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332   Industrial Wastewater Treatment, Recycling, and Reuse


          production of tea in India is approximately 857,000 tonnes, which is 27.4%
          of the total world production (Wasewar et al., 2008). It is said that 100 kg of
          green tea leaves produces 22 kg of dry mass on average and  18 kg tea goes
          for marketing. The remaining 4 kg of dry tea material is therefore wasted
           ¸
          (Cay et al., 2004). The amount of TW produced annually by the factories
          after processing is believed to be thousands of tonnes in India alone.


          8.2.2 Preparation and Activation of the Adsorbent
          The standard procedure for preparation of raw untreated samples for utiliza-
          tion as adsorbents involves washing, color removal, drying, powdering, and
          sieving to the desired sizes. Color removal is required so that interference can
          be avoided from water-soluble fractions of the sample under study. Surface
          activation of the adsorbent surface is necessary because it increases the surface
          area, porosity, and number of functional groups that are known to enhance
          the adsorption process. The activation procedure can involve either physical
          or chemical activation. The selection of the time and temperature of activa-
          tion needs to be optimized by characterizing the surface properties, such
          as surface area of the adsorbents obtained by treating the raw materials for
          different intervals of time and temperature. For the studies reported here,

          the activation temperature of 500 C was chosen as an optimum temperature

          because the products obtained at a temperature higher or lower than 500 C
          exhibited lower adsorption capacity, which is probably due to the collapse of
          the surface functional groups. In addition, all adsorbents were sieved to a
          particle size of 200–300 B.S.S. mesh size for use in adsorption studies.
             Physical activation has two forms: (1) carbonization of the material in an
          inert atmosphere and (2) activation of the char at high temperatures in the
          presence of carbon dioxide or steam (Ahmad et al., 2007). In the activation
          process, the density as well as the number of the pores can increase, and amor-
          phous decomposition products such as tars are burned off. However, the yield
          of the adsorbent is low in this method of activation, and thus the method is less
          preferred. This method is not included in the present study.
             Chemical activation is carried out by impregnation of chemical agents
          followed by pyrolysis in an inert atmosphere at a high temperature. The pur-
          pose of activation here is to enhance the adsorption efficiency besides car-
          bonizing the raw precursor without the evolution of huge amounts of fumes
          as in the case of physical methodology. Chemical activation is a preferred
          method over physical activation due to comparatively lower temperatures
          of 400–700 C. Also, the yield is higher since carbon burnoff is not required.
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