Arsenic Toxicity


Practice Essentials

Arsenic toxicity can occur through industrial exposure (see the image below); from contaminated wine, moonshine, or drinking water; or due to malicious intent. It may also occur through heavy metal contamination of herbal preparations and so-called nutritional supplements. A resurgence of interest in arsenic as a medicinal agent for the treatment of acute promyelocytic leukemias, multiple myeloma, myelodysplastic syndromes, and assorted resistant solid tumors may potentially contribute to increases in arsenic exposure.[1, 2]

View Image

"Blackwater" urine due to massive hemolysis, from a patient exposed to arsine at a gas tank cleaning operation.

See Clues on the Skin: Acute Poisonings, a Critical Images slideshow, to help diagnose patients based on their dermatologic presentations.

Signs and symptoms

Arsenic exposure is usually associated with suicide, malicious intent, homicide, or occupational exposure. A detailed history to determine the exposure includes the following:

Clinical effects of arsenic toxicity depend on the chronicity of exposure (eg, acute, chronic) and the chemical form involved, which may be inorganic arsenic (pentavalent arsenic and trivalent arsenic), organic arsenicals, or arsine gas. Frequently, patients exposed to arsenic have a garlic odor to their breath and tissue fluids.

Acute severe inorganic arsenic poisoning manifests with the following signs and symptoms:

Chronic inorganic arsenic poisoning has an insidious presentation, as follows:

Chronic inorganic arsenic poisoning is also associated with a number of chronic medical conditions (hypertension, diabetes mellitus, and peripheral vascular disease) as well as lung, bladder, and hepatic malignancies. Skin malignancies include squamous and basal cell carcinomas and Bowen disease. 

Arsine gas exposure manifestations are as follows:

See Presentation for more detail.


Laboratory testing

Other studies

See Workup for more detail.


Treatment of acute arsenic toxicity is supportive. Chelation therapy may be necessary in patients with inorganic arsenic poisoning. It has no role in arsine gas exposure.


The following chelating agents are used in the management of arsenic toxicity:

See Treatment and Medication for more detail.

For patient education resources, see the First Aid and Injuries Center. Also see the patient education article Chemical Warfare.


Arsenic, element 33, has a long and nefarious history; its very name has become synonymous with poison. In the 15th and 16th centuries, the Italian family of Borgias used arsenic as their favorite poison for political assassinations. Some even have suggested that Napoleon was poisoned by arsenic-tainted wine served to him while in exile.

The metal was reported as the causative agent in an outbreak of food-borne illness after a church gathering in which the coffee urn was apparently criminally contaminated with arsenic. This highlights the need for an index of suspicion when multiple individuals present to an emergency department temporally related and with similar symptoms and circumstances.[3]

Arsenic is typically considered a heavy metal and shares many toxic characteristics with the other heavy metals (eg, lead, mercury). Arsenic is ubiquitous in the environment. It ranks 20th in abundance in the earth's crust, 14th in seawater, and 12th in the human body.[4] In nature, arsenic exists in the metallic state in 3 allotropic forms (alpha or yellow, beta or black, gamma or grey) and several ionic forms.

Arsenic has been used as a medicinal agent, a pigment, a pesticide, and an agent of criminal intent. In the form of chromated copper arsenate (CCA), it was once used as part of the treatment to render architectural wood immune to pest infestation.

CCA was banned for use in the United States by the Environmental Protection Agency (EPA) in 2003, but a great deal of the treated wood continues to exist in the form of decks and other structures exposed to the elements. Data suggest that a significant quantity of arsenic may leach out from such wood into landfills and into the interiors of homes with existing CCA-treated decks.[5, 6, 7] Given the durability of the CCA-treated wood, such exposures may continue for decades. In the rodent model, exposure to CCA may produce significant renal pathology.

Arsenic may be found as a water or food contaminant, particularly in shellfish and other seafood, and often contaminates fruits and vegetables, particularly rice.

Currently, arsenic poisoning occurs through industrial exposure, from contaminated wine or moonshine, or because of malicious intent. In industry, arsenic is primarily used in the production of glass and semiconductors. The possibility of heavy metal contamination of herbal preparations, Ayurvedic medications, and so-called nutritional supplements must also be considered. There has been a resurgence of interest in arsenic as a medicinal agent for treatment of acute promyelocytic leukemias, multiple myeloma, myelodysplastic syndromes, and assorted resistant solid tumors.[1, 2]

Aresenic can contaminate well water or ground water. Contamination may occur from natural sources, or from hazardous waste (eg, mine tailings).


