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1.
简要介绍了江苏省火电厂已安装的烟气排放连续监测系统(CEMS)的现状,分析了CEMS运行中存在的问题,对CEMS的运行、管理和监督,提出了对策建议。  相似文献   

2.
2008年7月17下午,浙江环茂自控科技有限公司(以下简称环茂公司)与世界上最大的空气质量监测仪器生产厂家——美国赛默飞世尔科技公司,在杭州市西子国宾馆正式签署烟气排放连续监测系统(CEMS)战略合作协议,以共有品牌的CEMS新产品开拓中国烟气污染源在线监测市场。浙江省环境保护局副局长吴玉琛,浙江省环境保护科学设计研究院副院长、环茂公司董事长张胜军,环茂公司总经理张琰,赛默飞世尔中国区总裁蒋文康出席了签约仪式。  相似文献   

3.
总结了棉纺印染类项目常规生产工艺、产污环节及其特性,并剖析其项目环境影响评价工作中的常见问题与不足,从污染防治、清洁生产、循环经济及环境管理等方面出发,介绍了搞好棉纺印染类项目环境影响评价工作的要点。  相似文献   

4.
根据大气污染物排放浓度变化特点,将无偏GM(1,1)模型与神经网络模型组合,并以矩阵型输入方式替代传统的数列型数据输入方式,得到改进型灰色神经网络模型,称为UGMN模型。接着,采用烟囱入口烟气自动监控系统(CEMS)数据,将模型运用于贵州省某电厂白天及夜间两段时间段内大气污染物排放浓度的模拟与预测。研究结果表明UGMN模型预测精度较好,可以应用于火电厂大气污染物排放浓度预测。  相似文献   

5.
针对目前钢铁行业大气污染物清单编制和管理过程中存在的问题和需求,利用全国污染源排放在线监测(CEMS)数据、环境影响评价数据、环境统计数据、污染源普查数据等资料,建立了基于生产工艺的全国钢铁行业大气污染物排放清单管理系统,实现了排放清单的动态化管理和编制等功能。以山东省为例,验证了系统清单生成、输出等功能,结果显示2012年山东省钢铁企业SO_2、NO_x、烟粉尘排放量分别为15.23万、18.16万、8.97万t,其中烧结和高炉工艺是主要排污环节;从空间分布来看,莱芜、日照两市的钢铁企业污染排放量最大,SO_2、NO_x、烟粉尘排放量合计占山东省排放总量的50%左右。  相似文献   

6.
随着我国火电厂大气污染物排放标准的日趋严格,燃煤发电企业陆续开展环保装备升级改造工作,其中部分燃煤电厂已完成大气污染物超低排放改造工作。目前,针对超低排放改造后的成本效益,仍缺乏系统性的分析及评估。基于大量电厂运行DCS及CEMS数据,以某百万燃煤机组烟气污染物超低排放技术改造的情况为实际案例,采用费用-效益分析的方法,对其展开超低排放技术运行经济性评估及研究。同时,结合情景分析,研究负荷、含硫量及年发电时间等关键影响因素变化对污染物脱除成本的影响。结果表明:改造后,污染物(SO_2、NO_x及PM)脱除成本比改造前增加约13~20元·(MWh)-1,约占上网电价的2.8%~4.4%。改造后,该电厂SO_2、NO_x及PM排放绩效分别达到0.048、0.109及0.007 g·(k Wh)-1,每年可产生环境效益约1 344万元。此外,提升机组运行负荷能显著降低污染物脱除装备运行成本从实际运行平均负荷(66%负荷)提高到满负荷运行,FGD、SCR脱硝及ESP+WESP除尘单位发电量运行成本分别可下降约30.5%、32.1%和38.1%。  相似文献   

7.
京杭大运河宿迁段发生了氨氮、氟化物和砷两起突发性水污染事故,在对突发性水污染事故的污染源调查和应急监测工作进行总结的基础上,提出了环境监测工作中应对突发性水污染事故的工作原则和建议,供环境监测工作者参考.  相似文献   

8.
关于加强环境统计工作的思考   总被引:1,自引:0,他引:1  
姚诚 《污染防治技术》2007,20(4):33-34,63
针对江苏省环境统计工作中存在的问题,通过调查研究,提出了加强做好江苏省环境统计工作的有关对策.  相似文献   

9.
机场周围及起降“进近”、盘旋航线下的飞机噪声预测是环境保护部门对于新建机场提出的评价工作中的主要内容之一。国际上对飞机噪声已作大量工作,我国也于最近发布了飞机场环境噪声的限值标准及测量方法。但目前尚无技术规范对机场噪声预测工作提出具体要求。  相似文献   

