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What
is Water Pollution
Water pollution is an undesirable change in the physical, chemical,
or biological characteristics of a body of water that can negatively
affect the health, survival, or activities of humans and other living
organisms. Water is valuable to us because it
is necessary for so many things, but pollution limits it value and
usefulness. Therefore, much attention has been given
to studying sources of pollution, and finding ways to prevent and
treat water pollution.
Often, pollution is classified into two categories:
point source and nonpoint source pollution. Point source pollution
is a single, identifiable source that discharges (empties) pollutants
into the environment. Examples would include a leaking waste
storage container and a drainage pipe from a sewage treatment plant,
industry, or off a city street. Nonpoint source pollution's source
is more difficult to pinpoint because this pollution type can enter
a stream with runoff from a widespread land area. Examples
include farm fields, large construction sites, mining operations,
lawns, and parking lots. To help distinguish the
difference, think of point source pollution as pollution that could
be stopped if a cap or seal was placed over the discharge source
or small barrier around the source before entering the stream.
However, to stop nonpoint source pollution, you would need to build
a long cement barrier that would border beside the stream above
and below ground and catch the runoff from the adjacent land.
Water Pollution
Legislation
The Federal Water Pollution Control Act of 1972, renamed the Clean
Water Act of 1977 (amended also in 1981, 1987, 1993) is the government
legislation that seeks to protect the nation's vast water resources
from pollution. The 1972 act changed outdated water
pollution laws from 1899 and for the first time placed limitations
on point source pollution discharges and created surface water quality
standards. All factories, wastewater treatment plants,
and other point sources were given limits and permits for the amount
of conventional and toxic water pollutants they were allowed to
discharge. In order to meet the act's goal of eliminating
pollutant discharge into all navigable waters by 1985, industries
were to implement the "best practicable" pollution control equipment
by 1977 and more advanced equipment by 1983. All municipal
treatment plants were supposed to have secondary treatment practices
in place by 1977, and further improvements by 1983.
Revisions to the act and deadline extensions have occurred with
each of its amendments. However, the 1987 amendments
called for state management programs for nonpoint sources, a pollution
type generally overlooked previously. The Federal Government
also enacted the Safe Drinking Water Act of 1974, requiring the
EPA to establish national drinking water standards or maximum contaminant
levels for all pollutants that "may" have adverse effects on human
health.
Pennsylvania's water pollution control programs
date back to 1905 (Purity of Waters Act), and the first comprehensive
water pollution control state law, the "Clean Streams Law" was enacted
in 1937. This law has been strengthened with amendments
over time and addresses standards passed down by the Federal Government.
Sources of Western
Pennsylvania Water Pollution
A 1994 Department of Environmental Protection assessment of
water quality and biological conditions of waterways showed that
49,315 miles (91.4% of the 53,962 miles of Pennsylvania streams)
were meeting the Clean Water Acts "fishable/swimmable" goal. 8.6%
(4,647 miles) fail to meet the above criteria because of pollution
problems (Arway, 1997).
Acid Mine Drainage
- point and nonpoint source
Of the 8.6% of polluted streams, the biggest threat (56% or 2,596
miles) can be attributed to mineral resource extraction. 2,404
miles is affected by acid mine drainage (AMD). "The influx of untreated
acid mine drainage into streams can severely degrade both habitat
and water quality often producing an environment devoid of most
aquatic life and unfit for desired uses" (Kimmel, 1983).
AMD is acidic water with a pH often below 4.5 (see pH information
sheet for more information).
Coal is mined in two ways - underground mines
with tunnels or surface/strip mining (removal of land from the surface
to dig down to the coal seam). Acid mine drainage is often
the product of water running through abandoned mining operations
from the early 1900s, and to a lesser extent active mining.
Soil and crushed rock removed from above coal seams underground
is called overburden and can contain iron pyrite (FeS2, fool's gold).
The disturbance of this rock and soil exposes the pyrite to air
and water, creating a chemical reaction forming ferrous iron (Fe+3),
iron hydroxide (Fe(OH)3) and sulfuric acid (H2SO4).
