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DTIC ADA628189: Assessment of Oxidative Stress in Lungs from Sheep After Inhalation of Wood Smoke PDF

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Preview DTIC ADA628189: Assessment of Oxidative Stress in Lungs from Sheep After Inhalation of Wood Smoke

Toxicology195(2004)97–112 Assessment of oxidative stress in lungs from sheep after inhalation of wood smoke Myung S. Park, Leopoldo C. Cancio, Bryan S. Jordan, William W. Brinkley, ∗ Victor R. Rivera, Michael A. Dubick USArmyInstituteofSurgicalResearch,FortSamHouston,TX78234-6315,USA Received10March2003;receivedinrevisedform12September2003;accepted15September2003 Abstract Toelucidatepotentialdose-dependentmechanismsassociatedwithwoodsmokeinhalationinjury,thepresentstudyevaluated antioxidantstatusandtheextentofpulmonaryinjuryinsheepaftergradedexposuretosmoke.Adult,malesheep(n = 4–5 pergroup)wereanesthetizedandreceived0,5,10or16unitsofcooledwesternpinebarksmoke,correspondingto0,175, 350and560s,respectively,ofsmokedwelltimeintheairwaysandlung.Smokewasmixedata1:1ratiowith100%O to 2 minimizehypoxia.Plasmaandexpiredbreathsampleswerecollectedpre-smoke,and6,12,18,24,36and48haftersmoke exposure.Sheepwereeuthanatized48haftersmokeexposureandlungandairwaysectionswereevaluatedhistologicallyfor injuryandbiochemicallyforindicesofoxidativestress.Plasmathiobarbituricacidreactivesubstances(TBARS)were66and69% higherthancontrolsaftermoderateandseveresmokeexposureat48h,whereastotalantioxidantpotentialwasnotstatistically differentamonggroupsatanytimeafterexposure.LungTBARSshowedadose-dependentresponsetosmokeinhalationand wereapproximately2-,3-and4-foldhigher,respectively,thancontrolsafterexposureto5,10and16unitsofsmoke.Lung myeloperoxidase (MPO) activity was also higher in smoke-exposed animals than controls, and MPO activity was markedly elevated(19-and22-foldhigherthancontrolsinrightapicalandmediallobes)inresponsetoseveresmokeexposure.Smoke exposurealsoinducedadose-dependentinjurytotracheobronchialepitheliumandlungparenchyma.Takentogetherthesedata showthatfewindicesofoxidativestressrespondedinadose-dependentmannertogradeddosesofsmokeinhalation,although mostoftheindicesmeasuredinlungwereaffectedbythehighestdoseofsmoke.Additionaltimecoursestudiesarenecessaryto determinewhethertheseoxidantsareacauseoraconsequenceoftheairwayandlunginjuryassociatedwithexposuretowood smoke. ©2003ElsevierIrelandLtd.Allrightsreserved. Keywords Woodsmoke;Oxidantstress;Lipidperoxidation;Myeloperoxidase;Sheep 1. Introduction Smoke inhalation injury is a major comorbid fac- ∗ Correspondingauthor.Tel.:+1-210-916-3680; tor in patients with thermal injury, and has been fax:+1-210-916-2942. reported to occur in about 30% of patients with ma- E-mailaddress [email protected] (M.A.Dubick). jor burns (Herndon et al., 1985). Such patients with 0300-483X/$–seefrontmatter©2003ElsevierIrelandLtd.Allrightsreserved. doi:10.1016/j.tox.2003.09.005 Report Documentation Page Form Approved OMB No. 0704-0188 Public reporting burden for the collection of information is estimated to average 1 hour per response, including the time for reviewing instructions, searching existing data sources, gathering and maintaining the data needed, and completing and reviewing the collection of information Send comments regarding this burden estimate or any other aspect of this collection of information, including suggestions for reducing this burden, to Washington Headquarters Services, Directorate for Information Operations and Reports, 1215 Jefferson Davis Highway, Suite 1204, Arlington VA 22202-4302 Respondents should be aware that notwithstanding any other provision of law, no person shall be subject to a penalty for failing to comply with a collection of information if it does not display a currently valid OMB control number 1. REPORT DATE 2. REPORT TYPE 3. DATES COVERED 15 FEB 2004 N/A - 4. TITLE AND SUBTITLE 5a. CONTRACT NUMBER Assessment of oxidative stress in lungs from sheep after inhalation of 5b. GRANT NUMBER wood smoke. 