Lakes: Primary Production, Budgets and Cycling
Biogeochemical Systems -- OCN 401 27 September 2012
Reading: Schlesinger Chapter 7
Outline
1. Temperature / density relationship • Seasonal cycle of lake stratification
2. Carbon and nutrient cycling • Dissolved inorganic carbon speciation • Methods of measuring primary production • Nutrients and productivity / nutrient cycling • Carbon budgets • Nutrient budgets • Nitrogen fixation
3. Lake classification
4. Alkalinity and acid rain effects
1 Temperature / Density Relationship
• Water is densest at 4°C • Both ice and warmer water are less dense • Important implication: ice floats!
• If less-dense water is overlain by denser water, lake overturn occurs
• If denser water is overlain
by less-dense water, Heavier stable stratification occurs
Berner & Berner (1996)
Temperature Structure of a Typical Temperate Lake in Summer
• Epilimnion: warm surface waters • Metalimnion: zone of rapid temperature change (thermocline) • Hypolimnion: cooler, deep waters • Many tropical lakes are permanently stratified • Temperate lakes show seasonal break-down of temperature stratification
2 Seasonal Cycle of Lake Stratification
Early spring (after ice melt):
www.gvsu.edu
Late spring:
3 Summer:
• Dead organic matter sinks from the epilimnion to the hypolimnion
• The decay of this organic matter leads to O2 depletion of the hypolimnion
Early autumn:
4 Autumn:
Winter:
5 Berner & Berner (1996)
Temperature profiles over the year for a typical temperate lake Dashed line represents maximum density at 4 C
Dissolved Inorganic Carbon
(DIC, CO2) Speciation
- 2- DIC = CO2 = [CO2 (aq)] + [HCO3 ] + [CO3 ] Bicarbonate Carbonate ion ion
CO2 (g) CO2 (aq)
+ - CO2 (aq) + H2O H + HCO3
- + 2- HCO3 H + CO3
Thus, CO2 speciation is pH dependent:
6 CO2(aq)
Seawater values shown --- freshwater curves are shifted left ~0.8 pH
aob.oxfordjournals.org
Methods of Measuring Primary Production • Collect water sample • Incubate in clear and dark bottles • Measure either:
– Change in dissolved oxygen (O2) 14 14 - – Production of C-labeled POC (from C-HCO3 additions)
• Calculate results:
– Dark bottle: Respiration (for O2 only) – Clear bottle: Net primary production (P-R)
– Clear bottle - dark bottle: Gross primary production (for O2 only)
7 Lake Productivity is Linked to Nutrient Concentration
Comparison of lakes of the world:
(NPP) • Most lakes appear to be P-limited
• Other factors can be important (e.g., other nutrients, sunlight)
Nutrient Cycling in Lakes
• Large proportion of P is in plankton biomass; small proportion is “available” (dissolved in lake water)
• Turnover of P in the epilimnion is dominated by bacterial decomposition of organic matter
• When planktonic communities are N-limited, there is a shift from green algae to “blue-green algae”
(cyanobacteria) that fix N2
8 Export Ratio = percentage of PP that sinks to the hypolimnion:
• Export ratio is 10- 50% of NPP
• High hypolimnion concentrations of P are returned to the surface during seasonal mixing
• Turnover of P is incomplete, so some P is lost to sediments
Lake Carbon Budgets
• NPP within the lake is “autochthonous” production
• Note importance of macrophytes (i.e., rooted plants), which reflects the extent of shallow water in this lake
• Organic carbon from outside the lake is “allochthonous” production (12% of total carbon inputs)
9 In lakes with lower chlorophyll concentrations (i.e., lower productivity), respiration exceeds production:
• This reflects the increased importance of allochthonous carbon inputs
• 74% of organic inputs are respired in the lake
• 74% of that respiration occurs in the sediment (Many other lakes have more respiration in the water column)
• 7.8% of OC is stored in sediments, similar to rate of accumulation of soil organic matter -- but from a much lower NPP than is typical on lan, due to less efficient anaerobic respiration
10 Lake Nutrient Budgets
• Inputs: precipitation, runoff, N-fixation, groundwater • Loses: sedimentation, outflow, release of gases, groundwater
• Thus, nutrient budgets require an accurate water budget for the system
• Comparison of nutrient residence time with the water residence time gives an indication of the relative importance of internal biotic cycling and physical processes
• Most lakes show a substantial net retention of N and P
• Lakes with high water turnover, however, may show relatively low levels of N and P storage
(Experimental Lakes Area)
Most lakes show a net retention of N and P
11 Lake Nutrient Budgets Nitrogen Fixation
• Lakes with high rates of N fixation show large apparent accumulations of N
• However, the loss of N by denitrification typically far exceeds the input of N by fixation
– Denitrification removes fixed N as N2O and (especially) N2
Lake Classification
• Oligotrophic lakes are: • low productivity systems • nutrient depleted • frequently geologically young • typically deep, with a cold hypolimnion
• Eutrophic lakes are: • high productivity systems • nutrient rich • dominated by nutrients inputs from the surrounding watershed • often shallow and warm
12 Nutrient inputs to oligotrophic lakes are generally dominated by precipitation:
Sedimentation tends to convert oligotrophic lakes into eutrophic ones over time….
• Eutrophication: a natural process by which accumulation of sediment causes 1) lake shallowing and 2) a decrease in the volume of the hypolimnion, increasing O2 drawdown:
Berner & Berner (1996)
• Positive feedback: lower O2, less nutrient retention in sediments, higher productivity, higher rain of organic matter to hypolimnion • Cultural eutrophication: input of nutrients due to human activity accelerates the natural process of eutrophication
13 Alkalinity and Acid Rain Effects
• Alkalinity is roughly equivalent to the imbalance in charge from cations and anions: Alkalinity = cations – anions • The charge imbalance is “corrected” by changes in equilibrium in the DIC system
- 2- - + • Thus: Alkalinity = [HCO3 ] + 2[CO3 ] + [OH ] - [H ]
2- - • Alkalinity increases by processes that consume SO4 , NO3 or other anions, or that release DIC • Alkalinity decreases by processes that consume cations or DIC
+ 2- • Acid rain decreases alkalinity due to additions of H and SO4
14 Sensitivity of Lakes to Acid Rain Effects
Berner & Berner (1996)
Lecture Summary
• Physical properties of water, seasonal climate changes, and the surrounding landscape and geology are major controls on nutrient cycling and NPP in lakes
• Primary production is closely linked to nutrient supply
• Nutrient and carbon budget provide a key means of assessing lake biogeochemical cycling
• Eutrophication is a natural process, which can be accelerated by anthropogenic activity
• Acid rain has had profound impacts on some lakes; underlying geology is major factor on lake sensitivity
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