate consents (if required) and put measures in place to fulfil
the requirements of the consent.
Managing Run-Off • Minimise, where possible, the amount of exposed earth;
• Maintain a buffer strip to protect surface water (minimum of 5m);
• Regularly check waters for signs of pollution; and
• Prevent direct surface water run-off into drains.
Spillage Prevention • Store fuel, oil and chemicals away from drains and water bodies, and in
secondary containment in accordance with the appropriate pollution prevention
regulations (i.e. CIRIA). Storage will not be within 10 m of a watercourse and
will be bunded to 110% of capacity of the largest tank or 25% of the total
volume stored, whichever is the larger to contain the effects of any spills; RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 20
Issue Control Measure
• Store solvents, chemicals or paints in accordance with their COSHH
datasheets and oil storage regulations; and
• Implement procedures for storage, use, delivery, inspection and monitoring of
polluting substances.
• Where mobile fuel bowsers used, then:
─ Any flexible pipe, tap or valve will be fitted with a lock and will be secured
when not in use;
─ The pump or valve will be fitted with a lock and will be secured when not in
use;
─ All bowsers to carry a spill kit and relevant operatives must have spill
response training;
─ Portable generators or similar fuel containing equipment will be placed on
suitable drip trays.
• Clear labelling of containers so that appropriate remedial measures can be taken
in the event of a spillage;
• All drums to be quality approved and manufactured to a recognised standard;
• If drums are to be moved around the Site, they will be secured and on spill
pallets; and
• Drums will be loaded and unloaded by competent and trained personnel using
appropriate equipment.
Monitoring • Undertake regular visual inspection of watercourses on and near to the site for
signs of pollution;
• Undertake regular checks of outfalls and pipework to ensure they are clean
and clear of litter;
• Monitor and investigate any complaints, incidents and near-miss occurrences;
and
• Monitor bunds and machinery for leaks.
• Visual inspection of excavation works to monitor for any visible contamination.
• Environmental testing of excavated material where required to establish its
classification or suitability for a proposed receiving facility.”.
Emergency Preparedness
& Response
• Ensure site-based staff know who to contact in the event of a spillage, what to
do and from where to get equipment;
• Ensure appropriate spill kits are available (e.g. oil only, chemical or general
use) and adequately stocked;
• Adopt and test an emergency response plan/procedure; and
• Report environmental damage that cannot be rectified immediately to the
environmental regulator and take appropriate steps to remedy the damage
caused.
5.6 Noise and Vibration Management
The Contractor shall prepare a Noise and Vibration Management Plan to be included in the CEMP.
Noise and vibration will be controlled and limited so far as reasonably practicable so that sensitive
receptors are protected from excessive noise and vibration arising from construction.
Construction noise monitoring will be undertaken, where required, at appropriate noise -sensitive
locations in accordance with the construction noise criteria, assessment methodology and monitoring
requirements set out in Chapter 12 Noise and Vibration of t he EIAR.
Measures included in the Noise and Vibration Management Plan may include the following:
• Works will be phased in as much as possible to avoid noise at the site perimeter;
• Compressors brought on to the site to be silenced, or sound reduced models fitted with acoustic
enclosures;
• Pneumatic tools to be fitted with silencers or mufflers; RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 21
• Care to be taken when erecting or striking scaffolds to avoid impact noise from banging steel. All
operatives undertaking such activities to be instructed on the importance of handling the
scaffolds to reduce noise to a minimum;
• The majority of deliveries to be programmed to arrive during normal working hours only. Care to
be taken when unloading vehicles to minimise noise. Delivery vehicles to be routed so as to
minimise disturbance to local residents. Delivery vehicles to be prohibited from waiting within or
in the vicinity of the site with their engines running;
• Plant items to be properly maintained and operated according to manufacturers’
recommendations in such a manner as to avoid causing excessive noise;
• Plant to be sited so that the noise impact at nearby noise sensitive properties is minimised; and
• Implementing guidance set out in BS5228-1, which covers noise control on construction sites.
5.7 Landscape and Ecology Management
The berm fronting the public road will be constructed and verified in line with standard geotechnical
engineering practices. Material quality, compaction, and slope stability will be inspected and signed off
by a qualified engineer prior to handover.
The Contractor shall prepare a Landscape and Ecology Aftercare Plan to be implemented for 3 full
growing seasons after planting or 3 years after completion of the site, whichever is the longer. The
plan shall be included as part of the CEMP and shall include, without limitation, the following:
• Protection, management and maintenance of existing retained vegetation; and
• Protection, management and maintenance of new planting, seeding and habitat creation
areas.
Mitigation measures shall be implemented throughout the works area to manage potential impacts to
biodiversity. These shall include requirements on the Contractor to carry out the following:
• Consult and comply with the requirements of the planning conditions or statutory bodies with
respect to any sites or species protected by law, which are likely to be affected by the
construction, establishment and maintenance of the site;
• Comply with relevant biodiversity related legal requirements that give protection to a wide range
of plants, animals and birds, when undertaking any works which will affect protected species;
• No works shall be undertaken to any tree, hedge or other habitat in which any birds may be
nesting;
• The Contractor will be responsible for agreeing and implementing appropriate mitigation
measures, as detailed in the EIAR, and any other relevant documentation. A summary of the
EIAR mitigation measures is as following:
─ Pre-clearance ecological checks will be undertaken where required prior to vegetation
removal. If an active bird nest is identified, works capable of affecting the nest will cease and
appropriate exclusion and/or timing measures will be established by the ECoW. If a potential
or confirmed bat roost is identified, the relevant works will cease pending assessment by a
suitably qualified bat ecologist. Any requirement for licensing will be determined in accordance
with the applicable statutory requirements and, where appropriate, in consultation with NPWS.
─ . The ECoW will oversee necessary ditch trenching work to install the culverts identified as
being required with the CEMP detailing measures to be implemented during these works;
─ A protective development-free buffer of between 5 m and 12 m from all retained hedgerows
and trees has been designed into the proposed development, to be installed during the
construction phase;
─ Hedgerows will be enhanced through supplementary planting of native species and a
sensitive management regime used to enhance existing hedgerows for wildlife;
─ Planting of native wildflower meadow mix, native woodland mix, and native hedgerow
species as shown and detailed on the Landscape Mitigation Plan (Drawing LD.DRM.1.1). RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 22
─ Root protection zones of hedgerows and trees to be retained will be protected in order to
maintain any bat foraging and commuting potential. A minimum 10 m buffer will be
maintained around a tree located in the eastern boundary hedgerow identified to offer bat
potential to prevent disturbance;
─ The CEMP will detail nest avoidance precautions to be taken during the construction phase;
─ Where hedgerows and trees are to be removed, these will be cut to a minimum of 30 cm
above ground level over winter months to avoid impacts to nesting birds during the nesting
bird season;
─ Surface water / drain protective measures will be implemented to include the installation of
silt fences to minimise the risk of accidental pollution or sediment mobilisation ;
• The Contractor will provide method statements (including programming of activities) for approval
by Stream’s development team prior to works commencing. Works shall not start without agreed
method statements in place;
• The Contractor shall be responsible for ensuring all site workers are briefed on the ecological
sensitivities of the site and its environs through ‘toolbox talks’ and provision of clear information
about protected species and restricted areas and activities; and
• The Contractor shall produce a method statement for any works in close proximity to
watercourses. The method statement will include measures to prevent adverse impacts on
riparian habitats and should comply with the Water Management Plan. Work within or close to
river channels should be avoided where practicable.
5.8 Construction Traffic Management Plan
Construction access for the works area will utilise the existing access off the L2280 site frontage with
minor modifications such that it can suitably accommodate all construction vehicles entering and
exiting the site.
The Contractor will prepare a CTMP which will minimise the risk of traffic congestion on local roads
and maintain safety around the local road network associated with site traffic . This will improve the
safety for road users, limit congestion and reduce the carbon footprint of the staff where possible. The
CTMP will be included as part of the CEMP and its objectives will be to:
• Reduce journeys to and from the site;
• Identify measures aimed at avoiding disruption and inconvenience to local residents , businesses
and transient users of the area;
• Ensure safety of journeys to and from the site and plan on-site routes, one-way systems and
turning circles;
• Monitor compliance with speed limits;
• Communicate road restrictions either through road works, narrow roads and bridges with height
and/or weight restrictions;
• Identify suitable locations for parking facilities for private cars and plant, and minimise the
amount of car parking required;
• Identify sensitive areas;
• Prepare on-site roads to prevent dust and choose suitable materials for use on access roads - to
avoid transferring mud and dust;
• Ensure there are designated walkways on and around site;
• Ensure there are designated vehicular routes on-site with speed restrictions with access clearly
signposted;
• Ensure only designated access points and access roads will be used by site vehicles;
• Manage permission for road closure (if required) and ensure it is carried out by a competent
person;
• Develop a map showing delivery drivers' routes to site; RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 23
• Where possible, schedule site deliveries outside times of peak traffic volume;
• Have designated workers on-site to receive deliveries, direct vehicles on and off site, and act as
banksmen;
• Monitor vehicle movements to reduce the likelihood of queuing or causing congestion in and
around the local area; and
• Minimise the need for reversing vehicles (i.e. one-way systems) and potential nuisance issues
from reversing alarms.
The plan will be implemented from the date of start of site works and will be regularly monitored to
ensure that it is being adhered to and targets are being met. The CTMP will be prepared in
accordance with ‘The Essential Guide to Travel Planning’ published by the Department for Transport
and CIRIA's ‘Environmental good practice on site guide’ (C741).
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Maghernakelly, Drum, County Monaghan
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oCEMP 24
6. Reporting, Monitoring and Auditing
6.1 Reporting and Record Keeping
The Contractor should ensure that appropriate, detailed records are maintained during the
construction phase. Environmental records would include waste and site inspection records,
monitoring reports and where relevant, environmental incident and complaints records. In the event of
an environmental incident occurring at the site with the potential to cause environmental pollution, the
Site Manager or the CEMPc would notify the Stream development team and the relevant third parties,
as soon as practicable.
Any complaints and/or incidents would be reported to the CEMPc. The CEMPc would be responsible
for developing and maintaining a register of complaints and a register of incidents, with details on
follow-up actions.
6.2 Environmental Performance Monitoring
The CEMP Coordinator and relevant environmental specialists will undertake inspections and
monitoring in accordance with the CEMP and associated management plans. This will include
monitoring of construction traffic and compliance with agreed routing and d elivery arrangements;
maintenance of records relating to waste generation, classification, transport and destination; inspection
of soil, surface water, sediment and pollution-prevention controls; and environmental testing of
excavated material where required to establish its classification or suitability for a proposed receiving
facility. Construction noise and dust monitoring will be undertaken in accordance with Chapters 12 and
13 of the EIAR respectively.
Ecological supervision and monitoring will be undertaken by the ECoW and/or site environmental
personnel as required, including oversight of relevant vegetation clearance and ecological protection
measures. Archaeological monitoring will be undertaken in accordance with Chapter 15 of the EIAR.
The CEMP Coordinator will maintain appropriate environmental inspection and monitoring records and
will communicate environmental performance, incidents and any corrective actions through regular site
meetings.
6.3 Community Engagement & Liaison
The CEMP will include a strategy for proactive engagement with the local community and businesses
throughout the construction phase. This will include clear communication channels, points of contact,
advance notification of potentially disruptive works, and a procedure for addressing any concerns
residents or stakeholders raise.
7. Conclusion
This oCEMP has been prepared to demonstrate the commitment of Stream to environmental
management at the Proposed Development Site and outlines the work practices and control
measures that would be implemented by the Contractor throughout the construction phase to ensure
that potential environmental impacts are effectively managed, reduced or eliminated. The oCEMP and
subsequent CEMP are considered “live” documents and will be reviewed and updated as appropriate
as construction works progress.
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Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
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oCEMP 25
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Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 26
Appendix A - Resource & Waste Management Plan RECEIVED: 28/08/2026
Appendix 8.1 Resource & Waste Management Plan
Project Title: Proposed Renewable Biogas Plant, Maghernakelly Drum, County Monaghan
CLIENT
Stream
BioEnergy
Ireland Ltd
DOCUMENT REFERENCE
247501.0350WMR01a
DATE
10/07/2026
AWN Consulting Ltd, The Tecpro Building, IDA Business & Technology Park, Clonshaugh, Dublin 17, D17 XD90
REPORT
RECEIVED: 28/08/2026
DOCUMENT CONTROL SHEET
Document Control Sheet
Our Reference 247501.0350WMR01a
Original Issue Date 25/11/2025
Client: Stream BioEnergy Ireland Ltd
Revision Revision Date Description
a 10/07/2026 Design Update
Details Written by Approved by
Signature
Name Chonaill Bradley Fergal Callaghan
Title Principal Environmental Consultant Director
Date 10/07/2026 10/07/2026
Disclaimer
This report considers the specific instructions and requirements of our client. It is not intended for third -party
use or reliance, and no responsibility is accepted for any third party. The provisions in this report apply solely
to this project and should not be assumed applicable to other developments without review and modification. RECEIVED: 28/08/2026
Stream BioEnergy Ireland Ltd / 247501.0350WMR01a
AWN Consulting Ltd
TABLE OF CONTENTS
1. INTRODUCTION 1-1
2. OVERVIEW OF WASTE MANAGEMENT IN IRELAND 2
2.1 National level ........................................................................................................... 2
2.2 Regional Level .......................................................................................................... 3
2.3 Legislative Requirements ......................................................................................... 5
3. DESIGN APPROACH 6
3.1 Designing For Prevention, Reuse and Recycling ....................................................... 6
3.2 Designing for Green Procurement ............................................................................ 6
3.3 Designing for Off-Site Construction ......................................................................... 7
3.4 Designing for Materials Optimisation During Construction ...................................... 7
3.5 Designing for Flexibility and Deconstruction ............................................................ 7
4. DESCRIPTION OF THE DEVELOPMENT 8
4.1 Location, Size and Scale of the Development ........................................................... 8
4.2 Details of the Non-Hazardous Wastes to be Produced ........................................... 10
4.3 Potential Hazardous Wastes Arising ....................................................................... 11
4.3.1 Contaminated Soil ............................................................................................... 11
4.3.2 Fuel/Oils ............................................................................................................ 11
4.3.3 Invasive Plant Species ......................................................................................... 11
4.3.4 Asbestos ............................................................................................................ 12
4.3.5 Other Known Hazardous Substances ..................................................................... 12
5. ROLES AND RESPONSIBILITIES 13
5.1 Role of the Client ................................................................................................... 13
5.2 Role of the Client Advisory Team ........................................................................... 13
5.3 Future Role of the Contractor ................................................................................ 13
6. KEY MATERIALS & QUANTITIES 15
6.1 Project Resource Targets ....................................................................................... 15
6.2 Main Construction Waste Categories ..................................................................... 15
6.3 Demolition Waste Generation ................................................................................ 16
6.4 Construction Waste Generation ............................................................................. 16
6.5 Proposed Resource and Waste Management Options ............................................ 17
6.6 Tracking and Documentation Procedures for Off-Site Waste ................................. 20
7. ESTIMATED COST OF WASTE MANAGEMENT 21
7.1 Reuse ..................................................................................................................... 21
7.2 Recycling ............................................................................................................... 21
7.3 Disposal ................................................................................................................. 21
8. TRAINING PROVISIONS 22
8.1 Resource Manager Training and Responsibilities ................................................... 22
8.2 Site Crew Training .................................................................................................. 22
9. TRACKING AND TRACING / RECORD KEEPING 23
10. OUTLINE WASTE AUDIT PROCEDURE 24
10.1 Responsibility for Waste Audit ............................................................................... 24
10.2 Review of Records and Identification of Corrective Actions ................................... 24
10.3 Pest Management .................................................................................................. 24 RECEIVED: 28/08/2026
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11. CONSULTATION WITH RELEVANT BODIES 25
11.1 Local Authority ....................................................................................................... 25
12. CONCLUSION 26
13. REFERENCES 27
LIST OF TABLES
Table 6.1 Typical waste types generated and LoW codes (individual waste types may contain hazardous
substances) 15
Table 6.2 Waste materials generated on a typical Irish construction site 16
Table 6.3 Predicted on and off-site reuse, recycle and disposal rates for construction waste 16
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1. INTRODUCTION
AWN Consulting, a Trinity Consultants Team, has prepared this Construction and Demolition (C&D)
Resource & Waste Management Plan (RWMP) on behalf of Stream BioEnergy Ireland Ltd. The proposed
development will utilise anaerobic digestion (AD) (the Proposed Development) technology to generate
renewable energy in the form of biomethane from up to 99,000 tonnes of feedstock per annum consisting
of poultry manure along with cattle manure, and agri-food organic waste feedstock, sourced from the
surrounding area.
AD is a sustainable form of renewable energy production that occurs when micro-organisms break down
biodegradable material in the absence of oxygen in an enclosed system to produce a renewable biogas.
A full description is included in the Description of the Proposed Development Chapter of this EIAR and in
the statutory notices.
This plan provides information necessary to ensure that the management of C&D waste at the site is
undertaken in accordance with the current legal and industry standards including the Waste Management
Act 1996 as amended and associated Regulations 1, Environmental Protection Agency Act 1992 as
amended 2, Litter Pollution Act 1997 as amended 3,the National Waste Management Plan for a Circular
Economy 2024 - 2030 (NWMPCE) (2024) 4. In particular, this plan aims to ensure maximum recycling,
reuse and recovery of waste with diversion from landfill, wherever possible. It also provides appropriate
measures in relation to the collection and transport of waste from the site to prevent issu es associated
with litter or more serious environmental pollution (e.g. contamination of soil and/or water).
This RWMP includes information on the legal and policy framework for C&D waste management in Ireland,
estimates of the type and quantity of waste to be generated by the proposed plant and prescribes
measures for the management of different waste streams. The RWMP should be viewed as a live document
and will be regularly revisited throughout the project’s lifecycle so that opportunities to maximise waste
reduction / efficiencies are exploited throughout, and that data is collected on an ongoing basis so that it
is as accurate as possible.
This RWMP relates to construction of the Renewable Biogas Plant and associated works forming the
Proposed Development. Construction waste associated with the Linear Gas Grid Connection will be
managed separately by Gas Networks Ireland in accordance with its applicable construction, environmental
and waste management procedures.
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2. OVERVIEW OF WASTE MANAGEMENT IN IRELAND
2.1 National level
The Irish Government issued a policy statement in September 1998, Changing Our Ways 5, which identified
objectives for the prevention, minimisation, reuse, recycling, recovery and disposal of waste in Ireland.
The target for C&D waste in this report was to recycle at least 50% of C&D waste within a five year period
(by 2003), with a progressive increase to at least 85% over fifteen years (i.e. 2018).
In response to the Changing Our Ways report, a task force (Task Force B4) representing the waste sector
of the already established Forum for the Construction Industry, released a report entitled ‘Recycling of
Construction and Demolition Waste’ 6 concerning the development and implementation of a voluntary
construction industry programme to meet the Government’s objectives for the recovery of C&D waste.
In September 2020, the Irish Government published a policy document outlining a new action plan for
Ireland to cover the period of 2020-2025. This plan, ‘A Waste Action Plan for a Circular Economy’ 7
(WAPCE), replaces the previous national waste management plan, “A Resource Opportunity” (2012), and
was prepared in response to the ‘European Green Deal’ which sets a roadmap for a transition to an altered
economical model, where climate and environmental challenges are turned into opportunities.
The WAPCE sets the direction for waste planning and management in Ireland up to 2025. This reorientates
policy from a focus on managing waste to a much greater focus on creating circular patterns of production
and consumption. Other policy statements of a number of public bodies already acknowledge the circular
economy as a national policy priority.
The policy document contains over 200 measures across various waste areas including circular economy,
municipal waste, consumer protection and citizen engagement, plastics and packaging, construction and
demolition, textiles, green public procurement and waste enforcement.
One of the first actions to be taken was the development of the Whole of Government Circular Economy
Strategy 2022-2023 ‘Living More, Using Less’ (2021) 8 to set a course for Ireland to transition across all
sectors and at all levels of Government toward circularity and was issued in December 2021. It is
anticipated that the Strategy will be updated in full every 18 months to 2 years.
The Circular Economy and Miscellaneous Provisions Act 2022 9 was signed into law in July 2022. The Act
underpins Ireland’s shift from a "take-make-waste" linear model to a more sustainable pattern of
production and consumption, that retains the value of resources in our economy for as long as possible
and that will work to significantly reduce our greenhouse gas emissions. The Act defines Circular Economy
for the first time in Irish law, incentivises the use of recycled and reusable alternatives to wasteful, single-
use disposable packaging, introduces a mandatory segregation and incentivised charging regime for
commercial waste, streamlines the national processes for End-of-Waste and By-Products decisions,
tackling the delays which can be encountered by industry, and supporting the availability of recycled
secondary raw materials in the Irish market, and tackles illegal fly-tipping and littering.
The Environmental Protection Agency (EPA) of Ireland issued ‘Best Practice Guidelines for the Preparation
of Resource & Waste Management Plans for Construction & Demolition Projects’ in November 2021 10.
These guidelines replace the previous 2006 guidelines issued by The National Construction and Demolition
Waste Council (NCDWC) and the Department of the Environment, Heritage and Local Government
(DoEHLG) in 2006 11. The guidelines provide a practical approach which is informed by best practice in
the prevention and management of C&D wastes and resources from design to construction of a project,
including consideration of the deconstruction of a project. These guidelines have been followed in the
preparation of this document and include the following elements:
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► Predicted C&D wastes and procedures to prevent, minimise, recycle and reuse wastes;
► Design teams roles and approach;
► Relevant EU, national and local waste policy, legislation and guidelines;
► Waste disposal/recycling of C&D wastes at the site;
► Provision of training for Resource Waste Manager (RM) and site crew;
► Details of proposed record keeping system;
► Details of waste audit procedures and plan; and
► Details of consultation with relevant bodies i.e. waste recycling companies, Local Authority, etc.
Section 3 of the Guidelines identifies thresholds above which there is a requirement for the preparation of
a bespoke RWMP for developments. The new guidance classifies developments on a two -tiered system.
Developments which do not exceed any of the following thresholds may be classed as Tier 1 development,
which require a simplified RWMP:
► New residential development of less than 10 dwellings.
► Retrofit of 20 dwellings or less.
► New commercial, industrial, infrastructural, institutional, educational, health and other developments
with an aggregate floor area less than 1,250m2.
► Retrofit of commercial, industrial, infrastructural, institutional, educational, health and other
developments with an aggregate floor area less than 2,000m2; and
► Demolition projects generating in total less than 100m3 in volume of C&D waste.
A development which exceeds one or more of these thresholds is classed as Tier-2 development.
The Proposed Development is classified as a Tier 2 project having regard to its scale and nature and the
applicable EPA thresholds. Accordingly, this bespoke RWMP has been prepared in accordance with the
requirements for Tier 2 projects set out in the EPA Guidelines.
Other guidelines followed in the preparation of this report include ‘Construction and Demolition Waste
Management – a handbook for Contractors and Site Managers’ 12 , published by FÁS and the Construction
Industry Federation in 2002 and the previous guidelines, ‘Best Practice Guidelines for the Preparation of
Waste Management Plans for Construction and Demolition Projects’ (2006).
These guidance documents are considered to define best practice for C&D projects in Ireland and describe
how C&D projects are to be undertaken such that environmental impacts and risks are minimised and
maximum levels of waste recycling are achieved.
2.2 Regional Level
The Proposed Development is located in the Local Authority area of Monaghan County Council (MCC).
The Connacht-Ulster Region (CUR) Waste Management Plan 2015 – 2021, which previously governed
waste management policy in the MCC area, has been superseded as of March 2024 by the NWMPCE
2024 – 2030, the national waste management plan for Ireland.
The NWMPCE does not dissolve the three regional waste areas. The NWCPCE sets the ambition of the
plan to have a 0% total waste growth per person over the life of the Plan with an emphasis on non -
household wastes including waste from commercial activities and the construction and demolition sector.
This Plan seeks to influence sustainable consumption and prevent the generation of waste, improve the
capture of materials to optimise circularity and enable compliance with policy and legislation.
The national plan sets out the following strategic targets for waste management in the country that are
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National Targets
1B. (Construction Materials) 12% Reduction in Construction & Demolition Waste Generated by 2030.
3B. (Reuse Facilities) Provide for reuse at 10 Civic Amenity Sites, minimum.
Municipal landfill charges in Ireland are based on the weight of waste disposed. In the Region, charges
are approximately €140-160 per tonne of waste, which includes a €85 per tonne landfill levy introduced
under the Waste Management (Landfill Levy) (Amendment) Regulations 2015 (as amended)13. The Circular
Economy (Waste Recovery Levy) Regulations 2024 14 will also incur a levy of €10 per tonne for waste
accepted for recovery. This will include backfilling at authorised recovery sites and at municipal waste
landfills.
The Monaghan County Council Development Plan 2025 – 2031 (2025) 15 sets out a number of objectives
and policies for the Monaghan area in line with the objectives of the National Waste Management Plan,
including the following:
Waste Management Objectives
► WMO 1 To implement and support the strategic objectives of the National Waste Management Plan
for a Circular Economy 2024-2030 and any new or updated/subsequent versions.
► WMO 2 To implement the provisions of the Litter Management Plan 2021 – 2023 and any new or
updated/subsequent versions.
► WMO 3 To apply the ‘Polluter Pays’ Principle, proximity principle, and the precautionary principle in
respect of all waste management activities.
► WMO 4 To encourage best environmental practice in all agricultural, industry, business and local
authority activities.
► WMO 5 To support the circular and bioeconomy through the efficient use of resources and to support
any development proposals which contribute to this concept.
► WMO 6 To support the minimisation of waste creation and promote a practice of reduce , reuse and
recycle where possible, and to safeguard the environment by seeking to ensure that residual waste
is disposed of appropriately.
► WMO 8 To require that treatment/management of any contaminated material shall comply as
appropriate with the Waste Management Act 1996 (waste licence, waste facility permit) and under
the Environmental Protection Act 1992 (Industrial Emissions licensing, in particular the First Schedule,
Class 11 Waste).
► WMO 9 To ensure that all new waste management infrastructure is sited in accordance with the
provisions of the Waste Management Infrastructure Guidance for Siting Waste Management Facilities
included within the National Waste Management Plan for a Circular Economy 2024-2030.
► WMO 10 To have regard to the National Enforcement Priorities in the area of waste enforcement.
► WMO 12 To promote the sustainable management of poultry and other agricultural wastes through
renewable energy facilities to reduce nutrient runoff, improve water quality, minimise greenhouse
gas emissions, and support energy generation, while ensuring the protection of local and water
resources.
Waste Management Policies
► WMP 1 All proposals relating to management and disposal of Construction and Demolition
Materials and Waste must adhere to the Environmental Protection Agency Best Practice Guidelines
for the preparation of Resource and Waste Management Plans for Construction and Demolition
Projects 2024, and any new or updated/subsequent versions. RECEIVED: 28/08/2026
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2.3 Legislative Requirements
The primary legislative instruments that govern waste management in Ireland and applicable to the
development are:
► Waste Management Act 1996 as amended;
► Environmental Protection Agency Act 1992 as amended;
► Litter Pollution Act 1997 as amended;
► Planning and Development Act 2000 as amended 16;
► Circular Economy and Miscellaneous Provisions Act 2022.
One of the guiding principles of European waste legislation, which has in turn been incorporated into the
Waste Management Act 1996 as amended and subsequent Irish legislation, is the principle of “Duty of
Care”. This implies that the waste producer is responsible for waste from the time it is generated through
until its legal recycling, recovery or disposal (including its method of disposal). As it is not practical in most
cases for the waste producer to physically transfer all waste from where it is produced to the final
destination, waste contractors will be employed to physically transport waste to the final destination.
Following on from this is the concept of “Polluter Pays” whereby the waste producer is liable to be
prosecuted for pollution incidents, which may arise from the incorrect management of waste produced,
including the actions of any contractors engaged (e.g. for transportation and disposal/recovery/recycling
of waste).
It is therefore imperative that the Developer ensures that the waste contractors engaged by construction
contractors are legally compliant with respect to waste transportation, recycling, recovery and disposal.
This includes the requirement that a contractor handle, transport and recycle/recover/dispose of waste in
a manner that ensures that no adverse environmental impacts occur as a result of any of these activities.
A collection permit to transport waste must be held by each waste contractor which is issued by the
National Waste Collection Permit Office (NWCPO). Waste receiving facilities must also be appropriately
permitted or licensed. Operators of such facilities cannot receive any waste, unless in possession of a
Certificate of Registration (COR) or waste permit granted by the relevant Local Authority under the Waste
Management (Facility Permit & Registration) Regulations 2007 as amended or a Waste Licence granted by
the EPA. The COR / permit / licence held will specify the type and quantity of waste able to be received,
stored, sorted, recycled, recovered and/or disposed of at the specified site. RECEIVED: 28/08/2026
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3. DESIGN APPROACH
The client and the design team have integrated the ‘Best Practice Guidelines for the Preparation of
Resource & Waste Management Plans for Construction & Demolition Projects’ guidelines into the design
workshops, to help review processes, identify and evaluate resource reduction measures and investigate
the impact on cost, time, quality, buildability, second life and management post construction. Further
details on these design principals can be found within the aforementioned guidance document.
The design team have undertaken the design process in line with the international best practice principles
to firstly prevent wastes, reuse where possible and thereafter sustainably reduce and recover materials.
The below sections have been the focal point of the design process and material selections and will
continued to be analysed and investigated throughout the design process and when selecting material.
As noted in the EPA guidelines, the approaches presented are based on international principles of
optimizing resources and reducing waste on construction projects through:
► Prevention;
► Reuse;
► Recycling;
► Green Procurement Principles;
► Off-Site Construction;
► Materials Optimisation; and
► Flexibility and Deconstruction.
3.1 Designing For Prevention, Reuse and Recycling
Undertaken at the outset and during project feasibility and evaluation the Client and Design Team
considered:
► Establishing the potential for any reusable site assets (buildings, structures, equipment, materials,
soils, etc.);
► The potential for refurbishment and refit of existing structures or buildings rather than demolition
and new build (No demolition required);
► Assessing any existing buildings on the site that can be refurbished either in part or wholly to meet
the Client requirements ; and
► Enabling the optimum recovery of assets on site.
3.2 Designing for Green Procurement
Waste prevention and minimisation pre-procurement have been discussed and will be further discussed in
this section. The Design Team will discuss proposed design solutions, encourage innovation in tenders and
incentivise competitions to recognise sustainable approaches. They will also discuss options for packaging
reduction with the main Contractor and subcontractors/suppliers using measures such as ‘Just -in-Time’
delivery and use ordering procedures that avoid excessive waste. The Green procurement extends from
the planning stage into the detailed design and tender stage and will be an ongoing part of the long-term
design and selection process for this development.
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3.3 Designing for Off-Site Construction
Use of off-site manufacturing has been shown to reduce residual wastes by up to 90% (volumetric building
versus traditional). The decision to use offsite construction is typically cost led but there are significant
benefits for resource management. Some further considerations for procurement which are being
investigated as part of the design process are listed as follows:
► Modular buildings as these can displace the use of concrete and the resource losses associated with
concrete blocks such as broken blocks, mortars, etc.;
• Modular buildings are typically pre-fitted with fixed plasterboard and installed insulation,
eliminating these residual streams from site.
► Use of pre-cast structural concrete panels which can reduce the residual volumes of concrete blocks,
mortars, plasters, etc.;
► The use of prefabricated composite panels for walls and roofing to reduce residual volumes of
insulation and plasterboards;
► Using pre-cast hollow-core flooring instead of in-situ ready mix flooring or timber flooring to reduce
the residual volumes of concrete/formwork and wood/packaging, respectively; and
► Designing for the preferential use of offsite modular units.
3.4 Designing for Materials Optimisation During Construction
To ensure manufacturers and construction companies adopt lean production models, including maximising
the reuse of materials onsite as outlined in section 3.1, structures should be designed with the intent of
designing out waste. This helps to reduce the environmental impacts associated with transportation of
materials and from waste management activities. This includes investigating the use of standardised sizes
for certain materials to help reduce the amount of offcuts produced on site, focusing on promotion and
development of off-site manufacture.
