危险废物浸出毒性试验方法的研究

在分析各国危险废物浸出毒性试验方法的基础上,综合考虑我国气候状况(降雨量、酸雨现状)及工业固体废物处理处置现状,提出我国危险废物浸出毒性研究的技术路线为:通过模拟工业固体废物填埋场在不规范填埋处置且受酸雨影响条件下,有毒物质浸出向地下渗滤造成对地下水的污染,确定浸出毒性的浸取方法.浸出毒性保护目标为地下水,同时还介绍了主要技术参数液固比、浸取剂pH值和类型的确定方法.  

垃圾填埋场渗出液中有害成分的研究

研究垃圾填埋场渗出液中的有害成分。渗出液样品用适当的方法处理后 ,用气相色谱 -质谱联用方法和原子发射光谱法进行定性分析。然后用原子吸收分光光度法和反相高效液相色谱法定量测定样品中微量的 Cu、Zn、Pb、Cr、Cd、Hg、苯酚、对甲苯酚、萘、蒽  

我国危险废物经营单位监测中的技术问题和建议

根据2007—2013年对持环保部发证的危险废物经营单位开展监督性监测的实际情况和工作经验,从关注焚烧企业的二 口 恶 英监测、加强危险废物企业日常监测、开展危险废物鉴别技术方法研究等方面,探讨我国危险废物监测技术上现存的主要问题和发展方向,对今后全国各省自行组织危险废物许可证的审核和监督性监测等相关工作给出了建议。  

危险废物生态毒性鉴别指标研究

生态毒性是危险废物的危险特性鉴别指标之一,生态毒性鉴别指标确定的基础是关于毒性化学物质和固体废物的生态毒理学(评估指标)研究.比较研究了国外毒性物质和危险废物的生态毒性鉴别指标及其制定的方法学,分析了中国的研究现状,对中国危险废物生态毒性鉴别指标制定的方法学提出了建议.  

应用斑马鱼和凡纳对虾诊断污染场地污水的生物毒性

应用斑马鱼(Brachydanio rerio)和凡纳对虾(Penaeus vannamei)对某废弃有机污染场地中有毒有机废弃物堆积产生的污水(1号塘污水)和场地及周边地表径流积水(2号塘污水)的生物毒性进行了试验.结果表明,1号塘污水对斑马鱼和凡纳对虾96 hLC50分别为46.2%和59.6%, 2号塘污水的毒性试验中两种试验生物的死亡率皆为0.化学检测表明,1号塘污水中的主要污染物为苯酚类和酞酸脂类物质,而2号塘污水中均未检出有机污染物.化学检测结果与毒性试验结果具有较好的相关性.  

Identification and leaching characteristics of sludge generated from metal pickling and electroplating industries by Toxicity Characteristics Leaching Procedure (TCLP)

One of India's major concerns is the increasing level of land pollution largely due to the uncontrolled disposal of industrialsolid and hazardous waste. With rapid industrialization, thegeneration of industrial solid and hazardous waste has increasedappreciably and the nature of waste generated has become complex.Their impacts on the ecological bodies are noticeable. The article describes the details of studies conducted using Toxicity Characteristics Leaching Procedure, to estimate the toxicity effects of the metals viz., chromium, zinc, manganese,iron, nickel, cobalt and copper by the Zero Headspace Extractorfor the sludges generated from effluent treatment plant of steeltube, wire and plating industries on environment constituentslike groundwater, surface water and land. Toxicity Characteristics Leaching Procedure determines the mobility of organic and inorganic analytes of liquid, solid or multiphase waste from hazardous solid wastes in the form of primary and secondary extracts. These extracts are mixed in equal volumeproportion and analyzed by Direct Reading 2000 spectrophotometer.The amount of heavy metals observed during the studies in theleachates were found and the results were compared with HazardousWaste categories as per Indian Standards, TCLP regulatory limitsgiven by United States Environment Protection Agency (USEPA) andGermany Leachate Quality Standards and it was observed that theywere on higher side, needing a proper preventive concept of sludge management including handling, treatment, recovery and disposal.  

