Arsenic contamination of groundwater

Groundwater arsenic contamination areas

Arsenic contamination of groundwater is a form of groundwater pollution which is often due to naturally occurring high concentrations of arsenic in deeper levels of groundwater. It is a high-profile problem due to the use of deep tube wells for water supply in the Ganges Delta, causing serious arsenic poisoning to large numbers of people. A 2007 study found that over 137 million people in more than 70 countries are probably affected by arsenic poisoning of drinking water. The problem became serious health concern after mass poisoning of water in Bangladesh.[1] Arsenic contamination of ground water is found in many countries throughout the world, including the US.[2]

The World Health Organization recommends limiting arsenic concentrations in water to 10 μg/L, although this is often an unattainable goal for many problem areas due to the difficult nature of removing arsenic from water sources.[3]

Approximately 20 major incidents of groundwater arsenic contamination have been reported.[4] Of these, four major incidents occurred in Asia- in Thailand, Taiwan, and Mainland China.[5] Locations of potentially hazardous wells have been mapped in China.[6]

Speciation of arsenic compounds in water

Arsenic contaminated water typically contains arsenous acid and arsenic acid or their derivatives. Their names as "acids" is a formality; these species are not aggressive acids but are merely the soluble forms of arsenic near neutral pH. These compounds are extracted from the underlying rocks that surround the aquifer. Arsenic acid tends to exist as the ions [HAsO4]2− and [H2AsO4]− in neutral water, whereas arsenous acid is not ionized.

Arsenic acid (H3AsO4), arsenous acid (H3AsO3) and their derivatives are typically encountered in arsenic contaminated ground water.

Contamination in specific nations and regions

South America

An analysis of water and food consumption in Socaire, a rural village in Chile, found that between November 2008 and September 2009, the total intake of arsenic by the villagers correlated with the amount of water and local produce consumed.[7]

The central portion of Argentina is affected by arsenic-contaminated groundwater. Specifically, the La Pampa produces water containing 4–5300 microgram per liter.[8]

South Asia

Bangladesh

Arsenic contamination of the groundwater in Bangladesh is a serious problem. Prior to the 1970s, Bangladesh had one of the highest infant mortality rates in the world. Ineffective water purification and sewage systems as well as periodic monsoons and flooding exacerbated these problems. As a solution, UNICEF and the World Bank advocated the use of wells to tap into deeper groundwater. Millions of wells were constructed as a result. Because of this action, infant mortality and diarrheal illness were reduced by fifty percent. However, arsenic has been found in the wells[9][10] and, in 2008, approximately 57 million residents used water contaminated with arsenic from these shallow wells.[11] 20% of the total deaths are related to arsenic related cancer.[12][13][14] The Bangladeshi government limits arsenic concentration in water to 50 μg/L, which is 5 times more than the WHO recommended limit.[15]

In the Ganges Delta, the affected wells are typically more than 20 meters and less than 100 meters deep. Groundwater closer to the surface typically has spent a shorter time in the ground, therefore likely absorbing a lower concentration of arsenic; water deeper than 100 meters is exposed to much older sediments which have already been depleted of arsenic.[16]

The issue came to international attention in 1995.[17][18][19] One study conducted in Bangladesh involved the analysis of thousands of water samples as well as hair, nail, and urine samples. It found 900 villages with arsenic above the government limit.

Criticism has been leveled at the aid agencies, who denied the problem during the 1990s while millions of tube wells were sunk. The aid agencies later hired foreign experts who recommended treatment plants that were inappropriate to the conditions, were regularly breaking down, or were not removing the arsenic.[20]

According to a British Geological Survey study in 1998 on shallow tube-wells in 61 of the 64 districts in Bangladesh, 46 percent of the samples were above 0.01 mg/L and 27 percent were above 0.050 mg/L. Based on the estimated 1999 population of Bangladesh, the study suggested that 28–35 million people may have been exposed to arsenic levels above 0.05 mg/L, and 46–57 million may have bee exposed at the lower but still concerning level of 0.01 mg/L.[21]

Throughout Bangladesh, as tube wells get tested for concentrations of arsenic,[22] ones which are found to have arsenic concentrations over the amount considered safe are painted red to warn residents that the water is not safe to drink.

India

In Bihar, groundwater in 13 districts have been found to be contaminated with arsenic with quantities exceeding 0.05 mg/L. All these districts are situated close to large rivers like Ganga and Gandak.[23]

In West Bengal, India, water is mostly supplied from rivers, open wells, or ponds. These may be contaminated with communicable diseases such as dysentery, typhoid, cholera, and hepatitis. Since the 1970s, non-governmental organisations in India have focused on sinking tube wells to provide drinking water uncontaminated by diseases, with the unforeseen side effect of exposing some people to arsenic-contaminated groundwater.[21][24]

Nepal

Nepal is subject to a serious problem with arsenic contamination. The problem is most severe in the Terai region, the worst being near Nawalparasi District, where 26 percent of shallow wells failed to meet WHO standard of 10 ppb. A study by Japan International Cooperation Agency and the Environment in the Kathmandu Valley showed that 72% of deep wells failed to meet the WHO standard, and 12% failed to meet the Nepali standard of 50 ppb.[25]

Pakistan

66% of 1200 samples tested contained arsenic above WHO recommended limit, threatening over 60 million residents. 50–60 million residents consume water with arsenic levels greater than 50 micrograms of arsenic per liter, levels far passing acceptable levels worldwide.[26]

United States

Regulation

A drinking water standard of 0.05 mg/L (equal to 50 parts per billion, or ppb) arsenic was originally established in the United States by the Public Health Service in 1942. After the passage of the Safe Drinking Water Act of 1974 (SDWA), the Environmental Protection Agency (EPA) was given the power to set the maximum containment levels (MCLs) of contaminants in public water supplies. In 1996 Congress amended the SDWA and created a Drinking Water State Revolving Fund to provide loans for water supply improvements, which increased the EPA's power to set mandates. This amendment created the "costs and benefits rule" to determine whether the cost of implementing new MCLs outweighs the health benefits. To maximize the costs and benefits of setting new MLCs, the EPA began allowing more affordable technology to be substituted that did not fully meet MLC standards because it was more affordable.

The EPA studied the pros and cons of lowering the arsenic MCL for years in the late 1980s and 1990s. No action was taken until January 2001, when the Clinton administration in its final weeks promulgated a new standard of 0.01 mg/L (10 ppb) to take effect January 2006.[27] The Bush administration suspended the midnight regulation, but after some months of study, the new EPA administrator Christine Todd Whitman approved the new 10 ppb arsenic standard and its original effective date of January 2006.[28] Many locations exceed this limit.[29] A 2017 Lancet Public Health study found that this rule change led to fewer cancer deaths.[30][31]

Many public water supply systems across the United States obtained their water supply from groundwater that had met the old 50 ppb arsenic standard but exceeded the new 10 ppb MCL. These utilities searched for either an alternative supply or an inexpensive treatment method to remove the arsenic from their water. In Arizona, an estimated 35 percent of water-supply wells were put out of compliance by the new regulation; in California, the percentage was 38 percent.[32]

The proper arsenic MCL continues to be debated. Some have argued that the 10 ppb federal standard is still too high, while others have argued that 10 ppb is needlessly strict. Individual states can establish lower arsenic limits; New Jersey has done so, setting a maximum of 0.005 mg/L (5 ppb) for arsenic in drinking water.[33]

A study of private water wells in the Appalachian mountains found that six percent of the wells had arsenic above the U.S. MCL of 0.010 mg/L.[34]

Case studies and incidents

Fallon, Nevada has long been known to have groundwater with relatively high arsenic concentrations (in excess of 0.08 mg/L).[35] Even some surface waters, such as the Verde River in Arizona, sometimes exceed 0.01 mg/L arsenic, especially during low-flow periods when the river flow is dominated by groundwater discharge.[36]

A study conducted in a contiguous six-county area of southeastern Michigan investigated the relationship between moderate arsenic levels and 23 disease outcomes. Disease outcomes included several types of cancer, diseases of the circulatory and respiratory system, diabetes mellitus, and kidney and liver diseases. Elevated mortality rates were observed for all diseases of the circulatory system. The researchers acknowledged a need to replicate their findings.[37]

Water purification solutions

Access to clean drinking water is fraught with political, socio-economic, and cultural inequities. In practice, many water treatment strategies tend to be temporary fixes to a larger problem, often prolonging the social issues while treating the scientific ones.[38] Scientific studies have shown that interdisciplinary approaches to water purification are especially important to consider, and long-lasting improvements involve larger perspectives than strict scientific approaches.[39]

Small-scale water treatment

A review of methods to remove arsenic from groundwater in Pakistan summarizes the most technically viable inexpensive methods.[40] Most small-scale treatments focus on water after it has left the distribution site, and are thus more focused on quick, temporary fixes.

A simpler and less expensive form of arsenic removal is known as the Sono arsenic filter, using three pitchers containing cast iron turnings and sand in the first pitcher and wood activated carbon and sand in the second.[41] Plastic buckets can also be used as filter containers.[42] It is claimed that thousands of these systems are in use and can last for years while avoiding the toxic waste disposal problem inherent to conventional arsenic removal plants. Although novel, this filter has not been certified by any sanitary standards such as NSF, ANSI, WQA and does not avoid toxic waste disposal similar to any other iron removal process.

