Original article
Colony aggregations in Apis mellifera L
B Oldroyd A Smolenski S Lawler A Estoup R Crozier
1 School of Genetics and Human Variation, La Trobe
University,
Bundoora, Victoria 3083;2Division of Science, La Trobe
University, Albury-Wodonga Campus,
Wodonga, Victoria 3689, Australia;3CNRS, laboratoire de
biologie et génétique
évolutives,avenue de la Terrasse, 91198 Gif-sur-Yvette, France
(Received
28September
1994;accepted
27January 1995)
Summary —
Naturalaggregations
of A mellifera L have not beenreported.
However, in the related species A dorsata,aggregations
of colonies are common. A survey of thespatial
distribution of feral A mellifera colonies showed that they too can be markedlyclumped,
with up to 10 colonies/ha. For these heavilyclumped
colonies, we inferred queen genotype from workersamples
for:1)
malate de-hydrogenase; 2)
a mitochondrial DNApolymorphism;
and3)
a microsatellite locus. Theaggregation
examined was
composed
of colonies headedby potentially
related(ie parent/offspring
orsister)
queens, and unrelated colonies. Thus, it is
likely
thatexisting
colonies attract swarms and that swarms may notalways
travel far from the natal nest in an environment that is replete with nesting sites.Apis
mellifera/ Apis
dorsata/ swarming
/ nest site / Nasonovpheromone / genetic
relationships / microsatellite / mitochondrial DNAINTRODUCTION
This
study
wasprompted by
a casual obser- vation in a caravanpark
inDevonport,
Tas-mania,
Australia of 12 colonies of feralhoney
bees(Apis mellifera)
all within 200 m of each other(Oldroyd
etal, 1995).
Thisseemed an
extraordinary density
ofhoney
bees. Densities of feral colonies are
typi- cally
estimated as 0.5-5colonies/km 2 (reviewed by
Ratniekset al, 1991; Oldroyd et al, 1994). Aggregations
arecompletely unexpected
on the basis of Lindauer’s(1961)
comment thathoney-bee
swarmsprefer
distant nest sites tonearby
ones, andthe observation of Hubell and Johnson
(1977)
thatstingless
bee nests have a uni-form rather than a random or
clumped
spa- tial distribution. We thereforesurveyed
apopulation
of feralhoney
bees to determinehow often
aggregations
of colonies occur in thespecies.
The distance travelled
by
swarms to nat-ural nest sites can be inferred
by measuring
the dance
tempo
of the consensus dancesjust prior
to thedeparture
of the swarm forthe new nest.
(The
dancetempo
encodes the distance of thepotential
nest site fromthe swarm
(von Frisch, 1967).)
On thisbasis,
most natural swarms move 500-1 500 m
from the natal nest
(Lindauer, 1951, 1955;
Seeley and Morse, 1977), although
scoutshave been
reported
to dance for nest sitesover 10 km from the natal nest
(Villa, 1993).
Lindauer
(1955) suggested
that swarmsaware of 2 nest sites of
equal
value select the more distant 1 to move to.However,
this conclusion wasquestioned by Seeley
and Morse
(1977)
andJaycox
and Parise(1980, 1981). They
showed that under con-trolled conditions where swarms were
offered nest cavities of
equal
merit at dif-ferent distances from the
cluster,
swarms had apreference
for the nearest nest site.If,
asJaycox
and Parise(1980, 1981)
and
Seeley
and Morse(1977) suggest,
swarm movement is small when there is an
abundance of suitable cavities near the clus- tered swarm, then
aggregations
of relatedcolonies in
cavity-rich
environments would result.Aggregations
causedby
limitedswarm
dispersal
wouldcomprise
afamily
group. On the other
hand,
if swarms areattracted to
existing
colonies distant from the natal nest, thenaggregations
wouldcomprise
unrelated colonies.In A
mellifera,
noaggregations
of any kind have beenreported.
Thisimplies
thatnatural swarms have a
greater tendency
todisperse
thanJaycox
and Parise(1980, 1981) suggest,
that suitable nest sites are rare in mostenvironments,
orsimply
thatsystematic
searches forhoney-bee
nestshave not revealed the
phenomenon.
