GEOPHYSICALRESEARCHLETTERS,VOL. 27,NO. 17,PAGES2605-2608,SEPTEMBER1, 2000 Ozonedestructionand productionratesbetweenspringand autumn in the Arctic stratosphere D. W. Fahey1,2, R. S.Gaol,2, L. A. DelNegro3, E.R.Keim4, S.R. KawaS, R.J. Salawitch6, P.O.Wennberg7, T. F. HaniscoS, E. J.LanzendorfS, K. K. PerkinsS, S.A. Lloyd9, W. H. Swartz9,10, M. H. Proffittl,2, J.J.Margitan6, J.C.Wilson11, R.M. StimpfieS, R.C.Cohen12, C.T. McElroy13, C.R.Webster6, M. Loewenstein14, J.W. Elkins3,T. P. Bui14 Abstract. In situ measurements of radicalandlong-livedspecies were made in the lower Arctic stratosphere(18 to 20 km) 03 destructionand productionprocesses Stratospheric 03 abundances representa balancebetween betweenspringand early autumnin 1997. The measurementsdestruction andproduction processes andtransport.Thereactions include 0 3, C10,OH, HO2,NO, NO2,N20, CO, andoverhead listed in Table 1 representthe principal chemical processes 03. A photochemical boxmodelconstrained bytheseandother controlling03 productionanddestruction in the lower summer observationsis used to compute the diurnally averaged stratosphere [Nevison et al., 1999;Laryet al., 1997]. Ozoneis destruction andproduction ratesof 03 in thisregion. The rates destroyedin catalytic cycles involving nitrogen,hydrogen, showa strongdependence on solarexposure andambient03. chlorine,and brominespeciesand in reactionwith O atoms. Total destruction rates, which reach 19%/month in summer, Ozoneproduction occursprimarilythroughoxygenphotolysis revealthe predominant role of NOx andHOx catalyticcycles (R14). Production termsfrom CO andCH4 oxidationare small throughout theperiod. Production of 03 is significant onlyin and are neglectedhere. The destruction andproduction terms midsummer air parcels.A comparison of observed 03 changes associated with theprocesses in Table 1 aregroupedin Table2. with destructionrates and transport effects indicates the The groupingby reactivefamily is not uniquesince some predominant roleof destruction in spring andanincreased roleof catalyticcyclesinvolvereactivespeciesfrom more than one transportby early autumn. family. Thetermsuse[X] for theconcentration of species X, ki for the kinetic rate coefficientof Ri, Ji for the photolysisrate Introduction coefficient of Ri, andCi for branching terms.The 03 destruction ratesfor an air parcelareobtained by integration Measurements of a wide rangeof reactiveand long-lived andproduction species wereobtained in thelowerstratosphere usingtheNASA of the termsin Table 2 over a diurnal cycle. In additionto rate coefficientsand pressure,the integrationrequiresthe diurnal ER-2high-altitude research aircraftaspartof thePhotochemistry abundances of 12 species:OH, HO2, NO, NO2, C10, BrO, C1ONO2, BrONO2, O, 02, 03, andCO. projectin 1997. POLARISwasdesigned to explorethedecrease of Ozone Loss in the Arctic Region In Summer(POLARIS) of 0 3 thatoccurs between springandautumnat northern high latitudes[Newmanet al., 1999;FaheyandRavishankara, 1999]. Observed and derived parameters Ozonedestruction andproduction ratesin sampledair masses are Measurements providedby instruments on boardthe ER-2 calculated usinga photochemical box modelconstrained by the aircraft are used directly and indirectly to constrain a available in situ and remote observations. photochemical box modeland the integrationof diurnalO3 change.ThoseusedhereareNO, NO2,OH, C10,CO, O3,NOy, N20, halon-1211, CFC-11,SF6,surface area(SA) of background 1Aeronomy Laboratory, NationalOceanicandAtmospheric Administration, Boulder, CO 2Cooperative Institute