Document 2JbqVOq1y6aKKJXdpkMYkDbK6
FILE NAME Roofing ROOF DATE 1985 May
DOC ROOF006
DOCUMENT DESCRIPTION NIOSH - Health Hazard Evaluation Report Asbestos Shingle Tear
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PREFACE
The
Hazard Evaluations
and
Technical
Assistance
Branch of NIOSH conducts
workplace These
field
investigations investigations
of possible health hazards in the are conducted under the authority of Section 20 of
29 U.S.C. 669 which
the
Occupational Safety and Health Act of 1970
written
authorizes the Secretary of Health and Human Services fofolleomwpilnogyeaes to
request from any employer or authorized representative
has
whether
substance normally found in the place of employment
determine
any
toxic effects in such concentrations as used or found
potentially
The Hazard Evaluations and Technical Assistance Branch also provides upon medical nursing and industrial hygiene technical and consultative
rasesqiusetsatnce TA to Federal state and local agenciehsealltahbohrazairnddsustarnyd atnod other groups or individuals to control occupational prevent related trauma and disease
of Mention
Mention
company names or products does not constitute endorsement by
Tartitu Tartitu for Occupational Safety and Health
the
HETA 84-321-1590
MAY 1985 ASBESTOS SHINGLE TEAR ROCKFORD ILLINOIS
NIOSH INVESTIGATOR Laurence D. Reed
I. SUMMARY
In May 1984 the National Institute for Occupational Safety and Health NIOSH received a request to evaluate occupational exposure to airborne asbestos fibers during the tear of an old asbestos shingle
roof from a residential building On May 12 1984 a NIOSH investigator conducted an environmental evaluation of the tear operation Seventeen personal breathing samples were collected
for approximately two hours to measure potential exposure to airborne levels of asbestos fibers Ten of these samples were collected from
the tear crew 2 from the post tear clean crew and 5 from
workers applying new asbestos shingles
For the five tear workers the airborne asbestos fiber
concentrations ranged from 0.04 to 0.16 fibers per cubic centimeter of air cc arithmetic mean 0.09 cc For the two clean workers the asbestos fiber concentrations ranged from 0.13 to 0.16 cc mean 0.14 cc Finally for the 5 workers applying new shingles the fiber concentrations ranged from 0.03 to 0.08 cc mean 0.05 cc NIOSH recommends exposure to asbestos be reduced to the lowest feasible
limit
NIOSH certified half respirators with efficiency particulate
filters were worn by all members of the tear and clean crews Considering the documented air concentration levels for the tear operation half respirators should be considered the minimum level of respiratory protection face respirators should also be worn
by personnel working adjacent to and concurrent with the tear and clean operations
Based on the results of this evaluation NIOSH investigators concluded
that there was a hazard from exposure to airborne asbestos fibers
during the tear of an asbestos shingle roof Recommendations directed at reducing worker exposures are contained in Section VII of this report
KEYWORDS
SIC 1761 Roofing and Sheet Metal Work asbestos shingles roofing tear operations
Page 2 - Health Hazard Evaluation Report No. HETA 84-321
II INTRODUCTION
In May 1984 NIOSH received a request to evaluate occupational exposure to airborne asbestos fibers during the manual tear of an old asbestos shingle roof from a large residential building On May 12 1984 a NIOSH investigator conducted an environmental evaluation of roofing workers for exposure to airborne asbestos fibers
III BACKGROUND
The tear operation was performed by 7 workers on May 12 1984 During the hour procedure old asbestos shingles were removed from the roof using handled wedges The loosened shingles and debris were then shoveled from the roof and moved by wheelbarrow to trucks for
discarding During the tear operation several other workers were applying a new asphalt roof to adjacent and previously cleared
portions of the building
All workers involved in the tear operation wore certified face respirators with efficiency particulate filters No
other protective clothing was worn
IV EVALUATION DESIGN AND METHODS
On May 12 1984 17 personal breathing and 4 area air samples were collected from workers on open mixed cellulose ester fiber filters
for approximately 2 hours at a flow rate of 2.0 liters per 1pm All of these samples were analyzed for fiber count
NIOSH Method CAM 239 utilizing phase contrast microscopy
minute
according to
PCM Six
of these samples were further analyzed for fiber
qualitative analysis of the particulate material transmission electron microscopy TEM The TEM
size and for
on the filters using analysis was performed
according to the Zumwalde procedure outlined in NIOSH Publication No. 77-204 The PCM method for fiber counting detects fiber greater than 5 micrometers um in length and greater than 0.2 um in diameter and is the fiber count used for comparison with the existing environmental exposure criteria listed in Section V of this
report The TEM method detects fibers of all sizes
Two area air samples 1 upwind 1 downwind were collected on the roof during the hour tear operation using weighed polyvinyl chloride PVC filters for total particulate weight Two other area samples were collected from inside the residential building One of the samples was collected from the interior of the building and the
