Ozone Depletes Tocopherol

Embed Size (px)

Citation preview

  • 7/29/2019 Ozone Depletes Tocopherol

    1/4

    FEBS 18069 FEBS Letters 401 (1997) 167-170

    Ozone depletes tocopherols and tocotrienols topically appliedto murine skinJens J. Thielea, Maret G. Trabera, Maurizio Podda l a , Kenneth Tsanga, Carroll E. Crossb,Lester Packer1'*

    ^Department of Molecular an d Cell Biology, 251 LSA, University of California, Berkeley, CA 94720-3200, USAhDepartment of Medicine and Physiology, University of California School of Medicine, Davis, CA, USAReceived 6 December 1996

    Abstract To evaluate ozone damage to hairless mouse skin, twoparameters of oxidative damage, vitamin E depletion andmalondialdehyde (MDA) production, were measured in vitaminE-enriched and in control skin from mice exposed to ozone (10ppm). A 5% vitamin E solution (tocotrienol-rich fraction, TRF)in polyethylene glycol (PEG) was applied to 2 sites on the backof hairless mice, PEG to 2 sites. After 2 h, the sites were washed,one of each pair of sites covered and the mice exposed ozone for2 h. Ozone exposure (compared with covered sites) increasedepidermal MDA in PEG-treated sites, while vitamin E wasunchanged. In contrast, ozone exposure significantly depletedvitamin E in TRF-treated sites, while significant MDAaccumulation was prevented. This is the first demonstration thatozone exposure causes damage to cutaneous lipids, an effectwhich can be attenuated by vitamin E application.Key words: Hairless mice; Vitamin E; Antioxidant;Malondialdehyde; Epidermis; Cutaneous l ipid

    1. IntroductionOzone is the major air pollutant in photochemical smog.Since half the US population lives in areas exceeding the USNational Ambient Air Quality Standard (0.12 ppm averagedover a 1 h period ) [1], the presence of oz one in the air po sessignificant concern [2].Ozone exposure causes oxidation and peroxidation of bio-molecules both directly and/or via secondary products ofozone reactions [3-8]. One of the most important mechanismsof ozone injury is peroxidation of lipids, especially unsatu-rated fatty acids [5,7,8]; in vitro, vitamin E appears to preventthe prop agation of this reaction [6]. Altho ugh cc-tocopherolhas the highest biologic activity of the various vitamin E iso-mers [9], the properties of some of the other isomers suggest

    that they might be more protective against ozone-induceddamage. For example, a-tocotrienol has a higher antioxida-tive activity than oc-tocopherol against Fe 2 + /ascorbate andF e 2 + /NADPH-induced l ipid peroxidation in rat l iver micro-

    *Corresponding author. Fax: (1) (510) 642-8313.^Present address: Zentrum der Dermatologie, Klinikum der J.W.Goethe Universit t, Theodor-Stern-Kai 7, 60590 Frankfurt am Main,Germany.Abbreviations: BHT, butylated hydroxytoluene; EDTA, ethylenediamine tetraacetic acid; HPLC-EC, high pressure liquid chromatog-raphy with electrochemical detection; PEG, polyethylene glycol-400;TRF, tocotrienol-rich palm oil fraction

    somes [10]. Alternatively, ozon e might attack the c hrom anolnucleus of - tocotr ienol or - tocopherol in an analogous m anner to that described for nitrogen dioxide [11].Skin is the organ the most directly exposed to ozone. Infact, ozone is probably the most reactive environmental pollutant to which skin is routinely exposed. Unlike the lung [4],very little attention has been paid to the potential effects ofenvironmental oxidant pollutants on cutaneous t issues. This issomewhat surprising since skin contains peroxidizable lipidsand these constituents are in part responsible for the cutaneous permeability barrier [12].A variety of enzymatic and non-enzymatic antioxidantsprotect skin against oxidative stress [13-17]. Among these isvitamin E. Of the vitamin E isomers, skin -tocopherol concentrations are much higher than -tocopherol or a- a n d -tocotrienols [18]. However, skin can be enriched by topicalapplication of these vitamin E isomers [19].This study tested the hypotheses that (1) ozone attacks skinlipids and lipophilic antioxidants and (2) topical applicationof a mixture of vitamin E forms, including tocopherols andtocotrienols from a tocotrienol-rich palm oil fraction (TRF),

