Waste generation and treatment (env_wasgt)

National Reference Metadata in ESS Standard for Quality Reports Structure (ESQRS)

Compiling agency: Central Statistics Office (CSO) – waste generation (non-EPA licenced facilities) Key responsibilities:Collection and processing of data on waste generated by non-EPA licensed enterprises and by quarries not reporting to EPA; estimation of waste generation for whole population of enterprises from sample data returns and EPA licensed enterprise data (including quarries reporting to EPA), contribution to quality report, transfer of datasets and quality report to Eurostat via EDAMIS.   Environmental Protection Agency (EPA) – waste generation (EPA licenced facilities, NACE A, waste treatment facility waste, household waste) and waste treatment Key responsibilities:Collection and processing of waste treatment and waste treatment facility data; collection and processing of waste generation by EPA licensed enterprises (Industrial Emissions Directive (IED)/Integrated Pollution Control (IPC) licences) and a number of non-EPA licensed quarries; estimation of NACE A sector waste (model), estimations of generation of secondary waste; collation of household waste generation data including an estimation of unmanaged household waste; preparation of waste treatment data table (Table 2), waste treatment facility data table (Table 3) and of part of the quality report.


Eurostat metadata
Reference metadata
1. Contact
2. Statistical presentation
3. Statistical processing
4. Quality management
5. Relevance
6. Accuracy and reliability
7. Timeliness and punctuality
8. Coherence and comparability
9. Accessibility and clarity
10. Cost and Burden
11. Confidentiality
12. Comment
Related Metadata
Annexes (including footnotes)
 



For any question on data and metadata, please contact: Eurostat user support

Download


1. Contact Top
1.1. Contact organisation

Central Statistics Office (CSO) – waste generation (non-EPA licenced facilities)

Key responsibilities:
Collection and processing of data on waste generated by non-EPA licensed enterprises and by quarries not reporting to EPA; estimation of waste generation for whole population of enterprises from sample data returns and EPA licensed enterprise data (including quarries reporting to EPA), contribution to quality report, transfer of datasets and quality report to Eurostat via EDAMIS.

 

Environmental Protection Agency (EPA) – waste generation (EPA licenced facilities, NACE A, waste treatment facility waste, household waste) and waste treatment

Key responsibilities:
Collection and processing of waste treatment and waste treatment facility data; collection and processing of waste generation by EPA licensed enterprises (Industrial Emissions Directive (IED)/Integrated Pollution Control (IPC) licences) and a number of non-EPA licensed quarries; estimation of NACE A sector waste (model), estimations of generation of secondary waste; collation of household waste generation data including an estimation of unmanaged household waste; preparation of waste treatment data table (Table 2), waste treatment facility data table (Table 3) and of part of the quality report.

1.2. Contact organisation unit

CSO
Environment and Climate Division

EPA
Waste Statistics Team

1.5. Contact mail address

CSO
Linh Nolan – Ardee Road, Rathmines, Dublin 6, D06FX52, Ireland

EPA
Deirdre French – Environmental Protection Agency, Johnstown Castle Estate, Churchtown, Wexford, Y35W821, Ireland


2. Statistical presentation Top
2.1. Data description

Generation:
The data is collected and collated in accordance with the Regulation on waste statistics (EC) No. 2150/2002, amended by Commission Regulation (EU) No. 849/2010.  Details of the data sources for waste generation are included in Section 3.1.  The information on waste generation has a breakdown by source (based on NACE classification and household activities) and by waste categories (according to the European Waste Classification (EWC) for statistical purposes).  All values are provided in tonnes.

Treatment:
The data is collected and collated in accordance with the Regulation on waste statistics (EC) No. 2150/2002, amended by Commission Regulation (EU) No. 849/2010.  Details of the data sources for waste treatment are included in Section 3.1.  The information on waste treatment is broken down to five treatment types (recovery, incineration with energy recovery, other incineration, disposal on land and land treatment) and by waste categories. All values are provided in tonnes.

2.2. Classification system

As per regulation, three data tables are provided:

Table 1. Waste Generation: The waste generation dataset is classified by the European Waste Classification (EWC Stat) categories and sources are defined by the NACE Rev.2 categorisation. 

Table 2. Waste Treatment: The waste treatment dataset is classified by the European Waste Classification (EWC Stat) categories and treatment operations are as defined in Directive 2008/98/EC.

Table 3. Waste Treatment Facilities: The waste treatment facilities dataset is classified by the number of facilities, capacity, the treatment operations (as defined in Directive 2008/98/EC) and the NUTS 2 regions.

2.3. Coverage - sector

Generation: Waste generated by all economic activities (NACE Codes) and households.

Treatment: Waste treatment includes data for final treatment only.

2.4. Statistical concepts and definitions

As defined by Regulation on Waste Statistics (EC) No. 2150/2002, amended by Commission Regulation (EU) No. 849/2010.

2.5. Statistical unit

A. Waste generation:

  1) CSO Waste Generation Survey data: enterprises

  2) EPA data: licensed enterprises under the Industrial Emissions Directive (IED) and Integrated Pollution Control (IPC) Licensing, quarries, households

 

B. Waste treatment data: treatment facilities

 

C. The units used for reporting are as follows:

  1. Weight reported in tonnes
  2. Waste economic sector origin reported by NACE code
  3. Waste classification origin reported in European Waste Classification (EWC Stat)
  4. Waste treatment location reported in NUTS2 (IE04, IE05 or IE06)
2.6. Statistical population

Generation: The statistical population was all waste generated in the Republic of Ireland.

Treatment: The statistical population was all waste finally treated in the Republic of Ireland.

2.7. Reference area

Generation: The reference area for the waste generation dataset is the Republic of Ireland.

Treatment: The reference area for the waste treatment dataset is the Republic of Ireland which is broken down into the NUTS regions (IE04, IE05 and IE06) for the waste treatment capacity and waste treatment facilities numbers data.

2.8. Coverage - Time

Reference year: 2020

2.9. Base period

Not applicable.


3. Statistical processing Top
3.1. Source data

Generation:

Table 1 data was collated from a number of sources, as described below:

  • Data returns from the CSO Waste Generation Survey for non-EPA licensed enterprises.
  • Data reported through Environmental Performance Reporting (EPR – see Additional Notes below) by EPA licensed enterprises and a number of quarries: in 2020, all EPA licensed enterprises, whether they were obligated under PRTR or not, reported waste data via the EPA EPR system. In addition to EPA licensed enterprises, the EPR system was also used to collect waste information on quarries obligated under PRTR. Thus for the purposes of this quality report, the term ‘EPA licensed enterprises‘ includes the PRTR obligated quarries.
  • Waste collection and facility permit annual data reported to the National Waste Collection Permit Office (NWCPO).
  • NACE 37 sewage sludge data from urban wastewater treatment regulation reporting.
  • Household data: Waste collection permit annual data reported to NWCPO; data from EPA waste statistics survey of local authorities, provide information on household waste brought to waste infrastructure such as civic amenity sites, bring banks and Pay to Use (PTU) compactors; data from producer responsibility initiative compliance schemes provide information on household WEEE and portable batteries brought for treatment; data from Authorised Treatment Facilities (ATF) estimate End-of-Life Vehicles (ELV) arising from households.
  • Data models estimate information on NACE A. For these models data was used from the following organisations/sources:
    • EPA
    • CSO
    • Teagasc
    • Farmplastics.ie
    • UK Agricultural Supply Trade Association
    • Nix Farm pocketbook 2006
    • Department for Environment, Food & Rural Affairs, UK
    • Driver & Vehicle Licensing Agency, UK
    • Department of Transport
    • Department of Agriculture, Food and the Marine
    • Veterinary Medicines Department and Irish Medicines Board
    • RPS Consultants
    • SHAWG.org.uk
    • Pig Progress.net
    • Scottish Government
    • AEA.uk.com
    • Department for Environment, Food and Rural Affairs Department of Agriculture, Environment and Rural Affairs (Northern Ireland)
    • Welsh Government, Knowledge and Analytical Services
    • The Scottish Government, Rural and Environment Science and Analytical Services

 

Treatment:

The main data sources used in compiling the information presented in Tables 2 and 3 are:

• EPR
• Waste collection and facility permit annual data reported to NWCPO.
• Administrative data on urban wastewater treatment sludges, provided to EPA by Irish Water.
• Enterprise surveys (biennial survey for the purpose of Waste Statistics Regulation reporting):
   o IED/IPC-licensees (large scale industrial activities) – PRTR/EPR returns (administrative data);
   o Sample survey of non-EPA licensed companies carried out by CSO.

The number and types of facilities to be reported in Table 3 are estimated by pin-pointing the facilities that carry out final recovery and disposal in IE in the waste treatment surveys carried out by EPA waste statistics, in information submitted by the local authorities to EPA waste statistics and urban wastewater treatment reporting, in EPR and NWCPO data, and in the CSO Waste Generation Survey information.