other was collected near an open window
Page 3 - Health Hazard Evaluation Report No. HETA 84-321
V. EVALUATION CRITERIA
A. Environmental Criteria
As a guide to the evaluation
exposures NIOSH field staff criteria for assessment of a
of the
employ
number
hazards posed by workplace
environmental evaluation
of chemical and physical
agents These criteria are intended to suggest levels of exposure to which most workers may be exposed up to 10 hours per day 40
hours per week for a working lifetime without experiencing adverse
health effects It is however important to note that not all
workers will be protected from adverse health effects if their
exposures are maintained below these levels A small percentage
may experience adverse health effects because of individual
susceptibility a existing medical condition and a
hypersensitivity allergy
The primary sources of environmental evaluation criteria for the
workplace are 1 NIOSH Criteria Documents and Recommendations
2 the American Conference of Governmental Industrial Hygienists
ACGIH Threshold Limit Values TLV's and 3 the U.S. Department
of Labor OSHA recommendations
OSHA standards
occupational health standards Often the NIOSH and ACGIH TLV's are lower than the corresponding
Both NIOSH recommendations and ACGIH TLV's usually
are based on more recent information than are the OSHA standards
The OSHA standards also may be required to take into account the feasibility of controlling exposures in various industries where the agents are used the recommended standards by contrast are based primarily on concerns relating to the prevention of
occupational disease In evaluating the exposure levels and the
recommendations for reducing these levels found in this report it should be noted that industry is legally required to meet only
those levels specified by an OSHA standard
A weighted average TWA exposure refers to the average
airborne concentration of a substance during a normal 8- to hour
workday Some substances have recommended short exposure
limits or ceiling values which are intended to supplement the TWA where there are recognized toxic effects from high short
exposures
.
' atnf?
.
Page 4 - Health Hazard Evaluation Report No. HETA 84-321
Increased health risk resulting from occupational exposure to
asbestos has been well documented in the scientific literature
Initially asbestos was associated with a chronic and debilitating lung disease called asbestosis which normally occurred following long exposures to high levels of asbestos fibers More recently asbestos has also been linked to several types of cancer including mesothelioma a rare cancer of the chest and abdominal lining and cancers of the lung esophagus stomach and colon These cancers usually appear many years after the initial contact with asbestos and sometimes result from short and low level exposures This indicates that there may not be a safe level of exposure to asbestos for the elimination of all cancer risk Additionally cigarette smoking in combination with asbestos
exposure greatly increases the risk of developing lung cancer
Listed below fibers
are
the
evaluation
criteria
for
airborne
asbestos
Source
NIOSH
Environmental Exposure Limit
Lowest Feasible Limit
ACGIH
2.0 cc chrysotile asbestos
OSHA
2.0 cc
VI RESULTS AND DISCUSSION
A bulk sample of the asbestos shingle was analyzed laboratory and was found to contain 30 chrysotile
by a NIOSH
asbestos
contract
The airborne concentrations of asbestos fibers for the 17 personal breathing samples ranged from 0.03 to 0.16 cc Table I Ten of the 17 personal samples were collected from the tear crew and the concentrations of these samples ranged from 0.04 to 0.16 cc
arithmetic mean 0.09 cc Two of the 17 personal samples were
collected from the clean crew and the concentration for these samples ranged from 0.13 to 0.16 cc arithmetic mean 0.14 cc
The other 5 personal samples were collected from workers applying new shingles The range of concentrations for these 5 personal samples was
0.03 to 0.08 cc arithmetic mean 0.05 cc The airborne asbestos concentrations for the 4 area samples ranged from 0.02 to 0.14 cc
Page 5 - Health Hazard Evaluation Report No. HETA 84-321
For the 6 samples 4 personal 2 area which were further analyzed by
TEM Table 1 the airborne concentrations of asbestos fibers ranged from 0.32 to 1.12 cc 4 personal 0.32 to 1.12 cc 2 area 0.51 to 0.74 cc All 6 samples showed higher fiber concentrations when analyzed by TEM than by PCM because TEM detects fibers of all sizes In addition the TEM analysis of these 6 samples showed the primary particulate constituents of the filters to be aluminum and iron compounds as well as organic material All of the asbestos fibers measured by TEM were chrysotile asbestos
Because of temperature and humidity conditions 75 20 RH during sampling the measured airborne concentrations of asbestos fibers are probably lower than actual concentrations because of the build of electrostatic charge on the sampling cassettes This charge build
resulted in a visibly substantial accumulation of fibers on the inside
of the cassettes
The highest level mean 0.14 cc of airborne asbestos fibers was found during the post tear clean operation The mean fiber concentration for personal samples taken during the tear operation 0.09 cc was approximately double the mean concentration 0.05 cc for the new shingle application workers Both upwind and downwind area asbestos concentrations were low 0.02 cc However the area sample taken within the building near the open window was comparatively high 0.14 cc indicating contamination from the tear and | clean operation
