Construction Air Quality Impact Calculator

Model dust and exhaust impacts with simple inputs. Test controls early, before crews arrive onsite. Get clear screening results that guide cleaner site decisions.

Calculator Inputs

Enter values, choose presets, and apply controls for a screening estimate.
White theme • Responsive grid

Units
Used in your export report.
Enter 1–3650 days.
Enter 0.5–24 hours.
Use 0 for fully electric sites.
L/hr per machine
Changes baseline emission factors.
m
Higher wind generally disperses pollutants faster.
Default 50 m is common for screening.
Select the main dust-generating activity.
Adjusts sensitivity weighting for impact.
Used to estimate AQI change.

Diesel controls

Stacking reductions
Select multiple controls to reduce emissions and fuel use.
%
Applied to PM; scaled for NOx.

Dust controls

Fugitive dust
Choose practical measures for the main dust source.
%
Stacks with selected dust controls.

Advanced overrides

Use these when you have measured factors or project-specific assumptions.
g/L
g/L
Applied per liter of diesel consumed.
g/m²/day
Used with disturbed area and duration.
Reset

Example Data Table

Sample scenario illustrating typical inputs and outputs.
Scenario Days Machines Area Distance Dust controls Engine baseline Total PM (kg) Est. AQI
Baseline earthworks 14 3 3,000 m² 250 m None Improved diesel ~9.7 Moderate
With dust suppression 14 3 3,000 m² 250 m Water + Cover Improved diesel ~6.1 Lower increase
Modern engines + controls 14 3 3,000 m² 250 m Water + Cover + Wheel wash Modern diesel ~4.6 Often improved
Example values are illustrative and will vary by site and equipment.

Formula Used

1) Diesel emissions
Fuel used (L) = machines × fuel rate (L/hr) × hours/day × days × fuel multiplier
PM (kg) = Fuel used (L) × PM factor (g/L) ÷ 1000
NOx (kg) = Fuel used (L) × NOx factor (g/L) ÷ 1000
Controls are stacked as: remaining = Π(1 − reductionᵢ), capped at 95%.
2) Fugitive dust screening
Dust PM (kg) = disturbed area (m²) × dust rate (g/m²/day) × days ÷ 1000
Dust controls are stacked the same way as diesel controls.
3) Receptor concentration estimate
Mixing volume (m³) = π × distance² × mixing height
PM increment (µg/m³) ≈ PM total (kg) × 10⁹ ÷ mixing volume
Wind dispersion factor scales concentration down with higher wind.
4) AQI and impact score
AQI is computed from total PM2.5 using standard PM2.5 breakpoints.
Impact score uses a saturating curve on weighted PM and NOx, adjusted for distance, wind, and receptor sensitivity.

How to Use This Calculator

  1. Choose a unit system, then enter duration and work hours.
  2. Enter machines and fuel rate, or set machines to zero.
  3. Select dust activity, disturbed area, distance, and receptor type.
  4. Apply diesel and dust controls that match your site plan.
  5. Use advanced overrides if you have better emission factors.
  6. Press Calculate impact to see results above the form.
  7. Download CSV or PDF to share with your team.

Source inventory for construction activities

Quantify air impacts by separating diesel exhaust from fugitive dust. Enter realistic workdays, shift hours, machines, and fuel rate to estimate fuel use and tailpipe PM and NOx. Select the dominant dust activity and disturbed area to screen dust PM. When scopes change, re-run scenarios to compare phases such as earthworks, demolition, hauling, or concrete cutting and confirm which drivers dominate total mass and daily production targets.

Engine tier and fuel sensitivity

Emission factors in the tool are expressed as grams per liter of fuel. Moving from legacy diesel to modern engines sharply lowers PM and NOx, even if fuel use is unchanged. If fuel rate is uncertain, adjust the multiplier to reflect heavy loading, idling, cold starts, and extended queuing, and operator behavior. Use the advanced override fields when you have certified fleet factors or measured fuel burn.

Dust control effectiveness planning

Controls stack as remaining emissions after each reduction, capped to avoid unrealistic totals. Typical site measures include water application, covering stockpiles, wheel washing, stabilizing haul roads, and limiting vehicle speed. The calculator helps you test combinations and identify the smallest set that achieves meaningful reduction. Treat results as planning-level; validate chosen controls with inspections, moisture targets, traffic routing, record application rates, and maintenance schedules.

Receptor and dispersion interpretation

The concentration increment uses a simplified mixing volume based on distance and mixing height, then applies a wind dispersion factor. Longer distances, higher winds, and industrial receptors generally reduce risk, while schools and hospitals increase sensitivity. Use the AQI category as a communication shorthand, not a compliance determination. If predicted increments are high, consider monitoring, rescheduling tasks, adding barriers, notifying nearby occupants, and track complaints.

Documentation and reporting outputs

After calculation, export CSV for cost, schedule, or environmental logs, and PDF for toolbox talks and stakeholder briefings. Record the assumptions that matter most: days, machines, fuel rate, dust area, distance, wind, receptor type, and chosen controls. For repeatable reporting, keep a library of baseline and mitigated scenarios with version notes, including dates and approvers. Align outputs with permit conditions, local standards, and project environmental management plans.

FAQs

1. What does the impact score represent?

It is a comparative index built from weighted PM and NOx, adjusted for distance, wind, and receptor sensitivity. Use it to rank scenarios and prioritize controls, not as a legal compliance metric.

2. Should I enter monitored AQI data here?

No. The calculator estimates a screening AQI from modeled PM2.5 increments. If you have monitors, use them to validate assumptions, tune controls, and document real-world performance alongside the scenario results.

3. How do I select control reductions?

Start with realistic values from your dust plan, vendor specifications, and past projects. Stack only the measures you will actually implement, then test sensitivity by lowering reductions to account for imperfect coverage and maintenance.

4. Why does distance affect results strongly?

The model assumes emissions mix within a volume that grows with the square of distance. As receptors move farther away, the same mass is diluted into more air, producing a smaller concentration increment.

5. Can I model electric equipment?

Yes. Choose the electric preset to set tailpipe factors to zero, then keep dust sources and site controls active. If upstream electricity emissions matter for your reporting, capture them separately in your sustainability accounting.

6. Is this suitable for permitting submissions?

It is designed for planning and communication. For permits, follow local guidance, approved dispersion models, and required averaging times. Use this tool to build scenarios, collect inputs, and justify mitigation selections.

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Important Note: All the Calculators listed in this site are for educational purpose only and we do not guarentee the accuracy of results. Please do consult with other sources as well.