A critical review on various remediation approaches for heavy metal contaminants removal from contaminated soils
Graphical abstract
Introduction
Owing to the fast industrialization and overpopulation during the last few decades, there has been a massive increase in xenobiotic components including metals in the environment (Qin et al., 2020). The excessive entry of these components into the environment leads to human and environmental health issues. Even at low concentrations, heavy metals affect plants, soil, humans, plants, and animals, because these metal wastes are generally toxic in nature (Priya and Nagan, 2015; Elizabeth Rani et al., 2021). Due to various pollution exposures into the environment, the air, water, and land get contaminated. Air pollution can impact the quality of soil and water resources significantly (ECCC, 2013). Soil pollution occurs when pollutants, such as heavy metals, hydrocarbons, and pesticides, are released or disposed of. By contaminating precipitation and falling into water and soil habitats, air pollution can have an impact on the quality of soil and water bodies (Manisalidis et al., 2020). Water pollution can contribute to soil pollution and vice versa (Ahmed and Sulaiman, 2001; Lu et al., 2015). Harmful substances from wastewater can permeate into the soil from the water bodies. These may impose serious consequences on human health and the environment (Ashbolt, 2015). Subsequently, there are many new blooming advances to the recycling/re-use of wastewater. This effluent must be cleaned and recycled according to the most basic requirements, such as usability, recycling and cost. This is a major concern for developing nations (Jawed et al., 2020).
Wastewater usually contains toxins, such as cleansers, pesticides, prepared nourishment, drugs, and, organic/inorganic toxins (e.g. heavy metals and organic or inorganic salts). The improper disposal of wastewater into the environment contaminates the soil. The spectrum of nonbiodegradable heavy metals, such as chromium (Cr), cadmium (Cd), lead (Pb), mercury (Hg), iron (Fe), arsenic (As) and selenium (Se), brings exceptional prosperity but also frequent issues. There is also an insistent need for these metals to be separated from wastewater to make wastewater reusable. Traditional innovations remain accessible for effective remediation, for example, substance precipitation, surface adsorption (Jawed et al., 2020), film filtration (Chen et al., 2018; Naghdali et al., 2019), particle trade, photocatalysis, and flocculation. In all these methods, the most capable method to remove heavy metals from wastewater is the adsorption on nanomaterials because other methods do not adequately remove such heavy metals and their cut-off emphasis has pursued appropriate clearing (Hasan et al., 2018; Meepho et al., 2018). This would decrease the accumulation of waste metals into the soil underneath.
It is therefore vital to deploy advanced and site-specific remediation technologies that can effectively and safely remediate soils polluted by heavy metals (Ok et al., 2020). In the last several decades, different soil remediation technologies have been implemented (Murtaza et al., 2014; Sabir et al., 2015; Khan et al., 2021). These methods focus on decreasing the maximum and/or bioavailable heavy metal concentrations in the soil and their possible mechanisms in the food supply chain (Bhargava et al., 2012; Hou et al., 2020). Traditional methods for remediating heavy metals from polluted soils are based on physical, chemical, and biological methods that can be used to remediate contaminated soil in conjunction with each other. The majority of these methods, despite their high performance, are expensive, environmentally harmful, and time-consuming (Ahmed et al., 2021). Financial and technological effects and challenges have made soil clean-up a difficult job. The realistic application of these traditional methods to remediate soils poses many limitations and a certain degree of threats.
This present review examines the various technologies currently available for heavy metal remediation in terms of mechanisms, advantages, drawbacks, applicability, and costs. This review examines the methods for treating heavy metal-contaminated soils using physicochemical, biological, and techniques that combine these approaches, as well as the potential toxicity of metals after treatment, the interaction of metals with soil constituents, the difficulties of using this modification for site remediation, and potential opportunities. This review has also focused on remediation strategies for soils polluted with heavy metals, which include essential things required to properly remediate contaminated soils. This includes particular approaches that are implemented and being used at various locations. This paper explores the origins and risks of heavy metals in the soil and addresses methods and influencers for microbial remediation thereby this offers a valuable guide for restoring the health of the soil ecosystem. The data are used to determine the most useful remedial technology for the treatment of contaminated soils. This study will be of great use to industrial site owners who are tainted by long-term historical waste. This study has also focused on farmers with soils that are currently polluted with metal and are interested in improving the quality of their goods, or to urban gardeners who intend to improve the quality of the land.
Section snippets
Heavy metals and their pollution
Many heavy metals are dangerous in nature since they can easily aggregate in soils, dust and water, posing a serious impact on the environment. For instance, if the polluted farmland soil is exposed to heavy metal contaminants, these contaminants can be rapidly transferred to the surrounding water environment (e.g. surface water and groundwater) (Khan et al., 2015). As a result, these toxic metal poses many hazardous impacts in regards to the agricultural products, accumulate inside the food
Remediation methods for extracting heavy metals
Heavy metals are converted into various forms after they have been released into the environment. Their accessibility decreases versus their resting duration in the soil (Li et al., 2018). Types of exchangeable metals and aqueous solvents are considered suitable for plants. Due to their presence of toxic circumstances, these heavy metals can be remedied again from soil (Caussy et al., 2003). Table 2 evaluates the benefits and drawbacks of these developments in remediation.
Future challenges and prospects
Soil contamination by heavy metals has occurred through man-made activities at millions of sites with a total of 20 million hectares of land. Heavy metal soil pollution appears to be of crucial importance, given the possible consequences on human and environmental life, as a result of rapid industrialization and urbanization. Cultivation through industrial effluents, for instance, has contributed to a wide area of agricultural land being contaminated but has indirectly contributed to crop
Conclusion
The evaluation of remediation strategies used to clean up polluted soil discovered that the efficiency of these procedures was below expectations. The multiple technical and economical components of remediation make it tough. As a result, typical soil remediation methods are ineffective on polluted areas. Heavy metal removal from polluted soil is an expensive and time-consuming technique. Furthermore, the extra pollutants released into the environment by these cleanup approaches are limited.
Credit author statement
Saravanan Rajendran: Conceptualization, Writing - Original Draft, Formal analysis, Funding acquisition; Investigation; Methodology; Project administration; Resources. T A.K. Priya: Conceptualization, Formal analysis. Kuan Shiong Khoo: Writing - Review & Editing, Investigation, Visualization. Tuan K.A. Hoang: Writing - Review & Editing. Hui-Suan Ng: Writing - Review & Editing. Heli Siti Halimatul Munawaroh: Writing - Review & Editing. Ceren Karaman: Writing - Review & Editing. Yasin Orooji:
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
The author (SR) acknowledges the support of ANID through the project ANID/FONDAP/1511001. The author (AKP) grateful to KPRIET for providing resources and infrastructure for the preparation of this article. This work was supported by the Fundamental Research Grant Scheme, Malaysia [FRGS/1/2019/STG05/UNIM/02/2] and MyPAIR-PHC-Hibiscus Grant [MyPAIR/1/2020/STG05/UNIM/1]. This work was also supported by the UCSI University Research and Innovation Grant under project code [REIG-FAS-2020/028]. This
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