ED^ United States

Environmental Protection Agency

Office of Chemical Safety and
Pollution Prevention

Final Risk Evaluation for

Asbestos
Part 1: Chrysotile Asbestos

Systematic Review Supplemental File:

Data Quality Evaluation for
Epidemiological Studies of Ovarian and Laryngeal

Cancers

December 2020


-------
Table Listing

l Acheson et al. 1982: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes 3

2	Acheson et al. 1982: Evaluation of Cancer for Lung Cancer Mortality Outcomes . 6

3	Newhouse and Sullivan 1989: Evaluation of Cancer for Ovarian Cancer Mortality

Outcomes	 ^

4	Newhouse and Sullivan 1989: Evaluation of Cancer for Female Lung Cancer Mor-

tality Outcomes 	12

5	Newhouse and Sullivan 1989: Evaluation of Cancer for Male and Female Lung

Cancer Mortality Outcomes 	15

6	Newhouse and Sullivan 1989: Evaluation of Cancer for Laryngeal Cancer Mortal-

ity Outcomes	 18

7	Gardner and Powell 1986: Evaluation of Cancer for Ovarian Cancer Mortality

Outcomes	21

8	Gardner and Powell 1986: Evaluation of Cancer for Female Lung Cancer Mortality

Outcomes	24

9	Gardner and Powell 1986: Evaluation of Cancer for Male and Female Lung Cancer

Mortality Outcomes	27

10	Gardner and Powell 1986: Evaluation of Cancer for Laryngeal Cancer Mortality

Outcomes	 30

11	Pira et al. 2017: Evaluation of Cancer for Lung Cancer Mortality Outcomes ... 33

12	Pira et al. 2017: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes gg

13	Mamo and Costa 2004: Evaluation of Cancer for Ovarian Cancer Mortality Out-

comes 	39

14	Mamo and Costa 2004: Evaluation of Cancer for Female Lung Cancer Mortality

Outcomes	42

15	Mamo and Costa 2004: Evaluation of Cancer for Male and Female Lung Cancer

Mortality Outcomes	44

16	Mamo and Costa 2004: Evaluation of Cancer for Laryngeal Cancer Mortality

Outcomes	46

17	Germani et al. 1999: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes 49

18	Germani et al. 1999: Evaluation of Cancer for Lung Cancer Mortality Outcomes 52

19	Germani et al. 1999: Evaluation of Cancer for Laryngeal Cancer Mortality Out-

comes 	 55

20	Tarchi et al. 1994: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes 53

21	Tarchi et al. 1994: Evaluation of Cancer for Female Lung Cancer Mortality

Outcomes	 60

22	Tarchi et al. 1994: Evaluation of Cancer for Male and Female Lung Cancer

Mortality Outcomes	62

23 Tarchi et al. 1994: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

	 64

2 of 65


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Table 1: Acheson et al. 1982: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes

Study Citation: Acheson, E. D., Gardner, M. J., Pippard, E. C., Grime, L. P. (1982). Mortality of two groups of women who manufactured gas masks
from chrysotile and crocidolite asbestos: a 40-year follow-up Occupational and Environmental Medicine, 39(4,4), 344-348

Data Type:	gasmask	manufacturing	women	ovarian-Cancer

HERO ID:	32

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

Medium	X 0.4	0.8 The study setting was described and details on the

mask manufacturing process and products were pro-
vided. Subjects were included based on residence
in Blackburn in 1939 and indication of mask manu-
facturing on their employment records from the Of-
fice of Population Censuses and Surveys. There is
some uncertainty whether employment records from
this resource would be complete for all women in the
area.

High	X 0.4	0.4 A small number of women (4) died before the follow-

up period began (1951), but this is not expected to
appreciably bias the results. No other indication of
loss-to-follow-up was provided.

Medium x 0.2	0.4 Rates of mortality for England and Wales (1951-

1980) were used to compare with women from Black-
burn. Local mortality rates 1968-1978 were used to
adjust for location. The study authors note that
rates of cause-specific mortality for the relevant area
(Blackburn, Leyland, and Preston) were only avail-
able for this time period. Applying mortality rates
from this specific time period to the full follow-up
period may insert some uncertainty into the results.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
High

x 0.5

NA
x 0.5

1.5

NA
0.5

Exposure was assessed by employment at each of the
asbestos gas mask manufacturing facilities only.

Temporality was established. Women residing in
Blackburn in 1939 with employment records showing
gas mask manufacturing were followed until 1980.
This is a sufficiently long follow-up period for deter-
mining rates of cause-specific mortality.

Domain 3: Outcome Assessment

Continued on next page

3 of 65


-------
. continued from previous page

Study Citation: Acheson, E. D., Gardner, M. J., Pippard, E. C., Grime, L. P. (1982). Mortality of two groups of women who manufactured gas masks
from chrysotile and crocidolite asbestos: a 40-year follow-up Occupational and Environmental Medicine, 39(4,4), 344-348

Data Type:	gasmask	manufacturing	women	ovarian-Cancer

HERO ID:	32

Domain



Metric

Rating^

MWF*

Score

Comments^



Metric 7:

Outcome measurement or characterization

Medium

x 0.667

1.33

Vital status was determined form 1951 to 1980 for
all subjects. It was not expressly stated, however,
vital status was presumably obtained from the Na-
tional Health Service Central Register. Mortality
from cancer was detailed using ICD-8 codes. His-
tological confirmation of cancer deaths was not de-
scribed.



Metric 8:

Reporting Bias

Medium

x 0.333

0.67

Outcomes prespecified in the abstract, introduction,
and methods were provided either qualitatively or
quantitatively in the results. SMR estimates were
provided with observed cases, expected cases, and
confidence intervals.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Metric 11: Co-exposure Confounding

Medium	x 0.5	1 Only women were included in the analysis. Age-

and calendar period-specific (in 5-year bins) mor-
tality rates were calculated, accounting for age and
time period. Individual smoking information was
not available and not accounted for in the analysis.

Medium	X 0.25 0.5 Covariate information was presumably obtained

from the same source as vital status and
employment—the National Health Service Central
Register, Office of Population Censuses and Surveys.
Medium X 0.25 0.5 Masks manufactured at the Blackburn facility were

noted to contain only chrysotile, charcoal, and
merino wool. Crocidolite was not reported to be
used at the relevant manufacturing facility.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Metric 14: Reproducibility of analyses

Medium	X 0.4	0.8 Cause-specific mortality for women employed in the

mask manufacturing industry in Blackburn were de-
termined by calculating SMRs using the person-
years method. This is an appropriate design for the
study question.

Medium X 0.2	0.4 A total of 570 women were included in the analy-

sis and followed for a total of 14,324 person-years.
This is a sufficiently large population to detect an
effect. The number of women observed with ovarian
cancer was relatively low (n=5) and may need to be
interpreted with caution.

Medium	X 0.2	0.4 Analyses were adequately described and could be re-

produced given original data.

Continued on next page

4 of 65


-------
. continued from previous page

Study Citation: Acheson, E. D., Gardner, M. J., Pippard, E. C., Grime, L. P. (1982). Mortality of two groups of women who manufactured gas masks

from chrysotile and crocidolite asbestos: a 40-year follow-up Occupational and Environmental Medicine, 39(4,4), 344-348
Data Type:	gasmask_manufacturing_women_ovarian-Cancer

HERO ID:	32

Domain

Metric

Rating^

MWF*

Score

Comments^



Metric 15

Statistical models

Medium

x 0.2

0.4

The statistical methods used were
tails on the area adjustment were
this was not the primary outcome

transparent. De-
limited, however,
of the study.

Domain 6: Other Considerations for Biomarker Selection and Measurement











Metric 16

Use of Biomarker of Exposure



NA

NA





Metric 17

Effect biomarker



NA

NA





Metric 18

Method Sensitivity



NA

NA





Metric 19

Biomarker stability



NA

NA





Metric 20

Sample contamination



NA

NA





Metric 21

Method requirements



NA

NA





Metric 22

Matrix adjustment



NA

NA





Overall Quality Determination1"

Medium

1.9

Extracted

Yes





MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating,
ft This metric met the criteria for high confidence as expected for this type of study

5 of 65


-------
Table 2: Acheson et al. 1982: Evaluation of Cancer for Lung Cancer Mortality Outcomes

Study Citation: Acheson, E. D., Gardner, M. J., Pippard, E. C., Grime, L. P. (1982). Mortality of two groups of women who manufactured gas masks
from chrysotile and crocidolite asbestos: a 40-year follow-up Occupational and Environmental Medicine, 39(4,4), 344-348

Data Type:	gasmask	manufacturing	women	lung-Cancer

HERO ID:	32

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

Medium	X 0.4	0.8 The study setting was described and details on the

mask manufacturing process and products were pro-
vided. Subjects were included based on residence
in Blackburn in 1939 and indication of mask manu-
facturing on their employment records from the Of-
fice of Population Censuses and Surveys. There is
some uncertainty whether employment records from
this resource would be complete for all women in the
area.

High	X 0.4	0.4 A small number of women (4) died before the follow-

up period began (1951), but this is not expected to
appreciably bias the results. No other indication of
loss-to-follow-up was provided.

Medium x 0.2	0.4 Rates of mortality for England and Wales (1951-

1980) were used to compare with women from Black-
burn. Local mortality rates 1968-1978) were used
to adjust for location. The study authors note that
rates of cause-specific mortality for the relevant area
(Blackburn, Leyland, and Preston) were only avail-
able for this time period. Applying mortality rates
from this specific time period to the full follow-up
period may insert some uncertainty into the results.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
High

x 0.5

NA
x 0.5

1.5

NA
0.5

Exposure was assessed by employment at each of the
asbestos gas mask manufacturing facilities only.

Temporality was established. Women residing in
Blackburn in 1939 with employment records showing
gas mask manufacturing were followed until 1980.
This is a sufficiently long follow-up period for deter-
mining rates of cause-specific mortality.

Domain 3: Outcome Assessment

Continued on next page

6 of 65


-------
. continued from previous page

Study Citation: Acheson, E. D., Gardner, M. J., Pippard, E. C., Grime, L. P. (1982). Mortality of two groups of women who manufactured gas masks
from chrysotile and crocidolite asbestos: a 40-year follow-up Occupational and Environmental Medicine, 39(4,4), 344-348

Data Type:	gasmask	manufacturing	women	lung-Cancer

HERO ID:	32

Domain



Metric

Rating^

MWF*

Score

Comments^



Metric 7:

Outcome measurement or characterization

Medium

x 0.667

1.33

Vital status was determined form 1951 to 1980 for
all subjects. It was not expressly stated, however,
vital status was presumably obtained from the Na-
tional Health Service Central Register. Mortality
from cancer was detailed using ICD-8 codes. His-
tological confirmation of cancer deaths was not de-
scribed.



Metric 8:

Reporting Bias

Low

x 0.333

1.0

Outcomes prespecified in the abstract, introduction,
and methods were provided either qualitatively or
quantitatively in the results. SMR estimates were
provided with observed cases, expected cases, and
confidence intervals. Reported cases included one
mesothelioma case

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Metric 11: Co-exposure Confounding

Medium	x 0.5	1 Only women were included in the analysis. Age-

and calendar period-specific (in 5-year bins) mor-
tality rates were calculated, accounting for age and
time period. Individual smoking information was
not available and not accounted for in the analysis.

Medium	X 0.25 0.5 Covariate information was presumably obtained

from the same source as vital status and
employment—the National Health Service Central
Register, Office of Population Censuses and Surveys.

