地表水采测分离现场监测质量监督与量化评估

分析了地表水采测分离现场监测引入社会化服务后面临的质量监管难点,从建立监测人员能力考核和资质管理制度、制定质量监督和评估机制、完善现场采样监测质控要素和原始记录清单等3个方面讨论了采测分离模式现场监测的质控管理措施。在此基础上,制定了涵盖技术人员资质能力、机构监测能力、质控样品合格率、交接样品合格率和现场质量抽查结果等5个要素的量化评估方案,并明确了各要素包含的评价指数及权重。     

浅谈全面加强现场监测的质量监督

简述了现场监测质量监督的重要性;明确了做好现场监测质量监督的前提条件;并从现场监测人员业务水平状况、现场监测准备、现场监测仪器日常管理、现场监测工作、数据、报告审核等5个环节详细论述了如何加强质量监督,提高现场监测的质量和效率.     

基于EQI的新疆生产建设兵团生态质量监测体系构建

在推动开展全国生态质量监测评估的背景下，分析了新疆生产建设兵团生态监测工作现状及开展生态质量监测的必要性。从优化生态环境监测机构职能、强化生态质量监测人才培养机制、推进科技项目引领示范等角度，提出了兵团生态质量监测体系的构建思路，以及生态质量综合监测站建设、生态质量样地监测、生态遥感监测与评价等重点任务。     

开展水质手工监测质量核查工作的思考

水环境质量监测数据是客观评价水质状况、反映水污染防治成效、实施水环境管理与决策的基本依据。提高水环境监测数据质量,是建立科学制定水生态环境治理政策的重要前提,是实现生态环境治理体系和治理能力现代化的内在需要,也是深入打好碧水保卫战、提高政府公信力、维护公众环境权益的有力保障。然而,目前新疆水环境质量监测工作尚存在许多亟待完善的问题,监测数据失真现象时有发生,导致监测结果难以客观真实反映新疆水环境质量实际状况。为了加强水环境质量监测的监督管理,本文分析了新疆水环境质量监测工作存在的问题以及开展水质手工监测质量核查工作的必要性,并对如何开展水质手工监测质量核查进行了深入探讨。     

关于四川省社会化生态环境监测机构监管的现状与思考

本文分析了四川省社会化生态环境监测机构发展的原因与现状,指出了社会化生态环境监测机构存在的问题,阐述了四川社会化生态环境监测机构监管的现状,提出了构建责任明确的生态环境监测责任体系、加强监测数据质量监管、合理利用环境经济学手段等监管的思考和建议。     

环境监测实验室质量监督之管见

阐述了环境监测实验室质量监督的重要性及加强质量监督的组织保证、制度建设、工作程序和如何发挥监督作用的思考,以期改善忽视质量监督的局面,进一步提高监测工作质量.     

火力发电企业排污自行监测质量提升

针对目前火力发电企业排污自行监测过程中存在的质量管理体系不完善、手工监测能力不足、对外委监测机构监督环节薄弱等突出问题,从质量管理体系建设、质量控制机制建立、第三方检测机构选择及智能化手段应用四个方面提出火力发电企业排污自行监测质量提升改进建议,为自行监测数据结果的科学性、准确性提供可靠的质量保证。     

生态环境监测机构数据质量技术判断常见方法探讨

环境监测数据是客观评价环境质量状况、反映污染治理成效、实施环境管理与决策的基本依据。为了进一步加强环境监测过程管理,有效提高环境监测数据质量,以列举法对影响生态环境监测机构数据质量的样品采集、运输、交接和实验室分析等监测活动的各环节进行了技术分析,梳理总结了数据质量技术判断的常见方法,旨在为环境管理部门开展监督管理提供经验借鉴。同时,就进一步提高生态环境监测机构的监测数据质量提出了建议。     

