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Dust Explosion Risk in an Oral Solid Dosage Transfer Room

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Dust Explosion Risk in an Oral Solid Dosage Transfer Room

An oral solid dosage plant transfers 500 kg batches of a lactose–microcrystalline cellulose blend from a fluid-bed dryer to a bin through a pneumatic line. The dust has Kst 120 bar·m/s, MIE 25 mJ, and MEC 60 g/m³. The bucket elevator sits in a room with a 15 kW motor; equipment bonding is incomplete, and compressed air is used for housekeeping. A 2 mm dust layer covers beams and cable trays. The site wants to increase fines recycle to 20% to improve yield and reduce waste. A recent audit noted no dust hazard assessment for the room and no explosion venting on the receiving bin; the existing vent is blanked. Production argues that the material is food-grade and therefore not explosive.

1. Evaluate the food-grade argument and the significance of the measured dust parameters.

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Food-grade status describes purity and intended use, not explosion hazard. The measured Kst of 120 bar·m/s shows a dust that can produce a significant pressure rise; MIE of 25 mJ is low enough that static discharge can be an ignition source; MEC of 60 g/m³ is within the range easily generated by transfer, conveying, and compressed-air cleaning. A 2 mm layer on beams and cable trays is a secondary explosion fuel load. The blanked vent and missing dust hazard assessment mean the room has not been evaluated for containment, venting, isolation, or ignition control. The correct conclusion is that the material is explosible under the measured conditions and the facility needs a dust hazard assessment before further operation or increased fines recycle.

2. Recommend controls for housekeeping, bonding, venting, and the proposed 20% fines recycle.

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Apply the hierarchy of controls. Eliminate compressed-air cleaning; use vacuum cleaning with conductive, bonded hoses and avoid dust clouds. Bond and ground all conductive equipment, including the bin, ducting, elevator, and temporary containers, and verify low-resistance paths. Replace the blanked vent with a designed explosion-relief path to a safe outdoor location, or use containment, suppression, or inerting if venting is not feasible. Provide isolation between the bin, elevator, and room to prevent flame propagation. Control ignition sources in the room: suitable motor enclosure, no hot work, and static controls. For the 20% fines recycle, test the recycled blend for Kst, MIE, MEC, and particle size; higher fines can increase explosion severity and dustiness. Update the dust hazard assessment and management of change before the recycle is introduced.

3. Define verification and acceptance criteria to confirm the controls remain effective.

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Verification should be documented and periodic. Confirm bonding resistance on all equipment to a defined criterion, with records and rechecks after maintenance. Confirm the explosion-relief design basis, vent area, and discharge path, and inspect for blockage or unauthorized blanking. Set housekeeping acceptance criteria for dust layers based on the dust hazard assessment, with defined frequencies and vacuum equipment checks. Verify that the 20% recycle blend has been tested and that the process remains within the assessed dust parameters. Include training for operators on ignition sources, housekeeping, and emergency response. Audit the room after changes, investigate any layer buildup or bonding failure, and update the dust hazard assessment whenever material attributes or equipment change.