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Secondary
Production
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Primary
Production: despite general dependence of
secondary on primary production, sometimes poor measure/predictive of secondary
production:
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Phytoplankton
may be no good food for zooplankton
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Primary
production is more than zooplankton can consume, large part of primary
production sinks out of watercolumn: sedimentation
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Part
of primary production enters microbial loop with less transfer to higher
trophic levels
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Asumption:
Production = D
biomass / D
time
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Problem:
hard to follow distinct population or cohort (individuals of same generation/
age) and/or same body of water over extended times
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Cohort
analysis: Knowing succession time of developmental
stages (cohorts), number of individuals per cohort and average body mass
can provide secondary production

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Changes
with life stage, season, food supply; may be negative in winter when zooplankton
don‘t feed and lose weight
The Study of
Zooplankton Production
1. Laboratory-scale
experiments
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study
individual organisms in small volumes of water; typically food requirements/prefereces,
transfer efficiencies, physiological responses upon stressors (temperature,
salinity, UV, etc.); depend on easy to handle species, mostly herbivorous
copepods
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Grazing
rates: selected food organisms are added in known numbers, disappearence
of food is quantified; Food uptake is mostly linear above a minimum threshold
food concentration and below food saturation
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Predator-Prey
Oscillations:Predators will grow after their food source has grown to
provide enough food for rapid reproduction; predators will decrease food
abundance until they become food limited; grazing pressure decreases,
thereby food can proliferate again, etc.

2. Enclosed systems
experiments
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also
referred to as mesocosm
experiments – large containers of seawater or plastic bag-encolosed seawater
in situ to study interaction of trophic levels and their responses upon
environmental changes
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Mesocosm
> 1000 L; microcosm
10 – 1000 L
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Problems:
lack of natural turbulence, growth on wall of containers, careful choice
of vessel material as to toxicity and chemical absorption
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Benthic
species can be
included by open-bottom systems mounted to the sea floor; still dwellers
and in-bottom fauna may move in and out through the sediment (sediment
enclsoures by deep collars)
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Benefits:
studies of pollution effects in large water bodies without impact on the
environment; time-series in the order of zooplankton generation times within
the same water body

More
information on the "plankton tower " (lower picture, upon delivery) used
by the Max-Planck-Institute for Limnology in Plön, Germany, klick
here!
3. Computer simulation
of marine systems
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Concept:
Known data and measured variables are fed into mathematic models to describe
(static models) or predict (dynamic models) not measured or not measurable
natural processes
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Types
of models: contain variable numbers of „compartments“
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Parameters:
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Forcing
functions: irradiance, nutrient concentrations,
contrains on proudction
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Physiological
functions: non-linear reaction of organisms
to forcing functions
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Phasing
functions: modify (speed up or slow down)
physiological functions, e.g. temperature dependence of physiological reactions
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Advantages:
Models can describe or predict what we cannot yet measure due to technical
difficulties; especially predictive models can describe the potential outcome
of „what if“ scenarios and are helpful in management and mitigation projects
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Problems:
Models rely on numerous assumptions and generalizations; number of „compartments“
is always less than natural complexity of ecosystems; models cannot subsitute
for real life measurements; models have to be verfied for each new ecosystem/region
applied to by „ground truth data“
4. Biomass-specific
production: the P/B Ratio
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P/B ratio:
Production / Biomass, mostly on annual scale, but shorter time scales are
possible; i.e. P/B = 300 of phytoplankton means that phytoplankton produces
annually 300 times its own biomass; land plants are high biomass but slow
growth organisms, thus their P/B is only 0.2-0.5!
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Decrease
with size and body mass within and among different species
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Decrease
with each trophic level by one order of magnitude (remember transfer efficiency
among trophic levels ca. 10% only!)
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