塑料及塑料添加剂环境管理的政策分析

我们现在所使用的塑料制品(如一次性餐具、塑料袋、家具和儿童玩具等)很可能含有多种有毒添加剂,使用再生塑料制造的物品中含有POPs物质。严格的风险管理法规和塑料再生分类利用规则的缺失,将让我们暴露于大量的有毒物质中！
废弃塑料及塑料添加剂的环境释放、环境行为和生态/健康危害的研究如何开展,包括我们特别关注的微塑料、塑料的阻燃剂添加剂等的研究进展;欧美对废弃塑料及塑料添加剂的环境管理政策及具体措施如何,我国有着怎样的环境管理策略和方法等等。欢迎您带着这些问题在本次讲座中寻找答案！
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有机微污染物在污水处理过程中的变化研究

多环芳烃等有毒有机微污染物对污水处理综合指标BOD、COD和TOC等的贡献极小,但危害却很大.采用固相萃取的前处理方法和GC/MS、GC/μECD的分析方法,针对北京市某污水处理厂的总泵进水、二沉出水以及混凝沉淀出水中有机氯农药、多环芳烃和酚类的浓度进行分析.研究结果表明,在不同处理工艺段中,有机氯农药、多环芳烃和酚类的质量浓度分别为nd～10、nd～835、nd～3 248 μg/L.所有检出化合物均未超出中国污水与地表水相应标准限值,其中多环芳烃和酚残留水平较高,应为重点监测对象.这些污染物多数能够在二级处理过程中得到有效去除,但混凝沉淀并没有显著地进一步去除效果.     

乙炔基雌二醇对稀有鮈鲫肾脏的毒性效应

研究了环境相关水平的人工合成雌激素乙炔基雌二醇对稀有鲫肾脏的慢性毒性.结果表明,当暴露浓度达到20ng·L-1以上时,稀有鲫的肾脏指数显著增大,具有明显的剂量效应关系,肾脏组织表现出明显的病理学特征,肾小管内腔扩大,严重出血,有的被一种嗜曙红物质所填充,肾小管壁的管状上皮细胞严重肿大并出现退化和坏死,肾小管之间的间隙组织大量出现.肾脏的肿大导致了畸形个体出现.因此乙炔基雌二醇不仅可以导致鱼类的内分泌干扰效应,而且可以引发严重的肾脏组织损伤;鱼的肾脏指数和肾脏病理学变化可以作为评价环境雌激素类化合物毒性效应的敏感指标;由于稀有鲫对雌激素类物质具有较高的敏感性,将其应用为污染监测的模型动物也是可能的.     

利用主动和被动采样技术和发光菌毒性测试评价水中有机污染物的毒性

提出利用能够模拟生物吸收过程的半渗透膜采样技术(SPMD)富集疏水性有机污染物,然后进行生物毒性测试．这一方法在原理上不同于传统主动富集．生物毒性测试技术体系,能够模拟生物富集和产生毒性的过程．用三油酸脂半渗透膜采样技术对洋河和北京市高碑店污水处理厂水样进行富集,并采用海洋发光菌P．phosphoreum T3和青海弧菌V．qinghainesis Q67发光菌对原水样和经过富集的水中有机污染物进行毒性测试．研究结果表明,洋河水中存在导致急性毒性的有机物,主要来自宣化工业区,以取代苯类化合物(如：硝基芳烃)为主,相比于此类物质,持久性有机污染物对急性毒性的贡献不大．对高碑店污水厂进行的实验表明,用发光菌方法直接测定污水,很难解释急性毒性变化规律．而采用SPMD技术富集水中有机污染物后进行毒性测试,结果和化学分析数据相当吻合．结合SPMD的优点,推荐用该方法作为环境有机有毒污染物毒性监测和生态风险评价的样品前处理手段．     