Medium X 0.25 0.5 Masks manufactured at the Blackburn facility were

noted to contain only chrysotile, charcoal, and
merino wool. Crocidolite was not reported to be
used at the relevant manufacturing facility.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Metric 14: Reproducibility of analyses
Metric 15: Statistical models

Medium	X 0.4	0.8 Cause-specific mortality for women employed in the

mask manufacturing industry in Blackburn were de-
termined by calculating SMRs using the person-
years method. This is an appropriate design for the
study question.

Medium X 0.2	0.4 A total of 570 women were included in the analysis

and followed for a total of 14,324 person-years. This
is a sufficiently large population to detect an effect.

Medium	X 0.2	0.4 Analyses were adequately described and could be re-

produced given original data.

Medium	X 0.2	0.4 The statistical methods used were transparent. De-

tails on the area adjustment were limited, however,
this was not the primary outcome of the study.

Continued on next page

7 of 65


-------
. continued from previous page

Study Citation: Acheson, E. D., Gardner, M. J., Pippard, E. C., Grime, L. P. (1982). Mortality of two groups of women who manufactured gas masks

from chrysotile and crocidolite asbestos: a 40-year follow-up Occupational and Environmental Medicine, 39(4,4), 344-348
Data Type:	gasmask_manufacturing_women_lung-Cancer

HERO ID:	32

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 6: Other Considerations for Biomarker Selection and Measurement

Metric 16

Use of Biomarker of Exposure

NA

NA

Metric 17

Effect biomarker

NA

NA

Metric 18

Method Sensitivity

NA

NA

Metric 19

Biomarker stability

NA

NA

Metric 20

Sample contamination

NA

NA

Metric 21

Method requirements

NA

NA

Metric 22

Matrix adjustment

NA

NA

Overall Quality Determination1"

Medium

2.0

Extracted

Yes





MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

8 Of 65


-------
Table 3: Newhouse and Sullivan 1989: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_women	ovary-Cancer

HERO ID:	3082792

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition
Metric 3: Comparison Group

Medium	X 0.4	0.8 Retrospective occupational mortality cohort includ-

ing 13 450 subjects (men and women) first employed
between 1941 and 1979 in one factory located in
the UK. Follow-up is until 1986. Nine men and one
woman with unknown dates of birth have been ex-
cluded from the original cohort. At the end of 1979,
2.6% of workers had emigrated. Setting of the plant
is well described. No other details are provided on
participants.

High	X 0.4	0.4 Little loss to follow-up due to emigration (2.6%).

Medium	X 0.2	0.4 Although not clearly spelled out in this reference,

Berry and Newhouse 1983 (HERO ID 43) mentions
use of national death rates as comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Medium

x 0.5

NA
x 0.5

1.5

NA

Exposure assessed based solely on duration of em-
ployment at the plant. Job titles were not available.
Exposure levels are reported at the plant level (over
20 fibers/ml before 1931, 5-20 f/mL from 1931-1950,
less than 5 f/mL after 1970).

Adequate follow-up (43 years) for cancer mortality
to be observed.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Low

Metric 8: Reporting Bias	Medium

X 0.667 2 Death certificates from the National Health Service
Central Registrar, were coded to

the 8th revision of the International Classification of
Disease (ICD). There are no other details provided
on outcome assessment, and ICD codes are only re-
ported for chronic respiratory diseases.

X 0.333 0.67 Some cancer mortality results are reported for "other
causes", some are spelled out in the text, but it is
unclear if all are reported. Exposure levels are re-
ported at the plant level (over 20 fibers/ml before
1931, 5-20 f/mL from 1931-1950, less than 5 f/mL
after 1970).

Domain 4: Potential Confounding/Variable Control

Continued on next page

9 of 65


-------
.. . continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_women	ovary-Cancer

HERO ID:	3082792

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 9:
Metric 10

Metric 11

Covariate Adjustment
Covariate Characterization

Co-exposure Confounding

Medium
Low

Low

x 0.5
x 0.25

x 0.25

1

0.75
0.75

Sex, age and period were accounted for. Smoking
was not accounted for.

There is no discussion of covariate characterization,
but likely it came from employment records and
death certificates.

There is no specific discussion of potential co-
exposures, however the occupational setting sug-
gests potential for other exposures, which could be
differential depending on the job titles of the work-
ers.

Domain 5: Analysis

Metric 12

Metric 13

Metric 14
Metric 15

Study Design and Methods

Statistical power

Reproducibility of analyses
Statistical models

Medium

Medium

Medium
Medium

x 0.4

x 0.2

x 0.2
x 0.2

0.8

0.4

0.4
0.4

SMRs were calculated using the subject year
method, with 90% confidence intervals
(90% CI). Poisson or normal approximation were
used depending on the number of observed deaths.

The number of participants, number of observed
deaths and length of follow-up are adequate.

Basic details are provided in the report.

Adequate models. SMRs based on 30 or fewer deaths
confidence intervals were

computed with the exact method based on the Pois-
son distribution. The normal approximation was
used for others.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.3



Extracted



Yes







Continued on next page . ..

10 of 65


-------
. continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of

Industrial Medicine, 46(3,3), 176-179
D at a Type:	Asbestos_workers_SMR_women_ovary- Cancer

HERO ID:	3082792

Domain	Metric	Rating ^ MWF* Score	Comments^

* MWF = Metric Weighting Factor

t High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

+ The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

if any metric is Unacceptable

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

11 of 65


-------
Table 4: Newhouse and Sullivan 1989: Evaluation of Cancer for Female Lung Cancer Mortality Outcomes

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_women	lung-Cancer

HERO ID:	3082792

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition
Metric 3: Comparison Group

Medium	X 0.4	0.8 Retrospective occupational mortality cohort includ-

ing 13 450 subjects (men and women) first employed
between 1941 and 1979 in one factory located in
the UK. Follow-up is until 1986. Nine men and one
woman with unknown dates of birth have been ex-
cluded from the original cohort. At the end of 1979,
2.6% of workers had emigrated. Setting of the plant
is well described. No other details are provided on
participants.

High	X 0.4	0.4 Little loss to follow-up due to emigration (2.6%).

Medium	X 0.2	0.4 Although not clearly spelled out in this reference,

Berry and Newhouse 1983 (HERO ID 43) mentions
use of national death rates as comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Medium

x 0.5

NA
x 0.5

1.5

NA

Exposure assessed based solely on duration of em-
ployment at the plant. Job titles were not available.
Exposure levels are reported at the plant level (over
20 fibers/ml before 1931, 5-20 f/mL from 1931-1950,
less than 5 f/mL after 1970).

Adequate follow-up (43 years) for cancer mortality
to be observed.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Low

Metric 8: Reporting Bias	Medium

X 0.667 2 Death certificates from the National Health Service
Central Registrar, were coded to

the 8th revision of the International Classification of
Disease (ICD). There are no other details provided
on outcome assessment, and ICD codes are only re-
ported for chronic respiratory diseases.

X 0.333 0.67 Some cancer mortality results are reported for "other
causes", some are spelled out in the text, but it is
unclear if all are reported. Exposure levels are re-
ported at the plant level (over 20 fibers/ml before
1931, 5-20 f/mL from 1931-1950, less than 5 f/mL
after 1970).

Domain 4: Potential Confounding/Variable Control

Continued on next page

12 of 65


-------
.. . continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_women	lung-Cancer

HERO ID:	3082792

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 9:
Metric 10

Metric 11

Covariate Adjustment
Covariate Characterization

Co-exposure Confounding

Medium
Low

Low

x 0.5
x 0.25

x 0.25

1

0.75
0.75

Sex, age and period were accounted for. Smoking
was not accounted for.

There is no discussion of covariate characterization,
but likely it came from employment records and
death certificates.

There is no specific discussion of potential co-
exposures, however the occupational setting sug-
gests potential for other exposures, which could be
differential depending on the job titles of the work-
ers.

Domain 5: Analysis

Metric 12

Metric 13

Metric 14
Metric 15

Study Design and Methods

Statistical power

Reproducibility of analyses
Statistical models

Medium

Medium

Medium
Medium

x 0.4

x 0.2

x 0.2
x 0.2

0.8

0.4

0.4
0.4

SMRs were calculated using the subject year
method, with 90% confidence intervals
(90% CI). Poisson or normal approximation were
used depending on the number of observed deaths.

The number of participants, number of observed
deaths and length of follow-up are adequate.

Basic details are provided in the report.

Adequate models. SMRs based on 30 or fewer deaths
confidence intervals were

computed with the exact method based on the Pois-
son distribution. The normal approximation was
used for others.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.3



Extracted



Yes







Continued on next page . ..

13 of 65


-------
. continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of

Industrial Medicine, 46(3,3), 176-179
Data Type:	Asbestos_workers_SMR_women_lung-Cancer

HERO ID:	3082792

Domain	Metric	Rating ^ MWF* Score	Comments^

* MWF = Metric Weighting Factor

t High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

+ The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

if any metric is Unacceptable

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

14 of 65


-------
Table 5: Newhouse and Sullivan 1989: Evaluation of Cancer for Male and Female Lung Cancer Mortality Outcomes

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_combined	lung-Cancer

HERO ID:	3082792

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition
Metric 3: Comparison Group

Medium	X 0.4	0.8 Retrospective occupational mortality cohort includ-

ing 13 450 subjects (men and women) first employed
between 1941 and 1979 in one factory located in
the UK. Follow-up is until 1986. Nine men and one
woman with unknown dates of birth have been ex-
cluded from the original cohort. At the end of 1979,
2.6% of workers had emigrated. Setting of the plant
is well described. No other details are provided on
participants.

High	X 0.4	0.4 Little loss to follow-up due to emigration (2.6%).

Medium	X 0.2	0.4 Although not clearly spelled out in this reference,

Berry and Newhouse 1983 (HERO ID 43) mentions
use of national death rates as comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Medium

x 0.5

NA
x 0.5

1.5

NA

Exposure assessed based solely on duration of em-
ployment at the plant. Job titles were not available.
Exposure levels are reported at the plant level (over
20 fibers/ml before 1931, 5-20 f/mL from 1931-1950,
less than 5 f/mL after 1970).

Adequate follow-up (43 years) for cancer mortality
to be observed.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Low

Metric 8: Reporting Bias	Medium

X 0.667 2 Death certificates from the National Health Service
Central Registrar, were coded to

the 8th revision of the International Classification of
Disease (ICD). There are no other details provided
on outcome assessment, and ICD codes are only re-
ported for chronic respiratory diseases.

X 0.333 0.67 Some cancer mortality results are reported for "other
causes", some are spelled out in the text, but it is
unclear if all are reported. Exposure levels are re-
ported at the plant level (over 20 fibers/ml before
1931, 5-20 f/mL from 1931-1950, less than 5 f/mL
after 1970).

Domain 4: Potential Confounding/Variable Control

Continued on next page

15 of 65


-------
.. . continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_combined	lung-Cancer

HERO ID:	3082792

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 9:
Metric 10

Metric 11

Covariate Adjustment
Covariate Characterization

Co-exposure Confounding

Medium
Low

Low

x 0.5
x 0.25

x 0.25

1

0.75
0.75

Sex, age and period were accounted for. Smoking
was not accounted for.

There is no discussion of covariate characterization,
but likely it came from employment records and
death certificates.

There is no specific discussion of potential co-
exposures, however the occupational setting sug-
gests potential for other exposures, which could be
differential depending on the job titles of the work-
ers.

Domain 5: Analysis

Metric 12

Metric 13

Metric 14
Metric 15

Study Design and Methods

Statistical power

Reproducibility of analyses
Statistical models

Medium

Medium

Medium
Medium

x 0.4

x 0.2

x 0.2
x 0.2

0.8

0.4

0.4
0.4

SMRs were calculated using the subject year
method, with 90% confidence intervals
(90% CI). Poisson or normal approximation were
used depending on the number of observed deaths.

