Introduction
Toxic waste is waste material that can cause death or injury
to living creatures. It spreads quite easily and can contaminate lakes and
rivers. The term is often used interchangeably with “hazardous waste”, or
discarded material that can pose a long-term risk to health or environment. Toxic waste may be produced by heavy industry, but also comes from residential use (e.g. cleaning products, cosmetics, lawn care products), agriculture (e.g. chemical fertilizers, pesticides), the military (nuclear weapons testing, chemical warfare), medical facilities (e.g. pharmaceuticals, radioisotopes), and light industry, such as dry cleaning establishments. Toxic waste comes in many forms, such as liquid, solid, or sludge and it contains chemicals, heavy metals, radioisotopes, dangerous pathogens, or other toxins.
The substance which causing toxic effect to a living
organism is called Toxicant. Lets we see about the toxic mechanism and
some details about toxic chemical substances.
Mechanism
of Toxicity
Step 1 – Delivery: From the Site of exposure to the
target
¢ Ultimate
toxicant
Chemical
species that reacts with the endogenous target molecule or critically alters
the biological environment
Original
chemical (parent)
Metabolite
or a reactive oxygen or nitrogen species generated by biotransformation
Endogenous
molecule
¢ Concentration
depends on the bodies ability to increase of decrease the concentration at the
target site
Accumulation and Pre-systematic Elimination
¢ Accumulation
Facilitated
by absorption, distribution to the site of action, reabsorption, and toxication
(metabolic activation)
¢ Work
against accumulation
Presystemic
elimination
Distribution
away for target site
Excretion
detoxication
Absorption vs. Presystemic elimination
¢ Absorption
Transfer
from the site of exposure into the system circulation
¢ Presystemic
Elimination
Toxin
may be eliminated before reaching the systemic circulation
Eliminated
via GI mucosal cells, liver or lungs
First
pass effect
Could
cause injury to GI mucosa, liver or lungs
Distribution to and Away from Target
¢ Exit
blood and enter the extra cellular space
¢ Affect
the surface or interior of a tissue cell
Excretion
Removal
of xenobiotic from the blood and their return to the external environment
Physical
mechanism
Biotransformation
is chemical
Depends
on physiochemical properties of toxicant
Major
excretory organs – kidney and liver
Efficiently
remove hydrophilic chemicals (acids, bases)
Toxication
¢ Biotransformation
to harmful products is called toxication or metabolic activation. The
followings are the medium which causes detoxication.
Electrophiles
¢ Positively
charged
Free
radicals
¢ Unpaired
electrons
Nucleophiles
¢ Negatively
charged
Redox-active
reactants
¢ Can
donate or accept electrons
Detoxification
Biotransformation
that eliminate the ultimate toxicant or prevent its formation
May
be competing with toxication
Adding
a functional group
Step 2: Interaction With target and alteration of
biological environment
¢ Exit
blood and enter the extra cellular space
¢ Affect
the surface or interior of a tissue cell
Step 3: Cellular Dysfunction Injury
- Interference with a chemical that transmits a message across a neural synapse (for example, the inhibition of the enzyme acetyl cholinesterase by organophosphate pesticides).
- Lethal Injury or cell death
Step4: Disrepair
¢ Many
toxicants alter macromolecules that may lead to damage of cell, tissue, or
complete organism
·
Repair of Proteins: Oxidation of proteins, Repair
by using reductants – NADPH, Molecular chaperones – refold altered proteins, Proteolytic
degradation- remove damaged proteins
·
Repair of Lipids: Oxidation of lipids , Reductants
– glutathione reductase
·
Repair of DNA: Nuclear DNA is stable. Various
repair mechanism (chromatin), Mitochondria DNA – lacks histones and repair
mechanisms.
·
Cellular repair: Repair of damaged neurons, Axonal damage is repaired if cell body is
intact
·
Tissue Repair:
Ø Apoptosis
Ø
Initiated
by cell injury
Ø
Cell
shrinks
Ø
Nuclear
and cytoplasmic materials condense
Ø
Membrane
fragments and Eliminating cells that can become cancerous.
