Pollution Prevention
and Control Technologies for Plating Operations
Section 3 - Chemical Recovery
3.4 ION EXCHANGE
3.4.8 Residuals Generation
The primary residuals from ion exchange recovery processes are
the regenerants (eluates) and backwash solutions. The regenerants
are concentrated wastes and the backwash is dilute. Both solutions
are either caustic or acidic, depending on the resin type and
application. High metal bearing regenerates (typically cation
resin) are: (1) sometimes reused directly in the bath; (2) further
processed to recover the metal (e.g., electrowinning); (3) waste
treated; or (4) sent to an off-site recovery facility. Low metal
bearing regenerants (typically anion resin) and backwash solutions
are typically treated on-site. Waste treatment processes generate
sludge that is an EPA listed hazardous waste (F006).
The volume of regenerant produced will depend on the regeneration
requirement (e.g., lbs of acid per ft3 of resin) and the concentration
of acid used (typically 1 to 5%). The regeneration requirement
will depend on the resin type, application (metal or complex being
recovered) and the configuration (cocurrent vs counterflow). Typical
volumes of regenerant are 20 to 50 gal/ft3 of resin. The volume
of regenerant waste is sometimes reduced by reusing the last portion
of the regenerant, which will be less contaminated with metal
and contains free acid. Backwash volumes depend mostly on the
equipment design and the application. Typically, backwashing generates
25 to 75 gal/ft3. The backwash is partly reused by some equipment
vendors as make-up water for regenerant, in an effort to reduce
the total waste volume generated. Because backwash contains only
dilute concentrations of pollutants it is typically not a major
concern and is treated on-site and discharged. However, for shops
working toward zero discharge, the backwash volume could present
a significant problem. Both backwash and regenerant can processed
by evaporation to reduce the volume requiring disposal. However,
this increases the capital and operating costs of the system.
Also, evaporation of hazardous wastes is sometimes regulated as
a RCRA technology and may require a permit to operate.
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