h tt p : / / w w w . b j m i c r o b i o l . c o m . b r /
Industrial
Microbiology
Staphylococcus
xylosus
fermentation
of
pork
fatty
waste:
raw
material
for
biodiesel
production
Roger
Vasques
Marques
a,∗,
Matheus
Francisco
da
Paz
a,
Eduarda
Hallal
Duval
b,
Luciara
Bilhalva
Corrêa
a,
Érico
Kunde
Corrêa
aaLaboratoryofWastes,FederalUniversityofPelotas,Pelotas,RS,Brazil
bAnimalProductsInspectionLaboratory,FederalUniversityofPelotas,CampusCapãodoLeão,CapãodoLeão,RS,Brazil
a
r
t
i
c
l
e
i
n
f
o
Articlehistory:
Received8October2015 Accepted17February2016 Availableonline21April2016 AssociateEditor:SolangeInes Mussatto Keywords: Sustainability Microorganism Staphylococcusxylosus Wasterecovery Slaughterhousewaste
a
b
s
t
r
a
c
t
The needforcleanersourcesofenergyhasstirredresearchintoutilisingalternatefuel sourceswithfavourableemissionandsustainabilitysuchasbiodiesel.However,thereare technicalconstraintsthathinderthewidespreaduseofsomeofthelowcostraw materi-alssuchasporkfattywastes.Currentlyavailabletechnologypermitstheuseoflipolytic microorganismstosustainablyproduceenergyfromfatsources;andseveral microorgan-ismsandtheirmetabolitesarebeinginvestigatedaspotentialenergysources.Thus,theaim ofthisstudywastocharacterisetheprocessofStaphylococcusxylosusmediatedfermentation ofporkfattywaste.Wealsowantedtoexplorethepossibilityoffermentationeffectinga modificationinthelipidcarbonchaintoreduceitsmeltingpointandtherebyactdirectlyon oneofthemaintechnicalbarrierstoobtainingbiodieselfromthisabundantsourceoflipids. PorkfattywastewasobtainedfromslaughterhousesinsouthernBrazilduringevisceration ofthecarcassesandthekidneycasingofslaughteredanimalswasusedasfeedstock. Fer-mentationwasperformedinBHIbrothwithdifferentconcentrationsoffattywasteandfor differenttimeperiodswhichenabledevaluationoftheeffectoffermentationtimeonthe meltingpointofswinefat.Thelowestmeltingpointwasobservedaround46◦C,indicating thatthesechemicalandbiologicalreactionscanoccurundermilderconditions,andthat suchpre-treatmentmayfurtherfacilitateproductionofbiodieselfromfattyanimalwaste. ©2016SociedadeBrasileiradeMicrobiologia.PublishedbyElsevierEditoraLtda.Thisis anopenaccessarticleundertheCCBY-NC-NDlicense(http://creativecommons.org/
licenses/by-nc-nd/4.0/).
Introduction
Contemporarysociety reliesontheuseofvariousformsof energytomeetandachievethebestqualityoflife;andthe
∗ Correspondingauthor.
E-mail:rogermarquesea@gmail.com(R.V.Marques).
products and processes being used tothat end essentially relyonanuninterruptedsupplyofenergywhichalsoneeds tobeofhighquality, becompetitivelypricedandleave the leastpossibleimpactontheenvironment.Theglobalenergy matrixlargelydependsontheuseoffossilfuelsandisthus
http://dx.doi.org/10.1016/j.bjm.2016.04.018
1517-8382/©2016SociedadeBrasileiradeMicrobiologia.PublishedbyElsevierEditoraLtda.ThisisanopenaccessarticleundertheCC BY-NC-NDlicense(http://creativecommons.org/licenses/by-nc-nd/4.0/).
