供水管网生物膜有机物的二氯乙腈与二氯乙酰胺生成特性

在饮用水输配系统中,来源于管壁生物膜的有机物可能耗氯并生成消毒副产物(DBPs),包括二氯乙腈(DCAN)与二氯乙酰胺(DCAcAm)等高毒性含氮DBPs(N-DBPs).研究考察管网常见的细菌与其胞外聚合物(EPS)以及模拟管壁生物膜氯化与氯胺化后DCAN与DCAcAm的生成,并与天然有机物(NOM)和水源水有机物进行比较.结果显示,铜绿假单胞菌、恶臭假单胞菌与藤黄微球菌与氯反应生成的DCAN、DCAcAm浓度分别为1.48～2.02、0.21～0.38μg·mg~(-1)(mg~(-1)以TOC计),高于同反应条件下NOM的生成量;相比于氯化反应,3株细菌细胞氯胺化生成的DCAN与DCAcAm浓度明显更低.3株菌的EPS也是氯与氯胺化反应生成DCAN与DCAcAm的前体物,且其氯胺化反应生成的DCAcAm浓度高于氯化反应生成的.与NOM、水源水相比,模拟管壁生物膜氯化后生成的N-DBPs与三氯甲烷(TCM)浓度比更高,表明生物膜有机物比NOM与水源水有机物更倾向生成DCAN与DCAcAm类N-DBPs,且模拟管壁生物膜氯胺化的DCAcAm生成量高于氯化反应的,说明管壁生物膜有机物是供水管网系统中DCAN与DCAcAm类N-DBPs的重要前体物.     

Insights into multidimensional transport flux from vertical observation and numerical simulation in two cities in North China

This study represents the first quantitative evaluation of pollution transport budget within the boundary layer of typical cities in the Beijing-Tianjin-Hebei (BTH) region from the perspective of horizontal and vertical exchanges and further discusses the impact of the atmospheric boundary layer (ABL)-free troposphere (FT) exchange on concentration of fine particulate matter (PM_2.5) within the ABL during heavy pollution. From the perspective of the transport flux balance relationship, differences in pollution transport characteristics between the two cities is mainly reflected in the ABL-FT exchange effect. The FT mainly flowed into the ABL in BJ, while in SJZ, the outflow from the ABL to the FT was more intense. Combined with an analysis of vertical wind profile distribution, BJ was found to be more susceptible to the influence of northwest cold high prevailing in winter, while sinking of strong cold air allowed the FT flowing into the ABL influence the vertical exchange over BJ. In addition, we selected a typical pollution event for targeted analysis to understand mechanistic details of the influence of ABL-FT exchange on the pollution event. These results showed that ABL-FT interaction played an important role in PM_2.5 concentration within the ABL during heavy pollution. Especially in the early stage of heavy pollution, FT transport contributed as much as 82.74% of PM_2.5 within the ABL. These findings are significant for improving our understanding of pollution transport characteristics within the boundary layer and the effect of ABL-FT exchange on air quality.     

First-trimester free beta (hCG) screening for Down syndrome

Maternal serum free beta (hCG) levels are elevated (median 2·20 MOM) in the first trimester of pregnancy in 38 Down syndrome cases as compared with appropriate controls. This observation may form the basis for its use as a marker in screening for Down syndrome in the first trimester. Altered levels of the free beta analyte are observed in pregnancy conditions or complications other than Down syndrome.     

甲基橙褪色法测定生活饮用水中余氯的探讨

在酸性介质中,余氯使甲基橙褪色,最大吸收波长510 nm,摩尔吸光系数A510=5.41×10-3 l/mol·cm,余氯质量浓度在(0.05～1.00) mg/l范围内遵守朗伯--比耳定律.对甲基橙溶液的加入量、样品溶液褪色后其吸光值的稳定性等方面作了条件试验,同时与邻联甲苯胺(OT)比色法和N,N-二乙基对苯二胺(DPD)分光光度法进行比对测定,结果表明三种方法测定结果基本一致.     

液氯泄漏事故模拟分析

针对1996年1月21日在西班牙发生的一起液氯泄漏事故的后果进行了模拟分析。模拟分析结果同事故实际所造成的后果是一致的。表明采用基于数学模型的事故后果模拟分析具有一定程度的可靠性。对于救灾和对重大危险源编制应急事故预案有一定程度的指导意义。     

氯灭活地下水源中3种优势真菌的效能与机制

地下水源中真菌大量繁殖会产生嗅味,引发毒性反应以及产生大量肉眼可见的絮状物,严重影响供水水质.以地下水源中3种优势真菌木霉属、青霉属、枝孢属为研究对象,以氯为消毒剂,通过研究真菌孢子胞内物质泄漏,胞外三磷酸腺苷(ATP),脱氧核糖核酸(DNA)和蛋白质增加及孢子形态变化,探明了氯灭活3种真菌孢子的效能与机制.结果表明,氯灭活真菌孢子符合一级动力学,满足Chick模型,3种真菌的耐氯性为:木霉属青霉属枝孢属,真菌孢子尺寸越大,亲水性越强,灭活效果越好.氯灭活后,胞内物质泄漏,胞外特征物质(ATP、DNA、蛋白质)显著增加;氯对细胞表面破坏严重,灭活后真菌孢子凹陷,表面褶皱.综上所述,氯首先作用于孢子表面,降低孢子的可培养性,进一步作用使细胞的通透性屏障受损,导致胞内特征物质释放,以致孢子死亡.     

液氯泄露环境风险评价

文章以如东易昌化工有限公司为例,按照《建设项目环境风险评价导则》的要求,在对液氯的理化性质及危险性识别的基础上,分别进行了风险识别、伴生/次生危险性分析、源项分析等工作,确定了此次风险评价采用的相关标准,采用导则推荐的多烟团模式进行了事故发生后液氯泄露的环境风险预测和评价,得出了不利气象条件下的事故风险影响范围,求得了最大风险值,并从氯气瓶库及供氯站设置、生产过程等方面提出了相关的风险管理措施。     

我国建设内陆核电站对环境的影响

未来十年我国内陆核电将处在快速增长的阶段,本文以内陆核电站发电原理为基础,考察污染产生种类及成因,探讨我国内陆核电站在正常运营情况下可能对环境产生的影响,并思考发展方向。     

氯碱企业生产过程中的重大危害分析及对策

分析了氯碱企业生产过程中的重大危害为中毒和火灾爆炸,提出了相应的对策.     

曝气生物滤池的短程硝化特性

通过控制进水pH值实现曝气生物滤池的短程硝化。工艺运行结果表明,对于进水pH值为8.22~8.57,NH4+-N平均容积负荷为0.5 kg/(m3.d),水温为17.5~20.2℃,曝气生物滤池溶解氧质量浓度平均为4.5 mg/L的条件下能够同步实现95%的NH4+-N去除率和80%的NO2--N积累率。通过分析FA和FNA沿滤池高度的变化特征,发现滤池底部(0~5 cm)区域短程硝化反应主要由FA控制,中部(5~15 cm)区域是由FA和FNA共同掌控;而上部区域(15~50 cm)则是由FNA控制,FNA沿滤池高度的快速增加是确保工艺实现稳定亚硝酸盐积累的重要原因。