Reference
Formula quick-reference index
Core FE equations plus the PE-depth relationships added across the ten modules. Each block links back to the explanation, assumptions, worked example, and exam traps. Use the level markers to separate quick FE review from PE design analysis.
Topic 1: Fluid Properties & Hydrostatics
↑ Topic 1: Fluid Properties & Hydrostatics
γ = ρg
| γ | specific weight — weight per unit volume |
| ρ | mass density — mass per unit volume |
| g | gravitational acceleration, 32.2 ft/s² (9.81 m/s²) |
↑ Topic 1: Fluid Properties & Hydrostatics
SG = γsubstance / γwater
| SG | specific gravity, dimensionless |
↑ Topic 1: Fluid Properties & Hydrostatics
ν = μ / ρ
| μ | dynamic (absolute) viscosity |
| ν | kinematic viscosity |
↑ Topic 1: Fluid Properties & Hydrostatics
p = γh
| p | gauge pressure at depth h |
| h | vertical depth below the free surface |
↑ Topic 1: Fluid Properties & Hydrostatics
FR = γ hc A
| FR | magnitude of hydrostatic force on a plane surface |
| hc | vertical depth of the surface's centroid |
| A | area of the surface |
↑ Topic 1: Fluid Properties & Hydrostatics
yp = yc + Ixx,cycA
| yp | distance from the free surface to the centre of pressure, measured along the incline |
| yc | distance from the free surface to the centroid, measured along the incline |
| Ixx,c | second moment of area about the centroidal axis (rectangle: bh³/12, with h along the incline) |
Topic 2: Buoyancy & Flotation
↑ Topic 2: Buoyancy & Flotation
Fb = γfluid · Vdisplaced
| Fb | buoyant force, acting vertically upward through the centroid of the displaced volume |
| Vdisplaced | volume of fluid displaced = submerged volume of the body only |
↑ Topic 2: Buoyancy & Flotation
Floating equilibrium: W = Fb
| W | total weight of the floating body |
↑ Topic 2: Buoyancy & Flotation
GM = MB − GB stable if GM > 0
| G | centre of gravity of the body |
| B | centre of buoyancy (centroid of submerged volume) |
| M | metacentre — where the tilted buoyant-force line crosses the body's centreline |
| MB = I0/Vsub | distance from B to M; I0 is the second moment of the waterplane area about its centroidal axis |
Topic 3: Continuity, Energy & Momentum
↑ Topic 3: Continuity, Energy & Momentum
Q = A1V1 = A2V2
| Q | volumetric flow rate (discharge) |
| A | cross-sectional area normal to the flow |
| V | mean velocity through the section |
↑ Topic 3: Continuity, Energy & Momentum
ρ1A1V1 = ρ2A2V2
| Used when density changes (gases, compressible flow). For water, ρ cancels and you get Q = AV. |
↑ Topic 3: Continuity, Energy & Momentum
p1/γ + V1²/2g + z1 + hA = p2/γ + V2²/2g + z2 + hT + hL
| p/γ | pressure head |
| V²/2g | velocity head |
| z | elevation head (same datum for both points!) |
| hA | head added by a pump |
| hT | head removed by a turbine |
| hL | total head loss between 1 and 2 |
↑ Topic 3: Continuity, Energy & Momentum
ΣF = ρQ(β2V2 − β1V1)
| ΣF | vector sum of forces on the fluid (pressure + weight + reaction), in the chosen direction |
| β | momentum correction factor, ≈ 1.0 for turbulent flow — the exam usually lets you drop it |
Topic 4: Pipe Flow
hf = f LD V²2g
| hf | friction head loss |
| f | Darcy friction factor (dimensionless — not the Fanning factor, which is f/4) |
| L, D | pipe length and diameter |
| V | mean velocity |
Re = VDν laminar: f = 64Re
| Re | Reynolds number; laminar below ≈ 2,300, turbulent above ≈ 4,000 |
| ν | kinematic viscosity of the fluid |
Turbulent f: Haaland approximation 1/√f ≈ −1.8 log[(ε/3.7D)1.11 + 6.9/Re]
| ε | absolute roughness of the pipe wall (commercial steel ≈ 0.00015 ft) |
| Use the Moody chart or Colebrook equation equivalently; Haaland is calculator-friendly. |
V = 1.318 · C · R0.63 · S0.54 (English units, V in ft/s)
| C | Hazen-Williams roughness coefficient (≈ 150 new PVC, 130 new steel, 100 old cast iron) |
| R | hydraulic radius = A/P (D/4 for a full circular pipe) |
| S | slope of the energy grade line = hf/L |
hm = K V²2g
| K | minor loss coefficient (entrance ≈ 0.5, exit = 1.0, valves/fittings from tables) |
| Equivalently, fittings can be converted to an equivalent length of straight pipe. |
Series pipes: Q is the same everywhere; head losses add. Parallel pipes: head loss is the same in each branch; discharges add.
