上海市废弃电器电子产品回收现状及分析

基于废弃电器电子产品产生量大、价值高、危害性强等特点,阐述了对它们进行回收处理的必然性。文中在调研上海市废弃电器电子产品回收量、预测其产生量的基础上,阐明了在家电以旧换新的政策下上海市废弃电器电子产品具有很高回收率以及废弃电视机的所占比例极高的特点,并分析了产生这种现象的原因。     

废弃电器电子产品配套法规加紧制定规范回收处理

自2009年2月<废弃电器电子产品回收处理管理条例>(以下简称"条例")公布以来,环境保护部开展了集中调研活动,积极推动"条例"的贯彻实施.     

基于无线射频识别技术的废旧汽车回收模型建立及应用研究

针对中国废旧汽车回收过程中缺乏有效信息系统支撑及先进信息采集手段等问题,将无线射频识别技术(RFID)引入到废旧汽车的回收中.从提高回收决策水平、完善产品信息、增加回收价值3个角度阐述了废旧汽车回收对RFID的应用需求.根据循环经济的"3R"原则及RFID的特性,构建了基于RFID的废旧汽车回收模型,分析了废旧汽车回收过程中各主体活动和RFID的应用流程,并提出了RFID应用在废旧汽车回收利用中的建议.     

改进属性识别法在水质评价中的应用

为克服水质综合评价过程中指标权重带有主观性的弱点,提出了基于数据驱动技术确定权重的改进属性识别法,综合利用分类标准信息和样本信息进行迭代确定权重.采用浮桥河水库枯水期水质监测资料进行水质评价,验证了该模型用于水质综合评价的可行性.     

土地处理技术在污水资源化中的应用

简述了污水资源化的现状与常规技术及土地处理技术的特点，结合工程实例分析了土地处理技术在污水资源化中的应用条件、应用方向，指出土地处理技术是我国污水资源化的重要组成部分。     

低温等离子体技术及其在柴油机排气处理中的应用

概述了等离子体特点及分类，介绍了低温等离子体的产生及其净化柴油机排气的应用进展，分析了低温等离子体技术有效处理柴油机排气的机理，阐述了未来低温等离子体处理柴油机排气的主要方向与应用前景。     

膜分离技术在印染废水分质处理与分段回用中的应用

印染废水具有水量大、种类多、色度高、成分复杂和污染严重等特点,如果将各部分废水混合后再处理,很难找到合适的解决工艺,因此应采取分质处理和分段回用的方法,膜分离技术在这方面有较强的针对性.基于近年的文献调研,综述了膜分离技术处理退浆、洗毛和染色等废水及回收聚乙烯醇(PVA)、羊毛脂、染料等资源的研究情况,主要讨论了膜材料、膜孔径以及运行工艺条件等因素对印染废水处理效果的影响.     

离子交换技术在电解锰工业废水处理中的应用

电解锰工业废水中含有的重金属污染物毒性大,且不被生物降解,加上排放浓度越来越高、排放标准控制越来越严,从而使此类废水的处理成为难题。目前,离子交换技术在重金属废水的达标排放处理中取得了不少成果,并在工程中有了卓有成效的应用,因此讨论了影响该技术的各项参数,包括pH值、原水浓度、树脂用量、接触时间和运行条件等。     

土地处理技术在污水资源化中的应用

简述了污水资源化的现状与常规技术及土地处理技术的特点 ,结合工程实例分析了土地处理技术在污水资源化中的应用条件、应用方向 ,指出土地处理技术是我国污水资源化的重要组成部分     

3S技术在环境影响评价中的应用

3S（GIS、GPS、RS）技术在发达国家已得到广泛应用,中国政府管理部门也已高度重视,因此在介绍了3S各项技术功能的基础上,进一步阐述了在环境影响评价中的应用,以及3S集成技术在中国当前环境影响评价中的应用前景。     

我国电子废弃物管理与资源化对策

电子废弃物对人类环境的影响,已成为全球化的问题.通过对发达国家关于电子废弃物管理以及资源化技术的进展回顾,针对我国目前的情况提出相应的对策：制定延伸生产者责任以及有害物质的停用限期的相应法规;建立电子废弃物回收网络体系;通过国家政策和经济的扶持,尽快建立专门处理电子废弃物的机构;加快我国电子废弃物处理技术的步伐,尽快提高现有工艺及设备.     

