Title: Why Study Continental Aquatic Systems
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2Unusual or Extreme Habitats
- Adaptations to Extremes
- Saline Lakes
- Hot Springs
- Cold Habitats
- Temporary Waters and Small Pools
- Ultra-Oligotrophic Habitats
- Deep Subsurface Habitats
- Neuston
3Molecular Adaptations to Extremes
- DNA- stabilized against high temperature by more
binding proteins, more CG pairs - RNA- more extensive regions of base pairing in
areas that need to hold conformation - Membranes- higher temperatures increase
saturation, branching and length. In Archaea,
ether lipids
4Molecular Adaptations to Extremes, continued
- Proteins- thermal stability, more ? sheets and ?
helix, hydrophobic core, high external charge - Salt- water is limiting. Need ways to stabilize
proteins from too many ionic interactions.
Complex animals pump out salt, halophilic
bacteria and Archaea are isotonic with water.
Some organisms use glycerol to remain isotonic - Lack of water- similar to salt. Organisms in
temporary habitats must be able to withstand
desiccation
5Saline Lakes
- Closed basins, evaporation balances with inputs.
Many lakes on earth are saline - Chemistry dependent upon watershed
- Limitation by O2 may be important because
solubility decreases with increased salinity - Brine shrimp can be important consumers, will not
coexist with fish - Aral Sea in Russia was the fourth largest lake in
the world but irrigation has decreased the lake
area by half. Dust storms from dried lake basin
now cause health problems
6Brine shrimp Artemia franciscana (ASLO image
gallery)
7Salinity Tolerance
8Hot Springs
- Thermophilic- heat loving organisms
- Bacteria and Archaea only inhabit highest
temperatures - Chemistry variable from very acidic to basic
- Acid springs dominated by sulfide sulfur
oxidizing bacteria common
9Upper Temperature Tolerances
10Emerald pool- Yellowstone (waymark.com)
11Adaptation to Hot Temperatures
12Community Dynamics in Hunters Hot Spring
13Cold Habitats
- Arctic habitats
- Organisms inhabit ice and snow
- Snow algae color snow pink
- Arctic lakes can be ice-free for only a month or
two - Antarctic lakes always have an ice cover
14Watermelon snow (www.estes-park.com)
15Temporary Waters and Small Pools
- Can be categorized by permanency
- Generally lack fish, larger pools can be
important for large crustacea and amphibian
breeding - Prairie potholes important for waterfowl
- Small pools in plants etc. form unique habitat.
Important for mosquito larvae - Some vernal pools (e.g. California) have high
numbers of endemic species
16Ultra-Oligotrophic Habitats
- Very low nutrients can be stressful
- If carbonate low enough, mollusks cannot survive
- Organisms grow slowly
17 ultra-oligotrophic Waldo Lake(www.waldocats.org
/ )
18Deep Subsurface Habitats
- All inhabited by microbes as long as liquid water
exists - Found at depths to 940 m
- Fungi rare, Bacteria and Archaea most common,
protozoa top predators - Active microbes found in waters isolated for 1200
years - Some may run off methanogenesis, H2 and CO2 come
from rocks. Only ecosystem on earth not
ultimately dependent upon photosynthesis
19Water Surface Layer
- Neuston- microbes at surface, Pleuston-
macrorgansims at surface - Unique chemical and biological habitat
- Extreme, high light and UV
- Velia capria use chemical that lowers water
tension to move up to 10 cm/s
20Organisms of the Water Surface
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22Nutrient Use and Remineralization
- Use of nutrients
- Nutrient limitation and relative availability
- Resource ratios and stoichiometry of primary
producers - Stoichiometry of heterotrophs, their food, and
nutrient remineralization
23Use of Nutrients
- Uptake into cell, Michaelis-Menten V uptake,
S substrate conc. Ks half saturation
constant - Monod equation, growth µ is growth rate
- Droop equation links concentration in cell (Q)
and minimum concentration in cell for growth (Q0)
to growth
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25Nutrient Limitation and Relative Availability
- Relative availability of nutrients
- Nutrient limitation
- The Paradox of the Plankton and nutrient
limitation
26Relative Availability of Nutrients
27Concept of Nutrient Limitation
- Leibigs Law of the Minimum
- The case for multiple nutrient limitations
28Hutchinsons Paradox of the Plankton
- Competitive exclusion principle- only one
organism is a best competitor for a limiting
resource and will dominate - Leibigs Law- only one nutrient limits
- Observation- most phytoplankton cells have
similar composition - The Paradox- why are there commonly 100s of
species of phytoplankton in a lake?
