利用pH值梯度研究建筑砂浆的酸蚀程度

在两种不同ｐＨ值模拟酸雨和３种浸泡时间条件下，据ｐＨ值梯度测定了各类保护剂处理建筑砂浆试件的酸化层厚度，从而判定保护剂的保护效果，了解酸蚀程度。并分析了影响酸化层厚度的因素。     

麻石文丘里洗涤吸收器在APV尾气处理上的应用

介绍了ＡＰＶ喷雾干燥尾气的性质，原尾气系统存在的问题，改造中采取的措施、原理、流程和取得的效果。实践证明，用“麻石文丘里一次降温、洗涤—ＸＰ型塔板二次洗涤—旋流除雾器除雾”的改造方案，取代原“换热器降温—喷淋塔洗涤—折流脱水器脱水”的流程，取得了良好的降温、洗气和除雾效果，且工程费用低。     

比较研究：德国的企业补充养老保障制度

在养老保障制度中,越来越多的国家采取“三支柱：模式,即法定养老保险为第一支柱,企业补充保障（在我国称为企业年金）为第二支柱,而个人补充保障则为第三支柱.这三大支柱在整个养老保障制度中相互补充,为人们的老年生活构筑一张坚实的保障网络.     

聚天冬氨酸对土壤吸附、解吸汞的机制研究

为揭示土壤中添加聚天冬氨酸(PASP)后其对汞的吸附、解吸过程,探究了不同PASP用量对土壤吸附解吸汞的机制及有机质、pH、汞初始浓度等因素的影响.结果 表明,PASP可显著抑制土壤对汞的吸附,促进土壤对汞的解吸,在PASP用量为300 mg时,其吸附量、解吸量分别是未添加PASP时的0.68、27倍;有机质与PASP...     

典型喀斯特地区土壤退化机理探讨:不同土地利用类型土壤水分性能比较

我国西南喀斯特生态脆弱区以土壤退化为核心的环境退化形势严峻.揭示土壤退化过程和退化机理,是认识喀斯特这个特殊环境的土地生态系统诸多环境退化问题的一个重要途径.本文选择黔中猫跳河流域上游长顺县广顺乡典型喀斯特景观为研究区,通过野外采样和实验室分析,对不同土地利用类型的土壤水分性能进行了比较研究,以探讨喀斯特地区土壤退化的过程与机理.结果表明,与基本无退化的本底林地相比较,草地土壤的水分性能明显变劣,表现为:土壤的持水能力下降,田间持水量和毛管持水量分别下降49.5%和56.2%;土壤供水能力降低,总有效含水量下降56.4%;土壤渗透性能减弱,150 min饱和渗水量减少70.1%.土壤的这些水分特征与土壤发生的强度和速度都有着非常密切的关系,草地土壤水分性能的这种退化将加剧土壤的侵蚀.可以认为,在西南典型喀斯特地区,土壤的水分退化是土壤退化的一个关键过程和因素.     

Fenton试剂处理选矿废水机理研究

研究了用Fenton试剂处理选矿废水中残余的黄药,分别考查了氧化时间、反应初始pH值、Fe2+浓度及H2O2用量对黄药降解效果的影响,用正交试验确定了4个因素的最好条件。结果表明:初始pH值和H2O2用量是影响去除效果的主要因素;氧化时间为60 m in,反应初始pH=4,[Fe2+]=20 mg/L,[H2O2]=20 mg/L,黄药的浓度为125 mg/L时,黄药的去除率达到99.5%;初步探讨了Fenton试剂净化废水中黄药的机理是.OH自由基先将黄药氧化为过氧化黄原酸盐,再将其氧化为CO2,黄药得到去除。     

PM10-PM2.5冲击采样器的研制与开发

在颗粒物研究中,分级采样是一种常用的监测方法,而冲击采样器是颗粒物分级采样的重要仪器.根据斯托克斯数,对PM10-PM2.5冲击采样器设计参数进行了详细分析,并对PM10-PM2.5的捕集效率特征进行了分析.结果表明,PM10-PM2.5冲击采样器具备理想的PM10和PM2.5捕集效率,PM10冲击采样器、PM2.5冲击采样器切割粒径分别为9.94、2.43μm,均在其允许误差范围内.     

