生活垃圾焚烧二噁英排放对人群健康影响研究进展

综述了二噁英对人体健康的危害特性, 以及我国生活垃圾焚烧厂二噁英排放浓度水平，及其周边环境空气和土壤中二噁英污染浓度水平、人群暴露途径、剂量和健康影响。指出，现有研究显示，我国生活垃圾焚烧排放的二噁英浓度在合理范围之内，垃圾焚烧厂周边人群二噁英暴露量普遍低于世界卫生组织（WHO）推荐的容许标准，但也有研究发现，垃圾焚烧会导致周边环境介质中二噁英浓度水平增高。提出，应重点关注垃圾焚烧排放二噁英的长期低剂量暴露对人群健康的影响。     

炉排型城市生活垃圾焚烧炉排气中二(口恶)(口英)污染状况及存在问题

选择四种规模不同的炉排型生活垃圾焚烧炉,分别对其排放烟气中的二(口恶)(口英)进行测定,从不同炉排型垃圾焚烧炉二(口恶)(口英)的排放现状并结合实际调查结果表明,不同炉型的生活垃圾焚烧炉存在一些共性问题,尚需加强垃圾焚烧的炉前、炉中及烟气处理各个环节的运行管理.     

生活垃圾焚烧炉烟气新标准可达性分析

对《生活垃圾焚烧污染控制标准》(GB 18485—2001)和《生活垃圾焚烧污染控制标准》(GB 18485—2014)中各项指标的排放限值作比较,并探讨了二噁英、重金属、酸性气体、烟尘、碳氧化物等烟气污染物的控制措施。结合2010—2014年浙江省部分生活垃圾焚烧厂"三同时"验收废气监测数据,对排放指标的达标情况作分析,结果表明,采用"3T+E"焚烧工艺+SNCR脱硝+半干法脱酸+活性炭喷射+布袋除尘器除尘的烟气污染控制技术,可以同时满足脱氮、脱酸、除尘,以及去除重金属和二噁英的要求。     

燃煤机组烟气脱硫超低排放技术研究

文章重点介绍了目前我国燃煤机组烟气脱硫超低排放技术,并列举了一些已经实现烟气脱硫超低排放技术改造的燃煤机组工程实例和运行效果。     

基于燃煤电厂超低排放的汞分布特性研究

为掌握超低排放改造后烟气处理装置对汞分布的影响,选择6台有代表性的超低排放火电机组进行现场测试。通过对火电机组入炉煤、炉渣、飞灰、脱硫石膏、末端烟气等样品的测试,得出不同燃烧产物中汞的分布:底渣和湿除出水的汞含量极微;电除尘底灰中的汞所占比重相对较大,平均汞含量占燃烧产物中总汞的比例可达57.97%。依据质量平衡原理,计算出不同超低排放改造工艺路线对汞的协同脱除效率为87.26%~95.60%,并分析了不同污染控制设备对汞排放的影响。     

生活垃圾焚烧烟气中重金属排放水平及影响因素分析

通过对浙江省生活垃圾焚烧炉排放烟气中重金属的监测,分析生活垃圾焚烧烟气中重金属排放水平。结果表明,汞及其化合物的检出率最高,为95.7%,其次为铬和锰,检出率均为60%,且在不同的焚烧炉中重金属排放浓度差异较大,检出率最低的为铊和镉,且排放浓度均较低;焚烧炉排放烟气中汞及其化合物、镉+铊及其化合物、锑+砷+铅+铬+钴+铜+锰+镍及其化合物排放浓度均低于国标排放限值,最大占标率分别为76%、4%、21.9%。焚烧烟气中的重金属含量与焚烧垃圾中的重金属含量有关,烟气通过废气处理设施,可有效地减少重金属等污染物的排放。     

