Water Quality
Evaluate stormwater pollutant loading and treatment requirements for the project.
Section progress
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Water Resources · Watershed hydrology, stormwater, channels, culverts, networks and hydraulic structures.
Deliverable: Water quality analysis with pollutant load estimate and TMDL compliance narrative.
Minimum tables, figures and equations for Water Quality
Tables — at least 7
- Table — trial sections or sizes considered, with the capacity of each and the selection decision
- Table — final selected geometry for every element: dimensions, thickness, grade, spacing, elevation
- Table — inlet, pipe, culvert and outlet sizing with slope, capacity and headwater depth
- Table — ultimate limit state check summary: demand, capacity, ratio, pass or fail, governing clause
- Table — serviceability check summary: deflection, crack width, settlement, freeboard or velocity against its limit
- Table — factors of safety achieved against the factor required, per failure mode
- Table — pre- versus post-development peak flows by design storm
Figures — at least 5
- Figure — free body diagram of each isolated element, fully labelled with loads, reactions, dimensions and axes
- Figure — shear and moment (or pressure and velocity) diagrams for each force-carrying element
- Figure — dimensioned section or plan of each designed element
- Figure — capacity versus demand plot, interaction diagram, or rating curve as applicable
- Figure — hydraulic grade line and energy grade line profile
Equations — at least 8
- Equation — equilibrium equations written out for each free body (sum of forces and sum of moments, or continuity and energy)
- Equation — the internal force relations V(x) and M(x), or the momentum/thrust relation, used to compute each element's demand
- Equation — the resulting demand at the critical section of each element, with numeric substitution
- Equation — the capacity expression for each element type, shown with full numeric substitution and units
- Equation — the sizing criterion that sets the final dimension (for example required area, depth or diameter)
- Equation — each limit state check written as demand over capacity with numbers substituted
- Equation — the factor of safety calculation for each failure mode checked
- Equation — outlet scour velocity and riprap sizing check
Number every table and figure (Table 4.x, Figure 4.x), caption it, and refer to it by number in your text. Number displayed equations and show the substitution with units. These counts are minimums — add whatever else your design needs.
Engineering documentation standard — required in every Chapter 4 subsection
These rules are graded on every subsection. Work that misses them is capped on technical accuracy, exhibits, codes and communication, whatever the quality of the prose.
Code and standard references
- Every requirement, factor, coefficient, limit and allowable you apply cites the governing document AND the exact section, article or sub-article number — e.g. ACI 318-19 §22.5.5.1, AISC 360-22 Chapter J, Section J3.6, AASHTO LRFD 10th Ed. Article 3.6.1.2.2, ASCE 7-22 §12.8.1, ASTM D2487, state DOT manual section, local stormwater manual chapter.
- Give the edition or year of every document the first time it appears, then use a consistent short form.
- Where a code equation is used, quote the equation number (e.g. Eq. 22.5.5.1) next to your displayed equation.
- Where you depart from a code provision, state the clause you are departing from and the engineering justification.
- List every code, standard and manual actually used in a Codes and Standards table at the start of the subsection.
Citations for statements
- Every statement of fact, value taken from elsewhere, material property, soil parameter, rainfall depth, unit cost or published method carries an in-text citation (APA) to its source.
- Field and lab data cite the report, boring log, gauge, survey file or test number and its date.
- Manufacturer data cites the product literature and revision date; software results cite the program, version and model file name.
- Uncited assertions are treated as assumptions and must appear in the assumptions table with a justification.
- Every in-text citation resolves to a full entry in the reference list.
Step-by-step calculations
- Structure every calculation the same way: (1) objective, (2) governing code clause, (3) equation in symbolic form with the equation number, (4) definition of each symbol, (5) numerical substitution, (6) result with units, (7) comparison against the limit and the pass/fail statement.
- Show the substitution line — never jump from the formula to the answer.
- Number displayed equations sequentially (Eq. 4.1, 4.2, …) and refer to them by number in the text.
- State the load or flow combination governing each calculation by name.
- Carry consistent significant figures and round only at the reported result; state the rounding convention once.
- Present repetitive element checks in a calculation table with one row per element and the same column order throughout.
Free body diagrams and figures
- Draw a separate free body diagram for each isolated element — no combined sketches standing in for several members.
- Dimension every FBD: span, depth, thickness, cover, eccentricity, embedment, slope, pipe diameter, wall height — with the dimension lines and values shown.
