4.8 Article

Small artificial waterbodies are widespread and persistent emitters of methane and carbon dioxide

Journal

GLOBAL CHANGE BIOLOGY
Volume 27, Issue 20, Pages 5109-5123

Publisher

WILEY
DOI: 10.1111/gcb.15762

Keywords

ditch; drainage; greenhouse gas; inland waters; pond; stream

Funding

  1. European Research Council [725546]
  2. FORMAS [2018-01794, 2020-00950]
  3. NERC [NE/N018087/1]
  4. NERC [NE/N018087/1] Funding Source: UKRI
  5. Formas [2020-00950, 2018-01794] Funding Source: Formas
  6. European Research Council (ERC) [725546] Funding Source: European Research Council (ERC)

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Inland waters serve an active role in the global carbon cycle by emitting large volumes of greenhouse gases. Research has highlighted the potential importance of small, artificial waterbodies like drainage ditches and constructed ponds as significant emission hotspots. Greenhouse gas emissions from these artificial waterbodies are positively related to nutrient status and are larger per unit area compared to natural systems, contributing to the global carbon cycle.
Inland waters play an active role in the global carbon cycle and emit large volumes of the greenhouse gases (GHGs), methane (CH4) and carbon dioxide (CO2). A considerable body of research has improved emissions estimates from lakes, reservoirs and rivers but recent attention has been drawn to the importance of small, artificial waterbodies as poorly quantified but potentially important emission hotspots. Of particular interest are emissions from drainage ditches and constructed ponds. These waterbody types are prevalent in many landscapes and their cumulative surface areas can be substantial. Furthermore, GHG emissions from constructed waterbodies are anthropogenic in origin and form part of national emissions reporting, whereas emissions from natural waterbodies do not (according to Intergovernmental Panel on Climate Change guidelines). Here, we present GHG data from two complementary studies covering a range of land uses. In the first, we measured emissions from nine ponds and seven ditches over a full year. Annual emissions varied considerably: 0.1-44.3 g CH4 m(-2) year(-1) and -36-4421 g CO2 m(-2) year(-1). In the second, we measured GHG concentrations in 96 ponds and 64 ditches across seven countries, covering subtropical, temperate and sub-arctic biomes. When CH4 emissions were converted to CO2 equivalents, 93% of waterbodies were GHG sources. In both studies, GHGs were positively related to nutrient status (C, N, P), and pond GHG concentrations were highest in smallest waterbodies. Ditch and pond emissions were larger per unit area when compared to equivalent natural systems (streams, natural ponds). We show that GHG emissions from natural systems should not be used as proxies for those from artificial waterbodies, and that artificial waterbodies have the potential to make a substantial but largely unquantified contribution to emissions from the Agriculture, Forestry and Other Land Use sector, and the global carbon cycle.

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