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Dioxins And Pcbs

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    Dioxins And Pcbs



    Dioxins And Pcbs - Transcript



    Dioxins and PCBs

    Acute (?? ) and chronic (?? ) toxicity
    • Acute toxicity refers to a rapid and serious response
    to a high but short-lived dose.
    – Acute poisons interfere with essential physiological
    processes, leading to a variety symptoms of distress, even
    death.
    • Chronic toxicity refers to a time-lagged response to a
    relatively low but prolonged exposure.
    – Effects are more subtle.
    – Set in motion a chain of biochemical events that lead to
    disease states, including cancer.

    Index of acute toxicity:LD50
    LD50 is the lethal dose for 50% of a population.
    Dose is expressed as the weight of a chemical consumed by an
    experimental animal per kg of body weight of the animal.

    LD50 of selected chemicals for rats or mice
    Chemical LD50 (mg/kg) Chemical LD50 (mg/kg)
    Sugar 29,700 Caffeine 130
    ethanol 14,000 DDT 100
    Vinegar 3,310 Arsenic 48
    Table salt 3,000 Parathion 3.6
    Atrazine 1,870 Nicotine 1
    Malathion 1,200 Dioxin (TCDD) 0.001
    Aspirin 1,000 Botulin toxin 0.00001
    Almost every chemical is toxic at some level, and the difference
    between toxic and nontoxic chemicals is a matter of degree.

    Dioxins (??? ): General structures
    • The term dioxins denotes a family of chemical
    compounds, known as polycholorinated dibenzo-
    para-dioxins (PCDDs) and polycholrinated
    dibenzofurans (PCDFs)
    O
    O
    Dibenzodioxin
    PCDD
    O
    Dibenzofuran
    PCDF
    Clx Cly
    Clx
    Cly
    General structure

    Dioxins: Congeners
    Congener: a member of the same class, or group.
    Each individual PCDD or PCDF is termed a congener.
    There are 75 PCDD congeners and 135 PCDF congeners.
    O
    O
    Dibenzodioxin
    PCDD
    O
    Dibenzofuran
    PCDF
    1
    2
    3
    4
    7
    8
    9
    6
    9
    8
    7
    6
    1
    2
    3
    4
    O
    O
    2378-TCDD
    O
    2378-TCDF
    Cl
    ClCl
    Cl Cl
    Cl
    Cl
    Cl

    Toxicity of Dioxins
    • Extraordinary toxic to lab animals (LD50 in male guinea
    pigs is only 0.6 µg/kg)
    – Birth defects
    – Cancer
    – Skin disorders
    – Liver damage
    – Suppression of the immune systems
    • Variation in toxicity among species is large.
    – Male guinea pig, oral, LD50 is 0.6 µg/kg.
    – Hamster, intraperitoneum, LD50 is 3000 µg/kg.
    • Risk to humans is less clear

    Human risk of dioxin exposure
    • USEPA concludes that dioxins likely increase cancer
    incidence.
    • WHO classifies 2378-TCDD as a probable human
    carcinogen.
    • At high levels, PCDDs cause chloracne (??? ), a
    painful skin inflammation.
    • Risk from breathing dioxin-laden air is minimal.
    • The main exposure route for human is dietary (meat,
    dairy products, and fish). (Due to bioaccumulation of
    dioxins)
    • Absorption of dioxins by infant through mothers’ milk
    is efficient.

    Multiple exposure pathways

    Biochemistry of dioxin toxicity
    • PCDD/Fs are planar aromatic molecules.
    • The planar structure allows them to bind to Ah (Aryl
    hydrocarbon) receptor protein that is present in all
    animal species.
    • The Ah receptor interacts with the cell’s DNA.
    • Dioxin toxicity is roughly proportional to the strength of
    binding to the Ah receptor.
    • This explains that 2378-TCDD is the most toxic one.

    Dioxin toxicity varies among the congeners
    Congener PCDD series PCDF series
    2378 1 (defined) 0.1
    12378 0.5 0.05
    23478 0.5
    123478,
    123678,
    123789
    0.1 0.1
    (also include 234678 congener)
    1234678 0.01 0.01 (also include 1234789 congener)
    octachloro 0.001 0.001
    International Toxicity Equivalency Factors (TEF) for
    PCDDs and PCDFs
    The TEFs allow the conversion of various congener concentrations into
    a single toxicity equivalent quantity (TEQ)

    Dioxin toxicity: general rules
    • TCDD is the most toxic of the dioxins
    • Toxicity decreases when Cl atoms are removed
    from 2,3,7,8 positions or added to the
    remaining positions on the rings.
    • There are similar toxicity pattern for PCDD and
    PCDF series.

    How much dioxin do we congest?
    Estimated Dietary Intakes of PCDD/Fs per day
    Country Dietary Intake (pg I-TEQ/day)
    Canada 92
    Germany 62-100
    Italy 260-480
    Japan 63
    Netherlands 70
    Norway 51-85
    Russia 139
    UK 70
    US 18-192
    Hong Kong 105
    Source: An Assessment of Dioxin Emissions in Hong Kong, HKEPD, 2000.

