arsenic and manganese poisoning

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Arsenic and Manganese poisoning Ratchaneewan Sinitkul, MD. Department of Pediatrics Faculty of Medicine Ramathibodi Hospital Mahidol University

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Page 1: Arsenic and manganese poisoning

Arsenic and Manganese poisoning

Ratchaneewan Sinitkul, MD.Department of Pediatrics

Faculty of Medicine Ramathibodi HospitalMahidol University

Page 2: Arsenic and manganese poisoning

พระพ�ทธมหาสุ�วรรณปฏิ�มากร หร�อหลวงพ�อทองคำ�า ประดิ�ษฐานท��ว�ดิไตรม�ตรว�ทยารามวรว�หาร กร�งเทพฯ

Page 3: Arsenic and manganese poisoning

แผนท��แสุดิงแหล�งแร�ทองคำ�าในประเทศไทย

1. พ�(นท��ท��อย)�ในแนวพาดิ ผ�านต�(งแต�

เลย หนองคำาย เพชรบู)รณ, พ�จิ�ตร นคำรสุวรรคำ, ลพบู�ร�

ปราจิ�นบู�ร� สุระแก.ว ชลบู�ร�และระยอง

2. พ�(นท��ท��อย)�ในแนวพาดิ ผ�านต�(งแต� เช�ยงราย

แพร� ล�าปาง อ�ตรดิ�ตถ์, สุ�โขท�ย และตาก

โคำรงการสุาราน�กรมไทยสุ�าหร�บูเยาวชน โดิยพระราชประสุงคำ,ในพระบูาทสุมเดิ2จิ พระเจิ.าอย)�ห�ว http://kanchanapisek.or.th/

Page 4: Arsenic and manganese poisoning

การท�าเหม�องแร�ทองคำ�า1. เหม�องเป3ดิ  - อย)�ไม�ล4ก- ใช.พ�(นท��มาก 

2. เหม�องใต.ดิ�น   - อย)�ล4ก- ใช.พ�(นท��หน.าเหม�องน.อย

และต้�องทำอ�โมงค์� เพื่��อเข้�สู่��แหล�งแร่�

โคำรงการสุาราน�กรมไทยสุ�าหร�บูเยาวชน โดิยพระราชประสุงคำ,ในพระบูาทสุมเดิ2จิ พระเจิ.าอย)�ห�ว http://kanchanapisek.or.th/

Page 5: Arsenic and manganese poisoning

เหม�องแร�ทองคำ�าในประเทศไทย• แหล�งแร�ทองคำ�าชาตร�

ข้องบร่�ษั�ทำอ�ค์ร่ไมนิ่��ง จำกั�ด อยู่��ในิ่เข้ต้ร่อยู่ต้�อ ข้องอเภอ ทำ�บค์ล�อ จำ�งหวั�ดพื่�จำ�ต้ร่ และอเภอวั�งโป่(ง จำ�งหวั�ดเพื่ชร่บ�ร่ณ์� ซึ่,�งม-

กัร่ทำเหม�องต้�.งแต้�ป่ลยู่ พื่.ศ. ๒๕๔๔ อ-กัแห�งค์�อ• แหล�งแร�ทองคำ�าภู)ท�บูฟ้7า

ข้องบร่�ษั�ทำทำ��งค์ จำกั�ด อยู่��ทำ-�ต้บลเข้หลวัง อเภอวั�งสู่ะพื่�ง จำ�งหวั�ดเลยู่ เร่��มสู่ร่วัจำต้�.งแต้� พื่.ศ. ๒๕๓๔ ป่4จำจำ�บ�นิ่ม-กัร่ทำเป่5นิ่

เหม�องผล�ต้แร่�แล�วั

โคำรงการสุาราน�กรมไทยสุ�าหร�บูเยาวชน โดิยพระราชประสุงคำ,ในพระบูาทสุมเดิ2จิ พระเจิ.าอย)�ห�ว http://kanchanapisek.or.th/

Page 6: Arsenic and manganese poisoning

การร�อนและเล�ยง เพ��อหาแร�ทองคำ�าบูร�เวณล�าห.วย

โคำรงการสุาราน�กรมไทยสุ�าหร�บูเยาวชน โดิยพระราชประสุงคำ,ในพระบูาทสุมเดิ2จิ พระเจิ.าอย)�ห�ว http://kanchanapisek.or.th/