3.5 Designing for Flexibility and Deconstruction
Design flexibility has and will be investigated throughout the design process to ensure that where possible
products (including buildings) only contain materials that can be recycled and are designed to be easily
disassembled. Material efficiency is being considered for the duration and end of life of a building project
to produce; flexible, adaptable spaces that enable a resource-efficient, low-waste future change of use;
durability of materials and how they can be recovered effectively when maintenance and refurbishment
are undertaken and during disassembly/deconstruction. RECEIVED: 28/08/2026
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4. DESCRIPTION OF THE DEVELOPMENT
4.1 Location, Size and Scale of the Development
The Proposed Development will utilise AD technology to generate renewable biogas from up to 99,000
tonnes of organic waste feedstocks per annum. it will comprise a state-of-the-art AD facility designed to
meet the highest environmental and safety standards.
As shown in Figure 4.3 and in the Proposed Site Layout Plan, the Proposed Development comprises a
number of integrated elements including:
► 1 - Administration Building (with associated surface level car parking);
► 2 - Main Process Building (with associated vehicle service areas);
► 3 - Odour Control System (with associated emission stack);
► 4 - Bunded Tank Farm (accommodating the vast majority of tanks that require containment);
► 5 - Digestate Treatment Plant (Evaporator);
► 6 - Digestate Drying Plant;
► 7 - Pellet Hall (for fertiliser storage);
► 8 - Combined Heat and Power (CHP) Building (accommodating two CHP Units);
► 9 - Boiler Unit;
► 10 - Shared Emission Stack (Digestate Drying Plant, CHP and Boiler Units);
► 11 - CO2 Liquefaction Plant;
► 12 - Biogas Upgrade Plant (BUP);
► 13 - Biogas Treatment Plant (Biological De-sulphurisation Units);
► 14 - Gas (Holder) Buffer Dome;
► 15 - Weighbridges and Wheel Washes;
► 16 - Liquid Feedstock Storage Tanks (silos);
► 17 - Backup Gas Flare;
► 18 - Fuel Storage Tank;
► 19 - Gas Grid Entry Unit;
► 20 - Fire Water Storage Tank;
► 21 - Liquefied Petroleum Gas (LPG) Storage Tanks (Propane);
► 22 - Freshwater Storage Tank (Underground);
► 23 - Staff and Visitor Parking;
► 24 - Control Building;
► 25 - Transformer; and
► 26 - Back-Up generator.
Other integrated elements include:
► Internal road and footway provision;
► Engineered stormwater drainage system;
► Landscaping and Earthworks;
► Lighting;
► Fencing and security gates; and
► Site entrance/exit off the L2280 Drumcall Road with gated frontage. This shall include localised
widening and realignment of this road and reconfiguration of the junction with the R189.
A full description is included in Description of the Proposed Development Chapter of this EIAR and in the
statutory notices.
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Figure 4.1 Proposed Site Location Red Line Boundary
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Figure 4.2 Proposed Site Layout & Redline Boundary
4.2 Details of the Non-Hazardous Wastes to be Produced
There will be no demolition associated with the Proposed Development and as such there will be no
demolition waste produced.
The earthworks model prepared by McAdam identifies approximately 98,420 m³ of excavated material, of
which approximately 79,900 m³ of suitable excavated soil and stone will be reused within the Renewable
Biogas Plant site for engineering fill, landscaping and screening berms. This results in a net surplus of
approximately 18,520 m³. For the purposes of the environmental assessments, this quantity has been
conservatively rounded to approximately 18,600 m³ of surplus excavated soil and stone requiring removal
from the site.
The surplus material will be removed by suitably authorised contractors for appropriate reuse, recovery or
disposal at an appropriately authorised receiving facility or facilities.
During the construction phase there may be a surplus of building materials, such as timber off-cuts, broken
concrete blocks, cladding, plastics, metals and tiles generated. There may also be excess concrete during
construction which will need to be disposed of. Plastic and cardboard waste from packaging and supply of
materials will also be generated. The contractor will be required to ensure that oversupply of materials is
kept to a minimum and opportunities for reuse of suitable materials are maximised.
Waste will also be generated from construction workers e.g. organic / food waste, dry mixed recyclables
(waste paper, newspaper, plastic bottles, packaging, aluminium cans, tins and Tetra Pak cartons), mixed RECEIVED: 28/08/2026
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non-recyclables and potentially sewage sludge from temporary welfare facilities provided on site during
the construction phase. Waste printer / toner cartridges, waste electrical and electronic equipment (WEEE)
and waste batteries may also be generated infrequently from site offices.
4.3 Potential Hazardous Wastes Arising
4.3.1 Contaminated Soil
Excavated material will be subject to visual inspection and, where required to establish its classification or
suitability for a proposed receiving facility, appropriate environmental testing will be undertaken prior to
removal from the site.
In the unlikely event that any potentially contaminated material is encountered, it will need to be
segregated from clean / inert material, tested and classified as either non-hazardous or hazardous in
accordance with the EPA publication entitled ‘Waste Classification: List of Waste & Determining if Waste
is Hazardous or Non-Hazardous’ 17 using the HazWasteOnline application (or similar approved classification
method). The material will then need to be classified as clean, inert, non-hazardous or hazardous in
accordance with the EC Council Decision 2003/33/EC 18, which establishes the criteria for the acceptance
of waste at landfills.
In the unlikely event that Asbestos Containing Materials (ACMs) are found within the excavated material,
the removal will only be carried out by a suitably permitted waste contractor, in accordance with the
Safety, Health and Welfare at Work (Exposure to Asbestos) Regulations 2006-2010 19 and the Best Practice
Guidance for Handling Asbestos (2023) 20. All asbestos will be taken to a suitably licensed or permitted
facility.
In the unlikely event that hazardous soil, or historically deposited waste is encountered during the
construction phase, the contractor will notify MCC and provide a Hazardous / Contaminated Soil
Management Plan, to include estimated tonnages, description of location, any relevant mitigation,
destination for disposal / treatment, in addition to information on the authorised waste collector(s).
4.3.2 Fuel/Oils
Fuels and oils are classed as hazardous materials; any on-site storage of fuel / oil, and all storage tanks
and all draw-off points will be bunded and located in a dedicated, secure area of the site. Provided that
these requirements are adhered to and the site crew are trained in the appropriate refueling techniques,
it is expected that there will be only small volumes of fuel / oil waste generated at the site. Any fuel / oil
waste generated will be stored in a bunded area/storage unit pending collection by a suitably permitted
contractor for transfer to a suitably licenced facility.
4.3.3 Invasive Plant Species
A site survey was undertaken by Veon (Project ecologist). This included a site walkover survey of the
entire site, and around part of the outside perimeter to search for any invasive species listed on the Third
Schedule of the European Communities (Birds and Natural Habitats) Regulations 2011 (as amended).
There were no schedule 3 invasive species, such as Japanese Knotweed located on site.
Further detail on the invasive species survey can be found in the Biodiversity Chapter of the EIAR.
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4.3.4 Asbestos
As there is no demolition associated with the Proposed Development, it is unlikely that quantities of
asbestos or asbestos containing materials (ACMs) will be located on site.
If any asbestos is detected, the removal of asbestos or ACMs will be carried out by a suitably qualified
contractor and ACMs will only be removed from site by a suitably permitted / licenced waste contractor,
in accordance with the Safety, Health and Welfare at Work (Exposure to Asbestos) Regulations 2006-2010
and the Best Practice Guidance for Handling Asbestos (2023). All material will be taken to a suitably
licensed or permitted facility.
4.3.5 Other Known Hazardous Substances
Paints, glues, adhesives and other known hazardous substances will be stored in designated areas. They
will generally be present in small volumes only and associated waste volumes generated will be kept to a
minimum. Wastes will be stored in appropriate receptacles pending collection by an authorised waste
contractor.
In addition, WEEE (containing hazardous components), printer toner / cartridges, batteries (Lead, Ni-Cd
or Mercury) and / or fluorescent tubes and other mercury containing waste may be generated from during
C&D activities or temporary site offices. These wastes, if generated, will be stored in appropriate
receptacles in designated areas of the site pending collection by an authorised waste contractor.
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5. ROLES AND RESPONSIBILITIES
The Best Practice Guidelines on the Preparation of Resource Waste Management Plans for Construction
and Demolition Projects promotes that a suitably qualified Resource Manager (RM) with expertise in waste
and resource management to implement the RWMP should be appointed. The RM may be performed by
number of different individuals over the life-cycle of the Project, however it is intended to be a reliable
person chosen from within the Planning/Design/Contracting Team, who is technically competent and
appropriately trained, who takes the responsibility to ensure that the objectives and measures within the
Project RWMP are complied with. The RM is assigned the requisite authority to meet the objective and
obligations of the RWMP. The role will include the important activities of conducting waste checks/audits
and adopting construction methodology that is designed to facilitate maximum reuse and/or recycling of
waste.
5.1 Role of the Client
The Client is the body establishing the aims and the performance targets for the project.
► The Client has commissioned the preparation and submission of this RWMP as part of the design and
planning submission;
► The Client is to commission the preparation and submission of an updated RWMP as part of the
construction tendering process;
► The Client will ensure that the RWMP is agreed on and submitted to the local authority and their
agreement obtained prior to commencement of works on site;
► The Client will request the end-of-project RWMP from the Contractor.
5.2 Role of the Client Advisory Team
The Client Advisory Team or Design Team is formed of architects, consultants, quantity surveyors and
engineers and is responsible for:
► Drafting and maintaining the RWMP through the design, planning and procurement phases of the
project;
► Appointing a RM to track and document the design process, inform the Design Team and prepare the
RWMP.
► Including details and estimated quantities of all projected waste streams with the support of
environmental consultants/scientists. This will also include data on waste types (e.g. waste
characterisation data, contaminated land assessments, site investigation information) and prevention
mechanisms (such as by-products) to illustrate the positive circular economy principles applied by the
Design Team;
► Handing over of the RWMP to the selected Contractor upon commencement of construction of the
development, in a similar fashion to how the safety file is handed over to the Contractor;
► Working with the Contractor as required to meet the performance targets for the project.
5.3 Future Role of the Contractor
The Construction Contractors will be responsible for:
► Preparing, implementing and reviewing the RWMP throughout the construction phase (including the
management of all suppliers and sub-contractors) as per the requirements of the EPA guidelines;
► Identifying a designated and suitably qualified RM who will be responsible for implementing the
RWMP;
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► Implementing waste management policies whereby waste materials generated on site are to be
segregated as far as practicable;
► Where on-site processing of construction materials is proposed, the Contractor will ensure that all
applicable waste authorisations and regulatory requirements are satisfied prior to commencement of
such activities.
► Identifying all destinations for resources taken off-site. As above, any resource that is legally classified
as a ‘waste’ must only be transported to an authorised waste facility;
► End-of-waste and by-product notifications addressed with the EPA where required;
► Clarification of any other statutory waste management obligations, which could include on -site
processing;
► Full records of all resources (both wastes and other resources) will be maintained for the duration of
the project; and
► Preparing a RWMP Implementation Review Report at project handover.
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6. KEY MATERIALS & QUANTITIES
6.1 Project Resource Targets
Project specific resource and waste management targets for the site have not yet been set and this
information will be updated for these targets once these targets have been confirmed by the client.
However, it is expected for projects of this nature that a minimum of 70% of waste is fully re-used,
recycled or recovered. Target setting will inform the setting of project-specific benchmarks to track target
progress. Typical Key Performance Indicators (KPIs) that will be used to set targets include (as per
guidelines):
► Weight (tonnes) or Volume (m3) of waste generated per construction value;
► Weight (tonnes) or Volume (m3) of waste generated per construction floor area (m2);
► Fraction of resource reused on site;
► Fraction of resource notified as by-product;
► Fraction of waste segregated at source before being sent off-site for recycling/recovery; and
► Fraction of waste recovered, fraction of waste recycled, or fraction of waste disposed.
6.2 Main Construction Waste Categories
The main non-hazardous and hazardous waste streams that could be generated by the construction
activities at a typical site are shown in Table 6.1 The List of Waste (LoW) code (2018) for each waste
stream is also shown.
Table 6.1 Typical waste types generated and LoW codes (individual waste types may contain
hazardous substances)
Waste Material LoW Code
Concrete, bricks, tiles, ceramics 17 01 01-03 & 07
Wood, glass and plastic 17 02 01-03
Treated wood, glass, plastic, containing hazardous substances 17-02-04*
Bituminous mixtures, coal tar and tarred products 17 03 01*, 02 & 03*
Metals (including their alloys) and cable 17 04 01-11
Soil and stones 17 05 03* & 04
Gypsum-based construction material 17 08 01* & 02
Paper and cardboard 20 01 01
Mixed C&D waste 17 09 04
Green waste 20 02 01
Electrical and electronic components 20 01 35 & 36
Batteries and accumulators 20 01 33 & 34
Liquid fuels 13 07 01-10
Chemicals (solvents, pesticides, paints, adhesives, detergents etc.) 20 01 13, 19, 27-30
Insulation materials 17 06 04
Organic (food) waste 20 01 08
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* Individual waste type may contain hazardous substances
6.3 Demolition Waste Generation
There will be no demolition associated with the Proposed Development.
6.4 Construction Waste Generation
Table 6.2 shows the breakdown of C&D waste types produced on a typical site based on data from the
EPA National Waste Reports 21 and the joint EPA & GMIT study 22.
Table 6.2 Waste materials generated on a typical Irish construction site
Waste Types %
Mixed C&D 33
Timber 28
Plasterboard 10
Metals 8
Concrete 6
Other 15
Total 100
Table 6.3, below, shows the estimated construction waste generation for the proposed Project based on
the gross floor area of construction and other information available to date, along with indicative targets
for management of the waste streams. The estimated amounts for the main waste types (with the
exception of soils and stones) are based on an average large-scale development waste generation rate
per m2, using the waste breakdown rates shown in Table 6.2. These have been calculated from the
schedule of development areas provided by the architect.
Table 6.3 Predicted on and off-site reuse, recycle and disposal rates for construction waste
Waste Type Tonnes Reuse Recycle /
Recovery Disposal
% Tonnes % Tonnes % Tonnes
Mixed C&D 112.4 10 11.2 80 90.0 10 11.2
Timber 95.4 40 38.2 55 52.5 5 4.8
Plasterboard 34.1 30 10.2 60 20.4 10 3.4
Metals 27.3 5 1.4 90 24.5 5 1.4
Concrete 20.4 30 6.1 65 13.3 5 1.0
Other 51.1 20 10.2 60 30.7 20 10.2
Total 340.8 77.4 231.4 32.0
In addition to the waste streams in Table 6.3, The earthworks model prepared by McAdam identifies
approximately 98,420 m³ of excavated material, of which approximately 79,900 m³ of suitable excavated
soil and stone will be reused within the Renewable Biogas Plant site for engineering fill, landscaping and
screening berms. This results in a net surplus of approximately 18,520 m³. For the purposes of the
environmental assessments, this quantity has been conservatively rounded to approximately 18,600 m³
of surplus excavated soil and stone requiring removal from the site.
The surplus material will be removed by suitably authorised contractors for appropriate reuse, recovery or
disposal at an appropriately authorised receiving facility or facilities.
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It should be noted that until final materials and detailed construction methodologies have been confirmed,
it is difficult to predict with a high level of accuracy the construction waste that will be generated from the
proposed works as the exact materials and quantities may be subject to some degree of change and
variation during the construction process.
6.5 Proposed Resource and Waste Management Options
Waste materials generated will be segregated on-site, where it is practical. Where the on-site segregation
of certain wastes types is not practical, off-site segregation will be carried out. There will be skips and
receptacles provided to facilitate segregation at source, where feasible. All waste receptacles leaving the
site will be covered or enclosed. The appointed waste contractor will collect and transfer the wastes as
receptacles are filled. There are numerous waste contractors in the Monaghan region that provide this
service.
All waste arisings will be handled by an approved waste contractor holding a current waste collection
permit. All waste arisings requiring disposal off-site will be reused, recycled, recovered or disposed of at a
facility holding the appropriate registration, permit or licence, as required.
There will be no burning of any rubbish on site.
National End-of-Waste Decision EoW-N001/2023 (Regulation 28) published by the EPA in September 2023,
establishes criteria determining when recycled aggregate resulting from a recovery operation ceases to be
waste. Material from this proposed plant will be investigated to see if it can cease to be a waste under the
requirements of the National End of Waste Criteria for Aggregates.
During construction, some of the sub-contractors on site will generate waste in relatively low quantities.
The transportation of non-hazardous waste by persons who are not directly involved with the waste
business, at weights less than or equal to 2 tonnes, and in vehicles not designed for the carriage of waste,
are exempt from the requirement to have a waste collection permit (per Article 30 (1) (b) of the Waste
Collection Permit Regulations 2007, as amended). Any sub-contractors engaged that do not generate more
than 2 tonnes of waste at any one time can transport this waste off-site in their work vehicles (which are
not designed for the carriage of waste). However, they are required to ensure that the receiving facility
has the appropriate COR / permit / licence.
Written records will be maintained by the contractor(s), detailing the waste arising throughout the C&D
phases, the classification of each waste type, waste collection permits for all waste contactors who collect
waste from the site and COR / permit / licence for the receiving waste facility for all waste removed off-
site for appropriate reuse, recycling, recovery and / or disposal.
Dedicated bunded storage containers will be provided for hazardous wastes which may arise, such as
batteries, paints, oils, chemicals, if required.
The anticipated management of the main waste streams is outlined as follows:
Soil, Stone and Clay
The waste hierarchy states that the preferred option for waste management is prevention and minimisation
of waste, followed by preparing for reuse and recycling / recovery, energy recovery (i.e. incineration) and,
least favoured of all, disposal. The excavations are required to facilitate construction works so the preferred
option (prevention and minimisation) cannot be accommodated for the excavation phase.
Excavation is required to facilitate construction of the Proposed Development. The design has sought to
maximise the reuse of suitable excavated material within the site, with approximately 79,900 m³ proposed
for reuse as engineering fill, landscaping and screening berms. A net surplus of approximately 18,520 m³, RECEIVED: 28/08/2026
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conservatively rounded to approximately 18,600 m³ for assessment purposes, will require off -site
management.
The waste hierarchy will be applied in determining the appropriate management route for this surplus
material. Appropriate reuse and recovery options will be prioritised where technically and legally
appropriate, with disposal used where reuse or recovery is not available or suitable.
At the time of preparation of this RWMP, Carrickamore Quarry, Carrickmacross, Co. Monaghan has been
identified as a potential receiving facility with available capacity. Subject to availability at the time of
construction and compliance with the applicable waste acceptance criteria, this facility may receive some
or all of the surplus excavated soil and stone. The final receiving facility or facilities will be selected by the
appointed Contractor prior to commencement of the relevant excavation works, having regard to the
applicable waste authorisation, available capacity and waste acceptance criteria. Other suitably licensed
or permitted recovery or disposal facilities may therefore be used where appropriate.
The final destinations for construction waste streams will be confirmed by the appointed Contractor prior
to removal from the site. In relation to surplus excavated soil and stone, Carrickamore Quarry has been
identified as a potential receiving facility as described above, subject to availability and applicable
acceptance criteria at the time of construction.
The material may be deemed a by-product (and not as a waste). If this is the case, it will be done in
accordance with Regulation 27 of the European Communities (Waste Directive) Regulations 2011, as
amended, which requires that certain conditions are met and that by-product notifications are made to
the EPA via their online notification form. Excavated material should not be removed from site until
approval from the EPA has been received. The potential to reuse material as a by-product will be confirmed
during the course of the excavation works, with the objective of eliminating any unnecessary disposal of
material.
The next option (beneficial reuse) may be appropriate for the excavated material, pending environmental
testing to classify the material as hazardous or non-hazardous in accordance with the EPA Waste
Classification – List of Waste & Determining if Waste is Hazardous or Non-Hazardous publication. Clean
inert material may be used as fill material in other construction projects or engineering fill for waste
licensed sites. Beneficial reuse of surplus excavation material as engineering fill may be subject to further
testing to determine if materials meet the specific engineering standards for their proposed end use.
Any nearby sites requiring clean fill/capping material will be contacted to investigate reuse opportunities
for clean and inert material. If any of the material is to be reused on another site as a by-product (and
not as a waste), this will be done in accordance with Regulation 27. Similarly, if any soils/stones are
imported onto the site from another construction site as a by-product, this will also be done in accordance
with Regulation 27. Regulation 27 will be investigated to see if the material can be imported onto this site
for beneficial reuse instead of using virgin materials.
If the material is deemed to be a waste, then removal and reuse / recovery / disposal of the material will
be carried out in accordance with the Waste Framework Directive (Directive 2008/98/EC), the Waste
Management Act 1996 as amended, the Waste Management (Collection Permit) Regulations 2007 as
amended and the Waste Management (Facility Permit & Registration) Regulations 2007 as amended. Once
all available beneficial reuse options have been exhausted, the options of recycling and recovery at waste
permitted and licensed sites will be considered.
In the event that contaminated material is encountered and subsequently classified as hazardous, this
material will be stored separately to any non-hazardous material. It will require off-site treatment at a
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Bedrock
While it is not envisaged that bedrock will be encountered, if bedrock is encountered, it is anticipated that
it will not be crushed on site. Any excavated rock is expected to be removed off-site for appropriate reuse,
recovery and / or disposal. If bedrock is to be crushed on-site, the appropriate mobile waste facility permit
will be obtained from MCC.
Silt & Sludge
During the construction phase, silt and petrochemical interception will be carried out on run-off and
pumped water from site works, where required. Sludge and silt will then be collected by a suitably licensed
contractor and removed off-site.
Concrete Blocks, Bricks, Tiles & Ceramics
The majority of concrete blocks, bricks, tiles and ceramics generated as part of the construction works are
expected to be clean, inert material and will be recycled, where possible. If concrete is to be crushed on-
site, the appropriate mobile waste facility permit will be obtained from MCC.
Hard Plastic
As hard plastic is a highly recyclable material, much of the plastic generated will be primarily from material
off-cuts. All recyclable plastic will be segregated and recycled, where possible.
Timber
Timber that is uncontaminated, i.e. free from paints, preservatives, glues, etc., will be disposed of in a
separate skip and recycled off-site.
Metal
Metals will be segregated, where practical, and stored in skips. Metal is highly recyclable and there are
numerous companies that will accept these materials.
Plasterboard
There are currently a number of recycling services for plasterboard in Ireland. Plasterboard from the
construction phases will be stored in a separate skip, pending collection for recycling. The site Manager
will ensure that oversupply of new plasterboard is carefully monitored to minimise waste.
Glass
Glass materials will be segregated for recycling, where possible.
Waste Electrical & Electronic Equipment (WEEE)
Any WEEE will be stored in dedicated covered cages / receptacles / pallets pending collection for recycling.
Other Recyclables
Where any other recyclable wastes, such as cardboard and soft plastic, are generated, these will be
segregated at source into dedicated skips and removed off-site.
Non-Recyclable Waste
C&D waste which is not suitable for reuse or recovery, such as polystyrene, some plastics and some
cardboards, will be placed in separate skips or other receptacles. Prior to removal from site, the non-
recyclable waste skip / receptacle will be examined by a member of the waste team (see Section 8) to RECEIVED: 28/08/2026
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determine if recyclable materials have been placed in there by mistake. If this is the case, efforts will be
made to determine the cause of the waste not being segregated correctly and recyclable waste will be
removed and placed into the appropriate receptacle.
Asbestos Containing Materials
In the unlikely event that any asbestos or ACM is found on-site it will be removed by a suitably competent
contractor and disposed of as asbestos waste before the works begin. All asbestos removal work or
encapsulation work must be carried out in accordance with the Safety, Health and Welfare at Work
(Exposure to Asbestos) Regulations 2006-2010.
Other Hazardous Wastes
On-site storage of any hazardous wastes produced (i.e. contaminated soil if encountered and / or waste
fuels) will be kept to a minimum, with removal off-site organised on a regular basis. Storage of all
hazardous wastes on-site will be undertaken so as to minimise exposure to on-site personnel and the
public and to also minimise potential for environmental impacts. Hazardous wastes will be recovered,
wherever possible, and failing this, disposed of appropriately.
On-Site Crushing
It is currently not envisaged that the crushing of waste materials will occur on-site. However, if the
crushing of material is to be undertaken, a mobile waste facility permit will first be obtained from MCC and
the destination of the accepting waste facility or if an application under regulation 28 will be made using
National End-of-Waste Decision EoW-N001/2023, will be supplied to the MCC waste unit.
It should be noted that until a construction contractor is appointed it is not possible to provide information
on the specific destinations of each construction waste stream. Prior to commencement of construction
and removal of any waste offsite, details of the proposed destination of each waste stream will be provided
to MCC by the project team.
6.6 Tracking and Documentation Procedures for Off-Site Waste
All waste will be documented prior to leaving the site. Waste will be weighed by the contractor, either by
a weighing mechanism on the truck or at the receiving facility. These waste records will be maintained on
site by the nominated project RM (see Section 8).
All movement of waste and the use of waste contractors will be undertaken in accordance with the Waste
Framework Directive (Directive 2008/98/EC), the Waste Management Act 1996 as amended, Waste
Management (Collection Permit) Regulations 2007 as amended and Waste Management (Facility Permit &
Registration) Regulations 2007 and amended. This includes the requirement for all waste contractors to
have a waste collection permit issued by the NWCPO. The nominated project RM (see Section 8) will
maintain a copy of all waste collection permits on-site.
If the waste is being transported to another site, a copy of the Local Authority waste COR / permit or EPA
Waste Licence for that site will be provided to the nominated project Waste Manager (see Section 8). If
the waste is being shipped abroad, a copy of the Transfrontier Shipping (TFS) notification document will
be obtained from DCC (as the relevant authority on behalf of all Local Authorities in Ireland) and kept on-
site along with details of the final destination (COR, permits, licences, etc.). A receipt from the final
destination of the material will be kept as part of the on-site waste management records.
All information will be entered in a waste management recording system to be maintained on-site.
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7. ESTIMATED COST OF WASTE MANAGEMENT
An outline of the costs associated with different aspects of waste management is outlined below. The total
cost of C&D waste management will be measured and will take into account handling costs, storage costs,
transportation costs, revenue from rebates and disposal costs.
7.1 Reuse
By reusing materials on site, there will be a reduction in the transport and recycle / recovery / disposal
costs associated with the requirement for a waste contractor to take the material off -site. Clean and inert
soils, gravel, stones, etc., which cannot be reused on-site may be used as access roads or capping material
for landfill sites, etc. This material is often taken free of charge or at a reduced fee for such purposes,
reducing final waste disposal costs.
7.2 Recycling
Salvageable metals will earn a rebate, which can be offset against the costs of collection and transportation
of the skips.
Clean, uncontaminated cardboard and certain hard plastics can also be recycled. Waste contractors will
charge considerably less to take segregated wastes, such as recyclable waste, from a site than mixed
waste.
Timber can be recycled as chipboard. Again, waste contractors will charge considerably less to take
segregated wastes, such as timber, from a site than mixed waste.
7.3 Disposal
Landfill charges are currently at around €140 - €160 per tonne which includes a €85 per tonne landfill levy
specified in the Waste Management (Landfill Levy) Regulations 2015 as amended. The Circular Economy
(Waste Recovery Levy) will also incur a levy of €10 per tonne for waste accepted for recovery. This will
include backfilling at authorised recovery sites and at municipal waste landfills. In addition to disposal
costs, waste contractors will also charge a collection fee for skips.
Collection of segregated C&D waste usually costs less than municipal waste. Specific C&D waste
contractors take the waste off-site to a licensed or permitted facility and, where possible, remove
salvageable items from the waste stream before disposing of the remainder to landfill. Clean soil, rubble,
etc., is also used as fill / capping material, wherever possible.
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8. TRAINING PROVISIONS
A member of the construction team will be appointed as the RM to ensure commitment, operational
efficiency and accountability in relation to waste management during the C&D phases of the development.
8.1 Resource Manager Training and Responsibilities
The RM will be responsible for conducting a waste audit at the site during the C&D phase of the project.
The RM will be given the responsibility and authority to select a waste team if required, i.e. members of
the site crew that will aid them in the organisation, operation and recording of the waste management
system implemented on site.
The details of the RM are as follows:
► Contact Name: David Mullan
► Contact Company: Stream Bioenergy Ireland Limited
► Email: david.mullan@streambioenergy.ie
The RM will have overall responsibility to oversee, record and provide feedback to the client on everyday
waste management at the site. Authority will be given to the Waste Manager to delegate responsibility to
sub-contractors, where necessary, and to coordinate with suppliers, service providers and sub-contractors
to prioritise waste prevention and material salvage.
The RM will be trained in how to set up and maintain a record keeping system, how to perform an audit
and how to establish targets for waste management on site. The RM will also be trained in the best
methods for segregation and storage of recyclable materials, have information on the materials that can
be reused on site and be knowledgeable in how to implement this RWMP.
8.2 Site Crew Training
Training of site crew in relation to waste is the responsibility of the RM and, as such, a waste training
program will be organised. A basic awareness course will be held for all site crew to outline the RWMP
and to detail the segregation of waste materials at source. This may be incorporated with other site training
needs such as general site induction, health and safety awareness and manual handling.
This basic course will describe the materials to be segregated, the storage methods and the location of
the Waste Storage Areas (WSAs). A sub-section on hazardous wastes will be incorporated into the training
program and the particular dangers of each hazardous waste will be explained.
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9. TRACKING AND TRACING / RECORD KEEPING
Records will be kept for all waste material which leaves the site, either for reuse on another site, recycling
or disposal. A recording system will be put in place to record the waste arisings on Site.
A waste tracking log will be used to track each waste movement from the site. On exit from the site, the
waste collection vehicle driver will stop at the site office and sign out as a visitor and provide the security
personnel or RM with a waste docket (or Waste Transfer Form (WTF) for hazardous waste) for the waste
load collected. At this time, the security personnel will complete and sign the Waste Tracking Register with
the following information:
► Date
► Time
► Waste Contractor
► Company waste contractor appointed by, e.g. Contractor or subcontractor name
► Collection Permit No.
► Vehicle Reg.
► Driver Name
► Docket No.
► Waste Type
► LoW
► Weight/Quantity
The waste vehicle will be checked by security personal or the RM to ensure it has the waste collection
permit no. displayed and a copy of the waste collection permit in the vehicle before they are allowed to
remove the waste from the site.
The waste transfer dockets will be transferred to the RM on a weekly basis and can be placed in the
Waste Tracking Log file. This information will be forwarded onto the MCC Waste Regulation Unit when
requested.
Each subcontractor that has engaged their own waste contractor will be required to maintain a similar
waste tracking log with the waste dockets / WTF maintained on file and available for inspection on site
by the main contractor as required. These subcontractor logs will be merged with the main waste log.
Waste receipts from the receiving waste facility will also be obtained by the site contractor(s) and
retained. A copy of the Waste Collection Permits, CORs, Waste Facility Permits and Waste Licences will
be maintained on site at all times and will be periodically reviewed by the RM. Subcontractors who have
engaged their own waste contractors, will provide the main contractor with a copy of the waste collection
permits and COR / permit / licence for the receiving waste facilities and maintain a copy on file, available
for inspection on site as required.
RECEIVED: 28/08/2026
Stream BioEnergy Ireland Ltd / 247501.0350WMR01a
AWN Consulting Ltd 24
10. OUTLINE WASTE AUDIT PROCEDURE
10.1 Responsibility for Waste Audit
The appointed RM will be responsible for conducting a waste audit at the site during the C&D phase of
the proposed Project. Contact details for the nominated RM will be provided to the MCC Waste Regulation
Unit after the main contractor is appointed and prior to any material being removed from site.
10.2 Review of Records and Identification of Corrective Actions
A review of all waste management costs and the records for the waste generated and transported off-site
will be undertaken mid-way through the construction phase of the proposed Project.
If waste movements are not accounted for, the reasons for this will be established in order to see if and
why the record keeping system has not been maintained. The waste records will be compared with the
established recovery / reuse / recycling targets for the site. Each material type will be examined, in order
to see where the largest percentage waste generation is occurring. The waste management methods for
each material type will be reviewed in order to highlight how the targets can be achieved.
