ASPECTS OF THE TROPHIC NICHE
OF MELIPONA MARGINATA MARGINATA LEPELETIER
(APIDAE, MELIPONINAE)
A. KLEINERT-GIOVANNINI V.L. IMPERATRIZ-FONSECA
Departumento dc Ecologia Gera1 do Instituto de Biocicncias da Universídade de Sao Pauio.
05508. SaoPauio.Brasi!.
SUMMARY
Pollen and honey samples were colleted once every two weeks from the food pots of two colonies of
Melipona marginata marginata Lepeleticr for a twelve-month period (August/ 1981 to July/ 1982).
Altogether, 173 pollen types were found, belonging to 38 plant families in the samples from both colonies, although the really important sources (with representation of 10 % or over) for good collection
were represented by only 11 plant species (9 in pollen samples and 8 in honey samples) belonging to six
families. An interesting point is that from all the visited plant species, the most represented in both type of samples were trees.
The plant families which occurcd most in pollen samples were : Myrtaccae, Solanaceae, Melastoma- taccae, and Leguminosae. In honey samples, the same sequence was observed, but the last two families
appeared in the opposite order.
The niche size as indicated by the number of pollen types fails to highlight the relative importance of plant species visited for food and assumes utilization of resources to be homogeneous.
As regards niche size, as calculated by SHANNON-WEAVER’S diversity index, both colonics had lower values than any other bee species in the same area and used the sources visited least homogeneously.
Summer was the season when both colonics showed the greatest similarity in terms of the sources
visited for pollen. As far as honey samples arc concerned, autumn and early winter were the times when the two colonies overlapped most.
INTRODUCTION
The basic ideas
concerning trophic
nichetheory
come from DARWIN(1859)
and his detailed discussion of the
possibility
thatecologically
related forms cancoexist. Darwin
pointed
out thatspecies belonging
to the same genus com-monly
showgreat similarity
of habits andconstitution,
so that if there iscompetition
betweenthem,
it is far more acute thancompetition
betweenspecies
of different genera.The modern
concept
ofniche,
formulatedby
HUTCHINSON(1957)
andbroadened
by
LEVINS(1968),
MACARTHUR(1968),
VANDERMEER(1972)
andP
IANKA
(1976),
considers that every measurable feature of the environment canbe associated with a coordinate in a
hyperspace
with n dimensions. Anorganism’s
niche is theregion
of this space in which its fitness ispositive.
Inother
words,
niche is no more than ahypervolume
with ndimensions,
wherethe axes are biotic and abiotic critical factors which determine the existence of
species.
LEVrNS(1968)
stresses that theonly
axes, or nichedimensions,
whichshould be considered are the variables which serve to
separate species,
andalong
whichspecies
can be ranked in series.Melipona marginata
has been chosen for thepresent analysis
for a numberof reasons. The first has do to with the low
representativity
of bees of the genusMelipona
in thesamples
of relative abundance obtained so far(KNOLL, 1985).
Before the introduction ofApis,
these bees wereimportant honey producers.
A second reason is the fact that the introduction of the African bee into Brazil coincided with thebeginning
of intense deforestation in most of thecountry :
this led to microclimaticchanges
and reduced theavailability
ofsuitable sites for nidification
by
bees which almostexclusively
nest in treehollows,
as in the case of this genus.In South and Central
America,
before theimpact
causedby
the introduc- tion of the Africanhoneybee (Apis mellifera adansonii)
and theresulting spread
of africanizedhoneybees,
nostudy
of resourcesharing by
the communi- ties had been made. Theecological
success of africanized bees was undoub-tedly responsible
for the excellent studies resourcessharing
among thestingless
bees of Costa Rica
by
JOHNSON and HUBBELL(1974, 1975)
and HUBBEL andJ
OHNSON
(1977, 1978),
while ROUBIK(1978, 1979, 1980) attempted
toanalyse
the
impact
of the africanized bee’s arrival on the native social beecommunity
of French Guiana.
The
methodologies
used in thestudy
mentioned above included observa-tion, counting
andcollecting
bees whenvisiting flowers,
and sugar baits sweetened to differentdegrees.