The number of participants, number of observed
deaths and length of follow-up are adequate.

Basic details are provided in the report.

Adequate models. SMRs based on 30 or fewer deaths
confidence intervals were

computed with the exact method based on the Pois-
son distribution. The normal approximation was
used for others.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.3



Extracted



Yes







Continued on next page . ..

16 of 65


-------
. continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of

Industrial Medicine, 46(3,3), 176-179
Data Type:	Asbestos_workers_SMR_combined_lung-Cancer

HERO ID:	3082792

Domain	Metric	Rating ^ MWF* Score	Comments^

* MWF = Metric Weighting Factor

t High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

+ The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

if any metric is Unacceptable

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

17 Of 65


-------
Table 6: Newhouse and Sullivan 1989: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_men	larynx-Cancer

HERO ID:	3082792

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition
Metric 3: Comparison Group

Medium	X 0.4	0.8 Retrospective occupational mortality cohort includ-

ing 13 450 subjects (men and women) first employed
between 1941 and 1979 in one factory located in
the UK. Follow-up is until 1986. Nine men and one
woman with unknown dates of birth have been ex-
cluded from the original cohort. At the end of 1979,
2.6% of workers had emigrated. Setting of the plant
is well described. No other details are provided on
participants.

High	X 0.4	0.4 Little loss to follow-up due to emigration (2.6%).

Medium	X 0.2	0.4 Although not clearly spelled out in this reference,

Berry and Newhouse 1983 (HERO ID 43) mentions
use of national death rates as comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Medium

x 0.5

NA
x 0.5

1.5

NA

Exposure assessed based solely on duration of em-
ployment at the plant. Job titles were not available.
Exposure levels are reported at the plant level (over
20 fibers/ml before 1931, 5-20 f/mL from 1931-1950,
less than 5 f/mL after 1970).

Adequate follow-up (43 years) for cancer mortality
to be observed.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Low

Metric 8: Reporting Bias	Medium

X 0.667 2 Death certificates from the National Health Service
Central Registrar, were coded to

the 8th revision of the International Classification of
Disease (ICD). There are no other details provided
on outcome assessment, and ICD codes are only re-
ported for chronic respiratory diseases.

X 0.333 0.67 Some cancer mortality results are reported for "other
causes", some are spelled out in the text, but it is
unclear if all are reported. Exposure levels are re-
ported at the plant level (over 20 fibers/ml before
1931, 5-20 f/mL from 1931-1950, less than 5 f/mL
after 1970).

Domain 4: Potential Confounding/Variable Control

Continued on next page

18 of 65


-------
.. . continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of
Industrial Medicine, 46(3,3), 176-179

Data Type:	Asbestos	workers	SMR_men	larynx-Cancer

HERO ID:	3082792

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 9:
Metric 10

Metric 11

Covariate Adjustment
Covariate Characterization

Co-exposure Confounding

Medium
Low

Low

x 0.5
x 0.25

x 0.25

1

0.75
0.75

Sex, age and period were accounted for. Smoking
was not accounted for.

There is no discussion of covariate characterization,
but likely it came from employment records and
death certificates.

There is no specific discussion of potential co-
exposures, however the occupational setting sug-
gests potential for other exposures, which could be
differential depending on the job titles of the work-
ers.

Domain 5: Analysis

Metric 12

Metric 13

Metric 14
Metric 15

Study Design and Methods

Statistical power

Reproducibility of analyses
Statistical models

Medium

Medium

Medium
Medium

x 0.4

x 0.2

x 0.2
x 0.2

0.8

0.4

0.4
0.4

SMRs were calculated using the subject year
method, with 90% confidence intervals
(90% CI). Poisson or normal approximation were
used depending on the number of observed deaths.

The number of participants, number of observed
deaths and length of follow-up are adequate.

Basic details are provided in the report.

Adequate models. SMRs based on 30 or fewer deaths
confidence intervals were

computed with the exact method based on the Pois-
son distribution. The normal approximation was
used for others.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.3



Extracted



Yes







Continued on next page . ..

19 of 65


-------
. continued from previous page

Study Citation: Newhouse, M. L., Sullivan, K. R. (1989). A mortality study of workers manufacturing friction materials: 1941-86 British Journal of

Industrial Medicine, 46(3,3), 176-179
D at a Type:	Asbestos_workers_SMR_men_larynx- Cancer

HERO ID:	3082792

Domain	Metric	Rating ^ MWF* Score	Comments^

* MWF = Metric Weighting Factor

t High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

+ The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

if any metric is Unacceptable

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

20 of 65


-------
Table 7: Gardner and Powell 1986: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_ovary-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Low

Metric 2: Attrition

Metric 3: Comparison Group

High
Low

X 0.4	1.2 Retrospective occupational cohort study of 2167

workers (1510 men and 657 women) employed be-
tween 1941 and 1983 in chrysotile asbestos ce-
ment products factories in England, South Wales
and Sweden . This study combines three occupa-
tional cohorts. Only the results for men are de-
scribed. The periods of employment varied be-
tween plants/studies. Eligibility criteria vary be-
tween plants (employment for at least 6 months
(plant 1), Thomas et al 1982 HERO ID 207), 3
months (plant 2/Swedish cohort, Ohlson and Hog-
stedt 1985 HERO D: 3083459 ), none for plant 3
(Garner et al 1986 HERO ID 3083223)

Follow-up for ascertainment of vital status was until
December 1977 (plant 1), 1982 (plant 2) and Decem-
ber 1984 for plant 3. Comparability of cohorts is not
discussed.

X 0.4	0.4 Loss to follow -up was minimal: 5% in Plant 1, 2% in

Plant 2/Swedish cohort (1%), 30% for men in Plant
3 cohort.

X 0.2	0.6 SMRs were estimated using England and Wales

for comparison population (plants 1 and 3), and
Swedish national death rates (Plant 2 cohort), is
is unclear what the comparison population for total
mortality rates were calculated.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposures were based on employment at the re-
spective plants, Industrial hygiene measures are de-
scribed confirming exposure. For the combined anal-
yses type of job was not considered.

Follow-up sometimes ended the year after employ-
ment, making it an inadequate length of time for
cancer mortality to be observed.

Domain 3: Outcome Assessment

Continued on next page

21 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_ovary-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Metric 7:

Outcome measurement or characterization

Low

x 0.667

Metric 8: Reporting Bias

Medium

x 0.333 0.67

Sources were different by cohort. Plant 1 and 3
cohorts used death certificates from the National
Health Service Central Register and the Department
of Health and Social Security. ICD codes are listed
for Plant 1 cohort. In the Plant 2 cohort, vital status
was traced through the death and burial books of the
parishes. Death certificates were checked with the
Swedish National Central Bureau of Statistics and
the officially determined underlying cause of death
has been used. ICD codes are not listed for cohort
3. There is potential for outcome misclassification
from death certificates. In addition, for the analy-
sis combining the three cohorts, there is high poten-
tial misclassification due to various sources, national
practices, etc .

Measured outcomes were reported, out unclear how
the reference population was used for the combined
cancers across cohorts.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization
Metric 11: Co-exposure Confounding

Low	X 0.5	1.5 Although not specifically stated, age and calendar

year were accounted for in the Plant-specific analy-
ses, making it likely that the total SMR would be
adjusted similarly.

Low	X 0.25 0.75 No discussion of covariate characterization, likely

from plant records and death certificates.

Medium X 0.25 0.5 For plant 2: "The vast majority of asbestos used

was chrysotile but 630 tons of amosite were used
between 1949 and 1951 and 400 tons of crocidolite
in 1962. The use of these amphiboles was estimated
to be less than 1% of all asbestos used." Plant 3
only used chrysotile asbestos except for a "small"
amount of amosite during 4 months in 1976. This is
not expected to appreciably bias the results.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Medium X 0.4	0.8 Adequate design and methods. SMRs were esti-

mated using Poisson distribution assumptions (plant
2), or by the person years method using a computer
program (Plants 1 and 3).

Medium X 0.2	0.4 2167 workers (1510 men and 657 women) were in-

cluded in the analysis, however the short follow-up
may limit the power to detect an effect.

Continued on next page

22 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the

Society of Occupational Medicine, 36(4,4), 124-126
Data Type:	Asbestos_workers_SMR_ovary-Cancer

HERO ID:	3083384

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 14
Metric 15

Reproducibility of analyses
Statistical models

Medium
Low

x 0.2
x 0.2

© ©

Unclear how/what the referent group was used for
the combined cohorts analysis.

There is no description of how the combined SMRs
were calculated.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.6



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

23 of 65


-------
Table 8: Gardner and Powell 1986: Evaluation of Cancer for Female Lung Cancer Mortality Outcomes

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_lung-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Low

Metric 2: Attrition

Metric 3: Comparison Group

High
Low

X 0.4	1.2 Retrospective occupational cohort study of 2167

workers (1510 men and 657 women) employed be-
tween 1941 and 1983 in chrysotile asbestos ce-
ment products factories in England, South Wales
and Sweden . This study combines three occupa-
tional cohorts. Only the results for men are de-
scribed. The periods of employment varied be-
tween plants/studies. Eligibility criteria vary be-
tween plants (employment for at least 6 months
(plant 1), Thomas et al 1982 HERO ID 207), 3
months (plant 2/Swedish cohort, Ohlson and Hog-
stedt 1985 HERO D: 3083459 ), none for plant 3
(Garner et al 1986 HERO ID 3083223)

Follow-up for ascertainment of vital status was until
December 1977 (plant 1), 1982 (plant 2) and Decem-
ber 1984 for plant 3. Comparability of cohorts is not
discussed.

X 0.4	0.4 Loss to follow -up was minimal: 5% in Plant 1, 2% in

Plant 2/Swedish cohort (1%), 30% for men in Plant
3 cohort.

X 0.2	0.6 SMRs were estimated using England and Wales

for comparison population (plants 1 and 3), and
Swedish national death rates (Plant 2 cohort), is
is unclear what the comparison population for total
mortality rates were calculated.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposures were based on employment at the re-
spective plants, Industrial hygiene measures are de-
scribed confirming exposure. For the combined anal-
yses type of job was not considered.

Follow-up sometimes ended the year after employ-
ment, making it an inadequate length of time for
cancer mortality to be observed.

Domain 3: Outcome Assessment

Continued on next page

24 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_lung-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Metric 7:

Outcome measurement or characterization

Low

x 0.667

Metric 8: Reporting Bias

Medium

x 0.333 0.67

Sources were different by cohort. Plant 1 and 3
cohorts used death certificates from the National
Health Service Central Register and the Department
of Health and Social Security. ICD codes are listed
for Plant 1 cohort. In the Plant 2 cohort, vital status
was traced through the death and burial books of the
parishes. Death certificates were checked with the
Swedish National Central Bureau of Statistics and
the officially determined underlying cause of death
has been used. ICD codes are not listed for cohort
3. There is potential for outcome misclassification
from death certificates. In addition, for the analy-
sis combining the three cohorts, there is high poten-
tial misclassification due to various sources, national
practices, etc .

Measured outcomes were reported, out unclear how
the reference population was used for the combined
cancers across cohorts.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization
Metric 11: Co-exposure Confounding

Low	X 0.5	1.5 Although not specifically stated, age and calendar

year were accounted for in the Plant-specific analy-
ses, making it likely that the total SMR would be
adjusted similarly.

