CDC 4B051 Vol 3/6
edit code 03
again by yours truly
Skin
Ceiling
Excursions
Short term
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Area
Grab
Swipe
Active
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Bacon bomb
Long pipette
Handheld dipper.
Plastic polypropylene line glass jar attached to a rope.
Weekly during times of high usage
When readings indicate there is no chlorine in the water
If an illness occurs as a result of someone using the hot tub/spa
Immediately after the hot tub/spa has been drained and cleaned
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Permissible Exposure Limit (PEL).
Short-term Exposure Limit (STEL).
Excursion Limit
Ceiling Limit.
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When you need to confirm indirect reading instrument sampling results
When an immediate answer is necessary or time is a constraint
When you don’t have access to indirect reading instruments
When you are in a potentially explosive atmosphere
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Collect as many samples as possible for each water source.
Know how the water sampling equipment should be operated
Ensure accurate results from drinking water sampling
Determine ranges for water contaminants
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Invalid sampling results
Skin contact hazard to the user
Damage to the sampling equipment
No problem as long as the contamination was minimal
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Reagents can damage the soil if not collected after use
Reagents can leave residue on the sampling equipment.
Reagents must be stored separate from any non-compatible materials
Reagents can cause inhalation hazards if not used in a well-ventilated area
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Documentation is not necessary.
A minimum of three samples is recommended
Samples should be taken on three different days
Samples should be random, collected over time, and from different workers
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Air
Soil
Water
Chemicals
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It is the most conservative
It exploits the device’s capabilities
This accounts for atmospheric changes
It makes DOEHRS data entry the most efficient
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Keep an unopened tube with the samples
Sample another worker away from the process
Open and immediately seal the media in the work area
Leave an opened tube in an area throughout sampling
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Does not establish controls for exposures
The AIHA model strives for continuous improvement
The AIHA model is very different from the AF model.
The AIHA model is best used as an initial assessment.
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Working
Internal.
Regulatory
Authoritative.
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Determine workforce size
Determine if they are effective
Determine the maximum risk employee(s).
Acquire funding for additional Personal Protective Equipment (PPE).
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Samples must be verified prior to analysis
Samples must be traceable from collection through analysis
Samples should be redundantly labeled according to 49 CFR Part 172
Samples should be sent by standard United States Postal Service (USPS) mailing procedures.
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DREL 2800
DREL 2010
M272 water testing kit
Bacteriological water test kit
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12 hours
24 hours
36 hours.
48 hours
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Monthly
After use
Before use.
Before and after use
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Before anyone enters the pool
During minimum load conditions
During the busiest time of the day
When requested by the swimming pool facility manager
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Sample collected over a period of time.
Instantaneous sample to provide quick estimate
Samples taken must be analyzed by a certified laboratory
Samples taken to demonstrate compliance with health standards
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None.
One
Three
Eight.
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Ml
Mg
M2. (its m squared, but I don't know how to type that... "sucks to your assmar")
No conversion required.
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There is no difference.
The AF model is an “iterative” approach
The DOD model does not include a control plan
Each process is designed to yield different results
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R2A Agar
EC medium
M-Endo broth
M-FC medium
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Obtain data for documentation
Produce results via a “shoot from the hip” method
Produce a cyclical process for prioritizing controls needed
Achieve equal probability of selecting an exposure period in the similar exposure group (SEG) during the assessment
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Contaminants, saturation, and air flow
Flammability, volume, and conductivity
Compound(s), density, and metallic oxide
Temperature, relative humidity, and carbon dioxide
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28 days
24 hours
2–7 days
0.25 hours
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Filters
Sorbent tubes
Fritted bubblers
Passive dosimeters
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Fritted bubbler
Sorbent tube.
Cyclone
Filters
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The HAPSITE contains internal gas standards.
The survey method completes calibration
Additional peaks and a high background is indicated.
Standby mode sufficiently calibrates the instrument.
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Ensure the correct laboratory analysis method was conducted
Ensure the results are compared to the correct type of standard
Ensure all individuals potentially affected are listed in supportive documentation
Ensure the correct units of measurement for sample and standard are being used
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Provide accurate documentation for reporting in DOEHRS
Comprehensively complete a Conceptual Site Model (CSM).
Increase confidence in characterizing and controlling potential threats
Provide information to fill the “gaps” inherent in HRA data gathering
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Never hold the bottle by the neck
Always used good personal hygiene
Never lay the bottle down on the ground
Always flush out the bottle before taking the sample
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Is soft
Is corrosive.
Is a health risk.
Can cause aesthetic problems
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Photoionization (PID).
Indirect reading instrument
Flame ionization detectors (FID).
Hazardous Air Pollutants on Site (HAPSITE).
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Measure the effects of temperature and pressure changes during shipping
Measure the effects of temperature and pressure changes during the sampling process.
Determine if any contamination occurred after calibrating the sampling pumps and before sampling began
Determine if any contamination occurred from the time the media was opened until the time it reached the laboratory.
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The extent of contamination before any cleanup is conducted
If any contamination exists after a cleanup process
The need for personnel protective equipment
If there are any hazards to personnel
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These ensure water data is accurate and useful
These eliminate the need for field quality control samples
These affect the reporting procedures required
These eliminate the need for equipment calibration
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Media collection efficiency is low
Media collection efficiency is high
Concentrations are expected to be low
Concentrations are expected to be high.
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Toxic gas monitors
Personal sampling pumps
Hand-held sampling pump
Combustible gas monitors
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Bucket and screw
Trowel and shovel
Split spoons and push tube
Veihmeyer tube and trier sampler
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Ensure the Maximum Contaminant Level Goal (MCLG) is enforced
Determine which Acute Exposure Guideline Levels (AEGL) exposure level has been reached
Ensure the worker can escape from a contaminated environment without irreversible health effects.
Ensure the worker is properly trained to understand and avoid Agency for Toxic Substance and Disease Registry (ASTDR) occupational risk levels for inhalation
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Equipment blanks contain preservatives
Trip blanks are provided by the laboratory
Trip blanks only measure the temperature of the blank
Equipment blanks are analyzed differently than other samples
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3 hours
7 hours.
8 hours
10 hours.
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Completes chain of infection
Indicates what equipment should be used
Indicates where possible contamination exists
Provides pictorial view of sampling area
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The criteria provided to you by civil engineering
The requirements provided by your MAJCOM BE
The historical performance of your drinking water system
The regulatory requirements for your drinking water system
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