The acid can dissolve other minerals and metals from surrounding
rock, and can itself dissociate (break apart) yielding sulfate (SO4-2)
extra hydrogen ions (H+) to the water (lowering the pH). So
the acid mine drainage finds its way into groundwater and/or surface
water, adding acidity (lowering the pH). In a different process
it is possible that neutral or alkaline mine drainage (NAMD) may
be produced.
AMD releases toxic metals such as iron, aluminum,
and manganese from surrounding rocks. When iron in the water
comes in contact with dissolved or atmospheric oxygen, it oxidizes
and precipitates out (drops out) and becomes the yellowish-orange
stain on the bottom of the stream. These streams are
often nicknamed "yellow boys". This can also happen
with the other metals - aluminum (white) and manganese (black).
These metals can clog fish gills causing breathing complications
or cause deformities to young fish. When they settle on the
stream bottom, they fill in spaces between rocks where insects live
or insect and fish eggs are laid, even smothering the eggs.
Acid mine drainage can and does have a myriad
of negative effects upon the environment. In streams that
are not well buffered by carbonate rocks, severe stress is placed
upon all life within the stream because of the lowered pH levels
(see pH information sheet for more information).
Surface coal mining can be the source of much soil erosion to a
stream because of the removal of vegetation and disturbance of the
land surface.
There are ways of treating acid mine drainage.
Since the late seventies, state and federal laws require that surface/strip
mining companies restore the land to a state which is, as near as
possible, to its original state. This includes the replanting
and landscaping of the old site. AMD coming out of surface
and underground mining operations can be treated either passively
or actively.
Active treatment methods use strong alkaline
chemicals (limestone, soda ash or sodium carbonate, caustic soda
or sodium hydroxide, and ammonia) to neutralize the acid.
In the process, metals precipitate out and have to be removed and
securely stored. Active treatment is expensive to use over
long periods of time, can be chemically dangerous, and is labor
intensive.
Passive treatment methods generally employ
channels, limestone, vegetation, ponds
and wetlands to mitigate the acidity problem. Limestone
rids the extra hydrogen ions that make the water acidic. Wetland
plants can take up, store, and process metals. And the natural process
of metals reacting with oxygen and settling out of the water can
be a useful solution. An example of a passive system for mitigation
of acid mine drainage has been undertaken by one project participating
school, Chartiers Valley High School.
The Scrubgrass Run Watershed Project attempts
to treat the acid mine drainage problem in Scrubgrass Run, which
eventually empties into Chartiers Creek and the Ohio River. Two
ponds were set up trying to remove the metals from the water.
The first induces the reaction of iron and oxygen to take place
allowing the iron to precipitate in the form of rust. The
water, which is supposed to be devoid of iron as well as oxygen,
is then channeled into the second pond. Aeration is the main
purpose of the second pond, adding oxygen to the water before sending
it off to Scrubgrass Run. The treatment process is a challenging
work in progress as Chartiers Valley seeks ways to keep oxidized
iron in the first pond, and to better aerate the second pond. For
more information on this project contact them at http://members.tripod.com/scrubgrass/.
(photo from Scrubgrass website)
Oil and Gas Extraction
- point source
Though less of a threat to streams as coal mining, this type of
mineral extraction is still a problem in Western Pennsylvania.
Oil and gas development includes the drilling, stimulation (fracturing
of underground rock formations with pressure), and the production
of oil and gas deposits buried underground. The
geologic history of the region has created some rich reserves of
gas and oil. Ever since Colonel Edwin Drake drilled America's
first oil well in 1859 in Titusville, PA, the industry has grown
to meet society's demand for fossil fuels.
Operating wells produce brine (salty water)
with some toxics such as metals and phenols (organic hydroxy acid
that is corrosive, smelly, and poisonous). Sometimes this
brine enters streams untreated deliberately or illegally by operator
or through storage container leaks. Oil spills and broken
pipes can also be a problem, adding crude oil to streams.
