Unité des microorganismes d'intérêt laitier et alimentaire EA 3213, UFR ICORE 146, Université de Caen-Basse Normandie, 14032, Caen Cedex 5, France.
Rev Environ Contam Toxicol. 2011;213:55-111. doi: 10.1007/978-1-4419-9860-6_3.
In this review, we address the identification of residual chemical hazards in shellfish collected from the marine environment or in marketed shellfish. Data, assembled on the concentration of contaminants detected, were compared with the appropriate regulatory and food safety standards. Moreover, data on human exposure and body burden levels were evaluated in the context of potential health risks.Shellfish farming is a common industry along European coasts. The primary types of shellfish consumed in France are oysters, mussels, king scallops, winkles,whelks, cockles, clams, and other scallops. Shellfish filter large volumes of water to extract their food and are excellent bioaccumulators. Metals and other pollutants that exist in the marine environment partition into particular organs, according to their individual chemical characteristics. In shellfish, accumulation often occurs in the digestive gland, which plays a role in assimilation, excretion, and detoxification of contaminants. The concentrations of chemical contaminants in bivalve mollusks are known to fluctuate with the seasons.European regulations limit the amount and type of contaminants that can appear in foodstuffs. Current European standards regulate the levels of micro-biological agents, phycotoxins, and some chemical contaminants in food. Since 2006, these regulations have been compiled into the "Hygiene Package." Bivalve mollusks must comply with maximum levels of certain contaminants as follows:lead (1.5 mg kg-1), cadmium (1 mg kg-1), mercury (0.5 mg kg-1), dioxins (4 pg g-1 and dioxins + DL-PCBs 8 pg g-1), and benzo[a]pyrene (10 μp.g kg-1).In this review, we identify the levels of major contaminants that exist in shellfish(collected from the marine environment and/or in marketed shellfish). The follow-ing contaminants are among those that are profiled: Cd, Pb, Hg, As, Ni, Cr, V,Mn, Cu, Zn, Co, Se, Mg, Mo, radionuclides, benzo[a]pyrene, PCBs, dioxins and furans, PAHs, TBT, HCB, dieldrin, DDT, lindane, triazines, PBDE, and chlorinated paraffins.In France, the results of contaminant monitoring have indicated that Cd, but not lead (< 0.26 mg kg-1) or mercury (< 0.003 mg kg-1), has had some non-compliances. Detections for PCBs and dioxins in shellfish were far below the regulatory thresholds in oysters (< 0.6 pg g-l), mussels (< 0.6 pg g-1), and king scallops (< 0.4 pg g-1). The benzo[a]pyrene concentration in marketed mussels and farmed shellfish does not exceed the regulatory threshold. Some monitoring data are available on shellfish flesh contamination for unregulated organic contaminants.Of about 100 existing organo stannic compounds, residues of the mono-, di-, and tributyltin (MBT, DBT, and TBT) and mono-, di-, and triphenyltin (MPT, DPT,and TPT) compounds are the most frequently detected in