29Resource Ratios and Stoichiometry of Primary
Producers
- Nutrient remineralization
- What short-term processes control the levels of
dissolved inorganic nutrients such as ammonium
and phosphate? - Processes leading to remineralization
- Remineralization as a source of nutrient pulses
in lentic systems
30Redfield Ratio
- 106161 CNP by moles
- Algal cells have approximately this composition
under balanced growth - When N is limiting, may have 10651
- When P is limiting, may have 206321
- When N and P are limiting, may have 500161
- Can serve as an index of nutrient limitation
31Nutrient Remineralization
- Usually uptake is high enough that nutrients
would be completely exhausted without
remineralization (regeneration) - The concentration of dissolved nutrients is an
amount, the flux through that pool is a rate.
These two should not be confused - Phosphate and ammonium concentrations can be very
low in a eutrophic lake
32Short-Term Processes can lead to an Equilibrium
Value of Nutrient Concentration
- Change in nutrient conc uptake - regeneration
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34Processes that lead to Nutrient Remineralization
- Leakage from healthy cells, excretion from
animals - Heterotrophic activities of bacteria
- Viral infections cause lysis of cells
- Nutrient remineralization often dominated by
microbial processes - In some cases, moving animals assist nutrient
import (salmon, hippos, migrating zooplankton)
35Nutrient Pulses
- Large algal cells are poor competitors for
nutrients at low concentrations (low surface area
to volume ratio) - Pulses of nutrients may last long enough to give
large cells an advantage if they run into the
patches, but are they stable? - Lehman and Scavia experiment
36Stoichiometry of Heterotrophs, their Food, and
Nutrient Remineralization
- Heterotrophs remineralize nutrients in excess of
need - Assume 9 C of energy needed for each C used for
growth, and growth is at Redfield ratio - A heterotroph needs food at 1000161. If it
eats food at 106161, it will excrete N and P
37Bacterial Remineralization Depends on Food Source
38Zooplankton Differ in Stoichiometry so vary in
Food Requirements and Remineralization
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40Trophic State and Eutrophication
- Definition of trophic state
- Why does nutrient pollution resulting in algal
blooms matter in lakes? - Natural and cultural processes of eutrophication
- Relationships among nutrients, water clarity, and
phytoplankton - Mitigating lake eutrophication
- Managing eutrophication in streams and wetlands
- Case studies of eutrophication
- Eutrophication and wetlands
41Definition of Trophic State
- Based on nutrients or producer biomass
- A way to describe a continuum of possible trophic
states - Useful in comparing systems across large areas
(e.g. an oligotrophic lake in Iowa may be
eutrophic in Idaho) - To be more accurate we should refer to
heterotrophic state and autotrophic state
42Two Trophic Classification Systems for Lakes
(autotrophic state)
43Why Does Nutrient Pollution Resulting in Algal
Blooms Matter in Lakes?
