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Relationship between levels of dioxin in food and blood in some areas of Vietnam

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Objectives: To assess levels of dioxin in food and human blood and determine the relationship between levels of dioxin in food and human blood in some areas of Vietnam. Subjects and method: A cross-sectional study on 108 human blood samples including males and females, 33 samples of chicken, 33 samples of pork and 33 samples of fish were collected at 33 sites in 16 provinces.

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RELATIONSHIP BETWEEN LEVELS OF DIOXIN IN FOOD AND

BLOOD IN SOME AREAS OF VIETNAM

Vu Tung Son*; Doan Huy Hau*

Vu Chien Thang*; Ha The Tan*

SUMMARY

Objectives: To assess levels of dioxin in food and human blood and determine the relationship between levels of dioxin in food and human blood in some areas of Vietnam Subjects and method: A cross-sectional study on 108 human blood samples including males and females, 33 samples of chicken, 33 samples of pork and 33 samples of fish were collected

at 33 sites in 16 provinces Samples were then quantified with high resolution gas chromatography mass spectrometry (HRGC/HRMS) by the U.S EPA 1613 B Result: Levels of dioxin in blood in the sprayed area was (10.34 pg/g lipid) higher than in the unsprayed area (6.94 pg/g lipid) with p < 0.05 The levels of dioxin in blood in the dioxin-contaminated area was (9.62 pg/g lipid) higher than in the non-contamination area (8.24 pg/g lipid) with p < 0.05 For food, chicken had the highest dioxin content Chicken and pork were positively correlated with dioxin content in human blood Conclusion: Levels of dioxin in blood in the area sprayed with herbicides was higher than in the unsprayed area Similarly, they were higher in the dioxin contamination than in the non-contamination area Chicken and pork have positive corelation with dioxin content in human blood

* Keywords: Dioxin; Dioxin in food; Dioxin in blood; Relationship.

INTRODUCTION

Persistent organic pollutants (POPs)

include a group of pollutants that are

semi-volatile, persistent in the environment,

bio-accumulative and toxic for humans

and aminals Two groups of POPs, namely

polychlorinated dibenzo-p-dioxins (PCDDs),

poly-chlorinated dibenzofurans (PCDFs)

and polychlorinated biphenyls (PCBs) are

persistently organic pollutants of great

concern because of their high toxicity and

tendency to bioaccumulate through the food chain These contaminants can be formed as unintentional by products of a number of chemical processes, as well as

in almost combustion process More than

90 percent of dioxin penetrates the human body through food Therefore, the aim of

this study is: To evaluate the relationship

between levels of dioxin in food (chicken, pork and fish) and those in blood in several regions of Vietnam

* Vietnam Military Medical University

Corresponding author: Vu Tung Son (tungsonhvqy@gmail.com)

Date received: 11/09/2017

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SUBJECTS AND METHODS

1 Subjects

- The first subject: People who have

lived in study area for at least 15 years

(no occupational exposure to dioxin), including

males and females After that, they were

taken blood to quantify levels of dioxin

- The second subject: Food (chicken,

pork and fish) which was collected at the

same area; blood samples (food specimens

were collected in the lake or market)

Afterward, they were quantified levels of

dioxin

2 Methods

33 samples of chicken, 33 samples of

pork, 33 samples of fish and 108 samples

of blood were collected in 33 wards of

16 provinces in Vietnam (Hoabinh, Hagiang,

Thainguyen, Ninhbinh, Thanhhoa,

Nghean, Quangtri, Hue, Lamdong,

Kontum, Hochiminh City, Binhduong,

Dongnai, Longan, Kiengiang, Angiang)

Samples were selected based on the characteristics of each region The areas were sprayed with herbicides during the war (from the 17th parallel to the south, which was encrypted “B”) and the area was unsprayed with herbicides during the war in Vietnam (from the 17th parallel to the North, which was encrypted “A”)

In turn, each area was divided into those

at risk of dioxin contamination, which was encrypted “1” (industrial production area

or the area was sprayed directly with herbicides) and those without dioxin contamination, which was encrypted “0”

At each sampling point, each food was taken from 6 to 10 specimens and then were pulled to one sample For blood specimen, each person was taken 10 mL whose blood samples were grouped by age and gender

The sample size and sampling according

to US EPA (United States Environmental Protection Agency) guidelines

Encode:

A The area was not sprayed with herbicides during the war in Vietnam

B The areas were sprayed with herbicides during the war

AB-0 Areas are non-dioxin contamination at both A or B

AB-1 Areas were at risk of dioxin contamination at both A or B

* Analysis:

Quantification 7 PCDD (polychlorinated dibenzo para dioxins) and 10 PCDF (polychlorinated dibenzofurans) in blood and food by method US EPA 1613B, then compute WHO TEQ concentrations (toxic equivalents)

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RESULTS

Table 1: Levels of PCDD/F (TEQ) in blood by region

TEQ (pg/g lipid)

p-value

< 0.001

Average TEQ was 9.21 pg/g lipid; average TEQ in blood at the areas which were sprayed with herbicides during the war was 10.34 pg/g lipid higher significantly than the area without herbicides in the same period (6.94 pg/g lipid) (p < 0.001)

Table 2: Levels of PCDD/F (TEQ) in blood by contaminated areas

TEQ (pg/g lipid)

p-value

0.04

Average TEQ in blood in the area at risk of dioxin contamination (AB-1) was 9.26 pg/g lipid, higher significantly than those without dioxin contamination (AB-0) (8.24 pg/g lipid) (p < 0.05)