non-renewable.Thisisworrisomeasinternationalagencies monitoringenergysourcespredicta60%reductioninoiland coalsupplywithinthenext15years,whichwillinturnleadto aphenomenalriseinextraction,productandprocesscosts.1–3
Thispredicteddecreaseinenergyresources,constitutesone ofthegreatestchallengesofoursocietyandhasresultedin researchintoandimprovementofalternatetechnologiesthat ensureenergysustainability.Biofuelsareapertinent exam-plewhichwhilebeingobtainedfromrenewablerawmaterials suchasbiomass,effluentsandfattywaste,arealsoless pollut-ingbecausetheircombustionresultsinmuchloweremission levelsofcarbon monoxide,sulphurcompounds, particulate matterandaromatichydrocarbons.4–8 Therefore,the
devel-opmentofbiofuelsfromagro-industrialwasteconstitutesan importantalternative asthese can be furthertransformed into second-generation biofuels that do not compete with agriculturefor resources, havenegligible costcompared to vegetablesourcesandareplentifulincountrieswith agricul-turalpotency.9–13Technologicalproblemscontinuetoprevent
the economic, attractive and sustainable use ofpork fatty wastefortheproductionofbiodiesel,oneofthemisthehigh coldfilter pluggingpoint, which precludes its use in vehi-clesoperatinginregionswithtemperaturesbelow15◦Cdue to crystal formation, leading to low or none viscosity.14–16
The high melting point of pork fat (>70◦C) demands sig-nificant energy consumption to liquefy this waste, which contributes to an increase in the final price of biodiesel fromsuchsources.Thus,eventhoughtherawmaterialhas a lower cost compared to vegetable oils, improvements in thetechnologytotransformporkfattywaste intobiodiesel arerequiredtomakethisaneconomicallycompetitivefuel source.17
Biofuelproductionnow increasinglyreliesontheuse of microorganisms,eitherforthedirectorfortheassisteduse oflipidsasbiofuels.18–22Therefore,aprocessthatuses
lipoly-ticmicroorganismsforbothtreatmentandrecoveryofanimal fattywaste showpromise asaworkablestrategythatuses agro-industrial waste for biodiesel production with desir-ablequalitycharacteristicsandundereconomicallyfeasible conditions.23–26 Staphylococcus xylosus,a Gram-positive
coc-cus,isamicroorganismthatfitstheserequirementsasithas GRAScertification(GenerallyRecognisedAsSafe),knownto haveproteolyticand lipolyticactivity,andregularlyusedin thefoodindustryespeciallyforfermentationofmeat prod-ucts as well as for the production and intensification of flavour,colourstabilisationandperoxidedecomposition.27–29
Importantly, apart from these in vivo applications, S. xylo-sus and other bacteria from the same genus also secrete exoenzymes that catalyse lipid-based reactions.22,30–35 A
useful example of such secreted enzymes is the serine acetyltransferase(E.C.3.1.1.3),whichiscapableofcatalysing alcoholysis,esterification,transesterificationandhydrolysis, amongothers.36,37Additionally,theeasewithwhichS.xylosus
canbeisolated andculturedmakesit apotential enhance-ment agent in the use of pork fatty wastes for biodiesel production.38
Giventhese favourable characteristics, the mainaim of this study wasto investigatethe process characteristics of porkfattywastefermentationbyS.xylosus.Wealsowantedto explorethepossibilityofthisfermentationeffectingachange
inlipid carbonchainstoreduceits meltingpointand thus actdirectlyononeofthemaintechnicalbarrierstoobtaining biodieselfromthisabundantsourceoflipids.
Material
and
methods
Collectionofsamples
The fatty waste was collected from freshly slaughtered animalspriortothewashingofthecarcassesfroma slaugh-terhouseinsouthernBrazil.Inordertocollectthefatwith the leastblood contaminationaspossible,the fatty kidney sheathsof25carcasses,eachweighingapproximately0.6kg wereremoved,collectedintosterilebags,transportedonice, andimmediatelysubjectedtofermentation.Allanalyseswere performedintriplicate.
Bacterialculturesandgrowth
S.xylosusNRRLB-14776wasculturedinBrain-HearthInfusion broth(BHI–Acumedia–NeogenCorporation®7116A,Brazil) aspreviouslydescribedbyMaurielloetal.27untilrequired
ini-tialcellmassconcentration(8.0logCFUmL−1),afterwhicha loopofbacteriumwastransferredtotheBHIbrothand incu-batedat35±0.1◦Covernight.
Porkfattywastefermentation
The experiment followed a fully randomised two-factorial designwiththreerepetitionswherein thetwofactors were fermentation time(1.5, 3.0,4.5, 6.0and 7.5h)and fat con-centrationofthe BHIbroth(2,4,6,8,10,50,60,70,80 and 90%).