我国电子废弃物管理与资源化对策

电子废弃物对人类环境的影响,已成为全球化的问题。通过对发达国家关于电子废弃物管理以及资源化技术的进展回顾,针对我国目前的情况提出相应的对策:制定延伸生产者责任以及有害物质的停用限期的相应法规;建立电子废弃物回收网络体系;通过国家政策和经济的扶持,尽快建立专门处理电子废弃物的机构;加快我国电子废弃物处理技术的步伐,尽快提高现有工艺及设备。     

废电子电器回收处理体系研究

分析了废电子电器回收处理体系的问题,提出了一种适合我国国情的废电子电器回收处理体系模式,并对国家对废电子电器回收处理体系的支持问题进行了讨论。     

新时期医疗废物处置技术体系的变革及发展

近20年来,我国在推进医疗废物无害化管理和处理处置方面开展了大量的工作,成绩举世瞩目。但处于新的历史时期,如何更好地基于可行技术,探索与其相匹配的管理模式,解决医疗废物处理处置短板已成为迫在眉睫的工作。我国目前存在针对医疗废物处理处置技术适用性考虑不足、农村及偏远地区医疗废物处置能力缺乏、医疗废物应急处置能力存在短板以及医疗废物领域科技创新能力有待提升等问题。因此,结合各种医疗处置技术特点及适用性,提出基于技术的适用性推进医疗废物处理处置技术布局优化、通过管理和技术进步解决农村和边远地区医疗废物处置难题、合理配置疫情期间应急处置能力以及推进科技创新等建议,为打造新时期医疗废物处理处置技术体系提供参考。     

Levels of PCDD/Fs,PCBs and PBDEs in breast milk of women living in the vicinity of a hazardous waste incinerator: Assessment of the temporal trend

The concentrations of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), polychlorinated biphenyls (PCBs) and polybrominated diphenyl ethers (PBDEs) were determined in breast milk from women living in the vicinity of a hazardous waste incinerator (HWI) in Catalonia, Spain. The results were compared with the levels obtained in previous surveys carried out in the same area in 1998 (baseline study), 2002 and 2007. The current total concentrations of 2,3,7,8-chlorinated PCDD/Fs in breast milk ranged from 18 to 126 pg g⁻¹ fat (1.1–12.3 pg WHO₂₀₀₅-TEQ_PCDD/F), while the total levels of PCBs ranged from 27 to 405 pg g⁻¹ fat (0.7–5.3 pg WHO₂₀₀₅-TEQ_PCB). In turn, PBDE concentrations (sum of 15 congeners) ranged 0.3–5.1 g g⁻¹ fat, with a mean value of 1.3 ng g⁻¹ fat. A general decrease in the concentrations for PCDD/Fs, both planar and total PCBs, and PBDEs in breast milk was observed. The levels of PCDD/Fs, PCBs, and PBDEs in milk of women living in urban zones were higher than those corresponding to industrial zones (41%, 26%, and 8%, respectively). For PCDD/Fs and PCBs, the current decreases are in accordance with the reduction in the dietary intake of these pollutants that we have also observed in recent studies carried out in the same area of study.     

非定态SO2制酸工艺在铅精矿烧结烟气治理中的应用

介绍了非定态SO2制酸工艺的特点、流程及其在铅精矿烧结烟气治理中的应用效果.该工艺具有良好的社会效益、环境效益和较好的经济效益,具有较高的推广应用价值.     

Breakthrough Curves Characterization and Identification of an Unknown Pollution Source in Groundwater System Using an Artificial Neural Network (ANN)

Contamination of groundwater constrains its uses and poses a serious threat to the environment. Once groundwater is contaminated, the cleanup may be difficult and expensive. Identification of unknown pollution sources is the first step toward adopting any remediation strategy. The proposed methodology exploits the capability of a universal function approximation by a feed-forward multilayer artificial neural network (ANN) to identify the sources in terms of its location, magnitudes, and duration of activity. The back-propagation algorithm is utilized for training the ANN to identify the source characteristics based on simulated concentration data at specified observation locations in the aquifer. Uniform random generation and the Latin hypercube sampling method of random generation are used to generate temporal varying source fluxes. These source fluxes are used in groundwater flow and the transport simulation model to generate necessary data for the ANN model-building processes. Breakthrough curves obtained for the specified pollution scenario are characterized by different methods. The characterized breakthrough curves parameters serve as inputs to ANN model. Unknown pollution source characteristics are outputs for ANN model. Experimentation is also performed with different number of training and testing patterns. In addition, the effects of measurement errors in concentration measurements values are used to show the robustness of ANN based methodology for source identification in case of erroneous data.     

Distribution of PCDDs and PCDFs in Soils Collected from the Denver Front Range - Principal Components Analysis of Diffuse Dioxin Sources (10 pp)