In addition, forests are cleared for installing pumps and dirt access
roads are carved through the landscape, adding soil erosion and
siltation threats to streams.
Agriculture
- usually nonpoint source
Agriculture, the largest industry in Pennsylvania, is also the second
major source of stream pollution (Arway, 1997). To keep
land rich with nutrients, especially nitrates and phosphates, liquid
and granular chemical fertilizers and animal manure are applied
to farm fields. If applied in excess or doing non-growing
seasons, the fertilizers can be washed off the fields and into nearby
streams, stimulating excessive plant growth (algae and aquatic weeds).
This can turn a waterway into a green soupy mess and aquatic weeds
can frustrate swimmers, fisherman, and boaters. When
the vegetation dies, aerobic (oxygen using) bacteria decompose it
and use oxygen from the water. The decline in oxygen
can cause aquatic life to suffer or even die. This process
is called eutrophication. See the nitrates and phosphates
information sheets for more information.
Wind and rain runoff sends soil into streams,
creating turbid (cloudy) conditions. This soil settles
out on the bottom of the stream (called sedimentation) and can destroy
insect habitat, places for fish and insects to lay eggs, and even
smother existing eggs. (See the turbidity information
sheets with more information). Soil erosion can be caused
by poor plowing techniques, such as failing to till fields with
the contours of the land. There are even no-till or conservation
tillage methods that hold moisture better and prevent erosion.
Failing to have crop cover during non-growing seasons or on unused
fields is another source of soil erosion. Plant roots help
keep soil in place, and maintaining a healthy riparian (streamside)
vegetative zone can reduce the amount of soil erosion that reaches
a stream. In addition, plants in riparian zones can soak up
extra nutrients before they enter a stream.
Livestock is both a source of nutrients and
soil erosion. Animal manure can add nutrients and harmful
bacteria to a stream, especially if the livestock graze near or
even in a stream. These animals can also erode banks
and trample down vegetation that holds back erosion. Stream fencing
and specially designed stream crossing areas can help keep livestock
from damaging stream banks or adding
waste directly to the stream.
Pesticides (herbicides and insecticides)
are chemicals used by farmers that were developed to control plant
and animal pests. If applied incorrectly to fields
or in excess, these chemicals can enter a stream through wind and
water erosion and can negatively affect all creatures - pest and
non-pest. Pesticides can be toxic to aquatic animals
at even low levels and can contaminate drinking water sources.
By following the label specifications for the amount and season
for pesticide applications, and by being careful with aerial applications,
the amount of these chemicals entering streams can be reduced.
In addition, there are non-chemical approaches to pest management
(biological control) practices that can be used.
Irrigation systems that withdraw water from
nearby streams can disrupt the stream system. Lowering the
water level can increase the temperature of the waterway because
shallower water warms faster than deeper water. Plus
shallow water can disturb fish habitats and mussels that were normally
underwater along stream edges can be exposed and vulnerable to death
and predators.
Deforestation
- nonpoint source
Pennsylvania is blessed with some very productive forests
filled with trees (such as black cherry, pine, and oak) well sought
after by timbering / lumber companies. Unsustainable
forestry practices can harm streams in a number of ways.
When trees are removed, especially if all trees are removed from
an area, soil erosion will increase because there are no roots to
hold soil in place and there is no leaf cover to lessen the impact
of raindrops. Removing riparian zone trees during forestry
practices intensifies soil erosion and eliminates an effective tool
for catching uphill soil that washes toward the stream.
The removal of streamside vegetation eliminates shade from the stream,
thus increasing the temperature of the water (thermal pollution).
See the temperature information sheet. Soil and
silt can also be washed off the many dirt logging roads that are
constructed to reach remote parts of a forest.
Acid Rain - nonpoint
source
Rain is naturally acidic (pH of 5.6) because of carbon dioxide in
the air reacting with water to form carbonic acid, which can dissociate
producing extra hydrogen ions. Thanks to human activity (atmospheric
pollutants from fossil fuel burning, industrial processes, and automotive
exhausts), we have increased the acidity of some precipitation.