Thefermentationwascarriedoutundersemi-solid-state conditions and consisted ofpork fatty waste asthe water insolublecomponentthatprovidednutrients(primarily car-bon)andanchorageformicroorganisms,apartfromBHIbroth andtheinoculum(1%,v/v).Thefattywastewasmelted,dried, filtered (filter paper Whatman 12.5cm), ground and sieved througha0.5mmsieve(32mesh).Next,thefatwassterilised bymembranefiltrationandasepticallyweighedinsterile plas-tic bags. Afterthe addition ofthe required volume ofBHI brothwiththenecessaryinitialcellconcentrationofboththe strainsofS.xylosus,thebagswereplacedina“Stomacher” homogeniser(SPLabour–modelSP-190-type)for2minand thentransferredtosterileErlenmeyerflasks;thetotal fermen-tationvolumewas200mL.Theflaskswerekeptinashaker incubator(35±0.1◦C,bufferpH7.0,100rpm)forinitiationof fermentation,andformaintenanceofaerobicconditionsin thereactor.Dissolvedoxygenwasmeasuredwithaportable oximeter (LUTRON DO-5519) and dissolved oxygen satura-tionwasmaintainedat100%throughoutfermentation.The choiceofgrowthconditionsandculturemediumusedwere basedonpreviouslyreportedoptimalgrowth conditionsfor
S.xylosus.27Fermentationwasinterruptedatthementioned
targetanalyticalpoints,whichcorrespondedtotendifferent concentrationsoftesting;andsamplesofapproximately1g wereasepticallycollectedfromeachErlenmeyerflaskand sub-jectedtomeltingpointanalysis.
Meltingpointanalysis
Testtubescontainingapproximately1gofsamplewere par-tially immersedin avolumetricflask withwater and kept onaheatingmantlethatslowlyincreasedthetemperature from30◦Cto80◦C.39Thismethoddetectsthreetemperatures
thatcharacterisethemeltingpointsofthreedifferentfatty acidsasdescribedbyDouareetal.40AsKnotheandDunn41
havereportedthatinitialandfinalmeltingtemperaturesare affectedbythequantityofthesamplebeinganalysed,only coretemperatureofthesamplewasconsidered.Meltingpoint ofthenon-fermentedfattywastewasdeterminedaccording toAOCSmethodology.39
Statisticalanalysis
ThenormalityofdatawastestedusingShapiro-Wilk’stest, homoscedasticitywastestedwiththeHartleytest,andresidue independence was tested using graphical analysis. After ensuringthat the assumptions were met,analysis of vari-ance (ANOVA) was performed using F test on values with
p<0.05.Experimentaldatawereanalysedusingresponse sur-facemethodologytofitasecond-orderpolynomialequation thatwasgeneratedusingregression.Theresponsewas ini-tiallyfit tofactorsusingmultipleregression andthe initial modelselectionwas basedon: (a) lowresiduals;(b)low
p-value;(c)lowstandarddeviation;and(d)highR2.Asecond orderpolynomialequation was thenfitted tothe response data(Eq.(1)). y=ˇ0+
ˇixi+ ˇii·x2i + ˇijxixj (1)wherey isthe response factor (fattywaste melting point),
xi is the first independent factor (fermentation time), xj is
thesecondindependentfactor(fatconcentration),ˇ0 isthe intercept,ˇiand ˇj arethefirst-ordermodelcoefficients,ˇii
and ˇjj are the quadratic coefficients for the factors i and
j and ˇij is the linear model coefficient of the interaction
betweenfactorsiandj.AlldatawereanalysedusingTheR Projectsoftware(version3.1.0,TheRFoundation®).Statistical parametersshowingap-valuelowerthan0.05wereconsidered significant.
Results
Meltingpoint
Theestimatedvaluesforthevariousfactorsarepresentedin
Table1,andthep-valuesindicatedthatmostofthecoefficients
weresignificantandthaterrorinmodeldesignwasminimised whenallofthesecoefficientswereconsideredtogether. Addi-tionally,thefinalestimatedresponseofthemodeladequately representedrealvaluesandtheestimatedvaluesofthese fac-tors.
Thefinalresponsemodelequationwasderived(Eq.(2))and theresponsesurfaceforthisequation(Fig.1)showsthatthe meltingpointtendstodecreasewhenintermediate fermenta-tiontimeswerereachedandformedacellpointbetweenfour andfivehoursofthefermentationprocess.Atthistime-point, italsoappearsthatthefatconcentrationofthemedium sig-nificantlycontributes(linearly)totheobservedphenomenaas thelevelcurvesatthispointhaveanearnullslope.
100 90 80 Melting point (ºC) Fat concentr ation ( %) Ferm entation t ime (h) 70 60 50 40 80 70 60 50 40 30 20 10 0 1 2 3 4 5 6 7 8
Fig.1–Responsesurfaceplotrepresentingtheeffectsoffat concentration,fermentationtimeandtheirreciprocal interactiononporkfattywastemeltingpoint.
