CDC 4B051 Vol 3/6
edit code 03
again by yours truly
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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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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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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Working
Internal.
Regulatory
Authoritative.
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Permissible Exposure Limit (PEL).
Short-term Exposure Limit (STEL).
Excursion Limit
Ceiling Limit.
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PAC–1
PAC–2
PAC–3.
PAC–4
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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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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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Area
Grab
Swipe
Active
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Air
Soil
Water
Chemicals
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Integrated
Passive
Area
Grab
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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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Step 1- State the problem
Step 2- Identify the decision
Step 3- Identify the information inputs
Step 5- Develop the analytical approach
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The broad plan for maintaining quality in all aspects of sample collection.
The steps to be taken to determine validity of sampling and analytical procedures.
The specific procedures recommended by the USAFSAM Laboratory Sampling Guide
A checklist of pitfalls to avoid when developing, implementing and completing a sampling strategy.
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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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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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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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Color comparator
Litmus test paper
Colilert color comparator
Heterotrophic plate count
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DREL 2800
DREL 2010
M272 water testing kit
Bacteriological water test kit
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Bacon bomb
Long pipette
Handheld dipper.
Plastic polypropylene line glass jar attached to a rope.
Pasteur pipet
40 ml glass vial
Cubitaner sampler
Whirl-Pak sample bag
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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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Chemicals, microbiological, metals
Microbiological, metals, chemicals
Metals, chemicals, microbiological.
Chemicals, metals, microbiological
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1 percent chlorine solution; 0.5 minutes
1 percent chlorine solution; 2 minutes
1 percent chlorine solution; 1 minute
1 percent chlorine solution; 3 minutes
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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12 hours
24 hours
36 hours.
48 hours
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Repeat the sampling
Record the residual as the higher of the two standards
Record the residual as the lower of the two standards
Record the residual as the reading between the two standards
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Is soft
Is corrosive.
Is a health risk.
Can cause aesthetic problems
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Distilled
Deionized
Buffer solution
Calibration fluid that comes with the pH pen
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Absence/confirmation method
Presence/deficiency method
Absence/validation method
Presence/absence method
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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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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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Immediately recommend the pool be superchlorinated
Collect repeat samples from different sections of the pool
Recommend to the medical group commander the pool be closed
Collect repeat samples from the sections where you originally took samples
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Measure the exact number of live heterotrophic organism in the water
Determine the quality of the water following superchlorination
Measure changes in the swimming pool treatment process
Determine the number of fecal coliforms in the water
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R2A Agar
EC medium
M-Endo broth
M-FC medium
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28 days
24 hours
2–7 days
0.25 hours
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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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Samples are handled differently
Samples are taken at the same location
Samples are taken using different collection methods.
Samples are intended to compare laboratory differences
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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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Collection to analysis
Analysis to data reporting
Collection to data reporting
Sampling shipment to analysis
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Ensures your samples will not leak during transport
Helps detect unauthorized tampering of your samples
Prevents unwanted contaminates from getting into the container
Prevents your sample containers from being damaged during shipment
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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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Use the most current Environmental Restoration Program (EPA) standard
Use the most current Occupational Safety and Health Act (OSHA) standard
Use the most current standard listed in the Threshold Limit Value (TLV) Booklet
Use the most current and stringent occupational and environmental exposure limit (OEEL).
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The applicable Air Force Office of Safety and Health (AFOSH) Standard.
The Occupational Safety and Health Act (OSHA) criteria.
The latest data management system
Flight’s locally developed criteria.
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Conducting a thorough QA/QC process
Comparing results to a selected standard
Comparing current results to previous survey(s).
Using your chain of command for their decision
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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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Compliance screening
Instantaneous sample
Direct reading or screening compliance
Indirect reading or continuous monitoring
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