公众对煤矿区地质灾害的感知与适应行为研究

煤矿区的地质灾害较为常见,而且随着开采时间的推移地质灾害问题日益严重。公众对煤矿区地质灾害的感知与适应行为直接与他们的生命财产相关,同时还关系到政策法规的制定。通过对煤矿区公众的问卷调查发现,公众对地质灾害的严重程度和灾害原因感知是比较准确的,但仍有相当比例的公众选择采取无效的紧急适应行为,有近三分之一的公众没有考虑采用迁移的适应行为。公众对煤矿区地质灾害适应行为的背后涉及利益相关方的博弈。     

低分子量有机化合物对MnO_2和土壤氧化锰的还原溶解作用

为考察土壤锰氧化物的还原溶解行为,本文选取常见的根系分泌的8种有机酸(抗坏血酸、香草酸、柠檬酸、草酸、酒石酸、水杨酸、半胱氨酸和邻苯二甲酸)和1种酚类化合物(邻苯二酚),人工合成的Mn O2和5种富含氧化锰的土壤(广东徐闻的砖红壤、海南澄迈的砖红壤、云南昆明的砖红壤、浙江嵊县的红壤和江苏南京的黄棕壤),研究了有机化合物对氧化锰的还原溶解作用.结果表明,较低p H和较高温度有利于有机化合物对Mn O2的还原溶解.在p H 4.5—5.5和温度5—45℃范围内,不同有机化合物还原溶解Mn O2能力的大小顺序为:邻苯二酚半胱氨酸抗坏血酸香草酸柠檬酸草酸≈酒石酸水杨酸≈邻苯二甲酸.邻苯二酚、半胱氨酸和抗坏血酸对土壤中氧化锰也有较强的还原溶解能力.当5种土壤比较时,徐闻砖红壤中还原溶解出的锰量最高,其次为昆明砖红壤,嵊县红壤中还原溶解出的锰量最小.当有还原性有机化合物存在时徐闻砖红壤、昆明砖红壤和澄迈砖红壤中的氧化锰容易发生还原溶解反应,增加土壤中可溶态和交换态Mn2+的含量,并可能对植物产生锰毒害.     

Hydrogen peroxide (H2O2) requirement for the oxidation of crude oil in contaminated soils by a modified Fenton's reagent

The oxidation of soil organic matter (SOM) and total petroleum hydrocarbon were investigated in two soils at eight different hydrogen peroxide (H₂O₂) concentrations to determine the optimal H₂O₂ dosage for the efficient remediation of soils contaminated by crude oil with minimal SOM removal. In our study, H₂O₂ concentrations up to 1100 mM increased the SOM destruction up to 10%–15% in the two soils while no improvement of the crude oil removal efficiencies was observed. The results indicate that the destruction of SOM significantly limits the oxidation of crude oil because SOM might consume H₂O₂ more effectively than crude oil at H₂O₂ concentrations above 1100 mM. In addition, H₂O₂ concentrations higher than 1100 mM were not expected for both soils because of the extremely rapid H₂O₂ decomposition, and low H₂O₂ utilization, of both soils.     

浅析环境监测如何在《重点区域大气污染防治“十二五”规划》实施中发挥作用研究

《重点区域大气污染防治"十二五"规划》是中国第一部综合性大气污染防治的规划,涉及14个城市,四川省属于《重点区域大气污染防治"十二五"规划》中面积最大的成渝城市群,约占该规划区的面积达10.7%。为更好地促进该规划的实施,四川省编制了《重点区域大气污染防治"十二五"规划四川省实施方案》。环境监测是环境保护及管理工作的基础,论文简要分析了在四川省规划实施过程中,环境监测的工作重点、工作方向以及应如何发挥作用。     

在用机动车环保管理——《2013年中国机动车污染防治年报》（第Ⅳ部分）

环境保护部日前发布《2013年中国机动车污染防治年报》,公布了2012年全国机动车污染排放状况。本期“研究成果展示”专栏以六篇形式连载。本文刊载关于在用机动车环保管理的内容,以飨读者。该年报指出,2012年,全国参加环保定期检验的汽车共有5561．7万辆,占全国汽车保有量的51．3％。天津、重庆、等61个城市汽车环保定期检验率达到80％以上。截至2012年底,全国累计核发环保检验合格标志5981．3万枚,标志发放率达到55．2％。天津市、长春、南京、杭州等32个城市机动车环保检验合格标志发放率达到90％以上。截至2012年底,北京、重庆、天津、辽宁、江苏、内蒙古、陕西、山西、安徽、四川10省（自治区、直辖市）环境保护部门成立了专门的省级机动车环保监管机构;长春、南京、青岛等84个城市组建了相应的市级机动车环保监管机构,与2010年相比、全国共增加机动车专职监管机构27个。2012年,天津市、河北省、四川省政府出台了省级机动车污染防治管理办法;呼和浩特市人大通过了机动车污染防治条例;邢台、晋城、佳木斯等市政府出台了机动车污染防治政府规章。     

纳米Ag粒子原位杂化PVDF超滤膜的抗污染性能

以AgNO3为前驱体,聚偏氟乙烯(PVDF)为聚合物基体,聚乙烯吡咯烷酮(PVP)为分散剂和成孔剂,N,N-二甲基甲酰胺(DMF)为还原剂和溶剂,利用相转化法制备了纳米Ag粒子原位杂化PVDF超滤膜.采用扫描电镜、透射电镜、原子力显微镜及接触角测定仪对杂化膜的结构和性能进行了表征.结果表明:原位形成的纳米Ag粒子均匀地分散在聚合物基体中,纳米Ag粒子的添加改善了PVDF膜的亲水性能.以腐殖酸和牛血清蛋白作为污染物的代表,考察了Ag/PVDF膜的抗有机污染性能.以大肠杆菌、耐甲氧西林金黄色葡萄球菌及活性污泥作为微生物的代表,考察了杂化膜的抗生物污染性能.结果证实了与纯PVDF膜相比,Ag/PVDF膜通量衰减较慢,可有效抑制微生物的生长,表面受活性污泥污染程度小,具有显著的抗有机污染和抗生物污染性能.     