Inorganic forms of arsenic are more toxic than organic forms. The trivalent forms are more toxic and react with thiol groups, while the pentavalent forms are less toxic but uncouple oxidative phosphorylation. Very few organ systems escape the toxic effects of arsenic.

Trivalent inorganic arsenic inhibits pyruvate dehydrogenase by binding to the sulfhydryl groups of dihydrolipoamide. Consequently, conversion of pyruvate to acetyl coenzyme A (CoA) is decreased, citric acid cycle activity is decreased, and production of cellular ATP is decreased. Trivalent arsenic inhibits numerous other cellular enzymes through sulfhydryl group binding. Trivalent arsenic inhibits cellular glucose uptake, gluconeogenesis, fatty acid oxidation, and further production of acetyl CoA; it also blocks the production of glutathione, which prevents cellular oxidative damage.

Effects of pentavalent inorganic arsenic occur partially because of its transformation to trivalent arsenic; toxicity proceeds as outlined above. More importantly, pentavalent arsenic resembles inorganic phosphate and substitutes for phosphate in glycolytic and cellular respiration pathways. Consequently, high-energy phosphate bonds are not made, and uncoupling of oxidative phosphorylation occurs. For example, in the presence of pentavalent arsenic, adenosine diphosphate (ADP) forms ADP-arsenate instead of ATP; the high-energy phosphate bonds of ATP are lost.

Arsenic has been shown to produce oxidative stress. In a small pilot study of environmentally exposed children, arsenic altered monocyte superoxide anion production and inhibited nitric oxide production.[8]

Arsenic trioxide has been shown to cause a significant prolongation of cardiac action potential duration at many levels of repolarization producing conduction delay and increased triangulation. Electrolyte imbalance appears to enhance this toxicity.[9]

Arsenic appears to inactivate endothelial nitric oxide synthase, leading to a reduction in production and bioavailability of nitric oxide. Chronic arsenic exposure also has been associated with inducing/accelerating atherosclerosis, increasing platelet aggregation and reducing fibrinolysis.[10]  Long-term exposure to low to moderate arsenic levels has been associated with increased cardiovascular disease incidence and mortality.[11]  Arsenic exposure has also been associated with incident type 2 diabetes.[12]  

In the Strong Heart Family Study, arsenic exposure was measured in urine samples from 1,337 American Indian adults (average age 30.7 years, 61% female) and echocardiographic assessment was performed. With a two-fold increase in urinary arsenic, the researchers found a 47% greater chance of left ventricular hypertrophy in the group as a whole, and a 58% greater chance in participants with increased or high blood pressure (blood pressure at least 120/80 mm Hg or using pressure-lowering medication). The participants drank water from private wells in areas where groundwater is contaminated with arsenic. None of the participants had diabetes or heart disease at the start of the 5-year study.[13]

Arsenic is listed as a presumed carcinogenic substance based on the increased prevalence of lung and skin cancer observed in human populations with multiple exposures (primarily through industrial inhalation).




According to the American Association of Poison Control Centers' (AAPCC) National Poisoning Data System (NPDS), in 2017, there were 737 single exposures related to arsenic (excluding pesticides) and 17 exposures related to arsenic-containing pesticides. Of the pesticide exposures, 47% (8 of 17) occurred in children younger than 6 years, whereas almost 63% of the nonpesticide exposures occurred in adults (462 of 737).[14]

Ayotte et al mapped out the probability of high (> 10 μg/L) arsenic levels in domestic wells in the coterminous United States. These authors estimated that of the approximately 44.1 million people in the US who use water from domestic wells, 2.1 million are exposed to water with high arsenic levels.[15]

Worldwide, up to 100 million people are at risk of exposure to unacceptable arsenic levels in either well water or ground water. Numerous "outbreaks" of excessive arsenic in water and food from an assortment of natural and anthropological causes have occurred.