超低排放下燃煤电厂颗粒物排放特征分析研究

选取6家经过超低排放改造的燃煤电厂,对湿法脱硫(WFGD)和湿式电除尘器(WESP)进出口烟气中TPM、PM_(10)、PM_(2.5)、PM_1进行测试,分析研究超低排放下燃煤电厂颗粒物的排放特征及电除尘器后净化设备对颗粒物的脱除效果。结果表明,6家电厂TPM、PM_(10)、PM_(2.5)、PM_1排放浓度分别为0.75~2.36、0.71~2.12、0.65~1.96、0.51~1.57 mg/m~3。分析烟气中颗粒物粒径分布可知,除尘器后,PM10占TPM质量比低于40%,且比例随烟气经过WFGD和WESP而逐渐降低。WFGD对PM2.5有较好的脱除效果,而WESP对PM1脱除效果显著。为满足超低排放标准,6家电厂除尘器后脱除设备综合除尘效率大多在85%以上。计算得到6家电厂TPM、PM_(10)、PM_(2.5)、PM_1排放因子,与超低排放改造之前同等级燃煤电厂相比,6家电厂不同粒径颗粒物排放因子均显著降低,也远低于西方发达国家燃煤电厂颗粒物排放因子。     

典型行业废水特征有机污染物排放控制标准探讨

通过对典型行业废水有机污染物排放现状的调查研究，探讨我国现有污水排放标准存在的问题，即现有的标准不能有效控制废水特征有机污染物排放。依据美国环保局多介质环境模型，用不同方法计算水介质排放环境目标值，用该值作为标准限值，评价典型行业废水有机污染物监测结果。针对典型行业废水有机污染物排放特征，提出制订排放控制标准的建议。     

生活垃圾焚烧项目竣工环保验收自查要点探讨

简述了生活垃圾焚烧项目的行业特点,指出,验收自查是整个验收工作的基础也是最重要的环节。提出,应以《建设项目竣工环境保护验收技术指南污染影响类》为依据,从自查依据、自查方式、自查内容以及对自查结果的处理几方面做好项目验收自查工作,确保验收工作的顺利开展,为项目验收提供参考和保障。     

典型超低排放烟气中颗粒物组分特征研究

为了解超低排放改造后工业源烟气颗粒物排放状况及其组分特征,于2020年1—5月对2家垃圾焚烧企业和2家燃煤电厂外排烟气开展了调查,同步采集外排烟气中的可过滤颗粒物（FPM）和可凝结颗粒物（CPM）,测定质量浓度及其离子组分、元素组分,对各组分浓度范围及平均值进行统计评价。结果表明：4家企业外排烟气中CPM和FPM质量浓度平均值的比值分别为30.5,10.3,3.0,0.94,CPM的排放不可忽视;离子分析结果发现,烟气处理过程中产生的铵离子和硫酸根离子等水溶性离子,在FPM中基本未检出,在CPM中检出且浓度较高;金属元素分析结果发现,检出的铬（Cr）、镍（Ni）、铅（Pb）3种元素主要存在于FPM中,而砷（As）、汞（Hg）元素则更多地存在于CPM中;CPM中水溶性离子为主要成分,以水溶性离子作为CPM排放的控制因子是可行的。     

Toxic Environmental Releases from Medical Waste Incineration: A Review

Toxic releases from medical waste incineration comprising organic emissions such as polychlorinated dibenzo-dioxin/furan (PCDD/Fs) and polycyclic aromatic hydrocarbons (PAHs), inorganic emissions and ashes containing toxic metals have been reviewed. Attempts made by various investigators to reduce/eliminate emissions have also been included. Legislations concerning emission standards for medical waste incinerators have been discussed.     

Modeling Waste Incineration for Life-Cycle Inventory Analysis in Switzerland

This paper proposes a mathematical model for life-cycle inventory analysis (LCI) of waste incineration in Switzerland. In order to model conventional and new incineration technologies adequately, fundamental aspects of the different technologies relevant for the LCI are discussed. The environmental impact of these technologies strongly depends on the assessment of the long-term emissions of the solid incineration residues and is therefore related to value based decisions about the time horizon considered. The article illustrates that the choice of the landfill model has a significant influence on the results of life-cycle assessment of waste incineration.     