Upon completion of the C&D phase, a final report will be prepared, summarising the outcomes of waste
management processes adopted and the total recycling / reuse / recovery figures for the development.
10.3 Pest Management
A pest control operator will be appointed as required to manage pests onsite during the construction phase
of the project. Organic and food wastes generated by staff will not be stored in open skips, but in closed
waste receptacles. Any waste receptacles will be carefully managed to prevent leaks, odours and pest
problems.
RECEIVED: 28/08/2026
Stream BioEnergy Ireland Ltd / 247501.0350WMR01a
AWN Consulting Ltd 25
11. CONSULTATION WITH RELEVANT BODIES
11.1 Local Authority
The final destinations for construction waste streams will be confirmed by the appointed Contractor prior
to removal from the site. In relation to surplus excavated soil and stone, Carrickamore Quarry has been
identified as a potential receiving facility as described above, subject to availability and applicable
acceptance criteria at the time of construction.
RECEIVED: 28/08/2026
Stream BioEnergy Ireland Ltd / 247501.0350WMR01a
AWN Consulting Ltd 26
12. CONCLUSION
Adherence to this plan will also ensure that waste management during the construction phase at the
Proposed Development is carried out in accordance with the requirements in the EPA’s Best Practice
Guidelines for the Preparation of Resource & Waste Management Plans for Construction & Demolition
Projects and the MCC Waste Bye-Laws and the NWMPCE.
RECEIVED: 28/08/2026
Stream BioEnergy Ireland Ltd / 247501.0350WMR01a
AWN Consulting Ltd 27
13. REFERENCES
1. Waste Management Act 1996 as amended.
2. Environmental Protection Agency Act 1992 as amended.
3. Litter Pollution Act 1997 (S.I. No. 12 of 1997) as amended.
4. Regional Waste Management Planning Offices, The National Waste Management Plan for a Circular
Economy 2024 – 2030 (2024).
5. Department of Environment and Local Government (DoELG) Waste Management – Changing Our
Ways, A Policy Statement (1998).
6. Forum for the Construction Industry – Recycling of Construction and Demolition Waste.
7. Department of Communications, Climate Action and Environment (DCCAE), Waste Action Plan for
the Circular Economy - Ireland’s National Waste Policy 2020-2025 (Sept 2020).
8. DCCAE, Whole of Government Circular Economy Strategy 2022-2023 ‘Living More, Using Less’
(2021).
9. Circular Economy and Miscellaneous Provisions Act 2022.
10. Environmental Protection Agency (EPA) ‘Best Practice Guidelines for the Preparation of Resource
and Waste Management Plans for Construction & Demolition Projects’ ( 2021).
11. Department of Environment, Heritage and Local Government, Best Practice Guidelines on the
Preparation of Waste Management Plans for Construction and Demolition Projects (2006).
12. FÁS and the Construction Industry Federation (CIF), Construction and Demolition Waste
Management – a 14 (2002).
13. Waste Management (Landfill Levy) Regulations 2015 (as amended).
14. Circular Economy (Waste Recovery Levy) Regulations 2024.
15. Monaghan County Council (MCC), Monaghan County Development Plan 2025 – 2031 (2025).
16. Planning and Development Act 2000 (S.I. No. 30 of 2000) as amended.
17. EPA, Waste Classification – List of Waste & Determining if Waste is Hazardous or Non-Hazardous
(2018).
18. Council Decision 2003/33/EC, establishing criteria and procedures for the acceptance of waste at
landfills pursuant to Article 16 of and Annex II to Directive 1999/31/EC.
19. Safety, Health and Welfare at Work (Exposure to Asbestos) Regulations 2006-2010.
20. Local Government Ireland, Best practice guidance for handling asbestos (2023).
21. Environmental Protection Agency (EPA), National Waste Database Reports 1998 – 2020 and the
Circular Economy and National Waste Database Report 2021 – 2022.
22. EPA and Galway-Mayo Institute of Technology (GMIT), EPA Research Report 146 – A Review of
Design and Construction Waste Management Practices in Selected Case Studies – Lessons Learned
(2015).
23. European Commission, Guidelines for the waste audits before demolition and renovation works of
buildings (May 2018). RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 27
Appendix B - Summary of Environmental Mitigation
Measures
RECEIVED: 28/08/2026
August 2026 | 17-1
Table of Contents
17 Summary of Mitigation & Monitoring Measures .................................................................. 17-2
17.1 Introduction .......................................................................................................................... 17-2
17.1.1 Construction Phase Mitigation Measures ............................................................................. 17-5
17.1.2 Operational Phase Mitigation Measures .............................................................................. 17-8
17.1.3 Monitoring .......................................................................................................................... 17-11
Table of Tables
Table 17-1 Incorporated Design Mitigation ....................................................................................... 17-2
Table 17-2 Construction Phase Mitigation Measures ........................................................................ 17-5
Table 17-3 Operational Phase Mitigation Measures ......................................................................... 17-8
RECEIVED: 28/08/2026
August 2026 | 17-2
17 Summary of Mitigation & Monitoring Measures
17.1 Introduction
A key objective of the Environmental Impact Assessment process is to identify likely significant
environmental effects at the pre-consent stage and, where necessary, to identify measures to avoid,
prevent, reduce or otherwise mitigate such effects. This chapter summarises the incorporated design
measures, mitigation measures and monitoring measures identified in Chapters 4 to 16 of the EIAR.
The mitigation and monitoring measures applicable to the Renewable Biogas Plant will be
incorporated, as appropriate, into the detailed design, Construction Environmental Management Plan
(CEMP), operational procedures and other relevant management plans. Construction-phase measures
will be incorporated into the CEMP and other relevant construction management plans prior to
commencement of the applicable works, while operational measures will be implemented through
the design and operation of the facility and, where applicable, through the Industrial Emissions
licensing regime.
The Linear Gas Grid Connection does not form part of the Proposed Development for which planning
permission is sought and will be delivered separately by Gas Networks Ireland under the applicable
statutory consenting process. The Applicant does not have control over the detailed design,
construction or operation of the Linear Gas Grid Connection and cannot commit Gas Networks Ireland
to particular mitigation or monitoring measures. Accordingly, where mitigation or monitoring
measures are identified in this EIAR in respect of the Linear Gas Grid Connection, they are presented
as recommendations for implementation by Gas Networks Ireland, having regard to GNI's applicable
statutory, technical, environmental, construction and operational management requirements.
Table 17-1 Incorporated Design Mitigation
Aspect Mitigation
Population &
Human Health
▪ Plant uses best available technologies and systems with planned preventative maintenance to
minimise equipment failure.
▪ Operated by skilled and trained personnel qualified to manage a biogas facility.
▪ Feedstock delivered in covered HGVs and handled within enclosed buildings to contain odours.
▪ Main process building sealed; negative pressure maintained with ventilation and air extraction
systems.
▪ Extracted air treated via scrubbers, biofilters, and activated carbon filters; discharged through 40m
stack to ensure pollutant dispersion.
▪ Fast-acting roller doors and air curtains at HGV entry points reduce fugitive emissions and odour.
▪ Noise reduction via earth berms along southern and eastern boundaries, acoustic enclosures for
noise sources, and controlled HGV entry/exit times (07:00–19:00).
▪ Water protection via proper storage, containment, drainage systems, emergency procedures,
training, and spill kits; adherence to Land & Soil and Water & Hydrology mitigation.
▪ No significant impacts on human health from Water & Hydrology, Hydrogeology, Land, Soils, or
Geology; no further mitigation required.
▪ Visual/landscape design mitigates impacts through site regrading, berm formation, and colour
scheme; landscape mitigation measures detailed in Landscape Design Statement and Plan. RECEIVED: 28/08/2026
August 2026 | 17-3
Aspect Mitigation
Landscape &
Visual
▪ Earthworks regrade site so primary structures sit within the landform, reducing height and visual
prominence.
▪ Berms (~6 m high) along southern and eastern boundaries provide screening from public roads
and receptors.
▪ Additional roadside berm along L-road frontage limits visibility and integrates development into
landscape.
▪ Facility layout clusters taller, complex structures to the west, away from public view; main process
building inside berm for coherence and reduced visual clutter.
▪ Grouping and consolidation of plant elements create a unified and legible built form.
▪ Colour scheme designed to blend with surrounding landscape: greens on lower sections, light grey
on upper sections to echo natural backdrop.
Material
Assets:
Traffic &
Transport
▪ Site access via L2280 on northern road frontage; local road improvements proposed (widening and
realignment).
▪ Roadworks confined to public road or applicant-controlled lands.
▪ Occasional local feedstock traffic may arrive via L2280 from Drum, but mostly existing traffic will
divert into the site.
▪ Main HGV traffic will use adjoining regional road network for both construction and operational
phases.
▪ Internal pedestrian provision includes segregated circulation routes.
▪ High-quality, slip-resistant materials for crossings; dropped crossings designed with shallow
gradients for accessibility for all users.
Material
Assets:
Built Services
▪ Surface Water Management: Engineered drainage system with controlled collection and
attenuation; infrastructure sized to prevent exceedance flows, reduce sediment transport, and
protect downstream systems.
▪ Foul Water & Welfare: On-site welfare facilities during construction with sealed systems;
permanent foul water infrastructure segregates solid and liquid streams for safe containment and
off-site management.
▪ Water Supply: Process water sourced from reused liquid fractions, attenuated stormwater, and on -
site well; potable water connection included as back-up.
▪ Power Supply: Overhead lines re-routed around site; plant self-supplies via on-site CHP engines;
backup supply capacity confirmed; utility works conducted safely to minimise service interruptions.
▪ Telecommunications: Connections utilise existing adjacent networks.
▪ Gas Infrastructure: Gas grid connection follows GNI standards, established corridors, and
incorporates isolation, pressure control, and monitoring.
▪ Protection of Existing Services: Layout avoids unnecessary interaction with underground services;
all works comply with regulatory and utility-provider standards.
Material
Assets:
Waste
▪ Suitable excavated soil and stone will be reused within the Renewable Biogas Plant site for
engineering fill, landscaping and screening berms. Approximately 18,600 m³ of surplus excavated
soil and stone will require off-site management in accordance with the RWMP.
▪ Correct classification and segregation of soils to identify and manage any potentially contaminated
material.
▪ Visual inspection and environmental soil testing (hydrocarbons, metals, PAHs, standard soil
classification) to prevent negative impacts on workers, water, and soil.
Land & Soils ▪ Proper storage and containment of hazardous substances to prevent contamination.
▪ Engineered drainage systems designed in line with best practice, standards, and relevant
guidelines.
▪ Design measures embedded to minimise potential adverse effects on land, soils, and geology. RECEIVED: 28/08/2026
August 2026 | 17-4
Aspect Mitigation
Water
(Hydrology &
Hydrogeology)
▪ Proper storage and containment of hazardous substances to prevent contamination of water.
▪ Engineered drainage systems designed according to best practice, standards, and guidelines.
▪ Design measures embedded to minimise adverse effects on hydrogeology and hydrology.
Biodiversity ▪ Engineered stormwater drainage system designed to manage runoff and reduce
sediment/pollutant transport, following SuDS principles and CIRIA C753.
▪ Indoor delivery, handling, and processing of feedstock within sealed systems to prevent
environmental contamination.
▪ Impermeable surfaces and bunded containment systems for all tanks and pipework to prevent
spills (CIRIA C736 compliant).
▪ Stormwater reuse via AD process; discharge only when storage is full, with attenuation to match
greenfield runoff (1 in 100-year event + climate change allowance).
▪ Channel drains, swales, and oil-water interceptors incorporated to treat runoff before discharge or
reuse.
▪ Containment and recycling of all process effluent and wash-down water to AD process.
▪ Maintenance of ≥5 m ecological buffer zones around ditches to protect amphibian routes and
water quality.
▪ Multi-stage odour control system and backup gas flare to minimise odour and GHG emissions; all
combustion and stacks comply with EPA limits.
▪ Bunding and secondary containment of all raw material, fuel, fire water, and liquid waste tanks to
prevent leaks/spills.
▪ Road improvements at site entrance (widening, realignment) and wheel washes to reduce traffic
impacts, dust, and sediment transfer.
▪ Retention of existing hedgerows and treelines where possible; replacement planting where loss
occurs.
▪ Landscape mitigation includes native hedgerows, woodland species (high, low, understorey), and
wildflower planting to enhance biodiversity and integrate with local habitat.
Noise &
Vibration
▪ Earth berms along southern and eastern boundaries reduce noise emissions from the site.
▪ All site processes occur within the fully enclosed main process building.
▪ Fast-acting roller shutter doors at HGV entry points maintain buildings closed at all times.
▪ External plant and equipment designed to comply with operational noise limits.
Air Quality ▪ Feedstock delivery, handling and processing will take place within enclosed buildings maintained
under negative pressure. Extracted air will be treated through the odour control system prior to
discharge through the 40 m stack. Fast-acting doors and air curtains will minimise fugitive
emissions during vehicle access. Process emission points will be designed and operated in
accordance with the applicable IE Licence requirements.
Climate ▪ Adequate attenuation and drainage designed to manage increased rainfall and potential future
flooding.
▪ Compliance with Part L 2022 (Buildings Other Than Dwellings) and targeting minimum A3 BER.
▪ Energy hierarchy “Be Mean, Be Lean, Be Green” applied:
o Be Mean: High-performance U-values, improved air tightness, reduced thermal bridging.
o Be Lean: Low-energy plant, natural ventilation, daylight use, energy-efficient LED lighting.
o Be Green: Renewable technologies including CHP, heat pumps, and solar PV.
▪ Provision of electric vehicle charging and bicycle parking.
▪ Incorporation of water efficiency measures, e.g., low consumption sanitary fittings.
Cultural
Heritage
▪ Excavated material reused to form screening berms on southeastern and northwestern site areas.
▪ Berms planted to integrate development into the landscape and reduce visual impact, especially
from east and south. RECEIVED: 28/08/2026
August 2026 | 17-5
Aspect Mitigation
▪ Plant structures designed to reflect local agricultural building styles and colours to blend with the
surrounding landscape.
▪ Existing field boundary between the site and hilltop enclosure retained to minimise visual
distraction from the recorded monument.
Major
Accidents &
Disasters
▪ The Renewable Biogas Plant incorporates process-safety and containment measures including
bunded storage, leak detection, pressure control and shutdown systems, appropriate separation
and containment of hazardous materials and emergency response arrangements. The detailed
design will be subject to applicable process safety studies and statutory requirements. The Linear
Gas Grid Connection will be designed and operated in accordance with GNI's applicable safety,
integrity and monitoring requirements.
17.1.1 Construction Phase Mitigation Measures
Table 17-2 Construction Phase Mitigation Measures
Aspect Mitigation
Population &
Human Health
▪ Biogas Plant: Implementation of mitigation measures as set out in the specialist chapters
▪ Gas Grid: Implementation of mitigation measures as set out in the specialist chapters
Landscape &
Visual
▪ Adherence to the CEMP, with a qualified CEMP Coordinator appointed for the construction
duration.
▪ Implementation of good site management: perimeter hoarding, controlled site lighting, tidy site,
proper storage/compound placement, dust minimisation, clean public areas.
▪ Full tree and hedgerow protection following BS5837, with measures implemented per the
Arboricultural Report.
▪ Embedded mitigation by design at Biogas Plant Site:
o Site regraded to set primary structures into landform, reducing height and visual prominence.
o 6 m high berm created along southern and eastern boundaries for screening.
o Additional roadside berm introduced.
o Layout clusters taller elements to the west, away from receptors.
o Main building positioned internally to reduce clutter and create coherent massing.
o Colour scheme using local landscape tones (greens at lower levels, light grey upper
sections).
▪ Landscape mitigation proposals:
o Minimise views of structures and assimilate development into the landscape.
o Reinforce landscape character and existing features.
o Improve biodiversity by diversifying vegetation.
o Shape berms to reflect natural drumlin topography.
o Use mature planting to accelerate early screening.
o Replant / reinforce boundaries where vegetation removal occurs.
▪ Hedgerow measures:
o Western boundary hedgerow retained and bolstered (under-planting, whip planting,
advanced nursery stock).
o New ‘Type 2’ hedgerows planted on southern boundary (3–4m maintained height).
▪ Native woodland planting introduced around boundaries and internal locations, using mixed
canopy layers and local provenance stock.
▪ Native wildflower seeding along northern boundary near entrance to soften views.
▪ Linear Gas Grid Connection: Construction and reinstatement will be undertaken by Gas Networks
Ireland in accordance with its applicable construction and environmental management RECEIVED: 28/08/2026
August 2026 | 17-6
Aspect Mitigation
requirements. Disturbed road verges and vegetation will be appropriately reinstated following
completion of the works.
Material
Assets:
Traffic &
Transport
▪ General Construction Traffic: Construction Traffic Management Plan (CTMP) & ‘Construction
Environmental Management Plan’ (CEMP)
Material
Assets:
Built Services
▪ Implementation of all construction-phase mitigation in Section 7.9.2, including coordination with
service providers, verification of underground services, utility surveys (GPR & electromagnetic),
exclusion zones, strict quality control for pipe laying, and full adherence to the CEMP at the
Biogas Plant.
▪ Linear Gas Grid Connection: Protection of existing utilities and services will be undertaken by Gas
Networks Ireland in accordance with its applicable technical, construction and utility-coordination
requirements, including service verification, safe excavation and appropriate quality-control
procedures..
Material
Assets:
Waste
▪ Biogas Plant – Litter Pollution: The Contractor will be required to fully implement the RWMP
throughout the duration of the proposed construction phase.
▪ Biogas Plant – Unlicensed Waste Collection (Illegal Dumping): All waste leaving the site will be
recorded and copies of relevant documentation maintained.
▪ Biogas Plant – Insufficient Waste Facilities: All waste leaving the site will be recorded and copies
of relevant documentation maintained.
▪ Biogas Plant – Lack of Waste Classification: All waste material leaving site will be correctly
classified and segregation prior to removal where possible.
▪ Gas Grid: Construction resources and waste arising from the pipeline works will be managed by
Gas Networks Ireland in accordance with its applicable construction, environmental and waste
management procedures and relevant waste legislation.
Land & Soils ▪ Renewable Biogas Plant:
• Excavation, stockpiling and soil handling will be managed in accordance with the CEMP,
SSWMP and RWMP.
• Excavated material will be subject to visual inspection and, where required to establish its
classification or suitability for a proposed receiving facility, appropriate environmental testing will
be undertaken.
• Appropriate controls will be implemented for refuelling, concrete works, storage of hazardous
materials, sediment control and accidental spills.
• Suitable excavated material will be reused within the site where practicable and surplus material
will be transferred by suitably authorised contractors to appropriately authorised receiving
facilities.
▪ Linear Gas Grid Connection:
• Soil excavation, handling, reinstatement, pollution prevention and management of excavated
material will be undertaken by Gas Networks Ireland in accordance with its applicable
construction and environmental management procedures.
Water
(Hydrology &
Hydrogeology)
▪ Renewable Biogas Plant:
• Implementation of the CEMP and Soil and Surface Water Management Plan.
• Appropriate sediment and surface-water controls, including silt-control measures and
management of runoff from disturbed areas.
• Controlled refuelling and storage of fuels and chemicals, provision of spill-response equipment
and appropriate management of concrete works.
• Appropriate management, treatment and/or disposal of water arising from excavations. RECEIVED: 28/08/2026
August 2026 | 17-7
Aspect Mitigation
▪ Linear Gas Grid Connection:
• Gas Networks Ireland will implement appropriate pollution-prevention, excavation-water,
sediment-control and spill-response measures in accordance with its applicable construction and
environmental management requirements. Specific water-protection measures will apply in the
vicinity of the three identified watercourse crossings.
Biodiversity ▪ All mitigation from CEMP and specialist chapters (Air Quality, Landscape, Land & Soils, Noise &
Vibrations, Water) adopted for ecological protection.
▪ Outline CEMP and Soil & Surface Water Management Plan set out measures for managing
construction impacts on biodiversity.
▪ Flora and Fauna:
o Ecological Clerk of Works (ECoW) oversees hedgerow clearance, ensures mitigation, and
supervises replanting.
o Hedgerows enhanced via supplementary native planting; rotational cutting to maintain habitat
diversity; minimum height of 2 m.
o Root protection zones retained to maintain bat foraging and commuting potential.
o Hedgerows and trees to be removed are cut at minimum 30 cm above ground.
o Pre-clearance checks will be undertaken where required prior to vegetation removal. If an
active bird nest is identified, works capable of affecting the nest will cease and appropriate
exclusion and/or timing measures will be established by the ECoW. If a potential or confirmed
bat roost is identified, the relevant works will cease pending assessment by a suitably
qualified bat ecologist. Any requirement for licensing will be determined in accordance with
the applicable statutory requirements and, where appropriate, in consultation with NPWS.
o Ecological protection, biosecurity and reinstatement measures associated with the Linear
Gas Grid Connection will be implemented by Gas Networks Ireland in accordance with its
applicable construction and environmental management procedures.
Noise &
Vibration
▪ Biogas Plant: Construction noise impacts on surrounding NSLs controlled using best practice
measures from BS 5228-1.
▪ Gas Grid Connection: Best-practice construction noise and vibration controls will be implemented
in accordance with BS 5228 and GNI's applicable construction and environmental management
requirements.
Air Quality ▪ Control of construction dust (from construction activities and trackout) using measures in line with
IAQM Guidance (2024) and Section 13.11.1.
Climate ▪ Greenhouse Gas Emissions:
o Appoint competent contractor to undertake waste audits, identify materials for
reuse/recycling.
o Reuse materials on-site where possible.
o Prevent vehicle engine idling.
o Maintain and inspect plant and machinery regularly.
o Minimise material waste through proper timing and ordering.
o Source materials locally where possible to reduce transport CO₂ emissions.
• Vulnerability to Future Climate Change:
o Contractor to mitigate effects of extreme rainfall/flooding, winds/storms, temperature
extremes, fog, lightning, hail via site risk assessments and method statements.
o All construction materials accompanied by certified datasheets specifying limiting operating
temperatures.
Cultural
Heritage
▪ Biogas Plant:
o Direct negative effect on AA1: Preservation by record through licensed archaeological
excavation. RECEIVED: 28/08/2026
August 2026 | 17-8
Aspect Mitigation
o Following completion of the licensed archaeological excavation of AA1, topsoil stripping and
other initial ground disturbance across the remainder of the Renewable Biogas Plant site will
be subject to archaeological monitoring by a suitably qualified archaeologist under the
appropriate licence. Should previously unidentified archaeological material be encountered,
works in the affected area will cease pending assessment and consultation with the National
Monuments Service.
▪ Gas Grid:
o Potential negative effect on below-ground archaeology within Zone of Notification (ZoN) of
RMP MO022-009, ringfort: Section 12 Notification of Works and licensed archaeological
monitoring of ground disturbance.
Major
Accidents &
Disasters
▪ Renewable Biogas Plant:
• Construction will be undertaken in accordance with the CEMP, Health and Safety Plan and
applicable statutory safety requirements.
• Appropriate procedures will apply to the storage and use of compressed gas cylinders, fuels and
other potentially hazardous materials and to works during extreme weather.
▪ Linear Gas Grid Connection:
• Pipeline construction, tie-in and commissioning activities will be undertaken by Gas Networks
Ireland in accordance with its applicable construction, commissioning, safety and emergency-
response requirements.
17.1.2 Operational Phase Mitigation Measures
Table 17-3 Operational Phase Mitigation Measures
Aspect Mitigation
Population &
Human Health
▪ Biogas Plant (Landscape and Visual Impacts): Implementation of mitigation measures as set out
in the specialist chapters
▪ Biogas Plant (Air Quality): Implementation of mitigation measures as set out in the specialist
chapter
▪ Biogas Plant (Traffic Generation): Implementation of mitigation measures as set out in the
specialist chapter
▪ Biogas Plant (Noise Emissions): Implementation of mitigation measures as set out in the
specialist chapters
Landscape &
Visual
▪ Landscape planting (hedgerows, woodland, wildflower areas) allowed to mature, providing long-
term screening and integration into landscape character.
▪ Boundary planting maintains a 3–4 m height; woodland thicket reaches 8–10 m to break up
massing.
▪ Linear Gas Grid Connection: Following construction, affected road surfaces, verges and other
disturbed areas will be reinstated by Gas Networks Ireland in accordance with its applicable
reinstatement requirements.
Material
Assets:
Traffic &
Transport
▪ Operational Traffic: Driver Induction Training
▪ Operational Traffic: Site Records
Material
Assets:
Built Services
▪ Implementation of SuDS-based stormwater drainage design and maintenance/upgrade of on-site
built services at the Biogas Plant in accordance with service provider requirements. RECEIVED: 28/08/2026
August 2026 | 17-9
Aspect Mitigation
▪ No operational-phase mitigation measures required for the Gas Grid connection infrastructure
(maintained by GNI).
Material
Assets:
Waste
▪ Biogas Plant – Unlicensed Waste Collection (Illegal Dumping): The Operator will ensure that all
waste leaving the Site will be transported by suitable permitted contractors and taken to suitably
registered, permitted or licensed facilities.
▪ Biogas Plant – Poor Waste Segregation: The Operator will ensure that all waste materials will be
stored in colour coded bins or other suitable receptacles in designated, easily accessible
locations. Bins will be clearly identified with the approved waste type to ensure there is no cross
contamination of waste materials.
▪ Biogas Plant – Litter Pollution: The Operator will ensure that all waste collected from the Site of
the proposed Development will be reused, recycled or recovered, where possible, with the
exception of those waste streams where appropriate facilities are c urrently not available.
▪ Gas Grid: N/A
Land & Soils ▪ Biogas Plant – Accidental Spills, Leaks and Discharges: Regular inspection of surface water
drainage system including hydrobrake, separators / interceptors, and foul sewers is
recommended ensure no accidental discharge occurs to underlying geology. Full ad herence to
and implementation of the OEMP.
▪ Biogas Plant – Increased Sediment Run Off from Hardstanding Areas carrying Sediment and
Pollutants into the Soil and Bedrock Off-Site: Regular inspection of surface water drainage system
including hydrobrake, separators / interceptors, and foul sewers is r ecommended ensure no
accidental discharge occurs to underlying geology. Full adherence to and implementation of the
OEMP.
▪ Biogas Plant – Future Maintenance Works on Underground Services and Infrastructure involving
Soil Excavations and Soil Disturbance and Disposal: Regular inspection of surface water drainage
system including hydrobrake, separators / interceptors, and foul sewers is recommended ensure
no accidental discharge occurs to underlying geology. Full adherence to and implementation of
the OEMP.
▪ Gas Grid – No impact: Not Required
Water
(Hydrology &
Hydrogeology)
▪ Renewable Biogas Plant:
• Implementation and maintenance of the permanent surface water management system,
including rainwater harvesting, attenuation, flow controls, proprietary surface-water treatment
measures and hydrocarbon interception.
• Inspection and maintenance of bunding, drainage and containment infrastructure.
• Supplementary groundwater abstraction will be operated within the sustainable yield established
through pump testing.
▪ Linear Gas Grid Connection:
• Following construction and reinstatement, no specific operational hydrology or hydrogeology
mitigation is required.
Biodiversity ▪ Lighting: Operational lighting will be designed and operated to minimise unnecessary light spill
onto retained hedgerows, treelines and other potential bat commuting and foraging features.
Lighting will be kept to the minimum necessary for safe operation of the facility.
▪ Noise: Potentially noisy equipment housed within buildings or acoustic containers; noise
engineered to minimise impacts on fauna.
▪ Surface water & process effluent:
o Impermeable site surfaces; bunds and containment for all tanks and pipework.
o Process effluent and wash-down water contained and recycled to AD process to prevent
spillages to drains or nearby streams.
▪ SuDS measures: Rainwater harvesting, attenuation storage, oil/water separators, and silt traps to
manage surface water runoff. RECEIVED: 28/08/2026
August 2026 | 17-10
Aspect Mitigation
▪ Foul drainage: Treated in on-site package treatment plant and recirculated to AD process.
▪ Regulatory compliance: IE License from EPA ensures strict environmental operation
requirements.
Noise &
Vibration
▪ Biogas Plant:
o Plant noise limits implemented.
o Site vehicle movements restricted during daytime.
▪ Gas Grid: : Following construction and reinstatement, the buried pipeline will not comprise an
active operational noise or vibration source and no specific operational mitigation is required.
Air Quality ▪ Operational phase process emissions controlled under IE licence conditions.
Climate ▪ Greenhouse Gas Emissions:
o Incorporate design mitigation relating to operational energy usage.
▪ Vulnerability to Future Climate Change:
o Incorporated design mitigation for drainage and building design.
Cultural
Heritage
▪ Biogas Plant:
o RMP MO022-008, hilltop enclosure: Incorporated design mitigation including screening
berms and planting.
Major
Accidents &
Disasters
▪ Renewable Biogas Plant:
• Operation in accordance with applicable process-safety, containment, inspection, leak-detection
and emergency-response procedures.
• Detailed process-safety studies, including HAZOP as appropriate, will inform the final design
and operating procedures.
• A Firewater Retention Risk Assessment will be completed in accordance with EPA guidance and
any required retention measures will be incorporated prior to operation.
• Emergency response arrangements will address credible loss-of-containment, fire, explosion,
severe-weather and other relevant scenarios.
▪ Linear Gas Grid Connection:
• The pipeline will be operated and monitored by Gas Networks Ireland in accordance with its
applicable safety, integrity, leak-detection, inspection and emergency-response requirements.
RECEIVED: 28/08/2026
August 2026 | 17-11
17.1.3 Monitoring
Monitoring will be undertaken throughout the construction and operational phases of the Renewable
Biogas Plant, as appropriate, to verify the effective implementation of the mitigation measures
identified within the specialist chapters of this EIAR and to confirm compliance with the relevant
planning, environmental and regulatory requirements.
During construction, the CEMP Coordinator and relevant environmental specialists will undertake
inspections and monitoring in accordance with the CEMP and associated management plans. This will
include monitoring of construction traffic and compliance with agreed routing and delivery
arrangements; maintenance of records relating to waste generation, classification, transport and
destination; inspection of soil, surface water, sediment and pollution-prevention controls; and
environmental testing of excavated material where required to establish its classification or suitability
for a proposed receiving facility. Construction noise and dust monitoring will be undertaken in
accordance with the requirements identified in Chapters 12 and 13 respectively.
Ecological monitoring will include supervision and inspection by the Ecological Clerk of Works and/or
site environmental personnel as required during construction, including oversight of relevant
vegetation clearance and ecological protection measures. Following completion of the development,
the Landscape and Ecology Aftercare Plan will provide for monitoring and management of retained
vegetation, new planting, seeding and habitat creation areas for a minimum of three growing seasons
or three years following completion, whichever is longer.
Archaeological monitoring will be undertaken in accordance with the measures set out in Chapter 15.
This will include the licensed archaeological excavation and preservation by record of AA1 prior to the
relevant construction works and archaeological monitoring of topsoil stripping and initial ground
disturbance across the remainder of the Renewable Biogas Plant site. Any previously unidentified
archaeological material encountered during the works will be managed in consultation with the
National Monuments Service and in accordance with the applicable statutory requirements.
During operation of the Renewable Biogas Plant, monitoring will be undertaken through the facility's
operational management systems and, where applicable, in accordance with the requirements of the
Industrial Emissions Licence. This will include maintenance of waste and traffic records; inspection and
maintenance of surface water drainage, treatment, attenuation and containment infrastructure;
operational emissions monitoring; and operational noise monitoring in accordance with IE Licence
requirements. Appropriate inspection, integrity testing and monitoring of containment, storage,
process safety, leak detection and emergency response systems will also be undertaken as part of the
operation of the facility.