VII DISCUSSION AND RECOMMENDATIONS
The following recommendations should help reduce worker exposure to
airborne asbestos fibers
1. All workers involved in the tear and clean operations should wear certified half respirators with efficiency particulate filters
Considering the documented air concentrations this should be considered the minimum level of respiratory protection for the tear clean and new shingle application personnel All respirators should be properly fitted cleaned inspected for maintenance problems and placed in a lock bag after each use Also the efficiency filter media should be changed
periodically particularly when breathing through the respirator
becomes labored
Page 6 ~ Health Hazard Evaluation Report No. HETA 84-321
2. To help minimize airborne levels of asbestos fibers the roof should be wetted with water or some other wetting agent before the tear operation
Where feasible building occupants should be evacuated during asbestos shingle tear and clean operations
To minimize contamination of the inside of the building door's and windows should be closed off and the heating conditioning system should be turned off during tear and clean operations
To help minimize the exposure of the roofing workers and their family members NIOSH recommends that contaminated work clothes be removed and placed in a bag for commercial laundering before leaving the work site These clothes should be washed after each
use
VIII REFERENCES
1 National Institute for Occupational Safety and Health Criteria for a recommended standard occupational exposure to asbestos Cincinnati Ohio National Institute for Occupational Safety and Health 1977. DHEW publication no NIOSH 77-169
National Institute for Occupational Safety and Health NIOSH occupational health guidelines for chemical hazards Cincinnati Ohio National Institute for Occupational Safety and Health 1981. DHHS NIOSH publication no 81-123
American Conference of Governmental Industrial Hygienists
Threshold limit values for chemical substances and physical agents
in the workroom environment and biological exposure indices with intended changes for 1984-85 Cincinnati Ohio ACGIH 1984
National Institute for Occupational Safety and Health Occupational diseases a guide to their recognition Cincinnati Ohio National Institute for Occupational Health 1977. DHEW NIOSH publication no 77-181
Revised ed Safety and
Occupational National Institute for
industrial environment
Safety and Health it's evaluation and control
The
Cincinnati
Ohio 1973.
National Institute for Occupational Safety and Health DHEW NIOSH publication no 74-117
Proctor NH Hughes JP Chemical hazards of the workplace
Philadelphia J.B. Lippencott Company 1978
Page 7 - Health Hazard Evaluation Report No. HETA 84-321
IX AUTHORSHIP AND ACKNOWLEDGEMENTS
Report Prepared by
Laurence D. Reed|
Industrial Hygiene Industrial Hygiene
Engineer
Section
Field Assistance by
John Barnhard
Health United
and
and Safety Specialist Union of Roofers Waterproofers
Allied Workers
Originating Office
Hazard Evaluations and Technical Assistance Branch
Division of Surveillance Hazard Evaluations and Field Studies
Report Typed By
Jacqueline Grass Typist Industrial Hygiene
Section
X. DISTRIBUTION AND AVAILABILITY OF REPORT
Copies of this report are currently available upon request from NIOSH Division of Standards Development and Technology Transfer Publications
Dissemination Section 4676 Columbia Parkway Cincinnati Ohio 45226 After 90 days the report will be available through the National
Technical Information Service NTIS 5285 Port Royal Springfield
Virginia 22161. Information regarding its availability through NTIS
Cincinnati can be obtained from NIOSH Publications Office at the
address Copies of this report have been sent to
1. United Union of Roofers Waterproofers and Allied Workers 2 NIOSH Region V 3 OSHA Region V
For the purpose
shall be posted employees for a
of informing affected employees copies of this by the employer in a prominent place accessible
period of 30 calendar days
report
to the
Table I
Asbestos Fiber Concentration for Personal and Area Samples
Asbestos Roof Shingle Tear
Rockford Illinois HETA 84-321
May 12 1984
Job Classification
Sample Duration
Asbestos Concentration cc
Personal
Tear il
20-9 31-10
Tear 2
21-9 34-11
Tear 3 Tear 4
26-9 9 34-10
22-9 33-10
Tear 5
23-9 33-10
New Shingle 1 New Shingle 2 New Shingle 3 New Shingle 4 New Shingle 5 Asbestos Clean 1
Asbestos Clean 2
19-10 16-10 11-10 10-10 36-10
44-11
40-11
Area Area 1
inside building - shelf
45-11
;
Area 2
inside building - window
Area 3
roof - upwind
45-11 52-10
Area 4
roof ~ downwind
01-10
Neasured by Phase Contrast Microscopy PCM
2 Heasured by Transmission Electron Microscopy
TEM
PCM1
30.64 0.16 0.14 0.11
0.04 0.08
0.06 0.09 0.08 0.11 0.03 0.03 0.07 0.04 0.08 0.13
0.16
0.05
0.14
0.02
0.02
TEM2
0.75 1.12
0.32 .37
0.51 0.74
WET AN
INMENS Fi
TRAND TRAND HUMAN SERVICES
- MEALTH SERVICE
CENTERCENS TERS FOR DISEASE CONTROL
NATIONAL INSTITUTE FOR OCCUPATIONAL SAFETY AND HEALTH ROBERT ROBERT A. TAFT LABORATORIES
4676 COLUMI PARKWAY CINCINNATI OHIO 45226
PEN
OFFICIAL BUSINESS Y FOR PRIVATE USE 300
Third Class lail
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