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Data extracted in September 2022
Note to the reader: This general fiche summarises the environmental and climate impacts of PEATLAND MANAGEMENT found in a systematic review of 4 synthesis research papers[1]. These papers were selected from an initial number of 471 obtained through a systematic literature search strategy, according to the inclusion criteria reported in section 4.
As each synthesis research paper involves a number of primary research papers - ranging from 8 to 93 -, the assessment of impacts relies on a large number of results obtained mainly in field experiments (carried out in situations close to real farming environment), and sometimes in lab experiments or from model simulations.
1. DESCRIPTION OF THE FARMING PRACTICE
Description | · A peatland is a type of wetland with a naturally accumulated layer of peat at the surface due to organic matter production exceeding decomposition[2]. Peatlands are generally classified as bogs and fens. Bogs are fed mainly by rain and snow, while fens develop in landscape depressions and are fed with surface and/or ground water. Other names referring to peatlands found in this review are swamp, and wet heath, though the search string included more synonyms (see section 4). Carbon-rich soils are included in this definition. These soils have and organic layer usually with >15 % of organic matter. However, the synthesis papers included in this review do not clearly define what they consider carbon-rich soils and thus we rely on authors’ knowledge and criteria to include individual studies in their reviews. · This review focuses on peatlands under agricultural use and thus, and though not clearly stated on the papers reviewed, includes mostly drained peatlands. · This review includes interventions towards an improved and more sustainable management of peatlands. Specific interventions have been proposed such as low tillage, ban of burning, paludiculture, etc[3]. In this literature review we have found evidence for the following management interventions: o No fertilisation. Fertilisers are natural or synthetic substances containing chemical elements such as nitrogen (N), phosphorus (P) and potassium (K) that are applied to soils to improve growth and productiveness of plants[4]. Fertilisation, and in particular N inputs in wetlands, might promote greenhouse gas emissions by changing element cycling[5]. Here, no fertilised peatlands are compared to fertilised ones. o Grazing is a method of animal husbandry in which livestock are allowed to feed outdoors consuming wild vegetation. The direction and magnitude of grazing impacts on ecosystem properties depends on grazing management such as stocking density, grazing duration and grazer species[6]. Here, grazed peatlands (comprising different management intensities and levels of drainage) are compared to mowed peatlands. o No burning. Burning is a routinely vegetation management practice conducted in some in some areas with the objective of stimulating the growth of grasses, maintaining these areas in young productive successional stages and increasing heterogeneity at the landscape scale and thus, supporting biodiversity[7]. However, peatland burning releases carbon to the atmosphere and banning this practice has been suggested as a measure to reduce GHG emissions. o Low intensity farming comprises a wide variety of farming practices analysed together and that refer mainly to the maintenance of permanent and extensive grasslands and fallowing in peatlands, including extensive livestock grazing, mowing and the lack of fertiliser inputs[8]. |
Key descriptors | · These fiches focus on peatlands and the management practices conducted in these ecosystems. However, some of these farming practices are also explored more broadly without distinguishing the habitat type devoted to agricultural use in other sets of fiches (i.e, organic fertilisation and grazing fiches). · This review does not include peatland conservation or restoration, which are assessed in separate sets of fiches (i.e., peatland conservation and restoration). |
2. DESCRIPTION OF THE IMPACTS OF THE FARMING PRACTICE ON ENVIRONMENT AND CLIMATE
We reviewed the impacts on peatlands of different management practices, namely, the banning of fertilisation, banning of burning, grazing, and low intensity farming (interventions) compared, respectively, to fertilised, burned, mowed and high intensity farmed (in this case, intensively grazed) peatlands as (comparators) (Table 1).
The table below shows the number of synthesis papers reporting positive, negative or no effect, based on the statistical comparison of the intervention and the control. In addition, we include, if any, the number of systematic reviews reporting relevant results but without statistical test of the effects (uncertain). The numbers between parentheses indicate the number of synthesis papers with a quality score of at least 50%. Details on quality criteria can be found in the methodology section of this WIKI.
The 4 synthesis papers included studies conducted in Europe and 3 had a quality score higher than 50%. Some synthesis papers reported results for more than one impact or different effects for the same impact.
Table 1. Impacts in peatlands of no burning, no fertilisation, grazing and low intensity farming compared, respectively, to burned, fertilised, mowed and high intently farmed peatlands.