5c. PROGRAM ELEMENT NUMBER 6. AUTHOR(S) 5d. PROJECT NUMBER Park M. S., Cancio L. C., Jordan B. S., Brinkley W. W., Rivera V. R., 5e. TASK NUMBER Dubick M. A., 5f. WORK UNIT NUMBER 7. PERFORMING ORGANIZATION NAME(S) AND ADDRESS(ES) 8. PERFORMING ORGANIZATION United States Army Institute of Surgical Research, JBSA Fort Sam REPORT NUMBER Houston, TX 78234 9. SPONSORING/MONITORING AGENCY NAME(S) AND ADDRESS(ES) 10. SPONSOR/MONITOR’S ACRONYM(S) 11. SPONSOR/MONITOR’S REPORT NUMBER(S) 12. DISTRIBUTION/AVAILABILITY STATEMENT Approved for public release, distribution unlimited 13. SUPPLEMENTARY NOTES 14. ABSTRACT 15. SUBJECT TERMS 16. SECURITY CLASSIFICATION OF: 17. LIMITATION OF 18. NUMBER 19a. NAME OF ABSTRACT OF PAGES RESPONSIBLE PERSON a REPORT b ABSTRACT c THIS PAGE SAR 16 unclassified unclassified unclassified Standard Form 298 (Rev. 8-98) Prescribed by ANSI Std Z39-18 98 M.S.Parketal./Toxicology195(2004)97–112 combined smoke inhalation and thermal injuries tend 2. Materialsandmethods tobehemodynamicallyunstableandgenerallyrequire about 50% more initial crystalloid fluid for resusci- 2.1. Animalpreparation tation than estimated for the burn surface area alone (Navar et al., 1985; Thompson et al., 1986; Demling Twenty1-to2-year-oldneuteredmalesheep(Ovis et al., 1995). In addition, inhalation injury report- aeries,RambouilletX),weighing24to33kg,andfree edly accounts for 20–84% of the mortality in burned ofantibodiestoCoxiellaburnetti,wereobtainedfrom individuals, and is associated with higher mortality a commercial source and used in the study. Animals rates for every age and burn size category (Herndon were observed for 1 week in temperature-controlled, et al., 1985; Thompson et al., 1986; Shirani et al., indoor runs, were treated for potential parasites (1% 1987). ivermectin,1ml/75lb)andwerefedcommercialchow Smoke associated with structural fires, arises from andwateradlibitum.Theywerefastedfor24hbefore the combustion or pyrolysis of wood and the vari- tracheostomy and instrumentation. All animals were ous natural and synthetic fabrics, plastics and other maintained in a facility approved by the Association common materials available today (Wong et al., forAssessmentandAccreditationofLaboratoryAni- 1984; Alarie, 2002). Such acute lung injury resulting malCareInternational. from inhalation of these products involves complex The day before smoke or sham-smoke exposure, pathophysiologic processes that may not manifest sheep were sedated with ketamine (5mg/kg i.v.) into clinically significant symptoms for 24–72h and midazolam (0.275mg/kg i.v.) and orotracheally (Ruddy, 1994). Impairment of mucocilliary function, intubated with a 7mm i.d. cuffed tube. A chest ra- inflammatory responses such as interstitial edema, diograph was taken to exclude animals with active neutrophil infiltration, generation of oxygen free rad- lung disease. Under isoflurane anesthesia (2–4%), icals and pseudomembrane formation have all been a femoral artery was catheterized with a Silastic reported as potentially important consequences and cannula; an external jugular vein was catheterized mechanisms of smoke inhalation injury (Hubbard with an introducer sheath (8.5Fr, American Edwards etal.,1991;Younetal.,1992;FitzpatrickandCioffi, Laboratories Inc., Irvine, CA), followed by an 8-Fr 1994, Ruddy, 1994; Lalonde et al., 1995). Direct balloon-tipped pulmonary-artery catheter; and open alveolar damage, including alveolar edema, may also cystostomy and insertion of a urinary catheter were occurdependingonthedoseofsmoke,thetoxicityof performed. A tracheostomy