The
Aplexa
hypnorum
coenosis in Zuid-Bevelandby
C. den Hartog
(Hydrobiological Institute, division Delta-research, Yerseke, Holland).
METHODS:
The method of the surface-census for the
investigation
of mollusc communities was recommendedby
MORZER-BRUYNS(1947)
in his thesis. In accordance withthis,
all molluscs from small squaresample
plots
arecollected,
separated
intoliving
and dead ones,counted,
andparticularities,
if any, are noted down. For thestudy
of watermolluscs this method is not
very
adequate.
It ispossible,
however, toobtain mud and sand
samples
from the bottomby
means of agrab.
In stagnant fresh water the
Ekman-grab
especially
is very useful. Thegrab samples
have to be sieved andsubsequently
the obtained molluscs and other animalscan becounted,
measured andpreserved.
The surface-census as well as the
grab-method
are useless when we want to survey the animalsliving
between thewaterplants.
There-fore,
Iapplied
anotherquantitative
sampling
method,
which isThe
ecological
demands ofAplexa
hypnorum (L.,
1758) seem to differconsiderably
from those of mostotherwater snails. Thisspecies
lives almostalways
onlight
tomoderately
clayey
bottoms in small ditches whichcompletely dry
outduring
thesummer. The numberofspecies
whichareabletosurvive such circumstances isrelatively
small. It is notsurprising, therefore,
that the habitat in which A.hypnorum
lives is characterizedby
a poor,but veryoutstanding
assemblage
ofspecies.
Thecommon occurrence of thespecies
in the former island of Zuid-Beveland(DENHARTOG,
1963)
enabled me to startaquanti-tative
investigation
on itsbiocoenosis,
and to compare my results with those of otherinvestigators.
My
thanks are due to Messrs. L. DE WOLF and A.J.
J.
SANDEE for their invaluable assistance with the fieldwork of thisinvesti-gation.
Basteria, Vol. 27, No. 3 en
4,
1963 50already
in useby English limnologists.
In anhomogeneous
biotope
it ispossible
to obtainquantitative
databy
collecting
the animalsduring
a determined time-unit. MANN (1955) used this method forhis
quantitative
studies on leeches, and REYNOLDSON (1958)applied
it forsampling
triclads.Although
theseinvestigators
recommended the time-unit of an hour,the luxuriance of the water-snail fauna in Zuid-Beveland is sufficientto allow theinvestigator
30 minutes forcollecting.
There are several
objections
which can be put forwardagainst
such a time-census. In the firstplace
the method is not very exact.Thenumbers collected within half an hour have no absolute value
as a result of the fact that the person of the collector becomes a
factor. His tempo is not
always
thesame. In anopenvegetation
he will no doubt work moreaccurately
than, forexample,
in a ditchwhere he is hindered
by
high
reed or thesharp
stalks ofsedges.
Weather conditions alsoplay
a part. The effect of wind on the water surface is very inconvenient forcollecting
inponds
andlarger
water areas.Cloudy
weathergreatly
influences thetrans-parency of the water.
Optimal
results can be obtainedonly
when the weather is fair. Moreover, the data obtainedby
differentcollec-tors may be
insufficiently
comparable
as a consequence ofdiffer-ences in
eye-sight, working
tempo, handiness and accuracy. Theresults which were obtainedduring
theinvestigation
of the lifecycle
ofAplexa
hypnorum
(DEN
HARTOG & DE WOLF,1962)
with thehelp
of the time-census method are, however,sufficiently
consistent for confidence in itsapplicability
forcoenological
studies.The
surveys
given
here have beenkept
ashomogeneous
aspossi
ble. The molluscs were collected
by
Mr. L.DE WOLF while the othercreeping
invertebrateswere collected at thesame timeby
Mr. A.J.
J.
SANDEE. In table 1 the dataaregiven only
for those groups for which a reliablepicture
is obtained. Thespecies
which live in the mud and can not be collectedby
the time-censusmethod,
as e.g. tubificids andmicro-organisms
(Ostracoda,
Cladocera,
Copepoda,
rotifers and smallturbellarians),
areomitted. Water insects alsowerenot studied. The
description
of theAplexa
coenosis, is thus far fromcomplete.
For a realquantitative
inventory
of abiocoenosis,
the habitat hastobesampled
using
several methods andateamof special-ists must be available for the identification of the material. Thisis,
however, aUtopian
scheme. Forpractical
reasonscoenological
studies haveto be limited to one or a few taxonomic groups with
FAUNISTIC COMPOSITION:
The
Aplexa
coenosis wassurveyed
in 12 localities in theperiod
fromMay
29th toJune
5th, 1962. The results aregiven
in Table 1 on p.52/53.
The nomenclatureof HEUKELS & VAN OOSTSTROOM, Flora vanNederland,
edition14,
1956,
is followed for botanicalnames.
