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Andrew S. Kane, Ph.D.
Environmental Health Program
College of Public Health & Health Professions
KANE@UFL.EDU
Principles of Toxicology
The Study of Poisons
WATER BIOLOGY
WATER BIOLOGY
PHC 6937; Section 4858
PHC 6937; Section 4858
“The problem with toxicology is not the practicing
toxicologists, but chemists who can detect, precisely,
toxicologically insignificant amounts of chemicals”
Rene Truhaut, University of Paris (1909-1994)
?
Sources of Environmental Chemicals
Air Emissions
Industrial Processes
Incinerators
Gasoline and diesel exhaust
Spraying of agricultural chemicals
Water Discharges
Industrial effluents
Sewage effluent
Non-Point Sources
Surface run-off from roads and agricultural land
Leachate from dump-sites
Accidental spills
Household Chemical Use
• Aquatic animals as environmental sentinels
Toxicology…………
• Is the study of the harmful effects of chemicals and physical
agents on living organisms
• Examines adverse effects ranging from acute to long-term
• Is used to assess the probability of hazards caused by adverse
effects
• Is used to predict effects on individuals, populations and
ecosystems
Descriptive Toxicology: The science of toxicity testing to provide
information for safety evaluation and regulatory requirements.
Mechanistic Toxicology: Identification and understanding cellular,
biochemical & molecular basis by which chemicals exert toxic effects.
Regulatory Toxicology: Determination of risk based on descriptive
and mechanistic studies, and developing safety regulations.
Federal agencies: FDA (FDCA- Federal Food, Drug & Cosmetic Act)
EPA (FIFRA-Federal Insecticide, Fungicide and Rodenticide Act)
EPA (TSCA-Toxic Substance Control Act)
EPA (CERCLA- Comprehensive Env Response, Compensation, &
Liability Act); Superfund
DOL (OSHA-Occupational Safety and Health Administration)
An interdisciplinary field…
Clinical Toxicology: Diagnosis and treatment of poisoning;
evaluation of methods of detection and intoxication, mechanism of
action in humans (human tox, pharmaceutical tox) and animals
(veterinary tox). Integrates toxicology, clinical medicine, clinical
biochemistry/pharmacology.
Occupational Toxicology: Combines occupational medicine and
occupational hygeine.
Environmental Toxicology: Integrates toxicology with sub-
disciplines such as ecology, wildlife and aquatic biology,
environmental chemistry.
An interdisciplinary field…
Approach
Classical Toxicology Mechanistic Toxicology
ADME
Target Organ Effects
Mechanisms of Cell
Injury and Cell Death
In vitro/In vivo Models
Whole Animal Studies
Gene Environment Interactions
Susceptible Populations
Susceptible Populations
Diagram of quantal
dose-response
relationships
Approximate acute LD50s for selected chemical agents
Relative Toxicity
Comparison of dose-response relationship for two
different chemicals plotted on a log dose-probit scale
“All substances are poisons: there is none which is not a
poison. The right dose differentiates a poison and a
remedy.” Paracelsus (1493-1541)
Dose
Effect
Absorption
Distribution to tissues
Metabolism
Excretion
Classical Toxicology
Dose: Amount of chemical an organism is
exposed to per unit of body weight
(mg/kg b.wt)
Exposure: Concentration of a chemical in either
the air or water through which
the exposure occurs
Dose vs Exposure
Concentrations in liquids or solids:
ppt = parts per thousand (g/L; ‰; PSU); easily confused
ppm = parts per million (µg/mL = mg/L or µg/g = mg/kg)
ppb = parts per billion (ng/mL = µg/L or ng/g = µg/kg)
Concentrations in air:
mg vapor/m3 =molecular weight (ppm)/24.45
ppm = ug/m3
Exposure concentrations
Primary Routes of Exposure
Gastrointestinal
Respiratory
Dermal (skin)
There are tremendous differences in the absorption of
compounds depending on the route of exposure due to
physiological differences between these organs.
Great differences between various species.
Metabolism
Metabolites: conversion products of substances,
often mediated by enzyme reactions.
Bioactivation (activation): production of
metabolites that are more toxic than the parent
substance.
Detoxication: production of metabolites that are
less toxic than the parent substance.
Xenobiotics
Xenobiotics
Accumulation
(storage in body fat, bone)
Phase I metabolism
(bioactivation or inactivation)
oxidation, reduction, hydrolysis
Phase II metabolism
(bioinactivation) conjugation
Extracellular mobilization
Biliary excretion
Plasma circulation
Renal excretion
highly lipophilic
metabolically stable
lipophilic polar hydrophilic
polar
hydrophilic
Overview of possible types of phase I biotransformation reactions
Oxidation reactions:
Loss of electrons, often
addition of O to replace H
Reduction reactions:
Gain of electrons, often
addition of H to replace O
Hydrolysis reactions:
Water interacts with
substrate such that O2
makes bond
Phase II Conjugation Reactions
Routes of Elimination
Biliary
Renal
Fecal
Respiratory
Pharmacokinetic Parameters
Volume of distribution: Vd = Total dose/[blood]
The apparent volume of distribution (Vd) is the volume of fluid
which the drug would occupy if it were evenly distributed
through that volume at the concentration measured in the
plasma (central compartment).
Vd is a convenient method for describing how well a drug is
removed from the plasma and distributed to the tissues.
However, it doesn't provide any specific information about
where the drug is or whether it is concentrated in a particular
organ. A large volume of distribution implies wide distribution, or
extensive tissue binding, or both. Conversely, ionized drugs that
are trapped in plasma, will have small volumes of distribution.
Pharmacokinetic Parameters
Half-life:
The half-life (t1/2) is the time taken for the xenobiotic
concentration to decline by 50%. It is related to the
rate constant by the following:
t1/2 = 0.693/ kel
50 % of the xenobiotic is lost in 1.00 half-life
90 % of the xenobiotic is lost in 3.32 half-lives
95 % of the xenobiotic is lost in 4.32 half-lives
99 % of the xenobiotic is lost in 6.64 half-lives
Pharmacokinetic Parameters
Elimination rate constant: kel = 2.303 x slope
The serum level curve observed
from a xenobiotic eliminated by a
first order process.
A plot of this same data using a
log scale on the y-axis results in
a straight line.
Pharmacokinetic Parameters
Octanol Water Partition
Coefficient (Kow)
• Ratio of the concentration
of a chemical in octanol and
in water at equilibrium and
at a specified temperature.
• Predict solubility
• Predict bioaccumulation
Bioaccumulation
• Accumulation of substances, such as pesticides or other organic
chemicals in an organism or part of an organism.
• Biological sequestering through respiration, diet, epidermal (skin) contact.
• Results in the organism having a higher concentration of the substance
than the concentration in the surrounding environment.
• Amount depends on the rate of uptake, the mode of uptake, how quickly
the substance is eliminated, transformation of the substance, the lipid
content of the organism, the Kow of the substance, and environmental
factors, and other biological and physical factors.
• General rule: the more hydrophobic a substance is the more likely it is to
bioaccumulate in organisms. Exceptions (e.g. methylmercury).
• Bioconcentration refers only to the uptake of substances into the organism
from water alone. Bioaccumlation is the more general term because it
includes all means of uptake into the organism.