was then performed, the chemicals present in the smoke, and/or as a con- and a 9-mm, low-pressure, cuffed tracheostomy tube sequence of surfactant denaturation (Herndon et al., (Shiley, Mallinckrodt Medical TPI, Irvine, CA) was 1985; Fitzpatrick and Cioffi, 1994; Nieman et al., inserted. The animals were recovered overnight in an 1995). animalintensive-careunit(ICU). Anumberofstudieshavelinkedantioxidants,both endogenousanddietary,asplayingimportantrolesin 2.2. Smokeinhalation preventing lung injury from exposure to various en- vironmental toxicants (Cross et al., 2002; Ho, 2002). The following day, animals were anesthetized In our further characterization of the effects of wood with sodium pentobarbital (25mg/kg i.v.). Once smoke inhalation on antioxidant status, the present general anesthesia was confirmed, a neuromuscu- study evaluated whether indices of an oxidant stress lar blocking agent was given (pancuronium bromide in plasma and lung from sheep exposed to graded 0.03–0.04mg/kgi.v.).Thesedrugswereredosed,and doses of smoke followed a dose-dependent pattern. anintravenousanalgesic(buprenorphine0.005mg/kg) Sheephavelongbeenemployedtoinvestigatesmoke was administered, whenever necessary. All animals inhalation injury. This injury is reproducible, dose remained anesthetized and mechanically ventilated, dependent (Hubbard et al., 1988; Kimura et al., using a pressure control mode, for the remainder of 1988; Shimazu et al., 1996) and mimics that ob- the study (Siemens 900C ventilator, Siemens-Elema, servedinhumans(Traberetal.,1985;Hubbardetal., Solna, Sweden). The animals were fasted, and main- 1991). tenance intravenous fluid (5% dextrose in lactated M.S.Parketal./Toxicology195(2004)97–112 99 Ringer’s solution at 2ml/kgh) was given throughout smoke exposure, similar to other studies of smoke the48-hexperimentalperiod. inhalation in sheep (Sakurai et al., 1999; Tasaki On the day of injury, each animal was randomized et al., 2002), and were moved back to the animal tooneoffourgroupsdescribedbelow.Smokeinhala- ICU,wheretheywerehousedinindividualmetabolic tioninjurywasinducedusingthetechniqueemployed cages.Arterialbloodpressure,heartrate,andperiph- at our Institute over the past 10 years (Ogura et al., eral oxygen saturation were continuously monitored. 1994; Harrington et al., 2001; Tasaki et al., 2002). Arumentubewasplacedfortherestofthestudy. Fifty grams of pine wood bark (Decorative Western Bark, Far West Forests Inc., Tempe, AZ) were cut 2.3. Serumoxidantstressmarkers into1cm2chipsandwereplacedinacruciblefurnace (Lindberg/BlueM laboratory furnace, model 56622, Blood samples were drawn at preinjury, 6, 12, 18, Asheville,NC).Thefiringchamberofthefurnacewas 24,36and48haftersmokeexposureintoheparinized ◦ heatedto400 C.Thechamberwassuppliedwithdes- tubes. The blood was centrifuged in a clinical cen- iccated air at 6.0l/min, to support combustion and to trifuge, and resultant plasma samples were stored at facilitate flow of the smoke from the chamber into a −70◦Cforlessthan3monthsuntilanalyzed.Thiobar- 5.5lPlexiglasmixingboxandreservoir.Thisreservoir bituric acid reactive substances (TBARS), expressed alsoreceived100%oxygenat6l/min,ataratioof1:1, as nanomoles of malondialdehyde per milliliter of to permit the smoke to cool to ambient temperature plasma, were determined in the butanol phase as de- ◦ (approximately25.5 C)toeliminatethermalinjuryto scribed by Naito et al. (1993). Ferric reducing ability the airway, to facilitate mixing, and to minimize hy- of plasma (FRAP), as an index of its antioxidant poxiaintheanimal.Thetemperatureofthesmokewas status, was determined spectrophotometrically by the measuredjustproximaltothetracheostomytubeusing methodofBenzieandStrain(1996). a thermistor-tipped pulmonary-artery catheter. Three minutes after