School of Public Health (Shenzhen), Sun Yat-sen University, Guangdong 510275, China.
Department of Chemistry and Biochemistry, Utah State University, Logan, UT 84322, USA.
Sci Total Environ. 2021 Oct 15;791:148412. doi: 10.1016/j.scitotenv.2021.148412. Epub 2021 Jun 10.
To better manage pesticide pollution in surface soils, we introduced a first-order-kinetics-based screening model to evaluate the steady-state concentrations of pesticides in surface soils while considering degradation, volatilization, plant uptake, and precipitation processes. For each process, we developed a spatiotemporal-pattern-based model using spatiotemporal variables, including air temperature (T), relative humidity (RH), and rainfall intensity (I), to characterize the overall dissipation rates (k) of pesticides in the soil. These dissipation rates were converted to fate factors (FFs), which are commonly used in life cycle analyses. The results indicate that, in general, the k values increase with increasing T and I and decrease with increasing RH. This is because increased T boosts the degradation, volatilization, and plant uptake processes, whereas increased RH lowers the plant transpiration rate. Also, the simulation for over 700 pesticides indicated that the degradation process dominates the overall dissipation of most pesticides in the soil, and the volatilization process contributes the least. In addition, we simulated chlorpyrifos FFs for Brazil, China, the US, and the European Union (EU) using the annual average T, RH, and I values. The results indicate that, in general, Brazilian federal units have the smallest FFs and the narrowest simulated FF range because of their humid tropical climates. Meanwhile, the EU member states have the largest FFs and the widest FF range because of their range in locations. In addition, our simulated results show that the surface soils in the high-latitude regions could accumulate more chlorpyrifos than those in low-latitude regions because of the larger simulated FFs. Furthermore, we parameterized our model using 737 pesticides with the USEtox, thereby providing an alternative approach to simulate the steady-state concentration of pesticides in surface soils from the USEtox available data. The model developed herein is a useful screening tool for predicting pesticide concentrations in surface soil worldwide to improve soil and ecological health risk management.
为了更好地管理地表土壤中的农药污染,我们引入了一个基于一级动力学的筛选模型,以评估考虑降解、挥发、植物吸收和沉淀过程的地表土壤中农药的稳态浓度。对于每个过程,我们使用时空变量(包括空气温度 (T)、相对湿度 (RH) 和降雨强度 (I))开发了一个时空模式模型,以描述农药在土壤中的整体消散率 (k)。这些消散率被转换为通常用于生命周期分析的归宿因子 (FF)。结果表明,一般来说,k 值随 T 和 I 的增加而增加,随 RH 的增加而降低。这是因为升高的 T 促进了降解、挥发和植物吸收过程,而升高的 RH 降低了植物蒸腾速率。此外,对超过 700 种农药的模拟表明,降解过程主导了大多数农药在土壤中的整体消散,而挥发过程的贡献最小。此外,我们使用年均 T、RH 和 I 值模拟了巴西、中国、美国和欧盟 (EU) 的氯吡硫磷 FF。结果表明,一般来说,由于其潮湿的热带气候,巴西联邦单位的 FF 最小,模拟的 FF 范围最窄。同时,由于地理位置的不同,欧盟成员国的 FF 最大,FF 范围最宽。此外,我们的模拟结果表明,由于较大的模拟 FF,高纬度地区的地表土壤可能比低纬度地区积累更多的氯吡硫磷。此外,我们使用 USEtox 中的 737 种农药对我们的模型进行了参数化,从而提供了一种从 USEtox 可用数据模拟地表土壤中农药稳态浓度的替代方法。本文开发的模型是一种预测全球地表土壤中农药浓度的有用筛选工具,可用于改善土壤和生态健康风险管理。