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Singer, and A.A. Rimm. Air pollution and emergency department visits for asthma among Ohio Medicaid recipients, 1991-1996. Environ Res, 2003. 91(1): p. 21-8."&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POP jМt“h?­l8bкY?EPA Standard Health Functions"2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002"Emergency Room Visits, RespiratoryEmergency Room Visits, AsthmaOzone D8HourMax Peel et al.е Atlanta, GA•Peel, J.L., P.E. Tolbert, M. Klein et al. 2005. Ambient air pollution and respiratory emergency department visits. Epidemiology. Vol. 16 (2): 164-74.c&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPіЮщё…L?XўХFмUA?EPA Standard Health Functionsc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002"Emergency Room Visits, RespiratoryEmergency Room Visits, AsthmaOzone D8HourMaxWilson et al. е Portland, MEжWilson, A.M., C.P. Wake, T. Kelly et al. 2005. Air pollution and weather, and respiratory emergency room visits in two northern New England cities: an ecological time-series study. Environ Res. Vol. 97 (3): 312-21.c&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPњ~jМt“h?ќЉёвMbP?EPA Standard Health Functionsc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002"Emergency Room Visits, RespiratoryEmergency Room Visits, AsthmaOzone D8HourMaxWilson et al. еManchester, NHжWilson, A.M., C.P. Wake, T. Kelly et al. 2005. Air pollution and weather, and respiratory emergency room visits in two northern New England cities: an ecological time-series study. Environ Res. Vol. 97 (3): 312-21.c&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPќЉёвMbPПќЉёвMb`?EPA Standard Health Functionsc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, RespiratoryHA, All RespiratoryOzone D8HourMaxBurnett et al.б Toronto, CANPM2.5(Warm season. 8-hour max from 1-hour max.БBurnett, R.T., et al. Association between ozone and hospitalization for acute respiratory diseases in children less than 2 years of age. Am J Epidemiol, 2001. 153(5): p. 444-52.&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPK‘,П€?ј7џxc?EPA Standard Health Functions2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, RespiratoryHA, All RespiratoryOzone D8HourMaxSchwartzЫ New Haven, CTPM10*Warm season. 8-hour max from 24-hour mean.–Schwartz, J. Short term fluctuations in air pollution and hospital admissions of the elderly for respiratory disease. Thorax, 1995. 50(5): p. 531-538.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPޘɝ8]?у‡t"ЏN?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, RespiratoryHA, All RespiratoryOzone D8HourMaxSchwartzЫ Tacoma, WAPM X@X@000030002CC:\Program Files\BenMAP 3.0\Air Quality Grids\2020c3_ozone_base.aqgCC:\Program Files\BenMAP 3.0\Air Quality Grids\2020c3_ozone_zero.aqg CMAQ 12km Nation - ClippedфOzonex  D1HourMax D1HourMax D24HourMean D24HourMean D8HourMax D8HourMax D8HourMean D8HourMean CMAQ 12km Nation - Clipped X@X@000030002 X@X@000030002 MortalityMortality, Non-AccidentalOzone D8HourMax Ito et al.е*Warm season. 8-hour max from 24-hour mean.™Ito, K., S.F. De Leon, and M. Lippmann. Associations between ozone and daily mortality: analysis and meta-analysis. Epidemiology, 2005. 16(4): p. 446-57.c((1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*AIncidence*POP*AЄOфIв5S?A‡oЂ]/?хХг<‘qf?5Scalar to convert annual mortality rate to daily rateEPA Standard Health Functionsc2020 Mortality IncidenceUnited States Census X@X@000030002 X@X@000030002 MortalityMortality, Non-AccidentalOzone D8HourMaxSchwartzе 14 US cities(Warm season. 8-hour max from 1-hour max.œSchwartz, J. How sensitive is the association between ozone and daily deaths to control for temperature? Am J Respir Crit Care Med, 2005. 171(6): p. 627-31.cB(1-(1/((1-Incidence)*EXP(Beta*DeltaQ)+Incidence)))*Incidence*POP*AIncidence*POP*A;cž•Дт;?b4Z9Sœ#?