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The
unique thing about oxygen is that it can diffuse directly between the air and water
and this diffusion is improved by both air and water turbulence. The addition
of chemicals to water will usually result in lower dissolved oxygen due to stimulation
of biological processes.
Thus,
it is biological processes, even though they are impacted by physical
and chemical conditions that play the most important role in regulating
dissolved oxygen concentrations in surface waters. Plants growing in water
release oxygen during photosynthesis and both plants and animals living
in water consume this oxygen in respiration. The rate of photosynthesis
is affected primarily by temperature, light, nutrient levels, species
of plants, abundance of plants, and water turbulence, although several
other factors may be involved.
Photosynthesis
is carried out in water primarily by microscopic plants called phytoplankton.
When these organisms die they settle to the bottom and are decomposed
by bacteria. This bacterial decomposition also uses up oxygen. When additional
organic matter is added to water other than that generated in the water
through photosynthesis, there is a greater biological oxygen demand (BOD)
for the aerobic digestion of these carbon compounds. The BOD is defined
as the amount of oxygen used over time to degrade organic matter and is
the most commonly used parameter in the analysis of oxygen resources in
water. Unlike terrestrial environments, oxygen is typically a limiting
factor in aquatic ecosystems.
Dissolved
oxygen (DO) concentrations are expressed as milligrams of oxygen per liter
of water (mg/L). The amount of DO affects what types of aquatic life are
present in a stream, because many species of fish and macroinvertebrates
are sensitive to low DO levels. DO also regulates the availability of
certain nutrients in the water. Many physical and biological factors affect
the amount of dissolved oxygen in a stream. The physical factors that
influence DO are temperature, altitude, salinity, and stream structure.
Temperature inversely controls the solubility of oxygen in water; as temperature
increases, oxygen is less soluble.
In contrast, there is a direct relationship between atmospheric pressure
and DO; as the pressure increases due to weather or elevation changes,
oxygen solubility increases. Salinity also reduces the solubility of oxygen
in water. However, because some streams in have relatively low salinity
values, this factor is typically disregarded for calculations.
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Stream
structure also influences DO concentrations. Atmospheric oxygen becomes
mixed into a stream at turbulent, shallow riffles, resulting in increased
DO levels. Because there is less surface interaction between water and
air in slow-moving water and deep sections of a stream, DO concentrations
often decrease between surface and bottom measurements. The biological
processes of photosynthesis and respiration also affect dissolved oxygen
concentrations in streams. As aquatic plants photosynthesize, they give
off large amounts of DO during daylight hours. However, respiration from
aquatic vegetation, microorganisms, and algae consume oxygen at all hours
of the day and night. A stream experiencing an algal bloom exhibits large
daily fluctuations in DO as extreme oxygen production during the day contrasts
with the bacterial decomposition of algal detritus at night. Thus, the
lowest concentrations of DO in the summer are typically observed just
before dawn.
Biochemical
oxygen demand (BOD) is another important factor that effects DO concentrations
in streams. BOD is the amount of oxygen consumed by microbial decomposition
of organic waste, and is measured by the change in DO in a sealed water
sample over a five-day incubation period. High levels of organic pollution,
such as that from sewage treatment plants, agricultural runoff, or industrial
wastes, can significantly increase the BOD in a stream. Relatively healthy
streams will have a 5-day BOD reading of less than 2 mg/L, whereas polluted
streams may approach 10 mg/L.
Dissolved
oxygen is affected greatly by physical, chemical and biological processes.
A change in either one can easily affect the another. It is the delicate
interaction of the three that create a favorable or unfavorable DO rate.
But research has shown that it may be largely the biological process that
influences DO rates.
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