In the related
species A dorsata,
thegiant honey
bee ofAsia, aggregations
of coloniesare common
(Seeley
etal, 1982; Seeley, 1985,
p150).
Colonies tend toaggregate
in groups of 2-60 under a
single
rockledge
or on a
single
tree(Koeniger
andKoeniger, 1980).
Theseaggregations
are not due tolimitations of available nest sites. Trees of identical form and
species
but with no Adorsata colonies are often found next to trees with
large
numbers of nests(personal
observation,
but seeSeeley et al, 1982).
Itis not known if these
aggregations
are afamily
group or arecompletely
unrelated.In this
study
wereport
thespatial
distri-bution of 28 feral A mellifera colonies found in a survey of seven 500 x 100 m
plots
in amixed
Eucalyptus
camaldulensis(red gum)
and
E largiflorens (black box)
woodland. Anextremely
dense naturalaggregation
of 10colonies was selected and
genetic
markerswere used to infer
genetic relationships
among these colonies to see ifthey
com-prised
afamily
group or a random aggre-gation.
MATERIALS AND METHODS
Study
sites andcolony
locationThis
study
was conducted inWyperfeld
National park in north-west Victoria, Australia.Beekeeping
is prohibited in the
park,
butOldroyd et al (1994)
estimated that there are 77 feral colonies/km2,
in the 0.5-1 km wide band of E camaldulensis / E
largiflorens
woodland that borders thedry
creekbed that passes
through
thepark.
This is anextremely high density
of feral bee colonies(Otis,
1990; Ratnieks et al,1991), and
reflects the very favourable environment forhoney
bees. The dis- tribution of mallee(Eucalyptus spp)
and banksia(Banksia ornata)
species provide anexceptionally
rich and varied nectar and
pollen
resource(Oldroyd
et al,1994). Oldroyd et al (1994)
esti-mated that there are up to 11 000 hollows/km2 in the black box and red gum trees that line the creek, and that many of these are suitable cavities for
honey-bee
nests.Despite occupation by
native fauna, it seems veryunlikely
that hollows are alimiting
resource for bees.Seven 500 x 100 m sites were
pegged
outwith metal fence posts
(see Oldroyd
et al, 1994, for a fulldescription).
Sites were separatedby
atleast 0.5 km and up to 6 km
(fig 1).
Sites wereeach divided into five 10 000 m2sectors,
aligned
north/south.
In March and
April
1993, each tree in theplots
was
carefully
examined for the presence ofhoney-
bee colonies.
Only
2 species of tree exist in theplots
examined(red
gum and blackbox).
Mosttrees were 10-20 m
high,
with the occasional 30 m individual. Trees arequite sparsely
distributed.Thus bee colonies are
relatively
easy to locate.Trees were examined in fine weather when the
temperature exceeded 18°C, and known colonies were
foraging freely.
Each tree was carefullyexamined from 4 compass
points by
pairs ofobservers. To ensure careful observation, a sketch was made of each of the 1 982 trees within the plots. The number of hollows
(defined
as ahole that
might potentially
lead to adry cavity
of> 4
I volume)
was also recorded. When colonieswere found, their location was recorded. All trees were
carefully
re-examined inSeptember
1993 by a second pair of observers. The location of overwintered colonies was checked, and a fewcolonies missed in the first survey were located at that time. Sketch maps of the location of all colonies were then made.
Colony aggregations
Bees from a natural
aggregation
were obtained fordetailed
genetic analysis,
to determine if theaggregation comprised
of related colonies. Sam- ple bees werecaught
eitherby aspiration
of beesat the entrance, or
by
the use of ladders andlong-
handled insect nets. Bees were frozen in
liquid nitrogen,
and stored at -70°C untilrequired.
Protein and DNA extraction
Frozen thoraces from 8-24
(usually 12)
bees percolony
were eachground
in 100μl
distilled water in a 1.5 mlmicrocentrifuge
tube. Ten microlitres of supernatant was removed and reserved for protein electrophoresis. Theremaining
materialwas used for extraction of total nucleic acid
by
the method outlined in
Oldroyd et al (1995).
