Page 112 - Plant design and economics for chemical engineers
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88  PLANT  DESlGN  AND ECONOMICS FOR CHEMICAL ENGINEERS
       TABLE 10
       Comparative requirements for processing 1700 lb BOD  /  day by various
       aerobic systems
                                             Biological loading
        System               Area, acres     lb  BOD/lOOO   ft3  BOD removal,  %

        Stabilization  pond    57t            0.09-0.23           70-90
        Aerated  lagoon        5.75s          1.15-1.60          80-90
        Activated sludge
         Extended              0.23          11.0-30.0            95:
         Conventional          0.08          33.0-400             90
         High rate             0.046         57.0-150             70
        Trickling  filter
         Rock                  0.2-0.5       0.7-50              40-70
         Plastic disks         0.02-0.05     20-200              50-70

           t 5 ft deep
           $  loftdeep



       aerobic systems, anaerobic treatment is more sensitive to toxic materials and is
       more difficult to control.


        Solid  Waste  Disposal
       Solid wastes differ from air and water pollutants since these wastes remain at
       the point of origin until a decision is made to collect and dispose of them. There
        are several means of disposal available including recycling, chemical conversion,
        incineration, pyrolysis, and landfill. Federal regulations, local conditions, and
       overall economics generally determine which method is the most acceptable.

       RECYCLING  AND  CHEMICAL  CONVERSION.  Resource recovery is a factor often
       overlooked in waste disposal. For example, specific chemicals may often be
       recovered by stripping, distillation, leaching, or extraction. Valuable solids such
       as metals and plastics can be recovered by magnets, electrical conductivity,
       jigging, flotation, or hand picking. Process wastes may at times also be converted
       to saleable products or innocuous materials that can be disposed of safely. The
       former would include hydrogenation of  organics  to produce fuels, acetylation of
       waste cellulose to form cellulose acetate, or nitrogen and phosphorus enrich-
       ment of wastes to produce fertilizer.

       INCINERATION.  The controlled oxidation of solid, liquid, or gaseous com-
       bustible wastes to final products of carbon dioxide, water, and ash is known as
       incineration. Since sulfur and nitrogen-containing waste materials will produce.
       their corresponding oxides, they should not be incinerated without considering
       their effect on air quality. A variety of incinerator designs are available.
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