    Average content of 2378-TCDD in various
    foodstuff (U.S)
    Food TCDD (pg/g)
    Ocean fish 500
    Meat 35
    Cheese 16
    Sour cream 10
    Cream 7.2
    Ice cream 5.5
    Cottage cheese 2.1
    Milk 1.8
    Coffee 0.1
    Orange juice 0.2

    Formation of dioxins
    • Combustion
    – In any situation where Cl, C, H, and O come into contact with
    heat, PCDD/Fs could be formed as trace by-products.
    – Dioxin emission correlates with the Cl content of the
    combustion feed.
    • Paper pulp bleaching with chlorine
    – Chlorine is used to bleach paper pulp.
    – PCDDs are formed probably through chlorination of the
    phenolic groups in lignin.
    • Manufacture of certain chlorophenol chemicals
    – Dioxin was produced as a contaminant of the herbicide 2,4,5-
    T, a component of Agent Orange

    Formation of dioxins in combustion processes
    • Incomplete combustion of organic wastes in the combustion
    chamber leads to the formation of organic fragments which
    serve as organic precursors to the PCDD/F molecule.
    • The waste provides a source of chlorine, and of metals. The
    latter are incorporated into fly ash, which carries over to the
    cooler (250-400oC) post-combustion zone of the incineration
    system.
    • The organic precursors adsorb onto the surface of the fly ash
    in the post-combustion zone, and following a complex
    sequence of reactions which are catalyzed by metals
    (primarily copper) in the fly ash, lead to the formation of
    PCDD/Fs along with other chlorinated trace organics.
    PCDF contamination from PCB oxidation
    High-
    temperature
    step

    Dioxin emission inventory (US)

    Agent orange
    • 50:50 mix of two herbicides: 2,4-D and 2,4,5-T.
    • Used as a defoliant for broad-leaf trees during Vietnam
    war.
    • Contains dioxins as contaminants.
    • In 1966, dioxin residues were found in fish, shell-fish,
    and mother’s milk in the Vietnam target areas.
    • In 1978 and 1979, Vietnam veterans in the U.S. began
    complaining of a variety of symptoms such as
    numbness, skin rashes, liver problems, and birth defects
    in their children.

    Estimated Dioxin emission inventory
    (1997 in HK)
    Sources Emission (g I-TEQ)
    MSW combustion 21-27
    Coal combustion 0.4-20
    Clinical waste
    combustion
    0.4-1.8
    Land fill gas combustion 0.2-0.3
    Non-ferrous metals 0.1-1.0
    Cement manufacture 0.32
    Crematoria 0.024
    Cars 0.005-0.51
    Goods vehicles 0.061-0.11
    Buses 0.016-0.023
    Motorcycles 0.0001-0.006
    Source: An Assessment of
    Dioxin Emissions in Hong
    Kong, HKEPD, 2000.

    Dioxin: Are there natural sources?
    • Analysis of archived UK soil samples dating from the
    pre-1900s confirmed the presence of dioxins. (Large
    scale manufacture and use of chlorinated chemicals started
    after 1900s.)
    • Wood burning emits dioxin
    – NaCl in wood ? HCl in combustion zone
    • Organochlorines are widely produced by a variety of
    microorganisms.

    Man-made sources outweigh natural sources
    Dioxin deposition on Lake Siskiwit
    on an island in Lake Superior
    From 1940 to 1970
    •deposition increased
    eightfold.
    •Great expansion in the use
    of Cl
    •Forest fires diminished by
    more than a factor of four
    After 1970
    •Deposition decreased
    •2,4,5-T phaseout

    Polychlorinated biphenyl (PCB)
    a total of 209 congeners
    Polychlorinated biphenyl
    PCB
    Clx Cly
    Excellent insulators, chemically stable,
    low flammability and vapor pressure.
    Used as coolant in power transformers
    and capacitors.
    Additional uses:
    •Heat transfer fluids in machinery
    •Plasticizers for PVC and other polymers
    •De-inking agents for recycled newspapers

    Toxicity of PCBs
    Test scores of 4-year-old children
    vs. PCB concentrations in the
    umbilical cord serum at birth.
    Effects of in utero PCB exposure
    •Less toxic than PCDD/Fs, but
    more abundant than PCDD/Fs
    in the environment.
    •Probable carcinogen
    •Cause skin chloracne.
    •Learning deficits.

    EPA orders General Electric to dredge PCBs from Hudson
    River (Source: Pollution Online newsletter, 12/4/2001)
    WASHINGTON, Dec 04, 2001 (AP WorldStream via COMTEX) –
    The Bush administration ordered tons of PCBs removed from New York's
    upper Hudson River, setting in motion one of the largest dredging operations in
    the nation's history. General Electric Co. dumped 1.3 million pounds (585,000
    kilograms) of PCBs into the river before the federal government banned the
    pollutants in 1977. The company bitterly opposes dredging, which expected to
    cost GE dlrs 500 million.
    ….
    PCBs, used as insulation and a coolant, have been linked to cancer in
    laboratory animals. The EPA classifies the oily substance as a probable
    carcinogen and says PCBs pose risks to wildlife and to people who eat fish
    from the Hudson. GE released PCBs from its plants in Fort Edward and
    Hudson Falls, about 40 miles (64 kilometers) north of Albany. The cleanup
    will include locations in that stretch, reaching almost down to the capital city.
    …..

    Study questions
    1. What is acute toxicity? What is the index to express
    acute toxicity?
    2. What is chronic toxicity? Give an example of
    chronic health effect.
    3. Draw chemical structures of dioxins and PCBs.
    What are congeners?
    4. Does dioxins bioaccumulate? Why?
    5. What are the major sources for dioxins?