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1.
2006—2012年广东省机动车尾气排放特征及变化规律   总被引:1,自引:0,他引:1       下载免费PDF全文
利用广东省年鉴及实地调查资料,基于COPERTⅣ模型计算并分析了2006─2012年广东省珠三角和非珠三角地区的机动车尾气排放清单.结果表明:研究地区2006─2012年机动车保有量上升,国Ⅲ、国Ⅳ车辆所占比例提高,其中珠三角地区优化程度大于非珠三角地区;2006─2012年2个地区污染物(CO、VOC、NOx、PM2.5)排放因子均有降低,降幅在24.54%~57.89%之间.机动车污染物排放量上升趋势及贡献特征地区性差异明显,2006─2012年非珠三角地区CO、VOC排放量分别上升了37.20%、26.93%,增幅高于珠三角地区,而珠三角地区2012年的NOx、PM2.5排放量增幅(分别为21.65%、14.60%)高于非珠三角地区.轻型客车是2个地区CO和VOC的主要贡献车型,贡献率均达46.96%以上,并且处于上升状态,但珠三角地区增幅小于非珠三角地区;重型客车和重型货车是2个地区NOx、PM2.5的主要来源,贡献率均在40.78%以上.  相似文献   
2.
珠三角表层沉积物的有机碳及其与卤系阻燃剂的关系   总被引:1,自引:0,他引:1  
测定了珠江三角洲130个表层沉积物中总有机碳(TOC)和10类卤系阻燃剂(HFRs)的含量,并探讨了TOC与HFRs之间的关系.结果表明:珠三角表层沉积物TOC范围为0.16%~5.76%,平均值为1.25%,呈现明显的空间变化.在工业化程度较高的东莞和广州,沉积物中HFRs与TOC有显著的相关性,而西江和珠江口沉积物中HFRs与TOC的相关性较差,可能与珠江三角洲水动力过程、电子垃圾拆解活动和HFRs不同的来源有关.  相似文献   
3.
A highly resolved temporal and spatial Pearl River Delta (PRD) regional emission inventory for the year 2006 was developed with the use of best available domestic emission factors and activity data. The inventory covers major emission sources in the region and a bottom–up approach was adopted to compile the inventory for those sources where possible. The results show that the estimates for SO2, NOx, CO, PM10, PM2.5 and VOC emissions in the PRD region for the year 2006 are 711.4 kt, 891.9 kt, 3840.6 kt, 418.4 kt, 204.6 kt, and 1180.1 kt, respectively. About 91.4% of SO2 emissions were from power plant and industrial sources, and 87.2% of NOx emissions were from power plant and mobile sources. The industrial, mobile and power plant sources are major contributors to PM10 and PM2.5 emissions, accounting for 97.7% of the total PM10 and 97.2% of PM2.5 emissions, respectively. Mobile, biogenic and VOC product-related sources are responsible for 90.5% of the total VOC emissions. The emissions are spatially allocated onto grid cells with a resolution of 3 km × 3 km, showing that anthropogenic air pollutant emissions are mainly distributed over PRD central-southern city cluster areas. The preliminary temporal profiles were established for the power plant, industrial and on-road mobile sources. There is relatively low uncertainty in SO2 emission estimates with a range of −16% to +21% from power plant sources, medium to high uncertainty for the NOx emissions, and high uncertainties in the VOC, PM2.5, PM10 and CO emissions.  相似文献   
4.
We present the continuously measurements of volatile organic compounds(VOCs) at a receptor site(Wan Qing Sha, WQS) in the Pearl River Delta(PRD) region from September to November of 2017. The average mixing ratios of total VOCs(TVOCs) was 36.3 ± 27.9 ppbv with the dominant contribution from alkanes(55.5%), followed by aromatics(33.3%). The diurnal variation of TVOCs showed a strong photochemical consumption during daytime,resulting in the formation of ozone(O3). Five VOC sources were ...  相似文献   
5.
Breakthrough curves, on a semi-log scale, from tests in porous media with block-input of viruses, bacteria, protozoa and colloidal particles often exhibit a typical skewness: a rather slowly rising limb and a smooth transition of a declining limb to a very long tail. One-site kinetic models fail to fit the rising and declining limbs together with the tail satisfactorily. Inclusion of an equilibrium adsorption site does not seem to improve simulation results. This was encountered in the simulation of breakthrough curves from a recent field study on the removal of bacteriophages MS2 and PRD1 by passage through dune sand. In the present study, results of laboratory experiments for the study of this issue are presented. Breakthrough curves of salt and bacteriophages MS2, PRDI, and phiX174 in 1 D column experiments have been measured. One- and two-site kinetic models have been applied to fit and predict breakthrough curves from column experiments. The two-site model fitted all breakthrough curves very satisfactorily, accounting for the skewness of the rising limb as well as for the smooth transition of the declining limb to the tail of the breakthrough curve. The one-site model does not follow the curvature of the breakthrough tail, leading to an overestimation of the inactivation rate coefficient for attached viruses. Interaction with kinetic site 1 is characterized by relatively fast attachment and slow detachment, whereas attachment to and detachment from kinetic site 2 is fast. Inactivation of viruses and interaction with kinetic site 2 provide only a minor contribution to removal. Virus removal is mainly determined by the attachment to site 1. Bacteriophage phiX174 attached more than MS2 and PRD1, which can be explained by the greater electrostatic repulsion that MS2 and PRD1 experience compared to the less negatively charged phiX174.  相似文献   
6.
