纳米银的生物分布及其影响因素研究进展

纳米银(AgNPs)以其独特的抗菌性能在生物医药和消费品中得到大量应用。然而,随着人类接触AgNPs的机会增多,AgNPs暴露的潜在危害也不容忽视。体内研究表明,AgNPs可以通过经口、呼吸、腹腔、静脉等途径进入机体,进而通过血液或淋巴液的流动分散到全身不同组织器官。而不同的暴露方式、暴露剂量、AgNPs粒径、表面包被和电荷以及暴露器官本身的特点可能对AgNPs在体内的分布与蓄积产生影响。因此,本文系统地总结了AgNPs进入生物体的途径及其在生物体内的组织分布,讨论了影响AgNPs体内生物分布和蓄积的因素。     

经皮肤暴露四溴双酚A对Wistar雄性大鼠的毒性效应

尘/土以及含阻燃剂产品的皮肤接触是四溴双酚A(TBBPA)重要的人体暴露途径。为研究TBBPA经皮肤亚慢性暴露毒性效应,选择无特定病原菌级别(SPF级)Wistar雄性大鼠作为受试生物,分别设空白对照组(K)、溶剂对照组(Z),以及20mg·kg~(-1)(A)、60 mg·kg~(-1)(B)、200 mg·kg~(-1)(C)、600 mg·kg~(-1)(D)共4个不同剂量的TBBPA暴露组,采用皮肤接触的方式连续暴露90 d。暴露期间观察大鼠状态并称重,于第91天解剖大鼠,分离主要脏器称重计算脏器系数,并对暴露皮肤进行组织病理学检查。研究发现,经皮肤暴露TBBPA后,90 d暴露期间不同实验组Wistar大鼠在表观形态、行动、进食方面无差异,TBBPA暴露导致大鼠体重略微降低,但各处理组间大鼠体重无显著差异;90 d暴露后不同剂量组间大鼠的器官脏器系数没有显著的剂量-效应关系,不同剂量组大鼠皮肤暴露区域均有一定程度的炎症细胞浸润及部分组织胶原间隙增宽。研究结果表明,TBBP A 90 d亚慢性皮肤暴露对Wistar大鼠无明显毒性效应。     

团头鲂谷胱甘肽S-转移酶基因的克隆及其在氨氮胁迫中的表达分析

谷胱甘肽S-转移酶(glutathione S-transferase,GST)是一类多功能蛋白家族,主要参与解毒和抗氧化防御过程。为了研究GST在团头鲂(Megalobrama amblycephala)肝脏解毒过程中的作用,克隆并分析了团头鲂1个谷胱甘肽S-转移酶基因(命名为MaGST)cDNA序列,采用实时荧光定量PCR研究了其在氨氮胁迫下的表达规律。MaGST包含1个长218个氨基酸的完整开放阅读框,具有GST蛋白家族的保守碱基和保守结构域。通过MEGA 5.0软件分析系统进化树发现,团头鲂GST与其他动物mu型GST聚为一簇,表明团头鲂GST属于mu型GST。荧光定量PCR结果显示MaGST基因在团头鲂各组织中均有表达,在肝脏和鳃中表达量最高,肌肉中表达量最低,同时在氨氮胁迫过程中该基因在肝和鳃中的表达规律相似,均在胁迫期间表达量显著上调;氨氮胁迫24 h时鳃和肝组织均存在组织损伤。研究结果提示在团头鲂肝脏和鳃组织中GST基因参与了氨氮胁迫的解毒过程。将该基因的编码区重组到p ET-21(a+)载体后在大肠杆菌中得到诱导表达,重组MaGST的GST活力为(10.36±0.68)U·mg~(-1)蛋白。     

北京海淀区夏季交警对多环芳烃的暴露

用个人采样装置测定了北京海淀区交警夏季多环芳烃(PAHs)暴露.以16种PAHs之和计,气态和颗粒物吸附态的平均暴露浓度分别为(1 520±759)ng/m³和(148±118)ng/m³,显著高于定点对照测定结果[气态(588±228)ng/m³,颗粒物吸附态(52±50)ng/m³].交警和对照点具有致癌作用的高环化合物总暴露浓度分别是(14.9±5.9)ng/m³和(6.7±3.6)ng/m³,主要来自颗粒物吸附态暴露.暴露量具有显著的日波动特征,主要受温度和湿度影响.气态浓度与湿度正相关,与温度负相关,颗粒物吸附态浓度则与温度和湿度看不到显著相关关系.     

化学品环境暴露评估模型研究进展

各国政府高度重视化学品生产使用引发的环境问题,研发了一系列环境暴露预测模型,包含了点源暴露到面源暴露各种排放模式,局部暴露、区域暴露及洲际暴露的各种预测尺度,筛选评估到确认水平的不同评估层级,用于评估化学品的潜在风险。本文从模型功能、机理出发,综述了化学品环境暴露评估涉及的排放估计、水/土/气、多介质以及食物链评估模型,以期为推动我国化学品环境暴露模型的研发提供参考。     

典型氯碱污染场地环境风险评价

以广东某氯碱化工污染场地为研究区域,采集了场地22个土壤及地下水样品,分析了25项污染物在不同区域的分布特征及其来源。监测结果表明,煤炭堆场与锅炉房区土壤受重金属铅、镍污染。六六六、四氯化碳、三氯甲烷、六氯苯、苯是场地的特征污染物,主要分布在危险品仓库、漂洗车间与四氯化碳车间。根据监测结果开展了不同暴露途径致癌风险值及非致癌危害商的计算。结果表明,部分样品表层土壤中上述有机污染物的基于人体健康致癌风险指数均超过10-6,最高达到1.65×10-2,表明风险水平高;非致癌危害在各暴露途径下也超过可接受值1,最高达5.59×104,表明风险水平高。说明对于存在高风险的区域必须进行采取合适的措施进行修复,减缓场地再利用后对人群健康的影响。     

