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Dry deposition of reduced and reactive nitrogen: A surrogate surfaces approach.

机译:还原氮和反应性氮的干法沉积:替代表面法。

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Nitrogen deposition constitutes an important component of acidic deposition to terrestrial surfaces. However, deposition flux and ambient concentration measurement methods and are still under development. A new sampler using water as a surrogate surface was developed in the Department of Environmental Engineering at Illinois Institute of Technology. This study investigated nitrate and ammonia dry deposition to the water surface sampler, a Nylasorb filter, a citric acid impregnated filter, and a greased strip on the dry deposition plate.; The nitrogen containing species that may be responsible for nitrate dry deposition to the WSS include nitrogen monoxide (NO), nitrogen dioxide (NO{dollar}sb2{dollar}), peroxyacetyl nitrate (PAN), nitrous acid (HNO{dollar}sb2{dollar}), nitric acid (HNO{dollar}sb3{dollar}), and particulate nitrate. The experimental measurements showed that HNO{dollar}sb3{dollar} and particulate nitrate are the major nitrate contributors to the WSS. Ammonia sources to the water surface are ammonia gas (NH{dollar}sb3{dollar}) and ammonium (NH{dollar}sb4sp+{dollar}). The experimental results showed that these two species are the sole sources to ammonium deposition.; Comparison between the measured deposition velocity of SO{dollar}sb2{dollar}, and HNO{dollar}sb3{dollar}, shows that their dry deposition velocities are statistically the same at the 95% confidence level and NH{dollar}sb3{dollar} deposition velocity and the water evaporation rate are also the same. It was also shown that the air side MTC of two different compounds were correlated to the square root of the inverse of the molecular weight for compounds.; The measured MTC was tested by the application of two models, the resistance model and the water evaporation model. The resistance model prediction of the MTC was very close to the measured value but the evaporation model prediction was not. This result is compatible with the finding of Yi, (1997) who used the same WSS for measurements of SO{dollar}sb2.{dollar}; The experimental data collected in this research project was used to develop an empirical model to measure the MTC that is {dollar}rm {lcub}klover D{rcub}{dollar} = 0.0426{dollar}rm ({lcub}lvrhoover mu{rcub})sp{lcub}0.8{rcub}({lcub}muover rho {lcub}rm D{rcub}{rcub})sp{lcub}0.33{rcub}{dollar}; This model was statistically tested to verify that the measured MTC and the model prediction was statistically the same mean at the 95% confidence level. This indicates that the model can be used to predict the MTC of chemicals that have only air side resistance.
机译:氮沉积是酸性沉积到陆地表面的重要组成部分。然而,沉积通量和环境浓度测量方法仍在开发中。伊利诺伊理工学院环境工程系开发了一种使用水作为替代表面的新型采样器。该研究调查了硝酸盐和氨在水表面采样器上的干沉降,Nylasorb过滤器,柠檬酸浸渍的过滤器以及干沉降板上的油脂条。可能导致硝酸盐干沉降至WSS的含氮物质包括一氧化氮(NO),二氧化氮(NO {dollar} sb2 {dollar}),过氧乙酰硝酸盐(PAN),亚硝酸(HNO {dollar} sb2 {美元},硝酸(HNO {dollar} sb3 {dollar})和微粒硝酸盐。实验测量表明,HNO {sb3 {dollar}和硝酸盐颗粒是WSS的主要硝酸盐贡献者。水表面的氨源是氨气(NH {dollar} sb3 {dollar})和铵盐(NH {dollar} sb4sp + {dollar})。实验结果表明,这两个物种是铵沉积的唯一来源。对SO {sdol2} sb2 {dollar}和HNO {dollar} sb3 {dollar}的测量沉积速度的比较表明,在95%置信水平和NH {dollar} sb3 {dollar上,它们的干沉积速度在统计学上是相同的。 deposition沉积速度和水蒸发速率也相同。还显示出两种不同化合物的空气侧MTC与化合物分子量倒数的平方根相关。通过使用两个模型(电阻模型和水蒸发模型)对测得的MTC进行了测试。 MTC的电阻模型预测与测量值非常接近,而蒸发模型预测则与测量值非常接近。这一结果与Yi(1997)的发现是一致的,Yi(1997)使用相同的WSS来测量SO {sdol2}。在此研究项目中收集的实验数据用于建立经验模型来测量MTC,即{rm} rm {lcub} klover D {rcub} {dollar} = 0.0426 {dollar} rm({lcub} lvrhoover mu {rcub })sp {lcub} 0.8 {rcub}({lcub} muover rho {lcub} rm D {rcub} {rcub})sp {lcub} 0.33 {rcub} {dollar};对该模型进行了统计测试,以验证在95%置信度下测得的MTC和模型预测在统计学上均值相同。这表明该模型可用于预测仅具有空气侧阻力的化学品的MTC。

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