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Connecticut Water Trails Association |
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Connecticut Water Trails Program Water Trails & Water Pollution
What Are The Properties And Dangers Of Water Pollutants?
Many different chemicals are regarded as pollutants, ranging from simple inorganic ions to complex organic molecules.
The water pollutants are all divided up into various classes. Every class of pollutants has its own specific ways of entering the environment and its own specific dangers. All classes have major pollutants in it that are known to many people, because of the various health effects.
Organic Pollutants
Organic compounds are compounds that consist of long bonds, usually made up of carbon. Many organic compounds are basic fabrics of living organisms. Molecules built of carbon and of carbon and hydrogen are non-polar and have little to no water solubility. They have little to no electrical charge.
The behavior of organic compounds is dependent upon their molecular structure, size and shape and the presence of functional groups that are important determinants of toxicity.
It is important to know the structure of organic compounds, in order to predict their fate in living organisms and the environment. The organic compounds that are dangerous to the environment are all man-made and have only existed during the last century.
There are many different types of organic pollutants, examples are:
Hydrocarbons. These are carbon-hydrogen bonds. They can be divided up into two classes, the first being single-bonded alkanes, double bonded alkenes and triple bonded alkynes (gasses or liquids) and the second being aromatic hydrocarbons, which contain ring structures (liquids or solids). Aromatic hydrocarbons such as PAH's are much more reactive than any of the first class kinds of hydrocarbons.
PCB's are stable and unreactive fluids that are used as hydraulic fluids, coolant/ insulation fluids in transformers and plasticizers in paints. There are many different PCB's. None of them are water-soluble. In many countries PCB's are restricted.
Insecticides
such as DDT's are very dangerous because they accumulate in fat tissues
of lower animals and then enter the food chain. They have been
restricted for decades.
Inorganic Fertilizers
Some inorganic pollutants are not particularly toxic, but are still a danger to the environment because they are used so extensively. These include fertilizers, such as nitrates and phosphates. Nitrates and phosphates cause algal blooms in surface water, which causes the oxygen level of the water to decline. This causes oxygen starvation because of the uptake of oxygen by microrganisms that brake down algae. This is called eutrophication.
Metals
Metals can react to dangerous products with other
ions. They are often involved in electron transfer reactions involving
oxygen. This can lead to the formation of toxic oxyradicals.
Metals can form metalloids and then bond to
organic compounds to form lipophilic substances that are often highly
toxic and can be stored in the fat-supply of animals and humans. Metals
can also bond to cellular macromolecules in the human body.
Metals cannot be broken down into less harmful
components, as they are non-biodegradable. The only chance organisms
have against metals is to store them in body tissues where they cannot
do any harm.
Radioactive Isotopes
The half-lives and the ways of decay of radioactive
isotopes determine how dangerous they are to humans. Humans create all
radioactive isotopes in the nuclear industry. There are still debates
going on about whether the benefits of nuclear power exceed the dangers
of radioactive radiation. When an atom of a radioactive substance
decays, it can produce four kinds of particles: alpha, beta, gamma and
neutrons.
Alpha particles can only travel a short distance
through air and human tissues, but they can be very damaging if they
collide with cells because of their large mass. They are positively
charged.
Beta particles are more penetrating, but they do
much less damage than alpha particles. They are negatively charged.
Gamma rays are highly penetrating. Their damage is
similar to that of beta rays.
Neutrons are liberated through radiation and react
with other elements through collision. They are the basis for nuclear
fission in a reactor.
The radioactivity of a substance is measured in
bequerels, but this does not express the amount of tissue damage the
radiation causes. That is why the amount of radiation causing 1 kg of
tissue to absorb 1 joule of energy is now expressed in grays. Different
kinds of radiation can do different kinds of damage, because the energy
is imparted into tissues in different ways. This is expressed in
sieverts. An amount of alpha radiation can do twenty times the damage of
the same amount of beta radiation. Radioactive matter has to be held in
storage for different periods of time, in order to erase the danger. How
long it has to be stored depends upon the half-life of the isotopes; the
time taken for half of the atoms of a radioactive isotope to decay.
What Are The Specific
Ways Through Which Water Pollutants Enter The Environment?
