Environment and Water Simulators
Environmental simulators for air quality, emissions, dispersion, ventilation, water treatment, desalination, and stormwater.
Adjacent categories
Simulator list
How to Use
- Select your simulation type: air quality modeling, emission dispersion, ventilation analysis, water treatment process, or stormwater management
- Input process parameters—for emissions dispersion enter stack height (m), exhaust velocity (m/s), temperature differential (K), and ambient wind speed; for water treatment specify flow rate (m³/h), influent concentration (mg/L), and treatment residence time (min)
- Configure categorical filters (cat-filter) to isolate specific pollutants, treatment stages, or environmental zones, then execute simulation to generate concentration profiles, removal efficiency curves, and compliance reports
Worked Example
Industrial wastewater treatment plant: influent ammonia concentration 45 mg/L, design flow 500 m³/h, activated sludge basin residence time 6 hours. Apply nitrification filter selecting cat-filter for biological treatment stage. Simulator calculates ammonia removal rate of 92% with final effluent 3.6 mg/L, confirming compliance with discharge limit of 5 mg/L. Stack emissions case: chemical facility stack diameter 1.2 m, exhaust temperature 120°C, ambient 15°C, wind speed 3.5 m/s. Ground-level SO₂ concentration at 500 m downwind: 0.8 ppm, acceptable under EPA one-hour standard of 75 ppb when accounting for atmospheric dispersion using Gaussian plume model.
Practical Notes
- Apply cat-filter to separate point-source emissions from fugitive dust; stormwater modeling requires separate categorical treatment since first-flush effects concentrate pollutants in initial 12–25 mm rainfall depth
- Ventilation simulations in enclosed spaces (e.g., parking garages, industrial workshops) use air changes per hour (ACH)—6 ACH minimum for CO removal; coordinate with exhaust stack height to prevent short-circuiting
- Desalination reverse-osmosis units operate 40–85% recovery; higher recovery increases concentrate salinity and scaling risk; cross-flow velocity typically 0.3–0.6 m/s to minimize membrane fouling