Another way ofdetermining
what food sourcesbees use is
pollen analysis
of the material collectedby them,
as has been doneby
ABSY and KERR(1977) ;
IWAMA and MELHEM(1979) ;
ABSY et al.(1980) ;
E
NGEL and DINGEMANS-BAKELS
(1980) ;
SOMMEIJERBt Cll.(1983) ;
IMPERATRIZ-FoNSECA et al.
(1984) ;
KERR et al.(1984)
inrespect
to severalspecies
ofstingless
bees. These authors focused theirstudy
on the botanicalaspect
while CORTOPASSI -L
AURINO
(1982),
MOUGA(1984)
and RAMALHO et al.(1985)
dealtmore
broadly
with theproblem
of thetrophic
nichesoccupied by bees, using
parameters
which indicated thedegree
ofdiversity
andoverlap
in the resourcesused.
The aim of the
study
was toidentify
the food sources(pollen
andnectar)
used
by Melipona marginata marginata Lepeletier by
means ofpollen analysis.
The data obtained were used to determine the
trophic
nichesize,
evennessindex and
percentage overlap
of the two colonies considered.MATERIAL AND METHODS
Samples of pollen (3-4 g per sample) and honey (6-7 g per sample) were collected from the newly
constructed food pots of two colonies of Melipona marginata marginata Lepeletier (Mi and M2) once
every two weeks for a year (August 1981 to July 1982). Altogether, 95 samples were taken, 48 samples
of honey (24 from each colony) and 47 of pollen (24 from colony M, and 23 from colony M2).
The colonies were kept in rational hives (Nocu!n-NeTO, 1970) in the Bee Laboratory of the
General Ecology Department, Bioscience Institute, University of Sao Paulo. The area around the Bioscience Institute has diversified native and foreign plant species and a small scmi-dcciduous forest of native species (approximately 10 hectares) (RAMALHO et al., 1985).
Each pollen sample was submitted to the acetolysis process according to ERDTMAN’S method (1960).
The technique used for the honey samples was that described by LouvEAux et al. (1970), as modified by
I WAMA
and MELHEM (1979).
Three slides were prepared for each sample, and the material was identified in terms of the
morphological characteristics of the pollen grains. It was then compared with the existing material in the reference slide collection housed in the Bee Laboratory and with specialized literature, in an attempt to reach an identification at the level of species.
The frequency with which pollen types were represented was determined by counting about 1 000
pollen grains in each sample (VERGERON, 1964). The percentage obtained for the fortnightly samples were
added up in order to obtain the monthly pollen spectrum of each of the colonies studied. A note was
made of the pollen types which were not counted but were seen to be present in the samples ; the notes
were used when calculating and analysing the results.
Based on the data for pollen spectra, a number of ecological parameters related to the trophic niches
of these bees were calculated :
a) Trophic niche size : this parameter was determined both by the monthly total for pollen types found and by the percentage for each pollen types in the samples. This latter datum was >calculated using
SanNrioN-wenvex’s diversity index (T949) : 1
pi = proportion of each pollen type found in samples of colony in question during month considered.
In = natural logarithm.
b) Evenness : this parameter indicates the degree of gathering uniformity among the various plant species vistied by the colonies during the month considered ; it was reached by the following formula (P
IELOU , 1977) : 1
H’ max. = In of the total number of pollen types present in the samples. The index may vary from 0 to 1, i.e. from heterogeneous utilization of resources to homogeneous use.
c) Trophic niche overlap : two indices were used for this calculation : c
l
- The first index (SettoeNEa, 1968) takes the proportions of the various pollen types found in the
samples to indicate the percentage similarity of food gathering between the two colonies each month :
pi m
,
= proportion of the i sources visited by colony M, in the month considered.pi M
, = idem for colony Mz.
C2
- The second index (CODY, 1974) takes the number of plant species found in the samples but does not
consider their representativity :
nM!h,_ = number of pollen types common to colonies M, and M, in month considered.
n MI
= total number of pollen types found in samples of colony M, in month considered.
n M
, = idem for colony M,.
The results were statistically analyzed to find the degree of correlation between the various parameters calculated, and to see whether there were any differences between the two colonies studied.
The coefficient used to calculate the correlations was PenttsoN’s, and the differences were determined
using Student’s t-test.
