三-（2,3-二溴丙基）異氰脲酸酯對大鼠肝毒性的線粒體途徑作用機(jī)制

三-（2,3-二溴丙基）異氰脲酸酯對大鼠肝毒性的線粒體途徑作用機(jī)制摘要：本文研究了三-(2,3-二溴丙基)異氰脲酸酯對大鼠肝毒性的線粒體途徑作用機(jī)制。采用大鼠體內(nèi)實(shí)驗(yàn)觀察了不同劑量的三-(2,3-二溴丙基)異氰脲酸酯對肝臟損傷的影響，并使用熒光染色和電子顯微鏡觀察了線粒體的形態(tài)和數(shù)量變化。結(jié)果顯示，三-(2,3-二溴丙基)異氰脲酸酯劑量依賴性地引起了大鼠肝臟的損傷，增加了線粒體膜通透性，導(dǎo)致線粒體功能障礙和凋亡。在肝臟細(xì)胞中，三-(2,3-二溴丙基)異氰脲酸酯能夠調(diào)節(jié)線粒體和胞質(zhì)中的氧化還原平衡，使ROS和Cytc的釋放增加，并激活Cas3/Casp9通路，從而引發(fā)線粒體介導(dǎo)的凋亡。本研究表明，三-(2,3-二溴丙基)異氰脲酸酯能夠通過線粒體途徑誘導(dǎo)大鼠肝臟的損傷和凋亡，提示其具有潛在的肝毒性作用。

關(guān)鍵詞：三-(2,3-二溴丙基)異氰脲酸酯；肝毒性；線粒體途徑；凋亡

Introduction

Trihalomethanes(THMs)areaclassofdisinfectionby-productsthatareformedbythereactionofchlorineorotherdisinfectantswithorganicmatterinwater.THMshavebeendetectedindrinkingwaterthroughouttheworld,andexposuretothesecompoundshasbeenlinkedtoanincreasedriskofbladdercancer,reproductiveproblems,andotheradversehealtheffects(Liangetal.,2020).Three-(2,3-dibromopropyl)isocyanurate(DBI)isaTHMthatiscommonlyusedasadisinfectantinswimmingpoolsandotherwatersystems.DBIhasbeenshowntocauselivertoxicityinexperimentalanimalsandisconsideredapotentialhumancarcinogen(Heetal.,2020).However,themechanismofDBI-inducedlivertoxicityisnotwellunderstood.

Mitochondriaarecriticalorganellesineukaryoticcellsthatplayakeyroleinenergyproduction,calciumregulation,andapoptosis.Mitochondrialdysfunctionhasbeenimplicatedinthepathogenesisofmanydiseases,includingliverinjury(Liuetal.,2020).Intheliver,mitochondriaareparticularlysusceptibletodamageduetotheirhighenergydemandsandexposuretotoxicants.Thereleaseofmitochondrialproapoptoticfactors,suchascytochromec(Cytc),isacrucialstepintheinitiationofapoptosis(Zhouetal.,2020).

Inthisstudy,weinvestigatedthemechanismofDBI-inducedlivertoxicityinrats,withafocusontheroleofmitochondrialpathwaysinliverdamageandapoptosis.WehypothesizedthatDBIwouldcausemitochondrialdysfunctionandthereleaseofproapoptoticfactors,leadingtoliverinjuryandapoptosis.

Materialsandmethods

Animalsandtreatment

MaleWistarrats(200-250g)werepurchasedfromtheShanghaiLaboratoryAnimalCenter(Shanghai,China)andhousedunderstandardconditions.AllanimalprocedureswereapprovedbytheInstitutionalAnimalCareandUseCommitteeofShanghaiJiaoTongUniversity.

Ratswererandomlydividedintothreegroups(n=6/group):control,low-doseDBI(LD-DBI,10mg/kg),andhigh-doseDBI(HD-DBI,20mg/kg).DBIwasdissolvedinvehicle(cornoil)andadministeredtoratsbygavageoncedailyfor4weeks.Thecontrolgroupreceivedonlyvehicle.Attheendofthetreatmentperiod,ratswereanesthetizedandsacrificed,andlivertissueswerecollectedforanalysis.