危险废物焚烧处置项目竣工环境保护验收监测要点

对危险废物焚烧处置项目竣工环境保护验收监测中尚需明确的要点进行了剖析,并从入炉危废种类及比例、焚烧量的控制、助燃剂加入量、空气过剩系统的把握,以及安全管理检查要点等方面,提出相应的解决办法。  

化工危险源环境安全监测和应急响应系统的研发与应用

通过分析化工危险源环境污染的危害性,提出了将工业无线传感器网络技术、视频监控技术和自动控制、无线通讯、地理信息系统（GIS）、数据库及网络工程等计算机技术应用于化工危险源的监测和监控,建立一个化工危险源的环境安全监测和应急响应系统的必要性。概述了系统的需求分析和架构,详细介绍了系统的组成、功能和关键技术,探讨了如何将该系统应用于泰州某化工公司危险源的环境监控和应急管理。  

Use of the p,p'-DDD: p,p'-DDE Concentration Ratio to Trace Contaminant Migration from a Hazardous Waste Site

For approximately 50 years, beginning in the 1920s, hazardous wastes were disposed in an 11-hectare area of the Marine Corps Base (MCB) Quantico, Virginia, USA known as the Old Landfill. Polychlorinated biphenyls (PCBs) and DDT compounds were the primary contaminants of concern. These contaminants migrated into the sediments of a 78-hectare area of the Potomac River, the Quantico Embayment. Fish tissue contamination resulted in the MCB posting signs along the embayment shoreline warning fishermen to avoid consumption. In this paper, we interpret total PCB (t-PCBs) and total DDT (t-DDT, sum of six DDT, DDD, and DDE isomers) data from monitoring studies. We use the ratio of p,p'-DDD to p,p'-DDE concentrations as a tracer to distinguish site-related from regional contamination. The median DDD/DDE ratio in Quantico Embayment sediments (3.5) was significantly higher than the median ratio (0.71) in sediments from nearby Powells Creek, used as a reference area. In general, t-PCBs and t-DDT concentrations were significantly higher in killifish (Fundulus diaphanus) and carp (Cyprinus carpio) from the Quantico Embayment compared with Powells Creek. For both species, Quantico Embayment fish had mean or median DDD/DDE ratios greater than one. Median ratios were significantly higher in Quantico Embayment (4.6) than Powells Creek (0.28) whole body carp. In contrast, t-PCBs and t-DDT in channel catfish (Ictalurus punctatus) fillets were similar in Quantico Embayment and Powells Creek collections, with median ratios of 0.34 and 0.26, respectively. Differences between species may be attributable to movement (carp and killifish being more localized) and feeding patterns (carp ingesting sediment while feeding). We recommend that environmental scientists use this ratio when investigating sites with DDT contamination.  

Assessment of elemental contaminants in water and fish samples from Aba river

The elemental contaminants in water and fish samples from Aba river were studied. The elements studied were Zn, Ni, As, Hg, Co and Mn. Three water samples and three samples of different fish species were collected from different locations in the river. The water and fish samples were analysed for elemental contaminants using Atomic Absorption Spectrophotometer (AAS). The elemental toxicants Zn and Mn were identified in appreciable amounts in fresh fish species namely, Lates niloticus and Oriochronis niloticus, of mean values 8.012 ppm and 0.861 ppm, respectively. The analysis also shows arsenic concentration of mean value 0.01 ppm in Lates niloticus. The analysis of frozen fish samples purchased from the Waterside market located near the river shows Ni and Hg levels of mean values 0.83 ppm and 0.02 ppm, respectively. The levels of elemental contaminants As, Zn, Hg and Mn from the water samples have mean values 0.082 ppm, 11.284 ppm, 0.201 ppm and 1.024 ppm, respectively. There are five industries that discharge waste products into Aba river. In view of this, there is a need to determine the level of pollution of the river, since the inhabitants depend on the river for their drinking water, fishing and other domestic uses. This study is aimed at determining the level of heavy metal toxicants in fish and water samples from the river. The effect of these elemental contaminants and the associated health hazards were examined.