initiation of pyrolysis, the smoke was 2.4. Lungtissueanalysis drawn from the reservoir into a hand-operated piston and was delivered to the animal via its tracheostomy Sheep were euthanatized 48h after smoke expo- using modified ventilator circuit tubing with a man- sure using a standard veterinary euthanasia solution ualbreath-holdvalve.Thetidalvolumeofeachsmoke that provided an overdose of pentobarbital, and lung breathwascontrolledbyanadjustablestoponthepis- parenchymafromrightandleftapical,medialanddi- tonsetat30ml/kg(Shimazuetal.,1987).Oneunitof aphragmaticlobeswerecollectedandstoredat−70◦C smoke was defined as 5 such breaths; each breath in- for later assays. Oxidized and reduced glutathione cluded a 7-s inspiratory hold as previously described weredeterminedspectrophotometricallyusingtheen- (Harrington et al., 2001). Group I (control, n = 5) zymaticassaydescribedbyAnderson(1985).Briefly, received no smoke, group II (mild, n = 5) received total glutathione concentration in 5-sulfosalicylic 5 units of smoke, group III (moderate, n = 5) re- acid-precipitated supernatants was determined by a ceived10units,andgroupIV(severe,n=5)received 5,5(cid:6)-dithiobis(2-nitrobenzoic acid)-glutathione reduc- 16 units. All animals received the same number of tase recycling assay. Oxidized glutathione was deter- piston-driven tidal volumes regardless of the smoke mined by the same assay after reduced glutathione dose over a period of 17min. Based on this regimen, was derivatized by incubating the 5-sulfosalicylic the mild, moderate and severe exposure groups were acid-precipitated supernatants with 2-vinylpyridine subjected to 175, 350 and 560s of smoke dwell time for 1h at room temperature. Reduced glutathione intheairwaysandlungs,respectively.Thecontrolan- concentrations were determined by subtracting the imals received the same number of breaths via the concentration of oxidized glutathione from the total sameapparatus,butwithoutsmoke. concentration (Anderson, 1985). TBARS and FRAP Immediately following smoke exposure, arterial- in lung tissue were determined as described above. blood-gasanalysiswasperformedandthecarboxyhe- Myeloperoxidaseactivitywasdeterminedbyamodi- moglobin(COHb)levelwasmeasuredbycooximetry. fication of the method of Trush et al. (1994). Briefly, Animals were ventilated with 100% O for 2h after tissues were homogenized in 50mM potassium 2 100 M.S.Parketal./Toxicology195(2004)97–112 phosphate buffer pH 6.0 containing 0.5% hexade- croscopicexamination.Histologicgradingoftracheal, cyltrimethylammonium bromide. The homogenates bronchialandpulmonaryinjurywasperformedusing then underwent three freeze–thaw cycles and soni- thepreviouslydescribedscoringsystem(Tasakietal., ◦ fication, followed by incubation at 60 C in a water 1997). The tracheal/bronchial injury score is as fol- bath for 2h to extract myeloperoxidase and reduce lows: interfering substances. Samples were centrifuged at 10,000×g for 30min at 4◦C. Myeloperoxidase ac- Injury Description score tivity was determined in the resultant supernatant using o-dianisidine as substrate. Protein concentra- 0 Normal tionsweredeterminedwithacommercialkit(BioRad 1 Somelossofcilia,and/orapical Laboratories,Richmond,CA). respiratoryepithelium 2 Markedattenuationofpseudostratified 2.5. Exhaledbreathanalysis epitheliumorasinglelayerofepithelium 3 <50%segmental/focalulcerationof Before injury and 6, 12, 18, 24, 36, and 48h af- epithelium ter injury, exhaled nitric oxide (NO) was assayed by 4 >50%ulcerationofepithelium a chemiluminescence method using a Sievers model Parenchymal damage was evaluated at the apical, NOA 280 nitric oxide analyzer (Sievers Instruments, medial and diaphragmatic lobes of both lungs. The Boulder,CO).Basically,exhaledgaswassampledvia pulmonaryinjuryscoreisasfollows: asidestreamportaccordingtothemanufacturer’sstan- dard protocol. Two-point calibration of the analyzer Injury Description wasperformeddaily.BecauseNOwaspresentinvari- score ableconcentrationsininspiredair,animalswereven- 0 Normal tilatedbeforeandduringNOcollectionwithamixture 1 Minimaltomildlythickenedalveolar ofnitrogenandoxygenknowntobefreeofNO. septae,afewinflammatorycellsora At these same timepoints, exhaled breath conden- small,singlefocusofinflammatorycells sate was collected for the measurement of H O . A 2 2 2 Thickenedalveolarseptaewithmultifocal segment of sterile ventilator tubing was connected areasofincreasedinflammatorycells to the existing ventilator circuit, and was submerged 3 Diffuseinflammationand/oredemathat in bucket of dry ice for 40min. The ice precipitate affects<50%ofthesection in the tubing was then collected, placed in a sterile vial, and stored at −70◦C until analysis. Measure- 4 Diffuseinflammationand/oredemathat affects>50%ofthesection ment of H O in expired air condensate was deter- 2 2 minedspectrophotometricallyasdescribedbyGallati Parenchymal samples from right and left lung and Pracht (1985), using horseradish peroxidase were also excised for the determination of blood-free (HRPP)-catalyzed oxidation of tetramethylbenzidine. wet-to-drylungratiousingthemethoddescribedpre- Briefly, 100(cid:1)l of 420(cid:1)M of tetramethylbenzidine viously (Drake et al., 1980) as modified by Ogura and 10(cid:1)l of HRPP were mixed with 100(cid:1)l of ex- et al. (1994). Bilateral apical, medial and diaphrag- pired air condensate. The reaction product was mea- matictissuesampleswereweighedandhomogenized sured spectrophotometrically (Abs 450nm) using an with an identical weight of distilled water. Duplicate automated plate reader. The absorbance is directly samples of the homogenate and venous blood were ◦ proportional to the amount of H O with a detection weighed and dried at 80 C for 48h. Dry weights 2 2 limitofapproximately0.1(cid:1)MH O . were measured and the wet-to-dry ratios of the ho- 2 2 mogenate and blood were calculated. To determine 2.6. Histology the hemoglobin levels in the homogenate and blood, 20(cid:1)l of the homogenate supernatant or the diluted Atthetimeofeuthanasia,sectionsoflungandtra- blood was added to 2.5ml of Drabkin’s solution chea were excised for H&E staining and light mi- and the absorbance of both solutions was measured M.S.Parketal./Toxicology195(2004)97–112 101 spectrophotometrically at 540nm. From these data, Table1 thefractionofbloodinthewetanddrylungsections Effectsofsmokeinhalationinsheeponbloodcarboxyhemoglobin andlungwet:dryweightsa could be calculated and subtracted from the total wet and dry weights. Blood-free wet-to-dry weight ratio Carboxyhemoglobin Lungwet:dryweight wasthencalculatedasdescribed(Drakeetal.,1980). concentrations(%) ratio Control 6.3±0.64 4.5±0.2 Mild 42.3±5.1∗ 5.1±0.3 2.7. Statisticalanalysis Moderate 78.0±8.8∗ 5.5±0.4 Severe 91.9±1.3∗ 6.9±0.3∗ Data analysis employed SPSS v. 10.1 (SPSS, a Data expressed as mean±S.E. for four to five animals per Inc., Chicago, IL). As appropriate, one-way or group.Seetextfordefinitionsofsmokedoses. repeated-measures analysis of variance was per- ∗ P<0.05fromcontrol. formed,withseverityofinjuryasthebetween-groups factor. Post-hoc tests corrected for multiple compar- in the mild group died at 36h, because of airway ob- isons were performed to compare each injured group struction.Therestoftheanimalsliveduntilthecom- to the control group at various time points. Correla- pletionofthe48-hstudy. tions were run within a lobe to determine Pearson Arterial COHb levels measured immediately after correlation coefficients among the doses of smoke smokeinhalationcorrespondedinstepwisefashionto andthevariablesofoxidativestress.AP<0.05was the dose