DNAwas resuspended in 50 ml of 1 x Tris-EDTA buffer.
Protein
electrophoresis
The 10
μl
crude extracts wereelectrophoresed
for 20 min on cellulose-acetate
gels (Helena
Lab- oratories, Beaumont, TX,USA)
at 200 V in a 0.08 M Tris-EDTA-maleic acidrunning
buffer (pH8.2).
Malatedehydrogenase isozymes (Sylvester,
1976; Cornuet,1979)
were visualisedby coating
gels
with 8 ml 1% molten agar to which 0.6 ml 0.1 M Tris-HCl(pH 8.0),
0.4 ml each of 0.04 M nicotinamide adenine dinucleotide and 1 M di-sodium malate
(pH 7.0),
and 0.2 ml each of 0.145 Mmethylthiazoyle
blue and 0.065 Mphenazine methosulphate
had been added. Three alleles were scored as S, M and Faccording
tothe amount of anodal
migration.
Where geno- types wereambiguous, they
were re-runagainst
known standards on the same
gel.
Microsatellites
One primer of the microsatellite locus A107
(Estoup
et al,1994)
wasradioactively
end-labelled. In a total reaction volume of 10
μl,
the γ-phosphate
from 33P-dATP(Dupont)
was trans-ferred to the 5’-terminus
primer-2, using
T4polynucleotide
kinase(Promega).
The reaction contained 70 mM Tris-HCl, 10 mMMgCl 2 ,
2 μMprimer,
5μl 33 P-dATP,
and 4 units ofpoly-
nucleotide kinase. The reaction was incubated for 30 min at 37°C and was
stopped by heating
to90°C for 2 min.
Polymerase
chain reactions(PCRs)
were per- formed in 10μl
of a mixturecontaining
1μl
ofundiluted
sample
DNA, 0.167 mM of each dNTP,1 μg BSA, 0.4
μM
unlabelled primer, 0.02μM
labelled
primer,
1 xPromega
reaction buffer and0.4 units of
Promega Taq polymerase.
PCR tem- peratureprofiles
for microsatellite A107 weregiven
inEstoup et al (1994).
PCR products wererun on standard 6%
polyacrylamide sequencing gels
with M13 control DNAsequencing
reactionsrun on the same
gel
as size standards. Microsatel- lite alleles were scored asfragment lengths
inbase pairs.
Mitochondrial DNA
The
region
between the NDII-COII genes of thehoney-bee
mitochondrial genome contains a HincII restriction site in some individuals but not in others. PCRs wereperformed
in a Perkin-Elmer 480thermocycler using
thefollowing
primersdesigned
from Crozier and Crozier(1993):
5’TCCCACAAATAAAACCCCAAGATT 3’
5’ CCACAAATTTCTGAACATTGACC 3’
which flank the
region
between NDII and COII.The reaction mixture
(total
volume 50μl)
con-tained 1
μl
of undilutedsample
DNA, 25pmol
ofeach
primer,
10 nmol of each dNTP, 0.8 units ofTaq
polymerase (Promega)
and 1.5 mMMgCl 2 .
A
ramped
temperatureprofile
wasperformed
withthe
following
steps: 92°C 1 min, 45°C 1 min, ramp to 64°C over 2 min, hold 1.5 min(10 cycles);
ramp to 92°C over 1 min, hold 0.5 min, 45°C 1
min, ramp to 64°C over 2 min, hold 3 min
(5 cycles);
ramp to 92°C over 1 min, hold 0.5 min, 45°C 1 min, ramp to 70°C over 3 min, hold 2 min(15 cycles).
Five microlitres of PCR product were
digested
with 5 units of HincII
(Promega)
in a total volumeof 25
μl according
to the manufacturer’s direc- tions.Digests
were electrophoresed in 1%agarose
gels
for 2 h at 70 V, and stained with ethidium bromide. Two patterns were discernible,1 with 2 bands
(scored
as typeA),
and 1 with asingle
band(type B).
