18-Env-B5 Industrial & Hazardous Waste Management · May 2016
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
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; Basel Convention on the Control of Transboundary Movements of Hazardous Wastes (1989); Canadian Nuclear Safety Commission (CNSC) regulations on radioactive waste; provincial hazardous waste regulations (e.g. BC's Environmental Management Act and Hazardous Waste Regulation).
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.
| Characteristic | Municipal (domestic) | Industrial — cannery | Hazardous |
|---|---|---|---|
| Flow pattern | Steady, predictable diurnal pattern | Seasonal/batch (harvest-driven), can be highly intermittent | Often low-volume, batch or intermittent |
| BOD5 strength (assumed, mg/L) | ~200–300 | ~1000–2000 (organic-rich) | Highly variable; BOD often secondary to toxicity |
| TSS strength (assumed, mg/L) | ~200–250 | ~500–1500 (peels, pulp) | Variable; may include process solids/sludge |
| Toxicity | Low | Low to moderate (low if food-grade process only) | High (heavy metals, solvents, cyanide, etc.) |
| Biodegradability | Highly biodegradable | Highly biodegradable | Often poorly biodegradable / can inhibit biological treatment |
| Regulatory regime | Municipal sewer-use bylaw | Sewer-use bylaw + possible pretreatment order | Full hazardous-waste manifest/tracking regulation |
How waste management would differ, and why: