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18-Env-B5 Industrial & Hazardous Waste Management · May 2014

Question 10 of 18: Removing Metals From Industrial Wastewater

Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)

Notes on this paper

Reference texts: Nemerow & Dasgupta, Industrial and Hazardous Waste Treatment, 2nd ed.; Metcalf & Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed.; Davis & Cornwell, Introduction to Environmental Engineering, 6th ed.; LaGrega, Buckingham & Evans, Hazardous Waste Management, 2nd ed.; CCME, Guidelines for the Management of Biomedical Waste in Canada (1992); Canadian Environmental Protection Act (CEPA), 1999; provincial Environmental Protection / Hazardous Waste Regulations (e.g. BC's Hazardous Waste Regulation, O.Reg. 347 in Ontario).

All eighteen questions are compulsory on this paper and are answered in full below.

Question 10: Removing Metals From Industrial Wastewater (4 marks)

Question text not reproduced: the examination questions are © Engineers and Geoscientists BC. Open the official past paper (linked at the top of this page) to read the question, then follow the worked solution below.

The standard approach is chemical precipitation followed by solid–liquid separation. Most heavy metals form highly insoluble hydroxides at an elevated pH, so the wastewater is dosed with an alkali (lime, Ca(OH)2, or caustic soda, NaOH) to raise the pH into the metal's minimum-solubility range, converting the dissolved metal ion into an insoluble hydroxide precipitate; a polymer coagulant/flocculant is then added to aggregate the fine precipitate into a settleable floc, which is removed by clarification (gravity settling) and, for a final polish, filtration. Example: chromium removal from an electroplating rinse water. Hexavalent chromium (Cr6+, as chromate/dichromate) does not precipitate directly as a hydroxide, so it is first chemically reduced to the trivalent form (Cr3+) using sulfur dioxide or sodium metabisulfite under acidic conditions ($\text{pH}\approx2$–3): $$2\,CrO_4^{2-} + 3\,SO_2 + 4\,H^+ \rightarrow Cr_2(SO_4)_3\text{-type products} + \dots$$ the pH is then raised to about 8–9 with lime, precipitating Cr(OH)3, which settles out as a hydroxide sludge that is dewatered and disposed of as a hazardous (or, where permitted and economical, metal-recovery) waste. Other common metals (Cu, Zn, Ni, Cd) are removed by the direct hydroxide-precipitation step without the reduction stage, each at its own optimum precipitation pH; sulfide precipitation and ion exchange are alternative technologies used where a lower residual metal concentration or metal recovery is specifically required.