forResearch in Environmental Sciences, Universityof Colorado,Boulder,CO 3NOAA ClimateMonitoringandDiagnostics Laboratory, Boulder, CO 4TheAerospace Corporation, LosAngeles,CA 5NASA GoddardSpaceFlightCenter,Greenbelt,MD 6NASAJetPropulsion Laboratory, Pasadena, CA 7Divisionof GeologyandPlanetarySciences, California Instituteof Technology,Pasadena, CA 8Department of Chemistry, HarvardUniversity, Cambridge, MA 9TheJohnsHopkinsUniversityAppliedPhysicsLaboratory, Laurel, MD 10Department of Chemistry andBiochemistry, University of Maryland,CollegePark,MD 1•Department of Engineering, Universityof Denver,Denver, CO 12Department of Chemistry, Universityof California, Berkeley,CA 13Atmospheric Environment Service,Downsview, Ontario, Canada 14NASA Ames ResearchCenter, Moffett Field, CA Copyright 2000bytheAmerican Geophysical Union. Papernumber2000GL011404. 0094-8276/00/2000GL011404505.00 sulfate aerosol, overhead O3 column, effective surface reflectivity,pressure (P), temperature (T), latitude,longitude, and measurement time. The sourceand uncertaintyfor mostof these in situ measurementsare describedelsewhere[Del Negro et al., 1999; Gao et al., 1997; Herman et al., 1999]. An air parcelis definedby a 100saveragemeasurement alongthe flight track when the solarzenith angle(SZAs) is lessthan 85ø. The full diurnaldependences of OH andC10 are estimated for eachair parcelby scaling theSZArelationships in Wennberg etal. [1994] to therespectiveair parcelmeasurement. Photolysis ratecoefficients for anair parcelareavailablefrom two independent calculations [Salawitchet al., 1994;Swartzet al., 1999]. Both calculations usea spherical,isotropicmultiplescattering modelof theatmospheric radiationfield,incorporating photolysis cross-sections, observed overhead 03 (columnamount abovethe aircraft),andsurfacereflectivity. Changesin overhead 0 3 vary from climatologicalvaluesalong the flight track, significantlyaffectingthe local radiationfield. The j values calculated for POLARIS generallyshowgoodagreement (+_15%) with eachother[Del Negroet al., 1999]. Valuesofjls, 03, and pressure arecombined to calculate thediurnaldependence of O atomsusingthesteadystaterelation[O] = j15103]/k16102][M]. A diurnalphotochemical box modelis usedhereto calculate the diurnaldependence of NO2, HO2, C1ONO2,BrONO2,and 2605 2606 FAHEY ET AL.: OZONE MEASUREMENTS IN THE ARCTIC STRATOSPHERE Table 1. Reactions usedin diurnalintegration of 03 change. 1 2 3 4 OH+O3 -->HO2+202 HO2+O3 -->OH+O2 C10+HO2 -->HOCl+O2 BrO+HO2 -->HOBr+O2 10 11 12 BrO+C10-• Br+CI+O2 BrONO2+hv-• Br+NO3 NO2+O(3p)_,xNO+O2 13 O(3p)+o3_,x202 (panelsG- I) which rangefrom 0.3 to 1.3 partsper billion by volume (ppbv).SinceNOyvalues arenearlyconstant (panels JL), theNOx/NOyratiochanges in a similarmanner to NO2. The enhanced valuesof NO2 and NOx/NOyin midsummer are attributedto the extent of continuousSE that occursat high latitudes near solstice [Farman et al., 1985; Fahey and 5 C10+O(3p)-->CI+O2 14 O2+hv-• 20(3p) Ravishankara,1999; Gao et al., 1999]. Continuousexposureof 6 C1ONO2+hv-->CI+NO3 15 O3+hv _,xO(3p)+o2 stratospheric air parcelscausesN205 productionto ceasebecause 7 NO3+hv-->NO+O2 16 O(3p)+O2+M-• O3+M NO3, the intermediatein the productionof N205, is rapidly 8 NO3+hv-->NO2+O 17 OH+CO+O2 -,, HO2+CO2 photolyzed. 