the evolution of infanticide by females in mammals · specifically, female infanticide occurs where...
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1
Theevolutionofinfanticidebyfemalesinmammals
DieterLukas1,2*&EliseHuchard1,3
1)DepartmentofZoology,UniversityofCambridge,DowningStreet,CB23EJCambridge,U.K.
2)DepartmentofHumanBehaviour,Ecology,andCulture,MPIforEvolutionaryAnthropology,DeutscherPlatz6,04103Leipzig,Germany
3)InstitutdesSciencesdeL'EvolutiondeMontpellier,UMR5554,CNRS,UniversitédeMontpellier,Montpellier,France
*)Authorforcorrespondence:[email protected]
ORCID:DieterLukas:0000-0002-7141-3545;EliseHuchard:0000-0002-6944-449X
Keywords:socialcompetition;sexualselection;phylogeneticcomparison;sociality;kinship
Abstract
Inmostmammalianspecies,femalesregularlyinteractwithkin,anditmaythusbedifficultto
understand the evolution of some aggressive and harmful competitive behaviour among
females,suchasinfanticide.Here,weinvestigatetheevolutionarydeterminantsofinfanticide
byfemalesbycombiningaquantitativeanalysisofthetaxonomicdistributionofinfanticide
withaqualitativesynthesisofthecircumstancesofinfanticidalattacksinpublishedreports.
Ourresultsshowthatfemaleinfanticideiswidespreadacrossmammalsandvariesinrelation
tosocialorganizationandlife-history,beingmorefrequentwherefemalesbreedingroups
andinvestmuchenergyintoreproduction.Specifically,femaleinfanticideoccurswherethe
proximity of conspecific offspring directly threatens the killer’s reproductive success by
limitingaccesstocriticalresourcesforherdependentprogeny,includingfood,shelters,care
orasocialposition. Incontrast, infanticide isnot immediatelymodulatedbythedegreeof
kinship among females, and females occasionally sacrifice closely related juveniles. Our
findingssuggest that thepotentialdirect fitness rewardsofgainingaccess to reproductive
resourceshaveastrongerinfluenceontheexpressionoffemaleaggressionthantheindirect
fitnesscostsofcompetingagainstkin.
2
Introduction
Recent work has emphasized that competitive strategies of female mammals are often
strikinglysymmetricaltothoseobservedinmales,includingdisplaysandornaments,fighting
andweaponry, dominance hierarchies, and reproductive suppression by evicting rivals or
suppressing their reproduction [Clutton-Brock2007,2013;Stockley&Bro-Jørgensen2011;
Clutton-Brock& Huchard 2013]. Interactions among conspecificmalemammals are often
contextualandtemporallylimitedtocompetitionoveraccesstomatingpartners,andstudies
ofmalesocialityhavethereforerevolvedaroundmodelsof intrasexualselection[Emlen&
Oring1977;Connor&Krützen2015].Incontrast,femalemammalsaretypicallyphilopatric,
with neighbouring females living in adjacent homeranges or sharing the same group
throughouttheirlives,sothatinteractionsamongfemalescommonlyinvolvekinandoccur
across extended periods and multiple settings [Clutton-Brock 2016]. Females may thus
competeoveradiversityofresources-includingfood,resourcesnecessarytobreed(burrows,
homerange),oroffspringcare[Clutton-Brock2007]-andoftendosowiththeirrelatives.It
has therefore proven difficult to identify the determinants of overt female-female
competition,whichcanvaryacrossspeciesandcontexts,especiallyinthecaseofextremely
harmfulbehavioursuchasinfanticide[Clutton-Brocketal.2001;Youngetal.2006].
Thekillingofrivals’offspringrepresentsaviolentmanifestationofintrasexualcompetition,
andasignificantsourceofjuvenilemortalityinsomepopulations[Palombit2012],withadults
ofbothsexescommittinginfanticide.Ithasbeenintenselystudiedinmalemammals,where
fiftyyearsoffieldresearchhaveshownthatithasevolvedasasexuallyselectedstrategyover
accesstomatingpartners.Incaseswherethepresenceofadependentoffspringpreventsthe
motherfrombecomingpregnantagain,committinganinfanticideallowsthekillertocreate
3
extrareproductiveopportunities inpolygynoussocietieswhereoneorafewalphamale(s)
monopolizematingopportunitiesovershortperiodsbeforelosingdominancetoothers[van
Schaik& Janson2000; Lukas&Huchard2014; Palombit 2015]. In contrast, little is known
aboutthedeterminantsandconsequencesofinfanticidebyfemalesotherthanthemother,
although itmaybemoreprevalent than infanticidebymales,bothwithinandacross taxa
[Blumstein2000;Digby2000].Unlikemales,femalekillersdonotbenefitfromextramating
opportunities[Agrelletal.1998;Digby2000],becausemalemammalsgenerallydonotinvest
intooffspringcaretotheextentthatitwouldpreventthemfrommatingwithotherfemales
[Kleiman&Malcom1981]. Ifanything,killingadependentjuvenilemayexacerbatefemale
matingcompetitionbyspeeding-uptheresumptiontofertilityforthemotherofthevictim.
Several plausible scenarios explaining the occurrence of infanticide by females have been
proposed based on a synthesis of natural observations [reviewed by Digby 2000].
Symmetricallytothepatternsobservedformaleinfanticide,predationfornutritionalgains
(H1:‘exploitation’hypothesis)maynotprovideageneralexplanationforfemaleinfanticide
askillershaverelativelyrarelybeenobservedtoconsumevictimspartiallyorentirely (e.g.
[Goodall 1986; Blumstein 2000]). Instead, hypotheses regarding the adaptive benefits of
femaleinfanticidehavefocusedonhowkillingsmightfacilitateaccesstoresourcesthatare
critical to successful reproduction (H2: ‘resource competition’ hypotheses) [Digby 2000].
Femalekillersmightbedefendingaccesstoanexclusiveterritoryorshelterwhentheytarget
victimsoutsidetheirhomerange(H2.1:‘breedingspace’hypothesis)(asinblack-tailedprairie
dogs [Hoogland 1985] or Belding’s ground squirrels [Sherman 1981]). In species where
femalesonlyassociatetemporallytobreed,killersmaydefendaccesstotheirownmilk,by
discouragingattemptstosucklefromunrelatedjuveniles(H2.2:‘milkcompetitionhypothesis)
(asinNorthernelephantseals:[LeBoeufetal.1973]). Inspecieswhobreedcooperatively,
4
killersmaydefendaccesstoextraoffspringcarebygroupmatesotherthanthemotherby
alteringthehelper-to-pupratiointheirowngroup(H2.3:‘allocare’hypothesis)(asinmeerkats
[Clutton-Brocketal.2001;Youngetal.2006],bandedmongooses[Gilchrist2006;Cantetal.
