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There are three main ways of
studying a waterway to determine its health and quality.
They include:
Chemical
Testing
The condition of a waterway can be determined
through a series of chemical tests. Chemical tests can sometimes
pinpoint exactly what substance is polluting the waterway or the
pollution source. Chemical testing has a longer history for being
used to determine stream health, although biological monitoring
is becoming more common. A biological test can indicate that a waterway
is polluted, but chemical tests can help identify the exact pollutants.
Because chemical testing is the most accurate and reliable method
in water testing, chemical testing is the method performed on drinking
water. Chemical testing may also assist in locating sources of pollution.
For example, if the tests indicate that a high concentration of
phosphates and nitrates are present in the water downstream of a
farm but not upstream, one could hypothesize that fertilizer runoff
is occurring around the farm. A list of chemical tests that are
performed to determine water quality are listed below:
- Alkalinity-Resistance to
change in pH or acidity
- Ammonia - Form of nitrogen,
a nutrient for plants
- Calcium - Natural from
rocks, incorporated into a "hardness" test
- Chloride - From salts,
sea water, or industry
- Chlorine-Common disinfectant
to kill pathogens
- Chromium- Toxic, corrosion
inhibitor added to industrial cooling processes
- Conductivity-Dissolved
organic matter within water
- Copper-May exist naturally
as a soluble salt or suspended solid
- Cyanide - Toxic waste product
of metal plating operations
- Dissolved O2-Presence
of O2 molecule in water
- Fluoride - Added to municipal
water to strengthen teeth
- Hardness - Calcium, Magnesium
and determines if water is soft or hard
- Iron-Natural, but in excess
can indicate acid mine drainage
- Magnesium - Natural from
rocks, incorporated into a "hardness" test
- Manganese- Needed by plants
and animals, causes a bitter taste, also stains laundry
- Nitrogen-Required by plants
& animals to produce protein
- pH-Measurement of hydrogen
ion concentration, determines if water is acidic or basic
- Phosphorus-Limiting growth
agent in most organisms, causes too much growth if in excess
- Salinity - Concentration
of all ionic constituents of halides and bicarbonates (salts)
- Silica - Natural nutrient
for diatoms, used in their skeletal structures
- Sulfates- Mineral common
in water, nutrient, can be from acid mine drainage if in excess
- Sulfide - From anaerobic
(no O2) bacterial breakdown of organic waste, rotten
egg smell
- Temperature-Different aquatic
organisms thrive in different temperature ranges
- Total Dissolved Solids-
minerals, organic matter, and nutrients dissolved, (not merely
suspended) in the water
- Turbidity-Cloudiness of
water from visible sediments and particles
- Zinc-Industrial effluents
contribute large amounts of zinc
Biological
Testing
The plants and animals that inhibit waterways
are good indicators of the water's quality. A person can study the
insects, fish, mussels, algae, other plant life, bacteria, and streamside
creatures to make conclusions about a stream's health. The more
variety of aquatic life present in a waterway, the better. The variety
of life in any habitat is called biodiversity. In a healthy
stream, many different types of insects or fish will be found throughout
the stream. If only a few species dominates the waterway, then something
about the stream is unhealthy.
Insects, molluscs, and worms living in streams
and rivers are examples of macroinvertebrates (big enough to be
seen by naked eye), or benthic (bottom dwelling) organisms.
Microinvertebrates are insects that need a microscope to be seen.
Benthic macroinvertebrates can be very accurate in detecting overall
changes in water quality (not necessarily specific chemical parameters)
because they: 1) reflect long-term condition of the stream from
a variety of sources, 2) are ubiquitous, have high species diversity,
and are more sensitive to changes in the ecosystem than fish communities,
3) live in bottom of waterway, where pollution associated water
quality problems can be magnified. Fish and mussels can also categorize
the health of a stream. It is debatable about which can reflect
long term pollution trends better - fish or insects.
Every waterway in the world has the potential
to host a variety of insects in its waters. However, many streams
lose this capability when altered by pollutants naturally or through
human interference. By polluting waterways, we disturb where the
insects live in the stream, what they eat, and the chemical levels
of the water that they can tolerate.
