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Dioxin

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    6/97211127 NEWS ZERO

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    2001

    3

    10-80CommitteeCau

    810-80CommitteeDr.Hung

    20023

    5

    1

    Quang Tri

    Ha Tinh

    9

    2

    2003

    7

    3

    8

    10-80Committee

    Dr.Xuan

    2004

    8

    4

    8

    1

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    2005

    8

    5

    2006

    1

    1

    8

    6

    8

    26

    11

    2

    2007

    8

    2

    7

    9

    27

    11

    Committee33

    2008

    3

    10-80Committee

    Dr.Hung

    8

    28

    9

    8

    Binh Dinh

    Ha Nam

    2009

    2

    10-80Division

    Dr.Hung

    5

    Dr.Son

    8

    9

    8

    29

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    2010

    2

    210-80DivisionDr.Hung

    810

    930

    11

    51

    11

    3

    2011

    1

    /

    5

    8

    11

    8

    31

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    ()

    Cam Chinh Commune, Cam Lo District,Quang Tri Province

    ()

    Cam Phuc Commune, Cam Xuyen District,Ha Tinh Province

    194592

    (210)33(88%)

    7,877(90%=60)

    80%

    VND() 1=VND250

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    /

    8524 /7.2

    (1965-71)

    168-550 kg

    /4311/4300( 60%)

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    0.0

    2.0

    4.0

    6.0

    8.0

    10.0

    12.0

    14.0

    PCDDs PCDFs PCDD/F

    (pg/g

    fat)

    n=9)

    n=9)

    P

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    0

    2000

    4000

    6000

    8000

    10000

    0.0 5.0 10.0 15.0 20.0 25.0 30.0 35.0 40.0 45.0(pgTEQ/g lipid)

    (IU//37

    )

    N=43

    R=-0.340

    P=0.026

    N=41

    R=-0.453

    P=0.003

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    0

    10

    20

    30

    40

    50

    60

    0 5 10 15 20 25 30 35 40 45(pgTEQ/g lipid)

    (cm)

    N=43

    R= -0.373

    P=0.012

    N=41

    R= -0.268

    P=0.082

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    This questionnaire was developed by Kusama et al. (2005)

    as a tool to estimate the habitual nutrient intake of the

    Vietnamese population

    About FFQ for Vietnamese

    Full-size photographs

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    Standardizedcoefficients

    P-value Adjusted R2

    TEQ-PCDDs0.367

    Area a 0.610 ***

    TEQ-PCDFs

    0.472

    Area a 0.686 ***

    Fluorine 0.257 **

    Non-animal lipid 0.223 **

    Zinc -0.138 0.068

    TEQ-Total

    0.469

    Area a 0.683 ***

    Fluorine 0.236 **

    Non-animal lipid 0.203 **

    BMI 0.177 *

    Zinc -0.146 0.054

    Area had the highest association with dioxin

    *p

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    Standardizedcoefficients P-value Adjusted R

    2

    TEQ-PCDDs

    0.065Fluorine 0.267 *

    Fiber -0.212 0.080Total FA 0.168 0.147

    TEQ-PCDFs

    0.119

    Fluorine 0.389 **

    Zinc -0.300 *

    Non-animal lipid 0.247 *

    BMI 0.203 0.078TEQ-Total

    0.120

    Fluorine 0.442 **

    Zinc -0.335 *

    BMI 0.221 0.056

    Non-animal lipid 0.221 *

    Total FA 0.199 0.080

    The adjusted R2values of regression were small

    *p

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    Standardizedcoefficients P-value Adjusted R

    2

    TEQ-PCDDs

    0.221

    BMI 0.428 *

    Ash 0.346 *

    Non-animallipid 0.258 0.122

    Copper -0.254 0.080

    TEQ-PCDFs

    0.399

    Linoleic -0.726 ***

    Selenium -0.518 **

    Energy 0.443 **

    Protein -0.435 **Animal lipid -0.404 **

    BMI 0.291 *

    TEQ-Total

    0.212

    Linoleic -0.495 **

    Energy 0.466 *

    BMI 0.379 *

    Selenium -0.300 0.061

    The adjusted R2values of regression were higher than in the sprayed areaAll models had an association between BMI and dioxins