- Taste and odor problems
- Blooms of toxic algae
- Aesthetics (people less willing to pay to live
near, or recreate on, eutrophic lakes) - Fish kills
44Natural and Cultural Processes of Eutrophication
- Classical view that lakes slowly become more
eutrophic as they fill and become shallow,
eventually succession leads to a marsh, then a
meadow - Many large lakes may be oligotrophic for much of
their history - Natural eutrophication can occur, but
eutrophication caused by humans (cultural
eutrophication) is a world-wide problem
45Relationships among Nutrients, Water Clarity and
Phytoplankton
- Managing eutrophication in lakes requires
understanding of correlations between nutrients
and algal biomass - Management of fish populations can also include
consideration of trophic state
46Nutrient-Biomass Relationships
47Linking Lake Clarity to Nutrients
48Mitigating Lake Eutrophication
- Control of nutrient sources
- internal versus external loading
- Treatment in the lake
- Macrophyte removal
49Steps to Mitigate External Loading
50Why Eutrophication should be Controlled before
the Hypolimnion goes Anoxic
- FePO4 dissociates in anoxic conditions
- If hypolimnion goes anoxic then PO43- is
continuously recycled from sediments into the
water column, and mixed into the epilimnion - Can take many years to recover from
eutrophication even if point sources and
non-point sources are controlled
51Methods for Controlling Macrophytes
52Managing Eutrophication in Streams and Wetlands
- Methods not as clearly defined for streams and
wetlands, methods for streams more developed than
for wetlands - In general, principles are the same, control of
nutrient sources is better than treating the
symptoms
53Relationship Between Algal Biomass and Nutrients
in Streams
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55Case Studies of Eutrophication
- Lake Washington
- Lake Trummen
- Lake Tahoe
- Lake Okeechobee
- The Clark Fork River
56Lake Washington
- Noticed shift to eutrophic algal species
- Sewage diverted from Lake Washington in 1960s
- Cyanobacteria dropped out
- Were able to control trophic state before
hypolimnion went anoxic
57Effect of Nutrient Control in Lake Washington
58Lake Trummen
- In Sweden, 1 m deep, poor water quality, frequent
fish kills - Controlled point and non point sources to lake in
1960s but problems continued - Calculated that it would take hundreds of years
for nutrients in sediments to wash back out - Top half meter of sediments dredged and sold as
topsoil. Improved water quality to allow fish
survival and human recreation
59Lake Tahoe
- Ultra-oligotrophic lake on Nevada, California
border - Water retention time 700 years
- Septic systems were polluting lake, N limitation
(detergent inputs) - After sewage pumped out of basin, P limitation
(watershed disturbance increased N inputs) - Secchi depths are now 20 m rather than 40 m
historically - Future of lake uncertain
60Everglades/ Okeechobee
- Ag fertilizer runoff caused algal blooms in
Okeechobee and loss of native plant and algal
communities in Everglades (cattail replacing
sawgrass) - Canals and locks decreasing natural flushing
- Trying to restore natural hydrology
- Experimenting with using wetland areas to scrub P
from incoming waters - Agricultural lobby very powerful, and huge tax
base in Southern Florida, so this is a charged
issue - Not clear if the problems will be solved
61Eutrophication and Wetlands
- Wetlands serve as nutrient sinks
- Better at N than P removal because there is no
equivalent process to denitrification in the P
cycle - May work to remove plant biomass and allow
re-growth (bulk removal of P) - Many natural wetlands are oligotrophic, and
nutrient pollution destroys natural system
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63Behavior and Interactions among Microorganisms
and Invertebrates
- Behavior of microorganisms
- Interaction types in microbial communities
- Predation and parasitism
- Competition
- Mutualism facilitation and syntrophy
- Chemical mediation of microbial interactions
64Behavior of Microorganisms
- Motility
- Taxis
- moving toward or away from stimulus
- phototaxis, light
- geotaxis, gravity
- chemotaxis, chemicals
- magnetotaxis, magnetic fields
65Relative Rates of Movement of Organisms
66Random Walk Model of Chemotaxis
67Interaction Types in Microbial Communities
- Density-mediated versus trait-mediated
interactions - Direct verses indirect interactions
68Predation and Parasitism
- Viruses
- Consumption of small cells
- Scrapers and shredders
- Filter feeders
- Selectivity of particle feeders
- Microbial adaptations to avoid predation
- Parasitism
- Other exploitative interactions
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70Viruses
- All organisms have them
- May control algal blooms and bacterial
populations at times - Can be a problem in fish aquaculture
- Some small protozoa can engulf viruses
- Human disease viruses can survive in water
- Inactivated in natural environment over time
- May move genetic material across taxonomic lines
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72Consumption of Small Cells and Particles
- Function of particle size
- too small, the solution is too viscous, or
collection apparatus is too small - too large and wont fit in mouth
- Function of particle concentration
- Function of particle quality
- Greatest rates when entire assemblage is consumed
73Consumption and Particle Size
74Consumption and Concentration Energetic
Considerations
Protozoa increase consumption then level off
Daphnia slows down when particles are dense
75Consumption by Taxonomic Group
76Avoiding Predation
- Mechanical
- size (too small or too large)
- spines (chemical cues may induce protection)
- Chemical
- toxins (must be a majority in community, e.g.