In Bangladesh, more than 95% of the water supply to over 138 million people is potentially arsenic contaminated at levels exceeding the US EPA and WHO action limits.[16, 17]  If international efforts at elimination of the risk are unsuccessful, it is estimated that a substantial proportion of the Bangladesh population will develop arsenic-related diseases such as pulmonary and skin cancers as well as cardiovascular and renal disease.

In addition to the concentration of arsenic in the water, the prevailing diet existing in the affected areas may place the citizens at increased risk for toxicity from the arsenic. A population survey found that individuals who had diets deficient in certain B vitamins and antioxidants appeared to have greater risk of arsenic dermatoses. An inverse correlation was found between consumption of vitamins A, C, and E, riboflavin and folic acid, and the existence of dermatological manifestations or chronic arsenic exposure.[18]

Men are more likely to experience industrial arsenic exposure than women. As in many reported cases of poisoning, the majority of reports of exposure to arsenic-containing pesticides occur with children younger than 6 years as the victim (16 of 31), whereas, when nonpesticide arsenic exposure is involved, the majority are in adults older than 20 years (426 of 667).[14]


According to the American Association of Poison Control Centers' (AAPCC) National Poisoning Data System (NPDS), 9 patients suffered major effects and 1 died from exposure to nonpesticide arsenic exposure in 2017.[14]

An association between exposure to arsenic and the development of Alzheimer disease has been proposed.[19]  In addition, an apparent link exists between arsenic exposure and gestational diabetes and potential long-term effects on the infants born to mothers consuming arsenic-contaminated water (among other sources) during pregnancy.[20, 21]


Arsenic exposure is usually suicidal, malicious, homicidal, or occupational. To reveal the exposure, record a careful work history on individuals with symptoms of a painful peripheral neuropathy. If the setting is not occupational, a careful epidemiological history of those affected and those unaffected must be undertaken.

Exposure to arsine gas is usually the result of an occupational accident; in most cases, the worker presents promptly and ideally is brought in with the material safety data sheet (MSDS). One case report indicates that the presentation may be more insidious: In this report, a man in his 20s presented to an emergency department complaining of bloody urine and vomiting 34 hours after an apparent exposure to arsine in the workplace. Laboratory evaluation revealed arsenic in his blood and urine, and an industrial hygiene evaluation of his worksite was able to reproduce his exposure.[22]

Determining unusual cases requires a careful history regarding dietary and nutritional habits, particularly the use of nutritional supplements and ayurvedic medicines, hobbies, and alcohol abuse.[23]

Often, patients with neurological symptoms are subjected to "heavy metal screens" by their primary care practitioners or even neurologists. Often, the laboratories used are not the standard medical reference laboratories, and the results are of questionable reliability. In other cases, the results are reported in concentration of total arsenic in urine or blood, and this is not generally accepted as valuable in the determination of possible exposure or toxicity.




In inorganic arsenic poisoning, clinical effects depend on the chronicity of exposure, as follows:

Toxicity from arsine gas exposure manifests as headache, abdominal pain, nausea vomiting, acute hemolysis, hemoglobinuric renal injury, and death. Hemoglobinuria causes the urine to appear black (see the image below), and the patient becomes rapidly obtunded and shocky. Shaking chills are often described in these patients.

View Image

"Blackwater" urine due to massive hemolysis, from a patient exposed to arsine at a gas tank cleaning operation.




Children may encounter arsenic trioxide as a rodenticide or herbicide. Examine for both arsenic and cholinesterase-inhibitor exposure. Possible transdermal absorption from exposure to pressure-treated wood, now banned for use by the US EPA, has been reported.

Adults may be exposed through work in a metal foundry, mining, glass production, or the semiconductor industry.

Arsenic has been found to contaminate such common items as wine, glues, and pigments. Arsenic is commonly found in many foods both in its apparently nontoxic organic form and also in the more toxic inorganic form. Such arsenic has been reported in milk and dairy products, beef, pork, poultry, and cereal. Arsenic is also often found in rice, representing a potentially serious source of exposure in certain at-risk populations.

Arsenic exists in significant concentrations in some shallow wells dug for provision of clean water in some underdeveloped countries.



