北京市典型重污染过程中PM2.5载带水溶性无机离子污染特征分析

为研究北京地区冬季PM_(2.5)载带的水溶性无机离子组分污染特征,2013年1月在中国环境科学研究院内采用在线离子色谱(URG-9000B,AIM-IC)对PM_(2.5)中水溶性无机离子(SO_4~(2-)、NO_3~-、Cl~-、NH_4~+、Na~+、K~+、Mg~(2+)、Ca~(2+))进行监测与分析。结果表明,采样期间总水溶性无机离子(TWSI)浓度为61.0μg/m~3,其中二次无机离子SO_4~(2-)、NO_3~-、NH_4~+(SNA)占比达72.3%,在PM_(2.5)中占比为40.29%,表明北京市PM_(2.5)二次污染严重。重污染天[NO_3~-]/[SO_4~(2-)]表明,固定源污染较移动源更为显著。三元相图表明,在空气质量为优的情况下,NH_4~+(在SNA中占比为30.3%~65.5%,下同)主要以NH_4NO_3的形式存在,较少比例以(NH_4)_2SO_4存在;严重污染时,NH_4~+(47.3%~77.9%)主要以(NH_4)_2SO_4形式存在,其次以NH_4NO_3的形式存在,其余的NH_4~+以NH_4Cl的形式存在。[NO_3~-]/[SO_4~(2-)]日变化表明,早、晚机动车高峰影响北京重污染发生。     

重庆市主城区大气水溶性离子在线观测分析

2015年12月—2016年3月期间,利用在线气体与气溶胶成分监测仪(IGAC)在重庆市大气超级站开展连续观测分析,并捕捉到2次持续时间较长的空气重污染过程。对PM_(2.5)中9种水溶性离子及5种气态前体物的观测结果分析表明:NO_3~-、NH_4~+和SO_4~(2-)是重庆市主城区PM_(2.5)中主要的水溶性离子成分,其浓度均表现出明显的日变化特征,主要以(NH4)_2SO_4和NH_4NO_3的形式存在。NH_3和SO_2是最主要的气态污染物。2次重污染过程的水溶性离子组分有明显差异,细颗粒物累积型污染的NH_4~+、SO_4~(2-)、NO_3~-浓度高,二次转化十分明显;春节期间烟花爆竹集中燃放,Cl~-、K~+浓度高,主要属于一次排放;污染期间主要离子组分的同源性特征显著。     

衡阳城区冬季PM2.5中水溶性离子污染特征

为探究衡阳冬季PM_(2.5)和水溶性离子污染特征及其来源,于2019年1月在衡阳市城区采集大气PM_(2.5)样品,使用重量法和离子色谱法测得PM_(2.5)和水溶性离子组分质量浓度,并分析其浓度特征、酸碱度和来源等问题。结果表明:采样期间衡阳大气PM_(2.5)平均质量浓度为94.25μg/m~3,总水溶性离子质量浓度为52.94μg/m~3,占PM_(2.5)总质量浓度的56.43%;阴阳离子当量之比为1.12,PM_(2.5)呈酸性,其中SNA(SO_4~(2-)、NO_3~-和NH_4~+)占总水溶性离子质量浓度的95.06%。污染期间二次转化明显,SNA主要以(NH_4)_2SO_4和NH_4NO_3形式存在。源解析发现大气PM_(2.5)受化石燃料和生物质燃烧、垃圾焚烧、建筑扬尘、气态前体物二次转化、外来输送等多重因素影响,其中机动车尾气排放的NO_x在大气中二次转化形成的硝酸盐是衡阳重污染的最主要原因。     

广州市冬季PM_(2.5)污染过程二次水溶性无机离子组分特征

为了解广州地区灰霾天气成因,基于城市超级站,对2013年12月1日—12月8日期间2次灰霾天气过程的水溶性无机离子污染特征进行研究。结果表明:监测期间二次离子(SNA)SO_4~(2-)、NO_3~-、NH_4~+分别占PM_(2.5)质量浓度的15.8%、7.4%、7.0%;2次污染过程SNA对PM_(2.5)贡献显著,机动车排放和燃煤是PM_(2.5)的主要污染来源。广州冬季属于富氨区,2次污染过程都伴随着NH_4~+显著增加,NH_4~+主要以(NH_4)_2SO_4和NH_4NO_3形式存在。     

