Institute of Natural Resources and Agrobiology of Salamanca (IRNASA-CSIC), Cordel de Merinas 40-52, 37008, Salamanca, Spain.
Institute of Natural Resources and Agrobiology of Salamanca (IRNASA-CSIC), Cordel de Merinas 40-52, 37008, Salamanca, Spain.
Ecotoxicol Environ Saf. 2019 Oct 30;182:109395. doi: 10.1016/j.ecoenv.2019.109395. Epub 2019 Jul 1.
Adding organic amendments to soil could modify the bioavailability of herbicides and lead to changes in the microbial community's activity and structure. The objective here was to study the dissipation and total mass balance of C-labeled prosulfocarb applied at two rates (4 and 10 mg kg) in unamended and green compost (GC)-amended soil. Soil dehydrogenase activity (DHA) and phospholipid fatty acid (PLFA) profile analysis were determined to evaluate the effect of herbicide residues on microbial community's activity and structure over the dissipation period. The dissipation rate of prosulfocarb decreased after soil amendment due to higher herbicide adsorption by the amended soil. The 50% dissipation time (DT) increased 1.7 times in the unamended soil when the concentration of prosulfocarb increased 2.5 times. The mass balance results indicate that the sum of water and organic extractable fractions represented the highest amounts up to the dissipation of 50% C-prosulfocarb. The C-herbicide was then mainly mineralized (up to 11%-31%) or formed non-extractable residues (up to 35%-44%). The amount of C-prosulfocarb residues extracted with methanol was slightly higher in amended soils than in unamended ones. C-prosulfocarb mineralization was higher in unamended soils than in amended ones. The formation of non-extractable residues was continuous, and increased over time. Soil DHA decreased in the unamended soil and was maintained in the GC-amended soil at the end of the assay. The microbial structure was barely disturbed over the prosulfocarb degradation process, although it was clearly influenced by the application of GC. The results obtained reveal the influence organic amendment has on herbicide bioavailability to decrease its biodegradation and buffer its impact on the soil microbial structure.
向土壤中添加有机肥料可能会改变除草剂的生物可利用性,并导致微生物群落活性和结构发生变化。本研究旨在研究以两种浓度(4 和 10 mg kg)施用于未施肥和绿肥(GC)施肥土壤中的 C 标记的砜嘧磺隆的消解和总质量平衡。通过测定土壤脱氢酶活性(DHA)和磷脂脂肪酸(PLFA)谱分析来评估除草剂残留对微生物群落活性和结构的影响。由于受施肥土壤中更高的除草剂吸附的影响,砜嘧磺隆在土壤施肥后消解速度降低。在未施肥土壤中,当砜嘧磺隆浓度增加 2.5 倍时,50%消解时间(DT)增加了 1.7 倍。质量平衡结果表明,水和有机可提取分数的总和在 50% C-砜嘧磺隆消解之前代表了最高的含量。然后,C-除草剂主要被矿化(高达 11%-31%)或形成不可提取的残留(高达 35%-44%)。用甲醇提取的 C-砜嘧磺隆残留量在施肥土壤中略高于未施肥土壤。未施肥土壤中 C-砜嘧磺隆的矿化作用高于施肥土壤。不可提取的残留形成是连续的,且随时间增加。在未施肥土壤中,DHA 降低,而在整个试验结束时 GC 施肥土壤中则保持不变。在砜嘧磺隆降解过程中,微生物结构几乎没有受到干扰,尽管 GC 的应用明显影响了微生物结构。研究结果表明,有机肥料的添加会影响除草剂的生物可利用性,从而降低其生物降解能力,并缓冲其对土壤微生物结构的影响。