 

Additional Notes:

CSO carried out a sample survey of non-EPA licensed enterprises under the Statistics (Waste Generation) Order 2021 (S.I. No. 661 of 2021) to collect waste generation data in relation to Regulation (EC) No 2150/2002. Information from this survey is supplemented with information on waste generation obtained from EPA licensees which are further described below.

The Environmental Protection Agency (EPA) publishes national statistics on waste generation and management in IE under the Ireland’s Circular Economy Programme. The reports and data releases provide information on municipal waste, hazardous waste and specific waste streams (e.g. packaging waste, waste electrical and electronic equipment, end-of-life vehicles and waste tyres).  The national waste data collection is carried out in such a way as to ensure that the waste data gathered can be used for Waste Statistics Regulation reporting and as a data source to meet other EU waste reporting obligations.

Each year, the EPA surveys local authorities, the National Waste Collection Permit Office (NWCPO), licensed and permitted waste recovery and disposal operators (including some IED/IPC activities where waste treatment takes place onsite) and producer compliance schemes, to gather data on waste generation and treatment in IE, and on imports and exports of waste.   National Waste Reports and waste data releases are available for download at https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/.

To obtain waste generation data by economic sectors for the Waste Statistics Regulation, data from EPA licensed IED/IPC installations (submitted under condition of licence) and data from non-licensed activities (Waste Generation Survey carried out by CSO) are compiled every second year.

A four-tier system of authorisation has been established for the regulation of waste recovery and disposal activities in IE. A waste recovery or disposal activity at a facility is either:

  • an exempted activity (no authorisation required),
  • requires a waste (or IED/IPC) licence,
  • requires a waste facility permit, or
  • requires a waste certificate of registration/registration certificate.

Collectors of waste are required to have a waste collection permit, as prescribed under the Waste Management (Collection Permit) Regulations 2007 (as amended).

If the waste disposal or recovery activity is set out in the Third and Fourth Schedules to the Waste Management Acts 1996 as amended, a waste licence is required. If the activities on site meet the descriptions set out in the First Schedule to the Environmental Protection Agency Act 1992 as amended or IED Directive, an IED/IPC licence is needed.

Depending on the authorisation required, activities are controlled either by the EPA or by local authorities. There are currently 31 local authorities in IE. All non-exempted local authority waste facility activities are regulated by the EPA.

Where the EPA seeks waste data from local authorities, or from activities permitted by local authorities, the data are sought under the following legislation:

  • Section 32 of the Waste Management (Collection Permit) Regulations 2007, as amended.
  • Section 24 of the Waste Management (Facility Permit and Registration) Regulations 2007, as amended.
  • Section 6 (4) of the Waste Management (Shipments of Waste) Regulations 2007.
  • Urban Wastewater Treatment Regulations, 2001 (SI 254 of 2001), as amended.

EPA licensed activities are required under condition of the licence to submit an Annual Environmental Report (AER) and, where applicable, a return under the Pollutant Release and Transfer Register (PRTR), both of which include waste management records.  A new system has been developed in the EPA called the Environmental Performance Reporting (EPR) online application.  The EPR webform collects the data needed to fulfil the reporting requirements, including your statutory obligations, for:  

  • Pollutant Release and Transfer Register (PRTR) 
  • Large Combustion Plant Directive (LCP) 
  • Annual Environmental Reporting under licence/permit
  • Waste statistics
The EPA’s waste statistics team also surveys waste operators where data required for legislative reporting are not currently provided under EPR reporting systems.
3.2. Frequency of data collection

Generation and Treatment: Data are collected on a biennial basis for Waste Statistic Reporting.

3.3. Data collection

GENERATION:

Non-domestic sector: enterprises in NACE Rev 2 Sectors B-U (non-EPA licensed facilities)

CSO Waste Generation Survey:
A sample survey was conducted by the CSO to provide waste generation data of enterprises in NACE sectors not captured in EPA administrative data. In selecting the sample, CSO identified and excluded enterprises that provided administrative data to EPA in the CSO business register. Consequently, a sample was drawn from a population which covered enterprises in NACE Rev 2 sectors B – U and which had 3 or more employees. The sample size was 5929 enterprises. Of this amount, there were approximately 2372 unique returns. However, not all of these returns were included in the final analysis for waste generation once they were combined with data from the EPA and reviewed for quality. This survey is conducted biennially for the purpose of collecting data for the Waste Statistics Regulation.

 

NACE A - Agriculture, Fisheries and Forestry

Models were used to determine the waste generation for NACE A (1-3), as follows:

Agriculture

The quantities of non-natural wastes arising from agriculture are not specifically captured as part of the reporting for national waste statistics. To estimate the waste generated for this sector, the EPA decided to use three approaches:

  1. Information on the quantity and type of farm hazardous waste collected as part of the FHW collection campaign that operated in nine collection centres across IE in 2017; which was used to derive national estimates of the quantities and types of farm hazardous waste generated.
  2. Information and expert knowledge from national agencies/departments were used to assess the quantity of waste generated from the placement of products on the market (e.g. CSO, farm plastics, veterinary medicines etc.); and
  3. The waste model developed by the EA (England and Wales), SEPA, and NIEA for wastes which were not collected during the pilot farm hazardous waste scheme, or where no information exists on a national basis to derive waste estimates by applying relevant per unit waste ratios to Irish data.

 

Waste estimates based on Pilot Farm Hazardous Waste Collection Scheme

The Farm Hazardous Waste (FHW) collection campaign was a collaborative project led by the EPA working with a cross-government team that includes Teagasc, DAFM, Department of Communications, Climate Action and Environment (DCCAE) and local authorities and supported by the Irish Farmers Association (IFA), Bord Bia, hazardous waste contractors, local livestock marts, agri-businesses and rural development groups at nine centres across IE.

The aims of the FHW collection campaign were:

  1. to facilitate the collection, recovery and disposal of hazardous wastes from farms in accordance with national and European waste legislation;
  2. to quantify and characterise farm hazardous waste (including de-registered pesticides); and
  3. to research the need for a national farm hazardous waste collection scheme. 

A total of 1,975 farmers used the bring centres and deposited 136 tonnes of farm hazardous waste and over 67 tonnes of WEEE. The analyses of waste type per farm type generally reflect farming operations for a specific farm type e.g. dairy, beef, sheep, tillage and mixed farming. The FHW collection campaign was partially funded by the state (46%) with the remainder (54%) paid by farmers who were issued with certificates of disposal.

The information on the type and quantity of wastes gathered during this collection was used to estimate the quantities of these wastes generated on an annual basis per waste type. From the 2017 FHW collection campaign an average weight per waste type per farm was calculated and was then multiplied by the number of farms in the country, i.e. 137,500. As the waste collected represents legacy and current waste generated, an assumption was made that the quantity per farm represents approximately five years of waste.

 

Waste estimates based on information of products placed on the market

Information on product placed on the market was used to estimate the amounts of agricultural waste plastic and used sheep dip. Information on the quantities of farm plastic waste was provided by the Irish Farm Film Producers Group (IFFPG). This estimate was based on quantities of farm plastic placed on the market and tonnages of waste plastic collected under the farm plastic collection and recycling service. The Veterinary Medicines Department of the Irish Medicines Board (IMB) provided estimates of the quantity of spent sheep dip generated per year. The calculation is based on the quantity of sheep dip placed on the market averaged over a four-year period. Dilution and uptake factors were then applied to estimate the quantity of spent sheep dip generated in 2020.

 

Waste estimates based on U.K. Waste Model

The Agricultural Waste Estimates Model used by the EA (England and Wales), the SEPA, and NIEA has been developed in the U.K. over several years by Marcus Hodges Environment and BDB Associates to provide estimates of waste quantities arising in the agricultural sector. Initially created on behalf of the Environment Agency in 1998, the model was subsequently developed, modified and extended as part of a research project funded by Biffaward under the Landfill Tax Credit Scheme. The model has been used in the U.K to assist the U.K. Government, the EA and other agricultural bodies to estimate wastes arising and to develop national regulations and strategies to manage this waste stream.

The U.K. model was developed by an extensive consultation and literature review. It comprises calculation methodologies for 41 wastes and by-products. Each of these methodologies was established using MS Excel and derives a ‘unit waste estimate’ for a specific waste stream. This value links the quantity of a specific waste or by-product generated each year to a single agricultural unit (eg the quantity of agrochemical packaging per hectare, or the quantity of milk waste per dairy head). The unit weight estimates were generated by using a combination of a mass balance approach and a bottom-up farm practice approach. To generate estimates for specific areas, such as regions or counties, the unit waste estimates are linked to the appropriate agricultural and horticultural census data for the specified year.