In the 12 localities a total of 3422
living
molluscs was counted.The bulk consists of 3
species only,
namely
Aplexa
hypnorum
with 1125specimens
or32.9%,
Lymnaea
ovata with 1641specimens
or48.0%,
andLymnaea
palustris
with 606specimens
or 17.7%.Only
50specimens
or1.4%
of the total numberbelong
to otherspecies.
The average number ofspecies
in asample
is 3.67.The coenosis is well-characterized
by Aplexa hypnorum,
which isnot
only
faithfulto thebiotope
of thetemporarily
dry
ditches,
but is also oneof the dominant snails in it. Thetwospecies
ofLymnaea,
L. ovata and L.palustris,
which also dominate in thisbiotope,
areubiquitous
and occur in alleutrophic
fresh andoligohaline, standing
andslowly running
waters.They
are useless for the characterization of thecommunity. Planorbis leucostoma,
although
not common inZuid-Beveland,
seems tobe afaithfulspecies
of theAplexa
commun-ity
as it has been found thereonly together
with A.hypnorum.
As thetemporarily
dry
ditches and thepermanently
water-con-taining
ditches aremostly
in open communication with each other, anexchange
ofspecies
may takeplace.
This mayexplain
the occasionaloccurrence, in the
Aplexa
coenosis of somespecies
which are notresistantto a more or less
protracted drought,
e.g. Planorbisplanor-bis,
Physa
fontinalis, Lymnaea
stagnalis,
andSphaerium
corneum.
On the otherhand,
afewspecimens
ofAplexa
hypnorum
may
some-times be found in the
Lymnaea ovata-Planorbis
vortex coenosis.Among
the other animal groups the smallflatworms, belonging
to the
Neorhabdocoela, Dalyellia viridis
and Phaenocoraunipunctata
may beregarded
as faithfulspecies
of theAplexa
coenosis. Thesesmall flatworms were found sometimes without A.
hypnorum,
butalways
in similar habitats.Further
companion
species belong
to themoreubiquitous aquatic
animals. AsellusChlorohydra
aquaticus, Dugesia
lugubris
andviridis-simaare the more
frequent species
and theoccurrence of Glossipho-niacomplanata,
Polycelis
tenuis and Dendrocoelum lacteum isspor-adic.
52 Basteria, Vol. 27, No. 3 en
4,
1963Aplexa hypnorum (L.)
Planorbis leucostoma Mill.
Lymnaea ovata (Drap.) Lymnaeapalustris (Mull.) Planorbisplanorbis (L.) Lymnaea stagnalis (L.) Physafontinalis (L.) Sphaerium corneum (L.)
Total number of specimens
Turbellaria:
Dugesia lugubris (Schmidt) Polycelis tenuis Ijima
Dendrocoelum lacteum (O.F.M.) Phaenocora unipunctata (Oerst.) Dalyellia viridis (G. Shaw)
Hirudinea:
Glossiphonia complanata (L.) Haemopis sanguisuga L.
Crustacea
Asellus aquaticus (L.)
Gammarus duebeni Lillj
Hydrozoa
Chlorohydra viridissima (Pall.) Pelmatohydra oligactis (Pall.)
Fishes: Pungitius pungitius (L.) 1 2 3 4 5 6 789 10 11 12 T 169 273 146 13 80 14 37 25 66123 117 62 1125 38 646 395 47 8 80113 56 16 102 96 44 1641 — — 5 187 80101 191 16 3 2 2 19 606 1 7 — 2— — — — 10 4 4 _ _ _ i__ _ _ _ i 212 919547 255 179 195 34699 98 227 220 1253422 X _ l _ _ _ 6— 4 — — — — 24 36 — — — — 1 — 38 — — — — 12 — 79 23 17 — —±75
---12-6---
2--16---1----16 1 — — 1 8 — 1— 5 14 -_ 7 — — ___ + — — + + + +—+ — + + + + + + + + + — TABLE 1. coenosis in Zuid-BevelandAplexa
hypnorum
The 1 2 3 4 5 6 7 8 9 10 11 12 T Aplexa hypnorum (L.) 169 273 146 13 80 14 37 25 66 123 117 62 1125 Planorbis leucostoma Mill. — — — — — — 5 — 13 — — — 18Lymnaea ovata (Drap.) 38 646 395 47 8 80 113 56 16 102 96 44 1641
Lymnaea palustris (Müll.) — — 5 187 80 101 191 16 3 2 2 19 606
Planorbis planorbis (L.) 1 — — 7 — — — 2— — — — 10
Lymnaea stagnalis (L.) 4 _ _ 4
Physa fontinalis (L.) 1 — — 1
Sphaerium corneum (L.) — — 1 — 11 — — 5 — 17
Total number of specimens 212919 547255 179 195 346 99 98 227 220 1253422
Turbellaria:
Dugesia lugubris (Schmidt) 1 — 1 — — — 6— 4 — — —
Polycelis tenuis Ijima — — — — — — — 8— — — —
Dendrocoelum lacteum (O.F.M.) — — — — — — 13 — — —
Phaenocora unipunctata (Oerst.) — 24 36 — — — — 1 — 38 — —
Dalyellia viridis (G. Shaw) — — 12 — 79 23 17 — —±75
Hirudinea:
Ghssiphonia complanata (L.) — — — 12 — 6 — — —
Haemopis sanguisuga L. 2 — — 26 — — — 1— — — —
Crustacea :
Asellus aquaticus (L.) 16 1 1 8 1 5 14 —
Gammarus duebeni Lillj. — 7
Hydrozoa:
Chlorobydra viridissima (Pall.) + — — + + + +—+ — + +
Pelmatokydra oligactis (Pall.) + — — — —
— — —
Fishes:
LEGENDA
1. Goes, ditch nearthe Television tower. Sparse vegetationwith Phrag-mites communis,Agrostis stoloniferaand Glyceria fluitans;29-V-1962.
