β射线法空气PM_(10)监测结果的准确性探讨

目前国内有很多地市使用β射线法仪器监测空气PM10,本文结合实际,在国内PM10连续自动监测质量控制体系相对薄弱且国家尚未开展标准膜片检定与溯源的情况下,对在用β射线法仪器PM10监测结果的准确性进行了一些实验探讨,期望能提供给同行参考。     

新疆城市环境空气PM_(10)自动监测仪器质控巡检工作探析

随着城市环境空气质量自动监测业务现代化的飞速发展,新疆城市共安装38套PM10环境空气自动监测系统。本文通过对新疆19个城市空气自动监测系统PM10的巡检和质控考核,发现近几年来该系统运行维护中的诸多问题,从而提出仪器维护注意事项,以期提高新疆城市PM10监测数据质量,准确反映环境空气质量状况,为环境管理和政府决策提供更加科学、准确、可靠的基础监测数据。     

利用空气自动监测车仪器对空气自动监测站仪器进行质量保证及质量控制的可行性分析

通过对辖区内空气自动监测车仪器与4家公司空气自动监测站仪器的比对分析,得出了空气自动监测车仪器与空气自动监测站仪器的PM10、SO2、NO2相对误差分别为:-32.8%、4.4%、-8.7%,仪器之间显现出良好的线性关系,从比对结果来看,利用空气自动监测车对空气自动监测站进行质量保证和质量控制是可行的.     

β射线吸收法双通道PM_(2.5)/PM_(10)监测装置性能探究

根据中国环境保护产品认证标准(CCEP)的技术规范,结合美国环境保护署(EPA)关于环境空气监测参考指标和等效检测方法,对赛默飞世尔最新开发的双通道颗粒物自动监测装置的主要性能指标进行分析表征。用3台待测双通道5028i型和2台参照单通道5014i型颗粒物自动监测装置连续2个月自动监测大气颗粒物PM2.5和PM10,考察双通道颗粒物自动监测装置关于仪器精度、仪器准确度、流量稳定性和准确性等方面的性能。     

空气自动监测与连续监测测定值的对比分析

确定空气自动监测与连续监测的相关性,对保证监测数据的连续性、可比性和正确判断环境空气质量的变化规律有重要的作用。对比实验空气的自动监测系统和连续监测系统,两者的监测值存在一定差异。1　实验1 1　分析方法SO2、NO2、PM10的自动监测方法和连续监测方法见表1。表1　SO2、NO2、PM10的自动监测方法和连续监测方法项目自动监测连续监测SO2ISO/CD10498紫外-荧光法GB/T15262-94甲醛吸收副玫瑰苯胺分光光度法NO2ISO7996化学发光法GB/T15435-95Saltzman法PM10β射线法GB6921-86重量法1 2　主要仪器自动监测仪(采样系统为…     

基于空气质量自动监测站PM10滤纸的新型大气二NFDA1英监测技术研究

通过典型空气质量自动监测站PM10滤纸(结合气固相分配模拟)和传统大流量大气采样仪的比对试验,探讨了基于空气质量自动监测站PM10滤纸的新型大气二英监测技术的可行性。研究表明,基于空气质量自动监测站PM10滤纸的大气固相二英毒性当量浓度和指纹特征与传统大流量大气监测技术的监测结果具有很好的可比性;基于空气质量自动监测站PM10滤纸气固相分配模拟(利用Harner-Bidleman模型)的大气二英毒性当量浓度和指纹特征与传统大流量大气监测技术的监测结果具有很好的可比性。与传统大流量大气监测技术相比,基于空气质量自动监测站PM10滤纸的新型大气二英监测技术可以利用现有的大气自动监测网络和气固相分配模型,具有采样成本低、代表性强和易于普及等优点,适合不同区域尺度大气二英的长期同步监测。     

基于GIS的石家庄市PM10和PM2.5时空分布研究

利用2018年261个乡镇环境空气自动监测站监测数据,结合GIS空间分析技术,对石家庄市PM10和PM2.5的时空污染特征进行了研究。结果表明,石家庄地区PM10和PM2.5污染的空间分布整体表现为西北部山区好于东南部的平原地区,主城区好于周边县(市、区)的特征。采暖期PM10和PM2.5的污染程度明显重于非采暖期。PM2.5稳定性差于PM10,PM10和PM2.5的稳定性与污染程度具有一定的负相关性,表现出污染越轻的区域稳定性越差。两者的日均值浓度变化在时间序列上呈极强正相关,且污染越重的区域时间相关性越强。与日均值相关性不同,污染程度越轻的区域PM10和PM2.5年均值的线性相关性越强。     