The EPA used this model to estimate the quantities of agrochemical packaging, animal feed bags (paper), seed bags (paper), animal health packaging, CFCs gases and containers, machinery waste, milk waste and waste tyres generated in 2020. Some minor modifications were made to the model to better reflect the farming practices in IE. Applying this model to IE, however it was assumed that crop and livestock farming practices in the U.K. are broadly similar to farming practices carried out in IE. Amendments to the model were based on local knowledge and consultations with various individuals and technical organisation’s. Numerous other sources of information available in IE were investigated and used, where appropriate, in deriving estimates for these wastes. Figures for national herd numbers and hectares of different crops grown in IE were obtained from the CSO Crop and Livestock survey 2020 as this is the most comprehensive and most recent information available in this sector. The categories of livestock and crop types did not exactly match the U.K.'s definition in some cases and where this occurred, a "best fit" match was made.

 

Livestock Mortality & Stillborn Waste

For 2020, the EPA provided a waste estimate for mortality and stillborn mortality waste for cattle, pigs and sheep. The waste estimate was based on deriving the mortality rate for cattle, sheep and pigs from the overall population and assigning average weights per animal to provide a livestock mortality waste figure.

The following information sources were utilized to determine the mortality rates among mature and newborn sheep cattle & pigs as well as the average weights per animal: DAFM, Animal Identification Movement (AIM) Bovine Statistics report, Teagasc Calf nutrition, Irish sheep breeding current status and future plans, Teagasc animal nutrition, Teagasc Calf weight targets, Teagasc Pig herd performance report, Sheep health and welfare report and Teagasc Irish sheep breeding.

The CSO Crop and livestock survey provided number of total number of cattle, pigs and sheep to which the relevant mortality rates were applied and average weight per animal.

 

Fisheries

Similar to the agriculture sector, information on wastes generated by the fishing industry is not specifically captured as part of EPA national waste statistics. To provide an estimate of the quantities and types of non-natural wastes generated by the fishing sector, the EPA decided to use elements of the model developed by the SEPA for this sector. Applying this model to IE, the EPA assumed that fishing practices in Scotland are broadly similar to fishing practices in IE.

The main waste streams generated by fishing operations and captured as part of this work are:

  1. Waste oil and domestic waste generated by the national sea fishing fleet;
  2. Fish waste (mortalities) from salt water fish farms; and
  3. Fish waste (mortalities) from freshwater fish farms.

Estimates of non-natural wastes generated by the sea water fishing fleet are based on a small sample of fishing vessels where wastes were collected. These data were then scaled up to the national fleet of vessels in work that was undertaken by the Sea Fisheries Protection Authority (SFPA).

The estimate does not take into account other causal factors that may affect waste generation such as vessel type or the length of fishing trips. Therefore, the degree of confidence in the waste estimate is low. To get more accurate information, a more extensive and comprehensive survey would be required. The SFPA derived unit weight estimates for waste oils and domestic waste generated per tonne of fish landed from a limited survey that was carried out.

In relation to fish waste (mortalities) from both salt and fresh water fish farms, the unit weight estimates derived for the SEPA model were applied to the annual production figures for farmed fish supplied by BIM, the Irish Sea Fisheries Board. No information on the types and quantities of other wastes generated (such as nets, plastic fish boxes, packaging, waste oils) by the fish farming sector was available from BIM.

 

Forestry

As with the agriculture and fisheries sectors, the types and quantities of non-natural wastes generated by the forestry sector is not specifically captured as part of EPA national waste statistics data collection. To overcome this and provide an estimate of the quantities and types of non-natural wastes generated by this sector, the EPA used the model provided by SEPA.

In applying the forestry commission estimate of waste generated per hectare it was assumed that the forestry waste generated in the U.K. is similar in amounts generated and in its composition. The composition of the waste generated in the U.K. is below:

  1. Used oils;
  2. Chemical deposits and residues;
  3. Metallic wastes;
  4. Paper and cardboard waste;
  5. Plastic waste;
  6. Batteries;
  7. Mixed waste (non-hazardous)

The waste types and quantities used in the SEPA model are based on estimates provided by the U.K. Forestry Commission for 2006. The IE Forest Service does not compile data on the quantity of non-natural wastes generated by this economic sector. The quantities and types of waste generated were used to derive a unit weight estimate per hectare of forestry. The U.K. unit waste estimate and proportion per waste type was applied to the 2017 national figure for forestry in IE, supplied by the Forest Service of the DAFM. The Forest Service of the DAFM compiles the National Forest Inventory at five year intervals, the most recent of which is 2017.

The model does did not take account of other potential causal factors that may affect waste generation such as extent of forestry mechanisation, composition of tree types etc.

 

NACE B - Extractive waste generation

EPR is the main source for information on the generation of extractive waste.

The main waste types/categories of extractive waste reported are tailings. The EPA has very limited data on inert waste (overburden, waste rock) and no reported quantities on the generation of clean soil. Very often the licensee may use waste rock/soil as a by-product or use it for engineering purposes on site. At the mining sites, waste rock is generally crushed/ screened on site for use as construction fill.

Excavated topsoil used on site (e.g. used in screening bunds during operation and replaced during restoration) is not considered to be waste and thus not reported.

The EPA has waste data for mine tailings (‘ponds’) for each of the EPA licensed mining sites and other extractive waste facilities. Only tailings disposed of over ground are reported. Tailings sent back underground for engineering purposes in roof support are now classed not as a waste as this is used as engineering material (European Court of Justice Case C-114/01, judgement Sept 2003). Please note that identifying the material is difficult using the administrative data sources available to us.

Please note that EPA datasets excludes some non-hazardous mining residues which were previously reported as wastes but are now considered a resource, subsequent to a 2003 ruling by the European Court of Justice; these materials comprised of surplus rock stored on-site prior to being used off-site as an engineering material, and non-hazardous tailings used as engineered backfill in the mine construction process.

The question of a material being considered a waste or not has an impact on waste data reporting. Each quarry has to be looked at on a case by case basis. It is not so much a case of what material is considered a waste or not a waste but more what is the operator going to do with material. Is overburden e.g. used for landscaping, acoustic berms, engineering works on site? There may be a need for end-of-waste or by-products decisions.

The EPA currently has very limited data for the smaller facilities which are neither EPA licensed nor permitted by local authorities (i.e. quarrying works solely handling inert extractive waste). We also do not have records for the smaller peat extracting sites <50 ha (as these fall below IPC licensing thresholds).

The allocation of mining waste to NACE section B or C is generally not an issue as the EPA can report by NACE and this is specific for each facility.

 

NACE 37

Information on sewage sludges generated by NACE 37 was obtained from data supplied to the EPA by Irish Water in accordance with the Irish Urban Wastewater Treatment Regulations, 2001 (SI 254 of 2001), as amended.  Irish Water is the utility that looks after all public waste and drinking water treatment in IE.

 

NACE sectors 38 and 46.77

Information from EPA waste statistics EPR returns and NWCPO waste facility permit annual returns was used to estimate waste generation by NACE sectors 38 and 46.77. 

Following Eurostat guidance from previous years (by email), 46.77 facilities were distinguished from NACE 38 facilities by identifying whether or not the main business of the facility arose from dismantling and selling parts for reuse.

EPA returns were investigated to estimate the amount of secondary waste arising at waste treatment facilities, and they provided information on consumption residues from waste treatment facilities. CSO scaled primary waste data provided by EPA for NACE 38 facilities up to national level.

The manual on waste statistics explains that treatment residues are to be reported as secondary waste if the treatment resulted in a considerable change of the chemical and/or physical structure of the waste. Table five on page 19 of the draft revised manual (March 2022) on waste statistics lists repackaging and temporary storage as the waste treatment operations that do not change the physical or chemical nature of waste. Therefore, the waste treatment operations not listed are assumed to give rise to secondary waste. This is in line with recommendations concerning the use of European LoW chapter 19 entries.

To estimate secondary waste, the EPA waste statistics datasets were therefore used to identify chapter 19 10 XX and 19 12 XX LoW entries.  Calculations were completed to determine the amount of 19 10 XX and 19 12 XX waste generated at the facilities.  It was noted that C&D mineral residues may fall into W128_13, so they were pulled out and reported under W121 (Mineral Wastes from C&D).  It is planned to refine the secondary waste data accuracy for the next reporting round by looking at waste flows in more detail.

The tonnages sent offsite were corrected for:

  • material that entered the facility as segregated waste and was added to a chapter 19 entry waste stream without treatment; and
  • for chapter 19 entry material that was accepted onsite from another waste facility, not treated at the facility under investigation, and pooled with treated material for transfer offsite.

Metal shredder output was counted as secondary waste if it was sent offsite for further treatment. However, once it reached end-of-waste at the shredding facility, it was counted as recycled. Further refinement of the ELV data will be completed for the next reporting round.