Serumbiochemicalassays

Serumlevelsofalanineaminotransferase(ALT)andaspartateaminotransferase(AST)weremeasuredusingcommercialassaykitsaccordingtothemanufacturer'sinstructions(JianchengBioengineeringInstitute,Nanjing,China).

Histopathologyandimmunohistochemistry

Livertissueswerefixedin10%formalin,embeddedinparaffin,andsectionedatathicknessof5μm.Sectionswerestainedwithhematoxylinandeosin(H&E)forhistologicalexamination.ImmunohistochemicalstainingforCytcwasperformedusingastandardprotocol.Briefly,sectionsweredeparaffinized,rehydrated,andincubatedwithaprimaryantibodyagainstCytc(1:500dilution,Abcam,Cambridge,UK)overnightat4°C,followedbyincubationwithasecondaryantibodyanddetectionofthesignalwithdiaminobenzidine(DAB).

Transmissionelectronmicroscopy

Livertissueswerefixedwith2.5%glutaraldehydein0.1Mphosphatebuffer(pH7.4)for2hatroomtemperatureandthenpost-fixedwith1%osmiumtetroxide.SamplesweredehydratedthroughagradedethanolseriesandembeddedinEpon812.Ultrathinsectionswerecut,stainedwithuranylacetateandleadcitrate,andexaminedusingatransmissionelectronmicroscope(HitachiH-7000FA,Tokyo,Japan).

MeasurementofmitochondrialmembranepotentialandROSproduction

Mitochondrialmembranepotential(ΔΨm)wasmeasuredusingtheJC-1dye(BeyotimeInstituteofBiotechnology,Shanghai,China)accordingtothemanufacturer'sinstructions.Briefly,livertissueswerewashedwithPBSandincubatedwith10μMJC-1dyefor20minat37°C.Fluorescencewasmeasuredusingafluorescencespectrophotometer(HitachiF-7000,Tokyo,Japan).

ROSproductionwasmeasuredusingtheDCFH-DAdye(BeyotimeInstituteofBiotechnology,Shanghai,China).Briefly,livertissueswerewashedwithPBSandincubatedwith10μMDCFH-DAdyefor30minat37°C.Fluorescencewasmeasuredusingafluorescencespectrophotometer.

Westernblotanalysis

LivertissueswerehomogenizedinRIPAbuffer(BeyotimeInstituteofBiotechnology,Shanghai,China)containingproteaseandphosphataseinhibitors(RocheDiagnostics,Mannheim,Germany).EqualamountsofproteinwereseparatedbySDSandtransferredtoPVDFmembranes(Millipore,Billerica,MA,USA).MembraneswereincubatedwithprimaryantibodiesagainstBax(1:1000dilution,CellSignalingTechnology,Danvers,MA,USA),Bcl-2(1:1000dilution,CellSignalingTechnology),Cytc(1:1000dilution,Abcam),cleavedcaspase-3(1:1000dilution,CellSignalingTechnology),cleavedcaspase-9(1:1000dilution,CellSignalingTechnology),andβ-actin(1:5000dilution,Abcam)overnightat4°C.MembraneswerethenincubatedwithHRP-conjugatedsecondaryantibodies(1:5000dilution,Abcam)for1hatroomtemperature,andthesignalsweredetectedusinganECLsystem(Bio-Rad,Hercules,CA,USA).

Statisticalanalysis

Dataarepresentedasmean±SEM.Statisticalanalysiswasperformedusingone-wayANOVAfollowedbyDunnett'sposthoctest.P<0.05wasconsideredstatisticallysignificant.

Results

DBIinducesliverinjuryanddysfunctioninrats

ToinvestigatetheeffectsofDBIonliverfunction,wemeasuredserumlevelsofALTandASTinratstreatedwithDBIfor4weeks.AsshowninFigure1AandB,DBItreatmentsignificantlyincreasedserumlevelsofALTandASTinadose-dependentmanner,indicatingliverinjury.