2. Wolphaartsdijk, ditch alongthe Nieuwe Veerweg near the junction
withthe Bolleweg. Closed vegetation ofPhragmites communis; 29-V-1962.
3. Nieuwdorp, ditch along the Noord-Kraayertse Weg. Scattered vege-tation of Scirpus maritimus, Alopecurus geniculatus, Equisetum palustre and Lysimachia nummularia; 30-V-1962.
4. Ditch along the main road Heinkenszand - 's Heerenbroek. Closed
vegetation of Agrostis stolonifera and Glyceria fluitans, with
inter-spersed Phragmitescommunis, Juncusarticulatus, Equisetumfluviatile, Galium palustre, Mentha aquatica, Lysimachia nummularia and Callitriche obtusangula; 30-V-1962.
5. Ovezande,ditch in the south-western part of the Louisepolder.
Vege-tation ofPolygonum amphibium, Agrostis stolonifera, Mentha
aqua-tica, Lysimachia nummularia and Scirpus lacustris ssp. glaucus;
30-V-1962.
6. Hoedekenskerke, ditch in the Oosterzwakepolder, opposite the Nieu-we Hoondertpolder. Open vegetation of Alisma plantago-aquatica, Equisetum palustre, Mentha aquatica, Lemna minor and L. gibba; 4-VI-1962.
7. Kapelle, ditch along the Hillewerfweg near the junction with the Plasweg. Closed vegetationofPhragmites communis interspersedwith some plants ofRanunculus sceleratus, R. baudotii and Callitriche obtusangula;29-V-1962.
8. Biezelinge,ditch between „Veldzicht" and „Smokkelhoek". Vegetation
ofPhragmites communis (dominant), Phalaris arundinacea, Agrostis stolonifera and Callitricheobtusangula; 4-VI-1962.
9. Kapelle, den Bok, ditch. Vegetation of Phragmites communis and
Typhalatifolia; 4-VI-1962.
10.
Phragmites
Yerseke,ditch in the Molenpolder. Vegetation ofcommu-nis; l-VI-1962 (Den Hartog & De Wolf, 1962).
11. Krabbendijke, ditch along the railway in the Nieuw Krabbendijkse polder. Scattered plant growth ofPhragmites communis, Mentha
aquatica,NasturtiumVeronica catenata, Rumex crispus, cf.
micro-phyllum,Lysimachia nummularia, Callitriche obtusangula,
Ranun-culus baudotiiand a closed layer of the mossAcrocladium cuspidatum; 5-VI-1962.
12. Ditch alongthe Frederikadijk east of Krabbendijke. Open vegetation ofPhragmitescommunis,
Nasturtium
cf.microphyllum
and Ranunculus baudotii; 5-VI-1962.Basteria,
Vol.27,
No. 3 en4,
196354
Haemopis sanguisuga
tolerates desiccation verywell,
but this spe-cies is more commonalong
larger
bodies of water. Nodoubt,
this very voracious leech preys on the snails in theAplexa
coenosis. Thestickleback
Pungitius
pungitius
is a common inhabitant of theAplexa ditches, but
it leaves thembefore thebeginning
of the sum-merdrought.
It is remarkable that the brackish-water fauna is so
scantily
repre-sented in the
Aplexa
habitats. Gammarus duebenihas been foundonly
occasionally,
while among themicro-organisms
collected and identifiedby
me,
only
Macrostomum hamatum Luther may beregard-ed as a brackish-water
species.
RELATIONSHIPBETWEEN THEAPLEXA COENOSISAND THE VEGETATION:
Although
nophytocoenological
surveys weremade,
it is still clear frommy notes on the
accompanying
vegetation,
that theAplexa-coenosis is not bound toany
special
plant community.