of smoke, showing a significant difference consideredstatisticallysignificant. amonggroups(P<0.001)andbetweeneachinjured groupandthecontrolgroup(P<0.001)(Table1).In 3. Results addition, lung wet:dry weight ratios were correlated tothedoseofsmoke,butonlythehighestsmokedose Twoanimalsintheseveregroupwereeuthanatized resultedinawet:dryweightratiosignificantlyhigher at 29 and 36h, because of terminal pulmonary fail- thancontrols(Table1). ure(inabilitytomaintainaPaO2of60mmHg,despite Plasma protein concentrations were significantly FiO = 100% and PEEP = 15cmH O). One animal lower in the severe smoke exposure group at 24, 36 2 2 Fig. 1. Plasma protein concentrations in smoke-exposed sheep. Data represent mean±S.E. from four to five animals per group. (∗) P<0.05fromcontrols. 102 M.S.Parketal./Toxicology195(2004)97–112 and 48h compared with controls (Fig. 1). Plasma but the differences were not statistically significant protein concentrations in the mild and moderate (Fig. 2). Generally, these values remained elevated smoke-exposedanimalsgenerallyremainedsimilarto throughout the 48-h experimental period, particularly controllevelsthroughouttheexperimentalperiod. in the moderate smoke-exposed group. Overall, the response to smoke inhalation was variable and no 3.1. Serum, breath and tissue oxidative dose-dependent effect of smoke exposure on plasma stressmarkers TBARS concentrations was observed (Fig. 2). At 48haftersmokeexposure,plasmaTBARSwere66% PlasmaTBARSappearedtoriseinanimalsexposed and 69% higher in the moderate and severe smoke tosmokecomparedwithcontrolsat6hafterexposure, exposed groups than controls. In contrast to TBARS Fig.2.Top-PlasmaThiobarbituricacidreactivesubstances(TBARSs)concentrationsinsmoke-exposedsheep.Bottom-Totalantioxidant potential in plasma from smoke-exposed sheep. Data represent mean±S.E. from four to five animals per group. (∗) P < 0.05 from controls. M.S.Parketal./Toxicology195(2004)97–112 103 levels, plasma antioxidant potential was not signif- Inlungtissuespecimenscollected48haftersmoke icantly affected by smoke exposure in any group exposure, a dose-dependent increase in TBARS con- (Fig. 2). Although, plasma antioxidant potential centrations were observed in both left and right was consistently lower in the mild smoke ex- lung lobes (Fig. 3). In all lobes from moderate and posure group compared with the other groups, severe smoke exposed animals, TBARS were sig- the baseline level was also low, suggesting that nificantly higher than controls, with levels about smoke exposure induced no significant effect in this 3- and 4-fold higher than controls (Fig. 3). Lung group. antioxidant potential appeared to be generally af- In addition, expired hydrogen peroxide or NO lev- fected by all doses of smoke, but only the severe els measured in expired air were not significantly groupachievedstatisticalsignificancecomparedwith affected by smoke exposure at any time during the controls, with values 20–25% lower than controls experimentalperiod(datanotshown). (Fig.4). Fig.3.TBARSconcentrationsinlunglobes(apical(upper),medial(middle)anddiaphragmatic(lower))fromsmoke-exposedsheep.Data representmean±S.E.fromfourtofiveanimalspergroup.(∗)P<0.05fromcontrols. 104 M.S.Parketal./Toxicology195(2004)97–112 Fig. 4. Total antioxidant potential in lung lobes from smoke-exposed sheep. Data represent mean±S.E. from four to five animals per group.