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18-Env-B5 Industrial & Hazardous Waste Management · May 2017

Question 1 of 19: Plan of Action for a Land-Constrained 50% Expansion

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; Canadian Nuclear Safety Commission (CNSC) regulations on radioactive waste under the Nuclear Safety and Control Act; provincial hazardous waste regulations (e.g. BC's Environmental Management Act and Hazardous Waste Regulation).

Question 1: Plan of Action for a Land-Constrained 50% Expansion (10 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.

With the footprint fixed and no acquisition or relocation possible, the only lever left is to make the existing treatment train, and the waste it has to treat, work harder within the same envelope. As the consultant I would build the plan of action around two parallel tracks — reduce the load the plant actually has to handle, and increase the treatment capacity achievable within the current tankage — rather than any single fix, since a 50% production increase rarely translates into a 50% treatment-load increase if source controls are applied first.

  1. Waste minimization audit first. Conduct an in-plant material balance/waste survey of every process stream before touching the treatment plant — a genuine reduction in generated BOD/TSS/flow reduces the capacity gap the plant has to close.
  2. Water reuse and counter-current rinsing. Cascade rinse waters and recycle treated effluent for non-potable uses (washdown, cooling makeup) to cut hydraulic loading growth well below the 50% production increase.
  3. Stream segregation. Separate concentrated, low-volume streams from dilute, high-volume ones so each can be treated (or recovered) by the process best suited to it, instead of diluting a recoverable stream into the whole flow.
  4. Check the plant's real hydraulic/organic headroom. Many plants are designed with a safety margin or peaking factor; a capacity audit (SOR, F/M, SRT, weir loading against as-built ratings) may show more spare capacity than the nameplate flow suggests.
  5. Intensify treatment within the existing tankage. Convert conventional activated sludge to a higher-rate configuration (raise MLSS, add fixed-film media such as IFAS/MBBR to boost biomass density per m3, or step up aeration capacity) so the same tank volume treats a higher load.
  6. Upgrade clarification and solids-liquid separation. Replace conventional clarifiers with high-rate plate/tube settlers or dissolved-air flotation, or add membrane filtration (MBR), to raise hydraulic throughput per unit of footprint.
  7. Equalization instead of new tankage. Add or repurpose a tank as a flow/load equalization basin so peak loads (not just the average) are attenuated, letting the downstream biological stage be sized on a lower design load.
  8. Off-site disposal for the increment. Investigate a surcharge/discharge agreement to send the incremental flow (raw or pretreated) to the municipal sewer if the municipal plant has spare capacity, rather than expanding on-site treatment at all.
  9. Phased production scheduling. Where feasible, stagger batch operations so the peak instantaneous waste load is spread over more hours, reducing the peak design flow the fixed footprint must accommodate.
  10. Vertical and below-grade siting. Where no additional plan-area exists, evaluate stacking process units vertically or installing below-grade tankage on the existing site to add hydraulic capacity without a larger footprint.

These measures are presented roughly in the order I would pursue them — minimization and reuse first because they are the cheapest and reduce the problem at its source, followed by process intensification, then equalization and off-site options, with new below-grade or vertical construction as a last resort inside the existing boundary. The final plan would combine several of these rather than relying on any single measure, and would be documented in a technical memorandum submitted to the regulator early in the process to confirm the approach is acceptable before capital is committed.

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