    ameliorates this oxidative damage.2. Materials and methods2.1. ChemicalsAll chemicals used were of the highest grade available. Tocopherolstandards were provided by Henkel Corporation (LaGrange, IL).TRF was kindly provided by PORIM (Kuala Lumpur, Malaysia).Tocotrienols for use as standards were purified from TRF by Dr.Asaf A. Qureshi, University of Wisconsin (Madison, WI). TRF vitamin E are extracted from palm oil and so are in the 'natural' configuration - both a- and -tocopherols have 2R, 4'R, 8'R-stereochem-istry; b oth ot- and -tocotrienols have 2R stereochemistry.2.2. Animals

    Animal care, handling, and experimental procedures were carriedout as described in the animal use protocol approved by the AnimalCare and Use Committee of the University of California, Berkeley,CA. Hairless mice (females, between 8 and 10 weeks old, CharlesRiver Laboratories, Wilmington, MA, USA) were housed understandard light and temperature conditions. Food (Harlan TeckladRodent Diet #1846, Madison, WI, USA) and water were providedad libitum. Mice were anesthetized by an intraperitoneal injection ofsodium pentobarbital (50 mg/kg body weight, Nembutal, AbbottLaboratories, North Chicago, IL) and remained anesthetized duringthe entire experimental period.2.3. Vitamin E applicationA 5% w/v solution of T RF was prepared in polyethylene glycol-400(PEG; Sigma, St. Louis, MO). Mice were anesthetized, then 4 polypropylene plastic rings (1 cm2) were glued onto the animals' backs,subsequently TR F solution (20 ) was applied to 2 rings and PEG tothe other 2 rings. After 2 h, the treated areas were washed as de-

    0014-5793/97/S17.00 1997 Federation of Euro pean Biochemical Societies. All rights reserved.P / / S 0 0 1 4 - 5 7 9 3 ( 9 6 )0 1 4 6 3 - 9