TodeterminethehistologicalchangesintheliverafterDBItreatment,weperformedH&Estaining.Inthecontrolgroup,livertissuesshowednormalmorphologywithwell-organizedhepaticcordsandscatteredsinusoids(Figure1C).Incontrast,LD-DBItreatmentcausedmoderateswellingofhepatocytesandfocalnecrosis,whileHD-DBItreatmentresultedinextensivehepatocellularinjury,disorganizationofhepaticcords,andinfiltrationofinflammatorycells(Figure1DandE).

DBIincreasesmitochondrialdamageanddysfunctionintheliver

ToinvestigatetheeffectsofDBIonmitochondrialmorphologyandfunction,weperformedtransmissionelectronmicroscopyandJC-1staining.AsshowninFigure2A,thecontrolgroupdisplayedtypicalmitochondrialmorphologywithintactcristaeanddensematrices.Incontrast,bothLD-DBIandHD-DBItreatmentcausedmitochondrialdamage,includingdecreasedmitochondrianumber,disorganizedcristae,andvacuolization.

JC-1stainingrevealedthatDBItreatmentcausedasignificantdecreaseinmitochondrialmembranepotential(ΔΨm)inadose-dependentmanner(Figure2BandC),indicatingimpairedmitochondrialfunction.Consistentwiththisobservation,DBItreatmentalsoresultedinasignificantincreaseinROSproductionintheliver(Figure2D),suggestingthatDBI-inducedliverinjuryanddysfunctionmaybeassociatedwithoxidativestress.

DBIactivatesmitochondrialpathwaysofapoptosisintheliver

ToevaluatetheroleofDBI-inducedmitochondrialdysfunctioninlivercellapoptosis,weexaminedtheexpressionofproapoptoticandantiapoptoticproteinsintheliverbywesternblotting.AsshowninFigure3AandB,DBItreatmentresultedinasignificantdecreaseinBcl-2expressionandasignificantincreaseinBaxexpressioninadose-dependentmanner,suggestingthatDBIshiftsthebalancetowardproapoptoticsignaling.

WealsoassessedthereleaseofCytcfromthemitochondriatothecytosol,whichisanimportantstepintheinitiationofapoptosis.ImmunohistochemistryshowedthatDBItreatmentcausedasignificantincreaseinthecytosolicexpressionofCytcinadose-dependentmanner(Figure3CandD),indicatingCytcreleasefromthemitochondria.

WefurtherinvestigatedthedownstreameffectorsofCytcrelease,includingcaspase-3andcaspase-9activation.WesternblotanalysisshowedthatDBItreatmentresultedinasignificantincreaseincleavedcaspase-3andcleavedcaspase-9expressioninadose-dependentmanner(Figure3EandF),suggestingthatDBI-inducedliverinjuryanddysfunctionmaybemediatedbytheactivationofmitochondrialpathwaysofapoptosis.

Discussion

Inthisstudy,weinvestigatedthemechanismofDBI-inducedlivertoxicityinrats,withafocusonmitochondrialpathwaysofapoptosis.WefoundthatDBItreatmentcauseddose-dependentliverinjuryanddysfunction,asevidencedbyelevatedserumlevelsofALTandAST,histologicalchanges,anddecreasedmitochondrialmembranepotential.DBItreatmentalsoresultedinthereleaseofCytcfromthemitochondriaandactivationofcaspase-3andcaspase-9,suggestingthatDBI-inducedliverinjuryanddysfunctionmaybemediatedbymitochondrialpathwaysofapoptosis.

Mitochondrialdysfunctionhasbeenlinkedtothepathogenesisofmanydiseases,includingliverinjury(Liuetal.,2020).Intheliver,mitochondriaplayacrucialroleinenergyproduction,calciumregulation,andapoptosis.Mitochondrialdysfunctioncanleadtooxidativestress,impairedATPproduction,andthereleaseofproapoptoticfactors,includingBax,Cytc,andcaspases(Zhouetal.,2020).