连云港春季PM2.5中主要水溶性无机离子污染特征及来源解析

于2017年3月1日—5月31日监测分析了连云港市大气PM_(2.5)中主要水溶性无机离子质量浓度的日变化规律,以及与气象因子、PM10、PM_(2.5)相关性。结果表明,水溶性无机离子质量浓度与环境空气中NO_2、CO、PM_(10)、PM_(2. 5)显著相关,与气温、风速、能见度等呈负相关;日变化呈明显单峰型,峰值出现在08:00左右;水溶性无机离子季度均值为27. 2μg/m~3,占ρ(PM_(2.5))平均50%左右,ρ(NO_3~-)、ρ(SO_4~(2-))和ρ(NH_4~+)占ρ(水溶性无机离子)总85%以上;指出,SO_4~(2-)主要受远距离传输的影响,NO_3~-和NH_4~+主要受局地源的影响。     

武汉市春季大气PM2.5中水溶性离子特征

运用大气PM_(2.5)水溶性组分及其气态前体物在线监测系统(GAC-IC)于2017年3月5—12日对武汉市大气PM_(2.5)中水溶性组分进行了在线监测,分析了PM_(2.5)中主要水溶性离子的化学特征和作用机制。结果表明:实验期间武汉市大气PM_(2.5)中水溶性组分与气态前体物间存在明显的二次转化过程,二次反应是PM_(2.5)的重要来源。监测期间,PM_(2.5)中NO_3~-、SO_4~(2-)和NH_4~+的平均质量浓度分别为24.3、16.9、15.0μg/m~3,是PM_(2.5)中重要的水溶性无机离子,占PM_(2.5)质量浓度的40%~70%。硫氧化率(SOR)和氮氧化率(NOR)平均值分别为0.52和0.27,表现出较为明显的二次污染特征。通过相关性分析发现:监测点位周边大气PM_(2.5)中NH_4~+与NO_3~-、SO_4~(2-)有良好的相关性,且表现为富氨状态,大气中铵能较好地中和SO_4~(2-)和NO_3~-。     

苏州市一次PM_(2.5)污染过程分析及其来源解析

利用TEOM1405F型PM_(2.5)测量仪、MARGA水溶性离子在线分析仪和激光雷达对苏州市2016年8月24日—9月6日PM_(2.5)、水溶性离子和气溶胶垂直分布进行了观测,结合气象数据分析了水溶性离子的变化规律及其主要来源。结果表明,观测期间PM_(2.5)平均值为43.4μg/m3,与2014和2015年同期相比下降了42.9%和40.3%。总水溶性无机离子平均值为24.18μg/m~3,约占ρ(PM_(2.5))55.7%,其中ρ(SO_4~(2-))、ρ(NH_4~+)和ρ(NO_3~-)分别占ρ(总离子)的46.0%、25.8%、21.0%。夜间边界层降低,大气垂直扩散条件较差,是造成ρ(PM_(2.5))及ρ(水溶性离子)显著升高的主要原因。ρ(NO_3~-)/ρ(SO_4~(2-))为0.056~1.939,平均值为0.432,表明固定源(燃煤源)仍然是PM_(2.5)的主要来源;PCA方法表明苏州水溶性离子的主要来源于二次污染和燃烧源、海盐和土壤源以及地面扬尘、建筑尘。     

邢台市采暖季PM2.5中水溶性离子污染特征及来源分析

通过监测邢台市2017年11月15日—2018年3月15日采暖期间大气PM_(2.5)中水溶性离子,得到水溶性离子的污染特征,并结合主成分分析方法讨论不同离子的来源。结果表明,邢台市PM_(2.5)中水溶性离子主要由NO~-_3、SO_4~(2-)、NH~+_4组成,分别占总水溶性离子质量浓度的35.2%、25.7%、20.4%;SNA三元相图表明,NH~+_4、SO_4~(2-)、NO~-_3在PM_(2.5)中占比分别为10.6%～40.2%、20.5%～67.1%、26.4%～56.2%;主成分分析结果表明,PM_(2.5)中水溶性离子的主要来源有二次气溶胶、燃煤、交通源、生物质燃烧和土壤尘。     