种群水平生态风险评价方法概述及其在环境管理中的应用

生态风险评价的目的是保护生态系统功能的完整性、稳定性和持久性,为环境风险管理提供理论依据。然而,目前常见的用于保护生物的化学污染物浓度阈值大多是以个体水平的毒性试验结果为基础,忽略了物种在时间和空间相互作用等因素,不能够完全保护生态环境安全和生态系统功能的延续性。本文从生态风险评价的概念、目的和意义引出种群水平生态风险评价在环境管理应用的重要性,综述了种群水平生态风险评价的科学问题(如密度依赖、遗传变异和空间结构等),归纳了种群水平风险评价主要模型方法及其应用(如Euler-Lotka方程、预测矩阵、个体模型、空间模型和动态能量预算模型等),列举了各国现有法律法规中关于种群水平生态风险评价的规定,以期为种群水平生态风险评价方法研究及在环境管理中的应用提供有益借鉴。     

不同地域人发中重金属污染特征与来源解析

以某高校新生发样为研究样本,将生源地分为东北、西北、西南、华北、华南、华中、华东7个地域,采用电感耦合等离子发射光谱法对发样中所含铬、铜、镍、铅、锌进行测定,通过非参数检验及偏相关性检验分析不同地区发样中重金属含量与性别、身体质量指数(BMI)的关系。结果显示,所采集发样中铬、铜、镍、铅、锌的含量变化范围依次为0.22~101.84、0.36~112.24、0.70~128.75、1.39~136.13、1.12~719.50μg/g;发样中重金属浓度的地区排序为东北>华东>华北>西北>华中>西南>华南。聚类分析和主成分分析结果显示,不同地区发样中重金属的来源有所差异:东北、西北、华北地区发样中重金属可能主要来源于燃煤、工业生产过程、机动车排放,方差贡献率分别为39.47%、25.78%、22.89%;华中、华东、西南、华南地区发样中重金属可能主要来源于工业生产过程、机动车排放、冶金化工过程,贡献率分别为47.76%、27.51%、18.24%。相关性检验显示,男性发样内铬、铜、镍、铅含量高于女性。其中,偏胖或偏瘦女性存在较高的铅暴露风险;40.2%的男性发锌含量低于正常值下限,24.4%的女性发锌含量低于正常值下限,且偏瘦女性发内缺锌现象显著;男、女发铜含量高于正常值上限的比例分别为91.8%、85.6%,存在不同程度的铜暴露风险。     

Evidence for the Stepwise Behavioral Response Model (SBRM): the effects of Carbamate Pesticides on medaka (Oryzias latipes) in an online monitoring system

The Stepwise Behavioral Response Model (SBRM), which is a conceptual model, postulated that an organism displays a time-dependent sequence of compensatory Stepwise Behavioral Response (SBR) during exposure to pollutants above their respective thresholds of resistance. In order to prove the model, in this study, the behavioral responses (BRs) of medaka (Oryzias latipes) in the exposure of Arprocarb (A), Carbofuran (C) and Methomyl (M) were analyzed in an online monitoring system (OMS). The Self-Organizing Map (SOM) was utilized for patterning the obtained behavioral data in 0.1 TU (Toxic Unit), 1 TU, 2 TU, 5 TU, 10 TU and 20 TU treatments with control. Some differences among different Carbamate Pesticides (CPs) were observed in different concentrations and the profiles of behavior strength (BS) on SOM were variable depending upon levels of concentration. The time of the first significant decrease of BS (SD-BS) was in inverse ratio to the CP concentrations. Movement behavior showed by medaka mainly included No effect, Stimulation, Acclimation, Adjustment (Readjustment) and Toxic effect, which proved SBRM as a time-dependence model based on the time series BS data. Meanwhile, it was found that SBRM showed evident stress-dependence. Therefore, it was concluded that medaka SBR was both stress-dependent and time-dependent, which supported and developed SBRM, and data mining by SOM could be efficiently used to illustrate the behavioral processes and to monitor toxic chemicals in the environment.     