Topic 5: Pumps & System Curves
↑ Topic 5: Pumps & System Curves
Hsys = Hstatic + KQ²
| Hsys | total head the system demands at flow Q |
| Hstatic | static head: elevation lift + (pdischarge − psuction)/γ |
| KQ² | friction + minor losses, which scale with the square of flow |
↑ Topic 5: Pumps & System Curves
Operating point: the (Q, H) where the pump curve crosses the system curve.
↑ Topic 5: Pumps & System Curves
Q2Q1 = N2N1 H2H1 = (N2N1)² P2P1 = (N2N1)³
| Q | discharge |
| H | head |
| P | power |
| N | rotational speed (or impeller diameter D) |
↑ Topic 5: Pumps & System Curves
Water power: P = γQHη English shortcut: bhp = Q(gpm) × H(ft)3960 × η
| η | pump efficiency as a decimal |
| The 3960 shortcut already includes unit conversions for water — do not multiply by γ again. |
↑ Topic 5: Pumps & System Curves
NPSHA = patm/γ − pv/γ ± hs − hL,suction > NPSHR
| NPSHA | net positive suction head available from the system |
| NPSHR | net positive suction head required by the pump (from its curve) |
| pv | vapour pressure of the liquid at its temperature |
| hs | static suction head: + if the supply sits above the pump, − if the pump must lift (suction lift) |
| hL,suction | head loss in the suction piping |
Topic 6: Open-Channel Flow
V = (k/n) · R2/3 · S1/2 Q = AV
| V | mean velocity |
| Q | discharge |
| k | unit constant: 1.486 for English units (ft/s), 1.0 for SI |
| n | Manning's roughness coefficient (concrete ≈ 0.013, earth ≈ 0.022, natural channel ≈ 0.03–0.05) |
| R | hydraulic radius = A/P, where P is the wetted perimeter |
| S | longitudinal slope of the channel (energy slope for uniform flow) |
Rectangular: A = by, P = b + 2y Trapezoidal: A = (b + zy)y, P = b + 2y√(1+z²) Full circular: R = D/4
| b | bottom width |
| y | flow depth |
| z | side slope, horizontal:vertical |
| Do NOT use R = D/4 for a partly full pipe — recompute A and P for the actual depth. |
Fr = V / √(g·Dh) with Dh = A/T
| Fr | Froude number: < 1 subcritical, = 1 critical, > 1 supercritical |
| Dh | hydraulic depth = area / top width T (for a rectangle, Dh = y) |
Rectangular channels: yc = (q²/g)1/3 and Emin = 3yc/2
| yc | critical depth |
| q = Q/b | discharge per unit width |
| E = y + V²/2g | specific energy — minimised at critical depth |
Topic 7: Hydrology & Runoff
Qp = C · i · A
| Qp | peak runoff rate (cfs when i is in in/hr and A in acres — the units work out) |
| C | runoff coefficient (0–1); use an area-weighted composite for mixed land use |
| i | rainfall intensity for a duration equal to the time of concentration, tc |
| A | drainage area |
Composite C = Σ(CjAj) / ΣAj
| tc | time of concentration — travel time from the hydraulically most distant point |
S = 1000/CN − 10 (inches) Ia = 0.2S
| CN | curve number, 0–100 (higher = more runoff); from TR-55 tables by soil group and cover |
| S | potential maximum retention after runoff begins |
| Ia | initial abstraction — interception, depression storage, early infiltration |
Q = (P − Ia)²(P − Ia) + S for P > Ia; Q = 0 otherwise
| Q | direct runoff depth (inches) |
| P | storm rainfall depth (inches) |
tp = ΔD/2 + 0.6 tc qp = 484 A / tp
| tp | time to peak (hr) |
| qp | peak of the unit hydrograph (cfs) |
| ΔD | unit storm duration (hr) |
| A | area in square miles |
Topic 8: Groundwater Flow
Q = K · i · A with i = dh/dl
| Q | discharge through the porous medium |
| K | hydraulic conductivity (permeability) |
| i | hydraulic gradient — head loss per unit length, dimensionless |
| A | bulk cross-sectional area normal to flow (solids + voids) |
v = Q/A (Darcy flux) vs = v/n (seepage velocity)
| v | discharge per unit bulk area — not the actual pore-water speed |
| vs | true average velocity through the pores |
| n | porosity |
Confined (constant thickness b): q = T · (dh/dl), T = K·b