2014],ormarmoset [Digby1995]).Finally, inspecieswho live instablegroups,killersmay
defend their offspring’s future social status (in species with stable hierarchies) or group
membership (in species with forcible evictions) by eliminating future rivals (H2.4: ‘social
status’hypothesis)(asinsomeOldWorldprimates[Hrdy1976;Digby2000]).
Here, we present an investigation of the distribution and circumstances of infanticide by
femalemammals,basedondatafrom289speciescollectedfromtheprimaryliterature.The
combinationofaquantitative synthesisof the taxonomicdistributionof infanticidewitha
qualitativeanalysisofthecircumstancesof infanticidalattacks(includingtraitsofthekiller
and victim) can contribute to reveal the ecological, life-history or social determinants of
female reproductive competition across mammalian societies, and their relevance to the
occurrence of female associations and interactionswithin and amongmatrilines.We first
summarizethesocialorganisationandlife-historiesofspeciesinwhichinfanticidebyfemales
hasbeenobserved,inordertoevaluatetheconditionsunderwhichreproductivecompetition
among females appears to be particularly intense (Table 1). Next, we perform specific
phylogenetic analyses to test core predictions generated by each hypothesis to assess
whetherfemaleshavebeenobservedtocommitinfanticideinspeciesinwhichtheyaremost
likely to benefit from such killings. In addition, we investigate whether population-level
informationonthetraitsofkillersandvictimsarecompatiblewithpredictionsgeneratedby
eachhypothesis.AllourpredictionsandtestsaresummarizedinTable2.Wefirstshowthat,
acrossallspecies,thedistributionandoccurrenceofinfanticidebyfemalesisbetterexplained
5
byresourcecompetitionthanbyexploitation.Wenexttestwhetherinstanceswherefemales
killoffspringinneighbouringranges(‘breedingspacehypothesis’)aremostlikelyexplainedby
competitionover breeding space; instanceswhere females kill offspringborn in the same
breeding association by competition over milk (‘milk competition hypothesis’); instances
where females kill offspring in groups where usually only a single female reproduces by
competition over offspring care (‘allocare hypothesis’) ; and instances where females kill
offspringborn ingroupswithmultiplebreedersbycompetitionoversocialstatusorgroup
membership (‘social status hypothesis’). This analytical framework relies on a rough
categorizationofthecircumstancesoffemaleinfanticide,andtheoccurrenceofinfanticidein
agivenspeciesmaybeexplainedbymultiplereasons,butouraimistoprovideastartingpoint
fortheinvestigationofthelikelycausesandsituationsunderwhichfemaleinfanticidemight
occur.
6
Materials&Methods
FollowingDigby[2000],weuseabroaddefinitionofinfanticideas‘anactbyoneormorenon-
parentsthatmakesadirectorsignificantcontributiontotheimmediateorimminentdeathof
conspecificyoung’.Thisdefinitionexcludesmatricidesandincludescaseswhereinfantsdieas
theresultofthephysicalaggression(directinfanticide)aswellascaseswheretheenforced
neglect of an infant, such as kidnapping, ultimately causes death (indirect infanticide).
Althoughthelattercasesareoftenexcludedfromstudiesofinfanticideduetotheirproximate
formof‘overzealous’allomaternalcare[Hrdy1976],theirultimateconsequence-infantdeath
- contributes to shape their evolution as infanticidal behaviour. We included infanticide
records from both wild and captive populations for which the killer was unambiguously
identifiedasanadultfemale.Speciesforwhichnocaseofinfanticidehaseverbeenobserved
wereincludedonlyifdetailedobservationsonindividualfemalesandjuvenileswereavailable,
eitherfromrepeatedcaptiveobservationsorfromfieldstudiesoccurringacrossatleastthree
reproductiveseasons,tominimizetheriskofmisclassifyingthemas“non-infanticidal”.For
eachspecies,werecordedwhetherobservationsoccurredinacaptivesettingorundernatural
conditions.Datawere collected from systematic searches through the scientific literature,
startingwithmajorreviewsonthetopicoffemaleinfanticide[Wasser&Barash1983;Agrell
etal.1998;Ebensperger1998;Blumstein2000;Digby2000;Ebensperger&Blumstein2007;
Stockley&Bro-Jorgensen2011;Clutton-Brock&Huchard2013]andperformingbackwardand
forwardcitationsearchestoidentifyrelevantobservations.
For thecomparativeanalyses,weextracteddata foreachspecies inoursampleon: social
organisation (classified as: solitary breeders [home-ranges of breeding females do no
completelyoverlapwithanyotherbreedingindividual],pairbreeders[home-rangescontain
7
asinglebreedingfemaleandasinglebreedingmaleoverlapbutmaycontainadditionalnon-
breeding individuals],associatedbreeders [femalessharethesamespace forbreedingbut
associationsareunstableandtendnottolastbeyondthebreedingseason],orsocialbreeders
[severalbreedingfemalessharethesamehome-rangeacrossmultiplebreedingseasons])[
Lukas & Clutton-Brock 2017]; female philopatry and dispersal (whether most breeding
femaleshavebeenbornintheircurrentlocality/grouporelsewhere)[Lukas&Clutton-Brock
2011];carnivory(whetherthedietofaspeciesincludesmeatornot)[Wilmanetal.2014];
infanticidebymales(whethermaleshavebeenobservedtokillconspecificyoung)[Lukas&
Huchard2014];environmentalclimaticharshness(aprincipalcomponent,withhighvalues
indicatingthatrainfallislowandtemperaturesarecoldandunpredictableacrosstheknown
rangeofaspecies)[Boteroetal.2014];maternalinvestment(meanbodysizeofoffspringat
weaning times mean number of offspring per year divided by mean body mass of adult
females)[Siblyetal.2014];theuseofburrowsornestholesforbreeding(informationwas
takenfromthepapersusedtoextractinformationontheabsenceorpresenceofinfanticide
byfemales);littersize(numberofoffspringperbirth);offspringmassatbirth(grams);weaning
age (age in days at which offspring are independent); inter-birth interval (time between
consecutivebirths indays)Jonesetal.2009];energeticvalueofmilk (MJ/mlbasedonthe
protein,sugar,andfatcomposition)[Langer2008;Barton&Capellini2011;Hinder&Milligan
2011]; offspring care by fathers and/or non-parental group members (whether offspring
receivesmilk or food, or are being regularly carried, by groupmemberswho are not the
mother) [Lukas & Clutton-Brock 2017]; dominance hierarchies and mechanisms of rank
acquisition in social groups (whether all adult females can be arranged in a dominance
hierarchyandifso,whetheranindividual’srankisinfluencedbyageand/ornepotism);and
forcibleevictions(whetherfemalesuseaggressiontoexcludeotherfemalesfromtheirown
8
socialgroup).Foreachspeciesinwhichfemaleshadbeenobservedtokillconspecificyoung,
we used the primary literature to record as much information as possible regarding
characteristics of the killer (age and reproductive state) and of the victim (age, sex, and
relatednesstokiller)totestspecificpredictions.ThefulldatasetisprovidedinSupplementary
Table1(comparativedata)andSupplementaryTable2(individualcharacteristicsdata),with
allreferencesfordataspecificallycollectedhereinSupplementaryFile1.