In the United States small "under the sink" units have been used to remove arsenic from drinking water. This option is called "point of use" treatment. The most common types of domestic treatment use the technologies of adsorption (using media such as Bayoxide E33, GFH, activated alumina or titanium dioxide)[43] or reverse osmosis. Ion exchange and activated alumina have been considered but not commonly used.

Chaff-based filters have been reported to reduce the arsenic content of water to 3 μg/L (3 ppb). This is especially important in areas where the potable water is provided by filtering the water extracted from the underground aquifer.[44]

In iron electrocoagulation (Fe-EC), iron is dissolved nonstop using electricity, and the resulting ferric hydroxides, oxyhydoxides, and oxides form an absorbent readily attracted to arsenic. Current density, the amount of charge delivered per liter of water, of the process is often manipulated in order to achieve maximum arsenic depletion.[45] This treatment strategy has primarily been used in Bangladesh,[46] and has proven to be largely successful. In fact, using iron electrocoagulation to remove arsenic in water proved to be the most effective treatment option.[47]

Large-scale water treatment

In some places, such as the United States, all the water supplied to residences by utilities must meet primary (health-based) drinking water standards. Regulations may require large-scale treatment systems to remove arsenic from the water supply. The effectiveness of any method depends on the chemical makeup of a particular water supply. The aqueous chemistry of arsenic is complex, and may affect the removal rate that can be achieved by a particular process.

Some large utilities with multiple water supply wells could shut down those wells with high arsenic concentrations, and produce only from wells or surface water sources that meet the arsenic standard. Other utilities, however, especially small utilities with only a few wells, may have no available water supply that meets the arsenic standard.

Coagulation/filtration (also known as flocculation) removes arsenic by coprecipitation and adsorption using iron coagulants. Coagulation/filtration using alum is already used by some utilities to remove suspended solids and may be adjusted to remove arsenic.[48]

Iron oxide adsorption filters the water through a granular medium containing ferric oxide. Ferric oxide has a high affinity for adsorbing dissolved metals such as arsenic. The iron oxide medium eventually becomes saturated, and must be replaced. The sludge disposal is a problem here too.

Activated alumina is an adsorbent that effectively removes arsenic. Activated alumina columns connected to shallow tube wells in India and Bangladesh have removed both As(III) and As(V) from groundwater for decades. Long-term column performance has been possible through the efforts of community-elected water committees that collect a local water tax for funding operations and maintenance.[49] It has also been used to remove undesirably high concentrations of fluoride.

Ion exchange has long been used as a water softening process, although usually on a single-home basis. Traditional anion exchange resins are effective in removing As(V), but not As(III), or arsenic trioxide, which doesn't have a net charge. Effective long-term ion exchange removal of arsenic requires a trained operator to maintain the column.

Both reverse osmosis and electrodialysis (also called electrodialysis reversal) can remove arsenic with a net ionic charge. (Note that arsenic oxide, As2O3, is a common form of arsenic in groundwater that is soluble, but has no net charge.) Some utilities presently use one of these methods to reduce total dissolved solids and therefore improve taste. A problem with both methods is the production of high-salinity waste water, called brine, or concentrate, which then must be disposed of.

Subterranean arsenic removal (SAR) technology SAR Technology

In subterranean arsenic removal, aerated groundwater is recharged back into the aquifer to create an oxidation zone which can trap iron and arsenic on the soil particles through adsorption process. The oxidation zone created by aerated water boosts the activity of the arsenic-oxidizing microorganisms which can oxidize arsenic from +3 to +5 state SAR Technology. No chemicals are used and almost no sludge is produced during operational stage since iron and arsenic compounds are rendered inactive in the aquifer itself. Thus toxic waste disposal and the risk of its future mobilization is prevented. Also, it has very long operational life, similar to the long lasting tube wells drawing water from the shallow aquifers.

Six such SAR plants, funded by the World Bank and constructed by Ramakrishna Vivekananda Mission, Barrackpore & Queen's University Belfast, UK are operating in West Bengal. Each plant has been delivering more than 3,000 liters of arsenic and iron-free water daily to the rural community. The first community water treatment plant based on SAR technology was set up at Kashimpore near Kolkata in 2004 by a team of European and Indian engineers led by Bhaskar Sen Gupta of Queen's University Belfast for TiPOT.[50][51][52][53]

SAR technology had been awarded Dhirubhai Ambani Award, 2010 from IChemE UK for Chemical Innovation. Again, SAR was the winner of the St. Andrews Award for Environment, 2010. The SAR Project was selected by the Blacksmith Institute – New York & Green Cross- Switzerland as one of the "12 Cases of Cleanup & Success" in the World's Worst Polluted Places Report 2009. (Refer: www.worstpolluted.org).

Currently, large scale SAR plants are being installed in US, Malaysia, Cambodia, and Vietnam.

Nanotechnology based arsenic remediation

Nanomaterials with intrinsically high surface energy prepared using naturally abundant ingredients can be helpful in creating green products. Using nanomaterials, it is possible to effectively destroy microorganisms, adsorb arsenic and fluoride, remove heavy metals and degrade pesticides usually found in water.[54][55] Researchers have looked at new methods to synthesize iron oxide/hydroxide/oxyhydroxide compositions in the laboratory and used them for water purification. A product aptly titled, AMRIT,[56] meaning elixir in Indian languages, developed by the Indian Institute of Technology Madras, is an affordable water purification technology based on advanced materials, which has been validated through research articles[57][58] and patents[59][60][61][62][63][64][65][66][67][68] and has been approved for national implementation in India. The technology can remove several anions, especially arsenate and arsenite (two common species present in arsenic-contaminated water) and fluoride from water. Currently, this technology is delivering arsenic-free water to about 10,00,000 people every day.[69] AMRIT uses an adsorbent based on a simple method to maintain the metastable 2-line ferrihydrite (named as CM2LF) phase at room temperature, by confining it in biopolymeric cages.[58] It can handle concentrations of arsenic and colloidal iron reaching up to 100-800 µg/L and 50 mg/L, respectively and brings the output concentration below the permissible limit set by EPA of 10 µg/L and 200 µg/L, respectively. The arsenic adsorption capacity of the composite is 1.4 to 7.6 times better than the available compositions, in field conditions. Hundreds of units have been tested in the arsenic belt of India which are continuously running in the field for several years.[70] Complete water purification units in various capacities ranging from tens of liters to millions of liters have been implemented. AMRIT has been applied in various forms of community water purifiers, which are easy to use, have a low cost of maintenance and generates zero sludge. It can be operated at 300 LPH (liters per hour) to 100,000 LPH flow rates. The cost of clean water using this technology in the arsenic affected areas is under 2.5 paisa ($0.0006) per liter which includes the cost of the operator running the plant, necessary consumables, and electricity used for pumping and distribution. No electricity is needed for filtration. It can be implemented at any level - domestic, community, or municipal – levels anywhere in the world and can be integrated easily with other technologies.

The adsorption properties of CM2LF and its uptake mechanism have been investigated thoroughly.[71] Subsequent research on making this technology greener with further improvement in removal capacity and inclusion of sustainability metrics in the manufacture and operation has been reported.[72] In its entirety, AMRIT provides a compelling solution for achieving the United Nations millennium development goal of sustainable access to safe drinking water.

Dietary intake

Researchers from Bangladesh and the United Kingdom have claimed that dietary intake of arsenic adds a significant amount to total intake where contaminated water is used for irrigation.[73][74][75]