Approach Considerations

Arsenic screening prior to fractionation

Retrospective data analysis of urine arsenic results from previously tested samples concluded that performing a total arsenic screen before fractionation reduces the number of samples requiring fractionation by more than 91%.[25] A reflex approach of either testing for total arsenic or a heavy metal panel that includes total arsenic can function as a screening test to determine which samples need further evaluation for potential arsenic toxicity.[25]



Laboratory Studies

Obtain a complete blood cell count (CBC) with indices and a reticulocyte count. Microcytic hypochromic anemia is common. Acute hemolytic anemia is characteristic of arsine exposure. Measure serum electrolytes, including calcium and magnesium, particularly in patients with severe vomiting and diarrhea. Type and screen or crossmatch blood for the transfusion in patients exposed to arsine gas.

A test for plasma arsenic concentrations is helpful but rarely available until after the decision to treat is made. Blood arsenic concentrations should not exceed 50 mcg/L. In patients with arsenic poisoning, blood arsenic concentrations commonly range from several hundred to several thousand micrograms per liter. The reported half-life of arsenic in blood immediately following ingestion is in hours, while whole-body clearance may be in days or months and is apparently dose-related.

Urine studies

A urine spot test for arsenic can be helpful.

A 24-hour urine collection for total arsenic excretion can be diagnostic and useful following therapy. A 24-hour clearance of more than 50 mcg is unusual (be sure the patient has not consumed seafood for at least 3 days prior to urine collection). Because nutritional sources of arsenic are not unusual, the laboratory must "speciate" the arsenic into organic and inorganic moieties. The inorganic arsenic is responsible for symptoms and signs of arsenic toxicity. This point is extremely important, since using just the total arsenic level may lead to unnecessary treatment for many patients.

Various species of arsenic may be recovered in a urine specimen. The human body begins to metabolize inorganic arsenic into various organic forms after a short period of time. Metabolites include methylarsonic acid (MMA) and dimethylarsenic acid (DMA). It should be possible for the laboratory to separate these species from the usual dietary organic forms.

Additional urine studies may include the following:



Imaging Studies

An abdominal radiograph may reveal the presence of radio-opaque densities and may resemble an upper GI series.



Other Tests

Nerve conduction studies may confirm the peripheral neuropathy. This may be particularly important because the classic stocking-glove distribution suggests another etiology.

Cardiac arrhythmias and, in rare cases, cardiac failure have been reported as resulting from arsenic toxicity. Electrocardiography is therefore indicated.



Approach Considerations

Treatment of acute inorganic arsenic toxicity is supportive. Chelation therapy should be considered in symptomatic patients. The efficacy of chelation therapy in providing either laboratory or clinical improvement in intoxicated patients is lacking. Chelation is not indicated for arsine gas exposure. 

Generally, organic arsenical compounds found in the urine are not an indication of arsenic toxicity and do not warrant therapeutical intervention.

Arsenic clearance by dialysis is substantial, and hemodialysis may be indicated if available within a short time after exposure. However, hemodialysis, in the absence of renal failure, has not been shown to alter medical outcome. 

Once arsenic distributes into the tissues, treatment may be unsuccessful. Clinical trials are not available, but attempting to remove arsenic from the plasma before it reaches the tissues makes sense.

In arsine exposure, hemolysis may be severe and life threatening, and no data suggest that chelation therapy can alter this. Arsine appears to rapidly bind to the erythrocytes, making them likely to lyse and release more toxin to contaminate other cells. The use of multiple transfusions and perhaps exchange transfusion may be necessary.

Many patients will develop profound peripheral neuropathy requiring extensive rehabilitation. Rehabilitation should be started as promptly as the clinical picture allows.



Emergency Department Care

Hemodynamic stabilization is of primary importance, and large amounts of crystalloid solutions may be required because of significant gastrointestinal (GI) losses (ie, vomiting, diarrhea). In the face of acute blood loss, the use of blood products may be critical in sustaining the life of the victim.

The use of GI decontamination is controversial and may confuse the clinical picture. For acute arsenic ingestions, orogastric lavage is recommended if the patient presents rapidly or plain radiography indicates that arsenic is present in the stomach. Activated charcoal does not adsorb arsenic appreciably and is not recommended for patients in whom co-ingestants are not suspected. Whole bowel irrigation with polyethylene glycol may be effective to prevent GI tract absorption of arsenic. The use of invasive gastric-emptying procedures has been reported in dire cases, but these attempts do not seem to be fruitful.

