Arsenic Contamination Needs Serious Attention: An Opinion and Global Scenario
Abstract
:1. Introduction
2. Global Status and Impact (Continent-Wise)
2.1. Origins of Arsenic Contamination
2.1.1. Anthropogenic Sources
- 1.
- Mining and smelting: These processes can release large amounts of arsenic into the air and water, contaminating ecosystems present nearby and posing health risks to communities residing in proximity to such activities [22].
- Tailings and waste disposal: Improper disposal of mining waste and tailings can lead to the release of arsenic into surrounding environments, exacerbating contamination.
- Airborne dispersal: The airborne dispersion of arsenic during mining and smelting operations poses a threat to air quality and can contribute to widespread environmental contamination.
- 2.
- Industrial effluents: Industrial processes, including the production of chemicals, metals, and semiconductors, can discharge arsenic-containing wastewater into rivers and streams, presenting a serious global concern [23].
- Unregulated discharge: Lack of proper regulations and treatment facilities can result in uncontrolled discharge of arsenic-containing effluents, exacerbating the contamination of water bodies.
- Cumulative impact: The cumulative impact of multiple industrial activities in a region can significantly amplify the overall arsenic burden in aquatic ecosystems.
- 3.
- Coal combustion: Burning coal for energy production releases arsenic into the air, significantly contributing to the severe contamination of water, soil, and environmental resources [24].
- Coal ash disposal: Improper disposal of coal ash, containing concentrated arsenic, poses a direct risk to soil and water resources, leading to prolonged contamination.
- Atmospheric deposition: Arsenic released into the air during coal combustion can undergo atmospheric deposition, further contaminating terrestrial and aquatic environments.
- 4.
- Agricultural practices: The use of arsenic-based pesticides and herbicides in agriculture stands out as a major source of soil and water contamination, especially in regions with intensive agricultural activities [25].
- Runoff and leaching: Arsenic-based chemicals in agriculture can contribute to soil contamination through runoff and leaching, impacting water quality in nearby water bodies.
- Residue accumulation: Persistent accumulation of arsenic residues in soils, resulting from prolonged agricultural use, poses a continuous threat to crop quality and human health.
2.1.2. Geogenic Sources
- Geographical variability: The prevalence of arsenic in groundwater exhibits geographical variability, with certain regions being more susceptible to natural arsenic contamination [26].
- Hydrogeological factors: Hydrogeological conditions, such as the presence of certain minerals and the type of aquifers, play a crucial role in arsenic mobilisation in groundwater [26].
2.1.3. Biogenic Sources
2.2. Impacts of Arsenic Contamination
2.2.1. Environmental Ramifications
- Biodiversity loss: The disruption of ecosystems due to arsenic accumulation can lead to biodiversity loss, affecting various plant and animal species.
- Food chain contamination: Arsenic entering aquatic environments can contaminate the food chain, with potential cascading effects on higher trophic levels.
- Long-term soil effects: The persistence of arsenic in soil can have enduring effects, affecting the long-term productivity and health of terrestrial ecosystems.
2.2.2. Health Impacts on Humans
- Residential proximity: Communities residing in close proximity to arsenic-contaminated water sources face a higher risk of chronic health issues due to prolonged exposure.
- Vulnerable populations: Children, pregnant women, and individuals with compromised immune systems may be more vulnerable to the adverse health effects of arsenic exposure.
- Mitigation challenges: Implementing effective mitigation measures is challenging, especially in resource-limited regions, exacerbating the health risks associated with arsenic contamination.
2.3. Continent-Wise Breakdown of Arsenic Contamination
2.3.1. Asia
- Bangladesh: Bangladesh is one of the countries most severely affected by arsenic contamination. Millions of people in rural areas depend on groundwater for drinking and a high amount of naturally occurring arsenic has led to widespread health problems [33].
- India: Arsenic contamination is a concern in several Indian states, particularly in the Ganges-Brahmaputra delta region. West Bengal and Bihar are among the worst affected areas. Arsenic contamination in communities across India has surged by ~145% in the past seven years [34]. Also, arsenic contamination has been reported in some districts of Uttar Pradesh, Punjab, Assam, and Jharkhand.
- Vietnam: Some regions in Vietnam, including the Mekong Delta, have reported arsenic-contaminated groundwater, posing a risk to the population’s health.
2.3.2. South America
- Argentina: Around four million individuals in Argentina are exposed to excessive amounts of As in their drinking water. Elevated amounts (>1000 µg/L) of As have been identified in the Chaco-Pampean Plains and Cuyo sections of the Andes, which are located in the country’s centre and northwestern regions, respectively [35].