10.
论述了加速城乡一体化建设过程中,加强环境保护工作的紧迫性;提出了以优美乡镇创建为抓手,生态县(市)、生态省建设为载体,整体推进环境保护工作,从而推动城乡一体化进程。  相似文献   

11.
Heavy metal pollution in China: Origin,pattern and control   总被引:21,自引:2,他引:21  
GOAL, SCOPE AND BACKGROUND: Heavy metal is among one of the pollutants, which cause severe threats to humans and the environment in China. The aim of the present review is to make information on the source of heavy metal pollution, distribution of heavy metals in the environment, and measures of pollution control accessible internationally, which are mostly published in Chinese. METHODS: Information from scientific journals, university journals and governmental releases are compiled focusing mainly on Cd, Cu, Pb and Zn. Partly Al, As, Cr, Fe, Hg, Mn and Ni a included also in part as well. RESULTS AND DISCUSSION: In soil, the average contents of Cd, Cu, Pb and Zn are 0.097, 22.6, 26.0 and 74.2 mg/kg, respectively. In the water of the Yangtze River Basin, the concentrations of Cd, Cu, Pb and Zn are 0.080, 7.91, 15.7 and 18.7 microg/L, respectively. In reference to human activities, the heavy metal pollution comes from three sources: industrial emission, wastewater and solid waste. The environment such as soil, water and air were polluted by heavy metals in some cases. The contents of Cd, Cu, Pb and Zn even reach 3.16, 99.3, 84.1 and 147 mg/kg, respectively, in the soils of a wastewater irrigation zone. These contaminants pollute drinking water and food, and threaten human health. Some diseases resulting from pollution of geological and environmental origin, were observed with long-term and non-reversible effects. CONCLUSIONS: In China, the geological background level of heavy metal is low, but with the activity of humans, soil, water, air, and plants are polluted by heavy metals in some cases and even affect human health through the food chain. RECOMMENDATIONS AND OUTLOOK: To remediate and improve environmental quality is a long strategy for the polluted area to keep humans and animals healthy. Phytoremediation would be an effective technique to remediate the heavy metal pollutions.  相似文献   

12.
Acid rain and acidification research are indeed a multidisciplinary field. This field evolved from the first attempts to mitigate acid freshwater in the 1920s, then linking acid rain to the acidification in late 1950s, to the broad project-concepts on cause and effect from the late 1960s. Three papers from 1974, 1976 and 1988 demonstrate a broad approach and comprise scientific areas from analytical chemistry, biochemistry, limnology, ecology, physiology and genetics. Few, if any, environmental problems have led to a public awareness, political decisions and binding limitations as the story of acid rain. Acid precipitation and acidification problems still exist, but at a lower pressure, and liming has been reduced accordingly. However, the biological responses in the process of recovery are slow and delayed. The need for basic science, multidisciplinary studies, long time series of high-quality data, is a legacy from the acid rain era, and must form the platform for all future environmental projects.  相似文献   