RESULTS
During
the twelve-monthcollecting period,
173pollen types
were found in thepollen
andhoney samples
taken fromMelipona marginata marginata, belonging
to 32 differentplant
families. Ofthese,
105 were used to collectpollen
and 124 to collect nectar.As for the colonies taken in
isolation, colony M t
visited 121plant species,
76 to
gather pollen
and 87 togather
nectar. In thesamples
fromcolony M 2
120
pollen types
werefound,
74 of them in thepollen samples
and 91 in thehoney samples.
The 10 % lower limit was considered the
point
at which theplant species
found in
samples began
toacquire importance
for the bees as a source of food(R AMALH
O
andK LEINERT -GIO VA N N INI,
inpress.).
Tabl. 1 shows a list of the
pollen types
whichappeared
in thehoney
andpollen samples
from the two colonies withpercentages
of more than 1 %.Those with more than 10 %
representativity
are shown inparentheses.
It canbe seen that
during
the twelve-monthcollecting period only
26pollen types (14
in the
pollen samples
and 26 in thehoney samples), belonging
to 15plant
families,
were found withpercentages
of more than 1 %. Of these26, only
11 1types (9
in thepollen samples
and 8 in thehoney samples), belonging
to sixfamilies,
had over 10 %representativity.
Fig. 1,
2 show the results forpercentages
ofplant species
visitedby
colonies
M,
andM 2 respectively
forpollen
collection. In both colonies thesame nine
pollen types appeared
with more than 10%,
andonly
themonthly representativity
in thesamples
varied :Eucalyptus
spp, Psidium guayava, Solanum sp1,
Solanum sp2,
Tibouchina spp, Miconiatype,
Mimosadaleoides, Myroxylon balsamum,
and Morusnigra.
It can be seen that
Eucalyptus
spp was amajor
genus forpollen gathering
in both
colonies,
as it was wellrepresented
in almost all months of the year,especially
insamples
fromcolony M 2 .
Anotherspecies
from the samefamily (Myrtaceae),
Psidium guayava, wasimportant
forpollen gathering only
inNovember,
and was also more visitedby colony M 2 .
Another
well-represented
genus wasSolanum,
with twospecies :
one ofthese
(sp 1)
was the dominantspecies
in October for both colonies. This genusappeared
withrepresentative percentages
insamples
inAugust, September, October, November, May
and June.The
family
Melastomataceae wasrepresented by
Tibouchina spp andby
the
pollen type
named Miconia. The former genusappeared
withhigh
percen-tages
inFebruary
andMarch,
both incolony M,
andM 2 .
Its leastsignificant
occurence was in March for
colony M,.
As for Miconiatype,
itappeared
inthe
histograms
for both coloniesonly
in December 1981.Mimosa daleoides and
Myroxylon
balsamumrepresented
thefamily Legu-
minosae in the
pollen samples
from both colonies. InJanuary,
the formerspecies
occured with similarpercentages
forcolony M,
andcolony M 2 ,
and wasalso found in
April
inM 2 .
The secondspecies
was found inJuly,
and occurred incolony M,
with ahigher percentage.
The last
family represented
in thepollen samples
with more than 10 %representation
was thefamily Moraceae,
with onespecies
Morusnigra, present
inAugust
andSeptember
incolony M,,
andonly
inSeptember
incolony M,.
The number of
pollen types appearing
with less than 10 % varied from 10 to 27 in thesamples
fromcolony M,,
and from 6 to 24 in those fromM Z ;
the10 to 20 bracket was the most
frequent
in both colonies.Fig. 3,
4 show themonthly pollen spectrum
for thehoney samples
fromcolonies
M,
andM 2 respectively.
Fiveplant species
were found with more than 10 %representation
incolony M I ,
whereas inM 2
there wereeight
suchspecies.
Thefollowing pollen types
were common to both colonies :Eucalyptus
spp, Psidium guayava, Solanum sp
1,
Tibouchina spp, and Mimosa daleoides.Colony M 2
contained three furtherpollen types
in addition to the latter five : Alchorneasidaefolia, Leguminosae 1,
and Miconiatype.
As observed for the
pollen samples, pollen types
which were not represen- ted in themonthly pollen spectrum
of acolony
werealways
found withpercentages
of less than 10 % insamples
from the othercolony.
Eucalyptus
spp was found in all months of the year in bothcolonies ;
itappeared
with more than 50 ‘% inAugust
andSeptember 1981,
and fromMarch to
July 1982,
and was found inFebruary
1982 incolony M 2 .