北京市废弃物处理温室气体排放特征

基于《2006年IPCC国家温室气体清单指南》推荐的方法，结合《省级温室气体清单编制指南（试行）》和《城市温室气体核算工具指南》的部分数据与核算范围，针对固体废弃物填埋、焚烧和废水处理等过程，核算了北京市2005-2014年废弃物处理过程中温室气体总排放量。结果表明：2005-2014年北京市废弃物处理过程温室气体总排放量呈逐渐上升趋势，2014年温室气体总排放量比2005年增长98%。10年间，固体废弃物填埋过程一直是最主要的温室气体排放源，到2014年排放量达到最大，为416.3×10⁴t二氧化碳当量（CO₂e）。废弃物填埋、废水处理和废弃物焚烧过程占总排放量的比例分别为78.5%（CO₂e质量分数，下同）、13.5%和8%。结合已有研究，系统优化国内7个典型城市废弃物处理温室气体排放因子，核算7个城市排放情况，并对比分析了北京市排放情况。     

广州生活垃圾处理的思路与对策

简述了广州生活垃圾生成与处理的现状。指出了广州生活垃圾处理存在的主要问题,对广州市未来10 a—15 a生活垃圾产生量进行了预测。在对生活垃圾填埋和焚烧处理成本进行比较的基础上,提出了广州生活垃圾处理的行动内容。     

生活垃圾与危险废物焚烧二噁英类排放特征研究

对某省52家焚烧企业(21家生活垃圾和31家危险废物)排放烟气数据进行了分析,结果表明,两类焚烧企业二噁英类17种单体分布有所不同,生活垃圾焚烧烟气中浓度较高的是O8CDD和O8CDF;危险废物焚烧烟气中较大的是2,3,4,7,8-P5CDF、2,3,7,8-T4CDD和1,2,3,7,8-P5CDD;两类焚烧企业二噁英类单体对I-TEQ贡献最高的都是2,3,4,7,8-P5CDF,贡献率分别为0. 7%～45%和10%～67%;两者的17种二噁英类与I-TEQ的相关性分析表明,1,2,3,7,8-P5CDF在2类焚烧炉中与I-TEQ均存在较高的相关性,其相关系数分别0. 932和0. 927,可以作为潜在的测定指示物。     

Incineration of hazardous wastes

Glaxo has practiced incineration of liquid and gaseous wastes for over twenty years and currently operate eleven liquid and gas incinerators in the United Kingdom and Singapore. The liquid incinerators burn, as their main streams, those solvents that cannot be recovered and recycled within the processes. The early installations were for readily combustible solvents only. However, there has been a progressive move into the destruction of more difficult and hazardous wastes, with the consequential requirements for more sophisticated technology, in the belief that the responsible destruction of waste should be tackled near to its source. The eventual aim is to be self-sufficient in this area of waste management. The incineration of hazardous liquid and gaseous waste has presented a series of design, operational and monitoring problems into account which have all been successfully overcome. The solutions take into account the environmental consequences of the operations from both liquid and gaseous emissions. In order to ensure minimal environmental impact and safe operation the best practicable technology is employed. Environmental assessment forms part of the process development and permitting procedures.Plenary speaker.     

A source study of atmospheric polycyclic aromatic hydrocarbons in Shenzhen, South China

Air pollution has become a serious problem in the Pearl River Delta, South China, particularly in winter due to the local micrometeorology. In this study, atmospheric polycyclic aromatic hydrocarbons (PAHs) were monitored weekly in Shenzhen during the winter of 2006. Results indicated that the detected PAHs were mainly of vapor phase compounds with phenanthrene dominant. The average vapor phase and particle phase PAHs concentration in Shenzhen was 101.3 and 26.7 ng m^???3, respectively. Meteorological conditions showed great effect on PAH concentrations. The higher PAHs concentrations observed during haze episode might result from the accumulation of pollutants under decreased boundary layer, slower wind speed, and long-term dryness conditions. The sources of PAHs in the air were estimated by principal component analysis in combination with diagnostic ratios. Vehicle exhaust was the major PAHs source in Shenzhen, accounting for 50.0% of the total PAHs emissions, whereas coal combustion and solid waste incineration contributed to 29.4% and 20.6% of the total PAHs concentration, respectively. The results clearly indicated that the increasing solid waste incinerators have become a new important PAHs source in this region.     

