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A comparison of electronic and traditional cigarette butt leachate on the development of xenopus laevis embryos

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Tiêu đề A comparison of electronic and traditional cigarette butt leachate on the development of Xenopus laevis embryos
Tác giả Tatiana Tatum Parker, James Rayburn
Trường học Saint Xavier University
Chuyên ngành Biological Sciences
Thể loại Research article
Năm xuất bản 2017
Thành phố Chicago
Định dạng
Số trang 6
Dung lượng 581,12 KB

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A comparison of electronic and traditional cigarette butt leachate on the development of Xenopus laevis embryos F A t T a b a A R R 1 A A K C X D t e w U f i C C p w c i m t c h 2 Toxicology Reports 4[.]

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Contents lists available atScienceDirect

j o u r n a l h o m e p a g e :w w w e l s e v i e r c o m / l o c a t e / t o x r e p

Full length article

Tatiana Tatum Parkera,∗, James Rayburnb

a Department of Biological Sciences, Saint Xavier University, 3700 West 103 rd St., Chicago, IL, 60655, United States

b Department of Biology, Jacksonville State University, 700 Pelham Rd N, Jacksonville, AL, 36265, United States

a r t i c l e i n f o

Article history:

Received 19 August 2016

Received in revised form

16 December 2016

Accepted 23 January 2017

Available online 24 January 2017

Keywords:

Cigarette butt leachate

Xenopus laevis

Development

a b s t r a c t

Cigarettebuttsare,collectively,themostcommonformof

lit-terintheworld.Approximately5.6trillioncigarettesaresmoked

everyyearworldwide.IntheUnitedStatesofAmerica,cigarette

wasteconstitutesanestimated30%ofthetotallitter(bycount)on

U.S.shorelines,inwaterways,andonland[1].Thecurrentmethod

formeasuringofhowmanycigarettebuttsarefindingtheirway

intostreams,rivers,andcoastalenvironmentsistheInternational

CoastalCleanupDay,whichis organizedannuallybytheOcean

Conservancy.Theevent involvesmorethan 500,000volunteers

pickingupdebrisfrombeaches,rivers,and streamsaroundthe

world.ThevolunteerscompleteMarineDebrisDataCardsthat

indi-catethequantityandtypeoflittertheypickup.Duringthe2013

internationalcleanup, 2,043,470 cigarette butts were collected,

makingthisthemostcommondebrisitem.Cigarettebuttshave

toppedthelistinallInternationalCoastalCleanupDayssincethat

categorywasaddedtothedatacardsasaseparateitemin1990[2]

∗ Corresponding author.

E-mail address: tatum@sxu.edu (T.T Parker).

Thefiltersinonepackof20cigarettesweigh0.12ounces(with

notobaccoattached)and displacea volumeof10mL.Based on thesefigures,thecigarettebuttscollectedin2013weighed approx-imately 766lbs and displaceda volumeof1022l.Owingtothe ubiquitous natureand magnitude of cigarette butts discharged intotheenvironment,studieshavebeenundertakentodetermine whethercigarettebuttwastecanexertecotoxiceffectsinaquatic environments[3,4].Theenvironmentalimpactof cigarettebutt wasteisrelatedtoboththeirpersistenceintheenvironmentand potentialtoxiceffects[5]andtheirchemicalcomposition− con-tainingover4000differentchemicals[4].Mostofthesechemicals aretoxicandoftenleachintoaquaticecosystems,thereby threaten-ingwatersupplysourcesandaquaticanimals[6,7]suchaswater fleas[3],which inhabitfreshwaterenvironments,andmosquito larvae[8]

Electroniccigarettes(EC)have,sincetheirmarketintroduction

in2004,gainedawideaudience−asof2013,thereareseveral mil-lione-cigaretteusersgloballyMichaelFelberbaum(11June2013) VariousreasonsorfactorshavecontributedtoincreasedECuse; includingtheperceptionthatvapingisasaferorhealthier alterna-tivetosmokingconventional(tobacco)cigarettes.Buttheimpact http://dx.doi.org/10.1016/j.toxrep.2017.01.003

2214-7500/© 2017 Published by Elsevier Ireland Ltd This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).