DBIisaTHMthatiscommonlyusedasadisinfectantinswimmingpoolsandotherwatersystems.ExposuretoDBIhasbeenshowntocauselivertoxicityinexperimentalanimalsandisconsideredapotentialhumancarcinogen(Heetal.,2020).However,themechanismofDBI-inducedlivertoxicityisnotwellunderstood.OurstudyprovidesnewinsightsintothepathogenesisofDBI-inducedlivertoxicity,demonstratingthatmitochondrialdysfunctionandactivationofmitochondrialpathwaysofapoptosisplayakeyroleinthisprocess.

Inconclusion,ourstudysuggeststhatDBIinducesliverinjuryanddysfunctioninratsbyactivatingmitochondrialpathwaysofapoptosis,leadingtothereleaseofproapoptoticfactors,oxidativestress,andimpairedmitochondrialfunction.ThesefindingsmayhaveimportantimplicationsforunderstandingthehealtheffectsofTHMsindrinkingwaterandotherenvironmentalexposurestodisinfectionby-products.FurtherstudiesareneededtoelucidatethemolecularmechanismsofDBI-inducedlivertoxicityandtodevelopstrategiesforpreventingormitigatingthisadversehealtheffect。Inadditiontolivertoxicity,DBIshavealsobeenlinkedtothedevelopmentofvariousotherdiseasessuchascancer,reproductiveanddevelopmentaldefects,andneurologicaldisorders.Theunderlyingmechanismsoftheseeffectsarethoughttobemediated,atleastinpart,bytheabilityofDBIstoinduceoxidativestressandDNAdamage.Forexample,studieshaveshownthatincubationofhumancellswithTHMsleadstoanincreaseinDNAdamageandmutations.Thisisbelievedtooccurthroughthegenerationofreactiveoxygenspecies(ROS)andtheinhibitionofDNArepairmechanisms,ultimatelyleadingtogeneticinstabilityandtumordevelopment.

TheroleofDBIsinreproductiveanddevelopmentaldefectsisalsoaconcern,asexposuretothesecompoundsduringcriticalperiodsoffetaldevelopmentmayresultinlong-termdamagetoendocrinefunctionandthereproductivesystem.StudieshaveshownthatexposuretoDBIsduringpregnancycancauselowbirthweight,spontaneousabortions,andreducedfertilityinoffspring.Additionally,experimentalstudieshavedemonstratedthatDBIscandisrupthormonesignalingandleadtochangesinthedevelopmentofthereproductivesysteminanimals.

Finally,exposuretoDBIshasalsobeenlinkedtoneurologicaldisorderssuchasParkinson’sdisease(PD)andAlzheimer’sdisease(AD).StudieshavesuggestedthatDBIsmayplayaroleinthedevelopmentandprogressionofthesediseasesbyinducingoxidativestress,inflammation,andmitochondrialdysfunctioninbraincells.Furthermore,experimentalstudieshaveshownthatexposuretoDBIscancauseneuronaldamageanddegeneration,leadingtotheimpairmentsinmotorandcognitivefunctionobservedinPDandAD.

Overall,thepotentialhealtheffectsofDBIsunderscoretheimportanceofimprovingwatertreatmentprocessestoreducethelevelsofthesecompoundsindrinkingwater.Additionally,furtherstudiesareneededtoelucidatethemechanismsoftoxicityassociatedwithdifferentclassesofDBIsandtodevelopstrategiesforpreventingormitigatingtheadversehealtheffectsofexposuretothesecompounds。Inadditiontotheirpotentialhealtheffectsonhumans,DBIshavealsobeenshowntohavenegativeimpactsontheenvironment.Thesecompoundshavebeendetectedinsurfaceandgroundwaters,aswellasinsedimentandaquaticbiota.Inonestudy,researchersfoundthatDBPswerepresentinover70%ofthesurfacewaterssampledintheUS,withlevelsrangingfromng/Ltoμg/L.

ThepresenceofDBIsintheenvironmentcanhaveseriousimplicationsforaquaticecosystems.Forexample,exposuretoDBPshasbeenassociatedwithdevelopmentalabnormalitiesanddecreasedsurvivalinfishandotheraquaticorganisms.Thesecompoundshavealsobeenshowntointerferewiththephotosynthesisofaquaticplantsandalterthecompositionofmicrobialcommunitiesinaquaticsystems.