石家庄市春季大气颗粒物的铅污染特征

为了解石家庄市2016年春季大气颗粒物的铅污染特征及来源,利用单颗粒气溶胶质谱仪(SPAMS),分析了大气中含铅颗粒的化学成分。结果表明: 研究期间大气环境中含铅颗粒数浓度共出现11次跳跃式升高,跳跃时间段内石家庄均处于轻度污染过程。从成分分析来看,含铅颗粒分为纯铅颗粒、Pb与K(Pb-K)、OC(Pb-OC)、Cl(Pb-Cl)、混合颗粒等八大类。观测结果表明:Pb-K颗粒最多,占到含铅颗粒的84.4%；其次为纯铅颗粒,占比为13.0%。与石家庄市污染源谱库比对进行来源解析,得到Pb-K颗粒主要来自生活垃圾焚烧源, 纯铅颗粒主要来自工业源。结合石家庄市大气污染源排放清单和后向气流轨迹分析,推测含铅颗粒可能来自市区西南方向某区县的生活垃圾焚烧企业。     

Exploring the “not in my backyard” effect in the construction of waste incineration power plants - based on a survey in metropolises of China

Waste incineration power plants have become the best option in face of the increasing amount of garbage in China's cities. However, constructing waste incineration power plants will cause “not in my backyard” (NIMBY) effect in the public. To identify variables causing this effect and measure the effect quantitatively, we designed and carried out a random survey in four metropolises in China. Of the 3133 questionnaires distributed, 3066 are thought to be effective. Males, persons with higher educational levels, or with higher income, or having underaged children in their families, or thinking their neighborhoods are upscale ones are willing to pay more to avoid the construction of waste incineration power plants in their surroundings than others. In addition, provided that the respondents deem that the construction of waste incineration power plants would have an impact on their lives, they are willing to pay more no matter they own their departments or not. Finally, the estimated willingness to pay (WTP) to avoid the waste incineration power plants is 105 yuan to 133 yuan per month. Hence, the government should treat the NIMBY syndrome well in the construction of waste incineration power plants, with WTP being one perspective to persuade the public.     

The composition, trend and impact of urban solid waste in Beijing

This paper provides an overview of the trend of generation, composition, and management of municipal solid waste, and estimates the carbon emissions arising from municipal solid waste management in Beijing. The correlation analysis conducted shows that the generation of municipal solid waste in Beijing has been growing steadily, showing high correlations (r > 0.9) to the total GDP, per capita income, and the population. Food waste showed an increasing trend since 1990. Compared with the results of an investigation in 1990, ash and woodchips content in 2003 declined from 56% to 17%, while the percentage of paper and plastic increased from 10% to 29% over the same period. The calorific value of the municipal waste also increased, from 2,686 kJ/kg in 1990 to 4,667 kJ/kg in 2003, indicating that the waste is suitable for incineration. Currently, the source separation ratio of municipal waste is approximately 15%. About 94% of all the collected solid waste goes to the landfill while 4% is composted and 2% is incinerated. A moderate garbage collection fee is applied to both permanent and temporary residents in Beijing, but the willingness to pay for solid waste collection and treatment is still low. Under current treatment mode, the total amounts of carbon emission from waste disposal sites and incineration increased with the increase of municipal solid waste, from 29.8 Gg in 1990 to 84.5 Gg in 2003, including 83.3 Gg of CH₄ and 22.0 Gg of CO₂. The data availability and methodological challenges in monitoring the quantity and characteristics of municipal solid waste are discussed.