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

      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

      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

       Jyoti Kushawaha and Deeksha Aithani

       School of Environmental Sciences, Jawaharlal Nehru University, New Delhi, India

      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).

      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).

      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

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