Abstract
Soil faunal activity can be a major control of greenhouse gas (GHG) emissions from soil. Effects of single faunal species, genera or families have been investigated, but it is unknown how soil fauna diversity may influence emissions of both carbon dioxide (CO2, end product of decomposition of organic matter) and nitrous oxide (N2O, an intermediate product of N transformation processes, in particular denitrification). Here, we studied how CO2 and N2O emissions are affected by species and species mixtures of up to eight species of detritivorous/fungivorous soil fauna from four different taxonomic groups (earthworms, potworms, mites, springtails) using a microcosm set-up. We found that higher species richness and increased functional dissimilarity of species mixtures led to increased faunal-induced CO2 emission (up to 10%), but decreased N2O emission (up to 62%). Large ecosystem engineers such as earthworms were key drivers of both CO2 and N2O emissions. Interestingly, increased biodiversity of other soil fauna in the presence of earthworms decreased faunal-induced N2O emission despite enhanced C cycling. We conclude that higher soil fauna functional diversity enhanced the intensity of belowground processes, leading to more complete litter decomposition and increased CO2 emission, but concurrently also resulting in more complete denitrification and reduced N2O emission. Our results suggest that increased soil fauna species diversity has the potential to mitigate emissions of N2O from soil ecosystems. Given the loss of soil biodiversity in managed soils, our findings call for adoption of management practices that enhance soil biodiversity and stimulate a functionally diverse faunal community to reduce N2O emissions from managed soils.
| Original language | English |
|---|---|
| Pages (from-to) | 1886-1898 |
| Number of pages | 13 |
| Journal | Global Change Biology |
| Volume | 26 |
| Issue number | 3 |
| Early online date | 6 Oct 2019 |
| DOIs | |
| Publication status | Published - Mar 2020 |
Funding
We thank Tamás Salánki for extracting the potworms, mites and springtails from our soil samples, and Remco Hamoen for his assistance by obtaining the X‐ray micro tomography scans (XRT) using CAT‐AgroFood equipment. In addition, we would like to thank Jaap Nelemans, Willeke van Tintelen and Gerlinde Vink for their assistance in the laboratory. This research was supported by a grant from the Netherlands Organization for Scientific Research/Earth and Life Sciences (NWO‐ALW, grant number 823.01.016). We thank Tam?s Sal?nki for extracting the potworms, mites and springtails from our soil samples, and Remco Hamoen for his assistance by obtaining the X-ray micro tomography scans (XRT) using CAT-AgroFood equipment. In addition, we would like to thank Jaap Nelemans, Willeke van Tintelen and Gerlinde Vink for their assistance in the laboratory. This research was supported by a grant from the Netherlands Organization for Scientific Research/Earth and Life Sciences (NWO-ALW, grant number 823.01.016).
| Funders | Funder number |
|---|---|
| NWO-ALW | |
| Netherlands Organization for Scientific Research/Earth | |
| Netherlands Organization for Scientific Research/Earth and Life Sciences | 823.01.016 |
Keywords
- community composition
- functional dissimilarity
- GHG mitigation
- net diversity effect
- soil-derived GHG emission
- species richness