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Lec 5: Gases (DO & CO2) and pH
•Factors affecting Oxygen Concentrations•Inorganic & Organic Carbon and the Carbonate Cycle
Wednesday:Cole, J.J. et al. 1994. Carbon dioxide supersaturation in the surface waters of lakes.
Science 265:1568-1570.
Dissolved Gases1. Gases constitute one class of chemical impurities of
water: some essential for life, some inert, others toxic2. Properties of gases governed by both chemical and
physical laws3. Gases tend toward equilibrium between the concentration
in the atmosphere and that dissolved in water 4. Equilibrium (saturation) amount of each gas dissolved in
water dependent on:a. Pressure (atmospheric pressure, elevation: increasing pressure
increases solubility)b. Salinity (increasing salinity reduces solubility)c. Temperature (increasing temperature reduces solubility)
5. Solubility of a gas is independent of the concentrations of other gases in solution
2
Atmospheric vs. Dissolved Gas Concentrations
(% by volume)
Nitrogen 78.08 42 1Oxygen 20.95 35 3Argon 0.934Carbon dioxide 0.033 23 2100Others 0.003
Gas Atmosphere Dissolvedin water
RelativeSolubility
Nitrogen and Phosphorus are important plant nutrients3
Oxygen• 90% of water (by weight) but not biologically
available or important in this form• Probably the most important single indicator of
aquatic conditions for biota• Concentration in water generally expressed as
PPM (Parts per million) = mg/l, or as percentsaturation:
Amount PresentSolubility
• Determination– DO Probe and meter– Chemically (Winkler method and modifications)
4
5
Oxygen - Forms and Transformations
• 21% of atmosphere is O2• Aerobic/anaerobic - oxic/anoxic (hypoxic)• Oxygen drives redox (next slide)• Saturation concentration of dissolved
O2 depends on atmospheric pressure and temperature
• Photosynthesis produces oxygen, respiration consumes it
Potential Energy and Redox
Pot
entia
l ene
rgy
Activation energy
Net energy yield
Ammonium
Nitrate
Oxidizing environment
Going with potential energy
Activation energy
Net energy yield
Ammonium
Nitrate
Reducing environment
Going with potential energy
Pot
entia
l ene
rgy
Activation energy
Net energy cost
Ammonium
Nitrate
Going against potential energy
Activation energy
Net energy cost
Ammonium
Nitrate
Going against potential energy
6
• Which form of N is preferred by primary producers?• How to they convert to the preferred form?
Factors affecting Oxygen Conc. 1. Diffusion from atmosphere (Often less important than
photosynthesis). Diffusion rate depends on:a. Wave action
(rate increases with increasing wave action)b. Atmospheric pressure
(rate increases with increasing atmospheric pressure)c. Oxygen saturation of water
(rate decreases with increasing saturation)d. Salinity (rate decreases with increasing salinity)e. Moisture content of air
(rate decreases with increasing humidity)2. Photosynthesis (Often more important than atmospheric
diffusion). May contribute more than 50% of the oxygen in water. Photosynthesis may contribute 5mg O2/cm2/day
8
Nomogram for Determining Saturation of Oxygen at Different Temperatures
0 10 20 305 15 25
1401201008060
4020
1030
50
0 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17
0 2 3 4 5 6 7 8 9 10 11 121
Temperature (degrees C)
% Saturation
Oxygen (mg./liter)
Oxygen (cc./liter)
0 760 1.00500 714 1.06
1000 671 1.131500 631 1.202000 594 1.282500 560 1.36
Elev.(m)
Pressure(mm Hg) Factor
10 mg/l O2 at 20OC = 123% saturation at sea level
10 mg/l O2 at 20OC = 148% (1.20 x 120) saturation at 1500 m (~5000 ft)
7
9
1. Photosynthesis and respiration often result in daily fluctuations in the O2 concentration of surface water
a. May reach 200% saturation in late afternoonb. May fall to 50% saturation by dawn
2. Oxygen losses due to:a. Respiration b. Decomposition
3. Oxygen distributed in the water column mostly by currents4. Summer stratification may limit amount of dissolved
oxygen in the hypolimnion
Oxygen Losses and Fluctuations
10
Mid-SummerOxygen Profiles
123456789
10
0
0 5 10 15 0 5 10 15
123456789
10
0
O2 mg/l O2 mg/l
Dep
th (m
)
T
T
T
T
O2 O2
O2 O2
1. OrthogradeLow productivity
2. ClinogradeHigh productivity
3. Positive HeterogradeIncreased solubility in the
metalimnion due to temperature
Concentrations of algae in the metalimnion
4. Negative HeterogradeHigh metalimnetic
respiration and/or decomposition
Orthograde
Clinograde
PositiveHeterograde
NegativeHeterograde
Dep
th (m
)
11
*
O2 Profiles for Shallow Dimictic Lakes
• Crystal Lake:unproductive, transparent, with deep photosynthesis
• Other Lakes - range from moderately productive to highly productive
• All lakes except Adelaide showmetalimnetic oxygen maxima
0 1 2 3 4 5 6 7 8 9 10 11 12 13 1 2 3 4 5 6 7 8 9 10 11 12 13 14
0 2 4 6 8 10 12 14 16 18 20 22 24 26 2 4 6 8 10 12 14 16 18 20 22 24 26 2802468
1012141618
02468
101214161820
Temperature OC
Dissolved Oxygen (mg/l)
Dep
th (m
)
TOC[O2]S
[O2][O2]S
[O2]STOC
TOC
[O2]
[O2]
[O2]S
TOC
Crystal Lake,Wisc.
