B3-CONTROLS AND PPE Flashcards
What are the 8 Principles of Good Practice
Design and operate processes and activities to minimise emission, release and spread of substances hazardous to health.
Take into account all relevant routes of exposure – inhalation, skin and ingestion – when developing control measures.
Control exposure by measures that are proportional to the health risk.
Choose the most effective and reliable control options that minimise the escape and spread of substances hazardous to health.
Where adequate control of exposure cannot be achieved by other means, provide, in combination with other control measures, suitable personal protective equipment.
Check and review regularly all elements of control measures for their continuing effectiveness.
Inform and train all employees on the hazards and risks from substances with which they work, and the use of control measures developed to minimise the risks.
Ensure that the introduction of measures to control exposure does not increase the overall risk to health and safety.
Additional controls for Carcinogens, Mutagens and Asthmagens
COSHH Reg 7(5): Where not RP to prevent exposure:
(a) Totally enclose process and handling systems (unless not RP).
(b) Prohibit eating, drinking and smoking in areas that may be contaminated by carcinogens or mutagens.
(c) Clean floors, walls, etc. regularly.
(d) Designating potentially contaminated areas and using warning signs.
(e) Safe storage, handling and disposal, including using closed and clearly labelled containers.
“Adequate Control” for carcinogens, mutagens and asthmagens
COSHH (Reg 7) states that control of exposure to most hazardous substances will only be treated as adequate if the:
appropriate Workplace Exposure Limit (WEL) is not exceeded; and
eight “principles of good practice” have been applied.
Stricter Control for Carcinogens, Mutagens and Asthmagens
Regulation 7 requires a stricter level of control where:
the substance is either carcinogenic /mutagenic (R45, R46, R49 or is listed in Schedule 1 of COSHH);
or can cause occupational asthma (R42, R42/43 or is listed in Section C of “Asthmagen? Critical Assessments of the Evidence for Agents Implicated in Occupational Asthma”).
Then control of exposure to the hazardous substances will only be treated as adequate if:
the appropriate WEL is not exceeded;
the eight “principles of good practice” have been applied;
and
exposure is reduced to as low a level as is reasonably practicable.
The hierarchy of controls of COSHH regulation 7
Eliminate exposure
Substitute the substance
Modify work
Total enclosure
Engineering controls
Minimise numbers exposed
PPE
Three main types of asbestos commonly used were:
Crocidolite (blue).
Amosite (brown).
Chrysotile (white).
Common Illnesses from Asbestos
Asbestosis
Lung Cancer
Mesothelioma
Diffused plural thickening
managing asbestos in non-domestic premises reg 4 of car
The duty holder must:
Carry out an assessment - to identify ACMs, their location and condition.
Assume that materials are ACMs - unless evidence that they are not.
Keep an up-to-date register of ACMs, their location and condition.
Assess the risks - of exposure to fibres from these ACMs.
Establish a plan - to manage these materials.
Provide information - to anyone likely to work on or disturb the ACMs (e.g. contractors).
Monitor and review - the assessment and plan
Outline Asbestos Surveys
Management survey:
should be carried out to identify the asbestos risk for normal day-to-day occupation and maintenance of the building,
normal non-invasive (i.e. materials are not removed or damaged during the survey
samples may be taken for analysis.
Refurbishment and demolition survey:
should carried out if there is planned upgrade, refurbishment or demolition work on premises where ACMs potentially exist.
is normally invasive and destructive premises must be vacant before it can take place; and cannot be re-occupied until certified as fit for re-occupation.
MANAGEMENT PLAN
Determined by the condition of the ACM?
Good condition - label but leave undisturbed.
Damaged but acceptable – cover, encapsulate or otherwise make safe, label and leave in place.
Poor condition or likely to be disturbed – remove.
State the criteria when work with asbestos can be considered to be ‘unlicensed’.
Sporadic exposure and low intensity, risk assessment shows the control limit is not exceeded,
short maintenance activities,
asbestos fibres are firmly linked,
sealing ACM’s that are in good condition, air monitoring, collection and analysis of samples
CONTROL MEASURES FOR ASBESTOS
Carry out a risk assessment.
Prepare a written plan of work.
Only carry out licensed asbestos work if he holds a licence – note exceptions.
Notify the enforcing authority at least 14 days before licensed work starts (some non-licensable work also notifiable).
Provide information, instruction and training.
Prevent or reduce exposure to asbestos.
Ensure that control measures are used.
Maintain control measures.
Provide protective clothing.
Prepare and practise procedures to deal with accidents, incidents and emergencies.
Prevent or reduce the spread of asbestos.
Ensure premises and plant are kept suitably clean.
Ensure work areas are designated and marked as asbestos areas or respirator zones as appropriate.
Carry out air monitoring.
Ensure that any air monitoring carried out is done by suitably accredited persons using the approved standard method.
Carry out health surveillance for all workers who undertake licensed work.
Provide adequate washing and changing facilities.
Ensure that ACMs are appropriately stored and disposed of.
CONTROL LIMITS FOR ASBESTOS
In the UK limits are established by the Control of Asbestos Regulations 2012:
The control limit is 0.1 fibres cm3 of air averaged over a continuous period of 4 hours.
