18-Env-A4 Water and Wastewater Engineering · May 2014
Question 4 of 5
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
Notes on this paper
National Exams — May 2014 — 04-Env-A4 / Water and Wastewater Engineering. 3 hours duration; closed book with one aid sheet written on both sides; an approved calculator is permitted. Question 1 is compulsory; any three of the remaining four questions constitute a complete paper (only the first four of Questions 2–5 in the work book are marked); all five questions are solved below for completeness. Each question is worth 25 marks.
Reference texts. Metcalf & Eddy, Wastewater Engineering: Treatment and Resource Recovery (5th ed.); MWH's Water Treatment: Principles and Design (3rd 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.
(a) Oxygen demand and air requirement for 95% BOD removal (10 marks)
Given.
Quantity
Value
Average flow, $Q$
15,000 m³/d
Primary effluent BOD5, $S_0$
150 mg/L
Required BOD removal
95%
Observed sludge yield, $Y_{obs}$
0.8 kg TSS/kg BOD5 removed
Find. The net oxygen demand (kg O2/d) and the corresponding air requirement (m³ air/d).
Approach. Convert the BOD5 removed to an oxygen demand using the ultimate-BOD conversion factor, credit back the oxygen equivalent of the biomass that leaves as waste sludge, then convert the net oxygen demand to an air volume via air's oxygen content and an assumed field oxygen-transfer efficiency.
Biomass (waste sludge) produced. Using the given observed yield,
$$P_x = Y_{obs}\times\Delta BOD_5 = 0.8\times2137.5 = \boxed{1710\ \text{kg TSS/d}}$$
Net oxygen demand. Converting BOD5 to ultimate oxygen demand with $f=BOD_L/BOD_5\approx1.47$ (from the standard $BOD_5/BOD_L=0.68$ relation) and crediting 1.42 kg O2 per kg of biomass carbon that leaves as waste sludge rather than being oxidized (Metcalf & Eddy AOTR relation):
$$AOTR = f\cdot\Delta BOD_5 - 1.42\,P_x = 1.47(2137.5)-1.42(1710) = 3142.1-2428.2 = \boxed{713.9\ \text{kg O}_2/\text{d}}$$
Air requirement. Air at standard conditions has density ≈1.2 kg/m³ and an oxygen mass fraction of 23.2%, so 1 m³ of air carries $1.2\times0.232=0.2784$ kg O2. Assuming a field oxygen-transfer efficiency $OTE=8\%$ (typical for diffused/mechanical aeration, per check note below):
$$\text{Air} = \frac{AOTR}{1.2\times0.232\times OTE} = \frac{713.9}{1.2\times0.232\times0.08} = \frac{713.9}{0.02227} = \boxed{32{,}055\ \text{m}^3\ \text{air/d}}$$
(b) Aeration tank volume (8 marks)
Given. $SRT = 4$ d, $MLSS = 2000$ mg/L, and the biomass production $P_x=1710$ kg TSS/d from part (a).
Find. Required aeration tank volume $V$.
Approach. At steady state, the mass of biomass in the reactor ($MLSS\times V$) turns over once every SRT (biomass wasted per day, $P_x$, times SRT), so $SRT = (MLSS\cdot V)/P_x$ rearranges directly for $V$.
Hydraulic retention time check.
$$HRT = \frac{V}{Q}\times24 = \frac{3420}{15{,}000}\times24 = \boxed{5.47\ \text{h}}$$
This falls within the typical 4–8 h HRT range for conventional activated sludge, confirming the tank size is physically reasonable.
Check: the exam gives no kinetic coefficients ($k_d$, $a'$, $b'$) or aeration transfer-efficiency data, so this solution assumes (i) the standard $BOD_5/BOD_L=0.68$ ultimate-BOD conversion, (ii) the standard 1.42 kg O2/kg-biomass cell-mass credit, and (iii) an 8% field oxygen-transfer efficiency typical of diffused aeration — all standard Metcalf & Eddy design assumptions used because the question supplies the observed yield $Y_{obs}$ specifically to let the net (post-cell-credit) oxygen demand be computed rather than the gross BOD-only figure.