烟尘烟气监测全程序质量监督评价方法研究

建立了烟尘、烟气监测全程序质量监督体系,确定了监督检查工作需要控制的环节,并细化了各环节需要重点关注的内容。以层次分析法等关键技术为基础,通过赋予监测全过程各环节不同的指标权重,建立了统一化、标准化的综合评价模式。研究将评价体系分为2个层次,一级指标3个,二级指标19个,并确定了每个指标的测评内容及计算方法。将该体系应用于6家监测机构的质量监督工作,证明其实用性和适用性良好。     

流域水环境监测质量管理系统设计与实现

目前的水环境监测工作需要建立统一的水环境监测质量管理系统,这对于各级、各地水环境监测质量控制信息的规范化录入和分级汇总统计、信息共享具有重要的意义.在分析目前水环境监测质量管理存在问题的基础上,基于网络服务、地理信息等技术,设计实现了水环境监测质量管理系统.利用该系统,各级、各地水环境监测质量管理部门能够进行监测机构、持证人员、监测项目、仪器设备等信息的录入和定期维护,同时共享监测方法、政策法规、标准规范、标准物质等信息.同时上级管理部门能够查看、统计所辖部门的水环境监测质量控制信息,从而为流域水环境突发事件应急资源调配、辅助决策等提供信息支撑.     

我国沙尘暴灾害及其治理对策初步研究

分析研究了沙尘暴的成因、时空分布、发展趋势及造成的灾害，结合国外经验提出了我国治理的对策建议。     

新疆室内环境污染监测和治理工作现状与建议

针对目前室内环境监测工作出现的种种问题,就如何规范的开展室内环境监测工作,更好地为社会提供真实、准确、有效的监测数据,本文提出相关的探讨。     

太原市冬、夏季醛酮化合物污染特征及来源分析

针对太原市空气臭氧污染较为严重的问题,开展臭氧主要前体物醛酮化合物质量浓度及其变化规律研究.利用2,4-二硝基苯肼固相吸附/高效液相色谱方法,通过对太原市2019年冬季和夏季大气的醛酮化合物进行分析,发现太原市冬季总醛酮化合物的平均质量浓度为13μg/m3,低于夏季的27μg/m3.其中甲醛、乙醛和丙酮质量浓度最高,且...     

Dissipation and residue of metalaxyl and cymoxanil in pepper and soil

A simple and accurate method of determining metalaxyl and cymoxanil in pepper and soil was developed by ultra-performance liquid chromatography–photodiode array detection. The limits of detection were 0.015 mg/kg for metalaxyl and 0.003 mg/kg for cymoxanil. The limits of quantification were 0.05 mg/kg for metalaxyl in pepper and soil as well as 0.01 mg/kg for cymoxanil in pepper and soil. Recoveries of pepper and soil were investigated at three spiking levels and ranged within 77.52 to 102.05 % for metalaxyl and 87.15 to 103.21 % for cymoxanil, with relative standard deviations below 9.30 %. For field experiments, the half-lives of metalaxyl were 3.2 to 3.9 days in pepper and 4.4 to 9.5 days in soil at the three experimental locations in China. At harvest, pepper samples were found to contain metalaxyl and cymoxanil well below the maximum residue limit MRLs of the European Union (EU) following the recommended dosage and the interval of 21 days after last application.     

Disembodied and Disembedded? The Social and Economic Implications of Atmospheric Change and Biodiversity

The social and economic implications of atmospheric change on biodiversity need to be seen in a global context of major shifts in the conceptualization and management of our relationship with nature. Traditionally, we have conceptualized the atmosphere and the other creatures of the biosphere as separate from the human, but their quasi-autonomy is now becoming subject to more and more human management. This raises not only economic issues, but social, political, and ethical concerns that will have substantial influence on public policy. Among these are the commodification of genetic material; the privatization of traditional knowledge; and the management of information. In this broader context, the paper examines an array of current and proposed strategies of response to changes in biodiversity as a result of climatic and other stresses.     

