Evaluations of Estuary
Quality
By Connie Wood
Fall 97
Summary
The purpose of this paper is to list and describe
some the evaluations used to determine the quality of estuaries.
Specific tests, locations and standards are given.
Location
The locations are on the Texas Gulf Coast. They
include Galveston Bay, San Antonio Bay, Corpus Christi Bay,
Laguna Madre and small estuaries found along the Texas coast.
Tests preformed
Tests performed to determine estuary quality are bottom
life, light penetration, sediment contaminants, fish pathology,
dissolved oxygen levels, pH, temperature, and conductivity.
Measuring Estuary Quality:
Water Temperature
One of the most important measurements of water quality
monitoring is water temperature. It has an effect on chemical,
physical and biological processes. Some examples of these
processes are solubility of compounds, rate of reactions, water
density, inversions and mixing, feeding, reproduction and the
abundance of organisms. Extended periods of high temperatures may
make an aquatic area unsuitable for certain organisms that would
be able to live there the rest of the year. Fish larvae and eggs
usually require smaller temperature range than adult fish.
Generally fish prefer a slow change in temperature rather than a
rapid change. As water temperatures decrease, the ability to hold
dissolved oxygen increases. One situation of how temperature
effects water quality is during the summer as water temperature
increases, dissolved oxygen levels decrease, metabolism of
aquatic organisms increase, and microorganisms that consume waste
organics use oxygen faster. All of these factors put stress on
the aquatic system. One indication of poor water quality in
estuaries would be a sudden or large increase in water
temperature. In a coastal area, an increase of 5 degrees Celsius
above the normal level for that season, or an increase of 32
degrees Celsius would indicate a concern.
Light Penetration
Another measurement used to determine estuary quality is light
penetration. A Sect disk is one way to measure this
characteristic. Light penetration or visibility of the water
indicates the presence of things such as particles of silt or
algae growth. The color of the water effects the transparency.
Sediments suspended in water can block sunlight to submerged
plants and carry nutrients, pesticides or other pollutants
through the water.
Dissolved Oxygen
Dissolved oxygen is another indicator of estuary water quality.
It is usually measured in milligrams per liter or parts per
million. Fish, invertebrates, plants and aerobic bacteria require
oxygen. Temperature influences DO greatly. Water with a
temperature of 31 degrees Celsius will only hold about half as
much oxygen as water with a temperature of 1 degree Celsius. The
amount of DO in an estuary depends on wind, water flow and
thermal upwelling and mixing. It also depends on the type and
amount of aquatic plants, algae and phytoplankton that produce
oxygen as a by-product of photosynthesis. Hypoxia refers to water
with low DO levels and anoxia refers to water with no DO levels.
Too many aquatic plants and animals can consume most of the
oxygen. Too many aquatic plants or increased alga growth can
result form the elevated concentrations of nitrogen and
phosphorus in the water. These two nutrients may come from
run-off from farms, golf courses, fertilized yards and sewage
plant effluent. Since DO is dependent on temperature, standards
for DO in estuaries are also tied to temperature measurements.
Generally a reading of no less that 5 mg/l is acceptable.
Measuring pH
A measurement of pH is also used to determine estuary water
quality. pH is a measure of how acidic or basic a substance is.
Coastal areas normally vary from pH 7-8. In general, wetlands,
swamps, and other forested areas will have lower pH levels. pH
level changes can indicate such conditions as photosynthetic
uptake of carbon dioxide or oxygen deficient waters. Heavy
rainfall or inflow of contaminants can also change pH levels.
Water with pH lower than 5.0 or higher that 9.0 should be
investigated. One key indicator of algae bloom is the presence of
increased pH and DO levels.
Remote sensing
Another type of monitoring of estuary quality is
the use of remote sensing. Remotely sensed data from aircraft and
satellites provide information about estuary systems. The Earth
Scan Laboratory (ESL) captures satellite images from the Gulf of
Mexico, most of the Atlantic, the extreme eastern Pacific, the
Northern Caribbean and the land masses from Hudson Bay to
northernmost South America. Also included in remote sensing data
are images from the Geostationary Operational Environment
Satellites (GEOS). This satellite system transmits thermal and
visible imagery from most of the Western Hemisphere every thirty
minutes. This information is used to monitor and analyze coastal
and deep-gulf circulation, coastal sediment transport, storm
formation, oil spills, and vegetation conditions.
Additional factors of Estuary quality
Estuaries are places where fresh water from rivers and salt water
from oceans mix. Salinity is a major factor affecting the
physical makeup of estuaries. The salinity levels decrease as the
estuary moves inland and as the volume of freshwater changes.
Conductivity measurements correlate to salinity and the amount
other dissolved solid in water. Wastewater discharge and
fertilizer runoffs are activities that might change the
conductivity of estuary water.
EPA Test results
During the 1991-93 testing periods, EPA rated the following
estuary areas for quality. Tests included bottom life condition,
DO, light penetration, sediment contaminants and fish pathology.
Corpus Christi Bay was rated overall fair with poor conditions
for bottom life (59 +- 13%), and light penetration (<10%)
(37+/- 13%). DO levels less than 2ppm were rarely observed.
Galveston Bay was rated overall poor to fair. Areas of concern
were bottom life, light penetration<10%, sediment contaminants
and fish pathology. San Antonio Bay was rated overall good to
fair. Only bottom life conditions and light penetration were
rated poor. Matagorda Bay was rated good overall. Bottom life
conditions were rated poor. Laguna Madre was rated good overall.
Bottom life was the only poor condition reported there.
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Revised: December 22, 1999