Psidiumguayava, which was
present
in thepollen samples
for November in bothcolonies,
was alsoonly
visited in November for nectargathering, although
itsrepresentation
waslower, especially
insamples
fromcolony M,.
In the
honey samples,
thefamily
Solanaceae wasrepresented by
asingle species (Solanum
sp1).
Incolony M,,
thisspecies
was found inOctober, November,
December andMay,
while inM 2
it was found inSeptember
andOctober.
In
samples
fromcolony M i ,
thefamily
Melastomataceae hadonly
onerepresentative,
Tibouchina spp ; this genus was visited inFebruary
for bothnectar and
pollen
and in Novemberonly
for nectar. Insamples
fromcolony M,,
in addition to Tibouchina spp, which was foundonly
inFebruary,
thesame
pollen type
as that found inpollen samples
inDecember,
Miconiatype,
was found in the
honey samples
for the same month.Mimosa
daleoides,
whichrepresented
thefamily Leguminosae
in bothcolonies,
wasimportant
for nectargathering
in December andJanuary
incolony M I ,
and inJanuary
andFebruary
incolony M,, although
in the latter month itappeared
withrelatively
lowrepresentation.
Another member of thesame
family,
known asLeguminosae 1, only
occurred incolony M 2
inJuly
1982.
One
family
notrepresented
inpollen samples
but found with more than 10 o/.,representativity
inhoney samples
was thefamily Euphorbiaceae.
Onespecies
in thefamily,
Alchorneasidaefolia,
was found in Novemberonly
incolony M 2 .
It can be seen that the number of
pollen types
with less than 10 %representation
wassignificantly higher
inhoney
than inpollen samples
throu-ghout
the year,showing
that bees visited alarger
number ofplant species
fornectar
gathering
purposes, untilthey
settled down with one or a fewspecies
which could
provide
for their needs.The
plant family
with mostspecies represented
insamples,
bothpollen
and
honey,
wasLeguminosae,
followedby Compositae, Euphorbiaceae
andMyrtaceae (Fig. 5).
If thepercentage
occurence isconsidered, although
thefamily Leguminosae occupied
thetop position
asregards
the number ofrepresentatives, Myrtaceae
was most visited for bothpollen
and nectar, aboveall for the latter. Of the
species belonging
to thisfamily, Eucalyptus
spp accounted for 88.5 % of the totalpercentage
occurence inpollen samples,
andfor 97.4 % in
honey samples,
as can be seen inFig.
6. In bothtypes
ofsample,
the second most visitedfamily
wasSolanaceae,
with ahigher
percen-tage
occurence inpollen samples.
The next most visited families were Melasto-mataceae and
Leguminosae
forpollen,
with these same families in the reverseorder for the
honey samples.
The
family Leguminosae
was notimportant
inpercentage
terms,especially
in
pollen samples. Here,
twoplants species
alone accounted forvirtually
allthe occurences of this
family :
Mimosa daleoides(48.3 %),
andMyroxylon
balsamum
(43.4 %).
The restcorresponded
topollen
collected from the other 12pollen types belonging
to thisfamily.
Inhoney samples,
Mimosa daleoidesaccounted for 64.5 % of the total
representation
of thefamily Leguminosae,
while the
remaining
35.5 ‘% were shared among the otherplant species belonging
to thisfamily
and found to bepresent.
Fig.
7 shows themonthly trophic
niche size in relation topollen gathering,
as indicated
by
the number ofplant species
visited. November was the month when thehighest
number ofplant species
visitedby colony M,
was found(30),
and the lowest value
(13)
was found in March andMay. Comparing
individualmonths,
it can be seenthat, except
forNovember,
there was an absence ofpronounced
variation in the number ofpollen types observed,
in contrast with thefindings
forcolony M,,
where variation wasgreater. M 2
visited thelargest
number of
plant species
inApril (27),
and the smallest inFebruary (7).
Generally speaking, however,
the two curves aresimilar,
and the differences found between the values were notstatistically significant (P
>0.99).
This
figure
also shows the number ofpollen types
cummon to the twocolonies,
and the total number of resources usedby
both over the wholeperiod.
It can be seen that the number ofplant species
common to bothcolonies was
always
less than the number ofpollen types
found for eachcolony.