Sporadic and of low intensity means that the concentration of asbestos in the air does not exceed 0.6 f/cm3 measured over 10 minute period
How does a LEV (Local exhaust ventilation) System operation?
Operate by removing contaminated air at the point of generation and ducting it away from work areas. The contaminated air might then be cleaned and is then exhausted to atmosphere.
LEV System Types – by Hood Design
Enclosing Hood
Receiving (Receptor) Hood
Capturing (Captor) Hood
LEV General Principles of Hood Design
Enclose the source as much as possible.
Position the hood as close as possible to the source.
Take advantage of speed and direction of contaminant.
Match the hood size to the process and cloud size.
Keep contaminant away from worker’s breathing zone.
Minimise eddies within the hood.
Make sure the hood is practical and comfortable to use.
Trial and test before putting into full use.
LEV DUCTING
As straight as possible (to maintain laminar flow).
Gentle bends and acute angle joins.
Well supported.
Sufficient airflow to prevent deposition of solids.
Access ports for regular cleaning.
LEV FILTER OR PURIFYING SYSTEM:
Must be appropriate.
Toxic gases may need to be neutralised.
Particulates often removed by cyclone or bag filter.
Explosion risk may exist with dusts or vapours/gases.
VARIOUS AIR CLEANING DEVICES CAN BE USED:
PARTICLE COLLECTORS:
Fabric filters.
Cyclones.
Electrostatic precipitators.
GAS/VAPOUR COLLECTORS:
Thermal oxidisers (destroy solvents).
Scrubbers (remove contaminants).
Recovery units (collect and reclaim).
LEV FANS AND MOTORS:
Correct type for the system.
Correct capacity:
Sufficient power.
Margin for overloads.
Centrifugal fans are typical.
LEV DISCHARGE TO ATMOSPHERE:
Discharged air must not re-enter buildings until diluted down to negligible concentrations.
Discharge is normally via a ‘stack’.
Emissions to Atmosphere:
Extracted air must not re-enter building.
SOURCE STRENGTH, CAPTURE ZONES AND CAPTURE VELOCITY
SOURCE STRENGTH: Combination of the volume rate of release of the contaminant cloud, the cloud volume, shape and speed and the contaminant concentration.
Worker exposure depends on many things including: source strength and distance from source
CAPTURE ZONE - the area around the inlet to the LEV system that the system is extracting contaminated air from.
CAPTURE VELOCITY – the air velocity required at a contaminant source to overcome the movement of the contaminant cloud and draw it into the hood.
LEV Testing statutory
Engineering controls such as LEV are subject to statutory examination and test: COSHH - 14 months CLAW -14 months CAR - 6 months By a competent person.
Proof of competence for LEV testing
Proof of competence might mean qualified through:
British Occupational Hygiene Society (BOHS),
Chartered Institution of Building Service Engineers (CIBSE) or
Institute of Local Exhaust Ventilation Engineers (ILEVE).
There is a UKAS accreditation scheme for LEV Thorough Examination and Test (TExT
Sources of Information available to the examiner:
LEV system commissioning report. LEV user manual. System logbook. Previous LEV system statutory report. Confirmation that there have been no changes to the LEV, layout or process since the last test.
Stages of LEV testing (Big question, might take a while to get head round it)
Stage 1 – Thorough Visual and Structural Inspection of LEV
Examination of:
All external parts of the system for damage, wear and tear.
Internal duct and hatch seals.
Filter material and any built-in filter pressure gauges.
Filter cleaning devices to ensure they work properly.
Water flow and sump in a wet scrubber.
Monitors and alarms fitted to the system.
The fan and associated drive mechanism, e.g. fan belt.
Three Stages to Carrying Out TestingStage 2 – Measuring Technical Performance
Quantitative methods are used to measure the technical characteristics of the LEV system for comparison against its design specification:
Transport velocity and duct velocity.
Static pressure.
Face velocity.
Transport Velocity
The air velocity required to convey particles and prevent deposition in ducts.
Duct velocity can be directly measured using pitot tube.
Static Pressure Difference between inside and outside air. Measured using pressure gauge: Manometer. Diaphragm gauge.
Face Velocity
The average velocity of air at the open front face of a hood or booth.
Measured using an anemometer.
The face of the inlet is divided up into an imaginary grid.
The air velocity is measured at the centre of each imaginary rectangle.
Readings can be averaged and each reading compared to the average to note the degree of variation.
Variations over 20% of average indicate that the airflow distribution is uneven and requires adjustment.
Three Stages to Carrying Out TestingStage 3 – Assessing Control Effectiveness
Qualitative techniques are used to assess the effectiveness of the LEV system. These often involve the visualisation of air movement using different techniques:
Dust lamp (Tyndall beam). Smoke.
Dust Lamp (Tyndall Illumination)
A powerful light illuminates the dust cloud.
The cloud is viewed obliquely to the light beam and a screen is used to shield the lamp.
Cloud is observed directly or photographed.
Smoke
Smoke produced as a single cloud.
Used to visualise air movement.
Can be formed by:
Smoke tubes.
Smoke generators.
Smoke pellets.