Landscape and ecological monitoring will continue during the establishment period to confirm the
successful establishment of proposed planting and habitat enhancement measures and to identify any
requirement for replacement planting or remedial management. Monitoring and maintenance will
thereafter continue as appropriate as part of the long-term landscape management of the site. RECEIVED: 28/08/2026
August 2026 | 17-12
The Linear Gas Grid Connection will be delivered separately by Gas Networks Ireland and the Applicant
cannot commit GNI to particular monitoring measures. The monitoring measures identified in the
specialist chapters in respect of the Linear Gas Grid Connection are therefore presented as
recommendations for implementation by GNI. These include, as appropriate, verification of soil,
water, pollution-prevention, ecological and reinstatement measures during construction;
archaeological monitoring in the vicinity of RMP MO022-009 in accordance with the applicable
statutory requirements; and operational inspection, integrity monitoring and leak detection in
accordance with GNI's applicable regulatory, technical, environmental and safety procedures. No
specific operational noise, air quality or hydrological monitoring has been identified as necessary in
respect of the buried Linear Gas Grid Connection following construction and reinstatement.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
oCEMP 28
Appendix C - Soil and Surface Water Management Plan RECEIVED: 28/08/2026
P
SOIL AND SURFACE WATER
MANAGEMENT PLAN
(SSWMP)
August 2026
STREAM BIOENERGY IRELAND LIMITED
PROPOSED RENEWABLE BIOGAS PLANT
Maghernakelly & Drumcall, Drum, County
Monaghan
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report
Soil and Surface Water Management Plan (SSWMP)
Table of Contents
1. Introduction ................................................................................................................................. 1
1.1 Overview ............................................................................................................................. 1
1.2 Objectives ........................................................................................................................... 1
1.3 Guidance ............................................................................................................................ 1
1.4 Proposed Site ..................................................................................................................... 2
2. Earthworks .................................................................................................................................. 4
3. Surface Water .............................................................................................................................. 5
3.1 Construction Management ................................................................................................. 5
3.2 Surface Water Protection Measures ................................................................................... 5
4. Surface Water Drainage Management ...................................................................................... 6
4.1 Site Drainage Management ................................................................................................ 6
4.2 Soil Management ................................................................................................................ 7
4.3 Management & Mitigation Measures .................................................................................. 7
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 1
1. Introduction
1.1 Overview
This Soil and Surface Water Management Plan (SSWMP) forms an appendix to the outline Construction
Environmental Management Plan (oCEMP) and supports the planning application by Stream BioEnergy
Ireland Limited to Monaghan County Council for the proposed Renewable Biogas Plant and associated
works at Maghernakelly and Drumcall, Drum, County Monaghan (the ‘Proposed Development’). This
SSWMP relates to construction of the Proposed Development and does not govern construction of the
separately delivered Linear Gas Grid Connection.
This SSWMP has been updated following the Further Information request issued by Monaghan County
Council in March 2026 and the subsequent refinement of the Proposed Development. In particular, the
Soil Relocation Area previously included within the planning application has been removed. Suitable
excavated soil and stone will be reused within the Renewable Biogas Plant site where appropriate, with
surplus material managed off site in accordance with the Resource and Waste Management Plan.
Stream’s proposal involves the use of anaerobic digestion (AD) technology to generate renewable
biogas from organic waste materials. Biogas generated by the proposed plant would be upgraded on
site to biomethane and exported to the gas network to replace fossil fuel derived natural gas.
The SSWMP details the control and management measures for avoiding, preventing, or reducing any
significant adverse impacts within the surface water environment during the construction phase, most
notably through the disturbance of materials (i.e. soils). The control and management measures set out
within this plan are deemed best practice in the protection of surface water during construction.
1.2 Objectives
This SSWMP has been prepared to allow the appointed Contractor to plan the works so as to minimise
and mitigate soil and surface water issues occurring on site during the construction phase. The plan will
subsequently be revised as required to confirm/update the details of construction provided within the
document (e.g. actions and control measures, method statements etc.).
The main objective of this SSWMP for the project will be to:
• Develop a strategy for soil and surface water management ensuring that the site is compliant
with relevant regulations and best practice at all stages ;
• Identify surface water and drainage issues on site during the works;
• Facilitate the implementation of surface water management measures during the works to
address any issues that may arise; and
• Avoid adverse impacts and increased pollution risk within the catchment of the Coolkill Lough
Stream.
1.3 Guidance
The SSWMP and the control and management measures relating to surface water management have
been prepared with regard to the following guidance documents, where relevant:
• Control of Water Pollution from Construction Sites. Guidance for Consultants and Contractors
(C532) (Construction Industry Research and Information Association) (CIRIA) 2002);
• Control of Water Pollution from Linear Construction Projects. Technical Guide (C648) (CIRIA
2006a);
• Control of Water Pollution from Linear Construction Projects. Site Guide (C649) (CIRIA 2006b);
• Environmental good practice on site guide (fifth edition) (C811) (CIRIA 2023)
• Safety, Health and Welfare at Work (Construction) Regulations 2013 – S.I. No. 291 of 2013; and RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 2
• Guidelines on Protection of Fisheries During Construction Works in and Adjacent to Waters
(Inland Fisheries Ireland (IFI) 2016).
The measures set out in this SSWMP comprise generally applicable good construction practice for the
management of soil and surface water and would apply to the construction works irrespective of the
presence or absence of any downstream European Site.
1.4 Proposed Site
As shown on Figure 1-1 below, the topography of the proposed development site slopes gradually
from the adjacent local roads to the northeast and west, then rises steeply towards a high point to the
south (close to the adjacent farm property). The highest elevation is in the south-west at 111.75m
Above Ordnance Datum (mAOD) and lowest elevation in the north-east at 90.00 mAOD.
Figure 1-1 Site Topography
The topographical data indicates natural drainage towards the north-east. As shown on Figure 1-2, a
land drain along the northern field boundary of the proposed development site conveys surface water
runoff via a culvert under the R189 into another land drain along the northern boundary of the L2320
(Drumgole Road), which is hydrologically connected to the Coolkill Lough Stream, which rises to the
northeast of the L2320.
A number of land drains are also aligned along the eastern and western field boundaries which
essentially separate the site from the adjacent local road network. A ditch also runs through the
central hedgerow on the proposed development site, connecting with the land drain aligned along the
eastern field boundary. As such, all land drains convey field drainage / surface run-off to the land drain
running to the north of the proposed development site. With the exception of these land drains, there
are no watercourses on the site. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 3
Figure 1-2 Land Drains & Flow Direction
As described above, the drainage ditch along the northern field boundary conveys surface water
runoff via a culvert under the R189 into another drainage ditch, which is hydrologically connected to
the Coolkill Lough Stream (essentially forming the upper part of the catchment for this watercourse).
This stream flows through a sequence of small waterbodies (such as Coolkill Lough, Drumgale
Lough, Drumhay Lough) and areas of poor drainage that are interspersed amongst the surrounding
drumlin terrain. The nature of the terrain creates a long and extended hydrological pathway as it
meanders through the sequence of low points before joining the Dromore River at Cootehill. The
Coolkill Lough Stream (IE_NW_36D020700) is a registered watercourse located approximately 395 m
north-east of the culvert on the proposed development site.
The accompanying Flood Risk Assessment concludes that the Renewable Biogas Plant site is located
within Flood Zone C and is at low risk from the sources of flooding considered. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 4
2. Earthworks
The earthworks model identifies approximately 98,420 m³ of excavated material, of which approximately
79,900 m³ of suitable excavated soil and stone will be reused within the Renewable Biogas Plant site
for engineering fill, landscaping and screening berms . This results in a net surplus of approximately
18,520 m³. For the purposes of the environmental assessments, this has been conservatively rounded
to approximately 18,600 m³ of surplus excavated soil and stone requiring removal from the site.
The surplus material will be removed off site by suitably authorised contractors for appropriate reuse,
recovery or disposal at an appropriately authorised receiving facility or facilities, to be identified by the
appointed Contractor prior to commencement of the relevant excavation works. Excavated material
awaiting reuse within the site will be temporarily stockpiled and managed in accordance with this
SSWMP and the Resource and Waste Management Plan.
Proposed earthworks include regrading the site to provide level surfaces for various proposed
buildings and plant. To accommodate this, the existing land will require bulk cut & fill to enable
movement of materials to establish the plateau levels required. Any site won material suitable for
reuse will be redistributed throughout to maximise use and minimise import and export requirements.
Given the existing site levels, earthworks are generally required to:
• allow site access roads to lead onto the existing public road network.
• limit maximum gradients for proposed roads and footpaths within the site.
• provide relatively flat areas for buildings, tank farms and turning areas for large vehicles.
The proposed development ties into existing site levels at all boundaries. Proposed external levels
range from 91.00m to 95.00mAOD across the northeast boundary, with a sequence of tiers being
formed across the site to facilitate the development so that t he site is functional.
Earthwork screening berms will be constructed to the southeast and northwest of the proposed
development site. The berm to the southeast will be approximately 9 m above existing levels, while
the berm to the northwest will be approximately 3 m above the adjacent roadway. The berms shall be
constructed with side slopes of typically 1:2 on the internal (site) face, with a 1:3 slope to the external
face visible from the roads and surrounding areas. Berms will be compacted, engineered and finished
to prevent slope failure, erosion, or loss of material onto the public road.
RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 5
3. Surface Water
3.1 Construction Management
During construction the existing drainage ditches will remain the primary mechanism and pathway
available for the mobilisation of suspended sediments within the surface water environment and shall
be the main focus of measures implemented during the works to ensure the water environment is
protected.
Surface water from the widened section of the L2280 (Drumcall Road) will continue to be managed by
the current land drain arrangement, with new drainage ditches constructed along the upgraded road
section that will connect into the existing ditch conveying water to the Coolkill Lough Stream.
Runoff control and drainage management are key elements in terms of mitigation against impacts on
surface water bodies. Two distinct methods will be employed to manage drainage water within the
proposed development. The first method involves ‘keeping clean water clean’ by avoiding disturbance
to natural drainage features, minimising any works in or around artificial drainage features, and
diverting clean surface water flow around excavations, construction areas and temporary storage
areas.
The second method involves collecting any drainage waters from works areas within the site that
might carry silt or sediment, and nutrients, to route them towards stilling ponds prior to controlled
diffuse release over vegetated surfaces. There will be no direct discharges to surface waters.
The drainage design is intended to maximise erosion control, which is more effective than having to
control sediment during high rainfall. Such a system also requires less maintenance. The area of
exposed ground will be minimised. The drainage measures wil l prevent runoff from entering the works
areas of the site from adjacent ground, to minimise the volume of sediment-laden water that has to be
managed.
3.2 Surface Water Protection Measures
The following outlines potential surface water protection measures that will be employed by the
appointed Contractor during construction works on the site as required to ensure that surface runoff
from the developed areas of the site will be of a high quality and will therefore not impact on the
quality of downstream surface water bodies.
3.2.1 Silt Fences
Silt fences will be installed as an additional surface water protection measure around existing
drainage ditches, as required. These will be installed as single, double or a series of triple silt fences,
depending on the space available and the anticipated sediment loading. Up to three silt fences may
be deployed in series.
All silt fencing will be formed using Terrastop Premium or equivalent silt fence product. Silt fences will
be inspected regularly to ensure water is continuing to flow through the fabric, and the fence is not
coming under strain from water backing up behind it.
3.2.2 Interceptor Drains
Interceptor drains will be installed upgradient of works areas as required to collect surface flow runoff
and prevent it reaching excavations and construction areas of the site where it might otherwise have
come into contact with exposed surfaces and picked up silt and sediment. The drains will be used to
divert upslope runoff around the works area to a location where it can be redistributed over the ground
surface as sheet flow. This will minimise the volume of potentially silty runoff to be managed within the
construction area. The material excavated to make the drain will be compacted on the downslope
edge of the drain to form a diversion dike. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 6
3.2.3 Check Dams
The velocity of flow in the interceptor drains, particularly on sloped sections of the channel, will be
controlled by check dams as required. These will be installed at regular intervals along the drains to
ensure flow is non-erosive. Check dams can also be installed in existing drainage channels that will
receive waters from works areas of the site, if required.
Check dams will restrict flow velocity, minimise channel erosion and promote sedimentation behind
the dam.
3.2.4 Level Spreader
A level spreader will be constructed at the end of each interceptor drain to convert concentrated flows
in the drain, into diffuse sheet flow on areas of vegetated ground, as required. The levels spreaders
will be located downgradient of any proposed works areas in locations where they will not contribute
further to water ingress to construction areas of the site.
3.2.5 Vegetation Filters
Vegetation filters are the existing vegetated areas of land that will be used to accept surface water
runoff from upgradient areas. The selection of suitable areas to use as vegetation filters will be
determined by the size of the contributing catchment, s lope and ground conditions.
Vegetation filters will carry outflow from the level spreaders as overland sheet flow, removing any
suspended solids and discharging to the groundwater system by diffuse infiltration.
Vegetation filters will not be used in isolation for waters that are likely to have higher silt loadings. In
such cases, silt-bearing water will already have passed through stilling ponds prior to diffuse
discharge to the vegetation filters via a level spreader.
3.2.6 Siltbuster
A “siltbuster” or similar equivalent piece of equipment will be available to filter any water pumped out
of excavation areas, if necessary, prior to its discharge to stilling ponds or swales.
Siltbusters are mobile silt traps that can remove fine particles from water using a proven technology
and hydraulic design in a rugged unit. The mobile units are specifically designed for use on
construction sites.
3.2.7 Silt Bags
Dewatering silt bags allow the flow of water through them while trapping any silt or sediment
suspended in the water. The silt bags provide a passive non-mechanical method of removing any
remaining silt contained in the potentially silt-laden water collected from works areas within the site.
Dewatering silt bags are an additional drainage measure that can be used on interceptor drains and
will be located wherever it is deemed appropriate. The silt bag will allow the water to flow through the
geotextile fabric and will trap any of the finer silt and sediment remaining in the water after it has gone
through the previous drainage measures.
4. Surface Water Drainage Management
4.1 Site Drainage Management
All materials and equipment necessary to implement the drainage measures outlined above will be
brought on-site in advance of any works commencing.
An adequate quantity of terram, stakes, etc. will be kept on site at all times to implement the drainage
design measures as necessary. The drainage measures outlined in the above will be installed prior to,
or at the same time as the works they are intended to drain. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 7
The works programme for the initial construction stage of the development will also take account of
weather forecasts and predicted rainfall in particular. Large excavations and movements of
soils/subsoil or vegetation stripping will be suspended or scaled back if heavy rain is forecast. The
extent to which works will be scaled back or suspended will relate directly to the amount of rainfall
forecast.
The effectiveness of drainage measures designed to minimise runoff entering works areas and
capture and treat potentially silt-laden water from the works areas will be subject to regular inspection
by the Site Manager, who will respond to changing weather, ground or drainage conditions on the
ground as the project proceeds, to ensure the effectiveness of the drainage design is maintained. This
may require the installation of additional silt fences; interceptor drains etc. as deemed necessary on-
site.
In the unlikely event that works are giving rise to siltation of watercourses, the Site Manager will stop
all works in the immediate area around where the siltation is evident. The source of the siltation will be
identified and additional drainage measures, as outlined above, will be installed in advance of works
recommencing.
4.2 Soil Management
Excavated soil and stone awaiting reuse within the Renewable Biogas Plant site will be temporarily
stockpiled in appropriately located areas. Temporary stockpiles will be managed to minimise erosion
and sediment mobilisation, including through appropriate siting, profiling, covering or stabilisation and
the use of sediment controls where required.
Suitable excavated material will be reused within the site for engineering fill, landscaping and screening
berms. Surplus excavated soil and stone which cannot be reused within the site will be removed off site
in accordance with the Resource and Waste Management Plan.
During formation of the permanent screening berms, appropriate sediment-control measures, including
silt fencing where required, will be installed downslope of the works to control surface water runoff and
minimise the potential for sediment mobilisation. The berms will be progressively formed, compacted
and finished in accordance with the relevant engineering requirements and will be topsoiled and
vegetated as soon as practicable following completion of the relevant earthworks. Until vegetation has
established and the berm surfaces have stabilised, runoff from the berms will continue to be managed
through the temporary drainage and sediment control measures set out in this SSWMP.
.
4.3 Management & Mitigation Measures
As outlined in the oCEMP, the following surface water management and mitigation measures will be
employed to prevent impact to surface water:
Issue Control Measure
General Water
management
• Identify potential pollution pathways and receptors on site;
• Define suitable controls to prevent pollution entering pathways and reaching
receptors;
• Identify temporary drainage patterns on site where interceptor channels and
site drainage towards settlement features should be;
• Protect local drains using appropriate measures (as described above); and
• Gain any appropriate consents (if required) and put measures in place to fulfil
the requirements of the consent.
Managing Run-Off • Minimise, where possible, the amount of exposed earth;
• Maintain a buffer strip to protect surface water (minimum of 5m);
• Regularly check waters for signs of pollution; and
• Prevent direct surface water run-off into drains. RECEIVED: 28/08/2026
Proposed Renewable Biogas Plant
Maghernakelly, Drum, County Monaghan
August 2026
Environmental Report 8
Issue Control Measure
Spillage Prevention • Store fuel, oil and chemicals away from drains and water bodies, and in
secondary containment in accordance with the appropriate pollution prevention
regulations (i.e. CIRIA). Storage will not be within 10 m of a watercourse and
will be bunded to 110% of capacity of the largest tank or 25% of the total
volume stored, whichever is the larger to contain the effects of any spills;
• Store solvents, chemicals or paints in accordance with their safety (COSHH)
datasheets and oil storage regulations; and
• Implement procedures for storage, use, delivery, inspection and monitoring of
polluting substances.
• Where mobile fuel bowsers used, then:
− Any flexible pipe, tap or valve will be fitted with a lock and will be secured
when not in use;
− The pump or valve will be fitted with a lock and will be secured when not in
use;
− All bowsers to carry a spill kit and relevant operatives must have spill
response training;
− Portable generators or similar fuel containing equipment will be placed on
suitable drip trays.
• Clear labelling of containers so that appropriate remedial measures can be
taken in the event of a spillage;
• All drums to be quality approved and manufactured to a recognised standard;
• If drums are to be moved around the Site, they will be secured and on spill
pallets; and
• Drums will be loaded and unloaded by competent and trained personnel using
appropriate equipment.
Monitoring • Undertake regular visual inspection of watercourses near to the site for signs
of pollution;
• Undertake regular checks of outfalls and pipework to ensure they are clean
and clear of litter;
• Monitor and investigate any complaints, incidents and near-miss occurrences;
and
• Monitor bunds and machinery for leaks.
Emergency Preparedness
& Response
• Ensure site-based staff know who to contact in the event of a spillage, what to
do and from where to get equipment;
• Ensure appropriate spill kits are available (e.g. oil only, chemical or general
use) and adequately stocked;
• Adopt and test an emergency response plan/procedure; and
• Report environmental damage that cannot be rectified immediately to the
environmental regulator and take appropriate steps to remedy the damage
caused.
RECEIVED: 28/08/2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 3.1
SITE SELECTION
ENVIRONMENTAL ANALYSIS
Stream BioEnergy Ireland Limited
AUGUST 2026
RECEIVED: 28/08/2026
ww.mhplanning.ie
DUBLIN
Kreston House, Arran Court
Arran Quay, Dublin 7, D07 K271
T. +353 (0) 1 804 4477
CORK OFFICE
6 Joyce House, Barrack
Square
Ballincollig, Cork, P31 YX97
T. +353 (0)21 420
8710
May 23 Site Screening
Planning & Environmental Screening
Monaghan Sites
1. Introduction
This Briefing Note is a preliminary analysis of two additional sites that Stream BioEnergy have
identified in Cootehill, Co. Monaghan; Site A (Figure 1) and Site B (Figure 2). The objective is to
contribute to the site selection process i.e., to recommend a preferred site having regard to
planning and environmental critieria, for the development of an Anaerobic Digestion (AD)/
Biomethane Plant, that would process poultry litter. It is understood that the client will have other
factors to consider that will influence the selection of the preferred site.
Site A is located along the R189 at Drumgarkin, Tonnagh, Dyan and Freame Mount Demesne TD.,
Cootehill, Co. Monaghan.
Site B is located along along the R189/L2280, Maghernakelly & Drumcall TD., Cootehill, Co.
Monaghan
Figure 1: Location of Sites RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 2
1.1 Planning History
A search of the Monaghan online planning database did not identify a planning history for either
site.
2. Planning Context
2.1 Zoning
Neither site is within any defined settlement or zoning under the Monaghan County Development
Plan (CDP) 2019-2025. Both sites are located within the “Remaining Rural Area” as shown in Figure
2.
Figure 2 CDP Zoning
Site A
Site B RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 3
Section 2.8.2 of the Development Plan indicates that ‘Remaining Rural Area’ lands, which are also
referred to as ‘Category 2’ lands, comprise: “all other rural areas outside of the settlements and
the rural areas under the strong urban influence.”
Within this chapter, the Economic Strategy is “to continue to provide for employment generating
uses that are locational based including, but not limited to, agribusiness, rural-based tourism and
renewable energy projects.” (Emp added)
The proposed development would service the poultry sector which generates approx. 255,000
tonnes of manure, contributes more than €600m to the economy annually and supports over
5,000 jobs, of which some 3,500 are in Monaghan, Cavan and the wider Border region.
The CDP confirms the constraints that exist in Co. Monaghan with respect to the management,
and specifically the land spreading of organic fertilisers generated from intensive agriculture
within the county.
“County Monaghan is noted for its intensive agricultural activities, and it benefits significantly from its
successful poultry and mushroom industries. Substantial quantities of broiler litter, layer manure, spent
mushroom compost and other intensive agricultural manures are dependent on off-site disposal.
Grasslands Counties, such as Monaghan, have limited spreading opportunities; have many sensitive
water bodies, substantial areas of wet soils and soils with high runoff risk. In addition, the demand for
nitrogen and phosphorus in many grassland farming situations can largely be met by on-farm bovine
manures.”
The Development Plan highlights that;
“The sustainable development of this industry depends on quality waste management systems that take
account of nutrient balances, sensitive water bodies, topography and soil conditions. Applicants for
planning or Integrated Pollution Prevention Control and Industrial Emission Licensing should refer to
Maps 8.1 Sensitive Surface Waters and 8.2 Sensitive Groundwaters and Landfills. Applicants should
consult with the local authority in relation to disposal arrangements for pig and poultry manure as well
as spent mushroom compost.”
In a Study, commissioned by Monaghan County Council in 2021, the significant quantity of poultry
manure being produced within the county and transported for land spreading outside Co.
Monaghan is highlighted. A recommendation of that study is;
“The industry should investigate and develop sustainable outlets for poultry manure to reduce the
reliance on land spreading e.g., fuel for alternative and renewable energy production (anaerobic
digestion, combined heat and power). This is an opportunity for the sector to seek improvements,
improve efficiency, establish best practice and become a leader in sustainable poultry farming. The
establishment of alternative outlets for poultry waste e.g., anaerobic digestion would provide benefits
in terms of improving the sector’s circular economy and provide scope for the sector to avail of Climate
Change Action Fund and other possible financial supports that may be available.”
Having regard to the purpose of this proposed development it is reasonable to conclude that it
aligns with the Development Plan’s economic strategy for areas identified as ‘Remaining Rural
Area’. The plant’s location within an area with a high concentration of poultry farms, and its
purpose, to manage the waste arisings and generate renewable energy, and in so doing;
i. contributing to protecting the local environment (soils and water) RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 4
ii. facilitating the future expansion of the poultry industry; and,
iii. contributing to energy security,
aligns with the principles of proper planning and sustainable development, subject to meeting
other relevant development management critieria.
2.2 Renewable Energy Policy
The Development Plan includes significant support for renewable energy (RE) technologies and
the planning authority is required to adopt a favourable approach to RE developments.
Specifically, the Development Plan requires that projects involving indigenous sources of energy
such as inter alia biogas from farm slurry be assessed with the prime policy of the Planning
Authority to permit developments that are environmentally sustainable and in accordance with
the proper planning of the area.
Monaghan County Council acknowledges the potential of bioenergy to realise several objectives
contained in the Development Plan in the areas of Energy Supply and Energy Security, Climate
Change, Environmental Quality and Pollution Economic Development & Rural Development. In
this context Monaghan County Council will promote and support its development and proposals
for Bio-energy related development shall be considered on a case-by-case basis in accordance
with planning and environmental considerations.
The following policies would be relevant to the proposed development;
EECSO 1 To afford a high level of environmental protection in County Monaghan through the
provision of quality environmental services which adhere to the precautionary principle, to
provide for sustainable development through the promotion of energy efficiency and renewable
energy to deliver a low carbon future for County Monaghan, to implement measures to reduce
the human causes of climate change and to consider its effects when formulating development
plan policies.
EP 1 To support and advance the provision of renewable energy resources and programmes in
line with the Government’s National Renewable Energy Action Plan (NREAP), the Governments’
Energy White Paper “Irelands Transition to a Low Carbon Energy Future (2015-2030) and any other
relevant policy adopted during the lifetime of this plan.
EP 4 To support the production of sustainable energy from renewable sources such as wind, solar,
bioenergy and the development of waste to energy/Combined Heat and Power Schemes at
suitable locations and subject to compliance with the Habitats Directive.
EP 9 To work in partnership with local communities to develop energy efficient and renewable
energy projects to benefit the local area subject to development management standards.
ENP 1 To encourage and facilitate renewable energy proposals at suitable locations where it is
demonstrated the development will not have a detrimental impact on the visual and residential
amenities of the surrounding area and other matters of acknowledged importance where it is
located and assessed in line with the criteria set out in Section 15.20 of the Monaghan County
Development Plan 2019-2025. RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 5
2.3 Development Management Criteria
The assessment of a project within these landholdings would be a merits-based assessment that
would have regard to the nature of existing land uses, environmental sensitivities and the ability
of the project to comply with development management standards.
The Development Plan highlights (section 15.20) that in assessing planning applications for RE
projects development, particular regard will be shown to the following:
i. Impact on the residential amenities of the area including noise and odour;
ii. Scale and layout of the project, any cumulative effects due to other projects and the
extent to which the impacts are visible across the local landscape.
iii. Visual impact of the proposal with respect to protected views, scenic routes and
designated scenic landscapes.
iv. Impact on nature conservation, ecology, soil, hydrology, groundwater, archaeology,
built heritage and public rights of way.
v. Proximity of development to aquifers and water courses and its impact on them.
vi. Impact of development on the road network in the area.
Having regard to the nature of the proposed feedstock development management critieria with
respect to poultry units should be considered, and we would advise applying the following set
back distance for this type of proposal,
A unit shall not be developed at a distance of less than one hundred metres from a dwelling within
the rural area (i.e., outside of a designated settlement) unless the third party has given written consent,
witnessed by a solicitor or a peace commissioner. (emp. added)
RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 6
3. Environmental Context
3.1 Transportation
Both sites are well located with respect to the regional road network as shown below.
Site B Site A
Figure 3: Road Network, Monaghan CDP 2019-2025 RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 7
Both sites are located in Dawson Grove ED. (No. 44) where there is one licensed and two
unlicensed poultry facilities (Figure 3).
Both proposed locations are geographically advantageous with respect to the greatest
concentration of poultry facilities in the northwest region of Co. Monaghan.
Figure 4: Distribution of Poultry Farm in Co. Monaghan (Source: Baseline Study Poultry Sector Co. Monaghan)
Site A & B RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 8
3.2 Landscape Character
The County Monaghan Landscape Character Assessment (2008) has been reviewed to identify the
landscape character and sensitivity of both proposed sites.
Site A is within that area identified as ‘Farmed Lakelands’, Landscape Character Type (LCT) No. 5
and Site B is within the ‘Drumlin Foothills’ LCT No. 3. Notably, Site B represents a transitional
location, being located at the boundary of LCT 3 and 5.
Figure 5: Landscape Character Types
The ‘Farmed Lakelands’ LCT is described as,
‘areas feature pastoral land uses and are dominated by the presence of frequent large loughs’.
The key characteristics are listed as:
The Lakeland corridor between Lough Muckno and the County boundary at Cootehill is
essentially a low-lying farmed landscape containing large Loughs punctuated by
Site B
Site A RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 9
prominent drumlins. This low-lying landscape is enclosed physically and visually by upland
drumlin farmlands located to the north and south of the area.
The landcover is predominantly pasture, although there are tracts of forestry and
woodland around the loughs.
The Dumlin Foothills are described as;
“landscape comprises a mixed topography of rising ground interspersed with chains of drumlins of a
low height albeit located in this elevated context. This landscape comprises a transition from the
pastoral lowland of the Drumlin Farmland (LCT 2) or Farmed Lakelands (LCT5) to a better drained
pastoral upland.”
The key characteristics of the ‘Drumlin Foothills’ LCT are listed as:
Rising ground with small to medium sized drumlins predominantly in a north to south
orientation.
Mid to long ranging views.
A patchwork of predominantly small sized well drained fields defined typically by native
hedgerows and used for pasture.
Patches of heath (Calluna spp) and gorse (Ulex spp).
Isolated farm and residential properties
The proposed sites are situated within Ballybay Castleblayney Lakelands Landscape Character
Areas (LCA), which is described as a low lying lakeland landscape which extends across the width
of Monaghan County. It is present as a channel located between two upland ridgelines. The
landscape contains widely spaced drumlin hills which, on the west side, exhibit in part, an east
west pattern or alignment. This character area contains numerous loughs, the majority of which
present as highly scenic landscapes. RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 10
)
Figure 6: Landscape Character Area
Within this LCA, it is considered that this is a highly scenic landscape. The farmland is generally in
very good condition and the variable drumlin topography and inter drumlin hollows is a key
contributing factor to character and high scenic quality. The lough and lough shore landscape
settings comprising reeds and riparian vegetation are highly scenic and ecologically valuable.
These would be highly sensitive to any form of development.
The landscape management principles aim to:
The designed landscapes and remnants of same serve to enhance landscape character
and scenic quality. Management plans should include for the replacement of conifer
planting with deciduous species or the use of such species as outliers to screen conifer
plantings from view.
The planting of commercial coniferous forestry near the shorelines of the lakes should be
avoided.
The maintenance of the hedgerows as an integral part of the farmed field pattern is
encouraged. Wire fence boundaries should be replaced with hedgerow plantings.
Site A & B RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 11
The lake ecological and water quality environment will require protection from sources of
pollutants and inappropriate development.
In conclusion, this is an area with a sensitive visual envelope and the design of the plant including
configuration, scale and landscaping will require attention at the design stage.
3.3 Designated Views / Routes
It is a policy SPR 1 for Scenic Routes/Views ‘To prohibit development that would disrupt or adversely
affect a view from/along any scenic route as identified in Appendix 5.’
Both sites are at a distance from the designated scenic routes in Co. Monaghan. The proposed
Site A is the closest site with approx. 4.37km northwest of Tattybrack Scenic Drive. Due to the
existing landscape setting and distance between both sites, there will be no visibility and adverse
impacts from the development is unlikely (Figure 8).
3.3.1 Policy for Scenic Routes/Views
Policy Detail
SRP 1 To prohibit development that would disrupt or adversely affect a view from/along any
scenic route as identified in Appendix 5.
Figure 7: Scenic Views & Routes RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 12
Policy Detail
SRP 2
To protect the scenic quality of lakes by prohibiting development located between a
public road and a lake where the development would interrupt a view of the lake or
adversely affect its setting or its wildlife habitat.
Development may be permitted between a public road and the lakeshore where the
development is screened from the lake by existing topography or vegetation.
3.4 Ecology
The sites are not located within a Natura 2000 site and the closest is 15km away. This is a
significant benefit having regard to the weight that the Habitats Directive carries in the planning
process.
Figure 8: Ecological Designations
The closest ecological designation is a proposed Natural Heritage Area, less than 1km from Site A.
Proposed NHAs (pNHAs) are non-statutory sites of significance for wildlife and habitats with
limited protection. Their ecological value is recognised in the Development Plan which does have
statutory footing.
Drumgole Lough is proposed for:
“One of the most striking features of the lake is the presence of large areas of reedswamp dominated
by Common (Phragmites communis). In addition to reed swamp there are small areas of wet grassland RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 13
dominated by Soft Rush (Juncus effusus) and Creeping Buttercup (Ranunculus repens). Although birdlife
on the lake is limited, Whooper Swans frequent the site during the winter months.”
“A group of ten main inter-drumlin lakes plus several smaller areas of water stretching along the River
Dromore between Cootehill and Ballybay. Nice areas of wet woodland and reed swamp. Important
wintering wildfowl population, including Whooper swans, great crested grebe and lapwings.”
