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Order Cladocera - Waterfleas
About 70 species of waterfleas make their homes in the waters of the
Great Lakes basin. Of these, only a handful make up the bulk of the open
water biomass. Leptodora
kindtii is a native predatory waterflea. Two recent invaders, Cercopagis
pengoi and Bythotrephes
cederostroemi are also common predatory cladocerans. Larger members
of the Daphnia family are most common in the spring: Daphnia
retrocurva nearshore, Daphnia
galeata in the deep clear waters, and Ceriodaphnia
sp. in the warm upper waters. Smaller waterfleas in the
families Bosminidae and Chydoridae become more abundant in the summer
and fall: Bosmina in
the cool, well-oxygenated waters, Eubosmina in
warm epilimnetic waters and Chydorus in
the eutrophic and near-benthic waters.
The Great Lakes have 4 species of predatory waterfleas, the natives Leptodora
kintii and Polyphemus
pediculus, and two exotics - Cercopagis
pengoi and Bythotrephes
cederstroemi. These are raptorial predators which grasp protozoans,
rotifers, and small zooplankton with their forelegs. All other native
Great Lakes waterfleas are herbivores, feeding on phytoplankton,
attached vegetation or decaying organic material. Most use their
legs to generate a current, filter appropriate sized food particles,
and pass them to the mouth. The Chydoridae and Macrothricidae have
modifications to their legs which enable them to cling to vegetation
and/or detritus and scrape food particles from the surfaces.
Most cladocerans can reproduce by parthenogenesis (asexual reproduction),
females producing 2-20 eggs per brood that develop into young without
fertilization by males. As a result, males are not present in the population
for much of the year. As long as environmental conditions remain favourable
females will continue to reproduce in this manner, producing only female
offspring. Eggs are laid inside a brood chamber along the back of the
animal and are released as free-swimming juveniles when the parent molts.
If the environment starts to deteriorate due to overcrowding, lack of
food, oxygen depletion. or simply seasonal changes, eggs are produced
that develop into males and females capable of sexual reproduction. These
females produce eggs that once fertilized by the males are capable of
surviving extended periods of harsh conditions such as drying or freezing
(sometimes called resting stages). Each female produces only 1-2 such
eggs in a specialized brood chamber called the ephippia. When the female
molts, ephippia are released - eggs remain in the ephippia until conditions
trigger hatching. In this manner cladoceran populations survive through
winter and periods of drought. Some zooplankton resting stages are believed
to have survived centuries buried in sediment. When environmental conditions
are again favourable the eggs hatch and produce parthenogenic females.
Cladocerans have hard exoskeletons and molt many times as they grow.
Many species show changes in shape as they grow - characteristic of age,
season, or environmental conditions.
Order Profiles and General Information -
- "Zooplankton of the Great Lakes" by Balcer, Korda and Dodson.
1984.
The
Cladoceran Body Plan A
Key to Cladocerans (Crustacea) of British Columbia (includes most