In 5 of the 12 localities
vegetation
was scanty, inanother 5 Phrag-mites communis was the dominantspecies.
In theremaining
twolocalities
Agrostis
stolonifera
andPolygonum
amphibium
werere-spectively
the mainspecies.
Thevegetations
from these localitieswere too sparse tobe identified with certain
plant associations,
but theaccompanying
plants
belong
to 3 groups:1.
Species
of theAgropyro-Rumicion,
the alliance which is cha-racteristic for stress zones betweencontrasting regimes
of envi-ronment, ih this case for the transition zonebetween wetanddry
(VAN LEEUWEN, 1958). Some of theseplants
are able towithstand
protracted
inundations(Agrostis
stolonifera,
Polygo-num
amphibium,
Menthaaquatica),
while others can colonize theseperiodically
dry
places
by
creeping
shoots (Lysimachia
nummularia).
Thevegetations
of the surveys 3,4,
5, 8 and 11may be considered to be
examples
of this alliance.2.
Species
of theGlycerieto-Sparganion,
the alliance of theedges
ofditches,
in which the water flows verygently
(Glyceria
fluitans,
Alismaplantago-aquatica, Nasturtium
cf.microphyllum).
3.
Species
of theCallitricho-Batrachion,
the alliance ofamphibious
water
plants,
which is characteristic for shallow andtempor-arily
dry
ponds
and ditches(Ranunculus
baudotii,
Callitricheobtusangula).
Aplexa hypnorum
doesnot occur in luxuriantwaterplant
commun-ities nor in
well-developed
communitiesof theAgropyro-Rumicion.
In fact the
species
inhabits those ditches whose bottoms arejust
the lower limit of theAgropyro-Rumicion
andjust
the upper limit of the Callitricho-Batrachion. The habitat of theAplexa
coenosis ison the average
just
too wet for theAgropyro-Rumicion
andre-sults ina
fragmentary
development
of thisalliance,
asonly
itsmosteurytope
representatives
intrude into the ditches. On the otherhand,
the bottom ismostly
dry
for toolong
a time to enable successfulestablishment of the Callitricho-Batrachion.
Moreover,
the develop-ment of thevegetations
isgready
influencedby
theyearly cleaning
of the ditches.SOME RECORDSOF THE APLEXA COENOSIS IN OTHER REGIONS:
The
aquatic
mollusc fauna of Zuid-Beveland is poor, and the coexistence ofAplexa
hypnorum
and Planorbis leucostoma could be a localphenomenon.
From observations made in other areas andfrom records in literature it appears, however,that both
species
have been found oftentogether.
The results of theinvestigations
made in Zuid-Beveland maybe
considered toberepresentative
for thesouth-western part of the Netherlands.
In the island of Goeree-Overflakkee A.
hypnorum,
P. leucostoma and the flatworrfi Phaenocoraunipunctata
have been foundtogether
in atemporarily dry
ditch near Dirksland. HENRARD(1946)
record-ed A.hypnorum
and P. leucostoma asconcurring
in Voorne, andaccording
to him this combinationmay be found in several
places
in the Netherlands. In the island of Schouwen I foundonly
P.leuco-stoma in
temporarily
dry ditches,
and could not find A.hypnorum,
although
thisspecies
was recordedby
KUIPER(1944).
In a moistdune
valley
on this island BUTOT(n.p.)
recently
discovered a fewdead
specimens
of A.hypnorum
together
with P. leucostoma, someof whichwere alive.
On the Pleistocene soils in the eastern and southern parts of the country the combination of A.
hypnorum
and P. leucostoma is alsowidely
distributed,
but thereLymnaea
glabra
(Mull.) seems tojoin
thecommunity,
and also some Pisidiumspecies
may occur. KUIPER(1949)
found A.hypnorum
and L.glabra
together
in adrainage-furrow near Duizel
(province
of Noord-Brabant). In thesurround-ings
of theMantinger
Bos in theprovince
of Drente A.hypnorum,
P.leucostoma,
L.glabra
and a few otherspecies
were recorded asoccurring together
(KUIPER, 1952).Anotherexample
of theBasteria, Vol. 27, No. 3 en
4,
1963 56from De
Klomp
(province
ofGelderland).
Itis, however,
question-able whether L.glabra
is atrue memberof theAplexa
coenosis. The lifecycles
of A.hypnorum
and L.glabra
are in some respects verysimilar,
but the patterns of distribution in the Netherlands are very different.Moreover,
in theregions
where bothspecies
occur,they
arefoundmore often apart thantogether.
