Title: Water Qualtiy: Dissolved Oxygen, pH, Alkalinty
1 Water Qualtiy Dissolved Oxygen, pH, Alkalinty
2Chemical Properties dissolved oxygen
- along with temperature, dissolved oxygen (DO), is
important in metabolic regulation - dissolved oxygen concentration and temp both
determine the environmental niche aquaculture
organisms occupy - occupation of niches is controlled by a complex
set of behavioral and physiological
(acclimatorial) activities - acclimation is slow wrt D.O. (hours, weeks)
3Chemical Variables dissolved oxygen
- although oxygen is rather abundant in the atm
(21), it is only slightly soluble in water (6
mg/L is not much) - implications to fish/invertebrates?
- Even metabolic rates of aqua-communities can
effect rapid changes in D.O. - this effect increases with temp (interaction)
- solubility decreases with increased temp/sal
- other factors BP (direct), altitude (indirect),
impurities (indirect)
4Oxygen Solubility Curve
5Chemical Variables dissolved oxygen
- factors affecting D.O. consumption
- water temperature (2-3x for every 10oC)
- environmental (medium) D.O. concentration
(determines lower limit) - fish size (Rc greater for small vs. large)
- level of activity (resting vs. forced)
- post-feeding period, etc. (2x, 1-6 hrs post
feeding)
6Oxygen Consumption vs. Sizefor Channel Catfish
(26oC)
O2 cons. Rate Increase in
(mg/kg/hr) oxygen consumption Fish size
(g) Nonfed Fed from feeding () 2.5 880 1,230 40
100 400 620 55 500 320 440 38 1,000 250 400
60
From Lovell (1989)
7Chemical Variables dissolved oxygen
- What might be considered minimal levels of
maintenance of D.O.? - hard to determine due to compounding effects
(cant standardize conditions) - major factor exposure time
- for most species
- long-term 1.5 mg/L
- medium term 1.0 mg/L
- short-term 0.3 mg/L
8Chemical Variables dissolved oxygen
- In general warm-water species are more tolerant
of low D.O. concentrations - Ictalurus punctatus adults/1.0 mg/L,
fingerlings 0.5 mg/L - Procamberus clarkii adults/2.0 mg/L,
juveniles/1.0 mg/L - Litopenaeus vannamei adults/0.5-0.8 mg/L
- Litopenaeus stylirostris adults/1.2-1.4 mg/L
9Chemical Variables dissolved oxygen
- Many practical aquaculturists will recommend that
D.O. concentrations do not drop below 6.0 mg/L - this is an impractical guideline in that this
level can seldom be achieved at night - a more practical guideline might be to maintain
D.O. levels around 90 saturation - no lower than 25 saturation for extended periods
10Chemical Variables dissolved oxygen/behavior
- if D.O. levels in the medium are adequate, fish
meet increased demands due to locomotion or
post-feeding by increased rate of ventilation or
large gulps of water - declining D.O. seek zones of higher D.O.,
reduce activity (reduced MR), stop consumption of
feed - compensatory point when D.O. demand cannot be
met by behavioral or physiological responses
11Chemical Variables dissolved oxygen/behavior
- upon reaching compensatory point gaping at
surface, removal of oxygen from surface - shown in both fish and invertebrates
- small aquatic animals are more efficient
- some oxygen provided by glycolysis or anaerobic
metabolism, but blood pH drops - pH drop in blood reduces carrying capacity of
hemoglobin (hemocyanin?)--gt death
12Oxygen/Temperature Interaction
- Oxygen consumption increases with temperature
until a maximum is achieved - peak consumption rate is maintained over a small
temp range - consumption rate decreases rapidly as temp
increases - lethal temperature finally achieved
13Chemical Variables dissolved oxygen/sources
- major producer of D.O. in ponds is primary
productivity (up to 80), diffusion is low (lt3) - incoming water can often be deficient depending
upon source water conditions - major consumers primary productivity, aquatic
species (density dependent), COD - diel fluctuation
- indirect relationships (algae, secchi)
14Oxygen Budget
15Diel Oxygen Fluctuation
- Typical pattern oxygen max during late
afternoon - difference in surface vs. benthic for stratified
ponds - dry season faster heating at surface and less
variation
16Influence of Sunlight on Photosynthesis/O2
Production
17Photorespiration predictable
18Chemical Variables total alkalinity