хХг<‘qf?5Scalar to convert annual mortality rate to daily rateEPA Standard Health Functionsc2020 Mortality IncidenceUnited States Census X@X@000030002 X@X@000030002 MortalityMortality, Non-AccidentalOzone D8HourMax Bell et al.д 95 US cities*Warm season. 8-hour max from 24-hour mean.xBell, M.L., et al. Ozone and short-term mortality in 95 US urban communities, 1987-2000. Jama, 2004. 292(19): p. 2372-8.c((1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*AIncidence*POP*A$~Vєт1?иF.ГxL?хХг<‘qf?5Scalar to convert annual mortality rate to daily rateEPA Standard Health Functionsc2020 Mortality IncidenceUnited States Census X@X@000030002 X@X@000030002 MortalityMortality, All CauseOzone D8HourMax Levy et al.е US and non-US(Warm season. 8-hour max from 1-hour max.œLevy, J.I., S.M. Chemerynski, and J.A. Sarnat. Ozone exposure and mortality: an empiric bayes metaregression analysis. Epidemiology, 2005. 16(4): p. 458-68.c((1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*AIncidence*POP*A šіњ~]R?бЬˆСВˆ'?хХг<‘qf?5Scalar to convert annual mortality rate to daily rateEPA Standard Health Functionsc2020 Mortality IncidenceUnited States Census X@X@000030002 X@X@000030002 MortalityMortality, All CauseOzone D8HourMax Bell et al.е US & non-US*Warm season. 8-hour max from 24-hour mean.лBell, M.L., F. Dominici, and J.M. Samet. A meta-analysis of time-series studies of ozone and mortality with comparison to the national morbidity, mortality, and air pollution study. Epidemiology, 2005. 16(4): p. 436-45.c((1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*AIncidence*POP*AC| €ё J?~;ьœв+?хХг<‘qf?5Scalar to convert annual mortality rate to daily rateEPA Standard Health Functionsc2020 Mortality IncidenceUnited States Census X@X@000030002 X@X@000030002 MortalityMortality, CardiopulmonaryOzone D8HourMax Huang et al.е 19 US cities*Warm season. 8-hour max from 24-hour mean.ИHuang, Y., F. Dominici and M. L. Bell. 2005. Bayesian hierarchical distributed lag models for summer ozone exposure and cardio-respiratory mortality. Environmetrics. Vol. 16: 547–562. c((1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*AIncidence*POP*AQДШvОŸJ?9•cвѓ0?хХг<‘qf?5Scalar to convert annual mortality rate to daily rateEPA Standard Health Functionsc2020 Mortality IncidenceUnited States Census 10*Warm season. 8-hour max from 24-hour mean.–Schwartz, J. Short term fluctuations in air pollution and hospital admissions of the elderly for respiratory disease. Thorax, 1995. 50(5): p. 531-538.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPС”}—ћ2t?&– ф]?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, RespiratoryHA, Chronic Lung DiseaseOzone D8HourMaxMoolgavkar et al.ЭMinneapolis, MNPM10, CO'All year. 8-hour max from 24-hour mean.НMoolgavkar, S.H., E.G. Luebeck, and E.L. Anderson. Air pollution and hospital admissions for respiratory causes in Minneapolis St. Paul and Birmingham. Epidemiology, 1997. 8(4): p. 364-370.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPXЮќj`?’ЅЃђHT?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, Respiratory HA, PneumoniaOzone D8HourMaxMoolgavkar et al.ЭMinneapolis, MNPM10, SO2, NO2'All year. 8-hour max from 24-hour mean.НMoolgavkar, S.H., E.G. Luebeck, and E.L. Anderson. Air pollution and hospital admissions for respiratory causes in Minneapolis St. Paul and Birmingham. Epidemiology, 1997. 8(4): p. 364-370.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPK< lЪe?Мp|RїH?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, Respiratory HA, PneumoniaOzone D8HourMaxSchwartzЪ Detroit, MIPM10'All year. 8-hour max from 24-hour mean.­Schwartz, J. Air Pollution and Hospital Admissions For the Elderly in Detroit, Michigan. American Journal of Respiratory and Critical Care Medicine, 1994 150(3): p. 648-655.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPZXk8vj?ѕdўб7iJ?