Adelaide Lake,Wisc.
Silver Lake,Wisc.
Akagi Okono, Japan
12
Note areas of DO deficit
Development of a ClinogradeOxygen Curve
0 1 2 3 4 5 6 7 8 9 10 11 12
0
2
4
6
8
10
12
14
16
18
20
22
Depth(m)
Dissolved Oxygen (mg/l)
IMay
IIJune
IIIJuly
IVAug.
Lake Mendota,Wisc.
Processes responsible for this pattern?
13
Productive and ConsumptiveAspects of Lake Morphology
Productive Aspect Consumptive Aspect
High volume to surface area ratio lakes
Low volume to surface area ratio lakes
What other factors might affect this balance?14
Carbon
• Forms of Carbon• Transformations of Carbon• A General Introduction to Nutrient
Cycling and the Carbon Cycle
15
Carbon Dioxide
• Generally, the most important source of carbon for photosynthesis
• Involved in buffering the pH of neutral and alkaline lakes
• The measurement of CO2 in all of its forms is called “Alkalinity”
16
Lake Nyos Disaster• 1700 people and many livestock died near
Lake Nyos in Cameroon in 1986• A survivor reported a 25m high water surge
and odor of rotten eggs• Caused by catastrophic release of
supersaturated CO2 from the hypolimnion• CO2 probably came from volcanic activity• Landslide or cool weather released the gas• Building up again, using pipes to release
pressurized water17
The Carbon Dioxide Cycle
(photosynthesis)
Plants
(respiration)
Plants
Animals
dissolvedorganicmaterial
Bacteria
O2
O2
O2
O2
Carbon dioxide in Solution
respiratory CO 2
respiratory CO 2
respiratory CO 2
non-biological oxidationCO2
Organic CarbonInorganic Carbon
(mainly CO 2 ) 18
Forms of Carbon• Inorganic Carbon-bicarbonate equilibrium
– Carbon dioxide: CO2
– Carbonic acid: H2CO3
– Bicarbonate: HCO3-
– Carbonate: CO32-
• Organic Carbon
CO2 + H2O↔ H2CO3 ↔HCO3- + H+ ↔CO3
2- + 2H+
-In which direction will PP drive these reactions?
19
Carbon Dioxide Cycle in Lakes
Phytoplankton (Euphotic Zone)
H2O+CO2<—>H2CO3<—>HCO3– + H+<<—>2HCO3<—>CO3
=
CO2
H2O
+Ca++
CaCO3
Sediments
20
Proportions of the formsof CO2 in Relation to pH
pH CO2 HCO3– CO3
=
4 0.996 0.004 1.26 x 10-9
5 0.962 0.038 1.20 x 10-7
6 0.725 0.275 0.91 x 10-5
7 0.208 0.792 2.60 x 10-4
8 0.025 0.972 3.20 x 10-3
9 0.003 0.966 0.03110 0.000 0.757 0.243
Free Bicarbonate Carbonate
21
3 4 5 6 7 8 9 10 11 12pH
0.0
0.2
0.4
0.6
0.8
1.0
Pro
porti
on o
f tot
al in
orga
nic
C CO2 (H2CO3) HCO3-
CO32-
Forms of CO2 in Water in Relation to pH
22
Daily Fluctuations inEpilimnetic O2 and CO2
60
50
40
30
20
10
0
360
350
340
330
320
310
3001800 2400 600 1200 1800
CO2(µm)
Sunset Sunrise
O2(µm)
Time
CO2O2
1823