Sulfur dioxide (SO2) and nitric oxide (NOx) gases are sent into
the atmosphere, are chemically changed, and return to the earth
as wet deposition (rain, sleet, or snow) or dry deposition (dust
particles).
The rain that falls in Pennsylvania averages
a pH between 4.0 and 4.5. America's most acidic precipitation
centers around Pennsylvania, Ohio, and New York. The Pennsylvania
Fish and Boat Commission claims the Pennsylvania receives more acid
rain than any other U.S. state. Why
is this? Pennsylvania is downwind of and is part of
the industrial belt of the country - the big cities along the Great
Lakes like Chicago, Detroit, Cleveland, and inland cities in Ohio,
Illinois, Indiana, and Pennsylvania. Pittsburgh is also
part of this industrial belt. These cities add air pollutants
that create acid rain, and Pennsylvania is in the downwind weather
patterns containing this rain.
Whether or not acid rain is a problem to
streams depends on the geology of a region. Luckily, most
of Western Pennsylvania rocks, bedrock, and soil contain calcium
carbonate and magnesium carbonate, which can neutralize the acid
(get rid of the extra hydrogen ions). This acid buffering
capacity is called alkalinity, which has an information sheet later
in the handbook. Acid rain does become a
problem in Western Pennsylvania stream in major storm events, where
surface runoff does not allow the acidic precipitation to come in
contact with the buffering geology of the region. Quick
acidic snowmelts can also cause these "acid spikes" to a stream.
The stream's pH will recover eventually from these acid spikes.
Acid rain can also add to the high concentration of acidity in acid
mine drainage streams - streams that recover less successfully from
their low pHs.
Sewage - point
source
Sewage is the third worst Pennsylvania stream pollutant affecting
400 miles of streams (Arway, 1997). Even though wastewater
treatment facilities are supposed to treat sewage before anything
is released to a waterway, some municipal plants in Western Pennsylvania
are outdated. Some towns have storm drains hooked up to sewage
lines and during storm events; the sewage treatment plant cannot
handle the flood of water and sewage and may release untreated sewage
to the stream. Some outdated plants fail to remove all
oxygen demanding organic solids through their treatment process,
and some outdated plants are too small to meet the need of an increased
community population. Luckily there have been great
efforts to update facilities to meet government regulations.
Rural homes use backyard septic systems to treat sewage, which can
have failing processes or leaking storage components. This
adds extra sewage to the groundwater and streams.
Sewage is harmful to a stream for a number
of reasons. Sewage contains organic matter, which is
broken down by bacteria in a stream. This aerobic (oxygen
using) bacteria lowers oxygen levels in a stream (increased biological
oxygen demand). There is a natural balance of organic
substances in a stream (from dead plant and animal parts in and
around a waterway) that need to be decomposed, but adding extra
sewage organics can unbalance the system. Sewage
is also rich in nutrients. As mentioned in the agriculture
section, extra nutrients in a stream can also disrupt the stream
ecosystem.
There are other problems with sewage additions.
Turbidity (cloudiness) of the water can increase as sewage suspended
solids are added. Untreated waste can also include chemicals,
metals, and pesticides, possibly from industries connected to municipal
systems. Pathogens (organisms that cause disease) exist
in untreated sewage, and can be successfully killed with chlorination
or ultraviolet light. However, chlorine can be toxic
to a stream if used in excess during this treatment.
Wastewater can also be higher in temperature than the stream water,
adding thermal pollution to the stream.
Industry - point
source
Even though the Department of Environmental Protection Regional
Offices regulate and control permits to reasonably limit industrial
discharge, pollutants may still enter streams from various Western
Pennsylvania industries. Below is a chart of industrial
pollutants.
| Power Plants |
Heat, silt, chlorine |
| Steel Mills/ Manufacturing |
Heat, metals, acids, oil, cyanide, phenols
(organic hydroxy acid that is corrosive, smelly, and poisonous) |
| Food Processing/ Slaughterhouse |
Organic matter (blood, fat, meat parts
and juices), chlorine. |
| Paper Mill |
Organic matter, acids, sulfites, metals,
heat, chlorine. |
| Tannery |
Organic matter, acids, metals |
| ALL of the above |
Air pollution that can cause acid rain |
Urbanization / Suburban
Areas - point source and nonpoint source
Urban areas can place much stress on waterways because of the concentration
of people and the alteration of land. Some of the problems
previously discussed are associated with urbanization and suburban
areas - industry, sewage disposal, and acid rain - but there are
others worth mentioning.
