饮用水水源地严格管理水质的对策分析——对实行严格水资源管理问题上的看法和建议

2012年1月国务院发布了《关于实行最严格水资源管理制度的意见》,这是众所关注的要事,实行了最严格水资源管理的原则精神以及确定县级以上政府负总责的规定.但对如何严格管理的技术路线和对策措施上,特针对现实中存在的主要问题提出以下3点看法和建议:①达到地面水环境质量Ⅱ类水质的饮用水水源地不一定未受污染;②保护区内企业车间排水口符合第一类污染物最高允许排放浓度规定是满足饮用水水源地要求的必要条件;③《地面水环境质量标准》(GB 3838-2002)对第一类污染物规定的Ⅱ类水质,是否体现了水环境背景值有较大存疑.     

天津市环境空气中恶臭感官定量评价分析

为研究环境空气恶臭污染特征,以天津市区为研究区域,分别在夏秋两季对天津市内六区的环境空气中恶臭感官浓度进行了监测。结果显示,在观测期间臭气浓度在限值（以《恶臭污染物排放标准》厂界臭气浓度限值20作为参照）范围以内的样品数量夏季占63％,而秋季占18％;通过多元线性回归方法建立了典型恶臭污染物与恶臭感官浓度的定量表达式,计算出典型恶臭污染物对市区环境空气的臭气浓度贡献率占59％。通过对实测值与预测值的拟合情况的分析,表明该回归方程可以较好的预测天津市环境空气中夏季恶臭感官浓度。     

在用车I／M制度的脆性及脆性源研究

I／M制度作为一个系统存在着脆性源,如果该制度在运行过程中控制不好脆性源,则其有效实施将受到影响。利用系统脆性理论对该制度进行分析研究找出L／M制度系统的脆性源以及解决措施是其分析研究的目的。在系统子因子中从业人员素质、仪器设备是最大的脆性源,但是其均被维修企业和检测企业所包含。综合分析研究结果显示,由于其在维修企业的脆性度比在检测企业的脆性度大,所以维修企业是该制度最重要的脆性源。用系统脆性理论分析方法分析I／M制度的脆性是一种科学、有效和实用的方法,具有较好的应用前景,为保障更好的运行I／M制度以有效的控制在用车的排放提供了理论依据。     

浦东新区“十二五”主要工业污染物排放总量预测及控制对策研究

文章以2010年污染源普查动态更新数据为基础,分析了目前浦东新区主要工业污染物的排放现状,掌握了浦东新区工业源主要能源消耗及污染物排放情况,重点工业源主要污染物行业分布和时空分布。根据浦东新区社会经济发展和环境保护的实际情况,采用情景分析法,设置三种不同工业增加值年增长率情景对浦东新区2015年主要工业污染物的排放量进行了预测,并结合浦东新区“十二五”主要污染物排放总量控制目标作了可达性分析,在此基础上,提出了浦东新区“十二五”主要工业污染物总量控制的对策措施。     

饮用水源地污染物监控与应急预警机制

为实施流域饮用水资源有效保护,从技术管理层面分析流域水资源共享过程中标准体系的构成与作用。对现阶段实施的生活饮用水卫生标准、地表水环境质量标准和排水标准中涵盖的有机污染物进行对称性分析,指出标准体系中存在的技术风险以及生活污水和工业废水混排存在的管理风险,并针对管理风险提出应急预警对策。     

城区地表径流面源污染和河道水环境治理的研究

河流为人类提供了多样的生态服务功能,然而城市化对河流生态系统健康状况造成严重的影响。随着点源污染的有效管理控制,非点源污染降雨径流己成为造成城市地表水环境污染的主要原因。为了改善河道水质,引调清水激活城市内河水体,提高河道的水环境自净能力,有效改善城市水环境。文章以南京河西水系为例,利用Saint-Venant方程组对水系建立一维水动力模型,并通过汇流结点水位法对方程组进行数值求解;对WASP5水质模型进行二次开发用于水质模拟;建立水质模型和一维河网水动力模型的耦合模型,将水动力模型计算所得到的水动力参数耦合到WSAP5水质模型中,模拟降雨过程以及引调清水过程的河网各河段的水质变量浓度,得出降雨径流对河流的污染程度以及引清冲污措施对河流水质改善的效果并优化调水过程。     

风浪作用下海岸区域的酸性污染物扩散

基于风浪和水流计算模型,综合考虑风浪作用的影响,建立了计算酸性污染物的输移扩散模型。通过计算三门湾海域在常浪向情况下四个时刻的污染物排放模式,将有无风浪影响的两者结果进行对比,初步分析了风浪作用下的酸性污染物扩散规律。结果认为:潮型、排放时刻、风浪等因素都会使酸性污染物的扩散面积与污染持续时间发生变化;并且在该方向风浪影响下,扩散面积与污染持续时间都有减小的趋势。     