 

Waste Generation by Households

Household waste generation in the economy is based on data reported by waste collection permit holders (kerbside collections), on WEEE and battery compliance scheme data, on EPA waste statistics surveys of local authorities and on the CSO Quarterly National Household Survey (QNHS). 

Household waste generation data reported for 2020 reference year is the sum of:

(i)      Household kerbside collections of mixed residual, mixed dry recyclables, organics and segregated glass waste;

(ii)    Waste brought by householders to authorised infrastructure such as bring banks, civic amenity sites, PTU compactors;

(iii)  Waste portable batteries and WEEE collected by producer responsibility initiative compliance schemes as provided for under national regulations;

(iv)  Occasional local authority collections for specific household generated waste streams such as Christmas trees, hazardous wastes, bulky wastes and local authority housing clear-outs;

(v)    Bulky waste (skip) collections from households;

(vi)  Estimate of ELVs brought to ATFs by householders; and

(vii) Estimate of unmanaged household waste (as described under the section Annual survey returns for EPA waste statistics and NWCPO above).

Data for (i) and (v) are collated from annual environmental returns by permitted waste collectors (private sector and local authority) collected by NWCPO. Data for (ii) to (iv) are collated from the annual EPA waste statistics survey of local authorities, landfills and from WEEE and battery compliance schemes. Data for (vi) are from waste permit annual records collected by NWCPO. Data for (vii) are estimated by EPA based on data from waste collection permit holders, local authorities and CSO QNHS.

 

TREATMENT:

Each year, the EPA requests waste data for the previous calendar year from local authorities and waste licensed and permitted facilities.

EPR requires respondents to report using LoW entries and waste descriptions. Treatment operations (recovery and disposal) are classified by Waste Statistics Regulation recovery and disposal codes. LoW entries are converted to EWC-Stat classifications for purposes of Waste Statistics Regulation reporting. Facilities are asked to submit details of wastes accepted, stored, finally treated on site, and sent off site for treatment for the calendar year. The survey respondents are asked to split the waste accepted into waste from IE and waste from abroad. They are also asked to provide percentages of packaging and municipal waste for all entries of waste accepted; percentages of packaging, municipal and construction and demolition waste for entries of waste finally treated onsite and sent offsite; and offsite destinations (IE and abroad) for all waste transfers. Facility operators are required to provide offsite recycling and recovery percentages for waste transfers abroad.

Each return is validated. Queries arising on the return, and the close out actions taken, are recorded. No data verification visits were carried out to due to the Covid 19 pandemic restrictions. As waste management practices and regulation have continued to evolve and mature, the EPA’s experience is that the availability and quality of waste management information has improved since the first IE national waste report in 1995.

 

Identification of relevant treatment facilities

The EPA has developed a contacts list of waste activities for national reporting purposes. Most EPA licensed waste facilities and a selection of local authority permitted waste facilities are included. These facilities are asked to provide waste data on top of their annual environmental reporting obligations (administrative data). Each year our contacts list is revised based on knowledge gained during the previous national waste statistics data collection (e.g. new recycling/recovery facilities and new waste streams of national interest). Waste information from the majority of permitted waste facilities and a small number of EPA facilities are taken from their annual environmental report through the NWCPO or ERP online systems.

 

Data collection on treated quantities

The vast majority of facilities that carry out final treatment of waste also carry out pre-treatment and transfers of other waste streams. IE waste treatment facilities can therefore not be neatly split into final treatment and pre-treatment/transfer facilities. The EPA identifies the type of treatment carried out (final or pre-treatment or transfer) for each waste stream at facility level and reports accordingly.

Waste undergoing final treatment in IE was summarised for set two Waste Statistics Regulation reporting. The EPA counted material where it was disposed of or backfilled, where energy was recovered from it, or where it entered a production process or was designated as end-of-waste. This rationale was applied most of the time. However, there were ambiguities and exceptions, which are listed below:

  1. Material such as e.g. shredded wood is at times passed on to private persons or farms before an official end-of-waste designation has taken place. In theory the material leaves the facility and the waste treatment network as waste and is then recovered at many private locations, which do not have waste authorisations. This material was counted as recovered in IE at the last waste facility.
  2. Some recovered waste oil is passed on to specific users, which are outside the waste industry. This recovered waste oil is counted as recovered (energy recovery) at the waste treatment facility.
  3. In accordance with the recycling definition given in Article 3 of the Waste Framework Directive, we classified material (mainly wood and oil) recovered at a waste facility and used as a fuel offsite, as energy recovered rather than recycled.
  4. Parts for reuse from ELV dismantling were not counted as waste despite the fact that they enter the treatment facility as part of an ELV, and therefore as waste. As the ELV Directive does not consider parts for reuse as waste, they are, at present, left out of the IE waste estimates. This decision will be reviewed if necessary.
  5. Metal shredder output that reached end-of-waste at the shredding facility was counted as recycled. Note that the EPA only counted the material that actually reached end-of-waste at the facility as recycled. The same rationale was applied to the treatment of glass waste at waste treatment facilities.
  6. In case of composting facilities, the material accepted specifically for composting was counted as recycled. In accordance with Eurostat guidance and to make the information comparable to other countries, the total amount of material accepted for composting was counted as recycled. Please note that this leads to double counting of compost screenings. These are removed from composted/to be composted material and sent to landfill. They are therefore first counted as recycled at composters and then counted as disposed of or backfilled at landfills.
  7. Sludges that were generated and transferred to designated spreadlands by a permitted waste contractor were counted as recycled (rather than omitted and designated as internally recycled).
  8. For landfill leachate, only leachate that went to waste facilities for final treatment was counted in the waste treatment data.  Any leachate that went to a waste water treatment plant (or to a waste facility and then onto a wastewater treatment plant) was not counted in the data, as per the guidance manual.
  9. The majority of textiles, wood and paper are exported for treatment.

 

Data collection on number and capacity of treatment facilities

The number and types of facilities to be reported in dataset three are estimated by pin-pointing the facilities that carry out final recovery and disposal in IE in the waste treatment surveys carried out by EPA waste statistics, in information submitted by the local authorities to EPA waste statistics and urban wastewater treatment reporting, in PRTR/EPR and NWCPO data, and in the CSO sample survey information.

There were several difficulties in doing this and they are listed below.

  1. Material such as e.g. shredded wood is at times passed on to private persons or farms before an official end-of-waste designation has taken place. In theory, the material leaves the facility and the waste treatment network as waste and is then recovered at many private locations, which do not have waste authorisations. As the number of private offsite destinations is unknown, the last waste treatment facility was counted as the recovery facility.

    Similar situations arose for recovered waste soil, shredded, crumbed waste tyres and treated waste oil and a comparable approach was taken.  EPA Waste Statistics team takes part in an ongoing discussion on how best to deal with waste facilities transferring material that is still waste to offsite destinations other than waste companies.
  1. A similar situation also occurred with treated sludges from urban wastewater or industrial facilities, that were transferred to forestry or agricultural land for recovery. In the absence of indications of the number of farms or forestry enterprises used for sludge recovery, no spreadlands were reported in the number of treatment facilities.
  2. For WEEE, it was calculated that there were 75 companies that were taking back WEEE and preparing it for re-use.  These companies would not be considered waste facilities as they do not have waste authorisations.  For the purpose of reporting, the 75 companies were reported as one facility.

Please note that facilities that carried out several categories of final treatment operations listed in dataset three (e.g. backfilling and recycling), are counted under each relevant category.

For waste capacity data, there is no finalised national database of capacities at waste treatment facilities in IE.  A desk-top study commenced in 2022 which aims to extract capacity information from electronically available EPA licences and waste facility permits from NWCPO’s permit register.  A working group is currently working on this register.

 

3.4. Data validation

CSO Waste Generation Survey Data

Survey returns were checked to ensure response data was read in correctly through SAS processing programs and visual inspection.

• Survey returns were checked for missing waste codes (i.e. amount and description of waste indicated in return but no waste code information). For missing codes, where possible, the most appropriate code was identified based on waste description and then inserted into the source survey returns file.

• Data that appeared incorrect (e.g. too high) were compared with data from previous surveys if available and/or to similar types (e.g. enterprise in same NACE and similar employee figures) and adjusted accordingly. For some of these situations, returns were also checked for the correct reporting unit (tonnes instead of kilograms or litres).

 

EPA Data

Desktop validation of EPR returns was carried out by the EPA’s PRTR team, the EPA waste statistics team and the CSO environment team.  Furthermore, the NWCPO data is validated by Local Authority staff and the EPA.  