(∗)P<0.05fromcontrols. Lung GSH concentrations were not consistently moderate and severe smoke exposure. Severe smoke different from controls in any smoke exposed group exposure resulted in 53% higher GSSG levels than (Table 2). Only left medial (middle) GSH concen- controls in right diaphragmatic (lower) lung lobes trations were significantly lower than controls after (Table2).Moderatesmokeexposureresultedinhigher M.S.Parketal./Toxicology195(2004)97–112 105 Table2 Effectsofsmokeinhalationinsheeponlungreduced(GSH)andoxidized(GSSG)glutathioneconcentrationsa Rightapical Rightmedial Rightdiaphragmatic Leftapical Leftmedial Leftdiaphragmatic GSH Control 10.8±1.7 12.8±1.1 12.2±2.2 12.2±1.5 14.1±0.9 9.5±1 Mild 11.8±1.7 11.6±1.1 9.3±0.7 13.2±2 13.9±1.5 14.2±1.2∗ Moderate 13.9±1.7 10.1±1.5 11±0.99 14.8±1.4 9.2±0.9∗ 7.6±0.4 Severe 7.8±0.7 8.6±1.8 10.9±1.54 13.4±1.1 9.8±0.4∗ 10.8±1 GSSG Control 0.63±0.04 0.60±0.16 0.51±0.02 0.60±0.07 0.70±0.05 0.75±0.02 Mild 0.74±0.05 0.58±0.09 0.49±0.03 0.78±0.14 0.98±0.14 0.74±0.11 Moderate 0.91±0.05∗ 0.67±0.12 0.90±0.12∗ 1.08±0.15∗ 0.82±0.11 0.85±0.07 Severe 0.73±0.05 0.95±0.09 1.03±0.11∗ 1.00±0.13 0.83±0.08 0.91±0.12 a Dataexpressedasmean±S.E.nmol/mgproteinforfourtofiveanimalspergroup. ∗ P<0.05fromcontrol. GSSG levels in right diaphragmatic and left apical 4. Discussion (upper)lobescomparedwithcontrols(Table2). Mild and moderate smoke exposure resulted in Thesmokegeneratedfromthepyrolysisofwoodis slightly higher MPO activity in most lung lobes knowntocontainover200compounds,includingcar- compared with controls, although few data achieved bonmonoxide,nitrogenoxides,sulfuroxides,aldehy- statistical significance due to variability in the data des, polycyclic aromatic hydrocarbons and respirable (Fig. 5). In contrast, severe smoke exposure ele- particulate matter (Pierson et al., 1989; Larson and vated MPO activity in apical and medial lung lobes Koenig,1994;Zelikoffetal.,2002).Inaddition,wood compared with controls (Fig. 5). For example, MPO smoke can generate stable carbon-centered radicals activity in the right apical and medial lobes was 19- and hydroxyl radicals (Lachocki et al., 1989; Pryor, and 22-fold higher, respectively, than controls. In 1992; Kou et al., 1997; Leonard et al., 2000). This addition, MPO activity in the right upper lobe was information has generated much interest in determin- significantlycorrelatedwiththedoseofsmoke. ingthehealtheffectsofsubchronicandchronicexpo- sure to individuals exposed to smoke generated from woodburning stoves (Tesfaigzi et al., 2002; Zelikoff 3.2. Histology et al., 2002). The present study, however, focused on theacuteeffectsofwoodsmokeinhalationthatmight Based on the criteria described in the Materials occur in a structural fire (Wong et al., 1984; Barillo and Methods section, a dose-dependent increase in etal.,1994). tracheal injury score was observed in response to In the present study a dose-related rise in blood smoke inhalation, as confirmed by correlation analy- carboxyhemoglobin (COHb) concentrations was ob- sis (Fig. 6). The predominant observations following served immediately after smoke exposure. It is well moderate or severe smoke exposure in trachea, were recognized that carbon monoxide is one of the major loss of cilia, epithelial attenuation, ulceration of res- toxicants of smoke in fires (Alarie, 2002). For exam- piratory mucosa and serocellular/mucocellular cast ple, average blood COHb levels exceeding 50%, and formation. Although correlation analysis also noted sometimes as high as 60–80% have been observed thatlungparenchymalinjuryscoresweredoserelated, in victims of fires and blood COHb levels exceeding onlytheseveresmokeexposureproducedstatistically 50% have often been cited as evidence for carbon higher injury scores compared with controls (Fig. 6). monoxide related deaths in humans (Fitzpatrick and Severe wood smoke exposure resulted in the largest Cioffi,1994;Alarie,2002).Asnoted,however,anum- number of diffusely distributed inflammatory cells, beroffactorscancontributetofire-associateddeaths, andedemainlung,comparedwiththeothergroups. and blood COHb levels can be higher or lower than

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