铬渣的热解无害化处理

采用热解工艺无害化处理铬渣,探讨了稻秆在铬渣无害化处理中的作用.研究了热解温度、稻秆与铬渣质量比、铬渣粒径及保温时间对铬渣热解无害化处理的影响,并分析了热解前后热解产物中铬元素形态的变化.结果表明,热解工艺能有效地将铬渣中Cr(Ⅵ)还原,稻秆热解过程中产生的气相挥发分对Cr(Ⅵ)的还原起核心作用.较为适宜的热解条件:热解温度为400 ℃,稻秆与铬渣质量比为0.10,铬渣粒径<2 000 μm,保温时间为10 min.在该热解条件处理下,热解产物中的Cr(Ⅵ)质量浓度为121 mg/kg,低于热解前铬渣中的Cr(Ⅵ)(3 400 mg/kg).热解后,可交换态及碳酸盐结合态铬含量降低,大部分铬转化成了稳定的有机结合态和残渣态,极大地降低了铬渣的危害.第一作者:张大磊,男,1982生,博士研究生,研究方向为固体废弃物热处理.     

Bioaccumulation and tissue distribution of organochlorine pesticides (OCPs) in freshwater fishes: a case study performed in Poyang Lake,China’s largest lake

Concentrations and tissue distribution of organochlorine pesticides (OCPs) in different tissues of freshwater fish, silver carp (Hypophthalmichthys molitrix) and bighead carp (Aristichthys nobilis), collected from Poyang Lake, China’s largest shallow lake, and were studied. OCPs were detected with the observed concentrations ranging from 280.67 to 1,006.58 ng/g wet weight (ww) for bighead carp and from 67.28 to 930.06 ng/g ww for silver carp. Composition analysis demonstrated OCPs in both fish were from the same polluted environment, and then, the species-specific bioaccumulation might be mainly due to the different fish age as well as the different feeding habits elucidating from the stable carbon (δ¹³C) and nitrogen (δ¹⁵N) isotope analysis. Tissue distribution indicated that dietary intake was the major exposure route of OCPs for both fish and higher accumulation potency of OCPs by the hepatobiliary-related tissues (such as liver, kidney, bile, and heart). The higher metabolic activities of these tissues elucidating from the higher values of δ¹⁵N might be the potential-determined factor responsible for the tissue-specific accumulation.     

Photocatalytic oxidation of triclosan

In the spring of 2003, there was an outbreak of the severe respiratory syndrome (SARS) in Hong Kong. Health concerns have thus triggered an increased and predominant use of various types of household cleansing agents such as triclosan (5-chloro-2-(2,4-dichlorophenoxy)phenol). However, it has been reported recently that triclosan could be photochemically converted to toxic 2,8-dichlorodibenzo-p-dioxin (2,8-Cl(2)DD) in the environment. It is therefore necessary to develop environmentally friendly methods for the treatment of triclosan. To this end, photocatalytic degradation of triclosan in aqueous solution was conducted using TiO(2) (Degussa P25) under irradiation of UV light (lambda < 365 nm). It was found that triclosan could be degraded by this approach. Hydrogen peroxide was added to enhance the degradation process, and the optimal initial hydrogen peroxide concentration for triclosan degradation was 0.005% (w/v). Product identification indicated that triclosan oxidation occurred at its phenol moiety and yielded quinone and hydroquinone intermediates. The formation of a dichlorophenol intermediate in triclosan degradation suggested bond-breaking of the ether linkage occurred during the process. Moreover, no chlorinated dibenzo-p-dioxin congener was detected. These findings confirm that the photocatalytic degradation of triclosan is an environmentally friendly process.