18-Env-A6 Solid Waste Engineering and Management · December 2018
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.); 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.
i. Aerobic composting of organic municipal waste. Aerobic composting is the controlled biological decomposition of the putrescible (biodegradable organic) fraction of MSW by mesophilic then thermophilic microbial populations in the presence of oxygen, converting biodegradable organics plus O₂ into CO₂, H₂O, heat and a stabilized, humus-like end product. It requires the process to be held within workable ranges of moisture (≈50–60%), carbon-to-nitrogen ratio (≈25–30:1) and aeration (turning or forced air) as it passes through a mesophilic → thermophilic (55–65°C, sufficient for pathogen and weed-seed destruction) → curing sequence. Its significance is twofold: it diverts a large, highly putrescible fraction of MSW away from landfill disposal — directly reducing the methane generation described in Question 4(a) and extending remaining landfill airspace — and it produces a marketable soil amendment, giving the diversion program a revenue offset rather than a pure cost. Increasingly it is also a regulatory requirement, with several Canadian provinces now banning organics from landfill disposal outright.
ii. Landfill leachate. Leachate is the liquid that percolates through the refuse mass once infiltrating precipitation, the waste's own initial moisture and water released by decomposition together exceed the refuse's field capacity; as it moves through the waste it dissolves and entrains contaminants, arriving at the base of the cell with high BOD₅/COD, elevated ammonia-nitrogen, dissolved solids and, depending on the waste stream, heavy metals and chlorinated organics. Its significance is that it is the single greatest uncontrolled environmental liability of a landfill — left unmanaged it migrates to groundwater or surface water — which is why the composite liner and leachate collection system shown in Question 3(a) exist specifically to intercept and route it to treatment. Leachate strength and composition are not static: they evolve through the five biological phases described in Question 5, so a leachate management system must be designed for decades of changing character, not a single fixed influent quality.
iii. Landfill closure and post-closure care. Closure is the set of engineered activities performed at the end of a cell's or site's active operating life — placing a final low-permeability cap and drainage layer, grading the surface for positive drainage, establishing vegetated topsoil, and capping or tying-off remaining gas and leachate infrastructure. Post-closure care is the extended monitoring and maintenance period that follows — typically 25–30 years under most provincial regulation — during which leachate collection and treatment continue, landfill gas is still monitored and collected/flared, groundwater monitoring wells are sampled on a fixed schedule, and the cap is inspected and repaired as it settles. Its significance is that waste continues generating leachate and gas for decades after the last load is placed (see Question 5), so closure and post-closure care are not optional cleanup but an integral, must-be-funded phase of the facility's design life; regulators require an approved closure/post-closure plan and financial assurance (a bond or trust fund) before an operating permit is even issued, which protects the public from an abandoned, unmonitored site.
iv. Windrow and aerated static pile composting techniques. Both are mechanical means of supplying the aeration and moisture control that aerobic composting needs. In the windrow method, feedstock is formed into long, triangular or trapezoidal piles roughly 1–2 m high that are periodically turned by a mechanical windrow turner, which re-introduces oxygen, releases excess heat and re-homogenizes moisture and temperature across the pile. In the aerated static pile (ASP) method, the pile is built once over a network of perforated pipes connected to a blower; forced or induced air supplies oxygen without physically turning the material, and the pile is often finished with a layer of screened compost or a biofilter cover to control odour and insulate against heat loss. Their significance lies in the design tradeoff each represents: windrow composting needs more land and mobile turning equipment but has a lower capital cost, while ASP has a smaller footprint and tighter process control (temperature and airflow can be monitored and adjusted directly) with generally lower odour release, at a higher capital cost — a choice a design engineer makes based on available land, budget and proximity to sensitive receptors (see Question 2(b)).
v. Key concerns with a landfill. The principal engineering and management concerns are: leachate generation and the groundwater/surface-water contamination risk it carries if the liner and collection system underperform; landfill gas generation, which is both a methane explosion/migration hazard for nearby structures and a significant greenhouse-gas source if uncollected; remaining site life and capacity, i.e. the rate at which permitted airspace is being consumed against the community's growing waste stream; siting and land-use conflict, since a landfill's traffic, odour, noise and perceived property-value impact routinely trigger public opposition ("NIMBY") during permitting; long-term post-closure liability, since decades of monitoring and maintenance cost continue long after tipping-fee revenue effectively ends; differential settlement of the cover (and of any structure later built on the closed site) as the refuse mass continues to compress and decompose; and vector/nuisance control (birds, rodents, litter) during active operation. Together these concerns are why a landfill is one of the most heavily regulated and engineered facility types in the solid waste system, rather than simply "a hole for waste."