Arsenic contamination, effects and remediation techniques: A special look onto membrane separation processes
Graphical abstract
Introduction
Arsenic (As), the 20th most abundant element, has become a worldwide concern (Chai, 2019). As is mostly associated with igneous and sedimentary rocks, particularly sulfidic ores (Chai, 2019). Natural phenomena for instance weathering, biological and volcanic activity, along with anthropogenic activities (such as mining, fossil fuels burning, pesticide and herbicide application and crop desiccants) are responsible for the leakage of arsenic into the ecosphere. Arsenic exists mainly in four oxidation states: arsine (As3−), arsenic (As°), arsenite (As3+) and arsenate (As5+), besides the environmental forms including arsenious acids, arsenic acids, methylarsenic acid, dimethylarsinic acid, arsine, among others.
Arsenic has been detected in both inorganic and organic forms in groundwater, surface water and sediments (Borba et al., 2004; Dsikowitzky et al., 2013; Dummer et al., 2015; Klassen et al., 2009; Liang et al., 2016; Nickson et al., 2005). Furthermore, several studies have reported the presence of organoarsenic compounds in fish and other aquatic fauna and flora (Grotti et al., 2008; Jankong et al., 2007). In the environment, human arsenic exposure may occur through ingestion, inhalation, or absorption through the skin, however, ingestion is the predominant type of arsenic exposure. Various As effects were described due to short-term and long-term exposure, these include respiratory (Gerhardsson et al., 1988; Hopenhayn-Rich et al., 1998; Mazumder et al., 1997; Milton et al., 2001), hepatic (Guha Mazumder, 2001; Naqvi et al., 1994; Santra et al., 2000, 1999), neurological (Bansal et al., 1991; Chhuttani et al., 1967; Grantham and Jones, 1977; Wagner et al., 1979), renal (Gerhardt et al., 1978; Hopenhayn-Rich et al., 1998; Shiobara et al., 2001), reproductive (Léonard and Lauwerys, 1980; Squibb and Fowler, 1983), mutagenetic (Astolfi et al., 1981; Bencko et al., 1988) among others. Furthermore, emerging evidence suggests that cofactors such as genetics, diet, and other environmental exposures are important determinants of arsenic toxicity in moderately exposed populations (Watson, 2015). As a consequence of this widespread contamination and given the effects and toxicity, the World Health Organization (WHO) has set a guideline for 10 μg/L as the drinking water standard.
Because exposure to low levels of As can be fatal to human health, and given the increasingly strict legislation, treatment of contaminated water is critical. Removal of As is highly dependent on the polluted water's chemistry and composition. In most of the reported major incidences As occurs as As(III), therefore, an As(III) to As(V) oxidation stage is considered necessary in most cases in order to achieve the satisfactory results. It is important to notice that most drinking water treatment plants (DWTP) uses simple physical-chemical processes such as oxidation followed by coagulation-flocculation. This route for As treatment has several drawbacks such as low removal efficiency and the formation of by-products (for example, oxidation byproducts and arsenical sludge) can be a further potential source for secondary As pollution. In fact, DWTPs are not conventionally designed aiming for arsenic removal. Some of the most used technologies will be discussed in this review, such as, oxidation, coagulation-flocculation, adsorption, ion exchange and, in particular, membrane technologies.
A concise overview of the current knowledge of arsenic occurrence, effects and mostly the treatment options, focusing on membrane separation processes is presented. A systematic literature search was carried out in Web of Science comprising the Web of Science core database; Derwent innovations index; KCI-Korean journal database; Russian science citation index and SciELO citation index using combinations of keywords including arsenic, removal, occurrence, drinking water treatment plants (DWTP), ion exchange, membrane separation processes (MSP), reverse osmosis (RO), nanofiltration (NF), adsorbents, biosorption, oxidation, forward osmosis (FO), membrane distillation (MD), electrodialysis (ED), among others. The cited references were also checked to find more relevant studies. This combined databased resulted in 11,605 articles between 1945−2019. The areas that accounted for more than 80 % of the total articles were engineering, environmental sciences, chemistry, water resources, toxicology, and public environmental occupational health. In Fig. 1 the concern for this topic is highlighted by the exponential growth in publications containing the aforementioned keywords. Lastly, from this database, further selection was made based on article relevance, date and importance, these comprised to more than 200 studies that were consulted and cited in this work.
Section snippets
Arsenic sources, occorrence and mobilization
Arsenic is a naturally occurring metalloid whose presence can be intensified due to industrial and anthropic activities. Under natural oxidation conditions, dissolved arsenic tends to be sequestered by secondary minerals, in particular by adsorption on mineral clays, iron and manganese oxyhydroxides (Yang et al., 2015). However, As species can be easily desorbed under alkaline conditions and, therefore, concentrations above those established by regulatory agencies (WHO: 10 μg/L (Ravenscroft et
Exposure pathways and effects
Essentially, humans can be exposed to As by three different pathways; via direct consumption of drinking water; via consumption of contaminated food – where the exposure by drinking water is not elevated; and via respiratory for dust and fumes. The exposure via dermal absorption can be disregarded when compared to other exposure pathways because the rates of dermal absorption are generally low (<10 %) (Mandal and Suzuki, 2002). Currently, the first exposure pathway is known as the major source
Remediation technologies
Given the effects that exposure to arsenic has, the importance of remediation technologies is highlighted. In order to reduce the health risk posed by direct intake of As polluted drinking water or by consumption of food grown in soil irrigated with As contaminated water, strategies need to be established to mitigate the toxicity and availability of As from soil to food. Below, the methods coagulation/flocculation, adsorption, ion exchange, and membrane separation processes will be covered, and
Future perspectives
For more than centuries, the access to high quality drinking water has been crucial for the society development and growth. Not only is easy to perceive our dependence on water resources, but also the limitation in attaining potable standards in a near term. As water becomes scarcer, alternatives have been sought to attain current and future requirement in an old and never-ending discussion. While predicting the future demand and ability to provide drinking water would be challenging, recent
Concluding remaks
Considering arsenic occurrence and its contamination effects, it is necessary to propose effective treatment forms. Drinking water treatment plants, most of them based on conventional treatment process, were not design for As removal, and for that reason it is still found in drinking water in concentrations above the recommendation by several environmental agencies and health organizations. Because of that, advanced treatment as the membrane separation processes have standing due to its
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This research was funded by Coordination of Superior Level Staff Improvement (CAPES); National Council for Scientific and Technological Development (CNPq); Foundation for Research Support of the State of Minas Gerais (FAPEMIG).
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