Analysis of genetic
dataEach queen genotype was inferred from her worker genotypes for MDH and A107
by
the fol-lowing
rules:i)
ahomozygous
worker infers that the queen carries that allele;ii)
two workershomozygous
for 2 different alleles means thatthe queen is
heterozygous
for those 2 alleles;iii)
if an allele is present in all workers the queen is
probably homozygous
for that allele; andiv)
if allworkers carry one of 2 alleles, then the queen is
likely
to beheterozygous
for those 2 alleles. Incombination, these rules can almost
always
resolve cases which are
ambiguous by
asingle
rule. With the data set used, queen genotype
could be
unambiguously
inferred for all queens.From queen genotype, some assessment of the relatedness of colonies can be made. Off-
spring
queens must share the same mt-DNA typeand at least 1 allele at both the MDH and microsatellite loci as the parent queen. Super- sister queens will also share mt-DNA type and
at least 1 allele at each nuclear locus. Half-sister queens or
grand-daughter
queens may not share alleles at both loci, but will have the same mt- DNA type. Unrelated queens may or may not share nuclear loci and mt-DNA type.RESULTS
A total of 27 colonies were located in the survey area, a mean
(± se)
of 0.77 ± 1.21colonies per 10 000 m2
plot.
A mean of111.6 ± 50.0
(range 29-242)
hollows werepresent
in eachplot
and 56.6 ± 19.2(range 24-92)
trees. There werenon-significant
correlations between the number of bees and the number of hollows
(r = 0.26;
P >0.1)
and the number of trees(r = 0.30;
P >0.05)
perplot.
Thus variance in numbers of trees or hollows perplot
is insufficient toexplain
any variation incolony
numbers.The location of each
colony
within the 7plots
isgiven
infigure
2.By inspection,
thereappears to be a non-random distribution of
colonies,
with aparticularly strong
aggre-gation
in sector 4 ofplot
7(fig 2).
An addi-tional cluster of 9 colonies was located out- side the
plots by
fortuitousdiscovery (fig 1).
The usual way to determine if a
population
of
organisms
isspread randomly
or in aggre-gations
is to compare the distribution oforganisms
persampling
unit to the Poisson distribution(Ludwig
andReynolds, 1988).
The distribution of
organisms
isexpected
tofollow the Poisson distribution if the organ- isms are scattered
randomly
in the environ- ment, and thenegative
binomial distribution if theorganisms
areaggregated.
Theobserved distribution of colonies and the
expected
distributions under the 2 theoretical models aregiven
in table I.They
show thatthe observed distribution differs
significantly
from the Poisson distribution
(χ 5 2
=187.7,
P
< 0.001 )
but not from thenegative
binomialdistribution
(χ 4 2
=5.83,
P> 0.25).
Theseresults indicate that the colonies were
strongly aggregated
in theenvironment,
butshould be treated with some caution.
Because the
expected
values in the tails of the distributions are verylow,
inflated val-ues of
χ 2
areexpected (Sokal
andRohlf, 1981). If
classes with smallexpected
valueare
pooled
so the minimumexpected
valueis around
3,
there is nosignificant
differencebetween the observed
frequency
distribu-tion and those
expected
under the Poisson(χ
1
2
=1.0,
P> 0.5)
ornegative
binomial dis- tributions(χ 1 2
=0.21,
P> 0.75).
Ludwig
andReynolds (1988)
recommendthat these distribution tests should not be used if the number of
sampling
units is < 40,as in this case. For smaller number of sam-
pling units, they
recommend the index ofdispersion, ID,
which isequal
tos 2 /x where
s2 and x are the variance and mean of
colony
number between the 35 100 x 100 mplots.
From the data in tableI,
ID has the value1.9,
which islarger
thanunity,
andagain suggests
that the colonies arestrongly clumped. Ludwig
andReynolds (1988)
sug-gest
that ID valuescomputed
from < 30sampling
units are Poisson distributedand,
if this is so, the ID from these data issignif- icantly greater
thanunity, again suggesting
a
strongly aggregated
distribution of coloniesin the field
(χ 2 34 = 65.0,
P <0.01). If
ID val-ues are
computed
from more than 30 sam-pling units, Ludwig
andReynolds suggest
that ID can be tested for deviation from
unity
with the d statistic:
which tends to the normal distribution.
Again,
this statistic
strongly suggests
aclumped
distribution
(d=3.21, P < 0.01).