In addition to performing comparisons assessing contrasts in the presence or absence of
infanticideacrossallspeciesinoursample,weclassifiedspeciesintodifferenttypesaccording
to each of the four resource competition hypotheses (Table 2): for the breeding space
hypothesis, we only included instances of infanticide in which females did not share a
homerangewiththemotherofthevictims;forthemilkcompetitionhypothesis,werestricted
the sample to associated breeders; for the allocare hypothesis, we only included pair
breeders;andforthesocialcompetitionhypothesis,weonlylookedatsocialbreeders.
For the comparative analyses, the phylogenetic relatedness between specieswas inferred
fromtheupdatedmammaliansupertree[Rollandetal.2014].Wefittedseparatephylogenetic
modelsusingMCMCglmm[Hadfield&Nakagawa2010]toidentifytheextenttowhicheach
of thepredictedvariables (Table2)explains thepresenceof infanticideby femalesacross
species (binary response,assumingacategorical familyof traitdistribution).Following the
recommendationsofHadfield[2010],wesetthepriorsusinganuninformativedistribution
(withvariance,V,setto0.5andbeliefparameter,nu,setto0.002).Eachmodelwasrunthree
timesfor100,000iterationswithaburn-inof20,000,visuallycheckedforconvergenceand
foragreementbetweenseparateruns.
9
Results
Socialorganisationandinfanticidebyfemales
Infanticidebyfemaleshasbeenobservedin89(31%)ofthe289mammalianspeciesinour
sample(Table1).Femaleinfanticide(ofanytype)varieswiththesocialorganisationandis
more frequentwhen females breed in groups (Figure 1): it has been observed in 43% of
associatedbreeders,in36%ofpairbreeders,andin30%ofsocialbreeders,butonlyin18%
ofsolitarybreeders.Acrossallspecies,femalesareequallylikelytokilloffspringwhenthey
arephilopatric(47of135species,34%)thanwhentheydispersetobreed(17of59species,
29%)(effectoffemaledispersalonpresenceofinfanticidebyfemales:-10.1,95%CI-39.3–
11.3,p=0.34)buttherearedifferencesfortwotypesofsocialorganisation:acrossassociated
breedersinfanticideonlyoccursinphilopatricspecies;whileacrosspairbreedersinfanticide
ismorelikelytooccurinspeciesinwhichfemalesdisperse(Table1).Acrossallgroup-living
species (associated breeders, pair breeders with helpers, social breeders), there is no
relationship between levels of average relatedness among female group members and
whether infanticidebyfemalesofoffspringborninthesamegroupdoes(medianlevelsof
averagerelatednessacross10species0.09,range0.01-0.38)ordoesnotoccur(medianlevels
ofaveragerelatednessacross24species0.21,range-0.03-0.52)(effectoflevelsofaverage
relatednessonpresenceofinfanticidebyfemales:-21.1,95%CI-81.4–10.1,p=0.18).Across
species inwhichgroupsaremore stable (excludingassociatedbreederswheregroupsare
sometimesdifficulttodefineandcanbeverylarge),levelsofaveragerelatednessareslightly
higherwheninfanticideoccurs(seealso[Lukas&Clutton-Brock2018]).Thepopulation-level
informationshowinstancesofkillersbeingclosekinofthevictimin33%ofspecies(22/65),
witheithergrandmotherskillingtheirgrandchildrenorauntskillingtheirnieces.
10
Life-historiesandinfanticidebyfemales
Energetic investment into reproduction bymothers is higher in species with any form of
infanticidebyfemalescomparedtotheremainingspecies,withspecieshavinglargeroffspring
massatbirth,shortertimetoweaningandbetweenbirths,andlargerlittersizes(Table1).
However,thesepatternsencounteredacrossallspeciesdonotreflectageneralassociation
between infanticideandall thesetraits,but rather the fact thateachdifferentscenarioof
infanticideisassociatedwithspecificlifehistories,characterizedbyoneoracoupleofthese
traits.Femalesininfanticidalspecieswherethereisusuallyasinglebreedingfemaleperhome
range (extraterritorial infanticide and infanticide in pair breeders) have larger litters than
females inspecieswithout infanticide(Table1).Species inwhichfemaleskilloffspring ina
breedingassociationarecharacterizedbyfast-growingoffspring,whileoffspringarerelatively
smallatbirthinspeciesinwhichfemaleskilloffspringinstablegroups(Table1).
11
Old W
orld Primates
Hares
Squirrels
MarmotsMiceMarsupialsBats
Mongooses
Felids
Canids
Bears
Seals & sealions
Martens
Ungulates
New World monkeys
Great apes
Lemurs
extraterritorial infanticideinfanticide: associated breederinfanticide: pair breederinfanticide: social breeder
solitary breederpair/coop. breederassociated breedersocialbreeder
Figure1:Thedistributionofthedifferentformsofinfanticidebyfem
alesinrelationtothesocialorganisationacrossthemam
malianspeciesinour
sample(forpicturecreditseeSupplem
entaryFile2).