13.
GOAL, SCOPE AND BACKGROUND: [corrected] Historically, landfills have been the simplest form of eliminating urban solid waste with the minimum cost. They have been the most usual method for discarding solid waste. However, landfills are considered authentic biochemical reactors that introduce large amounts of contaminants into the environment in the form of gas and leachates. The dynamics of generation and the movement of gas in landfills depend on the input and output parameters, as well as on the structure of the landfill and the kind of waste. The input parameters include water introduced through natural or artificial processes, the characteristics of the urban solid waste, and the input of atmospheric air. The main output parameters for these biochemical reactors include the gases and the leachates that are potentially pollutants for the environment. Control systems are designed and installed to minimize the impact on the environment. However, these systems are not perfect and a significant amount of landfill gas could be released to the atmosphere through the surface in a diffuse form, also known as Non-controlled emission. In this paper, the results of the Non-controlled biogenic gas emissions from the Lazareto landfill in Tenerife, Canary Islands, are presented. The purpose of this study was to evaluate the concentration of CH4 and CO2 in the soil gas of the landfill cover, the CH4 and CO2 efflux from the surface of the landfill and, finally, to compare these parameters with other similar landfills. In this way, a better understanding of the process that controls biogenic gas emissions in landfills is expected. METHODS: A Non-controlled biogenic gas emission survey of 281 sampling sites was carried out during February and March, 2002. The sampling sites were selected in order to obtain a well-distributed sampling grid. Surface landfill CO2 efflux measurements were carried out at each sampling site on the surface landfill together with soil gas collection and ground temperatures at a depth of 30-40 cm.The CH4 efflux was computed from CO2 efflux and from the ratio CH4/CO2 in the soil gas. Soil gas samples were collected at a depth of 30-40 cm using a metallic probe and 20 cc hypodermic syringes, and later stored in evacuated 10 cc vacutainers for laboratory analysis of bulk composition. The gas sample was introduced in a vacutainer filled with deionized water and displacing the water until the vacutainer was filled with the gas sample in order to avoid air contamination from entering. The surface landfill temperature of the landfill was measured at a depth of 40 cm using a digital thermometer type OMEGA 871A. Landfill gases, CO2 and CH4, were analyzed within 24 hours using a double channel VARIAN micro-GC QUAD CP-2002P, with a 10 meter PORAPLOT-Q column, a TCD detector, and He as a carrier gas. The analysis temperature was 40 degrees C and the injection time was 10 msec. Surface landfill CO2 efflux measurements were performed using a portable NDIR spectrophotometer Licor-800 according to the accumulation chamber method (Chiodini et al. 1996). The data treatment, aimed at drawing the flux map and computing the total gas output, was based on the application of stochastic simulation algorithms provided by the GSLIB program (Deutsch and Journel 1998). RESULTS: Diffuse CH4 and CO2 efflux values range from negligible values up to 7,148 and 30,573 g m(-2) d(-1), respectively. The spatial distribution of the concentration and efflux of CO2, CH4 and soil temperature, show three areas of maximum activity in the landfill, suggesting a non-uniform pattern of diffuse degassing. This correlation between high emissions and concentration of CO2, CH4 and soil temperatures suggests that the areas of higher microbial activity and exothermic reactions are releasing CO2 and CH4 to the atmosphere from the landfill. Taking into consideration the spatial distribution of the CO2 and CH4 efflux values as well as the extension of the landfill, the Non-controlled emission of CO2 and CH4 to the atmosphere by the Lazareto's landfill are of 167 +/- 13.3 and 16 +/- 2.5 t d(-1), respectively. DISCUSSION: The patterns of gas flow within the landfill seem to be affected by boundary materials at the sides. The basalt layers have a low permeability and the gas flow in these areas is extensive. In this area, where a basalt layer does not exist, the flow gas diffuses toward the sea and the flux emissions at the landfill surface are lower. This behavior reflects the possible dissolution of gases into water and the deflection of gases towards the surface at the basalt boundary. The proximity to the sea, the installation of a palm tree garden and, as a result, the contribution of water coming from the watering of this garden has reactivated the system. The introduction of sea water into the landfill and the type of boundary could be defining the superficial gas discharges. CONCLUSIONS: Results from this study indicate that the spatial distribution of Non-controlled emission of CO2 and CH4 at the Lazareto's landfill shows a non-uniform pattern of diffuse degassing. The northeast, central and northwest areas of the Lazareto's landfill are the three areas of high emissions and concentration of CO2 and CH4, and high temperatures. The correlation between high emissions and the concentration of CO2, CH4, and the high temperatures suggest that the areas of higher microbial activity and exothermic reactions are releasing more CO2 and CH4 to the atmosphere from the landfill. A high concentration of CO2 is probably due to the presence of methanotrophic bacteria in the soil atmosphere of the landfill. Patterns of gas flow within the landfill seem to be affected by boundary materials (basalt layers) of low permeability, and side boundaries of the flux emissions at the surface are higher. At the sides of seawater and sediment boundaries, flux emissions at the landfill surface are lower. This behavior reflects a possible dissolution of gases into the water and the deflection of gases towards the surface at the basalt boundary. With this study, we can compare the data obtained in this landfill with other landfills and observe the different levels of emission. The proximity to the sea and the installation of the palm tree garden palms and, as a result, the contribution of water coming from the watering of this garden has reactivated the system. Many landfills worldwide located in similar settings could experience similar gas production processes. RECOMMENDATIONS AND PERSPECTIVES: The need for investigating and monitoring sea water and sediment quality in these landfills is advisable. Concentrations and fluxes of contaminants and their impact in the area should be assessed. With this study we can compare the data obtained in these landfills with other landfills and observe the different levels of emission.  相似文献   