Low	X 0.25 0.75 No discussion of covariate characterization, likely

from plant records and death certificates.

Medium X 0.25 0.5 For plant 2: "The vast majority of asbestos used

was chrysotile but 630 tons of amosite were used
between 1949 and 1951 and 400 tons of crocidolite
in 1962. The use of these amphiboles was estimated
to be less than 1% of all asbestos used." Plant 3
only used chrysotile asbestos except for a "small"
amount of amosite during 4 months in 1976. This is
not expected to appreciably bias the results.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Medium X 0.4	0.8 Adequate design and methods. SMRs were esti-

mated using Poisson distribution assumptions (plant
2), or by the person years method using a computer
program (Plants 1 and 3).

Medium X 0.2	0.4 2167 workers (1510 men and 657 women) were in-

cluded in the analysis, however the short follow-up
may limit the power to detect an effect.

Continued on next page

25 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the

Society of Occupational Medicine, 36(4,4), 124-126
Data Type:	Asbestos_workers_SMR_lung-Cancer

HERO ID:	3083384

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 14
Metric 15

Reproducibility of analyses
Statistical models

Medium
Low

x 0.2
x 0.2

© ©

Unclear how/what the referent group was used for
the combined cohorts analysis.

There is no description of how the combined SMRs
were calculated.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.6



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

26 of 65


-------
Table 9: Gardner and Powell 1986: Evaluation of Cancer for Male and Female Lung Cancer Mortality Outcomes

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_lung	combined-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Low

Metric 2: Attrition

Metric 3: Comparison Group

High
Low

X 0.4	1.2 Retrospective occupational cohort study of 2167

workers (1510 men and 657 women) employed be-
tween 1941 and 1983 in chrysotile asbestos ce-
ment products factories in England, South Wales
and Sweden . This study combines three occupa-
tional cohorts. Only the results for men are de-
scribed. The periods of employment varied be-
tween plants/studies. Eligibility criteria vary be-
tween plants (employment for at least 6 months
(plant 1), Thomas et al 1982 HERO ID 207), 3
months (plant 2/Swedish cohort, Ohlson and Hog-
stedt 1985 HERO D: 3083459 ), none for plant 3
(Garner et al 1986 HERO ID 3083223)

Follow-up for ascertainment of vital status was until
December 1977 (plant 1), 1982 (plant 2) and Decem-
ber 1984 for plant 3. Comparability of cohorts is not
discussed.

X 0.4	0.4 Loss to follow -up was minimal: 5% in Plant 1, 2% in

Plant 2/Swedish cohort (1%), 30% for men in Plant
3 cohort.

X 0.2	0.6 SMRs were estimated using England and Wales

for comparison population (plants 1 and 3), and
Swedish national death rates (Plant 2 cohort), is
is unclear what the comparison population for total
mortality rates were calculated.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposures were based on employment at the re-
spective plants, Industrial hygiene measures are de-
scribed confirming exposure. For the combined anal-
yses type of job was not considered.

Follow-up sometimes ended the year after employ-
ment, making it an inadequate length of time for
cancer mortality to be observed.

Domain 3: Outcome Assessment

Continued on next page

27 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_lung	combined-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Metric 7:

Outcome measurement or characterization

Low

x 0.667

Metric 8: Reporting Bias

Medium

x 0.333 0.67

Sources were different by cohort. Plant 1 and 3
cohorts used death certificates from the National
Health Service Central Register and the Department
of Health and Social Security. ICD codes are listed
for Plant 1 cohort. In the Plant 2 cohort, vital status
was traced through the death and burial books of the
parishes. Death certificates were checked with the
Swedish National Central Bureau of Statistics and
the officially determined underlying cause of death
has been used. ICD codes are not listed for cohort
3. There is potential for outcome misclassification
from death certificates. In addition, for the analy-
sis combining the three cohorts, there is high poten-
tial misclassification due to various sources, national
practices, etc .

Measured outcomes were reported, out unclear how
the reference population was used for the combined
cancers across cohorts.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization
Metric 11: Co-exposure Confounding

Low	X 0.5	1.5 Although not specifically stated, age and calendar

year were accounted for in the Plant-specific analy-
ses, making it likely that the total SMR would be
adjusted similarly.

Low	X 0.25 0.75 No discussion of covariate characterization, likely

from plant records and death certificates.

Medium X 0.25 0.5 For plant 2: "The vast majority of asbestos used

was chrysotile but 630 tons of amosite were used
between 1949 and 1951 and 400 tons of crocidolite
in 1962. The use of these amphiboles was estimated
to be less than 1% of all asbestos used." Plant 3
only used chrysotile asbestos except for a "small"
amount of amosite during 4 months in 1976. This is
not expected to appreciably bias the results.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Medium X 0.4	0.8 Adequate design and methods. SMRs were esti-

mated using Poisson distribution assumptions (plant
2), or by the person years method using a computer
program (Plants 1 and 3).

Medium X 0.2	0.4 2167 workers (1510 men and 657 women) were in-

cluded in the analysis, however the short follow-up
may limit the power to detect an effect.

Continued on next page

28 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the

Society of Occupational Medicine, 36(4,4), 124-126
Data Type:	Asbestos_workers_SMR_lung_combined-Cancer

HERO ID:	3083384

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 14
Metric 15

Reproducibility of analyses
Statistical models

Medium
Low

x 0.2
x 0.2

© ©

Unclear how/what the referent group was used for
the combined cohorts analysis.

There is no description of how the combined SMRs
were calculated.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.6



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

29 of 65


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Table 10: Gardner and Powell 1986: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_larynx-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Low

Metric 2: Attrition

Metric 3: Comparison Group

High
Low

X 0.4	1.2 Retrospective occupational cohort study of 2167

workers (1510 men and 657 women) employed be-
tween 1941 and 1983 in chrysotile asbestos ce-
ment products factories in England, South Wales
and Sweden . This study combines three occupa-
tional cohorts. Only the results for men are de-
scribed. The periods of employment varied be-
tween plants/studies. Eligibility criteria vary be-
tween plants (employment for at least 6 months
(plant 1), Thomas et al 1982 HERO ID 207), 3
months (plant 2/Swedish cohort, Ohlson and Hog-
stedt 1985 HERO D: 3083459 ), none for plant 3
(Garner et al 1986 HERO ID 3083223)

Follow-up for ascertainment of vital status was until
December 1977 (plant 1), 1982 (plant 2) and Decem-
ber 1984 for plant 3. Comparability of cohorts is not
discussed.

X 0.4	0.4 Loss to follow -up was minimal: 5% in Plant 1, 2% in

Plant 2/Swedish cohort (1%), 30% for men in Plant
3 cohort.

X 0.2	0.6 SMRs were estimated using England and Wales

for comparison population (plants 1 and 3), and
Swedish national death rates (Plant 2 cohort), is
is unclear what the comparison population for total
mortality rates were calculated.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposures were based on employment at the re-
spective plants, Industrial hygiene measures are de-
scribed confirming exposure. For the combined anal-
yses type of job was not considered.

Follow-up sometimes ended the year after employ-
ment, making it an inadequate length of time for
cancer mortality to be observed.

Domain 3: Outcome Assessment

Continued on next page

30 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the
Society of Occupational Medicine, 36(4,4), 124-126

Data Type:	Asbestos	workers	SMR_larynx-Cancer

HERO ID:	3083384

Domain

Metric

Rating^ MWF* Score

Comments^

Metric 7:

Outcome measurement or characterization

Low

x 0.667

Metric 8: Reporting Bias

Medium

x 0.333 0.67

Sources were different by cohort. Plant 1 and 3
cohorts used death certificates from the National
Health Service Central Register and the Department
of Health and Social Security. ICD codes are listed
for Plant 1 cohort. In the Plant 2 cohort, vital status
was traced through the death and burial books of the
parishes. Death certificates were checked with the
Swedish National Central Bureau of Statistics and
the officially determined underlying cause of death
has been used. ICD codes are not listed for cohort
3. There is potential for outcome misclassification
from death certificates. In addition, for the analy-
sis combining the three cohorts, there is high poten-
tial misclassification due to various sources, national
practices, etc .

Measured outcomes were reported, out unclear how
the reference population was used for the combined
cancers across cohorts.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization
Metric 11: Co-exposure Confounding

Low	X 0.5	1.5 Although not specifically stated, age and calendar

year were accounted for in the Plant-specific analy-
ses, making it likely that the total SMR would be
adjusted similarly.

Low	X 0.25 0.75 No discussion of covariate characterization, likely

from plant records and death certificates.

Medium X 0.25 0.5 For plant 2: "The vast majority of asbestos used

was chrysotile but 630 tons of amosite were used
between 1949 and 1951 and 400 tons of crocidolite
in 1962. The use of these amphiboles was estimated
to be less than 1% of all asbestos used." Plant 3
only used chrysotile asbestos except for a "small"
amount of amosite during 4 months in 1976. This is
not expected to appreciably bias the results.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Medium X 0.4	0.8 Adequate design and methods. SMRs were esti-

mated using Poisson distribution assumptions (plant
2), or by the person years method using a computer
program (Plants 1 and 3).

Medium X 0.2	0.4 2167 workers (1510 men and 657 women) were in-

cluded in the analysis, however the short follow-up
may limit the power to detect an effect.

Continued on next page

31 of 65


-------
. continued from previous page

Study Citation: Gardner, M. J., Powell, C. A. (1986). Mortality of asbestos cement workers using almost exclusively chrysotile fibre Journal of the

Society of Occupational Medicine, 36(4,4), 124-126
Data Type:	Asbestos_workers_SMR_larynx-Cancer

HERO ID:	3083384

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 14
Metric 15

Reproducibility of analyses
Statistical models

Medium
Low

x 0.2
x 0.2

© ©

Unclear how/what the referent group was used for
the combined cohorts analysis.

There is no description of how the combined SMRs
were calculated.

Domain 6: Other Considera
Metric 16
Metric 17
Metric 18
Metric 19
Metric 20
Metric 21
Metric 22

ions for Biomarker Selection and Measurement
Use of Biomarker of Exposure
Effect biomarker
Method Sensitivity
Biomarker stability
Sample contamination
Method requirements
Matrix adjustment



NA
NA
NA
NA
NA
NA
NA

NA
NA
NA
NA
NA
NA
NA



Overall Quality Determination1"

Low



2.6



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

32 of 65


-------
Table 11: Pira et al. 2017: Evaluation of Cancer for Lung Cancer Mortality Outcomes

Study Citation: Pira, E., Romano, C., Donat , F., Pelucchi, C., La Vecchia, C., BofFetta, P. (2017). Mortality from cancer and other causes among
Italian chrysotile asbestos miners Occupational and Environmental Medicine, 74(8,8), 558-563

Data Type:	Italian	chrysotile	miners	lung	cancer-Cancer

HERO ID:	5060134

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Medium x 0.4

Metric 2: Attrition

Metric 3: Comparison Group

High

x 0.4

Medium x 0.2

0.8 Subjects were drawn from the employment records
of an Italian asbestos mine (n=1056 men). Those el-
igible had worked for the mine for at least one year
between 1930 and 1989. Description of the mine set-
ting was described including some historical occupa-
tional measurements of dust and asbestos. There is
potential for some healthy worker effect in this pop-
ulation.

0.4 The study authors note that the cause of death could
not be determined for a small sample (n=6), and a
small percentage (3.8%) of participants emigrated or
were otherwise lost to follow-up. This level of attri-
tion is not expected to appreciably bias the results.

