Monitoring:Monitoring
Model Application: Temperature
Model Application: Point/Nonpoint Nutrient Loadings
Model Application: Eutrophication
Model Application: Temperature and Dissolved Oxygen
Data Required to Support Reservoir Water Quality Modeling
Assuming that reservoir water quality monitoring will include the effects of nutrients and primary production on other water quality variables, e.g., dissolved oxygen (DO), the following types of data are required:
- Boundary conditions
- Initial conditions
- Site description/geometry/bathymetry
- Parameters (e.g. coefficients)
- In-pool/release observations (for calibration/verification)
Boundary Conditions
The types of boundary conditions required for reservoir water quality models consist of the following:
- Inflowing tributaries
- Other non-point source runoff
- Point source loadings
- Outflows
- Meteorology
- Sediment fluxes (for older models)
Tributary monitoring needs are shown in the table below. The variables shown in the "more complete" list are in addition
to the minimum list. Variable groupings are for convenience only.
Minimum | More Complete | Frequency |
---|---|---|
Q = Flow Rate T = Temperature |
C= Conductivity DO = Dissolved Oxygen pH TDS = Total Dissolved Solids → (Enough samples to correlate to C) |
D or C D or C D or C |
TOC = Total Organic Carbon | DOC or POC = Dissolved or Particulate Org. Carbon | W |
SRP = Sol. Reactive Phosphorous TP = Total Phosphorous |
TDP = Total Dissolved P TIP = Total Inorganic P → (i.e. total reactive and acid-hydrolyzable P) DIP = Dissolved Inorganic P → (can get organic forms from these) |
W W W |
NO2+NO3-N = nitrite and nitrate nitrogen |
TKN = Total Kjeldahl N | W |
NH4-N = Ammonium N | Filtered TKN TSS = Total Suspended Solids ISS or VSS = inorganic or volatile suspended solids → (These are not critical unless turbidity and its impacts are of concern. SS do affect P partitioning in some models, light, and water density) Chl a = chloryphyll a ALK = alkalinity Si = dissolved silica |
W W W W W W |
- Note: D = daily, W = weekly or on that order, C = continuous recording
- Note: D = daily, W = weekly or on that order, C = continuous recording
In Pool/Release Observations
Observations are required from within the reservoir pool and preferably in the release for model calibration and verification. One study period (e.g. a year) is typically used for calibration, and another period (e.g. another year with completely different hydrology ) is used for verification. Some in-pool observation profiles should be taken at frequent depth intervals (e.g., one meter), while others can be less detailed. Depth intervals for the less detailed profiles (i.e., grab samples for chemical analysis) should be detailed enough to characterize sharp gradients in concentration. One in-pool station should be near the dam (about several hundred meters from dam) and over the channel. Two or more stations should be placed at other locations, e.g., mid pool and headwaters.
Release temperature and DO should be monitored (primarily for selective withdrawal verification) daily, as a minimum, at conventional dams; hourly recordings are preferred at peaking hydropower dams.
In-pool profile monitoring needs are shown below. Again, the variables shown in the "more complete" list are in addition
to the minimum list. Variable groupings are for convenience only.
Minimum Necessary | More Complete |
---|---|
In-situ | |
T, DO, C, pH at about 1.0 meter intervals depending on depth. Need to characterize sharp gradients. |
None |
Samples for chemical analysis (depth intervals can be less frequent than those for in-situ) | |
Chl a | algal biomass (dry) and type |
TOC | DOC or POC |
SRP | TDP |
TP | TIP DIP → (can get organic forms from these) |
NO2+NO3-N | TKN |
NH4-N | Filtered TKN |
light trans (e.g. Secchi depth) | TDS (enough samples to correlate to C, cond.) TIC = Total Inorganic Carbon or CO2 ALK Si TSS, ISS, or VSS dissolved (i.e. reduced) Fe total Fe dissolved (i.e. reduced) Mn total Mn total dissolved sulfide SO4 = sulfate FeS = iron sulfide |
Notes:
- TDS important only if concentrations are high enough to affect water density or impact water supply uses.
- Fe, Mn, S, FeS, and SO4 important if concerned about the affect of anoxia on the release of these problem constituents from bottom sediments and possible release to the downstream environment.
Reference
Data Required to Support Reservoir Water Quality Modeling - full text