Derivation of predicted no effect concentrations (PNEC) for 2,4,6-trichlorophenol based on Chinese resident species

2,4,6-Trichlorophenol (2,4,6-TCP) is a common chemical intermediate and a by-product of water chlorination and combustion processes, and is a priority pollutant of the aquatic environment in many countries. Although information on the toxicity of 2,4,6-TCP is available, there is a lack of information on the predicted no-effect concentration (PNEC) of 2,4,6-TCP, mainly due to the shortage of chronic and site-specific toxicity data. In the present study, acute and sub-chronic toxicity of 2,4,6-TCP on six different resident Chinese aquatic species were determined. PNEC values were calculated and compared by use of two approaches: assessment factor (AF) and species sensitivity distribution (SSD). Values for acute toxicity ranged from 1.1 mg L⁻¹ (Plagiognathops microlepis) to 42 mg L⁻¹ (Corbicula fluminea) and the sub-chronic no observed effect concentrations (NOECs) ranged from 0.05 mg L⁻¹ (Mylopharyngodon piceus) to 2.0 mg L⁻¹ (C. fluminea). PNECs obtained by the assessment factor approach with acute (AF = 1000, 0.001 mg L⁻¹) or chronic (AF = 10, 0.005 mg L⁻¹) toxicity data were one order of magnitude less than those from SSD methods (0.057 mg L⁻¹). PNEC values calculated using SSD methods with a 50% certainty for 2,4,6-TCP was less than those obtained by use of the USEPA recommend final chronic value (FCV) method (0.097 mg L⁻¹) and the one obtained by use of the USEPA recommend acute-to-chronic (ACR) methods (0.073 mg L⁻¹). PNECs derived using AF methods were more protective and conservative than that derived using SSD methods.     

Derivation of aquatic predicted no-effect concentration (PNEC) for 2,4-dichlorophenol: comparing native species data with non-native species data

2,4-Dichlorophenol (2,4-DCP) is known as an important chemical intermediate and an environmental endocrine disruptor. There is no paper dealing with the predicted no-effect concentration (PNEC) of 2,4-DCP, mainly due to shortage of chronic and site-specific toxicity data. In the present study, toxicity data was obtained from the tests using six Chinese native aquatic species. The HC₅ (hazardous concentration for 5% of species) was derived based on the constructed species sensitivity distribution (SSD), which was compared with that derived from literature toxicity data of non-native species. For invertebrates, the survival no-observed effect concentrations (NOECs) were 0.05 and 1.00 mg L⁻¹ for Macrobrachium superbum and Corbicula fluminea, respectively. NOECs based on fishes’ growth were 0.10, 0.20 and 0.40 mg L⁻¹ for Mylopharyngodon piceus, Plagiognathops microlepis and Erythroculter ilishaeformis, respectively. For aquatic plant Soirodela polyrhiza, NOEC based on concentration of chlorophyll was 1.00 mg L⁻¹. A final PNEC calculated using the SSD approach with a 50% certainty based on different taxa ranged between 0.008 and 0.045 mg L⁻¹. There is no significant difference between HC₅ derived from native and that from non-native taxa.     

Effects of estrone on the early life stages and expression of vitellogenin and estrogen receptor genes of Japanese medaka (Oryzias latipes)

The fertilized eggs of Japanese medaka (Oryzias latipes) were exposed to estrone (E1) at 5–5000 ng L⁻¹ for 15 d, and the hatched fry were exposed continuously to the same concentrations for the additional 15 d. Adverse effects on hatchability, time to hatching, and gross abnormalities occurred at 50 ng L⁻¹ or above. Then the fry were divided into a continual exposure group, and a water recovery group. When the fry were exposed to E1 for another 60 d, there was a decrease in the hepatosomatic index (HSI) of males and the influence disappeared in the water recovery group. The gonadosonatic index (GSI) of females at 500 ng L⁻¹ decreased significantly in another 60 d exposure. While the fry were maintained in dechlorinated tap water for 60 d, a significant decrease in female GSI was observed at 50 ng L⁻¹ or above. An increased GSI was found in males in both continual exposure and water recovery groups at all E1 treatments. Quantitative RT-PCR showed that vitellogenin-I (Vtg-I) gene expressions in the female liver were significantly down-regulated at 50 ng L⁻¹ in the continual exposure group, and at 500 ng L⁻¹ in the water recovery group, while male Vtg-I genes were significantly up-regulated for all E1 treatments. In addition, all E1 treatments caused sex reversal of males. These results suggest that E1 at 5 ng L⁻¹ or above have unrecoverable impacts on the gonadal growth and development of medaka, even if only early life stages were exposed to E1.