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Arsenic in Drinking Water.


Sources

Arsenic exposure has a number of sources:

* Arsenic is widely distributed throughout the earth's crust.

* Arsenic is introduced into water through the dissolution of minerals and ores, and concentrations in groundwater in some areas are elevated as a result of erosion from local rocks.

* In some areas, industrial effluents contribute arsenic to water.

* Arsenic is also used commercially (e.g., in alloying agents and wood preservatives).

* Combustion of fossil fuels is a source of arsenic in the environment through dispersed atmospheric deposition.

* Inorganic arsenic is also used commercially (e.g., in alloying agents and wood preservatives).

* Inorganic arsenic can occur in the environment in several forms, but in natural waters, and thus in drinking water drinking water

supply of water available to animals for drinking supplied via nipples, in troughs, dams, ponds and larger natural water sources; an insufficient supply leads to dehydration; it can be the source of infection, e.g. leptospirosis, salmonellosis, or of poisoning, e.g.
, it is mostly found as trivalent trivalent /tri·va·lent/ (tri-va´lent) having a valence of three.

tri·va·lent
adj.
Having valence 3.



tri·va
 arsenite or pentavalent pentavalent

having a valence of five.


pentavalent antimony compounds
see antimony.

pentavalent organic arsenicals
includes the pharmaceuticals arsanilic acid, roxarsone, nitarsone. See also organic arsenical.
 arsenate ar·se·nate
n.
A salt of arsenic acid.



arsenate

an uncommon garden pesticide, as lead arsenate, or as antifungal spray on fruit trees or cattle tick dip as sodium arsenate.
. Organic types of arsenic, abundant in seafood, are much less harmful to health and are readily eliminated by the body.

* Drinking water poses the greatest threat to public health from arsenic. Exposure at work, as well as from mining and industrial emissions, may also be significant locally.

Effects

Chronic arsenic poisoning, as occurs after long-term exposure through drinking water, is very different from acute poisoning. Immediate symptoms of an acute poisoning typically include vomiting, esophageal and abdominal pain, and bloody "rice water" diarrhea. Chelation therapy Chelation Therapy Definition

Chelation therapy is an intravenous treatment designed to bind heavy metals in the body in order to treat heavy metal toxicity.
 may be effective in acute poisoning but should not be used against long-term poisoning.

The signs and symptoms of long-term arsenic poisoning appear to differ among individuals, population groups, and geographic areas. Thus, there is no universal definition of the disease caused by arsenic. This circumstance complicates the assessment of the burden arsenic places on health. Similarly there is no method of distinguishing cases of internal cancer that were caused by arsenic from cancers induced by other factors.

Nevertheless, the following information is known about the effects of arsenic exposure on health:

* Long-term exposure via drinking water can cause cancer of the skin, lungs, urinary bladder urinary bladder
n.
A musculomembranous elastic receptacle in the anterior part of the pelvic cavity serving as the temporary storage place for urine.
, and kidneys.

* Increased risks of lung and bladder cancer bladder cancer

Malignant tumour of the bladder. The most significant risk factor associated with bladder cancer is smoking. Exposure to chemicals called arylamines, which are used in the leather, rubber, printing, and textiles industries, is another risk factor.
 and of arsenic-associated skin lesions Skin Lesions Definition

A skin lesion is a superficial growth or patch of the skin that does not resemble the area surrounding it.
Description

Skin lesions can be grouped into two categories: primary and secondary.
 have been observed at arsenic concentrations of less than 0.05 milligrams per liter (mg/L) of drinking water.

* Absorption of arsenic through the skin is minimal, and thus handwashing, bathing, and doing laundry with water containing arsenic do not pose health risks.

* With long-term exposure, the first changes are usually observed in the skin: pigmentation pigmentation, name for the coloring matter found in certain plant and animal cells and for the color produced thereby. Pigmentation occurs in nearly all living organisms.  changes, then hyperkeratosis hyperkeratosis /hy·per·ker·a·to·sis/ (-ker?ah-to´sis)
1. hypertrophy of the stratum corneum of the skin, or any disease so characterized.

2. hypertrophy of the cornea.
. Cancer is a late phenomenon and usually takes more than 10 years to develop.