0.4 Mortality rates for males from the Piedmont Region
were used as a comparison group. This is a suf-
ficiently similar group, however, the study authors
note that mortality rates were not available for cer-
tain periods (e.g., 1946-1954) and rates from adja-
cent periods of time were used instead (1955-1959
rates applied to 1946-1954).

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Medium x 0.5

Not Rated NA
High	x 0.5

NA
0.5

Descriptions of the mine and occupational surveil-
lance was described. Estimates of historical mean
concentrations were 37 fibre/mL up to 1950 and 5
fibre/mL between 1971 and 1976. Exposure was de-
termined by employment at the asbestos mine only.

Subjects were followed until loss to follow-up, their
death, 85th birthday, or through 2014. This is a
sufficiently long follow-up period.

Domain 3: Outcome Assessment

Continued on next page

33 of 65


-------
.. . continued from previous page

Study Citation: Pira, E., Romano, C., Donat , F., Pelucchi, C., La Vecchia, C., BofFetta, P. (2017). Mortality from cancer and other causes among
Italian chrysotile asbestos miners Occupational and Environmental Medicine, 74(8,8), 558-563

Data Type:	Italian	chrysotile	miners	lung	cancer-Cancer

HERO ID:	5060134

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 7:

Outcome measurement or characterization

Medium

x 0.667

1.33

Cause specific mortalities were obtained from death
certificates collected from population registers, mu-
nicipal registration offices, and local health authori-
ties. Causes of death were coded using ICD-9, how-
ever, the study authors did not report whether can-
cer cases were histologically confirmed. It's unclear
if there may be any misclassification from obtaining
vital status or cause of death from various sources.

Metric 8:

Reporting Bias

High

x 0.333

0.33

Outcomes specified in the abstract, introduction,
and methods were provided in the results. SMRs
were presented with observed cases, expected cases,
and a confidence interval.

Domain 4: Potential Confounding/Variable Control









Metric 9:

Covariate Adjustment

Medium

x 0.5

1

SMRs for male miners were calculated, stratified for









age- and calendar-year-specific mortality rates. In-
formation on individual smoking behavior was de-
scribed, but was not accounted for in the analysis.

Metric 10:

Covariate Characterization

Medium

x 0.25

0.5

Covariates were presumably drawn from employ-
ment records

Metric 11:

Co-exposure Confounding

Low

x 0.25

0.75

Co-exposures are not expressly discussed. There
may be additional occupational exposures in this
group, which may depend on job title or position.

Domain 5: Analysis











Metric 12:

Study Design and Methods

Medium

x 0.4

0.8

SMRs were used to assess differences in cause-









specific mortality rates between employees of an as-
bestos mine compared to a reference population in
the same region. This is an appropriate design for
the study question.

Metric 13:

Statistical power

Medium

x 0.2

0.4

There were a sufficient number of employees in-
cluded in the analysis. No concerns with low case
numbers.

Metric 14:

Reproducibility of analyses

Medium

x 0.2

0.4

The analysis was well-described and could be repro-
duced with original data.

Metric 15:

Statistical models

Medium

x 0.2

0.4

The method for calculating SMRs was transparent
and appropriate.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16:

Use of Biomarker of Exposure



NA

NA



Metric 17:

Effect biomarker



NA

NA



Metric 18:

Method Sensitivity



NA

NA



Metric 19:

Biomarker stability



NA

NA



Continued on next page . ..

34 of 65


-------
.. . continued from previous page

Study Citation: Pira, E., Romano, C., Donat , F., Pelucchi, C., La Vecchia, C., Boffetta, P. (2017). Mortality from cancer and other causes among
Italian chrysotile asbestos miners Occupational and Environmental Medicine, 74(8,8), 558-563

Data Type:	Italian	chrysotile	miners	lung	cancer-Cancer

HERO ID:	5060134

Domain



Metric

Rating^

MWF*

Score

Comments^



Metric 20:

Sample contamination



NA

NA





Metric 21:

Method requirements



NA

NA





Metric 22:

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium

1.8

Extracted

Yes

MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; X MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

This metric met the criteria for high confidence as expected for this type of study

35 of 65


-------
Table 12: Pira et al. 2017: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

Study Citation: Pira, E., Romano, C., Donat , F., Pelucchi, C., La Vecchia, C., BofFetta, P. (2017). Mortality from cancer and other causes among
Italian chrysotile asbestos miners Occupational and Environmental Medicine, 74(8,8), 558-563

Data Type:	Italian	chrysotile	miners	laryngeal	cancer-Cancer

HERO ID:	5060134

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

Medium	X 0.4	0.8 Subjects were drawn from the employment records

of an Italian asbestos mine (n=1056 men). Those el-
igible had worked for the mine for at least one year
between 1930 and 1989. Description of the mine
setting was described including some historical oc-
cupational measurements of dust and asbestos.

High	X 0.4	0.4 The study authors note that the cause of death could

not be determined for a small sample (n=6), and a
small percentage (3.8%) of participants emigrated or
were otherwise lost to follow-up. This level of attri-
tion is not expected to appreciably bias the results.

Medium	X 0.2	0.4 Mortality rates for males from the Piedmont Region

were used as a comparison group. This is a suf-
ficiently similar group, however, the study authors
note that mortality rates were not available for cer-
tain periods (e.g., 1946-1954) and rates from adja-
cent periods of time were used instead (1955-1959
rates applied to 1946-1954).

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
High

x 0.5

NA
x 0.5

1.5

NA
0.5

Descriptions of the mine and occupational surveil-
lance was described. Estimates of historical mean
concentrations were 37 fibre/mL up to 1950 and 5
fibre/mL between 1971 and 1976. Exposure was de-
termined by employment at the asbestos mine only.

Subjects were followed until loss to follow-up, their
death, 85th birthday, or through 2014. This is a
sufficiently long follow-up period.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization

Medium X 0.667 1.33 Cause specific mortalities were obtained from death

certificates collected from population registers, mu-
nicipal registration offices, and local health authori-
ties. Causes of death were coded using ICD-9, how-
ever, the study authors did not report whether can-
cer cases were histologically confirmed. It's unclear
if there may be any misclassification from obtaining
vital status or cause of death from various sources.

Continued on next page

36 of 65


-------
.. . continued from previous page

Study Citation: Pira, E., Romano, C., Donat , F., Pelucchi, C., La Vecchia, C., BofFetta, P. (2017). Mortality from cancer and other causes among
Italian chrysotile asbestos miners Occupational and Environmental Medicine, 74(8,8), 558-563

Data Type:	Italian	chrysotile	miners	laryngeal	cancer-Cancer

HERO ID:	5060134

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 8:

Reporting Bias

High

x 0.333

0.33

Outcomes specified in the abstract, introduction,
and methods were provided in the results. SMRs
were presented with observed cases, expected cases,
and a confidence interval.

Domain 4: Potential Confounding/Variable Control









Metric 9:

Covariate Adjustment

Medium

x 0.5

1

SMRs for male miners were calculated, stratified for









age- and calendar-year-specific mortality rates. In-
formation on individual smoking behavior was de-
scribed, but was not accounted for in the analysis.

Metric 10

Covariate Characterization

Medium

x 0.25

0.5

Covariates were presumably drawn from employ-
ment records

Metric 11

Co-exposure Confounding

Low

x 0.25

0.75

Co-exposures are not expressly discussed. There
may be additional occupational exposures in this
group, which may depend on job title or position.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

SMRs were used to assess differences in cause-









specific mortality rates between employees of an as-
bestos mine compared to a reference population in
the same region. This is an appropriate design for
the study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

There were a sufficient number of employees in-
cluded in the analysis. No concerns with low case
numbers.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The analysis was well-described and could be repro-
duced with original data.

Metric 15

Statistical models

Medium

x 0.2

0.4

The method for calculating SMRs was transparent
and appropriate.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium



1.9



Extracted	Yes

Continued on next page . ..

37 of 65


-------
. continued from previous page

Study Citation: Pira, E., Romano, C., Donat , F., Pelucchi, C., La Vecchia, C., Boffetta, P. (2017). Mortality from cancer and other causes among

Italian chrysotile asbestos miners Occupational and Environmental Medicine, 74(8,8), 558-563
Data Type:	Italian_chrysotile_miners_laryngeal_cancer-Cancer

HERO ID:	5060134

Domain

Metric

Rating^

MWF* Score

Comments^



MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

38 of 65


-------
Table 13: Mamo and Costa 2004: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian	asbestos	product	workers	ovarian	cancer-Cancer

HERO ID:	6912534

Domain Metric



Rating^

MWF*

Score

Comments^

Domain 1: Study Participation











Metric 1: Participant selection



High

x 0.4

0.4

Subjects consisted of former employees of an
asbestos-based products manufacturing plant in
Grugliasco, Italy, hired before 1971. Subjects were
followed from 1981 through 1995.

Metric 2: Attrition



Medium

x 0.4

0.8

The initial study sample consisted of 1653 employ-
ees. The study authors note that the analysis sample
consisted of 967 individuals, selected as 18-74 y of
age, with concern about dropping older individuals.

Metric 3: Comparison Group



Medium

x 0.2

0.4

The study authors attempted to find a similar popu-
lation to the asbestos-products employees by using a
reference population consisting of residents from the
same area (Turin) whom were manual workers—this
was an attempt to mitigate healthy worker effect.

Domain 2: Exposure Characterization











Metric 4: Measurement of Exposure



Low

x 0.5

1.5

Exposure was determined by occupation only. Ba-
sic descriptions of the asbestos product facility were
provided.

Metric 5: Exposure levels



Not Rated

NA

NA



Metric 6: Temporality



Medium

x 0.5

1

Subjects employed in 1971 were followed-up from
1981 to 1995 which is a sufficiently long follow-up
period to detect an effect.

Domain 3: Outcome Assessment











Metric 7: Outcome measurement or

characterization

Medium

x 0.667

1.33

Causes of death were obtained from the Italian Na-
tional Registry of Deaths (ISTAT) and consulting
death certificates at the Piedmont Cancer Registry.
It was not reported whether cancer cases were his-
tologically confirmed, and it appears that causes of
death were coded using ICD-9 .

Metric 8: Reporting Bias



High

x 0.333

0.33

Outcomes specified in the abstract, introduction,
and methods were provided in results. SMRs were
provided with the number of cases and 95% confi-
dence intervals.

Domain 4: Potential Confounding/Variable Control











Metric 9: Covariate Adjustment



Medium

x 0.5

1

Individual smoking behaviors were not able to be









controlled for.



Continued on

next page .







39 of 65


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. continued from previous page

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian	asbestos	product	workers	ovarian	cancer-Cancer

HERO ID:	6912534

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 10

Covariate Characterization

Medium

x 0.25

0.5

Covariates were largely not collected except sex,











which was presumably taken from employment











records.

Metric 11

Co-exposure Confounding

Medium

x 0.25

0.5

This is an occupational cohort and co-exposures











were not addressed. Co-exposures may be present











depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

SMRs were calculated to estimate the effect of oc-











cupational asbestos exposure on cancer mortality











rates. This is an appropriate study design for the











study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 967 individuals were included in the anal-











ysis sample, which is sufficiently large to detect an











effect. There is some concern for the limited number











of cases of laryngeal and ovarian cancer mortality (3











and 1, respectively) which may make estimates un-











stable.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The analysis was sufficiently described and could be











reproduced given original data.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of sex-specific SMRs was detailed











and transparent. No concerns.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium



2.0



Extracted	Yes

Continued on next page . ..

