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231.
环境损害事件发生后,行政机关第一时间应清除损害并进行评估与修复,但我国生态环境损害的救济立法规定相对粗糙,难以具有执行力.而《瑞典环境法典》则从本国国情出发制定其环境损害评估与修复制度,污染发生后环境监督机关迅速进入污染区域调查并制作报告,明确事后治理责任主体,并通过环境质量标准确定损害修复应达到的水平并开展损害修复工... 相似文献
232.
抚顺市大气重金属污染的植物监测与分析研究 总被引:1,自引:0,他引:1
采用生物富集原理,利用松针对抚顺地区大气中重金属元素的分布情况进行了监测与分析,结果表明:抚顺地区三种不同的松树对不同金属元素的富集能力是不同的,总体上看沙松的富集能力略高于油松和落叶松;工业区、交通干道和居民区松针中富集的金属含量高于农村地区;从不同的海拔高度上来看,在500米以下的低空大气中金属元素的分布量比高海拔地区高;不同金属元素间存在一定的相关关系。 相似文献
233.
234.
简要分析了日本“3·11”大地震后发生的2起炼油厂火灾事故,对日本在地震中的一些经验教训进行了总结,根据本次及近几年地震对石化企业的破坏情况,分析了地震中石化装置的薄弱环节,并提出对石化行业的启示。 相似文献
235.
Yingqian Yang Chengcheng J. Fei Bruce A. McCarl 《Journal of the American Water Resources Association》2023,59(4):652-664
In the United States, thermal power plant electrical generators (EGs) are large water diverters and consumptive users who need water for cooling. Retrofitting existing cooling systems to dry cooling and building new facilities with dry cooling can save water and reduce EG's vulnerability to drought. However, this can be an expensive source of water. We estimate that the cost of water saved by retrofitting cooling in existing EGs ranges from $0.04/m3 to $18/m3 depending on facility characteristics. Also water savings from building new EGs with dry cooling ranges in cost per unit water from $1.29/m3 to $2.24/m3. We compare costs with that for water development projects identified in the Texas State Water Plan. We find the water cost from converting to dry cooling is lower than many of the water development possibilities. We then estimate the impact of climate change on the cost of water saved, finding climate change can increase EG water use by up to 9.3% and lower the costs of water saved. Generally, it appears that water planners might consider cooling alterations as a cost competitive water development alternative whose cost would be further decreased by climate change. 相似文献
236.
The comprehensive control efficiency for the formation potentials(FPs) of a range of regulated and unregulated halogenated disinfection by-products(DBPs)(including carbonaceous DBPs(C-DBPs), nitrogenous DBPs(N-DBPs), and iodinated DBPs(I-DBPs)) with the multiple drinking water treatment processes, including pre-ozonation, conventional treatment(coagulation–sedimentation, pre-sand filtration), ozone-biological activated carbon(O_3-BAC) advanced treatment, and post-sand filtration, was investigated. The potential toxic risks of DBPs by combing their FPs and toxicity values were also evaluated.The results showed that the multiple drinking water treatment processes had superior performance in removing organic/inorganic precursors and reducing the formation of a range of halogenated DBPs. Therein, ozonation significantly removed bromide and iodide,and thus reduced the formation of brominated and iodinated DBPs. The removal of organic carbon and nitrogen precursors by the conventional treatment processes was substantially improved by O_3-BAC advanced treatment, and thus prevented the formation of chlorinated C-DBPs and N-DBPs. However, BAC filtration leads to the increased formation of brominated C-DBPs and N-DBPs due to the increase of bromide/DOC and bromide/DON.After the whole multiple treatment processes, the rank order for integrated toxic risk values caused by these halogenated DBPs was haloacetonitriles(HANs)》haloacetamides(HAMs) haloacetic acids(HAAs) trihalomethanes(THMs) halonitromethanes(HNMs) 》I-DBPs(I-HAMs and I-THMs). I-DBPs failed to cause high integrated toxic risk because of their very low FPs. The significant higher integrated toxic risk value caused by HANs than other halogenated DBPs cannot be ignored. 相似文献
237.
通过试验研究,探索了焦化废水生物脱氮半生产性启动条件,指出了顺利启动的关键技术是适宜的接种污泥及必须提供的环境条件。 相似文献
238.
韶钢水泥厂在进行干法生产时,会产生大量的粉尘,严重影响生产和厂区周围居民的正常生活,危害严重。通过一些综合防治措施,不仅保护了环境,而且还可回收数量可观的有价原料、成品或半成品。 相似文献
239.
The disposal of sewage sludge from municipal waste water treatment plants is suffering from raising costs.The gasification is an alternative way of treatment, which can reduce the amount of solid residues that must be disposed from a water treatment plant. The produced gas can be used very flexible to produce electrical energy, to burn it very cleanly or to use it for upgrading.The gasification in the fluidised bed and the gas cleaning with the granular bed filter has shown successful operation. A demonstration plant in Balingen was set up in 2002 and rebuilt to a larger throughput in 2010. As a next step a demonstration plant was built in Mannheim and is now at the end of the commissioning phase. Nowadays the product gas is blended with biogas from sludge fermentation and utilized in a gas engine or combustion chamber to produce heat. In the future the process control for a maximized efficiency and the removal of organic and inorganic impurities in the gas will be further improved. 相似文献
240.