4 research outputs found

    Gaseous Mercury Emissions From Soil Following Forest Loss And Land Use Changes: Field Experiments In The United States And Brazil

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    Forest ecosystems are a sink of atmospheric mercury, trapping the metal in the canopy, and storing it in the forest floor after litter fall. Fire liberates a portion of this mercury; however, little is known about the long-term release of mercury post deforestation. We conducted two large-scale experiments to study this phenomenon. In upstate New York, gaseous mercury emissions from soil were monitored continually using a Teflon dynamic surface flux chamber for two-weeks before and after cutting of the canopy on the edge of a deciduous forest. In Brazil, gaseous mercury emissions from soil were monitored in an intact Ombrophilous Open forest and an adjacent field site both before and after the field site was cleared by burning. In the intact forest, gaseous mercury emissions from soil averaged-0.73±1.84ngm-2h-1 (24-h monitoring) at the New York site, and 0.33±0.09ngm-2h-1 (daytime-only) at the Brazil site. After deforestation, gaseous mercury emissions from soil averaged 9.13±2.08ngm-2h-1 in New York and 21.2±0.35ngm-2h-1 at the Brazil site prior to burning. Gaseous mercury emissions averaged 74.9±0.73ngm-2h-1 after burning of the cut forest in Brazil. Extrapolating our data, measured over several weeks to months, to a full year period, deforested soil is estimated to release an additional 2.30gha-1yr-1 of gaseous mercury to the atmosphere in the Brazilian experiment and 0.41gha-1yr-1 in the New York experiment. In Brazil, this represents an additional 50% of the mercury load released during the fire itself. © 2014 The Authors.96423429Almeida, M.D., Lacerda, L.D., Bastos, W.R., Herrmann, J.C., Mercury loss from soils following conversion from forest to pasture in RondÔnia, Western Amazon, Brazil (2005) Environ. Pollut., 137 (2), pp. 179-186Bahlmann, E., Ebinghaus, R., Ruck, W., Development and application of a laboratory flux measurement system (LFMS) for the investigation of the kinetics of mercury emissions from soils (2006) J.Environ. Manag., 81 (2), pp. 114-125Carpi, A., Frei, A., Cocris, D., McCloskey, R., Contreras, E., Ferguson, K., Analytical artifacts produced by a polycarbonate chamber compared to a teflon chamber for measuring surface mercury fluxes (2007) Anal. Bioanal. Chem., 388 (2), pp. 361-365Carpi, A., Lindberg, S.E., Sunlight-mediated emission of elemental mercury from soil amended with municipal sewage sludge (1997) Environ. Sci. Technol., 31 (7), pp. 2085-2091Carpi, A., Lindberg, S.E., Application of a teflon(TM) dynamic flux chamber for quantifying soil mercury flux: tests and results over background soil (1998) Atmos. Environ., 32 (5), pp. 873-882Choi, H.D., Holsen, T.M., Gaseous mercury fluxes from the forest floor of the Adirondacks (2009) Environ. Pollut., 157 (2), pp. 592-600Comte, I., Lucotte, M., Davidson, R., Reis de Carvalho, C., Assis Oliveira, F., Rousseau, G., Impacts of land uses on mercury retention in long-time cultivated soils, Brazilian Amazon (2013) Water Air Soil Pollut., 224 (4), pp. 1-14Friedli, H.R., Arellano, A.F., Cinnirella, S., Pirrone, N., Initial estimates of mercury emissions to the atmosphere from global biomass burning (2009) Environ. Sci. Technol., 43 (10), pp. 3507-3513Friedli, H.R., Radke, L.F., Lu, J.Y., Banic, C.M., Leaitch, W.R., MacPherson, J.I., Mercury emissions from burning of biomass from temperate North American forests: laboratory and airborne measurements (2003) Atmos. Environ., 37 (2), pp. 253-267Friedli, H.R., Radkel, L.F., Luz, J.Y., (2001) Mercury in Smoke from Biomass FiresGustin, M.S., Stamenkovic, J., Effect of watering and soil moisture on mercury emissions from soils (2005) Biogeochemistry, 76 (2), pp. 215-232Hansen, M.C., Potapov, P.V., Moore, R., Hancher, M., Turubanova, S.A., Tyukavina, A., Townshend, J.R.G., High-resolution global maps of 21st-century forest cover change (2013) Science, 342 (6160), pp. 850-853Lacerda, L.D., de Souza, M., Ribeiro, M.G., The effects of land use change on mercury distribution in soils of Alta Floresta, Southern Amazon (2004) Environ. Pollut., 129 (2), pp. 247-255Lindberg, S., Bullock, R., Ebinghaus, R., Engstrom, D., Feng, X., Fitzgerald, W., Seigneur, C., Asynthesis of progress and uncertainties in attributing the sources of mercury in deposition (2007) AMBIO J. Hum. Environ., 36 (1), pp. 19-33Lindberg, S.E., Meyers, T.P., Development of an automated micrometeorological method for measuring the emission of mercury vapor from wetland vegetation (2001) Wetl. Ecol. Manag., 9 (4), pp. 333-347Lindberg, S.E., Price, J.L., Airborne emissions of mercury from municipal landfill operations: a short-term measurement study in Florida (1999) J.Air Waste Manag. Assoc., 49 (5), pp. 520-532Lindberg, S.E., Zhang, H., Gustin, M., Vette, A., Marsik, F., Owens, J., Fitzgerald, C., Increases in mercury emissions from desert soils in response to rainfall and irrigation (1999) J.Geophys. Res., 104 (D17), p. 21879Lindberg, S.E., Zhang, H., Vette, A.F., Gustin, M.S., Barnett, M.O., Kuiken, T., Dynamic flux chamber measurement of gaseous mercury emission fluxes over soils: part 2 - effect of flushing flow rate and verification of a two-resistance exchange interface simulation model (2002) Atmos. Environ., 36 (5), pp. 847-859Magarelli, G., Fostier, A., Influence of deforestation on the mercury air/soil exchange in the Negro River Basin, Amazon (2005) Atmos. Environ., 39 (39), pp. 7518-7528Mauclair, C., Layshock, J., Carpi, A., Quantifying the effect of humic matter on the emission of mercury from artificial soil surfaces (2008) Appl. Geochem., 23 (3), pp. 594-601Melendez-Perez, J.J., Fostier, A.H., Santos, J.C., Carvalho, J.A., Soil and biomass mercury emissions during a prescribed fire in the Amazonian rain forest, Atmos (2014) Environ., 96, pp. 415-422Moore, C., Carpi, A., Mechanisms of the emission of mercury from soil: role of UV radiation (2005) J.Geophys. Res. Atmos., 110 (D24), p. 9. , doi:D24302Salimon, C.I., Wadt, P.G.S., de Souza Alves, S., Decrease in carbon stocks in an oxisol due to land use and cover change in southwestern Amazon (2009) Ambiente Água Interdiscip. J. Appl. Sci., 4 (2), pp. 57-65Santos, H.G., Jacomine, P.K.T., Anjos, L.H.C., Oliveira, V.A., Oliveira, J.B., Coelho, M.R., Cunha, T.J.F., (2006) Sistema brasileiro de classificação de solosSiegel, S.M., Siegel, B.Z., Temperature determinants of plant-soil-air mercury relationships (1988) Water Air Soil Pollut., 40 (3), pp. 443-448Sigler, J., Lee, X., Munger, W., Emission and long-range transport of gaseous mercury from a large-scale Canadian boreal forest fire (2003) Environ. Sci. Technol., 37 (19), pp. 4343-4347Song, X., Van Heyst, B., Volatilization of mercury from soils in response to simulated precipitation (2005) Atmos. Environ., 39 (39), pp. 7494-7505Turetsky, M.R., Harden, J.W., Friedli, H.R., Flannigan, M., Payne, N., Crock, J., Radke, L., Wildfires threaten mercury stocks in northern soils (2006) Geophys. Res. Lett., 33 (16), p. 16403(2011) Soil Report for Orange County, , M 7, USDA Natural Resources Conservation Service, U.S. Department of Agriculture, New York, N.R.C. Service (Ed.)Veiga, M., Meech, J., Oñate, N., Mercury pollution from deforestation (1994) Nature, 368 (6474), pp. 816-817(2013) Average Weather for New York, USA, , http://weatherspark.com/averages/31081/New-York-United-States, WeatherSpark Retrieved February 22, 2013, from:(2013) Average Weather for Rio Branco, Brazil, , http://weatherspark.com/averages/33477/Rio-Branco-Acre-Brazil, WeatherSpark Retrieved January 18, 2013, from:Xiao, Z.F., Munthe, J., Schroeder, W.H., Lindqvist, O., Vertical fluxes of volatile mercury over forest soil and lake surfaces in Sweden (1991) Tellus B, 43 (3), pp. 267-279Xin, M., Gustin, M., Johnson, D., Laboratory investigation of the potential for re-emission of atmospherically derived Hg from soils (2007) Environ. Sci. Technol., 41 (14), pp. 4946-4951Zhang, H., Lindberg, S.E., Barnett, M.O., Vette, A.F., Gustin, M.S., Dynamic flux chamber measurement of gaseous mercury emission fluxes over soils. Part 1: simulation of gaseous mercury emissions from soils using a two-resistance exchange interface model (2002) Atmos. Environ., 36 (5), pp. 835-84