Above we saw about hoe the toxic mechanism works. Now the
following info is going say about some toxic chemical substance which we handle
daily in our life…
Toxicants
which we use in our daily life
Automotive
Corrosive / Poisonous Cleaners
Lawn & Garden
Lighting
|
Other
Paints and Stains
|
Now we know about what is mean toxicity and its mechanism.
Now we are going to see about some toxic substance and their chemical
character.
Some
Toxic Chemicals:
1) Cyanide toxicityCyanide toxicity is generally considered to be a rare form of poisoning; however, cyanide exposure occurs relatively frequently in patients with smoke inhalation from residential or industrial fires. Cyanide poisoning also may occur in industry, particularly in the metal trades, mining, electroplating, jewelry manufacturing, and radiographic film recovery. It is also encountered in fumigation of ships, warehouses, and other structures. Cyanides are also used as suicidal agents, particularly among health-care and laboratory workers, and they can potentially be used in a terrorist attack.
Numerous forms of cyanide exist, including gaseous hydrogen cyanide (HCN), water-soluble potassium and sodium cyanide salts, and poorly water-soluble mercury, copper, gold, and silver cyanide salts. In addition, a number of cyanide-containing compounds, known as cyanogens, may release cyanide during metabolism. These include, but are not limited to, cyanogen chloride and cyanogen bromide (gases with potent pulmonary irritant effects), nitriles (R-CN), and sodium nitroprusside, which may produce iatrogenic cyanide poisoning during prolonged or high-dose intravenous (IV) therapy (>10 mcg/kg/min).
Industry widely uses nitriles as solvents and in the manufacturing of plastics. Nitriles may release HCN during burning or when metabolized following absorption by the skin or gastrointestinal tract. A number of synthesized (e.g., polyacrylonitrile, polyurethane, polyamide, urea-formaldehyde, melamine) and natural (e.g., wool, silk) compounds produce HCN when burned. These combustion gases likely contribute to the morbidity and mortality from smoke inhalation.
Finally, chronic consumption of cyanide-containing foods, such as cassava root or apricot seeds, may lead to cyanide poisoning.
Overall, depending on its form, cyanide may cause toxicity through parenteral administration, inhalation, ingestion, or dermal absorption.
2) Benzene Toxicity
Benzene
is a colourless liquid with a sweet odour. It evaporates into the air very
quickly and dissolves slightly in water. It is highly flammable and is formed
from both natural processes and human activities.
Benzene
is widely used in the United States; it ranks in the top 20 chemicals for
production volume. Some industries use benzene to make other chemicals which
are used to make plastics, resins, and nylon and synthetic fibres. Benzene is
also used to make some types of rubbers, lubricants, dyes, detergents, drugs,
and pesticides. Natural sources of benzene include volcanoes and forest fires.
Benzene is also a natural part of crude oil, gasoline, and cigarette smoke.
- Industrial processes are the main source of benzene in the environment.
- Benzene can pass into the air from water and soil.
- It reacts with other chemicals in the air and breaks down within a few days.
- Benzene in the air can attach to rain or snow and be carried back down to the ground.
- It breaks down more slowly in water and soil, and can pass through the soil into underground water.
- Benzene does not build up in plants or animals.
- Outdoor air contains low levels of benzene from tobacco smoke, automobile service stations, exhaust from motor vehicles, and industrial emissions.
- Indoor air generally contains higher levels of benzene from products that contain it such as glues, paints, furniture wax, and detergents.
- Air around hazardous waste sites or gas stations will contain higher levels of benzene.
- Leakage from underground storage tanks or from hazardous waste sites containing benzene can result in benzene contamination of well water.
- People working in industries that make or use benzene may be exposed to the highest levels of it.
- A major source of benzene exposure is tobacco smoke.
