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lentic system
“still waters” - slowly flowing open body of water in a depression not in contact with the ocean
what are the three general characteristics of rivers?
distinct edges
homogenous bottoms
well-mixed water
tectonic lakes
formed by faulting
rift lakes or grabbers
commonly steep sided and very deep
formed by uplifting of sea floor
Horst lakes (block tilting)
commonly shallow
volcanic lakes
formed within calderas of extinct volcanos
commonly steep and very deep
formed with lava cuts off and dams rivers
glacial lakes
formed by actions of glaciers
most common type of lake
cirque (tarn lakes), valley, and kettle lakes
other types of lakes
artificial (reservoirs)
dammed lakes (natural and artificial)
sinkholes (karst regions)
floodplain lakes (oxbow, levee)
playa, dune, meteorite lakes and ponds
morphometry
size, shape, depth
attributes impact lake function (productivity)
zonation of lakes
littoral (can drive photosynthesis)
pelagic (limnetic - middle of the lake)
profundal (benthic, too deep to drive photosynthetic work)
photic zone
deep enough for light, P/R > 1
aphotic zone
no light, P/R < 1
thermocline
steep transition of temperature, based on the density of the water
compensation depth
P = R
light
reflected, absorbed, scattered
declines with depth
photic, aphotic zones
affected by turbidity, color, algae, POM
temperature
varies with season, depth, latitude, and altitude - thermal stratification
epilimnion
high oxygen
metalimnion
thermocline
hypolimnion
low oxygen
water motion
driven by wind
substratum
basin dependent
dissolved oxygen
may be low in hypolimnion of some lakes (clinograde profile - stratified lake)
may be high in hypolimnion of some lakes (orthograde profile - well-mixed lake)
salinity
species richness declines with salinity
may cause stratification
acidity pH = -log(H+)
few species tolerate very high or very low pH
a bell curve
nutrients (nitrogen and phosphorus)
P (often the limiting nutrient in lakes)
oligotrophic (unproductive)
low nutrients
not much oxygen saturation
low biota and productivity
high light
deep lake with steep sides
eutrophic (productive)
high nutrients
great variation in oxygen saturation
high biota and productivity
low light
shallow lakes with gently sloping sides
biological taxa
macrozooplankton (>200 um)
malacostracans, copepods, cladocerans, daphnia
microzooplankton (<200 um)
rotifers, protozoa, copepods
phytoplankton taxa: cyanophyta
gas vesicles, nutrient fixing, grazing resistant
phytoplankton taxa: chlorophyta
increased SA, stay near the surface, rapid reproducers
phytoplankton taxa: bacillariophyta
diatoms, grazing resistant, asexual and sexual reproduction
phytoplankton taxa: chrysophyta
golden/brown algae, two flagella, can transfer between autotrophic and heterotrophic
phytoplankton taxa: cryptophyta
extremely small, grazing resistant
phytoplankton taxa: pyrrophyta
grazing resistant, has toxins, spinning mechanism
basic food chain: pelagic zone
large fish (piscivorous), smaller fish (zooplanktivorous), zooplankton, phytoplankton
basic food chain: profundal (benthic) zone
fish, invertebrates (collectors), detritus
complex food web: pelagic zone
piscivorous fish also eat nektonic invertebrates
planktivorous fish also eat nektonic invertebrates and carnivorous zooplankton
nektonic invertebrates and carnivorous zooplankton eat herbivorous zooplankton
herbivorous zooplankton eat in the microbial loop
protozoan eat bacteria (DOM/POM), very small algae, cyanobacteria, flagellates
complex food web: profundal (benthic) zone
fish can directly eat detritus
in shallow lakes, periphyton may be important
in some lakes, there may be fish that eat detritus and/or algae
littoral zone
rocky shores (much like stony streams)
plants (macrophytes) provide complex structure producing complex food webs
submergent plants
all photosynthetic parts are underwater
floating plants
rooted & unattached
all photosynthetic parts are on the surface
emergent
rooted in sediment - photosynthetic parts can be either above or below
four energy sources in the littoral zone
detritus, macrophytes, periphyton, phytoplankton
diversity
littoral > pelagic > profundal
what are the 6 reasons that cause complex interactions in food webs?