40 of 65


-------
. continued from previous page

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian_asbestos_product_workers_ovarian_cancer-Cancer

HERO ID:	6912534

Domain	Metric	Rating ^ MWF* Score	Comments^

* MWF = Metric Weighting Factor

t High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

+ The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

if any metric is Unacceptable

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

41 Of 65


-------
Table 14: Mamo and Costa 2004: Evaluation of Cancer for Female Lung Cancer Mortality Outcomes

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian	asbestos	product	workers	lung	cancer	female-Cancer

HERO ID:	6912534

Domain Metric



Rating^

MWF*

Score

Comments^

Domain 1: Study Participation











Metric 1: Participant selection



High

x 0.4

0.4

Subjects consisted of former employees of an
asbestos-based products manufacturing plant in
Grugliasco, Italy, hired before 1971. Subjects were
followed from 1981 through 1995.

Metric 2: Attrition



Medium

x 0.4

0.8

The initial study sample consisted of 1653 employ-
ees. The study authors note that the analysis sample
consisted of 967 individuals, selected as 18-74 y of
age, with concern about dropping older individuals.

Metric 3: Comparison Group



Medium

x 0.2

0.4

The study authors attempted to find a similar popu-
lation to the asbestos-products employees by using a
reference population consisting of residents from the
same area (Turin) whom were manual workers—this
was an attempt to mitigate healthy worker effect.

Domain 2: Exposure Characterization











Metric 4: Measurement of Exposure



Low

x 0.5

1.5

Exposure was determined by occupation only. Ba-
sic descriptions of the asbestos product facility were
provided.

Metric 5: Exposure levels



Not Rated

NA

NA



Metric 6: Temporality



Medium

x 0.5

1

Subjects employed in 1971 were followed-up from
1981 to 1995 which is a sufficiently long follow-up
period to detect an effect. It's not clear whether
individuals were followed between 1971 and 1981.

Domain 3: Outcome Assessment











Metric 7: Outcome measurement or

characterization

Medium

x 0.667

1.33

Causes of death were obtained from the Italian Na-
tional Registry of Deaths (ISTAT) and consulting
death certificates at the Piedmont Cancer Registry.
It was not reported whether cancer cases were his-
tologically confirmed, and it appears that causes of
death were coded using ICD-9 .

Metric 8: Reporting Bias



High

x 0.333

0.33

Outcomes specified in the abstract, introduction,
and methods were provided in results. SMRs were
provided with the number of cases and 95% confi-
dence intervals.

Domain 4: Potential Confounding/Variable Control











Metric 9: Covariate Adjustment



Medium

x 0.5

1

Individual smoking behaviors were not able to be









controlled for.



Continued on

next page .







42 of 65


-------
... continued from previous page

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian_asbestos_product_workers_lung_cancer_female-Cancer

HERO ID:	6912534

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 10

Covariate Characterization

Medium

x 0.25

0.5

Covariates were largely not collected except sex,











which was presumably taken from employment
records.

Metric 11

Co-exposure Confounding

Medium

x 0.25

0.5

This is an occupational cohort and co-exposures











were not addressed. Co-exposures may be present











depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

SMRs were calculated to estimate the effect of oc-











cupational asbestos exposure on cancer mortality











rates. This is an appropriate study design for the











study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 967 individuals were included in the anal-











ysis sample, which is sufficiently large to detect an











effect.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The analysis was sufficiently described and could be











reproduced given original data.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of sex-specific SMRs was detailed











and transparent. No concerns.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium

2.0

Extracted

Yes





MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

43 of 65


-------
Table 15: Mamo and Costa 2004: Evaluation of Cancer for Male and Female Lung Cancer Mortality Outcomes

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian	asbestos	product	workers	lung	cancer	combined-Cancer

HERO ID:	6912534

Domain Metric



Rating^

MWF*

Score

Comments^

Domain 1: Study Participation











Metric 1: Participant selection



High

x 0.4

0.4

Subjects consisted of former employees of an
asbestos-based products manufacturing plant in
Grugliasco, Italy, hired before 1971. Subjects were
followed from 1981 through 1995.

Metric 2: Attrition



Medium

x 0.4

0.8

The initial study sample consisted of 1653 employ-
ees. The study authors note that the analysis sample
consisted of 967 individuals, selected as 18-74 y of
age, with concern about dropping older individuals.

Metric 3: Comparison Group



Medium

x 0.2

0.4

The study authors attempted to find a similar popu-
lation to the asbestos-products employees by using a
reference population consisting of residents from the
same area (Turin) whom were manual workers—this
was an attempt to mitigate healthy worker effect.

Domain 2: Exposure Characterization











Metric 4: Measurement of Exposure



Low

x 0.5

1.5

Exposure was determined by occupation only. Ba-
sic descriptions of the asbestos product facility were
provided.

Metric 5: Exposure levels



Not Rated

NA

NA



Metric 6: Temporality



Medium

x 0.5

1

Subjects employed in 1971 were followed-up from
1981 to 1995 which is a sufficiently long follow-up
period to detect an effect.

Domain 3: Outcome Assessment











Metric 7: Outcome measurement or

characterization

Medium

x 0.667

1.33

Causes of death were obtained from the Italian Na-
tional Registry of Deaths (ISTAT) and consulting
death certificates at the Piedmont Cancer Registry.
It was not reported whether cancer cases were his-
tologically confirmed, and it appears that causes of
death were coded using ICD-9 .

Metric 8: Reporting Bias



High

x 0.333

0.33

Outcomes specified in the abstract, introduction,
and methods were provided in results. SMRs were
provided with the number of cases and 95% confi-
dence intervals.

Domain 4: Potential Confounding/Variable Control











Metric 9: Covariate Adjustment



Medium

x 0.5

1

Individual smoking behaviors were not able to be









controlled for.



Continued on

next page .







44 of 65


-------
... continued from previous page

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian_asbestos_product_workers_lung_cancer_combined-Cancer

HERO ID:	6912534

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 10

Covariate Characterization

Medium

x 0.25

0.5

Covariates were largely not collected except sex,











which was presumably taken from employment
records.

Metric 11

Co-exposure Confounding

Medium

x 0.25

0.5

This is an occupational cohort and co-exposures











were not addressed. Co-exposures may be present











depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

SMRs were calculated to estimate the effect of oc-











cupational asbestos exposure on cancer mortality











rates. This is an appropriate study design for the











study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 967 individuals were included in the anal-











ysis sample, which is sufficiently large to detect an











effect.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The analysis was sufficiently described and could be











reproduced given original data.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of sex-specific SMRs was detailed











and transparent. No concerns.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium

2.0

Extracted

Yes





MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

45 of 65


-------
Table 16: Mamo and Costa 2004: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian	asbestos	product	workers	laryngeal	cancer-Cancer

HERO ID:	6912534

Domain Metric



Rating^

MWF*

Score

Comments^

Domain 1: Study Participation











Metric 1: Participant selection



High

x 0.4

0.4

Subjects consisted of former employees of an
asbestos-based products manufacturing plant in
Grugliasco, Italy, hired before 1971. Subjects were
followed from 1981 through 1995.

Metric 2: Attrition



Medium

x 0.4

0.8

The initial study sample consisted of 1653 employ-
ees. The study authors note that the analysis sample
consisted of 967 individuals, selected as 18-74 y of
age, with concern about dropping older individuals.

Metric 3: Comparison Group



Medium

x 0.2

0.4

The study authors attempted to find a similar popu-
lation to the asbestos-products employees by using a
reference population consisting of residents from the
same area (Turin) whom were manual workers—this
was an attempt to mitigate healthy worker effect.

Domain 2: Exposure Characterization











Metric 4: Measurement of Exposure



Low

x 0.5

1.5

Exposure was determined by occupation only. Ba-
sic descriptions of the asbestos product facility were
provided.

Metric 5: Exposure levels



Not Rated

NA

NA



Metric 6: Temporality



Medium

x 0.5

1

Subjects employed in 1971 were followed-up from
1981 to 1995 which is a sufficiently long follow-up
period to detect an effect.

Domain 3: Outcome Assessment











Metric 7: Outcome measurement or

characterization

Medium

x 0.667

1.33

Causes of death were obtained from the Italian Na-
tional Registry of Deaths (ISTAT) and consulting
death certificates at the Piedmont Cancer Registry.
It was not reported whether cancer cases were his-
tologically confirmed, and it appears that causes of
death were coded using ICD-9 .

Metric 8: Reporting Bias



High

x 0.333

0.33

Outcomes specified in the abstract, introduction,
and methods were provided in results. SMRs were
provided with the number of cases and 95% confi-
dence intervals.

Domain 4: Potential Confounding/Variable Control











Metric 9: Covariate Adjustment



Medium

x 0.5

1

Individual smoking behaviors were not able to be









controlled for.



Continued on

next page .







46 of 65


-------
. continued from previous page

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian	asbestos	product	workers	laryngeal	cancer-Cancer

HERO ID:	6912534

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 10

Covariate Characterization

Medium

x 0.25

0.5

Covariates were largely not collected except sex,











which was presumably taken from employment











records.

Metric 11

Co-exposure Confounding

Medium

x 0.25

0.5

This is an occupational cohort and co-exposures











were not addressed. Co-exposures may be present











depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

SMRs were calculated to estimate the effect of oc-











cupational asbestos exposure on cancer mortality











rates. This is an appropriate study design for the











study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 967 individuals were included in the anal-











ysis sample, which is sufficiently large to detect an











effect. There is some concern for the limited number











of cases of laryngeal and ovarian cancer mortality (3











and 1, respectively) which may make estimates un-











stable.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The analysis was sufficiently described and could be











reproduced given original data.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of sex-specific SMRs was detailed











and transparent. No concerns.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium



2.0



Extracted	Yes

Continued on next page . ..

47 of 65


-------
. continued from previous page

Study Citation: Mamo, C., Costa, G. (2004). Mortality experience in an historical cohort of chrysotile asbestos textile workers Global asbestos congress
2004 in Tokyo,

Data Type:	Italian_asbestos_product_workers_laryngeal_cancer-Cancer

HERO ID:	6912534

Domain	Metric	Rating ^ MWF* Score	Comments^

* MWF = Metric Weighting Factor

t High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

+ The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

4	if any metric is Unacceptable

Overall rating =

J]. (Metric Score; x MWF;) / J] . MWFj

(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

48 of 65


-------
Table 17: Germani et al. 1999: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated
for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134

Data Type:	Italian	women	asbestosis	ovarian	cancer-Cancer

HERO ID:	709605

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

Medium	X 0.4	0.8 Study participants were drawn from the Italian Na-

tional Institute for Insurance of Occupational Acci-
dents (INAIL). Eligibility criteria were not expressly
stated beyond membership in the asbestosis com-
pensation cohort and being alive at the study's onset
(1979). Most women entered the asbestosis compen-
sation cohort around 50 years of age; some healthy
worker effect may be present.

High	X 0.4	0.4 The number of individuals lost to follow-up was pro-

vided and appeared minimal for all groups (total
cohort = 0.6 percent). The study authors do not
suggest any other missing data.

Low	X 0.2	0.6 Rates of mortality in the asbestosis compensation

cohort were compared with Italian national mortal-
ity rates, stratifying for gender-, age-, and calendar
period-specific rates. This represents consideration
of potential covariates. The study group of those
compensated for asbestosis may have been different
from national comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
High

x 0.5

NA
x 0.5

1.5

NA
0.5

Exposure was assigned only by the women's occupa-
tion. No further characterization of the occupational
exposure was provided.

Asbestosis compensation cohort members were eligi-
ble if they were alive and enrolled at the end of 1979.
Women were followed until October 1997, allowing
for a sufficient follow-up period.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Medium

x 0.667 1.33 The cause of death was obtained for deceased sub-
jects from the Registry Office of the municipality of
residence or death. Causes of death were coded ac-
cording to ICD-9 codes, but no details were provided
about histological confirmation.

