JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 102, NO. D3, PAGES 3671-3682, FEBRUARY 20, 1997 Carbon aerosols and atmospheric photochemistry D. J. Lary, 1 A.M. Lee,• R. Toumi,2 M. J. Newchurch, 3 M. Pirre,4 and J. B. Renard 4 Abstract. Carbon aerosolsare produced by all combustion processes. This paper investigatessome possibleeffects of heterogeneousreduction of atmospheric constituents on carbon aerosols. Reduction of HNO3, NO2, and 03 on carbon aerosols may be an important effect of increased air traffic that has not been consideredto date. It is shown that if HNO3, NO2 and 03 are heterogeneously reduced on atmospheric amorphous carbon aerosols, then a significant, lower stratospheric ozone loss mechanism could exist. This ozone loss mechanism is almost independent of temperature and does not require the presenceof sunlight. The mechanismcan operate at all latitudes where amorphouscarbon aerosolsare present. The relative importance of the mechanismincreaseswith nightlength. The reduction of HNO3 on carbon aerosolscould also be a significant renoxification processwherevercarbon aerosolsare present. Owing to the very different soot levels in the two hemispheres,this implies that there should be a hemisphericassymetry in the role of these mechanisms. The renoxification lea,ds to simulated tropospheric HNO3/NO• ratiosthat are closeto thoseobserved.In contrastto the stratospheric response,the troposphericproduction of NO• due to the reduction of HNO3 would lead to tropospheric ozone production. Introduction erally overestimate the HNO3 abundance,particularly The recent World Meteorological Organization (WMO) inthetroposphere (e.g. Chatfield, 1995); third, totroassessments [WMO, 1992, 1994] reported thatforthe pospheric ozone production. first time there were statistically significantdecreasesin ozone in all seasons in both the northern and southern Heterogeneous Reactions on Carbon Aerosols hemispheres at mid latitudesand high latitudes during Thlibi andPetit [1994]studiedthe interactionof soot the 1980s,and that most of this decreaseoccurredin with NO v. They found that hydrogenatoms on the the lowerstratosphere.This hasalsobeensupportedby soot surface play an important role in the interaction, trendsderivedfrom ozonesondes [Logan,1994]. If this HCN being observedin the desorbedproducts. Thlibi ozone loss is due to in situ chemistry, the mechanism andPetit [1994]foundthat at the temperaturescloseto involved must be able to operate at all temperatures. thosefound in the atmospherethe gas/solidinteraction In contrast to the ozone loss that occurs in the strato- sphere,thereis an observedozoneincreasein the troposphere.This paperexaminesthe role of amorphouscarbon aerosols in reducingatmosphericconstituents.This is relevant to several issues,including the following: first, midlatitude,lowerstratospheric ozonelossand its temperature, altitude, and seasonaldependence;second, to atmosphericrenoxification,wheremodelsgen• CentreFor AtmosphericScience,CambridgeUniversity,Cambridge, England. quickly converted both NO2 and HNOa into NO. NO was the main product formed, with CO2, CO, N2, and N20 being minor products. (It wouldthereforebe interestingto seeif slightly larger N20 concentrationsare observedin aircraftflight corridors.)NO reactedon the soot at a rate which was at least i order of magnitude slower than both NO2 and HNOa. In the presenceof oxygen,NO is expectedto be par- tially convertedinto NO2 [Thlibi and Petit, 1994]. It is likely that three of the NOv/soot reactionsthat will be important for the atmosphere are 2Departmentof Physics,Imperial College,London,England. 3Earth SystemScienceLaboratory,Universityof Alabama in HNOa carb?n NO2 Huntsville. 4Laboratoire de Phsyique et Chimie de l'Environnement. CNRS, Orleans. France. HNO3 0148-0227 / 97/ 96JD-02969$09.00 • NO NO2 ca-L• n NO Copyright1997 by the AmericanGeophysicalUnion. Paper number 96JD02969. carbon (1) (2) (3) The exact fate of the oxygenand hydrogenatoms in theseprocesses is important and needsto be examined 3671 3672 further. LARY Direct ET AL.: CARBON AEROSOLS AND ATMOSPHERIC ozone loss can also occur on carbon aerosols. Oa c•rbon > O2 (4) PHOTOCHEMISTRY The evaluationof DeMote et al. [1994]recommends a reaction probability for Os on carbon/sootof 3 x 10-2. Fendeland Ott [1993]reportfast Os losson 10 to 100 nm solidcarbon agglomerates,with an estimated Taboret al. [1993, 1994]measuredthe accommo- reactionprobabilitynear3 x 10-2. Fendelet al. [1995] dation coefficientfor NO2 uptake on solid amorphous report that submicron carbon or iron aerosolparticles carbon. Like Thlibi and Petit [1994],they foundthat destroy ozone efficiently;the sticking coefficientof Os NO2 was reduced on the solid amorphouscarbon to to the particlesis of the orderof 10-4 . They conclude yieldNO. If atmospheric NO2 is reducedin thiswayon that particles present in the stratospheremay repre- solidamorphouscarbonthen it representsa significant sent a significantsink for Os. Smith et al. [1988]renighttimelossof Os asthe reductionof NO2 is actually port that the ozone/sootreactionis first orderin ozone, with CO, CO2 and H20 the only stable gaseousprodthe rate limiting step of the catalytic cycle ucts. Stephenset al. [1986]measuredCO, CO2 and NO• carbon NO+Oa NetOs O2 as products with an O2 produced for each O3 re- > NO > NO•+O• carbon • (5) acted. Stephenset al. [1986]measureduptake coefficientswhichvariedfrom 10-s to 10-5 depending on 02 the carbon sample and Os exposure. The Os reaction probability on carbon aerosolsis clearly dependent on This ozonelosscycleis unusualin that it can occur the carbon aerosol'ssurface history. Consequently,in duringthe night. It doesnot requirethe presence of this study,a stickingcoefficient of 1 x 10-5 wasused sunlight.However,the cyclealsoproceeds duringthe for Os to O2 conversionas a lower limit, so that the day. The cyclehas little effecton other NOv species effects on the ozone should be at least those reported because as soon as the NO is formed it is almost im- mediately converted back in to NO2. This cycle should play a role whenever there are carbon aerosols. There is, of course,the possibility that the active sites for physisorption will become saturated and so will take no further part in the heterogeneousprocess. If this is the case, then desorptioncould be initiated by heating and the presenceof UV light. Another important issue is whether oxygen atoms are produced;if they are, this may partially or completelynegate the ozonelossmechanism just described. These are all areas that need to be further investigated. here, and, in fact, will probably be greater. Production, Carbon Transport, and Characteristics of Aerosols Atmospheric soot particles are produced by the incomplete combustion of fossil and other fuels. Combustiongeneratedaerosolscan affect the atmospherein two main ways, via light absorption(e.g., Shaw and Stamnes, 1980; Porch and MacCracken, 1982; Cess, 1983;Rosenand Hansen,1984) and via heterogeneous reactionson their surfaces(e.g., Tabor et al., 1993, Taboret al. [1993, 1994]report an accommodation1994). Heterogeneous reductionof atmosphericcon- coefficientfor NO2 uptake on solid amorphouscarbon stituents on carbon aerosols is a possibility that has of (4.8 4- 0.6) x 10-2. They foundthat the onlyma- been largely overlookedup until now, but it could acjor product wasNO corresponding to about 60% of the tually be very important. NO2 adsorbed on the surface. Consequently, in this The present subsonicair traffic occursmainly in the study, a '/value for the heterogeneousreductionof NO2 northern hemisphere,with about 30% to 50% flying to NO of 2.8 x 10-2 wasused. ThlibiandPetit [1994] abovethe tropopause[Schumann,1994]. Future highspeedcivil transport(HSCT) systemshavebeenpro- found that the reduction of HNOs into NO also oc- curson carbonaerosols.Rogaskiet al. [1996,alsoper- posed to fly in the middle and lower stratosphere. In sonalcommunication,1996]measuredan uptake value 1990, about 176 Mt of aviation fuel was used. To put of (3.8 4- 0.8) x 10-2. For the lengthof their exper- this into context,this aviationfuel constitutesabout 6% iments(<45 min) they observedno time dependence.of all petrol productsand providesabout 3% of the CO2 They found that the major products of the heteroge- releasedby the burningof fossilfuels. Global fuel conneous interaction of HNOs with soot were H20, NO2, sumptiongrowsby about 3% per year, with a doubling and NO. They lookedfor O2 and N2 productionbut did expectedwithin the next 18 to 25 years. Presentemisnot observeany. They determinedthe product yield for sionsby spaceflight are about a factor of 10,000times each species.NO2 was the dominant NO• product. It smaller than those from aviation. The present aviawas a factor of 5 larger than the NO yield. They mea- tion traffic has already caused a considerable increase suredthat, on average,for every three HNOa molecules in NO• concentrations (between30% to 100%)in the lost to the surface, two NOx moleculesare releasedto uppertroposphere alongmain flight routes[Schumann, the atmosphere.Consequently,in this study, a sticking coefficientof 4.2 x 10-s wasusedfor HNOs to NO conGraphitic carbonparticlescan be transportedon the versionanda stickingcoefficient of 2.1 x 10-2 wasused global scaleand so are able to reach remote regions. for HNOs to NO2 conversion. Long-rangetransport of graphitic carbon particlesof LARY ET AL.- CARBON AEROSOLS AND ATMOSPHERIC PHOTOCHEMISTRY 3673 at least 2000 km from the closestsignificantsourcere- It is rather surprisingthat most of the soot aerosolsare gionhasbeenobservedat groundlevel stationsthrough- not actually entrained in sulphate aerosols. Blake and aerosols out the westernArctic [Stonehouse, 1986;Rosenet al., Kato [1995]speculatedthat aircraft-generated 1981; Heintzenber9,1982; Rosenand Novakov,1983]. may constitute poor condensationnuclei. However, Trace elementand meteorologicalanalysessuggestthat Kiircher et al. [1996]find strongevidencethat aircraft even longer-rangetransport from midlatitudes between soot is responsiblefor the buildup of visible contrails. 5,000 and 10,000km awayhad taken place [Rahn and KSrcheret al. [1996]showthat the observationis consistent with model results under the assumptionthat McCaffrey,1980;Bartie et al., 1981]. Horizontal profilesof graphitic carbon particles have soot getscoatedby a liquid H2SO4/H20 solution,posbeen provided by missionssuch as the National Oceano- graphicand AtmosphericAdministration(NOAA) airplane sampling programme during March and April 1983 [Schnellet al., 1994; Rosenand Hansen, 1984; Hansen and Rosen, i984]. it has been found that graphitic carbon particles are presentthroughout the siblyalsocontainingHNOa, andthat the sootcoretriggers heterogeneous freezing of water ice during plume cooling. They found that the observationscannot be explained by assumingdry soot upon which ice nucleates results strongly point toward the fact that aircraft soot arctic tropospherewith upper layers typically contain- leavesthe jet enginesalready entrainedin a liquid sulfuric acid solution. This is also very likely to be true in ing more particles than at ground level. Pusechelet al. [1992]reportedthat upper tropo- cases where no visible ice contrails form. Even if soot spheric aircraft emissionsof soot presently represent would be emitted without coating, quick coagulation with in situ nucleatedH2SO4/H20 aerosols approximately0.3% by massof the backgroundstrato- processes sphericaerosols.Blake and Karo [1995]recentlypre- might entrain them into droplets. This would be simisented an overview of black carbon soot measurements lar to the Kuwaiti oil fire plumesstudied by, for exammade in the upper troposphereand lower stratosphere, ple, Parun9o et al. [1992],where carbonhad become k.-,+...... Ar•Oq •,•A ONONT nncl they annfirm thi,q finclinp'. entrained within liquid droplets. It could be that the They alsopoint out that for volcanicallyquiescentperi- soot is entrained in dropletscloseto the aircraft, but in ods, if surfaceareas are consideredinstead of mass, the the far-field situation as measured by Blake and Karo surface area of carbon aerosolsis comparable to that of [1995],the sootis no longerentrainedwithin a droplet. It seemsthat biomassburning does not contribute sulphate aerosols. In fact, the surface area of carbon aerosolsmay be more than that of sulphate aerosols significantly to the upper tropospheric, lower stratoduring volcanically quiescentperiods. This is because sphericsootloading. Blake and Karo [1995]foundthat carbon aerosolsare typically not spherical, but rather the measured latitudinal distribution of black carbon havea fractal geometry.Blakeand Karo [1995]consid- soot between 10 and 11 km covaried with commercial ered two extreme cases and calculated the surface area air traffic use, suggestingthat aircraft fuel combustion of the carbon particles as if they were all spheresor as if is the principal source of soot at this altitude. In adthey had a purely fractal geometry.The fractal surface dition, they found that at latitudes where there is a area calculationgavean area that was 30 times greater lot of commercial air traffic, significant levels of black than the area calculated if all the carbon aerosols were carbon soot were measuredeven at 20 km. This suggests that aircraft-generated soot injected just above assumedto be 20 nm spheres. Colbeck and Nyeki[1992]presenteda reviewof fractal the tropopausemay be transported to higher altitudes. structures as applied to environmental aerosols. They By assigning upper and lower estimates on the total point out that the atmospheric lifetime of particles is fuel burned in the stratosphere by aircraft and compardependent on their terminal velocity, which is related to ing this to the measured soot concentrations, a black the fractal dimensionof the particles. Many natural ob- carbon soot residence time of between 4 and 12 months jects such as coastlines and clouds may be represented wasderivedby Blake and Karo [1995]. Baum#ardneret al. [1996]report resultsfrom a new by fractal theory. A basic property of fractal objects is instrument which can simultaneously measure aerosol that they obey the scalingrelationship' diameter between0.4 and 10 ttm and whichwasrecently N ocBD (6) flown on the NASA ER2 aircraft during a stratospheric where N is the number of features, R is the resolution measurement campaign. The measured stratospheric of measurements,and D is the fractal dimension of the refractive indicesdo not agreewell with theoretical preobject. Fractal clusterssedimentmore slowly than com- dictions, and vertical profiles suggestthe presenceof pact spheresof the samemass.Berry [1989]calculated nonsphericalor absorbingparticlesin the altitude range that clusters composedof 1000 individual spherulesof of 7 to 9 km. One possibility is that Baumgardner et radius20 nm fall at approximately 100m yr-• if D:1.8 al. [1996]observedcarbonaerosols. ascompared with i km yr-• for solidclusters(D:3). In the Arctic boundarylayer a low HNOa/NOx ratio Blake and Kato [1995]state that the carbonaerosol has been inferred from measurements. Therefore, if the distributions they presented did not account for soot soot reduction actually occurs, since the Arctic is where that had been entrained within sulphuric acid droplets. soot accumulates,we would expect to seethe low values 3674 LARY ET AL.' CARBON AEROSOLS AND ATMOSPHERIC that are seen. The observationstherefore subjectively profilesover Kiruna support the reduction of HNO3 on soot. These findings point to the potential importance of NOu/amorphouscarboninteractionson the local and iiiIillill i,iiiiiilliiiiiiiiiii t 10- global scalein the stratosphereand the troposphere.If the aviation fuel consumption is set to double in the next 18 to 25 years, it is likely that the carbon surface area will also double, while increasesof up to a factor .,•! of 10 couldoccurin flight corridors[WMO, 1994].This / lOO opens the possibility that on the hemisphericscale the carbon surface area could be double that PHOTOCHEMISTRY of the back- - groundsulphateaerosolsurfaceareaduringvolcanically quiescentperiods, and 10 times that of the background ß AMON data Simulation A sulphate aerosolsurfacearea in flight corridors. Such a ........ Simulation B Simulation C large surface area could therefore be a potentially im1000 portant site for heterogeneousatmospheric chemistry, 0.001 0.01 0.1 1.0 10.0 which really should be thoroughly investigatedwith a (ppbv) senseof urgency. It is not only nitrogen speciesthat could be reduced Figure 1. SecondEuropeanStratosphericArctic and _ on carbon aerosols. For example, HOC1 could be reduced to HC1, and HOBr could be reducedto HBr. This could be significantin polar regions,where the production of HC1 can becomethe rate limiting step for further chlorine activation. These processesalso need detailed examination. Mid-latitudeExperiment(SESAME) campaigncomparisonfor the simulatedNO2 profilesover Kiruna on February10, 1995. SimulationA (solidline) wasa control simulation whichincludes a standardstratospheric chemistry scheme.Simulation B (dashedline) included the reductionof HNO3 and NO2 on carbon aerosols, both with a 7 valueof 2.8 x 10-2 and a carbonaerosol surface areaof 1 tzm2/cm 3. Simulation C (dot-dashed line) wasthe sameassimulationB, exceptthe 7 value Comparison With Observations for the reductionof HNO3 was reducedby a factor of Since there is uncertainty associatedwith the rate at which HNO3 and NO2 is reduced on carbon aerosols, this sectioncomparessomeobservationswith model 10. culations that include the reduction of HN03 and NO2 heterogeneouscarbon reactions. Simulation B includes on carbon aerosols. the reductionof HNO3 and NO2 on carbonaerosols, both with a 7 value of 2.8 x 10-2. SimulationC was SESAME Comparison the same as simulationB, except the 7 value for the Figure 1 showsthree simulationsthat wereperformed reductionof HNO3 was reducedby a factor of 10 to with a three-dimensional chemicaltransportmodel[Chip- a value of 2.8 x 10-3. The simulations included the perfieldet al., 1996],whichusedmeteorological analy- hydrolysisof N205, C1ONO2,and BrONO2 on sulphate sesto specifythe circulation. The model was integrated for 12 days and usedresultsfrom a seasonalintegration, which had been integrated from November 22, 1994, in aerosols. Figure 1 showsthat the NO2 observationsare brack- gration had been initialized itself from a combinationof etedby simulations that includedheterogeneous carbon reactions(simulations B andC). This is not conclusive proofthat the proposedcarbonmechanismdoesoccur, two-dimensional but it does make it clear that without order to initialize each simulation. chemical The fields and data seasonal from inte- instru- some kind of ments on board the UARS satellite. This integration is presentlybeing usedto investigatethe anomalouslylow renoxificationmechanism,whether it is the mechanism postulatedhere or someother mechanism,the vertical 03 amountsseenduringthe 1994/1995northernwinter profilesof NO2 arenot wellsimulatedwhenthe hydroly(as observedby Manne•let al. [1996]). The modelwas sis of N205 on sulphateaerosolsis included. The N20, sampled during each simulation at the same time and hydrolysisused in this study is the temperature and position relevant to measurementsof NO2 made by 'Ab- compositiondependentdata recommendedby DeMote sorptionpar MinoritairesOzoneet NOx' (AMON) at et al. [1994]. A slowerN20, hydrolysison sulphate night inside the polar vortex on February 10, 1995, over aerosolswould clearly also increasethe simulated NOx Kiruna during the SecondEuropean StratosphericArc- concentration. The required renoxification mechanism tic and Mid-latitude Experiment(SESAME)campaign needsto operate up to altitudes of around 25 to 30 km. It is unclear what the transport mechanismwould be [Hermannet al., 1996]. Simulation A was a control simulation that includes a standard stratosphericchemistry schemewithout any for carbon aerosol to be found at these altitudes within the polar vortex. LARY ET AL' CARBON AEROSOLS AND ATMOSPHERIC ATMOS Data • 0.2/.zm%m • soot 3675 77.1oS, 147.1oE, 15:46 GMT, 9 November1994 44.6øN, 140.3øE, 7:17 GMT, 6 November1994 ß ..... PHOTOCHEMISTRY ß ..... 0 •m2/cm • soot............. 0.1fi,m%m • soot 0.5fi,m%m• soot..... I/•m2/cm • soot 35• ATMOSData 0.2/.zm%m • soot 0 •m2/cm • soot............. 0.1/•m2/cm • soot 0.5fi,m2/cm • soot..... I/.zm%m • soot 35- -35 -35 _ _ _ -30 I • 30-- _ 30 I _ _ _ 25 'O _ ::3 _ _ • - { I I -2O _ _ _ _ _ _•15 15- L•5 15-_ _ _ _ •10 -10 • •{ 0.03 0.06 100.01 0.1 HNOJNO• o.o3 o.06 0.3 0.1 o.6 1.o 3.0 6 0 10.0 HNOJNO• Figure 1. SecondEuropeanStratospheric Arctic and Mid-latitudeExperiment(SESAME) campaign comparisonfor the simulatedNO2 profilesover Kiruna on February 10, 1995. Simulation A (solidline) wasa controlsimulationwhichincludesa standardstratospheric chemistryscheme. SimulationB (dashedline) includedthe reductionof HNOa and NO2 on carbonaerosols, both with a 7 valueof 2.8 x 10-2 and a carbonaerosolsurfaceareaof 1 pm2/cm3. SimulationC (dot-dashed line) wasthe sameas simulationB, exceptthe 7 valuefor the reductionof HNOa was reduced by a factor of 10. ATMOS ATLAS3 Comparison Figure 2 showsthe effect of the reduction of HNO3 the northernhemispherehas a larger sootloadingthan the southernhemisphere.The best agreementbetween the model simulations and the ATMOS ATLAS3 ob- and NOa on carbonaerosols(Table 1) on the vertical servationsin the northern hemispherefalls closeto the profilesof NOa and the HNO3/NO•: ratio in the north- simulation with 0.2/•m2/cm3. This is in generalagree- ern and southern hemispherescompared to the Atmo- sphericTraceMoleculeSpectroscopy (ATMOS) Experiment ATLAS3 measurementsmade during November 1994. The model used was the AUTOCHEM column ment with the SESAME comparisondescribed above. In contrast, the best agreementbetween the model simulations and the ATMOS ATLAS3 observations in the southern hemisphere falls close to the simulation with modeldescribedby Lary [1996]and Lary et al. [1995, 0.1/•m2/cm3. This is consistent with the fact that the 1996]. The columnmodel was run for 7 days starting southernhemispherehas a lowersootloading. Figure 2 from the ATMOS ATLAS3 vertical profiles of temperalsoshowshow sensitivethe HNO3/NOx ratio is to the ature, 03, NO, NO2, N205, HNO3, HNO4, C1ONOa, H20, CO, CO2, CH4 and NaO. Below 25 km the diurnal correction to the NO2 profiles is very important [Newchurch et al., 1996]. soot loading. An increaseof the soot loading by a fac- tor of 10 reducesthe HNO3/NOx ratio by a factor of approximately 100 in the lower stratosphere. Including the reduction of HNO3 on soot leads to a simulated It can be seenfrom Figure 2 that above25 km there is HNOa/NOx ratio within the observed rangeof the averexcellentagreementbetweenthe modeland the observa- age free troposphericratio of 1-9 reported by Chatfield tions in both hemispheres.Below 25 km there is a slight [1995]. contrast between the hemispheres. As noted above, • .... c comparisons• not conclusivelyprove that the reduction on carbon aerosolsactually occurs but they show that the reduction of NO2 and HNO3 is at least Table 1. Carbon Reduction Reactions Included in This Study sphericassymetryin the observedNO2 and HNOa/NO• Reaction HNO3 HNO3 NO2 03 consistent with observationsand can explain the hemi- carbon > > carbon > carbon > carbon 7 used NO2 NO NO 02 2.1 x 10-2 4.2 x 10-3 2.8 x 10-2 1 x 10-s ratio vertical profiles. To say this another way, a renoxification mechanism, whether it is the one postulated here or a completely different mechanism, can improve the agreement between observationsand simulations of the observedNOs partitioningif it is more effectivein the northern hemispherethan the southern hemisphere. Toumi et al. [1993]consideredthe ATMOS HNO3/ NO• ratio and concluded that the current recommen- 3676 LARY ET AL.: CARBON AEROSOLS AND ATMOSPHERIC PHOTOCHEMISTRY dations for the sulphate N2Os lossare too fast to agree HNOa/NO• ratio [Chatfield,1995].Figure3 alsoshows with observations. Considineet al. [1992], studying that the heterogeneousreduction of NO2 and Os on limb infraredmonitorof the stratosphere (LIMS) data, amorphouscarbon aerosolis quite rapid. The rate of and McElroy et al. [1992]usingATMOS data, alsocon- Os reduction is likely to be faster than that displayed cluded that the current recommendations for the sul- in Figure 3, as a lowerlimit 7 valueof only 10-5 has phate N2Os lossare too fast to agreewith observations. been used. Figure 2 showsthat including heterogeneousreduction Including the heterogeneousreduction of NO2 and of HNO3 on carbon aerosolsimproves the agreement HNOa by amorphouscarbonaerosolsincreases the night- betweenthe simulatedand observedHNO3/NOx ratio time NO concentration(Figure4). Without the hetero- in the lower stratosphere of the northern hemisphere geneous reductionof NO2 and HNOa modelspredictan by providing a renoxificationmechanism.Now that we NO/NOy ratio that is almostzero. have seen that the reduction of HNO3 and NO2 is at least consistent with observations, the next section ex- Figure3 shows thatthemidnightrateoftheheteroge- neousreductionof NO2 on amorphouscarbonaerosolis amines in detail the sensitivity of the proposedmech- a functionof both temperatureandthe amorphous carbon aerosol surface area. The rate varies between 10a anisms to carbon surface area, temperature, altitude, and day length. molecules cm-3 s-• for an amorphous carbonaerosol Sensitivity Experiments surfaceareaof lessthan i/•m 2 cm-3 and 106molecules cm-3 s-• for an amorphous carbonaerosol surfacearea To examine the role of HNO3, NOa and 03 reduction of 10/•m2 cm-3 at 200K. Sincethe midnight rateof reaction of NO2 with O3 closelyfollowsthe rate of re- on amorphouscarbon aerosolsin the lowerstratosphere and the upper troposphereat mid-latitudes a set of idealisedmodel simulationswere performed. The numerical model usedfor thesesimulationswas AUTOCHEM, ductionofNO2to NO ontheamorphous carbonaerosol, it can be seenfrom Figures3 and 4 that the reduction of NO2 to NO on the amorphouscarbonaerosolis the rate-limitingstepof the catalyticozonelosscyclemen- a modeldescribed by Lary [1995]andLaw et al. [1995, 1996]andFisherandLary [1995].In the simulations a tioned above. stationary air parcel at 45øN was considered.The sim- ulationsincludedthe hydrolysisof NaOs, C1ONOaand BrONOa on sulphate aerosols. With a reactionprobabilityfor O3 of just 10-5, at low carbon aerosolsurfaceareasthe direct lossof O3 on the carbonis likely to be faster than the catalytic lossdueto the production of NO (Figure3). Forhigh carbonaerosolsurfaceareasthe direct lossof O3 on the carbonis likely to be slowerthan the catalyticlossdue to the productionof NO. By wayof a comparison, under In the first set of sensitivity experiments the tem- the sameconditions,the corresponding ozonelossrate perature of an air parcel at 70 mb at equinox was at noon due to the reactionof HO2 with 03, i.e., the varied between 200 K and 240 K and the amorphous rate of the major ozonelosscycle,is approximately105 Carbon Surface Area and Temperature Dependence molecules cm-3 s-• at 200K, risingto 106molecules 10/•m2 cm-3. Foreachof theseconditions a 7-daysim- cm-3 s-• at 240 K. An ozonelossrate that can reach carbon aerosol surface area was varied between 0 and 106molecules cm-3 s-• istherefore clearlya significant ulation was performed. Although the observedhemisphericaveragecarbon aerosolsurfacearea is typicallyaround1/•m acm-3, much higher areas do exist locally, for example, in aircraft wakes. In addition, becauseit is likely that the carbon aerosol abundance will double over the next 25 ozone loss rate. Figure 3 showsthat the midnight rate of the heterogeneousreduction of HNO3 on amorphouscarbon aerosolis a function of both temperature and the amorphous carbon aerosolsurface area. The rate varies be- years,carbonaerosolareasup to 10/•macm-3 were tween3 x 103molecules cm-3 s-• for an amorphous considered. carbonaerosolsurfacearea of lessthan i /•m2 cm-3 Figure 3 showsthat the heterogeneousreduction of up to 8 x 103molecules cm-3 s-• for an amorphous HNO3 on amorphouscarbon aerosol is a significant carbonaerosolsurfaceareaof 10/•m2 cm-3 at 240 K. renoxificationprocessthan can obviouslycontinuethroug]This renoxificationby the reductionof HNO3 provides out the day. For example, Figure 4 is for midnight. additional NOs which can take part in the catalytic When no carbon aerosolsare present, then the simu- destruction of ozone. Figure 4 showsthat the additional ozone losscaused lation predictsthat approximately80% of NOy is in the form of HNO3. However, with the assumed7 val- by the heterogeneous reductionof HNO3, NO2 and O3 ues, increasingthe carbonarea to just 1 /•macm-3, on amorphouscarbon aerosolover the 7-day simulation a value close to the current hemispheric average, re- periodreaches nearly3% (80 ppbv)for an amorphous ducesthe HNO3/NOy ratio to approximately0.5. Thus carbonaerosolsurfaceareaof 10 •um2 cm-3. It is noterenoxification on carbon aerosolswill also be important worthy that the additionalozonelosscausedby the hetin the troposphere and could explain the current dis- erogeneousreduction of NOu is almost independentof crepancy between observed and modeled values of the temperature if the 7 value is not temperature depen- LARY ET AL.: CARBON AEROSOLS AND ATMOSPHERIC PHOTOCHEMISTRY Midnightrate of Midnightrate of HNO --) 0 I 2 3 4 240L i___ l • .•• 5 H 6 7 8 9 10 o I 240 I I .j...I !. I...•..... I...t..I...t....I.._[.. :.:•.-•':.: :.-:,... '-'•:.. ;,.'• 3677 ,.::-..:...,..-....-......:. ..... .................................................................. •'- 2 --) NO 3 4 5 6 -'•....j:•?,'•x-:• *:-:. :':':':... ::•.....:.:•.:j:•.:.:: :: ;::-'::":..-...:. _.::::;"'"':•.:..:.• . •'"'":•"" '"':•..•':::i:::' <"•••:'•"•""'"•"'''" "•':"•: '""' "'"' """:<•:•:• :<"' "":"' ...... ••- 7 8 9 o '' -•••'.:.-d ' ::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::: '""•"'" ======================================== '"'""'"' :': ........................................ "•• ---•'•••:i:; "•:. :" 220 i•1t' •• ............... f• ::;::':½::;'::::::'•':•'R"\v' ==================================== 35795"'"'"""•':•'"'•J!? I• '•J:..'f• - ._.".. •..•:,•;;:- --.--• ::.<::' :...'::.'.• •.• ......... •=•:-:-.-•.--__-•-_-•:_•__-_:. • .-..-.•-•----------•-•----.-.-.--•.•.-.•..•..•••...;:.:• • i::.,.'.• • :':':' •-. ::'""- :•.•i 38928 :•..'•::;ii: :' "' !•' :'•"'::'•:• a '-<':' ..................... '"'•"••' "--"--' • :•, . 220 ""-'-':'-'-'-'-'-" 28255 5651 ..... •..,•,::.:.:.,+:: 5207 -'. •,• ;•i -.. 210 26035 4919'"'"• :<"½'•' '":' ' 4285":'"'"•:"•iiii '"" 24598 21427 3057 '""':"<<'"" "::• :' 15287 200 0 200 I 2 3 Carbon 4 5 Aerosol 6 7 Surface 8 9 IJiJ•JJJJ• ................. 0 10 I 2 ':•"::::'•'•"••'••••••• 3 Carbon Area 4 5 Aerosol 6 7 Surface 8 g 10 g 10 Area Midnightrate of Midnightrate of -> NO 0 I 2 3 4 5 6 7 8 g .................. *'"'•-:':••:•::-••••••••::'?-.:,<• ,e..-.-'-• ................................ •.. ..... 153506 -.:..-:...-•. ..-....• :.., .':. ::'..:::: • 126362 '""';'" '";'•'•:•!•}! '-" • ''" ,•••... •,,,,,,,•<:,,•., ........... ,..•.;..<.•.•,::• 230- v 200326 "!i'i'i'!!: ?:i!:!':' • :::::::::::::::::::::: '- .:.:.-.. :.x, ;:.:.:.:.:.:.:-:.' l::: 78179,•,•... -,...•.,-<,,....,: 57395 ""::• •.• •::.. 37138 '"'-"•.., .•. .'-:•'.: ß 2 Carbon 3 4 5 6 7 5 6 7 8 220 E ß ::::::::::::::::::::::::::::::::: ..... .::...::.::::: ::-::....: .... ........ :...::::..:::::..:--<......,..-.::: :•,,:-:•:-:.--, '-• .....<•:• --...'.-. .':. ...... ...:::....-:.-: ....... -.................... .......... .......•....••...• ß:::.:-:-<.::::'::: ,•:••••••:.... :::::::::::::::::: '"•:'::::'::::::-:,,, ,•:,..'.:....•:: ,,,,•:•G ,,-, ,,,. :::.:...:.:..:.. ::.::,:::: ,-.., .:..::.:::..: .. 55256...... •J•V• ::. :.. ::::.:::• g::::...........•:.:.:.::: •.,:..:5•.:::•! • g...'"•'"':•<;::::'• ":' •':::::: 'f 48753 ... •:•.. :•:.::..-:.-::..:..'::...-.:.::':.:?-:•..':.• •o,:.':,•!• .'.:<.:.::. ,•-..: .... ..."...'•-. e..:?: •' :.:::::::::.: ',, 42347 '"' '•':"i .:::::::::::::::: 36038 •....••. •-.••--.•••••:...-:: ........................... .::::::..-::: .....::,- i""" mo- • ::•::.:.....-::::::: .-<....:::.'::•:: --':. :.. ,,.. :e.••.-..":.•...'.:• o, o,-:-:,. ::--.•::..-::: •, ::......... :-,,,..: ........... •' '•'•••"'...........-....-.. '"'. '•..•":-•: :"":'"""' "'"'"' '"'"::* .......... .:::::::::.:. .[- 200 8 9 10 Aerosol Surface Area •"-'""'"'"'""" ':"•:••:•••iii' "•..:-',..•_ _,•'.-'.-""• ':'"•••••••••1: ••ltl•'' ....... ..""ßß f 0 I I [ I [ 2 Carbon I 3 i I 4 i I 5 Aerosol • "',. : """ "•i: •. :'<<'" .... ::::;:::.::::.. ::• 23698'•"'":'½ :..,,.., .:...,..:,:..... :,..:: ,::: :,.::::..: ,•,. :.-...:.:: ..:.•.. .,.,, :..'.,,:"' :•. .:•:::...: .:::.:,, . :.200 V"':....... i....... :'"":i-':'";' .....:-•"r'W'm'.....i'.....,' 'i ", I 4 •:" ":'•:•:ii "'"" '" .............. - ............... • •.,: "'••':••"-•i .................. :":••'*'' ß' . ß,•••••.-..•: ,.:, :-'-':..::-'-'.-:::' ...... 0 3 •J•['"'"'"'"'""'"•:':•:•:•:•••:.. :iii :•••JJ•'":•":':""•••:•'.•. .... •":•" '• •"< •!::...:'::::i?:::.: '•...-'••::•-"..•.,,,<....,.%..,.'..-..-.,•. •-'.'-'--..... :<-:<--:...,s•::•-::::.... - ..'I • 230-•------'-----'--"---"---•"•"•'•••'•'••"'•;••• -'• ,•". • 2 240 - ß'.... •--..-....-.._._. •.•...•.....,,,••....•••••••• .-,<--.• I o 10 ....'-;-'-.__.._ ..... :...._:_-:-:-:_-.s."-'---'-'--'-'-•:-•'.:.. '::::'...:.-:::<• :.%4.4.-:.•:.<:,-: :,-.:::=.• ..:.:• •.......-.......:: :..:: :,: .... I 6 • ': I 7 Surface [ I [ 8 I 9 • 11692 ] i10 Area Figure 3. Resultsfor midnight at the end of a set of 7-day simulations. During the 7-day simulationsthe air parcelwas kept at 70 mb, 45øN at equinox. The temperature and amorphous carbon aerosolsurfacearea present were kept constantfor each air parcel through out the 7-day period. The resultsare plottedas a functionof temperature. (in Kelvin) and the amorphous carbonaerosolsurfaceareain pm• cm-a. Note that eachplot hasa differentcontourinterval. dent. This is in contrast, for example, to the hydrolysis sphere,irrespectiveof the temperature, and it is likely of N20.s where althoughthe 7 value is only weakly tem- that it contributes to the observed ozone trends. This peraturedependent,the N205 concentration is strongly mechanismwill increasein importance with the increase temperaturedependent.For amorphous carbonaerosol surface areas that are closeto the hemispheric average, the additional ozone loss is of the order of 0.3-0.5% over the period of the 1-weeksimulation. in the abundance of carbon aerosol. It is therefore a mechanism that must be accounted for when consider- ing the impact of increasedair transport and all combustion processeson the atmosphere. Figure4 showsthat the nighttimeozonelossdue Altitude Dependence to the heterogeneous reductionof HNO3 and NO• has In the secondset of sensitivity experiments the altisubstantiallyreducedthe nighttimeozonelifetimefrom around 350 months without reduction on carbon to just tude of the air parcel was varied between 10 and 25 km. Figure 5 showsthe additional 03 losscausedby includ52 monthswith a carbonareaof only 1 Fm2 cm-3. ing the heterogeneousreduction of HNO3 and NO2 on Heterogeneous reduction ofHNO3,NO2 and03 thereamorphous carbon aerosol as a function of altitude and forerepresents a potentiallyimportantin situozoneloss mechanismwhich can operate throughout the day at all latitudes in the lower stratosphereand upper tropo- carbon aerosolsurface area. It is immediately apparent that in the stratosphere the enhancedlevelsof NOx lead 3678 LARY ET AL.: CARBON AEROSOLS AND ATMOSPHERIC PHOTOCHEMISTRY Midnight Midnightrate of HNOJNO• NO + O• --) NO• + O• 0 I 240 I 2 3 4 5 ' i • • I. • I • •---...:-:-:-:•.,--.-:::::::::: ....... 230• 6 7 8 9 0 10 I 3 4 5 ,..I .,...J • • I • J • J -. x,• 2 6 7 • 8 9 10 •. [.. •..[. ].....!....1..... •.'"•'•---',••••••••• ""•'"'•'" '"••-':'-"""-•:""•'"' '-"'"':' "•'"'• ß ' -,,',, -.-••••••:., 0.511--'-'-:---'"•-'-•.•ii •230-::::::::::::::::::::::::::::::::::::::::: 0.421 '" '"•" :::" ';':' --' ::'• •.--x,•,x,•-,,-•-,.**;<....*•:•:._-..-•_::•_ ...'-:.,...-, -'.-- v 0.339 -•--••••• ••••:-.......................... --N"'"'•i "':" '" '"'"'" .......... •,.c<;•...-<..-..-.:..-<.--cc:•-• -.:.c:.-.::•.::¾ .• • :::::';:-'.':-*, :•.:..-.:.:.:.:,<•:&':.::.::•: :•.A•,:, •, ,,, 13i8•8 102822 ............. '•": '84783 .......................... ••"•••••••• •'"'""•'"'•" -"•. '•••-..-,,•' ""':"•ßß--ß -'"'"'""•••:':'••••••••••-.-:it'••"''" '.... ' '•-'"'"" '"""' ...................... '"'••••••••!i• '••'" ' ,• 220- 0.245 ß :::::::::::::::::::::::::::::: I-- 210-' ............... :-'.-:-'.•:'• -'•i•." ••:':"'•':•••:•.... .................. E 0.147 o.128 ' 7959 •_yu I ' 0 I I ' I 2 ' I • 3 I 4 • I 5 .• I • 6 I 7 ' I • 8 I 9 • 0.221 0.195'""(•.'• :.:.: :.,.-.....:.....---.. :.:..--:.:.:c.:.:.:-:.-:•..-<½.:..:A:•- :--:-: ..:.:-:.:---:. :-:-.---.•.-:.: • 200 I 0 10 1 2 3 4 Midnight 2 3 4 5 7 8 9 10 Midnight NOJNO, I 6 Carbon Aerosol Surface Area Carbon Aerosol Surface Area 0 5 6 NO/NO• 7 8 9 10 240 _ J,...:.:.:•...:•.:.:...•!i....,....:•.:....:.....:•.... ;•..:l.:•:.:.i!:i ..... J......,..L...,J:........L,,J..,,.-.•. ...... 0.657 .........,,•••••••.•--•------------• ..•.,,,-..•.....••,•:. ,,,, ,, ,,.,•••- ,.-, 230- ....................... ...:..,-.....::::::,: ,; ........... ,:, ,. ,. ,..... ,.......... ,. %N•'""l•,, ......... 'x----"':-•:'••.:..:.!•,,:-;.':'½•:' '••'"""--":•••;•••• ''•" •'•'- -' ....... "•'"' '•'"'•••0.491.......... •••••• •._ .-<•.-,,•,:.:••,, ........... •; ..,,,,-•••• v ,;.. :-:-:.:.... :..y:.::::::::: ,,, 230 0.446 .................... 0.372 ""i• !i•i•i:'-' 0.333 A• t• 22o- r• •.. I-- 210- .,...::,•-..-. 0.304 •.,,,. x..• 0.272 '""•'•<.....:'J:• ...,-' ............ 0.219""•-.'{i ":*:•:•" '"''' _ •...,,,,,,•:•:•...,•••! ................ ,,•.. ,.•.• ...•..,,.• ,:•...,,•..•':-•'•i •............ '•. .............. ..-• '"• 220 __• .':•;•, "' ;", ..'.::.' '""'•••:.:i•:i • _• •:-'-'.•..-'.;;•:• • -•.-'.:'•i,':' -:•'---'-•'"•'"'"':"•--' "% "'"'"'""'•"%' ....... •- ::..:,.• .•":• '• "' 4.50 E_ 04-:•;;;i '""-: :-•:-•......-. ----- E ,.:----,•,,,•r -,ß, -"•,•%•• ::::::::::::::::::::::::::::::::: 2.58E-04 :.:.:..:....:• I-. ,,.,., ,.,...• •"•"•"':••••••'.-•••: .................. •.":•" ':" .'/•,::i;:!:iiiiiii:ii::!•:;;!!!:!i!ii!i!i:i!::i:i:: 1.43E-04 L•'•-';•'..-.••..-..-••..:..:ii:::::::•...•:.::::•%¾:.?'!::•::•?:?.:::.::i:.i:.i:::.:.?:•i •"'"•"'""'""'•"'"'•'••':-,,,,• .......... 0.162 "'""' ':':'""':•' :"•:• ":"" -• ................ • ...... •....•....,, ....-.-..-,,•,_____-.•...•:••:.••....... •====================================== !•--'" """' "'-'••,. '":•':•--' "•"'' "'' '%••'" ••-:::'"::.::i:'-?-'":.;!::::??. ½ •....--••.....,....• ........................ .•••••••:•j•.::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::::: 200 !•""""•'"'"'"' '-''" '•'" 0 I 2 3 Carbon ::,oo -•.•`••`:•••.••••••••;•i!•:•:•:.•;•::•:•::•::i:•::::•.•:.•::•:•:• '%11•"'""""'•' ................ "' ......... :.;:-;:.-:-:.- ••"'"'"'" '•" '"'•:'••'•••••'""'" :'"" ':•: ':': :: '::: i:" ':':':'i"::: ':,' •:-":'; '•' :'½ 4 5 Aerosol 6 7 Surface 8 9 10 0 I Area 2 3 Carbon 4 5 Aerosol 6 7 Surface 8 9 10 9 10 Area AdditionalOzone loss(%) due to reactions on carbon 0 I 2 I ß ' ' 3 4 5 6 7 8 240 ................... ......•.........,,,..•...:,•••;:•,•,% .......... •.. ¾:• •:,'"'"'"'•"•'••••....'••,..• ••,••••x,,• ,,••..... •!!!i;:•!?•i?:::•..-::. •:::•::•! .... :-:•:>..',"'"""'-'" ' :•.• • x :.:;:;::•:;• 2.74::::::::::::::::: :::::::::::::::::::::::::: :::::' % ';;-'•'"-;--- .•'::::::::. "-..:,. ...':.:.'. <•$.-• • -...,,:,:.-, ............ 2.48 ========================= ..... :..--.-.................. •.:.:..,.-,:' .....'•..-.:.:..-.:.:.:*'-'::::-"-':-•'•. • :•,:':':":.,:':-'".',.•-,• ....:::.:!i:::&,.. ......................... -:,;%•, -.,. ß;-----..-,---•-,-.... :4..-.::..:.:44•.''"---"-'-'-'-'-'-'-'-'-•-'-:.•••:.... -,:.-::::.'.-: • "• '--------------"-"-' .......................... ;:s.::.-'.::::,•,.'.•::::::• .............. • •.================================= .:::•7.".'.-.'.'.'.'.'.'.'.'.'.'.'. 2.32 ::':':'::':'":::• ....:"•'"'""•?',•,i !:;?,',ii?,i!!! 2.•5':'"""'""-"'•-?-::•-:.-: ::::-. ,-.i':-,"•. "t•••'• ..i:i:i:i:ii::!::..•---• .,:..'.:.,--.-:;•-:.: -'•:------'•'::•--'-:: :........................ -........................ ':::"-.•"'."": '"'"'•'*•'•••• "•'"'"'•' ...-.....-.-.-.-.-.-.._-. 842.6' ::•"•ii '"•:" '"'":::' ' 595.2 ::::::: ................. ======================== 471.1"-'•?¾<.• i::i•, '" ,•_• ................. .•..•••.. -,•, ,:•:•:! ....... • :,,-...'.-o-;.:j.;.-ii.:'::,•.•!•½',•i'.,•.,•-,-'•.•:•11;ii:-• ======================= 1.73:,•'"'.' ......... •::• ,,, ••....,....:••:•••:•••••\•i•iiii::::ill .............. • .. :::::::::::::::::::::::::::::::::::::::: 391.8 ?,• -•"'•,••••'•"•,•,:iiiii:•::iiiiiiii•-. ............... ' '' ":::•-':"':':-':-'::::::•':::::';•::•'::•::'::'::' •':';;:;::• ......... 333.9 259.9 "'":'"':'"•'• ":-.-' 233.2 0 I 2 Carbon 3 4 5 Aerosol 6 7 Surface 8 Area 9 10 .......................................................... -•:.-,:•,:.:•:.-.:.:,.-,;•:,-,.•.•.•. ........ 1.94 220 -•,., x -. •........ ...... ,,,....•,....•?,•.-:•,,• • ,,;.... • , :::::::::::::::::::::::::::::::::::::: ....................... 0 •.:.:.:.:.:. ::::::::::::::::::::::::::::::: :.::..::.:.: :_:_:. 0. I 2 3 4 5 6 7 Carbon Aerosol Surface 8 9 10 Area Figure 4. Additional resultsfor midnightat the end of a set of 7-day simulations.During the sevenday simulationsthe air parcel was kept at 70 rob, 45øN at equinox. The temperature and amorphouscarbon aerosolsurfacearea presentwere kept constantfor each air parcel through out the 7-day period. The resultsare plotted as a functionof temperature(in Kelvin) and the amorphouscarbonaerosolsurfacearea in •m • cm-3. Note that eachplot has a different contourinterval. The NO/NO•, NO•/NO• and HNO3/NO• ratiosare dimensionless. The 03 losstime-scaleat midnight is in units of days. The additional 03 losscausedby includingthe heterogeneousreactions on amorphouscarbon aerosolover the 7 day simulation period is shown as a percentage. ::::::::::::::::::::: LARY ET AL.- CARBON AEROSOLS AND ATMOSPHERIC PHOTOCHEMISTRY AdditionalOzone loss (ppbv) AdditionalOzone loss(%) due to reactions on carbon due to reactions on carbon 0 I 2 3 4 5 6 7 8 9 0 10 I 3 2 4 5 6 7 8 9 10 I • I I I i I I I i.. I ! ....... !....... !..... 25.0:.:......< • • :':..-.:-•-• :'ß 3679 '"•:-':.....-'::'::-:•:•:::--i:i: ':!:• ::: •:i: •:i: •:: :i:i: ::i: •.i :i: i:i:i:i:i: i:i: i:i:i:i: i:i-:-i:i :::i:::i:i:i: i........... i:i:•:•:•:•:i:•:i:. _ ........ •:'"' ';'"' ½'"':':•" ':-:/'/';i:-i::iiiii:::•::i:-i::i!iiiii::i::i::i::i?:::111::11ii?•:'• '::•?:ii:::•::i::?:::::!i!i:•::ii•i•:•ii::ii?:?:i; 231.40........... 4.32 ?:::::::::::::?:?:(:::::: ::::::::::::::::::::::::: 3.42 ?:??:::?:?:?:?:?:?:: ;:k:'""'½":::::::::• ....... Zt•.,•O . .=============== ........... .-•.._::............................. •.-•••:...•••11:.!;....i:i. •.5o 2.87':•' '":•:"---------•---:•i "'"":':':"'"'::" 2.39•':':"::':' '""• .08 ..................... .? ix• '••••. :•':•'•"••' ..... '' ' '•' •"•. E ......................... •:"••' '": •••:••4;-•i 96.50 '"':'"':':" "':': "• ' 63.39 ''""'"•'x'•"':•••;-!:':"," - .............. •..•.•••:_•••••••!•,.• • :•,, .::-.: ..:• .:• _ 94• •:.•. •__ :[''•""•••••....'•i ""'"'" ' ............... ••••• - 100 iiiii! .................. ••:=• ...... 0 •'"'•'••'"'•'•"•'••:'"'••'•••_'_.• ................. *"•'""""" _ 12.5 I 2 3 Carbon 4 5 '"'" ' ' ' '•"••"••••'""'"•!6 7 Aerosol Surface 8 g o.oo 125 I:'•• "':'" ::"" 100 0 0 I 3 2 4 5 6 7 8 9 10 Carbon Aerosol Surface Area Area Figure 5. The altitudeand areadependence of 03 lossby the amorphous carbonaerosol mechanism. Negative valuescorrespond to anozoneproduction. (left)Additional03 losscaused byincluding theheterogeneous reactions onamorphous carbonaerosol (inpercent) overthe7-day simulation period.(Right)Additional03 losscaused by including the heterogeneous reactions on amorphous carbonaerosol(in ppbv)overthe 7-daysimulationperiod. to ozone loss, whereas in the troposphere the enhanced levels of NO• lead to ozone production. As there is much more carbon aerosol in the northern hemisphere than there is in the southern hemisphere, the heterogeneousreduction of HNO3, NO2, and O3 on amorphous carbon aerosol will give rise to different trends in the northern hemisphere and southern hemisphere. In the troposphere the renoxification that occurs on carbon aerosols would tend to increase the ozone concentration. If the carbon aerosolspresent are entrained within droplets, then the behavior may be quite different; this also needs to be examined. Owingto the shapeof .theozoneand NO• profilesthe largest additional Oa loss in terms of absolute magnitude is largest at higher altitudes. Therefore, if amorphous carbon aerosol can be transported from the aircraft flight corridorsup to 2• km, there will be a correspondingeffect on the O3 lossrate. Carbon aerosolsare much smaller and lighter than sulphate aerosols,and if, assuggested by Blakeand Karo [1995],mostof the soot is not within sulphate aerosols,there is the possibility that the carbon aerosolresidencetime is long enough to allow them to reach the midstratosphere. This may be, in part, due to their fractal surface area, which means that they sediment much slower than a sphere of the same mass. If this is the case, they may be able to influence stratospheric chemistry, even up to 30 km. There may be some indication of this in the comparison of ATMOS data and simulationspresentedin Figure 2. Figure 5 shows that increasing the carbon surface area from just 0 /•m2 cm-a to 1 /•m2 cm-3 has a marked effect on stratospheric ozone loss and tropospheric ozone production. Observations show that carbon aerosols are definitely present in the midlatitude lower stratosphere between 12 and 20 km. In relative terms, it can be seenfrom Figure 5 that the additional O3 loss causedby including the heterogeneousreduction of HNO3 and NO2 on amorphouscarbon aerosolis significantin this region.Solomonet al. [1996]showed that when a two-dimensional model is constrained with time-varyingaerosolobservations the shapeof the observed trends in ozone is reproduced, but their magni- tude is about 50% larger than that which is observed. The presenceof soot in the midlatitude lower stratospheremay help to explainpart of this discrepancybetween ozone observations and simulations. SincegasphaseHNO3 destructionis soslow,any processthat is a sink of HNOa is potentially significant. Midnight HNOJNO• 0 1 250 2 3 4 5 6 7 8 9 10 I ß •....•..•:...•..•.•••••:. ........................................ ................... •....':...• .................................. •'::•••••• •'"''' '"'"'•'"'•'' ' ' x ' 22.5 • 2o.o ....... E •'"'"" '•• "-" '"'•"-'"""•'•'""'•'•"-•••,•:.-':• '•'%'' •'.•-,..-.,'. •'• •'"' '"'" '"" '"'' ,.•:...,.,,¾-"'"'"'""'""' •,• -.--.•,•...-•. '""'•'"'""-•----------•••.. -• 15.oo i:K:!:i:i:i:i:!:!:!:.-': 10.00,>..:-•"•¾• 5.00 .,.., :•,,:•.:.-:,.-.'""•" '"":••" '"":•••' -"•-".. '""'" "'-"•.....•, ........... '''' ß .................. ..'-%•.-.::: '• <r: 1•.o ' ' 2.00 1.00 0.75 0.50 -•••••••••__•',..'-• ...................................... -ß 0.30 .•..•..............•... ,,......._.., ß o. "-""'"'"'"""'•""'""•'"'•"••:'•••••i:• 10.0 I 0 1 2 3 4 5 6 Aerosol Surface 7 8 9 10 Area Figure 6. The simulatedmidlatitudeHNO3/NO•. ratio as a function of altitude and carbon surface area. 3680 LARY ET AL.' CARBON AEROSOLS AND ATMOSPHERIC PHOTOCHEMISTRY AdditionalOzone loss(ppbv) AdditionalOzone loss (%) due to reactions on carbon due to reactions on carbon 0 I 2 3 4 5 6 7 8 9 10 0 I , I..... !.... .!. ....... !..... J..... ,a•:!. •:•.•>:•:.:.:., .... I , ...! ......... ,....... I............ ... ..::...:. :::• .......... I.......... I •12.4 ........................... ........ ............................. .................... ............. '••••:•.. '"'"""'""'""•'•' '•'•.'-•:::•&:•?a•: 12.8 I 2 3 4 5 6 7 8 9 10 13I::!i!ii?:::i;iiiii?: I.................... :..•...•:.••••••••• i•{ -.,.": ......... '-'i•!•!i•i!i•ii!i!!!i!!•! ......... ::::::::::::::::::::::::::::::::::::::::: • "•:.¾•::•,•..::i?:!::•::!i•::•::•::!:.i::ii: "•....'..., "-':<'-'-----'::-.... .'.....•.-.•.:.::.:.: :::::::::::::::::::::::: • '-. .... ::::::::::::::::::::::::: ß '•-."k• ii::i::iii::i::iii:::,• ::::::::::::::::::::::::::::: $4.$ '"'"'"':'::-•:' •, 11.a-: .............. •::....:..,..•:: o•:•....•:.:...: • •:•::•,.: •.•:•,.: .... •.•,.............. . ......:.:•:.:.:...::.•,• ........................ •, ii;:..i::?:ii?:i::',•-a.-'•, .:-::jii! •:::.•.::...:..-•:.•:.-!•, :•:••'•-,,'.• •' '0 i!i::i::i!ii• •-'•'••'••:• '••'" ........... '•""' •' .:::::::::::.' ,o ":-•..:..:.':.'.:•:.:-? :::::::::::::::::::::::::: ':•'%•:'"'i• :::! ..................... '::•':•':':':'•': ' .......... • ::: 1.$• iiii:ii•!i!i-• :iiiii: '0 11 ......... •:::::•........................ ...:.:•r...<.:.:_, . .................................... • ß'•,•t •.• 1õ.0 "-'-:'-':-• -...'-.-'•. ß :.:.:.:.:.:.::::..: -..............,.....•:._..••.::.>•:::•.•'•.•.,..:.•.•.,..>.•. ....... . •:•,_:.:__...._.::.:.:.:._:.............:.:<..:•:<.-.:.:.:.:.:.:.:.:-:-.-.-.:.:.:.:.:.:.:.:.:-:.:-:-:.:.:.:.: 0 I 2 3 4 5 6 7 8 9 10 Carbon Aerosol Surface Area 0 2 3 4 5 6 7 8 9 10 Carbon Aerosol Surface Area Figure 7. The seasonal dependence of 03 lossby the amorphous carbonaerosolmechanism. (Left)Additional03 losscaused byincluding theheterogeneous reduction ofNO2onamorphous carbonaerosol(in percent)overa 7-daysimulation.(Right)Additional03 losscausedby includingthe heterogeneous reduction of NO2on amorphous carbonaerosol (in ppbv)overa 7-day simulation. Figure 6 showsthat increasingthe carbonsurfacearea air traffic, then a significantrenoxification mechanism fromjust 0 to 1/•m• cm-3 reduces the HNO3/NOwra- exists. This mechanism leads to ozone loss in the strato- tio by a factor of about 8. Chatfield[1995]statesthat sphere and ozone production in the troposphere. The the averagefree troposphericHNO3/NOw ratio is be- stratospheric ozone loss mechanismis almost indepentween 1 and 9. As can be seen from Figure 6, this dent of temperature and does not require the presence is entirely consistentwith these simulations. It is also of sunlight. The mechanismcan operate at all latitudes clear that increasingthe carbonsurfacearea will sub- where amorphouscarbon aerosolsare present. The relstantially increaseNO• and the oxidizingcapacity of ative importance of the mechanism increasesslightly with nightlength. Including the heterogeneousreducthe troposphere(Figure5). tion of HNO• and NOa in model simulations predicts Seasonal Dependence a free troposphericand stratosphericHNO3[NOx ratio To investigatethe seasonaldependence of the mechanism,the third set of sensitivityexperimentsallowed the time of year to vary betweenthe summersolstice that is in good agreementwith observations. Further laboratory studies are urgently required to preciselyquantify the rate of reduction and investigate other possibleheterogeneousreactionson atmospheric amorphouscarbon aerosols.For example, chlorine and bromine speciessuch as HOC1 and HOBr may also be and the winter solstice. This corresponds to a day lengthof between9.5 and 13 hoursfor an air parcel at 45øN in the lower stratosphere.Figure 7 showsthat for relatively high carbon surfaceareasthe additional 03 losscausedby including the heterogeneous reduction of NO2on amorphouscarbon aerosolincreasesby movingfrom the summersolsticeto the wintersolstice, whereas at lower carbon surface areas there is little vari- ationwith day length. Sothe relativeimportanceof the mechanismtendsto increasewith the lengthof the night for high carbonaerosolloadings.At higherlatitudesthe mechanismmay lead to less ozone loss at some times, as there will be more NO2 present to deactivate reactive concentrations. chlorine,this will, in turn, lead to higher C1ONO2 reduced on carbon aerosols. Further field measurements are requiredto preciselyquantify the amount of amorphous carbon aerosolspresentin the atmosphere. An assessmentof the impact of carbon entrained within water or sulphuricacid droplets is also required. 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World Meteorological Organisation, Scientific assessmentof stratospheric ozone: 1991, Rep. 25, WMO Global Ozone Res. and Monit. Proj., Geneva, 1992. World Meteorological Organisation, Scientific assessmentof 3682 LARY ET AL.: CARBON AEROSOLS AND ATMOSPHERIC stratosphericozone: 1994, Rep. 37, WMO Global Ozone Res. and Monit. Proj., Geneva, 1994. D. J. Lary and A.M. Lee, Centre For Atmospheric Science, Department of Chemistry, Cambridge University, PHOTOCHEMISTRY M. Pirre and J. B. Renard, Laboratoire de Phsyique et Chimie de l'Environement. CNRS, Orleans, France. R. Toumi, Department of Physics, Imperial College, London, SW7 2BZ, England. LensfieldRoad, Cambridge,CB2 1EW, England. (e-mail: [email protected]) M. J. Newchurch, Earth System ScienceLab., University of Alabama in Huntsville, Huntsville, AL 35899, U.S.A. (ReceivedNovember22, 1995; revisedAugust26, 1996; acceptedAugust26, 1996.)
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