predatory and grazing guilds of vertebrates and invertebrates
multiple types of primary producers
omnivory
ontogenic niche shift
feedback loops
detritus, algae, and macrophyte based food webs
phytoplankton season #1: ice break and spring turnover
deep circulation (isothermal)
high wind speed - high water movement
light is increasing but low
water is cold
nutrients is high (Si, N, and P)
diatoms and small unicellular green algae are dominant (r-selected)
phytoplankton season #2: onset of stratification (late spring-summer)
wind slows - mixing decreases
light is high, temp increases
Si in epilimnion decreases
Si:P and Si:N ratios decrease
zooplankton increases
edible phytoplankton decreases
phytoplankton season #3: clearwater phase
zooplankton increases
algal populations crash due to grazing
water transparency increases
nutrient saturated growth can occur or a limited time again, but Si remains low (low competition)
phytoplankton season #4: late summer (early autumn)
algae competing at low nutrient levels
N and P supplied by zooplankton excretion
higher nutrient patches available to motile algae and storage specialists
cyanobacteria, gelatinous green, and dinoflagellates increase
fall mixing may generate secondary bloom (wind speed increases)
seasonal phases
succession of R to K selected species
bottom-up effects (eutrophic lakes)
surveys: correlations across lakes
uncontrolled, natural experiments: changes following increases or decreases in nutrient input
laboratory experiments: lose control
field experiments
small jars - diverge from natural conditions
large bags (mesocosm)
whole system - difficult to replicate
top-down effects (cascading effects)
important in mesotrophic and oligotrophic lakes
top-down effects: fish-zooplankton in Connecticut Lakes
observations
alewives present - small zooplankton species
alewives absent - large zooplankton species
natural experiment
huge shift in size of zooplankton after the introduction of alewives
why do large zooplankton species dominate when fish are absent?
hypothesis #1: large zooplankton are competitively superior over small zooplankton
observation
large zooplankton are very vulnerable to fish predation
results
exploitative competition
conclusions
large zooplankton are competitively superior if they are much larger than small zooplankton
if Daphnia decrease - increase in small zooplankton
if large zooplankton are not greatly larger than small zooplankton, then the outcome of competition is complex and often unpredictable
outcomes may depend more on abiotic factors
why do large zooplankton species dominate when fish are absent?
hypothesis #2: invertebrate predators (large zooplankton) reduce the abundance of small zooplankton
transfer experiment
results
small Daphnia alone, survived, not abiotic factors
small Daphnia and large Daphnia, survived, not competition
small Daphnia and large copepod, eliminated, predation
conclusions
invertebrate predation kept small Daphnia out of ponds, large Daphnia resistant to invertebrate predation
Peter Lake
4 trophic levels
piscivorous fish, planktivorous fish, zooplankton, phytoplankton
Tuesday Lake
3 trophic levels
planktivorous fish, zooplankton, phytoplankton
Peter and Tuesday Lake Experiment
add piscivores to tuesday (decrease Pl, increase zoo, decrease phyto)
matched the expectations
remove piscivores from peter (increase Pl, decrease zoo, increase phyto)
did not match the expectations
cannot remove all piscivores from the lake
slower interactions
planktivores hid in littoral zone
algae dominated by forms with increased with zooplankton grazing (grazing resistant)
habitat complexity: treatments with and without fish under three levels (insectivorous fish, invertebrate predator, invertebrate grazers/collectors)
fish biomass accrual dependent on habitat complexity
low: find prey - consumes all and starves, high predation
middle: less macrophytes but enough to survive, the highest fish biomass, moderate predation
high: low fish yield, macrophytes hiding, low predation
Flathead Lake, Montana
native cutthroat and bull trout lost due to overfishing
Flathead Lake Exotic species introduction
introduced lake trout and kokanee salmon as replacement
lake trout ate large zooplankton and small kokanee salmon
kokanee salmon ate large zooplankton
kokanee salmon run usotread to breed, served as food for bears and eagles
increased tourism and fishing
Flathead Lake secondary introduction
opossum shimp (Mysis) introduced into drainage as additional food for kokanee (but they also eat large zooplankton)
opossum shrimp outcompete kokanee salmon for large zooplankton via exploitative competition and reduce large zooplankton - kokanee eliminated
bears and eagles decrease (tourism fails), lake trout increase in number but decrease in size
secondary species introduction reduces biodiversity