江苏省环境监测现代化建设方案 ( 续 )

2.2.1.2　建设全省水质自动监测系统在市际交界断面、集中饮用水源地、太湖主要出入湖河道、长江及淮河流域的重点断面、南水北调东线江苏段等进行水质实时监控,减少污染事故的发生和因灾害带来的损失,预警饮用水源水质。今后5年,建成省级固定水质自动监测站38个,配置一批水质流动监测车。2.2.1.3　建设全省污染源自动监控系统在占全省65%COD排放量的省控重点污染源安装COD在线监测仪、pH计、污水流量计、等比例采样器;在占全省65%SO2排放量的大气重点污染源安装在线监测仪。建立省总控中心、各市分控中心,实现联网监控。2.2.2　建立遥…     

水质自动采样器在污染源在线监测中的应用

文章分析了我国水质自动采样器的技术现状和技术要求,指出了水质自动采样器与在线监测仪器配套使用过程中发挥的作用,在污染源减排三大体系建设中发挥的管理效能。     

便携式水质检测仪性能综合评价方法研究

目前便携式水质检测仪品种繁多,各种技术指标和性能尚无统一评价标准,导致仪器性能良莠不齐,监测数据质量难以保证,无法满足管理部门对环境监测数据的要求,检测机构在采购过程中也难以选择。为解决这一问题,建立了便携式水质检测仪综合评价方法,确定了综合评价指标,制定了综合评价标准,选择相关仪器及相关项目进行综合评价。结果表明,大部分便携式水质检测仪器在便携性、操作简易性等方面做得比较好,而在准确度、精密度等方面还有待提高。该评价方法综合考虑了影响便携式水质检测仪的各项因素,能够为全方位评价、选择便携式水质检测仪提供参考。     

负压式水质采样器的研制及应用

概述了我国目前水质采样技术规范和水质采样器的现状 ;阐述了负压式水质采样器的结构组成、工作原理及采样方法。该采样器不需电源、携带方便 ,可有效地控制采样深度并实现分层采样。     

对水质自动监测中测量值突变的判别与处理

以程序化方式介绍了判别水质自动监测中测量突变的原因。提出当发现某主要指标异常时，应查看相关指标的运行情况，再校准仪器，并人工同步分析样品。若测定结果的相对偏差大于5％，表明测量仪器故障；若相对偏差小于5％，应继续进行源水分析比对，以判别是仪器故障还是污染事故。通过实例分析，淮南市水质自动监测中DO测量值偏低的原因：一是取水泵安装位置不当，造成负压抽水，使水中DO溢出；二是流程太低，致使管道藻类大量繁殖，消耗了水中DO。解决方法：正确安装取水泵，并加大水泵抽水量，冲刷管道藻类。     

水质总氮、总磷在线自动分析仪的发展现状

对水质总氮和总磷在线自动分析仪的方法原理，主要类型，主要技术特点以及主要仪器型号等发展现状进行了评述。     

水质化学需氧量（COD）在线自动分析仪发展现状

对水质化学需氧量（COD）在线自动分析仪的方法原理、主要类型、主要技术性能以及主要仪器型号等发展现状进行了评述。     

水质凯氏氮标准样品的研究

提出了水质凯氏氮标准样品的研究方法。在研究过程中，完成了样品的配制、均匀性、稳定性等工作。经过多家实验室协作定值，确定了样品的标准值及不确定度，并提供使用。     

水质高锰酸盐指数在线自动分析仪的发展现状

对水质高锰酸盐指数在线自动分析仪的方法原理、主要类型、主要技术性能以及主要仪器型号等发展现状进行了评述。     

建立水质自动监测系统的思考

结合章郭水质自动监测系统的可行性研究，在建立水质自动监测系统过程中对监测站位的选取、监测项目的选择、水质自动监测系统的组成、数据的采集与处理、系统的维护及管理、存在的问题等方面进行探讨，水质自动监测系统的建设可以弥补水质监测的不足，同时为实施总量控制及环境管理提供了可靠的依据。     

废水中石油类总量控制监测的采样技术

污染物总量控制监测的关键是废水采样的时间和空间代表性问题。采用废水连续自动等比例采样器实现时间代表性,用优化点位解决空间代表性,结果表明以石油类为主要污染物的采样断面应选择在水跃区。     