9 BrO+O(3p)-->Br+O2 18 ' HO2+NO --> OH+NO2 After NOx, HOx cyclesare the next largestcontributor(2040%) to 03 destruction rates in all phases. The smallest contributions arefrom the C1/BrandO cycleswhichsumto about BrO. Themodelincludes theNOyinterconversion reactions as 20% in the spring and midsummerand slightly more in early usedby Gaoet al. [1999]to simulate theNOx/NOy ratioin autumn. The averagemixing ratiosof HO2, C10, and BrO are all POLARIS. All rate coefficientsare from DeMore et al. [1997] lessthan0.03 ppbv and significantlylessthanNO2 values(panel exceptfor the OH + HNO3, OH + NO2, andNO2 + O reactions G- I). The largestabsolutevaluesof the HO2 andC1/Brradicals [see referencesin Portmannet al., 1999]. ObservedSA values and their largestcontributionto 03 destructionoccurin early (0.5 - 1.5 !am2cm-3)are includedin the modelto determinethe autumn. This is consistentwith minimum values of NO2 rateof the heterogeneous reactionsN205 + H20 andBrONO2 + observedin late summerbecauseNOx moderatesthe abundance H20 [DeMore et al., 1997]. Other heterogeneous reactionsare of thesespecies[e.g.Nevisonet al., 1999;Wennberget al., 1994]. not importantat POLARIS temperatures(~ 220 - 230 K) [Del Forcedincreasesin NOx at constantNOy do not Negro et al., 1999]. Initial BrO concentrationsfor the box model proportionatelyincreasemodeled03 loss in the high-latitude areprovidedby calculations of the steadystatepartitioningof the summerstratosphere becauseof the NOx moderatingeffecton the Bry reservoir. Bry in an air parcelis estimated from the other losscycles [Nevisonet al., 1999]. This was also confirmed measurementsof N20, halon-1211, CFC-11, and SF6 as with selected box model runs in the POLARIS describedin Wamsleyet al. [1998]. The box model includesthe principal inorganicbromine speciesand their interconversion reactions[Lary et al., 1996]. The box model is constrainedby measuredC10, the diurnal POLARIS destructionratesdependmore fundamentallyon 03 and SE as shown in Figure 2 for the data in Figure 1. The positive correlationof the rates with 0 3 at constantSE is data set. The intriguing feature of the entire POLARIS data set. A similar dependence of OH,andconstant values of 03, SA,Bry,P, andT. correlationis also found separatelyin eachphase. Underlying Themodelis initialized withmeasured NO andNOyandwith this correlation are the overall positive correlations of the approximate steadystatevaluesof NO2, C1ONO2,N205, HNO3, HO2, and BrO. Good agreementhas generally been found betweenmeasuredand steadystatevaluesof NO2, C1ONO2, and HO2 in thelowerstratosphere [Del Negroet al., 1999;Stimpfieet al., 1999; Wennberget al., 1994]. The modelis integratedover 24 hrsfrom the measurement time usinga 100stime step. After 24 hrs,outputvaluesof N205, C1ONO2, HNO3, andBrO andthe initialinputvaluesof NO andNOyareusedto reinitialize the model. Integrationand reinitialization occursfor additional24- daytime-averaged abundances of NO2, HO2, andC10 with 03 in thedataset(figuresnot shown).At constant03 in Figure2, total destructionrates increase with SE. The SE changesare a combination of latitudinal and seasonal differences which are not separablehere (Figure 1). Diurnally averageddestructionrates will in general dependstrongly on SE since it increaseswith length-of-dayand sincedestructionand productionratesare zero at night. The extentto whichthe 03 andSE dependences found hereapplyto otherregionsof the stratosphere mustawait further hourperiods(about6) until furtherchangesin N205, C1ONO2, study. HNO3, and BrO valuesare negligible. With the model results The decreasein 03 valuesin the POLARIS aircraft data set and otherparameters,03 destructionand productionratesin an (60 - 70øN, 18-20 km) are very consistent(absolutevaluesand air parcelare obtainedby integrationof the respective processes month-to-month changes) with those in the more extensive in Table 2 overa diurnalcycle. Results The modelandobservational resultsare shownin Figure1 for the spring,midsummer,and early autumndata as a functionof latitude. Average total 03 destructionrates at 18 to 20 km (panels AC) are approximately 5%/month or greater throughout the data set with a maximum of about 19%/month above80øNin midsummer.The total destruction rate is offsetby 03 productionto yield the net destructionrate. The net 03 destructionratesare positive(decreasing03 tendency)for all of POLARIS exceptfor low latitudesin midsummer(panelB). The solarexposure(SE) valuesshownin panelsD throughF are the fractionof time that the SZA for an air parcelhasbeenlessthan 93ø in the past 1 or 5 daysas calculatedusingback trajectories. SE valuesmaximize in midsummer,reachingunity (continuous illumination)for parcelsfoundpolewardof 65øN. The difference between 1 and 5 day SE values is significant only for high latitudesin spring. The fractionalcontributionsto the total rates(panelsD- F) by NOx, HOx, C1/Br, and O processesindicatesthe predominant role of NOx, particularlyin the midsummerphase. The NOx contributioncorrelateswell with the averagedaytimeNO2 values satellitedata sets[Rosenlof, 1999] and with the sonde/satellite climatology for 1988 to 1996 [Logan and McPeters; 1999]. Average03 valuesfor 18 - 20 km for themonthpairsApril-May, June-July,andAugust-September are 2.6, 2.1, and 1.9 partsper millionby volume(ppmv),respectively, from POLARIS and2.4, 1.9, and 1.8 ppmv,respectively,from the climatology. The 03 decreasesin the aircraft data set are proportionatelysimilar to Table 2. 03 destruction andproductionterms Destruction Term by HOx by NOx by C1/Br byO {Clkl [OH]+k2[HO2]}[03] 2 k12[NO2][O] 2 (j7/(j7+Js)){ j6[C1ONO2]+jii[BrONO2]} (1+C2){k3[C10]+k4[BrO] } [HO2] 2{ks[C10]+k9[BrO]}[O]+ 2 kio[C10] [BrO] 2k1310][O3] Production Term by 0 2 2 J14102] HereCl = k2103]/{k18[NO]+k2103]+k3[C10]+k4[BrO ]} andC2 - kl[O3]/{k17[CO]+kl[O3]} FAHEY ET AL.' OZONE MEASUREMENTS Phase1, April 22 - May 13 o • 1.o i I , '= I •0.8 IN THE ARCTIC STRATOSPHERE Phase2, June26 - July 7 •........... !.......... D'. •el I 2607 Phase3, September8 - 23 •i ..lll_•[;$111111111111111111114111111111 / / /• '[ • NO• • C1& Br[• ..... ::2• .............. I • HOx m•+O ¸ • 0.4 ß•- 0.2 - • • 0.2 • 0o0 oo 30• 1.5 2o • •o• 0.0 o 3.0 lO 2: 2.5 c72.o 1.5 o 50 60 70 80 90 50 60 70 80 90 50 60 70 80 90 Latitude(degrees) Figure 1. Observationaldata and resultsof the photochemicalbox model calculationsas a functionof northernlatitudefor the three phasesof POLARIS. The total destructionrate is offset by the productionrate to obtainthe net destructionrate. Data are averagesof sampledair parcelsfound in 5ø latitudebins for ambientpressuresbetween50 and 80 hPa (-- 18 - 20 km). The numberof flights and 100s datapointsincludedin eachphaseare, respectively,9 and 600; 4 and 590; 6 and 530. More than one-half of the data pointsare obtainedbetween60øN and 70øN latitude in eachphase. The lines in panels(D-F) are the calculated1-day (thick-dashed)and 5-day (thin-dashed)solar exposure(SE) factors. Panels(D-F) representthe fractionalcontributionof the destructionprocessesin Table 2 to the total destructionrates. Panels (G-I) show the calculateddaytime averagemixing ratio of key radical speciesas used in the box model.Panels(J-L)showaverage observed 0 3 andNOy. Theverticalbarsshowthesamplevariance in eachlatitudebinfor the respectiveparameters.Ozonevaluesare expressedaspartsper million by volume(ppmv). decreasesin the associated0 3 column amounts[Newmanet