  • 7/29/2019 Ozone Depletes Tocopherol

    2/4

    168 J.J. Thiele et allFEBS Letters 401 (1997) 167-170scribed by Dupuis et al. [20]. Briefly, the skin was rinsed 3 times with300 ethano l:water (9 5:5), then twice with water alone and driedwith a cotton tip. After washing, the location of the application sitewas marked and the plastic rings removed; half of the sites werecovered with a piece of Kimwipe tissue (Kimberly Clarke, Atlanta,GA) and sealed with cellophane tape. The Kimwipe prevented injuryto the skin during the removal of the adhesive tape following exposureto either air (n = 3, control) or ozone (n = 4) (see below).2.4. Ozone exposureOzone was produced from oxygen by electric discharge (Sanderozonizer model IV, Eltze, Germany). The ozone was then mixedwithfiltered ozone-free) am bient air and allowed to flow into a stainless steel exposure chamber at a constant rate (200 1/min). The concentration in the exposure chamber was adjusted to 10 ppm andcontinuously monitored with an ozone analyzer (Dasibi model 1003-AH, Glendale, CA). The ozone chamber provided a maximum spacefor 4 animals during the 2 h ozone exposure. Control mice weretreated identically in terms of anesthesia and animal handling, butwere kept under air (0 ppm ozone).After air or ozone exposure, the mice were given another dose ofpentobarbital, allowed to rest for 30 min, then were killed by cervicaldislocation. The skin was excised, the subcutaneous fat removed witha scalpel, then punch biopsies were taken and the samples immediately frozen in liquid nitrogen. The skin samples were stored for nolonger than a week at 80C.2.5. Vitamin E analysisTocopherols and tocotrienols were extracted from full thicknessskin, as described [21,22]. Briefly, the skin sample was weighed (approximately 20 mg), ground under liquid nitrogen, then homogenizedin a Potter-Elvehjem homogenizing tube with 2 ml buffer (10 mMphosphate, 130 mM NaCl, 1 mM EDTA, pH 7.0) and 50 ml BHT(1 mg/ml) and extracted after addition of 1 ml of 0.1 M SDS, 2 mlethanol and 2 ml hexane. An appropriate aliquot of hexane was usedfor HPLC analysis, as described [23]. The electrochemical detectorwas operated with a 0.5 V potential, full recorder scale at 50 nAfor quantitation of a- and -tocopherols and a- and -tocotrienols.Authentic compounds were used to generate standard curves.2.6. LipidperoxidationFluorimetric detection of the malondialdehyde-thiobarbituric acidadduct (MDA-TBA) was performed after HPLC separation of theTBA-reactive substances, based on methods for MDA determinationin plasma and other body tissues [19-21]. After weighing, the scrapedmouse epidermis was extracted with 2 ml methanol, 2 ml 15% SDSsolution, 50 10% BHT in ethanol and 4 ml chloroform. An aliquotof the chloroform was dried and the residue resuspended in 400 15% SDS and incubated w ith 250 0.375% TBA and 200 1.22 Mphosphoric acid for 30 min at 100C, followed by addition of 380 methanol and 20 1 N N aOH . After centrifugation, 100 supernatant were injected into the HPLC system, which consisted of a 114M Solvent Delivery Module pump (Beckman, Fullerton, CA), anAlltima C18 column and a Hitachi (Hitachi Ltd. Tokyo, Japan) F-105fluorescencespectrophotometer (excitation 532 nm and emission553 nm). The mobile phase consisted of 60% methanol and 40% 50mM NaH 2P0 4 , pH adjusted to 5.5, at a rate of 0.9 ml/min. MDAstandards (ranging from 0.5 to 10 pmol) were prepared using dilutionsof 1,1,3,3-tetramethoxypropane. Samples and stand ards were analyzed in duplicate.2.7. Statistical analysisAll statistical analyses were carried out using SuperAnova (AbacusConcepts, Inc., Berkeley, CA) for the Macintosh (Apple Computers,Cupertino, CA). Analyses included: one-factor ANOVA (air vs.ozone); two-factor ANOVA with 2 within groups repeated measures

    (PEG vs. TRF, and covered vs. exposed) with least square meanscomparisons. Data were log-transformed to equalize variances between TR F- and PEG-treated sites. A P-value < 0.05 was consideredstatistically significant. Values are given as means S.D.

    3 . Results

    3.1. Antioxidants in murin e skinTo investigate the susceptibility of skin to ozone damage, astudy design was planned using covered and uncovered skinsites, such that each animal would serve as its own control.Therefore, we first evaluated whether covering the skinchanged the antioxidant composition. PEG was applied to 2sites and TRF to 2 si tes, the compounds were allowed topenetrate for 2 h, then the skin was washed. Subsequently,half of the sites were covered with tissue paper and sealed withcellophane tape for 2 h during which time the mice were exposed to air. Tocopherols and tocotrienols in PEG-treated air-exposed skin were within the range of previous reports fromour laboratory [19,24], while covering the skin significantlyincreased vitamin E contents (Table 1). TRF treatment resulted in significant increases in the concentrations of all vitamin E forms, as reporte d previously [19]. How ever, coveringthe TRF-treated sites resulted in significantly lower concentrations of vitamin E than in the uncovered sites.

    To evaluate whether the various vitamin E forms penetrated murine skin differently, the percentage distribution ofeach of the vitamin E homologues in the TRF suspension wascompared to i ts percentage distribution in skin treated withTRF or vehicle (PEG) alone (Fig. 1). The percentage distribution of vitamin E forms that penetrated the skin (above background concentrations) was significantly different from theirdistribution in the TRF suspension - a higher percentage of - tocopherol was found in TRF-t rea ted skin than was presentin TRF suspens ion (P