Table1–Estimativeresponsemodelregressioncoefficients,standarderror,tvalueandsignificanceoftheresponse surfacemodelforthemeltingpointbehaviourofporkfattywasteobtainedthroughS.xylosusfermentation.
Factor* Parameterestimate DF Standarderror Fvalue*
tvalue** p>t Generalmodel – 5 2.817 155.854* <0.001 Intercept 81.873 5 1.283 63.836** <0.001 X1 −15.650 5 0.574 −27.279** <0.001 X2 −0.128 5 0.036 −3.607* <0.001 X12 1.648 5 0.061 26.978** <0.001 X22 0.0005 5 <0.0001 1.452** 0.149 X1X2 0.022 5 0.0032 6.680** <0.001
Y=81.873−15.650X1−0.128X2+1.648X21+0.0005X22
+0.022X1X2 (2)
Discussion
Theresponsesurfaceplotofthefermentationprocessshows thattheinitialestimatedmeltingpointwas81.87◦C(X1=0;
X2=0),whichsignificantlydeclinedasfatconcentrationand fermentationtimeincreasedandthemaximumdecreasein estimatedmeltingtemperature(Y=44.8◦C)occurredbetween 4and5hoursoffermentationandat38–42%fat concentra-tion.Further,duringthisperiod,themeltingpointappearsto beinfluencedneitherbyfermentationtimenorbyfat concen-trationofthemedium,indicatingastabilisationinbacterial activitywhichinturnledtotheobserveddecreasein physi-cochemicalparameters.Fatconcentrationofthemediumdid notindividuallyinfluencemetabolicactivity asthemelting pointshowedanon-significantvariationovertherangeoffat concentrationusedintheexperiments.However,Fig.1also showsthatthereisapossibilityofaninteractionbetweenthe twoprocessvariables(i.e.,fatconcentrationandtime),with fermentationtimebeingthemostprominentfactorcapable ofeffectingamodificationinporkfattywaste.Theseprocess characteristicsareespeciallypromisingbecausearelatively cheapfeedstockwasused forfermentation. Wefoundthat after reaching the lowest estimated melting point, the fat waste then exhibitedan increasein melting pointas both fermentationtimeand fat concentrationincreased;similar processcharacteristicshavebeenpreviouslyreported.42
Zhou et al.43 have reported that sudden changes in
theoperationalconditionsofindustrialandlaboratory pro-cessesinvolvingmicroorganismscausesdisturbancesintheir metabolismand physiologicalactivity which inturn accel-erate or halt microbial growth. This reflects a period of adaptationthatmicrobesrequiretoadjustDNAsynthesisand RNAreplicationtosuitthechangesinculturemediumandto resumetheirgrowth.
Accordingly,ourdatasuggestthatoptimaloperating con-ditions were achieved at fat concentrations between 55% and62%andbetween3.8and4.5hoursoffermentation,as theseconditionsreducedthemeltingpointtoapproximately 45–47◦C.Theseinferencesarebasedontheassumptionsthat thebestprocessconditionsarethosethatresultinthe great-estdecreaseinmeltingpoint,usethehighestconcentration offattywastepossibleandrequiretheshortestfermentation timesoastoincreasetheeconomicfeasibilityoftheoverall process.
Conclusion
Basedontheresultspresentedherein,itispossibleto con-cludethat semi-solid fermentationofporkfatty wastes by
S.xylosuscauses adropupto36◦Cinmeltingpointunder idealprocessconditions.Thisimpliesthataliquidstate fer-mentationprocess,whichisclosertoambienttemperature, mayfacilitateareductioninreactioncostsandalsoproduce anincreaseinreactionyield.Further,processenhancements
suchasflowconditionsduringfermentation,wouldensure thatmilderprocessconditionsaresufficienttoachieve effi-ciency.Therefore,pre-treatmentofthefattywastecanhelp optimisetheproductionofbiodieselfromsuchagro-industrial wastesinaprocessthatisbotheconomicallyattractiveand sustainable.
Conflicts
of
interest
Theauthorsdeclarenoconflictsofinterest.
Acknowledgements
TheauthorsthanktheCoordinationfortheImprovementof Higher Education(CAPES–fromPortuguese)forthefinancial supportgiventothisresearch.
r
e
f
e
r
e
n
c
e
s
1.SinghSP,SinghD.Biodieselproductionthroughtheuseof
differentsourcesandcharacterizationofoilsandtheiresters
asthesubstituteofdiesel:areview.RenewSustainEnergyRev.
