Department of Environmental Protection, Estación Experimental del Zaidín -Consejo Superior de Investigaciones Cientificas (EEZ-CSIC), C/Profesor Albareda 1, 18008 Granada, Spain.
INRA, UMR 1347 Agroécologie, 17 rue Sully, B P 86510, 21065 Dijon Cedex, France.
Sci Total Environ. 2017 Feb 1;579:1111-1119. doi: 10.1016/j.scitotenv.2016.11.082. Epub 2016 Nov 30.
The fate and impact of pesticide on soil depend partly on the agricultural practices, such as prior treatment with pesticide and/or organic amendments. As a means of determining how the previous soil conditions can affect the fate of imidacloprid (IMI) and its effect on soil functions, experiments were made with soil samples, double-amended or not with either vine-shoot (W) or olive cake (O) vermicompost or contaminated or not with IMI. These soil samples, incubated for 3months, were placed in two microcosms (M1 with the pre-amended soils and M2 with the pre-exposed soils), treated with IMI and amended with vermicomposts and then incubated for 3months. The IMI distribution on soil fractions, sorption processes, dissipation kinetics, and biochemical as well as genetic structure and bacterial abundance were determined to assess the fate and impact of IMI on the soil. The addition of W vermicompost to the soil reduced the IMI availability. The dissipation kinetic in soils from M1 and M2 followed, respectively, a single first-order and a double first-order in parallel models. The lowest IMI persistence corresponded to the soil from M2 amended with O-vermicompost with DT50 and DT90 values of 67d and 265d, while in the other soils 90% dissipation required >512d. The vermicomposts-amended contaminated soils increased the dehydrogenase activity by 2- and 4-fold respect the control soils. However, the urease activity decreased due to the IMI influence. The changes in the bacterial community in the contaminated soil amended with O-vermicompost during incubation were correlated with the dissipation rate constant of IMI, suggesting a better tolerance of microorganisms to IMI. Thus, in the soil contaminated with IMI, the amendment with the vermicompost from olive cake can mitigate the impact of this insecticide on soil functions and promote its depuration capability while minimizing environmental risks.
农药在土壤中的命运和影响部分取决于农业实践,例如预先用农药和/或有机改良剂处理。为了确定先前的土壤条件如何影响吡虫啉(IMI)的命运及其对土壤功能的影响,我们用土壤样本进行了实验,这些土壤样本要么经过双倍的葡萄藤(W)或橄榄饼(O)蚯蚓粪肥的预施肥,要么经过 IMI 污染,要么没有经过 IMI 污染。这些土壤样本在培养 3 个月后,被放置在两个微宇宙(M1 为预施肥土壤,M2 为预暴露土壤)中,用 IMI 处理并与蚯蚓粪肥一起施肥,然后再培养 3 个月。为了评估 IMI 对土壤的命运和影响,我们确定了 IMI 在土壤中的分布、吸附过程、消解动力学以及生物化学、遗传结构和细菌丰度。向土壤中添加 W 蚯蚓粪肥降低了 IMI 的有效性。M1 和 M2 土壤的消解动力学分别遵循单一一级和一级平行模型。DT50 和 DT90 值分别为 67d 和 265d 的 O 蚯蚓粪肥施肥土壤中的 IMI 持久性最低,而在其他土壤中,90%的消解需要>512d。与对照土壤相比,蚯蚓粪肥施肥的污染土壤中的脱氢酶活性增加了 2-4 倍。然而,由于 IMI 的影响,脲酶活性降低。在培养过程中,用 O 蚯蚓粪肥施肥的污染土壤中细菌群落的变化与 IMI 的消解速率常数相关,这表明微生物对 IMI 的耐受性更好。因此,在受 IMI 污染的土壤中,用橄榄饼的蚯蚓粪肥进行施肥可以减轻这种杀虫剂对土壤功能的影响,并促进其净化能力,同时将环境风险降到最低。