algal bloom) - poor quality
- Behavioral
- escape
77Competition
- Exploitation versus interference competition
- Resource ratio theory
- Allelochemicals
78Resource Ratio Theory
79increasing
Species 2 wins, (low Si, high P)
Species 2, zero survival line
coexistence
PO43-
Species 1 wins, (high Si, low P)
Species 1, zero survival line
increasing
SiO42-
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81Mutualism Facilitation and Syntrophy
- Highly co-evolved mutualisms rare in freshwaters
relative to marine - N-fixing symbionts occur
- Syntrophy
- Nostoc-midge example
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83Chemical Mediation of Microbial Interactions
- Most microbial interactions mediated by chemicals
- All organisms use chemical cues
- Need to consider hydrodynamics (e.g. Reynolds
number) - unidirectional interactions in unidirectional flow
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85Predation and Food Webs
- Detritivory and omnivory
- Adaptation to predation pressure
- Adaptations of predators
- Non-lethal effects of predation
- Trophic levels, food webs, and food chains
- The trophic cascade
- Theoretical community ecology and aquatic food
webs
86Detritivory and Omnivory Many Organisms are
Omnivorous
87Using Stable Isotopes to Document Food Webs
- Several isotopes can be used to document food
webs. The most common ratios used are 15N/14N
and 13C/12C, expressed in parts per thousand - Nitrogen is heavier as you move up the food web.
Organisms track the C ratio in their food
88Examples of Isotopes in Food Webs
89Adaptation to Predation Pressure
- Mechanical
- size (too small or too large)
- spines (chemical cues may induce protection)
- Chemical
- toxins (must be large food item relative to
predator) - poor quality
- Behavioral
- escape (chemical, hydrodynamic, visual cues)
90Diel Vertical Migration in Daphnia
91Additional Behavioral Response of Daphnia
- May dive or swarm in response to chemicals
released when conspecifics are crushed - May produce diapausing eggs in response to
chemical cues - May reproduce more quickly at a smaller size
92Adaptations of Predators
- Hide and wait versus active foraging
- Sensory adaptations (sight, visual, hydrodynamic,
electrical, chemical) - Functional response versus numerical response
(Hollings functional response curves) - Predation only when predator pressure is lower
(e.g. many predators need to worry about being
prey)
93Functional Response Curves
94Foraging can be Modified by Food Density
95Non-lethal Effects of Predation
- Many predators dont kill prey, but can alter
their survival - Another prey species may be your savior if a
predator switches to that prey instead of you
when your population numbers are low - Macrophytes are not eaten entirely, but can be
grazed to some degree
96Trophic Levels, Food Webs, and Food Chains
- Food chains
- producers, primary consumers, secondary
consumers, decomposers - simple linear viewpoint
- Food webs
- allow for more complexity such as feeding at
different trophic level - more difficult to work with
97The Trophic Cascade
- Postulated since 1880 that predators can control
herbivores and increase biomass of producers - Top-down versus bottom-up control
- May use biomanipulation to control trophic state
98Conceptual Diagram of Trophic Cascade
99Biomanipulation in Netherland Lakes
100Trophic Cascade in a River
101Theoretical Community Ecology and Aquatic Food
Webs
- Are more diverse systems more stable?
- Is biodiversity related to ecosystem function?
- What controls lengths of food chains?
