24-MMP-B4 Mine Ventilation and Occupational Hygiene · May 2013
Question 6 of 6: Dilution Ventilation Design and Risk Management
Nivaar worked solution (AI-drafted; not reviewed by a licensed engineer)
Notes on this paper
National Exams (BC), 09-MMP-B4 Occupational Health, Safety and Loss Management
(Mine Ventilation and Occupational Hygiene), May 2013, 3 hours, open book with calculator
permitted. Answer any five of the six questions; every question (1-6)
is answered in full as a complete study resource.
Reference texts: Crowl & Louvar, Chemical Process Safety:
Fundamentals with Applications, 4th ed.; ACGIH, TLVs and BEIs and
Industrial Ventilation: A Manual of Recommended Practice; OSHA 29 CFR 1904
Recordkeeping; WorkSafeBC/BC Health, Safety and Reclamation Code for Mines.
Question 6: Dilution Ventilation Design and Risk Management (20 marks)
Find. The dilution air flow rate required to keep the area below
the TLV.
Approach. Convert the liquid evaporation rate to a molar vapour
generation rate, use the ideal gas law at the stated conditions to get the pure-vapour
volumetric generation rate, then divide by the TLV (as a volume fraction) and multiply
by the imperfect-mixing safety factor $K$ (ACGIH guidance: $K\approx1$–3
excellent, 3–5 good, 5–10 fair/average, >10 poor mixing — "average"
here is taken as $K=5$).
Required dilution air flow.
$$Q=\frac{\dot V_{vap}}{TLV}\times K=\frac{0.12}{50\times10^{-6}}\times5=\boxed{11982\ \text{ft}^3/\text{min}}$$
Quantity
Value
Vapour generation rate (pure RXP)
0.12 ft³/min
Required dilution ventilation rate, $Q$ ($K=5$)
≈ 11982 ft³/min (≈ 339 m³/h)
Roughly 12,000 cfm of dilution air is needed to hold this fugitive emission below
its TLV even though the raw vapour generation rate is only about 0.12 ft³/min of
pure solvent — the TLV of 50 ppm is a 20,000:1 dilution ratio on its own, and the
$K=5$ imperfect-mixing factor multiplies that by another 5× because real room air
never mixes perfectly with a point-source leak.
Check: "average" ventilation condition is taken as ACGIH mixing
factor $K=5$ (the mid-point of the commonly cited fair/average band); a poorer-mixing
facility (K=10, as used for the practice set below) would require twice this airflow for
the identical leak.
(b) Risk Management steps
Part (b) — Risk management in a hazardous operation follows a
cyclical, proactive sequence rather than a one-time calculation:
Fig. 6b — The five-step proactive risk-management cycle,
contrasted with a purely reactive (post-accident) response.
Hazard identification. Systematically identify every hazard
present in the operation (e.g. process hazard reviews, HAZOP, job safety analyses).
Risk assessment. For each identified hazard, estimate the
likelihood and severity of harm (risk = likelihood × consequence, exactly the
definition established in Question 2(c)) and rank hazards by the resulting risk
level.
Control design. Select controls for the highest-ranked risks,
following the hierarchy of controls (elimination/substitution preferred over
engineering, administrative, and PPE measures — the same inherent-safety
preference discussed in Question 2(b)).
Training and SOPs. Implement the chosen controls through written
procedures and worker training so they are actually followed in practice.
Audit and review. Periodically verify that controls remain
effective and that no new hazards have been introduced, feeding findings back into a
fresh round of hazard identification — closing the loop.
Example. A mine considering underground diesel-equipment operation
first identifies the hazard (diesel particulate matter and CO/NOx exposure in a
confined underground atmosphere), assesses the risk (high likelihood of daily exposure,
moderate-to-severe long-term respiratory consequence), designs controls following the
hierarchy (substitute to battery-electric equipment where feasible; if not, engineering
controls such as diesel particulate filters and forced ventilation; administrative
controls such as exposure-duration limits and rotation; PPE such as respirators as the
last line of defence), trains crews on the ventilation and exposure-limit procedures,
and then audits airborne DPM concentrations on a fixed schedule — feeding any
exceedance back into a reassessment of the controls, exactly as the domino/pentagon
models in Questions 1(a) and 5(c) show that interrupting any single link in the chain
prevents the loss.