Page 7: Arsenic and manganese poisoning

การแต�งแร�ทองคำ�า

1.การบูดิและแยกแร�2.การสุก�ดิแร�ทองคำ�าโดิยว�ธ�การทางเคำม�

โคำรงการสุาราน�กรมไทยสุ�าหร�บูเยาวชน โดิยพระราชประสุงคำ,ในพระบูาทสุมเดิ2จิ พระเจิ.าอย)�ห�ว http://kanchanapisek.or.th/

สุายพานล�าเล�ยงห�นท��บูดิแล.ว เข.าสุ)�กระบูวนการแยกแร�โดิยการละลายแร�

Page 8: Arsenic and manganese poisoning

ข�(นตอนการหลอมแท�งโลหะผสุม ซึ่4�งม�สุ�วนผสุมของแร� ทองคำ�า และแร�โลหะอ��น ก�อนน�าไปแยกโลหะท�(งหมดิออก

จิากก�น เพ��อให.ไดิ.เฉพาะทองคำ�าบูร�สุ�ทธ�:

โคำรงการสุาราน�กรมไทยสุ�าหร�บูเยาวชน โดิยพระราชประสุงคำ,ในพระบูาทสุมเดิ2จิ พระเจิ.าอย)�ห�ว http://kanchanapisek.or.th/

Page 9: Arsenic and manganese poisoning

Metals of concern

• Arsenic (As)• Manganese (Mn)• Cyanide: same as adult• Lead (Pb)• Cadmium (Cd)• Others: Cr, Fe, Co, Ni, Cu, Zn, Hg

Page 10: Arsenic and manganese poisoning

Arsenic

• Potential uses: effective poison, very effective against acute promyelocytic leukemia

• Antimetabolic and carcinogenic properties• Inorganic forms:

trivalent (arsenite): more toxic and carcinogenic, most industrial uses

pentavalent (arsenate)• Organic forms:

Natural: nontoxicDimethylarsenic acid: pesticides, very toxic

Page 11: Arsenic and manganese poisoning

Arsenic

Route of exposure• Ingestion• Inhalation• Placenta

Soil pica behavior: when children ingest large amounts of soil at a time (e.g. up to 1 teaspoon or 5,000mg)

Page 12: Arsenic and manganese poisoning

Arsenic

Sources of exposure: common in the environment• Natural

Groundwater Food chain (nontoxic, organic form): Seafood and fish

• AnthropogenicArsenic containing mineral ores Industrial processes

• Semiconductor manufacturing (gallium arsenide)• Fossil fuels• Wood treated with arsenic preservatives• Smelting (copper, zinc, lead) and refining of metals and ores• Glass manufacturing

Commercial products: Wood preservatives, pesticides, herbicides, fungicides Herbal remedies

Page 13: Arsenic and manganese poisoning

Food chain

Page 14: Arsenic and manganese poisoning

Source Intake*Iron def increase

GI absorption

Metabolism Elimination*:mostly in urine 10% in bile

WaterFoodAirOther

Inorganic arsenicwell absorbed (80–90%) from GI tract

T1/2(blood): 10 hrs

YesInorganic arsenic

Organic arsenic:Methylate arsenic

Total arsenic

Seafood

Organic arsenic T1/2(blood): 30 hrs

ArsenosugarsArsenolipids

Yes Other metabolites

Arsenobetaine No Arsenobetaine

*Humans are able to detoxify small amounts from inorganicorganic forms**Children are less able than adult

* Within 2-4 wks after exposure, the remaining body burden of arsenic is found in hair, skin, and nails.