al., 1999]. The net chemicaldestructionratesin Figure 1 for 60- 70øN havebeencomparedwith observed03 changesandthoseinferred from modeled transport terms [Rosenlof, 1999]. In spring and midsummerthe net destructionratesand observedratesof change role only in the Arctic summer period. The results show the predominanceof the NOx catalytic cycle over the HOx and C10/BrO cycles, arising from enhanced solar exposure. The (%/month) areverysimilar.In earlyautumnthenetchemical destruction rateexceedsthe observed rateof change.Transport processes arefoundto increase 0 3 morestronglyin earlyautumn thanspring.A quantitative comparison indicatesthatspringand midsummer0 3 changesare dominatedby chemicaldestruction g 25 " •' 0.6 0.7 0.8 SE 09 1.0"" mI 20 whereastransport dominates in early autumn. Independent evidence for thepredominant roleof chemically induced 03 • 15 changes in springandsummer comesfromanalysis of theO3/HF column abundance ratios [Toon etal.,1999] and fractal analysis • of the0 3 datatime series[Tucket al., 1999]. Summary and conclusions 10 ! , l, , I ,,, I 1.5 2.0 2.5 3.0 In situ observations of radicaland long-livedspeciesmadein the lower Arctic stratosphere(18 - 20 km) between spring and 03 (ppmv) autumnof 1997 were combinedwith a photochemicalbox model to calculatetotal and net 03 destructionrates. The ratesare 10Figure 2. Total 03 destructionratesfrom Figure 1 plottedversus 20%/month in spring and midsummer, decreasing to near observed03 in ppmv. The datapointsare 100saverageswith the 5%/monthin early autumn. Productionof 03 plays a significant 1-daySE value indicatedby the color legend. 2608 FAHEY ET AL.: OZONE MEASUREMENTS IN THE ARCTIC STRATOSPHERE reevaluationbased on laboratory studies, Geophys.Res. Lett., 26, destruction ratesincreasewith solarexposureandambient03 throughout thedataset. A comparison with transport calculations 2387-2390, 1999. showthat chemical03 destruction predominates overtransport Rosenlof,K., Estimatesof the seasonalcycleof massandozonetransport at highnorthernlatitudes,J. Geophys.Res.,104, 26511-26523,1999. effectsin springandthattransport andchemical03 changes are more comparable in late summer/early autumn. Ozone Salawitch,R. S., et al., The diurnalvariationof hydrogen,nitrogen,and chlorineradicals:Implicationsfor the heterogeneous productionof destructionrates and transport processesare both altitude dependent. Hence, the resultspresentedhere may not be generalized to loweror higheraltitudes.Theseresultsprovidean HNO 2, Geophys.Res.Lett., 21, 2551-2554, 1994. Stimpfle,R., et al., The couplingof C 10NO2, C 1O, andNO2 in thelower stratosphere from in situobservations usingthe NASA ER-2 aircraft,J. observationally basedreferencepointfor thecontinuedevaluation Geophys.Res., 104, 26705-26714, 1999. of observedspring/summer 03 changesand of atmospheric Swartz, W. H., et al., A sensitivitystudy of photolysisrate coefficients models used to calculate present and future abundancesof stratospheric 03. Acknowledgements Theauthors aregratefulfor support fromtheNASA UpperAtmospheric ResearchProgramand the Atmospheric Effectsof AviationProject,to J. A. Loganfor 0 3 data,to P. A. Newmanfor backtrajectories, andto S. G. Donnellyforinstrument support. References Del Negro, L. A., et al., Comparisonof modeledand observedvaluesof NO2 and JNO2duringthe Photochemistry of OzoneLossin the Arctic Regionin Summer(POLARIS) mission,J. Geophys.Res.,104, 2668726703, 1999. duringPOLARIS, J. Geophys.Res.,104, 26725-26735, 1999. Toon,G. C., et al., Ground-based observations of Arctic03 lossduring