12
Table1:Thesocialandlife-historyconditionsassociatedwiththedistributionofinfanticidebyfem
ales
Femalesarem
orelikelytocommitinfanticideingroup-livingspecies,butw
hetherbreedingfemalesarephilopatricordispersedoesnotappearto
beassociatedwiththedistributionofinfanticide.Ingeneral,speciesw
ithinfanticidebyfemalesarecharacterizedbyhighm
aternalinvestment,
withfem
aleshavinglargelitters,shortlactationalandinterbirthperiods,andrelativelylargeoffspring.
Sample of species
Type of infanticide
Infanticide isabsent
presentabsent
presentabsent
presentabsent
presentabsent
presentSam
ple size2
00
89
25
33
33
41
92
91
69
22
0
Fe
ma
les s
olita
ry (%
sp
ecie
s)
38
%1
6%
39
%7
6%
NA
NA
NA
NA
NA
NA
Fe
ma
le p
hilo
pa
tric (%
sp
ecie
s)
73
%6
8%
70
%7
0%
65
%1
00
%4
8%
31
%6
4%
63
%
Ma
tern
al in
ve
stm
en
t (pe
r ye
ar re
lativ
e to
bo
dyw
eig
ht)
39
%1
18
%4
7%
15
0%
48
%8
6%
11
0%
16
9%
29
%4
5%
Litte
r siz
e1
.62
.61
.73
.91
.52
.11
.94
1.3
1.3
Inte
rbirth
inte
rva
l (da
ys)
36
51
80
34
01
04
30
82
12
30
81
81
45
35
22
Ag
e a
t we
an
ing
(da
ys)
12
76
11
13
35
10
75
91
05
42
22
92
73
Offs
prin
g w
eig
ht (re
lativ
e to
bo
dyw
eig
ht)
3.6
%3
.9%
3.9
%2
.8%
3.5
%5
.9%
5.1
%2
.8%
5.1
%3
.0%
allall
associated breederspair breeders
social breeders
any extraterritorial
within-group
within-group
within-group
13
Table2:Testingthecorepredictionsgeneratedbythedifferenthypothesesproposedtoexplainthedistributionofinfanticidebyfemales
Foreachofthemainhypotheses,w
etestedtwocorepredictionsinphylogeneticcom
parisonsandtwopredictionsabouttheindividualtraitsfrom
thefieldobservations.Forthecomparisons,w
elistthesampleofspeciesincluded.
Type of infanticide /Predictions
Sample of species
on individual traitsany form
of infanticide - prim
arily in carnivoresN
okiller: any reproductive state
No
across all species - infanticide also by m
alesN
ovictim
: any ageN
oany form
of infanticide - harsher environm
entsYes
killer: gestating/lactatingYes
across all species - higher m
aternal investment
Yesvictim
: dependent on careYes
extraterritorial infanticide - m
ore burrow use
Yeskiller: gestating/lactating
Yesacross all species
- exclusive home-ranges
Yesvictim
: unweaned
Yesw
ithin group infanticide - higher energetic m
ilk contentN
okiller: lactating
Yes
across associated breeders - faster offspring grow
thM
aybevictim
: unweaned/killed during
nursing attempt
Yes
within group infanticide
- allocarers presentYes
killer: gestating/lactatingYes
across pair breeders - higher offspring to carer ratio
Yesvictim
: dependent on careYes
within group infanticide
- nepotistic hierarchy presentYes
killer: high social rankYes
across social breeders - evictions occur
Yesvictim
: any ageYes
H2.4: over social status
Core prediction(s)
Support?Support?
Hypothesis
H1: exploitation
H2: resource com
petition
H2.1: over space
H2.2: over m
ilk
H2.3: over allocare
14
-1.5(benign)
2.5(harsh)
environmental harshness
infanticide by females
absentpresent
5% 25% 100% 1000%
maternal energetic investmentinfanticide by fem
alesabsent
present
a)b)
Figure2:Factorsassociatedwithfem
alecompetitionandthedistributionofinfanticidebyfem
ales
Speciesinwhichfem
aleinfanticideispresentare,onaverage,characterizedby(a)livinginharsherenvironments(low
erandmoreunpredictable
rainfallandtemperatures)andby(b)higherm
aternalenergeticinvestment(totalm
assofweanedoffspringproducedperyearrelativetom
aternal
mass).Blacklinesindicatethem
edianacrossthespeciesinthesample,boxescontain75%
ofthevalues,andwhiskersextendtotheextrem
es.
15
H1:Exploitation
Wefindnosupportforpredictionssuggestingthatfemaleskillconspecificoffspringprimarily
forexploitation (Table2).Across species, infanticideby females isas likely tooccur in the
absenceofinfanticidebymales(44of147species,30%)asinitspresence(43of135species,
32%)(effectofpresenceofmaleinfanticideonpresenceoffemaleinfanticide2.1,95%CI-
13.5–16.9,p=0.74).Similarly,carnivorousspeciesarenotmorelikelytoshowinfanticideby
females(18of56species,32%)thaninspeciesinwhichmeatdoesnotconstituteanimportant
partofthediet(59of192species,31%)(effectofcarnivoryonpresenceoffemaleinfanticide
-0.7,95%CI-11.2–10.0,p=0.89).Theageofvictimsvariesfrombirthtobeyondindependence
acrossspecies,butismorehomogeneouswithineachtypeofinfanticide(seebelow),sothat
killingsdonotappearsimplyopportunistic.
H2:Resourcecompetition
Infanticide by females appearsmore likely to occur where competition over resources is
expectedtobemoreintense(Table2).Theclimaticenvironmentsofspeciesinwhichfemales
commit infanticide are harsher (as estimated by a principal component reflecting low
unpredictablerainfallandcoldseasons)thantheenvironmentsofspeciesinwhichinfanticide
hasnotbeenobserved(effectofenvironmentalharshnessonpresenceoffemaleinfanticide
7.0,95%CI -0.2–14.7,p=0.03,54specieswith infanticideand193without)(Figure2a). In
specieswhere females commit infanticide, they invest substantiallymore energy into the
productionofoffspring,beingable toproduce theequivalentof1.0 times theirownbody
massinoffspringmassperyear(numberofoffspringtimesmassofweanedoffspring;median
across 41 species, range 0.05 – 12.1 times) compared to 0.33 times in species in which
infanticidehasnotbeenobserved (medianacross77species, range0.03–11.1) (effectof
16
maternal energetic investment onpresenceof female infanticide 25.8, 95%CI 1.5 – 58.7,
p<0.001)(Figure2b).
