EU Landfill Reporting Obligations

Landfilling of waste – the EEA is not in charge of a comprehensive inventory of landfills as there is no such reporting obligation at European level

Landfills that are of a substantial size are reported (those receiving 10 tonnes per day or with a total capacity of 25 000 tonnes) and made available together with other activities in the industrial emission dataset (https://www.eea.europa.eu/ds_resolveuid/DAT-238-en) and the Industrial Emission Portal (https://industry.eea.europa.eu/).

Mapping Irish fires with NASA

Aghowle, Carlow

Aghowle Carlow on NASA’s Fire Information for Resource Management System

https://firms.modaps.eosdis.nasa.gov/map/#t:adv;d:2022-02-22..2022-03-24,2022-02-22;@-6.6,52.8,14z

Mourne Mountains (Spelga Dam & Cock and Hen Mountains)

https://www.belfasttelegraph.co.uk/news/northern-ireland/eight-fire-appliances-and-crews-ascending-mourne-mountains-to-tackle-gorse-fires-41477872.html

Ox Mountains, Foxford, Mayo

https://www.midwestradio.ie/index.php/news/56128-gorse-fires-on-the-ox-mountains-last-night-threatened-homes-and-properties

Claremorris, Mayo

Fivemiletown, Tyrone

Belfast

Kilkenny (Brandon Hill, south x3 sites)

https://twitter.com/StevieCahill/status/1507007531561881620/photo/2

Corbetstown, Offaly (peatland site?)

Agricultural atmospheric ammonia: identification & assessment of potential impacts

Reactive nitrogen pollution, particularly ammonia (NH3), when above critical limits adversely impacts biodiversity through eutrophication, acidification or direct toxic effect. Though total nitrogen deposition is a primary driver for species community changes and impacts, the concentration of ammonia should also be considered. Both total nitrogen deposition and ambient ammonia concentrations are above levels that can result in harm to biodiversity at many Natura 2000 sites across Europe and in Ireland. Reactive nitrogen is principally composed of both chemically reduced ammonia and ammonium (NH4+), alongside oxides of nitrogen (NOx). While traffic is the primary source of oxides of nitrogen, agriculture accounts for virtually all ammonia emissions in Ireland.


Although there is substantial evidence that reactive nitrogen causes negative impacts on biodiversity, the relationship between exposure to reactive nitrogen (dose) and negative ecological indicators (effect) is not always straightforward. The complexity of understanding dose-effect relationships increases if multiple factors with negative effects occur concurrently (e.g. adverse effects of air quality occurring at the same time as adverse effects of climate change). Additionally, adverse impacts of reactive nitrogen are likely to occur over long periods of time and may not be immediately visible during a site survey. It is recommended that, although indicators of negative effects may be observed during field visits, these indicators should be used alongside other evidence (such as monitored or modelled concentration or deposition, local sources, local knowledge) to build evidence of adverse impacts on a site. Essentially, ecological indicators alone should not be used as evidence of adverse impacts but rather considered as part of a suite of indicators. Survey indicators could include algal proliferation, presence of nitrogen tolerant species, absence of nitrogen sensitive species, presence of pink or decaying Reindeer Lichen (Cladonia portentosa) or of decaying Sphagnum spp.


A guidance document describing a framework for the assessment of impacts of ammonia emissions from intensive agricultural installations has recently been published in the Republic of Ireland by the Environmental Protection Agency (EPA). Similar guidance has also been published in Northern Ireland, England, Scotland and Wales as well as other European Member States on how reactive nitrogen should be assessed in the context of Environmental Impact Assessment (EIA), Appropriate Assessment (AA) and AA screening. Recent court rulings in the Netherlands support the need to implement science-based and defensible approaches to the assessment and management of agricultural emissions of nitrogen to the atmosphere. There have been two broad approaches applied within Europe to the assessment of potential reactive nitrogen and ammonia impacts on Natura 2000 sites, namely the Critical Criteria Approach and the Integrated Approach.


The Critical Criteria Approach prevents the development of new sources that have a significant potential to adversely affect Natura 2000 Sites but allows the development of sources that do not have significant adverse effects. The Critical Criteria Approach is currently adopted by the majority of Member States who have a policy of dealing with such emissions. The Integrated Approach provides a framework for reducing emissions from existing sources to create room for new activities such as infrastructure, housing or intensive agricultural installations. The Integrated Approach was adopted by the Netherlands in 2015. However, because it allowed credits for reductions to be gained prior to the gains being realised, it was deemed illegal by the Dutch Council of State in 2019. As a consequence, modifications to the integrated approach are currently being investigated in the Netherlands. However, the European Commission commended the integrated approach highlighting it as the most appropriate method to deal with the issue of adverse impacts of reactive nitrogen from agriculture.