- Label every force, pressure, reaction and moment with its symbol, magnitude and units, and show the sign convention and coordinate axes.
- Show supports and boundary conditions explicitly (pin, roller, fixed, elastic, buoyant, hydrostatic).
- Accompany each FBD with its shear, moment, thrust, pressure or hydraulic grade diagram at the same scale reference.
- Number and caption every figure (Figure 4.x) and refer to it by number in the narrative; add a scale or north arrow to plans.
Units and notation
- Every number in text, tables, figures and equations carries its unit — no bare numbers.
- Use one unit system throughout (US customary or SI); if both appear, give the converted value in parentheses consistently.
- Check dimensional homogeneity of each equation and say so — the units of both sides must match.
- Provide a nomenclature table defining every symbol with its unit.
Checking and verification
- Every calculation is checked by an independent route — hand check against software, alternative method, order-of-magnitude estimate, or a published worked example — and the check is shown, not just claimed.
- Report demand-to-capacity ratios and factors of safety against the required values, with the source clause for each required value.
- Include a verification/checking table: item, method of check, expected, obtained, difference, accept or revise.
- Sanity-check every result (magnitude, direction, plausibility) and state the conclusion.
- Record who checked the work and on what date; flag anything still unverified as an open item.
- State limitations and the range over which the result is valid.
How to complete this section
Do this next: Read the Water Quality lecture and the worked example so you know what "Water quality analysis with pollutant load estimate and TMDL compliance narrative." has to contain.
Not sure how to start or how much depth is expected? Read the fully written model example for this deliverable first — it shows the structure, tables and level of justification your advisor grades against.
Hydraulic Design Office — what this workspace teaches
Watershed hydrology, stormwater, channels, culverts, networks and hydraulic structures.
- Watershed delineation, land use, curve number and imperviousness
- Rainfall: IDF curves, design storms, return periods
- Rational Method and NRCS/SCS runoff methods with validity limits
- Hydrograph development and flood routing (HEC-HMS concepts)
- Open channel flow: Manning's equation, normal and critical depth, froude number
- Culvert hydraulics: inlet vs. outlet control, headwater, performance curves
- Storm sewer network design and hydraulic grade line
- Detention basin sizing, stage-storage-discharge and outlet structures
- Weirs, orifices and energy dissipation structures
- Stormwater BMPs, water quality volume and EPA guidance
End-of-term milestones
- Tuesday, November 17, 2026 — Poster printed and ready. 36 in × 48 in poster finalized and printed one week before the November 24 showcase.
- Wednesday, November 18, 2026 — Final document package uploaded for scoring. Chapters 4–5, calculation package, drawings and appendices uploaded in the app for advisor scoring.
- Wednesday, November 18, 2026 — Poster presentation to faculty and industry. Wednesday poster session — printed 36 in × 48 in poster presented in person; industry reviewers score communication and impact.
- Wednesday, November 25, 2026 — Oral presentation and defense (scored). Scored oral presentation and defense held on Wednesday, November 25.
Water Quality
Evaluate stormwater pollutant loading and treatment requirements for the project.
Section B
Engineering story
A real project situation that frames this module
Week 6: water quality is the item standing between the team and a reviewable hydrologic and hydraulic model with the sized conveyance. Evaluate stormwater pollutant loading and treatment requirements for the project. Review stalls on a single line: the team cannot show the record behind pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria).
Using a generic national EMC value when a local monitoring dataset is available. Because event mean concentration (EMC) and pollutant load estimation methods, the error does not stay local: it is carried into the design of record that drawings, quantities and cost are generated from, and every downstream product inherits it before anyone notices.
Downstream property owners, emergency responders and the utility carry the consequence. On this module specifically, the exposure runs through total Maximum Daily Load (TMDL) compliance considerations, and the cost of correction rises every week the hydrologic and hydraulic model with the sized conveyance moves closer to issue.
Decisions the engineer must make
- What record establishes pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria), and is that record in the project data inventory?
- Does EPA NPDES/SWMM (Current), MS4 Permit / TMDL guidance, govern here — and is that the edition adopted by the jurisdiction?
- What is the acceptance criterion for event mean concentration (EMC) and pollutant load estimation methods, and was it written before the result was known?
- Is Load = EMC × Volume × 2.72 (unit conversion factor) valid over the parameter range this project actually occupies?
- If the check fails, does the team revise the hydrologic and hydraulic model with the sized conveyance or raise a change request against the locked baseline?
Photo 1. Pump station: where system head curve, pump curve and operating point meet real hardware.
Capstone Studio instructional photograph
Section C
Why this matters
Professional
A licensed engineer defending water quality cites EPA NPDES/SWMM (Current), MS4 Permit / TMDL guidance, and shows the record behind each input. Your water quality analysis with pollutant load estimate and tmdl compliance narrative. is reviewed the same way — traceability is assessed before arithmetic.
Technical
Pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria) is what makes Load = EMC × Volume × 2.72 (unit conversion factor) usable on this project rather than a formula copied from a reference. Get it wrong and every quantity derived from it is wrong by the same factor.
Safety
The failure mode this module guards against is a conveyance or storage element overtopped by the design event. It reaches people through bMP pollutant removal efficiency data and treatment train performance, which is why the safety check is recorded explicitly here rather than inferred from a passing strength or performance check.
Economic
The design of record that drawings, quantities and cost are generated from is priced from this work. Quantities, unit costs and schedule float all trace to pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria); a late correction here is paid for as a change order, not a redline.
Environmental
Environmentally, this module fixes receiving-water quality, channel erosion and altered baseflow. Choosing conservatively without justification is not free — the excess shows up as material, energy and land that the project consumes for no measurable gain.
Community
Households and businesses in the floodplain the design is meant to protect inherit whatever this module decides — performance, accessibility, cost of ownership and resilience are set here, not at the ribbon-cutting.
Section D
Learning objectives
By the end of this module you will be able to:
- 1.Explain pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria), using this project's own conditions rather than a textbook case.
- 2.Evaluate event mean concentration (EMC) and pollutant load estimation methods, using this project's own conditions rather than a textbook case.
- 3.Interpret total Maximum Daily Load (TMDL) compliance considerations, using this project's own conditions rather than a textbook case.
- 4.Apply bMP pollutant removal efficiency data and treatment train performance, using this project's own conditions rather than a textbook case.
- 5.Compute the governing quantity from Load = EMC × Volume × 2.72 (unit conversion factor), with a unit audit on every term.
- 6.Apply EPA NPDES/SWMM (Current), MS4 Permit / TMDL guidance, and cite the section that governs your acceptance decision.
- 7.Produce water quality analysis with pollutant load estimate and tmdl compliance narrative. at a standard the floodplain administrator would accept without a second revision cycle.
Section E
Instructional content
Full lecture notes with figures and governing equations
Reading water quality as a practising engineer
Evaluate stormwater pollutant loading and treatment requirements for the project. That single sentence hides the substance of the module: pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria), and event mean concentration (EMC) and pollutant load estimation methods. Both must be established from project evidence before anything downstream is credible.
In water resources engineering, this work is the input to the hydrologic and hydraulic model with the sized conveyance. Total Maximum Daily Load (TMDL) compliance considerations — which is why this page asks you to record the source of every quantity, not just its value. The design of record that drawings, quantities and cost are generated from depends on it.
- Pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria)
- Event mean concentration (EMC) and pollutant load estimation methods
- Total Maximum Daily Load (TMDL) compliance considerations
- BMP pollutant removal efficiency data and treatment train performance
Photo 1. Reading water quality as a practising engineer in practice — Inlet capture during rainfall: gutter spread and inlet capacity decide whether the lane floods.
Capstone Studio instructional photograph
Governing relationships and how they are applied here
The relationships below govern water quality. Load = EMC × Volume × 2.72 (unit conversion factor) — each is valid only inside the parameter range this project occupies, so state that range before substituting.
Event mean concentration (EMC) and pollutant load estimation methods sets the values you place into these expressions. Any code-prescribed factor must match EPA NPDES/SWMM (Current); a factor lifted from a different edition silently changes the answer.
Load = EMC × Volume × 2.72 (unit conversion factor)
- Load = pollutant mass load (lb)
- EMC = event mean concentration (mg/L)
- Volume = runoff volume (ac-ft)
- 2.72 = unit conversion factor for mg/L·ac-ft to lb
Photo 2. Governing relationships and how they are applied here in practice — Aeration basin: detention time, loading rate and oxygen transfer as an operating process.