Although
all testssuggest
that thecolonies observed were
aggregated,
we rec-ommend cautious
interpretation.
The valid-ity
of tests of thesignificance
of ID values rests onassumptions
about their statisticaldistributions,
which may not be valid in this instance.Further,
the conclusion of aggre-gation
restssolely
on the very dense aggre-gation
of colonies in sector 4 of site 7(fig 2).
If this sector is excluded from theanaly-
sis then ID =
1.08,
which is notsignificantly
different from
unity (χ 2 33
=35.7,
P> 0.05).
The
genetic relationships
amongparental
queens in the
aggregation
at site 7 isgiven
in table II. The presence of 2 mitochondrial
types
demonstrates that there were at least 2lineages present. Only
queensheading
colonies 60 and 61, 56 and
62,
and 61 and 62 may behighly
related asparent-offspring
or
super-sister
queens. All other coloniesare more
distantly
related.DISCUSSION
This
study
is the first toreport
that a wildpopulation
of A mellifera colonies can form dense naturalaggregations.
Taber(1979) mapped
the location of 21 coloniesalong
the Verde river in Arizona.
Inspection
of hisfigure
1 alsosuggests
a non-random distri- bution of colonies.Further,
we have foundan additional
aggregation
of 9 colonies atWyperfeld (fig 1), and
anaggregation
of 12colonies at
Devonport
in Tasmania(Oldroyd
et
al, 1995).
We have learned that similar denseaggregations
ofhoney-bee
coloniesoccur in Louisiana
(TE
Rindererpersonal communication).
These observations sug-gest
that wild colonies of A mellifera may often be found inaggregations.
Thisphe-
nomenon is common in A dorsata
(Koeniger
and
Koeniger, 1980; Seeley et al, 1982),
and may occur in other
Apis species
wheredata are
lacking, although clumping
in Acerana and A florea was not observed
by Seeley
et al(1982).
IfApis
colonies often formaggregations,
then this is thecomplete
reverse of the situation in
stingless bees,
which have a uniform distribution of colonies,
presumably
to reducecompetition (Hubell
and
Johnson, 1977).
Note also that Wen- ner’s(1989)
map of thespatial
distribution of feralhoney-bee
colonies on Santa CruzIsland, California,
shows no hint of aggre-gation.
This may be because floral or nest site resources are limited there(Wenner, 1992).
Why
shouldhoney-bee
nests sometimesform
aggregations?
Severalhypotheses
areplausible.
Aggregation
is a result ofpreference
for swarms to travel a short distance from the natal nest
Jaycox and
Parise(1980, 1981) suggested
that swarms have a
preference
for the near-est of 2 otherwise
equal
nestsites,
while Lindauer(1955) suggested
that swarmswould take the more distant site. Our
study
shows that the
aggregated
colonies atWyperfeld comprised
somecompletely
unre-lated ones
(fig 3). Therefore,
while short dis-persal
distancesby
swarms mayexplain
some
aggregations,
this factor isunlikely
as an
explanation
of theaggregation reported
here.Short
dispersal
distance cannotexplain aggregations
of A dorsata colonies. A dor- sataregularly
undertakelong-distance migra-
tion which may exceed 200 km
(Koeniger
and
Koeniger, 1980; Dyer
andSeeley, 1994).
When a
migrating
swarm arrives at a newlocation,
it has the choice tojoin
anexisting aggregation,
or to settledistantly
from exist-ing
colonies(provided
that there are suffi- cient nest sitesavailable,
seebelow).
Aggregation
is a consequence of an uneven environmentHoney
bees often makeforaging trips exceeding
2 km(Knaffl, 1953; Beutler, 1954;
Wenner, 1992)
and over 6 km whenforage
is scarce
(Visscher
andSeeley, 1982).
Therefore all colonies in this
study
hadflying
ranges that
potentially overlapped
those ofcolonies at other sites. There was no nest
site,
floral or water resource at or near site 7 that was not withinflying
range of sites 2 and 5(fig 1). Site
5 inparticular
is less than 300 m from site 7(fig 1), and
the aggrega- tion of 9 colonies found outside theplots (fig 1)
is less than 2 km from site 5. No colonies were found at site 5. Twelve colonies were found at site 7. Sites werespecifically
selected for theirsimilarity.
