Document bo9XyReeeNLgjQw47vyKJ236
REPORT OF A PRELIMINARY SURVEY OF THE
BRASS FOUNDRY OF THE SCHAIBLE COMPANY CINCINNATI, OHIO
From the Kettering Laboratory In the Department of Preventive Medicine and Industrial Health, College of Medicine,
University of Cincinnati, Cincinnati, Ohio
H 0018570
Material* Source :
Method of Collection! Date of Collection: Required:
.\
Air Samples
Brass Foundry of The Schaible Company, 2620 Cook
Cincinnati, Ohio
Electrostatic precipitator, MSA carbon monoxide
November 13> 1952
Concentrations of lead, zinc and carbon monoxide dust counts
Results
Analysis Number
52A-7680
52A-768I
52A-7682
52A-7683
52A-7681+
(A)
Location
On charging platform between #8 and #9 furnaces
Temperature
Time of at Location
Sampling'
F
9:1+5 am
90
Between furnace platforms
9:55 am
-
On charging platform
between #5 and #6
furnaces
9:1+5 am
100
While skimming (three 10:10 am ladles)
-
On charging platform of Roda furnace
While casting on #1+
roller conveyor (up wind from fume)
10*00 am 10:20 am
120
73
Mgs . metal per
cubic meter of air
Lead
Zinc
0,36
2.60
-
1.00
-
6.00
2.03 1.18 . O.72
11.80
9*90
6.10
Mill parti
cubi of
Analysis Number
52A-7684
(B)
?2A-7o85 ?2A-786
?2A-7 87
)2A-7 88
32A-7689
52^-7690 )2A-7691
J2A -7711
I2A -7712
Location
While casting on #4
roller conveyor (in path of fume from ladles)
Time of Sampling
10525 am
While casting on large 1015 am power mold conveyor
At shake-out on #4
roller conveyor
10:35 am
At shake-out between the two power mold conveyors
10;30 am*
In area between mold 10;50 am ing machines #1 and#2
In area near molding 10:50 am machine #l6
In grinding room near 11:20 am drinking fountain
In core cleaning area in core room
Dust removed from pipes in core room near molding area
11:05 am
Dust removed from rafter in center of casting area
(a) Crystalline silica = 50^
Temperature at Location
op
75
74
76 76
** 71 80 -
"
Mgs . metal per
cubic meter of air
Lead
Zinc
2.54 40.80
Mill parti
cubi of
0*67 0.4l 0.40
6.45
3.70
5.54
0.31 O.065
0.145
0.100 0.63^
0.62^
2.13 0.26 0.88 O.75
2.59^(a)
6.29^(b)
(b) Crystalline silica = 2
Analysis Number
location
Area in front of furnaces (pouring area)
Time of Sampling
11:30 am
Temperature at Loc
0
cd
Mgs. metal per
cubic meter of air
Lead
Zinc
3- -
Millions of particles per
cubic meter of air
Carbon Monoxide (parts per million)
25
-b -
Remarks
1. Dust counts yielded fewer than 5 million particles per
cubic foot at the core making,shake-out, molding, and grinding
operations which were investigated on November 11* No samples
were collected in the "Wheelabrator1' area or in other areas where
sands are processed for use, A situation involving 5 million
particles per cubic foot of air is considered safe where dusts
containing more than 75 per cent of free silica are being handled.
2. All concentrations of carbon monoxide determined during
this cycle of operation were at or below the value of 100 p.p.m*
considered satisfactory for regular Industrial exposure of 8 hours
duration per day.
3* The concentrations of lead in the atmosphere at all
stations except in the core room and near molding machine #16
equaled or exceeded the concentration of 0.15 mg. per cubic meter
of air which is generally considered to be the maximum concentration
which should be permitted in workrooms in which men are employed
regularly for 8 hours daily. Except for samples 7689 7^9*-* and *
769T the concentrations of lead in the atmosphere exceeded the
generally accepted safe level by factors varying from 2.1 to 17.
The conditions with respect to lead exposure, therefore, are
hazardous, if men are exposed to them over sufficiently prolonged
periods of time.
ij.. Only one result on zinc (sample
B) exceeded the
value of 15 mgs. per cubic meter of air which is generally accepted
as satisfactory for industrial exposure,
5* The levels of lead or other contaminants found are repre
sentative only of one dayfs operations. The conditions which
prevail generally and regularly could be appraised only by
-5repeated analyses of the atmosphere under a variety of operating conditions.
Recommendations
1. An engineering survey should be made to determine the best
means for reducing the concentrations of the toxic materials in the atmosphere to safe levels. Such a survey would involve additional air sampling and analysis to determine the nature of the air entering the building, within the building, and discharged from the building. By reducing the amount of lead in the air to a safe level, safe conditions with reference to other toxic fumes . and gases will also be provided.
2. Periodic determinations should be made of the levels of
lead concentration in the urine and blood of all exposed persons. A medical program involving pre-employment and periodic exami nations should be tied in with this sampling program. Such a program also would involve considerations concerning the proper use and type of personal protective devices, the improvement of housekeeping, the provision of*an adequate locker room, wash room and eating room.
Prom the Kettering Laboratory in the Department of Preventive Medicine and Industrial Health, College of Medicine,
University of Cincinnati, Cincinnati, Ohio
Work and report by: J, Cholak L. J. Schafer D, Yeager
Date: December 1, 1952
Approved: Robert A. Kehce, M.D. Director