三峡库区消落带3种植物淹水后汞的动态变化及其对水体的影响

被淹没的植物是水库甲基汞异常升高的来源之一.为探寻淹水条件下三峡水库消落带植物中汞的动态变化特征及其对水体的影响,通过室内模拟试验,研究淹水条件下稗草、狗牙根、玉米秸秆中汞含量变化及其向水体释汞情况.结果表明,3种植物总汞含量范围为9.21~12.07 ng·g-1,甲基汞占总汞的质量分数约为1%~2%.淹水后,植物总汞含量逐渐降低,其降幅为35.81%~55.96%;而上覆水溶解态汞(DHg)浓度迅速上升,增幅为103.23%~232.15%,说明植物腐烂分解会向水体释放汞.淹水环境为植物体组织内甲基化提供了充裕条件,导致植物残体甲基汞含量升高,为初始含量的3.04~6.63倍,而上覆水溶解态甲基汞(DMe Hg)浓度也显著升高,为初始浓度的14.84~16.05倍.淹水期间,上覆水中DMe Hg与溶解氧(DO)浓度表现为极显著负相关,与可溶性有机碳(DOC)浓度存在显著正相关.而在整个淹水过程中,上覆水DHg浓度变化量为植物总汞释放量的41.74%~47.01%,且各植物残体总汞含量与上覆水DHg浓度存在极显著负相关.     

渭河陕西段潜流带沉积物重金属变化初步分析

为厘清潜流带沉积物重金属时空变化及与水量交换、沉积物颗粒结构间的关系,于2013年春夏两季对渭河陕西段5个研究断面66个测试点位沉积物的野外原位渗透系数、颗粒粒径、重金属含量进行分析.结果表明:影响渭河沉积物渗透系数的主要因素是沉积物粒径,同时沉积物垂向分层、排列组合也影响其渗透性能;沉积物重金属Cu、Zn、Pb、Cd质量分数在垂向上不同深度其含量大小不同,在时间上总体呈现春季夏季,富集系数(EF指数)分析结果显示春季Cu、Zn(除华县)、Pb(除眉县)、Cd富集严重且主要受人为输入源影响,夏季除Cd元素外,Cu、Zn、Pb的EF值均1.5,说明其含量主要来源于地壳和岩石圈的自然风化过程;Pearson相关分析发现粘土与粉砂(粒径0.075 mm)百分比与沉积物重金属质量分数呈弱相关,重金属粒径效应不显著,粒径不是控制重金属含量的主要环境影子;对单一重金属垂向不同深度含量进行相关性研究发现除Cd外,其余3种重金属在垂向上的相关系数均0.5(p0.01),说明单一重金属在垂向上具有同源性且存在相互迁移与转化.     

Effect of plant harvest on methane emission from two constructed wetlands designed for the treatment of wastewater

The emission of methane from two constructed wetlands [a free water surface flow system (FWS) and a subsurface flow system (SF)], constructed for the treatment of waste water, was evaluated at different sites inhabited by reeds (Phragmites communis), to test the effects of plant harvest. High methane emission was recorded immediately after harvesting in both wetlands. Several days after harvesting, the emission decreased in the FWS but remained high in the SF. The variation was significantly influenced by temperature, with lower emission and higher dissolved CH(4) in water occurring at lower temperatures. Both the emission and concentration of dissolved CH(4) were also influenced significantly by water quality, wetland design, level of stalk butt left above the water level, etc. The methane flux was explained on the basis of rizhospheric methanogenic and methanotrophic microbial populations. FISH analysis indicated the presence of Type A and Type B methanotrophs in both wetlands, and the methane flux was directly influenced by the quantitative variation in methanogenic and methanotrophic bacteria in both wetlands.     

PCDD/Fs in ambient air collected in Zagreb, Croatia

Levels of PCDD/Fs were measured at four different sites in Zagreb, capital of Croatia. Also one sample was taken during spontaneously initiated open fire on a landfill and one sample where garden waste of unknown content was burnt. Over period 1997–2000, 28 samples were collected and levels ranged between 9 and 306 fg I-TEQ m⁻³, except in the sample collected during landfill fire. Air PCDD/F levels in Zagreb at four sites were different and the highest levels were observed in industrial area. Seasonal variation of levels is also evident with higher levels in winter than in summer. Our results show that PCDD/F levels in ambient air collected in Zagreb are at lower end of the published data range. In general, homologue profiles were quite similar for all locations, the concentration of PCDD homologues increased while the concentration of PCDF homologues decreased with increasing degree of chlorination. PCDD/F levels in the landfill fire sample was 13 200 fg I-TEQ m⁻³ which are much higher than levels in garden waste burning sample or in sample collected at industrial site. During landfill fire, the concentration of 2,3,7,8-TCDF becomes even higher than the concentration of OCDF and is equal to the concentration of 1,2,3,4,6,7,8-HpCDF.