Page 143 - Materials Chemistry, Second Edition
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124                         Life Cycle Assessment of Wastewater Treatment


           strong and semi-strong wastes and may contain pharmaceutical items from sources
           such as unused medicines, soda pops, and other personal care items. Once disposed
           of into landfills, pharmaceutical items may be either used by microorganisms or
           incorporated into waste solids; however, the greater part are broken down in land-
           fill leachate (Musson and Townsend, 2009). The anaerobic conditions in landfills
           and nearby receiving groundwater are likely to reduce the biodegradation of natural
           compounds in leachate and groundwater, resulting in the diversity and stability of
           pharmaceutical items in groundwater (Erses et al., 2008).


           7.4.2  sepTic sysTeMs
           Septic systems, or on-site wastewater treatment systems, can likewise be critical
           sources of pharmaceutical items entering nearby surface water and groundwater.
           Septic systems are a typical way of taking care of wastewater in rural areas, and
           the crust underneath them can stretch out tens to hundreds of meters, defiling the
           groundwater and the environment. They allow water used locally to be dealt with
           and reused to recharge nearby groundwater supplies, thus possibly allowing pharma-
           ceuticals inadequately treated in septic frameworks to enter the underground water
           body.


           7.4.3  veTerinary Drugs
           The use of veterinary medications to prevent sickness and increase the profitability
           of producing domesticated animals is a developing concern and is possibly a path-
           way for natural pollution. For the most part, veterinary anti-microbials cannot be
           totally ingested or processed in vivo. Roughly 50%–100% of the anti-infective agents
           used are discharged through urine and feces, stored in waste tidal ponds, and after
           that discharged into the surrounding biological community, representing a potential
           danger to groundwater (Kim et al., 2011). The use of veterinary medication–con-
           taminated fertilizer for preparation may likewise result in the contamination of fun-
           damental groundwater (Hu et al., 2010).


           7.4.4  rivers anD lakes
           Sewage beginning with the water treatment plants is the most significant source
           of pharmaceuticals in common water bodies, followed by rural release and direct
           release. Pharmaceuticals in the stream or lake are adsorbed onto the dirt/residue,
           become diluted, and experience organic or potentially photochemical changes.
           Categories of pharmaceuticals determined in rivers in India are listed in Table
           7.2. The Cooum River, which runs through the metropolitan city of Chennai
           (population 8.9 million), was found to be contaminated with triclocarban (6.18
           µg/L), ibuprofen (2.32  µg/L), a carboxylic acid metabolite of an antiplatelet
           drug (1.37 µg/L), atenolol (3.18 µg/L), and amphetamine (0.984 µg/L) (Subedi
           et al., 2015).
              Ampicillin, ciprofloxacin, gatifloxacin, sparfloxacin, and cefuroxime were
           found  in  the  Yamuna  River  at  13.8,  1.4,  0.48,  2.1,  and  1.7  μg/L,  respectively
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