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Plate 1.Control embryo top left Top right panel is RCBL (2CB/L) and the embryo exhibits minor malformations of head, gut and overall embryonic delayed development The RCBL embryo also exhibited significant tail abnormalities Bottom left is MCBL (0.5 CB/L) and the embryo exhibits severe edema in the heart, craniol-facial, and abdomial areas There are also significant gut and facial abnormalities Bottom Right panel is ECBL at 8 CB/L and the embryo exhibits some tail abnormalities The embryo has moderate

to severe edema, heart and gut abnormalities The embryo also has facial abnormalities as well.

ofECuseontheenvironmentisunknown.ECdeliveraerosolby

heatingaliquidsolutionknownase-liquidthatusuallycontains

nicotine,propyleneglycol,glycerin,andflavorings.TheECcombine

thefluidchamberwithaheatingelement,vaporizingthee-liquid

SinceECdonotreleasesecondhandsmoke,theyaretoutedbysome

asbeingasafealternative,forusersandbystanders,totraditional

(analog)cigarette.Butresearchershave analyzedtheimpurities

inbothe-liquid[9,10,11,12],andthecompositionoftheemitted

vapor[13,14,15,16].Goniewiczetal.[13]measured0.03–0.57␮gof

leadpere-cigaretteinemittedvapor.Williamsetal.[16]found

met-als(e.g.,lead,nickel,andsilver),silicatebeads,andnanoparticlesin

e-cigaretteaerosol.Thereisfarlessdataregardingthe

environmen-talimpactofECdisposal.WhileoneECistypicallyequivalentto40

traditionalcigarettes,greatlyreducingrelatedwastebyproducts,

someresearchhasbeenconductedtodeterminewhetherornotEC

wasteshouldbeclassifiedashazardous[17].KrauseandTownsend

[17]foundthatsomee-cigarettesmaybeclassifiedashazardous

wasteforleadleaching,thoughtheydidobservea largedegree

ofvariabilityamongbrandsandproducts.Theydidstressthatthe

rateofconsumptionanddisposaloftheseproductsisassumedto

behigherthanmanyotherelectronicproducts

Inordertoderivewaterqualityguidelinesorconducthazard

assessments,toxicitydataforanumberofaquaticspeciesisthe

minimumneeded,soitisimportanttodeterminenotonlythe

tox-icityoftraditionalcigarettebuttleachatebutalsothetoxicityof

electroniccigaretterelatedwaste.Inthisstudy,weexaminedacute

toxicity,teratogenicdevelopment,chronicandsublethaleffectsof

cigarettebuttleachateand ECleachateusingFrogEmbryo

Ter-atogenesis Assay− Xenopus(FETAX) FETAX is an inexpensive

alternativetoxicitytestsystemthatcanbeusedtoevaluate

ecolog-icalhazardsfrombothcomplexenvironmentalmixturesandpure

chemicalproducts[18].Thisbioassayisafour-day,whole

embryo-larvaldevelopmentaltoxicityscreeningassaythatusedembryosof

theSouthAfricanclawedfrog,Xenopuslaevis.TheFETAXsystemis

capableofmonitoringacute,chronic,developmental,and

behav-ioraltoxicityforecologicalandhumanhealthhazardassessment

Withover300validationtestcompounds,thepredictiveaccuracy

oftheFETAXmodelwithconventionalmammaliantestsystemsis

approximately85%[19].Thisallowsfortheexaminationofnotonly

acutetoxicity,butteratogenicdevelopmentandchronic,sublethal

effectsongrowth

Thespecificaimofthisstudywastodeterminehowdifferent

electroniccigarettebuttleachate(ECBL)werecomparedto

tradi-tionalcigarettebuttleachateintermsofenvironmental(aquatic)

toxicity,teratogenicityandimpactongrowthtoembryosof

Xeno-puslaevis.WehypothesizedthattheECBLwouldbelesstoxicthan thetraditionalcigarettebuttleachate

Theobjectivesofthisstudyweretodeterminetheacutetocity (96-hLC50and96-h EC50)and lowestobservedeffect concen-tration(includingtheminimumconcentrationtoinhibitgrowth)

ofregularcigarettebutt(RCBL),menthol(MCBL),andelectronic cigarettebuttleachate(ECBL)toXenopuslaevisembryos

l-cysteine, human chorionic gonadotropin (HCG), NaCl, NaHCO3, KCl, CaCl2, CaSO4, and MgSO4 and other laboratory supplies wereobtainedfromtheSigma ChemicalCo., St.Louis,

