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18-Env-A2 Hydrology and Municipal Hydraulics Engineering · May 2014

Question 3 of 7: Snowmelt, Wastewater Collection, and IDF-Curve Application

Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)

Notes on this paper

National Exams — May 2014 — 04-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 (first five answers marked); all seven are solved below for completeness. Each question is worth 20 marks.

Reference texts. Chow, Open-Channel Hydraulics; Linsley, Kohler & Paulhus, Hydrology for Engineers (3rd ed.); Walski et al., Advanced Water Distribution Modeling and Management; Davis & Cornwell, Introduction to Environmental Engineering (6th ed.); Metcalf & Eddy, Wastewater Engineering: Treatment and Resource Recovery (5th ed.).

Question 3: Snowmelt, Wastewater Collection, and IDF-Curve Application (20 marks)

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) Engineering Methods for Snowmelt in Hydraulic-Structure Design

The temperature-index (degree-day) method estimates snowmelt rate as an empirical linear function of air temperature above a base value, $M = C_m(T - T_{base})$, where $C_m$ is a melt-rate coefficient calibrated to the basin. It requires only routinely available temperature records, so it is the practical workhorse for sizing a detention/retention basin or a culvert that must pass the spring freshet (combined snowmelt plus rain-on-snow) in a mountainous region, where a long radiation/energy-flux record is rarely available.

The energy-balance method instead explicitly sums every energy flux acting on the snowpack — net solar and longwave radiation, sensible and latent heat exchange with the atmosphere, conduction from the ground, and advected heat carried in by rain falling on snow — to compute the melt rate directly from physics. It is far more data-intensive (requiring radiation, wind, humidity and precipitation-temperature records) but more accurate, particularly for rain-on-snow events that the temperature-index method handles poorly, so it is reserved for higher-consequence structures such as a major spillway or dam outlet works protecting a mountainous valley from Spring flooding, where the added accuracy justifies the added data and analysis cost.

(ii) Wastewater Collection System Components

(a) Sanitary interceptor. An interceptor is a large trunk sewer that collects flow from numerous smaller lateral and trunk sanitary sewers across a service area and conveys the combined flow to the wastewater treatment plant (or to a major pumping station), typically running along a watercourse or the lowest practical grade line. Historically, interceptors were built to intercept the dry-weather (and a portion of wet-weather) flow from older combined sewer systems that previously discharged directly to the receiving water, routing it to treatment instead; they remain the backbone trunk of any regional collection system.

(b) Combined sewer system pumping station overflow. Where a pumping station lifts combined sewage but its firm pumping capacity is limited (sized for dry-weather flow plus only a portion of the wet-weather peak), a relief/overflow structure allows flow in excess of that firm capacity to overflow directly to the receiving water during large storms, rather than surcharging and flooding the upstream collection system or the station itself. Its function is to protect the collection system and station hardware from hydraulic overload, at the cost of an intermittent untreated wet-weather discharge — a legacy design feature that modern combined-sewer-overflow control programs (storage, separation, satellite treatment) are aimed at reducing.

(iii) Worked Example — Rational Method with the 25-Year IDF Curve

Given. A large paved parking lot draining to a proposed stormwater infiltration system, sized against the 25-year return period storm:

Given / assumed design data
QuantitySymbolValue
Contributing (paved) area$A$2.0 ha
Runoff coefficient, paved parking lot$C$0.90
Time of concentration$t_c$15 min
25-yr rainfall intensity at $t_c$ (from the supplied IDF curve)$i_{25}$≈ 100 mm/hr
Check: the exam supplies the IDF curve shapes only; $i_{25}=100$ mm/hr at $t_c=15$ min is a representative reading used here purely to illustrate the design procedure, consistent with the curve's shown range of roughly 0–150 mm/hr.

Find. The peak design discharge $Q$ to be handled by the infiltration system, using the Rational Method.

Approach. Read the 25-year intensity off the IDF curve at a duration equal to the parking lot's time of concentration, then apply the Rational Method (appropriate for this small, highly impervious, homogeneous catchment).

  1. Read the design intensity. Enter the "25 YEARS" curve at duration $=t_c=15$ min: $i_{25} \approx 100$ mm/hr (steepest/uppermost curve on the supplied figure, as expected for the least-frequent, most-intense event of the four shown).
  2. Apply the Rational Method. In SI units ($Q$ in m³/s, $C$ dimensionless, $i$ in mm/hr, $A$ in hectares): $$Q = \frac{C\,i\,A}{360} = \frac{(0.90)(100)(2.0)}{360} = \boxed{0.50\ \text{m}^3/\text{s}}.$$
  3. Apply to the infiltration system design. This peak inflow rate, together with the storm's total runoff volume ($\approx C\times$ rainfall depth $\times A$ over the storm duration), sizes the infiltration system's surface ponding/storage volume and the minimum infiltration (or overflow bypass) capacity needed so the 25-year event neither overtops the facility nor discharges faster than the underlying soil can infiltrate it.
QuantityValue
Design rainfall intensity, $i_{25}$ (illustrative)100 mm/hr
Peak design discharge, $Q$≈ 0.50 m³/s