意大利东部皮埃蒙特地区羚羊和野猪环境污染物的初步研究。

F. Ceriani, L. Chiesa, S. Panseri, F. Arioli
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引用次数: 0

摘要

有机氯农药(ocp)和多氯联苯(PCBs)是被归类为持久性有机污染物的合成氯化化合物,而《斯德哥尔摩公约》(2005年《斯德哥尔摩公约》)只有五溴四溴多溴联苯醚(PBDEs)被这样定义,以消除或限制持久性有机污染物的使用。有机磷杀虫剂是重要的环境和食品污染源,在农业中应用广泛。在多环芳烃(PAHs)中,苯并[a]芘被IARC列为第1组致癌物,苯并[a]芴被IARC列为2B组可能致癌物(IARC, 2012;研究,2010)。欧洲食品安全局(EFSA)发布了一份关于食品中存在的溴化阻燃剂对公众健康的风险的科学意见(EFSA, 2011年),2014年欧洲委员会要求成员国在未来两年内监测食品中存在的溴化阻燃剂(BFRs)(欧盟委员会,2014年)。由于它们的正辛醇/水分配系数(log K ow),它们在较高营养水平的动物体内积聚在脂肪组织、生物浓缩物和生物放大,通过长期接触可能导致内分泌紊乱和癌症(Wania等人,1995;Vallack et al., 1998)。本研究的目的是评估意大利东部皮埃蒙特羚羊和野猪中OCPs、多氯联苯、多溴二苯醚和多环芳烃的含量。2017年狩猎季节,从Verbania Cusio Ossola (VCO)共收集了20份岩羚羊和20份野猪肌肉样本(图1)。使用QuEChERS技术纯化和提取的肌肉样本采用GC-MS/MS进行化学分析,检测OCPs、多氯联苯、多溴二苯醚和多环芳烃,并根据SANTE 2017 (SANTE/11183/2017)进行验证。这些初步结果表明所研究的污染物普遍存在。岩羚羊(45%)体内多氯联苯的含量高于野猪(35%)。在野猪中未检测到多溴二苯醚,但在羚羊中发现多溴二苯醚,患病率为35%,浓度为0.25 ~ 1.52 ng g -1。在野猪(55% ~ 15%)和羚羊(32% ~ 35%)中发现的OCPs中,磷和磷的浓度范围为0.21 ~ 20.1 ng g -1。除1份野猪样品检出蒽(0.53 ng g -1)外,未检出多环芳烃。为了将环境污染与狩猎动物联系起来,进一步的研究正在进行中。
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Preliminary studies on environmental pollutants in chamois and wild boar from Eastern Piedmont, Italy.
Organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs) are synthetic chlorinated compounds classified as POPs whereas only the penta e tetra-brominated polybromodiphenyl ethers (PBDEs) are so defined by the Stockolm Convention (Stockholm Convention, 2005) in order to elimitate or restrict the use of POPs. Organophosphorus insecticides (OCPs) represent important environmental and food contamination sources, widely used in agriculture. Among polyciclic aromatic hydrocarbons (PAHs), benzo[a]pirene is classified by IARC in Group 1, as cancerogen  and Benzo[a]fluoranthene as a Group 2B, as possible cancerogen (IARC, 2012; IARC, 2010).  EFSA (European Food Safety Authority) has released a scientific opinion on the risks to public health related to the presence of brominated flame retardants in food (EFSA, 2011) and in 2014 European commission has asked Member States to monitor the presence of brominated flame retardants (BFRs) in food over the next two years (EC, 2014). Due to their heir n-octanol/water partition coefficient (log K ow ), they accumulate in fat tissue, bioconcentrate and biomagnify in the animals at the higher trophic levels, possibly causing, through chronic exposure, endocrine disruption and cancer (Wania et al., 1995; Vallack et al., 1998). The aim of this study is to evaluate the presence of OCPs, PCBs, PBDEs and PAHs in chamois and wild boar from Eastern Piedmont, Italy. A total of 20 chamois and 20 wild boar muscle samples were collected during the hunting season 2017, from Verbania Cusio Ossola (VCO) (Fig 1). The chemical analysis for the detection of OCPs, PCBs, PBDEs, and PAHs   was performed by GC-MS/MS on muscle samples purified and extracted using a QuEChERS technique, validated according to SANTE 2017 (SANTE/11183/2017). These preliminary results show the ubiquitary presence of the studied contaminants. PCBs have been found more in chamois (45%) than in wild boar (35%). No PBDEs were detected in wild boar but in chamois were found with a prevalence of 35%  and  concentration 0.25-1.52 ng g -1 . About OCPs, phorate and demeton were found in wild boar (55%-15%) and chamois (32%- 35%) with range concentrations 0.21-20.1 ng g -1 . No PAHs were detected, expect antharacene for one samples in wild boar (0.53 ng g -1 ). Further studies are in progress in order to correlate environmental contamination and game animals.
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