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chemicals detected in south African children
Project
Monitors environmental chemical exposure in remote communities in South Africa
Silicone wristbands
Worn by 5–6-year-old children
Worn for 72 hours
Wristbands collect environmental chemical exposures
Chemicals detected
Many chemicals identified, including known toxicants:
Plasticizers
DDT (insecticide)
Organophosphate esters (flame retardants)
PAHs (polycyclic aromatic hydrocarbons)
Source of PAHs
Mainly from family cooking over open fires
movement of chemicals in environment - exposome
Exposome
Measures all chemical exposures an individual experiences
Analyzes the overall impact of environmental chemicals on the body
Previous approach
Analyzed each chemical separately
Current approach
Can analyze many chemicals simultaneously
Uses samples such as a drop of blood
Chemical analysis
Depends on the physical and chemical properties of chemicals
Uses these properties to predict where a chemical will be found in the body/environment
ecozones in canada
Cyclical movement of toxins
Toxins can move through the environment and food chains
Exposure can occur independently of human control
Agricultural and urban-based regions
Issues include:
Drinking water quality
Urban congestion
Air pollution
Wildlife loss
Coastal regions
Problems include:
Declining fish stocks
Land-based pollution
Forestry impacts
Arctic regions
Reduced contamination of traditional foods
Environmental concerns linked to climate change impacts
environmental chemodynamics
Chemical movement in the environment
Chemicals move between different environmental compartments
Their physical and chemical properties determine their behavior and movement
Chemical partitioning
Properties of a chemical allow prediction of how it will distribute between:
Air
Water
Soil
Biological systems (living organisms)
what constitutes an environmental toxicant
persistence
bioaccumulation and biomagnification
toxicity
persistence
Half-life (T1/2) of toxic chemicals
Huge differences exist between half-lives of toxic chemicals
Atrazine: ~25 months
DDT: ~10 years
Chemical removal
Takes approximately 4 half-lives for a compound to be removed from the environment
Sources of these chemicals
Often used as:
Insecticides
Herbicides
Pesticides
Can also result from tobacco products
Sustained exposure
If the exposure rate is sustained, the half-life becomes irrelevant
Toxicants are continuously entering the system
bio accumulation and magnification
Bioaccumulation
Accumulation of contaminants from food and the environment
Positively correlated with lipophilicity
PCB example
Large cleanup attempts have occurred
Still found in the Great Lakes
Difficult to remove
Biomagnification
Due to food digestion and absorption
Contaminants can become concentrated in the GI tract
Levels increase in organisms as you move up trophic levels
Humans are at the top of the food chain, making us susceptible
DDE example
DDE is a metabolite of DDT
Low levels found in water
As it moves up the food chain, concentrations increase
Birds at higher trophic levels have much higher amounts of DDE
toxicity
Persistence, bioaccumulation, and biomagnification
Do not matter if the substance is not toxic
Ways of testing toxicity
Structure–activity relationships
In vitro tests
Short-term tests
Animal bioassays → being phased out
Epidemiological data
Long-term
Hard to rely on
Stockholm convention of persistent organic pollutants
Chemicals in the environment
Can come from many different sources
Many countries, including Canada, participate in international agreements
Stockholm Convention
Established in 2004
Focuses on persistent organic pollutants (POPs)
Considers:
Toxicity
Persistence
Bioaccumulation
Biomagnification
Goal
Eliminate or significantly reduce the release of POPs into the environment
Examples of POPs
Pesticides
Industrial chemicals
PCBs
DDEs
POPs in polar bears Canadian arctic
Chemical accumulation in polar bears
Many chemicals are found in bear adipose tissue
PCBs and DDE
Among the first chemicals identified
Included in the 12 POPs under the convention
Polar bears
Still contain high levels of PCBs and DDEs
PCBs in mothers and babies in Nunavik
PCBs and neurodevelopment
PCBs may be related to anxiety symptoms in Inuit preschoolers
PCBs have effects on child neurodevelopment
Effects of PCBs
Effects can differ depending on the endpoint being measured
applications of the Stockholm convention
Stockholm Convention
12 initial chemicals were outlined
Approaches for controlling chemicals
Annex A: Elimination
Complete ban of chemicals
Annex B: Restriction
Used when a chemical is considered absolutely essential
Example:
DDT was not globally eliminated
Restricted because it prevents malaria in Africa
Canada eliminated DDT because:
No malaria risk
Alternative options are available
Annex C: Unintentional production
Attempts to prevent unintentional production of chemicals
Updates to the convention
16 additional chemicals added in 2009
Some were:
Eliminated
Restricted
Difficult to find substitutes for
Meetings occur every year
Now approximately 30 chemicals are listed
Canada ratified the list of 21 chemicals
tetrabromodiphenyl ether and PFOA and PFOS
Tetrabromodiphenyl ether
Used as a flame retardant
Not approved for use in Canada
Gradually being replaced with alternative chemicals
Some alternatives may also have negative effects
PFAS chemicals
Examples:
PFOA
PFOS
Efforts are being made to replace them
Alternatives include short-chain compounds