This number was the same as the value forcolony M 2 only
inFebruary.
These data indicate a difference in the food sources visited each monthby
coloniesM,
andM 2
forpollen gathering.
InFebruary, evidently,
allthe
plant species present
in thesamples
fromM,
wererepresented
insamples
from
colony M,.
,.The
highest
values for the food sources which were common to both colonies were found inSeptember
and December(15),
while the lowest werefound in
February,
March and June(7).
The curve
showing
the total number ofplant species
visitedby
bothcolonies had three
peaks,
one in November(34),
a second inApril (31),
and athird in
July (36).
The lowest value wasFebruary (14).
The niche
size,
calculatedusing
SHANNON-WEAVER’Sdiversity
index(H’)
takes into account the
proportion
ofpollen types
found insamples, indicating
a
greater specifity
offoraging
as H’ diminishes. The indices calculated for both colonies showed nostatistically significant
differences(P
>0.99)
between thepairs
ofmonthly
values or between annual means(Fig. 8).
It can be seenhowever that the
highest
values found forM,
were forAugust
andNovember,
while the lowest
foraging diversity
was found inApril.
ForM 2 , diversity
reached a
peak
inSeptember
andgradually
fell to its lowestvalue,
which wasfor
February.
InMarch, diversity
increasedcompared
with thepreceding mongh,
and remained more or less constant in thefollowing
months.No
significant
correlation(r
=0.45 ;
P >0.05)
was found between the values calculatedby
the two methods forcolony M,.
In otherwords,
there wasno
correspondence
between the number ofpollen types present
insamples (n)
and the
degree
ofdiversity
shownby
bees’ visits to flowers(H’).
Forcolony M
2
, however,
the correlation waspositive
andsignificant (r
=0.91 ;
P <0.05).
In
honey samples,
themonthly
nichesize,
indicatedby
the number ofplant species
found in eachcolony,
was almostalways bigger
than for thepollen samples, showing
that the beesforaged
from alarger
number ofplant species
whencollecting
nectar(Fig. 9).
The lowest number ofpollen types
was found inFebruary (14)
forcolony M i ,
and thehighest
inJuly (28). Colony M 2
visited the lowest number of
plant species
inMay (12)
and thehighest
inMarch
(31).
A certain
correspondence
can be observed between themonthly
valuesobtained for the two
colonies,
with thepronounced exception
ofMay,
whencolony M,
visited twice as manyplant species
asM 2 - Statistically speaking,
however,
nosignificant
difference was found(P
>0.99)
between themonthly
values for the colonies.
In
Fig. 10,
which shows the values for niche size calculatedaccording
toS HANNON -W EAVER
’
S index
(H’),
it can be seen that thehighest diversity
occured in November for both colonies.
Colony M, foraged
with leastdiversity
in March and
colony M 2
inApril.
A
comparison
betweenFig.
9 and 10highlights
the fact thatalthough
thenumber of
plants species
found in eachcolony
in March waslarge,
thediversity
index(H’)
waslow, especially
forcolony M,,
which concentratedforaging
almostexclusively
onEucalyptus
spp.The number of
pollen types
common to both colonies reached its maxi-mum in
September (20)
and its minimum inApril
andMay (18).
The curveshowing
the total number ofplant species
visitedby
both colonies reached itspeaks
inMarch,
when 45pollen types
were found. The lowest value occurred inFebruary (21).
Similarity
to thepollen samples,
nosignificant
differences were found(P
>0.99)
between thepairs
ofmonthly
values for thecolonies,
or between the annual means of these values. The correlation between the values for niche size calculatedby
the two methods was notsignificant
for either of the two colonies studied(colony M, :
r= - 0.50 ;
P >0.05 ; colony
M, : r= - 0.(l03 ;
P >
0.05).
Fig.
11 shows the values for evenness(J’)
obtained withregard
topollen gathering.
Both colonies visitedplant species
mostuniformly
inAugust.
Colony M,
used resources mostheterogeneously
inApril,
while the month in whichM,
did so wasFebruary.
It can be seen that the curves for the two colonies are
relatively similar,
and no
significant
differences were found(P
>0.99)
either between thepairs
of values or between the annual means.
