A CSO Frontier Series Output- What is this?
In this chapter, we use CORINE Land Cover 2018 (CLC2018) to produce a national map of peatlands and heathlands in 2018 based on “Peat bogs” and “Moors & Heathlands” classes. We also use the land cover change dataset of CORINE Land Cover to report the change in “Peat bogs” and “Moors & Heathlands” spatial extent between 2012 and 2018 at national level.
The type of habitats included in the two CLC2018 classes are summarised in Table 2.1 below. The interpretations drawn in this chapter are only valid for the habitats included in each class. In the following text, we will use the terms Peat bogs and Moors & Heathlands to highlight the use of CLC2018 classes.
Table 2.1: Types of peatlands and heathlands included in the CORINE Land Cover 2018 (CLC2018) “Peat bogs” and “Moors & Heathlands” classes | |||
---|---|---|---|
Peatlands/Heathlands | Types of peatlands/heathlands habitats | CLC2018 “Peat bogs”1 | CLC2018 “Moors & Heathlands” |
Peatlands | Raised bogs | Yes | No |
Blanket bogs (Atlantic and Mountain) | Yes | No | |
Rich and poor fens | No | No | |
Transition mires and quaking bogs | Yes (quaking bogs only) | No | |
Heathlands | Dry heath | No | Yes |
Wet heath | No | Yes | |
Montane heath | No | Yes | |
1 This class includes areas of peat extraction. Refer to the CORINE Land Cover nomenclature guidelines. |
Peat bogs and Moors & Heathlands covered nearly 16% of the national territory in 2018. Peat bogs accounted for almost 14% of the total land cover whereas Moors & Heathlands represented nearly 2% (Table 2.2). Both land cover types were mostly found on the west coast, in the midlands and the Wicklow Mountains (Map 2.1).
Table 2.2 - Total area of Peat bogs and Moors & Heathlands in Ireland in 2012 and 2018 based on CORINE Land Cover 2012 and 2018 | ||||
no. of hectares | % | |||
Land cover type | 2012 | 2018 | 2018 | |
Peat bogs | 971,848 | 967,728 | 13.8 | |
Moors & Heathlands | 125,892 | 125,555 | 1.8 | |
Total area and proportion | 1,097,740 | 1,093,283 | 15.6 |
The estimated total spatial extent of Peat bogs and Moors & Heathlands slightly decreased between 2012 and 2018. This decline was mostly due to a reduction in the area of Peat bogs (Table 2.2). The majority of this change laid in a conversion from Peat bogs to Burnt areas (73%) and Transitional woodland/shrub (26%) (Table 2.3).
Table 2.3 - Additions and reductions in the total area of the Peat bogs and Moors & Heathlands between 2012 and 2018 based on CORINE Land Cover 2012 and 20181 | ||||||
no. of hectares | ||||||
Land cover type | Type of change between 2012 and 2018 | Burnt areas | Mineral extraction sites | Non-irrigated arable land | Transitional woodland/shrub | Total area |
Peat bogs | Additions2 | 275 | 0 | 0 | 0 | 275 |
Reductions3 | 5,525 | 65 | 20 | 1,839 | 7,449 | |
Net change | -5,250 | -65 | -20 | -1,839 | -7,174 | |
Moors & Heathlands | Additions2 | 190 | 0 | 0 | 0 | 190 |
Reductions3 | 1,632 | 0 | 2 | 55 | 1,689 | |
Net change | -1,442 | 0 | -2 | -55 | -1,499 | |
1 CORINE change dataset is at higher spatial resolution (5ha) than the standard land cover dataset (25ha). Table 2.2 | ||||||
and Table 2.3 are thus not comparable. See Background Notes for further details. | ||||||
2 Additions to extent from Burnt areas, Mineral extraction sites, Non-irrigated arable land, Transitional woodland/shrub | ||||||
3 Reductions to extent, area converted into Burnt areas, Mineral extraction sites, Non-irrigated arable land, Transitional woodland/shrub |
More than 66% of Peat bogs and Moors & Heathlands occurred in four counties in 2018: Donegal, Galway, Kerry and Mayo (Table 2.4). Almost 70% of all Peat bogs were located in these four counties, while almost 70% of all Moors & Heathlands were in Cork, Donegal, Kerry and Wicklow (Map 2.2 and Table 2.4). Although Peat bogs were found in all counties, Moors & Heathlands were not reported for five counties: Kildare, Longford, Meath, Offaly and Westmeath (Map 2.3 and Table 2.4).
To protect and conserve biodiversity, the European Union has developed two Directives aimed at designating nature conservation areas: the EU Directive on the Conservation of Habitats, Flora and Fauna (92/43/EEC) (hereafter EU Habitats Directive) and the EU Directive 2009/147/EC of the European Parliament and of the Council of 30 November 2009 on the conservation of wild birds (hereafter EU Birds Directive).
The EU Habitats Directive identifies threatened habitats and species for which special conservation measures are required through the designation of Special Areas of Conservation (SACs). Its Annex I lists these habitats, which includes peatlands and heathlands (Introduction - Table 1.1). It also establishes the Natura 2000 network comprising SACs and Special Protection Areas (SPAs) designated under the EU Birds Directive to protect the habitats of endangered and migratory species.
At national level, the Wildlife (Amendment) Act 2000 enables the statutory protection of Natural Heritage Areas (NHAs). These are areas of national importance for habitats and/or species that occur there. On a non-statutory basis, proposed NHA (pNHAs) are also part of this national network but have limited protections compared to NHAs.
Irish peatlands have been a primary target for designated SACs and NHAs areas. In 2015, the National Peatlands Strategy1 reported 53 raised bogs nominated as SACs and 75 as NHAs. For blanket bogs, 50 were designated as SACs and 73 as NHAs. In this section, we look at the spatial extent of Peat bogs and Moors & Heathlands in protected areas (i.e SACs SPAs NHAs and pNHAs) and unprotected areas.
Table 2.5 - Total area of Peat bogs and Moors & Heathlands under protected areas in 2018 | ||||||||
no. of hectares | % | |||||||
Land cover type | NHAs1 | pNHAs1 | SACs1 | SPAs1 | Total protected | Total unprotected | Total protected | |
Peat bogs | 41,289 | 313,522 | 336,773 | 121,973 | 421,585 | 546,143 | 43.6 | |
Moors & Heathlands | 2,422 | 43,092 | 55,788 | 19,587 | 63,947 | 61,608 | 50.9 | |
Total area and proportion | 43,711 | 356,614 | 392,561 | 141,560 | 485,532 | 607,751 | 44.4 | |
1 Protected areas are not exclusive from each other |
At national level, nearly half (44%) of Peat bogs and Moors & Heathlands occurred in protected areas in 2018. SACs and pNHAs were the protected areas covering the largest extent of Peat bogs and Moors & Heathlands (Table 2.5).
About 71% of all the protected Peat bogs and Moors & Heathlands were in Donegal, Galway, Kerry and Mayo (Map 2.4 and Table 2.6). Peat bogs and Moors & Heathlands located in the east of the country were more likely to be protected. The proportion of protected area of both land cover types exceeds 70% in counties Wexford, Wicklow, Monaghan, Louth, Dublin and Carlow (Map 2.5 and Table 2.6).
In the recently adopted System of Environmental Economic Accounting - Ecosystem Accounting (March 2021), ecosystem condition is defined as “the quality of an ecosystem measured in terms of its abiotic and biotic characteristics”. Abiotic features are non-living physico-chemical factors of an ecosystem (e.g. soil pH, humidity, temperature) whereas biotic features are living organisms of an ecosystem (e.g. plants, animals). The quality of an ecosystem is evaluated through its composition, structure and functions. The assessment of ecosystem condition is important in Ecosystem Accounting as it directly impacts the ecosystem's capacity to provide goods and services.
The measurement of condition involves two important steps. Firstly, key characteristics essential for the sustainability of the ecosystems need to be identified. The second step is the definition of a reference value which is compared with the current value of the ecosystem7,8. Both steps require a strong scientific knowledge of the functioning of ecosystems and their evolution over time.
Research projects on peatlands have been carried out by different organisations in Ireland, including recent ones funded by the Environmental Protection Agency (e.g., BOGLAND, QUBBES, AUGER, NEROS). These works tend to identify water (i.e. hydrological processes and physico-chemical properties), biodiversity (i.e. animal and plant species living in peatlands) and carbon stock and sink functions as important characteristics of peatlands2,9,10. Research is still ongoing and further work and discussions are needed at national level to agree on standard condition indicators along with standard baselines.
In this chapter, we report two proxy measures of condition for Peat bogs and Moors & Heathlands:
The definition of reference values as well as the link between both proxies and the ecosystem condition is challenging. Future editions of this publication will refine the measure of condition once the appropriate relevant indicators, along with their reference values, have been clarified at international and national level.
People in Ireland have a long history of cultural and economic ties with peatlands and heathlands. The extraction of peat through turf cutting has been the main source of heat for large numbers of rural households. However, human activities can disrupt the structure and functions of peatlands, notably through drainage and peat extraction. As such, land use is strongly related to the condition of peatlands and heathlands.
In this section we report the land use of Peat bogs and Moors & Heathlands based on data from Coillte, Bord na Móna, the Forest Service, the National Parks and Wildlife Service (NPWS) and the Department of Agriculture, Food and the Marine (DAFM).
Agriculture, Peat production, Forestry and Cultural related activities represented almost 80% of the total land use of Peat bogs and Moors & Heathlands in 2018 (Figure 2.1 and Table 2.7). Mainly through extensively grazed commonages areas, Agriculture was the largest land use for both land cover types with almost 70% for Peat bogs and more than 85% for Moors & Heathlands (Table 2.8).
Total area (hectares) | |
Agriculture | 71 |
Peat Production | 4.8 |
Forestry | 2.1 |
Cultural | 0.3 |
Other | 21.8 |
Table 2.8 - Land use categories for Peat bogs and Moors & Heathlands in 20181 | ||||||
no. of hectares | % | |||||
Land use type | Peat bogs | Moors & Heathlands | Total land use | Total land use | ||
Forestry2 | Broad-leaf forests | 2,016 | 196 | 2,212 | 0.2 | |
Conifer forests | 17,141 | 1,654 | 18,795 | 1.7 | ||
Mixed forests | 1,105 | 113 | 1,218 | 0.1 | ||
Felled and Windblown | 711 | 182 | 893 | 0.1 | ||
Peat production | Cutaway | 15,893 | 0 | 15,893 | 1.5 | |
Cutover | 2,026 | 0 | 2,026 | 0.2 | ||
Active peat production | 33,962 | 0 | 33,962 | 3.1 | ||
Agriculture2 | Agricultural usage | 666,922 | 109,502 | 776,424 | 71.0 | |
Cultural | Biodiversity areas and Archaeology | 3,511 | 26 | 3,537 | 0.3 | |
Other land use (includes natural peatlands and heathlands)2 | Other (including natural peatlands and heathlands) | 224,441 | 13,882 | 238,323 | 21.8 | |
Total area and proportion | 967,728 | 125,555 | 1,093,283 | 100.0 | ||
1 Based on usage data from Coillte, Bord na Móna, the Forest Service and DAFM. | ||||||
2 See Background Notes |
The second largest sector using Peat bogs, after Agriculture, was Peat production at almost 5%. Active peat production accounted for 65% of this land use type, while cutaway areas accounted for 31%. Forestry and Cultural activities represented less than 2.5% of Peat bogs land use. The majority of forestry land use on Peat bogs was coniferous forests (82%). Cultural related activities are aimed at education, research and biodiversity conservation and largely correspond to the creation of biodiversity areas (Table 2.8).
The hydrology of peatlands is one of their defining characteristics10. Disturbances in the water level can prevent peat formation and have a negative impact on biodiversity and the control of carbon emissions2,10. The spatial extent of drained peatlands thus represents a relevant proxy of condition.
Under the Arterial Drainage Act, 1945, and the Arterial Drainage (Amendment) Act, 1995, the Office of Public Works (OPW) carried out drainage and flood defence schemes to improve land for agriculture and mitigate flooding. The OPW has a statutory obligation to maintain these drainage schemes. For the same purpose, Drainage Districts schemes were carried out by the Commissioners of Public Works under different drainage and navigation acts from 1842 to the 1930s. The maintenance of Drainage Districts schemes is the responsibility of Local Authorities. For more information on both drainage schemes, refer to this link.
The OPW refers to lands drained or improved by the execution of drainage works through the Arterial Drainage and Drainage Districts schemes as benefiting lands. This section reports the spatial extent of benefiting Peat bogs.
Table 2.9 - Spatial extent of benefiting Peat bogs by land use type in 20181 | ||||||
no. of hectares | % | |||||
Land use type | Drained under Arterial Drainage schemes | Drained under Drainage Districts schemes | Drained under Arterial Drainage and Drainage Districts schemes | Total area of benefiting Peat bogs | Total area of benefiting Peat bogs | |
Agricultural | 7,506 | 1,650 | 294 | 9,450 | 1.0 | |
Peat production | 12,292 | 318 | 0 | 12,610 | 1.3 | |
Forestry | 1,396 | 252 | 71 | 1,719 | 0.2 | |
Cultural | 1,407 | 0 | 0 | 1,407 | 0.1 | |
Other land use (including natural peatlands and heathlands) | 17,903 | 2,151 | 235 | 20,289 | 2.1 | |
Total area and proportion | 40,504 | 4,371 | 600 | 45,475 | 4.7 | |
1 Based on the Arterial Drainage and Drainage Districts data from the Office of Public Works and the uses from Coillte, | ||||||
Bord na Móna, the Forest Service and DAFM |
In 2018 almost 5% of Peat bogs were benefiting lands, but no Moors & Heathlands were drained under the Arterial Drainage or Drainage Districts schemes. Almost all of the drainage work has been carried out under Arterial Drainage schemes only (Table 2.9). Counties in the midlands had the highest proportions of benefiting Peat bogs. Drainage works under these schemes affected 90% of the Peat bogs in county Meath and almost 70% in county Westmeath. There were no benefiting Peat bogs in the east coast counties (Map 2.6 and Table 2.10).
Almost half of the Peat bogs affected by Arterial Drainage and Drainage Districts schemes were also impacted by Peat production or Agriculture (Table 2.9). These Peat bogs are the most likely to be in bad condition. Less than 10% of the Peat bogs used for Forestry and 40% used for Cultural activities were altered by Arterial Drainage and Drainage Districts schemes. Under Cultural activities, these Peat bogs mostly corresponded to cutaways converted into biodiversity areas.
1. National Peatlands Strategy. (National Parks and Wildlife Service. Department of Arts, Heritage and the Gaeltacht, 2015).
2. Renou-Wilson, F. et al. BOGLAND: sustainable management of peatlands in Ireland - final report. (Environmental Protection Agency, 2011).
7. System of Environmental Economic Accounting - Experimental Ecosystem Accounting. (United Nations, 2012).
8. System of Environmental Economic Accounting - Experimental Accounting: Final draft. (United Nations, 2021).
9. Renou-Wilson, F. et al. Restored Peatlands/Organic Soils for Climate and Biodiversity Benefits (NEROS). (Environmental Protection Agency, 2018)
10. Renou-Wilson, F., Wilson, D., and Müller, C. Chapter 3.10. In BOGLAND: sustainable management of peatlands in Ireland - end of project reports. (Environmental Protection Agency, 2011).
Go to the next chapter: Spatial Extent and Condition based on Article 17 - EU Habitats Directive data
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