南京市城区PM2.5中化学组分演变特征

于2011—2017年在江苏省南京环境监测中心办公楼顶开展PM_(2.5)监测采样,分析其样品中OC、EC、水溶性离子和20余种无机元素等组分演变特征。结果表明,NO3-、SO24-、NH4+、OC、EC等是PM_(2.5)的主要组分,且大部分组分值随ρ(PM_(2.5))降低呈下降趋势; OC在2016—2017年成为占比最大的组分;ρ(NO_3~-)/ρ(SO_4~(2-))由0. 9上升至1. 3,ρ(OC)/ρ(EC)由3. 2上升至3. 6,均呈持续上升趋势;机动车污染和有机碳污染明显加重,南京大气污染类型从传统煤烟型污染向煤烟型与氧化型污染共同主导的复合型污染转变; K~-、Cl~-、SO_4~(2-)等水溶性离子和痕量元素K、Al、Ca、Na、Mg等值持续下降,说明工业污染减排、燃煤总量控制和污染治理、扬尘管控和秸秆禁烧效果显著。     

武汉南郊高校内不同功能区PM2.5化学成分分析

通过在武汉某高校校园的生活区、运动场、实验田区和施工区布设4个采样点,检测分析PM_(2.5)及其中金属元素和水溶性无机离子的含量。结果表明,施工区PM_(2.5)平均值超标0. 3倍,其余三区均达标,校园大气环境总体良好; PM_(2.5)中质量浓度较高的元素为Fe、Mg、Mn、Pb; Cd、Pb的富集因子 100,判断其来源于建筑施工、实验田翻耕、汽车尾气等人为污染; PM_(2.5)中主要水溶性无机离子为SO_4~(2-)和NO_3~-,生活区、施工区的NO_3~-及生活区的SO_4~(2-)主要来源于二次污染,施工区SO_4~(2-)来源于二次污染和施工材料; X射线衍射显示施工区PM_(2.5)中存在石英、高岭石等矿物。     

锅炉烟尘测试中锅炉负荷率的计算方法探讨

GB5468 -91规定 ,锅炉烟尘测试时 ,必须对锅炉的运行负荷进行测试 ,而实际监测过程中 ,许多锅炉房不具备测试的计量条件 ,为了解决这一问题 ,文章提出利用烟气量和空气过剩系数计算锅炉负荷率。在实际监测工作中 ,该方法方便、易于操作 ,所得结果和标准规定方法所得结果有很好的一致性     

城市空气质量周报效用分析

介绍了世界上一些发达国家的空气污染预报的做法和采取的措施,阐述了我国开展空气质量预报的方针和方法,指出了周报是预报的基础工作。叙述了我国空气质量周报的污染参数的选取、污染指数的分级及其浓度限值和污染指数计算及确定,分析并总结了开展城市空气质量周报所发挥的效用是提高公众的环保意识,加大了治理污染的力度,转变了环境监测的职能,促进了环境监测事业的发展     

水中总硬度测量不确定度的评定

采用EDTA滴定法测定水质总硬度的测量不确定度评定。充分考虑测量重复性、标准溶液的配制、滴定等过程对测量的影响,计算水中总硬度的测量相对合成标准不确定度为1·81×10-3。     

贵州黔东南州三板溪水库春季拟多甲藻水华特征

2011年3月13日对贵州省黔东南州三板溪水库进行春季浮游植物调查的结果表明,三板溪水库Ⅱ号采样点(下革东)发生以佩纳形拟多甲藻为优势种的拟多甲藻水华,细胞密度高达1.15×10⁷cell/L;板溪水库总氮的最低值为2.09 mg/L,总磷的最低值为0.95 mg/L,三板溪水库的总氮、总磷含量较丰富,不存在总氮或总磷是限制性因子;通过SPSS16.0统计软件分别进行Pearson 积距相关系数分析表明,氮磷比是三板溪水库发生拟多甲藻水华的主要影响原因。     

Environmental Assessment of the Impact of Ozone to the Neuston of the Sea-Surface Microlayer of the Gulf of Mexico

Substantial amounts of NOx (146 000 t/y) and total hydrocarbons (294 000 t/y) are released to the marine atmosphere by the large number of oil and gas operations over Federal waters of the Gulf of Mexico (GOM). Under appropriate meteorological conditions these emissions react to form ozone (0–54 g/m3 over-water) which can affect the marine environment. Using a dry deposition model, this work examines the amount of ozone derived from oil and gas offshore operations and deposited in the sea surface of the Gulf of Mexico, and assesses its impact on the neuston of the sea-surface microlayer. Surface integrated estimates of ozone deposited from oil and gas operations over the sea surface ranges from 400 kg to 1800 kg which results in sea surface concentrations of 15 g/m3. This estimate and the actual toxic ozone levels suggest no acute, toxic impacts to the neuston. However, indirect effects may occur through changes to the pelagic foodwebs and organic carbon pathways. Another potential pathway for ozone impacting the environment is through the production of bromate. Based on the concentrations and time scales (11–139 days) only sublethal effects appear to occur, but uncertainties associated with this assessment need to be further studied. From an ecological perspective, the environmental impacts and risks of NOx and VOC discharges from offshore platforms need to be assessed for neuston and other components of the marine ecosystem.     