Discharge of sewage water represents a mayor global
source of pollution. Domestic and industrial wastes are discharged unto
surface water through sewage systems. In some cases industrial waste is
released directly unto surface water. The quality of sewage water that
enters the surface water depends upon the pollutants that are present in
the sewage water and the extent to which it is treated before it is
brought in contact with surface water.
Domestic sewage water mainly consists of paper,
soap, urine, feces and detergents. Industrial wastes are varied and
depend upon the specific processes of the plants that they origin from.
Heavy metals are associated with mining and smelting
operations, chlorophenols and fungicides with pulp mills, insecticides
with mothproofing factories, several different organic chemicals with
the chemical industry and radioactive substances with nuclear power
plants.
On land the releases of industrial waste are closely
controlled, but offshore oil and manganese extraction lead to direct
discharge of pollutants into the seas. Radioactive waste is dumped into
the sea in large concrete barrels to decay, but often the barrels will
start to have defects after a while. Representatives of factories often
ship waste onto sea to dump it illegally, because it is very expensive
to have their water purified.
Oil is released into the sea through oil tankers and
shipwrecks and pesticides are applied to water to control aquatic pests.
Paints on boats will decay during long trips on the ocean and will
eventually end up in the water. During the growth period of crops nitrates and
phosphates are absorbed by plants, but when the plants die they are
released from dead plant material into the soil and will often end up in
surface water.
Except for the deliberate causes of surface water
pollution, pollutants can also enter the water environment accidentally,
for instance through atmospheric deposition. Pesticides can enter
surface water easily this way, because they are applied as droplets or
sprays. Pollutants present on land can enter surface water through heavy
rainfall or infiltrate into the soil and enter surface waters through
groundwater.
The effects of pollutants are noticed mostly in
small inland seas and lakes. This is because the oceans have a natural
dilution system for incoming pollutants, whereas lakes have no effective
outlet. Due to this, much depends upon the rate of degradation and
precipitation that will remove the pollutants from water.
How Are Pollutants
Transported Through Water?
Pollutants can exist in water in different states.
They can be dissolved or they can be in suspension, which means that
they exist in the form of droplets or particles. Pollutants can also be
dissolved in droplets or absorbed by particles. All states of pollutants
can travel great distances through water in many different ways.
Particulate matter may fall to the bottom of streams
and lakes or rise to the surface, depending on its density. This means
that it mostly remains on the same location when the water does not flow
very fast. In rivers, pollutants usually travel great distances. The
distance they travel depends upon the stability and physical state of
the pollutant and the speed of flow of the river. Pollutants can travel
farthest when they are in solution in a river that is fast flowing. The
concentrations on one site are then generally low, but the pollutant can
be detected on many more sites than when it would not have been so
easily transported.
In lakes and oceans pollutants are transported
through currents. There are many currents in the oceans, which are
wind-driven. This enables a pollutant to travel from one continent to
another.
We usually count on the ability of the oceans to
reduce pollutants in concentration, the so-called 'self-cleaning
ability' of oceans. But this does not always work, because the movement
of the currents in the oceans is not uniform. This causes inshore waters
to often have substantially higher levels of pollution than the open
sea. When persistent pollutants accumulate in fish or sea
birds they cannot only become a toxic danger to aquatic food chains,
they can also travel great distances within these animals and end up in
the food chains of non-polluted areas.
Which Factors
Determine The Movement And Distribution Of Pollutants In Water?
Physical processes determine the movement of
chemicals within water; movement depends upon properties of the
chemicals themselves and properties of the water. These processes will
be overviewed here.
Water is a polar liquid. This means that the oxygen
atom in a water molecule attracts the electrons of the hydrogen atoms,
so that these develop partial positive charges. The oxygen atom gets a
partial negative charge, through which it can attract atoms of other
water molecules to form hydrogen bonds. In non-polar compounds, such as
hydrocarbons, there is hardly any charge separation and consequently
they do not dissolve in water.
Water tends to form aggregates in which four other
molecules surround each water molecule. Cations and anions have an
affinity for the parts of water that carry an opposite charge, so that
the water aggregates are disrupted and the ions dissolve. Many organic
salts and polar organic compounds are water-soluble, but non-polar
organic liquids are not.