    COVID-19 in Adults With Congenital Heart Disease.

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    Adults with congenital heart disease (CHD) have been considered potentially high risk for novel coronavirus disease-19 (COVID-19) mortality or other complications. This study sought to define the impact of COVID-19 in adults with CHD and to identify risk factors associated with adverse outcomes. Adults (age 18 years or older) with CHD and with confirmed or clinically suspected COVID-19 were included from CHD centers worldwide. Data collection included anatomic diagnosis and subsequent interventions, comorbidities, medications, echocardiographic findings, presenting symptoms, course of illness, and outcomes. Predictors of death or severe infection were determined. From 58 adult CHD centers, the study included 1,044 infected patients (age: 35.1 ± 13.0 years; range 18 to 86 years; 51% women), 87% of whom had laboratory-confirmed coronavirus infection. The cohort included 118 (11%) patients with single ventricle and/or Fontan physiology, 87 (8%) patients with cyanosis, and 73 (7%) patients with pulmonary hypertension. There were 24 COVID-related deaths (case/fatality: 2.3%; 95% confidence interval: 1.4% to 3.2%). Factors associated with death included male sex, diabetes, cyanosis, pulmonary hypertension, renal insufficiency, and previous hospital admission for heart failure. Worse physiological stage was associated with mortality (p = 0.001), whereas anatomic complexity or defect group were not. COVID-19 mortality in adults with CHD is commensurate with the general population. The most vulnerable patients are those with worse physiological stage, such as cyanosis and pulmonary hypertension, whereas anatomic complexity does not appear to predict infection severity
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