- Benzene exposure also occurs from using condoms
Breathing
very high levels of benzene can result in death, while high levels can cause
drowsiness, dizziness, rapid heart rate, headaches, tremors, confusion, and
unconsciousness. Eating or drinking foods containing high levels of benzene can
cause vomiting, irritation of the stomach, dizziness, sleepiness, convulsions,
rapid heart rate, and death.
The
major effect of benzene from long-term (365 days or longer) exposure is on the
blood. Benzene causes harmful effects on the bone marrow and can cause a
decrease in red blood cells leading to anaemia. It can also cause excessive
bleeding and can affect the immune system, increasing the chance for infection.
Some
women who breathed high levels of benzene for many months had irregular
menstrual periods and a decrease in the size of their ovaries. It is not known
whether benzene exposure affects the developing foetus in pregnant women or
fertility in men.
Animal
studies have shown low birth weights, delayed bone formation, and bone marrow
damage when pregnant animals breathed benzene.
The
Department of Health and Human Services (DHHS) has determined that benzene is a
known human carcinogen. Long-term exposure to high levels of benzene in
the air can cause leukemia, cancer of the blood-forming organs.
Several
tests can show if you have been exposed to benzene. There is test for measuring
benzene in the breath; this test must be done shortly after exposure. Benzene
can also be measured in the blood; however, since benzene disappears rapidly
from the blood, measurements are accurate only for recent exposures.
In
the body, benzene is converted to products called metabolites. Certain
metabolites can be measured in the urine. However, this test must be done
shortly after exposure and is not a reliable indicator of how much benzene you
have been exposed to, since the metabolites may be present in urine from other
sources.
3)
The bipyridylium herbicides Toxicity
The
bipyridylium herbicides are quaternary ammonium salts. Their mode of action is
well understood and brought about by chemical changes that their di-cations
undergo in plant cells. Little attention has been paid to the role of the
anions, chloride and bromide in the products of the market. It is hypothesized
that these anions will form strong acids concomitant with the chemical changes
of the di-cations. Toxic effects in animals and humans, especially regarding
skin, epithelia and eyes, might be due to occurring hyperacidity in affected
cells. Therefore, a commercial product was transformed into a diacetate salt
that was tested in comparative trials with respect to herbicidal activity and
damage towards human monocytes. While the desired plant harming effect compared
very favorably with the marketed product, the damaging result with human monocytes
was substantially reduced.
The
scientific literature abounds in publications on the activity, mode of action,
toxicity and other aspects of the so-called bipyridylium herbicides (also
called quats) since their patenting and introduction on the market half a
century ago. The two main representatives paraquat (1,
1’-dimethyl-4,4’-bipyridinium dichloride) and diquat dibromide
(6,7-dihydrodipyrido (1,2-a:2’,1’-c) pyrazinediium dibromide) still prove
useful as contact herbicides and protect many crops worldwide. This,
notwithstanding widespread criticism based on the occurrence of numerous
accidents and fatalities incurred by users. For extensive reports on toxicity
and mode of action the reader’s attention is called to papers listed under.
In
chloroplasts or other affected plant cells these herbicides are initially
reduced to radical cations which, in turn, give rise to oxygen containing free
radicals. These attack the sensitive unsaturated lipids of the cell membrane by
peroxidation, eventually leading to the loss of membrane function. The
quat-derived cation-radical can be oxidized again to form a redox cycle in
which the di-cations (the quats) adopt the role of a catalyst.
Stoichiometry
requires that the di-cations must have, as in any salt, the equivalent of
anions as counterpart. In the case of paraquat two chloride ions, with diquat
two bromide ions establish the balance. On investigating the manufacturing
processes it turns out that the respective reagents used in the synthesis
dictate the nature of these anions. With paraquat which is formed by double
alkylation of 4,4’-dipyridyl with methyl chloride, it is the two chloride ions
that compensate the charges of the di-cation, with diquat on the other hand,
alkylation of 2,2’-dipyridyl is brought about by reaction with
1,2-dibromoethane. Here the positive charges of the di-cation are made up by
two bromide ions.