H2.1:Competitionoverbreedingspace
Thirty-twoofthe33speciesinwhichfemaleskilljuvenilesoutsidetheirownhome-rangekeep
theiroffspringinburrowsorholes,comparedto93ofthe163speciesinwhichinfanticideby
femalesappearsabsent(effectofburrowuseonthepresenceofinfanticidebyfemales14.4,
95% CI 6.0 – 22.9, p<0.001). The exception is Semnopithecus entellus, where “females
occasionally steal infants from a neighboring troop” [Hrdy 1976; Mohnot 1980]. In most
species in which females kill offspring in neighbouring home-ranges (25 of 33), females
generallyappearnottotolerateotherbreedingfemalesclosebyandmosthome-rangesonly
containasinglebreedingfemale(solitaryorcooperativelybreedingspecies),whileinmost
otherspecies females formassociationsorgroups (home-rangescontaina singlebreeding
femalein105outof268species)(effectofpresenceofasinglebreedingfemaleperhome-
rangeonpresenceofinfanticidebyfemales12.4,95%CI0.3–30.1,p=0.007).Inallcases,the
killerwaseitherpregnantorhaddependantyoungofherown(17specieswithobservations),
andalloffspringthatwerekilledwerenotyetweaned(17species).
H2.2:Competitionovermilk
Acrossassociatedbreeders, theenergycontentofmilkproducedbymothers in species in
which females have been observed to kill offspring within the same breeding space (2.8
MJ/100ml,medianacross8 species, range1.2-4.7) doesnotdiffer from thatof species in
whichsuchkillingshavenotbeenobserved(2.1MJ/100ml,medianacross7species,range
0.8-5.7)(meaneffectofmilkenergyonpresenceofinfanticidebyfemales2.0,95%CI-66.3–
17
83.1,p=0.97).Inassociatedbreederswithfemaleinfanticide,offspringdonotseemtohave
greater growth rates (they gain on average 0.28% of their adult bodymass per day until
weaning,medianacross9species,range0.04%-1.72%)thaninspeciesinwhichfemaleshave
notbeenobservedtokilljuveniles(offspringgainonaverage0.17%oftheiradultbodymass
perdayuntilweaning,medianacross11species,range0.05%-0.73%)(effectofpresenceof
infanticidebyfemalesonoffspringgrowthrate6.1,95%CI-16.2–35.4,p=0.59).Killersare
eitherpregnantorhavedependantyoung(21outof21species)andareold,withmostreports
suggesting that they had been observed to give birth in previous years (they are not
primiparous).Allvictimswerereportedtobeunweaned(22outof22species).In7outof14
infanticidereportsfromassociatedbreeders,victimswerekilledastheyattemptedtobreast-
feedfromthekiller.
H2.3Competitionoverallomaternalcare
Infanticidebyfemalesinpairbreedersoccursonlywhenfathersprovidecare(all16species)
whilefatherscareforoffspringinonly16ofthe39pairbreedingspeciesinwhichthisformof
infanticideisabsent.In15ofthe16pairbreederswithfemaleinfanticide,additionalhelpers
arepresent(cooperativebreeders),whilethereareonlyafurther7cooperativelybreeding
species in which females have not been observed to kill juveniles from their own group
(femaleinfanticideoccursin68%[15/22]ofcooperativebreedersversusin4%[1/23]ofpair
breeders in which there are no other helpers). Across species in which offspring receive
allocare,thenumberofpotentialallocarersishigherinspecieswith(3allocarerspergroup,
medianacross15species,range2-23)comparedtospecieswithout(2allocarerspergroup,
medianacross13species,range1-20)femaleinfanticide(effectofnumberofallocarerson
presenceofinfanticide25.3,95%CI1.9–48.6,p=0.02).Thekillerwasusuallythedominant
18
breeder(aswasregularlythecasein9of12species)andwaspregnantorwithdependent
infantsinallcases.Inmostinstancesthekillerandthevictimbelongedtothesamegroup(11
of14species),andwereconsequentlyrelated(10outof13species).Victimswereoftenafew
daysoldandalldependent.
H2.4:Competitionoversocialstatus
Ofthe27socialbreederswithfemalephilopatry(andavailabledata),femalegroupmembers
donotformsocialhierarchiesinthreespecies,hierarchicalrankisdeterminedbyageinfive
species,andrankisinfluencedbynepotismin19species.Femaleshavebeenobservedtokill
offspringborntoothergroupmembersineightoftheselatter19species,butinnoneofthe
specieswherenepotismdoesnotinfluencefemalerank(effectofpresenceofnepotisticrank
acquisition on presence of infanticide by females 134.1, 95% CI 28.8 – 238.1, p<0.001).
Femalesaremorelikelytokilloffspringborntootherfemalesinsocialbreedersinwhichthey
alsoaggressivelyevictotherfemalesfromtheirgroup(infanticidehasbeenobservedin6of
10specieswithevictionsand7of35withoutevictions)(effectofoccurrenceofevictionson
presenceofinfanticidebyfemales7.8,95%CI-0.2–14.4,p=0.02).Inalltwelvesocialbreeders
inwhichinfanticideeventshavebeenobserved,killerswereoldandhigh-ranking.Killerswere
neverpregnant, but in all caseshaddependant youngof their own.Victimswerenot yet
weaned,andin5outof12speciesvictimsmightberelatedtothekiller.Thereisonlyone
specieswherethedatasuggestthatfemalesmightpreferentiallykilloffspringofonesex:in
Macaca radiata (a species with female philopatry), female offspring appear to be the
predominantvictims.
19
Discussion
Ourfindingsestablishthatfemalecompetitioniswidespreadacrossmammalsandthatitis
frequentlyexpressedasintenselyascompetitionamongmales.Femaleshavebeenobserved
tokillconspecificjuvenilesinvariousspeciesandourcomparativeanalysesprovidesupport
to the idea that this behaviour may be adaptive under a wide range of circumstances.
Infanticide ismore likely tooccur in species inwhichmultiple adult females liveorbreed
togetherthanwherefemalesbreedsolitarily,andinfanticideappearsmostfrequentinspecies
where females only associate temporarily to breed. This may reflect the fact that
opportunitiestocommitandtoobserve infanticidesmaybegreaterwherefemales liveor
breedtogether.Withineachtypeofsocialorganisation,wedohoweverfindthatfemales,like
males,appeartocommitinfanticidewhenthepresenceofthevictimmightotherwiselimit
theirownreproductivesuccess.Whileinfanticidebymaleshasevolvedinresponsetoasingle
cause -mate competition - acrossmammals [Lukas&Huchard 2014; Palombit 2015], the
evolutionarydeterminantsofinfanticidebyfemalesareapparentlymorecomplex,asfemales
maycompeteovermultipleresources.