Recommendation: The sites should be assessed visually for their suitability for wintering birds.
If found to be a likely suitable site, winter bird surveys should be undertaken. Note the season
runs from October through to March and a full winter count would be required to support the
application.
Table 1: Sensitive Designation Sites
Site Option Designated Type Designated Name Min. Distance
A
Special Area of Conservation (SAC) Lough Oughter and Associated Loughs 15km
Special Protection Area (SPA) Lough Oughter 20km
Proposed Natural Heritage Area (pNHA) Dromore Lakes 930m
B
Special Area of Conservation (SAC) Lough Oughter and Associated Loughs 15km
Special Protection Area (SPA) Lough Oughter 20km
Proposed Natural Heritage Area (pNHA) Drumgole Lough 865m
3.5 Land & Soils
Both sites are within Rockcorry-Cootehill Ribbed Moraines. The County Geological Report has
stated that “These are the largest individual ribbed moraine features anywhere in the world and
therefore one of the most important geological terrains in Ireland.” RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 14
Figure 9: GeoHeritage Sites
3.6 Water Environment
The water environment for both sites is illustrated in the figure below. The Crosslea stream runs
through Site A and discharges into Dromore Lough, and it is assumed that the direction of
groundwater flow would also be toward the Lough. Both the river and lake are classified as being
‘At Risk’ under the Water Framework Directive.
Site B does not host a surface water feature i.e., river or stream.
The local groundwater body is ‘Not at Risk’. The groundwater vulnerability is L, Low and the aquifer
is assigned PI, Poor Aquifer - Bedrock which is Generally Unproductive except for Local Zones. RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 15
3.7 Flood Risk
The sites are not within a flood zone. Notably, the purpose of the Flood Maps is not to designate
individual properties or point locations at risk of flooding or to replace a detailed site-specific flood
risk assessment. The latter would be required at the application stage.
Figure 10: Water Environment RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 16
3.8 Cultural Heritage
This is an area that is generally rich in cultural heritage assets. Details including distance and detail
of the heritage features can be found in the Table below.
Figure 11: Cultural Heritage
Table 2: Cultural Heritage Sites
Site
Option Designated Type Designated Name Min.
Distance
A
Record of Protected Structure (RPS) Town House
Dartrey Post Office Lodge
420m
415m
National Inventory of Architectural
Heritage (NIAH)
Tonnagh House (Reg. No. 41402221) – Regional Rating
The Rectory (Reg. No. 41402213) – Regional Rating
Damien House (Reg. No. 41402214) – Regional Rating
Dartrey House (Reg. No. 41402212) – Regional Rating
50m
115m
420m
415m
Sites and Monuments Record (SMR) Ringfort – Rath (SMR No. MO022-009)
Ringfort – Rath (SMR No. MO022-018)
335m
360m
B Record of Protected Structure (RPS) Town House & Dartry Post Office Lodge 1500m RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 17
Site
Option Designated Type Designated Name Min.
Distance
National Inventory of Architectural
Heritage (NIAH)
Tonnagh House, The Rectory, Damien House & Dartrey
House 1450m
Sites and Monuments Record (SMR)
Hilltop enclosure (SMR No. MO022-008) notification zone
Souterrain (SMR No. MO022-007002)
Ringfort – Rath (SMR No. MO022-007001)
90m
450m
450m
Site A is close to several Protected Structures and the Site B landholding partially encompasses an
enclosure with associated notification buffer zone. The direct and indirect impacts including visual
impact of the proposed development upon heritage features will require consideration.
A brief description of the Protected Structures identified in Table 2 follows;
Tonnagh House is a detached
five-bay two-storey house, dated
1824, formerly in use as army
barracks, and later as seminary.
Now in use as outdoor education
centre.
The Rectory is a detached three-
bay two-storey over basement
red brick rectory, built c.1860,
having full-height projecting
central entrance bay to front
(east) elevation, approached by
flight of steps, box-bay window
and later conservatory extension
to rear, and second porch to
corner between house and coach
house. Now in use as house. RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 18
Damien House is Detached L-plan single-
storey house with attic, built c.1870, having
three-bay short wing and five-bay long wing.
Now in use as retreat centre for religious
community.
Dartrey House is Detached three-
bay single-storey gate lodge with
half-dormer attic, built 1847, on a
T-shaped plan centred on single-
bay single-storey gabled
breakfront. Now in use as house.
The SMR describes the hilltop enclosure within Site B as located on top of a drumlin and depicted
as a large oval embanked enclosure on the 1834 edition of the OS 6-inch map where it is described
in gothic lettering as a ‘fort’, and as a large hachured oval feature on the 1907 edition. The
enclosure is an oval grass-covered area (dims 107m NW-SE; 69m NE-SW) defined by a scarp (Wth
1.2-1.3m; H 1.7-1.9m) and hedge, with a field bank at its base N-SSE replaced by a farm track SSE-
WNW. An original entrance is not identified. The "zone of notification" is the area around each
monument that is intended to be used for the purposes of notification under Section 12 of the
National Monuments Acts 1930 to 2004.
RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 19
Figure 12: SMR No. MO022-008 (Source: Historic Environment Viewer)
A review of excavations.ie identified information on testing within this general location,
https://excavations.ie/report/2006/Monaghan/0016428/. It concludes no archaeological
significance.
Testing was carried out in Maghernakelly, Co. Monaghan. The site was located on the grounds of a
disused mushroom factory. Planning permission was granted for the construction of two residential
properties with associated garages and percolation areas. The site is situated in a valley immediately
across the road from MO022–009, a rath, and falls within the buffer zone surrounding it. Testing was
conducted on 6 December 2006.
Seven trenches were excavated. The topsoil had been removed and gravel and angular stones had been
placed under an average of 0.15m of concrete. Close to the entrance of the site the concrete was too
thick to remove with the toothed digger bucket and needed a rock breaker, therefore about 33m of
Trench 1 could not be excavated. No archaeological features, deposits or artefacts were found at this
site. The features found were a result of modern drainage.
Recommendation: The planning database, reg. ref. 072002 does not include scanned application
documents for this development. We would recommend requesting these documents from the
planning authority as the archaeology report may prove useful for further insight to the rath.
Having regard to the archaeological resource, it is noted that the preferred location for the
proposed development within Site B has been further refined to a 5.5-hectare plot outside the
notification zone and approx. 90m from the enclosure. RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 20
Figure 13: Site B (5.5-hectares)
4. Screening Matrix
The summary and comparison of the sites are showing in below Table:
Table 3: Screening Matrix
Category Consideration Recommendation Preferred
Option
Planning
History No planning history at either site N/A N/A
Zoning Not within zoning boundary
Consistent with
development plan policy and
objectives supporting the
rural economy and
renewable energy.
A & B
Development
Management
Both sites similar in terms of distance
to receptors
Having regard to policy with
respect to poultry houses, it
is recommended that the
layout would have at least
100m separation distance.
A & B
Transportation Both sites A & B are located adjacent to
a Regional Road and close to existing
The sightline should be
120m in both directions. A & B
RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 21
Category Consideration Recommendation Preferred
Option
poultry houses in the north-western
part of Co. Monaghan.
Sightlines to be checked
Visual Impact
While in different LCTs the sites are
within the same LCAs.
Sites are not close to designated scenic
views.
Detailed assessment
required at application
stage.
A & B
Ecology
Designated
Sites
Not within European Designed Site.
Input from ecologist
required. A & B
Land & Soil Both sites are geologically of national
importance.
Having regard to the
relatively small footprint in
the context of the overall
designation the impact is not
considered significant.
A & B
Water
Environment
Site B - no surface water feature
Site A - surface water feature
Having regard to the nature
of the feedstock, the
connectivity between Site A
and the land, the At Risk
status of surface water
features and the designation
B
Flood Risk Neither site is within an area identified
as at risk of flooding. A & B
Cultural
Heritage
Site A is close to several Protected
structures and Site B is close to a
enclosure and associated zone of
notification.
Excavations.ie records for a plot within
the site B townland confirms no
archaeology at that location.
Archaeological advice
required.
LVIA and Photomontages are
recommended in later
stages.
B
RECEIVED: 28/08/2026
Planning & Environmental Screening
January 2012 | 22
5. Conclusion
Having regard to the sensitivities that have been identified in this screening, on balance Site B is
the emerging preferred site for the proposed development, subject to further consideration
regarding proximity to sensitive receptors, access arrangements, visual envelope, and the cultural
heritage resource.
In this regard, we advised the client to engage with the landowner to secure a larger landbank to
allow for the flexibility that may be needed for mitigation measures and as set out in Section 3.8,
a site of 5.5 hectares with direct access to the public road and outside the zone of notification is
the preferred location within the Site B landholding.
6. Reference
Monaghan County Development Plan 2019-2025
County Monaghan Landscape Character Assessment 2008
Baseline Study Poultry Sector, Co. Monaghan 2021
https://www.floodinfo.ie/map/floodmaps/
https://maps.archaeology.ie/HistoricEnvironment/
https://gis.epa.ie/EPAMaps/
https://dcenr.maps.arcgis.com/apps/MapSeries/index.html?appid=a30af518e87a4c0ab2fbde2aa
ac3c228 RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 6.1
TRAFFIC COUNTS
Stream BioEnergy Ireland Limited
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AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 6.2
NETWORK FLOW DIAGRAMS
Stream BioEnergy Ireland Limited
RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:Figure
Oct 2025
03208NTS 1
Oct 2025
TWL
Oct 20 52Surveyed Weekday Daily
Turning Traffic Flows 07:00-19:00hrs
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:Monaghan Renewable Biogas Plant JMK JMK
Drawing Title
Project Title
123
N
SITE 2
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
(Tue 21 May 2024 07:00-19:00hrs)
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
SITE 1
L2320
R188
R189
L2280
2
3
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS2
TWL
Surveyed Weekday Morning Peak Hour
Turning Traffic Flows 08:00-09:00hrs
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
(Tue 21 May 2024 08:00-09:00hrs)
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS3
TWL
Surveyed Weekday Evening Peak Hour
Turning Traffic Flows 17:00-18:00hrs
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
(Tue 21 May 2024 17:00-18:00hrs)
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:Figure
Oct 2025
03208NTS 4
Oct 2025
TWL
Oct 20 52Forecast Weekday Daily
HGV Turning Traffic Generated
Period 07:00-19:00hrsTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
23
N
SITE 2
New HGV
HGVDiverted
Movement No.
Direction
Forecast Turning Traffic
Locally New (Diverted Traffic)
12
3 4 562
1
4 6
7
2 4
3
R189
1
5
6
7
8
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
SITE 1
L2320
R188
R189
L2280
2
3
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
8
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:Figure
Oct 2025
03208NTS 5
Oct 2025
TWL
Oct 20 52Forecast Weekday Daily
LV Turning Traffic Generated
Period 07:00-19:00hrsTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
23
N
SITE 2
New HGV
HGVDiverted
Movement No.
Direction
Forecast Turning Traffic
Locally New (Diverted Traffic)
12
3 4 562
1
4 6
8
2 4
3
R189
1
5
6
7
8
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
SITE 1
L2320
R188
R189
L2280
2
3
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
7
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:Figure
Oct 2025
03208NTS 6
Oct 2025
TWL
Oct 20 52Forecast Weekday AM Peak Hour
HGV Turning Traffic Generated
Period 08:00-09:00hrsTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
23
N
SITE 2
New HGV
HGVDiverted
Movement No.
Direction
Forecast Turning Traffic
12
3 4 562
1
4 6
7
2 4
3
R189
1
5
6
7
8
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
SITE 1
L2320
R188
R189
L2280
2
3
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
8
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:Figure
Oct 2025
03208NTS 7
Oct 2025
TWL
Oct 20 52Forecast Weekday PM Peak Hour
HGV Turning Traffic Generated
Period 17:00-18:00hrsTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
23
N
SITE 2
New HGV
HGVDiverted
Movement No.
Direction
Forecast Turning Traffic
12
3 4 562
1
4 6
7
2 4
3
R189
1
5
6
7
8
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
SITE 1
L2320
R188
R189
L2280
2
3
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
8
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS8
TWL
Baseline 2030
Opening Year AM Peak Hour
Do Nothing 08:00-09:00hrsTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS9
TWL
2030 AM Peak Hour
Opening Year 08:00-09:00hrs
Do Something - Proposed DevelopmentTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
Oct 2025
03208
Oct 2025Oct 20 52
Monaghan Renewable Biogas Plant
123
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS10
TWL
2035 Opening Year +5yrs
AM Peak Hour 08:00-09:00hrs
Do NothingTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS11
TWL
2035 Opening Year +5yrs
AM Peak Hour 08:00-09:00hrs
Do Something - Proposed DevelopmentTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
Oct 2025
03208
Oct 2025Oct 20 52
Monaghan Renewable Biogas Plant
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS12
TWL
2045 Opening Year +15yrs
AM Peak Hour 08:00-09:00hrs
Do NothingTelephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9
Monaghan Renewable Biogas Plant RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS13
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
Oct 2025
03208
Oct 2025Oct 20 52
Monaghan Renewable Biogas Plant
2045 Opening Year +15yrs
AM Peak Hour 08:00-09:00hrs
Do Something - Proposed Development
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
5
6
7
8
SITE 1
L2320
R188
R189
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L2320
2
3
4
8
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS14
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant
Baseline 2030
Opening Year PM Peak Hour
Do Nothing 17:00-18:00hrs RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS15
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
Oct 2025
03208
Oct 2025Oct 20 52
Monaghan Renewable Biogas Plant
2030 PM Peak Hour
Opening Year 17:00-18:00hrs
Do Something - Proposed Development
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS16
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant
2035 Opening Year +5yrs
PM Peak Hour 17:00-18:00hrs
Do Nothing RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS17
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
Oct 2025
03208
Oct 2025Oct 20 52
Monaghan Renewable Biogas Plant
2035 PM Peak Hour
Opening Year 17:00-18:00hrs
Do Something - Proposed Development
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS18
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant
2045 Opening Year +15yrs
PM Peak Hour 17:00-18:00hrs
Do Nothing RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS19
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
Oct 2025
03208
Oct 2025Oct 20 52
Monaghan Renewable Biogas Plant
2045 PM Peak Hour
Opening Year 17:00-18:00hrs
Do Something - Proposed Development
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9 RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS20
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant
Forecast Construction Traffic
Daily Traffic Generation 07:00-19:00hrs RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS21
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant
Forecast Construction Traffic
Morning Peak Hour 08:00-09:00hrs RECEIVED: 28/08/2026
Suite 5, Gowna Plaza,
Bracetown Business Park
D15 R59T
+353 (0)1 8253015
www.trafficwise.ie
info@trafficwise.ie
Date:Date:Date:
Scale:Project No:FigureNTS22
TWL
Telephone:
Website:
E-mail:Appendix B
Prepared:Approved:Checked:
JMK JMK
Drawing Title
Project Title
123
N
SITE 2
12
3 4 562
1
4 5 6
7 8 9
12
1110
1 2
3
4
5
6
3
R189
1
2
3
5
6
7
8
SITE 1
L2320
R188
R189
Oct 2025
03208
Oct 2025Oct 20 52
L2280
1
Junctions
R189/L2280/L2320 Priority Junction
R189/R188 Priority Junction
Proposed Development Access L2280
22
3
Light Vehicles
HGV
Movement No.
Direction
Junction Turning Counts
4
1
2
3
4
5
6
7
Links
R188 South of R189
R188 North of Ri89 (Rockcorry)
R189 East of R189
R189 South of L2280
R189 North of L2280 (Newbliss)
L2280 between Access and R189
L2280 west of Access
L23208
9
Monaghan Renewable Biogas Plant
Forecast Construction Traffic
Evening Peak Hour 17:00-18:00hrs RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 7.1
ELECTRICAL CONNECTION
FEASIBILITY
Stream BioEnergy Ireland Limited
RECEIVED: 28/08/2026
Bridge Street Centre
Portlaoise, Ireland
T: +353 57 8665400
F: +353 57 8665444
E: info@fingleton.ie
W: www.fingleton.ie
Fingleton White, Bridge Street Centre, Portlaoise, Co. Laois, Ireland, R32 W0CC Registered No: 86002
Directors: M. Lennon, J.Fingleton, F.O’Mahony, K. Fortune, A. Fingleton, D. Gleeson
David Mullan
Stream BioEnergy, Monaghan AD Plant,
22nd October 2025
Dear David,
Regarding the potential electrical connection and network to supply the site in development, there is a
10 kV overhead power line passing nearby that routes back to the Errigal substation, which has 38 kV
as primary voltage level and 10 kV as secondary voltage level and is the closest substation to the
site, indicating a potentially viable point of connection.
It is understood the site intends to seek a connection to this overhead power line to provide a backup
power supply to the site (c. 500 kVA). ESB overhead lines at 10 kV will typically handle load
capacities ranging from 500 kVA to 5 MVA, meaning the site’s backup electrical requirements would
be at the lower end of likely available capacity. The current loading state and exact capacity of this
power line is unknown, with final confirmation of capacity subject to ESB’s internal network
assessment which can only take place once a connection application is submitted referencing a valid
planning application number.
Yours Sincerely,
__________________________
Dermot Costelloe
Associate Director
Fingleton White & Co. Ltd.
Bridge Street Centre
Portlaoise, Co. Laois
Ph: +353 (0)57 8665 400
RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 8.1
RESOURCE & WASTE
MANAGEMENT PLAN
Stream BioEnergy Ireland Limited
RECEIVED: 28/08/2026
Appendix 8.1 Resource & Waste Management Plan
Project Title: Proposed Renewable Biogas Plant, Maghernakelly Drum, County Monaghan
CLIENT
Stream
BioEnergy
Ireland Ltd
DOCUMENT REFERENCE
247501.0350WMR01a
DATE
10/07/2026
AWN Consulting Ltd, The Tecpro Building, IDA Business & Technology Park, Clonshaugh, Dublin 17, D17 XD90
REPORT
RECEIVED: 28/08/2026
DOCUMENT CONTROL SHEET
Document Control Sheet
Our Reference 247501.0350WMR01a
Original Issue Date 25/11/2025
Client: Stream BioEnergy Ireland Ltd
Revision Revision Date Description
a 10/07/2026 Design Update
Details Written by Approved by
Signature
Name Chonaill Bradley Fergal Callaghan
Title Principal Environmental Consultant Director
Date 10/07/2026 10/07/2026
Disclaimer
This report considers the specific instructions and requirements of our client. It is not intended for third -party
use or reliance, and no responsibility is accepted for any third party. The provisions in this report apply solely
to this project and should not be assumed applicable to other developments without review and modification. RECEIVED: 28/08/2026
Stream BioEnergy Ireland Ltd / 247501.0350WMR01a
AWN Consulting Ltd
TABLE OF CONTENTS
1. INTRODUCTION 1-1
2. OVERVIEW OF WASTE MANAGEMENT IN IRELAND 2
2.1 National level ........................................................................................................... 2
2.2 Regional Level .......................................................................................................... 3
2.3 Legislative Requirements ......................................................................................... 5
3. DESIGN APPROACH 6
3.1 Designing For Prevention, Reuse and Recycling ....................................................... 6
3.2 Designing for Green Procurement ............................................................................ 6
3.3 Designing for Off-Site Construction ......................................................................... 7
3.4 Designing for Materials Optimisation During Construction ...................................... 7
3.5 Designing for Flexibility and Deconstruction ............................................................ 7
4. DESCRIPTION OF THE DEVELOPMENT 8
4.1 Location, Size and Scale of the Development ........................................................... 8
4.2 Details of the Non-Hazardous Wastes to be Produced ........................................... 10
4.3 Potential Hazardous Wastes Arising ....................................................................... 11
4.3.1 Contaminated Soil ............................................................................................... 11
4.3.2 Fuel/Oils ............................................................................................................ 11
4.3.3 Invasive Plant Species ......................................................................................... 11
4.3.4 Asbestos ............................................................................................................ 12
4.3.5 Other Known Hazardous Substances ..................................................................... 12
5. ROLES AND RESPONSIBILITIES 13
5.1 Role of the Client ................................................................................................... 13
5.2 Role of the Client Advisory Team ........................................................................... 13
5.3 Future Role of the Contractor ................................................................................ 13
6. KEY MATERIALS & QUANTITIES 15
6.1 Project Resource Targets ....................................................................................... 15
6.2 Main Construction Waste Categories ..................................................................... 15
6.3 Demolition Waste Generation ................................................................................ 16
6.4 Construction Waste Generation ............................................................................. 16
6.5 Proposed Resource and Waste Management Options ............................................ 17
6.6 Tracking and Documentation Procedures for Off-Site Waste ................................. 20
7. ESTIMATED COST OF WASTE MANAGEMENT 21
7.1 Reuse ..................................................................................................................... 21
7.2 Recycling ............................................................................................................... 21
7.3 Disposal ................................................................................................................. 21
8. TRAINING PROVISIONS 22
8.1 Resource Manager Training and Responsibilities ................................................... 22
8.2 Site Crew Training .................................................................................................. 22
9. TRACKING AND TRACING / RECORD KEEPING 23
10. OUTLINE WASTE AUDIT PROCEDURE 24
10.1 Responsibility for Waste Audit ............................................................................... 24
10.2 Review of Records and Identification of Corrective Actions ................................... 24
10.3 Pest Management .................................................................................................. 24 RECEIVED: 28/08/2026
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11. CONSULTATION WITH RELEVANT BODIES 25
11.1 Local Authority ....................................................................................................... 25
12. CONCLUSION 26
13. REFERENCES 27
LIST OF TABLES
Table 6.1 Typical waste types generated and LoW codes (individual waste types may contain hazardous
substances) 15
Table 6.2 Waste materials generated on a typical Irish construction site 16
Table 6.3 Predicted on and off-site reuse, recycle and disposal rates for construction waste 16
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1. INTRODUCTION
AWN Consulting, a Trinity Consultants Team, has prepared this Construction and Demolition (C&D)
Resource & Waste Management Plan (RWMP) on behalf of Stream BioEnergy Ireland Ltd. The proposed
development will utilise anaerobic digestion (AD) (the Proposed Development) technology to generate
renewable energy in the form of biomethane from up to 99,000 tonnes of feedstock per annum consisting
of poultry manure along with cattle manure, and agri-food organic waste feedstock, sourced from the
surrounding area.
AD is a sustainable form of renewable energy production that occurs when micro-organisms break down
biodegradable material in the absence of oxygen in an enclosed system to produce a renewable biogas.
A full description is included in the Description of the Proposed Development Chapter of this EIAR and in
the statutory notices.
This plan provides information necessary to ensure that the management of C&D waste at the site is
undertaken in accordance with the current legal and industry standards including the Waste Management
Act 1996 as amended and associated Regulations 1, Environmental Protection Agency Act 1992 as
amended 2, Litter Pollution Act 1997 as amended 3,the National Waste Management Plan for a Circular
Economy 2024 - 2030 (NWMPCE) (2024) 4. In particular, this plan aims to ensure maximum recycling,
reuse and recovery of waste with diversion from landfill, wherever possible. It also provides appropriate
measures in relation to the collection and transport of waste from the site to prevent issu es associated
with litter or more serious environmental pollution (e.g. contamination of soil and/or water).
This RWMP includes information on the legal and policy framework for C&D waste management in Ireland,
estimates of the type and quantity of waste to be generated by the proposed plant and prescribes
measures for the management of different waste streams. The RWMP should be viewed as a live document
and will be regularly revisited throughout the project’s lifecycle so that opportunities to maximise waste
reduction / efficiencies are exploited throughout, and that data is collected on an ongoing basis so that it
is as accurate as possible.
This RWMP relates to construction of the Renewable Biogas Plant and associated works forming the
Proposed Development. Construction waste associated with the Linear Gas Grid Connection will be
managed separately by Gas Networks Ireland in accordance with its applicable construction, environmental
and waste management procedures.
RECEIVED: 28/08/2026
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2. OVERVIEW OF WASTE MANAGEMENT IN IRELAND
2.1 National level
The Irish Government issued a policy statement in September 1998, Changing Our Ways 5, which identified
objectives for the prevention, minimisation, reuse, recycling, recovery and disposal of waste in Ireland.
The target for C&D waste in this report was to recycle at least 50% of C&D waste within a five year period
(by 2003), with a progressive increase to at least 85% over fifteen years (i.e. 2018).
In response to the Changing Our Ways report, a task force (Task Force B4) representing the waste sector
of the already established Forum for the Construction Industry, released a report entitled ‘Recycling of
Construction and Demolition Waste’ 6 concerning the development and implementation of a voluntary
construction industry programme to meet the Government’s objectives for the recovery of C&D waste.
In September 2020, the Irish Government published a policy document outlining a new action plan for
Ireland to cover the period of 2020-2025. This plan, ‘A Waste Action Plan for a Circular Economy’ 7
(WAPCE), replaces the previous national waste management plan, “A Resource Opportunity” (2012), and
was prepared in response to the ‘European Green Deal’ which sets a roadmap for a transition to an altered
economical model, where climate and environmental challenges are turned into opportunities.
The WAPCE sets the direction for waste planning and management in Ireland up to 2025. This reorientates
policy from a focus on managing waste to a much greater focus on creating circular patterns of production
and consumption. Other policy statements of a number of public bodies already acknowledge the circular
economy as a national policy priority.
The policy document contains over 200 measures across various waste areas including circular economy,
municipal waste, consumer protection and citizen engagement, plastics and packaging, construction and
demolition, textiles, green public procurement and waste enforcement.
One of the first actions to be taken was the development of the Whole of Government Circular Economy
Strategy 2022-2023 ‘Living More, Using Less’ (2021) 8 to set a course for Ireland to transition across all
sectors and at all levels of Government toward circularity and was issued in December 2021. It is
anticipated that the Strategy will be updated in full every 18 months to 2 years.
The Circular Economy and Miscellaneous Provisions Act 2022 9 was signed into law in July 2022. The Act
underpins Ireland’s shift from a "take-make-waste" linear model to a more sustainable pattern of
production and consumption, that retains the value of resources in our economy for as long as possible
and that will work to significantly reduce our greenhouse gas emissions. The Act defines Circular Economy
for the first time in Irish law, incentivises the use of recycled and reusable alternatives to wasteful, single-
use disposable packaging, introduces a mandatory segregation and incentivised charging regime for
commercial waste, streamlines the national processes for End-of-Waste and By-Products decisions,
tackling the delays which can be encountered by industry, and supporting the availability of recycled
secondary raw materials in the Irish market, and tackles illegal fly-tipping and littering.
The Environmental Protection Agency (EPA) of Ireland issued ‘Best Practice Guidelines for the Preparation
of Resource & Waste Management Plans for Construction & Demolition Projects’ in November 2021 10.
These guidelines replace the previous 2006 guidelines issued by The National Construction and Demolition
Waste Council (NCDWC) and the Department of the Environment, Heritage and Local Government
(DoEHLG) in 2006 11. The guidelines provide a practical approach which is informed by best practice in
the prevention and management of C&D wastes and resources from design to construction of a project,
including consideration of the deconstruction of a project. These guidelines have been followed in the
preparation of this document and include the following elements:
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► Predicted C&D wastes and procedures to prevent, minimise, recycle and reuse wastes;
► Design teams roles and approach;
► Relevant EU, national and local waste policy, legislation and guidelines;
► Waste disposal/recycling of C&D wastes at the site;
► Provision of training for Resource Waste Manager (RM) and site crew;
► Details of proposed record keeping system;
► Details of waste audit procedures and plan; and
► Details of consultation with relevant bodies i.e. waste recycling companies, Local Authority, etc.
Section 3 of the Guidelines identifies thresholds above which there is a requirement for the preparation of
a bespoke RWMP for developments. The new guidance classifies developments on a two -tiered system.
Developments which do not exceed any of the following thresholds may be classed as Tier 1 development,
which require a simplified RWMP:
► New residential development of less than 10 dwellings.
► Retrofit of 20 dwellings or less.
► New commercial, industrial, infrastructural, institutional, educational, health and other developments
with an aggregate floor area less than 1,250m2.
► Retrofit of commercial, industrial, infrastructural, institutional, educational, health and other
developments with an aggregate floor area less than 2,000m2; and
► Demolition projects generating in total less than 100m3 in volume of C&D waste.
A development which exceeds one or more of these thresholds is classed as Tier-2 development.
The Proposed Development is classified as a Tier 2 project having regard to its scale and nature and the
applicable EPA thresholds. Accordingly, this bespoke RWMP has been prepared in accordance with the
requirements for Tier 2 projects set out in the EPA Guidelines.
Other guidelines followed in the preparation of this report include ‘Construction and Demolition Waste
Management – a handbook for Contractors and Site Managers’ 12 , published by FÁS and the Construction
Industry Federation in 2002 and the previous guidelines, ‘Best Practice Guidelines for the Preparation of
Waste Management Plans for Construction and Demolition Projects’ (2006).
These guidance documents are considered to define best practice for C&D projects in Ireland and describe
how C&D projects are to be undertaken such that environmental impacts and risks are minimised and
maximum levels of waste recycling are achieved.
2.2 Regional Level
The Proposed Development is located in the Local Authority area of Monaghan County Council (MCC).
The Connacht-Ulster Region (CUR) Waste Management Plan 2015 – 2021, which previously governed
waste management policy in the MCC area, has been superseded as of March 2024 by the NWMPCE
2024 – 2030, the national waste management plan for Ireland.
The NWMPCE does not dissolve the three regional waste areas. The NWCPCE sets the ambition of the
plan to have a 0% total waste growth per person over the life of the Plan with an emphasis on non -
household wastes including waste from commercial activities and the construction and demolition sector.
This Plan seeks to influence sustainable consumption and prevent the generation of waste, improve the
capture of materials to optimise circularity and enable compliance with policy and legislation.
The national plan sets out the following strategic targets for waste management in the country that are
relevant to the development: RECEIVED: 28/08/2026
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National Targets
1B. (Construction Materials) 12% Reduction in Construction & Demolition Waste Generated by 2030.
3B. (Reuse Facilities) Provide for reuse at 10 Civic Amenity Sites, minimum.
Municipal landfill charges in Ireland are based on the weight of waste disposed. In the Region, charges
are approximately €140-160 per tonne of waste, which includes a €85 per tonne landfill levy introduced
under the Waste Management (Landfill Levy) (Amendment) Regulations 2015 (as amended)13. The Circular
Economy (Waste Recovery Levy) Regulations 2024 14 will also incur a levy of €10 per tonne for waste
accepted for recovery. This will include backfilling at authorised recovery sites and at municipal waste
landfills.
The Monaghan County Council Development Plan 2025 – 2031 (2025) 15 sets out a number of objectives
and policies for the Monaghan area in line with the objectives of the National Waste Management Plan,
including the following:
Waste Management Objectives
► WMO 1 To implement and support the strategic objectives of the National Waste Management Plan
for a Circular Economy 2024-2030 and any new or updated/subsequent versions.
► WMO 2 To implement the provisions of the Litter Management Plan 2021 – 2023 and any new or
updated/subsequent versions.
► WMO 3 To apply the ‘Polluter Pays’ Principle, proximity principle, and the precautionary principle in
respect of all waste management activities.
► WMO 4 To encourage best environmental practice in all agricultural, industry, business and local
authority activities.
► WMO 5 To support the circular and bioeconomy through the efficient use of resources and to support
any development proposals which contribute to this concept.
► WMO 6 To support the minimisation of waste creation and promote a practice of reduce , reuse and
recycle where possible, and to safeguard the environment by seeking to ensure that residual waste
is disposed of appropriately.
► WMO 8 To require that treatment/management of any contaminated material shall comply as
appropriate with the Waste Management Act 1996 (waste licence, waste facility permit) and under
the Environmental Protection Act 1992 (Industrial Emissions licensing, in particular the First Schedule,
Class 11 Waste).
► WMO 9 To ensure that all new waste management infrastructure is sited in accordance with the
provisions of the Waste Management Infrastructure Guidance for Siting Waste Management Facilities
included within the National Waste Management Plan for a Circular Economy 2024-2030.
► WMO 10 To have regard to the National Enforcement Priorities in the area of waste enforcement.
► WMO 12 To promote the sustainable management of poultry and other agricultural wastes through
renewable energy facilities to reduce nutrient runoff, improve water quality, minimise greenhouse
gas emissions, and support energy generation, while ensuring the protection of local and water
resources.