Impact | Metric | Intervention | Control | Positive | Negative | No effect | Uncertain* |
Increase biodiversity | No burning | Burning | 0 | 0 | 0 | 1 (0) | |
Decrease GHG emissions | CH4 emission | Grazing | Mowing | 0 | 0 | 1 (1) | 0 |
Low intensity farming | High intensity farming | 0 | 0 | 1 (1) | 0 | ||
No fertilisation | Fertilisation | 0 | 0 | 1 (1) | 0 | ||
N2O emission | Low intensity farming | High intensity farming | 0 | 0 | 1 (1) | 0 | |
No fertilisation | Fertilisation | 1 (1) | 0 | 0 | 0 | ||
Increase soil biological quality | No fertilisation | Fertilisation | 0 | 1 (1) | 0 | 0 | |
Increase crop yield | No fertilisation | Fertilisation | 0 | 1 (1) | 0 | 0 |
*Number of systematic reviews that report relevant results but without statistical test comparison of the intervention and the control.
3. DESCRIPTION OF THE KEY FACTORS INFLUENCING THE SIZE OF THE EFFECT
Only the factors explicitly studied in the reviewed synthesis papers with a significant effect are reported below. Details regarding the factors can be found in the Summaries of the meta-analyses.
Impact | Factors |
Increase soil biological quality | Climate (ref 1), Fertiliser type (ref 1), N application rate (ref 1) |
Increase crop yield | Soil P test at the beginning of the experiment (ref 3), P application rate (ref 3), Productivity without P fertilisation (ref 3) |
4. SYSTEMATIC REVIEW SEARCH STRATEGY
Keywords | TS=("wetland*" OR "marsh*" OR "fen*" OR "peatland*" OR "carbon-rich soil*" OR "carbon rich soil*" OR "wet meadow*" OR "wet soil*" OR "peat layer*" OR "water table*" OR "water layer*" OR “peat swamp*” OR “peat*” OR “water-saturated soil*” OR “black water*” OR “floodplain*” OR “histosol*” OR “mire*” OR “organic soil*” OR “estuar*” OR “mudflat*” OR "bog*") AND TS= ("rewett*" OR "land use change*" OR "land-use change*" OR "conserve*" OR "preserv*" OR "restor*" OR "conver*" OR "drain*" OR "undrain*" OR "protect*" OR "water retention" OR "colonization W/4 Thyfa" OR "colonization W/4 Sphagnum" OR "colonisation W/4 Thyfa" OR "colonisation W/4 Sphagnum" OR "set aside" OR “dry-rewet*” OR “irrigat*” OR “reveget*”) AND TS=("meta-analy*" OR "systematic* review*" OR "evidence map*" OR "global synthes*" OR "evidence synthes*" OR "research synthes*") AND TS=("wetland*" OR "marsh*" OR "fen*" OR "peatland*" OR "carbon-rich soil*" OR "carbon rich soil*" OR "wet meadow*" OR "wet soil*" OR "peat layer*" OR "water table*" OR "water layer*" OR “peat swamp*” OR “peat*” OR “water-saturated soil*” OR “black water*” OR “floodplain*” OR “histosol*” OR “mire*” OR “organic soil*” OR “estuar*” OR “mudflat*”) AND TS= ("plough*" OR "till*" OR "drain*" OR "water use" OR "machinery" OR "integrated pest management*" OR "IPM" OR "fertilis*" OR "fertiliz*" OR "paludicult*" OR "extensive W/4 management*" OR “burn*” OR “sustainable W/4 management*” OR “traditional W/4 management*” OR “prevention W/4 inva*” OR “eradication W/4 inva*” OR “control w/4 inva*” OR “graz*” OR “afforest*”) AND TS=("meta-analy*" OR "systematic* review*" OR "evidence map*" OR "global synthes*" OR "evidence synthes*" OR "research synthes*") or (SUBJAREA(AGRI OR ENVI) AND TITLE-ABS-KEY("wetland*" OR "marsh*" OR "fen*" OR "peatland*" OR "carbon-rich soil*" OR "carbon rich soil*" OR "wet meadow*" OR "wet soil*" OR "peat layer*" OR "water table*" OR "water layer*" OR “peat swamp*” OR “peat*” OR “water-saturated soil*” OR “black water*” OR “floodplain*” OR “histosol*” OR “mire*” OR “organic soil*” OR “estuar*” OR “mudflat*” OR "bog*") AND TITLE-ABS-KEY("rewett*" OR "land use change*" OR "land-use change*" OR "conserve*" OR "preserv*" OR "restor*" OR "conver*" OR "drain*" OR "undrain*" OR "protect*" OR "water retention" OR "colonization W/4 Thyfa" OR "colonization W/4 Sphagnum" OR "colonisation W/4 Thyfa" OR "colonisation W/4 Sphagnum" OR "set aside" OR “dry-rewet*” OR “irrigat*” OR “reveget*”) AND TITLE-ABS-KEY("meta-analy*" OR "systematic* review*" OR "evidence map*" OR "global synthes*" OR "evidence synthes*" OR "research synthes*")) AND (SUBJAREA(AGRI OR ENVI) AND TITLE-ABS-KEY("wetland*" OR "marsh*" OR "fen*" OR "peatland*" OR "carbon-rich soil*" OR "carbon rich soil*" OR "wet meadow*" OR "wet soil*" OR "peat layer*" OR "water