Several lines of evidence support this adaptive scenario of resource competition for the
occurrenceof infanticideby females.First, infanticideappearsassociatedwithvariation in
ecologyand life-history. Specifically, it ismost frequentlyobserved in species facingharsh
climatic conditions and making the greatest reproductive efforts; it is unlikely that such
associationsareduetovariationsinopportunitiestoobserveorcommitinfanticidesacross
species. Rather, the potential costs of sharing critical resourcesmight outweigh the risks
associatedwithcommittinginfanticideinsuchcircumstances.
20
Second, specific ecological determinants of female infanticide identified at the population
level by field studies also seem to predict its distribution across species. Extraterritorial
infanticideswerefoundtobemostfrequentinsolitaryspecieswherefemalesuseburrowsto
givebirthandterritoriestoraiseoffspring,allowingkillerstofree-upreproductivespacefor
theirownoffspring.Ourfindingsfurthershowthatfemaleinfanticideoccursinpairbreeders
wherehelpers–fathersoradditionalgroupmates-arepresent.Finally,patternsareslightly
more complex in social breeders. There, infanticidepreferentially occurs in specieswhere
aggressivecompetitionamongfemalesleadstotheevictionofsomeindividuals–generally
youngadults-fromthegroup,especiallyattimeswhengroupsizeincreases(e.g.[Kappeler
&Fichtel2012]).Insuchcases,killingunrelatedjuvenilesmaylimitfuturecompetitionand
therelatedriskofbeingevictedforthekiller’soffspring.Inaddition,insocialbreederswhere
femalesarephilopatric,infanticidewasonlyfoundtooccurwherefemalerankacquisitionis
nepotistic,ahierarchicalsystemwhereeachadditionaloffspringmaycontributetostrengthen
thesocialstatusofamatriline–andwhereinfanticidemayconsequentlyweakencompeting
matrilinesonthelongterm.
Anecdotalreportsoffemalepinnipedskillingorphansastheyattemptedtobreast-feedfrom
them inspired the hypothesis that females compete overmilk in specieswhere they only
associatetobreed[Digby2000].Whileourcomparativeanalysesdidnotrevealanydifference
in theenergycontentofmilkofassociatedbreeders inwhich infanticide ispresentversus
absent, associated breeders nevertheless comprise the species with the highest energy
contentofmilkandthefastestgrowthrates,andwefurtherfoundthatoffspringareweaned
atanearlierageinassociatedbreederswithinfanticidecomparedtothosewithoutit.The
lackofsupport forthemilkcompetitionhypothesis inouranalysesmaybeexplainedbya
21
noisydataset,wheretheabsenceofinfanticideinsomespeciesmaybeduetothefactthatit
goes undetected if it is hard to observe, or to the evolution of counter-adaptations that
protectoffspringagainstinfanticide.Alternatively,milkisnottheonlyresourceoverwhich
these femalescompete.Forexample, in the largebreedingcoloniesofpinnipeds, space is
sometimesveryrestricted[Baldietal.1996],especiallyintheimmediatevicinityoftheharem
leaders.Thesebullsoftenprotecttheirfemalesandcalvesfromattacksbyyoungermales,and
mayrepresentanothersourceofcompetitionforlactatingfemales.
It is likely that, in any given species, infanticide may be triggered by more than one
determinant-includingsomethatmaynotbeconsideredhere.Akillermayaccordinglyget
multiplebenefitsfromoneinfanticideevent,butmayalsocommitinfanticidesinmorethan
one context. For example, half of the species of pair breeders committing intra-group
infanticides also commit extraterritorial infanticides. It is therefore possible that different
types of female infanticide – following our classification - have followed a common
evolutionarypath.Specifically, it ispossible that infanticidalbehaviour initiallyemerged in
response to one particular pressure (e.g., competition over access to allocare) in a given
species,whichsubsequentlystartedtoextenditsexpressiontoothercompetitivecontexts
(e.g., competition over breeding territories). However, the limited number of species for
whichobservationaldataoninfanticideareavailable,aswellasheterogeneitiesinthesample
– such as an over-representation of group-living species – introduce uncertainty when
attemptingtoreconstitutetheevolutionaryhistoryofthetrait.Itisconsequentlyhardtoinfer
theancestralstate,whethereachinfanticidetypehasevolvedindependently,orhowmany
timesinfanticidalbehaviourhasemergedacrossmammals.
22
Inadditiontothenatureoftheresourcesthatmaydirectlylimitfemalereproductivesuccess
in various types of social organisations, contrasts in the occurrence of infanticide across
species reveal other broad patterns on female reproductive competition in mammals. In
particular,thelackofassociationbetweenfemaleinfanticideandphilopatryacrossspecies
(Table1),aswellasasynthesisofobservationsrevealingthatkillersandvictimsarecommonly
relatedinsomecontexts,suchasinpairbreederswherereproductivesuppressioniscommon
[Lukas&Clutton-Brock2018],suggestthatmatrilinealityandsubsequentincreasesinaverage
kinshipamongassociated femalesdoesnotnecessarily lead toa reduction in competition
among females. Some previous work suggested that mammalian females might be
predisposedtobehavepositivelyandcooperativelywithkin[diFiore&Rendall1994],such
thatspecieswithfemalephilopatrywouldbecharacterizedbystablesocialbonds[Silk2007].
However,thefactorsleadingtolimiteddispersalandthespatialassociationofkinfrequently
alsoresultinhighlocalcompetition[Frank1998]whichcanovercomethepotentialbenefits
ofcooperationamongkin [Westetal.2002].Studiesofcompetitionamongmales insuch
circumstanceshaveshownthatcontrastsinlevelsofaggressioncanbeexplainedbyvariation
inthepotentialdirectfitnessbenefitsofwinning[Westetal.2001],anditislikelythatthis
alsoappliestotheobservedpatternofinfanticidebyfemales–wherethedirectbenefitsof
infanticide in terms of increased access to a critical resource might outweigh its costs,
includingtheindirectfitnesscostsassociatedwithkillingrelatedjuveniles.
