宣化城区大气TSP浓度分布预测及控制措施

根据宣化区燃料消耗量和TSP直接排放量 ,统计出全区TSP排放总量。在明确了排放源参数和气象参数的前提下 ,利用ISCST3模型模拟预测TSP浓度空间分布。各受体点的TSP夏季平均浓度值有 2 0 6%超二级标准 ,冬季平均浓度值有 3 4 9%超二级标准。烈士陵园的污染状况明显好于区政府 ,而区政府则明显好于焦化厂 ,焦化厂的全年TSP月平均浓度均超二级标准。通过对TSP污染原因进行分析 ,针对宣化区的特殊情况提出了控制对策     

运输应激对二花脸和皮特兰猪血浆应激和代谢相关激素水平的影响

比较二花脸和皮特兰猪在2h运输过程中血浆ACTH、皮质醇、胰岛素和T3、T4水平的动态变化模式,以分析内分泌激素变化的品种特征.选用雄性二花脸猪10头,皮特兰猪6头,体重达20kg时安装颈静脉瘘管,1wk后运输试验,运输过程中不同时间点采集血样,放射免疫分析法测定血浆激素水平.上车后两品种猪ACTH水平缓慢上升,60min后达到峰值,下车后15min恢复至基础水平,运输过程中ACTH水平及变化幅度均未表现显著的品种差异;运输前皮质醇水平二花脸显著高于皮特兰猪,上车后两品种皮质醇均迅速上升,出发后15min达到峰值,下车后15min均快速恢复至基础水平,运输过程中皮特兰皮质醇上升的幅度显著高于二花脸猪;两品种胰岛素水平上车后均呈下降趋势,二花脸胰岛素水平总体上显著高于皮特兰猪;T3水平在上车后也表现快速下降,无论是T3水平还是其变化幅度均不表现显著的品种差异;皮特兰猪上车后T4水平稍微下降而二花脸猪显著下降,皮特兰T4水平总体显著高于二花脸猪.运输应激伴随血浆ACTH和皮质醇水平升高,而胰岛素、T3和T4水平下降,皮质醇水平升高的幅度能够反映猪的应激敏感性.图1参25     

Perchlorate as an environmental contaminant

Perchlorate anion (ClO4-) has been found in drinking water supplies throughout the southwestern United States. It is primarily associated with releases of ammonium perchlorate by defense contractors, military operations, and aerospace programs. Ammonium perchlorate is used as a solid oxidant in missile and rocket propulsion systems. Traces of perchlorate are found in Chile saltpeter, but the use of such fertilizer has not been associated with large scale contamination. Although it is a strong oxidant, perchlorate anion is very persistent in the environment due to the high activation energy associated with its reduction. At high enough concentrations, perchlorate can affect thyroid gland functions, where it is mistakenly taken up in place of iodide. A safe daily exposure has not yet been set, but is expected to be released in 2002. Perchlorate is measured in environmental samples primarily by ion chromatography. It can be removed by anion exchange or membrane filtration. It is destroyed by some biological and chemical processes. The environmental occurrence, toxicity, analytical chemistry, and remediative approaches are discussed.     

大气颗粒物上多环芳烃的识别和源解析的进展

本文对当前大气颗粒物上ＰＡＨｓ的识别和源解析的定量及定性和半定量的方法进行了综述，定性及半定量方法简便易行，但误差大；化学质量平衡法结果较准确具体，但ＰＡＨｓ会发生化学反应而降解，并且没有各种燃烧源较完整的ＰＡＨｓ成份谱，这已成为ＣＭＢ广泛推行的障碍；多元统计方法不考虑ＰＡＨｓ的降解，但要求数据量大，国内外的科学工作者用不同的方法和手段，使ＰＡＨｓ来源的识别和源解析工作有了一定进展。     

受体功能区结构与环境内分泌干扰效应生物差异的关系

环境中存在的多种内分泌干扰物能够与生物体内的天然激素受体选择性结合并产生多种生物效应,由于受体功能区三维结构的不同,其内分泌干扰活性存在着种间、种内、组织间等的种种差异,限制了不同物种间毒性效应的外推研究,增加了环境内分泌干扰物筛选和风险评价的难度.论文综述了基于受体介导的环境内分泌干扰物生物活性与相应受体选择性及受体功能区结构关系的研究进展,并利用分子模拟方法分析探讨了雌激素受体与部分化合物结合作用模式,讨论了目前存在的问题,对以后有关方面的研究提出了建议.     