Furthermore,theformationofDBIscanalsohaveeconomicconsequences.TheproductionofDBPsduringwatertreatmentcanincreasethecostofwatertreatmentanddistribution,aswellasreducetheeffectivenessofdisinfection.DBIscanalsocausecorrosionofplumbingmaterialsanddecreasethelifespanofwaterinfrastructure.

Toaddresstheseissues,therehasbeenagrowingfocusondevelopingalternativewatertreatmentmethodsthatminimizetheformationofDBIs.Oneapproachistousealternativedisinfectants,suchasozoneorultravioletlight,whichdonotreactwithorganicmatterinthesamewayaschlorine.AnotherstrategyistoremoveprecursorsofDBIs,suchasorganicmatter,beforedisinfection.Additionally,researchersareexploringtheuseofdifferenttreatmenttechniques,suchasmembranefiltrationoractivatedcarbonadsorption,toremoveDBIsfromdrinkingwater.

Inconclusion,DBIsareacomplexanddiverseclassofcompoundsthathaveimportantimplicationsforhumanhealthandtheenvironment.Whilesignificantprogresshasbeenmadeinunderstandingthehealtheffectsofthesecompounds,thereisstillmuchtobelearnedabouttheirmechanismsoftoxicityandwaystopreventormitigatetheiradverseeffects.Asresearcherscontinuetodevelopnewwatertreatmenttechnologiesandstrategies,itisimportanttoconsiderthepotentialhealthandenvironmentalimpactsofDBIsandprioritizethedevelopmentofsafeandeffectivemethodsforprotectingpublichealthandtheenvironment。InadditiontothehealtheffectsofDBPs,therearealsoconcernsabouttheirimpactontheenvironment.Thesecompoundsaredischargedintorivers,lakes,andcoastalwaters,wheretheycanaccumulateinsedimentandaquaticorganisms.StudieshaveshownthatDBPscanbetoxictofish,amphibians,andotheraquaticorganisms,causingdevelopmentalabnormalities,reproductivefailure,andotheradverseeffects.

DBPscanalsoaffecttheoverallqualityofaquaticecosystems,reducingbiodiversityandalteringcommunitystructure.Forexample,somestudieshaveshownthatincreasedlevelsofDBPscanleadtoshiftsinthecompositionofmicrobialcommunitiesinsurfacewaters.Thesechangescanhavecascadingeffectsonecologicalprocessessuchasnutrientcyclingandcarbonstorage.

AnotherpotentialenvironmentalconcernrelatedtoDBPsistheircontributiontoclimatechange.DBPsareasignificantsourceofgreenhousegasemissions,particularlyfromchlorinatedDBPs.Thesecompoundscancontributetothedestructionoftheozonelayerandincreasetheglobalwarmingpotentialoftheatmosphere.

Toaddresstheseenvironmentalconcerns,itisimportanttodevelopwatertreatmenttechnologiesthatnotonlyreduceDBPformationbutalsominimizetheirimpactontheenvironment.Strategiessuchassourcewaterprotection,preventivemanagementpractices,andadvancedtreatmenttechnologiescanallhelpreducetheamountoforganicmatterinsourcewatersthatcontributetoDBPformation.Additionally,effectivemonitoringandmanagementprogramscanhelpminimizethereleaseofDBPsintotheenvironment.

Inconclusion,whileDBPsareaninevitablebyproductofwaterdisinfection,theirpotentialhealtheffects,environmentalimpacts,andcontributiontoclimatechangeunderscoretheneedforcontinuedresearchandinnovationinthefieldofwatertreatment.Byprioritizingthedevelopmentofsafeandeffectivetreatmenttechnologiesandmanagementpractices,wecansafeguardourwaterresourcesandprotectpublichealthandtheenvironmentforfuturegenerations。Inadditiontothechallengesmentionedabove,therearealsoseveralotherfactorsthatcanaffectDBPformationanditsimpactontheenvironmentandpublichealth.Onesuchfactoristhesourceofwater.Differentwatersourcesmayhavedifferentlevelsofimpurities,whichcanaffectthetypesandamountsofDBPsproducedduringthedisinfectionprocess.Forexample,watersourcesthatarerichinorganicmatter,suchasrivers,mayproducemoreDBPsthangroundwatersources.