Ourstudycompilesfivedecadesofbehaviouraldataacrossspeciesandwithinpopulationsto
elucidate the determinants of infanticide by mammalian females, which are less well
understood than those of male infanticide. Our analyses suggest that the distribution of
female infanticide across species is a consequence of contrasts in social organisation;
23
infanticide is most frequent in species that breed in groups, which probably have more
opportunities for killings and also face greater breeding competition. Female infanticide
occurswheretheproximityofconspecificoffspringdirectlythreatensthekiller’sreproductive
successby limitingaccess to critical resources forherdependentprogeny, including food,
shelters, care or a social position. Finally, these data support the idea that female killers
occasionally sacrifice related juvenile conspecifics, andmay therefore actively harm their
indirectfitnessinordertomaximizetheirdirectfitness.
Acknowledgements
We thank Tim Clutton-Brock, Peter Kappeler, Oliver Höner and Eve Davidian for useful
discussions.
DataAccessibility
All data are provided in the supplementarymaterial and are deposited at the Knowledge
NetworkforBiocomplexitydoi:10.5063/F1ZG6QFR.
Authors’Contributions
Bothauthorscontributedtotheconceptionanddesignofthestudy,collectedandinterpreted
thedata,wrotethearticle,andgavefinalapproval;theanalysesweredonebyDLwithinput
fromEH.
CompetingInterests
Wehavenocompetinginterests.
24
Funding
DLwassupportedbytheEuropeanResearchCommission(grant294494-THCB2011toProf.T.
Clutton-Brock)andtheMaxPlanckSociety.EHwasfundedbytheANR(grantANR-17-CE02-
0008)duringthewriting-upofthismanuscript.
SupplementaryMaterial
This submission includes all data in Supplementary Tables 1 (comparative data) and 2
(population observations), with references for observations on infanticide by females in
SupplementaryFile1,andcreditsfortheanimaldrawingsusedinFigure1inSupplementary
File2.
References
1. Clutton-BrockT.2007SexualSelectioninMalesandFemales.Science318,1882–1885.(doi:10.1126/science.1133311)
2. Clutton-BrockT,HuchardE.2013Socialcompetitionanditsconsequencesinfemalemammals.J.Zool.289,151–171.(doi:10.1111/jzo.12023)
3. Clutton-BrockTH,HuchardE.2013Socialcompetitionandselectioninmalesandfemales.Philos.Trans.R.Soc.BBiol.Sci.368.(doi:10.1098/rstb.2013.0074)
4. StockleyP,Bro-JørgensenJ.2011Femalecompetitionanditsevolutionaryconsequencesinmammals.Biol.Rev.Camb.Philos.Soc.86,341–366.(doi:10.1111/j.1469-185X.2010.00149.x)
5. EmlenST,OringLW.1977Ecology,sexualselection,andtheevolutionofmatingsystems.Science197,215-223.(doi:10.1126/science.327542)
6. ConnorRC,KrützenM.2015MaledolphinalliancesinSharkBay:changingperspectivesina30-yearstudy.Anim.Behav.103,223-235.(doi:10.1016/j.anbehav.2015.02.019)
7. Clutton-BrockTH.2016MammalianSocieties.NewYork:WileyandSons.
8. YoungAJ,Clutton-BrockT.2006Infanticidebysubordinatesinfluencesreproductivesharingincooperativelybreedingmeerkats.Biol.Lett.2,385–387.(doi:10.1098/rsbl.2006.0463)
25
9. Clutton-BrockTHetal.2001Cooperation,Control,andConcessioninMeerkatGroups.Science291,478–481.(doi:10.1126/science.291.5503.478)
10.PalombitR.2012Infanticide:malestrategiesandfemalecounter-strategies.InTheEvolutionofPrimateSocieties,pp.432–468.Chicago:MitaniJC,CallJ,KappelerPM,PalombitRA,SilkJB.
11.vanSchaikCP,JansonCH.2000InfanticidebyMalesandItsImplications.CambridgeUniversityPress.
12. LukasD,HuchardE.2014Theevolutionofinfanticidebymalesinmammaliansocieties.Science346,841–844.(doi:10.1126/science.1257226)
13.PalombitRA.2015InfanticideasSexualConflict:CoevolutionofMaleStrategiesandFemaleCounterstrategies.ColdSpringHarb.Perspect.Biol.7.(doi:10.1101/cshperspect.a017640)
14.DigbyL.2000Infanticidebyfemalemammals:implicationsfortheevolutionofsocialsystems.InInfanticidebymalesanditsimplications,vanSchaikCPandJansonCH.
15.BlumsteinD.2000Theevolutionofinfanticideinrodents:acomparativeanalysis.pp.178–198.Cambridge:vanSchaikCPandJansonCH.
16.AgrellJ,WolffJO,YlönenH.1998Counter-StrategiestoInfanticideinMammals:CostsandConsequences.Oikos83,507–517.(doi:10.2307/3546678)
17.KleimanDG,MalcolmJ.1981TheEvolutionofMaleParentalInvestmentinMammals.InParentalcareinmammals,GübernickDJ;KlopferPH.
18.GoodallJ.1986ThechimpanzeesofGombe:patternsofbehavior.BelknapPressofHarvardUniversityPress.
19.HooglandJL.1985Infanticideinprairiedogs:lactatingfemaleskilloffspringofclosekin.Science230,1037–1040.(doi:10.1126/science.230.4729.1037)
20.ShermanP.1981ReproductivecompetitionandinfanticideinBelding’sgroundsquirrelsandotheranimals.InNaturalandSocialBehavior:RecentResearchandNewTheory,AlexanderRD,TinkleDW.