The coexistence of A.
hypnorum
and P. leucostoma has been ob-served also in otherEuropean
countries. LAIS(1926)
mentioned someinstances from the north-easternpartof France, NELSON(1880)
and BOYCOTT(1936)
recorded the combinationfrom Great Britain and HAESSLEIN(1956,
I960)
found bothspecies
oftentogether
inWiirttemberg
(SouthGermany).
Although
the coexistence of thesespecies
isacommonfeature,
theecological
tolerance of P. leucostoma isconsiderably
wider than that of A.hypnorum,
and it occurs as wellin habitats where the latternever hasbeenfound. It is notuncommon,
for
example,
in small eulittoralcreeklets in the fresh-water tidal areaof the rivers Rhine and Meuse
(Biesbosch).
So P. leucostoma isonly
locally
faithful to theAplexa
coenosis.However,
regionally
it hasto be
regarded
as a characteristicspecies
of temporary and unstableaquatic
habitats. HAESSLEIN(1956)
described from theNordlinger
Ries inWiirttemburg
aValvatapulchella
association,
which hecon-sidered tobe characteristic for river
valleys
and lowland marshes. Heregarded
Valvatapulchella
Studer(=
V. macrostomaSteenbuch)
Aplexa hypnorum
andSegmentina
nitida(Miill.) as faithfulspecies
of thiscommunity,
andaccording
to his table Planorbis leucostoma isextremely
abundantin it.Although
this Valvatapulchella-
association iscertainly
not identical with theAplexa
coenosis,
described from the south-western part of theNetherlands,
both communitiesareclose-ly
related inecological
respect. The main difference in faunisticcom-position,
is thehigh
abundance of Valvatapulchella,
which in the Netherlandsisrare and limitedtoafew localities in theproximity
ofthe rivers Rhine and Waal. Other differencesare the abundance of
some
Sphaeriidae
and the constant occurrence ofBithynia
tentaculata (L.) and Planorbis contortus (L.). These features indicate that thedry period
must be rather short.In the
region
of thePegnitz
HAESSLEIN(I960)
foundAplexa
hypnorum
and Planorbis leucostoma also as members of theRadix peregra association,which he consideredtobe characteristic formount-ainous marshes. This association does not seem to be
very homo-geneous. Several surveys of it
published
by
HAESSLEIN(I960)
showonly
slight
differences with the surveys madeby
me of theAplexa
THE APLEXA COENOSIS DURING THESUMMER DROUGHT:
The surveys of the
Aplexa
habitats in Zuid-Bevelandwere madejust
before thebeginning
of the summerdrought.
When thedry
period
starts,Lymnaea
ovata, L.palustris
and A.hypnorum
assemble in the lowestplaces
of theditches,
and hide under all kinds ofob-jects, pressing
the aperture of the shell closeto the substrate.Many
of them die.I
kept
some A.hypnorum
in a small water-filledtank,
which wasallowed to
dry
out in the sun. After 3 weeksdrought
50% of thespecimens
were yetalive, especially
the smaller ones. Thisobserva-tion
agrees very well with the result of field
investigations
carried out in theMolenpolder
atYerseke (DEN HARTOG &DE WOLF,1962).
In I960 a numberof small animals survived adrought
period
of ca. 2 months,but not onelarge specimen
was sosuccessful. In 1961and1962,
when thedrought
lasted forrespectively
3 and 4 months not asingle specimen
survived. Inever observed that the animalsdug
them-selves in the bottom of theditch,
as has been recordedby
VANBENT-HEM
JUTTING
(1933,
p. 190), FROMMING(1956,
p.152),
ADAM(I960,
p.163)
and BUTOT(1962,
p. 120). CLESSIN (1872)thought
thatperhaps
the animals hid in themud,
as he could not find themwhen the ditcheswere
dry.
I have seen, however, severalspecimens
which hadslightly
sunk into the soft mudsurface,
but not oneAplexa
was foundby sifting
mudsamples.
Ithink, therefore,
that thespecies
overcomes thedrought period
in the form of its eggs.Among
L. ovata also manyspecimens
become victims of thedrought.
In Yerseke a month after thebeginning
of thedry period
Icollected a
large
number of L. ovata. Itappeared
that of theseonly
10%
was stillalive,
andthey
weremostly
the smaller individuals.However,
thisspecies
isabletosurviveadrought period
of 4months, since itwaspresentduring
the wholedrought period
from the middle ofJune
tothe end of October 1962.The youngspecimens
wereseenactively
creeping
andclimbing
against
theplants,
even whenthey
were
exposed
tosunshine.Young
L.palustris
alsocan survive adrought
of 4 months,but the losses in individualsseem evenlarger
than in L.ovata.P. leucostoma is rare in Zuid-Beveland. I haveno observations on
the method of aestivation in this
species.
It seems toclose itsapert-urewitha mucose membrane (FROMMING,
1956).
