长江口九段沙水域有机氯农药分布

对九段沙（HCHs）水域采集滩涂水样以及沉积物，进行GC-ECD检测，研究有机氯农药的分布。结果表明，九段沙水域水体中六六六含量为6．6～17．1ng／L，平均值9．93ng／L，滩涂沉积物中的六六六含量为2．32～6．30ng／g；九段沙水域水体中滴滴涕（DDTs）含量4．99～46．6ng／L，平均值为18．53ng／L，滩涂泥样中的滴滴涕（DDTs）含量5．9～70．83ng／g。从异构体成分分析，九段沙水域受到了陆上林丹使用的影响，但是东海海水的冲刷能降低林丹所占六六六含量的比例；另外滴滴涕则显示较早期的污染，表现为代谢物（DDD和DDE）含量较高的现象，同时调查发现该水域在近期可能有滴滴涕输入。     

环境税收对墨西哥杀虫剂的影响

一种最理想的杀虫剂税将按照毒性程度对市场销售的物质加以区分．在墨西哥采取这一税收是准备将来扩展按照国际协议逐步淘汰并最终消除的杀虫剂名单的最有效的方法．本文分析了三种不同的环境征税方案的内涵：对所有的杀虫剂普遍征税15％（弥补目前免征增值税的状况）；根据毒性分别征税15％、10％、5％或者0％；对现在经审定的毒性最大的物质征税10%，税收必须用于恢复人类和生态系统健康以及赔付其他类型的损害。     

有机氯农药与乳腺癌发病的环境流行病学研究

为探讨乳腺癌发病与有机氯农药污染的关系,采用分阶段整群随机抽样的方法,按乳腺癌标化发病率高低抽取11个乡镇,再随机抽取行政村、自然村.测定各乡镇大米和土壤样品中有机氯各指标的含量,结合各乡镇的乳腺癌发病资料,进行统计分析.结果表明,各乡镇的乳腺癌标化发病率存在统计学显著性差异;大米中d-HCH、g-HCH、五氯酚钠以及土壤的d-HCH含量在各乡镇间有显著性差异;乳腺癌标化发病率与大米中PP-DDD含量呈负相关,相关系数为-0.609.说明经过近20年的降解过程,DDT的衍生物含量最终以PP-DDD居多,并且乳腺癌标化发病率与大米中PP-DDD含量呈负相关.     

珠江澳门河口沉积物柱样中有机氯农药的垂直分布特征

以GC/ECD内标法定量测定了沉积物柱样品中有机氯农药含量 ,以便探讨柱样中有机氯农药的垂直变化特征及可能的来源 .样品采自珠江澳门河口 ,柱样以2 10 Pb同位素法定年 .定量测定结果表明以BHCs、DDTs总量计算时 ,样品中含量分别为 0 4 8～ 2 6 2 8ng/ g、1 92～ 39 1 3ng/ g .柱样中农药含量随深度变化和珠江口区的水域水流量随年份的变化有着很好的对应性 .有机氯农药主要是来源于施用农药长期风化后的土壤 .样品中DDTs的浓度超过了河口沉积物化学品风险评价最低值标准 .     

无锡鼋头渚夜鹭卵中有机氯农药残留及其环境指示意义

分析了太湖鼋头渚夜鹭卵中的有机氯农药残留情况,发现在禁用近20年后,HCH的异构体、DDT及其代谢物、异狄氏剂以及环氧七氯在夜鹭卵中都不有同程度的检出,其中β－HCH和p,p‘-DDE的残留水平和检出率均很高,p,p‘-DDE平均达到了0.906ug/g(干重）。研究发现无锡夜鹭卵中多数有机氯农药残留水平平均高于江西共青城地区的样品。无锡夜鹭卵孵化率较低。可能与DDE残留量较高有关。夜鹭卵中有机氯农药残留水平具有指示环境污染的意义。     

有机氯类农药在残留剂量下联合诱导乳腺癌MCF-7细胞增殖的机制研究

有机氯类农药为已确定的环境雌激素,易在体内蓄积产生慢性毒性危害人体健康。选择单一存在时无明显雌激素效应的残留剂量进行联合试验,观察联合作用后雌激素效应的增减。选取乳腺癌MCF-7细胞作为研究对象,对残留剂量下六氯苯(HCB)、β-六六六(β-BHC)和p,p’-滴滴涕(p,p’-DDT)联合后的雌激素效应机制进行了研究。首先,运用MTT法观察3种有机氯类农药残留剂量下单独和联合作用对MCF-7细胞生长的影响;然后,运用流式细胞仪测定有机氯类农药联合对MCF-7细胞周期的影响;之后,采用Western Blot法测定有机氯类农药联合后ERα、ERβ、ERK1/2、p-ERK1/2、Ki67、c-Myc和Cyclin D1蛋白表达的变化。结果显示,β-BHC+p,p’-DDT组、HCB+β-BHC+p,p’-DDT组作用24 h后细胞增殖率为115.0%、120.1%,作用48 h后增殖率为121.2%、126.3%,其他联合组与对照相比未发生明显变化;β-BHC+p,p’-DDT组、HCB+β-BHC+p,p’-DDT组中MCF-7细胞的G1期细胞比例下降,S期细胞比例上升,细胞呈高增殖状态;β-BHC+p,p’-DDT组、HCB+β-BHC+p,p’-DDT组和雌二醇(E2)组作用48 h后,均降低ERα的蛋白表达,升高ERβ的蛋白表达,促进p-ERK1/2、Ki67、Cyclin D1和c-Myc的蛋白表达。研究表明,在单一作用时不具有雌激素效应的残留剂量下,仅β-BHC+p,p’-DDT联合组和HCB+β-BHC+p,p’-DDT联合组具有明显雌激素效应,其效应机制为经雌激素受体途径,激活ERβ蛋白表达,抑制ERα蛋白表达,促进p-ERK1/2、Ki67、c-Myc和Cyclin D1等相关蛋白的表达。     