空气自动监测中PM2.5与PM10 “倒挂”现象特征及原因

采用不同原理的自动监测仪器在不同季节同时测定PM2.5与PM10,对所得数据中的PM2.5与PM10"倒挂"现象进行分析。结果表明,当PM10采用振荡天平法时,PM2.5与PM10的"倒挂"率较高;冬季和夏季"倒挂"现象发生率明显高于其他季节;造成PM2.5与PM10"倒挂"的原因主要有监测过程中的随机误差,PM2.5与PM10的监测方法原理不同,监测方法之间存在显著差异等。     

乌鲁木齐市2011年冬季PM2.5/PM10浓度特征分析

利用乌鲁木齐市PM2.5//PM10自动监测数据,分析PM2.5与PM10的浓度分布特征和时间变化规律。结果表明,按照《环境空气质量标准》(二次征求意见稿)的标准限值,乌鲁木齐市冬季PM2.5污染重于PM10。PM2.5浓度为0.164mg/m3,超过二级年标准限值的3.7倍,超标率为73.9%。PM2.5浓度日变化曲线昼高夜低,呈单峰型,峰值出现在13:00~14:00(北京时间)。PM10中PM2.5所占比例较高,PM2.5/PM10为0.79,相关分析和检验显示PM2.5与PM10的线性相关显著,相关系数为0.92。     

大气颗粒物监测分析及今后研究课题

概述了 PM1 0 和 PM2 .5今后的研究方向。目前我国尚未开展 PM2 .5的常规监测 ,PM1 0 的自动监测中尚存在一些技术问题 ,且尚未公布 PM1 0 自动监测的技术性标准 ,为了满足各级环境监测站的工作需求 ,在附录中介绍了国外关于PM1 0 和 PM2 .5的监测仪器和方法标准 ,并介绍了 2 0 0 0年日本颁布的 PM2 .5自动监测技术规定     

自动监测仪器检测方法规范化的研究

文章对进口自动监测仪器检测方法的规范化进行了初步的研究 ,提出了一系列仪器检测的规范化方法。以 NO-NO2 -NOX 分析仪和 PM1 0 采样仪为例进行具体说明 ,然后给出了规范化验收的一般步骤 ,并且专门设计出在进行仪器验收时所用的记录表格。该规范化方法不仅可用于监测仪器的验收工作 ,同时可用于其它分析仪器的常规化质检工作     

Comparison of the SidePak personal monitor with the Aerosol Particle Sizer (APS)

The aim of this study was to compare the performance of the TSI Aerodynamic Particle Sizer (APS) and the TSI portable photometer SidePak to measure airborne oil mist particulate matter (PM) with aerodynamic diameters below 10 μm, 2.5 μm and 1 μm (PM(10), PM(2.5) and PM(1)). Three SidePaks each fitted with either a PM(10), PM(2.5) or a PM(1) impactor and an APS were run side by side in a controlled chamber. Oil mist from two different mineral oils and two different drilling fluid systems commonly used in offshore drilling technologies were generated using a nebulizer. Compared to the APS, the SidePaks overestimated the concentration of PM(10) and PM(2.5) by one order of magnitude and PM(1) concentrations by two orders of magnitude after exposure to oil mist for 3.3-6.5 min at concentrations ranging from 0.003 to 18.1 mg m(-3) for PM(10), 0.002 to 3.96 mg m(-3) for PM(2.5) and 0.001 to 0.418 mg m(-3) for PM(1) (as measured by the APS). In a second experiment a SidePak monitor previously exposed to oil mist overestimated PM(10) concentrations by 27% compared to measurements from another SidePak never exposed to oil mist. This could be a result of condensation of oil mist droplets in the optical system of the SidePak. The SidePak is a very useful instrument for personal monitoring in occupational hygiene due to its light weight and quiet pump. However, it may not be suitable for the measurement of particle concentrations from oil mist.     

西宁冬季PM2.5和PM10手工与自动监测现状研究

为研究PM_(2.5)和PM_(10)手工与自动监测仪器在高海拔地区的适用性,于2014年12月至2015年1月(冬季)在青海省西宁市开展了为期34 d的监测比对实验。PM监测数据表明:手工监测数据之间都有差异,除了受监测滤膜种类的影响,还存在监测仪器间的系统误差。石英滤膜的PM监测数据都高于聚丙烯滤膜,尤其是PM_(2.5)更为明显,偏高近1/4;石英滤膜与聚丙烯滤膜的PM监测数据具有较好的相关性,PM_(10)监测数据的相关系数为0.97。自动监测数据之间进行了同期比对研究,发现TEOM1405DF(微振荡天平法)和APM-2(β射线法)的PM监测值较低,BAM-1020(β射线法)的PM监测值最高;而Grimm(光散射法)的PM监测值居中。BAM1020配备动态加热系统(DHS),其PM监测数据比没有配备DHS的APM-2偏高40%。基于PM监测比对研究,建议在空气污染严重时加密对各监测仪器的运行维护,并加强长期观测以全面评估PM监测。     

RP-1400a大气颗粒物(PM10)监测仪的日常维护经验

RP-1400a大气颗粒物(PM10)监测仪的日常维护和常见故障排除方法的一些经验.     