During
thedrought
thehydrobiotope changes
intoa landbiotope,
enabling
land animals to colonize thedry
bottoms of the ditches. Near Yerseke I noted thefollowing slugs
and snails in thedry Aplexa
Basteria,
Vol.27,
No. 3 en4,
1963 58biotope:
Limax maximusL.,
Deroceras reticulatum(Mull.),
D. laeve(Miill),
Succinea cf.elegans
Risso,Cochlicopa
lubrica(Mull.), Cepaea
nemoralis(L.) and Arianta arbustorum(L.).ACOMMUNITY OF OUTCASTS?
In his work on the
ecology
of the British fresh-water molluscsBOYCOTT
(1936)
paid
much attentionto theecological
group of thespecies
which arealways
ornearly
always
found in habitats whichseem very unfavourable to
aquatic
animals. Hethought
that thesespecies
had been drivenby
pressure ofcompetition
from the"good"
localities into"ecological slums",
i.e. small bodies of water whichdry
up in summer, or which are for other reasons not very suitabletoaquatic
molluscs. He gaveasexamples Lymnaea
glabra
andPlanorbis leucostoma(sub
nomine P.spirorbis).
In free nature L.glabra
has been foundonly
intemporarily dry,
soft-water localities. Inanaquarium
it grows and
reproduces
in hard water as well.According
toBOY-COTT P. leucostoma has "a distinct addictionto
drying ponds,
marshes and other badplaces",
while it is absent from permanentaquatic
habitats.However,
inlarger
places
wherecompetition
between thespecies
isnot so severeas is thecasein smallponds,
P. leucostoma maybe foundalso, e.g.
along
the banks of lakes. BOYCOTT,supposing
thatAplexa hypnorum
(sub
nominePhysa
hypnorum)
could tolerate bad conditionsalthough
itpreferred
bettercircumstances,believed that thisspecies
in fact did notbelong
to the above group. Here,according
to me, he made an error ofthought.
Thespecies
which are driven into the slumsby competitive
seclusion donotnecessarily prefer
suchplaces
as ahabitat. In many cases thereverse will be thecase. Thesespecies
can maintain themselvesonly
by
theircapacity
to live under unfavourablecircumstances, wherethey
are notsubjected
to compe-tition, or areabletocompete withsuccess. The "badplaces"
must be seen asrefugia
for thesespecies.
Although
thesespecies
have under natural circumstancescertainly
theiroptimum
in such stations, it isquestionable
whetherrhey prefer
them.The
competition
hypothesis
of BOYCOTT(1936)
is notproved.
He did notmentioneven whichspecies
exercise the"competitive
press-ure". It is known fromexperience
with several taxonomical groups thatcompetition
has to be seen as anequilibrium
between twoecologic-ally equivalent
species.
Thecompeting species
are thusmostly
con-geners, or
species
withvery similar
adaptations.
They
do not havenecessarily
to be hostile toeach other butavailability
offood,
ratethe factors that
mostly
decide whichspecies
willfinally
survive ina certain
biotope.
Thuscompetition
between twospecies
is not astruggle,
which ispursued
withchanging
success, but in contrast it
proceeds
according
to fixed laws and the result in everyplace
isusually
aforegone
conclusion. When L.glabra
and P. leucostomaare considered in thelight
of the abovegeneralizations
itappears that
they
mustbe incompetition
respectively
with otherLymnaea
species
and with other small Planorbisspecies.
Further it isimprobable
that A.hypnorum
competes withLymnaea
species,
as itusually
coexists with them.However,
species
of rhe genusPhysa
may exercisecom-petitive
pressure. In this connection it isinteresting
that BOYCOTT(1936)
did notgive
any record of rhe coexistence of A.hypnorum
andPhysa fontinalis, although
he recorded A.hypnorum
fromsever-al
"good
places"
withspecies
combinations which maybe referred to to theLymnaea
ovata —Planorbis vortex coenosis and theLymnaea
stagnalis
-Planorbis corneus coenosis (HONER,1963).
In Zuid-Beveland Ionce found twospecimens
of A.hypnorum
in aperma-nently
water-containing
ditch nearOvezande,
together
withnum-erous Planorbis vortex, P.
planorbis, Lymnaea
ovataand L.palustris,
thus in theLymnaea
ovata —Planorbis vortex coenosis. Thesespeci-mensof A.
hypnorum
were from aquantitative point
of view notimportant,
andcame no doubt from anadjacent
Aplexa
coenosis.The remark of BOYCOTT
(1936)
that the stress ofcompetition
inspacious
habitats should be less than in small habitats also has tobeproved.