Capstone Studio instructional photograph
Constraints, adopted standards and the safety case for water quality
EPA NPDES/SWMM (Current), MS4 Permit / TMDL guidance, governs this module: Water quality compliance requirements
The safety case is explicit here. The failure mode is a conveyance or storage element overtopped by the design event; the people exposed are downstream property owners, emergency responders and the utility; the control that prevents it is bMP pollutant removal efficiency data and treatment train performance together with an independent check by someone who did not perform the work.
- Controlling criterion for this module: pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria).
- Adopted reference: EPA NPDES/SWMM (Current) — cite MS4 Permit / TMDL guidance by number.
- Failure mode guarded: a conveyance or storage element overtopped by the design event.
- Evidence produced: Water quality analysis with pollutant load estimate and TMDL compliance narrative..
Photo 3. Constraints, adopted standards and the safety case for water quality in practice — Aeration basin: detention time, loading rate and oxygen transfer as an operating process.
Capstone Studio instructional photograph
Where this method stops being valid
Every method has a domain of validity. State the range of geometry, loading, material behaviour or flow regime over which your approach holds, and state what you would do instead beyond it.
For this project, the boundary you are most likely to push is bMP pollutant removal efficiency data and treatment train performance. If you cross it, say so in writing, bound the error, and carry the limitation into your results chapter. A disclosed limitation is professional practice; a silent extrapolation is not.
Photo 4. Where this method stops being valid in practice — Aeration basin: detention time, loading rate and oxygen transfer as an operating process.
Capstone Studio instructional photograph
Section F
Engineering workflow
Steps
- 1. Assemble the inputs this module needs — pollutants of concern in urban stormwater runoff (TSS, nutrients, metals,…; event mean concentration (EMC) and pollutant load estimation methods — each with a unit and a source record.
- 2. Confirm EPA NPDES/SWMM (Current) is the adopted edition and locate MS4 Permit / TMDL guidance.
- 3. State the assumptions and the acceptance criterion for pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria).
- 4. Evaluate Load = EMC × Volume × 2.72 (unit conversion factor) term by term, carrying one extra significant figure.
- 5. Test the result against total Maximum Daily Load (TMDL) compliance considerations.
- 6. Audit units and run an order-of-magnitude check by hand before the number leaves your desk.
- 7. Obtain an independent check from a teammate who did not perform the work, and record their name and date.
- 8. Assemble water quality analysis with pollutant load estimate and tmdl compliance narrative. and submit it to the floodplain administrator for review.
Decision points
- Is every input behind pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria) traceable? If not — stop and collect the record.
- Does the result satisfy event mean concentration (EMC) and pollutant load estimation methods? If not — revise the work, never the criterion.
- Would the correction change the design of record that drawings, quantities and cost are generated from? If yes — raise a change-control request before proceeding.
- Have you ruled out the most common error on this module — using a generic national EMC value when a local monitoring dataset is available?
Quality checklist
- Documented: pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria)
- Documented: event mean concentration (EMC) and pollutant load estimation methods
- Documented: total Maximum Daily Load (TMDL) compliance considerations
- EPA NPDES/SWMM MS4 Permit / TMDL guidance cited by section number
- Units audited on every expression
- Acceptance criterion recorded before the result
- Independent check signed and dated
- Water quality analysis with pollutant load estimate and TMDL compliance narrative. attached and named per the course convention
Section H
Interactive visualization
Water Quality — step-through
Advance one frame at a time. Each frame adds one engineering decision to the previous state.
Step 1 of 6
Identify pollutants of concern from land use
Section I
Applicable codes and standards
EPA NPDES/SWMM
Current · MS4 Permit / TMDL guidance
Adopted design/analysis reference governing this module.
Relevance: Water quality compliance requirements
Reference the section number and edition in your calculation package. Do not reproduce code text.
Section J
Worked examples
Full engineering solution format
Section K
Common mistakes and how to avoid them
- Using a generic national EMC value when a local monitoring dataset is available
- Ignoring an applicable TMDL wasteload allocation for the receiving water
- Assuming BMP removal efficiency values apply outside the pollutant range they were tested for
- Treating pollutants of concern in urban stormwater runoff (TSS, nutrients, metals, bacteria) as a given instead of establishing it from a project record.
- Producing water quality analysis with pollutant load estimate and tmdl compliance narrative. without showing how event mean concentration (EMC) and pollutant load estimation methods was satisfied.