Silver near municipal wastewater discharges into western Lake Ontario,Canada

Because of the widespread use of silver nanoparticles in commercial products, discharges of municipal wastewater may be a point source of silver in the aquatic environment. We monitored two sites in western Lake Ontario impacted by discharges from wastewater treatment plants serving the City of Toronto. Concentrations of silver were elevated in bottom sediments and suspended sediments collected at the two sites. We also deployed two types of passive samplers in the water column at the two sites, the newly developed Carbon Nanotube Integrative Samplers for monitoring “CNIS-labile” silver and Diffusive Gradient in Thin Film samplers for monitoring “DGT-labile” silver. Results from these passive samplers indicated that the concentrations of silver at the two sites were either below detection limits or were in the ng/L range. In laboratory experiments where the sediments were re-suspended in Milli-Q water, a small proportion of the silver (i.e., <?25%) was labile and partitioned as colloidal or dissolved silver into the liquid phase after agitation. Nanoparticles tentatively identified as silver nanoparticles were detected by single-particle ICP-MS in suspension after agitation of both suspended and bottom sediments. Therefore, there is a need to assess whether silver species, including silver nanoparticles are transported from wastewater treatment plants into sediments in the aquatic environment. This study is unique in focusing on the in situ distribution of silver in natural waters and in sediments that are potentially impacted by urban sources of nanoparticles.     

太湖主要入湖河流排污控制量研究

利用2006—2008年的监测数据对太湖主要入湖河流的水环境状况进行了分析,通过对研究区工业污染源、农业污染源和城镇生活污水排污的分布以及入河情况的调查,对各种污染源的入河量进行了计算,根据确定的水质目标,分别计算出主要入湖河流以及区域水系的水环境容量和排污控制量。结果表明:15条主要入湖河流超标现象显著,近3a来污染程度有所波动,N、P污染最为严重。研究区内污染物入河量较大,未接管的生活源污染物入河量所占比重最大,各类污染物均在50%～60%之间;张家港市的污染物入河量最大,各类污染物所占比重达总入河量的18%～20%。研究区内河网密布,水环境容量分布不均匀,望虞河、直湖港、武进港等7条河流水环境容量较大,张家港市区域水环境容量较大。为保证水质达标,研究区内近期共须削减CODCr66554.38t/a、NH4-N8105.71t/a、TP1324.42t/a;远期共须削减CODCr96719.08t/a、NH4-N11541.45t/a、TP1788.71t/a。     

采用分段法研究新洋港入河污染物总量控制目标

将新洋港分为3段,分别对各段的生活、农业、工业污染源进行调查,分析了污染特征。根据社会经济发展情况预测了2012年和2015年的入河污染物总量。综合考虑水文水质和功能区等因素,采用模型计算了2012年和2015年的水环境容量,根据结果制定了新洋港入河污染物总量控制目标。     

过硫酸钠同时消解养殖尾水中总氮和总磷的探索

大部分池塘养殖尾水中总氮、总磷质量浓度偏高,测定过程中需要对样品进行稀释,耗时较长且影响准确度。实验室分析时,通常采用过硫酸钾对尾水样品进行消解,其配置过程对温度要求较高,易析出晶体,且耗时较长。而过硫酸钠易溶于水,受温度影响较小,易配制。因此,分别采用上述2种过硫酸盐消解液对样品进行消解并同时测定总氮、总磷的质量浓度,比较2种消解方式对校准曲线、加标回收率、养殖尾水实际样品测定的影响。结果表明,等质量或等物质的量的过硫酸钠消解液均能满足总氮、总磷的消解要求,且后者消解样品无须改变氢氧化钠的加入量和调整pH值,即可达到同等消解效果。因此,可采用等物质的量的过硫酸钠代替过硫酸钾同时消解养殖尾水中的总氮、总磷。     

Measurement of environmental pollutants using passive sampling devices--a commentary on the current state of the art

