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Development and Types of Passive Samplers for Monitoring Atmospheric NO2 and NH3 Concentrations

机译:用于监测大气中NO2和NH3浓度的无源采样器的开发和类型

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摘要

Numerous passive samplers based on the ‘Palmes-tube’ have been developed for ambient air monitoring. In each case, the diffusion path length and/or crosssectional area are modified to achieve the desired sampling rate. ‘Tube-type’ samplers are low sensitivity samplers suitable for long-term monitoring, whereas the ‘badge-type’ samplers have faster sampling rates suited to short-term monitoring. In the U.K., diffusion tubes are widely used for monitoring nitrogen dioxide (NO2) and ammonia (NH3). The open-ended diffusion tubes are prone to positive bias caused by incursion of wind eddies, leading to a shortening of the diffusion path. By using a porous membrane at the inlet, wind incursion is prevented, but an additional diffusion resistance is imposed and it is necessary to calibrate the tubes against a reference method to obtain an effective sampling rate. For NO2 sampling, positive bias also arises from the reaction of NO with O3 within the sampler. The interference from the chemical reaction is severe close to NO sources, with errors up to 30% for curbside locations when using the ‘tubetype’ sampler. In rural areas, where NO concentrations are small relative to NO2, these errors are small. In some implementations, there is also a negative bias overlong sampling periods caused by the degradation of trapped NO2. The low sampling rates of diffusion tubes make them too uncertain for use atbackground NH3 concentrations (<1 μg NH3 m-3) where they significantlyoverestimate concentrations. Badge-type samplers such as the ‘Willems badge’samplers permit accurate sampling at low ambient NH3 concentrations, but sufferfrom saturation at high concentrations and sensitivity to wind speed. A passivesampler optimised for monthly measurements of NH3 is reported here, togetherwith its application in the U.K. National Ammonia Monitoring Network.
机译:已经开发了许多基于“ Palmes管”的无源采样器,用于环境空气监测。在每种情况下,修改扩散路径的长度和/或横截面积以实现所需的采样率。 “管状”采样器是适用于长期监测的低灵敏度采样器,而“徽章”采样器具有适用于短期监测的更快的采样率。在英国,扩散管被广泛用于监测二氧化氮(NO2)和氨(NH3)。开放式扩散管易于因风涡的侵入而引起正偏压,从而导致扩散路径的缩短。通过在入口处使用多孔膜,可以防止风的侵入,但是会产生额外的扩散阻力,因此有必要根据参考方法对试管进行校准,以获得有效的采样率。对于NO2采样,采样器内NO与O3的反应也会产生正偏差。化学反应产生的干扰非常严重,接近NO源,使用“管状”采样器时,路边位置的误差高达30%。在NO浓度相对于NO2较小的农村地区,这些误差很小。在某些实施方式中,对由于捕获的NO2的降解而导致采样时间过长。扩散管的采样率低,使其在使用时不确定。NH3背景浓度(<1μgNH3 m-3)高估浓度。徽章类型的采样器,例如“威廉姆斯徽章”采样器允许在低环境NH3浓度下进行精确采样,但会受到影响高浓度下的饱和度以及对风速的敏感性。被动的一起报告了为每月测量NH3而优化的采样器其在英国国家氨监测网络中的应用。

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