SDS

Instant Power
®
Disposal & Drain Cleaner
are exceeded or symptoms are experienced.
Section 6 - Accidental Release Measures
6.1 Personal precautions, protective equipment and emergency procedures
Personal Precautions
Do not touch or walk through spilled material. Do not touch damaged containers or spilled
material unless wearing appropriate protective clothing.
Emergency Procedures
Keep unauthorized personnel away.
6.2 Environmental precautions
Avoid run off to waterways and sewers.
6.3 Methods and material for containment and cleaning up
Containment/Clean-up
Measures
Dike and control spill. Absorb with an inert material and transfer all material into a properly
labeled container for disposal. Wear appropriate protective clothing.
6.4 Reference to other sections
Refer to Section 8 - Exposure Controls/Personal Protection and Section 13 - Disposal
Considerations.
Section 7 - Handling and Storage
7.1 Precautions for safe handling
Handling
Read the entire label before using the product. Keep out of reach of children.
7.2 Conditions for safe storage, including any incompatibilities
Storage
Store at moderate temperatures. Storage Temperature: 120F Max, 35F Min, Indoor. Always store material in
its original container. Keep container tightly closed.
7.3 Specific end use(s)
Garbage disposer & drain cleaner.
Section 8 - Exposure Controls/Personal Protection
8.1 Control parameters
Exposure Limits/Guidelines
Result
Canada Ontario
United Kingdom
1,2-Propanediol
(57-55-6)
STELs
Not established
450 ppm STEL (calculated, total particulate and
vapour); 1422 mg/m3 STEL (calculated, total particulate
and vapour); 30 mg/m3 STEL (calculated, particulate)
TWAs
10 mg/m3 TWA (for assessing the visibility in a work
environment where 1,2-Propylene glycol aerosol is
present, aerosol only); 50 ppm TWA (aerosol and
vapor); 155 mg/m3 TWA (aerosol and vapor)
150 ppm TWA (total particulate and vapour); 474 mg/m3
TWA (total particulate and vapour); 10 mg/m3 TWA
(particulate)
8.2 Exposure controls
Engineering
Measures/Controls
Adequate ventilation systems as needed to control concentrations of airborne contaminants
below applicable threshold limit values. Good general ventilation should be used. Ventilation
rates should be matched to conditions. If applicable, use process enclosures, local exhaust
ventilation, or other engineering controls to maintain airborne levels below recommended
exposure limits. If exposure limits have not been established, maintain airborne levels to an
acceptable level.