4.7 Article

Microplastics in the agroecosystem: Are they an emerging threat to the plant-soil system?

Journal

SOIL BIOLOGY & BIOCHEMISTRY
Volume 148, Issue -, Pages -

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.soilbio.2020.107926

Keywords

Agroecosystem; Belowground C input; Plastic pollution; PLFA; Rhizosphere process

Categories

Funding

  1. UK Global Challenges Research Fund (GCRF) project
  2. UK-China Virtual Joint Centre for Agricultural Nitrogen (CINAg) - Newton Fund, via UK BBSRC [BB/N013468/1]
  3. UK-China Virtual Joint Centre for Agricultural Nitrogen (CINAg) - NERC [BB/N013468/1]
  4. Chinese Ministry of Science and Technology
  5. NERC [NE/S004548/1] Funding Source: UKRI

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Despite plastics providing great benefits to our daily life, plastics accumulating in the environment, especially microplastics (MPs; defined as particles <5 mm), can lead to a range of problems and potential loss of ecosystem services. Current research has demonstrated the significant impact of MPs on aquatic systems, but little is known about their effects on the terrestrial environment, especially within agroecosystems. Hereby, we investigated the effect of MPs type and amount on plant growth, soil microorganisms, and photoassimilate carbon (C) allocation. MPs had a negative, dose-dependent impact on plant growth affecting both above- and below-ground productivity (-22.9% and -8.4%). MPs also influenced assimilated C-14 allocation in soil (+70.6%) and CO2 emission (+43.9%). Although the activity of beta-glucosidase was suppressed by MPs, other C- and N-cycling related enzyme activities were not affected. The type and amount of MPs in soil greatly altered C flow through the plant-soil system, highlighting that MPs negatively affect a range of C-dependent soil functions. Moreover, MPs increased the soil microbial biomass (+43.6%; indicated by PLFAs), and changed the structure and metabolic status of the microbial community. The evidence presented here suggests that MPs can have a significant impact on key pools and fluxes within the terrestrial C cycle with the response being both dose-dependent and MPs specific. We conclude that MPs in soil are not benign and therefore every step should be made to minimise their entry into the soil ecosystem and potential to transfer into the food chain.

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