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, Respiratory HA, PneumoniaOzone D8HourMaxSchwartzЪMinneapolis, MNPM10'All year. 8-hour max from 24-hour mean. Schwartz, J. PM(10) Ozone, and Hospital Admissions For the Elderly in Minneapolis St Paul, Minnesota. Archives of Environmental Health, 1994. 49(5): p. 366-374.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPЯдыbIЮf?FШ›LvbU?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002 Hospital Admissions, Respiratory&HA, Chronic Lung Disease (less Asthma)Ozone D8HourMaxSchwartzЪ Detroit, MIPM10'All year. 8-hour max from 24-hour mean.­Schwartz, J. Air Pollution and Hospital Admissions For the Elderly in Detroit, Michigan. American Journal of Respiratory and Critical Care Medicine, 1994 150(3): p. 648-655.Ac&(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP Incidence*POPLНvЕ< l?4Ÿ‰h-U?EPA Standard Health FunctionsAc2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002School Loss DaysSchool Loss Days, All CauseOzone D8HourMax Chen et al.а Washoe Co, NVPM10, CO%All year. 8-hour max from 1-hour max.Chen, L., B.L. Jennison, W. Yang and S.T. Omaye. 2000a. Elementary school absenteeism and air pollution. Inhal Toxicol. Vol. 12 (11): 997-1016.Beta*C*DELTAQ*Incidence/B*POP*AIncidence/B*POP*A§Ѕ›}K$?Љz—Akt?0LІ F%й?+Scalar for % of school days in ozone seasonШ˜Л–Њ?"Study-specific school absence rate{ЎGсz„?Convert beta to proportionEPA Standard Health Functions2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002School Loss DaysSchool Loss Days, All CauseOzone D8HourMaxGilliland et al.бSouthern California&All year. 8-hour max from 8-hour mean.џGilliland, F.D., K. Berhane, E.B. Rappaport, D.C. Thomas, E. Avol, W.J. Gauderman, S.J. London, H.G. Margolis, R. McConnell, K.T. Islam and J.M. Peters. 2001. The effects of ambient air pollution on school absenteeism due to respiratory illnesses. Epidemi*(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A*BIncidence*POP*A*B`С§€€?xgц5а4r?0LІ F%й?+Scalar for % of school days in ozone season> зЃp=ю?7Population of school children at-risk for a new absenceEPA Standard Health Functions2000 Incidence and PrevalenceUnited States Census X@X@000030002 X@X@000030002Worker ProductivityWorker ProductivityOzone D8HourMaxCrocker and HorstН Nationwide'All year. 8-hour max from 24-hour mean.ЎCrocker, T.D. and R.L. Horst, Jr. Hours of Work, Labor Productivity, and Environmental Conditions: A Case Study. The Review of Economics and Statistics, 1981. 63: p. 361-368.@Œif (Q1 <> 0) then Result := Beta*((Q1-Q0)/Q1)*DAILYWAGEOUTDOOR*(MEDIAN_INCOME/NATL_MEDIAN_INCOME)*POP*(COUNT_FARM_EMPLOYED/POPULATION18TO64)^DAILYWAGEOUTDOOR*(MEDIAN_INCOME/NATL_MEDIAN_INCOME)*POP*(COUNT_FARM_EMPLOYED/POPULATION18TO64)EPA Standard Variablesц\ŠЋЪОЗ?EPA Standard Health Functions@EPA Standard VariablesUnited States Census X@X@000030002 X@X@000030002Acute Respiratory SymptomsMinor Restricted Activity DaysOzone D8HourMaxOstro and RothschildХ NationwidePM2.58-hour max from 1-hour max.ЃOstro, B.D. and S. Rothschild. Air Pollution and Acute Respiratory Morbidity - an Observational Study of Multiple Pollutants. Environ Res, 1989. 50(2): p. 238-247.@(1-(1/EXP(Beta*DELTAQ)))*A*POPA*POPž›6у4De?aœ"4@qI?рJvlт•?.mRAD18to64; Ostro and Rothschild, 1989, p 243.EPA Standard Health Functions@United States CensusMichigan. American Journal of Respiratory and Critical Care Medicine, 1994 150(3): p. 648-655.1Qualifier=All year. 8-hour max from 24-hour mean.Other Pollutants=PM10Location=Detroit, MI Year=1994Author=SchwartzMetric Statistic=NoneMetric=D8HourMaxPollutant=Ozone/Endpoint=HA, Chronic Lung Disease (less Asthma)/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 16 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.00130521347676595Beta Distribution=NormalBeta=0.00278391202243231/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65ЊReference=Schwartz, J. PM(10) Ozone, and Hospital Admissions For the Elderly in Minneapolis St Paul, Minnesota. Archives of Environmental Health, 1994. 