- Chile: Arsenic contamination is also prevalent in parts of northern Chile, with contaminated areas in regions such as Atacama and Antofagasta, primarily linked to mining activities. It poses environmental risks to local ecosystems and underscores the importance of responsible mining practices.
- Bolivia: Bolivia faces arsenic contamination challenges in regions with a history of mining, such as the Cerro Rico mountain in Potosí. The mining of silver, tin, and other minerals has resulted in arsenic pollution in soil and water. Furthermore, industrial activities and agricultural practices contribute to arsenic contamination in various parts of the country.
- Peru: Arsenic contamination in Peru is a significant concern in mining regions such as the Andean highlands and the Amazon rainforest. The extraction of copper, gold, and other minerals has led to the release of arsenic into the environment. Additionally, informal gold mining operations, known as artisanal and small-scale gold mining (ASGM), contribute to arsenic pollution in soil and water [36,37].
2.3.3. North America
- The United States: Arsenic contamination is not as widespread in the U.S., but certain areas, such as parts of the American Southwest, have reported elevated arsenic levels in groundwater, mainly due to geological factors. Historically tied to mining activities in Western U.S. states like Arizona and California, arsenic pollution has affected both water sources and local communities, highlighting the importance of stringent regulations and ongoing remediation efforts in the USA, where over 2 million people use drinking water from private wells with As concentrations exceeding the regulatory limit of 10 µg/L [38,39]. Approximately 7% of the sampled wells exhibited arsenic concentrations surpassing the maximum contaminant level (MCL) of 10 µg/L. Notably, the southwest region raised the most substantial concern, with approximately 16% of the tested drinking water wells surpassing the MCL for As concentration [40].
- Canada: In Canada, regions such as British Columbia and the Yukon Territory have grappled with arsenic contamination due to mining operations, necessitating vigilant monitoring and mitigation measures. Despite being geographically limited, these contamination cases emphasise the need for continued environmental protection and public health initiatives in affected areas. The Canadian government has implemented measures to monitor and mitigate arsenic pollution in the affected areas.
2.3.4. Africa
- Nigeria: Arsenic contamination has been reported in some regions of Nigeria, particularly in the northwestern part of the country. This contamination is often associated with the presence of arsenic-rich geological formations.
- Ethiopia: Some areas within Ethiopia, especially in the Great Rift Valley region, have experienced arsenic contamination in groundwater.
- Tanzania: Arsenic contamination has been reported in various parts of Tanzania, including the Dodoma area and other regions with geological conditions conducive to arsenic release into groundwater.
2.3.5. Europe
- Hungary: Hungary has faced arsenic contamination issues in groundwater sources, primarily in the northeastern region.
- Romania: Arsenic contamination in Romania has been a concern, particularly in regions with a history of mining, such as Maramureș, and due to incidents like the Baia Mare cyanide spill in 2000 [45]. Efforts to address contamination include stricter regulations and remediation measures in affected areas.
- Croatia: Arsenic contamination in Croatia’s part of the Pannonian Basin is notable in regions with historical mining activity, such as Sisak-Moslavina County. Additionally, industrial zones around cities like Osijek and Vukovar face arsenic pollution challenges. Efforts are underway to remediate contaminated sites and promote sustainable agricultural practices to reduce arsenic inputs in these areas.
- Serbia: Serbia’s part of the Pannonian Basin, particularly around the Bor mining complex in eastern Serbia, faces significant arsenic pollution due to historical mining activities. Industrial zones in cities like Belgrade and Novi Sad also contribute to arsenic contamination in soil and water. Remediation efforts and improved industrial waste management practices are being implemented to address arsenic pollution in these regions [46].