Short-chain alternatives are also showing potential toxicity
Regulation
Environment and health ministers stated they would:
Assess and regulate the entire chemical family
Not only individual compounds
PFOS and PFOA
PFAS
Includes industrial surfactants and dispersants
Used in:
Non-stick pans
Waterproofing
Firefighting foam
Exposure
Firefighters have the highest exposure
Exposure routes:
Oral intake (fish, drinking water)
Inhalation
Persistence
Human half-life: ~2.7 years
Quite persistent
Longer-chain PFAS → longer half-life
Groundwater persistence: 5–15 years
Sources
Produced as industrial by-products
Found in:
Airports
Military sites
Canada
PFAS in the Arctic
PFOA and PFOS found in surface water
Chemicals are dispersed throughout the Arctic
Chemicals produced in urban areas travel north through:
Wind
Water currents
Represents a global issue
High levels of PFOS and PBDEs found in polar bears
PFOA toxicity
Tetrabromo ether
Used as a flame retardant
Not approved for use in Canada
Gradually being replaced with alternative chemicals
Some alternatives may also have negative effects
PFAS chemicals
Examples:
PFOA
PFOS
Efforts are being made to replace them
Alternatives include short-chain compounds
Short-chain alternatives are also showing potential toxicity
Regulation
Environment and health ministers stated they would:
Assess and regulate the entire chemical family
Not only individual compounds
sses indsutrial surfacnats and diosperants like nonstick pan waterrooignf fir efighting foam firefighters have highest exposure expsore oral fish drinkinf water inhaltion half life humans 2.7 years quite persisnt llonger chain longer half life groundwater 5-15 years produced as indsutrial byprodcyst pfas in canada airports militaru pfoa and pfos in surface water artic chemicals are dispered all over arctoc chems produced in urban travel north from wind and water currents global issue only in surface water not in animals where theres bio and biomagnification high levels of pfos and pbdes in north polar bears
PFAS
Includes industrial surfactants and dispersants
Used in:
Non-stick pans
Waterproofing
Firefighting foam
Exposure
Firefighters have the highest exposure
Exposure routes:
Oral intake (fish, drinking water)
Inhalation
Persistence
Human half-life: ~2.7 years
Quite persistent
Longer-chain PFAS → longer half-life
Groundwater persistence: 5–15 years
Sources
Produced as industrial by-products
Found in:
Airports
Military sites
Canada
PFAS in the Arctic
PFOA and PFOS found in surface water
Chemicals are dispersed throughout the Arctic
Chemicals produced in urban areas travel north through:
Wind
Water currents
Represents a global issue
Bioaccumulation and biomagnification
PFAS detected in surface water
Not only in water — also found in animals where bioaccumulation and biomagnification occur
High levels of PFOS and PBDEs found in polar bears
animal studies: reproducitve, developmental, liver, kidney, immunological, canver, ( epidemological: incrwased cholesterol low infant birth weight immunolical canver thyroid hormone and endo crine disurutopn
Animal studies
Effects studied include:
Reproductive effects
Developmental effects
Liver effects
Kidney effects
Immunological effects
Cancer effects
Epidemiological studies
Associated with:
Increased cholesterol
Low infant birth weight
Immunological effects
Cancer
Thyroid hormone changes
Endocrine disruption
DuPont case
PFAS lawsuits
Personal injury lawsuits filed against DuPont
Related to contamination of drinking water in Ohio and Virginia
Involved exposure to PFAS chemicals
Settlement
Agreement reached after decades of exposure
Approximately $4 billion used to settle lawsuits involving PFAS use
“Forever chemicals”
PFAS are called forever chemicals
Difficult to remove from the environment
Regulation
Some PFOS and PFOA regulations are state-specific in the USA
occupational toxicology
Occupational toxicology
Application of toxicology principles and methods
Focuses on biological and chemical hazards in the workplace
Objective
Prevent adverse health effects in workers
Workers at risk
Miners
Farmers
Chemical plant workers
Firefighters
challenges in occupational toxicology
Workplace regulation challenges
Difficult to determine the middle ground between:
Industry regulations
Worker safety
Regulations
Must be put in place to protect workers
However, strict regulations can be:
Hard to enforce
Expensive
May drive away investors
May cause job losses
Linking illness to workplace exposure
Difficult to establish a clear link between illness and job exposure
Example:
Miner
Family history of cardiovascular disease
Difficult to determine if disease came from the workplace or other factors
continued
Latent interval
Time between exposure and disease expression
If exposure occurred 20 years ago, it is difficult to prove the disease is related to that exposure
Asbestos example
Easier to link exposure to disease because:
Physical asbestos fibres can be found in people’s lungs
Multifactorial nature of occupational diseases
Many diseases have multiple contributing factors
Occupational exposure may not be the only cause
exposure to disease prevention
Occupational exposure assessment
Determine what people are being exposed to
Consider:
Duration
Concentration
Frequency
Occupational standards
Can help decrease exposure
Protection methods
Use protective equipment
Surveillance
Can identify adverse health effects
Monitor workers to help protect them
Can perform biomonitoring with worker cooperation
biomonitoring of occupational exposure to BPA BPS and BPF