Evaluation of discrepancy between measured and modelled oxidized mercury species

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Abstract

L. Zhang et al. (2012), in a recent report, compared model estimates with new observations of oxidized and particulate mercury species (Hg2+ and Hgp) in the Great Lakes region and found that the sum of Hg 2+ and Hgp varied between a factor of 2 to 10 between measurements and model. They suggested too high emission inputs as Hg 2+ and too fast oxidative conversion of Hg0 to Hg 2+ and Hgp as possible causes. This study quantitatively explores measurement uncertainties in detail. These include sampling efficiency, composition of sample, interfering species and calibration errors. Model (Global/Regional Atmospheric Heavy Metals Model - GRAHM) sensitivity experiments are used to examine the consistency between various Hg measurements and speciation of Hg near emission sources to better understand the discrepancies between modelled and measured concentrations of Hg2+ and Hg p. We find that the ratio of Hg0, Hg2+ and Hgp in the emission inventories, measurements of surface air concentrations of oxidized Hg and measurements of wet deposition are currently inconsistent with each other in the vicinity of emission sources. Current speciation of Hg emissions suggests higher concentrations of Hg2+ in air and in precipitation near emission sources; however, measured air concentrations of Hg2+ and measured concentrations of Hg in precipitation are not found to be significantly elevated near emission sources compared to the remote regions. The averaged unbiased root mean square error (RMSE) between simulated and observed concentrations of Hg2+ is found to be reduced by 42% and for Hgp reduced by 40% for 21 North American sites investigated, when a ratio for Hg0: Hg2+: Hgp in the emissions is changed from 50:40:10 (as specified in the original inventories) to 90:8:2. Unbiased RMSE reductions nea ar emissions sources in the eastern United States t a and Canada are found to be reduced by up to 58% for Hg2+. Significant improvement in the model simulated spatial distribution of wet deposition of mercury in North America is noticed with the modified Hg emission speciation Meas surc e iement-related uncertainties leading to lower estimation of Hg2+ concentrations are 86%. Uncertainties yielding either to higher or lower Hg2+ concentrations are found to be 36%. Finally, anthropogenic emission uncertainties are 106% for Hg2+. Thus it appears that the identified uncertainties for model estimates related to mercury speciation near sources, uncertainties in measurement methodology and uncertainties in emissions can close the gap between modelled and observed estimates of oxidized mercury found in L. Zhang et al. (2012). Model sensitivity simulations show that the measured concentrations of oxidized mercury, in general, are too low to be consistent with measured wet dc e eposition fluxes in North America. Better emission inventories (with respect to speciation), better techniques for measurements of oxidized species and knowledge of mercury reduction reactions in different environments (including in-plume) in all phases are needed for improving the mercury models. © Author(s) 2013.

Figures

  • Table 1. Summary of literature data of Hg0, Hg2+ and Hgp measurements published from 2002 to 2010. All concentrations in pg m−3. Uncertainties, where available, and significant figures are as reported by authors. Hg2+/Hgp ratios were calculated from reported speciation data. “∼” indicates Hg2+/Hgp estimations based on concentration ranges reported by original authors.
  • Table 2. Description of model runs and most important parameters that were used in this study. The “base” experiment corresponds to configuration used in L. Zhang et al. (2012).
  • Table 3. Measurement details and limits of detection for Hg2+ and Hgp (all CVAFS; Tekran 2537A/1130/1135) at selected stations used for comparison with model results in L. Zhang et al. (2012). Method performance data and parameters as cited. MDL: method detection limit.
  • Table 4. Observation sites for data used in this study. Two site identifiers at the same location indicate co-located instrument data. Yearly means (pg m−3) for multiple years are similar. Sites were classified as C= close (60–90 pg m−3), and I= intermediate proximity to sources (30–60 pg m−3) and F = far from sources (0–30 pg m−3) according to model calculation results plotted in Fig. 5. PI and data providers as of October 2010.
  • Fig. 1. (a) Location of measurement sites evaluated: oxidized mercury (red) and wet deposition (blue). (b) Zoomed insert shows northeastern sampling and evaluation sites resolved. Sampling station at Alert, NU, at the northern tip of Ellesmere Island not shown.
  • Table 5. Quantitative uncertainty data for sampling, measurement (Tekran 2537A/1130/1135), emission and atmospheric chemistry-related parameters. Data are presented as calculated by the original authors. Summary discussed in Sect. 3.5.
  • Fig. 2. Comparison of modelled and observed (circles) concentrations for (a) Hg2+ (pg m−3) and (b) Hgp (pg m−3) considering emissions only (NoChem; see Table 2 for details). A considerable discrepancy is observed especially in regions of high concentrations.
  • Fig. 3. Spread of yearly means for different model runs and observations. For a detailed model run description, see Table 2. (a) Hg0, (b) Hg2+, (c) Hgp, (d) wet deposition.

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APA

Kos, G., Ryzhkov, A., Dastoor, A., Narayan, J., Steffen, A., Ariya, P. A., & Zhang, L. (2013). Evaluation of discrepancy between measured and modelled oxidized mercury species. Atmospheric Chemistry and Physics, 13(9), 4839–4863. https://doi.org/10.5194/acp-13-4839-2013

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