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77 Cards in this Set

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What are some possible explanations for this trend through time?

What are some possible explanations for this trend through time?

- Increased temp could decrease the amount of oxygen that can be in the water and could change the seasonal mixing


- Increased duration of stratification could cause
more seasonal oxygen depletion

What are three reasons DIC (dissolved inorganic carbon) are important in freshwater systems?

1) Main source of C for photosynthesis
2) Buffers water against pH changes
3) Pathway of C removal (and minerals) from the water

Nutrient

- Any element that an organism must acquire to live, grow, and reproduce. Energy for metabolism.

What are the 6 big macronutrients?

C, H, N, O, P, S (sounds like chinops)

Biogeochemical cycle

- Is a pathway by which a substance moves through biotic (biosphere) and abiotic (lithosphere, atmosphere, and hydrosphere) realms.

Name these:


CO2


H2CO3


HCO3-


CO32-


CaCO3


Ca(HCO3)2

- carbon dioxide


- carbonic acid


- bicarbonate


- carbonate


- calcium carbonate


- calcium bicarbonate

What adds up to give you the sum total of CO2 (DIC)?

ΣCO2 (DIC) = CO2 + HCO3- + CO32-

Alkalinity

- Amount and types of compounds that collectively increase the pH of water or acid neutralizing capability. Expressed as the total quantity of a base.

Buffering capacity

- Is the ability to resist pH changes.

Lake water pH is largely controlled by what?

- The buffering reactions of ionic forms of DIC: H2CO3 = carbonic acid, HCO3- = bicarbonate, and CO32- = carbonate.


- These compounds are largely derived from the weathering of rocks

Endorheic regions

- Basins that are closed hydrologic systems, they don't flow into the ocean.


- Soda lakes found in these regions have high pH because they contain high [Na2CO3] due to the inability to drain to the ocean, so are controlled mainly by precipitation

Distribution of ΣCO2 (DIC) in water is influenced by what 5 factors?

1) Atmospheric CO2 and solubility in water


2) Equilibrium reactions
3) Weathering of rock
4) Photosynthesis (sink)


5) Respiration (source)

How soluble is CO2 in water compared to O2?

- CO2 is very soluble in water and lakes tend to be supersaturated


- 200x as soluble as oxygen in water

How is the solubility of CO2 controlled?

- Inversely related to temp and salinity


- Directly related to pressure


- Influenced by ionic carbon complex

How does the addition or removal of CO2 to a system change the equilibrium and pH?

- CO2 input shifts equation to the right and decreases pH


- CO2 removal by photosynthesis shifts equation to the left and increases pH

Lake Whiting

- A massive calcium carbonate precipitation event


- The precipitation of CaCO3 (marl) occurs when high photosynthesis and temp (great losses of CO2) shifts the DIC equilibria.

Why study [P] and cycling?

- Key component of biomolecules (e.g. DNA, RNA, ATP, lipids)


- Often first element to limit algal growth


- Management implications (Detergent Wars of the 1960-70s)

Orthophosphate

PO4-3


- Is the most significant form of P. P is very reactive and tends to form insoluble compounds- especially under aerobic (oxidized) conditions.


- Is the most important, and the form that algae use, it is difficult to measure reliably

Liebig’s Law of Minimum

- The element present in the lowest [conc.] relative to its demand limits growth.

Redfield ratio

- Rapidly growing algae uptake ratios of C, N, and P in a characteristic proportion, 106C: 16N: 1P (by atom),

Luxury uptake

- In order to obtain the limiting resource (P), algae can store P in vacuoles when availability is high

Explain each part:



Total Phosphorus (TP) = DIP + DOP + PP


DIP – (<5%) dissolved inorganic phosphorus PO43-


DOP – organic colloids, less available
PP – particulate P, often largest % of P in lakes (>70%)

[TP] in natural waters ranges from:

< 1 ug l-1 to > 200 ug l-1


- Variation is high and reflects regional geology.


- Most NB lakes 10-50 ug l-1

Trophic status of an aquatic ecosystem

- Represents its level of nutrients and algal growth.

Explain how phosphorous would change in lakes with an orthograde O2 curve vs lakes with a clinograde O2 curve.

- Lakes with orthograde O2 curve show little variation in P with depth.


- Lakes with clinograde O2 curve show ↑ P in hypolimnion.


- P exchange regulated by oxygen supply and metabolism of decomposers.


- Sediment-water interface is key.

External (allochthonous) phosphorous sources

1) Atmospheric fallout (eg dust from erosion, fires, fossil fuels)


2) Ground water- very minor
3) Runoff and weathering of rocks/soils
4) Sewage and agriculture


5) Guano from animals (eg seabirds)

Internal (autochthonous) sources of P in lakes


1) Food web- excretion by zooplankton and fish (taken up quickly)


2) Algae and macrophytes


3) Sediments and benthos

Name transport mechanisms of P at the sediment-water interface.

- Diffusion


- Wind-induced turbulance


- Bioturbation


- Gas ebuilition


- Attached algae/BG's


- Rooted aquatic plants

Explain

Explain

- If you have an oxidized sediment-water interface, then there is a barrier to PO43- release from the sediments.

What happens to P movement when sediment-water interface is anoxic?

- If the interface goes anoxic, then the barrier erodes and you get internal loading of PO43- from the sediments.


- As redox potential ↓ = release of P, Fe, etc. increase markedly.

Iron (Fe) role interacting with P

- Iron (Fe) plays a key role as a binding agent under oxic conditions.


- Fe (III) oxide (ferric form) binds to orthophosphate preventing its release from the sediments.

How do we manage excess nutrient loading?

- Removal of P from wastewater in sewage treatment plants


- Prevent wastewater from entering rivers and lakes


- Buffer strips along nearshore areas to trap nutrients


- Add chemical agents that bind P

Why study N and its cycling?

- Biomolecules (e.g. proteins, DNA, chlorophyll) largely composed of N


- Major nutrient in all ecosystems


- Complex microbial-driven cycle


- Human activities adding huge amounts to biosphere


- N accumulating in global ecosystems!

N enters a drainage basin in many forms:

1) N2 gas (strong bonds) *(only available to primary producers when converted into ammonia NH3)


2) Inorganic N (all can be found in atmosphere)


NH4+ = ionized ammonia


NH3 = ammonia
NH2OH = hydroxylamine


NO2- = nitrite


NO3- = nitrate


3) Organic N


DON = dissolved organic N


PON = particulate organic N

Major transformations of N are:

- N fixation (N2 > NH3, anoxic conditions)


- Nitrification (NH3 > NO2- > NO3-, oxic)


- Denitrification (NO3- > NO2- > NO/N2O . N2, anoxic)


- Anammox ( NO2- and NH3 > N2, anoxic)


- Ammonification (organic N > NH3, oxic)

Sources of N in aquatic ecosystems

1) Direct deposition onto surface (NOx, mainly forms)


2) Allochthonous inputs from surface and groundwater interacting with soils


3) N fixation in water and sediments

N fixers in aquatic systems

- Cyanobacteria (blue-green) and heterotrophic bacteria (often found in sediments and water column)


- All N fixers have an enzyme complex called nitrogenase that catalyzes the reduction of N2 to NH3 (ammonia).

Heterocyst

- Cell in cyanobacteria where N fixation occurs.


- Light-dependent process.


- Protect enzyme from O2.

Nitrification

- Conversion of ammonia to nitrite and then to nitrate.


- Occurs aerobically by microbes.


- First is oxidation of ammonia to nitrite via hydroxyamine.


- Next is the oxidation of nitrite (NO2-) to nitrate (NO3-) by different set of bacteria.