气相色谱-离子阱-多级质谱法测定土壤中14种有机氯农药

有机氯农药（Organochlorine Pesticides,OCPs）是一类重要的难降解有机污染物,对土壤中这类农药的监测和研究非常必要,但土壤中有机氯农药残留前处理方法大多步骤繁琐,耗时耗溶剂,土壤样品的前处理远比液体和蔬菜等样品复杂,且在很大程度上样品的前处理决定着分析结果的准确性和可靠性.     

ASE 快速溶剂萃取仪提取持久性有机污染物（POPs）的应用（一）

持久性有机污染物（POPs）是指具有高毒性、生物蓄积型和半挥发性、在环境中持久存在且能在大气中长距离迁移并沉积回地球的极地地区,对人类监控和环境造成严重危害的有机化学污染物,1997年,联合国环境规划署决定对12种POPs物质立即采取行动减少或消除它们的产生.这12种有机污染物包括9种有机氯杀虫剂：滴滴涕、六氯苯、氯丹、     

Distribution of persistent organochlorine pesticides in tissue/organ of silver carp (Hypophthalmichthys molitrix) from Guanting Reservoir, China

The concentration of organochlorine pesticides（OCPs） in tissues and organs of silver carp（Hypophthalmichthys mofitrix） from Guanting Reservoir were investigated to evaluate the pollution potential and distribution of OCPs. A total of 16 OCPs were measured and the concentrations were in the range of 1.61-69.01 ng/g wet weight（ww） for total OCPs, 0.16- 0.75 ng/g ww for HCB. 0.75 -26.80 ng/g ww for SHCH（sum of α-,β-, γ- and δ-HCH） and 0.68-35.94 ng/g ww for SDDT（ sum of p, p＇-DDE, p, p＇-DDD, o, p＇-DDT and p, p＇- DDT）. The mean concentrations of total OCPs, HCB, ∑HCH, and ∑DDT were 18.04, 0.96, 7.14 and 9.28 ng/g ww, respectively. Among the organochlorine pesticides, β-HCH and p, p＇-DDE were the most dominant compounds in tissue and organ with the average concentrations of 4.42 and 8.14 ng/g, respectively. The results obtained in this study show that the levels of 16 OCP residues found in silver carps are low and pose no threat to human health and wildlife fed upon them on the basis of existing related quality guidelines. However, recent input of lindane and DDT might still exist in the area investigated and further investigation should be carried on.     

Biodegradation of imazapyr in typical soils in Zhejiang Province, China

The degradation of imazapyr in non-sterile and sterile soils from four sampling sites in Zhejiang, China was studied. The results showed that the half-lives of imazapyr in non-sterile soils were in the range of 30 to 45 d, while 81 to 133 d in sterile( by autoclaving) soils. It means the rate constants of imazapyr under non-sterile conditions were 2.3--4.4 times faster than that under sterile(by autoclaving)conditions, evidently indicating that the indigenous microorganisms in soil play an important role in the degradation of imazapyr. The different sterilization methods could result in different degradation rates of imazapyr. The heat of sterilization of soil largely decreased the degradation. However, the sterile treatment of soil by sodium azide had a different effect from that by autoclaving. Further more, the mechanism was also discussed. Biodegradation in four non-sterile soils accounted for 62% to 78% of imazapyr degradation. In contrast, less than 39% of imazapyr degradation was associated with chemical mechanisms. Therefore, the degradation mechanism was predominantly involved in biology including organisms and microorganisms in soil. Two imazapyr-degrading bacterial strains were isolated in enrichment culture technique and they were identified as Pseudomonas fluorescenes biotype [[ ( ZJX-5 ) and Bacillus cereus (ZJX-9),respectively. When added at a concentration of 50μg/g in mineral salts medium(MSM), ZJX-5 and ZJX-9 could degrade 81% and 87% imazapyr after 48h of incubation. For the treatment of incorporation of ZJX-5 or ZJX-9 into soil, the degradation rate enhanced 3-4 fold faster than that for control samples, which showed an important value in quick decontamination of imazapyr in soil.