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A Dietary Solution to Arsenic Poisoning in Bangladesh

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A Dietary Solution to Arsenic Poisoning in Bangladesh 2016 International Conference on Pulses For Health, Nutrition and Sustainable Agriculture for Drylands Marrakesh, Morocco April 2016 Judit E.G. Smits, DVM, PhD Professor, Ecosystem & Public Health Faculty of Veterinary Medicine ?
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A Dietary Solution to Arsenic Poisoning in Bangladesh

2016 International Conference on Pulses

For Health, Nutrition and Sustainable Agriculture for Drylands Marrakesh, Morocco

April 2016

Judit E.G. Smits, DVM, PhDProfessor, Ecosystem & Public Health

Faculty of Veterinary Medicine

?

As

As

As

As

Coal with high As content mountainous regions of China

Emerging in more water sources globally . . . .

In drinking wateremerging in areas

throughout Europe, North & South America

Mine tailings & dust

Known areas with natural arsenic contamination Ravenscroft et al. 2008

Health problems associated with arsenicosis

Hyperkeratosis & hyperpigmentation(thickening & blackening of skin)

Peripheral vascular disease- arterial blockage leading to gangrene of extremities

Cardiovascular disease - arsenic blocks major blood vessels

Hepatic disease – similar in humans & experimental animals

- hepatomegaly, fatty change

- liver fibrosis - decreased GSH

- increased oxidative damage

(MDA in liver, 8-OHdG in plasma)

Pulmonary & bladder cancer

70

100

130

160

190

220

250

280

MDA (nmol/mg of

protein)

PCC (ng/mg of

protein)

8-OHdG (ng/mg of

protein)

Rela

tive D

iffe

rence (

%)

CTR 0.4ppm 4ppm 40ppmControl vs arsenic 0.4, 4, 40ppm

MDA 8-OHdG

Liver damage from arsenic

Se builds the major anti-oxidant of the body (as glutathione – GSH)

controls free radical damage produced by normal metabolism

free radicals are much higher in malnourished people (+ - As toxicity)

Se enhances immune surveillance vs neoplastic (cancer) cells

Much of the earth’s soils

are deficient in Se lentil production

area in North America

IV injection of As & Se separately, produces the conjugate seleno-bis-arsinium ion (GS)2AsSe] excreted in bile, then feces

Zeng H, Uthus EO, & Combs GF,Jr. (2005) Mechanistic aspects of the interaction between selenium and arsenic. J of Inorganic Biochemistry, 99: 1269-1274.

Gailer J, et al. (2002) Biliary excretion of [(GS)(2)AsSe](-) after intravenous injection of rabbits with arsenite and selenate. Chem Research in Toxicology, 15: 1466-1471.

The story of selenium (Se)

Normal Se Severely deficient Se

Globally - soil is deficient in Se- some ‘hot spots’ have high Se - toxicity problems

- a few regions are just right

Good Se levels in Saskatchewan soils

- old sea bed – high selenium - crops take up selenium in seeds

0

100

200

300

400

500

600

Canada

Bangladesh

India

Australia

USA

Nepal

Syria

Tot

al Se c

once

ntra

tion

( µg.

kg-

1)

Se

medicinal uses to treat diseases such as syphilis

used as a growth promotant in poultry & swine feed

popular means of murder during Victorian times in the 19th century

In 1970’s in BD arsenic started appearing in ‘clean’ tube-well water

As 3+ is the most common form in drinking water in south Asia

in vivo As 5+ is normally reduced to the more toxic form, As 3+ during

metabolism

largest mass poisoning in history: WHO estimates that 140

million people are exposed to As levels > 50 ug/L (US EPA &

WHO limits of <10 ug/L)

History of arsenic

Shahrasti, Chandpur

1) Identify households with As ≥ 100 ppb in tube well water

- 102 wells tested- tube wells 60 – 120 ft deep- 92 As higher than 100 ppb

- 88% with As > 250 ppb

- no influence of well depthon As content

>250 ppb As

drinkingwater

standardAs < 50ppb

Arsenicosis in Bangladesh

Seeking the solution through Saskatchewan lentil

filter to remove arsenic

- defunct 10 yrs ago As

Conjugate

urinary & fecal Asexcretion

Se

WHO efforts for clean water:

Large vessels to collect rain water from roof

icddr.,b colleagues –Shahrasti field station

Lentils in storage inSharasti –

weekly distributionto families

6 Month Dietary Trial in Shahrasti, Bangladesh

Screening

well water

Arsenic ≥

100ppb

Day 1:

Physical exam

sample collection

3 months:

Physical exam

sample collection

6 months:

Physical exam

Sample collection

Physical examinations:

BMI, BP, NIOX MINO® lung inflammation exam

• Bi-weekly morbidity questionnaire

• Weekly lentil consumption log

• Weekly lentil consumption questionnaire

Block randomization

Recruitment:

Socio-demogr. questionnaire

Adult & child consent

Samples:

Macronutrients Sask. Lentils Idaho Lentils

Protein % by weight 26.22 27.73

Starch % by weight 38.00 37.00

TDF % by weight 8.48 6.66

Phytochemicals

Phytic acid g/kg 0.61 0.72

Minerals

Calcium mg/kg 328 378

Potassium g/kg 10.45 10.94

Sodium mg/kg 72 75

Magnesium mg/kg 786 943

Copper mg/kg 9.3 11.4

Iron mg/kg 75.75 65.3

Zinc mg/kg 42.15 51.9

Manganese mg/kg 16.9 14.6

Selenium mg/kg 0.854 0.029

Arsenic mg/kg <0.001 <0.001

Coauthors & Acknowledgements

Regina Krohn, PhD University of Calgary, Calgary, AB, Canada

Rubhana Raqib, PhD icddr,b, Dhaka, Bangladesh

Albert Vandenberg, PhD University of Saskatchewan, Saskatoon, SK, Canada

Funders

Global Institute for Food Security – (Government of Saskatchewan,

University of Saskatchewan, Potash Corp)

Saskatchewan Pulse Crop Development Board

Grand Challenges Canada- Stars in Global Health


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