Thenumber of hollows suitable for
nesting
beeswas similar and
universally high
among theplots (Oldroyd et al, 1994).
We found nosignificant
correlation between the number of colonies perplot,
and the number of trees or hollows.(Note however,
that some hol- lows that were too small to be favouredby
bee colonies were included in these
data.)
Itis therefore
extremely unlikely
that someunique
resource was available at site 7 thatwas not available to colonies at other sites.
Seeley
et al(1982) suggested
that aggre-gations
of many A dorsata colonies on par- ticular trees is a consequence of a short- age of suitablenesting
sites. Insupport
of thisclaim, they reported
that at 4 urbansites,
the average number of colonies per aggre-
gation
was10.0,
while in undisturbed for- est there were 1.7 colonies(n
=11). How-
ever, their conclusion presupposes that there is a
shortage
of sites in cities. Ourown observations
(unpublished)
are that Adorsata
successfully
nests on many human structures such as tallbuildings
and watertowers.
Further,
we have seenaggregations
in undisturbed forest which is
replete
withtrees suitable for
nesting.
Aggregation provides
increasednest defence
Although
coloniesrespond
to the alarmpheromones
of other colonies(eg,
Stort andGonçalves, 1991),
disturbance of 1 hiveusually
causes other colonies to become alerted rather than to attack.Seeley
et al(1982)
disturbed an A dorsata nest in orderto determine the response of
nearby
colonies.
They
observed thatnearby
colonies did not attack the
intruder, although they
did become alerted. A mellifera and A dorsata colonies have very fewenemies,
andsingle
colonies are wellequipped
todefend themselves without assistance.
Seeley et al (1982) suggested
that aggre-gation
may reduce theprobability
ofbeing
attacked
by reducing
theprobability
ofbecoming
thepredator’s
victim(Brock
andRiffenburgh, 1960).
This seems a very dif- ficulthypothesis
to test.Furthermore,
themajor predators
ofhoney
bees arelarge
mammals
including
humans and bears(Caron, 1990). Aggregation
would appear to increase the chances of detection and the likelihood ofpredation,
so we do notfavour this
hypothesis.
Aggregation improves mating efficiency Honey
bees mate on thewing,
apotentially
hazardous
activity (Moritz, 1985). Aggrega-
tion could reduce the time
required
for vir-gin
queens to locate a dronecongregation
area
(Ruttner
andRuttner, 1972; Koeniger
etal, 1994),
mate and return to the nest.Because the fitness of a
colony
isseverely
reduced if its queen does not return from a
mating flight,
there may bestrong
selectivereasons for
aggregating.
Moreimportantly, aggregations
may reduce theprobability
ofqueens
mating
withbrothers, provided
thataggregations
are notclosely
related groups.Sex in
honey
bees is determinedby
hetero-zygosity
at the sex locus(Crozier, 1975).
Diploid
individuals that arehomozygous
atthe sex locus are
male,
but are eatenby
workers at the first larval instar
(Woyke, 1963). Mating
with brothers reduces broodviability by causing
an increase in homo-zygosity
at the sex locus.Shaskolsky (1976), Page (1980), Page
and Metcalf(1982),
Crozier andPage (1985)
and Ratnieks(1990)
all argue that reduction of brood via-bility
causedby
the presence ofdiploid
drones could lead to the evolution of
polyandry.
Othermechanisms,
such as theaggregation
of unrelatedcolonies,
mayhelp
to avoid
inbreeding
and thegenetic
loadimposed by diploid
males. In A dorsata par-ticularly,
the duration of themating flight
isbrief
(<
10min,
Rinderer etal, 1993;
Koeniger
etal, 1994)
andproximity
to adrone
congregation
areacontaining
a diversepopulation
of drones may be veryimportant.
Our
genetic
data reveal that the colonies at site 7 were not allrelated,
and the aggre-gation
wascomprised
of at least 2 maternallineages,
andquite possibly
more. It is knownthat scout bees
searching
for nest sites areattracted
by
Nasonovpheromones (Free
etal, 1981 a, 1984; Kigatiira et al, 1986;
With- erell andLewis, 1986;
Schmidt andThoenes, 1987,1992;
Schmidtetal, 1989; Villa, 1993;
Winston
et al, 1993; Schmidt, 1994).