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Arsenic: metabolism

The intermediate metabolites, methylarsonous acid (MMA3+) and dimethylarsinous acid(DMA3+), are generated during this process, and these trivalent methylated arsenicals are now thought to be more toxic than even the inorganic arsenic species

Page 16: Arsenic and manganese poisoning

Arsenic: toxicokinetics

As5+ (Arsenate)

As3+ (Arsenite)

Methylarsenite (in liver)

Dimethylarsenite (readily eliminated – urine)

Page 17: Arsenic and manganese poisoning

Arsenic: systemic affectedAcute: high dose, inorganic(>3-5 mg/kg) ChronicGI: N/V, hematemesis, diarrhea, abdominal cramping

Fatigue and malaise

Nervous system: CNS: encephalopathyPNS- mimic Guillain-Barré syndrome

IQ

CVS: intractable shock, arrhythmia, heart failure

Bronchiectasis

Bone marrow suppression: pancytopenia Bone marrow suppression: aplastic anemia

Skin: Mee lines (white transverse creases across the fingernails )

Skin: eczematoid eruptions, hyperkeratosis, dyspigmentation, alopecia

Liver: hepatic dysfunction Hepatic dysfunction

Kidneys: proteinuria, hematuria, ARF Kidneys: Cancer

Carcinogen: bladder, lung, skin, kidney, liver, AML

Spontaneous abortion, still birth, preterm birth

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Arsenic-associated Change To Epigenome

• Low to moderate dose exposure to inorganic arsenic (iAS)DNA methylationmiRNA abundanceHistone modification

Bailey KA, Fry RC.Curr Environ Health Rep. 2014 Jan 19;1:22-34.

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Potential modes of action for Arsenic carcinogenesis

Arsenic exposure

Carcinogenesis

Altered DNA repair

Altered DNA Methylation

Chromosomal abnormality

Oxidative stress

Modification of cell

proliferation

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Arsenic: diagnosis

• Urine collection: test of choice*Children: timed urinary collection for 8-24 hrs Some methods does not distinguish organic and

organic formsabstain seafood ingestion > 5 days

• Blood: not recommend (short t1/2)• Hair and fingernail analyses: validity???

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Arsenic: treatment

• Decontamination• Chelation therapy:

dimercaprol (BAL) d-penicillamine succimer

Chronic poisoning: chelation therapy has not proven effective in relieving symptoms

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Woolf A, Wright R, Amarasiriwardena C, Bellinger D.Environ Health Perspect. 2002 Jun;110(6):613-6.

uncertain howthe water became contaminatedA 10-year-old male:

refer to PEH center with elevated blood, urine, hair [Mn]

Page 24: Arsenic and manganese poisoning

PEH center evaluation

Patient• Unremarkable PH and

examination• Patient’s grades and

behavior were excellent• Mother: for the past

several years teachers had consistently noted a difficulty with listening skills and following directions

Home and environment• Boston, Massachusetts, suburb

5years• Well was drilled to supply the

home with water• Water: turbid, metallic taste,

and left an orange-brown residue on clothes, dishes, and appliances

• Parents, 16 and 10 years boy• Only the younger boy had

abnormally high blood [Mn]

Woolf A, Wright R, Amarasiriwardena C, Bellinger D.Environ Health Perspect. 2002 Jun;110(6):613-6.

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Normal IQ but unexpectedly poor verbal and visual memory

Woolf A, Wright R, Amarasiriwardena C, Bellinger D.Environ Health Perspect. 2002 Jun;110(6):613-6.

Page 26: Arsenic and manganese poisoning

Management

• Advised to discontinue all residential use of the water from the well

• Interceded with town officials on the behalf of the family 3 mo later: a standpipe was dropped from the water main to the family home

• 18 mo later: Still in an age-appropriate grade Teachers: continued to remark on his difficulty in

remaining on task and his inattentiveness in class

Woolf A, Wright R, Amarasiriwardena C, Bellinger D.Environ Health Perspect. 2002 Jun;110(6):613-6.

Page 27: Arsenic and manganese poisoning

Manganese

• Light weight and durability• Inorganic: steel alloys, batteries, glass,

ceramics, incendiaries, fungicides, organic compounds , etc.