Do not delay provision of definitive chelation therapy and hemodialysis.




Chelation should be performed in patients with symptomatic arsenic toxicity, although the evidence of therapeutic benefit from chelation derives largely from animal studies. Chelation is principally useful for acute toxicity. In such cases, chelation should be started as soon as possible, because its efficacy declines rapidly with increasing time after exposure.[26]

The following agents are used for chelation of arsenic[27] :

In the United States, dimercaprol is the first-line agent for treating arsenic poisoning, but it is often in short supply. In animal experiments, repeated administration of dimercaprol has increased the brain uptake of arsenic.[28] Succimer and dimerval, which are water-soluble analogs of dimercaprol, have a higher therapeutic index than dimercaprol, but succimer is licensed in the United States only for use in childhood lead poisoning, and dimerval is not licensed for use in the US, although it is the international drug of choice for this indication.[27]

Sterile abscesses after the use of dimercaprol (BAL in oil) are not unusual. They initially may appear like erythematous macules, which spread or coalesce, and may continue to drain for some time.





Consultations may include the following:



Long-Term Monitoring

Perform a careful neurological evaluation in follow-up of all patients because the peripheral neuropathy, which may develop after an acute exposure, may not appear for 2-3 weeks.

Medication Summary

Chelation should be performed in patients with symptomatic arsenic toxicity, although the evidence of therapeutic benefit from chelation derives largely from animal studies. Chelation is principally useful for acute toxicity. In such cases, chelation should be started as soon as possible, because its efficacy declines rapidly with increasing time after exposure.[26]

Dimercaprol (BAL in Oil)

Clinical Context:  First-line agent available in the US for treating arsenic poisoning. Often in short supply, is one of the antidotes considered essential to be stocked by every ED.

Administered IM q4h, mixed in a peanut oil base. Excreted in urine and bile. May be administered to patients with renal failure.

Succimer (DMSA)

Clinical Context:  Licensed by the FDA for use only in childhood lead poisoning. Has been used worldwide as a heavy metal chelator and has been efficacious in treating arsenic intoxications. In the US, is only available in a bead-filled oral capsule of 100 mg.

Dimerval (DMPS)

Clinical Context:  Internationally accepted DOC for treating most heavy metal poisonings. Not licensed for use in the US and must be obtained from Helytex in Houston. Available as either a parenteral or oral form.

Class Summary

Bind heavy metals and to hasten excretion. By binding in plasma, they render heavy metals nontoxic.


Adam Blumenberg, MD, MA, Fellow Physician in Medical Toxicology, Assistant Clinical Instructor, Department of Emergency Medicine, Oregon Health and Science University School of Medicine

Disclosure: Nothing to disclose.


Sage W Wiener, MD, Assistant Professor, Department of Emergency Medicine, State University of New York Downstate Medical Center; Director of Medical Toxicology, Department of Emergency Medicine, Kings County Hospital Center

Disclosure: Nothing to disclose.

Specialty Editors

John T VanDeVoort, PharmD, Regional Director of Pharmacy, Sacred Heart and St Joseph's Hospitals

Disclosure: Nothing to disclose.

Michael J Burns, MD, Instructor, Department of Emergency Medicine, Harvard University Medical School, Beth Israel Deaconess Medical Center

Disclosure: Nothing to disclose.

Chief Editor

David Vearrier, MD, MPH, Associate Professor, Medical Toxicology Fellowship Director, Department of Emergency Medicine, Drexel University College of Medicine

Disclosure: Nothing to disclose.

Additional Contributors

David C Lee, MD, Research Director, Department of Emergency Medicine, Associate Professor, North Shore University Hospital and New York University Medical School

Disclosure: Nothing to disclose.

Steven Marcus, MD, Professor, Department of Preventive Medicine and Community Health, Associate Professor, Department of Pediatrics, Rutgers New Jersey Medical School, Rutgers University School of Biomedical and Health Sciences; Executive and Medical Director, New Jersey Poison Information and Education System; Consulting Staff, Departments of Pediatrics and Internal Medicine, University Hospital; Consulting Staff, Department of Pediatrics, Newark Beth Israel Medical Center

Disclosure: Nothing to disclose.