Waste Management Policies
► WMP 1 All proposals relating to management and disposal of Construction and Demolition
Materials and Waste must adhere to the Environmental Protection Agency Best Practice Guidelines
for the preparation of Resource and Waste Management Plans for Construction and Demolition
Projects 2024, and any new or updated/subsequent versions. RECEIVED: 28/08/2026
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2.3 Legislative Requirements
The primary legislative instruments that govern waste management in Ireland and applicable to the
development are:
► Waste Management Act 1996 as amended;
► Environmental Protection Agency Act 1992 as amended;
► Litter Pollution Act 1997 as amended;
► Planning and Development Act 2000 as amended 16;
► Circular Economy and Miscellaneous Provisions Act 2022.
One of the guiding principles of European waste legislation, which has in turn been incorporated into the
Waste Management Act 1996 as amended and subsequent Irish legislation, is the principle of “Duty of
Care”. This implies that the waste producer is responsible for waste from the time it is generated through
until its legal recycling, recovery or disposal (including its method of disposal). As it is not practical in most
cases for the waste producer to physically transfer all waste from where it is produced to the final
destination, waste contractors will be employed to physically transport waste to the final destination.
Following on from this is the concept of “Polluter Pays” whereby the waste producer is liable to be
prosecuted for pollution incidents, which may arise from the incorrect management of waste produced,
including the actions of any contractors engaged (e.g. for transportation and disposal/recovery/recycling
of waste).
It is therefore imperative that the Developer ensures that the waste contractors engaged by construction
contractors are legally compliant with respect to waste transportation, recycling, recovery and disposal.
This includes the requirement that a contractor handle, transport and recycle/recover/dispose of waste in
a manner that ensures that no adverse environmental impacts occur as a result of any of these activities.
A collection permit to transport waste must be held by each waste contractor which is issued by the
National Waste Collection Permit Office (NWCPO). Waste receiving facilities must also be appropriately
permitted or licensed. Operators of such facilities cannot receive any waste, unless in possession of a
Certificate of Registration (COR) or waste permit granted by the relevant Local Authority under the Waste
Management (Facility Permit & Registration) Regulations 2007 as amended or a Waste Licence granted by
the EPA. The COR / permit / licence held will specify the type and quantity of waste able to be received,
stored, sorted, recycled, recovered and/or disposed of at the specified site. RECEIVED: 28/08/2026
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3. DESIGN APPROACH
The client and the design team have integrated the ‘Best Practice Guidelines for the Preparation of
Resource & Waste Management Plans for Construction & Demolition Projects’ guidelines into the design
workshops, to help review processes, identify and evaluate resource reduction measures and investigate
the impact on cost, time, quality, buildability, second life and management post construction. Further
details on these design principals can be found within the aforementioned guidance document.
The design team have undertaken the design process in line with the international best practice principles
to firstly prevent wastes, reuse where possible and thereafter sustainably reduce and recover materials.
The below sections have been the focal point of the design process and material selections and will
continued to be analysed and investigated throughout the design process and when selecting material.
As noted in the EPA guidelines, the approaches presented are based on international principles of
optimizing resources and reducing waste on construction projects through:
► Prevention;
► Reuse;
► Recycling;
► Green Procurement Principles;
► Off-Site Construction;
► Materials Optimisation; and
► Flexibility and Deconstruction.
3.1 Designing For Prevention, Reuse and Recycling
Undertaken at the outset and during project feasibility and evaluation the Client and Design Team
considered:
► Establishing the potential for any reusable site assets (buildings, structures, equipment, materials,
soils, etc.);
► The potential for refurbishment and refit of existing structures or buildings rather than demolition
and new build (No demolition required);
► Assessing any existing buildings on the site that can be refurbished either in part or wholly to meet
the Client requirements ; and
► Enabling the optimum recovery of assets on site.
3.2 Designing for Green Procurement
Waste prevention and minimisation pre-procurement have been discussed and will be further discussed in
this section. The Design Team will discuss proposed design solutions, encourage innovation in tenders and
incentivise competitions to recognise sustainable approaches. They will also discuss options for packaging
reduction with the main Contractor and subcontractors/suppliers using measures such as ‘Just -in-Time’
delivery and use ordering procedures that avoid excessive waste. The Green procurement extends from
the planning stage into the detailed design and tender stage and will be an ongoing part of the long-term
design and selection process for this development.
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3.3 Designing for Off-Site Construction
Use of off-site manufacturing has been shown to reduce residual wastes by up to 90% (volumetric building
versus traditional). The decision to use offsite construction is typically cost led but there are significant
benefits for resource management. Some further considerations for procurement which are being
investigated as part of the design process are listed as follows:
► Modular buildings as these can displace the use of concrete and the resource losses associated with
concrete blocks such as broken blocks, mortars, etc.;
• Modular buildings are typically pre-fitted with fixed plasterboard and installed insulation,
eliminating these residual streams from site.
► Use of pre-cast structural concrete panels which can reduce the residual volumes of concrete blocks,
mortars, plasters, etc.;
► The use of prefabricated composite panels for walls and roofing to reduce residual volumes of
insulation and plasterboards;
► Using pre-cast hollow-core flooring instead of in-situ ready mix flooring or timber flooring to reduce
the residual volumes of concrete/formwork and wood/packaging, respectively; and
► Designing for the preferential use of offsite modular units.
3.4 Designing for Materials Optimisation During Construction
To ensure manufacturers and construction companies adopt lean production models, including maximising
the reuse of materials onsite as outlined in section 3.1, structures should be designed with the intent of
designing out waste. This helps to reduce the environmental impacts associated with transportation of
materials and from waste management activities. This includes investigating the use of standardised sizes
for certain materials to help reduce the amount of offcuts produced on site, focusing on promotion and
development of off-site manufacture.
3.5 Designing for Flexibility and Deconstruction
Design flexibility has and will be investigated throughout the design process to ensure that where possible
products (including buildings) only contain materials that can be recycled and are designed to be easily
disassembled. Material efficiency is being considered for the duration and end of life of a building project
to produce; flexible, adaptable spaces that enable a resource-efficient, low-waste future change of use;
durability of materials and how they can be recovered effectively when maintenance and refurbishment
are undertaken and during disassembly/deconstruction. RECEIVED: 28/08/2026
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4. DESCRIPTION OF THE DEVELOPMENT
4.1 Location, Size and Scale of the Development
The Proposed Development will utilise AD technology to generate renewable biogas from up to 99,000
tonnes of organic waste feedstocks per annum. it will comprise a state-of-the-art AD facility designed to
meet the highest environmental and safety standards.
As shown in Figure 4.3 and in the Proposed Site Layout Plan, the Proposed Development comprises a
number of integrated elements including:
► 1 - Administration Building (with associated surface level car parking);
► 2 - Main Process Building (with associated vehicle service areas);
► 3 - Odour Control System (with associated emission stack);
► 4 - Bunded Tank Farm (accommodating the vast majority of tanks that require containment);
► 5 - Digestate Treatment Plant (Evaporator);
► 6 - Digestate Drying Plant;
► 7 - Pellet Hall (for fertiliser storage);
► 8 - Combined Heat and Power (CHP) Building (accommodating two CHP Units);
► 9 - Boiler Unit;
► 10 - Shared Emission Stack (Digestate Drying Plant, CHP and Boiler Units);
► 11 - CO2 Liquefaction Plant;
► 12 - Biogas Upgrade Plant (BUP);
► 13 - Biogas Treatment Plant (Biological De-sulphurisation Units);
► 14 - Gas (Holder) Buffer Dome;
► 15 - Weighbridges and Wheel Washes;
► 16 - Liquid Feedstock Storage Tanks (silos);
► 17 - Backup Gas Flare;
► 18 - Fuel Storage Tank;
► 19 - Gas Grid Entry Unit;
► 20 - Fire Water Storage Tank;
► 21 - Liquefied Petroleum Gas (LPG) Storage Tanks (Propane);
► 22 - Freshwater Storage Tank (Underground);
► 23 - Staff and Visitor Parking;
► 24 - Control Building;
► 25 - Transformer; and
► 26 - Back-Up generator.
Other integrated elements include:
► Internal road and footway provision;
► Engineered stormwater drainage system;
► Landscaping and Earthworks;
► Lighting;
► Fencing and security gates; and
► Site entrance/exit off the L2280 Drumcall Road with gated frontage. This shall include localised
widening and realignment of this road and reconfiguration of the junction with the R189.
A full description is included in Description of the Proposed Development Chapter of this EIAR and in the
statutory notices.
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Figure 4.1 Proposed Site Location Red Line Boundary
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Figure 4.2 Proposed Site Layout & Redline Boundary
4.2 Details of the Non-Hazardous Wastes to be Produced
There will be no demolition associated with the Proposed Development and as such there will be no
demolition waste produced.
The earthworks model prepared by McAdam identifies approximately 98,420 m³ of excavated material, of
which approximately 79,900 m³ of suitable excavated soil and stone will be reused within the Renewable
Biogas Plant site for engineering fill, landscaping and screening berms. This results in a net surplus of
approximately 18,520 m³. For the purposes of the environmental assessments, this quantity has been
conservatively rounded to approximately 18,600 m³ of surplus excavated soil and stone requiring removal
from the site.
The surplus material will be removed by suitably authorised contractors for appropriate reuse, recovery or
disposal at an appropriately authorised receiving facility or facilities.
During the construction phase there may be a surplus of building materials, such as timber off-cuts, broken
concrete blocks, cladding, plastics, metals and tiles generated. There may also be excess concrete during
construction which will need to be disposed of. Plastic and cardboard waste from packaging and supply of
materials will also be generated. The contractor will be required to ensure that oversupply of materials is
kept to a minimum and opportunities for reuse of suitable materials are maximised.
Waste will also be generated from construction workers e.g. organic / food waste, dry mixed recyclables
(waste paper, newspaper, plastic bottles, packaging, aluminium cans, tins and Tetra Pak cartons), mixed RECEIVED: 28/08/2026
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non-recyclables and potentially sewage sludge from temporary welfare facilities provided on site during
the construction phase. Waste printer / toner cartridges, waste electrical and electronic equipment (WEEE)
and waste batteries may also be generated infrequently from site offices.
4.3 Potential Hazardous Wastes Arising
4.3.1 Contaminated Soil
Excavated material will be subject to visual inspection and, where required to establish its classification or
suitability for a proposed receiving facility, appropriate environmental testing will be undertaken prior to
removal from the site.
In the unlikely event that any potentially contaminated material is encountered, it will need to be
segregated from clean / inert material, tested and classified as either non-hazardous or hazardous in
accordance with the EPA publication entitled ‘Waste Classification: List of Waste & Determining if Waste
is Hazardous or Non-Hazardous’ 17 using the HazWasteOnline application (or similar approved classification
method). The material will then need to be classified as clean, inert, non-hazardous or hazardous in
accordance with the EC Council Decision 2003/33/EC 18, which establishes the criteria for the acceptance
of waste at landfills.
In the unlikely event that Asbestos Containing Materials (ACMs) are found within the excavated material,
the removal will only be carried out by a suitably permitted waste contractor, in accordance with the
Safety, Health and Welfare at Work (Exposure to Asbestos) Regulations 2006-2010 19 and the Best Practice
Guidance for Handling Asbestos (2023) 20. All asbestos will be taken to a suitably licensed or permitted
facility.
In the unlikely event that hazardous soil, or historically deposited waste is encountered during the
construction phase, the contractor will notify MCC and provide a Hazardous / Contaminated Soil
Management Plan, to include estimated tonnages, description of location, any relevant mitigation,
destination for disposal / treatment, in addition to information on the authorised waste collector(s).
4.3.2 Fuel/Oils
Fuels and oils are classed as hazardous materials; any on-site storage of fuel / oil, and all storage tanks
and all draw-off points will be bunded and located in a dedicated, secure area of the site. Provided that
these requirements are adhered to and the site crew are trained in the appropriate refueling techniques,
it is expected that there will be only small volumes of fuel / oil waste generated at the site. Any fuel / oil
waste generated will be stored in a bunded area/storage unit pending collection by a suitably permitted
contractor for transfer to a suitably licenced facility.
4.3.3 Invasive Plant Species
A site survey was undertaken by Veon (Project ecologist). This included a site walkover survey of the
entire site, and around part of the outside perimeter to search for any invasive species listed on the Third
Schedule of the European Communities (Birds and Natural Habitats) Regulations 2011 (as amended).
There were no schedule 3 invasive species, such as Japanese Knotweed located on site.
Further detail on the invasive species survey can be found in the Biodiversity Chapter of the EIAR.
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4.3.4 Asbestos
As there is no demolition associated with the Proposed Development, it is unlikely that quantities of
asbestos or asbestos containing materials (ACMs) will be located on site.
If any asbestos is detected, the removal of asbestos or ACMs will be carried out by a suitably qualified
contractor and ACMs will only be removed from site by a suitably permitted / licenced waste contractor,
in accordance with the Safety, Health and Welfare at Work (Exposure to Asbestos) Regulations 2006-2010
and the Best Practice Guidance for Handling Asbestos (2023). All material will be taken to a suitably
licensed or permitted facility.
4.3.5 Other Known Hazardous Substances
Paints, glues, adhesives and other known hazardous substances will be stored in designated areas. They
will generally be present in small volumes only and associated waste volumes generated will be kept to a
minimum. Wastes will be stored in appropriate receptacles pending collection by an authorised waste
contractor.
In addition, WEEE (containing hazardous components), printer toner / cartridges, batteries (Lead, Ni-Cd
or Mercury) and / or fluorescent tubes and other mercury containing waste may be generated from during
C&D activities or temporary site offices. These wastes, if generated, will be stored in appropriate
receptacles in designated areas of the site pending collection by an authorised waste contractor.
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5. ROLES AND RESPONSIBILITIES
The Best Practice Guidelines on the Preparation of Resource Waste Management Plans for Construction
and Demolition Projects promotes that a suitably qualified Resource Manager (RM) with expertise in waste
and resource management to implement the RWMP should be appointed. The RM may be performed by
number of different individuals over the life-cycle of the Project, however it is intended to be a reliable
person chosen from within the Planning/Design/Contracting Team, who is technically competent and
appropriately trained, who takes the responsibility to ensure that the objectives and measures within the
Project RWMP are complied with. The RM is assigned the requisite authority to meet the objective and
obligations of the RWMP. The role will include the important activities of conducting waste checks/audits
and adopting construction methodology that is designed to facilitate maximum reuse and/or recycling of
waste.
5.1 Role of the Client
The Client is the body establishing the aims and the performance targets for the project.
► The Client has commissioned the preparation and submission of this RWMP as part of the design and
planning submission;
► The Client is to commission the preparation and submission of an updated RWMP as part of the
construction tendering process;
► The Client will ensure that the RWMP is agreed on and submitted to the local authority and their
agreement obtained prior to commencement of works on site;
► The Client will request the end-of-project RWMP from the Contractor.
5.2 Role of the Client Advisory Team
The Client Advisory Team or Design Team is formed of architects, consultants, quantity surveyors and
engineers and is responsible for:
► Drafting and maintaining the RWMP through the design, planning and procurement phases of the
project;
► Appointing a RM to track and document the design process, inform the Design Team and prepare the
RWMP.
► Including details and estimated quantities of all projected waste streams with the support of
environmental consultants/scientists. This will also include data on waste types (e.g. waste
characterisation data, contaminated land assessments, site investigation information) and prevention
mechanisms (such as by-products) to illustrate the positive circular economy principles applied by the
Design Team;
► Handing over of the RWMP to the selected Contractor upon commencement of construction of the
development, in a similar fashion to how the safety file is handed over to the Contractor;
► Working with the Contractor as required to meet the performance targets for the project.
5.3 Future Role of the Contractor
The Construction Contractors will be responsible for:
► Preparing, implementing and reviewing the RWMP throughout the construction phase (including the
management of all suppliers and sub-contractors) as per the requirements of the EPA guidelines;
► Identifying a designated and suitably qualified RM who will be responsible for implementing the
RWMP;
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► Implementing waste management policies whereby waste materials generated on site are to be
segregated as far as practicable;
► Where on-site processing of construction materials is proposed, the Contractor will ensure that all
applicable waste authorisations and regulatory requirements are satisfied prior to commencement of
such activities.
► Identifying all destinations for resources taken off-site. As above, any resource that is legally classified
as a ‘waste’ must only be transported to an authorised waste facility;
► End-of-waste and by-product notifications addressed with the EPA where required;
► Clarification of any other statutory waste management obligations, which could include on -site
processing;
► Full records of all resources (both wastes and other resources) will be maintained for the duration of
the project; and
► Preparing a RWMP Implementation Review Report at project handover.
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6. KEY MATERIALS & QUANTITIES
6.1 Project Resource Targets
Project specific resource and waste management targets for the site have not yet been set and this
information will be updated for these targets once these targets have been confirmed by the client.
However, it is expected for projects of this nature that a minimum of 70% of waste is fully re-used,
recycled or recovered. Target setting will inform the setting of project-specific benchmarks to track target
progress. Typical Key Performance Indicators (KPIs) that will be used to set targets include (as per
guidelines):
► Weight (tonnes) or Volume (m3) of waste generated per construction value;
► Weight (tonnes) or Volume (m3) of waste generated per construction floor area (m2);
► Fraction of resource reused on site;
► Fraction of resource notified as by-product;
► Fraction of waste segregated at source before being sent off-site for recycling/recovery; and
► Fraction of waste recovered, fraction of waste recycled, or fraction of waste disposed.
6.2 Main Construction Waste Categories
The main non-hazardous and hazardous waste streams that could be generated by the construction
activities at a typical site are shown in Table 6.1 The List of Waste (LoW) code (2018) for each waste
stream is also shown.
Table 6.1 Typical waste types generated and LoW codes (individual waste types may contain
hazardous substances)
Waste Material LoW Code
Concrete, bricks, tiles, ceramics 17 01 01-03 & 07
Wood, glass and plastic 17 02 01-03
Treated wood, glass, plastic, containing hazardous substances 17-02-04*
Bituminous mixtures, coal tar and tarred products 17 03 01*, 02 & 03*
Metals (including their alloys) and cable 17 04 01-11
Soil and stones 17 05 03* & 04
Gypsum-based construction material 17 08 01* & 02
Paper and cardboard 20 01 01
Mixed C&D waste 17 09 04
Green waste 20 02 01
Electrical and electronic components 20 01 35 & 36
Batteries and accumulators 20 01 33 & 34
Liquid fuels 13 07 01-10
Chemicals (solvents, pesticides, paints, adhesives, detergents etc.) 20 01 13, 19, 27-30
Insulation materials 17 06 04
Organic (food) waste 20 01 08
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* Individual waste type may contain hazardous substances
6.3 Demolition Waste Generation
There will be no demolition associated with the Proposed Development.
6.4 Construction Waste Generation
Table 6.2 shows the breakdown of C&D waste types produced on a typical site based on data from the
EPA National Waste Reports 21 and the joint EPA & GMIT study 22.
Table 6.2 Waste materials generated on a typical Irish construction site
Waste Types %
Mixed C&D 33
Timber 28
Plasterboard 10
Metals 8
Concrete 6
Other 15
Total 100
Table 6.3, below, shows the estimated construction waste generation for the proposed Project based on
the gross floor area of construction and other information available to date, along with indicative targets
for management of the waste streams. The estimated amounts for the main waste types (with the
exception of soils and stones) are based on an average large-scale development waste generation rate
per m2, using the waste breakdown rates shown in Table 6.2. These have been calculated from the
schedule of development areas provided by the architect.
Table 6.3 Predicted on and off-site reuse, recycle and disposal rates for construction waste
Waste Type Tonnes Reuse Recycle /
Recovery Disposal
% Tonnes % Tonnes % Tonnes
Mixed C&D 112.4 10 11.2 80 90.0 10 11.2
Timber 95.4 40 38.2 55 52.5 5 4.8
Plasterboard 34.1 30 10.2 60 20.4 10 3.4
Metals 27.3 5 1.4 90 24.5 5 1.4
Concrete 20.4 30 6.1 65 13.3 5 1.0
Other 51.1 20 10.2 60 30.7 20 10.2
Total 340.8 77.4 231.4 32.0
In addition to the waste streams in Table 6.3, The earthworks model prepared by McAdam identifies
approximately 98,420 m³ of excavated material, of which approximately 79,900 m³ of suitable excavated
soil and stone will be reused within the Renewable Biogas Plant site for engineering fill, landscaping and
screening berms. This results in a net surplus of approximately 18,520 m³. For the purposes of the
environmental assessments, this quantity has been conservatively rounded to approximately 18,600 m³
of surplus excavated soil and stone requiring removal from the site.
The surplus material will be removed by suitably authorised contractors for appropriate reuse, recovery or
disposal at an appropriately authorised receiving facility or facilities.
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It should be noted that until final materials and detailed construction methodologies have been confirmed,
it is difficult to predict with a high level of accuracy the construction waste that will be generated from the
proposed works as the exact materials and quantities may be subject to some degree of change and
variation during the construction process.
6.5 Proposed Resource and Waste Management Options
Waste materials generated will be segregated on-site, where it is practical. Where the on-site segregation
of certain wastes types is not practical, off-site segregation will be carried out. There will be skips and
receptacles provided to facilitate segregation at source, where feasible. All waste receptacles leaving the
site will be covered or enclosed. The appointed waste contractor will collect and transfer the wastes as
receptacles are filled. There are numerous waste contractors in the Monaghan region that provide this
service.
All waste arisings will be handled by an approved waste contractor holding a current waste collection
permit. All waste arisings requiring disposal off-site will be reused, recycled, recovered or disposed of at a
facility holding the appropriate registration, permit or licence, as required.
There will be no burning of any rubbish on site.
National End-of-Waste Decision EoW-N001/2023 (Regulation 28) published by the EPA in September 2023,
establishes criteria determining when recycled aggregate resulting from a recovery operation ceases to be
waste. Material from this proposed plant will be investigated to see if it can cease to be a waste under the
requirements of the National End of Waste Criteria for Aggregates.
During construction, some of the sub-contractors on site will generate waste in relatively low quantities.
The transportation of non-hazardous waste by persons who are not directly involved with the waste
business, at weights less than or equal to 2 tonnes, and in vehicles not designed for the carriage of waste,
are exempt from the requirement to have a waste collection permit (per Article 30 (1) (b) of the Waste
Collection Permit Regulations 2007, as amended). Any sub-contractors engaged that do not generate more
than 2 tonnes of waste at any one time can transport this waste off-site in their work vehicles (which are
not designed for the carriage of waste). However, they are required to ensure that the receiving facility
has the appropriate COR / permit / licence.
Written records will be maintained by the contractor(s), detailing the waste arising throughout the C&D
phases, the classification of each waste type, waste collection permits for all waste contactors who collect
waste from the site and COR / permit / licence for the receiving waste facility for all waste removed off-
site for appropriate reuse, recycling, recovery and / or disposal.
Dedicated bunded storage containers will be provided for hazardous wastes which may arise, such as
batteries, paints, oils, chemicals, if required.
The anticipated management of the main waste streams is outlined as follows:
Soil, Stone and Clay
The waste hierarchy states that the preferred option for waste management is prevention and minimisation
of waste, followed by preparing for reuse and recycling / recovery, energy recovery (i.e. incineration) and,
least favoured of all, disposal. The excavations are required to facilitate construction works so the preferred
option (prevention and minimisation) cannot be accommodated for the excavation phase.
Excavation is required to facilitate construction of the Proposed Development. The design has sought to
maximise the reuse of suitable excavated material within the site, with approximately 79,900 m³ proposed
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conservatively rounded to approximately 18,600 m³ for assessment purposes, will require off -site
management.
The waste hierarchy will be applied in determining the appropriate management route for this surplus
material. Appropriate reuse and recovery options will be prioritised where technically and legally
appropriate, with disposal used where reuse or recovery is not available or suitable.
At the time of preparation of this RWMP, Carrickamore Quarry, Carrickmacross, Co. Monaghan has been
identified as a potential receiving facility with available capacity. Subject to availability at the time of
construction and compliance with the applicable waste acceptance criteria, this facility may receive some
or all of the surplus excavated soil and stone. The final receiving facility or facilities will be selected by the
appointed Contractor prior to commencement of the relevant excavation works, having regard to the
applicable waste authorisation, available capacity and waste acceptance criteria. Other suitably licensed
or permitted recovery or disposal facilities may therefore be used where appropriate.
The final destinations for construction waste streams will be confirmed by the appointed Contractor prior
to removal from the site. In relation to surplus excavated soil and stone, Carrickamore Quarry has been
identified as a potential receiving facility as described above, subject to availability and applicable
acceptance criteria at the time of construction.
The material may be deemed a by-product (and not as a waste). If this is the case, it will be done in
accordance with Regulation 27 of the European Communities (Waste Directive) Regulations 2011, as
amended, which requires that certain conditions are met and that by-product notifications are made to
the EPA via their online notification form. Excavated material should not be removed from site until
approval from the EPA has been received. The potential to reuse material as a by-product will be confirmed
during the course of the excavation works, with the objective of eliminating any unnecessary disposal of
material.
The next option (beneficial reuse) may be appropriate for the excavated material, pending environmental
testing to classify the material as hazardous or non-hazardous in accordance with the EPA Waste
Classification – List of Waste & Determining if Waste is Hazardous or Non-Hazardous publication. Clean
inert material may be used as fill material in other construction projects or engineering fill for waste
licensed sites. Beneficial reuse of surplus excavation material as engineering fill may be subject to further
testing to determine if materials meet the specific engineering standards for their proposed end use.
Any nearby sites requiring clean fill/capping material will be contacted to investigate reuse opportunities
for clean and inert material. If any of the material is to be reused on another site as a by-product (and
not as a waste), this will be done in accordance with Regulation 27. Similarly, if any soils/stones are
imported onto the site from another construction site as a by-product, this will also be done in accordance
with Regulation 27. Regulation 27 will be investigated to see if the material can be imported onto this site
for beneficial reuse instead of using virgin materials.
If the material is deemed to be a waste, then removal and reuse / recovery / disposal of the material will
be carried out in accordance with the Waste Framework Directive (Directive 2008/98/EC), the Waste
Management Act 1996 as amended, the Waste Management (Collection Permit) Regulations 2007 as
amended and the Waste Management (Facility Permit & Registration) Regulations 2007 as amended. Once
all available beneficial reuse options have been exhausted, the options of recycling and recovery at waste
permitted and licensed sites will be considered.
In the event that contaminated material is encountered and subsequently classified as hazardous, this
material will be stored separately to any non-hazardous material. It will require off-site treatment at a
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Bedrock
While it is not envisaged that bedrock will be encountered, if bedrock is encountered, it is anticipated that
it will not be crushed on site. Any excavated rock is expected to be removed off-site for appropriate reuse,
recovery and / or disposal. If bedrock is to be crushed on-site, the appropriate mobile waste facility permit
will be obtained from MCC.
Silt & Sludge
During the construction phase, silt and petrochemical interception will be carried out on run-off and
pumped water from site works, where required. Sludge and silt will then be collected by a suitably licensed
contractor and removed off-site.
Concrete Blocks, Bricks, Tiles & Ceramics
The majority of concrete blocks, bricks, tiles and ceramics generated as part of the construction works are
expected to be clean, inert material and will be recycled, where possible. If concrete is to be crushed on-
site, the appropriate mobile waste facility permit will be obtained from MCC.
Hard Plastic
As hard plastic is a highly recyclable material, much of the plastic generated will be primarily from material
off-cuts. All recyclable plastic will be segregated and recycled, where possible.
Timber
Timber that is uncontaminated, i.e. free from paints, preservatives, glues, etc., will be disposed of in a
separate skip and recycled off-site.
Metal
Metals will be segregated, where practical, and stored in skips. Metal is highly recyclable and there are
numerous companies that will accept these materials.
Plasterboard
There are currently a number of recycling services for plasterboard in Ireland. Plasterboard from the
construction phases will be stored in a separate skip, pending collection for recycling. The site Manager
will ensure that oversupply of new plasterboard is carefully monitored to minimise waste.
Glass
Glass materials will be segregated for recycling, where possible.
Waste Electrical & Electronic Equipment (WEEE)
Any WEEE will be stored in dedicated covered cages / receptacles / pallets pending collection for recycling.
Other Recyclables
Where any other recyclable wastes, such as cardboard and soft plastic, are generated, these will be
segregated at source into dedicated skips and removed off-site.
Non-Recyclable Waste
C&D waste which is not suitable for reuse or recovery, such as polystyrene, some plastics and some
cardboards, will be placed in separate skips or other receptacles. Prior to removal from site, the non-
recyclable waste skip / receptacle will be examined by a member of the waste team (see Section 8) to RECEIVED: 28/08/2026
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determine if recyclable materials have been placed in there by mistake. If this is the case, efforts will be
made to determine the cause of the waste not being segregated correctly and recyclable waste will be
removed and placed into the appropriate receptacle.
Asbestos Containing Materials
In the unlikely event that any asbestos or ACM is found on-site it will be removed by a suitably competent
contractor and disposed of as asbestos waste before the works begin. All asbestos removal work or
encapsulation work must be carried out in accordance with the Safety, Health and Welfare at Work
(Exposure to Asbestos) Regulations 2006-2010.
Other Hazardous Wastes
On-site storage of any hazardous wastes produced (i.e. contaminated soil if encountered and / or waste
fuels) will be kept to a minimum, with removal off-site organised on a regular basis. Storage of all
hazardous wastes on-site will be undertaken so as to minimise exposure to on-site personnel and the
public and to also minimise potential for environmental impacts. Hazardous wastes will be recovered,
wherever possible, and failing this, disposed of appropriately.
On-Site Crushing
It is currently not envisaged that the crushing of waste materials will occur on-site. However, if the
crushing of material is to be undertaken, a mobile waste facility permit will first be obtained from MCC and
the destination of the accepting waste facility or if an application under regulation 28 will be made using
National End-of-Waste Decision EoW-N001/2023, will be supplied to the MCC waste unit.
It should be noted that until a construction contractor is appointed it is not possible to provide information
on the specific destinations of each construction waste stream. Prior to commencement of construction
and removal of any waste offsite, details of the proposed destination of each waste stream will be provided
to MCC by the project team.
6.6 Tracking and Documentation Procedures for Off-Site Waste
All waste will be documented prior to leaving the site. Waste will be weighed by the contractor, either by
a weighing mechanism on the truck or at the receiving facility. These waste records will be maintained on
site by the nominated project RM (see Section 8).
All movement of waste and the use of waste contractors will be undertaken in accordance with the Waste
Framework Directive (Directive 2008/98/EC), the Waste Management Act 1996 as amended, Waste
Management (Collection Permit) Regulations 2007 as amended and Waste Management (Facility Permit &
Registration) Regulations 2007 and amended. This includes the requirement for all waste contractors to
have a waste collection permit issued by the NWCPO. The nominated project RM (see Section 8) will
maintain a copy of all waste collection permits on-site.
If the waste is being transported to another site, a copy of the Local Authority waste COR / permit or EPA
Waste Licence for that site will be provided to the nominated project Waste Manager (see Section 8). If
the waste is being shipped abroad, a copy of the Transfrontier Shipping (TFS) notification document will
be obtained from DCC (as the relevant authority on behalf of all Local Authorities in Ireland) and kept on-
site along with details of the final destination (COR, permits, licences, etc.). A receipt from the final
destination of the material will be kept as part of the on-site waste management records.
All information will be entered in a waste management recording system to be maintained on-site.
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7. ESTIMATED COST OF WASTE MANAGEMENT
An outline of the costs associated with different aspects of waste management is outlined below. The total
cost of C&D waste management will be measured and will take into account handling costs, storage costs,
transportation costs, revenue from rebates and disposal costs.
7.1 Reuse
By reusing materials on site, there will be a reduction in the transport and recycle / recovery / disposal
costs associated with the requirement for a waste contractor to take the material off -site. Clean and inert
soils, gravel, stones, etc., which cannot be reused on-site may be used as access roads or capping material
for landfill sites, etc. This material is often taken free of charge or at a reduced fee for such purposes,
reducing final waste disposal costs.
7.2 Recycling
Salvageable metals will earn a rebate, which can be offset against the costs of collection and transportation
of the skips.