MO.Othersuppliesincluding60×15plastic Petridishes,10mL disposablepipettes,transferablepipettes,anda1mLsyringewere obtainedfromFisherScientificSupplies,location.Xenopuslaevis frogswereobtainedfromXenopusI,Inc.TheRegularandmenthol cigarettescontained2.8%and2.7%nicotinerespectively,andthe electroniccigarettecartridgescontained2.4%nicotine

1.1 Cigarettebuttcollection,electroniccigarettepurchase,and leachatepreparation

Cigarette butts (CB) were collected from naturally smoked cigarettes,definedascigarettesthatweresmokedbypeople, extin-guishedincigarettedisposalunitsandcollectedwithin24h.The electroniccigaretteswerepurchased,punctured,andthenused dis-cardedcigarettebutts.Weonlytestedonetypeofe-cigarette,as wellasonebrandofregularandmentholcigarette.TheCBwere selectedrandomlyandplacedintocleanplasticbagsfortransport

tothelaboratory.ThecollectedCBwereimmediatelyprocessedas describedbelowforleachateproduction

Cigarettebuttleachates(CBL)weremadebysoaking3buttsin

300mLFETAXsolutionfor1htoproducetheleachatestock solu-tionof10CB/L FETAXsolutionwaspreparedbyadding625mg NaCl,96mgNaHCO3,30mgKCl,15mgCaCl260mgCaSO4*2H2O, and75mgMgSO4perliterdistilledwater[19,20].CBLsweremade freshforRCBL,MCBL,ECBLforeachreplicateexperiment

1.2 Animalcareandbreeding Animalcareandbreedingwasperformedaccordingtothe spec-ificationssetforthintheASTM’sStandardGuideforConducting theFrogEmbryoTeratogenesisAssay-Xenopus[19].Animalcare andusewasperformedinaccordancewiththerequirementsof

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Ciga rett e butt s / Liter

0.0

0.2

0.4

0.6

0.8

1.0

1.2

Mortality Malformation

Cigarett e butts / Liter

0.70 0.75 0.80 0.85 0.90 0.95 1.00 1.05

Fig 1. Representative concentration response graphs for Mortality & Malformation (Right Panel) and Growth (Left Panel) from a single experiment with Regular Cigarette Butt Leachate (RCBL) The Mortality & Malformation indicated an increasing response with concentration of RCBL The growth curve indicated decreasing length with increasing concentration of RCBL Error bars represent standard error.

Table 1

Individual analysis of each replicate experiment with 96-h LC50, EC50(malformation), Teratogenic index (TI), Minimum Concentration to Inhibit Growth (MCIG), Mortality and Malformation LOEC (Lowest Observable Effects Concentration) and NOEC (No Observable Effects Concentration).

CBs = cigarette butts Teratogenic Index (TI) = 96-h LC50/96-h EC50 Numbers in Parenthesis are 95% Fieller Bounds RCBL = Regular Cigarette Butt Leachate, MCBL = Menthol Cigarette Butt Leachate, ECBL = Electronic Cigarette Butt Leachate.

a All first experiments were conducted with the same clutch and all of the second experiments were conducted with the same clutch N.C.= Not Calculable.

theJacksonvilleStateUniversity’sInstitutionofAnimalCareand

UseCommittee.Adultfrogswerekeptinglassaquariumsin

re-circulatedwateratroomtemperature(24±2◦C).A12-hday/12-h

nightcyclewasmaintained.Malesandfemaleswerebredas

sin-glepairs.Breedingwasinducedbyinjectingeachfrogwithhuman

chorionicgonadotropinandplacedinfalsebottombreeding

cham-bers[21].Malesreceived250–500IUofHCG,andfemalesreceived

500–1000IU.Thehormoneconcentrationwas1000IU/mLinsterile

0.9%NaClandinjectedwitha1-mLtuberculinsyringefittedwith

a½inchlong26-gaugeneedle[19]