As detailed in section 6.3 below, the following validation exercises were completed:

  • Desktop validation of EPR returns was carried out by the EPA’s PRTR team, the EPA waste statistics team and the CSO environment team.  Any inconsistencies and coding errors (e.g. type of treatment, quantities, LoW entries) were corrected. 
  • Data for each waste class were interrogated to identify unlikely tonnages reported. These tonnages were queried and either confirmed or corrected.
  • Data on local authority permitted waste facilities were validated by regional and local authorities and by EPA waste statistics.
  • Data is compared with previous years at both return level and aggregate level.
  • The NACE codes for the waste generation by enterprises were taken from EPR or CSO business register. Only the main NACE code was considered for each enterprise.
  • LoW entries were used in EPR/NWCPO return, and these entries were converted to EWC-Stat classifications. Coding errors detected during validation of the surveys were corrected.
  • The data on waste household kerbside collections and bulky (skip) waste collections were gathered by NWCPO and validated by regional and local authorities and EPA waste statistics. The EPA validated the local authority survey data regarding waste accepted at civic amenity sites, bring banks and PTU compactors when received.
  • No data verification site visits were carried out due to the Covid-19 pandemic
3.5. Data compilation

Generation:

To obtain national waste generation, data from the CSO Waste Generation Survey and EPA licenced facilities were combined. The returns were then weighted to the CSO Business Register. Non-responses were corrected though higher weighting factors. The EPA also provided waste generation data for NACE A, 38, 46.77 and Households. (See section 3.3)

For reporting, the waste generation data LoW codes were converted into the EWC Stat 2 codes.  The waste quantities were then reported under the relevant NACE codes. Where particular EWC Stat 2 codes required conversion to dry weight, this was completed during the compilation stage.

 

Treatment:

Once the data was collected (as per section 3.3), the waste treatment data LoW codes were converted into the EWC Stat 2 codes.  The waste quantities were then reported under the relevant recovery or disposal codes.  For the facility and capacity data, each facility was assigned its relevant NUTS 2 code and were required the capacity quantities were also assigned for reporting under the NUTS 2 code.

 

3.6. Adjustment

No adjustments were made to the data other than the conversions of sludges to dry weight as required under the Regulation.  Where a dry weight was provided by a facility the dry weight was reported, otherwise conversions were applied as per the Regulation.


4. Quality management Top
4.1. Quality assurance

CSO

The CSO avails of an office wide Quality Management Framework (QMF). This framework allows all CSO processes and outputs to meet the required standard as set out in the European Statistics Code of Practice (ESCOP). The QMF foundations are based on establishing the UNECE’s Generic Statistical Business Process Model (GSBPM) as the operating statistical production model to achieve a standardised approach to Quality Management. All and any changes implemented to CSO processes and outputs require adherence to the QMF.

Where possible, enterprise information (e.g. NACE, employee numbers) were cross-checked between EPA returns data and the Business Register.

Aggregated waste tonnage figures were also compared with data from NWCPO.

Various data checks were performed throughout all stages of the data collection and analysis process.

 

EPA

Across all data flows, the EPA has a strong commitment to data quality in all teams and a strong ethos of applying rigorous validation and verification to data to ensure accuracy. In 2018, the EPA established a small data analytics team to champion the use of data science, spatial analysis, earth observation and data visualisation techniques, working in close collaboration with EPA subject matter experts.

Extending from and ongoing memorandum of understanding (MOU) with the CSO, the EPA secured a seconded statistician post in 2019, expanding its capacity for systematic data quality management.  This position has facilitated increased co-ordination between both organisations, including representation at the Formal Statistical Liaison Group, access to data quality management training provided by the CSO and the European Statistical Training Programme, and engagement with the National Data Infrastructure champions group.

Furthermore, the EPA took part in a Eurostat Peer Review in 2022.  Positive feedback was received from Eurostat on this Peer Review and a link to the report can be found in Section 4.2.

Therefore, as an Agency, the EPA is rigorous in data validation but it is evident that this is impacting on other dimensions of data quality such as cost effectiveness and timeliness. It is challenging to evidence decisions underpinning trade-offs across dimensions of data quality in the absence of systematic approaches to measuring the quality of statistical processes and products. In addition, data quality management is particularly challenging when dependent on data from external organisations where the Agency has limited input on the processes producing these data and therefore requires the carrying out of additional secondary validation and cross-checking by the EPA to ensure data quality. In 2021 the EPA Waste Statistics Team established an EPA-led network of public bodies involved in waste data collection, processing and reporting to address shortcomings and inefficiencies in the current regime in a coordinated way and drive improvements in the accuracy, timeliness and relevance of waste data. At the institutional level, the Agency would benefit from establishing a panel of data owners who will work together to advance data governance, a data management framework and data quality policies and processes within the organisation.

4.2. Quality management - assessment

 EPA

In 2022, the EPA received certification with the Irish Statistical System Code of Practice (ISSCoP) and the European Statistical Code of Practice (ES CoP) for reporting on the Joint OECD Eurostat Municipal Waste Indicator.

The results of the 2022 Eurostat Peer Review can be found at: https://www.cso.ie/en/media/csoie/aboutus-new/legislationgovernancedatapolicies/externalgovernance/europeanstatisticalsystem/Peer_Review_report_Ireland_2022.pdf


5. Relevance Top
5.1. Relevance - User Needs

CSO

The Waste Generation Survey was carried out to fulfil Regulation (EC) No 2150/2002 of the European Parliament and of the Council of 25 November 2002 on waste statistics.

The survey will also be useful in providing data on food waste. Beginning in mid-2022, EU Member States are required to report data on food waste generated as according to methodologies and formats indicated in:

(a) Commission Delegated Decision (EU) 2019/1597 of 3 May 2019 supplementing Directive 2008/98/EC of the European Parliament and of the Council and;

(b) Commission Implementing Decision (EU) 2019/2000 of 28 November 2019 laying down a format for reporting of data on food waste and for submission of the quality check report in accordance with Directive 2008/98/EC of the European Parliament and of the Council.

 

EPA

It is a strategic priority for the EPA to ensure that our data and information outputs are timely, relevant and accessible to our stakeholders. The EPA’s Strategic Plan 2022-2026 includes a deliverable for 2026 that ‘We will be using innovative and accessible ways to deliver timely and targeted data and information to meet’. This deliverable is reflected in and integrated throughout the EPA’s annual work programme which is aligned with the EPA’s Strategic Plan.

Specifically, with regards to delivering on the priority needs of our stakeholders in the waste sector, the annual work programme sets out clear tasks and key performance indicators for the Waste Statistics Team directly linked to the EPA’s strategic goals and outcomes; these include a commitment to fulfil all statutory EU reporting requirements and to deliver strong, effective and timely communication of waste data and associated evidence-based messages through a range of channels. Internal and external user needs are routinely taken into account by EPA management when developing the annual work programme and the accompanying communications plan for the year. This is reflected in decisions around the content of waste data releases and communication channels used. Examples of concerted user-focused commitments in the 2022 Work Programme include the publication of the national waste statistics summary report and the provision of more timely waste indicator data for national policy planning and evaluation purposes. The EPA’s longstanding active engagement in a wide range of national steering committees, working groups and industry fora serve to provide EPA managers with a good understanding and appreciation of the emerging needs of our stakeholders, while the newly-established EPA-led network of waste data authorities will provide a dedicated forum for two-way communication and obtaining feedback on the relevance and value of the EPA’s existing waste statistics outputs and evolving needs and priorities. The overarching goal of the network is to enhance the timeliness and relevance of national waste data outputs. Priority needs at national level are defined and documented in the Oversight and Performance Delivery Agreement between the EPA and DECC and in turn reflected in the EPA Work Programme.

The Waste Statistics Team carried out extensive stakeholder consultation during the period 2015- 2017, to help inform the original development of the EPA Waste Statistics website. A survey was carried out in 2015 to seek stakeholder feedback on the format, structure and content of EPA waste data publications and the mode of data releases. Stakeholders included in the survey were Eurostat, Department of Environment, Climate and Communications (DECC), other teams in the EPA, National Waste Collectors Permit Office (NWCPO), National Transfrontier Shipment Office (NTFSO), Waste Enforcement Regional Lead Authorities, Local Authorities, Non-Governmental Organisations, Consultants, Researchers, and the general public

In 2016/2017 the Waste Statistics Team met with key stakeholders, including DECC, the Irish Waste Management Association, the Regional Waste Management Planning Offices, the Waste Enforcement Regional Lead Authorities, the NWCPO and RPS Consulting, as well as EPA staff from various offices working in the waste area. The EPA Board of Directors also provided feedback on the content and structure of waste data releases.

To address this feedback, the Waste Statistics Team developed an approach centred on a “live” Electronic Waste Report at: https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/. The landing page presents waste sector-specific links that provide the latest available data and interpretive text updated on a periodic basis and time-stamped. This includes ‘First Look’ data from administrative data sources or subsets of EPA waste statistics data that, due to reduced scope, can be validated more quickly than fully processed survey data produced to meet legislative requirements. Web traffic to these pages is routinely monitored via Google Analytics and monthly reports are made available by the Communications Unit.