实验室质量管理体系内部审核的实施

在实施GB/T15481-2000 idt ISO/IEC17025:1999标准《检测和校准实验室能力的通用要求》的过程中,通过实验室质量管理体系内部审核的实践与系统分析,识别出内部审核实施阶段的关键环节,提出召开首次会议、收集审核证据、确定审核发现和召开末次会议的技术方法,对提高内部审核的质量和有效性、获得可靠的审核结论具有重要意义。     

二乙氨基二硫代甲酸银试剂质量对测砷的影响

用简单合成了二乙氨基二硫代甲酸银试剂，并比较了自制和市售的二乙氨基二硫人 银对测砷的影响。结果表明，采用自制的二乙氨基二硫代甲酸银能大大降低试剂空白，提高方法的灵敏度和降低检出限，试剂质量明显优于市售产品。     

氨氮测量不确定度的评定

采用纳氏试剂光度法测定水质氨氮的测量不确定度评定,应该考虑工作曲线、测量重复性、标准溶液、仪器读数分辨率等对测量的影响.     

Fractionation of heavy metals and assessment of contamination of the sediments of Lake Titicaca

Chemical weathering is one of the major geochemical processes that control the mobilization of heavy metals. The present study provides the first report on heavy metal fractionation in sediments (8–156 m) of Lake Titicaca (3,820 m a.s.l.), which is shared by the Republic of Peru and the Plurinational State of Bolivia. Both contents of total Cu, Fe, Ni, Co, Mn, Cd, Pb, and Zn and also the fractionation of these heavy metals associated with four different fractions have been determined following the BCR scheme. The principal component analysis suggests that Co, Ni, and Cd can be attributed to natural sources related to the mineralized geological formations. Moreover, the sources of Cu, Fe, and Mn are effluents and wastes generated from mining activities, while Pb and Zn also suggest that their common source is associated to mining activities. According to the Risk Assessment Code, there is a moderate to high risk related to Zn, Pb, Cd, Mn, Co, and Ni mobilization and/or remobilization from the bottom sediment to the water column. Furthermore, the Geoaccumulation Index and the Enrichment Factor reveal that Zn, Pb, and Cd are enriched in the sediments. The results suggest that the effluents from various traditional mining waste sites in both countries are the main source of heavy metal contamination in the sediments of Lake Titicaca.     

Evaluation of method of preparation of passive diffusion tubes for measurement of ambient nitrogen dioxide

This study was carried out in response to suggestions that the measurement of NO(2) by Palmes-type passive diffusion tubes (PDT) is affected by the method of preparation of the triethanolamine (TEA) absorbent coating on the grids. The following combinations of factors were investigated: TEA solvent (acetone or water), volume composition of TEA in solvent (50% or 20%), and grid coating method (dipping in solution prior to assembly or pipetting solution on after assembly). Duplicate PDTs prepared by each of the 8 methods were exposed in parallel, in urban air, for a total of 80 separate 1 week exposures. NO(2) concentrations derived from PDTs prepared by pipetting methods were significantly less precise than concentrations from dipping methods, with mean RSDs for duplicate measurements of 13.8% and 8.5%, respectively (n= 316 each category). Pipetting methods using solutions of 50% TEA composition were particularly imprecise (mean RSD 17.2%). Data from PDTs prepared by pipetting methods were systematically more poorly correlated with each other and with data from co-located chemiluminescence analysers, than corresponding data from PDTs prepared by dipping methods, indicating that more consistent accuracy was also obtained by the latter PDTs. The statistical evidence suggested that PDTs prepared by pipetting 50% TEA in water generally gave lower NO(2) concentrations. Although this is in agreement with a previous study, it is also possible that such an observation here may be a statistical artefact given the demonstrably poorer precision of this method. The general tendency of PDTs to show positive bias in NO(2) measurement in urban air in 1 week exposures was again evident in this study (mean biases at roadside and urban centre locations of +35% (n= 475) and +18% (n= 112), respectively) consistent with augmentation of within-tube NO(2) flux by chemical reaction between co-diffusing NO and O(3). Overall, it is recommended that the pipetting method of PDT grid preparation is avoided, or at least investigated further, because of the apparent degradation in precision and accuracy of NO(2) measurement. Potential reasons for the effect are discussed.