| T | transmissivity — the aquifer's headline property for confined flow |
| b | saturated thickness of the confined aquifer |
Unconfined (Dupuit): q = (K/2L)·(h1² − h2²) per unit width
| h | saturated thickness (water-table height above the impermeable base) |
| Assumes nearly horizontal flow — the Dupuit approximation; fine for gentle gradients. |
Confined: Q = 2πT(h2 − h1)ln(r2/r1)
| h1, h2 | hydraulic heads at radial distances r1, r2 from the well |
| T = Kb | transmissivity |
Unconfined: Q = πK(h2² − h1²)ln(r2/r1)
| Heads h are water-table heights above the aquifer base — and they enter squared. |
Topic 9: Water Treatment
Coagulation/flocculation: rapid mix then gentle stirring; design by detention time t = V/Q and the Camp number Gt
| Typical: rapid mix 30–60 s; flocculation 20–40 min; Gt ≈ 104–105. |
Sedimentation: surface overflow rate = QA weir loading = QLweir
| Surface overflow rate (gpd/ft²) | the controlling design parameter — particles settle if their settling velocity exceeds it |
| Weir loading (gpd/ft) | checked separately so settled sludge is not scoured over the weirs |
Filtration: filtration rate = Q/A (gpm/ft²); backwash reverses the flow to clean the media
| Rapid sand filters run ≈ 2–4 gpm/ft²; head loss grows as the bed clogs, triggering backwash. |
Disinfection: CT = C × T
| C | disinfectant residual concentration (mg/L) |
| T | contact time (min) — use T10, the time 90% of the water exceeds, for credit |
| CT (mg·min/L) | compared against regulatory tables for the target pathogen and disinfectant |
Topic 10: Wastewater Treatment
↑ Topic 10: Wastewater Treatment
BOD exerted at time t: y = L0(1 − e−kt) (base e) or y = L0(1 − 10−Kt) (base 10)
| y | oxygen consumed by time t |
| L0 | ultimate BOD |
| k, K | deoxygenation rate constants — k = 2.303K, so check which base the question uses |
↑ Topic 10: Wastewater Treatment
BOD5 ≈ 0.68 × L0 (for the standard k = 0.23 day−1, base e, at 20°C)
| Handy when a question gives one and asks for the other. |
↑ Topic 10: Wastewater Treatment
F/M = Q · S0V · X
| Q | influent flow |
| S0 | influent BOD5 |
| V | aeration tank volume |
| X | MLSS — mixed liquor suspended solids |
| Units: day−1; conventional plants run ≈ 0.2–0.5 day−1. |
↑ Topic 10: Wastewater Treatment
MCRT = mass of solids in the systemmass of solids wasted per day = V·XQwXw + QeXe
| Qw, Xw | waste sludge flow and concentration |
| Qe, Xe | effluent flow and suspended solids (often negligible) |
| MCRT in days; conventional ≈ 5–15 days, extended aeration 20–30+. |
↑ Topic 10: Wastewater Treatment
Surface overflow rate = QA Solids loading rate = (Q + Qr) · XA
| Qr | return sludge flow |
| Design SOR ≈ 400–700 gpd/ft²; solids loading ≈ 20–30 lb/day/ft² for conventional plants. |
↑ Topic 10: Wastewater Treatment
SVI = (settled volume in 30 min, mL/L) × 1000 / MLSS (mg/L) (mL/g)
| SVI < 100 good settling; > 150 suggests bulking. |
PE-depth additions
These relationships extend the core equations into the current PE WRE areas: Analysis and Design, closed- and open-conduit hydraulics, Hydrology, Groundwater and Wells, water quality, drinking-water distribution, and wastewater collection.
Q = CdA2√[2gΔh / (1 − (A2/A1)²)]
| Δh | piezometric-head difference |
| Cd | discharge coefficient |
Node: ΣQin − ΣQout = qdemand Loop: ΣhL = 0
y2/y1 = 0.5[√(1 + 8Fr1²) − 1]
ΔE = (y2−y1)³/(4y1y2)
P(≥1 in n years) = 1 − (1 − 1/T)n
2S2/Δt + O2 = I1 + I2 + 2S1/Δt − O1
s = QW(u)/(4πT), u = r²S/(4Tt)
s ≈ [2.3Q/(4πT)] log10(2.25Tt/r²S)
↑ Mass balance and distribution
Load (lb/day) = 8.34Q(MGD)C(mg/L)
Cout,CSTR = Cin/(1+kθ) Cout,PFR = Cine−kθ
↑ Collection and nutrient loading
Load (lb/day) = 8.34Q(MGD)C(mg/L)
Removal = [(Cin−Cout)/Cin]×100%
Printable version — free
Every formula on this page, condensed into a 2-page printable cheat sheet. Free — just enter your email to download.