In addition, in direct response to feedback received from policy makers and industry stakeholders, in September 2020 the Waste Statistics Team publishs the National Waste Statistics Summary Reports on an annual basis.  These are annual synthesis reports focused on drawing together the data and key messages from the multiple web data releases. The publication of these reports are accompanied by a press release highlighting the key findings.

Resources have also been allocated to developing other synthesis outputs including infographics, factsheets and videos to capture key policy-relevant trends and effectively communicate relevant messages to policy-makers and a wider audience. All outputs are published on the Publication section of the EPA’s National Waste Statistics web resource, making them easily and freely accessible.

The Waste Statistics Team has also made significant strides in recent years to make greater use of digital and social media to meet the needs of a wider audience. In addition to our traditional press releases, our waste data releases are now routinely accompanied by a series of tailored social media messages and 2-3 minute videos on the EPA’s Twitter, Instagram and LinkedIn accounts with relevant stakeholders tagged in maximise reach.

The ‘Contact Us’ section of the EPA website contains a query form that allows website users to submit queries and provide feedback, including feedback on the new EPA website. Following on from the redevelopment of the EPA website, external assessments are planned to assess overall user satisfaction and accessibility.

In terms of delivering on the priority needs of our stakeholders in the waste sector, these needs are integrated into the EPA’s annual work programme which is aligned with the EPA’s Strategic Plan and in particular the strategic 2026 deliverable ‘We will be using innovative and accessible ways to deliver timely and targeted data and information to meet’. The annual work programme sets out clear tasks and key performance indicators for the Waste Statistics Team linked to the EPA’s strategic goals and outcomes; these include a commitment to fulfil all statutory EU reporting requirements and to deliver strong, effective and timely communication of waste data and associated evidence-based messages through a range of channels. The EPA’s active engagement in a wide range of national steering committees, working groups and industry for a, as well as regular one-to-one meetings with DECC, provides the Waste Statistics Team with a good understanding and appreciation of the evolving needs of our stakeholders. External user needs are actively taken into account by EPA management when developing the annual work programme and the accompanying communications plan for the year.  This is reflected in decisions around the content of waste data releases and the annual waste summary report and the respective communication channels used. Examples of concerted user-focused commitments in the 2022 Work Programme include the publication of the National Waste Statistics Summary Report and the provision of more timely waste indicator data for national policy planning and evaluation purposes. Priority needs at national level are defined and documented in the Oversight and Performance Delivery Agreement between the EPA and DECC and in turn reflected in the EPA Work Programme.

5.2. Relevance - User Satisfaction

No official user satisfaction survey was conducted. However Eurostat is regularly in contact with any queries or feedback.

For EPA, as previously stated the Waste Statistics team is continuously seeking and addressing feedback from data users. Furthermore, the Waste Statistics Team is continuously adapting its data collection and processing, specifically for Waste Statistics Regulation. The EPA waste statistics team is also aware of differences between legislative reporting obligations such as not including C&D waste or ELVs in municipal household waste but counting them as household waste generated for Waste Statistics Regulation.

5.3. Completeness

The data tables submitted to Eurostat were fully completed.

5.3.1. Data completeness - rate

The data tables submitted to Eurostat were fully completed.


6. Accuracy and reliability Top
6.1. Accuracy - overall

Generation:

As indicated in section 3.5, the CSO Waste Generation Survey was a sample survey which included 5929 enterprises. The response rate was approximately 40%. To obtain national waste generation for the non-domestic sector, responses from the survey were combined with EPA licensed facilities data and then weighted to the CSO Business Register. There is a possibility that national data may not be complete due to respondents not reporting all waste items in their returns. Completeness may also be a risk if the responses received are not representative of the non-domestic sector at national level. The CSO attempted to minimize this risk by assigning weighting factors accordingly.

The drinking water sludge data included in the waste generation data is incomplete. It is planned to improve the reporting of drinking water sludges generation by engaging with Irish Water further to obtain drinking water sludge data.

 

Treatment:

For data on sludges from NACE 36, only a proportion of the drinking water treatment sludges generated were transferred to the waste treatment network.

Also, for CSO enterprise data for 2020 was not included. Further, analysis will be carried out on this data before the 2022 reporting to confirm its accuracy.

The Waste Statistics Team has an almost complete coverage of final waste treatment in Ireland (census information).

 

Additional notes:

The EPA Waste Statistics Team is strongly committed to presenting an accurate picture of national waste generation and treatment in Ireland. By using appropriate methodologies in combination with rigorous validation processes, the reported data are as close as possible to the real values.

Most EPA data included reported in the Waste Statistics Regulation tables arise from EPA-licenced and Local Authority-permitted waste facilities data and surveys of Local Authorities themselves.

In line with CSO Quality Standards and Guidelines for data collection and processing, internal consistency checks are conducted through reference with previous reported periods and external consistency checks are based collectors’ data from the NWCPO.

In addition, for EPR returns, the Waste Statistics team responds to licensed operators’ queries sent to a dedicated email or received via phone and provides ongoing advice and assistance to operators in completing the return. The team persistently follows up with non-respondents until a completed survey is received, involving the relevant EPA Enforcement Inspectors for non-responding facilities where appropriate. On the rare occasions when companies fail to respond, the Waste Statistics Team either carries out a site visit and obtains the required data on-site (which didn’t happen for 2020 data due to the Covid 19 pandemic) or alternatively uses data from external sources to approximate the non-respondent facility’s waste activities.

 

6.2. Sampling error

For the CSO Waste Generation Survey:
• A sampling plan was used which intended to capture data representative of national data (see section 6.3.1)
• In generating the sample, enterprises which reported high volumes of waste in WGS 2018 were included to ensure capture of this data.
• Efforts were made to maximise responses from enterprises by way of multiple reminders and finding alternate contact information where original contact information was incorrect or no longer active.

No sample surveys were carried out for waste generation by NACE A, 37, 38 and 46.77, for waste generation by households, and for waste treatment. Sampling errors were therefore not assessed for waste generation or treatment by these NACE Rev 2 sectors.

6.2.1. Sampling error - indicators

To be reviewed.

6.3. Non-sampling error

See sections 6.3.1-6.3.5.

6.3.1. Coverage error

Generation:

CSO

For the CSO Waste Generation Survey, to minimise coverage error, the following sampling design was used:

 • Sampling frame used was the business register

• Seven strata were used to select the sample from the frame. The strata were based on number of employees.

• Additionally, enterprises from the 2020 WGS with high volumes of waste were included in the sample.

 

EPA

Household waste: Most waste operators use customer registers to identify waste from households. The amount of commercial waste contained in the household waste reported is therefore likely to be negligible. However, it has been our experience that household waste arising from apartment blocks may wrongly be classified as commercial waste by the waste operators due to the size of the bins collected and/or their ‘customer’ being a property management company rather than the individual apartment dwellers. Efforts are being made to improve this aspect of reporting year on year, which will impact on reporting of quantity of household waste collected and percentage coverage of the collection service.

By-products: Article 27 of the European Communities (Waste Directive) Regulations, 2011 allows an economic operator to decide, under certain circumstances, that a material is a by-product and not a waste. Decisions made by economic operators under article 27 in IE, must be notified to the EPA. After consultation with the economic operator and the relevant local authority, the EPA may determine whether or not the notified material is waste.

In 2020, the EPA received by-product notifications for 3,217,523 tonnes of soil and stone material. Notifications for 155,200 tonnes were withdrawn. The EPA determined that 1,374,575 tonnes of the soil and stone notified were by-product and that 73,000 were waste. The estimated quantity of soil and stone material notified in 2020 for which no determination was made to date, amounted to 1,614,748 tonnes.

 It is important to note that by-product notifications do not necessarily mean that the material was generated or indeed moved. Economic operators may not have proceeded with the activities related to the by-product notifications.

However, if they did proceed, the materials would not have entered the waste management network. This means that the tonnages involved are not included in the 2020 waste statistics data.

 

Treatment:

The EPA waste statistics team receives EPR data from facilities authorised to treat waste most licensed and some permitted waste activities. Data from facilities that are not surveyed by EPA waste statistics are taken from annual returns (ARs).

Please note that facilities that carried out several categories of final treatment operations listed in dataset three (e.g. backfilling and recycling), are counted under each relevant category.

The Waste Statistics Team has an almost complete coverage of final waste treatment in Ireland (census information).

6.3.1.1. Over-coverage - rate

Generation:
Not calculated - to be reviewed.

Treatment:
To ensure there is no double counting, final treatment is only counted at the final step of the waste treatment process.  Also, when using multiple data sources, the Waste Statistics Team cross checks the data sources to ensure there is no overlap in data and deducts any quantities that are already reported.