It isusually
assumed that scouts are attracted because Nasonovpheromones guide
swarms and induce
clustering (Avitabile et al, 1975;
Freeet al, 1981 a, b).
Wesuggest
thatin
fact,
scouts from natural swarms areattracted to
existing
coloniesby
the pres-ence of Nasonov
pheromones,
and seekcavities in that area. In
evolutionary
terms,the presence of
existing
coloniesmight
indi-cate that:
i)
the local environment can sup-port bees;
andii)
the swarm’s future queens would havenearby
unrelated mates.Nearby
colonies
might
alsoprovide
some additionalcolony
defence. This attraction of scout beesby
Nasonovpheromones
may therefore beadaptive,
since it maypromote colony
aggre-gation.
Thelarge foraging
range of A dor- sata and A melliferaprobably
ensures thataggregation
does notimpair
survival due to intercolonialcompetition. Although
our pre- sent datasupport
theconjecture
that aggre-gated
colonies can beunrelated,
confirma- tionrequires
a more detailedgenetic analysis
of the
relationships
between new swarmsfound near
existing
colonies.Finally,
it should be noted that A mellifera colonies are foundsingly (fig 2)
as well as inaggregations.
This does not detract fromour
general argument
of atendency
toaggregation.
Founder colonies have a low survival rate, and established colonies havea low
reproductive
rate(Seeley, 1978).
Therefore
daughter
colonies may notalways
be found near established colonies. In envi- ronments where nest sites are rare, aggre-
gation
may not bepossible.
ACKNOWLEDGMENTS
We thank the rangers at
Wyperfeld
National Park,and all the officers of the
Department
of Conser-vation and Natural resources who
helped
us somuch. The Department also provided funds for the initial search
performed by
volunteers from the Australian Trust for Conservation Volunteers.Y Crozier provided expert molecular
biological
advice at all stages, and
designed
the mt-DNAprimers.
E Thextonbravely
scaled trees for the collectionsdespite
his innate fear of bees.Extremely
valuable comments on themanuscript
were
provided by
J Schmidt and A Poiani. L Jer-miin is thanked for
spirited
discussions on the statistics. Weespecially
thank T Rinderer for stim-ulating
discussions with BPO whilecontemplating
A dorsata
aggregations
in Thailand. The studywas
supported by
funds from the Australian Research Council to BPO and RHC and the Ian Potter Foundation to RHC.Résumé — Rassemblements de colonies chez
Apis
mellifera L. On n’a pas men- tionnéjusqu’à présent
de rassemblements naturels de coloniesd’Apis
mellifera. Pour- tant ces rassemblements sont courants chezl’espèce
voisineApis
dorsata. Nous avonsétudié la
répartition spatiale
des colonies sauvages d’A mellifera dans le parc national deWyperfeld
dansl’État
de Victoria en Aus- tralie(fig 1)
pour déterminer si les colonies d’A melliferapouvaient
aussi former des rassemblements. Le parcpossède
d’excel-lentes ressources en nourriture et de nom-
breux sites de nidification
(Oldroyd
etal, 1994).
L’étude aporté
sur 7 sites de 500 x100 m chacun. La
présence
de nidsd’abeilles a été examinée attentivement pour
chaque
arbre(N = 1982)
de ces par- celles. L’étude montre que, dans ce milieufavorable,
les colonies d’A mellifera se sont nettement rassemblées avec une densitépouvant
atteindre 10 colonies à l’ha(fig 2).
L’indice de
dispersion
ID(Ludwig
etRey- nolds, 1988)
atteint1,91.
C’estsignificati-
vement
supérieur
à l’unité(χ 2 34
=65,0 ;
P
< 0,01), ce qui indique
un écartsignifica-
tif de la distribution de Poisson et une
répar-
tition
spatiale
enagrégats.
