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Science implementation of a comprehensive mercury model in CMAQ framework to assess mercury fate in the atmosphere.

机译:科学地在CMAQ框架中实施了综合汞模型,以评估大气中的汞命运。

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摘要

The Community Multi-scale Air Quality (CMAQ) modeling system was designed to couple multiple atmospheric processes for "one atmosphere" modeling. It was also designed to have multi-scale capabilities so that separate models were not needed for urban and regional scale air quality modeling. Therefore, CMAQ is a useful tool to assess the transport and deposition of mercury. USEPA developed the mercury model coupled in CMAQ (CMAQ-Hg) for modeling of various atmospheric mercury species including GEM, RGM, and PHg. However, there exist issues caused by model assumptions/simplifications and incomplete understanding of mercury science. This research evaluates the model science commonly implemented in atmospheric mercury models, tests potential chemical mechanisms, develops and demonstrates an alternative dry deposition treatment of mercury species. I assessed the causes of the model uncertainties in terms of gas phase chemistry (oxidation rates, products, and potential reduction mechanism of mercury species), aqueous phase chemistry, aqueous phase speciation, aqueous phase sorption, dry deposition, wet deposition, initial and boundary conditions, emission inventory, domain grid resolution, and intercontinental mercury transport. The researcher selected the year 2001 for simulations. The study area comprises of contiguous Unites States (CONUS) domain, intercontinental transport, and climatic effects of air pollutants (ICAP) domain. The author utilized CONUS domain for the model uncertainty evaluation and testing, while the ICAP domain is used to study intercontinental mercury transport and its impact on the United States. The results show that assignment of mercury oxidation product is very sensitive to the concentration and depositions of various mercury species. More laboratory and field data regarding the oxidation speciation are needed to reduce model uncertainties. Aqueous Hg(II) reduction by HO 2· is the key reduction pathway for the current model configuration, although its occurrence in atmospheric water was questioned. In a sensitivity simulation for the July, 2001, the implemented rate constant needs to be reduced by an order of magnitude to offset the model overestimation of wet Hg deposition compared to the MDN observed data. In cold months CMAQ-Hg overestimates the wet deposition by 500%. From my calculation, this can be caused by the high Henry's law coefficient of HgCl2 at lower temperature. Because of the controversy of the aqueous HO2· or O2·- reduction pathway, I tested the two alternative reduction mechanisms, i.e., RGM photoreduction and RGM reduction by CO. In the sensitivity simulations, the researcher removed the HO 2· reduction and assigned the gas-phase mercury oxidation products by OH· and O3 to be 100% Hg(II). I found that a CO reduction rate of 5 x 10-18 cm 3 molecule-1 s-1 or a RGM photoreduction rate of 1 x 10-5 s-1 gives optimal model agreement to MDN data. When the rate constants are lower than 1 x 10-20 cm3 molecule-1 s-1 and 1 x 10-7 s-1, the model results will not be influenced. The proposed rate constants provide a preliminary estimate for further verification by more kinetic laboratory studies. Model results in the ICAP domain show that chemical forcing of background mercury is the most dominant factor leading to the dry and wet depositions in North America, contributing 65-95% of total mercury deposition at selected MDN sites. Incorporation of natural and/or re-emission of mercury in the emission inventory does not significantly affect mercury deposition (<2% in total deposition), while local anthropogenic emissions can have a significant contribution to the deposition in the U.S. (up to 34%). Although the direct contribution of Asian mercury emission to the dry and wet deposition in North America is lower than expected, its contribution to the global mercury background cannot be overlooked.;Keywords. Aqueous mercury sorption, atmospheric mercury, chemical mechanism, CMAQ, deposition, mercury reduction, mercury speciation, modeling.
机译:社区多尺度空气质量(CMAQ)建模系统旨在将多个大气过程耦合在一起以进行“一个大气”建模。它也设计为具有多尺度功能,因此城市和区域尺度的空气质量建模不需要单独的模型。因此,CMAQ是评估汞传输和沉积的有用工具。美国环保局开发了在CMAQ(CMAQ-Hg)中耦合的汞模型,用于对各种大气汞物种(包括GEM,RGM和PHg)进行建模。但是,存在由于模型假设/简化和对汞科学的不完全理解而引起的问题。这项研究评估了常用于大气汞模型的模型科学,测试了潜在的化学机理,开发并演示了汞物种的另一种干法沉积处理方法。我从气相化学(氧化速率,产物和汞物种的潜在还原机理),水相化学,水相形态,水相吸附,干法沉积,湿法沉积,初始和边界等方面评估了模型不确定性的原因。条件,排放清单,域网格分辨率和洲际汞传输。研究人员选择2001年作为模拟对象。研究领域包括连续的美国(CONUS)域,洲际运输和空气污染物的气候影响(ICAP)域。作者利用CONUS域进行模型不确定性评估和测试,而ICAP域则用于研究洲际汞运输及其对美国的影响。结果表明,汞氧化产物的分配对各种汞物种的浓度和沉积非常敏感。需要更多有关氧化形态的实验室和现场数据,以减少模型的不确定性。尽管有人质疑其在大气水中的存在,但是通过HO 2·还原Hg(II)水溶液是当前模型配置的关键还原途径。在2001年7月的灵敏度模拟中,与MDN观测数据相比,需要将实现的速率常数降低一个数量级,以抵消模型对湿Hg沉积的高估。在寒冷的月份,CMAQ-Hg高估了湿沉降500%。根据我的计算,这可能是由于在较低温度下HgCl2的亨利定律系数高所致。由于存在水合HO2·或O2·-还原途径的争议,我测试了两种替代的还原机制,即RGM光还原和CO还原RGM。在灵敏度模拟中,研究人员删除了HO 2·还原并分配了由OH·和O3组成的气相汞氧化产物为100%Hg(II)。我发现,CO还原速率为5 x 10-18 cm 3分子-1 s-1或RGM光还原速率为1 x 10-5 s-1可使MDN数据达到最佳模型一致性。当速率常数低于1 x 10-20 cm3分子-1 s-1和1 x 10-7 s-1时,模型结果将不会受到影响。提议的速率常数为进一步的动力学实验室研究提供了初步估计,以供进一步验证。 ICAP域中的模型结果表明,背景汞的化学强迫是导致北美干湿沉降的最主要因素,在选定的MDN站点占汞总沉积的65-95%。在排放清单中纳入汞的自然排放和/或再排放不会对汞的沉积产生重大影响(占总沉积的<2%),而本地人为排放可对美国的沉积产生重大影响(高达34% )。尽管亚洲汞排放对北美干湿沉积的直接贡献低于预期,但其对全球汞背景的贡献却不容忽视。汞的水吸附,大气中的汞,化学机理,CMAQ,沉积,汞还原,汞形态,建模。

著录项

  • 作者

    Pongprueksa, Pruek.;

  • 作者单位

    Lamar University - Beaumont.;

  • 授予单位 Lamar University - Beaumont.;
  • 学科 Engineering Environmental.
  • 学位 D.E.
  • 年度 2006
  • 页码 223 p.
  • 总页数 223
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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