16-Civ-B5 Water Supply and Wastewater Treatment · December 2019
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
Paper format. National Examination, December 2019 — 16-Civ-B5 Water Supply and Wastewater Treatment. Three hours; closed book with one aid sheet written on both sides; an approved Casio or Sharp calculator is permitted. Question 1 is compulsory; attempt any three of the remaining four. All five questions carry 25 marks, so the paper is marked out of 100. Every question is solved here, because the complete set is the study resource.
Reference texts for this subject. Metcalf & Eddy / Tchobanoglous, Stensel, Tsuchihashi & Burton, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill) — the primary reference for Q1(ii)–(iv), Q3 and Q5. Crittenden et al., MWH's Water Treatment: Principles and Design, 3rd ed. (Wiley) — coagulation, disinfection and filtration for Q1(i), Q1(v), Q2 and Q4(a). Davis, Water and Wastewater Engineering: Design Principles and Practice (McGraw-Hill) and Mihelcic & Zimmerman, Environmental Engineering: Fundamentals, Sustainability, Design (Wiley) — distribution systems and sewer hydraulics for Q4(b) and Q5. Canadian regulatory frame: Guidelines for Canadian Drinking Water Quality (Health Canada), the Canadian Environmental Quality Guidelines (CCME) for ammonia, and the federal Wastewater Systems Effluent Regulations (SOR/2012-139).
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.
Colloidal particles in a natural water — clay, silica, humic matter, bacteria — carry a negative surface charge and are held apart by electrostatic repulsion that overwhelms the van der Waals attraction between them. They are stable in the thermodynamic sense: Brownian collisions occur constantly, but the energy barrier prevents attachment, so the suspension never aggregates and the particles never settle. Coagulation is the deliberate destruction of that barrier, and it is achieved by three physically distinct routes, which in a real jar test operate together and in different proportions depending on dose, pH and turbidity.
Ionic (double) layer compression. Around each negatively charged particle the water organises itself into a Stern layer of tightly bound counter-ions and a diffuse layer in which the counter-ion excess decays with distance. The thickness of that diffuse layer is the Debye length, which depends only on the ionic strength of the bulk solution:
$$\kappa^{-1} \approx \frac{0.304}{\sqrt{I}}\ \text{nm} \quad (\text{1:1 electrolyte, }25\,{}^{\circ}\mathrm{C}), \qquad I = \tfrac{1}{2}\sum c_i z_i^2$$Adding an indifferent electrolyte raises I and compresses the diffuse layer, so the repulsive potential decays over a shorter distance and the energy barrier falls. A soft surface water of ionic strength 0.001 M carries a 9.6 nm double layer; raising the ionic strength to 0.01 M shrinks it to 3.0 nm and to 0.1 M shrinks it to below 1 nm, at which point van der Waals attraction dominates at every separation and the suspension coagulates without any charge neutralisation at all. Because I depends on the square of the ionic charge, counter-ion valence is decisive: the Schulze–Hardy rule gives critical coagulation concentrations in the ratio $1 : 1/2^6 : 1/3^6$, that is $1 : 1/64 : 1/729$ for mono-, di- and trivalent counter-ions. This is why aluminium and ferric salts, not sodium salts, are the coagulants of practice — and it is also why sea water is naturally coagulating and why an estuary deposits its sediment load where fresh water meets salt.
Adsorption and charge neutralisation, leading to sweep coagulation. When alum or ferric chloride is added at normal pH, the metal ion hydrolyses through a series of positively charged, polynuclear hydroxo species which adsorb specifically onto the negative particle surface and neutralise its charge; the zeta potential moves toward zero and the particles attach on contact. Overdosing reverses the charge and restabilises the suspension — the reason the jar-test curve has a minimum rather than a plateau. If the dose is pushed further, beyond the solubility limit of the metal hydroxide (roughly 20–60 mg/L of alum at pH 6–7.5), amorphous Al(OH)3(s) precipitates throughout the volume as a voluminous, low-density floc, and the colloids are physically enmeshed and swept out as that precipitate settles. This is sweep coagulation or sweep floc. It is remarkably robust — it works on low-turbidity waters that have too few particles to collide with one another, it is insensitive to modest overdosing, and it removes natural organic matter by adsorption onto the fresh hydroxide surface — but it consumes far more coagulant than charge neutralisation and produces a much larger volume of sludge.
