18-Env-A2 Hydrology and Municipal Hydraulics Engineering · Undated paper
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
National Exams — May 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 dry pond (extended-detention basin, normally empty between storms) is designed around a stage-storage-discharge relationship: an outlet control structure — typically a multi-stage riser combining a small low-flow orifice with a higher-capacity overflow weir — throttles the release rate so that the routed peak outflow for each targeted design storm does not exceed a specified target, with the required storage volume found from reservoir routing (the design inflow hydrograph in, the routed outflow hydrograph out, storage = the difference integrated over time).
For the stated objectives, the pond is typically designed with (at minimum) two control stages: an extended-detention (erosion-control) stage, sized to release the frequent, smaller storms (commonly the 1-year, or a "channel-forming" event) slowly — over 24–48 hours — through a small low-flow orifice, so that the post-development peak AND duration of erosive velocities in the receiving channel does not exceed the pre-development condition (matching only the peak, without also extending the duration near bank-full flow, still causes progressive channel erosion); and a flood-control stage, sized via a higher weir to attenuate the rarer, larger design storm (often the 100-year event, matching the low-lying residential development's flood-protection target) down to at or below the pre-development peak discharge for that storm.
Key design elements are: an emergency spillway sized to safely pass the extreme (e.g., 1:100-year-plus or PMF-derived) flow without overtopping the embankment, protecting the downstream residential development from a catastrophic dam-breach-style failure; sufficient freeboard between the maximum routed water surface and the top of the embankment; and a low-flow/forebay channel through the pond bottom to prevent nuisance ponding and mosquito breeding between storms, since a dry pond (unlike a wet pond) is not meant to hold a permanent pool. Because the pond is normally dry, sediment deposited during each storm must be periodically removed from the low-flow channel and forebay to keep the outlet structure's low-flow orifice from being buried or blocked, which would otherwise silently defeat the erosion-control stage's extended-detention function.
Given.
| Area | Area (ha) | Runoff coeff. $C$ | Time of concentration $t$ (min) |
|---|---|---|---|
| A1 (upstream) | 40 | 0.5 | 50 |
| A2 (downstream) | 60 | 0.6 | 80 (to outlet) |
100-year IDF curve (read from the supplied chart, Tr = 100 years, by tracing the topmost curve at high resolution and cross-checking against a fitted $i=a/(t+b)^c$ power curve through several clean off-gridline chart points): $i\approx104$ mm/h at duration 50 min; $i\approx75$ mm/h at duration 80 min (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 $t=t_1=50$ min (A1 only) | 5.78 m³/s |
| $Q$ at $t=t_2=80$ min (A1+A2 combined) | 11.67 m³/s |
| Governing 100-year design peak runoff | 11.67 m³/s |