14.
Grigorakis K  Rigos G 《Chemosphere》2011,85(6):899-919
Aquatic farming has been considered, during the last decades, as the fastest growing food production industry powered by governmental and technological impulsion. Compensation for fisheries decline, creation of new jobs and source of financial windfall are the most important benefits. However, similar to most of the human food-production activities, aquaculture raised several issues related to the environmental welfare and consumer safety. An effort to record the aquaculture-environment and -human safety interactions with regard to the Mediterranean mariculture, is attempted herein. We focused on this geographical area due to its individualities in both the hydrological and physicochemical characteristics and the forms of aquaculture activities. The cage farming of euryhaline marine fish species and more recently of bluefin tuna and mollusk farming are the dominating aquaculture activities. The impacts of these activities to the environment, through wastes offloads, introduction of alien species, genetic interactions, disease transfer, release of chemicals, use of wild recourses, alterations of coastal habitats and disturbance of wildlife, are analytically considered. Also the consumer safety issues related to the farming are assessed, including generation of antibiotic-resistant microorganisms, contaminants transferred to humans though food chain and other hazards from consumption of aquacultured items. Within these, the major literature findings are critically examined and suggestions for scientific areas that need further development are made. The major tasks for future aquaculture development in this region are: (i) to ensure sustainability and (ii) to balance the risks to public or environmental health with the substantial economical benefits. In regard with monitoring, tools must be created or adapted to predict the environmental costs and estimate consumer impact. At a canonistic and legal basis, the establishment of appropriate legal guidelines and common policies from all countries involved should be mandatory.  相似文献   

15.
National Park Development in China: Conservation or Commercialization?   总被引:1,自引:0,他引:1  
Wang G  Innes JL  Wu SW  Krzyzanowski J  Yin Y  Dai S  Zhang X  Liu S 《Ambio》2012,41(3):247-261
The rapid development of parks and ecotourism in China has attracted worldwide attention, not only for the beauty of the landscape that the parks are protecting but also for their abundant and often unique biodiversity. However, in some areas, the development of ecotourism has actually led to the degradation of local ecological, economic, and social systems. Using National Forest Parks for demonstration, this article analyzes the current political, institutional, legal, environmental, and economic issues concerning National Parks in China, and examines their potential future development. Although the intention of National Park systems in China is to raise environmental quality, and to protect biodiversity and social livelihoods, their success has varied. Future success will be measured by their capacity to reduce poverty, to promote long-term rehabilitation of wildlife habitats, and to simultaneously protect Chinese culture and biodiversity.  相似文献   

16.
影响有机污染物在土壤中的迁移、转化行为的因素   总被引:2,自引:0,他引:2  
本文介绍了有机污染物在土壤中的吸附与解吸附、渗滤、挥发和降解等行为过程。探讨了吸附与解吸附机理、土壤有机质含量和类型、水分含量及温度等对此过程的影响。依据某些典型的化合物行为模型,论述了影响土壤中有机污染物渗滤的因素。有机污染物需要先从土壤深层迁移至地表,然后挥发至大气,在土壤中迁移的速率较慢,控制着整个挥发过程,可用Fick 第二定律来描述。有机污染物在土壤中的非生物降解主要包括氧化- 还原、光解和水解等反应。土壤中的O2 含量、土壤有机质成分和含量、辐射强度、光谱分布、土壤水分含量、温度和pH 值等都会影响非生物降解过程。其中有些因素通过影响微生物的生物活性,还影响有机污染物的生物降解  相似文献   

17.
高温堆肥与蚯蚓堆肥对城市污泥重金属形态的影响   总被引:9,自引:0,他引:9  
李明 《环境工程学报》2008,2(10):1407-1412
采用高温堆肥和蚯蚓堆肥工艺,研究了城市污泥与锯末、粉煤灰或磷矿粉按不同比例混合堆肥前后重金属(Cu、Pb、Zn、Cd和As)交换态、碳酸盐结合态、铁锰氧化物结合态、有机结合态和残留态的变化。研究表明:高温堆肥和蚯蚓堆肥前后各试验污泥的重金属形态和含量呈现出不同的变化,都可以降低污泥中交换态Cu、Pb、Zn、Cd和As的含量;对于Cu和Pb,高温堆肥优于蚯蚓堆肥;对于Zn、Cd和As,蚯蚓堆肥优于高温堆肥。2种堆肥方式中,粉煤灰用量为10%的钝化效果优于20%,磷矿粉的钝化效果同粉煤灰一样。  相似文献   

