Université de Lorraine, INRA, UR AFPA, 2 Avenue de la Forêt de Haye, BP 172, 54505 Vandœuvre-lès-Nancy cedex, France.
Environ Sci Pollut Res Int. 2013 Jan;20(1):117-25. doi: 10.1007/s11356-012-1167-7. Epub 2012 Sep 8.
Residues of pesticides in fish farming productions from barrage ponds are seldom studied in spite of increasing health questionings and environmental concerns. The purpose of this study is to establish the pesticide contamination profiles of sediments and edible fish from five ponds in Northeastern France. Multi-residues method and liquid chromatography-tandem mass spectrometry analysis were used to quantify 13 pesticides (azoxystrobin, carbendazim, clomazone, diflufenican, dimethachlor, fluroxypyr, iprodion, isoproturon, mesosulfuron-methyl, metazachlor, napropamid, quizalofop and thifensulfuron-methyl). Ten sediments and 143 muscles samples were analysed, corresponding to two successive fishing campaigns (first fishing date and second fishing date (P2), about 1 year later) on five sites (noted C-0, C-25, C-45, C-75 and C-85 to express the increasing gradient of crop area). Isoproturon was present in all sediments samples (1.8-56.4 μg/kg dry weight). During P2 period, carbendazim was quantified in the fish of site C-0 (0.09 ± 0.02, 0.2 ± 0.1 and 0.17 ± 0.06 μg/kg wet weight (ww) for roach, carp and perch, respectively). Metazachlor was only quantified in perch of the site C-25 (0.13 ± 0.02 μg/kg ww). Concentrations of isoproturon were similar for the sites C-45 and C-75 with 0.4 ± 0.1 and 0.75 ± 0.06 μg/kg ww for carp and perch, respectively. Contamination of fish reflected generally concentrations in surroundings. Isoproturon was the most concentrated and its main source was water for perch while carp was exposed through both water and sediments, highlighting their life strategies in pond.
尽管人们对健康问题和环境问题的关注日益增加,但很少有研究关注水产养殖生产中来自拦河坝池塘的农药残留。本研究的目的是建立法国东北部五个池塘沉积物和食用鱼的农药污染概况。采用多残留方法和液相色谱-串联质谱分析,定量分析了 13 种农药(唑菌酯、多菌灵、氯唑草酮、氟咯草酮、二甲戊灵、氟草定、异丙隆、莠去津、甲磺隆、甲酰胺、异丙甲草胺、萘普胺和噻吩磺隆)。对 10 个沉积物和 143 个肌肉样本进行了分析,对应于两个连续的捕捞季节(第一次捕捞日期和第二次捕捞日期(P2),大约 1 年后)在五个地点(记为 C-0、C-25、C-45、C-75 和 C-85,以表达作物面积增加的梯度)。异恶草酮存在于所有沉积物样本中(1.8-56.4μg/kg 干重)。在 P2 期间,在 C-0 点的罗非鱼、鲤鱼和鲈鱼中定量检测到多菌灵(0.09±0.02、0.2±0.1 和 0.17±0.06μg/kg 湿重(ww))。仅在 C-25 点的鲈鱼中定量检测到甲酰胺(0.13±0.02μg/kg ww)。C-45 和 C-75 点的异恶草酮浓度相似,鲤鱼和鲈鱼的浓度分别为 0.4±0.1 和 0.75±0.06μg/kg ww。鱼类的污染总体上反映了周围环境的浓度。异恶草酮浓度最高,其主要来源是鲈鱼的水,而鲤鱼则通过水和沉积物暴露,突出了它们在池塘中的生活策略。