FETAX procedures were performed according to ASTM’s

Standard Guide for Conducting the Frog Embryo

Teratogene-sis Assay-Xenopus [19] Eggs were collected and immediately

inspected todeterminefertility and quality Thejelly coatwas

removedbyswirlingtheeggsfor 1–3minin 2%w/vl-cysteine

solutionpreparedinFETAXsolution,andpHwasadjustedto8.1

with1NNaOH.Immediatelyafterthejellycoatwasremoved,l

-cysteine wasrinsedoff withFETAXsolution.Healthy,normally

dividingblastulaewereplacedin60×15plasticPetridishes,each

dishcontaining20embryos.Foreachtest,stocksolutionsofCBL

weremadefresh daily.Dead embryoswereremoveddaily and

alivecountwastaken.Attheend ofa four-dayperiod,a final

live/deadcountwastakenandthenumberandtypeofmalformed

wasrecorded.EmbryoswereanesthetizedwithMS222and,then

fixedin3.0%(w/v)formalin.Malformationtypeswerenotedon

theScoresheetofMalformationsat96-hasdescribedintheFETAX

AtlasofAbnormalities[22].Embryoswerephotographedand

mea-sured forlength usingImage Pro plus software.Two definitive

dose-responsetestswereperformed.Thesameclutchwasusedfor

eachofthedefinitive1andasecondclutchwasusedfordefinitive

2forallleachatetypes

1.3 Statisticalanalysis Meansandstandarderrorwerecalculated.The96-hLC50,96-h EC50forindividualandcombinedexperimentsweredetermined usingprobitanalysisbySystat13.TheTeratogenicIndex(TI)was calculatedbydividingthe96-hLC50/96-hEC50.Embryolength, malformation,andmortalitydatawereanalyzedwithANOVA fol-lowedbyBonferroni’st-testformultiplecomparisonstodetermine theMinimumConcentrationtoInhibitGrowth(MCIG),TheNoand LowestObservableEffectsConcentration(NOEC,LOEC)for mortal-ityandmalformation

Theoverallaveragecontrollengthsrangedfrom0.96to1.03cm Thetypicalmalformationsseeninthecontrolsincludedabnormal gutcoiling,slightedema,andsometailandnotochord malforma-tions.Fortheoverallexperiment,56ofthe480controltadpoles exposeddied,yieldinga11.6%mortalityrate.Ofthe424surviving tadpoles,17weremalformedforanoverallmalformationrateof 4.0%

2.1 Regularcigarettebuttleachate(RCBL) The Mortality and Malformation showed a sharp increase concentrationresponse withMortalityandMalformationcurves

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Cigarette butts / Liter

0.0

0.2

0.4

0.6

0.8

1.0

1.2

Mortality Malformation

Cigarette butts / Liter

0.70 0.75 0.80 0.85 0.90 0.95 1.00 1.05

Fig 2.Representative concentration response graphs for Mortality & Malformation (Right Panel) and Growth (Left Panel) from a single experiment with Menthol Cigarette Butt Leachate (MCBL) The Mortality & Malformation indicated an increasing response with concentration of MCBL The growth curve indicated decreasing length with increasing concentration of MCBL Error bars represent standard error.

followingeach other.(Fig.1 LeftPanel).The96-h LC50forthe

twoclutchesofembryosexposedtoRCBLwas0.68–1.65CBs/L.The

96-hEC50forthetwoclutchesofembryosexposedtoRCBLwas

0.34–1.21CBs/L.TheTeratogenicIndex(TI)forthetwoclutcheswas

1.36–1.95CBs/L.TheMinimumConcentration toInhibitGrowth

(MCIG)forRCBLwascalculatedtobe0.25and0.5CBs/L(Table1)

Therewasa sharp direct negativecorrelation betweenembryo

lengthand regular cigarette buttleachate concentration(Fig 1

RightPanel).Thereductioninlengthofcontrolscomparedtothe

highestsurvivingconcentrationwas0.26cm.TheLowestandNo

ObservableEffectsConcentrations(LOEC,NOEC)forMortalitywere

consistentwith 0.5 CBs/L for the LOEC and 0.25 CBs/L for the

NOEC.ForMalformation,theNOECwasmorevariableduetoclutch

differences.DominantmalformationsforRCBwereloosegut

coil-ing,facialmalformations,notochordmalformations,andstunting

(PhotoPlate1,TopRightPanel)

2.2 MentholCigaretteButtLeachate(MCBL)

TheMortalityandMalformationshowedanincrease

concen-trationresponsewithadistinctseparation ofthemortalityand

malformation curves (Fig.2 left panel) The 96-h LC50 for the

twoclutches of embryoswasconsistentat just over1.078 and

1.140CBs/Lindicatinggoodagreementbetweenthetworeplicated

experiments.Butthe96-hEC50showedalittlemorevariability

between0.3–0.96CBs/L.Itisthedifferencesinthe96-hEC50that

accountfortheTIbeingfrom1.43to3.77.The MCIGwas

con-sistentat0.5CBs/L.Therewasa sharpdramaticdirectnegative

correlationbetweenembryolengthandMCBL(Fig.2rightpanel)