Atmospheric Change and Biodiversity: Co-Networks and Networking

Canada responded to the Global Biodiversity Convention by completing the Canadian Biodiversity Strategy in 1995. At the same time, Environment Canada also completed a national Science Assessment on Biodiversity. During this period, the Smithsonian Institution, in partnership with Parks and Environment Canada, initiated the implementation of a global biodiversity monitoring program in Canada. Under the auspices of the United Nations Man and the Biosphere Program, the SI/MAB monitoring protocols and plots have spread across Canada at an unprecedented rate. National champions in the science and educational sectors, working within an inter-disciplinary ecological framework, have guided the development, education, quality control and sharing of atmosphere-biodiversity observations electronically.Atmospheric-Biodiversity Networks and Networking have traditionally operated within separate mandates with little degree of integration. Air-Bio Networks were designed within an integrated framework to better understand the atmospheric stress on biodiversity and the adaptation actions, nationally and regionally. Detailed examples of the cumulative effects of climate change, stratospheric ozone depletion, acid deposition, ground-level ozone, suspended particulate matter and hazardous air pollutants on biodiversity will be discussed using a Southern Ontario case study. In addition, recommendations will be presented for future paired SI/MAB plots, linked networks and networking for adaptation within the context of climate, chemical and ecological gradients.     

Determination and study on dissipation and residue of bismerthiazol and its metabolite in Chinese cabbage and soil

A simple and accurate method for the determination of bismerthiazol and its metabolite 2-amino-5-mercapto-1,3,4-thiadiazole was developed in Chinese cabbage and soil by high-performance liquid chromatography-diode array detection in this study. The limits of detection were 0.06 mg/kg for bismerthiazol and 0.03 mg/kg for 2-amino-5-mercapto-1,3,4-thiadiazole, respectively. Recoveries of cabbage and soil were investigated at three spiking levels and were in the range of 84.0–96.0 % for bismerthiazol and 71.0–74.6 % for 2-amino-5-mercapto-1,3,4-thiadiazole, with relative standard deviations below 7.0 %. For field experiments, the half-life of bismerthiazol was 2.4–2.5 days in Chinese cabbage and 2.5–4.8 days in soil at the two experimental locations in China. Dissipation residues of 2-amino-5-mercapto-1,3,4-thiadiazole were lower than 0.72 mg/kg. Terminal residues of bismerthiazol and its metabolite were less than 3.0 and 0.3 mg/kg in Chinese cabbage, respectively. No bismerthiazol or metabolite residues were detected in soil on days 5, 7, 10, and 14 after the last spraying at the two dosage levels.     

环境监理与环境管理的区别与联系

阐述了环境监理与环境管理的关系，指出了以制度和程序规范两者的分工与合作可充分发挥环境监理在环境管理中的作用     

废旧干电池的环境污染防治及回收利用

介绍了各种干电池的基本化学组成，分析了废旧干电池污染环境的主要途径及对人类的危害，并就回收利用问题提出建议。     

Residues and dissipation of trifloxystrobin and its metabolite in tomatoes and soil

A simple residue analytical method using the quick, easy, cheap, effective, rugged, and safe (QuEChERS) procedure for the determination of trifloxystrobin and its metabolite trifloxystrobin acid (CGA321113) in tomato and soil was developed using high-performance liquid chromatography-tandem mass spectrometry (HPLC-MS/MS). The limits of detection were 0.0005 mg/kg for trifloxystrobin and 0.001 mg/kg for trifloxystrobin acid, respectively. The average recoveries in tomato and soil ranged from 73–99 % for trifloxystrobin and 75–109 % for trifloxystrobin acid, with relative standard deviations below 15 %. The method was then used to study the dissipation and residues in tomato and soil. The dissipation half-lives of trifloxystrobin in tomato were 2.9 days (Beijing) and 5.4 days (Shandong), while in soil were 1.9 days (Beijing) and 3.0 days (Shandong), respectively. The final results showed that the major residue compound was trifloxystrobin in tomato whereas it was its metabolite, trifloxystrobin acid, in soil. The final residues of total trifloxystrobin (including trifloxystrobin acid) were below the EU maximum residue limit of 0.5 mg kg^?1 in tomato 3 days after the treatment.