There was a
positive
andsignificant
correlation between niche size(H’)
and evenness
(J’),
both forcolony M, (r
=0.94 ;
P <0.05)
and forcolony M, (r = 0.89 ; P < 0.05).
Both colonies visited resources used for nectar
gathering
mosthomoge- neously
in November(Fig. 12).
The same values were found in March forcolony M,
andApril
forM,.
The curves
plotted
for the values of H’ and J’ withregard
to eachcolony
are very
similar,
withcoincinding
maxima andminima,
as can be seen from acomparison
of the two(Fig.
10 and12).
There was apositive
andsignificant
correlation between the values of H’ and
J’,
both forcolony M, (r
=0.99 ;
P <
0.05)
and forcolony ll!I2 (r
=0.99 ;
P <0.05).
There were nostatistically
significant
differences between the evenness indices calculated for the two colonies(P
>0.99).
Fig.
13 shows the values for theoverlap
between the resources used togather pollen,
calculatedaccording
to CODY(aM!M,)
andusing
SCHOENER’Sformula
(PS).
It can be seen that the values obtainedby
the two methodsplot
similar curves,
although
ScHOErrER’s index led togenerally higher
results. InSeptember, December, January
andFebruary,
values foroverlap
calculatedby
the second method were
higher
than 90%,
whereas thefindings using
CODY’Smethod were
always
less than 76 %.This
points
to theimportance
ofconsidering
theproportion
of eachplant species
visited forforaging
when it ispossible
to do so. Resourceoverlap
asshown
by
CODY’S index takes into accountonly
the total number of resourcesutilized,
while SCHOENER’S method establishes thedegree
ofsimilarity
betweenthe
proportions
of the variouspollen types
found insamples. High overlap
inthis case means that the
plant species
common to both colonies werepresent
in similar amounts, and those not found in one or the othercolony
werepresent
inrelatively
small amounts insamples,
oragain
that one of thespecies appeared
with such ahigh percentage
that the others hadonly
a smallinfluence on the results.
The lowest values for
overlap (PS)
were found in November and June : this may mean that theplant species
common to both colonies were visited indiffering proportions,
or that bees from the two colonies visited theplant species
not visitedby
both to agreater
extent. The annual means foroverlap
were as follows : 0.73 for
PS,
and 0.63 fora M M ,.
In order to find out whether the niche size of each
colony (H’)
was in any way related to thepercentage similarity (PS)
shown insamples
fromboth,
thevalues obtained were correlated. No
significant
correlation was found between niche size(H’)
andsimilarity
either forcolony M, (r
= -0.33 ;
P >0.05)
orM 2 (r
= -0.01 ;
P >0.05),
in otherwords,
there was no relation between alarger
or smaller niche and the
degree
ofsimilarity.
For the
honey samples,
inMarch, April
andMay,
thehighest
values ofPS
correspondend
to the lowest values ofoverlap
calculatedby
the CODYmethod
(Fig. 14).
Forexample,
in March 13pollen types
were common to bothcolonies ; colony M, foraged
from 27plant species
andcolony M 2
from31. The values found for
aM!M,
was 0.45.However,
the sources not common toboth,
which were observed to beplentiful,
were found insamples
in lowproportions.
InMarch, Eucalyptus
sppappeared
with veryhigh percentages
(over
90%)
and in similar amounts in bothcolonies, indicating
that of all theresources visited this genus was the main food source utilized and
confirming
the PS value for March
(0.91).
In December the
foraging similarity
index was lowest(0.38), despite
thefact that the number of
pollen types
common to both colonies waslarge (16)
in relation to the total number of
plant species
visitedby
coloniesM, (22)
andM
2 (23),
so that the CODY index wasrelatively high (0.71).
InDecember, plant species
visited athigher
ratesby
onecolony
had aproportionately
lowerrepresentativity
in the other.No
significant
correlation was found(r = - 0.60 ;
P >0.05)
between values of H’ and PS forcolony M i .
