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Updated: May 23, 2026

An Anaerobic Biosensor Assay for the Detection of Mercury and Cadmium
Published on: December 17, 2018
The interaction between cadmium and water induces a nonlinear response in nitrogen cycling in paddy soils by
Fangying Shi1, Huajun Fang2, Shulan Cheng3
1Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China; College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China.
Abstract:
Cadmium (Cd) contamination threatens agricultural soil health by disrupting soil nitrogen (N) supply capacity through the disruption of microbially mediated N cycling processes. Water management plays a critical role in regulating Cd bioavailability; however, the interactive effects of Cd stress and water regimes on N transformation and microbial mechanisms remain poorly understood. This study investigates the coupled "Cd-water-microbe-N cycle" framework in red paddy soils with Cd concentrations ranging from 0 to 10 mg kg-1 under flooded and non-flooded conditions. A 15N paired isotope labeling approach combined with a Markov chain Monte Carlo (MCMC) model was employed to quantitatively estimate the rates of major N transformation processes. Microbial community structure and functional gene responses were analyzed using HT-qPCR, high-throughput sequencing, and co-occurrence network analysis. Results showed that Cd effects were strongly water-dependent and concentration-specific. Under flooded conditions, Cd (0.3-10 mg kg⁻¹) reduced gross mineralization and immobilization rates by up to ∼20-40% while increasing nitrification and denitrification rates, resulting in negative net N supply and higher NO3- loss risk. In contrast, low-to-moderate Cd levels (0.3-3.0 mg kg⁻¹) under non-flooded conditions enhanced N transformation rates by ∼10-30%, maintaining a positive N supply. Microbial network analysis revealed that bacteria dominated functional differentiation, with low-dose Cd (≤1.5 mg kg⁻¹) promoting synergistic interactions and high Cd levels (≥6.0 mg kg⁻¹) causing network fragmentation and stronger inhibition of N cycling functions. This study provides mechanistic insights into the interactions among Cd contamination, water regimes, microbial networks, and N cycling, which may help inform management strategies for Cd-contaminated farmland.
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