Mathematics Applications for Environmental FE
Key Takeaways
- Unit conversions precede every calculation.
- Mass balance Q₁C₁+Q₂C₂=QoutCout.
- Geometry supplies area and P for Manning.
- pH uses base-10 logs; decay uses base e.
- Dimensional analysis catches unit errors.
Quick Answer: Environmental FE math is a workflow: audit units → write balance or geometry → search Handbook → compute → sanity-check magnitude. Master MGD conversions, mass balances, and log/exponential forms.
Unit
Conversion
Table
| Quantity | Common units | Key factor |
|---|---|---|
| Flow | MGD, gpm, ft³/s, m³/s | 1 MGD ≈ 1.547 ft³/s |
| Concentration | mg/L, μg/L, ppm | 1 mg/L ≈ 1 ppm in dilute water |
| Pressure | psi, ft H₂O, kPa | 1 psi ≈ 2.31 ft H₂O |
| Power | hp, kW | 1 hp = 0.746 kW |
Worked example: 8 MGD to ft³/s: ( 8 \times 1.547 = 12.4 \text{ ft}^3/\text{s} ).
Mass and
Volume
Balances
Steady-state control volume: inputs = outputs + accumulation (zero at steady state).
Air dilution: ( C_{stack} \times Q_{stack} = C_{ambient} \times Q_{total} ) for conservative tracers at downwind receptor (simplified).
Worked example: 2 m³/s at 30 mg/L mixes with 3 m³/s at 10 mg/L → ( C = (60+30)/5 = 18 \text{ mg/L} ).
Geometry for
Channels and
Basins
Trapezoidal channel: ( A = (b_1+b_2)y/2 ), ( P = b_1 + b_2 + 2y\sqrt{1+m^2} ) for side slope m horizontal:1 vertical.
Circular pipe full: ( A=\pi D^2/4 ), ( R_h = D/4 ).
Logarithms and
Exponentials
pH: ( \text{pH} = -\log_{10}[\text{H}^+] ). Decay: ( t = \ln(C_0/C_t)/k ).
Dimensional
Analysis
If result units do not match expected (mg/L·day vs. mg/L), revisit algebra before selecting from multiple choice.
Multi-Step
Problem
Template
- List givens with units.
- Identify governing relation (balance, Manning, decay).
- Convert to consistent set.
- Solve; compare to order-of-magnitude estimate.
Exam
Traps
- ppm in air ≠ mg/L in water without molecular weight and pressure.
- Percent by weight vs. by volume in chemical solutions.
- Adding concentrations instead of mass flows in blend problems.
Integration with
Other
Topics
Math supports hydrology (runoff depth), treatment (detention time τ=V/Q), and risk (unit conversions for dose). Weak algebra slows every knowledge area — drill conversions daily.
Exam trap: Handbook constants may be in US customary while the stem uses SI — convert once at the start, not mid-calculation.
FE Exam
Integration
Environmental FE items on this topic often combine regulatory classification with a quantitative step. Read the stem for the governing law (CWA, CAA, RCRA, OSHA) before selecting equations. Flag multi-step problems and return after your first pass — average time is under three minutes per question across 110 items.
Practice locating handbook relationships by keyword during timed drills. Confirm units on every constant: mg/L versus μg/m³, ft³/s versus MGD, and days versus seconds in decay and pumping problems are frequent error sources.
FE Exam Integration
Extended Unit Conversion Drill
| Convert | Factor | Example |
|---|---|---|
| ac-ft to gallons | × 325,851 | 100 ac-ft ≈ 32.6 Mgal |
| lb/day to kg/s | ÷ 190,486 | 10,000 lb/day ≈ 0.0525 kg/s |
| cfs-day to ac-ft | ÷ 43,560 | 50 cfs-day ≈ 1.15 ac-ft |
| hp to kW | × 0.746 | 100 hp = 74.6 kW |
Worked example: Pump 500 gpm against 80 ft head, efficiency 70%. Water horsepower WHP = QH/3960 = 500×80/3960 = 10.1 hp. Brake hp = 10.1/0.70 = 14.4 hp.
Three-Stream Mass Balance
River (Q=40 m³/s, C=8 mg/L) + Plant effluent (Q=2, C=30) + Tributary (Q=8, C=5):
[ C_{mix} = \frac{40(8)+2(30)+8(5)}{50} = \frac{320+60+40}{50} = 8.4\text{ mg/L} ]
Percent Removal and Effluent
If influent BOD = 220 mg/L and removal = 92%:
[ C_{eff} = 220(1-0.92) = 17.6\text{ mg/L} ]
Reverse problem: permit 15 mg/L at 220 mg/L influent requires 93.2% removal minimum.
Geometry — Circular Clarifier
Diameter D = 60 ft, sidewater depth = 10 ft. Volume V = π(30)²(10) = 28,274 ft³. At Q = 5 MGD = 3.47 cfs, detention (t = V/Q = 8140) s ≈ 2.26 h.
Log-Transform for Skewed Data
Geometric mean for n values: (GM = \exp(\frac{1}{n}\sum \ln x_i)). Three fecal coliform samples: 100, 200, 800 cfu/100 mL.
[ GM = \exp\left(\frac{\ln 100 + \ln 200 + \ln 800}{3}\right) = \exp(5.30) \approx 200\text{ cfu/100 mL} ]
Arithmetic mean = 367 — geometric mean is the compliance statistic for bacteria.
Reynolds Number Link
[ Re = \frac{vD}{\nu} ]
Transition from laminar to turbulent in pipes near Re = 4000. Darcy-Weisbach headloss rises with friction factor. Environmental FE ties Re to mixing, settling, and aeration basin hydraulics conceptually.
Percent by Weight vs. Volume
10% NaCl by weight in solution differs from 10% by volume. Always read the stem. Converting w/w to mg/L needs solution density — exam usually supplies density or uses dilute aqueous ≈ 1 g/mL.
Hazen-Williams vs. Manning Decision Tree
| Situation | Use |
|---|---|
| Pressurized pipe, full flow | Hazen-Williams |
| Open channel, free surface | Manning |
| Partially full sewer | Manning with geometry tables |
Hazen-Williams example: C=120, L=3000 ft, D=12 in, Q=3 cfs → head loss from handbook form; compare to pump head available.
Detention Time and Loading
[ \tau = \frac{V}{Q} \quad ; \quad \text{Surface loading} = \frac{Q}{A} ]
12 MGD is approximately how many ft³/s?
In dilute aqueous solutions, 1 mg/L is approximately:
Steady blend: Q₁=4 m³/s, C₁=5 mg/L; Q₂=1 m³/s, C₂=25 mg/L. Mixed C is: