Peatland Restoration in Ireland

The past 100 years in Europe and Ireland have seen degradation of wetlands, especially peatlands drained for agriculture, forestry and horticultural purposes (Connolly, 2018). In Ireland, the National Parks and Wildlife Service (NPWS), Coillte, Bord Na Móna and Irish Peatland Conservation Council (IPCC) are currently implementing the following peatland restoration measures described in detail below. Several extensive guidelines for rewetting Irish peatlands developed by National Parks and the Wildlife Service (NPWS) and Coillte and in the Mackin et al. (2017) and Pschenyckyj et al. (2021).

The Situation of Irish Peatlands

There are three major peatland types in Ireland: raised, blanket and fens. The raised peatlands can generally be found in the midlands, while blanket peatlands are generally found in the western part of Ireland. The typical peat depth of raised peatlands varies from 3-9 m, while depth of blanket peatlands vary from 0.5-7 m (O' Connell et al., 2021; Renou-Wilson et al., 2018). Similar to other Northern peatlands, Irish peatlands have developed over the millennia, and approximately occupying 20% of Ireland's land area (Pschenyckyj et al., 2021). The Irish peatlands have been subjected to drainage since the 1920s, especially for domestic peat harvesting, but this harvesting gradually translated into industrial peat extraction, planting of tress for commercial forestry and agriculture purposes (Pschenyckyj et al., 2021). Currently, only 18% of the Irish peatlands are in an undrained state, while 82% of peatlands are partially or fully drained for domestic and industrial peat extraction (Pschenyckyj et al., 2021).

Photo: With Permission of Freshwater Pearl Mussel Project (Dr. Patrick Crushell) and private landowner

1) Drain Blocking

The main purpose of drain blocking is raising the groundwater levels up to the top peat surface for reducing carbon losses to the atmosphere, runoff and subsidence. Before drain blocking is conducted, one has to identify the drain-blocking locations. These locations are identified using field surveys and aerial imagery (LIDAR) given in Mackin et al. (2017).

Drain blocking can be undertaken with dams made from peat or using plastic sheets. Where the ditch/drain depth is larger and wider, water flow may be significantly higher. In this case, a combination of plastic sheets and peat dams is required at same intervals as described below. According to NPWS, the drain blocking by plastic sheets and peat dams has proven to be effective. While they have shown to require minimal maintenance (Mackin et al., 2017) sphagnum communities were found within 10 years of drain blocking (Fernandez et al., 2014).

Identifying drain-blocking locations

The most efficient method for identifying drain-blocking locations is carrying out surface topography analysis using LIDAR. If LIDAR is not available, then traditional field survey methods are employed. When the traditional field survey methods cannot be employed then the manual method developed by the Irish peatland conservation council (IPCC) can be utilized. This method uses three sticks (each stick of 1m length) and spirit level for determining ground slope i.e. fall in the gradient (see figure above) or visit www.ipcc.ie for more information. This method involves inserting the first stick vertically on the edge of a drain/ditch and a second stick vertically on the other side of the bank. The third stick is held horizontally and levelled using a spirit level at the one-meter level at the downstream meter stick. The height difference between the two vertical sticks divided by 1m distance is the required slope.

Building dams Using plastic sheets

Another method of drain blocking is using plastic sheets. The plastic sheets inserted firmly into a drain, so that it can withhold the pressure of water accumulated on its one side. However according to Mackin et al. (2017) document, the plastic sheet should be buried 50 cm or more into the peatland. Similar to peat dams, three plastic sheets inserted into the ground for every 10 cm drop in elevation. However, one can utilize more than three plastic sheets, but it can be expensive. Where the ditch/drain depth is larger and wider, water flow may be significantly higher, in this case combination of plastic sheets and peat dams required at same intervals as described above. According to NPWS, the drain blocking by plastic sheets and peat dams has proven to be effective, having minimal maintenance (Mackin et al., 2017). According to the NPWS experience, the drain blocking approach had produced positive results with evidence of sphagnum communities found on drained peatlands within 10 years of drain blocking (Fernandez et al., 2014).

Photos: courtesy of Freshwater Pearl Mussel Project (Dr. Patrick Crushell and Mary McAndrew) and private landowner

2) Removal of Trees

Many of the Irish peatlands were planted with conifers for their economic value (Mackin et al., 2017). However, tree growth on these peatlands affected the amount of water available for sphagnum growth. In addition, the preparation for planting trees on raised peatlands included drainage, followed by fertilizer application, which significantly altered the ecohydrological conditions for Sphagnum mosses a key peat forming species (Mackin et al., 2017) lowering the water table, increasing evapotranspiration and decreasing precipitation, since some precipitation is intercepted by leaves.

Tree removal Techniques

Coillte, a commercial company managing Ireland’s forests are doing extensive work on rewetting formerly drained raised and blanket peatlands. The rewetting method employed by Coillte consists of clear-cutting commercial forestry, followed by brash removal and lastly drain-blocking using peat dams and plastic sheets. Coillte along with local organisations have restored a number of raised peatlands in Ireland, for example the Crosswood peatland (SAC), Lough Ree (SAC), Killyconny peatland (Cloghbally) (SAC), Girley peatland (NHA), Scohaboy peatland NHA and Wooddown.