Continued on next page

49 of 65


-------
. continued from previous page

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated
for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134

Data Type:	Italian	women	asbestosis	ovarian	cancer-Cancer

HERO ID:	709605

Domain





Metric

Rating^

MWF* Score

Comments^



Metric 8:

Reporting Bias



High

x 0.333 0.33

Outcomes specified in the abstract, introduction,
and methods were provided in the results. The re-
sults provide the number of observations, the SMR,
and a confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Metric 11: Co-exposure Confounding

Medium	x 0.5	1 SMRs were stratified for gender, age, and calendar

period. Individual smoking data was not available
and may be of concern for outcomes including lung
cancer.

Medium	X 0.25 0.5 Covariates were drawn from information collected by

INAIL for asbestosis compensation. It is not entirely
clear how INAIL may have collected the covariates.

Low	X 0.25 0.75 This is an occupational cohort and co-exposures

were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Metric 14: Reproducibility of analyses

Metric 15: Statistical models

Medium	X 0.4	0.8 SMRs were used to achieve the study objective of

comparing cause-specific mortality rates of an occu-
pational cohort to the Italian national population
(stratifying for relevant characteristics).

Medium x 0.2	0.4 A total of 631 women compensated for asbestosis

were included in the overall cohort, with 276 and 278
women in the textile and asbestos cement industry,
respectively.

Medium	X 0.2	0.4 The analysis is well described and transparent.

Given the same data, the analysis could be easily
reproduced.

Medium	X 0.2	0.4 SMRs and 95% confidence intervals were provided,

and the method to calculate the SMRs was suffi-
ciently explained.

Domain 6: Other Considerations for Biomarker Selection and Measurement

Metric 16

Use of Biomarker of Exposure

NA

NA

Metric 17

Effect biomarker

NA

NA

Metric 18

Method Sensitivity

NA

NA

Metric 19

Biomarker stability

NA

NA

Metric 20

Sample contamination

NA

NA

Metric 21

Method requirements

NA

NA

Metric 22

Matrix adjustment

NA

NA

Continued on next page

50 of 65


-------
. continued from previous page

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated

for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134
Data Type:	Italian_women_asbestosis_ovarian_cancer-Cancer

HERO ID:	709605

Domain

Metric

Rating^

MWF* Score

Comments^

Overall Quality Determination1"



Medium

1.9



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

51 Of 65


-------
Table 18: Germani et al. 1999: Evaluation of Cancer for Lung Cancer Mortality Outcomes

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated
for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134

Data Type:	Italian	women	asbestosis	lung	cancer-Cancer

HERO ID:	709605

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

Medium	X 0.4	0.8 Study participants were drawn from the Italian Na-

tional Institute for Insurance of Occupational Acci-
dents (INAIL). Eligibility criteria were not expressly
stated beyond membership in the asbestosis com-
pensation cohort and being alive at the study's onset
(1979). Most women entered the asbestosis compen-
sation cohort around 50 years of age; some healthy
worker effect may be present.

High	X 0.4	0.4 The number of individuals lost to follow-up was pro-

vided and appeared minimal for all groups (total
cohort = 0.6 percent). The study authors do not
suggest any other missing data.

Low	X 0.2	0.6 Rates of mortality in the asbestosis compensation

cohort were compared with Italian national mortal-
ity rates, stratifying for gender-, age-, and calendar
period-specific rates. This represents consideration
of potential covariates. The study group of those
compensated for asbestosis may have been different
from national comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
High

x 0.5

NA
x 0.5

1.5

NA
0.5

Exposure was assigned only by the women's occupa-
tion. No further characterization of the occupational
exposure was provided.

Asbestosis compensation cohort members were eligi-
ble if they were alive and enrolled at the end of 1979.
Women were followed until October 1997, allowing
for a sufficient follow-up period.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Medium

x 0.667 1.33 The cause of death was obtained for deceased sub-
jects from the Registry Office of the municipality of
residence or death. Causes of death were coded ac-
cording to ICD-9 codes, but no details were provided
about histological confirmation.

Continued on next page

52 of 65


-------
. continued from previous page

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated
for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134

Data Type:	Italian	women	asbestosis	lung	cancer-Cancer

HERO ID:	709605

Domain





Metric

Rating^

MWF* Score

Comments^



Metric 8:

Reporting Bias



High

x 0.333 0.33

Outcomes specified in the abstract, introduction,
and methods were provided in the results. The re-
sults provide the number of observations, the SMR,
and a confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Metric 11: Co-exposure Confounding

Medium	x 0.5	1 SMRs were stratified for gender, age, and calendar

period. Individual smoking data was not available
and may be of concern for outcomes including lung
cancer.

Medium	X 0.25 0.5 Covariates were drawn from information collected by

INAIL for asbestosis compensation. It is not entirely
clear how INAIL may have collected the covariates.

Low	X 0.25 0.75 This is an occupational cohort and co-exposures

were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Metric 14: Reproducibility of analyses

Metric 15: Statistical models

Medium	X 0.4	0.8 SMRs were used to achieve the study objective of

comparing cause-specific mortality rates of an occu-
pational cohort to the Italian national population
(stratifying for relevant characteristics).

Medium x 0.2	0.4 A total of 631 women compensated for asbestosis

were included in the overall cohort, with 276 and 278
women in the textile and asbestos cement industry,
respectively.

Medium	X 0.2	0.4 The analysis is well described and transparent.

Given the same data, the analysis could be easily
reproduced.

Medium	X 0.2	0.4 SMRs and 95% confidence intervals were provided,

and the method to calculate the SMRs was suffi-
ciently explained.

Domain 6: Other Considerations for Biomarker Selection and Measurement

Metric 16

Use of Biomarker of Exposure

NA

NA

Metric 17

Effect biomarker

NA

NA

Metric 18

Method Sensitivity

NA

NA

Metric 19

Biomarker stability

NA

NA

Metric 20

Sample contamination

NA

NA

Metric 21

Method requirements

NA

NA

Metric 22

Matrix adjustment

NA

NA

Continued on next page

53 of 65


-------
. continued from previous page

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated

for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134
Data Type:	Italian_women_asbestosis_lung_cancer-Cancer

HERO ID:	709605

Domain

Metric

Rating^

MWF* Score

Comments^

Overall Quality Determination1"



Medium

1.9



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

54 Of 65


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Table 19: Germani et al. 1999: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated
for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134

Data Type:	Italian	women	asbestosis	larynx	cancer-Cancer

HERO ID:	709605

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

Medium	X 0.4	0.8 Study participants were drawn from the Italian Na-

tional Institute for Insurance of Occupational Acci-
dents (INAIL). Eligibility criteria were not expressly
stated beyond membership in the asbestosis com-
pensation cohort and being alive at the study's onset
(1979). Most women entered the asbestosis compen-
sation cohort around 50 years of age; some healthy
worker effect may be present.

High	X 0.4	0.4 The number of individuals lost to follow-up was pro-

vided and appeared minimal for all groups (total
cohort = 0.6 percent). The study authors do not
suggest any other missing data.

Low	X 0.2	0.6 Rates of mortality in the asbestosis compensation

cohort were compared with Italian national mortal-
ity rates, stratifying for gender-, age-, and calendar
period-specific rates. This represents consideration
of potential covariates. The study group of those
compensated for asbestosis may have been different
from national comparison group.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
High

x 0.5

NA
x 0.5

1.5

NA
0.5

Exposure was assigned only by the women's occupa-
tion. No further characterization of the occupational
exposure was provided.

Asbestosis compensation cohort members were eligi-
ble if they were alive and enrolled at the end of 1979.
Women were followed until October 1997, allowing
for a sufficient follow-up period.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization Medium

x 0.667 1.33 The cause of death was obtained for deceased sub-
jects from the Registry Office of the municipality of
residence or death. Causes of death were coded ac-
cording to ICD-9 codes, but no details were provided
about histological confirmation.

Continued on next page

55 of 65


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. continued from previous page

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated
for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134

Data Type:	Italian	women	asbestosis	larynx	cancer-Cancer

HERO ID:	709605

Domain





Metric

Rating^

MWF* Score

Comments^



Metric 8:

Reporting Bias



High

x 0.333 0.33

Outcomes specified in the abstract, introduction,
and methods were provided in the results. The re-
sults provide the number of observations, the SMR,
and a confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Metric 11: Co-exposure Confounding

Medium	x 0.5	1 SMRs were stratified for gender, age, and calendar

period. Individual smoking data was not available
and may be of concern for outcomes including lung
cancer.

Medium	X 0.25 0.5 Covariates were drawn from information collected by

INAIL for asbestosis compensation. It is not entirely
clear how INAIL may have collected the covariates.

Low	X 0.25 0.75 This is an occupational cohort and co-exposures

were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis

Metric 12: Study Design and Methods

Metric 13: Statistical power

Metric 14: Reproducibility of analyses

Metric 15: Statistical models

Medium	X 0.4	0.8 SMRs were used to achieve the study objective of

comparing cause-specific mortality rates of an occu-
pational cohort to the Italian national population
(stratifying for relevant characteristics).

Medium x 0.2	0.4 A total of 631 women compensated for asbestosis

were included in the overall cohort, with 276 and 278
women in the textile and asbestos cement industry,
respectively.

Medium	X 0.2	0.4 The analysis is well described and transparent.

Given the same data, the analysis could be easily
reproduced.

Medium	X 0.2	0.4 SMRs and 95% confidence intervals were provided,

and the method to calculate the SMRs was suffi-
ciently explained.

Domain 6: Other Considerations for Biomarker Selection and Measurement

Metric 16

Use of Biomarker of Exposure

NA

NA

Metric 17

Effect biomarker

NA

NA

Metric 18

Method Sensitivity

NA

NA

Metric 19

Biomarker stability

NA

NA

Metric 20

Sample contamination

NA

NA

Metric 21

Method requirements

NA

NA

Metric 22

Matrix adjustment

NA

NA

Continued on next page

56 of 65


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. continued from previous page

Study Citation: Germani, D., Belli, S., Bruno, C., Grignoli, M., Nesti, M., Pirastu, R., Comba, P. (1999). Cohort mortality study of women compensated

for asbestosis in Italy American Journal of Industrial Medicine, 36(1,1), 129-134
Data Type:	Italian_women_asbestosis_larynx_cancer-Cancer

HERO ID:	709605

Domain

Metric

Rating^

MWF* Score

Comments^

Overall Quality Determination1"



Medium

1.9



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

57 of 65


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Table 20: Tarchi et al. 1994: Evaluation of Cancer for Ovarian Cancer Mortality Outcomes

Cohort mortality study of rock salt

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G., Valiani, M. (1994).
workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256

Data Type:	rock	salt	workers	ovarian	cancer	mortality-Cancer

HERO ID:	2739094

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

High	X 0.4	0.4 The setting and activities conducted in the rock salt

mine were described. All employees of the rock salt
mine for any duration of length between 1965 and
the end of 1989 were eligible (n=487).

High	X 0.4	0.4 Vital status was determined for all cohort members,

indicating no loss to follow-up. The cause of death
could not be determined for two individuals, which
is not expected to appreciably bias the results.

Medium	x 0.2	0.4 Rates of mortality were compared for employees in

a rock salt mine compared to those of the Tuscany
region (where the mine is located). It was not clear
whether age was considered for stratification when
calculating SMRs.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposure was based on employment at the rock salt
mine only.

