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Transport
movements of contaminants within or between environmental compartment or media
Chemical release from a source goes into an
environmental compartment (water,air, soil).
(Enviromental Compartment) Then it gets transported within
the compartment and then to another compartment (from water to soil, soil to air, soil to water, water to air).
(Environmental Compartment) Chemical may change in this
process during their time in these compartments
Fate
physical, chemical or biological transformations of contaminants in the environment
Fate and transport of chemicals is affected by their
physical-chemical properties, Ex: chemical that easily evaporates
How harmful a substance is depends on
physical-chemical properties of the substance
Volatility
How much it evaporates and the tendency for it to evaporate?
Polarity; Chemicals that are polar - they dissolve in
water because water is polar (LIKE DISSOLVES LIKE) non polar does not dissolve in water
Sodium chloride is polar and dissolves in
water
Oil is a lipid thus
they float and they are nonpolar
Dioxin is
nonpolar
Solubility
Water soluble toxins
Fat soluble toxins (lipophilic tendency)
not soluble in water but soluble in fats and lipids thus accumulating
Oxidation state
if an element is differently charged it will have different properties
Molecular weight
Heavier the molecule, less soluble in water
Consequences of lipophilic tendency
majority are organic materials
Bioaccumulation
building up over time, in individual organisms
Biomagnification
building up over time, across the levels in a food chain
Generally, higher-molecular-weight chemicals are:
More lipophilic and more persistent and Less volatile and less water-soluble
Persistence in environment
Quantified as a half-life in air, water, or soil and Affected by environmental conditions
Chemical is persistence
stays in the same form, doesn't break down chemically or physically
DDT - it does break down but it still is
dangerous, the properties do not change
environmental conditions
Sunlight, heavy metals, pH, oxygen availability and temperature, biological components
Toxicology
the science of the effects of toxic substances and of their fate and transport in the body
Ecotoxicology
in animal body
Environmental toxicology
studies fate and transport of the chemical before the chemical enters the body -- chemical from the source to the chemical that is in the body
Study of poisons
The science which studies toxic substances or poisons, that are substances which cause alteration or perturbation in the function of an organisms leading to harmful effects
Receptor
Organism (human) receiving exposure or dose
The human envelope
boundary that separates the interior of the body from the exterior environment → not only skin
Age
very important because it makes people more prone to exposure (elderly and young children)
General health
other illness may make one more receptive to the illness
General makeup
genetics from the family
Exposure
Contact with the human envelope - contact that is made with body (not the inner process yet)
Some chemicals can go through our skin; dimethyl mercury
went through the glove, through the skin into the blood.
Routes of exposure
Ingested (often greatest source of chemical exposure, 85%), Inhaled (air pollution, particles and volatiles, 10%), Absorbed through the skin (industrial, 5%)
Frequency of exposure
Exposure per time (month, year, day)
Exposure Assessment
Goal is to quantify exposure (or to find out Dose) - how much is in the tissue or what is the dosage
Methods draw on understanding of both
Environmental science (fate and transport of toxicants in environment)
Toxicology
(fate and transport of toxicants in the body)
Conceptual model of exposure begins with source of
exposure and concludes with toxicokinetics and effects in the body
Chemical comes close to the receptor
(microenvironment- then exposure - then absorbed dose - then biologically effective dose (not everything is biologically effective), it can be excreted through urine - this causes change in tissue structure or function - then possible health effect)
Toxicokinetics
the disposition of toxicants in the body
Quantifying exposure
Translating event of exposure into a dose estimate
Tools for area monitoring and personal monitoring
collect things from the microenvironment
Area monitoring
a filter inserted into the nozzle of a vacuum cleaner (a) collects dust to be analyzed in a laboratory
Personal monitoring
portable sampling device (b) incorporates a pump that takes a continuous air sample near the subject's breathing zone; the device also collects a sample of particulate matter over the whole period