 

6.3.1.2. Common units - proportion

To be reviewed.

6.3.2. Measurement error

Survey returns were received for the waste generated by enterprises dataset (CSO Waste Generation Survey and EPR).  A questionnaire and administrative data for the waste generated by households dataset (NWCPO, EPR and EPA waste statistics local authority surveys).  Waste treatment was mainly based on administrative data.

CSO

For the CSO Waste Generation Survey, to minimize measurement errors, a survey booklet with definitions and instructions were provided along with a helpdesk telephone number and email address. The CSO received many queries regarding identification of waste codes and estimating weights of waste generated.

 

EPA

In the EPA waste statistics returns, facility operators are asked to give the methods used to quantify the tonnages reported (i.e. weighbridge, estimate or other). Most waste facilities have a weighbridge, and generally waste in storage is estimated. The operators with weighbridges use weighbridge software reports to extract the data needed for the EPA waste statistics return. An automated mass balance is included in the waste treatment surveys and >5% difference between inputs and outputs (having consideration of waste in storage) are queried.

Each waste stream accepted at a facility is given an ID number. For each waste stream finally treated or transferred offsite, the ID number(s) of the waste accepted entries contributing to the finally treated or sent offsite entry is/are quoted. This allows the EPA waste statistics team to follow the flows of waste through each waste facility and determine whether or not the picture painted is plausible.

As in other years, any inconsistencies and suspect tonnages were queried with the waste treatment operators (e.g. appears to be kg instead of tonnes). Tonnages treated were compared with the previous year’s return. Each significant increase/decrease was queried with the operator to see if there was a genuine reason for the difference or if it was a measurement error. Some of the waste transfers are cross-checked (if company x reported sending waste to company y, does company y report on that waste?) to ensure measurement errors are minimised. However, the fact that there are often several movements of waste from the point of collection to the point of final treatment has the potential to introduce measurement errors (e.g. residual waste collected at kerbside is brought to a waste transfer station for bulking or baling, and then to a landfill for disposal or to another facility for further processing).

6.3.3. Non response error
Generation:
See sections 6.3.3.1 and 6.3.3.2 

Treatment:
The Waste Statistics Team has an almost complete coverage of final waste treatment in Ireland (census information). The data provided for waste treatment should be regarded as accurately reflective of the waste treatment in IE.

 
6.3.3.1. Unit non-response - rate

Generation:
For the 2020 CSO Waste Generation Survey, the response rate was approximately 40%. Possible reasons for non-responses include:
(a) Failed email addresses for enterprise and therefore the survey never reached the enterprise
(b) Company had ceased trading
(c) Company encountered difficulties in providing the data or refused to respond

Unit non-responses were accounted for in the weighting process.

Treatment:
N/A

6.3.3.2. Item non-response - rate

Generation
For the 2020 CSO Waste Generation Survey, it is probable that not every waste item was reported by each enterprise. Aggregated tonnage figures at waste item level were compared to previous surveys.

Treatment
N/A

6.3.4. Processing error

Returns were received for the waste generated by enterprises dataset (CSO Waste Generation Survey, EPR and NWCPO data), for the waste generated by households dataset (EPR and NWCPO) and for the waste treatment dataset.

For the CSO Waste Generation Survey, the following measures were taken:
(a) Data capture errors: prior to the launch of the survey, testing was performed to ensure that data were accurately recorded through the eForm system. After survey launch, the returns data file was regularly read into data analysis programs as well as visually inspected to ensure data was being captured correctly.
(b) Data editing: comparisons were made with previous years’ data and checked for consistency; high or odd figures were extracted for closer review; duplicate responses were also checked for and removed during the processing phase.

 

The majority of EPA data is captured in two online reporting systems (EPR and NWCPO). The data from these systems is exported into excel files for final use.

Desktop validation of EPR returns was carried out by the EPA’s PRTR team, the EPA waste statistics team and the CSO environment team. No data verification site visits were carried out due to the Covid-19 pandemic.

Data for each waste class were interrogated to identify unlikely tonnages reported. These tonnages were queried and either confirmed or corrected.

Data on local authority permitted waste facilities were validated by regional and local authorities and by EPA waste statistics.

The NACE codes for the waste generation by enterprises were taken from EPR or CSO business register. Only the main NACE code was considered for each enterprise.

LoW entries were used in EPR/NWCPO return, and these entries were converted to EWC-Stat classifications. Coding errors detected during validation of the surveys were corrected.

The data on waste household kerbside collections and bulky (skip) waste collections were gathered by NWCPO and validated by regional and local authorities and EPA waste statistics. The EPA validated the local authority survey data regarding waste accepted at civic amenity sites, bring banks and PTU compactors when received.

6.3.4.1. Imputation - rate

Generation:
Not calculated – to be reviewed.

Treatment:
N/A

6.3.5. Model assumption error

6.3.5. Model assumption error

Generation:

Models were used to estimate waste generation by NACE A. The models derive an estimate of non-natural waste generated for each unit (or area) of production. As previously stated, the waste models were developed by the EA (England and Wales), SEPA, and NIEA for:
1. Wastes which were not collected during the pilot farm hazardous waste scheme, or
2. Wastes where no information exists on a national basis to derive waste estimates by applying relevant per unit waste ratios to Irish data.


The model assumptions and methodologies are summarised below:
• Farm plastics by polymer type: Irish Farm Film Producers Group (IFFPG) research and farm plastics collection and recycling service
• Agrochemical packaging, animal feed bags and Animal health products packaging: U.K. model unit weight estimate applied to CSO Crop and Livestock Survey 2020 (Non calendar year-reported June to June.)
• Batteries: Used information gathered from the FHW Collection campaign 2017 & used FHW Collection campaign (2014) to apportion battery waste from WEEE waste (29%) as batteries were not recorded specifically reported outside of WEEE and then applied to CSO Farm Structure Survey 2016
• CFC’s: Used information gathered from the FHW Collection campaign applied to CSO Farm Structure Survey 2020 and U.K. model unit weight estimates for CFC containing equipment applied to CSO Crop and Livestock Survey 2018 (Non calendar year-reported June to June).
• Machinery Waste: U.K. model assumption, i.e., new sales = wastage+ exports. Applied to new tractor sales given in Irish Bulletin of Vehicle and Driver Statistics Bulletin, 2019.
• Milk waste: U.K. model unit weight waste estimated applied to CSO 2020 dairy cow numbers and 2007 Farm Structure Survey replacement rates.
• Waste oil: Used information gathered from the Irish FHW collection campaign and CSO Farm Structure survey 2016 to derive national estimates of wastes generated.
• Seed bags: U.K. model unit weight estimate used and applied to CSO Crop & Livestock survey 2020 (Non calendar year- reported June to June). Used relevant national expert advice to determine reseeding rates for grassland.
• Sheep dip: Used average quantity of sheep dip product placed on markets from 2009-12 and applied dilution and uptake factors to derive spent sheep dip.
• Tyres: U.K. model unit weight waste estimate used and applied to tractor numbers registered in 2019 and to scrapped tractor numbers estimated from new sales.
• Oil filters, paint, varnish, adhesive wastes, veterinary medicine wastes, corrosives, and pesticides: Used information gathered from the Irish FHW collection campaign and CSO Farm Structure survey 2016 to derive national estimates of wastes generated.
• Aerosol cans used for animal health: Used information gathered from the Irish FHW collection campaign 2014 (last year aerosols were reported as a waste line item) to provide approximate proportion of Aerosols within farmer’s waste before being applied to CSO Farm Structure survey 2018 to derive national estimates of wastes generated.
• Cattle, Pig and Sheep Mortality: Used information from multiple sources highlighted above to ascertain sheep mortality rate among the general population and applied average weight per animal to estimate waste

However, no quantitative error calculations or sensitivity analyses were carried out.

 

Treatment: No models were used in generating the waste treatment data.

 

6.4. Seasonal adjustment

Not applicable.

6.5. Data revision - policy
As per Eurostat policy.
 
Additionally, the EPAs Revision & Dissemination Policy for Official European Waste Statistics was published in November 2021 and is available on the EPA website at: https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/about-our-waste-statistics/revision--dissemination-policy/.  It includes the EPA Quality Statement for Official European Waste Statistics, which can also be found at:  https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/about-our-waste-statistics/quality-statement/  
 
6.6. Data revision - practice

All data submitted to Eurostat is intended to be final data. Where errors are later identified in the data Eurostat will be notified and updates of the data will be submitted via eDAMIS.

6.6.1. Data revision - average size

Not applicable.


7. Timeliness and punctuality Top
7.1. Timeliness

Target delivery to Eurostat is within 18 months after the end of the reference period.

7.1.1. Time lag - first result

Not applicable.

7.1.2. Time lag - final result

Not applicable.