    *p

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    0

    0.5

    1

    1.5

    0.86 0.68 0.48 0.31 0.17

    1.06 0.84 0.58 0.38 0.21

    100 25 10 5 2.5

    *** p

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    SCE

    []Atlas of Genetics and Cytogenetics in Oncology and Haematology http://atlasgeneticsoncology.org/Educ/Hempat_e.html

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    0.0

    100.0

    200.0

    T DD

    PolyCDD

    [ pg/g lipid ]

    T DD

    388

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    0.0

    0.5

    1.0

    1.5

    2.0

    2.5

    3.0

    3.5

    4.0

    TCDD

    SCE value

    [value/cell]

    T DD

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    SCE

    0.0

    0.1

    0.2

    0.3

    0.4

    0.5

    0.6

    0.0 0.5 1.0 1.5 2.0 2.5 3.0

    L

    o

    g

    S

    E

    Log PolyCDDs

    TCDD TCDD

    [ pg/g lipid ]

    [ value/cell ]

    y= 0.17x+0.03

    r=0.62

    Workshop on Agent Orange / Dioxin

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    Workshop on Agent Orange / Dioxin& Health in Vietnam

    [ Kanazawa, Japan ]2006.11.25 (Sat.) 9:30 16:45

    Place: Division of Health Sciences, Kanazawa University

    Room No. 4111Kanazawa University 10-80 Division

    Corresponding to:

    Teruhiko Kido

    Division of Health Sciences, KANAZAWAUNIVERSITY

    5-11-80 Kodatsuno, Kanazawa 920-0942Tel: 076-265-2565

    Sampling PointE PS-1

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    p g

    ( )

    Sampling PointL PS-3

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    3

    m

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    The spraying paths of

    Agent Orange

    The overlaid image of Landsat TM

    mosaiced imageries and spraying paths of

    all types of agents throughout Vietnam

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    Overlaying HBT on Satellite Images(1)

    These two images show the same areas

    Landsat MSS image taken on Oct. 22, 1972

    TNDVI Image(Transformed Normalized

    Difference

    Vegetation Index )

    Darker area Dense vegetation

    Whiter area Bare area

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    Overlaying HBT on Satellite Images(3)

    1989-01-24 1990-01-27

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    Overlaying HBT on Satellite Images(4)

    1993-02-04 Today

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    Kim Bang

    district,

    Ha Nam province

    Phu Cat

    district,

    Binh Dinh

    province

    Metabolic pathway of steroids

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    OH

    O

    O

    O

    O H

    OH

    C O

    C H 3

    H O

    O H

    OH

    O

    O H

    OH

    C O

    C H 3

    O

    C O

    C H 3

    O

    O HC O

    C H3

    O

    O HC O

    C H2

    O H

    O

    O O H

    C O

    C H2

    O H

    C H

    O

    OH O HC O

    3

    Dehydroepiandrosterone Testosterone

    Estradiol

    Androstenedione

    Cortisol

    Cortisone

    Pregnenolone Progesterone

    11-Deoxycortisol17-Hydroxypregnenolone 17-Hydroxyprogesterone

    Cholesterol

    O

    OH O HC O

    C H2

    O H

    Principle LC-MS/MS

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    Principle LC MS/MS

    LC

    Tandem MS

    Separeted steroid

    By LC

    Removal of the

    LC solvent

    1st MS

    Selection of molecular

    weight

    Collison

    cell

    2ndMS

    Determination of product ion

    Specifity

    Ionization on the LC-MS/MS

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    OC

    H2

    F

    F

    FF

    F

    O

    N+CH

    3

    Q1MS Q3MS

    E2-PFBZPY

    Precursor ion Fragmentation

    (Q2MS)

    Product ion

    450 500 550 600 650

    m/z

    2.5e6

    5.0e6

    7.5e6

    Intensity(cps)

    544.3

    100 200 300 400m/z

    3.0e6

    6.0e6

    9.0e6

    1.2e7

    1.5e7

    Intensity

    (cps)

    110.0

    435.3339.3

    181.1

    313.2

    m/z339

    m/z181

    m/z110

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    F, E

    T, DHT, DHEA, 4A, P4, E2

    T, DHT, DHEA, 4A, P4 E2

    - 1 - 2

    - 3

    LC-MS/MS

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    y = -15.545x

    2

    + 424.26x + 268.44

    R = 0.1119

    0

    1000

    2000

    3000

    4000

    5000

    6000

    7000

    0.00 5.00 10.00 15.00 20.00 25.00

    C

    s

    [

    p

    m

    l

    TEQ-TOTAL [pg-TEQ/mg lipid]

    Sprayed area N=16) Non-sprayed area N=9)

    CortisolTEQ TOTAL

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    y = -78.48x

    2

    + 2217.6x + 635.27

    R = 0.1839

    0

    5000

    10000

    15000

    20000

    25000

    30000

    0.00 5.00 10.00 15.00 20.00 25.00

    C

    s

    n

    [

    p

    m

    l

    TEQ-TOTAL [pg-TEQ/mg lipid]

    Sprayed area N=16) Non-sprayed area N=9)

    CortisoneTEQ TOTAL

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    y = 0.001x

    2

    - 0.031x + 0.3506

    R = 0.3851

    0.00

    0.05

    0.10

    0.15

    0.20

    0.25

    0.30

    0.35

    0.00 5.00 10.00 15.00 20.00 25.00

    E

    a

    o

    [

    p

    m

    l

    TEQ-TOTAL [pg-TEQ/mg lipid]

    Sprayed area N=16) Non-sprayed area N=6)

    EstradiolTEQ TOTAL

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    Salivary hormone levels in 3 years children at Phu Cat and Kim Bamg area

    Exp:2011, 8,10)

    Data:2011,10,10

    Data check::2011.12.10

    Phu Cat 52 3.87

    2.85 0.61

    0.52 51.12

    52.18

    hot spot)

    NS NS

    Kim Bang 59 3.34

    1.92 0.62

    0.76 91.96

    67.16

    Non-hot spot)

    0.002

    pg/mL

    Salivary hormone levels

    Area N

    ng/mL ng/mL

    Cortisone Cortisol DHEA

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    Research Location

    Major Hot

    spots

    Da Nang Airbase

    Phu Cat Airbase

    Bien Hoa Airbase

    ..

    Table 1 Geometrical means of concentrations of PCDD/PCDF congeners

    a d TEQs i b east milk f m the s f m six lati s i Viet am

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    Primiparae Multiparae

    TK PC ST CL CX KB TK PC ST CL CX KB

    (n = 43) (n = 23) (n = 26) (n = 27) (n = 38) (n = 19) (n = 104) (n = 36) (n = 54) (n = 69) (n = 37) (n = 44)

    PCDD congeners (pg/g lipid)

    2,3,7,8-TetraCDD 1.97 1.66 1.39 1.05 0.63 0.50 1.47 1.09 0.98 0.75 0.47 0.311,2,3,7,8-PentaCDD 4.68 5.17 4.91 3.20 1.42 1.65 4.03 3.44 3.44 2.03 0.93 1.03

    1,2,3,4,7,8-HexaCDD 2.21 2.35 2.22 1.78 0.51 0.69 2.34 1.67 2.04 1.38 0.35 0.58

    1,2,3,6,7,8-HexaCDD 8.56 8.69 8.70 8.11 1.40 1.55 8.34 5.46 6.56 5.63 0.89 1.22

    1,2,3,7,8,9-HexaCDD 2.70 3.18 2.67 2.18 0.47 0.71 2.67 2.21 2.21 1.54 0.30 0.51

    1,2,3,4,6,7,8-HeptaCDD 11.26 14.94 10.46 15.75 1.51 2.80 13.22 11.32 10.53 12.85 1.13 2.23

    OctaCDD 61.17 71.37 69.50 49.14 6.05 14.44 70.60 60.73 62.97 43.91 4.77 10.09

    PCDF congeners (pg/g lipid)

    2,3,7,8-TetraCDF 0.55 0.58 0.27 0.65 1.01 0.64 0.60 0.61 0.39 0.46 1.09 0.60

    1,2,3,7,8-PentaCDF 1.33 1.88 0.98 0.84 0.52 0.38 1.27 1.77 1.00 0.63 0.41 0.45

    2,3,4,7,8-PentaCDF 8.04 7.38 8.05 6.04 3.30 3.71 6.92 5.04 6.06 3.96 2.27 2.62

    1,2,3,4,7,8-HexaCDF 18.31 16.65 18.88 17.07 2.05 2.30 17.92 11.88 13.49 11.97 0.93 1.70

    1,2,3,6,7,8-HexaCDF 11.02 9.71 10.69 9.57 1.44 1.96 10.88 7.19 8.66 7.26 0.89 1.45

    1,2,3,7,8,9-HexaCDF 0.33 0.36 0.20 0.33 0.09 0.14 0.31 0.28 0.15 0.28 0.08 0.12

    2,3,4,6,7,8-HexaCDF 1.36 1.58 1.19 1.35 0.40 0.56 1.38 1.33 1.03 0.90 0.32 0.47

    1,2,3,4,6,7,8-HeptaCDF 12.82 16.40 11.48 12.68 1.29 1.83 13.17 13.23 9.28 10.64 0.66 1.241,2,3,4,7,8,9-HeptaCDF 1.50 1.70 1.03 1.89 0.11 0.19 1.31 1.31 0.78 1.45 0.10 0.16

    OctaCDF 0.63 0.99 0.49 0.19 0.11 0.26 0.61 1.00 0.52 0.25 0.12 0.29

    TEQs (pg/g lipid)

    PCDDs TEQ 8.33 8.50 7.93 5.78 2.34 2.59 7.21 5.75 5.86 3.92 1.62 1.66

    PCDFs TEQ 5.83 5.43 5.76 4.97 1.59 1.73 5.45 3.96 4.38 3.50 1.07 1.26

    PCDDs/PCDFs T EQ 14.29 14.05 13.85 10.89 3.97 4.33 12.77 9.87 10.34 7.56 2.72 2.94

    Abbreviations: TK, Thanh Khe district, Da Nang city; PC, Phu Cat district, Binh Dinh province; ST, Son Tra district, Da Nang city;

    CL, Cam Lo district, Quang Tri province; CX, Cam Xuyen district, Ha Tinh province; KB, Kim Bang district, Ha Nam province.

    and TEQs in breast milk of mothers from six populations in VietnamPrimiparae Multiparae

    TK PC ST CL CX KB TK PC ST CL CX KB

    (n = 43) (n = 23) (n = 26) (n = 27) (n = 38) (n = 19) (n = 104) (n = 36) (n = 54) (n = 69) (n = 37) (n = 44)

    PCDD congeners (pg/g lipid)

    2,3,7,8-TetraCDD 1.97 1.66 1.39 1.05 0.63 0.50 1.47 1.09 0.98 0.75 0.47 0.311,2,3,7,8-PentaCDD 4.68 5.17 4.91 3.20 1.42 1.65 4.03 3.44 3.44 2.03 0.93 1.03

    1,2,3,4,7,8-HexaCDD 2.21 2.35 2.22 1.78 0.51 0.69 2.34 1.67 2.04 1.38 0.35 0.58

    1,2,3,6,7,8-HexaCDD 8.56 8.69 8.70 8.11 1.40 1.55 8.34 5.46 6.56 5.63 0.89 1.22

    1,2,3,7,8,9-HexaCDD 2.70 3.18 2.67 2.18 0.47 0.71 2.67 2.21 2.21 1.54 0.30 0.51

    1,2,3,4,6,7,8-HeptaCDD 11.26 14.94 10.46 15.75 1.51 2.80 13.22 11.32 10.53 12.85 1.13 2.23

    OctaCDD 61.17 71.37 69.50 49.14 6.05 14.44 70.60 60.73 62.97 43.91 4.77 10.09

    PCDF congeners (pg/g lipid)

    2,3,7,8-TetraCDF 0.55 0.58 0.27 0.65 1.01 0.64 0.60 0.61 0.39 0.46 1.09 0.60

    1,2,3,7,8-PentaCDF 1.33 1.88 0.98 0.84 0.52 0.38 1.27 1.77 1.00 0.63 0.41 0.45

    2,3,4,7,8-PentaCDF 8.04 7.38 8.05 6.04 3.30 3.71 6.92 5.04 6.06 3.96 2.27 2.62

    1,2,3,4,7,8-HexaCDF 18.31 16.65 18.88 17.07 2.05 2.30 17.92 11.88 13.49 11.97 0.93 1.70

    1,2,3,6,7,8-HexaCDF 11.02 9.71 10.69 9.57 1.44 1.96 10.88 7.19 8.66 7.26 0.89 1.45

    1,2,3,7,8,9-HexaCDF 0.33 0.36 0.20 0.33 0.09 0.14 0.31 0.28 0.15 0.28 0.08 0.12

    2,3,4,6,7,8-HexaCDF 1.36 1.58 1.19 1.35 0.40 0.56 1.38 1.33 1.03 0.90 0.32 0.47

    1,2,3,4,6,7,8-HeptaCDF 12.82 16.40 11.48 12.68 1.29 1.83 13.17 13.23 9.28 10.64 0.66 1.24

    1,2,3,4,7,8,9-HeptaCDF 1.50 1.70 1.03 1.89 0.11 0.19 1.31 1.31 0.78 1.45 0.10 0.16

    OctaCDF 0.63 0.99 0.49 0.19 0.11 0.26 0.61 1.00 0.52 0.25 0.12 0.29

    TEQs (pg/g lipid)

    PCDDs TEQ 8.33 8.50 7.93 5.78 2.34 2.59 7.21 5.75 5.86 3.92 1.62 1.66

    PCDFs TEQ 5.83 5.43 5.76 4.97 1.59 1.73 5.45 3.96 4.38 3.50 1.07 1.26

    PCDDs/PCDFs T EQ 14.29 14.05 13.85 10.89 3.97 4.33 12.77 9.87 10.34 7.56 2.72 2.94

    Abbreviations: TK, Thanh Khe district, Da Nang city; PC, Phu Cat district, Binh Dinh province; ST, Son Tra district, Da Nang city;

    CL, Cam Lo district, Quang Tri province; CX, Cam Xuyen district, Ha Tinh province; KB, Kim Bang district, Ha Nam province.

    TK PC ST CL CX KB

    (n = 43) (n = 23) (n = 26) (n = 27) (n = 38) (n = 19)

    2,3,7,8-TetraCDD 1.97 1.66 1.39 1.05 0.63 0.50PCDDs/PCDFs T EQ 14.29 14.05 13.85 10.89 3.97 4.33

    TK PC ST CL CX KB

    (n = 104) (n = 36) (n = 54) (n = 69) (n = 37) (n = 44)

    2,3,7,8-TetraCDD 1.47 1.09 0.98 0.75 0.47 0.31

    PCDDs/PCDFs T EQ 12.77 9.87 10.34 7.56 2.72 2.94

    Multiparae

    Primiparae

    Figure Daily dioxin intake of nursing infants

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    105

    69

    27

    42

    60

    Vietnam

    Figure 3. Daily d ioxin intake of infants in Vietnam

    and some other countries

    JapanUnited StatesUnsprayedSprayedHot spot

    100

    90

    80

    70

    60

    50

    40

    30

    20

    10

    0

    94.4

    64.5

    25.4

    42

    60

    United State : Daily dioxin intake in during the first year of life (Source: Intake of dioxins and related compounds

    from food in US population. Schecter. A et al. J toxicol Environ Health A.2001 May 11; 63 (1):1-18)

    Japan: Daily dioxin intake in nursing infants (Source: Report on Tolerable Daily Intake (TDI)

    of Dioxins and Related Compounds. Environment Agency &Ministry of Health and Welfare 1999)

    105

    69

    27

    42

    60

    Vietnam

    Figure 3. Daily d ioxin intake of infants in Vietnam

    and some other countries

    JapanUnited StatesUnsprayedSprayedHot spot

    100

    90

    80

    70

    60

    50

    40

    30

    20

    10

    0

    94.4

    64.5

    25.4

    42

    60

    DDI = (volume of milk per day in ml)(fatcontent of milk/100)(PCDDs/PCDFs TEQ in breastmilk in pg/g lipid)/ (infant weight in kg).

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    D

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    Jinzu River

    Kumano RiverIda River

    (1967 to 1993) (per 1000 person)

    (Kagamimori S)

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    0- 5

    5-10

    10-2020-30

    30-4040-

    Prevalence of proteinuria

    with glucosuria ( )

    Jinzu River

    Kumano

    River

    Ida River

    Sea of Japan

    Sea of Japan

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    Jinzu River

    Kumano River

    Ida River

    (1971 to 1974)

    (Toyama Prefecture)

    ppm

    istribution of areas irrigated by

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    Jinzu River

    Kumano

    River

    Ida River

    Sea of Japan

    different river water

    Jinzu River

    Mixed

    The other river

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    76/97

    11131 30

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    77/97

    11131 30

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    78/97

    Kakehashi

    Riverbasin

    Ishikawa

    Jinzu River basinin Toyama

    AnnakaGunma

    Ichi River basin in Hyogo

    Tsushima, Nagasaki

    KoskaAkita

    Cadmium polluted areas in Japan

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    79/97

    5 2

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    80/97

    52

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    81/97

    64

    6

    4

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    82/97

    22

    22

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    83/97

    22

    Fig.1 Cd(g/L)

    1986

    Cd5g/L

    22

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    Fig.2 Cd(g/g Cr)

    1986

    Cd5g/g Cr

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    Table II. Estimated biological half-life of urinary cadmium groupedaccording to gender

    Estimated biological half-life and

    95%confidence intervals (years)

    Urinary Cadmium (g/L)Males 10.9 (8.8, 14.4)

    Females 11.5 (9.6, 14.5)

    Urinary Cadmium (g/g cr)

    Males 16.0 (13.0, 20.7)

    Females 20.4 (16.6, 26.2)95% CI; 95% confidence interval.

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    222

    20082-MG

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    87/97

    2

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    88/97

    (

    19

    3

    25

    1,359 1,54711.7

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    89/97

    89

    , ,

    BMI

  • 5/21/2018 Kido

    90/97

    BMI

    9

    1

    1 1

    65 65-74 75

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    91/97

    0.9

    1

    1.1

    65 65-74 75

    totally

    destroyed

    half destroyed

    partially

    destroyed

    * P

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    92/97

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    93/97

    211127 NEWS ZERO

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    Dan Duc NhuHo Dung Manh,Nguyen Hoang Viet, Pham The Tai

    Nguyen Ngoc Hung, Tran Mang Hung, Phung Tri Dung, Le Thi Hong Thom

    10-80

    Le Ke Son

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    13 1417COE

    B14-1617-19

    16 A

    19-22

    22-24

    22 B

    23-25

    10-24

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    96/97

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