- total alkalinity the total amount of titratable
bases in water expressed as mg/L of equivalent
CaCO3 - alkalinity is primarily composed of the
following ions CO3-, HCO3-, hydroxides,
ammonium, borates, silicates, phosphates - alkalinity in ponds is determined by both the
quality of the water and bottom muds - calcium is often added to water to increase its
alkalinity, buffer against pH changes
19Chemical Variables total alkalinity
- thus, a total alkalinity determination of 200
mg/L would indicate good buffering capacity of a
water source - natural freshwater alkalinity varies between 5
mg/L (soft water) to over 500 mg/L (hard water) - natural seawater is around 115-120 mg/L
- seldom see pH problems in natural seawater
- water having alkalinity reading of less than 30
mg/L are problematic
20Chemical Variables total alkalinity
- total alkalinity level can be associated with
several potential problems in aquaculture - lt 50 mg/L copper compounds are more toxic,
avoid their use as algicides - natural waters with less than 40 mg/L alkalinity
as CaCO3 have limited biofiltration capacity, pH
independent - low alkalinity low CO2 --gt low nat prod
- low alkalinity high pH
21Chemical Variables total hardness
- total hardness total concentration of metal ions
expressed in terms of mg/L of equiva- lent CaCO3 - primary ions are Ca2 and Mg2, also iron and
manganese - total hardness approximates total alkalinity
- calcium is used for bone and exoskeleton
formation and absorbed across gills - soft water molt problems, bone deformities
22Chemical Variables pH
- pH the level or intensity of a substances
acidic or basic character - pH the negative logarithm of the hydrogen ion
concentration (activity) of a substance - pH -log(1/H)
- ionization of water is low (1x10-7 moles of H/L
and 1x10-7 moles OH-/L) - neutral pH similar levels of H and OH-
23Chemical Variables pH
- at acidic pH levels, the quantity of H
predominates - acidic pH pH lt 7, basic pH gt7
- most natural waters pH of 5-10, usually 6.5-9
however, there are exceptions - acid rain, pollution
- can change due to atm CO2, fish respiration
- pH of ocean water is stable (carbonate buffering
system, later)
24Chemical Variables pH
- Other sources of change
- decay of organic matter
- oxidation of compounds in bottom sediments
- depletion of CO2 by phytoplankton on diel basis
- oxidation of sulfide containing minerals in
bottom soils (e.g., oxidation of iron pyrite by
sulfide oxidizing bacteria under anaerobic
conditions)
25Chemical Variables carbon dioxide
- normal component of all natural waters
- sources atmospheric diffusion, respiration of
cultured species, biological oxidation of organic
compounds - usually transported in the blood as HCO3-
- converted to CO2 at the gill interface, diffusion
into medium - as the level of CO2 in the medium increases, the
gradient allowing diffusion is less
26Chemical Variables carbon dioxide
- this causes blood CO2 levels to increase,
lowering blood pH - with lower blood pH, carrying capacity of
hemoglobin decreases, also binding affinity for
oxygen to hemoglobin - this phenomenon is known as the Bohr-Root effect
- CO2 also interferes with oxygen uptake by eggs
and larvae
27CO2 Level Affects Hemoglobin Saturation
28Chemical Variables carbon dioxide
- in the marine environment, excesses of CO2 are
mitigated by the carbonate buffering system - CO2 reacts with water to produce H2CO3, carbonic
acid - H2CO3 reacts with CaCO3 to form HCO3-
(bicarbonate) and CO32- (carbonate) - as CO2 is used for photosynthesis, the reaction
shifts to the left, converting bicarbonates back
to CO2 - what large-scale implications does this have?
29The Effect of pH on Carbonate Buffering
30Chemical Variables carbon dioxide
- Concentrations of CO2 are small, even though it
is highly soluble in water - inverse relationship between CO2 and
temperature/salinity - thus, CO2 solubility depends upon many factors
31Chemical Variable carbon dioxide
- CO2 is not particularly toxic to fish or
invertebrates, given sufficient D.O. is available - maximum tolerance level appears to be around 50
mg/L for most species - good working level of around 15-20 mg/L
- diel fluctuation opposite to that of D.O.
- higher levels in warmer months of year