As forcolony M,, however,
values of H’ had anegative
correlation with values of PS(r
= -0.75 ;
P <0.05) :
in otherwords,
the smaller the niche
size,
thelarger
the amount ofoverlap
withcolony M,
interms of the resources utilized for nectar
gathering. Thus,
in those months when the formercolony foraged
with leastdiversity,
theplant species
visitedmost were the same as those visited
by colony M 1
athigher
rates.DISCUSSION
The number of
pollen types
found insamples
from the two colonies ofMelipona marginata marginata (173)
was not very different from the amount found forTetragonisca angustula (180) (I MPERATRIZ -F ONSECA
etal., 1984)
andfor
Paratrigona
subnuda(120) (M OUGA , 1984)
in the same area. The number ofplant
families found forTetragonisca angustula
was45,
whereas the number of families found forMelipona marginata (32)
was closer to that foundby
M OUGA
(36).
If the results for
Melipona marginata
arecompared
with those forTetrago-
nisca
angustula
foundby
IMPERATRiz-FONSECA(1984)
and forMelipona quadri- fasciata
foundby
GUIBU(personal information)
on the Sao Paulo campus, itcan be seen that the number of
plant species
visited for nectar(124, 158,
and86
respectively)
washigher
than that found in thepollen samples (105, 140,
and
36),
and that the same is true for eachcolony
in isolation.A
BSY and KERR
(1977)
and ABSV et al.(1980)
studied bees in theAmazon,
and observed the same withregard
tosamples
fromMelipona seminigra
merrilae
(33 species
forpollen gathering,
and 49 fornectar).
In1929,
ROBERT-SON had
already
mentioned thatalthough
many bees limit theirpollen
collec-ting
to a small number ofplant species, they
obtain nectar from alarge variety
of
plants, although
this differencemany
not appearclearly
in the foodsamples.
He thereforesuggested
thatonly pollen collecting
be considered whendetermining
relations between bees and flowers.Thus,
MICHENER(1979)
usedthe term
broadly polytectic
to refer tospecies
which collectpollen
from many unrelatedplant species. Species
which limitpollen gathering
to a few relatedplant species, usually
from the same genus(or
even the samespecies),
arecalled
oligolectic (or monolectic). According
toM ICHENER ,
it may bepresumed
that most bee
species
collectpollen
from variousplant species (which
are notnecessarily related)
in thegreater part
of the communities in whichthey live, presenting
a variation in theplant species
visited in terms oflocality
andseason. These he called
narrowly polytectic.
Melipona margircata
can beplaced
in the latter of thesecategories (nar- rowly polytectic),
for even ifonly
thepollen types
with more than 1 %representativity
areconsidered, along
with thosepresent
withpercentages
ofmore than 10 % in
pollen samples,
it can be seen that theplant species
foundin these
samples belong
to arelatively large
number ofplant
families.C ORTOPASSI -L
AURINO
(1982)
also noted ahigh frequency
ofpollen types
with less than 1 % insamples
ofpollen
fromApis mellifera
andTrigona spinipes, although
the amount ofpollen types
with thisrepresentativity
waslarger
than that found inpollen samples
from the two colonies ofMelipona marginata
studied here. MOUGA(1984)
found the same in herpollen samples
from
Paratrigona
subnuda.The presence of a
large
number ofpollen grains
withextremely
lowrepresentativity
may be due to variousfactors,
such as contaminationby
thebees themselves
during foraging, and,
later on,during
foodprocessing ;
thepresence of
anemophilous pollen ;
or asampling
error(improbable,
as this factwas verified in all the
stingless
bees andApis rreellifera
colonieskept
in thesame
place
as the site for thisstudy).
A further
suggestion
is that thesepollen grains
mayrepresent potential
food sources
(in
this case, those with less than 10 %representativity
could alsobe
included),
used when more attractive blooms are notavailable,
or even thatchance
plays
apart
in the localization of source. It is easy toimagine
thatforagers leaving
acolony
togather
foodspread
out among the flowers at random. On their return to thecolony, they
communicate the existence or absence of arewarding bloom,
so thatonly
if the answer ispositive
do alarge
number of individuals leave the
colony
for the site found. If severalforagers
go out in search of food and
constantly
return withnegative
information for alonger period, however,
the number ofplant species
with lowpercentages present
in combs or foodpots
must be verylarge.
The
pollen types represented
with more than 10 % were considered thereally important
sources forpollen
and/or nectargathering during
theperiod analyzed.
The small number ofplant species
with this level ofrepresentativity
in
samples
from both colonies corroborates the ideaexpoundend
above.However,
the two colonies studied showed ahigh percentage
of visits tosources which
(with
theexception
ofEucalyptus spp)
are notnormally impor-
tant for