In
none of the numerous toxicological investigations were the possible roles or
effects of the anions taken into consideration. The observed symptoms could be
explained by the mode of action governed by the activity of the di-cation.
Furthermore, in the case of paraquat this omission seems obvious and
comprehensible, since chloride ions are ubiquitous in living cells. With
diquat, however, the weight of the bromide ions represents more than half the
weight of the herbicidal active substance. It is, therefore, somewhat
surprising that no attention was paid to the possible toxic effects of these
ions, inasmuch as these do not normally occur in appreciable amounts in living
matter. The belief must prevail that the role of these ions can be disregarded.
There
are observations which indicate that halides of the quats show chromatographic
parameters that differ from the ones of corresponding acetates. Quaternary
salts can be regarded as being derived from quaternary hydroxides which are
comparable in basic strength to alkali hydroxides. In the quats’ cases these
bases are too unstable to be known, because the inversely charged ions react
with one another leading to decomposition. Consequently it is well-known that
quats are unstable in an alkaline medium. If the quats di-cations undergo a
chemical reaction in which their electrical charge is reduced, stoichiometry
requires that the counterions, halides in our cases, will have to balance the
change in charges. In an aqueous system, such as the cytoplasm, this will be
achieved by combining with a proton and concomitant formation of a hydrogen
halide. Acidification of the medium is the consequence. As long as the
buffering capacity of the affected cell compartment can cope with the acid thus
formed all is well. If not, the cytoplasm and structures in touch will incur
damage that may lead to denaturation of proteins and loss of function.
That
aqueous solutions of the quats can corrode aluminum alloy containers was
recognized early on. The shiny metal surface reacts with the di-cation by
reducing it to the radical-cation or even further to an uncharged weak base
that cannot neutralize the hydrogen chloride or bromide formed. Therefore, the
solution turns acidic, leading to further and enhanced corrosion. Additives,
such as thiophosphates, were invented that shield the metal surface and prevent
corrosion
In
addition, the severe toxic attacks perpetrated by the quats on epithelia, eyes
and lungs resemble the ones that are observed on exposure of skin to the
mustard gases, phosgene or its dimer. Respiratory failure may result just as in
many cases of paraquat poisoning. The author is not aware of a direct
comparison of toxic effects of the two groups of substances in question.
Phosgene is a suitable agent for a qualitative comparison here, because in its
action which involves its hydrolysis or acylation of a substrate (e.g. proteins
in the pulmonary alveoli) hydrochloric acid and eventually the innocuous carbon
dioxide are the sole products formed. Similarly and confirmatively, pulmonary
toxic effects with alveolar damage can be brought about by mere aspiration of
sprayed dilute hydrogen chloride solution.
The
common denominator these toxic agents share is hydrogen halide. With the quats
it is formed on reduction of the di-cation; with the chemical warfare agents
mentioned it develops upon hydrolysis, in an alkylation or acylation reaction
that these agents can undergo. The warfare agents lack a bipyridylium
di-cation; nonetheless they exert a powerful toxic action.
It
has been well established that the cationic moiety of the quats is responsible
for the herbicidal activity. As hinted, little attention has been paid to the nature
of the anions. In order to measure their possible effect, other quats salts,
especially those of a weak acid had to be prepared and tested. The proven mode
of action now predicts the formation of a weak acid, unlike with the products
in use and the warfare agents. A diquat solution was chosen for the
experiments. Acetate ions suggested themselves for the exchange, being derived
from both a weak and physiological acid. The resulting diquat diacetate
solution was used for comparative herbicidal tests with Heuchera. This
ornamental plant is indigenous to California and was suggested by a botanist;
first, because it was not in a hibernating state and available in quantity, and
secondly its leaves are suitable for application of the test-solutions by pipets,
thus permitting indoor experiments. Not surprisingly, the expectation was
fulfilled. Judged by the rate and amount of wilting and crust formation the
diacetate solution proved at least as active as the commercial dibromide product.
Will
the new formulation with acetate ions as anionic counterpart be less toxic?
Experiments with animals were out of reach for the author but will eventually
be needed for final evaluation. Comparative tests with human monocytes were
commissioned. While in a Trypan Blue test the two solutions proved equally
active, pointing to equal damage of the cell walls, the two solutions differed
significantly in the so-called WST-1 test, when the 1 mM solution of the
diacetate behaved more closely to the control than to the solution of the
dibromide. At a tenfold higher concentration, however, the diacetate solution
was damaging, too. These results were corroborated by experiments at higher
temperature and reduced exposure time. Phase contrast microphotographs taken 72
hours after initiation of cell cultivation showed that the cells looked less
damaged than the ones that were treated with the commercial product’s solution.
Quantitative results, however, cannot be obtained from this test-setup.
It
can be expected that, at least in contaminations of vital surfaces (e.g. mucous
membranes or eyes), bipyridylium herbicidal solutions containing anions of weak
acids will prove less toxic than the commercially available products.
4) TCDD (2,3,7,8-Tetrachlorodibenzodioxin)
TCDD can produce both adaptive (beneficial) and adverse effects. One adaptive response is the induction of xenobiotic-metabolizing enzymes, which catalyze the metabolic processing of lipophilic chemicals to water-soluble derivatives, thereby facilitating their elimination via the urine. We are analyzing one such adaptive response, the induction of CYP1A1 gene transcription in mouse hepatoma cells, as a model for understanding the mechanism of dioxin action.
In experimental animals, TCDD elicits numerous adverse effects, raising concern about the risk it poses to public health. In humans, TCDD can produce the skin condition known as chloracne; the possibility that it also produces cancer, endocrine alterations, immunological changes, and/or birth defects (as it does in animals) is the subject of debate. Many individuals have been exposed to TCDD, primarily from dietary sources, although occupational and accidental exposures have also occurred. Thus, the population at potential risk for adverse effects is large. TCDD is a poor substrate for detoxification enzymes; therefore, it tends to persist in the body. Raising the concern that repeated exposures, even to "low" concentrations, may evoke harmful health effects. Knowledge of the mechanism of dioxin action may help in accessing its health risks while generating new insights into the regulation of mammalian gene expression.
Diseases caused by Toxic Chemicals:
Asbestosis and Mesothelioma: Asbestosis is caused by exposure to asbestos. It is a debilitating disease that results in reduced lung capacity and restricted breathing. Asbestosis progresses slowly by scarring and inflaming lung tissue. The disease can be treated, but not cured.
Asbestosis victims have a high risk of developing lung cancer or even mesothelioma, which is a fatal form of cancer. Mesothelioma affects specialized cells that line the membranes surrounding the chest and abdomen. Pleural mesothelioma causes severe respiratory problems.
Lung
Cancer: Smoking is the
main cause of lung cancer is the United States. Asbestos exposure is among
other major causes.
The
two main types of lung cancer are small cell lung cancer, in which the cancer
cells are small and round (almost 20% of lung cancers), and non–small cell lung
cancer, in which the cancer cells are larger (almost 80% of lung cancers).
Small cell lung cancer tends to spread more rapidly throughout the body than
other types of lung cancer. For a discussion of how lung cancer progresses, and
its treatment and diagnosis.
Chronic Beryllium Disease or Berylliosis: Chronic beryllium disease or berylliosis is always caused by beryllium exposure. It is a painful scarring of the lung tissue those results in fatigue and shortness of breath. Physicians may prescribe steroids to reduce the pain, but chronic beryllium disease is not curable.
Conclusion:
In this article we saw
about toxic chemical mechanism, some details about toxic chemicals, and
diseases caused by the toxic chemicals.
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