Different organisms have select tolerances
to pollutants found within the water. Organisms that are sensitive
to pollution will not inhabit those waters that are polluted. Some
of the pollution sensitive macroinvertebrates (sometimes
referred to as "group 1" organisms) examples include mayfly nymph,
stonefly nymph, caddisfly larva, and the water penny beetle larva.
Large numbers of pollution sensitive organisms generally indicate
good water quality. Their response to extreme pollution can be to
move by drifting (letting themselves get washed downstream to a
different location) or to die.
A second group of aquatic organisms are more
tolerable to a wide range of water quality conditions. Some of these
organisms include water striders, crayfish, and whirlygig beetles.
The pollution tolerable (group 3) organisms include blackfly
larvae, leeches, and aquatic worms. These creatures are not
sensitive to pollution, and may exist in very polluted waters.
A healthy stream will have organisms from
each group. Just because pollution tolerant creatures are present
does not mean the water is polluted. Check to see if there are any
bugs from the other more pollution sensitive groups. If a stream
does only contain group 3 organisms, it can be hypothesized that
the stream is currently significantly polluted. Based on insects
that you collect, the health of the stream can be calculated using
a Pollution Tolerance Index (PTI). This handbook includes
one for insects.
Pollution sensitive indexes are not restricted
to analyzing insect populations in a waterway. Other species, such
as fish, mussels, algae, and bacteria populations have also been
analyzed using the same strategy behind the insect pollution indexes.
In addition, the health of a waterway can also be estimated by observing
bird and mammal interaction with the waterway. If you never see
a common riverbank predator eat from a creek, (such as a raccoon),
or you never see deer drink from the waterway, then there might
be something wrong with the water.
Land
Use / Habitat Assessment
This approach analyzes the physical habitat
in and surrounding the waterway to identify possible pollution sources
running into the river. Land use assessment is a quick, practical
method of locating the source of pollutants found within the waterway.
The first step to assessing land usage surrounding the waterway
is to observe how the land surrounding the waterway is being used.
Different types of land use generate different types of pollutants.
Land use assessment is especially useful when human infrastructures
and land alterations surround the waterway. Classify the land surrounding
the water source as residential, commercial, agricultural, natural,
or industrial. There are two types of sources of pollutant sources
that enter waterways, point and nonpoint sources. Point source
pollution is simply pollution that's source can easily be identified
and pinpointed. Typical point sources of pollution are storm water
drains, industrial waste discharge, sewage plants, and construction
runoff. Even though point sources are regulated by law, they are
a major threat to waterways. Nonpoint sources of pollution are
scattered, diffuse sources of pollution that enter and are harder
to identify the exact location of entry. Nonpoint sources can be
identified or hypothesized by observing the land use surrounding
the water source. Examples include: a pollutant leaching through
the soil, nutrient enrichment from agricultural areas, storm runoff
over an urban setting, fertilizers and pesticides from lawns.
A land use / habitat assessment is the RCE,
or Riparian, Channel, and Environmental inventory. The RCE assessment
is a 16 characteristic analysis of the physical and biological conditions
for a 100 meter stretch in and along a stream. This assessment is
used primarily used in streams that have been heavily modified by
man. Land use, physical structures in the stream, and biota are
explored by the RCE. The riparian zone, the vegetation alongside
streams, is studied. They are important because they help control
floods, prevent soil erosion, take up extra nutrients, and provide
shade to the stream. Channel alteration, stream bank stability,
and substrate condition are also studied by the RCE. To prevent
flooding or to irrigate arid lands, humans usually modify channels.
However, the ecosystem of the steam is dramatically altered, for
pools and riffle zones become eliminated when the channels are manipulated.
Smoothing a channel also removes plants, logs, and boulders (snag
habitat). Alteration of a stream's channel drastically reduces the
biodiversity of the stream, because it removes habitat
diversity. The biota of the stream is also analyzed by the RCE.
A calculated score can be determined at the end of the RCE that
correlates with an overall stream condition (excellent - poor).
How You Will Study Your
Waterways in this Project:
There are tests and analysis methods to study
the chemical, biological, and land use/habitat characteristics of
waterways included in this handbook. Chemical testing is required
by the project throughout the school year, and biological and land
use/habitat assessment is encouraged. Together, they can help determine
the health of your stream and help you to better understand its
threats and protection needs. Have fun.
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