Great Lakes families except Cercopagidae)
An Image-Based Key To The Zooplankton Of The Northeast (USA)
The
Cladoceran Life Cycle
The
Waterflea - An introduction to the taxonomy of the sub-fossil remains
ot the Cladocera
Waterfleas
- Jan Parmentier & Wim van Egmond
Cladocerans
of the Thompson-Okanagan Region
MN
Sea Grant - Seiche Article - Our Lake Has Fleas
Distribution and Habitat
x=present
| Image Link |
Scientific Name |
Lake Superior |
Lake Michigan |
Lake Huron |
Lake Erie |
Lake Ontario |
Habitat |
| Family Leptodoridae |
|
|
|
|
|
|
 |
Leptodora kindtii |
x |
x |
x |
x |
x |
littoral and limnetic |
| Family Polyphemoidea |
|
|
|
|
|
|
 |
Polyphemus pediculus |
x |
x |
x |
|
x |
nearshore areas occassionally to
40m |
| Family Cercopagidae |
|
|
|
|
|
|
 |
Cercopagis pengoi |
|
x |
|
x |
x |
|
 |
Bythotrephes longiramus |
x |
x |
x |
x |
x |
|
| Family Sididae |
|
|
|
|
|
|
| |
Diaphanosoma spp. |
|
|
|
|
|
|
|
 |
Diaphanosoma brachyurum |
x |
x |
x |
x |
|
littoral |
 |
Diaphanosoma birgei |
x |
x |
x |
x |
x |
sheltered open waters at depths
of 3-6 meters |
 |
Latona setifera |
x |
x |
x |
x |
|
rare |
 |
Latonopsis occidentalis |
|
|
|
x |
|
|
 |
Sida crystallina |
x |
x |
x |
x |
x |
extremely patchy distribution |
| Family Holopedidae |
|
|
|
|
|
|
 |
Holopedium gibberum |
x |
x |
x |
x |
x |
littoral and pelagic, prefers cold
waters |
|
| Family Daphnidae |
|
|
|
|
|
|
| |
Ceriodaphnia spp. |
|
|
|
|
|
littoral and limnetic, usually
nearshore or in the warmer upper layers of water |
 |
Ceriodaphnia lacustris |
x |
x |
x |
x |
x |
| |
Ceriodaphnia laticaudata |
|
|
|
x |
|
| |
Ceriodaphnia pulchella |
x |
|
|
x |
|
 |
Ceriodaphnia quadrangula |
|
x |
x |
x |
|
 |
Ceriodaphnia reticulata |
|
|
|
x |
|
| |
Daphnia spp. |
x |
x |
x |
x |
x |
|
 |
Daphnia ambigua |
|
x |
x |
x |
|
very low abundances post-1970 |
 |
Daphnia galeata |
x |
x |
x |
x |
x |
Deep, transparent waters. |
 |
Daphnia longiremis |
|
x |
x |
x |
x |
Usually found below the thermocline
but above the poorly oxygenated regions |
 |
Daphnia lumholtzi |
|
|
|
|
|
Exotic. |
 |
Daphnia parvula |
|
x |
|
|
|
Green Bay and Milwaukee Harbor - rare |
|
 |
Daphnia pulex |
x |
x |
x |
x |
x |
easily confused with Daphnia
retrocurva so ID uncertain |
 |
Daphnia retrocurva |
x |
x |
x |
x |
x |
One of the most abundant cladocerans
in the Great Lakes. |
 |
Daphnia schodleri |
|
x |
|
|
|
Collected in 1970's |
| |
Scapholeberis spp. |
|
|
|
|
|
|
| |
Scapholeberis aurita |
|
x |
|
x |
|
Occassional, near surface, littoral. |
 |
Scapholeberis kingi |
x |
x |
|
x |
|
aka S. mucronata |
| |
Simocephalus spp. |
|
|
|
|
|
|
 |
Simocephalus exspinosus |
x |
|
|
|
|
|
 |
Simocephalus serrulatus |
|
x |
|
x |
|
Abundant in the littoral areas
of Lake Erie. |
 |
Simocephalus vetulus |
x |
|
|
x |
|
| Family Moinidae |
|
|
|
|
|
|
 |
Moina micrura |
x |
x |
|
|
|
generally low numbers but may reach high densities
in Green Bay |
| Family Bosminidae |
|
|
|
|
|
|
| |
Bosmina coregoni |
x |
|
|
|
|
|
| |
Bosmina liederi |
x |
|
|
|
|
|
 |
Bosmina longirostris |
x |
x |
x |
x |
x |
Found in cool, well-oxygenated
waters and littoral areas. Abundant during the summer. |
| |
Eubosmina spp. |
|
|
|
|
|
|
 |
Eubosmina coregoni |
x |
x |
x |
x |
x |
prefers warm, epilimnetic water.