Table 3: Levels of PCDD/F (TEQ) in chicken, pork and fish by region

TEQ (pg/g)

p

Chicken (pg/g lipid)

0.005

Pork (pg/g lipid)

0.07

Fish (pg/g wet weight)

0.4

Average TEQ in chicken, pork and fish in the areas sprayed with herbicides was higher than those unsprayed with herbicides However, only TEQ in chickens were different significantly with p < 0.05

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Table 4: Levels of PCDD/F (TEQ) in chicken, pork and fish by contaminated areas

Average TEQ in food in the area at risk of dioxin contamination (AB-1) was higher than non-contamination dioxin area (AB-0) However, there was no significant difference between the two regions with p > 0.05

Table 5: Corelate Pearson between TEQ in chicken, pork and fish and TEQ in blood

Levels of dioxin

(pg/g lipid)

TEQ

Number size

TEQ in blood were positively corelative to TEQ in chicken and pork (p < 0.05) with r = 0.25 and 0.2, respectively

Table 6: Correlate Pearson between TEQ in chicken, pork and fish and TEQ in

blood by region

TEQ in blood

by region

Number size

TEQ

TEQ in blood were positively associated with fish at unsprayed areas (p < 0.05) with

r = 0.38

TEQ (pg/g)

p

Chicken (pg/g lipid)

0.4

Pork (pg/g lipid)

0.08

Fish (pg/g wet weight)

0.6

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Table 7: Correlate Pearson between TEQ in chicken, pork and fish and TEQ in

blood by contaminated areas

TEQ in blood by

contaminated areas

Number size

TEQ

TEQ in blood were positively associated with fish at unsprayed areas (p < 0.05) with r = 0.46 and chicken at sprayed area (p < 0.05) with r = 0.3

DISCUSSION

The results showed that the content of

TEQ dioxin in our study was from several

times to dozens of times lower than that

in the study by the Hatfield Consultants

and Office of National Committee 33 in

Bienhoa Airport and Phucat Airport which

were reported in 2009 (5.64 - 8.350 pg/g

wet weight in fish) and 2011 (4.54 - 4,050 pg/g

wet weight in fish), respectively Because

the samples in the study by Hatfield and

Office 33 were taken in the dioxin hotpot

[1, 2] Compared with 187 studies by

Dario Consonni on 29,687 subjects from

26 countries in the world for 10 years

(1989 to 2010), our results were lower

than that his study (12.4 pg/g lipid) [3]

In terms of food, a monitoring study in

Latvia from the year 2009 - 2011 showed

that the TEQ content of chicken in both

sprayed and non-sprayed areas was

0.78 pg/g lipid, lower than that in our study

(4.41 and 1.8 pg/g lipid, respectively)

Specificially, TEQ content in all chicken

samples reached the allowable limit As

for pork, the TEQ content in our study

was (0.28 pg/g lipid) also higher than that

in above study and no pork samples with TEQ content exceeded the allowable limit For fish, the TEQ content in our study in both regions was lower than fish specimens

in Baltic (2.25 pg/g lipid), but our results were higher than fish samples in the ocean (0.11 pg/g lipid) In the monitoring study in Latvia, TEQ content in chicken was higher than in other types of meat, too [4]

Levels of dioxin in chicken, pork and fish were related those in blood depending

on the region and characteristics In particular, the content of chicken and pork had a statistically significant association with levels of dioxin in blood However, in terms

of characteristics, there was a positive corelation between dioxin content in fish and human blood in the areas unsprayed with herbicides When analyzing the dioxin-contaminated characteristics, there was a positive association between dioxin concentration in fish and blood in the non-contaminated dioxin area, meanwhile in dioxin-contaminated areas, there was also

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a positive correlation between dioxin content

in chicken and human blood

CONCLUSION

The level of dioxin in blood in the

sprayed areas was (10.34 pg/g lipid)

higher than in the unsprayed areas (6.94

pg/g lipid) (p < 0.001) The levels of dioxin

in blood in the dioxin-contaminated areas

was (9.62 pg/g lipid) higher than in the

non-contamination areas (8.24 pg/g lipid)

with p < 0.05 Chicken and pork have

positive correlation with dioxin content in

human blood

REFERENCES

1 Hatfield Consultants, Office of National

Committee 33 Comprehensive assessment of

dioxin contamination in Danang Airport, Vietnam:

Environmental levels, Human exposure and

options for mitigating impacts Hatfield Consultants West Vancouver British Columbia, Canada and Office of National Committee 33, MONRE Hanoi, Vietnam 2009

2 Hatfield Consultants, Office of the National Steering Committee 33, MONRE

Environmental and human health assessment

of dioxin contamination at Bienhoa Airbase, Vietnam 200 - 850 Harbourside Drive, North Vancouver, British Columbia, Canada V7P 0A3

2011

3 Consonni D, Sindaco R, Bertazzi P.A

Blood levels of dioxins, furans, dioxin-like PCBs, and TEQs in general populations: a review

1989 - 2010 Environment International 2012,

44, pp.151-162

4 Zacs D, Bartkevics V Polychlorinated

dibenzo-p-dioxins, dibenzofurans and dioxin-like polychlorinated biphenyls in food and feed

in Latvia in 2009-2011 Food Additives & Contaminants Part B, Surveillance 2014, 7 (3), pp.186-220

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