Water withdrawal for municipal drinking water
and industries is a problem that receives much attention especially
during drought years. Lowering the water level
can increase the temperature of the waterway because shallower water
warms faster than deeper water. Plus shallow water can
disturb fish habitats and mussels that were normally underwater
along stream edges can be exposed.
Thermal pollution is a serious problem because
shady streamside trees are often removed in urban areas, allowing
sunlight to heat the water. Rainwater that flows over hot
paved surfaces (roads and parking lots) is drained into a stream,
possibly increasing its temperature. During the winter,
road salt added to roads often washes into streams, increasing their
salinity and total dissolved solids concentrations.
Cars driving on those paved streets add air
pollutants to atmosphere that can create acid rain, and vehicles
can add pollutants more directly to a stream when they leak oil
or antifreeze onto roads and parking lots.
Homeowners can impact a stream. Improper
disposal of car waste (oil and antifreeze) changed at home, as well
as the improper disposal of other household wastes and toxins can
add to water pollution. Some homeowners dump wastes
into storm drains that empty directly into nearby creeks.
Many homeowners take great pride in a perfectly manicured lawn.
However, if lawn fertilizers and pesticides are used improperly
or in excess, they can wash into nearby waterways during rain events.
As urban sprawl continues in Western Pennsylvania
and more people move into suburbs, the development of these
areas can significantly degrade waterways. For instance, construction
sites for homes, businesses, and roadways can cause soil erosion
and siltation as vegetation is removed from the land.
Recreation Areas
- point source
To escape the city or home for a while, many people head to the
woods. The natural beauty of Pennsylvania draws millions
of visitors to its forests and waterways. Pennsylvania's
4.5 million acres of public land include 116 state parks (one of
the largest systems in the United States), and 2.1 million acres
of state forests (one of the largest in Eastern United States).
There are close to 54,000 miles of waterways, 2,500 lakes and ponds,
and 5,000 miles of trails (Department of Conservation and Natural
Resources, et.al, 1990's). Recreation use on public
and private land can to detrimental to the waterways that many people
come to enjoy.
Rural vacation homes and cabins can have
faulty septic systems or none at all. All terrain vehicles
(ATV's) can tear up land and cause soil erosion near streams.
Illegal ATV riding in a creek can destroy fish, mussel, and insect
habitats. Some hiking trails and "off roading" areas are being eroded.
Litter from hikers, boaters, fisherman, and campers can also be
an annoying problem.
Problem Streams
of Western Pennsylvania
Based on a Pennsylvania Department of Environmental Protection (Resources)
"1988 Pennsylvania Water Quality Assessment", a list of 20 waterways
of most concern due to pollution was created. The following
Western Pennsylvania waterways made that list - all are located
in southwest corner of the state:
| Waterway |
Miles Affected |
Problems |
| Allegheny River |
14.5 |
Pesticides, industrial wastes, acid
mine drainage |
| Monongahela River |
12.2 |
Pesticides, industrial wastes, acid
mine drainage |
| Ohio River |
40.0 |
Metals, reduced oxygen levels, pesticides,
acid mine drainage, industrial wastes, chemicals |
| Chartiers Creek (tributary to Ohio River) |
35.0 |
Metals, reduced oxygen levels, acid
mine drainage, pesticides, turbidity and suspended solids |
| Raccoon Creek (tributary to Ohio River) |
78.0 |
Metals, reduced oxygen levels, acid
mine drainage, turbidity and suspended solids, dissolved solids |
Source: Cuff, D.J. et al., 1989. The Atlas
of Pennsylvania
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