- Substituting into Load = EMC × Volume × 2.72 (unit conversion factor) outside the range where it is valid, and reporting the number anyway.
- Missing bMP pollutant removal efficiency data and treatment train performance, which is exactly the path to a conveyance or storage element overtopped by the design event.
- Designing to the average condition when the governing condition is the controlling one.
- Freezing a design before the constructability and access review that would have changed it.
- Ignoring constructability: a design that cannot be built safely is not a completed design.
- Omitting the safety check because the strength check passed.
- Referencing figures, tables, or sources that never appear in the reference list.
Section L
Industry case study
Documented failure related to water quality
A constructed civil works project where this module's decision was made incorrectly or skipped.
Official findings
- Published investigation identified a breakdown between analysis assumption and constructed condition.
Field observations
- The controlling assumption was documented nowhere in the design record.
- No independent check existed at the stage where the error entered the work.
Engineering interpretation
- Interpretation below is student analysis for instructional purposes, not an official finding.
- Map the failure to a step in your own workflow and state where your process would have caught it.
Lessons learned
- Document the assumption, then have someone else check it before it becomes construction.
Source: Summarize the published investigation; cite it in your reference list. Do not reproduce copyrighted report text.
Section M
FE Civil exam connection
Handbook FE Reference Handbook — water resources engineering section (record the section number from your handbook edition).
Exam topics
Handbook formulas
- Load = EMC × Volume × 2.72
Weak results here feed your FE Civil Academy weak-area queue for targeted practice.
Question 1 of 2
Score: 0/2In water quality, which item must be established BEFORE the analysis is run?
Section N
Apply it to your project — Water Quality
Complete this using your own capstone project data. Every field is saved to your project record and routed to your advisor with this module's submission.
Inputs and sources
Every value needs a traceable source.
| Quantity | Value | Unit | Source / record |
|---|
Assumptions and consequences
| Assumption | Basis | Consequence if wrong |
|---|
Self-check before submission
Section O
Design challenge
Consulting challenge — Water Quality
Your firm has been retained to deliver the water quality scope for a municipal client on a compressed schedule. Produce the technical position your firm would defend at a public meeting.
Client request: The client wants a defensible recommendation, the basis of design, and an honest statement of what remains unresolved.
Constraints
- Adopted local code edition governs; no exceptions without written variance.
- Budget and schedule are fixed; scope changes require change control.
- Public safety and accessibility requirements are non-negotiable.
Deliverables
- One-page basis of design
- Supporting calculation extract
- Risk and limitation statement
Evaluation
- Technical correctness
- Standard compliance
- Clarity of engineering judgment
- Honest treatment of uncertainty
Section P
Documentation workspace
Write the report section for this module in the academic editor
Section Q
File uploads
Accepted: PDF, DOCX, XLSX, CSV, PNG, JPG, ZIP
No files uploaded yet.
Section R
Deliverable and advisor review
Water quality analysis with pollutant load estimate and TMDL compliance narrative.
Submissions route to your assigned faculty advisor and are scored independently by faculty and administrator rubrics.
Reflection
What was the hardest engineering judgment in this module, and how did you resolve it?
Section S
ABET outcome mapping
Water quality analysis with pollutant load estimate and TMDL compliance narrative. with advisor review and dual scoring.
Assessment: Faculty rubric score and administrator rubric score on this module's submission.
Rubric: Engineering design · Target: 70% of students at or above 'meets expectations'.
Water quality analysis with pollutant load estimate and TMDL compliance narrative. with advisor review and dual scoring.
Assessment: Faculty rubric score and administrator rubric score on this module's submission.
Rubric: Engineering design · Target: 70% of students at or above 'meets expectations'.
Water quality analysis with pollutant load estimate and TMDL compliance narrative. with advisor review and dual scoring.
Assessment: Faculty rubric score and administrator rubric score on this module's submission.
Rubric: Engineering design · Target: 70% of students at or above 'meets expectations'.
Section T
References and further study
EPA NPDES/SWMM (Current)
Adopted reference — cite section numbers, do not reproduce text.
Water Quality — instructor design procedure
Course template for the calculation package format expected in the final report appendix.
NCEES FE Reference Handbook
Locate the equations used here and note the handbook section for exam recall.
Advisor meeting agenda item
Bring the unresolved decision from this module to your next weekly advisor meeting.