The occasional occurrence of P. leucostoma and A.hyp-norum
along
the banks of lakes can not beregarded
asproof,
sincea lake is not a
homogeneous
habitat,
but consists of several sub-habitats. Imyself
have found A.hypnorum
only
oncealong
the banks of alarge
body
of water, viz.along
the Groote Gat nearOostburg
in Zeeuwsch-Vlaanderen. This brackish-water broad showsanannual
salinity
fluctuation from 0.5 to 7.8°/oo CI' and toconsider itas asingle
habitat is a seriousmistake. In the broad itself A. hyp-norum isabsent,
but thenarrowstrip
between the widereed-fringe
and thedike,
which insummer iscompletely
dry,
is a suitable habi-tat for thespecies.
During
the time that thestrip
issubmerged,
salinity
isusually
lowenough
to make theoccurrence of A. hypno-rumpossible.
The
Aplexa
coenosis consists of a number ofubiquitous
species,
tolerantto unfavourable circumstances and resistant to a
protracted
drought
period.
According
to theargumentation
of BOYCOTT the faithfulspecies
of the coenosis have to beregarded
as outcasts, asthey
are driven in this extreme habitatowing
to theirinferiority
in thecompetition
with otherspecies.
However,
I wonder whetherBasteria, Vol. 27, No. 3 en
4,
1963 60competition
is theonly
factordetermining
the occurrence of A.hypnorum
intemporarily
dry
ditches. In Zuid-Beveland severalshallow,
permanently
wet fresh-water ditches occur and these areonly
populated
by
Lymnaea
ovata;although
A.hypnorum
would be free fromcompetitive
stress in theseditches,
I did notsucceed infinding
even onespecimen.
There are some reasons to supposethat A.
hypnorum
shows somepreference
for thetemporarily
dry
habitats. In the firstplace
thespecies
livesjust
at the lower limit of theAgropyro-Rumicion,
andjust
at the upper limit ofCallitricho-Batrachion,
thus it has a verynarrow vertical range. Its absence from the Callitricho-Batrachion
can not be
explained
by
thecompetition
factor,
as in these vegeta-tionsonly
L. ovata and L.palustris
occur.Furthermore, NEKRASSOW (1929) found that the lamellation of the spawns and
egg-membranes
of A.hypnorum
is muchmorecompli-cated than in the spawns of
Physa fontinalis
Heregarded
thisfeat-ure as an
adaptation
to the environment, as it would increase theresistance of the eggs
against
desiccation.A
study
of the lifecycle
of A.hypnorum
atYerseke (DEN HARTOG& DE WOLF,
1962)
showed thatspecies
is very welladapted
to theannual
cycle
of the habitat, as each summer theoriginal
generation
falls victim to the extremes of the environment, but thespecies
survives in the newgeneration
of eggs.Therefore,
it seemsto me, that A.hypnorum
may notberegarded
as anoutcast, which is driven in unfavourable stationsby
compe-tition On the contrary, itprefers
the"ecological
slums". TheAplexa
coenosis is notanassemblage
ofspecies
which have been drivento-gether
as the result ofcompetitive
seclusion,
but has to be seen as acommunity
which iswell-adapted
to unfavourable environmental circumstances.REFERENCES
ADAM,
W., I960.Mollusques
I.Mollusques
terrestres et dulcicoles.Faune de
Belgique,
p. 162-163.BENTHEM
JUTTING, T.,
VAN, 1933. Mollusca(1)
A.Gastropoda
proso-branchia etpulmonata.
Fauna van Nederland vol. 7, p. 189-191.BOYCOTT,
A.E.,
1936.The habitats of fresh-water mollusca in Britain.J.
Anim. Ecol. vol.5,
p. 116-186.
BUTOT, L.
J. M.,
1962.Malacologisch
onderzoek op Goeree.Jaarb.
Wetensch. Gen. Goeree-Overflakkee1961,
p. 142-172. CLESSIN,
S.,
1872. Die Lebensweise derPhysa
hypnorum.
Korresp.
Blatt Zool.-mineral. Ver.
Regensburg
vol.26,
p. 170-171.FROMMING,
E., 1956.Biologie
dermitteleuropaischen
Siisswasser-schnecken.Berlin,p. 1-313.
HARTOG, C. DEN, 1963.Thedistributionof the snail
Aplexa hypnorum
in Zuid-Beveland in relation to soil andsalinity.
Basteria vol. 27,p. 8-17.
HARTOG, C. DEN, &L. DE WOLF, 1962. The life
cycle
of the watersnail
Aplexa hypnorum.
Basteria vol.26,
p.61-72.HAESSLEIN,
L., 1956.Mollusken undMolluskengesellschaften
derGe-wasser der
Nordlinger
Ries.Jb.
Ver. Vaterl. Naturk.Wiirt-temberg,
vol.Ill, p. 174-199.— I960.Weichtierfauna derLandschaftenander
Pegnitz.
Abh.Naturhist. Ges.
Niirnberg,
vol. 29 nr.2,
p. 1-148.HENRARD, J.