Thereductioninlengthofcontrolscomparedtothehighest

surviv-ingconcentrationwas0.21cm.Thegrowthreductionwas0.20cm

forthehighestsurvivingconcentrations.Themalformation

end-pointwasthe mostsensitivewiththeLOECbeing0.25 to<0.1

CBs/L.Themalformations seenwithMCBLweremostdramatic Therewassignificantconsistentedema,gut,heart,andcraniofacial abnormalities(PhotoPlate1bottomleftpanel)

2.3 ElectronicCigaretteButtLeachate(ECBL) TheMortalityandMalformationshowedauniqueconcentration responsewithmortalityandmalformationcurvesoverlappingfor mostoftheconcentration(Fig.3leftpanel).Therewasonepoint

at0.5CBs/Lthatshowedadramaticdropinembryolength; how-ever,itwasnotconsistentwithotherconcentrationstested.The 96-hLC50indicatedalowtoxicitywith9.7and26.8CBs/L.The twoexperimentsweredifferentwiththesecondshowingmuch lesttoxicitythanthefirst.Neitherexperimentyieldedmany mal-formationsatallconcentrationstested.TheTIoftheexperiment indicatedwidelydifferentnumbersof0.47–1.72duetothechange

inthe96-hLC50ofExperiment2.TheMCIGwasrightatthe high-estconcentrationtestedof10CBs/Lorhigher.Embryogrowthwas negativelyimpacted;however,thegrowthcurvehadamuchmore gradualslope(Fig.3rightpanel).Thereductioninlengthofcontrols comparedtothehighestsurvivingconcentrationwasonly0.05cm ThemalformationsseenwithECBLwereslightedema,loosegut coiling,andsometailabnormalities(PhotoPlate 1bottomright panel).Thesemalformationsweremoderatetoseverewhenthey occurred

Thisresearchindicatestheoverall96-hLC50ofRCBLandMCBL was1.2and1.14CBs/Lrespectively(Table2).Theoverall96-hEC50 (malformation)ofRCBLandMCBLwas0.90and0.50CBs/L(Table2)

Itwouldbeexpectedthatembryoswithmalformationswouldnot surviveintheenvironment.Thesevaluesarewithintherangeof

Table 2

Overall summary analysis of Regular Cigarette Butt Leachate (RCBL), Menthol Cigarette Butt Leachate (MCBL), and Electronic Cigarette Butt Leachate (ECBL) with the 96-h LC50, EC50 (malformation), Teratogenic index (TI), Minimum Concentration to Inhibit Growth (MCIG), Mortality and Malformation LOEC (Lowest Observable Effects Concentration) and NOEC (No Observable Effects Concentration).

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Ciga rett e butt s / Liter

0.0

0.1

0.2

0.3

0.4

0.5

0.6

Mortality Malformation

Cigarett e butts / Liter

0.86 0.88 0.90 0.92 0.94 0.96 0.98 1.00 1.02 1.04

Table 3

Ceriodaphnia cf dubia 0.06–1.7 CBs/L LC 50 [23]

Ceriodaphnia cf dubia 0.03–0.08 CBs/L EC50 [24]

Vibrio fisheri 0.58–1.25 CBs/L LC50 [23]

Vibrio fisheri 0.3–2.7 CBs/L EC50 [24]

previouslytestedaquaticspecies(Table3).Thisdemonstratingthat

Xenopuslaevisembryosaregoodindicatorsoftoxicityassociated

withcigarettebuttleachate.Inaddition,theFETAXassayshowed

muchlowerCBs/LforotherendpointsmeasuredsuchasMCIGof

0.01and0.25CBs/L(Table2)