2010;14:200–216.
2.Internationalenergyagency–IEA.KeyWorldEnergyStatistics 2014.Paris:OECD/IEA;2014.http://www.iea.org/publications/
freepublications/publication/KeyWorld2014.pdf[Accessed
22.02.15].
3.BPGroupEnergyoutlook2035.2015.Availableat: <http://www.bp.com/energyoutlook>[Accessed01.06.15].
4.FargioneJ,HillJ,TilmanD,PolaskyS,HawthorneP.Land
clearingandthebiofuelcarbondebt.Science.
2008;319:1235–1238.
5.XueJ,GriftTE,HansenAC.Effectofbiodieselonengine
performancesandemissions.RenewSustainEnergyRev.
2011;15:1098–1116.
6.SantoriG,DiNicolaG,MoglieM,PolonaraF.Areview
analyzingtheindustrialbiodieselproductionpractice
startingfromvegetableoilrefining.ApplEnergy.
2012;92:109–132.
7.SelvamDJP,VadivelK.Anexperimentalinvestigationon
performance,emission,andcombustioncharacteristicsofa
dieselenginefueledwithmethylestersofwasteporklard
anddieselblends.IntJGreenEnergy.2013;10:908–923.
8.ShojaeefardMH,EtgahniMM,MeisamiF,BarariA.
Experimentalinvestigationonperformanceandexhaust
emissionsofcastoroilbiodieselfromadieselengine.Environ
Technol.2013;34:2019–2026.
9.BhattiHN,HanifMA,QasimM,RehmanAU.Biodiesel
productionfromwastetallow.Fuel.2008;87:2961–2966.
10.GuiMM,LeeKT,BhatiaS.Feasibilityofedibleoilvs.
non-edibleoilvs.wasteedibleoilasbiodieselfeedstock.
Energy.2008;33:1646–1653.
11.AnH,WilhelmWE,SearcySW.Biofuelandpetroleum-based
fuelsupplychainresearch:aliteraturereview.Biomass
Bioenergy.2011;35:3763–3774.
12.CarriquiryMA,DuXD,TimilsinaGR.Secondgeneration
biofuels:economicsandpolicies.EnergyPolicy.
2011;39:4222–4234.
13.GohCS,LeeKT.Second-generationbiofuel(SGB)in
SoutheastAsiavialignocellulosicbiorefinery:penny-foolish
butpound-wise.RenewSustainEnergyRev.2011;15:2714–2718.
14.JoshiRM,PeggMJ.Howpropertiesofbiodieselfuelblendsat
15.OnerC,AltunS.Biodieselproductionfrominedibleanimal
tallowandaexperimentalinvestigationofitsuseas
alternativefuelinadirectinjectdieselengine.ApplEnergy.
2009;86:2114–2120.
16.JanchivA,OhY,ChoiS.Highqualitybiodieselproduction
fromporklardbyhighsolventadditive.ScienceAsia.
2012;38:95–101.
17.JanaunJ,EllisN.Perspectivesonbiodieselasasustainable
fuel.RenewSustainEnergyRev.2010;14:1312–1320.
18.JangY,ParkJM,ChoiS,etal.Engineeringofmicroorganisms
fortheproductionofbiofuelsandperspectivesbasedon
systemmetabolicengineeringapproaches.BiotechnolAdv.
2012;30:989–1000.
19.SharmaM,SinghSS,MannP,SharmaM.Biocatalytic
potentialoflipasefromStaphylococcussp.MS1for
transesterificationofjatrophaoilintofattyacidmethyl
esters.WorldJMicrobiolBiotechnol.2014;30:2885–2897.
20.ThliverosP,KiranEU,WebbC.Microbialbiodieselproduction
bydirectmethanolysisofoleaginousbiomass.Bioresource
Technol.2014;157:181–187.
21.ZhangX,YanS,TyagiRD,SurampalliRY,ValéroJR.
Wastewatersludgeasrawmaterialformicrobialoil
production.ApplEnergy.2014;135:192–201.
22.ZhaoX,QiF,YuanC,DuW,LiuD.Lipase-catalyzedprocess
forbiodieselproduction:enzymeimmobilization,process
simulationandoptimization.RenewSustainEnergyRev.
2015;44:182–197.
23.YooHY,SimkhadaJR,ChoSS,etal.Anovelalkalinelipase
fromRalstoniawithpotentialapplicationinbiodiesel
production.BioresourceTechnol.2011;102:6104–6111.