Clean, uncontaminated cardboard and certain hard plastics can also be recycled. Waste contractors will
charge considerably less to take segregated wastes, such as recyclable waste, from a site than mixed
waste.
Timber can be recycled as chipboard. Again, waste contractors will charge considerably less to take
segregated wastes, such as timber, from a site than mixed waste.
7.3 Disposal
Landfill charges are currently at around €140 - €160 per tonne which includes a €85 per tonne landfill levy
specified in the Waste Management (Landfill Levy) Regulations 2015 as amended. The Circular Economy
(Waste Recovery Levy) will also incur a levy of €10 per tonne for waste accepted for recovery. This will
include backfilling at authorised recovery sites and at municipal waste landfills. In addition to disposal
costs, waste contractors will also charge a collection fee for skips.
Collection of segregated C&D waste usually costs less than municipal waste. Specific C&D waste
contractors take the waste off-site to a licensed or permitted facility and, where possible, remove
salvageable items from the waste stream before disposing of the remainder to landfill. Clean soil, rubble,
etc., is also used as fill / capping material, wherever possible.
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8. TRAINING PROVISIONS
A member of the construction team will be appointed as the RM to ensure commitment, operational
efficiency and accountability in relation to waste management during the C&D phases of the development.
8.1 Resource Manager Training and Responsibilities
The RM will be responsible for conducting a waste audit at the site during the C&D phase of the project.
The RM will be given the responsibility and authority to select a waste team if required, i.e. members of
the site crew that will aid them in the organisation, operation and recording of the waste management
system implemented on site.
The details of the RM are as follows:
► Contact Name: David Mullan
► Contact Company: Stream Bioenergy Ireland Limited
► Email: david.mullan@streambioenergy.ie
The RM will have overall responsibility to oversee, record and provide feedback to the client on everyday
waste management at the site. Authority will be given to the Waste Manager to delegate responsibility to
sub-contractors, where necessary, and to coordinate with suppliers, service providers and sub-contractors
to prioritise waste prevention and material salvage.
The RM will be trained in how to set up and maintain a record keeping system, how to perform an audit
and how to establish targets for waste management on site. The RM will also be trained in the best
methods for segregation and storage of recyclable materials, have information on the materials that can
be reused on site and be knowledgeable in how to implement this RWMP.
8.2 Site Crew Training
Training of site crew in relation to waste is the responsibility of the RM and, as such, a waste training
program will be organised. A basic awareness course will be held for all site crew to outline the RWMP
and to detail the segregation of waste materials at source. This may be incorporated with other site training
needs such as general site induction, health and safety awareness and manual handling.
This basic course will describe the materials to be segregated, the storage methods and the location of
the Waste Storage Areas (WSAs). A sub-section on hazardous wastes will be incorporated into the training
program and the particular dangers of each hazardous waste will be explained.
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9. TRACKING AND TRACING / RECORD KEEPING
Records will be kept for all waste material which leaves the site, either for reuse on another site, recycling
or disposal. A recording system will be put in place to record the waste arisings on Site.
A waste tracking log will be used to track each waste movement from the site. On exit from the site, the
waste collection vehicle driver will stop at the site office and sign out as a visitor and provide the security
personnel or RM with a waste docket (or Waste Transfer Form (WTF) for hazardous waste) for the waste
load collected. At this time, the security personnel will complete and sign the Waste Tracking Register with
the following information:
► Date
► Time
► Waste Contractor
► Company waste contractor appointed by, e.g. Contractor or subcontractor name
► Collection Permit No.
► Vehicle Reg.
► Driver Name
► Docket No.
► Waste Type
► LoW
► Weight/Quantity
The waste vehicle will be checked by security personal or the RM to ensure it has the waste collection
permit no. displayed and a copy of the waste collection permit in the vehicle before they are allowed to
remove the waste from the site.
The waste transfer dockets will be transferred to the RM on a weekly basis and can be placed in the
Waste Tracking Log file. This information will be forwarded onto the MCC Waste Regulation Unit when
requested.
Each subcontractor that has engaged their own waste contractor will be required to maintain a similar
waste tracking log with the waste dockets / WTF maintained on file and available for inspection on site
by the main contractor as required. These subcontractor logs will be merged with the main waste log.
Waste receipts from the receiving waste facility will also be obtained by the site contractor(s) and
retained. A copy of the Waste Collection Permits, CORs, Waste Facility Permits and Waste Licences will
be maintained on site at all times and will be periodically reviewed by the RM. Subcontractors who have
engaged their own waste contractors, will provide the main contractor with a copy of the waste collection
permits and COR / permit / licence for the receiving waste facilities and maintain a copy on file, available
for inspection on site as required.
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10. OUTLINE WASTE AUDIT PROCEDURE
10.1 Responsibility for Waste Audit
The appointed RM will be responsible for conducting a waste audit at the site during the C&D phase of
the proposed Project. Contact details for the nominated RM will be provided to the MCC Waste Regulation
Unit after the main contractor is appointed and prior to any material being removed from site.
10.2 Review of Records and Identification of Corrective Actions
A review of all waste management costs and the records for the waste generated and transported off-site
will be undertaken mid-way through the construction phase of the proposed Project.
If waste movements are not accounted for, the reasons for this will be established in order to see if and
why the record keeping system has not been maintained. The waste records will be compared with the
established recovery / reuse / recycling targets for the site. Each material type will be examined, in order
to see where the largest percentage waste generation is occurring. The waste management methods for
each material type will be reviewed in order to highlight how the targets can be achieved.
Upon completion of the C&D phase, a final report will be prepared, summarising the outcomes of waste
management processes adopted and the total recycling / reuse / recovery figures for the development.
10.3 Pest Management
A pest control operator will be appointed as required to manage pests onsite during the construction phase
of the project. Organic and food wastes generated by staff will not be stored in open skips, but in closed
waste receptacles. Any waste receptacles will be carefully managed to prevent leaks, odours and pest
problems.
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11. CONSULTATION WITH RELEVANT BODIES
11.1 Local Authority
The final destinations for construction waste streams will be confirmed by the appointed Contractor prior
to removal from the site. In relation to surplus excavated soil and stone, Carrickamore Quarry has been
identified as a potential receiving facility as described above, subject to availability and applicable
acceptance criteria at the time of construction.
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12. CONCLUSION
Adherence to this plan will also ensure that waste management during the construction phase at the
Proposed Development is carried out in accordance with the requirements in the EPA’s Best Practice
Guidelines for the Preparation of Resource & Waste Management Plans for Construction & Demolition
Projects and the MCC Waste Bye-Laws and the NWMPCE.
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13. REFERENCES
1. Waste Management Act 1996 as amended.
2. Environmental Protection Agency Act 1992 as amended.
3. Litter Pollution Act 1997 (S.I. No. 12 of 1997) as amended.
4. Regional Waste Management Planning Offices, The National Waste Management Plan for a Circular
Economy 2024 – 2030 (2024).
5. Department of Environment and Local Government (DoELG) Waste Management – Changing Our
Ways, A Policy Statement (1998).
6. Forum for the Construction Industry – Recycling of Construction and Demolition Waste.
7. Department of Communications, Climate Action and Environment (DCCAE), Waste Action Plan for
the Circular Economy - Ireland’s National Waste Policy 2020-2025 (Sept 2020).
8. DCCAE, Whole of Government Circular Economy Strategy 2022-2023 ‘Living More, Using Less’
(2021).
9. Circular Economy and Miscellaneous Provisions Act 2022.
10. Environmental Protection Agency (EPA) ‘Best Practice Guidelines for the Preparation of Resource
and Waste Management Plans for Construction & Demolition Projects’ ( 2021).
11. Department of Environment, Heritage and Local Government, Best Practice Guidelines on the
Preparation of Waste Management Plans for Construction and Demolition Projects (2006).
12. FÁS and the Construction Industry Federation (CIF), Construction and Demolition Waste
Management – a 14 (2002).
13. Waste Management (Landfill Levy) Regulations 2015 (as amended).
14. Circular Economy (Waste Recovery Levy) Regulations 2024.
15. Monaghan County Council (MCC), Monaghan County Development Plan 2025 – 2031 (2025).
16. Planning and Development Act 2000 (S.I. No. 30 of 2000) as amended.
17. EPA, Waste Classification – List of Waste & Determining if Waste is Hazardous or Non-Hazardous
(2018).
18. Council Decision 2003/33/EC, establishing criteria and procedures for the acceptance of waste at
landfills pursuant to Article 16 of and Annex II to Directive 1999/31/EC.
19. Safety, Health and Welfare at Work (Exposure to Asbestos) Regulations 2006-2010.
20. Local Government Ireland, Best practice guidance for handling asbestos (2023).
21. Environmental Protection Agency (EPA), National Waste Database Reports 1998 – 2020 and the
Circular Economy and National Waste Database Report 2021 – 2022.
22. EPA and Galway-Mayo Institute of Technology (GMIT), EPA Research Report 146 – A Review of
Design and Construction Waste Management Practices in Selected Case Studies – Lessons Learned
(2015).
23. European Commission, Guidelines for the waste audits before demolition and renovation works of
buildings (May 2018). RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 8.2
OPERATIONAL WASTE
MANAGEMENT PLAN
Stream BioEnergy Ireland Limited
RECEIVED: 28/08/2026
REPORT
Operational Waste Management Plan
Project Title: Proposed Renewable Biogas Plant, Maghernakelly Drum, County Monaghan
CLIENT
Stream
BioEnergy
Ireland Ltd
DOCUMENT REFERENCE
247501.0359WMR02
DATE
25/11/2025
AWN Consulting Ltd, The Tecpro Building, IDA Business & Technology Park, Clonshaugh, Dublin 17, D17 XD90 RECEIVED: 28/08/2026
DOCUMENT CONTROL SHEET
Document Control Sheet
Our Reference 247501.0359WMR02
Original Issue Date 25/11/2025
Client: Stream BioEnergy Ireland Ltd
Client Address:
Revision Revision Date Description
Details Written by Approved by
Signature
Name Chonaill Bradley Fergal Callaghan
Title Principal Environmental Consultant Director
Date 25/11/2025 25/11/2025
Disclaimer
This report considers the specific instructions and requirements of our client. It is not intended for third -party
use or reliance, and no responsibility is accepted for any third party. The provisions in this report apply solely
to this project and should not be assumed applicable to other developments without review and modification. RECEIVED: 28/08/2026
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TABLE OF CONTENTS
1. INTRODUCTION 1-1
2. OVERVIEW OF WASTE MANAGEMENT IN IRELAND 2
2.1 European Policy ....................................................................................................... 2
2.2 National level ........................................................................................................... 2
2.2.1 National Biomethane Strategy 2024 ........................................................................ 4
2.3 Regional Level .......................................................................................................... 4
2.4 Legislative Requirements ......................................................................................... 6
2.4.1 Agricultural Legislation........................................................................................... 7
2.4.2 Local Authority Guidelines ...................................................................................... 7
2.5 Regional Waste Management Service Providers and Facilities ................................. 8
3. DESCRIPTION OF THE DEVELOPMENT 9
3.1 Location, Size and Scale of the Development ........................................................... 9
3.1.1 Site Process ........................................................................................................ 11
3.2 Typical Waste Categories ....................................................................................... 14
3.3 List of Waste Codes ................................................................................................ 14
4. ESTIMATED WASTE ARISING 16
4.1.1 By-Products of the Anaerobic Digestion Process ..................................................... 16
5. WASTE STORAGE AND COLLECTION 18
5.1 Site Process Waste ................................................................................................. 18
5.1.1 Digestate ........................................................................................................... 18
5.2 General Waste ........................................................................................................ 18
5.3 Waste Collection .................................................................................................... 19
5.4 Additional Potential Waste Materials ..................................................................... 20
5.5 Pest Management .................................................................................................. 21
6. SUMMARY AND CONCLUSION 22
7. REFERENCES 23
LIST OF TABLES
Table 3.1. Feedstock Mix 12
Table 3.2 Typical Waste Types Generated and LoW Codes 14
Table 4.1 Estimated Waste Generation for Proposed Plant 16
Table 4.2 By-Products of the AD Process 16
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1. INTRODUCTION
AWN Consulting, a Trinity Consultants Company, has prepared this Operational Waste Management Plan
(OWMP) on behalf of Stream BioEnergy Ireland Ltd. The proposed development will utilise anaerobic
digestion (AD) technology to generate renewable energy in the form of biomethane from up to 99,000
tonnes of feedstock per annum consisting primarily of poultry manure along with cattle manure, and agri-
food organic waste feedstock, sourced from the surrounding area.
AD is a sustainable form of renewable energy production that occurs when micro-organisms break down
biodegradable material in the absence of oxygen in an enclosed system to produce a renewable biogas.
A full description of the proposed development is included in the Description of the Proposed Development
Chapter of this EIAR (Volume II) and in the statutory notices.
This OWMP has been prepared to ensure that the management of waste during the operational phase of
the proposed development is undertaken in accordance with the current legal and industry standards
including, the Waste Management Act 1996 as amended and associated Regulations 1, Environmental
Protection Agency Act 1992 as amended 2, Litter Pollution Act 1997 as amended 3, the National Waste
Management Plan for a Circular Economy 2024 - 2030 (NWMPCE) (2024) 4 and Monaghan County Council
(MCC) County of Monaghan (Segregation, Storage and Presentation of Household and Commercial Waste)
Bye-Laws (2019) 5. In particular, this OWMP aims to provide a robust strategy for the storage, handling,
collection and transport of waste generated at the site.
This OWMP aims to ensure maximum recycling, reuse and recovery of waste with diversion from landfill,
wherever possible. The OWMP also seeks to provide guidance on the appropriate collection and transport
of waste to prevent issues associated with litter or more serious environmental pollution (e.g.
contamination of soil or water resources). The plan estimates the type and quantity of waste to be
generated from the proposed development during the operational phase and provides a strategy for
managing the different waste streams.
At present, there are no specific national guidelines in Ireland for the preparation of OWMPs. Therefore,
in preparing this document, consideration has been given to the requirements of national and regional
waste policy, legislation and other guidelines.
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2. OVERVIEW OF WASTE MANAGEMENT IN IRELAND
2.1 European Policy
Directive (EU) 2018/2001 The Promotion of the Use of Energy from Renewable Sources 6
This Directive repeals the previous renewable energies directive 2009/28/EC, consolidates it with
Renewable Energy Directive. The RED Directive sets an overall renewable energy target of at least 42.5%
binding at EU level by 2030 - but aiming for 45%.
This directive establishes a common framework for the promotion of energy from renewable sources. It
sets a binding Union target for the overall share of energy from renewable sources in the Union's gross
final consumption of energy in 2030. It also lays down rules on f inancial support for electricity from
renewable sources, on self-consumption of such electricity, on the use of energy from renewable sources
in the heating and cooling sector and in the transport sector, on regional cooperation between Member
States, and between Member States and third countries, on guarantees of origin, on administrative
procedures and on information and training. It also establishes sustainability and greenhouse gas
emissions saving criteria for biofuels, bioliquids and biomass fuels. Supplementing Regulation 2019/807
lays down the criteria for determining high indirect land-use change-risk feedstock for which a significant
expansion of the production area into land with high carbon stock is observed and the certification of low
indirect land-use change-risk biofuels, bioliquids and biomass fuels.
Each Member State had flexibility to set targets across the heating, transportation and electricity sectors
to meet the overall renewable energy targets. Annex I indicated that the national target for Ireland for
the share of energy from renewable sources in gross final consumption of energy in 2020 was set at 16%.
While Annex 1a indicates that additional top ups applied for the period of 2021-2025 (2.3 percentage
points) and for the period of 2026-2030 (2.0 percentage points).
These targets have not been met in Ireland. The Directive also established specific rules for biofuels,
bioliquids and biomass fuels produced from food and feed crops. According to Article 2 of the Directive,
‘biofuels’ means liquid fuel for transport produced from biomass. The meaning of ‘biomass’ means the
biodegradable fraction of products, waste and residues from biological origin from agriculture, including
vegetal and animal substances, from forestry and related industries, including fisheries and aquaculture,
as well as the biodegradable fraction of waste, including industrial and municipal waste of biological origin.
Article 29 of the Directive established the sustainability criteria for biofuels and bioliquids. Annex V of the
Directive set out the rules for calculating the greenhouse gas impact of biofuels, bioliquids and their fossil
fuel comparators.
2.2 National level
The Irish Government issued a policy statement in September 1998 entitled ‘Changing Our Ways’ 7, which
identified objectives for the prevention, minimisation, reuse, recycling, recovery and disposal of waste in
Ireland. A heavy emphasis was placed on reducing reliance on landfill and finding alternative methods for
managing waste. Amongst other things, Changing Our Ways stated a target of at least 35% recycling of
municipal (i.e. household, commercial and non-process industrial) waste.
A further policy document, ‘Preventing and Recycling Waste – Delivering Change’ was published in 2002
8. This document proposed a number of programmes to increase recycling of waste and allow diversion
from landfill. The need for waste minimisation at source was considered a priority.
This view was also supported by a review of sustainable development policy in Ireland and achievements
to date, which was conducted in 2002, entitled ‘Making Irelands Development Sustainable – Review, RECEIVED: 28/08/2026
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Assessment and Future Action’ 9. This document also stressed the need to decouple economic growth and
waste generation, again through waste minimisation and reuse of discarded material.
In order to establish the progress of the Government policy document Changing Our Ways, a review
document was published in April 2004 entitled ‘Taking Stock and Moving Forward’ 10. Covering the period
1998 – 2003, the aim of this document was to assess progress to date with regard to waste management
in Ireland, to consider developments since the policy framework and the local authority waste management
plans were put in place, and to identify measures that could be undertaken to further support progress
towards the objectives outlined in Changing Our Ways.
In particular, Taking Stock and Moving Forward noted a significant increase in the amount of waste being
brought to local authority landfills. The report noted that one of the significant challenges in the coming
years was the extension of the dry recyclable collection services.
In September 2020, the Irish Government published a new policy document outlining a new action plan
for Ireland to cover the period of 2020-2025. This plan ‘A Waste Action Plan for a Circular Economy’ 11
(WAPCE), was prepared in response to the ‘European Green Deal’ which sets a roadmap for a transition
to a new economy, where climate and environmental challenges are turned into opportunities, replacing
the previous national waste management plan “A Resource Opportunity” (2012).
The WAPCE sets the direction for waste planning and management in Ireland up to 2025. This reorientates
policy from a focus on managing waste to a much greater focus on creating circular patterns of production
and consumption. Other policy statements of a number of public bodies already acknowledge the circular
economy as a national policy priority.
The policy document contains over 200 measures across various waste areas including circular economy,
municipal waste, consumer protection and citizen engagement, plastics and packaging, construction and
demolition, textiles, green public procurement and waste enforcement.
One of the first actions to be taken was the development of the Whole of Government Circular Economy
Strategy 2022-2023 ‘Living More, Using Less’ (2021) 12 to set a course for Ireland to transition across all
sectors and at all levels of Government toward circularity and was issued in December 2021. It is
anticipated that the Strategy will be updated in full every 18 months to 2 years.
The Circular Economy and Miscellaneous Provisions Act 2022 13 was signed into law in July 2022. The Act
underpins Ireland’s shift from a "take-make-waste" linear model to a more sustainable pattern of
production and consumption, that retains the value of resources in our economy for as long as possible
and that will to significantly reduce our greenhouse gas emissions. The Act defines Circular Economy for
the first time in Irish law, incentivises the use of recycled and reusable alternatives to wasteful, single-use
disposable packaging, introduces a mandatory segregation and incentivised charging regime for
commercial waste, streamlines the national processes for End-of-Waste and By-Products decisions,
tackling the delays which can be encountered by industry, and supporting the availability of recycled
secondary raw materials in the Irish market, and tackles illegal fly-tipping and littering.
Since 1998, the Environmental Protection Agency (EPA) has produced periodic ‘National Waste (Database)
Reports’ which as of 2023 have been renamed Circular Economy and Waste Statistics Highlight Reports
14 detailing, among other things, estimates for household and commercial (municipal) waste generation in
Ireland and the level of recycling, recovery and disposal of these materials. The 2024 National Circular
Economy and Waste Statistics web resource, which is the most recent study published, along with the
national waste statistics web resource (2024) reported the following key statistics for 2022:
► Generated – Ireland produced 3,190,000 t of municipal waste in 2022. This is a slight increase since
2021. Of this, 55% came from households and 45% came from commercial and public service
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► Managed –In 2022, a total of 1.76 million Household waste collected and treated by the waste
industry.
► Unmanaged – An estimated 36,970 tonnes of household waste was unmanaged waste i.e., not
disposed of in the correct manner in 2022.
► Recovered – A rounded 1.3 million tonnes of Ireland’s municipal waste went for incineration with
energy recovery in 2022. This tonnage is 43% of municipal waste managed and a marginal increase
on the 42% achieved in 2021.
► Recycled –Some 1.3 million tonnes of municipal waste generated in Ireland was recycled in 2022,
resulting in a recycling rate of 41%. This indicates that we face significant challenges to meet the
upcoming EU recycling targets for 2025 to 2035
► Of the municipal waste recycled in 2022, over 825,000 tonnes went for material recycling
(approximately the same as 2021) and over 480,000 tonnes were treated by composting/anaerobic
digestion (approximately the same as 2021 but up 37% in 2020). The large increase of
composted/anaerobically digested biowaste from 2020 is mainly due to a change in our way of
estimating home composting.
► Disposed – Ireland’s landfill rate for municipal waste managed was 15% in 2022. This is a 1%
decrease from 2021’s rate of 16%.
► Reuse – 54,800 tonnes of second-hand products we estimated by the EPA to have been reused in
Ireland in 2021. The average annual Reuse rate per person in Ireland is 10.6 kg per person.
2.2.1 National Biomethane Strategy 2024
The Irish Government is committed to supporting delivery of up to 5.7TWh of indigenously produced
biomethane by 2030. The first key step to delivering on this target was the publication of the National
Biomethane Strategy.
The Department of the Environment, Climate and Communications; Department of Agriculture, Food and
the Marine Ireland’s National Biomethane Strategy (2024) 15 sets out the necessary policy and regulatory
measures, and provides a roadmap, to developing a biomethane industry of scale in Ireland. The
development of the Strategy focused on a framework of five interlinking pillars seen as critical to target
delivery:
► Sustainability;
► Demand for biomethane;
► Bioeconomy and the circular economy;
► Economics of biomethane; and
► Enabling policy requirements.
The National Biomethane Strategy is Ireland’s first major policy statement on biomethane and is an
important milestone in the development of an indigenous sector. The Strategy sets out twenty-five actions
to be delivered in the coming years to enable the development of the sector. Along with providing supports
and policy certainty, these actions aim to improve the development timeline and economics of projects in
order to meet the 2030 target.
2.3 Regional Level
The proposed development is located in the Local Authority administrative area of Monaghan County
Council (MCC).
The Connacht-Ulster Region (CUR) Waste Management Plan 2015 – 2021, which previously governed
waste management policy in the MCC area, has been superseded as of March 2024 by the NWMPCE
2024 – 2030, the national waste management plan for Ireland.
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The NWMPCE does not dissolve the three regional waste areas. The NWCPCE sets the ambition of the
plan to have a 0% total waste growth per person over the life of the Plan with an emphasis on non -
household wastes including waste from commercial activities and the construction and demolition sector.
This Plan seeks to influence sustainable consumption and prevent the generation of waste, improve the
capture of materials to optimise circularity and enable compliance with policy and legislation.
The national plan sets out the following strategic targets for waste management in the country that are
relevant to the development:
National Targets
► 1A. (Residual Municipal Waste) 6% Reduction in Residual Municipal Waste per person by
2030.
► 2A. (Contamination of Materials) 90% of Material in Compliance in the Dry Recycling Bin.
► 2B. (Material Compliance Residual) 10% per annum increase in Material Compliance in the
residual bin. (90% by the end of 2030).
► 3A. (Reuse of Materials) 20kg Per person / year – Reuse of materials like cloths or furniture
to prevent waste.
Municipal landfill charges in Ireland are based on the weight of waste disposed. In the Munster Region,
charges are approximately €140-160 per tonne of waste, which includes a €85 per tonne landfill levy
introduced under the Waste Management (Landfill Levy) (Amendment) Regulations 2015 (as amended)15.
The Monaghan County Council Development Plan 2025 – 2031 (2025) 16 sets out a number of objectives
and policies for the Monaghan area in line with the objectives of the waste management plan.
Waste Management Objectives
► WMO 1 To implement and support the strategic objectives of the National Waste Management Plan
for a Circular Economy 2024-2030 and any new or updated/subsequent versions
► WMO 2 To implement the provisions of the Litter Management Plan 2021 – 2023 and any new or
updated/subsequent versions.
► WMO 3 To apply the ‘Polluter Pays’ Principle, proximity principle, and the precautionary principle in
respect of all waste management activities.
► WMO 4 To encourage best environmental practice in all agricultural, industry, business and local
authority activities.
► WMO 5 To support the circular and bioeconomy through the efficient use of resources and to support
any development proposals which contribute to this concept.
► WMO 6 To support the minimisation of waste creation and promote a practice of reduce, reuse and
recycle where possible, and to safeguard the environment by seeking to ensure that residual waste
is disposed of appropriately.
► WMO 8 To require that treatment/management of any contaminated material shall comply as
appropriate with the Waste Management Act 1996 (waste licence, waste facility permit) and under
the Environmental Protection Act 1992 (Industrial Emissions licensing, in particular the First Schedule,
Class 11 Waste).
► WMO 9 To ensure that all new waste management infrastructure is sited in accordance with the
provisions of the Waste Management Infrastructure Guidance for Siting Waste Management Facilities
included within the National Waste Management Plan for a Circular Economy 2024-2030.
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► WMO 12 To promote the sustainable management of poultry and other agricultural wastes through
renewable energy facilities to reduce nutrient runoff, improve water quality, minimise greenhouse
gas emissions, and support energy generation, while ensuring the protection of local and water
resources.
Waste Management Policies
► WMP 1 All proposals relating to management and disposal of Construction and Demolition Materials
and Waste must adhere to the Environmental Protection Agency Best Practice Guidelines for the
preparation of Resource and Waste Management Plans for Construction and Demolition Projects
2024, and any new or updated/subsequent versions.
► WMP 5 Development proposals for the infilling of lands for agricultural improvement, shall only be
acceptable where it is demonstrated by means of an Agricultural Improvement Plan how the infilling
of the lands will meet current farm management requirements or proposed future expansion and will
not adversely affect water quality and biodiversity.
2.4 Legislative Requirements
The primary legislative instruments that govern waste management in Ireland and applicable to the
proposed Development are:
► Waste Management Act 1996 as amended;
► Environmental Protection Agency Act 1992 as amended;
► Litter Pollution Act 1997 as amended;
► Planning and Development Act 2000 as amended;
► Circular Economy and Miscellaneous Provisions Act 2022.
These Acts and subordinate Regulations transpose the relevant European Union Policy and Directives into
Irish law.
One of the guiding principles of European waste legislation, which has in turn been incorporated into the
Waste Management Act 1996 as amended and subsequent Irish legislation, is the principle of “Duty of
Care”. This implies that the waste producer is responsible for waste from the time it is generated through
until its legal disposal (including its method of disposal). As it is not practical in most cases for the waste
producer to physically transfer all waste from where it is produced to the final disposal area, waste
contractors will be employed to physically transport waste to the final waste disposal site.
It is, therefore, imperative that the operator and staff undertake on-site management of waste in
accordance with all legal requirements and that the facilities management company employ suitably
permitted / licenced contractors to undertake off-site management of their waste in accordance with all
legal requirements. This includes the requirement that a waste contractor handle, transport and reuse /
recover / recycle / dispose of waste in a manner that ensures that no adverse environmental impacts occur
as a result of any of these activities.
A collection permit to transport waste must be held by each waste contractor which is issued by the
National Waste Collection Permit Office (NWCPO). Waste receiving facilities must also be appropriately
permitted or licensed. Operators of such facilities cannot receive any waste, unless in possession of a
Certificate of Registration (COR) or waste permit granted by the relevant Local Authority under the Waste
Management (Facility Permit & Registration) Regulations 2007, as amended, or a Waste Licence granted
by the EPA. The COR / permit / licence held will specify the type and quantity of waste able to be received,
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2.4.1 Agricultural Legislation
The application of manure (or digestate) to farmland is regulated under European Communities (Good
Agricultural Practice for Protection of Waters) Regulations S.I. No. 113 of 2022)17. Animal manure is
classified as a Category 2 animal by-product (ABP) under EC Regulation No. 1069/2009 18.
The use of biofertilisers on agricultural land is regulated under several existing and binding environmental
frameworks, including the following:
• The Nitrates Directive (91/676/EEC), as transposed into Irish law by the Good Agricultural Practice
for Protection of Waters Regulations (S.I. No. 113 of 2022, as amended by S.I. No. 393 of 2022,
S.I. No. 716 of 2022, S.I. 62 of 2023, S.I. 42 of 2025, and as may be further amendment from
time to time).
• The 2025 Nitrates Derogation Terms and Conditions (where applicable).
• The DAFM Code of Good Agricultural Practice for Reducing Ammonia Emissions from Agriculture
• Inland Fisheries Ireland’s Code of Practice for the Protection of Waters.
Collectively and together with other programmes and measures implemented by DAFM, the EPA and Inland
Fisheries, among others, landowners and occupiers are subject to stringent regulatory controls on nutrient
management, including timing, application rates, buffer zones, and prohibited spreading periods, designed
to protect inter alia water and air quality, and aquatic habitats.
The operator of the proposed development will not have operational, contractual, regulatory or financial
control over any individual third-party landowner or operator that proposes to use biofertiliser from the
proposed development on their landholding.
The relevant competent authorities under the Good Agricultural Practice regulatory framework include
DAFM and the EPA, while relevant local authorities have water quality testing and reporting obligations.
Compliance by landowners and occupiers is intended to be achieved through systematic planning,
reporting, inspection, testing, and regular compliance review requirements prescribed by the Good
Agricultural Practice framework.
The appropriate management of land in accordance with Good Agricultural Practice is the responsibility of
each individual third party landowner and occupier, under the regulatory supervision of DAFM and the
EPA, primarily.
Accordingly, the use of digestate on land is subject to an entirely separate regulatory framework that
provides for the effective management of land spreading of fertilisers to avoid and minimise any associated
environmental risks to land and soils, to water quality and aquatic habitats, and to air quality.
2.4.2 Local Authority Guidelines
The County of Monaghan (Segregation, Storage and Presentation of Household and Commercial Waste)
Bye-Laws (2019) were brought into force by MCC in 2019. The Waste Bye-Laws set a number of
enforceable requirements on waste holders and collectors with regard to storage, separation, presentation
and collection of waste within the MCC functional area. Key requirements under these Bye-Laws are:
► Documentary evidence, such as receipts, statements or other proof of payment, demonstrating
compliance with this bye-law shall be presented to an authorised person within a time specified in a
written request from either that person or from another authorised person employed by Monaghan
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► Containers used for the presentation of kerbside waste shall be maintained in such condition and
state of repair that the waste placed therein will not be a source of nuisance or litter;
► Containers used for the presentation of kerbside waste shall be held within the curtilage of the
premises where the waste is produced; and
► A holder shall not present waste for collection before 6 p.m. on the day before the approved time .
The full text of the Waste Bye-Laws is available from the MCC website.
2.5 Regional Waste Management Service Providers and Facilities
Various contractors offer waste collection services for the commercial sector in the MCC region. Details of
waste collection permits (granted, pending and withdrawn) for the region are available from the NWCPO.
A copy of all CORs and waste permits issued by the Local Authorities are available from the NWCPO
website and all Waste Licenses issued are available from the EPA.
RECEIVED: 28/08/2026
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3. DESCRIPTION OF THE DEVELOPMENT
3.1 Location, Size and Scale of the Development
The proposed development will utilise AD technology to generate renewable biogas from up to 99,000
tonnes of organic waste feedstocks per annum. it will comprise a state-of-the-art AD facility designed to
meet the highest environmental and safety standards.