Nous voudrionspourtant
faire remarquer que ce résultatdépend
du rassemblementparticulièrement
dense de colonies sur le site n° 7. Pour ce
rassemblement
remarquable
nous avonsdéduit le
génotype
de la reine enétudiant,
sur des échantillons
d’ouvrières,
lepoly- morphisme
de la malatedeshydrogénase
et de l’ADN mitochondrial et un locus micro- satellite. Le rassemblement étudié était com-
posé
de colonies dont les reines étaientpotentiellement apparentées (ie parent/des-
cendance ou
sœur)
et de colonies nonapparentées (fig 3 ;
tableauI).
Uneexpli-
cation vraisemblable
pourrait
être que, d’unepart,
des coloniesprésentes
attirent les essaims et que, d’autrepart,
dans un milieuriche en sites de nidification les essaims ne
s’éloignent
pastoujours
très loin du nidparental.
Nous pensons que des essaimspeuvent
évaluer des sites de nidificationproches
de colonies existantesprospères
comme
susceptibles
d’accroître leur survieen assurant aux futures reines de l’essaim
un
accouplement plus rapide
et en leur indi-quant
que le milieu convient bien aux abeilles.Apis
mellifera /essaimage
/ ADN mito- chondrial / microsatellite /degré parenté
Zusammenfassung —
Völkeransamm-lungen
beiApis
mellifera L.Über
natür- licheAnsammlungen
von A mellifera Völ- kernliegen
bisher keine Berichte vor. Bei der verwandten Art A dorsatagibt
es vieleBeobachtungen
überHäufungen
von Völ-kern an einem Standort. Um zu
bestimmen,
ob Völker von A mellifera ebenfalls in Häu-
fungen vorkommen,
untersuchten wir die räumlicheVerteilung
von wildlebenden A mellifera Völkern imWyperfield
National-park, Victoria,
Australien. Der Park bietethervorragende Nahrungs-
und Nistbedin- gungen für die Bienen(Oldroyd et al, 1994).
Die
Untersuchung
umfasste 4 Standorte mit einer Fläche vonjeweils
500 x 100 m, die in Bezirke von 100 x 100 m unterteilt wurden.Jeder einzelne Baum
(N = 1982)
innerhalbdieser Bezirke wurde
sorgfältig
auf dieBesiedlung
durch Bienen untersucht. Eszeigte
sich eine deutlichaggregierte
Ver-teilung
der Bienenvölker mit bis zu 10 Kolo- nien innerhalb von 10.000 m2(Abb 2).
DerDispersionsindex
nachLudwig
andRey-
nolds
(1988) betrug
ID = 1.91. Dies istsigni-
fikant
größer
als 1(χ 2 34
=65,0,
P< 0,01).
Dies deutet auf eine
signifikante
Abwei-chung
von einerPoissonverteilung
und eineaggregierte
räumlicheVerteilung
hin. Wirmöchten aber
anmerken,
daß diesesErgeb-
nis auf die besonders dichte
Aggregation
von Völkern am Standort 7 beruht. Für diese bemerkenswerte
Völkeransammlung
ermit-telten wir den
Genotypus
derKöniginnen
aus der
Untersuchung
von Arbeiterinnen-proben
ausPolymorphismen
von Malatde-hydrogenase
und mitochondrialerDNA,
sowie einem Mikrosatelliten-Locus. Die untersuchteAnsammlung
setzte sich ausKolonien mit
möglicherweise
verwandten(ie
Eltern/Nachkommen oderSchwestern)
und nichtverwandten
Königinnen
zusam-men
(Abb
3 und TabelleI).
Als wahr-scheinliche
Erklärung schlagen
wir vor, daßeinerseits bestehende Völker für Schwärme attraktiv sein
könnten,
und daß andererseits Schwärme sich in einerUmgebung
mit vie-len
Nistmöglichkeiten
nichtunbedingt
sehrweit von ihrer Mutterkolonie entfernen. Wir halten es für
möglich,
daß Schwärme Nist-plätze
nahe vonerfolgreich
bestehenden Völkern als förderlich für dasÜberleben
ein-schätzen,
da dies eine rascherePaarung
der
zukünftigen Königin gewährleistet
unddie
Eignung
des Standortes für Bienenvöl- keranzeigt.
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