The assessment of emissions of ammonia from agricultural developments, required for planning or licence consent, is predominantly undertaken using air dispersion modelling techniques. A range of dispersion modelling approaches are available for the assessment of impacts from agricultural development. These dispersion modelling approaches vary in complexity and accuracy with simple approaches generally overestimating impacts to provide a highly conservative indication of potential

impacts and more advanced modelling approaches generally providing a more representative, yet conservative indication of potential impacts. This Irish Wildlife Manual aims to summarise:
– The effects of emissions of ammonia from intensive agricultural sources and its deposition on biodiversity.
– The regulatory requirements for the assessment of these effects and the indicators of adverse effects including physical observations and theoretical limits used in modelling assessment.
– The approach recommended by the Irish EPA and approaches used in various European Countries that are currently used to assess and report on the potential effects of emissions of ammonia from agricultural development.
– A framework for high-level review of dispersion modelling assessment intended for non-expert users of dispersion models that details a non-technical basis to consider whether the critical components of a dispersion modelling study meet the requirements of dispersion modelling guidance issued by the Irish EPA.

There is no single publicly available database in Ireland that quantifies and locates ammonia emitting activities

Emissions from individual projects that are determined to be insignificant in isolation can be approved using a critical criteria approach. The use of the same approach for multiple projects, either concurrently or consecutively can result in baseline creep, where over time the combined impacts of individually insignificant projects result in a significant adverse impact, that may not be identified using a critical criteria approach.

The predominant source of ammonia in Ireland is cattle farming, which is well dispersed throughout the country. Intensive farming of pigs and poultry contributes a far lower proportion of total emissions of ammonia, but these activities are concentrated in a small number of high production areas, where the effects on biodiversity can be significant.

The border counties of Cavan and Monaghan have the highest concentrations of IED licensed and sub-threshold intensive agricultural facilities. Both Cavan and Monaghan also have high densities of cattle (cattle/km²) compared to the average cattle density in Ireland.

AIE: Access to list of Bord na Mona bog IDs, bog names, locations, IPPC licences, area in Ha, land use and drainage data

AIE Request COSEC00327

I refer to the request you made under the European Communities (Access to Information on the Environment) Regulations 2007 to 2018 (S.I. No. 133 of 2007, S.I. No. 662 of 2011, S.I. 615 of 2014 and S.I. No. 309 of 2018) (hereafter referred to as the AIE Regulations) for access to information in relation to GIS data of the following:

BSM Bog ID

BNM Bog No.
BNM Bog Name
BNM Bog group
County
IPPC Licence no.

Area in hectares (as per GIS system)

Main land use

Other land use

Drainage (pumped, gravity, part pumped)


Extension date by which decision will be made

As indicated in the acknowledgement of 23rd February 2022,  Bord na Móna Plc. is obliged to notify you of its decision on this request within one month of its receipt. However, Article 7(2)(b) of the AIE Regulations allows a public body to extend this time period up to a maximum of 2 months from the date on which the request was received, where the decision maker is unable, due to the volume or complexity of the request, to make a decision within the original one month period.

Records relevant to your request have been located by Bord na Móna plc.  However, issues have arisen with regard to the applicability of grounds for refusal under Article 9 of the AIE Regulations, which unfortunately it will not be possible to resolve within the one-month timeframe.   Therefore, I am extending the time for dealing with your request by one month from the date indicated to you in the acknowledgement letter. I will notify you of my decision as soon as possible, but at the latest by 21st April 2022.

Yours sincerely,

John MacNamara

Waste Council Directive 86/278/EEC on the protection of soil, when sewage sludge is used in agriculture

Reporting frequency: Annually

First report due: 31/08/2023

86/278/EEC 86/278/EEC Report on the use of sludge in agriculture: the quantities used, the criteria followed and any difficulties encountered 

Proposals for Reporting on the use of sludge

1) Names and addresses of the recipients of the sludge

2) Place where the sludge is to be used

3) Agricultural facilities receiving sludge

Note: dataset may include personal data and require secure data exchange

Reported Member State / Country Dataset

https://rod.eionet.europa.eu/instruments/514 Questionnaire on the implementation of Sewage sludge directive        

Reporting is based on questionnaire: https://eur-lex.europa.eu/legal-content/EN/ALL/?uri=CELEX:31994D0741

Initial Feedback from Member States:

Data is reported in a descriptive form (report)

Maybe Directive is under revision

We don’t have data

How is the data identified?  