As shown in Figure 3.2 and the Proposed Site Layout Plan included in the architectural suite of planning
drawings, the proposed development comprises a number of integrated elements including:
► 1 - Administration Building (with associated surface level car parking);
► 2 - Main Process Building (with associated vehicle service areas);
► 3 - Odour Control System (with associated emission stack);
► 4 - Bunded Tank Farm (accommodating the vast majority of tanks that require containment);
► 5 - Digestate Treatment Plant (Evaporator);
► 6 - Digestate Drying Plant;
► 7 - Pellet Hall (for fertiliser storage);
► 8 - Combined Heat and Power (CHP) Building (accommodating two CHP Units);
► 9 - Boiler Unit;
► 10 - Shared Emission Stack (Digestate Drying Plant, CHP and Boiler Units);
► 11 - CO2 Liquefaction Plant;
► 12 - Biogas Upgrade Plant (BUP);
► 13 - Biogas Treatment Plant (Biological De-sulphurisation Units);
► 14 - Gas (Holder) Buffer Dome;
► 15 - Weighbridges and Wheel Washes;
► 16 - Liquid Feedstock Storage Tanks (silos);
► 17 - Backup Gas Flare;
► 18 - Fuel Storage Tank;
► 19 - Gas Grid Entry Unit;
► 20 - Fire Water Storage Tank;
► 21 - Liquefied Petroleum Gas (LPG) Storage Tanks (Propane);
► 22 - Freshwater Storage Tank (Underground);
► 23 - Staff and Visitor Parking;
► 24 - Control Building;
► 25 - Transformer; and
► 26 - Back-Up generator.
Other integrated element include:
► Internal road and footway provision;
► Engineered stormwater drainage system;
► Landscaping and Earthworks;
► Lighting;
► Fencing and security gates; and
► Site entrance/exit off the L2280 Drumcall Road with gated frontage. This shall include localised
widening and realignment of this road and reconfiguration of the junction with the R189.
A full description is included in Description of the Proposed Development Chapter of this EIAR (Volume
II) and in the statutory notices.
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Figure 3.1 Proposed Site Layout & Redline Boundary RECEIVED: 28/08/2026
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Figure 3.2 Proposed Site Layout
3.1.1 Site Process
The process can be broadly divided into the following four main stages:
► Feedstock reception and pre-treatment;
► AD treatment;
► Post treatment (following the digestion process); and
► Energy generation and use.
An overview of the AD process is presented in the diagram below (Figure 3.3), with further details on each
of the elements presented in Description of the Proposed Development Chapter of this EIAR. RECEIVED: 28/08/2026
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Figure 3.3 Proposed Site Process
3.1.1.1 Feedstock Reception and Pre-treatment
The planned feedstock mix is outlined in Table 3.1.
The feedstock mix for the proposed development is predominantly poultry manure, with an annual range
of approximately 60,000 – 99,000 tonnes. Additional inputs include cattle manure (2,000 – 10,000 tonnes)
and agri-food organic material (5,000 – 39,000 tonnes). While poultry manure will form the majority of
feedstock, flexibility is built into the system to accept agri-food wastes, particularly during periods when
biosecurity concerns (e.g., avian influenza outbreaks) may restrict the availability or handling of poultry
manure. This ensures continuity of operation while maintaining compliance with biosecurity and health
regulations.
Table 3.1. Feedstock Mix
Feedstock Type Annual Quantity
(Up to 99,000
tonnes)*
Source
Poultry manure 60,000 – 99,000
tonnes
Material will be sourced from the significant
concentration of poultry farms in County Monaghan and
surrounding areas.
Cattle manure 2,000 – 10,000 tonnes Material will be sourced from cattle farms in the
immediate surrounding area.
Agri-food organic
material 5,000 – 39,000 tonnes This material will be sourced from food processing plants
in the surrounding area.
* Note that the combination of feedstock types received at the proposed development collectively will not exceed the 99,000 tonne
annual limit RECEIVED: 28/08/2026
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3.1.1.2 AD Treatment
Received material will be conveyed onwards to pre-treatment processing. Liquid derived primarily from
recirculated digestate and evaporator/ drier condensate, as well as harvested rainwater (and groundwater
/ mains water where required) will be mixed with incoming feedstock to dilute and achieve the required
consistency for processing through the system.
Feedstock blended in the mixing tanks will be pumped to the digester tanks located in the bunded tank
farm. Here the organic material is broken down in the absence of oxygen in an enclosed/sealed
environment to produce both biogas (methane and carbon dioxide) and digestate (the organic material
remaining after the AD process). This material is retained within the digester tanks for c.30 to 35 days
with the biogas collected within the roof space, which is connected to the biogas treatment system. The
AD process occurs 24 hours per day, 7 days per week and operates in temperatures ranging from c.35°C
to 40°C.
The digester tanks will each have a working volume of c.11,530m3 with external insulation and cladding
to retain heat. Material within the tanks will be continuously mixed to suspend the biomass.
Digestate will be displaced by gravity overflow from the digester tanks for onward treatment in the
pasteurisation process.
3.1.1.3 Post Treatment (Following the Digestion Process)
Digestate produced will be pumped to the pasteurisation tanks (located within the main process building).
Compliance with the Animal By-Product (ABP) Regulations requires pasteurisation at 70ºC for one hour.
Pasteurisation is a critical control point within the process, and the system will be designed so that any
loads not meeting the pasteurisation criteria will be recirculated and re-processed, providing no
opportunity for by-pass of this stage. The plant will include temperature monitoring equipment and a
reporting package for proof of batch time and temperature in order to demonstrate achievement of the
ABP sanitisation requirements.
The digestate will then be pumped to the dewatering plant (located within the main process building),
where it will be separated into solid (fibre) and liquid digestate fractions using centrifuge decanters. Fibre
digestate will be collected in a dedicated storage hall (fibre hall) in the main process building prior to being
transferred from the site (via HGVs) and exported for use in agricultural and / or horticulture markets that
have a demand for its valuable nutrient profile. HGVs will service the fibre hall in a manner similar to that
described above for the reception hall.
The plant is designed to further treat liquid digestate produced in the process. A portion of the liquid
digestate will be diverted through established ammonia stripping technology that denitrifies the liquid so
it can be recirculated to the start of the process to dilute the incoming feedstock. The ammonia stripping
stage will generate an ammonium sulphate fertiliser that will also be exported for use in markets with a
demand for this product.
The remainder of the liquid digestate will be treated in an evaporator plant that will thicken the liquid
fraction to produce a concentrate digestate as well as a condensate fraction. The condensate generated
is a clean water source that can be reused in the digestion process to offset reliance on mains water
supply. The concentrate digestate generated will be sent to the drying hall where it will be dried producing
a stable, pathogen free and nutrient rich fertiliser that can be exported off-site for use in horticulture /
agriculture (typically in pellet form). The drying process will also produce a condensate that can be
recirculated into the process. RECEIVED: 28/08/2026
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3.2 Typical Waste Categories
The typical non-hazardous and hazardous wastes that will be generated at the proposed development
from general operations will include the following:
► Organic (food) waste
► Package Treatment Plant Solids;
► Dry Mixed Recyclables;
► Mixed Non-Recyclable Waste;
► Glass;
► Cardboard;
► Plastic;
► Waste electrical and electronic equipment (WEEE) including computers, printers and other ICT
equipment;
► Waste Electrical and Electronic Equipment
► Oil and Oil Filters;
► Cleaning chemicals (paints, adhesives, resins, detergents, etc.); and
► Furniture (and from time-to-time other bulky waste);
Wastes should be segregated into the above waste types to ensure compliance with waste legislation and
guidance while maximising the re-use, recycling and recovery of waste with diversion from landfill
wherever possible.
Foul drainage collected from the on-site welfare facilities during operation will pass through a commercially
sized package treatment plant. It is estimated the plant will generate c.2m3/day of foul effluent. The use
of treated effluent in the AD process is normal practice and is more sustainable than sending to sewer
(where available) and adds to the circular economy model for the plant. It shall be pumped from the outlet
of the package treatment plant to an above ground storage tank with large volume capacity before being
drawn into the Main Process Building to aid the dilution of feedstock process and create a pumpable slurry.
This also reduces demand on external water supplies. Occasional removal of solids off-site (c. 0.5 tonnes
per annum) will be required (estimated once per year) to an appropriate facility, likely the McBreen waste
facility at Corranure, Co. Cavan located c.20km southwest of the site.
3.3 List of Waste Codes
In 1994, the European Waste Catalogue 19 and Hazardous Waste List 20 were published by the European
Commission. In 2002, the EPA published a document titled the European Waste Catalogue and Hazardous
Waste List 21, which was a condensed version of the original two documents and their subsequent
amendments. This document has recently been replaced by the EPA ‘Waste Classification – List of Waste
& Determining if Waste is Hazardous or Non-Hazardous’ 22 2018. This waste classification system applies
across the EU and is the basis for all national and international waste reporting, such as those associated
with waste collection permits, COR’s, permits and licences and EPA National Waste Database23.
Under the classification system, different types of wastes are fully defined by a code. The List of Waste
(LoW) code for typical waste materials expected to be generated during the operation of the proposed
development are provided in Table 3.1 below.
Table 3.2 Typical Waste Types Generated and LoW Codes
Waste Material LoW Code
Site Process waste
Septic Tank Sludge 20 03 04
Operational/Office Waste RECEIVED: 28/08/2026
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Waste Material LoW Code
Readily Biodegradable Hydraulic Oils 13 01 12*
Oil Filters 16 01 07*
Paper and Cardboard 20 01 01
Plastics 20 01 39
Metals 20 01 40
Mixed Non-Recyclable Waste 20 03 01
Glass 20 01 02
Biodegradable Kitchen Waste 20 01 08
Oils and Fats* 20 01 25/26*
Textiles 20 01 11
Batteries and Accumulators* 20 01 33* - 34
Printer Toner/Cartridges* 20 01 27* - 28
Green Waste 20 02 01
WEEE* 20 01 35*-36
Chemicals (solvents, pesticides, paints & adhesives, detergents, etc.)* 20 01
13*/19*/27*/28/29*30
Bulky Wastes 20 03 07
* Individual waste type may contain hazardous materials
1 Liquor & Digestate will be outside of specification, however, is included as a potential waste
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4. ESTIMATED WASTE ARISING
A waste generation model (WGM) developed by AWN, was used to predict waste types, weights and
volumes arising from operations within the proposed development. The WGM incorporates building area
and use and combines these with other data including from similar development operated by the applicant,
along with Irish and US EPA waste generation rates.
The waste generation from other operating and planned sites is based on waste generation rates per m2
floor area and incoming feedstocks.
Although feedstock to the proposed development shall be composed of organic waste only, provision shall
be made within the pre-treatment process for the inadvertent presence of inorganic materials within the
waste, which shall be managed accordingly. Unsuitable material removed by pre-treatment screening will
be exported off-site for further processing at appropriate permitted waste facilities.
The estimated waste generation for the proposed Development for the main waste types is presented in
Table 4.1
Table 4.1 Estimated Waste Generation for Proposed Plant
Waste Type Estimated Amount /
Annum (tonnes)
General Waste & Dry
Mixed recycling 20
Waste Oil 35
Waste Oil Filters 1
Metal 10
Package Treatment Plant
Solids 0.5
Total 66.5
4.1.1 By-Products of the Anaerobic Digestion Process
As set out in the Description of the Proposed Development Chapter of this EIAR, the AD process will
produce a range of by-products, the nature and volume of which will depend on the feedstock mix and
product demand within the local market. The typical annual quantities anticipated to be produced are
shown in Error! Reference source not found..
Table 4.2 By-Products of the AD Process
Product Annual Quantity Likely Application
Fibre digestate Up to 60,000 tonnes These sustainable fertiliser products will be derived from
pasteurised digestate and will be suitable for application in the
local agri-food sector, whether in horticulture or agriculture .
They can be applied for safe use wherever there is a suitable
need for the nutrients.. This creates an excellent circular
economy use for these materials that offsets the need for
artificial fertilisers.
Dried fertiliser /
pellets Up to 7,000 tonnes*
Ammonium sulphate Up to 9,000 tonnes RECEIVED: 28/08/2026
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Product Annual Quantity Likely Application
Biogenic CO2 Up to 15,000 tonnes
Food grade biogenic CO2 suitable for use in a range of
industries with a demand for this product in Monaghan and
other counties including beverage production, food processing
and packaging, greenhouses, refrigeration industry and
production of e-fuels and sustainable aviation fuels. RECEIVED: 28/08/2026
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5. WASTE STORAGE AND COLLECTION
This section provides information on how waste generated within the Site will be stored and collected.
This has been prepared with due consideration of the proposed Site layout as well as best practice
standards, local and national waste management requirements, including those of MCC. In particular,
consideration has been given to the following documents:
► BS 5906:2005 Waste Management in Buildings – Code of Practice24,
► The NWMPCE (2024);
► MCC, County of Monaghan (Segregation, Storage and Presentation of Household and Commercial
Waste) Bye-Laws (2019).
► MCC, The Monaghan County Development Plan 2025 – 2031 (2024); and
► BS 5906:2005 Waste Management in Buildings – Code of Practice.
5.1 Site Process Waste
The proposed development will generate digestate as a by-product of the AD process. Details of the AD
process are provided in Section 3.1.1.
5.1.1 Digestate
Digestate will be managed in compliance with the ABP Regulations and relevant environmental legislation.
Digestate fractions (solid fibre and liquid) will be stored in designated areas within the facility prior to
removal from site by authorised waste contractors. Documentation will be maintained in accordance with
ABP compliance requirements.
5.2 General Waste
Although feedstock to the proposed development will only comprise organic waste, provision shall be made
within the pre-treatment process for the inadvertent presence of inorganic materials within the waste,
which shall be managed accordingly. Unsuitable material removed by pre-treatment screening will be
exported off-site for further processing at appropriate licensed facilities.
Opportunity for waste prevention at the plant relates to the small amounts of office and canteen waste
that will be generated in the administration and welfare facilities, and from general usage and wastage of
materials as a result of the wider operation and maintenance of the plant.
A separate collection system will be provided for kitchen waste generated in the canteen. Food waste
from the canteen can be processed onsite and all other separately collected canteen waste will be
recovered/recycled off-site. Other wastes that will be generated in small quantities at the plant, including
waste oils and chemicals, general office waste, paper and packaging, will be separately collected and
transferred off-site for recovery, recycling or disposal.
Waste prevention awareness will be promoted, and a source segregation policy implemented as part of
the Environmental Management System (EMS) to maximise the recovery of potential recyclable materials
from these waste streams. This shall be managed through the implementation of an Operational Waste
Management Plan.
Site staff will be required to segregate general waste into the following waste categories within their unit:
► Dry Mixed Recyclables, RECEIVED: 28/08/2026
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► Mixed Non-Recyclables,
► Organic waste, and
► Glass.
The Site Office will store its waste within its own unit. Suitably sized bins should be strategically located
within the unit as required by site staff to facilitate segregation at source of these waste types.
Figure 5-1. Typical Waste Receptacles of Varying Size (240L and 1100L)
All mobile waste containers and should be clearly labelled and colour coded to avoid cross contamination
of the different waste streams. Graphical signage should be posted above or on the bins to show exactly
which wastes can be put in each.
If there is food preparation carried out in the site office, organic waste from kitchen should be collected
in bins as close to food preparation area as possible.
Based on the recommended bin requirements, it is anticipated that dry mixed recyclables, mixed non -
recyclables and organic waste will be collected on a weekly basis and glass collected less frequently as
required.
Other waste materials such as oil filters, hydraulic oil, batteries, WEEE, light bulbs and textiles/cloths will
be generated less frequently and in smaller quantities. Site staff will be required to store any of these
wastes in appropriate receptacles within their own unit pending collection by a waste contractor.
5.3 Waste Collection
There are numerous private contractors that provide waste collection services in the MCC area. All waste
contractors servicing the proposed development must hold a valid waste collection permit for the specific
waste types collected. All waste collected must be transported to registered / permitted / licensed facilities
only.
All waste receptacles should be clearly identified as required by waste legislation and the requirements of
the MCC Waste Bye-Laws. Waste will be presented for collection in a manner that will not endanger health,
create a risk to traffic, harm the environment or create a nuisance through odours or litter.
It is recommended that bin collection times are staggered to reduce the number of bins required to be
emptied at once and the time the waste vehicle is on-Site. This will be determined during the process of
appointment of a waste contractor.
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5.4 Additional Potential Waste Materials
In addition to the typical waste materials that are generated on a daily basis, there will be some additional
waste types generated from time to time that will need to be managed separately. A non-exhaustive list
is presented below.
Deposit Return Scheme
Most drinks containers can be recycled via the deposit return scheme, such as bottles, cans and tins made
from plastic, aluminum or steel can be returned once they are between 150ml and 3 litres in size and have
the Re-turn logo on them.
At the shops you can either return the containers:
► Using a Reverse Vending Machine (RVM)
► Manually in the shop
If a shop does not have a RVM but they sell containers with the Re-turn logo, the shop may allow you to
manually return containers in store, unless they have a take back exemption.
Locations of RVM machines can be found via the Re-turn website (www.re-turn.ie)
Green Waste
Green waste may be generated from external landscaping and internal plants / flowers. Green waste
generated from landscaping of external areas will be treated in the AD process on site.
Batteries
A take-back service for waste batteries and accumulators (e.g. rechargeable batteries) is in place in order
to comply with the S.I. No. 283/2014 - European Union (Batteries and Accumulators) Regulations 2014,
as amended. In accordance with these regulations, consumers are able to bring their waste batteries to
their local civic amenity centre or can return them free of charge to retailers which supply the equivalent
type of battery, regardless of whether or not the batteries were purchased at the retail outlet and
regardless of whether or not the person depositing the waste battery purchases any product or products
from the retail outlet.
The operator cannot use the civic amenity centre. They must segregate their waste batteries and either
avail of the take-back service provided by retailers or arrange for recycling / recovery of their waste
batteries by a suitably permited / licenced contractor. Facilties management may arrange collection,
depending on the agreement.
Waste Electrical and Electronic Equipment (WEEE)
The WEEE Directive (Directive 2002/96/EC) and associated Waste Management (WEEE) Regulations have
been enacted to ensure a high level of recycling of electronic and electrical equipment. In accordance with
the regulations, consumers can bring their waste electrical and electronic equipment to their local recycling
centre. In addition, consumers can bring back WEEE within 15 days to retailers when they purchase new
equipment on a like for like basis. Retailers are also obliged to collect WEEE within 15 days of delivery of
a new item, provided the item is disconnected from all mains, does not pose a health and safety risk and
is readily available for collection.
As noted above, the operator cannot use the civic amenity centre. They must segregate their WEEE and
either avail of the take-back / collection service provided by retailers or arrange for recycling / recovery of
their WEEE by a suitably permited / licenced contractor. Facilties management may arrange collection,
depending on the agreement.
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Printer Cartridge / Toners
It is recommended that a printer cartridge / toner bin is provided in the office where appropriate. The
operator will be required to store this waste within their office unit and arrange for return to retailers or
collection by an authorised waste contractor, as required.
Chemicals
Chemicals (such as solvents, paints, adhesives, resins, detergents, etc.) will be generated as part of the
processes on site. These will be stored in appropriately bunded containers prior to off-site removal and
appropriate recovery / recycling / disposal as required.
Any waste cleaning products or waste packaging from cleaning products generated by the operator that
is classed as hazardous (if they arise) will be appropriately stored within the operators’ own space.
Light Bulbs
Waste light bulbs (fluorescent, incandescent and LED) may be generated by lighting at the development.
It is anticipated that the operator will be responsible for the off-site removal and appropriate recovery /
disposal of these wastes.
Textiles
Where possible, waste textiles should be recycled or disposed of if contaminated. The operator will be
responsible for disposing of waste textiles appropriately.
Waste Oil and Filters
Waste oil and filters will need to be stored within the site on a bunded area or spill pallet and regular
collections by a dedicated waste contractor will need to be organised as required.
Furniture & Other Bulky Waste Items
Furniture and other bulky waste items (such as office furniture, etc.) may occasionally be generated by
the operator. The collection of bulky waste will be arranged, as required.
5.5 Pest Management
A pest control operator will be appointed if required to manage pests onsite during the operational phase
of this development. All waste generated within the development will be stored in closed waste receptacles
both within the designated areas and receptacles. Any waste receptacles will be carefully managed to
prevent leaks, odours and pest problems.
All areas will have access for potential control of vermin (if required) and be supplied with hot or cold
water, a drainage point and will be regularly inspected by facilities management to deter pests.
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6. SUMMARY AND CONCLUSION
This OWMP provides a strategy for segregation (at source), storage and collection of all wastes generated
within the site during the operational phase.
There is no likelihood of any significant production of waste arising from the nature of the development.
The digestate arising from the AD facility will be utilised as a soil conditioner and applied to farmland. The
application of the digestate will be done in accordance with European Communities (Good Agricultural
Practice for Protection of Waters) Regulations 2022 S.I. No. 113 of 2022).
The site staff will be responsible for managing waste and bringing waste from site to the collection point.
This WMP presents a waste strategy that complies with all legal requirements, waste policies and best
practice guidelines and demonstrates that the required storage areas have been incorporated into the
design of the development.
Implementation of this OWMP will ensure a high level of recycling, reuse and recovery at the development.
All recyclable materials will be segregated at source to reduce waste contractor costs and ensure maximum
diversion of materials from landfill, thus achieving the targets set out in the NWMPCE 2024 and the MCC
waste by-laws. RECEIVED: 28/08/2026
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7. REFERENCES
1. Waste Management Act 1996 as amended.
2. Environmental Protection Agency Act 1992 as amended.
3. Litter Pollution Act 1997 as amended.
4. Regional Waste Management Planning Offices, The National Waste Management Plan for a Circular
Economy 2024 - 2030 (2024).
5. Monaghan County Council (MCC) County of Monaghan (Segregation, Storage and Presentation of
Household and Commercial Waste) Bye-Laws (2019).
6. Directive (EU) 2018/2001 The Promotion of the Use of Energy from Renewable Sources (2018)
7. Department of Environment and Local Government (DoELG) Waste Management – Changing Our
Ways, A Policy Statement (1998).
8. Department of Environment, Heritage and Local Government (DoEHLG) Preventing and Recycling
Waste - Delivering Change (2002).
9. DoELG, Making Ireland’s Development Sustainable – Review, Assessment and Future Action (World
Summit on Sustainable Development) (2002)
10. DoEHLG, Taking Stock and Moving Forward (2004).
11. Department of Communications, Climate Action and Environment (DCCAE), Waste Action Plan for
the Circular Economy - Ireland’s National Waste Policy 2020-2025 (2020).
12. DCCAE, Whole of Government Circular Economy Strategy 2022-2023 ‘Living More, Using Less’
(2021).
13. The Circular Economy and Miscellaneous Provisions Act 2022.
14. Department of Agriculture, Food and the Marine Ireland’s National Biomethane Strategy (2024).
15. Waste Management (Landfill Levy) (Amendment) Regulations 2015 (as amended).
16. Monaghan County Council (MCC), Monaghan County Development Plan 2025 – 2031 (2025).
17. European Union (Good Agricultural Practice for Protection of Waters) Regulations 2022 (S.I. No.
113 of 2022).
18. European Parliament and Council. (2009). Regulation (EC) No 1069/2009 laying down health rules
as regards animal by-products and derived products not intended for human consumption and
repealing Regulation (EC) No 1774/2002.
19. European Waste Catalogue - Council Decision 94/3/EC (as per Council Directive 75/442/EC).
20. Hazardous Waste List - Council Decision 94/904/EC (as per Council Directive 91/689/EEC).
21. EPA, European Waste Catalogue and Hazardous Waste List (2002). RECEIVED: 28/08/2026
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22. EPA, Waste Classification – List of Waste & Determining if Waste is Hazardous or Non-Hazardous
(2018).
23. EPA, National Waste Database Reports 1998 – 2020 and the Circular Economy and National Waste
Database Report 2021 – 2023 (2025).
24. BS 5906:2005 Waste Management in Buildings – Code of Practice.
RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 9.1
NRA/TII RATING CRITERIA: SOILS &
GEOLOGICAL
Stream BioEnergy Ireland Limited
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APPENDIX 9.1
Appendix 9.1
NRA/TII Criteria for Rating the Magnitude and Significance of Soils and Geological Impacts at EIA Stage
National Roads Authority.
(NRA/TII, 2009).
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Table 1 Criteria for rating site Attributes – Estimation of Importance of Soil and
Geology Attributes (NRA)
Importance Criteria Typical Examples
Very High
Attribute has a high quality,
significance or value on a regional or
national scale
Degree or extent of soil
contamination is significant on a
national or regional scale
Volume of peat and/or soft organic
soil underlying route is significant on
a national or regional scale*
Geological feature rare on a
regional or national scale (NHA)
Large existing quarry or pit
Proven
economically extractable mineral
resource
High
Attribute has a high quality,
significance or value on a local scale.
Degree or extent of soil
contamination is significant on a local
scale.
Volume of peat and/or soft organic
soil underlying route is significant on
a local scale. *
Contaminated soil on site with
previous heavy industrial usage
Large recent landfill site for mixed
wastes
Geological feature of high value
on a local scale (County
Geological Site)
Well drained and/or high fertility
soils
Moderately sized existing quarry
or pit
Marginally economic extractable
mineral resource
Medium
Attribute has a medium quality,
significance or value on a local scale
Degree or extent of soil
contamination is moderate on a local
scale
Volume of peat and/or soft organic
soil underlying route is moderate on a
local scale*
Contaminated soil on site with
previous light industrial usage
Small recent landfill site for mixed
wastes
Moderately drained and/or
moderate fertility soils
Small existing quarry or pit
Sub-economic extractable mineral
resource
Low
Attribute has a low quality,
significance or value on a local scale
Degree or extent of soil
contamination is minor on a local
scale.
Volume of peat and/or soft organic
soil underlying route is small on a
local scale*
Large historical and/or recent site
for construction and demolition
wastes.
Small historical and/or recent
landfill site for construction and
demolition wastes.
Poorly drained and/or low fertility
soils.
Uneconomically extractable
mineral resource.
* relative to the total volume of inert soil disposed of and/or recovered
Source: Box 4.1: ‘Guidelines on Procedures for Assessment and Treatment of Geology for National Road Schemes’ by the
National Roads Authority (NRA, 2009)
RECEIVED: 28/08/2026
Monaghan Anaerobic Digester EIAR / 247501.0350
AWN Consulting Ltd 3
Table 2 Criteria for Rating Impact Significance at EIA Stage - Estimation Of Magnitude
of Impact on Soil / Geology Attribute (NRA)
Magnitude of
Impact Criteria Typical Examples
Large Adverse Results in loss of
attribute
Loss of high proportion of future quarry or pit reserves
Irreversible loss of high proportion of local high fertility
soils
Removal of entirety of geological heritage feature
Requirement to excavate / remediate entire waste site
Requirement to excavate and replace high proportion
of peat, organic soils and/or soft mineral soils beneath
alignment
Moderate Adverse
Results in impact on
integrity of attribute or
loss of part of attribute
Loss of moderate proportion of future quarry or pit
reserves
Removal of part of geological heritage feature
Irreversible loss of moderate proportion of local high
fertility soils
Requirement to excavate / remediate significant
proportion of waste site
Requirement to excavate and replace moderate
proportion of peat, organic soils and/or soft mineral
soils benath alignment
Small Adverse
Results in minor impact
on integrity of attribute
or loss of small part of
attribute
Loss of small proportion of future quarry or pit
reserves
Removal of small part of geological heritage feature
Irreversible loss of small proportion of local high
fertility soils and/or high proportion of local low fertility
soils
Requirement to excavate / remediate small proportion
of waste site
Requirement to excavate and replace small proportion
of peat, organic soils and/or soft mineral soils beneath
alignment
Negligible
Results in an impact on
attribute but of
insufficient magnitude to
affect either use or
integrity
No measurable changes in attributes
Minor Beneficial
Results in minor
improvement of attribute
quality
Minor enhancement of geological heritage feature
Moderate Beneficial
Results in moderate
improvement of attribute
quality
Moderate enhancement of geological heritage feature
Major Beneficial
Results in major
improvement of attribute
quality
Major enhancement of geological heritage feature
Source: Box 5.1: ‘Guidelines on Procedures for Assessment and Treatment of Geology, for National Road Schemes’ by the
National Roads Authority (NRA, 2009)
RECEIVED: 28/08/2026
Monaghan Anaerobic Digester EIAR / 247501.0350
AWN Consulting Ltd 4
Table 3 Rating of Significant Environmental Impacts at EIA Stage (NRA)
Importance of
Attribute
Magnitude of Importance
Negligible Small Adverse Moderate Adverse Large Adverse
Extremely High Imperceptible Significant Profound Profound
Very High Imperceptible Significant/moderate Profound/Significant Profound
High Imperceptible Moderate/Slight Significant/moderate Profound/Significant
Medium Imperceptible Slight Moderate Significant
Low Imperceptible Imperceptible Slight Slight/Moderate
Source: Box 5.4: Guidelines on Procedures for Assessment and Treatment of Geology for National Road Schemes’ by the
National Roads Authority (NRA, 2009)
RECEIVED: 28/08/2026
AUGUST 2026
VOLUME III
APPENDICES TO
ENVIRONMENTAL IMPACT ASSESSMENT REPORT
APPENDIX 9.2
MONAGHAN – COUNTY
GEOLOGICAL SITE REPORT
Stream BioEnergy Ireland Limited
RECEIVED: 28/08/2026
MONAGHAN - COUNTY GEOLOGICAL SITE REPORT
NAME OF SITE Rockcorry-Cootehill Ribbed Moraines
Other names used for site
IGH THEME IGH7 Quaternary
TOWNLAND(S) Too many to list … this portion of the field covers
over two hundred individual townlands, across an
area of 180 km2
NEAREST TOWN/VILLAGE Rockcorry, Cootehill (just inside Cavan)
SIX INCH MAP NUMBER Monaghan 17, 18, 22, 23
ITM CO-ORDINATES 666000E 891000N (centre of features)
1:50,000 O.S. SHEET NUMBER 28a GSI BEDROCK 1:100,000 SHEET NO. 8/9
Outline Site Description
These moraines form part of the largest field of ribbed moraines found anywhere in the world
(which also includes the Scotshouse-Redhills cross cutting ribbed moraines). The entire field
includes over 3,000 features and this subset, covering an area of 18 by 10 kilometres,
contains approximately 160 individual features. It includes the largest individual ribbed
moraines found anywhere in the world.
Geological System/Age and Primary Rock Type
The ribbed moraines were formed on bedrock of Silurian and Ordovician metasediments and
volcanic rocks. The features themselves are Quaternary in age, having been deposited at
the base of the ice sheet as it moved in a southeasterly direction during the maximum period
of the last Ice Age.
Main Geological or Geomorphological Interest
These ribbed moraines each contain many superimposed drumlins on their crests, and the
area has traditionally been known as the middle portion of the ‘Drumlin Belt’. Owing to their
size the ribbed moraines can only be seen using digital elevation modelling (DEM) and
satellite imagery.
This ribbed moraine field is not only unusual in its huge size and the size of individual
features around Rockcorry and Cootehill, but because they are interspersed with thick peat
deposits the features are quite striking. They form the perfect ‘ribbed’ topography.
The features are generally 5km–8km long and 800m or so wide, with individual
superimposed drumlins being c. 600m long and 100m–200m wide. They attain a maximum
height of about 50m but are typically 30m or so high. The largest individual feature is 10 km
long, 1 km wide and up to 45m high, and contains approximately 400 million tonnes of
sediment.
Site Importance – County Geological Site; recommended for Geological NHA
These are the largest individual ribbed moraine features anywhere in the world and therefore
one of the most important geological terrains in Ireland.
Management/promotion issues
This is an excellent site in terms of macro-scale Quaternary subglacial geomorphology. The
features are too large to undertake any conservation efforts on their part, but the landscape
itself is noteworthy and should be promoted as unique amongst landscape elements within
both the Monaghan County Development Plan, and in Landscape Characterisation.
Page 1 of 4 RECEIVED: 28/08/2026
A view across some of the Rockcorry-Cootehill ribbed moraines at Cargaghbane, east of
Cootehill.
Ribbed moraines near Latton, County Monaghan, looking south.
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