Inter-particle bridging. A long-chain, high-molecular-weight polymer — a polyacrylamide polyelectrolyte, or a natural polymer such as starch — adsorbs at a few segments onto one particle while the rest of the chain extends into solution as loops and tails, which then adsorb onto a second particle. The two are physically bridged by the polymer, and the resulting floc is far stronger and more shear-resistant than one held by charge neutralisation alone. Bridging is not primarily electrostatic: an anionic polymer can bridge negative particles even though both carry the same sign, provided divalent cations act as anchor points. It has two characteristic failure modes that must be named. An overdose saturates every available surface site so that no chain finds a vacant site on a second particle, and the suspension restabilises — steric stabilisation. And excessive shear in the rapid-mix stage folds the extended chain flat onto the particle it first touched, destroying the bridge before it forms; this is why polymer is dosed as a flocculant aid after the rapid mix, into a gently stirred flocculation basin at a velocity gradient G of 20–70 s−1, and not into the 700–1000 s−1 of the flash mixer.
Key requirements. An adequate distribution system must deliver, simultaneously and continuously:
The hydraulic difference, quantified. One calculation explains almost every entry in the comparison table. Given. A 250 mm main, Hazen–Williams C = 130, serving a demand of 40 L/s at a point 600 m from the source. Find. The head loss when that point is fed from one direction and when it is fed from two.
$$h_f = \frac{10.67\,L\,Q^{1.852}}{C^{1.852}D^{4.87}}$$Fed from one end, the whole 40 L/s travels the whole 600 m and $h_f = 1.72$ m. Closed into a loop, the same demand is fed from both directions, so each leg carries about 20 L/s over about 300 m, giving $h_f = 0.24$ m. The ratio is exactly $0.5\times0.5^{1.852} = 0.139$:
$$\boxed{\text{Looping the main removes 86 per cent of the head loss at the same demand}}$$Grid-iron (looped) system. Mains are laid on the street pattern and cross-connected at every intersection so that flow can reach any node from several directions. Advantages: no dead ends, so no stagnation and a uniform disinfectant residual; a break or a shutdown isolates one block instead of a whole branch; head loss and pressure fluctuation are much lower, as the calculation shows, so smaller pipes can carry the same fire flow; fire flow can be drawn from several mains at once; the system extends easily in any direction. Disadvantages: substantially more pipe, more valves and more fittings, so a higher capital cost; the flow distribution is statically indeterminate and must be solved iteratively (Hardy Cross or a network model), so design and calibration take more effort; more valves means more maintenance and a greater chance that a valve is left in the wrong position.
Dead-end (branched or tree) system. A trunk main with sub-mains and branches, each terminating. Advantages: the least pipe for a given coverage and therefore the lowest capital cost; flow direction and magnitude in every pipe are known by inspection, so design is simple and can be done by hand; it suits the ribbon development of rural roads, and valve counts are low. Disadvantages: every branch is a single point of failure — one break cuts off everyone downstream; water stagnates at each terminal, so the residual decays, sediment and biofilm accumulate, and taste, odour and coliform complaints cluster at dead ends, which then require a routine flushing programme that wastes water; the whole demand of a branch travels its full length, so head loss is high and pressures at the extremities are poor, particularly during a fire; and fire flow at any point can be supplied from one direction only.
Practice. Canadian municipal design (MMCD and the AWWA distribution standards) requires looping wherever it is practicable, and permits dead ends only for short temporary extensions or genuinely isolated services, where a flushing hydrant or automatic flushing device is then mandated at the terminus.
| Quantity | Value |
|---|---|
| Debye length at I = 0.001 / 0.01 / 0.1 M | 9.6 / 3.0 / 0.96 nm |
| Schulze–Hardy CCC ratio, mono : di : trivalent | 1 : 1/64 : 1/729 |
| Alum dose range for sweep floc | 20–60 mg/L at pH 6–7.5 |
| Velocity gradient: rapid mix / flocculation | G = 700–1000 / 20–70 s−1 |
| Minimum residual pressure during fire flow | 140 kPa (20 psi) = 14.1 m of water |
| Head loss, 40 L/s over 600 m: dead-end vs looped | 1.72 m vs 0.24 m (14 per cent) |