18-Env-A2 Hydrology and Municipal Hydraulics Engineering · May 2017
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
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 provides quantity control by temporarily storing the peak of the inflow hydrograph and releasing it slowly back to the downstream channel through a fixed, undersized outlet, so the pond's outflow peak is far lower (and delayed) relative to its inflow peak — unlike a wet pond, the basin drains completely between events and provides no permanent water-quality treatment pool. The basic design approach proceeds in stages: (1) develop the design inflow hydrograph for the contributing watershed at the target return period, typically using the Rational Method for peak flow (small catchments) or a unit-hydrograph/SCS method for the full hydrograph shape on larger catchments; (2) set the allowable release rate as the pre-development (pre-urbanization) peak discharge for the same storm, since the object of quantity control is to prevent the developed condition from increasing downstream peak flows and eroding the receiving channel; (3) size the outlet control structure (commonly a single low-flow orifice, or an orifice plus a higher emergency spillway for storms beyond the design event) to pass no more than that allowable release rate at the maximum design pool elevation; and (4) route the inflow hydrograph through the pond using the storage-indication (Puls) method, iteratively solving continuity $I(t)-O(t)=\dfrac{dS}{dt}$ together with the pond's stage-storage and stage-discharge relationships, to find the storage volume and maximum pool elevation actually required — the required live storage is essentially the area between the inflow and outflow hydrographs on a flow-vs-time plot. Because the stated objective here is reducing downstream erosion via a "reduced first-flush" release, the outlet is typically sized to draw the pool down slowly (an extended detention time of the order of 24–40 hours for the water-quality/erosion-control storm) rather than releasing at the maximum rate the flood-control storage alone would allow, since erosive channel velocities are driven by sustained moderate flows as much as by the single flood peak.
Given.
| Quantity | A1 | A2 |
|---|---|---|
| Area | 25 ha | 35 ha |
| Runoff coefficient, $C$ | 0.6 | 0.7 |
| Time of concentration, $t$ | 50 min | 75 min |
Find. The 25-year design peak runoff at the common outlet downstream of both catchments.
Approach. A2 lies downstream of A1, so the composite catchment has two possible controlling storm durations: (1) a storm just long enough for A1 alone to be fully contributing ($t=t_1=50\ \text{min}$, with A2's flow not yet arrived at the outlet), and (2) a storm long enough for the whole composite area to be contributing ($t=t_2=75\ \text{min}$, A2's own time of concentration, which governs the outlet because A2 is the more remote sub-area). The Rational Method $Q=\dfrac{C\,i\,A}{360}$ (with $Q$ in $\text{m}^3/\text{s}$, $i$ in mm/h and $A$ in ha) is evaluated for both candidate durations using a single storm intensity consistent with each duration, and the larger governs the design — using each sub-area's own (different) duration simultaneously would double-count intensity and is not physically consistent for a single design storm.
| Quantity | Value |
|---|---|
| Design intensity at $t_1=50$ min, $i_1$ | 88.5 mm/h |
| Design intensity at $t_2=75$ min, $i_2$ | 66.5 mm/h |
| Scenario A (A1 only), $Q_A$ | 3.69 m³/s |
| Scenario B (A1+A2), $Q_B$ | 7.30 m³/s |
| 25-year design peak runoff, $Q_{25}$ | 7.30 m³/s |