鼎湖山秋季大气细粒子及其二次无机组分的污染特征及来源   总被引:15,自引:13,他引:2  
刘子锐  王跃思  刘全  刘鲁宁  张德强 《环境科学》2011,32(11):3160-3166
利用大气颗粒物质量浓度分析仪(TEOM)及大气细粒子快速捕集及其化学成分自动在线分析系统(RCFP-IC)于2008年10~11月在中国科学院华南植物园鼎湖山定位站进行了大气细粒子(PM2.5)及其二次无机组分(SO42-、NH 4+和NO 3-)与相关污染气体组分的同步观测与分析,同时结合主成分分析和HYSPLIT轨...  相似文献   
7.
To clarify the aerosol hygroscopic growth and optical properties of the Pearl River Delta(PRD)region,integrated observations were conducted in Heshan City of Guangdong Province from October 19 to November 17,2014.The concentrations and chemical compositions of PM_(2.5),aerosol optical properties and meteorological parameters were measured.The mean value of PM_(2.5) increased from less than 35(excellent) to 35-75 μg/m~3(good) and then to greater than 75 μg/m~3(pollution),corresponding to mean PM_(2.5) values of 24.9,51.2,and 93.3 μg/m~3,respectively.The aerosol scattering hygroscopic growth factor(f(RH = 80%)) values were 2.0,2.12,and 2.18 for the excellent,good,and pollution levels,respectively.The atmospheric extinction coefficient(σext)and the absorption coefficient of aerosols(σ_(ap)) increased,and the single scattering albedo(SSA)decreased from the excellent to the pollution levels.For different air mass sources,under excellent and good levels,the land air mass from northern Heshan had lower f(RH) and σ_(sp) values.In addition,the mixed aerosol from the sea and coastal cities had lower f(RH) and showed that the local sources of coastal cities have higher scattering characteristics in pollution periods.  相似文献   
8.
珠江三角洲印刷行业VOCs组分排放清单及关键活性组分   总被引:5,自引:1,他引:4  
根据珠江三角洲地区印刷行业活动数据和不锈钢罐采样-气质联用技术,获取了印刷工艺VOCs成分谱,建立了该地区2010年印刷行业VOCs组分排放清单,研究了不同工艺排放的臭氧生成潜势.结果表明:该地区2010年印刷行业VOCs排放总量达8 591.26 t,深圳、东莞、佛山排放量较大.凹印是印刷行业主要VOCs排放工艺,排放量达5 762.01 t;平印和凸印次之,分别为1 954.01和37.82 t.不同工艺排放的VOCs组分差异较大,平印工艺排放的VOCs成分中异丙醇含量最多(306.58 t),其次为正庚烷(115.87 t);苯和甲苯是凸印工艺排放的VOCs成分中含量最大的2种化合物,分别达5.58和4.83 t;乙酸乙酯是凹印工艺排放的VOCs成分中的首要化合物,达2 482.85 t.凸印工艺排放的VOCs单位浓度臭氧潜势最大,达1.30 μg/m3,平印和凹印较小,分别为0.89和0.72 μg/m3,各工艺排放的含氧有机物对臭氧生成潜势的贡献均为最大.  相似文献   
9.
结合2008年11月18~25日期间珠三角地区的二次有机气溶胶(SOA)外场观测数据,验证区域空气质量模式WRF/Chem(weather research and forecasting model with chemistry)中两种SOA化学机制——VBS(volatile basis set)和SORGAM(secondary organic aerosol model)对珠三角SOA的模拟效果.VBS机制考虑了更为广泛的SOA前体物和化学老化过程,SOA模拟值更接近观测值,能合理反映SOA观测值的逐天变化趋势,与观测值的平均绝对偏差和相关性分别是-4.88μg·m-3和0.91,而SORGAM机制的分别为-5.32μg·m-3和0.18.利用VBS机制模拟区域内SOA的时空分布,结果显示SOA浓度具有显著的昼夜变化特征,浓度峰值出现在中午时段.受到输送和臭氧区域分布的影响,各城市SOA浓度差异显著,下风向的城市(如中山、珠海、江门)SOA浓度较高.  相似文献   
10.
2006~2019年珠三角地区臭氧污染趋势   总被引:12,自引:21,他引:12  
研究基于2006~2019年粤港澳珠江三角洲区域空气监测网络数据,利用Mann-Kendall检验法和Sen斜率法等统计方法计算了珠三角不同区域臭氧年际变化情况,并分析了变化的原因.结果表明:①2006~2019年珠三角平均臭氧浓度上升趋势显著(P<0.05),平均增长速率为0.80 μg·(m3·a)-1.2016年之后,臭氧平均增长速率为2.08 μg·(m3·a)-1,臭氧浓度增速加快.②珠三角臭氧浓度变化趋势有明显的空间差异和季节差异.中部地区臭氧年均浓度增加趋势显著,外围区域臭氧增加趋势不显著;臭氧增加趋势主要集中在夏季,其他季节变化趋势不显著.③珠三角臭氧变化趋势是由前体物和气象条件共同造成的,特别与NOx的浓度变化密切相关.2006~2019年珠三角中部区域NO2浓度明显下降,滴定效应减弱导致臭氧浓度增加;边缘地区NO2浓度变化较小,臭氧浓度未发生明显的改变.④随着前体物浓度的变化,珠三角臭氧生成敏感区的特征正在发生改变,VOCs控制区面积不断减少,协同控制区和NOx控制区面积逐渐增加,区域臭氧污染防治需要加强对前体物的协同控制.  相似文献   
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