首页> 外文期刊>Transactions of the ASABE >DESIGN AND EVALUATION OF A LOW-VOLUME TOTAL SUSPENDED PARTICULATE SAMPLER
【24h】

DESIGN AND EVALUATION OF A LOW-VOLUME TOTAL SUSPENDED PARTICULATE SAMPLER

机译:小体积总悬浮颗粒物采样器的设计与评估

获取原文
获取原文并翻译 | 示例
           

摘要

The regulation of paniculate matter (PM) emitted by agricultural sources, e.g., cotton gins, feed mills, and concentrated animal feeding operations (CAFOs), is based on downwind concentrations of paniculate matter less than 10 and 2.5 μm (PM{sub}10 and PM{sub}(2.5)) aerodynamic equivalent diameter (AED). Both PM{sub}10 and PM{sub}(2.5) samplers operate by pre-separating PM larger than the size of interest (10 and 2.5μm) prior to capturing the PM on the filter. It has been shown that Federal Reference Method (FRM) PM{sub}10 and PM{sub}(2.5) samplers have concentration measurement errors when sampling PM with mass median diameters (MMD) larger than the size of interest in ambient air. It has also been demonstrated that most PM from agricultural sources typically have particle size distributions with MMDs larger than 10 μm AED. The PM{sub}10 concentration measurement error can be as much as 343% for ambient PM with MMD = 20 μm. These errors are a consequence of the PM{sub}10 pre-separator allowing a larger mass of PM greater than 10 μm to penetrate to the filter than the mass of PM less than 10 am captured by the pre-separator. The mass of the particles greater than 10 μm that are allowed to penetrate to the filter introduces a substantial error in the calculated concentration of PM{sub}10. Researchers have reported that sampling PM larger than 2.5 μm AED resulted in a shift in the cutpoint of the pre-separator. If this is true for all PM{sub}10 and PM{sub}(2.5) samplers, then the resulting errors in measurement of ambient concentrations could be even larger. One solution to this problem is to measure the concentration of total suspended paniculate (TSP) matter and calculate the concentration of PM{sub}10 by determining the mass fraction of PM less than size of interest from the panicle size distribution (PSD). The "standard" high-volume TSP sampler operates at a volume rate-of-flow in excess of 1.13 m{sup}3min{sup}(-1) (40 ft{sup}3 min{sup}(-1)). Most of the current PM{sub}10 and PM{sub}(2.5) samplers operate at 1 m{sup}3 h{sup}(-1) (0.589 ft{sup}3 min{sup}(-1)). Other researchers reported that TSP samplers have a cutpoint of a nominal 45 [tm AED. The U.S. EPA specifies the engineering design parameters for TSP samplers. This article reports the engineering design and evaluation of a low-volume (1 m{sup}3 h{sup}(-1)) TSP sampler (TSP{sub}(LV)). The results suggest that the new TSP{sub}(LV) may be more robust and more accurate than the "standard" high-volume TSP sampler.
机译:由农业来源(例如轧花机,饲料厂和集中动物饲养业务(CAFOs))排放的颗粒物(PM)的调节基于小于10和2.5μm(PM {sub} 10和PM {sub}(2.5))空气动力学等效直径(AED)。 PM {sub} 10和PM {sub}(2.5)采样器的工作原理是,在将PM捕获到滤波器之前,将大于目标尺寸(10和2.5μm)的PM预分离。已经显示,当以质量中值直径(MMD)大于环境空气中所关注尺寸的PM进行采样时,联邦参考方法(FRM)PM {sub} 10和PM {sub}(2.5)采样器具有浓度测量误差。还已经证明,大多数农业来源的PM的粒径分布通常均具有大于10μmAED的MMD。对于MMD = 20μm的环境PM,PM {sub} 10浓度测量误差可能高达343%。这些错误是由于PM {sub} 10预分离器允许大于10μm的较大质量的PM渗透到过滤器中的结果,而不是由预分离器捕获的小于10 am的PM质量。允许渗透到过滤器中的大于10μm的颗粒质量在PM {sub} 10的计算浓度中引入了很大的误差。研究人员报告说,对大于2.5μmAED的PM进行采样会导致预分离器的临界点发生变化。如果对于所有PM {sub} 10和PM {sub}(2.5)采样器都是这样,那么在环境浓度测量中所产生的误差可能更大。解决该问题的一种方法是测量总悬浮颗粒(TSP)的浓度,并通过根据穗尺寸分布(PSD)确定小于目标尺寸的PM的质量分数来计算PM {sub} 10的浓度。 “标准”大体积TSP采样器的体积流量超过1.13 m {sup} 3min {sup}(-1)(40 ft {sup} 3 min {sup}(-1)) 。当前大多数PM {sub} 10和PM {sub}(2.5)采样器的工作频率为1 m {sup} 3 h {sup}(-1)(0.589 ft {sup} 3 min {sup}(-1)) 。其他研究人员报告说,TSP采样器的标称切点为45 [tm AED。美国EPA为TSP采样器指定了工程设计参数。本文报告了一种小体积(1 m {sup} 3 h {sup}(-1))TSP采样器(TSP {sub}(LV))的工程设计和评估。结果表明,新的TSP {sub}(LV)可能比“标准”大容量TSP采样器更健壮,更准确。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号