18.
This study compared the heavy metal bioaccumulation capacity in the epiphytic moss Scorpiurum circinatum and the epiphytic lichen Pseudevernia furfuracea, exposed in bags for 3 months in the urban area of Acerra (S Italy). The content of Al, As, Cd, Co, Cr, Cu, Fe, Mn, Mo, Ni, Pb, Ti, V, and Zn was measured by ICP-MS. The results showed that both species accumulated all the heavy metals assayed. The moss had the highest bioaccumulation capacity for all metals and showed a more constant and linear accumulation trend than the lichen. Intra-tissue heavy metal bioaccumulation was assessed by X-ray microanalysis applied to ESEM operated in high and low vacuum and ESEM modes.  相似文献   

19.
Goal, Scope and Background Fragrance preparations or perfumes are used in an increasing variety of applications, as for example washing, cleansing, personal care products, consumer goods or in applications to modify indoor air. However, up to now, little is known to the general or scientific public about their chemical identity and the use pattern of single substances, not even for high production volume chemicals. Some toxicological data are published for a comparatively small number of substances with a focus on sensitisation and dermal effects, while other effects are neglected. Information on ecotoxicity and environmental fate are rare, especially for long-term exposure. Data for a detailed hazard and risk analysis are available in exceptional cases only. According to the current legal situation, fragrance industry is self-regulated, which means that pre-market risk evaluation is not required for most fragrances. Odour and the ability to smell play a major role for wildlife for all taxonomic groups. Reproductive and social behaviour, defence, communication and orientation depend on volatile compounds which can be identical to those used in fragrance preparations. Our interdisciplinary approach leads to the question of whether and, if so, to what extent anthropogenic fragrances may influence life and reproduction of organisms in the environment. Main Features Information from literature on use, exposure and biological effects was combined to analyse the state of knowledge. Following an overview of the amounts of fragrances used in different consumer products and their release into the environment, the roles of odours in nature are shown for a selection of compounds. Existing regulation was analysed to describe the data basis for environmental risk evaluation. Finally, recommendations for further action are derived from these findings. Results Three main results were elaborated: First, fragrance substances are continuously discharged in large amounts into the environment, especially via the waste water. Second, there are some indications of negative effects on human health or the environment, although the data basis is very thin due to the self regulation of the fragrance industry and the regulatory situation of fragrance substances. Third, many odoriferous substances used by man are identical to those which are signal substances of environmental organisms at very low concentrations, thus giving rise to specific mode of actions in the ecosystem. Recommendations For the adequate risk assessments of fragrances, test results on their unspecific as well as their specific effects as signal substances are needed. This would imply prioritisation methods and development of useful test methods for specific endpoints for appropriate risk assessments. Before a comprehensive testing and evaluation of results has been finished, a minimization of exposure should be envisaged. Eco-labelling of products containing acceptable fragrance ingredients could be a first step and provide consumers with the respective information. Transparency concerning the fragrance ingredients used and their biological potency will help to build up confidence between producers and consumers. Conclusions and Perspectives The interdisciplinary approach, bringing together chemical, biological, toxicological and ecotoxicological data with information provided by manufacturers and with legal and consumer aspects, offers new insights into the field of fragrance substances used in consumer products. The amounts and application fields of fragrance substances increases while fate and effects in the environment are hardly known. The current legal situation is not suited to elucidate the effects of fragrances on human health and the environment sufficiently, especially as it was shown that fragrances may play a considerable role in the ecosystem on the behaviour of organisms. According to the precautionary principle, the lack of knowledge should best be tackled by reducing exposure, especially for compounds such as fragrance substances where no ethical reasons object a substitution by less hazardous chemicals. ESS-Submission Editor: Dr. Thomas Knacker (th-knacker@ect.de)  相似文献   

20.
This article reviews interactions and health impacts of physical, chemical, and biological weather. Interactions and synergistic effects between the three types of weather call for integrated assessment, forecasting, and communication of air quality. Today’s air quality legislation falls short of addressing air quality degradation by biological weather, despite increasing evidence for the feasibility of both mitigation and adaptation policy options. In comparison with the existing capabilities for physical and chemical weather, the monitoring of biological weather is lacking stable operational agreements and resources. Furthermore, integrated effects of physical, chemical, and biological weather suggest a critical review of air quality management practices. Additional research is required to improve the coupled modeling of physical, chemical, and biological weather as well as the assessment and communication of integrated air quality. Findings from several recent COST Actions underline the importance of an increased dialog between scientists from the fields of meteorology, air quality, aerobiology, health, and policy makers.  相似文献   

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