Process for sodium sulfide/ferrous sulfate treatment of hexavale

Liquid purification or separation – Processes – Making an insoluble substance or accreting suspended...

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210715, 210720, 210724, 210726, 210748, 210913, 423 55, C02F 152, C02F 170

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050008595

DESCRIPTION:


DESCRIPTION
DETAILED DESCRIPTION OF THE INVENTION

While the invention will be described primarily as related to processing waste streams from an electroplating facility, it will be appreciated that the process is useful for any waste stream containing appreciable amounts of heavy metal in order to minimize sludge generation. The reduction of hexavalent chromium (Cr.sup.+6) to trivalent chromium (Cr.sup.+3), while important in treating waste water comprising electroplating effluent, is not by itself the primary point of invention herein. The thrust of the invention is the treatment of metal bearing waste water in a novel process wherein significantly lower quantities of sludge are produced than is possible using conventional waste water treating processes.
Environmental Protection Agency (EPA) imposed limits for heavy metal concentrations in effluent from waste treatment plants at the Air Logistics Centers (ALCs) are set forth in TABLE I.


TABLE I ______________________________________ Concentration Constituent (mg/L) ______________________________________ Cadmium, Total 0.03 Chromium, Total 1.0 Chromium, Hexavalent 0.1 Copper, Total 0.1 Lead, Total 0.1 Nickel, Total 1.0 Zinc, Total 1.0 ______________________________________
Since 1980, the EPA has classified sludges bearing concentrations of such metals above permit limits as hazardous wastes and have required disposal in hazardous waste landfills, typically at a cost greater than $168 per ton. While certain processes, such as sludge dewatering, have been implemented to reduce the amount of sludge produced, no processes to date have been effective to reduce appreciably the amounts of generated sludge.
The commercially available Sulfex.TM. process is intended for precipitation of heavy metals, (not Cr.sup.+6 reduction) and produces a greater quantity of sludge than the conventional acid/SO.sub.2 /lime process. The process described in U.S. Pat. No. 4,705,639 referred to above is directed to a waste treatment scheme similar to that described herein; that prior process assumes 90-100% efficiency in transfer of electrons from a donor source to a selective recipient in a waste water stream containing many different and competitive ions. Such a process efficiency is not practical, and substantial excesses over stoichiometric quantities of treatment constituents may be required to effectively precipitate most heavy metal.
The invention can be illustrated by the following examples performed in demonstration of the invention and in definition of the process parameters thereof.


EXAMPLE I

Analyses were made of Cr.sup.+6 reduction and heavy metal removal in distilled water and electroplating wastes. Jar tests were conducted using Phipps and Bird six-paddle stirrer with an illuminated base. Beakers were filled with 800 ml of distilled water and 10 ml of a 2,000 milligrams per liter (mg/L) Cr.sup.+6 solution. The pH of each solution was adjusted with either caustic or lime. Appropriate volumes of 1,000 mg/L S.sup.-2 solution (Na.sub.2 S/9H.sub.2 O) was added to each beaker. The solutions were stirred at 100 rpm while the pH of each was adjusted as desired. After six minutes of stirring, the appropriate volume of a 1,000 mg/L ferrous solution (as FeSO.sub.4 /7H.sub.2 O) was added. It may be noted here that in the practice of the invention described herein the ferrous ion may be added in the form either as sulfate or chloride. The volume was brought to 1,000 ml with distilled water and pH adjusted again while the solutions were stirred at 100 rpm. After six minutes. mixing was slowed to 20 rpm for two minutes, during which period final pH adjustments were made. Stirring was stopped and the solutions were allowed to stand for two minutes. If required, the solution was filtered using a funnel with a cotton plug.
Cr.sup.+6 was determined using the 1,5-diphenyl carbohydrazide method and standard Hach Chemical Company procedures. Ferrous concentration was determined using the Hach procedures for the 1,10-phenanthroline method. Sulfide was determined using the Hach procedu

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