基于生态供受体理论的全国水土保持重要区识别

科学评估土壤保持功能是生态保护红线划定的基础.依据生态供受体理论,针对土壤保持服务对应的水土流失这一生态问题,从水土流失的供体（水土流失量）、受体（人口密度）、辐射传输（距离水体距离）三个方面构建模型,分析土壤保持功能的重要性.结果表明全国潜在侵蚀量577.34×10¹⁰t/a,潜在土壤侵蚀随着坡度和降水量的增加而增加.土壤保持功能极重要区面积98.98×10⁴km²,主要分布在西南地区的无量山和哀牢山,黄土高原东部,东南地区的浙闽丘陵,东部地区的鲁中山区、鲁东半岛,以及辽东半岛.西南地区山高、谷深、坡陡、流急、地形稳定性差等因素造成水土流失严重,维持该地区的水土保持功能极为重要;西北地区的黄土高原土质疏松且多暴雨导致水土流失比较严重,维持该地区土壤保持功能非常重要.对比常用的生态保护功能模型,供受体理论模型除考虑自然影响因素之外,突出了人类活动的因素,对评估生态保护功能与水土保持生态风险更客观.依据供受体理论构建的土壤保持模型适用于土壤保持功能和土壤潜在侵蚀风险的评估,可作为评估生态系统安全和划定生态保护红线的重要依据.     

基于模糊聚类的PM_(2.5)拟合组分选择模型的研究

提出了一种新的PM2.5源成分谱拟合组分选择模型,在充分考虑拟合过程的物理意义的基础上,采用聚类正确率作为组分选择的依据.实验验证,该模型能够准确获取较好的拟合主组分,相比与经验选或者手动盲选所得拟合结果,我们提出的模型将成功拟合(误差范围在0~0.05之间)的比例由40%提升到83%.     

鲤体内芳香烃受体的分离纯化及其与葸的相互作用

从暴露于污染物蒽的鲤肝脏中提取出芳香烃受体,并采用紫外可见分光光度计进行最大吸收波长扫描,再通过离子交换层析法分离纯化鲤体内的芳香烃受体,并采用聚丙烯酰胺凝胶电泳对受体进行鉴定,最后通过傅里叶变换红外光谱探讨芳香烃受体与蒽结合后的结构变化.结果表明,提取的芳香烃受体在280 nm处有特征吸收峰,测得质量浓度为27.3 mg/mL.通过离子交换层析法纯化了单一组分的受体蛋白质,其相对分子质量约为110 kD.测定了芳香烃受体的红外光谱,与蒽结合后其在一定波段的谱峰发生了明显位移,表明污染物配体蒽能与芳香烃受体结合,并对其蛋白二级结构产生明显影响.     

Time-dependent effects of chlordane on thyroid histological structure and function in rats

In order to study the time-dependent effects of chlordane on thyroid hormone levels and histological structure in rats, 120 healthy 4-week-old SD rats were divided randomly into 12 groups. Rats in treatment groups were treated orally by gavage with chlordane at a dose of 15 mg kg^?1 for 5, 10, 15, 20, 30, or 40 days, while rats in control group received an equal volume of corn oil. Serum levels of thyroxine (FT4), triiodothyronine (FT3), and thyroid stimulating hormone (TSH) were measured by radioimmunoassay. Sections of thyroids were dyed with hematoxylin–eosin to detect any pathological alterations. In chlordane treated groups, on day 5, changes in serum levels of FT4, FT3, and TSH were not found. On days 10 and 15, serum levels of FT4 and FT3 decreased, accompanied by increased levels of TSH. On days 20, 30 and 40, serum levels of these hormones returned to control values. As for alterations in histology, on day 10–15, follicular epithelium of the thyroid were found to proliferate into two layers in chlordane treated rats. On day 20, in focal areas the two-layer afollicular epithelia were observed to continuously proliferate into 3–4 layers of follicular epithelium, termed hyperplasia plaques. On days 30 and 40, solid buds and secondary follicles to solid buds were detected. The earliest alteration of thyroid hormones in treated SD rats occurred between 5 and 10 days with corresponding histopathologic changes. As the exposure time increased, the serum levels of hormones and histopathology altered in a time-dependent manner.