Relationship between dose and concentration at the target site
under different conditions of dose frequency and elimination rate
Pharmacokinetic Parameters
Haber’s Law
For many compounds…
The toxic effect of a substance is determined by
the product of the concentration and the
duration of the exposure
Dose-response relationship for representative
essential substances, such as vitamins or trace elements (e.g., Cr, Co, Se)
Hormesis
Effective, toxic and lethal dosages
• Acute effects do not predict chronic effects
• Doses causing chronic effects may not cause acute or
sub-acute effects
• In human and veterinary arenas chronic effects of a
chemical exposure may manifest themselves as a
common disease and go unnoticed
• SARs and Kow predictors
Acute vs Chronic Toxicity
Chemical Interactions
Additive: 2+3=5 (2 OPs - cholinesterase inhibition)
Synergistic: 2+2=20 (CCl4 + EtOH)
Potentiation: 0+2=10 (isopropanol + CCl4)
Antagonism: 4+6=8; 4+0=1
•Functional antagonism: 2 chemicals counterbalance each other by
producing opposite effects on the same physiologic function
(eg epinephrine + diazepam).
•Chemical antagonism (inactivation): chemical rxn between 2
compounds that produces a less toxic product (eg chelators and metals).
•Dispositional antagonism: alters A,D,M or E to that conc or duration at
target site is diminished (eg ipacac, charcoal, diuretics, SKF-525A or
piperonyl butoxide).
•Receptor anatagonists (blockers): clinical trtmt by competitive binding
to same receptor (eg atropine and OPs to block cholinesterase receptors;
tamoxifen as an anti-estrogen to lower risk of breast cancer).
Methods for Measuring the Acute Toxicity of
Effluents and Receiving Waters to Freshwater
and Marine Organisms
Methods for Measuring the Acute Toxicity
of Effluents and Receiving Waters to
Freshwater and Marine Organisms
Freshwater:
Ceriodaphnia dubia (daphnid)
Daphnia pulex and D. magna (daphnids)
Pimephales promelas (fathead minnow)
Oncorhyncus mykiss (rainbow trout)
Estuarine & Marine:
Mysidopsis bahia (mysid)
Cyprinodon variegatus (daphnids)
Menidia beryllina, M. menidia & M. peninsulae
(inland, Atlantic & tidewater silversides)
Methods for Measuring the Acute Toxicity
of Effluents and Receiving Waters to
Freshwater and Marine Organisms
Temperature
Light quality
Light intensity
Photoperiod
Test chamber size
Test solution volume
Renewal of test solutions
Density of test organisms
Aeration
Dilution water
Number of replicates
Age of test organisms
Test concentrations
Dilution factor
Test duration
Endpoints

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introtox-020909.pdf

  • 1. Andrew S. Kane, Ph.D. Environmental Health Program College of Public Health & Health Professions KANE@UFL.EDU Principles of Toxicology The Study of Poisons WATER BIOLOGY WATER BIOLOGY PHC 6937; Section 4858 PHC 6937; Section 4858
  • 2. “The problem with toxicology is not the practicing toxicologists, but chemists who can detect, precisely, toxicologically insignificant amounts of chemicals” Rene Truhaut, University of Paris (1909-1994) ?
  • 3.