7.2. Punctuality

Generation: The Waste Generation data was submitted to Eurostat in September 2022.

Treatment: The Waste Treatment data was submitted to Eurostat in October 2022.

The Quality report was submitted to Eurostat in December 2022.

The delay in reporting was due to a number of factors including other limited resources, new staff, covid illnesses and other unforeseen circumstances. Measures have been put in place to avoid any delays in future reporting.

7.2.1. Punctuality - delivery and publication

Generation: The waste generation data was submitted 2.5 months after the deadline.

Treatment: The waste treatment data was submitted almost 4 months after the deadline.


8. Coherence and comparability Top
8.1. Comparability - geographical

Generation:  Waste generation data is produced on a national level.

Treatment: Waste treatment data is produced on a national level for the overall treatment quantities. Waste facility numbers and capacity data are reported at a NUTS 2 level.

The data reported to Eurostat in the Waste Statistics Regulation draws on the same pool of data used in national reporting. Data from other EU member states are published on the Eurostat website and can be used for comparison. However methodologies are likely to differ between countries.

8.1.1. Asymmetry for mirror flow statistics - coefficient

To be reviewed.

8.2. Comparability - over time

All data are cross-checked with previous years at micro and aggregate level. Any method changes are included in the relevant quality reports.

Generation:
The amount of waste generated in Ireland increased by approximately 2.2 million tonnes from 2018 (13,986,757 tonnes) to 2020 (16,192,033 tonnes).

Note that there was a large increase in waste generation for NACE F. This was due primarily to two large enterprises that showed an increase in their waste generation for 2020 (as reported in the CSO Waste Generation Survey). Additionally, figures for 2018 may have been underestimated for this sector. The CSO will continue to look further into this and make amendments if required.

Treatment:
All data are cross-checked with previous years at micro and aggregate level. Any method changes are included in the relevant quality reports.The amount of waste treated in Ireland increased by 1.82 million tonnes from 2018 (12,260,094 tonnes) to 2020 (14,082,676).

8.2.1. Length of comparable time series

Waste Statistics Regulation data for Ireland are available on the Eurostat website for years dating back to 2004. In general, the data are comparable with previous years. Any changes to the data (collection, compilation, refinement) would be explained in the relevant quality reports.

Note that in 2012, the responsibility of the waste generation survey of Irish businesses was transferred from the EPA to the CSO.

Waste treatment data remains the responsibility of the EPA.

 

8.3. Coherence - cross domain

The data reported to Eurostat in the Waste Statistics Regulation draws on the same pool of data used in national reporting on waste. Therefore the data is to a high degree reflective of waste statistics produced in IE for other statistical reporting regimes for the same time period.

Additionally, the use of statistical units and the NACE classification of economic activities makes the waste domain coherent with economic statistics. This allows the computation of indicators based on economic variables. 

However, for the Regulation waste is reported by EWC Stat code, therefore, the waste data is reported in a more general material-oriented nomenclature.  All other waste reporting is reported by the source and material-based List of Waste (LoW) code classification system.

Furthermore, there are a number of differences in what should be included under specific waste definitions between the Waste Statistics Regulation and the Waste Framework Directive (WFD).  For example, ELVs are not considered household waste for WFD but are for Waste Statistics Regulation.  Also, the animal by-products sent for animal feed are not considered a waste under WFD but are still reportable under Waste Statistics Regulation. These differences should be taken into account when comparing data sets across domains.

8.4. Coherence - sub annual and annual statistics

Not applicable.

8.5. Coherence - National Accounts

To be reviewed.

8.6. Coherence - internal

Generation and Treatment

The waste generation data is to a high degree internally coherent (totals are equal to the sum of the breakdowns). Additionally, the Eurostat file for provision of data ensured that totals were equivalent to the sum of the individual components.


9. Accessibility and clarity Top
9.1. Dissemination format - News release

Not applicable.

9.2. Dissemination format - Publications

Results in relation to the Waste Statistics Regulation are published on the Eurostat waste statistics webpage: https://ec.europa.eu/eurostat/statistics-explained/index.php?title=Waste_statistics

The EPA also publishes waste statistics for IE on the following website:
https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/

 
9.3. Dissemination format - online database

Eurostat waste statistics database:
https://ec.europa.eu/eurostat/web/waste/data/database

The EPA also publishes waste statistics for IE on the following website:
https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/

9.3.1. Data tables - consultations

Not applicable.

9.4. Dissemination format - microdata access

Not applicable.

9.5. Dissemination format - other

Not applicable.

9.6. Documentation on methodology

A Quality Report is submitted to Eurostat as required. This report contains information on methodology.

Additionally the Manual for the Implementation of Regulation (EC) No 2150/2002 on Waste Statistics (Draft March 2022) was consulted on an ongoing basis during the data validation, compilation and reporting process.
(Eurostat waste statistics manual: https://ec.europa.eu/eurostat/web/products-manuals-and-guidelines/-/KS-RA-13-015)

The EPA is also currently in the process of refining its internal procedure for the gathering and compilation of data for the Waste Statistics Regulation to ensure even further accuracy and consistency when reporting the data. The EPA is also in the process of documenting an internal Waste Statistics Regulation standard operating procedure (SOP) and process maps to assist with future reporting.

9.7. Quality management - documentation

A Quality Report is submitted to Eurostat as required. This report contains information on quality management.

The EPA is also in the process of documenting an internal Waste Statistics Regulation standard operating procedure (SOP) and process maps to assist with future reporting.

9.7.1. Metadata completeness - rate

Not calculated - to be reviewed.

9.7.2. Metadata - consultations

To be reviewed.


10. Cost and Burden Top

Generation:

A query was included in the CSO Waste Generation Survey requesting respondents to indicate the time required to complete the survey. Based on responses to this query, the average completion time was approximately 37 minutes. However note that this does not include the time taken to gather information but rather to complete the survey form itself. The actual time to gather information for the survey and complete it online is likely much longer. To assist respondents, dedicated staff was available to manage a telephone helpline and email inbox specifically set up for the survey. A manual was also provided. Many respondents contacted the CSO by both telephone and email with queries. The most frequent queries related to identifying waste codes and estimating weights of waste generated.

 

Treatment:

As previously stated, one of the main administrative sources of data for waste treatment is from EPR. Through EPR, respondents provide data in relation to licence compliance, PRTR etc, (i.e. not just data for the purposes of Wasta Statistic Regulation). Therefore, it is not possible to specifically identify the burden for Waste Statistics Regulation reporting.

To support respondents to complete the administrative data the following measures have been put in place:
• A telephone helpline was provided for the respondents to all surveys;
• Guidance manuals were provided online where possible;
• A new EPR system was developed which integrates a number of compulsory surveys that would have previously been required to be completed separately and in addition their Annual Environmental Return requirements; and
• Improvements were made to the NWCPO portal, which now integrates surveys such as the Authorised Treatment Facility (ATF) survey.


11. Confidentiality Top
11.1. Confidentiality - policy

CSO

All information supplied to the CSO is treated as strictly confidential in accordance with Section 33 of the Statistics Act, 1993, and will be used for statistical purposes only. Aggregate data will be made available to Eurostat to meet the requirements of Regulation (EC) No. 2150/2002.

We will retain the survey data indefinitely as one of the purposes of the data collection is to obtain longitudinal information on waste generation by Irish businesses.

 

EPA

The EPA has a confidentiality statement in place for the use of Official European Waste Statistics, which was published on 10th November 2021. The confidentiality statement can be found on the EPA website at the following page: https://www.epa.ie/our-services/monitoring--assessment/waste/national-waste-statistics/about-our-waste-statistics/confidentiality-statement/

 

11.2. Confidentiality - data treatment

CSO

Individual company data are held confidentially. Repondents were also provided with a link to the Data Protection Transparency Notice (https://www.cso.ie/en/methods/tn/wastegenerationsurvey/) when completing the survey. Reporting of data is aggregated to national level by EWC-Stat code for waste items and NACE Rev 2 for economic activities. See also section 11.1.

 

EPA

The majority of waste data collected by the EPA for European and national reporting purposes are not collected primarily or exclusively for waste statistics purposes but under licence compliance and other European reporting purposes such as the Pollutant Release and Transfer Register (PRTR) Regulations 2007 and 2011.

Where specific subsets of EPA licensee data or waste data from other third-parties are collected and used solely for statistical reporting purposes, the EPA Waste Statistics Team applies strict statistical confidentiality provisions to these data. Results are published in aggregated form and measures are taken to ensure that details relating to an identifiable person or enterprise are not inadvertently divulged.

Individual company information is only reported if it relates to data that are already publicly available (e.g. for EPA licensed companies, summary waste management information in the AER is publicly available on EPA website, as required by condition of the licence).


12. Comment Top

None.


Related metadata Top


Annexes Top