基于本地污染源调查的杭州市大气污染物排放清单研究

基于实地调查数据并辅以统计数据,采用物料衡算法和排放因子法,估算了杭州市2015年大气污染物排放清单,并选取经纬度坐标、路网、航道、土地类型和人口等数据作为权重因子,研究了该地区各类排放源污染物排放空间分布特征.结果表明,杭州市2015年SO_2、NO_x、CO、VOCs、PM_(10)、PM_(2.5)和NH_3年排放总量分别为22.20×10~3、108.17×10~3、192.10×10~3、134.94×10~3、78.12×10~3、27.65×10~3和59.75×10~3t.工业源是杭州市SO_2排放的主要来源,移动源对NO_x和CO的排放贡献最为显著,扬尘源是杭州市PM_(10)和PM_(2.5)排放的最主要来源,其次为工业源;VOCs排放的主要来源依次为工业源、天然源和移动源;NH_3排放主要来自农业源.从空间分布来看,排放主要集中在中心城区及其周边的萧山、下沙、大江东、余杭和富阳等工业企业相对密集的区域.本研究建立的排放清单在污染源覆盖范围和排放因子方面仍然存在一定的不确定性,建议在后续研究中重点开展低、小、散企业及本地化排放因子调查研究工作,进一步提升大气污染物排放清单的准确度.     

废旧锌锰电池生物淋滤-水热法制备纳米锰锌铁氧体

以氧化硫硫杆菌(A.thiooxidans)和氧化亚铁钩端螺旋菌(L.ferrooxidans)为混合淋滤菌株对废旧锌锰电池进行了生物浸提,并以获取的淋滤液为前驱体,采用水热法制备出系列锰锌铁氧体软磁材料(Mn_(1-x)Zn_xFe_2O_4,x=0.2~0.8);结合X射线衍射(XRD)、扫描电镜-能谱(SEMEDX)、振动样品磁强计(VSM)、透射电镜(TEM)、红外光谱(FT-IR)、热重-差热分析(TG-DTA)等表征手段对制备材料的结构、形貌、磁学性能和稳定性进行分析.结果表明,在5%固液比(质量体积比,5 g/100 mL,以下均表述为"5%固液比")下,经过5 d的外源酸调控生物浸提,分别获得了84.5%、63.2%的Zn、Mn浸出效率;当Zn∶Mn∶Fe=0.4∶0.6∶2.0(物质的量比,即x=0.4)时,制备的纳米级Mn_(0.6)Zn_(0.4)Fe_2O_4性能最优,属纯相的立方尖晶石结构,颗粒分布均匀,饱和磁化强度(M_s)、剩余磁化强度(M_r)和矫顽力(H_c)分别为68.9 emu·g~(-1)、4.7 emu·g~(-1)和53.6 Oe,具有热稳定性和耐酸碱性,有望成为一种新型的水处理磁性材料.     

构建和谐社会做好服务与保障

沿海城市厦门市政府坚持“以人为本”的理念,切实把防震减灾工作纳入经济建设和社会发展的总体规划,努力营造全社会关心支持防震减灾工作的良好氛围,全面提高防震减灾能力,为构建和谐社会提供了有力的服务与保障。     

巨灾风险的评估与政策

2006年3月．在美国内华达州大学召开了巨大自然灾害风险减轻政策管理顾问论坛会议．会议主题涉及美国巨灾发生发展的趋势、巨灾风险的识别分析评估及其管理政策等。本文主要介绍地震巨灾的风险研究评估和提出的管理政策方案。     

惊世奇闻:人蚁大厮杀

这是发生在100年前一种特殊战斗,但许多人都觉得好像是发生在昨天的故事。一个夏日的早晨,亚马逊河畔的一个农场。场长西蒙,站在他办公室的窗前,一边凝望着窗外的绿树红花,一边细心地倾听着。正在这时,警察前来通知说:"根据邻近地区得来的消息,有一个长约10公里、宽约5公里的褐色     

水土气污染与人类自身生产

我国现实之患是旱涝沙,潜在之忧是水土气污染。这里水是指江河湖海和地下水,土是土壤,气为大气。水土气是养育人类的基本环境要素。即使是人类需要的生存环境,也得不到应有的珍惜和保护,这是人类的最大悲哀。960万平方公里陆地和300多万平方公里海洋足以让我国人民活得潇洒自在,健康快     

如何做好城市防震避险工作

对于生活在城市的居民来说,当遇到有感地震和破坏性地震时该如何识别、避险和逃生尤为重要。深入宣传教育,做好防震减灾准备工作心理承受能力与准备的程度成正比。地震知识掌握越多,防震物资准备越充分,思想准备越到位,震时就能够坦然面对,地震发生时就越能做到遇震不慌。反之,对地震常识一无所知,缺乏必要的思想与物资准备,     

新民市柳河水源地水环境健康风险评价

为了评价新民柳河水源地的供水安全,简要介绍水环境健康风险评价基本方法的基础上,建立了水环境健康风险评价模式.研究结果表明:①柳河水源地地面水基因毒物质为优先控制污染物;而地下水应着力控制躯体毒物质.②对于基因毒物质,监测断面优先控制污染物为As和Cr;而对于躯体毒物质,所有监测断面的优先控制污染物均为氨.③在所有监测断面中,柳河上断面等6处有毒污染物所致健康危害的个人年总风险数量级为10-5-10-4.在日后的管理过程中,应对这6处加大治理力度.④目前环境健康风险评价还没有包括在常规环境评价工作中,建议在今后的评价工作中应该逐步开展这方面的工作,以提高供水安全.     

Assessment of population exposure to particulate matter pollution in Chongqing, China

To determine the population exposure to PM(10) in Chongqing, China, we developed an indirect model by combining information on the time activity patterns of various demographic subgroups with estimates of the PM(10) concentrations in different microenvironments (MEs). The spatial and temporal variations of the exposure to PM(10) were illustrated in a geographical information system (GIS). The population weighted exposure (PWE) for the entire population was 229, 155 and 211 microg/m(3), respectively, in winter, summer and as the annual average. Indoor PM(10) level at home was the largest contributor to the PWE, especially for the rural areas where high pollution levels were found due to solid fuels burning. Elder people had higher PM(10) exposure than adults and youth, due to more time spent in indoor MEs. The highest health risk due to particulate was found in the city zone and northeast regions, suggesting that pollution abatement should be prioritized in these areas.     

Fate of anilide and aniline herbicides in plant-materials-amended soils

The fate of herbicides trifluralin, pendimethalin, alachlor and metolachlor in paddy field soils amended with plant materials was investigated. The plant materials were purple sesbania, vegetable soybean and rice straw. The investigation was performed at two temperatures (25 and 40 degrees C) and two soil water moistures (60 and 90% water-holding capacity). The results showed linear and Freudlich equations described the adsorption of amide compound to soil. Adsorption coefficient (K(d)) fit to linear equation were in general greater in plant material-amended soils than in non-amended soil, especially in soil amending with rice straw. Increasing temperature and soil water moisture content shortened the half-lives of compounds in various treated soils. The movement of compounds in the soil columns showed the maximum distribution of aniline type compound, trifluralin and pendimethalin, appeared at the upper top of 0 to 5 and 0 to 10 cm of soil column, respectively, and of anilide type, alachlor and metolachlor, were distributed at 0 to 25 cm of the soil column. The mobility of chemicals in the different treated soils was simulated by the behavior assessment model (BAM). There was no significant difference among different plant material incubated soils on dissipation and mobility of compounds in soils.