Source apportionment of PM10 and PM(2.5) at Tocopilla, Chile (22 degrees 05' S, 70 degrees 12' W)

Tocopilla is located on the coast of Northern Chile, within an arid region that extends from 30 degrees S to the border with Perú. The major industrial activities are related to the copper mining industry. A measurement campaign was conducted during March and April 2006 to determine ambient PM10 and PM(2.5) concentrations in the city. The results showed significantly higher PM10 concentrations in the southern part of the city (117 microg/m3) compared with 79 and 80 (microg/m3) in the central and northern sites. By contrast, ambient PM2.5 concentrations had a more uniform spatial distribution across the city, around 20 (microg/m3). In order to conduct a source apportionment, daily PM10 and PM(2.5) samples were analyzed for elements by XRF. EPA's Positive Matrix Factorization software was used to interpret the results of the chemical compositions. The major source contributing to PM(2.5) at sites 1, 2 and 3, respectively are: (a) sulfates, with approximately 50% of PM2.5 concentrations at the three sites; (b) fugitive emissions from fertilizer storage and handling, with 16%, 21% and 10%; (c) Coal and residual oil combustion, with 15%, 15% and 4%; (d) Sea salt, 5%, 6% and 16%; (e) Copper ore processing, 4%, 5% and 15%; and (f) a mixed dust source with 11%, 7% and 4%. Results for PM10--at sites 1, 2 and 3, respectively--show that the major contributors are: (a) sea salt source with 36%, 32% and 36% of the PM10 concentration; (b) copper processing emissions mixed with airborne soil dust with 6.6%, 11.5% and 41%; (c) sulfates with 31%, 31% and 12%; (d) a mixed dust source with 16%, 12% and 10%, and (e) the fertilizer stockpile emissions, with 11%, 14% and 2% of the PM10 concentration. The high natural background of PM10 implies that major reductions in anthropogenic emissions of PM10 and SO2 would be required to attain ambient air quality standards for PM10; those reductions would curb down ambient PM(2.5) concentrations as well.     

PM10 Concentration Measurements in Dublin City

Mass Concentration of ambient particulate matter with an aerodynamic diameter less than 10µm (PM10) are reported for the first time for a range of sites in Dublin City over a 6 month period from January 1st 1996 to June 30th 1996. PM10 gravimetric mass concentration measurements are made with low flow Partisol 2000 air samplers using an impaction type PM10 inlet and 47mm diameter glass fibre filters. In addition, much finer time resolution measurements (minimum sampling frequency of 30 minutes) are made using a tapered element oscillating microbalance (TEOM) PM10 mass monitor. These PM10 mass concentrations methods are also compared with mass concentration inferred using the standard black smoke method. Analysis of the ambient mass concentration data with reference to traffic density and meteorological influences are presented. Results for the first six months of 1996 show that the average PM10 values range from a high of 49 µg m-3 at the Dublin city centre site to 14 µg m-3 at one of the suburban sites. Intercomparison between PM10 and black smoke mass concentrations show that the relationship is site specific. Statistical analysis between PM10 levels and car traffic number show a positive correlation while a weak negative correlation is found between PM10 levels and rainfall amount, wind speed and air temperature.     

2005—2010年沙尘天气影响我国城市环境空气质量分析

根据2005年建成较完整的环保重点城市空气质量日报监测网后的监测数据,分析2005—2010年期间,影响113个环保重点城市空气质量的沙尘天气过程次数范围在每年5~14次之间,平均每年10次左右,总计59次。在此期间,影响113个重点城市空气质量的沙尘天气过程累计的影响时间总计130 d,平均在每年22 d左右。影响环保重点城市的沙尘天气过程主要集中在3—5月,在部分年份的1—2月、6月和11—12月也有出现。受沙尘天气影响,113个重点城市总共的超标天次平均每年在332 d次左右,每年范围在147~546 d次之间。其中,受沙尘暴天气影响的重污染天次平均每年在40 d次左右,每年范围在14~78 d次之间。受沙尘暴天气影响的超标天和重污染天主要出现在3~5月。近年来沙尘天气对我国尤其是北方地区的影响程度很大。每年沙尘天气过程对我国城市空气质量影响的时间不短,尤其在春季对我国东中部地区城市造成了很严重的影响,近年大范围的沙尘天气过程还影响到了我国东南包括台湾地区和香港澳门地区。     

浅谈阿图什市近3年干旱气候与沙尘暴的影响及其对策

为了研究阿图什市干旱气候的变化和沙尘暴频发的原因，利用阿图什市2005-2007年连续3年的降水量、湿度、PM10浓度、风速、温度与沙尘暴的频发次数相关的气象数据资料，提出改变干旱气候及减少沙尘暴频发的建议，为阿图什市发展生态城市建设提供科学依据。