table*" OR "water layer*" OR “peat swamp*” OR “peat*” OR “water-saturated soil*” OR “black water*” OR “floodplain*” OR “histosol*” OR “mire*” OR “organic soil*” OR “estuar*” OR “mudflat*”) AND TITLE-ABS-KEY("plough*" OR "till*" OR "drain*" OR "water use" OR "machinery" OR "integrated pest management*" OR "IPM" OR "fertilis*" OR "fertiliz*" OR "paludicult*" OR "extensive W/4 management*" OR “burn*” OR “sustainable W/4 management*” OR “traditional W/4 management*” OR “prevention W/4 inva*” OR “eradication W/4 inva*” OR “control w/4 inva*” OR “graz*” OR “afforest*”) AND TITLE-ABS-KEY("meta-analy*" OR "systematic* review*" OR "evidence map*" OR "global synthes*" OR "evidence synthes*" OR "research synthes*")) |
Search dates | No time restrictions |
Databases | Web of Science and Scopus, run in May 2022 |
Selection criteria | The main criteria that led to the exclusion of a synthesis paper were when the paper: 1) did not deal with peatlands or carbon-rich soils or the effects on peatlands could not be disentangled from those on wetlands; 2) was either a non-systematic review, a non-quantitative systematic review, or a meta-regression without mean effect sizes; 3) was not written in English. Synthesis papers that passed the relevance criteria were subject to critical appraisal carried out on a paper-by-paper basis. The search returned 471 synthesis papers potentially relevant for the practices object of our fiche. From the 471 potentially relevant synthesis papers, 332 were excluded after reading the title and abstract, and 135 after reading the full text according to the above-mentioned criteria. Finally, 4 synthesis papers were selected for peatland management. |
5. LIST OF SYNTHESIS PAPERS INCLUDED IN THE REVIEW OF THE FARMING PRACTICE IMPACTS
Ref. Num | Authors | Year | Title | Reference | DOI |
1 | Chen, M; Chang, L; Zhang, J; Guo, F; Vymazal, J; He, Q; Chen, Y | 2020 | Global nitrogen input on wetland ecosystem: The driving mechanism of soil labile carbon and nitrogen on greenhouse gas emissions | ENVIRONMENTAL SCIENCE AND ECOTECHNOLOGY, 4, 100063. | 10.1016/j.ese.2020.100063 |
2 | Haddaway, NR; Burden, A; Evans, CD; Healey, JR; Jones, DL; Dalrymple, SE; Pullin, AS | 2014 | Evaluating effects of land management on greenhouse gas fluxes and carbon balances in boreo-temperate lowland peatland systems | ENVIRONMENTAL EVIDENCE, 3(1), 1-30. | 10.1186/2047-2382-3-5 |
3 | Valkama, E; Uusitalo, R; Ylivainio, K; Virkajarvi, P; Turtola, E | 2009 | Phosphorus fertilization: A meta-analysis of 80 years of research in Finland | AGRICULTURE ECOSYSTEMS AND ENVIRONMENT, 130, 75-85. | 10.1016/j.agee.2008.12.004 |
4 | Stewart, GB; Coles, CF; Pullin, AS | 2005 | Applying evidence-based practice in conservation management: Lessons from the first systematic review and dissemination projects | BIOLOGICAL CONSERVATION, 126, 270-278. | 10.1016/j.biocon.2005.06.003 |
[1] Synthesis research papers include either meta-analysis or systematic reviews with quantitative results.
[2] Joosten, H & Clarke, D. 2002: Wise use of mires and peatlands: Background and principles including a framework for decision making. IMCG/IPS.
[3] Joosten, et al. 2012. Peatlands—Guidance for climate change mitigation, conservation, rehabilitation and sustainable use. Mitigation of climate change in Agriculture Series 5 (FAO).
[4] https://ec.europa.eu/eurostat/statistics-explained/index.php?title=Glossary:Fertiliser
[5] Chen, M; Chang, L; Zhang, J et al. 2020. Global nitrogen input on wetland ecosystem: The driving mechanism of soil labile carbon and nitrogen on greenhouse gas emissions. Environmental Science and Ecotechnology, 4, 100063.
[6] Paz-Kagan, T; Ohana-Levi, N; Herrmann, I et al. 2016. Grazing intensity effects on soil quality: a spatial analysis of a Mediterranean grassland. Catena, 146, 100–110.
[7] Stewart, GB; Coles, C F; Pullin, AS. 2005. Applying evidence-based practice in conservation management: Lessons from the First systematic review and dissemination projects, 126, 270–278.
[8] Haddaway, NR; Burden, A; Evans, CD; et al. 2014. Evaluating effects of land management on greenhouse gas fluxes and carbon balances in boreo-temperate lowland peatland systems. Environmental Evidence, 3.