典型持久性有机污染物在翅碱蓬中的分布特征

碱蓬是潮间带的常见优势种群,为了解其在持久性有机污染物从陆域向海洋迁移中所起的作用,利用GC-MS研究了东营和营口潮间带盐沼植物翅碱蓬不同器官及根系土中有机氯农药(OCPs)、多环芳烃(PAHs)、十溴联苯醚(BDE209)和多氯联苯(PCBs)的含量和分布特征.结果表明,4类持久性有机污染物在翅碱蓬中的污染水平依次为ΣPAHsΣOCPsBDE209ΣPCBs(96～1506ng/g、14～577ng/g、1.8～33ng/g和399～2161pg/g).营口潮间带沉积物中OCPs、PAHs和PCBs的污染水平高于东营,但这3类污染物在两地潮间带翅碱蓬叶子中的含量水平相当.OCPs在两地翅碱蓬各器官中的分布相同,即茎根叶,PAHs和PCBs2种污染物受根系土中有机质含量的影响,在翅碱蓬器官中呈现不同的分布.BDE209在东营潮间带的污染水平(19.7ng/g)高于营口(2.36ng/g),在碱蓬器官中呈现不同分布.     

Spatial variability of organochlorine pesticides （DDTs and HCHs） in surface soils from the alluvial region of Beijing, China

The spatial variability in the concentrations of 1,2,3,4,5,6-hexachlorocyclohexane (HCH) and 1,1,1-trichloro-2,2-bis-(p-chlorophenyl) ethane (DDT) in surface soils was studied on the basis of the analysis of 131 soil samples collected from the surface layer (0-20 cm depth) of the alluvial region of Beijing, China. The concentrations of total HCHs (including α-, β-, γ-, and δ-isomers) and total DDTs (i ncluding p,p'-DDT, p,p'-DDD, p,p'-DDE, and o,p'-DDT) in the surface soils tested were in the range from nondetectable to 31.72 μg/kg dry soil, with a mean value of 0.91, and from nondetectable to 5910.83 μg/kg dry soil, with a mean value of 32.13,respectively. It was observed that concentrations of HCHs in all soil samples and concentrations of DDTs in 112 soil samples were much lower than the first grade (50 μg/kg) permitted in "Environment quality standard for soils in China (GB15618-1995)". This suggests that the pollution due to organochlorine pesticides was generally not significant in the farmland soils in the Beijing alluvial region. In this study, the spatial distribution and trend of HCHs and DDTs were analyzed using Geostatistical Analyst and GS (513).Spatial distribution indicated how these pesticides had been applied in the past. Trend analysis showed that the concentrations of HCHs,DDTs, and their related metabolites followed an obvious distribution trend in the surface soils from the alluvial region of Beijing.     

Non-UV based germicidal activity of metal-doped TiO2 coating on solid surfaces

A stain-based screening method was developed to screen different catalyst coatings for their germicidal activity. A Baclight dead/live bacteria viability kit （invitrogen, molecular probes） was used for staining the cell. The screening was carried out following a standard procedure. This included loading cell suspension to solid surface and maintaining contact for 30 min, then staining with a mixture containing dyes. The stained cells were observed using an epifluorescent microscope and photographed with a CCD camera under UV. Metal-doped TiO2 coatings on AI plates were prepared and tested for non-UV germicidal activity without using UV. It was tested using model microorganisms such as Bakers Yeast （Saccharomyces cerevisiae）, Bacillus subtilis, Pseudomonas putida, and Escherichia coli. On the basis of the germicidal activity of catalyst and the degree of damage caused to the cells, the stained cells may appear green （viable）, green with red or yellow nuclei and yellow （compromised） or red （nonviable）. According to their stained color, cells were counted to calculate the percentage of dead, live, and compromised cells. Compromised cells are cells that grow very slowly after reculturing indicating a degree of reversible cell damage. Screening the germicidal activity using this staining method is accurate and efficient, and requires less time than the culture-based method. A modification to the procedure for measuring germicidal activity of rough surfaces or fibrous coatings was developed. Both TiO2 and metal-doped TiO2 （Ag, Pt, Au, Cu） possess non-UV based germicidal activity. The germicidal activity of TiO2 was found to be related with its wetting property and can be improved by UV irradiation before testing. It is not greatly affected by contact time, indicating a fast acting germicidal activity.