Participants were included if they were employed be-
tween 1965 and 1989, and followed only until 1989.
Those becoming eligible later during the eligibility
period may have had less time for onset of disease.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization High

Metric 8: Reporting Bias	High

X 0.667 0.67 Vital status and cause of death were determined at
the registrar's office of the individual subject's place
of residence or death using ICD-9 codes. The study
authors note that classification was carried out in-
dependently by two physicians.

X 0.333 0.33 Outcomes specified in the abstract, introduction,
and methods were provided in the results. Effect
estimates were provided as SMRs, observed cases,
expected cases, and a 90% confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Medium
Medium

x 0.5
x 0.25

0.5

Sex-specific SMRs were provided, however, individ-
ual smoking rates did not appear to be considered.

Covariates were presumably taken from employment
records.

Continued on next page

58 of 65


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... continued from previous page

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G.

workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256
Data Type:	rock_salt_workers_ovarian_cancer_mortality-Cancer

HERO ID:	2739094

Valiani, M. (1994). Cohort mortality study of rock salt

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 11

Co-exposure Confounding

Low

x 0.25

0.75

This is an occupational cohort and co-exposures
were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

Standardized mortality ratios were used to deter-









mine excess risk of various cause-specific mortalities
related to cancer. This is an appropriate study de-
sign for the study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 487 individuals (367 men, 120 women)
were in the analysis sample. There is some concern
due to the low number of cases of ovarian and laryn-
geal cancers, making the estimates unstable.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The description of the analysis was sufficient that,
given original data, the analysis could be repro-
duced.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of SMRs was transparent and model
assumptions appear to be met.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium

—> Low§





Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study
§ Evaluator's explanation for rating change: "Low number of mortality cases for ovarian cancer."

59 of 65


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Table 21: Tarchi et al. 1994: Evaluation of Cancer for Male and Female Lung Cancer Mortality Outcomes

Cohort mortality study of rock salt

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G., Valiani, M. (1994).
workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256

Data Type:	rock	salt	workers	lung	cancer	mortality-Cancer

HERO ID:	2739094

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

High	X 0.4	0.4 The setting and activities conducted in the rock salt

mine were described. All employees of the rock salt
mine for any duration of length between 1965 and
the end of 1989 were eligible (n=487).

High	X 0.4	0.4 Vital status was determined for all cohort members,

indicating no loss to follow-up. The cause of death
could not be determined for two individuals, which
is not expected to appreciably bias the results.

Medium	x 0.2	0.4 Rates of mortality were compared for employees in

a rock salt mine compared to those of the Tuscany
region (where the mine is located). It was not clear
whether age was considered for stratification when
calculating SMRs.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposure was based on employment at the rock salt
mine only.

Participants were included if they were employed be-
tween 1965 and 1989, and followed only until 1989.
Those becoming eligible later during the eligibility
period may have had less time for onset of disease.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization High

Metric 8: Reporting Bias	High

X 0.667 0.67 Vital status and cause of death were determined at
the registrar's office of the individual subject's place
of residence or death using ICD-9 codes. The study
authors note that classification was carried out in-
dependently by two physicians.

X 0.333 0.33 Outcomes specified in the abstract, introduction,
and methods were provided in the results. Effect
estimates were provided as SMRs, observed cases,
expected cases, and a 90% confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Medium
Medium

x 0.5
x 0.25

0.5

Sex-specific SMRs were provided, however, individ-
ual smoking rates did not appear to be considered.

Covariates were presumably taken from employment
records.

Continued on next page

60 of 65


-------
.. . continued from previous page

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G., Valiani, M. (1994). Cohort mortality study of rock salt
workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256

Data Type:	rock	salt	workers	lung	cancer	mortality-Cancer

HERO ID:	2739094

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 11

Co-exposure Confounding

Low

x 0.25

0.75

This is an occupational cohort and co-exposures
were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

Standardized mortality ratios were used to deter-









mine excess risk of various cause-specific mortalities
related to cancer. This is an appropriate study de-
sign for the study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 487 individuals (367 men, 120 women)
were in the analysis sample.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The description of the analysis was sufficient that,
given original data, the analysis could be repro-
duced.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of SMRs was transparent and model
assumptions appear to be met.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium



1.9



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; X MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

61 Of 65


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Table 22: Tarchi et al. 1994: Evaluation of Cancer for Female Lung Cancer Mortality Outcomes

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G.

workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256

Data Type:	rock	salt	workers	female	lung	cancer	mortality-Cancer

HERO ID:	2739094

Valiani, M. (1994). Cohort mortality study of rock salt

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

High	X 0.4	0.4 The setting and activities conducted in the rock salt

mine were described. All employees of the rock salt
mine for any duration of length between 1965 and
the end of 1989 were eligible (n=487).

High	X 0.4	0.4 Vital status was determined for all cohort members,

indicating no loss to follow-up. The cause of death
could not be determined for two individuals, which
is not expected to appreciably bias the results.

Medium	x 0.2	0.4 Rates of mortality were compared for employees in

a rock salt mine compared to those of the Tuscany
region (where the mine is located). It was not clear
whether age was considered for stratification when
calculating SMRs.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposure was based on employment at the rock salt
mine only.

Participants were included if they were employed be-
tween 1965 and 1989, and followed only until 1989.
Those becoming eligible later during the eligibility
period may have had less time for onset of disease.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization High

Metric 8: Reporting Bias	High

X 0.667 0.67 Vital status and cause of death were determined at
the registrar's office of the individual subject's place
of residence or death using ICD-9 codes. The study
authors note that classification was carried out in-
dependently by two physicians.

X 0.333 0.33 Outcomes specified in the abstract, introduction,
and methods were provided in the results. Effect
estimates were provided as SMRs, observed cases,
expected cases, and a 90% confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Medium
Medium

x 0.5
x 0.25

0.5

Sex-specific SMRs were provided, however, individ-
ual smoking rates did not appear to be considered.

Covariates were presumably taken from employment
records.

Continued on next page

62 of 65


-------
.. . continued from previous page

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G., Valiani, M. (1994). Cohort mortality study of rock salt
workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256

Data Type:	rock	salt	workers	female	lung	cancer	mortality-Cancer

HERO ID:	2739094

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 11

Co-exposure Confounding

Low

x 0.25

0.75

This is an occupational cohort and co-exposures
were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

Standardized mortality ratios were used to deter-









mine excess risk of various cause-specific mortalities
related to cancer. This is an appropriate study de-
sign for the study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 487 individuals (367 men, 120 women)
were in the analysis sample.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The description of the analysis was sufficient that,
given original data, the analysis could be repro-
duced.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of SMRs was transparent and model
assumptions appear to be met.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium



1.9



Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; X MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study

63 of 65


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Table 23: Tarchi et al. 1994: Evaluation of Cancer for Laryngeal Cancer Mortality Outcomes

Cohort mortality study of rock salt

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G., Valiani, M. (1994).
workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256

Data Type:	rock	salt	workers	larynx	cancer	mortality-Cancer

HERO ID:	2739094

Domain

Metric

Rating^ MWF* Score

Comments^

Domain 1: Study Participation

Metric 1: Participant selection

Metric 2: Attrition

Metric 3: Comparison Group

High	X 0.4	0.4 The setting and activities conducted in the rock salt

mine were described. All employees of the rock salt
mine for any duration of length between 1965 and
the end of 1989 were eligible (n=487).

High	X 0.4	0.4 Vital status was determined for all cohort members,

indicating no loss to follow-up. The cause of death
could not be determined for two individuals, which
is not expected to appreciably bias the results.

Medium	x 0.2	0.4 Rates of mortality were compared for employees in

a rock salt mine compared to those of the Tuscany
region (where the mine is located). It was not clear
whether age was considered for stratification when
calculating SMRs.

Domain 2: Exposure Characterization

Metric 4: Measurement of Exposure

Metric 5: Exposure levels
Metric 6: Temporality

Low

Not Rated
Low

x 0.5

NA
x 0.5

1.5

NA
1.5

Exposure was based on employment at the rock salt
mine only.

Participants were included if they were employed be-
tween 1965 and 1989, and followed only until 1989.
Those becoming eligible later during the eligibility
period may have had less time for onset of disease.

Domain 3: Outcome Assessment

Metric 7: Outcome measurement or characterization High

Metric 8: Reporting Bias	High

X 0.667 0.67 Vital status and cause of death were determined at
the registrar's office of the individual subject's place
of residence or death using ICD-9 codes. The study
authors note that classification was carried out in-
dependently by two physicians.

X 0.333 0.33 Outcomes specified in the abstract, introduction,
and methods were provided in the results. Effect
estimates were provided as SMRs, observed cases,
expected cases, and a 90% confidence interval.

Domain 4: Potential Confounding/Variable Control
Metric 9: Covariate Adjustment

Metric 10: Covariate Characterization

Medium
Medium

x 0.5
x 0.25

0.5

Sex-specific SMRs were provided, however, individ-
ual smoking rates did not appear to be considered.

Covariates were presumably taken from employment
records.

Continued on next page

64 of 65


-------
... continued from previous page

Study Citation: Tarchi, M., Orsi, D., Comba, P., De Santis, M., Pirastu, R., Battista, G.

workers in Italy American Journal of Industrial Medicine, 25(2,2), 251-256
Data Type:	rock_salt_workers_larynx_cancer_mortality-Cancer

HERO ID:	2739094

Valiani, M. (1994). Cohort mortality study of rock salt

Domain

Metric

Rating^

MWF*

Score

Comments^

Metric 11

Co-exposure Confounding

Low

x 0.25

0.75

This is an occupational cohort and co-exposures
were not addressed. Co-exposures may be present
depending on specific job titles and positions.

Domain 5: Analysis











Metric 12

Study Design and Methods

Medium

x 0.4

0.8

Standardized mortality ratios were used to deter-









mine excess risk of various cause-specific mortalities
related to cancer. This is an appropriate study de-
sign for the study question.

Metric 13

Statistical power

Medium

x 0.2

0.4

A total of 487 individuals (367 men, 120 women)
were in the analysis sample. There is some concern
due to the low number of cases of ovarian and laryn-
geal cancers, making the estimates unstable.

Metric 14

Reproducibility of analyses

Medium

x 0.2

0.4

The description of the analysis was sufficient that,
given original data, the analysis could be repro-
duced.

Metric 15

Statistical models

Medium

x 0.2

0.4

The calculation of SMRs was transparent and model
assumptions appear to be met.

Domain 6: Other Considerations for Biomarker Selection and Measurement









Metric 16

Use of Biomarker of Exposure



NA

NA



Metric 17

Effect biomarker



NA

NA



Metric 18

Method Sensitivity



NA

NA



Metric 19

Biomarker stability



NA

NA



Metric 20

Sample contamination



NA

NA



Metric 21

Method requirements



NA

NA



Metric 22

Matrix adjustment



NA

NA



Overall Quality Determination1"

Medium

—> Low§





Extracted



Yes







MWF = Metric Weighting Factor

High = 1; Medium = 2; Low = 3; Unacceptable = 4; N/A has no value.

The overall rating is calculated as necessary. EPA may not always provide a comment for a metric that has been categorized as High.

Overall rating =

]T\ (Metric Score; x MWF;) / J] . MWFj

if any metric is Unacceptable
(round to the nearest tenth) otherwise

where High => 1 to < 1.7; Medium => 1.7 to < 2.3; Low => 2.3 to < 3.0. If the reviewer determines that the overall rating needs adjustment, the original rating is
crossed out and an arrow points to the new rating.

^ This metric met the criteria for high confidence as expected for this type of study
§ Evaluator's explanation for rating change: "Low number of mortality cases for laryngeal cancer."

65 of 65


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