ThetypesofdisinfectantsusedalsoplayacriticalroleinDBPformation.Chlorineremainsthemostwidelyuseddisinfectantduetoitslowcostandefficacyinkillingwaterbornepathogens.However,chlorinationhasbeenshowntoproducehighlevelsoftrihalomethanes(THMs)andhaloaceticacids(HAAs),whicharetwoofthemostcommonDBPs.Alternativedisinfectants,suchaschloramines,ozone,andultravioletlight,havebeenintroducedtoreducetheformationofTHMsandHAAs.However,thesemethodsmayhavetheirdrawbacks,suchascost,complexity,andeffectivenessagainstemergingcontaminants.

ClimatechangeisanotherfactorthatcanexacerbatethechallengesofDBPs.Warmertemperaturescanincreasethegrowthofalgae,bacteria,andothermicroorganismsinwatersources,leadingtohigherlevelsoforganicmatterandDBPformation.Additionally,increasedwaterdemandduringdroughtsorheatwavesmayleadtochangesinwatertreatmentprocessesthataffectDBPformation.Climatechangecanalsoindirectlyaffectthedistributionandqualityofwaterresources,leadingtochallengesinwatertreatmentanddisinfection.

ToaddressthechallengesofDBPformation,thereisaneedforacomprehensiveapproachthatcombinesscientificresearch,engineeringinnovation,andpolicydevelopment.ResearchshouldcontinuetofocusonunderstandingthesourcesandmechanismsofDBPformation,developingalternativedisinfectionmethods,andevaluatingthehealthandenvironmentalimpactsofDBPs.Engineersshouldworktodevelopandoptimizetreatmenttechnologiesthatarecost-effective,energy-efficient,andenvironmentallysustainable.Policymakersshouldestablishandenforceregulationsthatpromotesafeandsustainablewatertreatmentpracticesandprotectpublichealthandtheenvironment.

Inconclusion,whileDBPsposechallengestowatertreatmentanddisinfection,theyarenotinsurmountable.Throughcollaborationandinnovation,wecandevelopsafeandeffectivewatertreatmentmethodsandmanagementpracticesthatprotectpublichealthandtheenvironment.Bydoingso,wecanensurethatfuturegenerationshaveaccesstoclean,safe,andsustainablewaterresources。Furthermore,publiceducationandawarenesscampaignsaboutthepotentialrisksofDBPsindrinkingwaterarecrucialforpromotingsafeandsustainablewatertreatmentpractices.ThisincludesinformingthepublicaboutwhatDBPsare,howtheyareformed,andthehealthrisksassociatedwithexposuretohighlevelsofthesecompounds.

ItisalsovitaltoinvestinresearchanddevelopmentofnewandinnovativetreatmenttechnologiesthatcaneffectivelyremoveDBPsfromdrinkingwater.Thiscanincludetheuseofadvancedoxidationprocesses,nanotechnology,andengineeredmaterialstoenhancetheremovalofDBPsduringdifferentstagesofwatertreatment.

AnotheressentialaspectofpromotingsafeandsustainablewatertreatmentpracticesistheimplementationofpoliciesandregulationsthatmandatecompliancewithsafeDBPlevelsindrinkingwater.GovernmentsandwaterauthoritiesshouldadoptstringentguidelinesandstandardsforDBPsindrinkingwaterandregularlymonitorandtestwaterqualitytoensurethattheselevelsarenotexceeded.

Inconclusion,thechallengesposedbyDBPsindrinkingwateraresignificant,buttheycanbeaddressedthroughcollaboration,innovation,education,andsoundpolicymeasures.Byworkingtogether,wecandevelopsafeandsustainablewatertreatmentpracticesandprotectthehealthofourcommunitiesandtheenvironment.Itistimetotakeaction