• Organic: gasoline and fuel oil additive, fungicides

• Essential in human nutrient: bone, metabolism of AA, lipids, CHO, enzyme

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Manganese

• Route of exposureIngestedInhaledPlacentaHuman milk

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Manganese

• Sources of exposureFoods: whole barley, rye and wheat, nuts, and leafy

green vegetableBeverages: tea, milk (soy> cow’s milk> human milk)Remedy: Chinese herbalPollution: air, water, and soil

Page 30: Arsenic and manganese poisoning

Manganese exposure

Blood brain barrier

Circulation

3-5% 100 %

• Children• Female• Iron deficiency• Low protein intake• Genetic modulation

Excretion: t1/2 40 days

• High dietary Ca2+

•High dietary PO4

3-

*esp.Neonate

Page 31: Arsenic and manganese poisoning

Manganese: clinical effectsAcute effects Chronic/long-term effects

Lungs: “metal fume fever” or manganese pneumonitis

Neurotoxicity: progressive “Manganese madness” Manganism: mimics Parkinson disease

Skin Pulmonary disease: chronic RS tract inflammation

Hepatic injury Reproductive toxicity: Decrease spermatogenesis (animal) Stillbirths and birth defects (cleft lip, imperforate anus, cardiac defects, and deafness)

IQ and learning problems

Page 32: Arsenic and manganese poisoning

Mn exposure and cognitive deficits

From Chang et al., 2010

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Both low and high B-Mn levels may have adverseneurological effects

From Claus Henn et al., 2010

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Manganese: diagnosis

• Normal rangesBlood: 4-15 µg/dL (bound to RBC)Serum: 0.4-0.85 µg/dLUrine: 1-8 µg/dL

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Biomarkers of manganese intoxication

• Biomarkers of exposure• Biomarkers of effect• Biomarkers of host susceptibility

No reliable biomarkers: complete scientific understanding of the mechanism of

toxicity remains undiscovered

Page 36: Arsenic and manganese poisoning

Biomarkers of Mn exposure

• Mn concentrations in body fluid: whole blood, plasma, or serum

1) reasonable indicator of exposure on a group basis; 2) reflects recent, active exposure; and 3) appears to be a modest indicator for distinguishing

Mn-exposed workers from control subjects at the individual level

Page 37: Arsenic and manganese poisoning

Manganese: treatment

• Chelation therapy Calcium disodium edetate (CaNa2EDTA)

increase urinary excretion

Page 38: Arsenic and manganese poisoning

Manganese: prevention

• Air pollution: < 0.05 µg/m3 (EPA)• Water supplies: < 50 µg/L (EPA)

Recommended daily intake• EPA: 0.14 mg/kg/day (adult)• The institute of Medicine(Washington,DC):

Infants 3 µg/day Adolescent males: 2.2 mg/day

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Chronic intake of heavy metals

• Carcinogenic hazards• Non-carcinogenic hazards

Neurologic and developmental involvement Endocrine disruptorEpigenetic

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Chemical mixtures and children’s health

• Evaluating health effects of single chemical exposures: under estimate the true effects

• Metal mixtures:Children: developmental and neurological effectsMore severe than exposure to each metal aloneLead: increased toxicity in the presence of other

metals e.g., Mn, Cd, Mercury (Hg), As

Claus Henn B, Coull BA, Wright RO.Curr Opin Pediatr. 2014 Apr;26(2):223-9.

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Chemical mixtures and children’s health

• Birth defects• Reproductive outcome• Cognitive and motor development

Claus Henn B, Coull BA, Wright RO.Curr Opin Pediatr. 2014 Apr;26(2):223-9.

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• Chitwan Valley, Nepal• Hospital-based birth cohort study with 100 pregnant women; 100 infants at 1 day after birth• Pb, As, and Zn concentrations in cord blood• Pb, As inverse neurodevelopment of newborns

• High levels of Pb or As exposure during prenatal induce retardation during in utero neurodevelopment

Page 43: Arsenic and manganese poisoning

As, Cd and Mn with neurodevelopment in children

• 50% increase in As levels (urine) 0.4 decrease in the IQ of children• 50% increase in Mn levels (hair)0.7 decrease in the IQ of children

• Mn exposure attention deficit disorder with hyperactivity

Rodríguez-Barranco M,et al. Sci Total Environ. 2013 Jun 1;454-455:562-77.

•2002-2012•As(18), Mn(17), Cd (6)•Neurodevelopmental or behavioral

As (13/18) Mn (14 /17) Cd(2/6)

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Proposed biomarkers

Andrade VM, et al..Biol Trace Elem Res. 2015 Feb 20.

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Thank you