Presentation Slides for Chapter 11, Part 2 of Fundamentals of Atmospheric Modeling 2nd Edition Mark Z. Jacobson Department of Civil & Environmental Engineering Stanford University Stanford, CA 94305-4020 jacobson@stanford.edu March 28, 2005 Alkene Reaction With Ozone Ethene (11.89) H C 37% H + O3 C H H O O H2 C Ethene O + H H C H O CH2 Ethene molozonide Formaldehyde H C O + 63% H Formaldehyde O C O H Criegee biradical H O* C O H Excited Criegee biradical Alkene Reaction With Ozone Criegee biradical reaction (11.90) + NO H C O O H C H Criegee biradical NO2 O H Formaldehyde Excited criegee biradical decomposition (11.91) 60% CO + H2O H C O H O* H Excited Criegee biradical C H O 21% CO2 + H2 O* Excited formic acid + O2 19% CO + OH + HO2 Alkene Reaction With Ozone Propene (11.92) H H3C C O + 7.5% C O H O H Formaldehyde M ethyl criegee biradical H 42.5% O H C O CH2 + O3 H3C Propene H3C O CH CH2 Propene molozonide H3C C O + H C O O* H Excited methyl criegee biradical H3C H O + C O C O 18.5% H H Acetaldehyde Criegee biradical Formaldehyde H3C 33.5% H C O + H Acetaldehyde C O O* H Excited criegee biradical Alkene Reaction With Ozone Methylcriegee biradical reaction + NO H3C C O O (11.93) H3C C H NO2 Methyl criegee biradical O H Acetaldehyde Excited methylcriegee biradical decomposition (11.94) 16% CH4 + CO2 H3C C O H3C O* H Excited methyl criegee biradical C H O O* Excited acetic acid 64% CH3 + CO + OH 20% CH3O + HO2 + CO Alkene Reaction With Nitrate Ethene --> nitrated organic radicals H H + NO3 C C H O C H O O H + O2 N CH2 O H Ethene (11.95) H O O O C CH2 N H O H Ethylperoxy nitrate radical Ethyl nitrate radical O + NO NO2 H C H3C C H + NO 3H H Propene O N C CH2 H3C Propyl nitrate radical C CH2 N O Ethoxy nitrate radical (11.96) O + O2 H O O C H3C O H Propene --> nitrated organic radicals O O O O CH2 N + NO H O Propylperoxy nitrate radical O C NO2 O O N CH2 O H3C Propoxy nitrate radical Aromatic Reaction With OH Toluene oxidation (11.97) CH2 + O2 + OH H2 C O O Benzylperoxy radical 8% H2O Benzyl radical O O CH3 CH3 H OH CH3 + OH Toluene 92% H OH + O2 Toluene-hydroxylradical adduct CH3 OH o-Hydroxytoluene + HO2 o-Cresol Aromatic Reaction With OH Benzylperoxy radical reaction with NO (11.98) H2C O H2C O O O + NO + O2 NO2 HO2 + NO Benzoxy radical H2C O Benzaldehyde N O O Benzylperoxy radical Benzyl nitrate CH Aromatic Rxn With Hydroxyl Radical Toluene-hydroxyl radical adduct reaction O O CH3 + NO H O CH3 H OH OH NO2 Toluene-hydroxyl radical adduct (11.99) Fate of Cresol Cresol --> methylphenylperoxy radical and nitrocresol (11.100) CH3 + OH, 2O2 CH3 O O 2HO2 Methylphenylperoxy radical OH CH3 CH3 o-Cresol + OH O + NO2 OH N H2O Methylphenoxy radical m-Nitrocresol O O Isoprene Reaction With OH (11.101) HO (1) O 16.4% H C H2C CH3 + OH, O 2 C CH2 Isoprene O O (2) 12.3% HO CH3 CH C C H2 CH2 HO CH 3 H C C (4) O H C 2 C O 23.6% H2 O O CH3 CH C C H2 (3) 12.3% HO C H2 CH3 C O O C H2 H C (6) 14.1% O Isoprene peroxy radicals All six products convert NO to NO2 O CH3 C H2C CH2 H C O (5) 21.2% OH C H2 H C C H2 CH3 C C H2 OH Fate of Isoprene Products Methacrolein production via second product O HO O CH3 + NO + O2 H C CH C C H2 CH2 CH3 C O NO2 H + CH2 HO2 Isoprene peroxy radical (11.102) C O H Formaldehyde M ethacrolein Methylvinylketone production via fifth product (11.103) O H C H2C O CH3 C C H2 + NO + O2 OH Isoprene peroxy radical H C H2C NO2 HO2 CH3 C H + O M ethylvinylketone C O H Formaldehyde Isoprene Reaction With Ozone (11.104) H C CH3 C H2C O H CH3 H C H2C CH3 C + O3 H + O CH2 H C CH3 C O O Ozonide product H C O O C O H H C Ozonide product O Formaldehyde CH3 CH2 O H + H2C C H Criegee biradical Methacrolein CH2 Isoprene C O H Criegee biradical Methylvinylketone H C C + O + C O H Formaldehyde Alcohol Reactions Methanol oxidation by OH (36-h lifetime) 85% H H C O H M ethanol O H + OH H C H H H H2O 15% H C O H M ethoxy radical (11.105) + O2 O H HO2 C H Formaldehyde Alcohol Reactions Ethanol oxidation by OH (10-h lifetime) (11.106) H 5% H H H H C C H H Ethanol C C H H O H O H + OH 90% H H2O 5% H C C O H H H H C C H H H H H HO2 O Ethoxy radical H + O2 C O C H H Acetaldehyde Carbon Bond Lumping Organic gases lumped into surrogate groups PAR (paraffins) -- Single carbon atoms with a single-bond between them OLE (olefins) -- Terminal carbon atom pair with a double-bond between the two atoms ALD2 -- Non-terminal carbon atom pairs with a double bond attached to one of the carbons and terminal two-carbon carbonyl groups [C-C(=O)H] KET -- Single carbon ketone groups (C=O) TOL (toluene) -- 7-carbon aromatics XYL (m-xylene) -- 8-carbon aromatics ISOP (isoprene) -- Terpenes UNR -- Unreactive Carbon Bond Lumping Ethane : 0.4 PAR + 1.6 UNR n-Butane : 4 PAR H H C C H H H H H H H C C C C H H H H H H H CH3 2,2,4-Trimethylpentane : 8 PAR H3C C H CH3 C C CH3 H2 CH3 Table 11.7 Carbon Bond Lumping H Trans-2-butene : 2 ALD2 H C C H H H H C C H H H Propene : 1 PAR + 1 OLE C CH2 H3C H C Propionaldehyde : 1 PAR + 1 ALD2 O CH2 CH3 Table 11.7 Carbon Bond Lumping O CH Benzaldehyde : 1 ALD2 + 5 UNR H3C CH2 Ethylbenzene : 1 PAR + 1 TOL CH3 CH3 1,2,3-Trimethylbenzene : 1 PAR + 1 XYL CH3 Table 11.7 Vertical Profile of Ozone O (ppmv) Altitude (km) Altitude (km) 40 3 30 20 O (molecules cm 3 -3 x 10 -12 Air (molecules cm -19 x 5 x 10 ) 10 ) -3 0 0 2 4 6 8 10 12 14 Fig. 11.3 Column Abundance of Ozone Fig. 11.4 Stratospheric Chemistry Ozone mixing ratios stratosphere ≈ 10 ppmv free troposphere ≈ 40 ppbv urban air ≈ 0.05 - 0.3 ppmv Ozone production in the stratosphere Oxygen photolysis (11.107-8) O2 + h O(1D) + O < 175 nm O2 + h O + O < 245 nm Stratospheric Chemistry Natural ozone formation (11.110) M O(1D) O (11.109) O + O2 + M Ozone photolysis O3 + h O3 + M (11.111) O2 + O(1D) < 310 nm (11.112) O3 + h O2 + O > 310 nm Natural Ozone Destruction by NOx Nitrous oxide reaction: 10% of N2O destruction (11.113) 64% 2NO N2O + O(1D) 36% N2 + O2 Nitrous oxide photolysis: 90% of N2O destruction N2O + h N2 + O(1D) (11.114) < 240 nm Natural Ozone Destruction by NOx NO catalytically destroys ozone in upper stratosphere (11.115-7) NO + O3 NO2 + O O + O3 NO2 + O2 NO + O2 2O2 Natural Ozone Destruction by HOx Hydroxyl radical formation in stratosphere O(1D) + (11.115) H2O 2OH CH4 CH3 + OH H2 H + OH Natural Ozone Destruction by HOx OH catalytically destroys ozone in lower stratosphere (11.121-3) OH + O3 HO2 + O3 2O3 HO2 + O2 OH + 2O2 3O2 Removal of HOx and NOx NO2 + OH HO2 + NO2 HO2 + OH M M HNO3 (11.118) HO2NO2 (11.119) H2O + O2 (11.124) Nitric acid and peroxynitric acid photolysis are slow Stratospheric Source of Water Vapor (11.125) CH4 + OH CH3 + H2O Percent difference in global ozone from 1979 monthly average from 1979 monthly average Changes in Monthly-Averaged Global Ozone From 1979-2001 5 El Chichon (April, 1982) M ount Pinatubo (June, 1991) 0 -5 -10 1980 1985 1990 Year 1995 2000 Fig. 11.5 Ozone (Dobson units) Ozone (Dobson units) Variation with Latitude of October Zonally-Averaged Ozone in ‘79, ‘99, ‘00 500 450 400 350 300 250 200 150 100 October zonal average 1979 2000 1999 -90 -60 -30 0 30 60 Latitude (degrees) 90 Fig. 11.6 Variation with Altitude of CFCs and Other Chlorinated Compounds HCFC-22 40 30 CFC-12 20 0 0 Tropopause 4 10 CCl (g) Altitude (km) Altitude (km) 50 CFC-11 100 200 300 400 500 600 Mixing ratio (pptv) Fig. 11.7 Variations With Altitude of CFCs and Other Chlorinated Compounds Photolysis of chlorinated compounds above 20 km Cl F C (11.126) Cl Cl + h F Cl C + Cl < 250 nm Cl (11.127) Cl F C F Cl Cl + h F C F + Cl < 230 nm Natural Sources of Chlorine Methyl chloride photolysis (11.130) H H C H Cl + h H H C < 220 nm + Cl H Methyl chloride scavenging by hydroxyl radical H H C H + OH Cl H2O H C H (11.128) Cl Chlorine Emission to Stratosphere Chemical Percent emission to stratosphere Anthropogenic sources CFC-12 (CF2Cl2) CFC-11 (CFCl3) Carbon tetrachloride (CCl4) Methyl chloroform(CH3CCl3) CFC-113 (CFCl2CF2Cl) HCFC-22 (CF2ClH) 28 23 12 10 6 3 Natural sources Methyl chloride (CH3Cl) Hydrochloric acid (HCl) 15 3 Total 100 WMO (1994) Ozone Destruction by Chlorine Chlorine catalytic ozone destruction cycle Cl + O3 (11.130) ClO + O2 (11.131) ClO + O Cl + O2 (11.132) O + O3 2O2 Only 1% of chlorine is typically active as Cl or ClO Conversion of Active Chlorine to Reservoirs Conversion of Cl and ClO Cl + (11.133) CH4 HCl + CH3 HO2 HCl + O2 H2 HCl + H H2O2 HCl + HO2 (11.134) Cl O Chlorine monoxide + NO2 O M N Cl O O Chlorine nitrate Conversion of Reservoirs to Active Chlorine HCl reservoir leaks HCl + (11.135) h H + Cl OH Cl + H2O O Cl + OH < 220 nm ClONO2 reservoir leaks O N Cl O O Chlorine nitrate O + h Cl + O < 400 nm N O Nitrate radical Ozone Destruction by Bromine CH3Br = methyl bromide (produced biogenically in the oceans and anthropogenically as soil fumigant) Photolysis of methyl above 20 km H H C H (11.137) H Br + h H C H + Br < 260 nm Ozone Destruction by Bromine Catalytic ozone destruction by bromine Br + O3 BrO + O O + O3 (11.138-40) BrO + O2 Br + O2 2O2 Conversion of Active Bromine to Reservoirs Conversion of Br and BrO (11.141) HO2 HBr + O2 H2O2 HBr + HO2 Br + (11.142) Br O Bromine monoxide + NO2 O M N Br O O Bromine nitrate Conversion of Reservoirs