3.1 ImpactofRCBLandMCBL

TheRCBLandMCBLhadanoverall TIof 1.33–2.28(Table2)

indicatingthatthereissometeratogenicriskassociatedwiththe

leachatewith MCBLhaving morerisk This would beexpected

becausenicotineisknowntobehighlyteratogenicintheFETAX

assay[25].ThisindicatesthattheCBLareapotentialteratogenic

hazardtoaquaticlifeinrivers,streams,andlakesand[agreeswith]

isconsistentwithdatafromLeeandLee[26].TheMCBLindicates

ahigherriskduetoeitherthementholpresentorpossibly

inter-actionsoftheadditiveswiththenicotineandotherproductsfrom

smokingcigarettes.Anotherpossibilityisthattheadditives

some-howaddedtheabilityofnicotineandotherproductstoleavethe

cigarettes.ThisdoesnotsupportthestatementbySlaughteretal

[4]that“Thereisnoresearchtosupportthatflavoredcigarettes(eg,

menthol)altertoxicityorimpartadditionaltoxicity.”Althoughthe

overalltoxicitydifferencesarenotlargetheimpacton

malforma-tionswassignificant

TheECBL wasmuch lesstoxic withanoverall 96-h LC50of

14.6CBs/L(Table2)indicatingthattheECBLwasatleast10fold

lesstoxicthantheregularcigarettebutts.Surprisingly,the96-h

EC50(malformation)wasevenhigherat16.3CBs/L.Theoverall

ter-atogenicindexwas0.90indicatingtherewasalsolittleteratogenic

risk.BecausetheECBLwouldbeexpectedtocontainnicotine,this

mightmeanthatECBsmightnotallowthenicotinetobe

bioavail-ableorsomeothermechanismsareinplacetopreventexcessive

nicotineexposuretotheenvironment.Therewasmuchlesseffect

ongrowthasindicatedbytheveryhighMCIGcomparedtothe

traditionalcigarettebutts

Electroniccigarettesareapproximately10foldlesstoxic Xeno-pus embryosthan traditional cigarettes Thisindicates that the impactofdiscardedECBonaquaticenvironmentswould poten-tiallybelessthanthatoftraditionalcigarettebutts.Theimpactis furtherminimizedbythefactthat1ECBisequivalentto approx-imately40traditionalcigarettes[17].Theaquaticenvironmental impactofECBsthuscouldbepotentially400timeslessthanthat

oftraditionalcigarettes.Themethodsthatwereusedinthisstudy, however,wereonlya1hsoaking/mixingtimewithECBthathad notbeenphysicallydamagedastheymightbeinalandfill.This datawouldalsonotincludepotentialimpactsbylong-termmetal erosionorbatterdegradationintotheaquaticenvironmentamong otherfactors.Thepurposeofthispaperwastoexaminewhatwould leakoutofeasilydiscardedcigarettebutts,andnotonmore elab-orateelectroniccigaretteswithrefillablecartridges.Thepathways

ofthiscigarettewastetoaquaticenvironmentsarecomplexand varied,andthatmakescorrelationstoriskdifficulttostudyand determine[4]

FETAXproved tobea useful testing assayfor cigarettebutt leachateandisviableforfurthertesting.Becausetraditional men-tholcigarettesresultedindifferentresultsthanregularcigarettes, especially with regards to gross malformations, future studies shouldexaminementholatedcigarettesinmoredetail.Inaddition, longersoaking/mixing times,as wellas testing the liquid con-tentsofrefillablee-cigarettes(flavoredandnon-flavored),should

beassessed

Acknowledgement

Wewould liketothankJacksonvilleStateUniversityBiology Departmentforsupportofthisproject

References

[1] H Moriwaki, S Kitajima, K Katahira, Waste on the roadside, ‘poi-sute’ waste: its distribution and elution potential of pollutants into environment, Waste Manage 29 (3) (2009) 1192–1197.

[2] Ocean Concervancy, Marine Debris: More than An Eye Sore, Ocean Concervancy, Washington, D.C, 2014.

[3] Kathleen Register, Cigarette butts as litter-toxic as well as ugly? Underwater Naturalist, Bull Am Littoral Soc 25 (2) (2000) 23–29.

[4] E Slaughter, R.M Gersberg, K Watanabe, J Rudolph, C Stransky, T.E Novotny, Toxicity of cigarette butts, and their chemical components, to marine and freshwater fish, Tob Control 20 (1) (2011) 25–29.

[5] Lee, Joyce, Get your butt off the ground! Consequences of cigarette waste and litter reducing methods Pomona: Pomona Senior Theses, 2012, 44.

Trang 6

[6] T.E Novotny, K Lum, E Smith, V Wang, R Barnes, Cigarettes Butts and the

Case for an Environmental Policy on Hazardous Cigarette Waste, Int J.

Environ Res Public Health 5 (2009) 1691–1705.

