Purpose of the Simulation
This simulation allows students to explore how converting conventional rooftops to green roofs can influence stormwater runoff and water quality in urban environments. The model helps students examine trade-offs between different pollutants and understand how green infrastructure can influence watershed health.
Students can investigate questions such as:
- How does increasing green roof coverage affect pollutant loads?
- Why might some pollutants decrease while others increase?
- What are the trade-offs involved in green infrastructure design?
- How might stormwater management decisions influence urban streams?
The simulation is particularly useful when discussing urban watersheds, stormwater pollution, and green infrastructure solutions.
Scientific Background
Urban Stormwater and Roof Runoff
In cities, large areas of impervious surfaces — such as roofs and pavement — prevent rainfall from infiltrating into soil. Instead, water runs off quickly into storm drains and nearby streams. As stormwater moves across surfaces, it picks up pollutants including:
- Atmospheric nitrogen deposition
- Dust and particulate matter
- Metals and trace elements
- Nutrients from organic debris
This runoff can contribute to water quality problems such as nutrient pollution and eutrophication in downstream waterways — including Scajaquada Creek and, ultimately, the Niagara River.
How Green Roofs Work
Green roofs replace traditional roofing materials with layered systems that typically include a waterproof membrane, drainage layer, lightweight growing media, and vegetation. These layers capture, store, and absorb rainfall through plant uptake, reducing the volume and velocity of stormwater leaving the roof. Environmental benefits include:
- Reduced stormwater runoff volume
- Delayed peak discharge during storms
- Urban heat island mitigation
- Habitat for pollinators and insects
- Improved building energy efficiency
- Aesthetic and psychological benefits
However, green roofs also alter the chemistry of the runoff water that does leave the roof — which is the central focus of this simulation.
Nutrient Dynamics in Green Roofs
Green roof substrates contain organic matter and mineral components that support plant growth. These materials influence runoff chemistry in complex ways. Research findings across multiple studies show consistent patterns:
- Nitrate (NO₃⁻) — plant/microbial uptake
- Ammonium (NH₄⁺) — nitrification + uptake
- Phosphorus (PO₄³⁻) — leaches from media
- Magnesium — mineral dissolution
- Boron — substrate amendments
Nitrogen decreases because plants and soil microbes actively take up nitrogen during growth. Phosphorus increases because it leaches from the growing media — particularly in younger roofs before the substrate weathers and equilibrates. The magnitude of these effects varies substantially depending on substrate composition, roof age, fertilizer use, vegetation type, rainfall intensity, and maintenance practices.
Model Assumptions & Limitations
To keep the simulation understandable for high school students, the model simplifies several aspects of real green roof behavior. Students who recognize these assumptions are practicing authentic scientific thinking.
| Model Assumption | What It Simplifies | Status |
|---|---|---|
| Fixed pollutant concentrations (mg/L) for each roof type | Real concentrations vary storm-to-storm, season-to-season, and by roof age | Simplified |
| Linear scaling of pollutant load with roof area | Real systems are non-linear; larger areas may have different detention times | Simplified |
| Uniform rainfall across the entire roof | Real storms have spatial gradients; some roof areas receive more water | Simplified |
| Identical green roof performance at all coverages | Performance depends on substrate age, vegetation, and design | Variable in reality |
| No evapotranspiration, detention, or first-flush effects | Green roofs retain some water; first flush carries higher loads | Not modeled |
| No seasonal variation in plant uptake | Nitrogen uptake is higher in summer growing season | Not modeled |
| No antecedent dry period effects | Longer dry periods accumulate more dry deposition before a storm | Not modeled |
Suggested Classroom Uses
Modeling Practice (NGSS / Science and Engineering Practices)
Students can use the simulation to analyze how changes in system inputs influence outputs, identify model limitations and assumptions, and propose improvements to the model.
Systems Thinking
The simulation is well-suited for discussions about trade-offs between pollutants and competing environmental goals.
Local Watershed Applications
Connect the simulation explicitly to local urban streams and stormwater systems. Students can investigate sources of nutrient pollution in their watershed, how green infrastructure could reduce runoff, and how other solutions compare — such as rain gardens, bioswales, or permeable pavement.
Extension Activities
- Have students design their own improved version of the simulation, specifying which variables they would add and why
- Compare green roofs with other stormwater management strategies (rain gardens, permeable pavement, bioswales) using cost-benefit analysis
- Investigate real green roof monitoring data — several universities publish long-term green roof runoff data
- Calculate watershed-scale runoff reductions if all Buffalo schools adopted green roofs
- Debate: should the Buffalo City School District prioritize green roof expansion at McKinley? Use simulation data plus economic and equity considerations