21.BoeufBJL,WhitingRJ,GanttRF.1973PerinatalBehaviorofNorthernElephantSealFemalesandTheirYoung.Behaviour43,121–156.(doi:10.1163/156853973X00508)
22.GilchristJS.2006Femaleeviction,abortion,andinfanticideinbandedmongooses(Mungosmungo):implicationsforsocialcontrolofreproductionandsynchronizedparturition.Behav.Ecol.17,664–669.(doi:10.1093/beheco/ark012)
23.CantMA,NicholsHJ,JohnstoneRA,HodgeSJ.2014Policingofreproductionbyhiddenthreatsinacooperativemammal.Proc.Natl.Acad.Sci.111,326–330.(doi:10.1073/pnas.1312626111)
26
24.DigbyL.1995Infantcare,infanticide,andfemalereproductivestrategiesinpolygynousgroupsofcommonmarmosets(Callithrixjacchus).Behav.Ecol.Sociobiol.37,51–61.(doi:10.1007/BF00173899)
25.HrdySB.1976CareandExploitationofNonhumanPrimateInfantsbyConspecificsOtherThantheMother.InAdvancesintheStudyofBehavior(edsJSRosenblatt,RAHinde,EShaw,CBeer),pp.101–158.AcademicPress.(doi:10.1016/S0065-3454(08)60083-2)
26.WasserSK,&BarashDP.1983Reproductivesuppressionamongfemalemammals:implicationsforbiomedicineandsexualselectiontheory.Quart.Rev.Biol.58,513-538.(doi:10.1086/413545)
27.AgrellJ,WolffJO&YlönenH.1998Counter-strategiestoinfanticideinmammals:costsandconsequences.Oikos83,507-517.(doi:10.2307/3546678)
28.EbenspergerLA.1998Strategiesandcounterstrategiestoinfanticideinmammals.Biol.Rev.73,321-346.
29.EbenspergerLA&BlumsteinDT.2007Nonparentalinfanticide.In:Rodentsocieties:anecologicalandevolutionaryperspective(eds.JOWolff&PSherman),pp.267-279.UniversityofChicagoPress,Chicago.
30.StockleyP&Bro-JørgensenJ.2011Femalecompetitionanditsevolutionaryconsequencesinmammals.Biol.Rev.86,341-366.
31.HrdySB.1976CareandExploitationofNonhumanPrimateInfantsbyConspecificsOtherThantheMother.InAdvancesintheStudyofBehavior(edsJSRosenblatt,RAHinde,EShaw,CBeer),pp.101–158.AcademicPress.(doi:10.1016/S0065-3454(08)60083-2)
32. LukasD,Clutton-BrockT.2017Climateandthedistributionofcooperativebreedinginmammals.R.Soc.OpenSci.4,160897.(doi:10.1098/rsos.160897)
33. LukasD,Clutton-BrockTH.2011Groupstructure,kinship,inbreedingriskandhabitualfemaledispersalinplural-breedingmammals.J.Evol.Biol.24,2624–2630.(doi:10.1111/j.1420-9101.2011.02385.x)
34.WilmanH,BelmakerJ,SimpsonJ,delaRosaC,Rivadeneira,MM,JetzW.2014EltonTraits1.0:Species-levelforagingattributesoftheworld'sbirdsandmammals.EcologicalArchivesE095-178.Ecology95,2027-2027.(doi:10.1890/13-1917.1)
35.BoteroCA,DorR,McCainCM,SafranRJ.2014Environmentalharshnessispositivelycorrelatedwithintraspecificdivergenceinmammalsandbirds.Mol.Ecol.23,259–268.(doi:10.1111/mec.12572)
36.SiblyRM,GradyJM,VendittiC,BrownJH.2014Howbodymassandlifestyleaffectjuvenilebiomassproductioninplacentalmammals.Proc.Roy.Soc.B281,20132818.(doi:10.1098/rspb.2013.2818)
37. JonesKEetal.2009PanTHERIA:aspecies-leveldatabaseoflifehistory,ecology,andgeographyofextantandrecentlyextinctmammals.Ecology90,2648–2648.(doi:10.1890/08-1494.1)
27
38. LangerP.2008Thephasesofmaternalinvestmentineutherianmammals.Zoology111,148–162.(doi:10.1016/j.zool.2007.06.007)
39.BartonRA,CapelliniI.2011Maternalinvestment,lifehistories,andthecostsofbraingrowthinmammals.Proc.Natl.Acad.Sci.U.S.A.108,6169–6174.(doi:10.1073/pnas.1019140108)
40.HindeK,MilliganLA.2011Primatemilk:proximatemechanismsandultimateperspectives.Evol.Anthropol.20,9–23.(doi:10.1002/evan.20289)
41.RollandJ,CondamineFL,JiguetF,MorlonH.2014FasterSpeciationandReducedExtinctionintheTropicsContributetotheMammalianLatitudinalDiversityGradient.PLOSBiol.12,e1001775.(doi:10.1371/journal.pbio.1001775)
42.HadfieldJD,NakagawaS.2010Generalquantitativegeneticmethodsforcomparativebiology:phylogenies,taxonomiesandmulti-traitmodelsforcontinuousandcategoricalcharacters.J.Evol.Biol.23,494–508.(doi:10.1111/j.1420-9101.2009.01915.x)
43.HadfieldJ.2010MCMCglmm:MarkovchainMonteCarlomethodsforgeneralizedlinearmixedmodelsretrievedfromcran.uvigo.es/web/packages/MCMCglmm/vignettes/Tutorial.pdf
43. LukasD&Clutton-BrockT.2018Socialcomplexityandkinshipinanimalsocieties.Ecol.Lett.21,1129-1134.(doi:10.1111/ele.13079)
44.MohnotSM.1980IntergroupinfantkidnappinginHanumanlangur.FoliaPrimatol.(Basel)34,259–277.(doi:10.1159/000155958)
45.KappelerPM,FichtelC.2012FemalereproductivecompetitioninEulemurrufifrons:evictionandreproductiverestraintinaplurallybreedingMalagasyprimate.Mol.Ecol.21,685–698.(doi:10.1111/j.1365-294X.2011.05255.x)
46.BaldiR,CampagnaC,PedrazaS,LeBoeufBJ.1996SocialeffectsofspaceavailabilityonthebreedingbehaviourofelephantsealsinPatagonia.Anim.Behav.51,717–724.(doi:10.1006/anbe.1996.0075)
47.DiFioreA,RendallD.1994Evolutionofsocialorganization:areappraisalforprimatesbyusingphylogeneticmethods.Proc.Natl.Acad.Sci.U.S.A.91,9941–9945.(doi:10.1073/pnas.91.21.9941)
48.SilkJB.2007SocialComponentsofFitnessinPrimateGroups.Science317,1347–1351.(doi:10.1126/science.1140734)
49.Frank,SA.1998FoundationsofSocialEvolution.PrincetonUniv.Press,Princeton.
50.WestSA,PenI,GriffinAS.2002Cooperationandcompetitionbetweenrelatives.Science296,72–75.(doi:10.1126/science.1065507)
51.WestSA,MurrayMG,MachadoCA,GriffinAS,HerreEA.2001TestingHamilton'srulewithcompetitionbetweenrelatives.Nature409,510-513.(doi:10.1038/35054057)