fishery products. Octyltins are not found in fishery products. Some bivalve mollusks show arsenic levels up to 15.8 mg kg-1. It seems that the levels of arsenic in the environment derive less from bioaccumulation, than from whether the arsenic is in an organic or an inorganic form. In regard to the other metals, levels of zinc and magnesium are higher in oysters than in mussels.To protect shellfish from chemical contamination, programs have been established to monitor water masses along coastal areas. The French monitoring network(ROCCH) focuses on environmental matrices that accumulate contaminants. These include both biota and sediment. Example contaminants were studied in a French coastal lagoon (Arcachon Bay) and in an estuary (Bay of Seine), and these were used to illustrate the usefulness of the monitoring programs. Twenty-one pesticidal and biocidal active substances were detected in the waters of Arcachon Bay during the summers from 1999 to 2003, at concentrations ranging from a few nanograms per liter to several hundred nanograms per liter. Most of the detected substances were herbicides, including some that are now banned. Organotin compounds have been detected in similarly semi-enclosed waters elsewhere (bays, estuaries, and harbors).However, the mean concentrations of cadmium, mercury, lead, and benzo[a]pyrene,in transplanted mussels, were below the regulatory limits.In 2007, the mean daily consumption of shellfish in the general French population was estimated to be 4.5 g in adults; however, a wide variation occurs by region and season (INCA 2 study). Tabulated as a proportion of the diet, shellfish consumption represents only 0.16% of overall solid food intake. However, the INCA 2 survey was not well suited to estimating shellfish consumption because of the small number of shellfish consumers sampled. In contrast, the mean consumption rate of bivalve mollusks among adult high consumers of fish and seafood products, i.e., adults who eat fish or seafood at least twice a week, was estimated to be 153 g week-1 (8 kg yr-1). The highest mean consumption is for king scallops (39 g week-1), followed by oysters (34 g week-1) and mussels (22 g week-1). Thus, for high seafood consumers, the contribution of shellfish to inorganic contaminant levels is 1-10% TWI or PTWI for Cd, MeHg, and Sn (up to 19% for Sn), and the arsenic body burden is higher for 22% of individuals studied.The human health risks associated with consuming chemical contaminants in shellfish are difficult to assess for several reasons: effects may only surface after long-term exposure (chronic risk), exposures may be discontinuous, and contamination may derive from multiple sources (food, air, occupational exposure, etc.).Therefore, it is not possible to attribute a high body burden specifically to shellfish consumption even if seafood is a major dietary contributor of any contaminant, e.g.,arsenic and mercury.The data assembled in this review provide the arguments for maintaining the chemical contaminant monitoring programs