From this we can conclude, that molecules that can
perform charge separation can easily dissolve in water, whereas
molecules that do not have charges are not very water-soluble.
A consequence of polarity is the hydrophobic effect.
In the process of forming aggregates with charged molecules water
actively excludes non-polar substances. This leads to the formation of
phospholipid bilayers, which contribute to the movement of hydrophobic
pollutants though membranes.
The level of hydrophobicity is determined by the
water/ octanol partition coefficient. The concentration of a compound in
octanol is divided through the concentration in water. The higher the
number that results from this calculation, the more hydrophobic the
compound in question is.
Whether a compound remains in the water is also
determined by its vapor pressure. Vapor pressure means the tendency of a
liquid or solid to volatilise. Vapor pressure increases when
temperatures rise, as surface molecules increase in kinetic energy. Then
more molecules in a watery solution have the tendency to vaporize, which
means they are no longer in solution.
The partition of the chemical between different
environmental compartments air, water and soil is another important
factor. The escaping tendency or 'fugacity' of a substance determines
the movement from one compartment to another.
Molecular stability is a factor that determines the
time a chemical remains in the environment and the distances it can
travel. In the environment chemical and biochemical processes, such as
hydrolyses and oxidation, break down chemicals. The break down is not
only determined by the stability of the chemical, but also by the
environmental factors temperature, level of solar radiation, pH and
nature of absorbing surface. For instance, the pH of water determines
the water-solubility of metals. Sometimes biotransformation of a
compound in the environment during break down is not very positive,
because it can lead to increased toxicity of a chemical.
How Do Organisms
Respond To Water Pollutants?
When pollution enters the body of an organism it
causes a variety of changes. These changes can either serve to protect
the organism against harmful effects or not.
The first response of an organism to pollutants is
to bring a protective mechanism into action. In most cases these
mechanisms maintain the detoxification of pollutants, but in some cases
they produce active substances that can cause more damage to the cell
than the original pollutant.
Another response is to reduce the availability of
pollutants by binding them to another molecule, to excrete or store
them.
Next to protective mechanisms an organism can also
bring a mechanism into action that repairs damage caused by pollutants.
Responds to toxicity and the uptake of pollutants
not only depends upon the pollutant that enters the organisms body, but
also upon the kind of organism in question.
What General Effects
Can Water Pollutants Have On Organisms?
Water pollutants can have many different effects on
organisms, always depending on the pollutant and the organism in
question. Here the general effects a pollutant can have are discussed.
Genotoxicity
Many compounds that enter the body of an organism
are known to cause damage to DNA. These compounds are called genotoxins,
due to their genotoxic effect.
Usually when pollutants damage DNA a natural repair
system in an organism will return it to its usual state, but when this
goes wrong for any particular reason cells with damaged DNA can divide.
Mutant cells are than produced and the defect can spread, causing the
offspring of the organism in question to have serious defects that are
often very damaging to their health.
Examples of genotoxins are PAH's, aflatoxin and
vinyl chloride.
In all of these genotoxins it is not the original
compound that reacts with DNA, for this is relatively stable. Highly
reactive short-lived products produced from the original compound by
enzymes usually cause the reactions.
Carcinogenity
Several pollutants are carcinogenic, which means
they can induce cancer in the body of humans and animals. Carcinogenic
pollutants are pollutants that play a role in one or more of the stages
of cancer development in an organism.
Pollutants can be inductors; this means that they
introduce cancer-forming properties in the cells of an organism. They
can also be promoters, which means that they promote the growth of cells
that have cancer-forming properties. Finally, they can be progressors,
which means that they stimulate unrestrained division and spreading of
cancer cells. When one of these substances is absent cancer cannot be
induced.
When cancer cells are malignant, they can spread
through the human body rapidly, causing defects to healthy cells and
immunity mechanisms. They will destroy normal body cells and cause
cancer in organs and systems.
Neurotoxicity
The nervous system of organisms is very sensitive to
toxic effects of chemicals, both naturally occurring and man-made.
Chemicals that cause neurological effects are called neurotoxins.