Very difficult to find the data in the NL

How is the geodata reported?  

AF – Agricultural and aquaculture facilities     

Nitrates Directive Report (91/676/EEC): Ireland’s Reporting Obligation

EC Reporting on water pollution by nitrates and action programmes taken in vulnerable zones.

Member States shall, in respect of the four-year period following the notification of this Directive and in respect of each subsequent four-year period, submit a report to the Commission containing the information outlined in Annex V.

Note: While the reporting comes from the EPA, they have confirmed that the summary text on farm activities, measures and inspections etc included in the report come directly from the Department of Agriculture Food and the Marine (DAFM).

The raw data on the farm activities, measures and inspections used by DAFM to create the summary in the report is held by DAFM

For the EPA’s annual assessment of water quality in relation to the nitrates derogation, DAFM provides the EPA with an image/map of the derogation farm locations. The most recent report, which includes the image/map of 2020 Derogation Herd Locations, is available on the EPA website. https://www.epa.ie/publications/monitoring–assessment/freshwater–marine/nitrogen-and-phosphorus-concentrations-in-irish-waters-2020.php

Reports are filed here:

EnvelopeNitrate Directive Article 10 Report 2016-2019 for Ireland Supplemental 4End24 Feb 2021
EnvelopeNitrate Directive Article 10 Report 2016-2019 for Ireland Supplemental 3End19 Feb 2021
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland Supplement 8End19 Feb 2021
EnvelopeNitrate Directive Article 10 Report 2016-2019 for Ireland Supplemental 2End22 Dec 2020
EnvelopeNitrate Directive Article 10 Report 2016-2019 for Ireland Supplemental 1End10 Nov 2020
EnvelopeNitrate Directive Article 10 Report 2016-2019 for IrelandEnd09 Nov 2020
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland Supplement 7End17 Oct 2017
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland Supplement 6End04 Oct 2017
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland supplement 5End28 Nov 2016
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland Supplement 4End22 Nov 2016
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland Supplement 3End13 Oct 2016
EnvelopeNitrates Directive Article 10 Report 2012-2015 for Ireland Supplement 2End14 Sep 2016
EnvelopeNitrate Directive Article 10 Report 2012-2015 for Ireland Supplement 1End18 Jul 2016
EnvelopeNitrate Directive Article 10 Report 2012-2015 for IrelandEnd29 Jun 2016
EnvelopeIreland Nitrates Directive Article 10 Report 2008-2011End16 Jul 2012
EnvelopeNitrates Report 2008 DeliveryEnd23 Oct 2008
EnvelopeNitrates ReportDraft22 Jul 2008

AIE: Section 12 Water Pollution Notice served by Leitrim County Council on Coillte in relation to LM02-FL0026 (Water Pollution at Derrynahimmirk, Rossinver, Co Leitrim)

3 December 2021

Reason for Inspection
Complaint received from Rural Water in relation to contamination of drinking water (well supply) supply serving 3 houses and land connection, contamination possible because of works on nearby forestry.

The Derrynahimmirk stream rises from agricultural land to South and discharges through the felled zone where, beyond the forestry site, it converges with the Glenaniff River before discharging to Lough Melvin. Due to the Glenaniff River’s drop from High to Good Status it forms part of the Blue Dot Catchments Programme, a collaborative initiative for the protection and restoration of rivers and lakes that have deteriorated since the 1st River basin management cycle in 2007.


One river crossing point was noted, its construction appears degraded with the stream clogged either side and lush grown in the stream. Sections of the stream are laden with sediment. At the lowest point of the site the stream is wider and faster flowing and the natural course has been altered by timber, brash and debris obstructing the flow path. Logs and timber debris were noted in the river further upstream. Damage was also noted to a small number of native trees within the buffer zone of the Derrynahimmirk Stream

Site Inspection Photos

Correspondence with Coillte

Reports

Results

Maps

Action 2016.5: Priority list of datasets for e-Reporting

Access to environmental information remains challenging

The new Open Data legislation only comes into play only the question of access is decided. An applicant must prove a right of access (eg via AIE/FOI) first, before making an application for Open Data access

Commission officials have gone through the relevant EU legislation, together with the Member States, and prepared a list of datasets on environmental reporting.

That list also reflects the data gaps identified during the evaluation of the state-of-implementation and the fitness of the Directive for its intended purpose (a so-called REFIT evaluation).