49(5): p. 366-374.1Qualifier=All year. 8-hour max from 24-hour mean.Other Pollutants=PM10Location=Minneapolis, MN Year=1994Author=SchwartzMetric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=HA, Pneumonia/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 15 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.000806Beta Distribution=NormalBeta=0.0032302/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65ЗReference=Schwartz, J. Air Pollution and Hospital Admissions For the Elderly in Detroit, Michigan. American Journal of Respiratory and Critical Care Medicine, 1994 150(3): p. 648-655.1Qualifier=All year. 8-hour max from 24-hour mean.Other Pollutants=PM10Location=Detroit, MI Year=1994Author=SchwartzMetric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=HA, Pneumonia/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 14 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.000761904761904762Beta Distribution=Normal Beta=0.00266/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65ЧReference=Moolgavkar, S.H., E.G. Luebeck, and E.L. Anderson. Air pollution and hospital admissions for respiratory causes in Minneapolis St. Paul and Birmingham. Epidemiology, 1997. 8(4): p. 364-370.1Qualifier=All year. 8-hour max from 24-hour mean.Other Pollutants=PM10, SO2, NO2Location=Minneapolis, MN Year=1997Author=Moolgavkar et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=HA, Pneumonia/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 13 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.00123809523809524Beta Distribution=Normal Beta=0.00196/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65ЧReference=Moolgavkar, S.H., E.G. Luebeck, and E.L. Anderson. Air pollution and hospital admissions for respiratory causes in Minneapolis St. Paul and Birmingham. Epidemiology, 1997. 8(4): p. 364-370.1Qualifier=All year. 8-hour max from 24-hour mean.Other Pollutants=PM10, COLocation=Minneapolis, MN Year=1997Author=Moolgavkar et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone!Endpoint=HA, Chronic Lung Disease/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 12 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.0017701386388408Beta Distribution=NormalBeta=0.00493143346816288/Incidence DataSet=2000 Incidence Threshold=0 Year=2020-Population Dataset=CMAQ 12km Nation - ClippedPollutant=OzoneLatin Hypercube Points=10\Control Air Quality Grid=C:\Program Files\BenMAP 3.0\Air Quality Grids\2020c3_ozone_zero.aqg]Baseline Air Quality Grid=C:\Program Files\BenMAP 3.0\Air Quality Grids\2020c3_ozone_base.aqgSelected CR FunctionsCR Function 21 Percentile=0C=0B=05Name A=mRAD18to64; Ostro and Rothschild, 1989, p 243. A=0.02137P2Beta=0P1Beta=0.00077644Beta Distribution=Normal Beta=0.002596.Functional Form=(1-(1/EXP(Beta*DELTAQ)))*A*POPBaseline Functional Form=A*POP End Age=64 Start Age=18­Reference=Ostro, B.D. and S. Rothschild. Air Pollution and Acute Respiratory Morbidity - an Observational Study of Multiple Pollutants. Environ Res, 1989. 50(2): p. 238-247.%Qualifier=8-hour max from 1-hour max.Other Pollutants=PM2.5Location=Nationwide Year=1989Author=Ostro and RothschildMetric Statistic=NoneMetric=D8HourMaxPollutant=Ozone'Endpoint=Minor Restricted Activity Days)Endpoint Group=Acute Respiratory Symptoms0CRFunction DataSet=EPA Standard Health FunctionsCR Function 20 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0Beta Distribution=None Beta=0.092755'Variable DataSet=EPA Standard VariablesœFunctional Form=if (Q1 <> 0) then Result := Beta*((Q1-Q0)/Q1)*DAILYWAGEOUTDOOR*(MEDIAN_INCOME/NATL_MEDIAN_INCOME)*POP*(COUNT_FARM_EMPLOYED/POPULATION18TO64)wBaseline Functional Form=DAILYWAGEOUTDOOR*(MEDIAN_INCOME/NATL_MEDIAN_INCOME)*POP*(COUNT_FARM_EMPLOYED/POPULATION18TO64) End Age=64 Start Age=18ИReference=Crocker, T.D. and R.L. Horst, Jr. Hours of Work, Labor Productivity, and Environmental Conditions: A Case Study. The Review of Economics and Statistics, 1981. 