to Active Bromine HBr and BrONO2 reservoir leaks (11.143) Br + H2O HBr + OH O O + h N Br O O Bromine nitrate Br + O < 390 nm N O Nitrate radical 30 Area of N. America 250 200 25 Area of Antarctic continent 150 100 50 1980 1985 1990 1995 Year 6 2) 2 Ozone hole area (106 km ) km Ozone minimum (Dobson units) 300 Ozone-hole area (10 Ozone minimum (DU) Change in Size of Antarctic Ozone Hole 20 15 10 5 0 2000 Fig. 11.8 Polar Stratospheric Cloud Reactions Type I Polar Stratospheric Clouds (PSCs) nitric acid and water temperature of formation < 195 K diameter ≈ 0.01 - 3 m number concentration ≈ 1 particle cm-3 Type II Polar Stratospheric Clouds Water ice temperature of formation < 187 K diameter ≈ 1 - 100 m number concentration ≈ 0.1 particle cm-3 Polar Stratospheric Cloud Reactions Reactions on Polar Stratospheric Cloud Surfaces (11.145-9) ClONO2(g) + H2O(a) HOCl(g) + HNO3(a) ClONO2(g) + HCl(a) Cl2(g) + HNO3(a) N2O5(g) + H2O(a) 2HNO3(a) N2O5(g) + HCl(a) ClNO2(g) + HNO3(a) HOCl(g) + HCl(a) Cl2(g) + H2O(a) Surface Reaction Rates First-order rate coefficient (s-1) (11.150) 1 k s,q v q q a 4 Thermal speed of impinging gas (cm s-1) vq 8k BT Mq (11.151) Reaction Probabilities Fractional loss of a species from the gas phase due to reaction with a particle surface. Accounts for diffusion of the gas to the surface and reaction with the surface. Reaction Reaction Probability Type I PSC Type II PSC ClONO2(g) + H2O(a) ClONO2(g) + HCl(a) N2O5(g) + H2O(a) N2O5(g) + HCl(a) HOCl(g) + HCl(a) 0.001 0.1 0.0003 0.003 0.1 0.3 0.3 0.01 0.03 0.3 Table 11.9 Polar Ozone Destruction Cl2 and HOCl photolysis in early spring (11.161-2) Cl2 + h 2Cl < 450 nm HOCl + h Cl + OH < 375 nm Chlorine nitrite photolysis in early spring ClNO2 + h Cl + NO2 (11.163) < 370 nm Polar Ozone Destruction Catalytic ozone destruction by dimer mechanism 2 x ( Cl + O3 (11.164-7) ClO + O2 ) M Cl2O2 ClO + ClO Cl2O2 + h < 360 nm ClOO + Cl ClOO 2O3 M Cl + O2 3O2 Polar Ozone Destruction A second catalytic cycle that involves bromine (11.169-72) Cl + O3 ClO + O2 Br + O3 BrO + O2 BrO + ClO 2O3 Br + Cl + O2 3O2 Conversion of Cl Reservoirs to Active Cl 1% Cl, ClO 37% ClONO 2 ClONO 2 HCl 62% HCl Before PSC and photolysis reactions Cl, ClO After PSC and photolysis reactions Fig. 11.9 Ozone Regeneration (Dobson column ozoneunits) Average global (Dobson units) Change in globally-averaged ozone column abundance during two global model simulations in which all ozone was initially removed and chlorine was present and absent, respectively. 350 300 No chlorine 250 200 150 With chlorine 100 50 0 0 10/1 100 200 300 1/7 4/17 7/26 Day and date of simulation 400 11/4 Fig. 11.10 Regeneration of Ozone Vertical Profile Time-evolution of modeled profile of ozone (a) mixing ratio and (b) number concentration at 34oN latitude, starting with zero ozone. 40 30 20 10 1h 6h 1d 5d 50 d 464 d 0 0 2 4 6 8 10 Ozone volume mixing ratio (ppmv) Altitude (km) Altitude (km) Altitude (km) Altitude (km) 40 30 20 1h 6h 1d 5d 50 d 464 d 10 0 0 10 20 Ozone (10 30 11 40 50 60 -3 molecules cm ) Fig. 11.11