Examples of dangerous neurotoxins are insecticides.
Neurotoxins all somehow disturb the normal
transmission of impulses along nerves or across synapses.
The consequences of neurotoxicity are varied. They
can be uncoordinated muscular tremors and convulsions, malfunction of
nerves and transmissions, dizziness and depression, or even total
malfunction of body parts. Neurotoxicity can be so serious, that
synapses are blocked. Synaptic block causes death as a result of
paralysis of the diaphragm muscles and respiratory failure.
Disturbance Of Energy
Transfer
Energy transformation in organisms is done through
mitochondria systems in the cells. On the mitochondrion ATP-molecules
are produced, which transfer energy through the body of an organism.
When ATP production is disturbed the energy transfer will cease. This
will make an organism tired and lifeless and unable to function
normally.
Reproductive Failure
Pollutants that cause reproductive failure due to
damage to the reproductive organs are called endocrine disruptors. There
are several ways in which a pollutant can act as an endocrine disruptor.
The first is an oestrogenic chemical. This is a
chemical that can imitate an oestrogen by binding to the oestrogen
receptor. This results in the induction of oestrogenic processes,
causing an organism to experience reproductive failure due to a
disturbance in the reproductive system.
An oestrogenic chemical can also block the effects
of endogenous oestrogens by binding to the oestrogenic receptor. This
causes masculization of female organisms.
It is also possible that female reproductive
chemicals are found in male organisms. This causes hermaphrodites.
Imposex has been widely reported in marine organisms, for instance with
dog whelks by tributyl tin.
Another series of problems is caused when chemicals
block the hormone receptor sites. In this case, the normal action of the
hormone is inhibited, as it cannot react with the receptor. This can
cause infertility when it occurs over a longer period of time.
Behavioral Effects
All behaviors are vulnerable to alteration by
pollutants. Foraging levels can deplete, resulting in reduced
production. Vulnerability to predators can increase, due to a depletion
of vigilance. In these ways, effects of pollutants on behavior result in
lowered production and higher mortality rates.
A common result of pollution is a loss of appetite
and thus less uptake of food. Searching for preys can also be affected,
due to effects of pollutants on learning, search strategy and sensory
systems.
These behavioral effects cause lower chances of
survival of organisms, mainly animals.
One property of pollutants that should always be
kept in mind is their possibility to interact with one another. Chemical
reactions that cause pollutants to combine can reduce their overall
chemical effect, but can also increase it, making a pollutant even more
dangerous to organisms.
How Is Toxicity Of
Water Pollutants Tested With Aquatic Animals?
Toxicity of chemicals in water can be tested with
aquatic animals as indicators. Toxicity tests with aquatic animals are
mainly concerned with direct uptake from water. The chemicals may be in
solution, in suspension or both.
To determine values for lethal concentrations
organisms are exposed to different concentrations. When an effect occurs
the effect-concentration of the chemical is noted. When the test-animal
dies the lethal concentration is noted. This way the toxicity of a
chemical is determined in a laboratory. When many of the test animals
die at low concentrations of a chemical it means that the chemical in
question is very toxic. When we know how toxic a chemical is, we also
know the effects of this chemical when a certain concentration is
present at a location.
The toxicity of a chemical for certain aquatic
organisms depends upon the present concentration of the chemical and the
time of exposure to the chemical. The time of exposure to a chemical
during a toxicity test depends upon the test animals that are being
used. Daphnia are often used for certain toxicity tests. These tests
commonly take only 24 to 48 hours. By contrast, fish toxicity tests take
longer, usually four days up to a week.
Data of such chemical toxicity tests not only show
how toxic a certain chemical is, they also give an indication of the
toxicity of a chemical in relation to other chemicals. Not all toxicity
tests work to lethal end-points; sometimes a change in behavior of an
aquatic animal is the indicator of toxicity of a certain chemical.
Toxicity tests are influenced by both the properties
of the chemical and the properties of the test organism. The
availability of the chemical to the test organism is always an important
factor, because the toxicity of a chemical declines when it is not
readily available to a test organism.
Laboratories can also perform toxicity tests for
chemicals present in water sediment nowadays.
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