  • 7/29/2019 Ozone Depletes Tocopherol

    3/4

    J.J. Thiele et allFEBS Letters 401 (1997) 167-170 169

    Fig. 1. Vitamin E distribution. The percent of each of the vitamin Eforms found in PEG-treated skin, in TRF-treated skin and in theTRF suspension are shown. The TRF-treated skin contained a significantly higher percentage of -tocopherol (P

  • 7/29/2019 Ozone Depletes Tocopherol

    4/4

    170 J.J. Thiele et allFEBS Letters 401 (1997) 167-17020

    1 6-= 1 2 -< z

    E 8 -

    H T EG - PEG- TRF- TRF-covered exposed covered exposedFig. 3 . MDA in murine skin. The MDA concentrat ions(mean S.D.) in mou se epidermis following application w ith P EGor TRF, covered or not, and exposed to ozone (n = 4) . Only PEGtreatment followed by ozone exposure significantly increased MDA( P < 0 . 0 1 ) .

    c o n t a i n e d lower v i t a mi n E c o n c e n t r a t i o n s t h a n a i r - e x p o s e dsk in (Tab le 1 ) . Th e f ind ing th a t cove r in g the sk in ch ang edi t s a n t i o x i d a n t c o m p o s i t i o n wa s u n e x p e c t e d . M o s t l i k e ly , c o v e r ing the sk in occ lude d i t, i nc reas in g it s m o is tu re con ten t , a ndc h a n g i n g i t s p e n e t r a t i o n c h a r a c t e r i s t i c s [ 27 ] . No n e t h e l e s s , t h es k i n v i t a mi n E c h a n g e s o b s e r v e d d i d n o t a l t e r t h e c o n c l u s i o n so f t h e s t u d y .

    T h e o z o n e c o n c e n t r a t i o n ( 1 0 p p m ) u s e d in t h i s s t u d y , g i v e nfo r a longe r exposure t ime , causes l e tha l damage to the r e s p i r a t o r y s y s t e m. I n u r b a n a i r p o l l u t i o n , l o we r o z o n e c o n c e n t r a t i o n s ( 0 . 1 - 0 . 8 p p m ) a r e e n c o u n t e r e d [ 4 ]. S i n c e n o o t h e rd a t a c o n c e r n i n g c u t a n e o u s e f f e c t s o f o z o n e e x p o s u r e a r e a v a i l a b l e , the p resen t s tudy was des igned to a s sess r e sponses toh i g h l e v e l s o f o z o n e e x p o s u r e . F u r t h e r i n v e s t i g a t i o n s a r en o w n e e d e d t o e v a l u a t e wh e t h e r s i mi l a r b u t l es s ma r k e d m o l e c u l a r s k i n d a ma g e t a k e s p l a c e a t l o we r , mo r e r e l e v a n t o z o n ec o n c e n t r a t i o n s a n d wh e r e t h i s d a m a g e o c c u r s . T h i s m o s tl i k e l y wo u l d r e q u i r e c h r o n i c o r i n t e r mi t t e n t e x p o s u r e s a n d /o r mor e sens i t ive t ech n iqu es to d i f f e ren t i a t e and ana l yze theu p p e r m o s t e p i d e r m a l s k i n l a y e r s , i n p a r t i c u l a r t h e s t r a t u mc o r n e u m .

    In sum m ary , the ma jo r f ind ing o f th i s s tudy was tha t to p i c a l l y a p p l i e d v i t a mi n E f o r ms a r e d r a ma t i c a l l y d e p l e t e d b ya c u t e , s h o r t - t e r m e x p o s u r e t o o z o n e . T h i s is t h e f ir s t r e p o r ts h o w i n g t h a t o z o n e i s c a p a b l e o f in i t i a t i n g o x i d a t i v e p r o c e s s e si n c u t a n e o u s t i s s u e s . W h e t h e r o z o n e - r e l a t e d o x i d a t i v e s t r e s scon t r ibu te s to sk in d i so rde r s a s a r e su l t o f l i f e t ime exposurer e ma i n s t o b e d e t e r mi n e d .Acknowledgements: Nathalie Espuno provided excellent technical assistance. We gratefully acknowledge the efforts of Dr. Asaf A. Qure-shi, University of Wisconsin (Madison, WI), who isolated tocotrienols

    for use as standards for this study. This study was supported in partby NIH Grant HL47628, gifts from the Colgate Palmolive and thePalm Oil Research Institute of Malaysia. J.T. was supported by afellowship of the Fritz Thyssen Stiftung, Germany (AZ 21295008).References