Anammox bacteria

- Oxidize ammonia in anaerobic conditions by using nitrite as the electron acceptor to produce N2.

Denitrification

- Conversion of nitrate to N2, thus removing bioavailable N and returning it to the atmosphere.


- Necessary in sewage treatment.


- It is an anaerobic process, occurring in soils, sediments, and anoxic zones of lakes.

Losses of N in aquatic systems
1) Outflow from surface and groundwater
2) Denitrification by bacteria (NO3- to N2)
- returns N2 back to atmosphere in gas form
3) Sedimentation of inorganic and organic N compounds

*Also annamox
Explain

Explain

- NH4+ quickly utilized by algae in upper layers


- Increase in NH4+ at thermocline because of anoxic processes


- During anoxia release of NH4+ occurs from the sediments. Nitrification ceases.

What’s so special about shallow lakes?

- Numerically dominant in lowland regions


- Humans depend on these systems


- High biodiversity where wetland and littoral habitat coincide


- Stability (?) > Alternative stable states

Shallow lake (pond)

- Permanent standing body of water where light penetrates to the bottom sediments- often, macrophytes cover the entire basin.

List some general characteristics of shallow lakes.

- Extensive littoral system


- Organisms can use macrophytes as cover from threats


- Different predation dynamics


- Important for waterfowl
- Lots of invertebrates


- More simple food webs

Origins and distribution and shallow lakes.

- Occur in abundance in lowland areas of gentle relief.


- Basins often formed by: glacial activity, river erosion (or movement), and wind deflation.


- Humans have created many for agriculture, industry, water storage, and recreation.

Characteristics of shallow lakes


- Nutrient loading is high (lowlands and small volume).


- Nutrient losses less and recycling occur faster- results in light availability regulating primary production.


- Macrophytes and periphyton dominate → habitat heterogeneity can lead to high biodiversity.


- No distinct hypolimnion and stratification is weak (polymictic).

Relationship between macrophytes and macroinvertebrates/fish

- Increase in macrophytes means more macroinvertebrates and more fish

Factors that maintain macrophyte dominance


- Reduced wave action or currents (e.g. geomorphic conditions)


- Uptake of P and N by submersed macrophytes
- Refugia for large zooplankton that graze on phytoplankton


- Large surface area for periphyton/epiphyton habitat


- High metabolism of macrophytes (e.g. restrict fish populations)

Daphnia sp.


- Key invertebrate grazer of phytoplankton


- Filter water to obtain algal food


- Can reach >100 individuals/ L


- Vulnerable to fish/invert predation


- Adapt in many ways to predation

Factors that maintain phytoplankton dominance


- Reduced grazing from zooplankton due to lack of refugia


- Suspension of sediments = ↓ light and poor macrophyte substrate


- Strong competition by algal & cyanobacteria


- Once established, high nutrient loads and dense phytoplankton tend to persist

How can habitat size and isolation can promote species richness in small lakes?

1) Richness ↑ with lake size,


2)Shallow lakes tend to be in either a fish-dominated, turbid state, or in a state with high macrophyte biomass,


3)Biodiversity is higher in a fish-poor vegetated lake than in a fish-dominated unvegetated lake of the same size, and


4) The occurrence of the vegetated state decreases with lake size.

Other control mechanisms on plant dominance in shallow lakes.

- Fish introduction: species that disturb the sediments prevent macrophytes from rooting
- Winterkill of piscivorous species (more pressure on zooplankton)


- Waterfowl and muskrat: voracious herbivores


- Humans: herbicide application, mechanical cutting, and biomass removal

Role of macrophytes in lakes

- Macrophytes influence the physical, chemical, and biological composition of lakes.