The detailed procedure of clear-cutting is mentioned in Mackin et al. (2017). Essentially, trees are cut using a specialized machine which removes all branches, by cutting them into the specified lengths. However, the weight of the machine might compact the peatland surface and hinder growth of sphagnum mosses during the post-rewetting phase. To minimize this, cut branches and timber are placed underneath the machine to create a buffer, reducing the pressure on the peatland surface. The buffer i.e. the brash mat is later removed. There are other methods of tree felling such as halo thinning, ring barking, specialist track machines, chain saws or using cables and winches (Mackin et al., 2017). The selection of appropriate method depends on site characteristics such as the wetness of the surface or the number of trees.

Peatland surface prior to (left) and after (right) pine tree removal and drain blocking. Notice the difference in increased Sphagnum growth after tree removal (Photo: with permission from John Derwin, NPWS, from Mackin et al., 2017)

Watch this video from Coillte on the Raised Bog Restoration Project Ireland, including tree removal from peatland sites:

3) Marginal Bunds

Marginal bunds are constructed for accumulating pools of water (0-20 cm depth) on cutover surfaces for the establishment of peat forming vegetation. These bunds are easily designed on cutover peatlands due to their flatter topography (Mackin et al., 2017). However, one should not allow the water depth behind the bund to exceed 50 cm, since it hampers Sphagnum growth. Bunds can be constructed from local available humified peat or from another site nearby (Mackin et al., 2017). The humified peat is dried for minimizing shrinkage and reducing its collapsing potential. The water accumulates behind the marginal bunds. The level needs to be regularly monitored and kept below 50 cm maintain good conditions for Sphagnum regrowth. The NPWS successfully installed such bunds in Killyconny cutover peatland in 2008 having less than 0.3% slope. The NPWS ecologists observed significant peat forming habitats behind the marginal bunds having water depths of less than 20 cm (Mackin et al., 2017).

Construction of 1 m high peat marginal bund and development of peat forming habitats in the shallow water having depth of less than 20 cm (Photo: With permission from Fernando Fernandez, NPWS, from Mackin et al., 2017)

4) Sphagnum inoculation

The Sphagnum inoculation method was developed by Qunity and Rocherfort (2003) on Canadian peatlands. This method involves creating necessary hydrological conditions for Sphagnum regrowth i.e. first executing drain blocking on cutover peatlands and expediting the Sphagnum regrowth by inoculation of the cutover surface with live Sphagnum from donor sites. The Irish peatland conservation council (IPCC) and Bord na Mona are currently conducting field trials on formerly drained Irish peatlands. A detailed procedure can be found here.

Watch this video from the Irish Peatland Conservation Council (IPCC) demonstrating the Canadian Sphagnum moss transfer technique on Irish cutover peatlands:

5) Raised Peatland Profiling

Raised peatland excavation and reprofiling are only performed on extremely drained and degraded peatlands, not having any vegetation i.e. industrially harvested peatland sites in Ireland. This method utilizes specialized excavators and bulldozers that will create berms for retaining water on the top of the peat surface. This measure is not extensively implemented in Ireland at present, except at the Bord na Mona industrial peatland site of Mount Lucas in Co. Offaly, where Bord na Mona successfully created wetland habitats, which will gradually transform into ombrotrophic Sphagnum peatlands (Mackin et al., 2017).

6) Bunding

The goal of bunding is creating water pools i.e. necessary hydrological conditions for Sphagnum regrowth. The NPWS has implemented this method in Raheenmore peatland, Co. Offaly. The NPWS constructed large bunds with the goal for retaining water at one place and slowing flow velocity after high precipitation events. However, designing, constructing and maintaining bunds are very expensive and there is a need to perform cost benefit analysis in Ireland (Mackin et al., 2017). This method is applicable on peatlands having slopes less than 0.3%, but not applicable for peatlands having steeper slopes, as they would not retain water or create water pools (Mackin et al., 2017).

Bund constructed at a wrong place using plastic sheets/plates that did not create any water pools behind the bunds (Photo: With permission from Patrick Crushell, NPWS, from Mackin et al., 2017)

Building Dams using peat

As per NPWS raised peatland restoration manual, if the groundwater levels upon drain or ditch blocking are within 10 cm from the top peat surface, then ecohydrological conditions for sphagnum regrowth will develop within 5 years (Kelly and Schouten, 2002). The drain blocking typically involves building peat dams in drains and ditches where elevation change is more than 10 cm given in Mackin et al. (2017). The number of peat dams required for drain blocking varies from one peat site to another, however, for effective drain blocking, minimum three or maximum 10 peat dams per 100 m drain length are required (McDonagh, 1996). Peat dams can be manually built or special machine having adapted tracks for minimal peat compaction can be used. The drain blocking process involves clearing of drain, extracting peat and piling peat layers on top of each other until depth of peat dam is well above the top peat surface. The peat dam is finally covering with “scraw” of the local vegetation mentioned in Mackin et al. (2017).

Further Watching

Hen harrier project: This is a European Innovation Project (EIP-AGRI) and this video explains why the water should not be drained from the bogs. Watch on YouTube

Girley peatland Co. Meath: This peatland is conserved by local stakeholders and the Irish Peatland Conservation Council (IPCC) for its peat forming vegetation i.e. Sphagnum mosses. Watch on YouTube

Coad peatland Co. Kerry: This peatland is a nature reserve located on the Ring of Kerry and Wild Atlantic Way. Watch this video by the Irish Peatland Conservation Council (IPCC) on YouTube