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Source Apportionment of Ammonia at Rocky Mountain National Park using Modeled Conservative Tracer Releases

机译:洛基山国家公园氨的源解析,采用了保守的示踪示踪剂模型

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All gaseous species show pronounced diurnal variability throughout the year. Typically minimum concentrations occur during evening hours and maximum in the late afternoon. NH_3 has the highest or greatest difference ratio, defined as (maximum median - minimum median)/(maximum median) of about 0.65, while NO_x and NO_y are also very high at about 0.50. The difference ratio for PM1.0 is lower but still high at 0.40. For the most part, the use of NH_x in the receptor model yielded higher correlations and variance explained than did URG data, suggesting either sources of reduced nitrogen other than ammonia or possibly the chemiluminescence measurement has a higher precision than the URG measurement. The relative apportionment between sources is approximately the same whether URG or chemiluminescence measurements are used. Two objectives of the study were to develop an approximate understanding of the relative contribution of ammonia sources in and outside the state of Colorado to measured reduced gaseous ammonia species in RMNP and to assess whether large ammonia emissions in the agricultural area of the Midwestern portion of the United States contributed significantly to ammonia in RMNP. In answer to the first question, the analysis suggests that slightly more ammonia measured at RMNP originates from instate sources. However, within in the uncertainty of the apportionment methodology, it is fair to say that it is about a 50:50 split between in-state versus out-of-state sources. In answer to the second question, it seems pretty clear that very little of measured ammonia at the receptor site had its origins in the Midwest. The model suggests that no more than about 10% of measured ammonia originates from sources east of eastern Colorado (102.3° longitude) Sources west of Colorado contribute on the order of 35-45% of measured ammonia, with California contributing on the order of 13%, eastern Utah 8%, and the Snake River valley of southern Idaho and Arizona contributing about 5-6%. The systematic correlation between diurnally varying local easterly winds measured at the receptor site and diurnal increases in measured NHx concentrations suggests Front Range transport into the receptor area. The inability of the WRF modeled winds to faithfully reproduce these systematic diurnal patterns suggests that the receptor model may be underestimating the contributions of Front Range and northeastern Colorado ammonia emissions. With that said, the receptor model suggests that, within the state of Colorado, on the average about an equal amount of ammonia is coming from western and central Colorado, and the Front Range including the Greeley area is at about 15%. Northeastern Colorado is estimated to contribute another 6%. The Yampa River valley is estimated to contribute about 4%. Concentrations of ammonia are highest during the summer and spring months when the northern Front Range of Colorado has its largest contributions. During the fall season, northeastern Colorado along with California and the Snake River valley contribute significantly. The winter season corresponded to the lowest measured concentrations, and source regions were primarily more local.
机译:全年所有气态物种均表现出明显的昼夜变化。通常最低浓度发生在晚上,最高浓度发生在傍晚。 NH_3具有最高或最大的差异比率,定义为(最大中位数-最小中位数)/(最大中位数)约为0.65,而NO_x和NO_y也很高,约为0.50。 PM1.0的差异率较低,但仍然很高,为0.40。在大多数情况下,与URG数据相比,在受体模型中使用NH_x产生的相关性和方差更高,这表明除氨以外的其他还原氮源或化学发光法的测量精度均高于URG的测量方法。无论使用URG还是化学发光测量,光源之间的相对分配大致相同。该研究的两个目标是,对科罗拉多州内外的氨源对测量RMNP中减少的气态氨物种的相对贡献进行大致了解,并评估该州中西部农业区是否排放大量氨。美国在RMNP中对氨的贡献很大。在回答第一个问题时,分析表明在RMNP处测得的氨略多于州内来源。但是,在分配方法的不确定性内,可以公平地说,州内和州外资源之间的分配比例约为50:50。在回答第二个问题时,似乎很清楚,在受体位置测得的氨很少来自中西部。该模型表明,不超过约10%的被测氨来自科罗拉多州东部(经度102.3°)以东的来源。科罗拉多州以西的氨源约占被测氨的35-45%,而加利福尼亚以13%来衡量%,犹他州东部8%,爱达荷州南部和亚利桑那州的Snake River山谷贡献约5-6%。受体位置处测得的局部东风的日变化与测得的NHx浓度的日变化之间的系统相关性表明前沿范围向受体区域的迁移。 WRF模拟的风无法如实地再现这些系统的昼夜模式,这表明接收器模型可能低估了Front Range和东北科罗拉多州氨气排放的贡献。话虽如此,受体模型表明,在科罗拉多州内,平均而言,大约等量的氨来自科罗拉多州的中西部,而包括格里利地区在内的前线范围约为15%。估计科罗拉多州东北部将贡献6%。扬帕河谷估计贡献约4%。夏季北部和春季北部科罗拉多地区贡献最大的夏季和春季月份,氨的浓度最高。在秋季,科罗拉多州东北部以及加利福尼亚州和斯内克河谷的影响很大。冬季对应于最低的测得浓度,而源区主要位于本地。

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