埃塞俄比亚农业土壤中农药残留、草甘膦的吸附和降解特性

IF 2.3 Q2 PUBLIC, ENVIRONMENTAL & OCCUPATIONAL HEALTH Environmental Health Insights Pub Date : 2025-01-03 eCollection Date: 2025-01-01 DOI:10.1177/11786302241311679
Bereket Ayenew, Endalkachew Getu
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引用次数: 0

摘要

背景:埃塞俄比亚小麦产量的下降被广泛归咎于害虫,这导致了农药使用量的增加,以提高生产力。影响农药从土壤渗入水体造成环境污染可能性的农药的吸收和降解程度尚未公布埃塞俄比亚土壤的情况。该研究旨在量化农药残留水平,评估草甘膦在土壤中的吸附能力和降解速度。材料与方法:采用QuEChERS萃取法测定各农药的浓度。采用间歇吸附法测定了车哈和定绍地区农业土壤对草甘膦的吸附能力。结果:12份土壤样品中检出6种不同数量的农药残留。草甘膦(24.00-219.31µg kg-1), s-甲草胺(23.67-220.67µg kg-1),毒死蜱(27.74 - 202.67µg kg-1), pyroxulam(14.67-50.65µg kg-1), florasulam(78.00-250.67µg kg-1),马拉硫磷(15.00-49.67µg kg-1)。结果表明,SD10土壤对草甘膦的吸附量为18.91 μg-1-n mLn g-1, SC1土壤对草甘膦的吸附量为114.66 μg-1-n mLn g-1;有机质和粘土含量是影响这一过程的主要因素。吸附实验数据表明,化学吸附是草甘膦吸附的主要过程,拟二级动力学模型拟合最佳(r2 = 0.99)。研究区土壤草甘膦降解速率差异显著(0.0076 ~ 0.0221周-1)。结果表明:影响草甘膦半衰期(草甘膦降解)的主要土壤变量是粘土浓度(r2 = 0.48;P = 0.013), pH值(r2 = 0.55;P = 0.0055),有机质(r2 = 0.74;P = 0.00027), Feox (r2 = 0.50;P = 0.0105), Alox (r2 = 0.73;p = .00046)。结论:土壤对草甘膦较弱的吸附能力可以作为土壤中农药残留危害土壤生物并通过径流和淋滤污染附近水体的一个很好的指标。
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Pesticide Residues, Glyphosate Adsorption and Degradation Characteristics in Ethiopian Agricultural Soils.

Background: The decline in wheat output in Ethiopia is widely attributed to pests, which has led to a rise in the usage of pesticides to boost productivity. The degree of pesticides sorption and degradation which influence the likelihood of environmental contamination from pesticides seeping into water bodies from soil has not yet been published for Ethiopian soils. The study aimed at to quantify the levels of pesticide residues, assess glyphosate's adsorption capabilities and degradation rate in the soils.

Materials and methods: QuEChERS method of extraction was employed to determine the concentration of the respective pesticides. The adsorption capacities of glyphosate in agricultural soils of Cheha and Dinsho districts were measured using batch adsorption techniques.

Results: Six pesticide residues were found in 12 soil samples at varied quantities. Glyphosate (24.00-219.31 µg kg-1), s-metolachlor (23.67-220.67 µg kg-1), chlorpyrifos (27.74 202.67 µg kg-1), pyroxulam (14.67-50.65 µg kg-1), florasulam (78.00-250.67 µg kg-1), malathion (15.00-49.67 µg kg-1). The experimental results showed that glyphosate was slightly sorbed at SD10 soil (18.91 μg-1-n mLn g-1) in comparison to SC1 soil (114.66 μg-1-n mLn g-1). Organic matter and clay content proving to be the principal factors influencing the process. According to adsorption experimental data, chemisorption is the major process in glyphosate adsorption, with the pseudo-second order kinetic model providing the best fit (R 2 = .99). The soils in the study area exhibit notable variations in glyphosate rate of degradation (0.0076-0.0221 week-1). The findings show that the main soil variables affecting the half-life (glyphosate degradation) were clay concentrations (R 2 = .48; P = .013), pH (R 2 = .55; P = .0055), Organic matter (R 2 = .74; P = .00027), Feox (R 2 = .50; P = .0105), and Alox (R 2 = .73; P = .00046).

Conclusion: The weak glyphosate adsorption capabilities of soils can be a good indicator that the pesticide residues in the soil are poised to endanger soil organisms and contaminate nearby water bodies through runoff and leaching.

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来源期刊
Environmental Health Insights
Environmental Health Insights PUBLIC, ENVIRONMENTAL & OCCUPATIONAL HEALTH-
CiteScore
3.20
自引率
22.20%
发文量
97
审稿时长
8 weeks
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