See also

References

  1. ↑ See:
  2. ↑ Smedley, PL; Kinniburgh, DG (2002). "A review of the source, behaviour and distribution of arsenic in natural waters" (PDF). Applied Geochemistry. 17 (5): 517–568. Bibcode:2002ApGC...17..517S. doi:10.1016/S0883-2927(02)00018-5.
  3. ↑ "Arsenic". www.who.int. Retrieved 2020-11-28.
  4. ↑ Mukherjee A.; Sengupta M. K.; Hossain M. A. (2006). "Arsenic contamination in groundwater: A global perspective with emphasis on the Asian scenario". Journal of Health, Population, and Nutrition. 24 (2): 142–163. JSTOR 23499353. PMID 17195556.
  5. ↑ Chowdhury U. K.; Biswas B. K.; Chowdhury T. R. (2000). "Groundwater arsenic contamination in Bangladesh and West Bengal, India". Environmental Health Perspectives. 108 (4): 393–397. doi:10.2307/3454378. JSTOR 3454378. PMC 1638054. PMID 10811564.
  6. ↑ Rodríguez-Lado L.; Sun G.; Berg M.; Zhang Q.; Xue H.; Zheng Q.; Johnson C.A. (2013). "Groundwater arsenic contamination throughout China". Science. 341 (6148): 866–868. Bibcode:2013Sci...341..866R. doi:10.1126/science.1237484. PMID 23970694. S2CID 206548777.
  7. ↑ Diaz, Oscar Pablo; Arcos, Rafael; Tapia, Yasna; Pastene, Rubén; Velez, Dínoraz; Devesa, Vicenta; Montoro, Rosa; Aguilera, Valeska; Becerra, Miriam (2015-05-22). "Estimation of Arsenic Intake from Drinking Water and Food (Raw and Cooked) in a Rural Village of Northern Chile. Urine as a Biomarker of Recent Exposure". International Journal of Environmental Research and Public Health. 12 (5): 5614–5633. doi:10.3390/ijerph120505614. PMC 4454988. PMID 26006131.
  8. ↑ Smedley P.L.; Kinniburgh D.G.; Macdonald D.M.J.; Nicolli H.B.; Barros A.J.; Tullio J.O.; Pearce J.M.; Alonso M.S. (2005). "Arsenic associations in sediments from the loess aquifer of La Pampa, Argentina". Applied Geochemistry. 20 (5): 989–1016. Bibcode:2005ApGC...20..989S. doi:10.1016/j.apgeochem.2004.10.005.
  9. ↑ Zheng, Y.; van Geen, A.; Stute, M.; Dhar, R.; Mo, Z.; Cheng, Z.; Horneman, A.; Gavrieli, I.; Simpson, H. J.; Versteeg, R.; Steckler, M. (2005-11-15). "Geochemical and hydrogeological contrasts between shallow and deeper aquifers in two villages of Araihazar, Bangladesh: Implications for deeper aquifers as drinking water sources". Geochimica et Cosmochimica Acta. 69 (22): 5203–5218. Bibcode:2005GeCoA..69.5203Z. doi:10.1016/j.gca.2005.06.001. ISSN 0016-7037.
  10. ↑ Zheng, Y.; Stute, M.; van Geen, A.; Gavrieli, I.; Dhar, R.; Simpson, H. J.; Schlosser, P.; Ahmed, K. M. (2004-02-01). "Redox control of arsenic mobilization in Bangladesh groundwater". Applied Geochemistry. Arsenic in Groundwater of Sedimentary Aquifers. 19 (2): 201–214. Bibcode:2004ApGC...19..201Z. doi:10.1016/j.apgeochem.2003.09.007. ISSN 0883-2927.
  11. ↑ Addy, Susan (Fall 2008). "Electrochemical Arsenic Remediation for Rural Bangladesh". University of California, Berkeley. Bibcode:2008PhDT.......160A.
  12. ↑ Uddin, Riaz; Huda, Naz Hasan (May 2011). "Arsenic Poisoning in Bangladesh". Oman Medical Journal. 26 (3): 207. doi:10.5001/omj.2011.51. ISSN 1999-768X. PMC 3191694. PMID 22043419.
  13. ↑ "How the West poisoned Bangladesh". The Independent. 2010-03-21. Retrieved 17 September 2017.
  14. ↑ "Bangladesh: 20 Million Drink Arsenic-Laced Water". Human Rights Watch. 2016-04-06. Retrieved 17 September 2017.
  15. ↑ Abedin, Mohammed Joinal; Feldmann, Jörg; Meharg, Andy A. (2002-03-01). "Uptake Kinetics of Arsenic Species in Rice Plants". Plant Physiology. 128 (3): 1120–1128. doi:10.1104/pp.010733. ISSN 0032-0889. PMC 152223. PMID 11891266.
  16. ↑ Singh A. K. (2006). "Chemistry of arsenic in groundwater of Ganges-Brahmaputra river basin" (PDF). Current Science. 91 (5): 599–606.
  17. ↑ David Bradley, "Drinking the water of death", The Guardian, 5 January 1995
  18. ↑ Amit Chatterjee; Dipankar Das; Badal K. Mandal; Tarit Roy Chowdhury; Gautam Samanta; Dipankar Chakraborti (1995). "Arsenic in ground water in six districts of West Bengal, India: the biggest arsenic calamity in the world. Part I. Arsenic species in drinking water and urine of the affected people". Analyst. 120 (3): 643–651. Bibcode:1995Ana...120..643C. doi:10.1039/AN9952000643.