  • 4. Sources of Environmental Chemicals Air Emissions Industrial Processes Incinerators Gasoline and diesel exhaust Spraying of agricultural chemicals Water Discharges Industrial effluents Sewage effluent Non-Point Sources Surface run-off from roads and agricultural land Leachate from dump-sites Accidental spills Household Chemical Use • Aquatic animals as environmental sentinels
  • 5. Toxicology………… • Is the study of the harmful effects of chemicals and physical agents on living organisms • Examines adverse effects ranging from acute to long-term • Is used to assess the probability of hazards caused by adverse effects • Is used to predict effects on individuals, populations and ecosystems
  • 6. Descriptive Toxicology: The science of toxicity testing to provide information for safety evaluation and regulatory requirements. Mechanistic Toxicology: Identification and understanding cellular, biochemical & molecular basis by which chemicals exert toxic effects. Regulatory Toxicology: Determination of risk based on descriptive and mechanistic studies, and developing safety regulations. Federal agencies: FDA (FDCA- Federal Food, Drug & Cosmetic Act) EPA (FIFRA-Federal Insecticide, Fungicide and Rodenticide Act) EPA (TSCA-Toxic Substance Control Act) EPA (CERCLA- Comprehensive Env Response, Compensation, & Liability Act); Superfund DOL (OSHA-Occupational Safety and Health Administration) An interdisciplinary field…
  • 7. Clinical Toxicology: Diagnosis and treatment of poisoning; evaluation of methods of detection and intoxication, mechanism of action in humans (human tox, pharmaceutical tox) and animals (veterinary tox). Integrates toxicology, clinical medicine, clinical biochemistry/pharmacology. Occupational Toxicology: Combines occupational medicine and occupational hygeine. Environmental Toxicology: Integrates toxicology with sub- disciplines such as ecology, wildlife and aquatic biology, environmental chemistry. An interdisciplinary field…
  • 8. Approach Classical Toxicology Mechanistic Toxicology ADME Target Organ Effects Mechanisms of Cell Injury and Cell Death In vitro/In vivo Models Whole Animal Studies Gene Environment Interactions Susceptible Populations Susceptible Populations
  • 10. Approximate acute LD50s for selected chemical agents Relative Toxicity
  • 11. Comparison of dose-response relationship for two different chemicals plotted on a log dose-probit scale
  • 12. “All substances are poisons: there is none which is not a poison. The right dose differentiates a poison and a remedy.” Paracelsus (1493-1541) Dose Effect
  • 14. Dose: Amount of chemical an organism is exposed to per unit of body weight (mg/kg b.wt) Exposure: Concentration of a chemical in either the air or water through which the exposure occurs Dose vs Exposure
  • 15. Concentrations in liquids or solids: ppt = parts per thousand (g/L; ‰; PSU); easily confused ppm = parts per million (µg/mL = mg/L or µg/g = mg/kg) ppb = parts per billion (ng/mL = µg/L or ng/g = µg/kg) Concentrations in air: mg vapor/m3 =molecular weight (ppm)/24.45 ppm = ug/m3 Exposure concentrations
  • 16. Primary Routes of Exposure Gastrointestinal Respiratory Dermal (skin) There are tremendous differences in the absorption of compounds depending on the route of exposure due to physiological differences between these organs. Great differences between various species.
  • 17. Metabolism Metabolites: conversion products of substances, often mediated by enzyme reactions. Bioactivation (activation): production of metabolites that are more toxic than the parent substance. Detoxication: production of metabolites that are less toxic than the parent substance.
  • 18. Xenobiotics Xenobiotics Accumulation (storage in body fat, bone) Phase I metabolism (bioactivation or inactivation) oxidation, reduction, hydrolysis Phase II metabolism (bioinactivation) conjugation Extracellular mobilization Biliary excretion Plasma circulation Renal excretion highly lipophilic metabolically stable lipophilic polar hydrophilic polar hydrophilic
  • 19.
  • 20. Overview of possible types of phase I biotransformation reactions Oxidation reactions: Loss of electrons, often addition of O to replace H Reduction reactions: Gain of electrons, often addition of H to replace O Hydrolysis reactions: Water interacts with substrate such that O2 makes bond
  • 21. Phase II Conjugation Reactions
  • 23. Pharmacokinetic Parameters Volume of distribution: Vd = Total dose/[blood] The apparent volume of distribution (Vd) is the volume of fluid which the drug would occupy if it were evenly distributed through that volume at the concentration measured in the plasma (central compartment). Vd is a convenient method for describing how well a drug is removed from the plasma and distributed to the tissues. However, it doesn't provide any specific information about where the drug is or whether it is concentrated in a particular organ. A large volume of distribution implies wide distribution, or extensive tissue binding, or both. Conversely, ionized drugs that are trapped in plasma, will have small volumes of distribution.