Units of absorbed dose:
mg/(kg*day) — does not need to be milligram can be microgram - time can be day, hour, minute
Other sources of exposure info
Questionnaires, diaries; How often you travel here and there, how long do they play at the
other sources of exposure info; Surrogate measures
Surrogate measures (measure of effect of a specific treatment that may correlate with a real)
Some chemicals can be hard to measure so you measure
another chemical that might be similar - for example; measuring hormonal changes as a result of some chemical in the body
Geographic information system (GIS)
Contaminants present in a lake, who will it contaminate
Dose; Quantification of exposure
Amount of substance a person has ingested inhaled or/and absorbed
Acute dose
refers to single dose, usually high - high single dose
Chronic dose
repeated or continuous low dose over time - longer period of time but repeated
Long term
low dose over a lifetime
Absorbed dose
quantify that passes through the human envelope
Biologically effective dose
quantity available to interact with vulnerable tissue
Actual amount that receptor site 'sees' vs. amount taken in (bioavailability factor)
Amount that causes the illness
Biologically effective dose divided by
absorbed dose gives you bioavailability factor → ranges from 0 to 1 = closer to 1 means it's very high and very toxic and then zero means that its small and less toxic
Multiple exposure (doses)
food additives, pesticides, air pollution = combined at same time - the combined effect of the chemicals can be beneficial or harmful
Chemical interaction; Antagonistic
both chemicals together are a smaller effect; if you take high dose of vitamin D it reduces cancer
Chemical interaction; Synergistic
both chemicals together are a worse effect; if you have asbestos exposure plus smoking → increases risk for cancer and lung diseases
Disposition of Chemicals in the Body; Toxicokinetics → disposition of toxicants in the body
Body burden - Absorption, Distribution, Metabolism, Storage, Excretion
Toxicodynamics
effects in the body (response)
Response
how we react to the illness/chemical
Nonspecific Response; burning
destruction of cells caused by exposure to high concentration of strong acids or bases
Nonspecific Response; Narcosis
depression in sensory activity, reversible, caused by alcohols, ethers and benzene (difficulty walking, breathing, can result in a coma)
Specific; Response
damages one specific area
Specific; Response damages include
Damage to excretory organs, Damage to respiratory organs, Damage to reproductive function, Mutagenesis , Carcinogenesis
Acute toxicity
rapid death
Result of short period of time
can even result in sudden death
Chronic toxicity
Slowly working, mixed with other illness, takes forever
DOSE MAKES THE POISON
Every chemical is harmful at some level of exposure, How much exposure causes a harmful response
What is that dosage that is enough?
different for different individuals, if you take vitamins, you take it in tablets but you also take it from food or drinks (multiple sources) thus you must be careful
Medication
there is a dosage present you can not have more than a specific amount
Something that you think is not poisonous can be poisonous in increased amounts examples;
Tylenol, Calcium, Coffee
Dose Response curves - Two key characteristics
Slope (potency of effect) and Threshold (potential for safe dose) →
LD 50
one single acute dose that causes mortality of 50% of experimental animals in the group in 14 days - anything after that does not count
Dose-Effect Curves; Essential nutrients
poor vitamin intake, you take more supplements and you don't stop but too much will cause a problem
Toxicity Testing ; Some doses are given special names
Highest non-zero dose at which no effect was observed - no observed adverse effect level (NOAEL)
Lowest dose at which an effect (some effect) was observed
lowest observed adverse effect level (LOAEL)
If a study shows both a NOAEL and a LOAEL, can infer that the threshold is
between them
Reproductive toxicity
effect on reproductive capacity
Developmental toxicity
effect on developing organism, including teratogenesis
Other Methods for Toxicity Testing
Case reports - Doctors have to study cases, Epidemiological studies - Population studies, Computer simulations - Computer tells you exposure modeling example - movement of mercury, Tissue cultures of cells and bacteria
Endpoint
physiological manifestation; first sign before the symptoms occur
Use of 'biomarkers' e.g. changes in hormone levels, protein markers, and enzyme induction - these can be indications that
a person is sick
There are also environmental biomarkers
present in soil