  1. Emadi A, Gore SD. Arsenic trioxide - An old drug rediscovered. Blood Rev. 2010 Jul-Sep. 24(4-5):191-9. [View Abstract]
  2. Lo-Coco F, Cicconi L, Breccia M. Current standard treatment of adult acute promyelocytic leukaemia. Br J Haematol. 2016 Mar. 172 (6):841-54. [View Abstract]
  3. Gensheimer KF, Rea V, Mills DA, Montagna CP, Simone K. Arsenic poisoning caused by intentional contamination of coffee at a church gathering--an epidemiological approach to a forensic investigation. J Forensic Sci. 2010 Jul. 55(4):1116-9. [View Abstract]
  4. Mandal BK, Suzuki KT. Arsenic round the world: a review. Talanta. 2002 Aug 16. 58(1):201-35. [View Abstract]
  5. Sigmon C, Patch S. A pilot survey of in-service home arsenic tracked in from chromated copper arsenate-treated decks. J Environ Health. 2010 Jan-Feb. 72(6):18-22. [View Abstract]
  6. Matos RC, Vieira C, Morais S, Pereira ML, Pedrosa J. Toxicity of chromated copper arsenate: a study in mice. Environ Res. 2010 Jul. 110(5):424-7. [View Abstract]
  7. Kamchanawong S, Veerakajohnsak C. Arsenic, chromium, and copper leaching from CCA-treated wood and their potential impacts on landfill leachate in a tropical country. Environ Technol. 2010 Apr 1. 31(4):381-94. [View Abstract]
  8. Luna AL, Acosta-Saavedra LC, Lopez-Carrillo L, Conde P, Vera E, De Vizcaya-Ruiz A, et al. Arsenic alters monocyte superoxide anion and nitric oxide production in environmentally exposed children. Toxicol Appl Pharmacol. 2010 Jun 1. 245(2):244-51. [View Abstract]
  9. Raghu KG, Yadav GK, Singh R, Prathapan A, Sharma S, Bhadauria S. Evaluation of adverse cardiac effects induced by arsenic trioxide, a potent anti-APL drug. J Environ Pathol Toxicol Oncol. 2009. 28(3):241-52. [View Abstract]
  10. Balakumar P, Kaur J. Arsenic exposure and cardiovascular disorders: an overview. Cardiovasc Toxicol. 2009 Dec. 9(4):169-76. [View Abstract]
  11. Moon KA, Guallar E, Umans JG, Devereux RB, Best LG, Francesconi KA, et al. Association Between Exposure to Low to Moderate Arsenic Levels and Incident Cardiovascular Disease: A Prospective Cohort Study. Ann Intern Med. 2013 Sep 24. [View Abstract]
  12. Grau-Perez M, Kuo CC, Gribble MO, Balakrishnan P, Jones Spratlen M, Vaidya D, et al. Association of Low-Moderate Arsenic Exposure and Arsenic Metabolism with Incident Diabetes and Insulin Resistance in the Strong Heart Family Study. Environ Health Perspect. 2017 Dec 20. 125 (12):127004. [View Abstract]
  13. Arsenic in drinking water may change heart structure. American Heart Association. Available at May 7, 2019; Accessed: May 8, 2019.
  14. Gummin DD, Mowry JB, Spyker DA, Brooks DE, Osterthaler KM, Banner W. 2017 Annual Report of the American Association of Poison Control Centers' National Poison Data System (NPDS): 35th Annual Report. Clin Toxicol (Phila). 2018 Dec. 56 (12):1213-1415. [View Abstract]
  15. Ayotte JD, Medalie L, Qi SL, Backer LC, Nolan BT. Estimating the High-Arsenic Domestic-Well Population in the Conterminous United States. Environ Sci Technol. 2017 Nov 7. 51 (21):12443-12454. [View Abstract]
  16. Ng JC, Moore MR. Arsenic in drinking water: a natural killer in Bangladesh and beyond. An urgent alternative watershed management strategy is needed. Med J Aust. 2005 Dec 5-19. 183(11-12):562-3. [View Abstract]
  17. Rodrigues EG, Bellinger DC, Valeri L, Hasan MO, Quamruzzaman Q, Golam M, et al. Neurodevelopmental outcomes among 2- to 3-year-old children in Bangladesh with elevated blood lead and exposure to arsenic and manganese in drinking water. Environ Health. 2016 Mar 12. 15:44. [View Abstract]