  • 24. Pharmacokinetic Parameters Half-life: The half-life (t1/2) is the time taken for the xenobiotic concentration to decline by 50%. It is related to the rate constant by the following: t1/2 = 0.693/ kel 50 % of the xenobiotic is lost in 1.00 half-life 90 % of the xenobiotic is lost in 3.32 half-lives 95 % of the xenobiotic is lost in 4.32 half-lives 99 % of the xenobiotic is lost in 6.64 half-lives
  • 25. Pharmacokinetic Parameters Elimination rate constant: kel = 2.303 x slope The serum level curve observed from a xenobiotic eliminated by a first order process. A plot of this same data using a log scale on the y-axis results in a straight line.
  • 26. Pharmacokinetic Parameters Octanol Water Partition Coefficient (Kow) • Ratio of the concentration of a chemical in octanol and in water at equilibrium and at a specified temperature. • Predict solubility • Predict bioaccumulation
  • 27. Bioaccumulation • Accumulation of substances, such as pesticides or other organic chemicals in an organism or part of an organism. • Biological sequestering through respiration, diet, epidermal (skin) contact. • Results in the organism having a higher concentration of the substance than the concentration in the surrounding environment. • Amount depends on the rate of uptake, the mode of uptake, how quickly the substance is eliminated, transformation of the substance, the lipid content of the organism, the Kow of the substance, and environmental factors, and other biological and physical factors. • General rule: the more hydrophobic a substance is the more likely it is to bioaccumulate in organisms. Exceptions (e.g. methylmercury). • Bioconcentration refers only to the uptake of substances into the organism from water alone. Bioaccumlation is the more general term because it includes all means of uptake into the organism.
  • 28. Relationship between dose and concentration at the target site under different conditions of dose frequency and elimination rate Pharmacokinetic Parameters
  • 29. Haber’s Law For many compounds… The toxic effect of a substance is determined by the product of the concentration and the duration of the exposure
  • 30. Dose-response relationship for representative essential substances, such as vitamins or trace elements (e.g., Cr, Co, Se) Hormesis
  • 31. Effective, toxic and lethal dosages
  • 32. • Acute effects do not predict chronic effects • Doses causing chronic effects may not cause acute or sub-acute effects • In human and veterinary arenas chronic effects of a chemical exposure may manifest themselves as a common disease and go unnoticed • SARs and Kow predictors Acute vs Chronic Toxicity
  • 33. Chemical Interactions Additive: 2+3=5 (2 OPs - cholinesterase inhibition) Synergistic: 2+2=20 (CCl4 + EtOH) Potentiation: 0+2=10 (isopropanol + CCl4) Antagonism: 4+6=8; 4+0=1 •Functional antagonism: 2 chemicals counterbalance each other by producing opposite effects on the same physiologic function (eg epinephrine + diazepam). •Chemical antagonism (inactivation): chemical rxn between 2 compounds that produces a less toxic product (eg chelators and metals). •Dispositional antagonism: alters A,D,M or E to that conc or duration at target site is diminished (eg ipacac, charcoal, diuretics, SKF-525A or piperonyl butoxide). •Receptor anatagonists (blockers): clinical trtmt by competitive binding to same receptor (eg atropine and OPs to block cholinesterase receptors; tamoxifen as an anti-estrogen to lower risk of breast cancer).
  • 34. Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms
  • 35. Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms Freshwater: Ceriodaphnia dubia (daphnid) Daphnia pulex and D. magna (daphnids) Pimephales promelas (fathead minnow) Oncorhyncus mykiss (rainbow trout) Estuarine & Marine: Mysidopsis bahia (mysid) Cyprinodon variegatus (daphnids) Menidia beryllina, M. menidia & M. peninsulae (inland, Atlantic & tidewater silversides)
  • 36. Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms Temperature Light quality Light intensity Photoperiod Test chamber size Test solution volume Renewal of test solutions Density of test organisms Aeration Dilution water Number of replicates Age of test organisms Test concentrations Dilution factor Test duration Endpoints