Mine Ventilation

Mine ventilation is the engineered movement of air to maintain a breathable underground atmosphere, dilute and remove airborne contaminants, and help control heat. It connects the mine’s openings, working areas, fans and ventilation controls into an operating system. This overview focuses on underground mines, where developing excavations and changing activities continually alter ventilation needs.[1]

Ventilation System Architecture

Primary ventilation establishes routes from intake openings, through working districts and service areas, to returns. The arrangement must account for contamination along each route: air passing one source can affect a downstream workplace. Auxiliary ventilation serves locations lacking adequate through-flow, such as blind development headings. Ducted systems may force air towards a heading, extract it, or combine these arrangements. Auxiliary fans depend on adequate primary supply and a suitable return path; poor positioning or imbalance can recirculate contaminated air.[1]

Stoppings separate flow paths, doors preserve access while maintaining separation, and passive regulators introduce adjustable resistance to distribute air.[2] Ducts and curtains also influence delivery. Holes, loose joints, constrictions and poorly arranged bends can reduce the quantity reaching a face. Consequently, a running fan does not demonstrate that a workplace receives its planned airflow.[3]

Airflow, Pressure and Network Behaviour

Airflow rate describes volume per unit time. Pressure differences drive movement through airways, whose resistance depends on length, cross-section, roughness and obstructions. For fixed geometry and air density, increasing airflow increases the pressure loss that the ventilation system must overcome. A fan’s operating flow depends on its interaction with the connected network, including other fans. Opening a connection or adjusting a regulator can therefore redistribute flow beyond the location of the change. Predictions also require a consistent air density basis.[2]

The U.S. ANSI/AMCA 214-21 standard for commercial and industrial fans defines distinct performance quantities:[4]

QuantityMeaning
Fan total pressureOutlet total pressure minus inlet total pressure. Total pressure includes static and velocity components.
Fan static pressureFan total pressure minus outlet velocity pressure; this is not simply the difference between outlet and inlet static pressures.
Air powerPower transferred by the fan to the air, dependent on both flow and pressure rise.
Shaft input powerMechanical power supplied to the impeller shaft.
Electrical input powerPower entering the fan drive system, including motor and applicable transmission/controller losses.

Fan total efficiency compares air power with shaft input; fan static efficiency uses the static pressure basis. An efficiency based on electrical input includes drive losses. Comparisons therefore need the same pressure convention, air density basis and power boundary. These definitions describe fan performance, not the effectiveness of contaminant control at a workplace.[4]

Establishing Ventilation Requirements

Requirements begin with an inventory of where people work, which activities occur and when they overlap. Development, production, maintenance and construction can create different contaminant loads. Material handling, ground support, blasting and diesel equipment need to be located within this inventory.[3] Relevant contaminants can include mineral dust, diesel particles and gases, blasting fumes and gases released from rock strata. The assessment must establish which are present and where they enter the air.[1]

Ventilation demand from diesel equipment depends on the engines and their use, emission control equipment and maintenance, as well as the air available at each workplace. Source reduction, ventilation and operating arrangements should be assessed together. It follows that reducing engine emissions does not, by itself, establish that every ventilation requirement has been met.[5]

A documented design basis should specify the activities allowed in each ventilated area and the measurements used to verify conditions. Ventilation capacity and the production schedule must agree: changes in the mobile fleet or working locations can require a revised allocation of air. Applicable legal requirements must be established for the mine’s jurisdiction and conditions, alongside its engineering criteria.[6]

Environmental Conditions and System Integration

Heat loads can include rock, diesel equipment and compression as air descends; moisture pickup also changes underground conditions.[1]

Thermal assessment considers temperature, humidity, air movement and radiant heat alongside workload and clothing. More airflow does not necessarily establish acceptable conditions, because its cooling effect depends on the air state and heat load. Refrigeration or other cooling measures may be required. These measures need coordination with contaminant control: local cooling air can disturb an intended ventilation pattern. The engineering implication is that thermal conditions and air quality need distinct acceptance checks, even when they share ventilation infrastructure.[7]

Routine operation and emergency arrangements need separate evaluation. The NSW Resources Regulator’s 2021 underground ventilation guide addresses loss of power to fans and interfaces with emergency plans for events including fire. Consequently, normal fan settings do not define an emergency operating strategy. The mine needs evaluated emergency arrangements, assigned responsibilities and a controlled process for ventilation changes.[6]