Abundant summer species, only recently observed in the Great
Lakes (post-1970). |
| |
Eubosmina longispina (?) |
|
|
x |
x |
x |
|
|
| Family Macrothricidae |
|
|
|
|
|
|
 |
Acantholeberis curvirostris |
|
|
x |
|
|
shallow waters of Georgian Bay, 1903 |
| |
Drepanothrix dentata |
x |
x |
|
|
|
rare - Isle Royale and Georgian Bay |
| |
Ilyocryptus
spp. |
|
|
|
|
|
|
| |
Ilyocryptus acutifrons |
|
x |
|
|
|
SE Lake Michigan 1980 |
 |
Ilyocryptus sordidus |
x |
x |
|
x |
|
littoral - rare |
 |
Ilyocryptus spinifer |
x |
|
|
x |
x |
variable abundance |
| |
Macrothrix laticornis |
x |
x |
|
x |
x |
rare |
| |
Ophryoxus gracilis |
|
x |
x |
|
|
littoral Georgian Bay and Green Bay |
| |
Wlassicsia kinistinensis |
|
x |
|
|
|
occassionally found among nearshore vegetation |
| Family Chydoridae |
|
|
|
|
|
|
 |
Acroperus harpae |
x |
x |
|
x |
|
littoral, benthic, abundant in
some areas of Green Bay |
| |
Alona spp. |
x |
|
|
|
|
|
 |
Alona affinis |
x |
x |
x |
x |
x |
benthic, near bottom in weedy littoral areas, |
 |
Alona circumfimbriata |
|
x |
|
|
|
littoral, benthic |
| |
Alona costata |
x |
x |
|
x |
|
low density, littoral, benthic |
 |
Alona guttata |
x |
x |
|
x |
|
low density, littoral, benthic |
| |
Alona lepida |
x |
|
|
|
|
planktonic, ID uncertain |
 |
Alona quadrangularis |
|
x |
|
x |
|
littoral, benthic |
| |
Alona rectangula |
x |
x |
|
x |
|
low density, littoral, benthic |
| |
Alonella spp. |
|
|
|
|
|
|
| |
Alonella excisa |
|
|
|
x |
|
rare |
| |
Alonella nana |
x |
|
|
x |
|
Isle Royale and littoral Lake Erie |
| |
Alonopsis elongata |
x |
|
|
|
|
rare |
| |
Anchistropus emaginatus |
x |
|
|
|
|
|
| |
Anchistropus minor |
x |
x |
x |
|
|
Isle Royale, Georgian Bay, Green Bay, weed-associated |
| |
Camptocercus spp. |
|
|
|
|
|
|
| |
Camptocercus macrurus |
|
|
|
x |
|
near bottom in weedy areas |
 |
Camptocercus rectirostris |
x |
x |
x |
x |
x |
littoral, occassional high local abundances |
|
| |
Chydorus
spp. |
x |
|
|
|
|
Nearshore and littoral - eutrophic,
usually found clinging to fliamentous algae. Epibenthic by
day. |
| |
Chydorus faviformis |
|
x |
|
|
|
| |
Chydorus gibbus |
x |
|
|
x |
|
| |
Chydorus globosus |
x |
|
x |
x |
|
| |
Chydorus latus |
|
|
|
x |
|
 |
Chydorus sphaericus |
x |
x |
x |
x |
x |
| |
Disparalona
spp. |
|
|
|
|
|
|
| |
Disparalona acutirostris |
x |
|
|
|
|
|
 |
Disparalona rostrata |
x |
x |
|
|
|
recent (1980) and rare to Lake Michigan |
| |
Eurycercus lamellatus |
x |
x |
x |
x |
x |
benthic, moving into the water
column at night |
 |
Graptoleberis testudinaria |
|
x |
x |
x |
|
very low numbers |
 |
Kurzia latissima |
|
|
x |
x |
|
occassional |
 |
Leydigia acanthocercoides |
|
|
|
x |
|
5 sites, 1960 |
 |
Leydigia leydigi |
|
x |
x |
x |
|
rare |
| |
Leydigia quadrangularis |
x |
|
|
|
|
|
 |
Monospilus dispar |
x |
|
x |
x |
|
<6 per cubic meter |
| |
Pleuroxus
spp. |
|
|
|
|
|
|
| |
Pleuroxus aduncus |
|
|
|
x |
|
Cedar Bay |
 |
Pleuroxus denticulatus |
|
x |
|
x |
|
littoral |
| |
Pleuroxus hastatus |
x |
|
|
|
|
open water 1893 |
| |
Pleuroxus procurvus |
|
x |
|
x |
|
|
| |
Pleuroxus striatus |
|
|
|
x |
|
4 nearshore locations |
| |
Rhynchotalona falcata |
x |
|
|
|
|
<1 per cubic meter |
Table drawn from "Zooplankton of the Great
Lakes: A Guide to the Identification and Ecology of the Common
Crustacean Species" by Mary Balcer, Nancy Korda and Stanley
Dodson. University of Wisconsin Press. 1984.
with additions from: Lake
Superior: an invasion coldspot? 2003. Igor A. Grigorovich, Alexei
V. Korniushin, Derek K. Gray, Ian C. Duggan, Robert I. Colautti&
Hugh J. MacIsaac. Hydrobiologia 499: 191-210. |
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