Passive sampling devices have been used since the 1970s to measure time-weighted average (TWA) or equilibrium concentrations of pollutants in various environmental matrices (e.g. air, soils and sediments and water). In recent years the popularity of using such samplers has increased and the technology in now well established for the measurement of atmospheric pollutants. This sector has a long experience of using passive samplers in the short- and long-term assessment of air quality in the local environment and on a global scale (e.g. within the United Nations Stockholm Convention on the trans-boundary movement of persistent organic pollutants (POPs) where large networks of samplers on a continental scale have been established). In comparison, the use of passive samplers for monitoring the aquatic environment has been slower to take off. There has, however, been a recent research drive to develop devices for measuring the wide range of pollutants that can be found in environmental waters (e.g. ground, surface, and marine). It is now being recognised that passive samplers can play a valuable role in monitoring water quality within a legislative framework such as the European Union's Water Framework Directive (WFD). The data from these devices can be used alongside the results obtained from conventional spot or bottle sampling to improve risk assessments and to inform decisions on undertaking potentially expensive remedial actions. Such monitoring techniques may have uses within the European Registration, Evaluation, Authorisation & restriction of CHemicals (REACH) Directive and the forthcoming European Marine Strategy Directive. It is expected that the aquatic monitoring sector will follow a transition similar to that which occurred in air monitoring where data obtained from passive samplers can use used within a legal framework. There has also been increased interest in extending the role of passive samplers to both the measurement of equilibrium concentrations and investigating the movement and release of the dissolved fraction of various pollutants in the pore water of sediments and soils.     

浅谈总量监测审验

总结了总量监测存在的问题,提出必须加强对总量监测的审验,阐述了总量监测审验的主要内容和操作。     

我国洗衣粉消费形成的COD总量测

根据水质COD重铬酸钾法，实测了市场上5种常见品牌洗衣粉的COD负荷值，得到其平均值为0．328（w／w）（绝干洗衣粉）。由我国使用量计算得到2005年洗衣粉形成的COD总量为88．87×10^4t，这相当于当年全国工业和生活COD排放总量的6．3％，全国生活COD排放总量的10．3％，2005年我国洗衣粉消费过程COD产污系数为1．86g／（d·人），需要对洗衣粉消费形成的COD总量水平予以必要的关注。     

Field comparison of three inhalable samplers (IOM, PGP-GSP 3.5 and Button) for welding fumes

Inhalable sampler efficiency depends on the aerodynamic size of the airborne particles to be sampled and the wind speed. The aim of this study was to compare the behaviour of three personal inhalable samplers for welding fumes generated by Manual Metal Arc (MMA) and Metal Active Gas (MAG) processes. The selected samplers were the ones available in Spain when the study began: IOM, PGP-GSP 3.5 (GSP) and Button. Sampling was carried out in a welding training center that provided a homogeneous workplace environment. The static sampling assembly used allowed the placement of 12 samplers and 2 cascade impactors simultaneously. 183 samples were collected throughout 2009 and 2010. The range of welding fumes' mass concentrations was from 2 mg m(-3) to 5 mg m(-3). The pooled variation coefficients for the three inhalable samplers were less than or equal to 3.0%. Welding particle size distribution was characterized by a bimodal log-normal distribution, with MMADs of 0.7 μm and 8.2 μm. For these welding aerosols, the Button and the GSP samplers showed a similar performance (P = 0.598). The mean mass concentration ratio was 1.00 ± 0.01. The IOM sampler showed a different performance (P < 0.001). The mean mass concentration ratios were 0.90 ± 0.01 for Button/IOM and 0.92 ± 0.02 for GSP/IOM. This information is useful to consider the measurements accomplished by the IOM, GSP or Button samplers together, in order to assess the exposure at workplaces over time or to study exposure levels in a specific industrial activity, as welding operations.     

Passive ammonia monitoring in the United States: comparing three different sampling devices

The need for ambient gaseous ammonia (NH(3)) measurements has increased in the last decade as reactive NH(3) concentrations and deposition fluxes show little change even with tightening standards on nitrogen oxides (NO(x)) emissions. Currently, there are several networks developing methods for adding NH(3) measurements in the U.S. Gaseous NH(3) measurements will provide scientists and policymakers data which can be used to estimate ecosystem inputs, validate air quality models including trends and regional variability, and evaluate changes to the environment based on additional emission reduction requirements and estimates of critical nitrogen load exceedances. The passive samplers described in this paper were deployed in duplicate or triplicate and collocated with annular denuders or continuous instruments to determine their accuracy. The samplers assessed included the Adapted Low-Cost Passive High Absorption (ALPHA), Radiello(?), and Ogawa passive samplers. The median relative percent differences (MRPD) between the reference method and passive samplers for the ALPHA, Radiello(?) and Ogawa were -2.4%, -37% and -44%, respectively. The precision between duplicate samplers for the ALPHA and Ogawa samplers, was 7% and 6%, respectively. Triplicate Radiello(?) precision was assessed using the coefficient of variation (CV). The CV for the Radiello(?) samplers was 10%. This article discusses the statistical results from these studies.