Measurement, Control and Verification

Ventilation surveys establish flow directions and quantities, pressure differences and environmental conditions. Compare these observations with the current ventilation plan and network model. Model results depend on how the physical system is represented and on the quality of its inputs. Treat measured agreement as evidence for the conditions surveyed, and reassess assumptions when predicting a changed network.[2]

Inspect the physical delivery system as well as instruments: damaged ducting, failed connections and poorly maintained curtains can explain differences between planned and delivered flow. Findings should relate to actual work locations rather than only to fan status.[3]

Airflow measurements describe transport; contaminant measurements test the air quality being controlled. For diesel exposure, NIOSH recommends assessing workplace airflow together with contaminant concentrations. These complementary checks help investigate whether deterioration reflects insufficient supply, increased emissions or altered air distribution. Assessments should represent relevant operating activity, so that a quiet-period measurement is not assumed to describe a busier production period.[5]

Changes to fans, controls or operating activities should be authorized, communicated and checked after implementation. Updated measurements then feed back into the plan, model and operating restrictions, connecting design assumptions with actual performance.[6]

References

  1. Department of Industry and Resources. Underground Ventilation (Metalliferrous Mines): Guideline. 1997. Edition: Version 1.0. Location: Section 1, printed p. 3; Sections 3.1–3.4, printed pp. 4–10. Report number: ZED569LF. Accessed: 2026-10-26. ↩1 ↩2 ↩3 ↩4
  2. Malcolm J. McPherson. Subsurface Ventilation Engineering. Location: Section 4.2.1, chapter pp. 4-3–4-4; Sections 5.1–5.2, chapter pp. 5-2–5-4; Section 6.1, chapter p. 6-2; Section 7.1, chapter pp. 7-1–7-2; Sections 7.4.1–7.4.2, chapter pp. 7-24 and 7-26; Sections 10.5–10.5.1, chapter pp. 10-25–10-26. Accessed: 2026-10-26. ↩1 ↩2 ↩3
  3. Workplace Safety North. Auxiliary Ventilation: Good Installation and Maintenance Practices for Miners. 2021. Location: Sections 1–3, printed pp. 1–2; auxiliary installation and maintenance examples, printed pp. 4–7. Accessed: 2026-10-26. ↩1 ↩2 ↩3
  4. Air Movement and Control Association International. Test Procedure for Calculating Fan Energy Index (FEI) for Commercial and Industrial Fans and Blowers. 2021. Location: Sections 3.22–3.43, printed pp. 3–5; Sections 3.66 and 3.70, printed pp. 6–7; Section 6.3, printed p. 10. Report number: ANSI/AMCA Standard 214-21. Accessed: 2026-10-26. ↩1 ↩2
  5. Aleksandar D. Bugarski; Samuel J. Janisko; Emanuele G. Cauda; James D. Noll; Steven E. Mischler. Diesel Aerosols and Gases in Underground Mines: Guide to Exposure Assessment and Control. 2011. Location: Section 1, printed pp. 1–2; Section 3.1, printed pp. 76–81. Report number: RI 9687; DHHS (NIOSH) Publication No. 2012-101. Accessed: 2026-10-26. ↩1 ↩2
  6. NSW Resources Regulator. Technical Reference Guide: Ventilation Control Plan – Guide for the development of a ventilation control plan in underground mines. 2021. Edition: Version 1. Location: Section 3.1, printed pp. 9–11; Sections 3.2.2.7–3.2.5, printed pp. 20–22. Accessed: 2026-10-26. ↩1 ↩2 ↩3
  7. Brenda Jacklitsch; W. Jon Williams; Kristin Musolin; Aitor Coca; Jung-Hyun Kim; Nina Turner. Criteria for a Recommended Standard: Occupational Exposure to Heat and Hot Environments. 2016. Edition: Revised Criteria 2016. Location: Chapter 5, printed p. 59; Sections 5.1.2–5.1.3, printed pp. 61–62; Sections 6.1.1 and 6.1.3, printed pp. 71 and 74. Report number: DHHS (NIOSH) Publication No. 2016-106. Accessed: 2026-10-26. ↩