2.3.6. Australia
2.3.7. Antarctica
3. Detection and Removal Methods
3.1. Detection Methods
3.2. Extraction Methods
4. Mitigation Approaches and Future Perspectives
4.1. Education and Public Awareness
4.2. Safe Water Supply Provision
4.3. Management of Agricultural Practices
4.4. Innovative Approaches Applied to Extraction
4.5. Regulatory Measures and Controls
5. Conclusions
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
References
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Continent | Countries Affected | Proportion of Globally Affected Areas | Proportion of Total Global Affected Population |
---|---|---|---|
Asia | 31 | 64% | 94% |
South America | 9 | 14% | 1.6% |
North America | 11 | 10% | 0.6% |
Africa | 20 | 9% | 3.7% |
Oceania | 4 | 2% | 0.01% |
Europe | 31 | 1% | 0.2% |
Method | Principle | Detection Range | Cost | Time Required | Advantages | Disadvantages |
---|---|---|---|---|---|---|
AAS | Absorption of arsenic-specific wavelengths | 1 µg/L to 1 mg/L | Moderate | Minutes | High sensitivity and specificity | Requires specialised equipment |
ICP-MS | Ionisation and mass analysis | 0.1 µg/L to 1 mg/L | High | Minutes | Exceptional sensitivity and accuracy | Expensive, complex, and time-consuming |
HPLC | Separation and quantification | 1 µg/L to 1 mg/L | Moderate | Minutes to hours | Can separate various arsenic species | Complex instrumentation and setup |
XRF | Excitation and detection of X-ray emissions | 1 mg/L to 100 mg/L | Moderate | Seconds | Non-destructive; useful for solid samples | Limited to bulk sample analysis |
Colorimetric sensors | Chemical reaction and formation of coloured change | 1 µg/L to 1 mg/L | Low | Minutes | Portable and easy to use | Limited to qualitative or semi-quantitative results |
Electrochemical sensors | Detection via electrochemical reactions (using different types of nanomaterials) | 1 µg/L to 1 mg/L | Low to Moderate | Minutes | Portable, rapid results, and low cost | May require electrode maintenance |
Biosensors | Use biological components for detection | 1 µg/L to 1 mg/L | Variable | Minutes | High specificity and potential for multiplexing | Limited to specific biological components, may require maintenance |
Method | Description | Advantages | Disadvantages |
---|---|---|---|
Coagulation and filtration | Addition of coagulants to form flocs and remove arsenic by filtration. | Effective for both As(III) and As(V), relatively low cost, and suitable for large-scale treatment. | Requires regular maintenance and monitoring of coagulant dosing; produces sludge that requires proper disposal. |
Adsorption | Use of adsorbent materials to capture arsenic on their surface. | Highly effective, relatively low operational costs, and can be used at both point-of-use and point-of-entry. | Limited capacity of adsorbents; requires periodic regeneration or replacement. |
Ion exchange | Use of ion exchange resins to exchange arsenic ions with other ions in the resin. | Highly effective for both As(III) and As(V); suitable for both small-scale and large-scale systems. | Requires regeneration or replacement of ion exchange resins; release of regenerant chemicals needs proper management. |
Reverse osmosis (RO) | Use of a semipermeable membrane to remove arsenic and other impurities by forcing water through the membrane. | Highly effective at removing arsenic; suitable for small-scale treatment and point-of-use systems. | Relatively high operational costs, generates wastewater, and requires maintenance of the RO system. |
Sedimentation | Allowing particles to settle out of the water after coagulation–flocculation. | Low cost and simple. | Requires sufficient settling time. |
Electrocoagulation | Passing an electric current through water to destabilise and coagulate arsenic particles. | Effective for both arsenic(III) and arsenic(V), reduced sludge production compared to conventional coagulation, and has potential for automation. | Requires electricity, maintenance of electrodes, and appropriate monitoring and control. |
Biological treatment | Use of specific bacteria to convert arsenic from soluble to insoluble form for removal. | Can be environmentally friendly and cost-effective. | Slower treatment process; requires specific conditions and careful monitoring. |
Solar oxidation and precipitation | Oxidise arsenic using sunlight and remove it by coagulation or filtration. | Low-cost method with minimal chemical use. | Weather-dependent; may require longer contact times. |
Zero-valent iron (ZVI) | Use of zero-valent iron media to reduce and adsorb arsenic from water. | Effective for As(V) removal. Relatively low-cost technology. | Limited efficacy for As(III) removal, making pre-oxidation necessary. Maintenance and replacement of iron media. |
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Bhat, A.; Ravi, K.; Tian, F.; Singh, B. Arsenic Contamination Needs Serious Attention: An Opinion and Global Scenario. Pollutants 2024, 4, 196-211. https://doi.org/10.3390/pollutants4020013
Bhat A, Ravi K, Tian F, Singh B. Arsenic Contamination Needs Serious Attention: An Opinion and Global Scenario. Pollutants. 2024; 4(2):196-211. https://doi.org/10.3390/pollutants4020013
Chicago/Turabian StyleBhat, Abhijnan, Kamna Ravi, Furong Tian, and Baljit Singh. 2024. "Arsenic Contamination Needs Serious Attention: An Opinion and Global Scenario" Pollutants 4, no. 2: 196-211. https://doi.org/10.3390/pollutants4020013
APA StyleBhat, A., Ravi, K., Tian, F., & Singh, B. (2024). Arsenic Contamination Needs Serious Attention: An Opinion and Global Scenario. Pollutants, 4(2), 196-211. https://doi.org/10.3390/pollutants4020013