* The relationship between arsenic exposure and other health effects is not clear-cut. Some studies have reported hypertensive hypertensive /hy·per·ten·sive/ (-ten´siv)
1. characterized by increased tension or pressure.

2. an agent that causes hypertension.

3. a person with hypertension.
 and cardiovascular disease Cardiovascular disease
Disease that affects the heart and blood vessels.

Mentioned in: Lipoproteins Test

cardiovascular disease 
, diabetes, and reproductive effects.

* In a province of China, exposure to arsenic via drinking water has been shown to cause a severe disease of the blood vessels leading to gangrene gangrene, local death of body tissue. Dry gangrene, the most common form, follows a disturbance of the blood supply to the tissues, e.g., in diabetes, arteriosclerosis, thrombosis, or destruction of tissue by injury. . This disease, known as "black-foot disease," has not been observed in other parts of the world, and it is possible that malnutrition contributes to its development. Studies in several countries have, however, demonstrated that arsenic causes other, less severe forms of peripheral vascular disease Peripheral Vascular Disease Definition

Peripheral vascular disease is a narrowing of blood vessels that restricts blood flow. It mostly occurs in the legs, but is sometimes seen in the arms.
.

Prevention and Control

The most important remedial action is prevention of further exposure through provision of safe drinking water. Alternative low-arsenic sources such as rainwater and treated surface water may be available in some circumstances.

Where low-arsenic water is not available, it is necessary to remove arsenic from drinking water. The cost and difficulty of this process increase as the targeted concentration lowers. They also vary with the concentration of arsenic in the source water; the chemical matrix of the water, including interfering solutes; the availability of alternative sources of low-arsenic water; mitigation technologies; and the amount of water to be treated.

* The technology for arsenic removal from piped water is moderately costly and requires technical expertise. It is inapplicable in some urban areas of developing countries and in most rural areas worldwide.

* New technologies, including co-precipitation, ion exchange, and activated alumina filtration are being field-tested.

* There are no proven technologies for the removal of arsenic at water collection points such as wells, hand pumps, and springs.

* Simple technologies for household removal of arsenic are few, must be adapted to, and must be proven sustainable in each setting.

* Some studies have reported preliminary successes with packets of chemicals for household treatment. Some mixtures combine arsenic removal with disinfection disinfection,
n the process of destroying pathogenic organisms or rendering them inert.

disinfection, full oral cavity,
n a procedure used to reduce active periodontal disease, usually completed within a certain short time frame.
.

Activities of the World Health Organization

The World Health Organization's (WHO's) norms for drinking-water quality go back to 1958. In that year, the International Standards for Drinking Water established 0.20 mg/L as an allowable concentration. In 1963, the standard was re-evaluated and reduced to 0.05 mg/L. In 1984, the 1963 standard was reaffirmed as WHO's "Guideline Value," and many countries have kept it as a national standard or an interim target. The last edition of the WHO Guidelines for Drinking-Water Quality, from 1993, established a new provisional guideline value of 0.01 mg/L.

A summary of an updated International Programme on Chemical Safety The International Programme on Chemical Safety (IPCS) is a collaboration between three United Nations bodies—the World Health Organization, the International Labour Organization and the United Nations Environment Programme.  Environmental Health Criteria Document on Arsenic, published by WHO, is available at [less than] http://www.who.int/pcs/ehc/summaries/ehc_224.htm#English[greater than].

A United Nations report on arsenic in drinking water has been prepared in cooperation with other U.N. agencies. It provides a synthesis of available information on chemical, toxicological, medical, epidemiological, nutritional, and public-health issues; develops a basic strategy for coping with the problem; and advises on removal technologies and water quality management. A draft of the report is available at [less than]http://www.who.int/water_sanitation_health/Arsenic/ArsenicUN Reptoc.htm[greater than].
COPYRIGHT 2001 National Environmental Health Association
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2001, Gale Group. All rights reserved. Gale Group is a Thomson Corporation Company.

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Article Details
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Publication:Journal of Environmental Health
Article Type:Brief Article
Geographic Code:1USA
Date:Sep 1, 2001
Words:917
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