18-Env-A2 Hydrology and Municipal Hydraulics Engineering · December 2019
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
National Exams — December 2019 — 18-Env-A2 / Hydrology and Municipal Hydraulics Engineering. 3 hours duration; closed book with an 8.5×11 in double-sided aid sheet; Casio or Sharp approved calculator only. Any five questions constitute a complete paper (only the first five answers in the work book are marked); all seven Problems are solved below for completeness. Each question is worth 20 marks.
Reference texts. Linsley, Kohler & Paulhus, Hydrology for Engineers (3rd ed.); Chow, Open-Channel Hydraulics; Walski et al., Advanced Water Distribution Modeling and Management; Metcalf & Eddy, Wastewater Engineering: Treatment and Resource Recovery (5th ed.); Davis & Cornwell, Introduction to Environmental Engineering (6th ed.); Guidelines for Canadian Drinking Water Quality (Health Canada); Canadian Council of Ministers of the Environment (CCME) water-quality guidelines.
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 stormwater wet pond (permanent-pool detention basin) is designed around a permanent pool sized to hold the target water-quality storm volume (in Canadian practice, typically the runoff volume from the 90th-percentile storm, or a stated depth over the contributing catchment) for a target hydraulic residence time — commonly on the order of 24–48 h — long enough for the settleable and semi-settleable fraction of total suspended solids (and the particulate-bound fraction of phosphorus/nutrients, which tends to sorb onto fine sediment) to settle out under quiescent conditions before the next storm's inflow displaces the treated water. Key design elements are: a sediment forebay at the inlet to capture coarse sediment separately (concentrating maintenance dredging in one accessible cell rather than across the whole pond); a length-to-width ratio of at least about 3:1 (with baffles/berms if the pond is more compact) to maximize the flow path and minimize hydraulic short-circuiting between inlet and outlet, which otherwise lets a portion of each storm's inflow bypass the design residence time; a permanent pool depth deep enough (typically 1–2 m) to resist re-suspension of settled sediment by wind-driven mixing and to limit algal growth in the photic zone; and an outlet control structure that releases the water-quality volume slowly (via a small orifice/reverse-slope pipe drawing from just below the permanent pool surface) while still passing larger design storms through a higher-capacity overflow, so the pond provides quality treatment for frequent small storms without becoming a flood-control liability for rare large ones.
Two maintenance issues. (1) Sediment accumulation in the forebay and main pool — as TSS is trapped by design, the forebay progressively fills and must be dredged/cleaned out on a scheduled interval (often every 5–10 years, sooner if the contributing catchment is under active construction), or the pond's effective treatment volume and residence time shrink and performance degrades; (2) vegetation, inlet/outlet and embankment upkeep — littoral (shallow marginal) vegetation must be maintained to take up dissolved nutrients and stabilize banks against erosion, while the inlet and outlet structures must be kept clear of debris/trash so that neither short-circuiting (blocked baffles) nor uncontrolled bypass (blocked low-flow orifice forcing everything over the emergency spillway) develops.
Given.
| Area | Area (ha) | Runoff coeff. $C$ | Time of concentration $t$ (min) |
|---|---|---|---|
| A1 (upstream) | 30 | 0.6 | 40 |
| A2 (downstream) | 50 | 0.7 | 60 (to outlet) |
100-year IDF curve (read from the supplied chart, Tr = 100 years): $i\approx116$ mm/h at duration 40 min; $i\approx88$ mm/h at duration 60 min (values read at the two durations of interest; chart-derived, ±10% engineering tolerance).
Find. The governing 100-year design peak runoff at the outlet, using the Rational Formula $Q=CiA/360$ ($Q$ in m³/s, $i$ in mm/h, $A$ in ha).
Approach. With two sub-catchments in series, the design storm duration that maximizes the OUTLET peak is not obvious a priori: a short, intense storm (duration = A1's own $t_c$) only lets A1 contribute at full intensity (A2 has not yet reached its own outlet-response time), while a longer storm (duration = A2's $t_c$, the time for the combined system to fully respond) lets the FULL combined area contribute, but at a lower intensity. Both candidate peaks are computed and the larger governs.
| Quantity | Value |
|---|---|
| $Q$ at $t=t_1=40$ min (A1 only) | 5.80 m³/s |
| $Q$ at $t=t_2=60$ min (A1+A2 combined) | 12.96 m³/s |
| Governing 100-year design peak runoff | 12.96 m³/s |