springand summer1997,J. Geophys.Res.,104, 26497-26510, 1999. Tuck, A. F., S. J. Hovde,andM. H. Proffitt,Persistence in ozonescaling under the Hurst exponentas an indicator of the relative rates of chemistryand fluid mechanicalmixing in the stratosphere, J. Phys. Chem. A, 103, 10445-10450, 1999. Wamsley, P. R., et al., Distribution of halon-1211 in the upper troposphere and lower stratosphere and the 1994 total brominebudget, J. Geophys.Res., 103, 1513-1526, 1998. Wennberg,P. O., et al., Removalof stratospheric 03 by radicals:In situ measurements of OH, HO2, NO, NO2, C10, and BrO, Science,266, 398-404, 1994. T. P. Bui and M. Loewenstein, NASA Ames Research Center, Moffett Field, CA 94035. R. C. Cohen, Department of Chemistry, University of California, DeMore, W. B., et al., Chemicalkineticsand photochemicaldata for use Berkeley,CA 94720. in stratospheric modeling,JPL Publ. 97-4, Jet Propul.Lab., Pasadena, L. A. Del Negro and J. W. Elkins, NOAA Climate Monitoring and Calif., 1997. DiagnosticsLaboratory,Boulder,CO 80303. Fahey, D. W., and A. R. Ravishankara,Summerin the stratosphere, D. W. Fahey, R. S. Gao, and M. H. Proffitt, NOAA Aeronomy Science, 285, 208-210, 1999. Laboratory,Boulder,Colorado,and CooperativeInstitutefor Researchin Farman,J. C., et al., Ozonephotochemistry in the Antarcticstratosphere EnvironmentalSciences(CIRES), Universityof Colorado,Boulder,CO in summer, Q. J. R. Meteorol. Soc., 111, 1013-1028, 1985. 80303. (MHP currentlywith WMO/AREP, GenevaSwitzerland). Gao, R. S., et al., Partitioningof the reactivenitrogenreservoirin the T. F. Hanisco, E. J. Lanzendorf, R. M. Stimpfle, K. K. Perkins, lower stratosphereof the southernhemisphere:Observationsand Departmentof Chemistry,HarvardUniversity,Cambridge,MA 02138. modeling,J. Geophys.Res.,102, 3935-3949, 1997. S. R. Kawa, NASA Goddard Space Flight Center, Greenbelt, MD Gao, R. S., et al., A comparisonof observations andmodelsimulationsof 20771. NOx/NOyin thelowerstratosphere, Geophys. Res.Lett.,26, 11531156, 1999. Herman,R. L., et al., Measurements of CO in the uppertroposphere and lower stratosphere,Chemosphere:Global Change Sci., 1, 173-183, 1999. Lary, D. J., Catalyticdestruction of stratospheric ozone,J. Geophys. Res., 102, 21515-21526, 1997. Lary, D. J., Gasphaseatmospheric brominephotochemistry, J. Geophys. Res., 101, 1505-1516, 1996. Logan, J. A., and R. D. McPeters,Ozone climatology, in Modelsand Measurements Intercomparison II, NASA/TM-1999-209554, 1999. Newman, P. A., et al., Prefaceto specialsection:Photochemistry of OzoneLossin the Arctic Regionin Summer(POLARIS), J. Geophys. Res., 104, 26481-26495, 1999. Nevison,C. D., S. Solomon,andR. S. Gao,Bufferinginteractions in the modeledresponse of stratospheric 0 3 to increased NOx andHNO3, J. Geophys.Res., 104, 3741-3754, 1999. Portmann,R. W., et al., Role of nitrogenoxidesin the stratosphere: A E. R. Keim, The AerospaceCorporation,Los Angeles,CA 90009. S. A. Lloyd, The Johns Hopkins University Applied Physics Laboratory,Laurel, MD 20723. J. J. Margitan, R. J. Salawitch,C. R. Webster,NASA Jet Propulsion Laboratory,Pasadena,CA 91109. C. T. McElroy, Atmospheric Environment Service, Downsview, Ontario, Canada. W. H. Swartz, The Johns Hopkins University Applied Physics Laboratory,Laurel, MD and Departmentof Chemistryand Biochemistry, Universityof Maryland,CollegePark,MD 20723. P.O. Wennberg,California Institute of Technology,Pasadena,CA 91125. J. C. Wilson, Department of Engineering, University of Denver, Denver, CO 80208. (ReceivedJanuary17, 2000; revisedMay 26, 2000; acceptedJune16, 2000)