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103Nonpredatory Interspecific Interactions among
Plants and Animals in Freshwater Communities
- Competition
- Mutualism and facilitation
- Other species interactions
- Complex community interactions
104Competition
- Difficult to establish in the field
- Primary producers compete for nutrients and
light, benthic for space - Can structure wetland plant communities
- Leads to evolutionary specialization (niche
partitioning) over time
105Niche Partitioning in Two Rotifers
106Mutualism and Facilitation
- Mutualism usually approached on a case-by-case
basis - Cichlid fish will brood in multi-species groups
to protect eggs from predators - Groups of wetland plants may facilitate each
other in harsh environments - Invertebrates may facilitate others in feeding
relationships
107Mutualism in 3 Tubificid Oligochaetes
108Other Species Interactions
- Many examples where one species has a strong
effect on another and the second little effect on
the first - Humans are the ultimate example, we harm many
species that have little influence on us. We
also help some species (e.g. sportsfish) that
have little effect on our survival
109Complex Community Interactions
- Disturbance
- Succession
- Indirect interactions
- Strong interactors
110Disturbance
- Response to disturbance dependent upon
characteristics of disturbance and organisms - Disturbance
- intensity
- areal extent
- frequency
- Organisms
- colonization ability
- resistance (e.g. diapause)
- distance to refugia
- growth rate
- What are some potential examples of disturbance
in wetlands, lakes, and streams?
111An Example of Harshness
Characterized by time since flood,
intensity of flood, time since dried,
length of dry period, and distance from source of
permanent water
112Succession
- Often represented as a predictable sequence of
community development after a disturbance or
change in environment - Seasonal succession in lakes
- Succession after reservoir construction
- Colonization after flooding in rivers
- Wetland restoration
113Seasonal Succession in Lakes
Concentration
Si
Total P
Large grazer resistant phytoplankton
Cyanobacteria
Diatoms
per L
Small body rapid growing zooplankton
per L
Large zooplankton
Biomass per m2
Macrophytes
Total young of the year fish
per m2
Larvae of individual fish species
Total Fish Biomass per m2
All fish
Stratification
Autumn mixing
Winter Spring Summer Autumn Winter
114Seasonal Succession in Fish Reproduction
115Seasonal Succession in Streams
Leaves in stream
Light at stream surface
Amount
Discharge
Discharge or temperature
Temperature
Biomass
Periphyton
Fast seasonal, insect larvae with summer
reproduction
Biomass
Biomass
Slow seasonal, insect larvae with winter growth
Long-lived species and quick reproducers (fish,
predators, mosses , FBOM feeders)
Biomass
Winter Spring Summer Autumn Winter
116Succession Following Reservoir Construction
- Macrophytes become established, community becomes
more diverse over decade or so - Productivity initially high because of nutrients
released from flooded vegetation - Fish and invertebrate communities shift from
riverine to lacustrine and pelagic lake species
117Succession and Wetland Restoration
- Two approaches
- let natural processes restore natural community
(e.g. from seed bank or come in on waterfowl
etc.) - re-introduce native species
- Often difficult to introduce species and get them
all to take - Some species will take a long time to come back,
if ever, so reintroduction needs to occur - A blend of the approaches should be taken
118Indirect Interactions
- How long are interaction chains in natural
communities? - Trophic cascade good example of indirect
interaction chains - Cladophora can benefit epiphytes (place to live)
and indirectly grazers. The grazers may help
Cladophora by lowering the amount of epiphytes
that compete for nutrients
119Indirect Interactions between Fish and Ducks
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121Fish Ecology and Fisheries
- Biogeographical determinants of fish assemblage
diversity - Physiological aspects influencing growth,
survival, and reproduction - Population dynamics of fishes
- Regulating exploitation of fish stocks
- Stocking fish for fisheries
- Aquaculture
122Biogeographical Determinants of Fish Assemblage
Diversity
- More diverse on large continents than small
- More diverse in old lakes and watersheds
- More diverse in tropics than temperate
- More diverse with more within-habitat diversity
- More diverse in larger rivers than small
123Fish Diversity with Distance Downstream
124Physiological Aspects Influencing Growth,
Survival, and Reproduction
- Energetics control growth, survival and
reproduction - Osmoregulation can be important, particularly for
andromedous species - Temperature, oxygen, food quantity and quality,
predator avoidance all important
125Energetics across a Gradient
126Temperature Interacts with Trophic State
127Effect of a Predator on Food Consumption
128Population Dynamics of Fishes