  19. ↑ Dipankar Das; Amit Chatterjee; Badal K. Mandal; Gautam Samanta; Dipankar Chakraborti; Bhabatosh Chanda (1995). "Arsenic in ground water in six districts of West Bengal, India: the biggest arsenic calamity in the world. Part 2. Arsenic concentration in drinking water, hair, nails, urine, skin-scale and liver tissue (biopsy) of the affected people". Analyst. 120 (3): 917–925. Bibcode:1995Ana...120..917D. doi:10.1039/AN9952000917. PMID 7741255.
  20. ↑ New Scientist, Interview: Drinking at the west's toxic well 31 May 2006.
  21. 1 2 World Health Organization, Arsenic in Drinking Water, accessed 8 November 2021.
  22. ↑ Geen, A. van; Zheng, Y.; Versteeg, R.; Stute, M.; Horneman, A.; Dhar, R.; Steckler, M.; Gelman, A.; Small, C.; Ahsan, H.; Graziano, J. H. (2003). "Spatial variability of arsenic in 6000 tube wells in a 25 km2 area of Bangladesh". Water Resources Research. 39 (5): 1140. Bibcode:2003WRR....39.1140V. doi:10.1029/2002WR001617. ISSN 1944-7973.
  23. ↑ "Groundwater in 13 Districts of Bihar contaminated with Arsenic". Biharprabha News. Retrieved 25 September 2013.
  24. ↑ The Times of India, 'Use surface water. Stop digging', interview, 26 September 2004.
  25. ↑ "Nepal: Filters to provide arsenic-free drinking water — OWSA: OneWorld South Asia - Latest news on sustainable development, features, opinions, interviews with NGO leaders and..." Archived from the original on 2012-08-04. Retrieved 2011-01-19.
  26. ↑ "Arsenic in drinking water threatens up to 60 million in Pakistan". Science | AAAS. 2017-08-23. Retrieved 11 September 2017.
  27. ↑ The history of arsenic regulation, Southwest Hydrology, May/June 2002, p.16.
  28. ↑ EPA announces arsenic standard for drinking water of 10 parts per billion, EPA press release, 10/31/2001.
  29. ↑ Twarakavi, N. K. C.; Kaluarachchi, J. J. (2006). "Arsenic in the shallow ground waters of conterminous United States: assessment, health risks, and costs for MCL compliance". Journal of American Water Resources Association. 42 (2): 275–294. Bibcode:2006JAWRA..42..275T. doi:10.1111/j.1752-1688.2006.tb03838.x. Archived from the original on 5 January 2013.
  30. ↑ Bakalar, Nicholas (2017-10-24). "Arsenic Reductions in Drinking Water Tied to Fewer Cancer Deaths". The New York Times. ISSN 0362-4331. Retrieved 2017-10-26.
  31. ↑ Nigra, Anne E.; Sanchez, Tiffany R.; Nachman, Keeve E.; Harvey, David E.; Chillrud, Steven N.; Graziano, Joseph H.; Navas-Acien, Ana (2017-10-22). "The effect of the Environmental Protection Agency maximum contaminant level on arsenic exposure in the USA from 2003 to 2014: an analysis of the National Health and Nutrition Examination Survey (NHANES)". The Lancet Public Health. 2 (11): e513–e521. doi:10.1016/S2468-2667(17)30195-0. ISSN 2468-2667. PMC 5729579. PMID 29250608.
  32. ↑ Alison Bohlen (2002) States move forward to meet new arsenic standard, Southwest Hydrology, May/June 2002, p.18-19.
  33. ↑ Megan A. Ferguson and others, Lowering the detection limit for arsenic: implications for a future practical quantitation limit, American Water Works Association Journal, Aug. 2007, p.92-98.
  34. ↑ John G. Shiber, "Arsenic in domestic well water and health in Central Appalachia, USA"
  35. ↑ Frederick Rubel Jr. and Steven W. Hathaway (1985) Pilot Study for removal of arsenic from drinking water at the Fallon, Nevada, Naval Air Station, Environmental Protection Agency, EPA/600/S2-85/094.
  36. ↑ M. Taqueer A. Qureshi (1995) Sources of Arsenic in the Verde River and Salt River Watersheds, Arizona, M.S. thesis, Arizona State University, Tempe.
  37. ↑ Jaymie R. Meliker, Arsenic in drinking water and cerebrovascular disease, diabetes mellitus, and kidney disease in Michigan: a standardized mortality ratio analysis Environmental Health Magazine. Volume 2:4. 2007. Accessed 9 Sept. 2008.
  38. ↑ Johnston, Richard Bart; Hanchett, Suzanne; Khan, Mohidul Hoque (2010-01-01). "The socio-economics of arsenic removal". Nature Geoscience. 3 (1): 2–3. Bibcode:2010NatGe...3....2J. doi:10.1038/ngeo735.