镉在方斑东风螺组织内的蓄积及镉的毒性：水相暴露与食物相暴露比较

为比较直接经水体与经营养传递的2种镉(cadmium,Cd)暴露方式对方斑东风螺(Babylonia areolata)不同组织Cd蓄积和毒性的差异,采用室内模拟法,将螺暴露于含Cd水体(Cd2+:100μg·L-1)或喂食含Cd饵料(牡蛎,34.56μg·g-1以干质量计,先经水体100μg·L-1Cd2+暴露达平衡)30d后再进行15d净化。结果显示,暴露期间,除食物相组螺胃肠道Cd浓度在第10天极显著高于对照组,但随后迅速下降外,其他各组织在2种途径及胃肠道在水相暴露时Cd的浓度均逐渐上升,暴露30d后肝胰脏中Cd浓度最高;净化期,螺鳃中Cd排出率较高,胃肠道与肝胰脏的排出率较低,至净化期末除食物相组鳃中Cd浓度与对照组无显著差异外,2种处理中其他各组织Cd浓度仍显著高于对照组。2种暴露途径中金属硫蛋白(metallothionein,MT)浓度仅在螺肝胰脏中逐渐增加,且与Cd的蓄积呈显著线性正相关。与食物相组相比,水相Cd暴露引起螺肝胰脏脂质过氧化水平(lipid peroxidation,LPO)更高,且内脏团中Cd与其亚细胞成分的金属敏感组分结合的百分比也更高。结果表明,Cd通过营养传递对螺产生的毒性较水体直接暴露低,但摄食是螺蓄积Cd的主要途径;净化后除鳃外水相暴露组螺各组织Cd的排出率较低;因此为了健康养殖与食用安全,东风螺工厂化养成时对饵料与水体Cd浓度的监测均应引起足够的重视。     

Poly- and perfluorinated compounds in household consumer products

Several household consumer products were analyzed for their content of perfluorooctanoate (PFOA), perfluorooctane sulfonate (PFOS), and fluorotelomer alcohols (FTOH) by nanoflow ultra performance liquid chromatography – mass spectrometry and gas chromatography – mass spectrometry. Among the investigated products, which are applied as sprays, were impregnating agents, cleaning agents, lubricants, and conditioners. In 14 of the 26 products analyzed, at least one polyfluorinated compound (PFC) was detected in 14 samples. 8?:?2 FTOH was the dominating PFC with concentrations up to 149?µg?mL^?1. The maximum concentration of PFOA was 14.5?µg?mL^?1, whereas PFOS was not detected in any sample. Investigated PFCs were mostly found in impregnating agents and lubricants, but were not detected in cleaning agents and conditioners. In FTOH-containing impregnating agents, similar ratios between 6?:?2 FTOH, 8?:?2 FTOH, and 10?:?2 FTOH were found. FTOH proportions in PFC-containing lubricants were similar as well. Total human exposure to PFC from consumer product aerosols for three different scenarios was estimated to be between 42.8 and 464?ng?kg^?1?per day.     

Chemical cocktail party in East Greenland: A first time evaluation of human organohalogen exposure from consumption of ringed seal and polar bear tissues and possible health implications

East Greenland polar bears (Ursus maritimus) are among the mammals with the highest bioaccumulated concentrations of organohalogen contaminants (OHCs). Since Greenlanders in this region ingest significant quantities of adipose tissue from polar bears and also ringed seals (Pusa hispida), initial conservative estimates of the daily oral exposure to this chemical cocktail are thus presented. The tolerable daily intake was exceeded approximately five-fold for polychlorinated biphenyls and chlordane pesticides and metabolites, while the estimated daily toxic equivalent (TEQ) (based on the 2,3,7,8-tetrachlorodibenzo-rho-dioxin toxicity equivalence factors) for East Greenland subsistence hunters was three- to ten-fold higher than the WHO ∑TEQ guidelines even though the estimations were conservative. The daily oral OHC exposure from polar bear and ringed seal blubber consumption is markedly high and needs to be reduced in order to remove this co-factor with respect to the influence on the development of chronic diseases. Furthermore, it is warranted that a physiologically based pharmacokinetic model for Greenlander's exposure to OHCs is constructed and that risk quotients calculated to estimate the threats to health for East Greenland subsistence hunters.     

The international toxicity equivalency factor (I‐TEF) method for estimating risks associated with exposures to complex mixtures of dioxins and related compounds∗

The International Toxicity Equivalency Factor (I‐TEF) method of risk assessment is a revised interim procedure for assessing the risks associated with exposures to complex mixtures of chlorinated dibenzo‐p‐dioxins and dibenzofurans (CDDs and CDFs). This updated scheme was developed by a working group of the North Atlantic Treaty Organization's Committee on the Challenges of Modern Society and has been officially adopted by the U.S. Environmental Protection Agency (EPA), Canada, Ontario Ministry of the Environment, the Nordic countries, the Netherlands, and the United Kingdom. Prior to the development of the I‐TEF method, at least ten slightly different schemes had been used throughout the world which complicated communication among scientists and regulatory agencies concerning the toxicological significance of complex mixtures of CDDs and CDFs. The I‐TEF approach facilitates risk communication internationally by reducing large volumes of analytical data into a single number‐International Toxicity Equivalents (I‐TEQ). As a result, the I‐TEF method represents an improvement in an already useful risk assessment/regulatory tool.