  18. Zablotska LB, Chen Y, Graziano JH, Parvez F, van Geen A, Howe GR, et al. Protective effects of B vitamins and antioxidants on the risk of arsenic-related skin lesions in Bangladesh. Environ Health Perspect. 2008 Aug. 116(8):1056-62. [View Abstract]
  19. Gong G, O'bryant SE. The Arsenic Exposure Hypothesis for Alzheimer Disease. Alzheimer Dis Assoc Disord. 2010 May 13. [View Abstract]
  20. Ettinger AS, Zota AR, Amarasiriwardena CJ, Hopkins MR, Schwartz J, Hu H, et al. Maternal arsenic exposure and impaired glucose tolerance during pregnancy. Environ Health Perspect. 2009 Jul. 117(7):1059-64. [View Abstract]
  21. Vahter M. Effects of Arsenic on Maternal and fetal Health. Annu Rev Nutr. June 2009. 29:381-399. [View Abstract]
  22. Yoshimura Y, Endo Y, Shimoda Y, Yamanaka K, Endo G. Acute Arsine Poiosning Confirmed by Speciation Analysis of Arsenic Compounds in the Plasma and urine by HPLC-ICP-MS. J Occupational Health. Nov 2011. 53:45-49. [View Abstract]
  23. Robert B. Saper, Russell S. Phillips, Anusha Sehgal, Nadia Khouri, Roger B. Davis, Janet Paquin, et al. Lead, Mercury, and Arsenic in US- and Indian-Manufactured Ayurvedic Medicines Sold via the Internet. JAMA. 2008. 300:915-923.
  24. Navarro B, Sayas MJ, Atienza A, Leon P. An unhappily married man with thick soles. Lancet. 1996 Jun 8. 347(9015):1596. [View Abstract]
  25. Hackenmueller SA, Strathmann FG. Total arsenic screening prior to fractionation enhances clinical utility and test utilization in the assessment of arsenic toxicity. Am J Clin Pathol. 2014 Aug. 142 (2):184-9. [View Abstract]
  26. Kosnett MJ. The role of chelation in the treatment of arsenic and mercury poisoning. J Med Toxicol. 2013 Dec. 9 (4):347-54. [View Abstract]
  27. Muckter H, Liebl B, Reichl FX, et al. Are we ready to replace dimercaprol (BAL) as an arsenic antidote?. Hum Exp Toxicol. 1997 Aug. 16(8):460-5. [View Abstract]
  28. Andersen O, Aaseth J. A review of pitfalls and progress in chelation treatment of metal poisonings. J Trace Elem Med Biol. 2016 Dec. 38:74-80. [View Abstract]
  29. Amster E, Tiwary A, Schenker MB. Case report: potential arsenic toxicosis secondary to herbal kelp supplement. Environ Health Perspect. 2007 Apr. 115(4):606-8. [View Abstract]
  30. Borak J, Hosgood HD. Seafood arsenic: implications for human risk assessment. Regul Toxicol Pharmacol. 2007 Mar. 47(2):204-12. [View Abstract]
  31. Duenas-Laita A, Perez-Miranda M, Gonzalez-Lopez MA, et al. Acute arsenic poisoning. Lancet. 2005 Jun 4-10. 365(9475):1982. [View Abstract]
  32. Fesmire FM, Schauben JL, Roberge RJ. Survival following massive arsenic ingestion. Am J Emerg Med. 1988 Nov. 6(6):602-6. [View Abstract]
  33. Gerhardt RE, Crecelius EA, Hudson JB. Moonshine-related arsenic poisoning. Arch Intern Med. 1980 Feb. 140(2):211-3. [View Abstract]
  34. Hall JC, Harruff R. Fatal cardiac arrhythmia in a patient with interstitial myocarditis related to chronic arsenic poisoning. South Med J. 1989 Dec. 82(12):1557-60. [View Abstract]

"Blackwater" urine due to massive hemolysis, from a patient exposed to arsine at a gas tank cleaning operation.

"Blackwater" urine due to massive hemolysis, from a patient exposed to arsine at a gas tank cleaning operation.

"Blackwater" urine due to massive hemolysis, from a patient exposed to arsine at a gas tank cleaning operation.