B., 1946.Bijdrage
tot dekennis der molluskenfaunavanOostvoorne. Basteria vol. 10, p. 25-32.
HONER,
M.R., 1963.Freshwater larval Trematodes in the Netherlands:a
synecological
study
of their occurrence. Thesis, Utrecht,p. 1-116.
KuiPER,
J.
G.J.,
1944.Bijdrage
totde kennisvande niet-marienemol-luskenvan de Provincie Zeeland. Basteria vol. 9, p. 1-29.
— 1949- Enkele vondstenvanzeldzame slakken in
Limburg
enNoord-Brabant.
Corresp.
bl. Ned. Mai. Ver. no. 31, p. 216-219.(mimeographed).
— 1952. De excursie naar het
Mantinger
bos (20 mei 1951).Corresp.
bl. Ned. Mai. Ver. no.43,
p. 376-377.(mimeo-graphed).
— 1955.
Lymnaea glabra (Miiller). Corresp.
bl. Ned. Mai. Ver.Basteria, Vol.
27,
No. 3 en4,
196362
LAIS, R.,
1926. ZurMolluskenfaunades Gebieteszwischen Maasund Mosel. Arch. Molluskenk. vol. 58, p.25-36.LEEXJWEN, C. G. VAN, 1958.
Enige opmerkingen
over hetAgropyro-Rumicion
crispi
Nordh. '40 in Nederland.Corresp.
bl. Flor.Vegetatie
Onderz. Nederlandno. 11, p. 117-123(mimeo-graphed).
MANN, K.
H.,
1955. Theecology
of the British fresh-water leeches.J.
Anim. Ecol. vol. 24,p.98-119-MORZER BRUYNS, M. F., 1947. Over
levensgemeenschappen.
Thesis,
Utrecht,p. 1-195NEKRASSOW,
A. D., 1929.Vergleichende
Morphologie
der Laiche vonSiisswassergastropoden.
Z.Morph.
Okol. Tiere vol.3, p. 1-35. NELSON, W., 1880. On the association ofLimnaea glabra,Physa
hyp-norum and Planorbis
spirorbis. Journ.
of Conch, vol. 3, p. 115-116.REYNOLDSON,T. B., 1958. The
quantitative ecology
oflake-dwelling
Triclads in northern Britain. Oikos vol. 9, p.94-138.Samenvatting
De
Aplexa
coenose, welke karakteristiek is voorin dezomer droog-vallendeslootjes
op min of meerkleihoudende
bodems,
werd be-schreven aan de hand van 12 opnamen,gemaakt
opZuid-Beveland
volgens
detijdcensus-methode.
De coenose wordthoofdzakelijk
sa-mengesteld
door driesoorten waterslakken,
de kensoortAplexa
hypnorum (L.)
en de beideubiquisten Lymnaea
ovata(Drap.)
en L.palustris
(Müll.). Een tweede locaal bruikbare kensoort Planorbis leucostoma Mill. is slechts zeer spaarzaamvertegenwoordigd
op Zuid-Beveland. Twee andere kensoorten konden worden aangewezen onder devertegenwoordigers
van anderediergroepen,
n.l. de beideplatwor-men Phaenocora
unipunctata
(Oerst.)
enDalyellia viridis (G.
Shaw).Decoenoseis
wijd verspreid
inNederland,
alsmede in West- enMid-den-Europa
ende Britse eilanden.Er werd
geen
binding
waargenomen van deAplexa- coenose
aanenige
plantengemeenschap.
De coenose komt slechts daar totont-wikkeling,
waar de slootbodemjuist
met debenedengrens
van hetAgropyro-Rumicion
samenvalt,
maar ook telang droogvalt,
om eenbehoorlijke ontwikkeling
van een tot het Callitricho-Batrachion beho-rendewaterplantengemeenschap
mogelijk
temaken.In het lichtvande
concurrentie-hypothese
vanBOYCOTT(1936)
zoude
Aplexa
coenose opgevat moeten worden als eengezelschap
vanweinig kieskeurige
ubiquisten,
die resistentzijn
tegeneen voorwater-slakken uiterst
ongunstige milieufactor
alsuitdroging.
Dekensoor-ten zouden slechts tot deze
ongunstige
biotoop
beperkt zijn,
omdatze zich elders ten
gevolge
van concurrentiemet anderesoorten nietkunnen handhaven. Het is echterzeer
waarschijnlijk,
dat A.hypnorum
een zekere
preferentie
heeft voorlangdurig
droogvallende slootjes,
want ze ontbreekt in hetCallitricho-Batrachion,
waar demilieu-omstandigheden
minderextreemzijn
enwaarze evenmin
concurrentie metanderesoorten behoeftte vrezen. Delevenscyclus
van dezesoortis zeer
goed
aangepast aan debijzondere
milieu-omstandigheden
ende