- Stock- population size
- Production- population growth
- Recruitment- number entering an age class
- Numerous indices to quantify stock, production,
age structure,and recruitment
129Regulating Exploitation of Fish Stocks
- Maximum sustainable yield- calculated when number
of adults and young known - Regulations used include size allowed, closed
seasons, gear, and number of fish removed - Closed seasons particularly useful for times when
fish are susceptible to harvesting (e.g. spawning
times)
130Stocking Fish for Fisheries
- Many fisheries managers stock fish
- Useful to boost native stocks
- Can introduce new species (e.g. lake species when
a reservoir or pond is made) - Some major problems with introductions include
disease, outcompeting native fishes,
hybridization with native fishes, lack of genetic
diversity in populations
131Aquaculture
- World fish production dominated by carp, an
important source of protein in many developing
countries - Management of aquaculture requires understanding
of ecology including trophic state, transmission
of disease, ecology of food organisms
132Global Production of some Freshwater Organisms
in 1989
133Zooplankton predators
Benthic predators
Foragers
0.7
2
0.5
Zooplankton
Benthic consumers
2
12
Phytoplankton
Periphyton
71
41
134Freshwater Ecosystems
- General approaches to ecosystems
- Groundwater ecosystems
- Streams
- Lakes and reservoirs
- Wetlands
- Comparison of freshwater ecosystems
135General Approaches to Ecosystems
- Trophic levels
- Energy flux budgets
- Efficiency of trophic levels not 100
- Nutrient budgets
136Trophic Pyramids and Energy Flux
137A Nutrient Flux Budget
138Biodiversity and Ecosystem Function
- Controversial
- Usually enough microbial diversity is present for
an ecosystem to function at same rate regardless
of diversity - Important in low diversity systems (e.g. if only
one species of shredder, then its absence will
substantially alter the ecosystem) - Benthic invertebrate diversity may alter nutrient
flux across sediment/water interface
139Groundwater Ecosystems
- Often rely on organic material washed in from
surface - Can be ultraoligotrophic
- Permeability and water flow very important,
animals common when large channels exist in
groundwater
140Relative Rates of Ecosystem Respiration
141Streams
- Flood pulse concept
- Autochthonous versus allochthonous production
- Nutrient spiraling
- River continuum concept
142Flood Pulse Concept
- The traditional idea was that floods were
disturbances - More recent realization that flooding is an
integral part of ecosystems - Moves materials to and from riparian flood zone
- Increases connectivity between oxbows and
wetlands in riparian areas and river - Resets communities
- Encourages reproduction of some species
143Autochthonous versus Allochthonous Production
- When light reaches system, more primary
production - Forested areas have large amounts of leaf input
- Metabolic measurements suggest almost all streams
are net heterotrophic, some just more so than
others
144Nutrient Spiraling
145River Continuum Concept
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147Lakes and Reservoirs
- View of lake ecosystems has expanded to include
watershed - Global surveys suggest that shallow lakes are
more common than deep (littoral zone important
part of ecosystem) - Surveys of CO2 shows supersaturation in most
lakes, indicating that heterotrophy is more
important that autotrophy
148Generalized Ecosystem Characteristics of
Temperate Lakes
149Wetlands
- Most productive ecosystems on earth
- Herbivory not very important in most systems
- Hydrology drives function, including flow
thorough and nutrient sources
150Pantanal, the Worlds Largest Wetland Ecosystem
Complex
- Brazil, Bolivia, Paraguay
- During wet season, floods connect pools
- During dry season, pools isolated and concentrate
fish and their predators - Home to many endangered species
- Plans underway to channelize river and decrease
the upper part of the wetland by half
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152Comparison of Freshwater Ecosystems across
Gradients
153Comparison of Trophic Webs
154Experimental Design in Aquatic Ecology
- Natural Experiments
- Simulation Modeling
- Manipulative Experiments
155Natural Experiments
- Things happen naturally to whole systems that can
be used to test ideas about those systems (Mt.
St. Helens) - Natural patterns can be determined via
correlation - Not causation, but does increase understanding of
systems
156Simulation Modeling
- Models can indicate where we lack knowledge
- Models can test scenarios where experimentation
is impossible (e.g., global warming) - Sensitivity analysis can be used to find the
variables that control the parameter of interest
157Manipulative Experiments
- To formally test a hypothesis, a manipulative
experiment is necessary - Need controls and replication
- When experiments are properly designed,
statistics can be used to test probability that a
specific result supports the hypothesis