Groundwater Geochemistry. Группа авторов
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Naresh K. Sethy Department of Chemical Engineering and Technology Indian Institute of Technology (BHU) Varanasi Uttar Pradesh India
Rahul Sharma Academy of Scientific and Innovative Research (AcSIR) CSIR‐National Physical Laboratory campus New Delhi India
Sushil Kumar Shukla Department of Transport Science and Technology Central University of Jharkhand Ranchi Jharkhand India
Anubhuti Singh Institute of Environment and Sustainable Development Banaras Hindu University Varanasi Uttar Pradesh India
Baljinder Singh Department of Biotechnology Panjab University Chandigarh India
Deepali Singh School of Environmental Sciences Jawaharlal Nehru University New Delhi India
Gurudatta Singh Institute of Environment and Sustainable Development Banaras Hindu University Varanasi Uttar Pradesh India
Priyanka Singh Institute of Environment and Sustainable Development Banaras Hindu University Varanasi Uttar Pradesh India
Sanchita Singhal Academy of Scientific and Innovative Research (AcSIR) CSIR‐National Physical Laboratory campus New Delhi India
Saurabh Kumar Singh School of Environmental Sciences Jawaharlal Nehru University New Delhi India
K. S. Sista Research and Development Tata Steel, Jamshedpur Jharkhand India
Srinivasa Gowd Somagouni Department of Geology Yogi Vemana University Kadapa Andhra Pradesh India
Arun Lal Srivastav Chitkara University School of Engineering and Technology Chitkara University Solan, Himachal Pradesh India
Anupma Thakur Academy of Scientific and Innovative Research (AcSIR) Ghaziabad Uttar Pradesh India Central Scientific Instruments Organisation Chandigarh India
Amit Kumar Tiwari Department of Chemical Engineering Birla Institute of Technology Mesra, Ranchi Jharkhand India
Dhanesh Tiwary Department of Chemistry IIT (BHU) Varanasi Uttar Pradesh India
Anamika Tripathi Pollution Ecology Research Laboratory Department of Botany Hindu College Moradabad Uttar Pradesh India
Ashutosh Tripathi Amity Institute of Environmental Sciences Amity University Noida, Uttar Pradesh India
Vinod Kumar Tripathi Department of Farm Engineering Institute of Agricultural Sciences Banaras Hindu University Varanasi Uttar Pradesh India
B. Verma Department of Chemical Engineering and Technology Indian Institute of Technology (BHU) Varanasi Uttar Pradesh India
Anusha Vishwakarma Department of Environmental Science Central University of Jharkhand Ranchi Jharkhand India
Chandrashekhar Azad Vishwakarma TERI School of Advanced Studies New Delhi India
Monika Yadav Department of Environmental Studies Faculty of Science The Maharaja Sayajirao University of Baroda Vadodara Gujarat India
1 Geogenic Pollutants in Groundwater and Their Removal Techniques
Jyoti Kushawaha and Deeksha Aithani
School of Environmental Sciences, Jawaharlal Nehru University, New Delhi, India
1.1 Introduction
Water resources are one of the essential resources of nature. Being fluid, water’s nature allows it to flow into the low‐pressure zone from the high pressure. On the surface, it is found in the geographical form of rivers and streams, and it flows with varying pace depending on the gravity, pressure, and geography of the area. The contact time of water with its geographical space is lower due to pace in surface water flow, and this is the reason it has far fewer or negligible geogenic contaminants compared to anthropogenic contaminants. In contrast, the subsurface water moves at a very slow pace (a few millimetres a day) through the pore spaces or cracks of the soil and rocks. Sometimes the water becomes stagnant, like in perched aquifers and in the impermeable hard rock terrains. This very low movement of aquifer waters (groundwater) allows more time for water to interact with the surrounding natural environment, which may be hard rock, soft rock, or soil and enriched with the geogenic constituents. The groundwater contamination largely depends on the soil geochemistry through which water travelled before reaching the aquifers (Achary 2014a). Hydrological processes are important in governing groundwater contamination. Minerals mobilize in the aquifer system in response to the constituents and minerals present in the rock matrix and their depositional history, along with geochemical conditions (Garduño et al. 2011).
Approximately 1.5 billion people are dependent on underground sources of water (Mukherjee et al. 2012); this is why geogenic pollution has become a major threat to groundwater contamination. Groundwater contaminated by the rock–water interaction has resulted in geologically induced constituents such as As, F, Fe, Mn, Se, Cr, etc. Long‐term intake of F‐contaminated groundwater leads to severe fluorosis, both dental and skeletal, as well as a range of non‐skeletal effects. As‐contaminated water caused severe health effects such as arsenicosis, skin cancer, respiratory problems, and other cancers. The commonly used remedial techniques for the removal of As and F from groundwater are membrane separation, ion exchange resins, coagulation‐precipitation (also known as Nalgonda technique), and adsorption filter beds. It is essential to understand the operational parameters before adopting these potential techniques for remediation such as the local water demand, water quality parameters, initial concentration, and daily basis water use patterns. As‐contamination is highest in the Indo‐Gangetic plain in the eastern and northeastern parts of India.
Geogenic contaminants, including arsenic, fluoride, and iron are commonly observed in nature. In India, the foremost geogenic contamination in aquifers is Arsenic and Fluoride (Garduño et al. 2011). Other contaminants include nitrate, phosphate, heavy metals and trace metals which may result of the human activities including domestic savage, septic tank, industrial effluents and agricultural practises (Madhav et al. 2018). In India, there are several states and districts which are affected by geogenic contamination such as Arsenic (10 states and 68 districts), Fluoride (20 states and 276 districts), and Iron (24 states and 294 districts) (CGWB 2014).
1.2 Arsenic
Arsenic is overarching with a variable amount in the Earth's crust, mostly in the form of arsenate and arsenite (WHO 2011). In water, generally, it is present as arsenate (As V) in oxidizing condition and as arsenite (As III) form in reducing condition. The fresh biomass, rainfall infringement in the recent alluvium may be the reason for the evacuation of As and Fe from the sediments or soils (Aulakh et al. 2009; Raju et al. 2012). It is introduced in water via different sources such as the dissolution of minerals, rocks, and soil, mining activity (mining waste), mineral smelting, coal combustion, industrial effluents, and through the dry and wet deposition of atmosphere's dust. It is used commercially as the alloy in the formation of semiconductors and in other electricals. Moreover, it used as a preservative for wood, and industrially in the textile, paper, and glass industries for processing. It is also used in pharmaceuticals, food additives, and pesticides