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Quality and Quantity Monitoring | Physical
Habitat Assessment |
Minimum Flow
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the Indices are Calculated | Back
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How the Indices are Calculated
With all the data gathered, the StreamWatch Stream
Health Index can finally be calculated. The index is designed
to compare current conditions with ideal summer streamflow,
water quality and habitat conditions for indicator fish at
the sampling site in each stream. In setting out to evaluate
habitat conditions for fish, we've assumed that protecting
riverine fish and other aquatic wildlife is a worthwhile goal
and we've had to make some assumptions about the parameters
that affect fish habitat. There are certain limitations on
the interpretation of the index:
- It does not reflect transient events affecting
water quality or quantity,
- it does not rate the fish for consumption,
- and it does not test for the presence of toxic
materials or fecal coliform bacteria in the water column.
Overview: The Stream Health index is arranged
so that the environmental quality increases with increasing
index (I = 1 for worst conditions; I = 100 for best conditions).
Calculation of the index consists of three steps: (1) calculation
of subindex scores for each of the parameters (2) aggregation
of the subindex scores into index scores for flow, water quality,
and habitat availability, and (3) aggregation of the three
index scores into the overall "Stream Health" index
. The table, below, shows the environmental parameters used
and the criteria against which they are scored.
|
Stream Health Index
Parameters
|
|
Index
|
Parameters
|
Scoring Criteria
|
| Flow
|
Streamflow
(weekly readings)
Readings at 10 streams |
Streamflow
requirements for each stream (R2Cross and wetted perimeter
methods) |
| Percentages
of Mean Annual Flows of each project stream (Tennant Method) |
| Low flows
(7Q10) calculated from USGS's STREAMSTATS for each stream |
| natural August
median flows (calculated with USGS's STEAMSTATS program) |
| Groundwater
level (weekly readings) Online readings of USGS Acton
well. |
Long term
records for the well |
Habitat
Avail. |
Channel flow
status |
EPA Rapid
Bioassessment Protocol for estimating Channel Flow Status |
Water
Quality |
Dissolved Oxygen (diurnal minimum) |
Massachusetts Water Quality
Standards EPA Ecoregion XIV statistics and fish tolerances |
| Temperature |
Massachusetts Water
Quality Standards and published fish tolerances |
| pH |
Massachusetts Water Quality
Standards and published fish tolerances |
| Total phosphorus |
EPA Ecoregion XIV nutrient
data |
| Total nitrogen |
EPA Ecoregion XIV nutrient
data |
| Total Suspended Solids |
Previous indices & published
fish tolerances |
(Step
1) Calculating the individual scores: Water quality metrics
are generally related to an index score along a rating curve.
The SWSH index used a combination of the Massachusetts Water
Quality Standards, regional averages, and biological tolerances
of the indicator fish to develop curves for the water quality
and flow parameters.
Below are sample curves developed for streamflow
in Danforth Brook, and dissolved oxygen. For example, if the
streamflow in Danforth Brook (a cold-water stream) were 1.7
cubic feet per second (cfs) and the dissolved oxygen concentration
were 6.5 mg/L on a given date, then the subindex scores for
streamflow and DO would be 50 and 64 respectively.


(Steps 2 & 3) Calculating the subindices
and overall index: The trick in calculating an index is
to combine the scores of the individual parameters in such
as way that the overall index: 
- gives a good picture of the overall score
of all of the subindices,
- the most important subindices (for fish habitat)
have the most influence over the overall index,
- and any low scoring subindex is not hidden
by the averaging process.
For
this index, the subindex scores within each group are combined
using a harmonic mean to get the index score. (For example,
the harmonic mean of the streamflow and the groundwater level
scores gives the flow subindex.) Finally the three index scores
are combined, again by calculating the harmonic mean, to get
the overall Stream Health index score.
Using the harmonic mean (rather than an average
or median) allows any low-scoring parameter to influence its
subindex more heavily, and any low-scoring subindex to influence
the overall index more heavily. For example, if water quality
and flow conditions were all good except for dissolved oxygen,
which was too low for fish to survive, the overall index should
be low.
Other Indices: While this is the
first time (that we are aware) that an index like this one
has been used to report habitat conditions on a weekly basis,
our index follows in the footsteps of many previous water
quality indices. A quick review of the literature shows that
much of the initial work on water quality indices was done
in the 70's and early 80's, although interest seems to be
reviving with indices now in use in Washington, Oregon, Ohio,
Colorado, Kansas, Texas, and British Columbia (see the Links
page under Water Quality Indices for links).
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