63: p. 361-368.1Qualifier=All year. 8-hour max from 24-hour mean.Location=Nationwide Year=1981Author=Crocker and HorstMetric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=Worker Productivity"Endpoint Group=Worker Productivity0CRFunction DataSet=EPA Standard Health FunctionsCR Function 19 Percentile=0C=0>Name B=Population of school children at-risk for a new absenceB=0.9452Name A=Scalar for % of school days in ozone seasonA=0.3929P2Beta=0P1Beta=0.00444489795918367Beta Distribution=Normal Beta=0.007824/Incidence DataSet=2000 Incidence and Prevalence:Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A*B*Baseline Functional Form=Incidence*POP*A*B End Age=17 Start Age=5 Reference=Gilliland, F.D., K. Berhane, E.B. Rappaport, D.C. Thomas, E. Avol, W.J. Gauderman, S.J. London, H.G. Margolis, R. McConnell, K.T. Islam and J.M. Peters. 2001. The effects of ambient air pollution on school absenteeism due to respiratory illnesses. Epidemi0Qualifier=All year. 8-hour max from 8-hour mean.Location=Southern California Year=2001Author=Gilliland et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone$Endpoint=School Loss Days, All CauseEndpoint Group=School Loss Days0CRFunction DataSet=EPA Standard Health FunctionsCR Function 18 Percentile=0!Name C=Convert beta to proportionC=0.01)Name B=Study-specific school absence rateB=0.05092Name A=Scalar for % of school days in ozone seasonA=0.3929P2Beta=0P1Beta=0.0049851Beta Distribution=NormalBeta=0.015763454/Incidence DataSet=2000 Incidence and Prevalence/Functional Form=Beta*C*DELTAQ*Incidence/B*POP*A*Baseline Functional Form=Incidence/B*POP*A End Age=17 Start Age=5™Reference=Chen, L., B.L. Jennison, W. Yang and S.T. Omaye. 2000a. Elementary school absenteeism and air pollution. Inhal Toxicol. Vol. 12 (11): 997-1016./Qualifier=All year. 8-hour max from 1-hour max.Other Pollutants=PM10, COLocation=Washoe Co, NV Year=2000Author=Chen et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone$Endpoint=School Loss Days, All CauseEndpoint Group=School Loss Days0CRFunction DataSet=EPA Standard Health FunctionsCR Function 17 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.00129256447552019Beta Distribution=NormalBeta=0.0034242807120887/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65ЗReference=Schwartz, J. Air Pollution and Hospital Admissions For the Elderly in Detroit, and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65 Reference=Schwartz, J. Short term fluctuations in air pollution and hospital admissions of the elderly for respiratory disease. Thorax, 1995. 50(5): p. 531-538.4Qualifier=Warm season. 8-hour max from 24-hour mean.Other Pollutants=PM10Location=Tacoma, WA Year=1995Author=SchwartzMetric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=HA, All Respiratory/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 11 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.000936405013913563Beta Distribution=NormalBeta=0.00177698674351627/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=65 Reference=Schwartz, J. Short term fluctuations in air pollution and hospital admissions of the elderly for respiratory disease. Thorax, 1995. 50(5): p. 531-538.4Qualifier=Warm season. 8-hour max from 24-hour mean.Other Pollutants=PM10Location=New Haven, CT Year=1995Author=SchwartzMetric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=HA, All Respiratory/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health FunctionsCR Function 10 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.00237703231117514Beta Distribution=NormalBeta=0.00817699115044248/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=1 Start Age=0ЛReference=Burnett, R.T., et al. Association between ozone and hospitalization for acute respiratory diseases in children less than 2 years of age. Am J Epidemiol, 2001. 153(5): p. 444-52.2Qualifier=Warm season. 8-hour max from 1-hour max.Other Pollutants=PM2.5Location=Toronto, CAN Year=2001Author=Burnett et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=HA, All Respiratory/Endpoint Group=Hospital Admissions, Respiratory0CRFunction DataSet=EPA Standard Health Functions CR Function 9 Percentile=0C=0B=0A=0P2Beta=0 P1Beta=0.002Beta Distribution=Normal Beta=-0.001/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=0рReference=Wilson, A.M., C.P. Wake, T. Kelly et al. 2005. Air pollution and weather, and respiratory emergency room visits in two northern New England cities: an ecological time-series study. Environ Res. Vol. 97 (3): 312-21.Location=Manchester, NH Year=2005Author=Wilson et al. Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone&Endpoint=Emergency Room Visits, Asthma1Endpoint Group=Emergency Room Visits, Respiratory0CRFunction DataSet=EPA Standard Health Functions CR Function 8 Percentile=0C=0B=0A=0P2Beta=0 P1Beta=0.001Beta Distribution=Normal Beta=0.003/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=0рReference=Wilson, A.M., C.P. Wake, T. Kelly et al. 2005. Air pollution and weather, and respiratory emergency room visits in two northern New England cities: an ecological time-series study. Environ Res. Vol. 97 (3): 312-21.Location=Portland, ME Year=2005Author=Wilson et al. Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone&Endpoint=Emergency Room Visits, Asthma1Endpoint Group=Emergency Room Visits, Respiratory0CRFunction DataSet=EPA Standard Health Functions CR Function 7 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.000529034191956111Beta Distribution=NormalBeta=0.000870459671260508/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=99 Start Age=0ŸReference=Peel, J.L., P.E. Tolbert, M. Klein et al. 2005. Ambient air pollution and respiratory emergency department visits. Epidemiology. Vol. 16 (2): 164-74.Location=Atlanta, GA Year=2005Author=Peel et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone&Endpoint=Emergency Room Visits, Asthma1Endpoint Group=Emergency Room Visits, Respiratory0CRFunction DataSet=EPA Standard Health Functions CR Function 6 Percentile=0C=0B=0A=0P2Beta=0P1Beta=0.00153061224489796Beta Distribution=NormalBeta=0.00300000000000001/Incidence DataSet=2000 Incidence and Prevalence6Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP&Baseline Functional Form=Incidence*POP End Age=34 Start Age=5ЙReference=Jaffe, D.H., M.E. Singer, and A.A. Rimm. Air pollution and emergency department visits for asthma among Ohio Medicaid recipients, 1991-1996. Environ Res, 2003. 91(1): p. 21-8.Location=Ohio cities Year=2003Author=Jaffe et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone&Endpoint=Emergency Room Visits, Asthma1Endpoint Group=Emergency Room Visits, Respiratory0CRFunction DataSet=EPA Standard Health Functions CR Function 5 Percentile=0C=0B=0<Name A=Scalar to convert annual mortality rate to daily rate A=0.0027397P2Beta=0P1Beta=0.000258673469387755Beta Distribution=NormalBeta=0.000812500000000003*Incidence DataSet=2020 Mortality Incidence8Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A(Baseline Functional Form=Incidence*POP*A End Age=99 Start Age=0ТReference=Huang, Y., F. Dominici and M. L. Bell. 2005. Bayesian hierarchical distributed lag models for summer ozone exposure and cardio-respiratory mortality. Environmetrics. Vol. 16: 547–562. 4Qualifier=Warm season. 