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Greenhouse gas emissions following biosolids application to farmland: Estimates from the DeNitrification and DeComposition model

生物固体 环境科学 温室气体 反硝化 土壤碳 农学 生长季节 污水污泥 一氧化二氮 二氧化碳 作物残渣 环境工程 甲烷 环境化学 生物能源 分解 氮气 土壤水分 土壤有机质 碳纤维 作物 污水处理 城市固体废物 厌氧消化 甲烷排放 中层 总有机碳
作者
Okenna Obi‐Njoku,Michael Yongha Boh,Ward Smith,Brian Grant,G.W. Price,Naseer Hussain,Joann K. Whalen,O. Grant Clark
出处
期刊:Science of The Total Environment [Elsevier]
卷期号:823: 153695-153695 被引量:16
标识
DOI:10.1016/j.scitotenv.2022.153695
摘要

Municipal wastewater sludge may be processed into biosolids and applied to farmland for crop production, rather than be disposed of in landfills. Biosolids supply plant nutrients and increase soil organic carbon but also contribute to the production of greenhouse gases (GHGs). Computational models must therefore be refined to estimate the contribution of these gases to national GHG inventories. The DeNitrification and DeComposition (DNDC) model was evaluated for processes regulating crop growth, GHGs and soil C&N dynamics to determine its suitability for informing policy decision-making and advancing Canada's GHG inventory. Three years (2017-2019) of data were collected from replicated corn (Zea mays L.) plots in Quebec, Canada. The plots received 120 kg of available N ha-1 y-1 in mesophilic anaerobically digested biosolids, composted biosolids, alkaline-stabilized biosolids, urea, or combinations of these, while control plots were left unfertilized. Treatments receiving digested biosolids emitted more nitrous oxide (N2O) during the growing season than other treatments, while carbon dioxide (CO2) emissions were similar between treatments. After calibration, DNDC estimates were within the 95% confidence interval of the measured variables. Correlation coefficients (r) indicated discrepancies in trends between the estimated and measured values for daily CO2 and N2O emissions. These emissions were underestimated in the early and mid-growing season of 2018. They were more variable from plots fertilized with composted or alkaline-stabilized biosolids than from those with digested biosolids. Annual N2O emissions (r = 0.8), crop yields (r = 0.5), and soil organic carbon (r = 0.4) were modelled with higher accuracy than cumulative CO2 emissions (r = 0.3) and total soil N (r = 0.1). These findings suggest that DNDC is suitable for estimating field-scale N2O emissions following biosolids application, but estimates of CO2 emissions could be improved, perhaps by disaggregating the biosolids from the soil organic matter pools in the decomposition subroutines.
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