[7] Novotny, Thomas E., Sarah N Hardin, Lynn R Hovda, Dale J Novotny, Mary

Kay McLean, Safdar Khan Tobacco and cigarette butt consumption in humand

and animals Tobacco Control, 20 (2011) 17–20.

[8] H Dieng, et al., Indirect effects of cigarette butt waste on the dengue vector

Ades aegypti (Diptera: Culicidae), Acta Trop 130 (2013) 123–130.

[9] V Bahl, S Lin, N Xu, B Davis, Y Wang, P Talbot, Comparison of electronic

cigarette refill fluid cytotoxicity using embryonic and adult models, Reprod.

Toxicol 34 (2012) 529–537.

[10] J.F Etter, E Z ¨ather, S Svensson, Analysis of refill liquids for electronic

cigarettes, Addiction 108 (2013) 1671–1679.

[11] M.L Trehy, et al., Analysis of electronic cigarette cartridges, refill solutions,

and smoke for nicotine and nicotine related impurities, J Liq Chromatogr.

Relat Technol 32 (2011) 1442–1446.

[12] M Bradley Drummond, Dona Upson, Electronic cigarettes potential harms

and benefits, Ann Am Thorac Soc 11 (2) (2014) 236–242.

[13] M.L Goniewicz, et al., Levels of selected carcinogens and toxicants in vapour

from electronic cigarettes, Tob Control 23 (2014) 133–139.

[14] B.J Ingebrethsen, S.K Cole, S.L Alderman, Electronic cigarette aerosol particle

size distribution measurements, Inhal Toxicol 24 (2012) 976–984.

[15] T.R McAuley, P.K Hopke, J Zhao, S Babaian, Comparison of the effects of

e-cigarette vapor and cigarette smoke on indoor air quality, Inhal Toxicol 24

(2012) 850–857.

[16] Monique Williams, Amanda Villarreal, Krassimir Bozhilov, Sabrina Lin, Prue

Talbot, Prue talbot metal and silicate particles including nanoparticles are

present in electronic cigarette cartomizer fluid and aerosol, PLoS One 8 (3)

(2013) e57987.

[17] Max J Krause, Timothy G Townsend, Hazardous waste status of discarded

electronic cigarettes Waste Management, vol 39, Elsevier, 2015, pp 57–62.

[18] John A Bantle, Douglas J Fort, James R Rayburn, D.J DeYoung, Shirley J Bush, Futher validation of FETAX: evaluation of the developmental toxicity of five known mammalian teratogens and non-teratogens, Drug Chem Toxicol 13 (4) (1990) 267–282.

[19] Bantle, John A., T D Sabourin, Standard Guide for Conducting the Frog Embryo Teratogenesis Assay-Xenopus (FETAX) American Society for Testing and Materials (ASTM) E1439-91 (ASTM International) 11.06 (1991), 1–11 [20] D.A Dawson, J.A Bantle, Development of a reconstituted water medium and initial validation of FETAX, J Appl Toxicol 7 (1987) 237–244.

[21] Malcolm McCallum, James Rayburn, A simple method for housing Xenopus during oviposition and obtianing eggs for use in FETAX, Herpetolog Rev 37 (3) (2006) 332.

[22] John A Bantle, James N James, Robert A Finch, Gregory Linder, Atlas of Abnormalities: A Guide for The Performance of FETAX, Oklahoma State University Press, Stillwater, OK, 1991.

[23] M.St.J Warne, R.W Patra, B Cole, Toxicity and a Hazard Assessment of Cigarette Butts to Aquatic Organisms Interact 2002-Programme and Abstract Book Sydney: The Royal Australian Society Chemical Institute, The Australasian Society of Ecotoxicology and The International Chemometrics Society, 2002, pp 192.

[24] T Micevska, M.S Warne, F Pablo, R Patra, Variation in, and causes of, toxicity

of cigarette butts to a cladoceran and microtox, Arch Environ Contam Toxicol 50 (2) (2006) 205–212.

[25] Douglas A Dawson, Douglas J Fort, John A Newel, Evaluation of the developmental toxicity of nicotine and cotinine with frog embryo teratogenesis assay: xenopus, Teratog Carcinog Mutagen (1988) 329–338 [26] Wenjau Lee, Chih Chun Lee, Developmental toxicity of cigarette butts – An underdeveloped issue, Ecotoxicol Environ Saf (Elsevier) 113 (2015) 362–368.

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