18-Env-A6 Solid Waste Engineering and Management · May 2015
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
Reference texts: Tchobanoglous, Theisen & Vigil, Integrated Solid Waste Management: Engineering Principles and Management Issues; Vesilind, Worrell & Reinhart, Solid Waste Engineering; Davis & Cornwell, Introduction to Environmental Engineering (6th ed.); Freeze & Cherry, Groundwater; CCME, Guidance Document on Landfill Gas Management; Canadian Environmental Protection Act, 1999.
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.
Aerobic composting requires several design considerations to be controlled together, because each governs a different limiting factor in the microbial decomposition process. Carbon-to-nitrogen (C:N) ratio, ideally 25–30:1, balances the carbon needed for microbial energy against the nitrogen needed for cell synthesis; it is important because a ratio outside this range either starves the population of nitrogen (slow, incomplete decomposition) or supplies excess nitrogen that volatilizes as odorous ammonia. Moisture content, targeted at 50–60% by weight, is important because water is the medium in which microbial metabolism occurs — too little halts activity, too much displaces the pore air needed for aerobic respiration and creates anaerobic, malodorous zones. Aeration/oxygen supply, provided by periodic turning or forced/passive aeration, must keep interstitial oxygen above roughly 5%; it is important because composting is fundamentally an aerobic process, and inadequate oxygen shifts the pile to slower, odour-generating anaerobic pathways.
Particle size and porosity govern both the surface area available for microbial attack and the free air space that allows oxygen to diffuse into the pile; particle size is therefore reduced by shredding (to accelerate decomposition) while a bulking agent (wood chips, yard trimmings) is often added to preserve structural porosity, since over-shredding a wet feedstock collapses the pore structure. Temperature is important both as a process indicator (thermophilic temperatures of 55–65 °C confirm active decomposition) and as a public-health control — most regulatory frameworks (e.g., CCME guidance, provincial organics-management regulations) require a sustained minimum temperature for a specified duration to achieve pathogen and weed-seed kill before the compost is deemed a finished, marketable product. Finally, pH (optimal 6–8) and turning frequency/retention time are managed to keep the process within the range microorganisms tolerate and to ensure every part of the pile passes through the required time-temperature regime, not just its hottest core.