  39. ↑ Karr, James R.; Dudley, Daniel R. (1981-01-01). "Ecological perspective on water quality goals". Environmental Management. 5 (1): 55–68. Bibcode:1981EnMan...5...55K. doi:10.1007/BF01866609. ISSN 0364-152X. S2CID 153568249.
  40. ↑ Fatima Hashmi and Joshua M. Pearce, "Viability of Small-Scale Arsenic-Contaminated Water Purification Technologies for Sustainable Development in Pakistan", Sustainable Development, 19(4), pp. 223–234, 2011. pdfOpen access full text
  41. ↑ "Evaluation of Performance of Sono 3-Kolshi Filter for Arsenic Removal from Groundwater Using Zero Valent Iron Through Laboratory and Field Studies" (PDF). (272 KiB)
  42. ↑ "Sono Arsenic Filter from Bangladesh" (PDF). Archived from the original (PDF) on 2012-02-06. Retrieved 2006-12-04. (102 KiB) – pictures with descriptions.
  43. ↑ Jing, Chuanyong; Liu, Suqin; Meng, Xiaoguang (2008-01-15). "Arsenic remobilization in water treatment adsorbents under reducing conditions: Part I. Incubation study". Science of the Total Environment. 389 (1): 188–194. Bibcode:2008ScTEn.389..188J. doi:10.1016/j.scitotenv.2007.08.030. ISSN 0048-9697. PMID 17897702.
  44. ↑ Newspaper article Archived 2012-04-17 at the Wayback Machine (in Hungarian) published by Magyar Nemzet on 15 April 2012.
  45. ↑ Addy, Susan E.A.; Gadgil, Ashok J.; Kowolik, Kristin; Kostecki, Robert (2009). "ElectroChemical Arsenic Removal (ECAR) for Rural Bangladesh—Merging Technology with Sustainable Implementation". doi:10.2172/982898. {{cite journal}}: Cite journal requires |journal= (help)
  46. ↑ van Genuchten, Case M.; Addy, Susan E. A.; Peña, Jasquelin; Gadgil, Ashok J. (2012-01-17). "Removing Arsenic from Synthetic Groundwater with Iron Electrocoagulation: An Fe and As K-Edge EXAFS Study". Environmental Science & Technology. 46 (2): 986–994. Bibcode:2012EnST...46..986V. doi:10.1021/es201913a. ISSN 0013-936X. PMID 22132945.
  47. ↑ Ratna Kumar, P; Chaudhari, Sanjeev; Khilar, Kartic C; Mahajan, S.P (2004). "Removal of arsenic from water by electrocoagulation". Chemosphere. 55 (9): 1245–1252. Bibcode:2004Chmsp..55.1245R. doi:10.1016/j.chemosphere.2003.12.025. PMID 15081765.
  48. ↑ Hering Janet G.; Katsoyiannis Ioannis A.; Theoduloz Gerardo Ahumada; Berg Michael; Hug Stephan J. (2017-05-01). "Arsenic Removal from Drinking Water: Experiences with Technologies and Constraints in Practice". Journal of Environmental Engineering. 143 (5): 03117002. doi:10.1061/(ASCE)EE.1943-7870.0001225.
  49. ↑ SARKAR, S; GUPTA, A; BISWAS, R; DEB, A; GREENLEAF, J; SENGUPTA, A (1 May 2005). "Well-head arsenic removal units in remote villages of Indian subcontinent: Field results and performance evaluation". Water Research. 39 (10): 2196–2206. doi:10.1016/j.watres.2005.04.002. PMID 15913703.
  50. ↑ 12 Cases of Cleanup & Success
  51. ↑ "World's Worst Polluted Places Report 2009"
  52. ↑ Scientific American
  53. ↑ Reuters Global
  54. ↑ Mukherjee, Sritama; Gupte, Tanvi; Jenifer, S; Thomas, Tiju; Pradeep, Thalappil (December 2019). Arsenic in Water: Speciation, Sources, Distribution, and Toxicology. Copyright © 2019 John Wiley & Sons, Inc. doi:10.1002/9781119300762.wsts0053. ISBN 9781119300762. S2CID 214108659.
  55. ↑ Mukherjee, Sritama; Gupte, Tanvi; Jenifer, S; Thomas, Tiju; Pradeep, Thalappil (29 December 2019). Arsenic in Water: Fundamentals of Measurement and Remediation. Copyright © 2019 John Wiley & Sons, Inc. doi:10.1002/9781119300762.wsts0054. ISBN 9781119300762. S2CID 212834619.
  56. ↑ "Arsenic free drinking water". Youtube. IIT Madras. Archived from the original on 2021-12-14. Retrieved 3 March 2020.
  57. ↑ Sankar, M. Udhaya; Aigal, Sahaja; Chaudhary, Amrita; S., Anshup; M. Maliyekkal, Shihabudheen; Kumar, A. Anil; Chaudhari, Kamalesh; Pradeep, T. (2013). "Biopolymer reinforced synthetic granular nanocomposites for affordable point-of-use water purification". Proc. Natl. Acad. Sci. 110 (21): 8459–64. Bibcode:2013PNAS..110.8459S. doi:10.1073/pnas.1220222110. PMC 3666696. PMID 23650396.
  58. 1 2 Kumar, A. Anil; Som, Anirban; Longo, Paolo; Sudhakar, Chennu; Bhuin, Radha Gobinda; Sen Gupta, Soujit; S., Anshup; Sankar, Mohan Udhaya; Chaudhary, Amrita; Kumar, Ramesh; Pradeep, T (2016). "Confined metastable 2-line ferrihydrite for affordable point-of-use arsenic-free drinking water". Adv. Mater. 29 (7): 1604260. doi:10.1002/adma.201604260. PMID 27918114.
  59. ↑ Pradeep, T.; Maliyekkal, Shihabudheen M.; S., Anshup; Sankar, M. Udhaya; Chaudhary, Amrita (2 December 2012). "Organic templated nanometal oxyhydroxide". Wo2011151725(A2).
  60. ↑ Pradeep, T.; Leelavathi, A.; Chaudhary, Amrita; Sankar, M. Udhaya; S., Anshup (31 July 2018). "Multilayer organic-templated-boehmite-nanoarchitecture for water purification". Us 10035131B2.
  61. ↑ Pradeep, T.; Sankar, M. Udhaya; Chaudhary, Amrita; Kumar, A. Anil; S., Anshup (14 December 2018). "Water filled organic templated metal oxide/hydroxide/oxyhydroxide particle network for water purification and a device thereof". In304463.
  62. ↑ Pradeep, T.; Chaudhary, Amrita; Sankar, M. Udhaya; S., Anshup (28 February 2018). "One container gravity fed storage water purifier". In293515.
  63. ↑ Pradeep, T.; Kumar, A. Anil; Sankar, M. Udhaya; Chaudhary, Amrita; S., Anshup (1 October 2019). "A granulation composition for powder ingredients". In322218.
  64. ↑ Pradeep, T.; Sankar, M. Udhaya; S., Anshup; Chaudhary, Amrita (31 March 2017). "Gravity-fed axial flow filter block for domestic water purifiers and the method of making the same". In282257.
  65. ↑ Pradeep, T.; Chaudhary, Amrita; Sankar, M. Udhaya; S., Anshup (2012). "Single container gravity-fed storage water purifier". Il229223A.
  66. ↑ Maliyekkal, Shihabudheen M.; S., Anshup; Pradeep, T. (10 June 2019). "Removal of fluoride, alkalinity, heavy metals and suspended solids simultaneously adsorbent synthesis, adsorbent composition and a device for affordable drinking water". In313917.
  67. ↑ Pradeep, T; Mukherjee, Sritama; Kumar, A. Anil (22 December 2017). "Method for preparing cellulose microstructures-templated nanocomposites with enhanced arsenic removal capacity and a purifier thereof". Wo2018122878A1.
  68. ↑ Pradeep, Thalappil; Mukherjee, Sritama; Kumar, A. Anil. "A method for preparing cellulose microstructures-templated nanocomposites with enhanced arsenic removal capacity, 201641044817, December 26, 2016, granted as patent no. IN337979 on June 4, 2020". {{cite journal}}: Cite journal requires |journal= (help)
  69. ↑ "Jeevajalam - Arsenic free drinking water - Documentary". Youtube. Archived from the original on 2021-12-14.
  70. ↑ "Jeevajalam II - How a few villages in Punjab managed arsenic and iron-free water". Youtube. Archived from the original on 2021-12-14.
  71. ↑ Sudhakar, Chennu; Kumar, A. Anil; Bhuin, Radha Gobinda; Sen Gupta, Soujit; Natarajan, Ganapati; Pradeep, T (2018). "Species-specific uptake of arsenic on confined metastable 2-line ferrihydrite: A combined Raman-XPS investigation of the adsorption mechanism". ACS Sustain. Chem. Eng. (6): 9990–10000. doi:10.1021/acssuschemeng.8b01217. S2CID 52952113.
  72. ↑ Mukherjee, Sritama; Kumar, A. Anil; Sudhakar, Chennu; Kumar, Ramesh; Ahuja, Tripti; Mondal, Biswajit; Pillalamarri, Srikrishnarka; Philip, Ligy; Pradeep, Thalappil (2019). "Sustainable and affordable composites built using microstructures performing better than nanostructures for arsenic removal". ACS Sustain. Chem. Eng. 7 (3): 3222–3233. doi:10.1021/acssuschemeng.8b05157. S2CID 104350518.
  73. ↑ Mustak Hossain (2006-07-13). "Toxic rice harvested in southwestern Bangladesh". SciDev.Net.
  74. ↑ Williams, P.N.; Islam, M. R.; Adomako, E. E.; Raab, A.; Hossain, S. A.; Zhu, Y. G.; Feldmann, J.; Meharg, A. A. (2006). "Increase in Rice Grain Arsenic for Regions of Bangladesh Irrigating Paddies with Elevated Arsenic in Groundwaters". Environ. Sci. Technol. 40 (16): 4903–4908. Bibcode:2006EnST...40.4903W. doi:10.1021/es060222i. PMID 16955884.
  75. ↑
    • Raghvan T. "Screening of Rice Cultivars for Grain Arsenic Concentration and Speciation". American Society of Agronomy Proceeding.

Further reading

This article is issued from Offline. The text is licensed under Creative Commons - Attribution - Sharealike. Additional terms may apply for the media files.