24.XingMN,ZhangXZ,HuangH.Applicationofmetagenomic
techniquesinminingenzymesfrommicrobialcommunities
forbiofuelsynthesis.BiotechnolAdv.2012;30:920–929.
25.CaspetaL,NielsenJ.Economicandenvironmentalimpacts
ofmicrobialbiodiesel.NatBiotechnol.2013;31(9):789–793.
26.XuX,KimJY,OhYR,ParkJM.Productionofbiodieselfrom
carbonsourcesofmacroalgaeLaminariajaponica.Bioresource
Technol.2014;169:455–461.
27.MaurielloG,CasaburiA,BlaiottaG,VillaniF.Isolationand
technologicalpropertiesofcoagulasenegativestaphylococci
fromfermentedsausagesofSouthernItaly.MeatSci.
2004;67:149–158.
28.MansourS,BaillyJ,LandaudS,etal.Investigationof
associationofYarrowialipolytica,Staphylococcusxylosus,and
Lactococcuslactisincultureasafirststepinmicrobial
interactionanalysis.ApplEnvironMicrobiol.
2009;7520:6422–6430.
29.CichoskiAJ,CansianAP,LuccioDIM.Viabilityof
Staphylococcusxylosusduringshelf-lifeofdulcedeleche
preparedbyvaccumevaporation.CiêncRural.
2011;41(11):2026–2031.
30.LanserAC,NakamuraLK.IdentificationofaStaphylococcus
warnerispeciesthatconvertsoleicacidto10-ketostearic
acid.CurrMicrobiol.1996;32:260–263,1996.
31.FieglerH,BrucknerR.Identificationoftheserine
acetyltransferasegeneofStaphylococcusxylosus.FEMS
MicrobiolLett.1997;148:181–187.
32.MosbahH,SayariA,BezzineS,GargouriY.Expression,
purification,andcharacterizationofHis-tagged
Staphylococcusxylosuslipasewild-typeanditsmutantAsp 290Ala.ProteinExprPurif.2006;47:516–523.
33.SouissiN,BougatefA,Triki-ellouzY,NasriM.Productionof
lipaseandbiomassbyStaphylococcussimulansgrownon
sardinella(Sardinellaaurita)hydrolysatesandpeptone.
AfricanJBiotechnol.2009;8:451–457.
34.BrodFCA,PelisserMR,BertoldoJB,etal.Heterologous
expressionandpurificationofaheat-tolerantStaphylococcus
xylosuslipase.MolBiotechnol.2010;44:110–119.
35.KimSH,KimS,ParkS,KimHK.Biodieselproductionusing
cross-linkedStaphylococcushaemolyticuslipaseimmobilized
onsolidpolymericcarriers.JMolCatalB:Enzymatic.
2013;85–86:10–16.
36.Al-zuhairS.Productionofbiodieselbylipase-catalyzed
transesterificationofvegetableoils:akineticstudy.Biotechnol
Progr.2005;21:1442–1448.
37.FengX,PattersonDA,BalabanM,EmanuelssonEAC.
Characterizationoftributyrinhydrolysisbyimmobilized
lipaseonwoolenclothusingconventionalbatchandnovel
spinningclothdiscreactor.ChemEngResDes.
2013;91:1684–1692.
38.JaegerKE,EggertT.Lipasesforbiotechnology.CurrOpin
Biotechnol.2002;13(4):390–397.
39.AmericanoilChemistsSociety–AOCS.AOCSOfficialMethod Cj1-94:MeltingPropertiesofFatsandOils.2009.
40.DouareM,diBariV,NortonJE,etal.Fatcrystallizationat
oil–waterinterfaces.AdvColloidInterfaceSci.2014;203:1–10.
41.KnotheG,DunnRO.Acomprehensiveevaluationofthe
meltingpointsoffattyacidsandestersdeterminedby
differentialscanningcalorimetry.JAmOilSoc.
2009;86:843–856.
42.MarquesRV,DuvalEH,CorrêaLB,CorrêaEK.Increaseof
unsaturatedfattyacids(lowmeltingpoint)ofbroilerfatty
wasteobtainedthroughStaphylococcusxylosusfermentation.
CurrMicrobiol.2015;71(5):601–606.
43.ZhouZ,MengF,LiangS,etal.Roleofmicroorganismgrowth
phaseintheaccumulationandcharacteristicsof
biomacromolecules(BMM)inamembranebioreactor.RSC