共查询到18条相似文献,搜索用时 93 毫秒
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烟尘测试中滤筒称重问题张萍萍(福建龙岩地区环境监测站,龙岩364000)①当滤筒放入天平称重时,滤筒湿度较天平内空气湿度小,产生吸湿现象,天平显示不稳。实验表明,最初称量的5个滤筒应放回干燥器内重新干燥、重新称量。②干燥时间的确定:实验表明,在内径为... 相似文献
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介绍了合格滤筒的筛选方法和采样滤筒在实验室分析中的质量控制,分析了影响滤筒称量恒重的原因,指出空气湿度、冷却时间和烘干时间对滤筒称量恒重都有影响. 相似文献
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介绍了影响滤简称量恒重的原因,指出空气湿度、冷却时间和烘干时间等对滤简称量恒重都有影响。提出使用标准空白滤筒、在平衡室中冷却、称量滤筒、并采用专用滤简盒和刚玉滤筒采样减小系统误差。 相似文献
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烟尘监测中应注意滤筒的质量控制 总被引:1,自引:0,他引:1
在烟尘监测中,采用玻璃纤维滤筒收集烟尘,实验室进行滤筒称量时,受实验室环境湿度、冷却时间、烘干时间等因素的影响,对监测结果有显著的影响,且呈现正误差。引入标准空白滤筒的恒重控制分析称量过程,可以消除这些因素引起的误差,提高烟尘监测分析质量。 相似文献
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简述了我国现阶段大气固定污染源颗粒物监测中遇到的问题及低浓度颗粒物采样与分析技术研究的必要性,归纳了国外低浓度颗粒物采样分析技术要点,包括大体积采样、滤筒上游采样设备堆积颗粒物的回收、有效称重步骤的确立等,并对我国开展低浓度颗粒物采样及分析技术研究提出了相关建议. 相似文献
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吴文龙 《环境监测管理与技术》2000,12(4):34-34
对总悬浮颗粒物的测定 ,常采用重量法。采样滤膜应放置在一定温度和湿度的平衡室内 2 4h ,并在此平衡室内进行称量。但目前有许多三、四级环境监测站并不具备如此的称量条件 ,往往在温度、湿度不恒定的条件下称量 ,导致滤膜称量的结果误差较大。为减少称量环境对称重的影响 ,通过多次实践 ,应用空白滤膜修正法 ,较好地解决了这一问题。1 称量操作采样前 ,先将滤膜编号 ,在天平室自然环境中平衡 2 4h ,再将各张滤膜称量并记录 ,抽取其中 1张作为对照空白滤膜。采样后取回的样品滤膜 ,需在天平室和对照空白滤膜再同时平衡 2 4h后称量。若… 相似文献
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BTPM-AS1PM_(2.5)全自动重量法监测仪是一种根据PM_(2.5)手工重量法原理设计的PM_(2.5)自动监测仪器,能够实现样品采集、滤膜平衡、滤膜称重等环节的自动化。采用线性回归分析法对PM_(2.5)全自动重量法监测仪器的监测结果与PM_(2.5)连续自动监测仪器、手工标准方法进行比对分析,讨论了该原理仪器的流量准确性、滤膜平衡效果、天平稳定性。结果显示:PM_(2.5)全自动重量法仪器监测结果与PM_(2.5)连续自动监测仪器、手工重量法监测结果的相关系数为0.927 2~0.994 1,监测结果之间具有较高的一致性,并且其样品采集、滤膜平衡、滤膜称重等关键环节的主要技术指标能够满足中国PM_(2.5)手工标准测定方法的相关要求。 相似文献
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碱性过硫酸钾氧化-气相分子吸收光谱法测定水中总氮 总被引:1,自引:0,他引:1
采用碱性过硫酸钾氧化-气相分子吸收光谱法测定水中总氮,用螺纹盖聚四氟乙烯消化管代替比色管,称重法校正体积,加大NaOH用量,讨论了干扰及消除办法。方法在0μg~20.0μg范围内线性良好,检出限为0.016 mg/L,标准溶液平行测定的RSD≤1.5%,实际水样加标回收率为99.2%~102%,测量结果的扩展不确定度为3.3%。 相似文献
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William T. Mason Jr. Philip A. Lewis Cornelius I. Weber 《Environmental monitoring and assessment》1983,3(1):29-44
Evaluation of analytical methods employed for wet weight (live or preserved samples) of benthic macroinvertebrates reveals that centrifugation at 140 x gravity for one minute yields constant biomass estimates. Less relative centrifugal force increases chance of incomplete removal of body moisture and results in weighing error, while greater force may rupture fragile macroinvertebrates, such as mayflies. Duration of specimen exposure in ethanol, formalin, and formol (formaling-ethanol combinations) causes significant body weight loss with within 48 hr formalin and formol cause less body weight loss than ethanol. However, as all preservatives tested cause body weight loss, preservation time of samples collected for comparative purposes should be treated