Note: There are no reporting obligations on members states (but suggestions can be made which will be transmitted to the relevant units in the Commission)

The main objectives for this action are to:

  • communicate environmental information priorities and expectations to Member States by clearly identifying the spatial data sets relevant for environmental reporting;
  • provide guidance on consistent mapping of reporting obligations and supporting data to INSPIRE spatial objects for the development of pan-European data sets;
  • identify reporting redundancies and explore opportunities for streamlining;
  • improve the timeliness and the quality of reported data.

The list is a ‘living inventory’ of environmental information needs and as such provides an instrument to:

  • incrementally build comparable INSPIRE maturity across member states for all INSPIRE components (metadata, services, interoperability, data sharing) based on a common setting;
  • plan tangible and usable INSPIRE deliverables for eReporting;
  • monitor progress on INSPIRE implementation in general and for the reporting use case in specific;
  • promote the reuse of the INSPIRE infrastructure for reporting purposes.

EU plan is to propose these e-reporting datasets be included on the upcoming list of high-value datasets (under Open Data Directive), which will have to be (a) available free of charge, subject to a two year derogation/exemption; (b) machine readable; (c) provided via APIs; and (d) provided as a bulk download, where relevant

Due to the time the above process will take, plus the addition of the 2-year derogation, we are looking to 2025-26 for implementation ?

89 datasets are currently listed

Summary List of Datasets

Information on Ambient Air Quality

List of major roads, railways, airports and agglomerations

Strategic Noise Maps

River Basin Districts and Competent Authorities

Characterisation of River Basin Districts

Monitoring Programmes / Location of monitoring stations (water)

Preliminary Flood Risk Assessment and Areas of Potential Significant Flood Risk

Flood Hazard Maps and Flood Risk Maps

Units of Management and Competent Authorities / Boundaries of management units / Competent Authority

Information on the subdivision of marine regions and subregions / Subdivisions of marine regions or subregions

Monitoring programmes / Location of monitoring stations / Marine monitoring stations

Report on Quality of Water for Human Consumption / Water supply zones and related monitoring information, attainment of limit values / DWD water supply zones

Identification of Bathing Areas / Bathing water areas (beaches falling under the Directive)

Information on monitoring results / Location of wastewater treatment plants, agglomerations, discharge points and sensitive areas (Location of UWWTD plants)

Information on monitoring results / Location of wastewater treatment plants, agglomerations, discharge points and sensitive areas (Location of discharge points linked to WFD water body)

Information on monitoring results / Location of wastewater treatment plants, agglomerations, discharge points and sensitive areas (Sensitive areas, less sensitive areas and catchments)

Monitoring and Implementation report / Monitoring data written text (NiD monitoring stations)

Vulnerable zones notification / Datasets of vulnerable zones

Implementation Report / Habitat types and species distribution and range data

Supporting reporting obligation under Habitats Directive

Habitat types, species distribution (Art. 17: implementation measures) / Habitat types and species distribution and range data (Various habitat maps using INSPIRE geographical grid system)

Location of Natura 2000 sites / Boundaries of NATURA 2000 sites

Birds geographical distribution (Art. 12: implementation measures)

ALIEN SPECIES Reporting on various issues, including on the surveillance system, actions plans, eradication and management measures etc.

Areas designated under national legislation for the purpose of nature protection including sites such as national parks and nature reserves. (This reporting obligation is an Eionet core data flow)

E-PRTR Report covering data reported by industrial facilities covering 65 economic activities within 9 industrial sectors (Article 7) / List of facilities and related emissions data

E-PRTR Report covering data reported by industrial facilities covering 65 economic activities within 9 industrial sectors / List of facilities and related emissions data (Information related to actual pollutant releases)

IED Reporting obligations on IED-installations (including data on competent authorities, permit information (e.g. derogations), and baseline reports) (Article 72) / List of installations, general information, contact information, competent authorities, and permit information (Location of industrial and agricultural installations falling under IED)

IED Transitional plans covering selected pollutants from the (large) combustion plants (Article 32) (Location of combustion plants)

IED (Information related to actual pollutant releases)

Boreholes for hydraulic fracturing (locations)

Seveso III location of establishments

Location of islands and isolated settlements that are exempted from permission of dumping waste

Landfill of waste – Location of landfill of waste sites

Mining Waste / operators of extractive waste facilities / Location of facilities (including exemptions)

Use of sludge in agriculture: the quantities used, the criteria followed and any difficulties encountered / Names and addresses of the recipients of the sludge / Place where the sludge is to be used / Agricultural facilities receiving sludge

Information regarding mercury located in the Member State territories (Location of storage facilities)