Background, Aims and Scope The Rocky Mountain Arsenal (RMA) is a US Army facility located northeast of Denver, Colorado that has been listed on the National Priorities List (NPL). It is currently being re-mediated under the authority of the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA) and the Superfund Amendments and Reauthorization Act of 1986 (SARA). As part of the remediation activities at RMA, indications were found that a source of polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) had existed on the RMA. As a result, investigations were undertaken to assess the possible nature and extent of any potential sources of PCDDs and PCDFs on the RMA site. In addition, other studies were conducted that examined PCDD/PCDF contamination in the Denver area. The goal of these studies was to examine nature and extent of PCDD/PCDF contamination both on the RMA as well as in the surrounding Denver area. The intent of this study was to characterize sources of dioxins (PCDDs) and dibenzofurans (PCDFs) at low environmental concentrations which might have originated from diffuse sources in the Denver Colorado area and in particular, the Rocky Mountain Arsenal (RMA) using Principal Component Analysis (PCA). Methods Over 200 soil samples were collected from the RMA and the Denver area. From the RMA, soil was collected as part of three studies that included a (1) random site-wide sampling of the RMA, (2) soils from the Western Tier Parcel (WTP), and (3) soils from Historic Use areas. Denver area soil samples were collected from five different land use categories: Residential, Agricultural, Open Space, Commercial, and Industrial. PCA was conducted on concentrations of 17 2,3,7,8-substuituted PCDD and PCDF congeners in 220 soil samples collected from the RMA and the Denver Front Range region. Results and Discussion PCA demonstrated the presence of possible minor sources of dioxins on the RMA. Current remediation efforts on RMA will result in the removal of these sources. Samples from the RMA were identified by the presence of a congener profile containing higher chlorinated PCDFs while the Denver Front Range areas were characterized by the presence of higher chlorinated PCDD congeners. The presence of a PCDF signature for the RMA samples does not necessarily indicate a major source of these contaminants on-site. Indeed, the relatively diffuse nature of the sample clusters would argue strongly against the presence of a single large source. Instead, the predominance of the PCDF congeners probably indicates the mixed industrial activities that took place on and near the site. Conclusion PCA results indicate that PCDD/PCDF profiles in soils collected from the RMA differed from those collected from the outlying Denver areas but that a major source of these contaminants was not present. Rather, the diffuse nature of sample clusters from the PCA indicated that the congener profile of RMA samples was most likely a result of the mixed industrial activities that historically have taken place on and near the site. PCA also indicated that many of the 'open area' (peripheral site-wide) RMA soils samples did not differ from Denver are reference congener profiles. This finding was also true for samples collected from the WTP that were essentially indistinguishable from Off-RMA reference samples. In addition, total TEQ concentrations in soils collected from WTP were similar to those measured in soils collected from the Denver Front Range areas indicating that lack of a major source of PCDD/PCDF within the WTP zones of the RMA. Recommendation and Outlook Analytical as well as statistical results of the soil congener data indicate that the WTP soils are indistinguishable from soils collected from non-industrial areas in the Denver area. This finding would support the recent 'de-listing' of the WTP from the other RMA areas and its' transfer to other authorities in the Denver area.     

The toxicity of soil samples containing TNT and other ammunition derived compounds in the enchytraeid and collembola-biotest

The effect of ammunition-like compounds and armament waste on the mortality and reproduction of terrestrial invertebrates was assayed by using two biotests: the enchytraeid-biotest withEnchytraeus crypticus and the collembola-biotest withFolsomia Candida. Toxicity was investigated by using standard soil (Lufa 2.2) spiked with 2,4,6-trinitrotoluene (TNT), hexahydro-l,3,5-trinitro-l,3,5-triazine (hexogen, RDX), octahydro-l,3,5,7-tetranitro-l,3,5,7-tetrazocine (octogen, HMX) and 2,4,6-triaminotoluene (TAT). Ecotoxicity was investigated with ammunition-contaminated soil material from the former ammunition plant “Tanne” at Clausthal-Zellerfeld (CTNTla) and the Brandplatz (incineration site) in Torgau-Elsnig (TETNT1a), Germany. TNT increased mortality and reduced reproduction of both test organisms corresponding to the concentrations used, whereas hexogen, octogen and TAT had no effect in the tested concentrations (1000-2000 mg/kg). From the two soil materials, TETNT1a was much more toxic than CTNT1a. The LC50(7d) in the enchytraeid-biotest was 570 mg TNT/kg and the EC50(28d) 369 mg TNT/kg soil material (dw). In the collembola-biotest the LC50(7d) was 185 mg TNT/kg and the EC50(28d) 110 mg TNT/kg soil matter (dw).     

Detection of transfluthrin and metofluthrin genotoxicity in the ST cross of the Drosophila Wing Spot Test

In this study, different concentrations of transfluthrin and metofluthrin have been assayed for genotoxicity by using the Wing Spot Test on Drosophila melanogaster. Standard cross was used in the experiment. Third-instar larvae that were trans-heterozygous for the two genetic markers mwh and flr³ were treated at different concentrations (0.0103 mg mL⁻¹, 0.103 mg mL⁻¹ for transfluthrin and 6 μg mL⁻¹, 60 μg mL⁻¹ for metofluthrin) of the test compounds. Feeding ended with pupation of the surviving larvae and the genetic changes induced in somatic cells of the wing’s imaginal discs lead to the formation of mutant clones on the wing blade. Results indicated that two experimental concentrations of transfluthrin and 60 μg mL⁻¹ metofluthrin showed mutagenic and recombinogenic effects in both the marker-heterozygous (MH) flies and the balancer-heterozygous (BH) flies.