8-hour max from 24-hour mean.Location=19 US cities Year=2005Author=Huang et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone#Endpoint=Mortality, CardiopulmonaryEndpoint Group=Mortality0CRFunction DataSet=EPA Standard Health Functions CR Function 4 Percentile=0C=0B=0<Name A=Scalar to convert annual mortality rate to daily rate A=0.0027397P2Beta=0P1Beta=0.000212270408163264Beta Distribution=NormalBeta=0.000794999999999997*Incidence DataSet=2020 Mortality Incidence8Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A(Baseline Functional Form=Incidence*POP*A End Age=99 Start Age=0хReference=Bell, M.L., F. Dominici, and J.M. Samet. A meta-analysis of time-series studies of ozone and mortality with comparison to the national morbidity, mortality, and air pollution study. Epidemiology, 2005. 16(4): p. 436-45.4Qualifier=Warm season. 8-hour max from 24-hour mean.Location=US & non-US Year=2005Author=Bell et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=Mortality, All CauseEndpoint Group=Mortality0CRFunction DataSet=EPA Standard Health Functions CR Function 3 Percentile=0C=0B=0<Name A=Scalar to convert annual mortality rate to daily rate A=0.0027397P2Beta=0P1Beta=0.000179550000000006Beta Distribution=NormalBeta=0.00112092399999997*Incidence DataSet=2020 Mortality Incidence8Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A(Baseline Functional Form=Incidence*POP*A End Age=99 Start Age=0ІReference=Levy, J.I., S.M. Chemerynski, and J.A. Sarnat. Ozone exposure and mortality: an empiric bayes metaregression analysis. Epidemiology, 2005. 16(4): p. 458-68.2Qualifier=Warm season. 8-hour max from 1-hour max.Location=US and non-US Year=2005Author=Levy et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=OzoneEndpoint=Mortality, All CauseEndpoint Group=Mortality0CRFunction DataSet=EPA Standard Health Functions CR Function 2 Percentile=0C=0B=0<Name A=Scalar to convert annual mortality rate to daily rate A=0.0027397P2Beta=0P1Beta=8.88775510204069E-5Beta Distribution=NormalBeta=0.000261299999999994*Incidence DataSet=2020 Mortality Incidence8Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A(Baseline Functional Form=Incidence*POP*A End Age=99 Start Age=0‚Reference=Bell, M.L., et al. Ozone and short-term mortality in 95 US urban communities, 1987-2000. Jama, 2004. 292(19): p. 2372-8.4Qualifier=Warm season. 8-hour max from 24-hour mean.Location=95 US cities Year=2004Author=Bell et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone"Endpoint=Mortality, Non-AccidentalEndpoint Group=Mortality0CRFunction DataSet=EPA Standard Health Functions CR Function 1 Percentile=0C=0B=0<Name A=Scalar to convert annual mortality rate to daily rate A=0.0027397P2Beta=0P1Beta=0.000149617346938777Beta Distribution=NormalBeta=0.000425500000000012*Incidence DataSet=2020 Mortality IncidenceRFunctional Form=(1-(1/((1-Incidence)*EXP(Beta*DeltaQ)+Incidence)))*Incidence*POP*A(Baseline Functional Form=Incidence*POP*A End Age=99 Start Age=0ІReference=Schwartz, J. How sensitive is the association between ozone and daily deaths to control for temperature? Am J Respir Crit Care Med, 2005. 171(6): p. 627-31.2Qualifier=Warm season. 8-hour max from 1-hour max.Location=14 US cities Year=2005Author=SchwartzMetric Statistic=NoneMetric=D8HourMaxPollutant=Ozone"Endpoint=Mortality, Non-AccidentalEndpoint Group=Mortality0CRFunction DataSet=EPA Standard Health Functions CR Function 0 Percentile=0C=0B=0<Name A=Scalar to convert annual mortality rate to daily rate A=0.0027397P2Beta=0P1Beta=0.000239285714285714Beta Distribution=NormalBeta=0.0011725*Incidence DataSet=2020 Mortality Incidence8Functional Form=(1-(1/EXP(Beta*DELTAQ)))*Incidence*POP*A(Baseline Functional Form=Incidence*POP*A End Age=99 Start Age=0ЃReference=Ito, K., S.F. De Leon, and M. Lippmann. Associations between ozone and daily mortality: analysis and meta-analysis. Epidemiology, 2005. 16(4): p. 446-57.4Qualifier=Warm season. 8-hour max from 24-hour mean. Year=2005Author=Ito et al.Metric Statistic=NoneMetric=D8HourMaxPollutant=Ozone"Endpoint=Mortality, Non-AccidentalEndpoint Group=Mortality0CRFunction DataSet=EPA Standard Health Functions