uniformly. Dry weight estimates of macroinvertebrates are not significantly affected by kind of preservative or duration of exposure. Constant dry weights are attained by oven drying at 103 °C at a minimum of four hours or vacuum oven drying (15 inches of mercury pressure) at 103 °C for a minimum of one hour. Although requiring more time in preparation than oven drying and inalterably changing specimen body shape, freeze drying (10 microns pressure, -55 °C, 24 hr) provides constant dry weights and is advantageous for long term sample storage by minimizing curatorial attention. Constant ash-free dry weights of macroinvertebrate samples are attained by igniting samples at 500–550 °C for a minimum of one hour with slow cooling to room temperature in desiccators before weighing. 相似文献
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Development and validation of methods for environmental monitoring of cyclophosphamide in workplaces
Methods to monitor contamination of workplaces with antineoplastic drugs have been developed and validated. Cyclophosphamide (CP) was used as a model compound as it is one of the most commonly used antineoplastic drugs. A wipe sampling method to detect contamination with CP at surfaces was developed. A personal air sampling method to sample gas and vapour on solid sorbent tubes and particles with filters was also developed. Wipe and filter samples were extracted and sorbent samples were eluted, all with ethyl acetate. The samples were analysed with liquid chromatography tandem mass spectrometry. (2)H(6)-labelled cyclophosphamide was used as an internal standard. The between-day precision was 2-5% for wipe samples, 4-6% for sorbent samples and 3-8% for filter samples. The limit of detection was 0.02 ng CP per sample for the wipe and filter methods and 0.03 ng CP per sample for the solid sorbent method. Wipe sampling on surfaces made of different materials resulted in mean recoveries between 78-106%. The desorption recovery was between 97-102% for the wipe samples, 97% for the sorbent samples and 101% for the filter samples. Samples were stable for up to 2 months at 5 degrees C and -20 degrees C and for about 2 d at room temperature. The developed methods were applied to the measurement of contamination with CP in a hospital pharmacy. Trace amounts of CP, 1.3 and 1.4 ng, were detected on surfaces in the pharmacy. 相似文献
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通过条件实验确定烘箱加热法的恒重条件,确定微波加热法、红外加热法和烘箱加热法测定固体废物水分含量的最佳样品称取量。采用3种方法的最佳条件分别测定了10余种不同类型的固体废物的水分含量,比较了3种方法的测定时间、精密度和测定值的差异性。结果表明:烘箱加热法的最佳恒重条件为前后2次测定差值不超过最终测定质量的±0.1%。烘箱加热法最优称样量范围为25~45 g,红外加热法和微波加热法的最优称样量分别为3.0 g和2.5 g。烘箱加热法所需测定时间最长,约8~28 h,红外加热法和微波加热法所需测定时间分别为4~65 min和1~2 min。3种方法中烘箱加热法精密度最好,且样品水分含量越高精密度越好,烘箱加热法、红外加热法和微波加热法的相对标准偏差范围分别为0.31%~12%、4.6%~18%和1.1%~22%。在0.05的显著性水平上,3种方法测定值不存在显著性差异。 相似文献