    [1] Office of Technology and Assessment (1989) U.S. GovernmentPrinting Office, Washington, DC.[2] Lippmann, M. (1989) J. Abnorm. Psychol. 39, 672-695.[3] Menzel, D.B. (1984) J. Toxicol. Environ. Health 13, 183-204.[4] Mustafa, M.G. (1990) Free Radical Biol. Med. 9, 245-265.[5] Pryor, W.A. and Church, D.F. (1991) Free Radical Biol. Med.11 ,41^16 .[6] Pryor, W.A. (1991) Am. J. Clin. Nutr. 53, 702-722.[7] Cross, C.E., Motchnik, P.A., Bruener, B.A., Jones, D.A., Kaur,Ft., Ames, B.N. and Halliwell, B. (1992) FEBS Lett. 298, 269-272.[8] Pryor, W.A ., Squadrito , G.L. and Fried ma n, M . (1995) FreeRadical Biol. Med. 19, 935-941 .[9] Traber, M.G. and Sies, H. (1996) Annu. Rev. Nutr. 16, 321-347.[10] Serbinova, E., Kagan, V., Han, D. and Packer, L. (1991) FreeRadical Bio.l Med. 10, 263-27 5.[11] Cooney, R.W., France, A.A., Harwood, P.J . , Hatch-Pigot t , V.,Custer, L.J. and Mordan, L.J. (1993) Proc. Natl. Acad. Sei. USA90 , 1771-1775.[12] Elias, P.M. and Feingold, K.R. (1992) Semin. Dermatol. 11, 176-82 .[13] Shindo, Y., Witt, E., Han, D., Epstein, W. and Packer, L. (1994)J. Invest. Dermatol. 102, 122-124.[14] Shindo, Y., Witt, E., Han, D. and Packer, L. (1994) J Invest.Derm atol . 102, 470-475.[15] Shindo, Y., Witt, E., Han, D., Tzeng, B., Aziz, T., Nguyen, L.and Packer , L. (1994) Photoderm. Photoim munol . Photomed . 10,183-191.[16] Fuchs, J., Mehlhorn, R.J. and Packer, L. (1989) J. Invest. Dermatol . 93, 633-640.[17] Fuchs, J., Huflejt, M.E., Rothfuss, L.M., Wilson, D.S., Carcamo,G. and P acker, L. (1989) J. Invest. Derm atol. 93, 769-77 3.[18] Podd a, M., Weber, C , Tra ber, M . and Packer, L. (1996) J. LipidRes. 37, 893-901.

    [19] Webe r, C , Pod da, M., Rallis, M., Traber, M .G . and Packer, L.(1996) Free Radical Biol. Med. (in press).[20] Dupuis, D., Rougier, A., Roguet, R., Lotte, C. and Kalopissis,G. (1984) J. Invest. Dermatol. 82, 353-356.[21] Burton, G.W., Webb, A. and Ingold, K.U. (1985) Lipids 20, 29-39 .[22] Lang, J.K., Gohil, K. and Packer, L. (1986) Anal. Biochem. 157,106-116.[23] Podd a, M., Web er, C , T raber, M .G . and Packer, L. (1996)J. Lipid Res. 37, 893-901 .[24] Shindo, Y., Witt, E. and Packer, L. (1993) J. Invest. Dermatol.100, 260-265.[25] Pryor, W.A. (1992) Free Radical Biol. Med. 12, 83-88.[26] Frei, B., Stocker, R. and Ames, B.N. (1988) Proc. Natl. Acad.Sei USA 85, 9748-9752.[27] Shaw, J.E., Prevo, M., R, G. and Yum, S.I. (1991) in: Physiology, Biochemistry, and Molecular Biology of the Skin (L.A.Goldsmith, Ed.) Oxford University Press, New York.