for shellfish. Moreover, the results presented herein suggest that monitoring programs should be extended to other chemicals that are suspected of presenting a risk to consumers, as illustrated by the high concentration reported for arsenic (in urine) of high consumers of seafood products from the CALIPSO study. In addition, the research conducted in shellfish-farming areas of Arcachon Bay highlights the need to monitor TBT and PAH contamination levels to ensure that these chemical pollutants do not migrate from the harbor to oyster farms.Finally, we have concluded that shellfish contamination from seawater offers a rather low risk to the general French population, because shellfish do not constitute a major contributor to dietary exposure of chemical contaminants. Notwithstanding,consumer vigilance is necessary among regular shellfish consumers, and especially for those residing in fishing communities, for pregnant and breast-feeding women,and for very young children.
在这篇综述中,我们将讨论从海洋环境中采集的贝类或市场销售的贝类中残留化学污染物的识别问题。我们将比较检测到的污染物浓度数据与适当的监管和食品安全标准。此外,还评估了人体接触和体内负荷水平与潜在健康风险之间的关系。贝类养殖是欧洲沿海地区的常见产业。法国消费的主要贝类包括牡蛎、贻贝、扇贝、海胆、海扇、蛤蜊、蛤和其他扇贝。贝类通过大量过滤水来提取食物,是极好的生物蓄积剂。存在于海洋环境中的金属和其他污染物根据其各自的化学特性分配到特定的器官中。在贝类中,积累通常发生在消化腺中,该器官在污染物的吸收、排泄和解毒中起作用。双壳贝类中化学污染物的浓度已知随季节而波动。
欧洲法规限制了食品中出现的污染物数量和类型。目前的欧洲标准规定了食品中的微生物、藻毒素和某些化学污染物的水平。自 2006 年以来,这些法规已被纳入“卫生一揽子计划”。双壳贝类必须符合某些污染物的最高限量,如下所示:铅(1.5 毫克/千克)、镉(1 毫克/千克)、汞(0.5 毫克/千克)、二恶英(4 皮克/克和二恶英+ DL-PCBs8 皮克/克)和苯并[a]芘(10 微克/千克)。
在这篇综述中,我们确定了贝类(从海洋环境中采集或市场销售的贝类)中存在的主要污染物的水平。以下是被 profiling 的污染物:Cd、Pb、Hg、As、Ni、Cr、V、Mn、Cu、Zn、Co、Se、Mg、Mo、放射性核素、苯并[a]芘、多氯联苯、二恶英和呋喃、多环芳烃、三丁基锡(TBT)、六氯苯(HCB)、狄氏剂、滴滴涕、林丹、三嗪、PBDE 和氯化石蜡。
在法国,污染物监测的结果表明,Cd 而不是铅(<0.26 毫克/千克)或汞(<0.003 毫克/千克)存在违规情况。在牡蛎(<0.6 皮克/克)、贻贝(<0.6 皮克/克)和扇贝(<0.4 皮克/克)中,贝类中检测到的多氯联苯和二恶英均远低于监管阈值。市场销售的贻贝和养殖贝类中苯并[a]芘的浓度未超过监管阈值。有关未受监管的有机污染物的贝类肉污染的一些监测数据是可用的。
在约 100 种现有的有机锡化合物中,单、二和三丁基锡(MBT、DBT 和 TBT)以及单、二和三苯基锡(MPT、DPT 和 TPT)化合物的残留物是在渔业产品中最常检测到的。辛基锡在渔业产品中不存在。一些双壳贝类的砷含量高达 15.8 毫克/千克。似乎环境中的砷水平与其是否以有机或无机形式存在关系不大,而更多地来自生物蓄积。关于其他金属,牡蛎中的锌和镁水平高于贻贝。
为了防止贝类受到化学污染,已经建立了计划来监测沿沿海地区的水体。法国监测网络(ROCCH)侧重于积累污染物的环境基质。这些基质包括生物区系和沉积物。在法国沿海泻湖(阿卡雄湾)和河口(塞纳河河口)研究了一些典型污染物,这些研究说明了监测计划的有用性。在 1999 年至 2003 年夏季,在阿卡雄湾的水中检测到了 21 种农药和生物杀灭剂活性物质,浓度范围从几纳克/升至数百纳克/升。检测到的大多数物质都是除草剂,包括一些已被禁用的物质。在其他半封闭水域(海湾、河口和港口)也检测到有机锡化合物。
然而,移植贻贝中的镉、汞、铅和苯并[a]芘的平均浓度均低于监管限值。
2007 年,法国普通人群中贝类的平均每日消费量估计为成年人 4.5 克;然而,地区和季节之间存在很大差异(INCA2 研究)。贝类消费占固体食物总摄入量的比例列入表中,仅为 0.16%。然而,INCA2 调查不太适合估计贝类消费,因为抽样的贝类消费者数量较少。相比之下,每周至少食用两次鱼类或海鲜产品的成年高海鲜消费者中双壳贝类的平均消费率估计为 153 克/周(8 公斤/年)。最高的平均消费是扇贝(39 克/周),其次是牡蛎(34 克/周)和贻贝(22 克/周)。因此,对于高海鲜消费者来说,贝类对无机污染物水平的贡献为 Cd、MeHg 和 Sn 的 TWI 或 PTWI 的 1-10%(Sn 高达 19%),并且 22%的研究个体的砷体负荷更高。
由于以下原因,很难评估食用贝类中的化学污染物对人体健康的风险:影响可能仅在长期暴露(慢性风险)后显现,暴露可能是不连续的,并且污染可能来自多个来源(食物、空气、职业暴露等)。
因此,即使海鲜是任何污染物(例如砷和汞)的主要饮食来源,也不能将高身体负荷专门归因于贝类消费。
本综述中汇编的数据提供了维持贝类化学污染物监测计划的论据。此外,本文所述的结果表明,监测计划应扩展到其他被怀疑对消费者构成风险的化学物质,例如,CALIPSO 研究中报告的高海鲜消费者尿液中高浓度的砷。此外,在阿卡雄湾贝类养殖区进行的研究强调了监测 TBT 和多环芳烃污染水平的必要性,以确保这些化学污染物不会从港口迁移到牡蛎养殖场。
最后,我们得出结论,贝类受海水污染对法国普通人群的风险相对较低,因为贝类在饮食中接触化学污染物的程度并不高。尽管如此,对于经常食用贝类的消费者,尤其是居住在渔业社区、孕妇和哺乳期妇女以及非常年幼的儿童,消费者应保持警惕。