- When macrophyte biomass is lost there can be:


• Change in habitat
• Reduced biodiversity
• Decreased water quality

Indicators of shifting alternative states

Far from threshold:


• Low variability
• High recovery rate


Approaching threshold:


• High variability
• Disturbances “pile up”


• Low recovery rate

Factors that may determine if shallow lakes are clear or turbid


- Nutrient concentrations - mainly [P]


- Zooplankton populations


- Macrophyte biomass
- Fish populations


- Climatic controls of water depth

Trophic cascades

- Can occur when predators reduce the abundance or alter behaviour of prey, thus releasing the next lower trophic level from predation creating cascading effects down the food chain

Sedimentation

- Is the key process to ontogeny- controlled by within-lake and catchment loadings.

Succession

- Phenomenon of change through time of plant communities, usually after disturbance.

Lake ontogeny (NOT succession)

- The developmental history of lentic waters.

Factors that maintain low-nutrient conditions

1. Negligible loading
2. Small littoral zone
3. Low phytoplankton levels


4. Oxic hypolimnion
5. Low DOM & its breakdown

Trophy

- The rate at which organic matter is supplied by or to a lake per unit time.


- Dystrophy “dark-water lakes”


- Oligotrophy


- Eutrophy

Dystrophic shallow pond

- Acidic and dark water

Characteristics of wetlands (bog, fen, marsh, swamp, peatland)

Transition between aquatic and terrestrial ecosystems


Water-saturated long enough to promote aquatic processes


Water table near surface & poorly drained soils


Specialized biota adapted to these conditions


Very productive ecosystem

Importance of wetlands

“Kidneys” of the landscape


Flood storage & mitigation


Protect against erosion


Important habitat and C sink

Indicators of environmental change

- Plant macrofossils (vegetation change)


- Pollen (vegetation change)
- Charcoal (fire history)
- Diatoms (aquatic environments)


- Protozoa (moisture levels)


- Phytoliths (disturbance)

Transition from a shallow lake (pond) to a terrestrial system

- Characterized by accumulation of organic matter in excess of degradation.


- Does not happen overnight, can take thousands of years.


- Shift in origin of nutrients from catchment to atmosphere.

Sphagnum overstory

- Waterlogged environment


- Mosses favoured: accumulation of nutrients in non-available form, vascular plants restricted


- Anaerobic conditions: reduced decomposition & nutrient availability, peat accumulation

Rheotrophic

- Nutrients derived from surface or groundwater

Ombrotrophic

- Nutrients derived from atmospheric sources

Quaking bogs

- Develop in deep basins of small surface area


- Mat encroachment toward the centre of the basin overlies littoral peat accumulations and much of the open water

Ontogeny results in water chemistry shifts

Rheophilous to Ombrophilous


- Large decrease in pH


- Increase in H


- Decrease in HCO3


- Decrease in salinity

Charismatic megaflora of the Bacillariophyceae


- Didymosphenia geminata (aka rock snot, Didymo)


- Benthic, colonial diatom native to Northern Hemisphere


- Clear, low-nutrient rivers
- Blooms reported worldwide after 1990s

Didymo stalk production results from what?

- Low inorganic [P]

Didymo impacts to habitat and higher trophic levels

Alter foodwebs
- periphyton (organisms that cling to other plants and surfaces) (Kilroy et al. 2005)
- benthic invert. (Gillis and Chalifour 2010) - fish behaviour and diet


Change river structure/function


- substrate


- aesthetics
- flow, e.g. hyporheic zone

Conditions favourable to Didymo that may promote blooms


1) Early ice-out extends growing season


- warmer/milder winter - potential to change way ice leaves, often scrapes bottom and disturbs bottom
2) Less disturbance (ice scour) & weaker/earlier freshet


3) Base-flow period extended
4) Lower inorganic [P] and reduced turbidity


5) Also hypothesized: N deposition, improved land-use, and fewer marine-derived nutrients


- N increases plant growth, so more plants would pull more P out of the soils, leaving
less to enter water systems
- Fish species that return to rivers from oceans die and provide nutrients - so reduction of
fish populations could affect nutrient levels