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Calibrated Passive Sampling - Multi-plot Field Measurements of NH3 Emissions with a Combination of Dynamic Tube Method and Passive Samplers
Published on: March 21, 2016
Legacy-buffered groundwater nitrate limits predictability from short-term hydroclimatic windows across intensive
Caipeng Yue1, Bingxin Lian2, Jiamin Zhang2
1School of Life Sciences, Zhengzhou University, Zhengzhou, 450001, China; School of Agriculture and Biomanufacturing, Zhengzhou University, Zhengzhou, 450001, China; Henan Funiu Mountain Biological and Ecological Environment Observatory, Zhengzhou University, Zhengzhou, 450001, China.
None:
Groundwater nitrate contamination in intensive croplands often persists despite strong short-term weather variability, suggesting that near-surface signals may not translate directly to aquifers. We tested this across a four-site south-to-north transect in Henan Province, China, under a wheat-maize rotation. For each sampling event, we quantified antecedent hydroclimatic windows from daily meteorological data, and measured depth-integrated (0-50 cm) soil inorganic N stocks, soil N-cycling enzyme activities, groundwater NO3--N, and nitrate isotopes (δ15N-NO3- and δ18O-NO3-). Principal component analysis summarized hydroclimatic variability into two dominant gradients: a dry-frequency axis (PC1) and an evaporative-demand axis (PC2). Drier antecedent conditions (higher dry-frequency scores) were consistently associated with greater 0-50 cm soil NO3- storage and coordinated changes in enzyme indices related to N turnover; the dry-frequency gradient accounted for 41% of the variance in soil NO3--N stocks. In contrast, groundwater nitrate showed weak short-term coupling across all window lengths, with only 19% of NO3- variability explained and no significant contemporaneous associations with short-term soil indicators or hydroclimate axes. Isotope patterns showed strong site- and stage-dependent scatter: groundwater δ15N-NO3- varied widely (3.5-17.5‰) while δ18O-NO3- remained narrow (7.0-8.9‰), consistent with mixing among multiple nitrate sources and transport lags that buffer legacy signals in the aquifer. These results help explain why groundwater nitrate remains poorly predictable from short-term surface indicators, and they support management strategies that prioritize sustained reductions in long-term N surplus and monitoring designs that account for subsurface storage and time lags.
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