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青藏高原典型城市拉萨市近地面臭氧污染特征   总被引:2,自引:1,他引:1  
拉萨市作为青藏高原典型城市,环境空气质量相对较好,但臭氧污染近年来有所凸显。对拉萨市臭氧的现状与污染特征进行分析基础上,探讨臭氧污染的影响因素。结果表明:拉萨市臭氧污染表现出"来得早,去得快"的特征,与内地城市相比,拉萨市臭氧质量浓度在3月即可达到全年平均值(2015年为105μg/m~3),而9月以后将低于全年平均值,并在春末夏初达到峰值;由于青藏高原海拔高,紫外线强,相对内陆地区臭氧均值偏高,2015年拉萨市臭氧年均值比北京市和成都市分别高出7.7%、29.0%,其小时浓度变化呈中午高、早晚低的特征;拉萨市臭氧的浓度变化受空气湿度、日照时间和日均气温的影响;生物质燃料的跨界传输可能也对青藏高原地区臭氧的来源产生一定影响。  相似文献   
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为实现以甲基橙为代表的偶氮类染料的高效降解,采用一种黏土矿物材料——Quantum Energy? Radiating Material(下称QE)为催化剂,系统分析了其在非均相类芬顿反应中的催化剂协同静态吸附作用,并考察了不同因素对甲基橙去除效果的影响,同时基于降解过程中Fe2+和总Fe析出量(以ρ计)、·OH等的变化过程,探讨了QE降解甲基橙的作用机制.结果表明,QE对甲基橙具有良好的吸附作用,同时,其作为非均相类芬顿催化剂对甲基橙的降解受到pH、温度、c(H2O2)、催化剂投加量等因素的影响.优化后的降解条件:初始ρ(甲基橙)为50 mg/L、QE投加量为5 g/L、c(H2O2)为100 mmol/L、pH为2、温度为60℃,在该条件下反应40 min后,甲基橙的去除率可达到99%.以叔丁醇作为·OH淬灭剂,随着c(叔丁醇)的增高,反应体系中甲基橙的去除率随之下降,说明·OH在该体系甲基橙降解中起重要作用;对在反应过程中Fe2+和总Fe析出量的监测数据表明,体系中QE对甲基橙的降解为均相芬顿反应、非均相芬顿反应和吸附作用协同作用的结果.研究显示,以QE为催化剂,通过吸附协同催化氧化作用可以有效处理含甲基橙的染料废水.   相似文献   
3.
Measurements of surface O3 and carbon monoxide(CO) were made from September 2009 to August 2011 at Dangxiong(30.48°N, 91.10°E, 4187 m a.s.l.), a remote highland site in a southern valley of the Nyainqêntanglha Mountains in the Tibetan Plateau, China. The monthly mean O3 mixing ratio ranged from 29.1 to 51.4 ppb, with an average of 38.5 ppb, and the maximum value was observed in May. The average diurnal cycle of O3 concentration showed a minimum in early morning and a maximum in the afternoon, with a broader "high platform" from the late morning to the late afternoon, and resembled that of surface wind speed. The concentration of surface O3 was highly significantly correlated with tropospheric column O3 over the regions surrounding Dangxiong and with that of surface O3 observed at a site north of the Nyainqêntanglha Mountains, suggesting a good regional representativeness of surface O3 at Dangxiong. In the afternoon when stronger winds blew, surface air showed distinct features of free-atmospheric air, with higher O3, lower CO, and lower relative humidity(RH). The negative O3–CO and O3–RH correlations in most months indicate a significant influence of air masses from the free troposphere. Trajectory analysis suggests that air masses originating from the south of the site make a negative net contribution to surface O3 and a positive contribution to CO and humidity, and those from the northwest sector contribute conversely to the respective quantities.  相似文献   
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采用逐步多元回归和主成分分析的方法研究了德兴铜矿周边土壤中重金属和土壤酶活性的关系.结果表明:德兴铜矿周边各功能区均受到不同程度的Cu、Cd污染,Pb、Zn未超过《土壤环境质量标准》(GB 15618--1995)二级标准;各功能区土壤酶活性有显著差别,逐步回归分析表明土壤酶活性与Cu、Zn全量、生物可利用态Cu含量有显著线性关系,而与Cd、Pb无明显相关;土壤酶活性和生物可利用态Cu呈负线性关系,而与残渣态Cu有正线性关系.主成分分析显示,土壤酶信息系统的第1、第2主成分可反映酶活性总变异的96.27%,根据第1主成分对功能区酶活性的分类结果与土壤生物可利用态Cu含量的分类结果基本一致,提示土壤酶活性指标可以反映土壤生物可利用态Cu含量.  相似文献   
5.
The current municipal solid waste management situation in Tibet   总被引:2,自引:0,他引:2  
The Tibetan Plateau has an average altitude of more than 4,000 m. The total area of Tibetan Plateau is 2,400,000 km2, which occupies 25% of the area of China. Due to the high altitude, the environment has low atmospheric pressure, low oxygen content, and low temperature, and is also fragile. Investigations concerning MSW generation and characteristics, MSW management, collection and transportation, and treatment and disposal of MSW covered four representative cities, including the urban areas of Lhasa city, Shigatse, Nedong of Lhoka and Bayi of Nyingtri. The results show that MSW generation in the urban areas of Lhasa city and Tibet were 450 t/d and 3,597 t/d, respectively, in 2006. However, accelerated economic development and flourishing tourism caused by the opening of the Qinghai-Tibet Railway (QTR) have greatly increased solid waste generation to a new high. It is predicted that MSW generation in Tibet will reach 4,026 t/d in 2010 and 4,942 t/d in 2020. MSW management and disposal lag behind MSW generation due to a number of factors such as equipment shortage, insufficient maintenance, exhaustion of waste treatment capacity and low recycling efficiency. Still, MSW in most areas is dumped in the open with no controls. Because no appropriate collection and treatment systems for leachate and landfill gas exist, untreated leachate is discharged directly into the environment, causing serious secondary pollution. Some suggestions on improving the MSW management system are presented in this paper.  相似文献   
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