Page 255 - Materials Chemistry, Second Edition
P. 255

236                         Life Cycle Assessment of Wastewater Treatment


              A wide assortment of agricultural waste and residues has been investigated for the
           removal of heavy metals. This chapter assesses the practicality of using agricultural
           waste biomass for heavy metal removal in light of

              •  Heavy metal adsorption limits of agricultural waste biomass
              •  The impacts of working parameters for process advancement
              •  Adsorption instruments
              •  Change strategies for creating better adsorbents


           11.5.4  MeMbrane filTraTion
           Membrane filtration innovations with various sorts of films indicate awesome guar-
           antee for heavy metal removal due to their high efficiency, simple operation, and
           space-saving features (Kurniawan et al., 2006; Barakat and Schmidt, 2010). The
           membrane forms used to remove metals from wastewater are ultra-filtration (UF),
           reverse osmosis (RO), nanofiltration, and electro-dialysis.

           11.5.4.1  Ultra-Filtration
           UF is a membrane procedure working at low transmembrane weights for the removal
           of dispersed and colloidal material. UF uses films that permit the passage of water
           and low–atomic weight solutes while retaining macromolecules and hydrated metal
           particles, which are bigger than the pore size of the membrane (Samper et al., 2009).
           Since the pore sizes of UF films are bigger than dispersed metal particles as hydrated
           particles or as low–atomic weight constructions, these particles would easily pass
           through UF films. To achieve high removal efficiency for metal particles, micel-
           lar enhanced ultra-filtration (MEUF) and polymer improved ultra-filtration (PEUF)
           have been proposed.
              MEUF has turned out to be a successful separation strategy to remove metal
           particles from wastewater. This separation strategy uses the addition of surfactants
           to wastewater. Whenever the concentration of surfactants in fluid systems is above
           the critical micelle concentration (CMC), the surfactant particles will assemble into
           micelles that can bind metal particles to form extensive metal-surfactant structures
           (Landaburu-Aguirre et al., 2009). The micelles containing metal particles can be
           retained by a UF film with pore sizes smaller than micelle sizes, while the untrapped
           species promptly go through the UF film. To achieve the best results, surfactants of
           electric charge opposite to that of the particles to be removed must be used. Sodium
           dodecyl sulfate (SDS), an anionic surfactant, is regularly chosen for the compre-
           hensive removal of heavy metal particles in MEUF. For MEUF, a surfactant is used
           to make micelles, while for complexation–ultrafiltration, complexation agents, for
           example, poly(ethylenimine) (PEI) and poly(acrylic acid), are used to specifically
           bind cations.
              PEUF has likewise been proposed as an achievable strategy to separate an awe-
           some assortment of metal particles from fluid streams. PEUF uses water-solvent
           polymer to complex metallic particles and form a macromolecule having a higher
           sub-atomic weight than the sub-atomic weight cut-off of the film. The macromol-
           ecules will be retained when they are pumped through UF film. From that point
   250   251   252   253   254   255   256   257   258   259   260