EA 4592 G&E, Bordeaux INP, Université Bordeaux Montaigne, Carnot ISIFoR, 1 Allée F. Daguin, 33607, Pessac, France; Bordeaux Métropole, Esplanade Charles de Gaulle, 33000, Bordeaux, France.
EA 4592 G&E, Bordeaux INP, Université Bordeaux Montaigne, Carnot ISIFoR, 1 Allée F. Daguin, 33607, Pessac, France.
Environ Pollut. 2022 Feb 15;295:118666. doi: 10.1016/j.envpol.2021.118666. Epub 2021 Dec 9.
Since the fifties, organochlorine pesticides (OCPs) had been used in agriculture to protect vegetables. Two decades after their ban by the Stockholm convention in 2001, OCPs are still present in agricultural soils inducing vegetable contamination with concentrations above Maximum Residue Level (MRL). This is a major concern for a 5 km peri-urban vegetable growing valley located in the south west of France. In the present work, the sampling method was developed to clarify the spatial distribution of one OCP, Dieldrin, and its relationship with soil properties at the scale of study area. A total of 99 soil samples was collected for physicochemical analyses and Dieldrin concentrations. Results show Dieldrin concentrations in soils up to 204 μg kg. The horizontal distribution of this pesticide is heterogeneous at the study area scale but homogeneous in each reference plot studied. About 85% of the contamination was located in the top soil layers (0-40 cm depth), but Dieldrin may still be quantified at a depth of 80 cm. Among all soil physicochemical parameters analysed, SOM was the most significantly related (P < 10) with Dieldrin concentrations, once different grain size fractions were considered. Moreover, results indicate a 33 times higher Dieldrin concentration and/or extractability for coarse sand than for other grain size fractions. These results show that the developed sampling method is adapted for the study area scale as it helps understanding the factors influencing the spatial distribution of Dieldrin. Historical amendments are the predominant factor for the horizontal contamination and deep ploughing for the vertical contamination. Also, the variations of coarse sand repartition in soils prevents identification of relationships between SOM and Dieldrin contamination in bulk soil. Further investigation is required to explain these relationships but these results highlight why no clear relationship between OCPs and SOM was previously identified.
自 20 世纪 50 年代以来,有机氯农药(OCPs)一直被用于农业来保护蔬菜。在 2001 年《斯德哥尔摩公约》禁止使用 OCP 二十年后,它们仍然存在于农业土壤中,导致蔬菜受到污染,浓度超过最大残留限量(MRL)。这是法国西南部一个 5 公里近郊区蔬菜种植谷的主要关注点。在本研究中,开发了一种采样方法,以阐明一种 OCP,狄氏剂,及其与研究区域土壤特性的空间分布关系。共采集了 99 个土壤样品进行理化分析和狄氏剂浓度分析。结果表明,土壤中的狄氏剂浓度高达 204μg/kg。该农药在研究区域尺度上的水平分布不均匀,但在每个参考样地内均匀。约 85%的污染位于表层土壤(0-40cm 深度),但在 80cm 深处仍可定量狄氏剂。在所分析的所有土壤理化参数中,有机质(SOM)与狄氏剂浓度的相关性最强(P < 10),同时考虑了不同的粒径分数。此外,结果表明,粗砂的狄氏剂浓度和/或提取率比其他粒径分数高 33 倍。这些结果表明,所开发的采样方法适用于研究区域尺度,因为它有助于了解影响狄氏剂空间分布的因素。历史修正是水平污染的主要因素,深耕是垂直污染的主要因素。此外,土壤中粗砂的分布变化阻止了在原状土壤中识别 SOM 和狄氏剂污染之间的关系。需要进一步研究来解释这些关系,但这些结果强调了为什么以前没有确定 OCPs 和 SOM 之间的明确关系。