18-Env-A1 Principles of Environmental Engineering · December 2019
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
National Exams — December 2019 — 18-Env-A1 / Principles of Environmental Engineering. 3 hours duration; closed book with a candidate-prepared 8.5×11 in double-sided aid sheet; Casio or Sharp approved calculator only. Any five questions constitute a complete paper (first five answers marked); all seven are solved below for completeness. Each question is worth 20 marks.
Reference texts. Davis & Cornwell, Introduction to Environmental Engineering (6th ed.); Metcalf & Eddy, Wastewater Engineering: Treatment and Resource Recovery (5th ed.); MWH’s Water Treatment: Principles and Design (3rd ed.); Sawyer, McCarty & Parkin, Chemistry for Environmental Engineering and Science; Guidelines for Canadian Drinking Water Quality (Health Canada); Canadian Council of Ministers of the Environment (CCME) water-quality and municipal solid-waste guidelines; Canadian Environmental Protection Act, 1999 (CEPA) and Canadian Environmental Assessment Act (CEAA 2012); Bies & Hansen, Engineering Noise Control; Andrews, Canadian Professional Engineering and Geoscience (professional ethics).
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.
A watershed-scale source-control strategy — establishing and enforcing vegetated riparian buffer zones along all watercourses draining agricultural land into the reservoir — is the most effective long-term protection: buffers intercept nutrient-laden surface runoff and shallow subsurface flow before it reaches open water, using vegetation uptake, infiltration and sediment trapping to reduce both dissolved N and particulate-bound P loading, and (unlike in-reservoir treatment) address the pollution at its source across the entire contributing watershed rather than only where it has already concentrated in the source water. Sustaining this over the long term additionally requires a watershed source-water protection plan coordinated with upstream agricultural operators (best-management-practice adoption, nutrient-management planning tied to the buffer program), since a buffer network alone can be undermined if upstream fertilizer-application practices continue unchanged.
Non-technical principle: the polluter-pays principle. Applying a carbon price (or equivalent charge) that makes greenhouse-gas emitters bear the cost of the emissions they generate creates a direct economic incentive to reduce emissions at the source, reducing the underlying driver of both worsened smog formation and surface-water thermal/eutrophication stress — a policy/economic lever rather than a piece of hardware, which is what makes it “non-technical.”
Preferred method: flight-path and operational noise-abatement procedures. Because it reduces the noise generated at (or reaching) the community in the first place rather than only attenuating it after the fact, it protects both indoor and outdoor noise exposure (barriers and insulation help indoors but do little for residents outside), is far lower-cost than large-scale barrier construction or a community-wide insulation retrofit program, and can be adjusted operationally as traffic patterns or community sensitivity change, whereas physical barriers/insulation are fixed, capital-intensive investments.
Technical principle — source control/best-available-technology (green infrastructure). Installing low-impact development features (bioswales, permeable pavement, distributed stormwater detention) across the sewershed physically reduces the volume of stormwater entering the combined system during a storm event, directly cutting the frequency and volume of overflow events through engineered infrastructure.
Non-technical principle — the polluter-pays principle applied as a stormwater utility fee. Charging property owners a fee proportional to their site’s impervious area (with credits for on-site stormwater management) creates a direct financial incentive for property owners to reduce runoff voluntarily (installing rain gardens, disconnecting downspouts), complementing the engineered green-infrastructure investment with a behavioural/economic lever rather than a piece of hardware.
The comparison shows the two principles are complementary rather than substitutes: the technical (green-infrastructure) solution physically removes stormwater volume from the system, while the non-technical (pricing) principle sustains and extends that reduction by giving every property owner in the sewershed an ongoing incentive to keep contributing to it.