Environment
INFORMATION FROM KODAK
Indoor Air Quality and Ventilation in
Photographic Processing Facilities
J-314(ENG) $10.00
Kodak’s health, safety,
and environmental
publications ar e avai l ab l e
to help you manage your
photographic proce ssin g
operations in a safe,
environmentally sound
and cost-effective manner
INTRODUCTION
The Occupational Safety and
Health Administration (OSHA)
presents a framework of federal
regulations that set chemical
exposure standards for the
workplace environment. These
standards outline allowable limits
that employees may be safely
exposed to during the work day.
Effective ventilation systems are an
important tool that will help
minimize employee exposure to
photographic processing
chemicals. While photographic
processing facilities are typically
considered to be a low hazard
workplace, indoor air quality
environment can be improved if
well engineered ventilation
systems are installed.
This publication will provide
information on the following
topics:
• Indoor air quality
• Exposure concepts
• Air contaminants
• Exposure standards and
guidelines
• Methods of evaluation
• Ventilation and work practice
control measures
This publication is a part
of a series of publications
on health and safety
issues affecting photographic
processing facilities.
It will help you understand
the role and proper use of
ventilation systems in the
workplace.
This publication is meant to assist others with their compliance programs. However, this is
not a comprehensive treatment of the issues. We cannot identify all possible situations and
ultimately it is the reader’s obligation to decide on the appropriateness of this information to
his/her operation.
©Eastman Kodak Company, 2002
INDOOR AIR QUALITY (IAQ)
The quality of the air in our homes,
schools, and places of business is an
important environmental health
issue. It is estimated that we spend
over 90% of our time indoors. It is
also important to note that the
design of buildings and ventilation
systems has changed dramatically
over the last 50 years as we have
moved toward more energy
efficient, climate controlled
environments. New or remodeled
buildings are more air tight, which
leads to less air exchange between
indoor air and fresh outdoor air. To
ensure good indoor air quality,
adequate fresh outdoor air must be
brought indoors. You can no longer
rely on leaking windows or other
pathways for outdoor air
infiltration. Indoor air quality (IAQ)
depends upon the ability of a
ventilation system to remove or
control the contaminants generated
within a space to acceptable levels.
When there is insufficient fresh
dilution air, IAQ problems can occur
which may result in a variety of
symptoms in building occupants
including:
• headache
• sinus congestion
• nausea
• eye, nose and throat irritation
• sneezing
• a metallic or sweet taste in mouth
• dizziness
Two terms are used to describe
IAQ health-related problems.
Sick Building Syndrome (SBS):
describes cases in which building
occupants experience acute health
and comfort effects that are
apparently linked to the time they
spend in the building, but in which
no specific illness or cause can be
identified. Basically, people enter
the building and experience
symptoms which clear up after they
leave the building.
Building Related Illness (BRI):
refers to symptoms of diagnosable
illness that can be directly attributed
to environmental agents (chemical,
biological or physical) in the
building air. In other words, people
enter and become ill from a known
agent in the building air but do not
necessarily get better after they
leave the building (examples:
Legionnaire’s disease, respiratory
infections, and humidifier fume
fever).
The causes of poor IAQ continue
to be studied extensively. In the
1980s the National Institute of
Occupational Safety and Health
(NIOSH) studied over 600 buildings
and identified the following as
potential causes of poor IAQ:
Inadequate ventilation 52%
Inside sources 17%
Outside sources 11%
Biological 5%
Building fabric 3%
Unknown 12%
Recent studies have lead some
experts to believe that biological
contamination (molds, fungi,
bacteria) may account for up to 30%
of the IAQ problems in buildings.
To help prevent IAQ problems,
we recommend that you assemble a
comprehensive program that is
preventive in focus. Specific
performance elements of your IAQ
program should include:
1. Developing and maintaining an
IAQ profile for each building
(year built, tenant operations,
number of people, type of
HVAC).
2. Developing and maintaining a
thorough understanding of
your IAQ requirements and
processes.
3. Maintaining up-to-date line
drawings and equipment
schedules for each HVAC
system.
4. Documenting the operational
parameters for each HVAC
system including scheduled
time of operation, temperature
and humidity set points,
seasonal variations, outside air
requirements, air flow
parameters.
5. Providing a process to identify,
investigate, track and respond
to IAQ-related complaints.
6. Maintaining a written
maintenance program and
relevant history of each HVAC
unit.
7. Providing a process to review all
major projects in or near the
building for their IAQ
implications.
8. Ensuring that HVAC systems
are commissioned and
periodically balanced.
9. Ensuring that the performance
of local exhaust systems are
periodically assessed.
10. Providing a process to review
health, safety and
environmental implications of
maintenance and housekeeping
chemicals used in the facility for
remodeling or construction
activities that may impact IAQ.
11. Requiring compliance with local
regulations or company
standards regarding smoking in
the workplace.
12. Requiring that personnel
involved in the design,
operation, evaluation and
maintenance of HVAC systems
are properly trained and aware
of new IAQ regulations and
trends.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 2
EXPOSURE CONCEPTS
ROUTES OF EXPOSURE
In a work environment where
chemicals are used, an individual
may potentially be exposed in three
ways:
• inhalation
• skin and eye contact
• ingestion
Inhalation is the most common
route of exposure for airborne
particulates, gases, and vapors.
Inhalation exposures are important
because many chemicals that enter
the lungs can pass directly into the
blood stream and be transported to
other areas of the body.
Skin contact can also be a
significant source of exposure which
can lead to adverse health effects.
Some chemicals can be absorbed
into the body through the skin while
others may cause irritation or rashes
(dermatitis). In addition, some
chemicals are potential eye irritants.
Ingestion is not con sidered to be a
significant problem in the
workplace. Inadvertent ingestion of
chemicals may occur if food or
beverages are consumed in chemical
handling areas or if good personal
hygiene practices are not followed,
i.e., washing hands before eating,
drinking, smoking, etc.
Air contaminants: are chemicals
that may be present in the air that
could be inhaled and may produce
adverse effects. These effects can be
divided into two classes:
• acute
health effects—an adverse
effect resulting from a single
exposure with symptoms
developing almost immediately
or shortly after exposure; the
effect is usually of short duration.
Symptoms may include irritation,
headache, dizziness, or nausea.
• chronic health effects—adverse
effects resulting from repeated
low level exposure, with
symptoms that develop slowly
over a long period of time. These
may affect target organs such as
the liver, kidney, or lungs or cause
cancer.
Dose Response: All chemicals are
toxic if taken into the body by the
right route of exposure and at a high
enough dose. As the dose increases,
there is a corresponding effect or
response.
Chemicals that require large doses
or exposure concentrations to
produce an adverse effect have a
low toxicity, while chemicals that
require smaller doses to produce an
adverse effect are considered more
toxic. For example, acetic acid is
irritating to the eyes and upper
respiratory system at low
concentrations, about 10 ppm.
Isopropyl alcohol is not irritating to
the eyes until concentrations reach
over 400 ppm. Based on this
comparison, acetic acid causes an
irritation at much lower
concentrations than isopropyl
alcohol.
AIR CONTAMINANTS
The air within buildings usually
contains a variety of air
contaminants. These contaminants
can originate from outside sources
(car/truck exhaust) or emissions
from inside sources (office
equipment, furnishings, carpet,
people, kitchens, janitorial
activities).
Whatever the source,
contaminants in the air fall into one
of two physical states of matter.
They are either:
• gases and vapors, or
• solids (particulates)
Gases/Vapors: The difference
between gases and vapors is their
physical state at standard
temperature and atmospheric
pressure (STP, 22.5°C, and 760 mm
Hg). A gas is in the gaseous state at
STP (examples: nitrogen, carbon
dioxide, sulfur dioxide). A vapor is a
gas from a substance that at STP is a
liquid (example, acetic acid).
Particulates: There are several
forms of particulate matter that can
be airborne. These include:
• dust
• fumes
• smoke
• mists
Dust results from the application
of energy to matter, by grinding,
sifting pouring solids, paper cutting,
etc. Dust particles have to be small
enough and light enough to be
airborne.
Fumes are generated by the
condensation of particles in the
vapor state from heated metals.
Fumes are typically smaller than
dust, more soluble, and are more
physiologically active. Fumes are
not generated during normal
photographic processing
operations.
Smoke results from incomplete
combustion and is made up of
extremely fine particles, even
smaller than fumes. Smoke is
extremely complex chemically,
containing thousands of chemical
substances. Unless something is
burning, smoke is not generated
during photographic processing
operations.
Mists result from the dispersion
of fine droplets by aerosolization of
any liquid (spray cans, nitrogen
agitation of tanks, electroplating).
Mists can be formed during the
mixing, recirculation or pouring of
liquids. Mist can also be generated
from foam on the surface of a liquid.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 3
As the bubbles burst, tiny droplets
of the liquid are released into the air.
The composition of a mist is usually
the same as the liquid from which it
was generated.
ANTICIPATED AIR
CONTAMINANTS
FROM PHOTOGRAPHIC
PROCESSING
OPERATIONS
Potential air contaminants
associated with photographic
processing operations will be
determined by the specific process
chemistry and the operating
conditions of the equipment. Some
photographic processing solutions
release small amounts of vapors
such as acetic acid and benzyl
alcohol or gases such as ammonia, or
sulfur dioxide. High-temperature
processing and nitrogen-burst
agitation of tank solutions may
increase the release of chemicals
into the air and generate mists from
the photographic processing
solutions. Depending on the
concentration in the air, these
chemicals could be irritating to the
eyes and respiratory tract, or create
odors. Although odor does not
always indicate safe versus unsafe
conditions, strong odors or the
presence of eye and/or respiratory
irritation can indicate that there is
not sufficient general dilution
ventilation or that the local exhaust
systems may not be capturing the air
contaminants effectively at their
source.
In order to assess whether or not
exposure to airborne chemicals
presents a health and safety hazard,
several exposure standards and
guidelines are available for
comparison.
EXPOSURE STANDARDS AND GUIDELINES
THE OCCUPATIONAL SAFETY AND HEALTH ADMINISTRATION (OSHA)
In 1970, OSHA reviewed existing
exposure guidelines and consensus
standards in the workplace, and
adopted these as OSHA regulations.
These exposure standards set
airborne concentration limits and
are legally enforceable. Two of the
major references used by OSHA at
that time were the 1968 Threshold
Limits Values (TLVs) published by
the American Conference of
Governmental Industrial H ygienists
(ACGIH) and Acceptable
Concentrations of Toxic Dusts and
Gases published by the American
National Standards Institute (ANSI).
Since 1970, OSHA has established
approximately 28 new chemicalspecific standards. These new
standards such as the one for
formaldehyde, are much more
comprehensive and detailed. These
new standards include additional
requirements for written programs,
training, personal protective
equipment, control measures,
medical surveillance, etc.
The airborne exposure limits
established by OSHA include:
Permissible Exposure Limit
(PEL): The allowable limit that is
representative of a worker’s
exposure, averaged over an 8-hour
day.
Short-term Exposure Limit
(STEL): The allowable limit that is
representative of a worker’s
exposure, averaged over 15 minutes.
Ceiling Limit (C): The airborne
concentration that is representative
of a worker’s exposure that should
not be exceeded.
Action Level (AL): For the
comprehensive standards
established by OSHA, an Action
Level may be specified. The Action
Level is typically
the concentration at which you may
have to address certain compliance
requirements such as employee
monitoring, training, or medical
surveillance.
1
⁄
of the PEL and is
2
AMERICAN CONFERENCE OF GOVERNMENTAL INDUSTRIAL HYGIENISTS (ACGIH)
ACGIH is a professional
organization whose members work
within the government or academia.
This organization annually
publishes a booklet entitled
Threshold Limit Values (TLVs) for
Chemical Substances and Physical
Agents and Biological Exposure
Indices (BEIs). ACGHI TLVs are
exposure guidelines and do not
have the effect of law. These values
change in response to new data and
are usually more rapidly updated
than OSHA limits.
The Threshold Limit Value (TLV)
refers to airborne concentrations of
substances and represents
conditions under which it is
believed that nearly all workers may
be repeatedly exposed day after day
without adverse health effects.
The ACGIH TLVs include:
Threshold Limit Value-TimeWeighted Average (TLV-TWA):
The time-weighted average
concentration for a normal 8-hour
workday and a 40-hour work week,
to which nearly all workers may be
repeatedly exposed, day after day,
without adverse effect.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 4
Threshold Limit Value-Short-
Term Exposure Limit (TLV-STEL):
The 15-minute TWA concentration
which should not be exceeded at any
time during a workday even if the 8hour TWA is within the TLV-TWA.
Exposure above the TLV-TWA up to
the STEL should not be longer than
15 minutes and should not occur
more than four times per day with at
least 60 minutes in between
exposures in this range.
Threshold Limit Value-Ceiling
(TLV-C): The concentration that
should not be exceeded during any
part of the working exposure.
OSHA Limits vs ACGIH
Guidelines: OSHA limits are legally
enforceable, whereas ACGIH limits
are guidelines. In most cases, the
ACGIH guidelines are the same or
lower than OSHA limits (there are a
few exceptions). When the values
are not the same, it is prudent to
follow the lower, more conservative
value.
Examples:
Chemical
Acetic acid 10 ppm 10 ppm
Ammonia 50 ppm 25 ppm
Formaldehyde 0.75 ppm 0.3 ppm
Sulfur dioxide 5 ppm 2 ppm
OSHA
PEL 8-hour
ACGIH
TLV 8-hour
(ceiling)
METHODS OF EVALUATION
THE PURPOSE OF COLLECTING AIR SAMPLES
Air samples are sometimes collected
to evaluate potential worker
exposure levels for comparison to
published exposure standards or
guidelines. The purpose of the
measurement may vary depending
on whether you are interested in
short-term exposure, full shift
exposure, or the exposure incurred
during a specific step or process. The
measurements represent a sampling
of the actual working conditions at
the time of sampling. Generally, the
more sampling data that are
available for a certain job/process/
task under a variety of conditions,
the better understanding and
confidence you will have in the
exposure measurements during that
process. As illustrated in Figure 1,
actual exposure can vary
substantially during the day. In
some cases, full-shift monitoring
may be the goal while in others, the
goal may be to understand shortterm exposure.
Figure 1
Typical Exposure Scenario
Actual
OSHA PEL
Concentration (ppm)
Basic Definitions
Sensitivity or Precision: how
reproducible is the sampling
method.
Accuracy: how close to the true value
is the sampling method.
8-hr
Avg.
4pm2pmNoon10am8am
MEASUREMENT TECHNIQUES
Direct Reading
These are measurement techniques
that can immediately indicate the
concentration of aerosols, gases, or
vapors by some means such as a dial
or meter or noting the color change of
an indicator chemical.
Colorimetric Detector Tubes
Several colorimetric, direct reading
detector tubes are useful for quick
assessments of airborne
contaminants associated with
photographic processing. A special
pump draws a specific volume of
room air through a detector tube. If
the contaminant is present, a color
change occurs along the length of the
tube that is directly proportional to
the concentration of the contaminant
in the air. Tubes are available for
acetic acid, sulfur dioxide, ammonia,
and many other gases and vapors.
The tubes are easy to use and
generally have an accuracy of ± 25%.
Other chemicals in the air may
interfere with the accuracy and
sensitivity of the tubes.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 5
Direct Reading Instruments
Many different direct reading
instruments are available for air
sampling measurements. Some of
these can be very specific to a
chemical (e.g., sulfur dioxide
analyzers) while others are
nonspecific (e.g., organic vapor
analyzer with photoionization [PID]
or flame ionization [FID] detectors).
Calibrate all instruments before and
after making any measurements.
Samples with Subsequent Laboratory Analysis
There are many air sampling
techniques that rely on collecting a
known volume of air followed by
laboratory analysis.
Passive diffusion badges are easy
to use and excellent for measuring
many volatile organic compounds.
This method is most useful for
measuring (quantifying) known
airborne contaminants. Although
passive badges are commonly
employed for measuring full shift
average exposures, they also can be
useful for short-term exposure
measurements.
Solid sorbent/tubes/bubblers are
similar in many ways to passive
badges except that air must be
actively drawn through the
sampling device using a calibrated
sampling pump. Numerous
laboratory techniques are available
for specific chemical analysis
following sample collection.
Grab samples refer to collecting a
volume of air at a certain point in
time. This technique can be useful
for assessing short-term exposures.
New canister samplers allow for the
sample to be drawn in over a much
longer period of time, if desired.
This technique is most useful for
volatile organic hydrocarbons.
VENTILATION AND WORK PRACTICE CONTROL MEASURES
Proper ventilation is important to
assure a safe and comfortable indoor
environment for photographic
processing areas. Several common
potential indoor air contaminants
can be associated with photographic
processing. These include: acetic
acid, sulfur dioxide, and ammonia.
These chemicals may be eye and
respiratory tract irritants depending
on their airborne concentrations.
Exposure guidelines and standards
for these chemicals have been
established to prevent significant
eye or respiratory tract irritation in
most workers. Significant eye or
respiratory tract irritation during
normal photographic processing or
maintenance operations may
indicate elevated levels of these
materials and the need for better
control.
General control strategies in order
of preference include:
• chemical substitution (where
possible)
• engineering controls (ventilation,
enclosures, process isolation)
• work practices or administrative
controls (operating procedures,
employee rotation)
• personal protective equipment
(safety glasses, gloves,
respirators)
Engineering controls that have
proven to be effective in minimizing
airborne levels of photographic
processing chemicals include:
• Good design and layout for
process flow and ergonomic
considerations
• Using dilution and local exhaust
ventilation
• Providing covers for processing
equipment tanks and chemical
storage tanks
GOOD FACILITY DESIGN
The proper location and layout of
photographic processing operations
is an important element in designing
a safe and healthy workplace.
General ventilation systems have
the potential to recirculate a
significant percentage of the air
returning from the photographic
processing areas. If the general
ventilation system also supplies
non-photographic processing work
areas, it is possible that the
photographic processing odors may
also impact these areas.
VENTILATION
Kodak studies of potential worker
exposure during automated
photographic processing operations
have indicated that vapors and
gases can be controlled to acceptable
levels through good general room
ventilation (dilution ventilation).
However, in some cases, local
exhaust for enclosed and/or open
tanks may be recommended.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 6
DILUTION VENTILATION
Dilution or general ventilation is
simply bringing in and distributing
enough fresh, uncontaminated air
(preferably outdoor air) to dilute the
indoor air contaminants to an
acceptable level.
Minimum recommendations for
general ventilation for buildings and
processes are provided by the
American Society of Heating,
Refrigeration and Air Conditioning
Engineers (ASHRAE).
For photographic processing
operations, ASHRAE Standard 621989 recommends:
• 0.5 cubic feet per minute (cfm) of
fresh outside air, per square foot
2
(ft
) of floor area (0.5 cfm/ft2),
assuming a maximum occupancy
of 10 persons/1000 ft
darkrooms.
For example, if the room where
photoprocessing takes place is 10 ft
x 20 ft x 8 ft, the floor area is 200 ft
and the room volume is 1600 ft
Based on 0.5 cmf/ft
need to supply at least 200 x 0.5 or
100 cfm of fresh outside air to the
space.
The number of “room air changes
per hour” is determined by the fresh
air supply rate. In the example, in
one hour 6000 ft
3
min) of fresh air entered the space
(room volume: 1600 ft
the room air changes per hour, you
divide the total amount of fresh air
that has entered the space by the
volume of the room:
3
6000 ft
/hr/1600 ft3 room volume =
3.75 air changes per hour.
It is important to note that the
ASHRAE recommendations
represent the minimum amount of
fresh air that should be supplied to
the space. Past recommendations
from Kodak have been as high as ten
air changes per hour.
2
in
3
2
, you would
.
(100 ft3/min x 60
3
). To calculate
2
When using dilution ventilation,
airborne contaminants are not
captured at the source. Instead, the
contaminated air is turned over and
replaced quickly enough to
minimize potential exposure and
related odors. To be most effective,
make sure you properly position the
supply air inlets and return air
outlets for good mixing/dilution of
the room air. Their placement must
minimize the potential for “short-
circuiting” or direct flow of supply
air to return with minimum room air
mixing (Figure 2). For a large room,
you may need supply air inlets and
return air outlets throughout the
room. Do not position the inlet and
outlets too close together.
Figure 2
Open tank processor with general room
dilution ventilation
LOCAL EXHAUST
VENTILATION
Local exhaust ventilation is used to
capture air contaminants close to the
source of generation, before they can
enter the general work room air.
This type of ventilation can be very
effective at controlling airborne
contaminants. A general room
exhaust system will reduce airborne
Supply Fresh Air
levels but is not considered local
exhaust ventilation. A local exhaust
system may be more expensive to
install than a general dilution
ventilation system, but requires less
air (and energy) to effectively
control the airborne contaminants.
When designing local exhaust
systems, the objective is to capture
contaminants close to the source and
draw the contaminated air stream
away from the air you breathe.
Avoid placing workstations
between the source (photographic
processor) and the inlet to the
exhaust hood.
You can find information on the
proper design of local exhaust
systems in the ACGIH Industrial
Ventilation Manual (ACGIH 2001).
The design must also consider the
required “make-up” air system
you’ll need to replace and condition
the air that is exhausted from the
building. In addition, it is also
important to review local laws and
ordinances regarding local exhaust
and any permit requirements with
local, state, or federal regulators.
RECOMMENDATIONS
MINILABS
General dilution ventilation
following the minimum fresh air
recommendations from ASHRAE
(0.5 cfm/ft
effective at controlling air
contaminants associated with
minilab processes. In some cases,
venting the dryer section of the
processor to outdoors may be
appropriate to prevent excessive
humidity (greater than 60% relative
humidity) and odors in the
workplace. Consult with the
processor manufacturer for specific
venting requirements.
2
of floor area) should be
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 7
S
LARGE PHOTOGRAPHIC PROCESSING FACILITIES
The most effective controls for
minimizing potential airborne
exposures and odors related to large
photographic processing operations
are a combination of both local
exhaust and dilution ventilation
(Figure 3). Fresh dilution air
be supplied to the darkroom at a rate
of 150 cfm per machine. If a machine
extends through a barrier into
another room, supply fresh dilution
air to both rooms. Depending on the
process chemistry, you may need
local exhaust at uncovered stabilizer
tanks or at the bleach fix tanks at a
rate of 170 cfm per machine
(Figure 4). In many cases, exhaust is
also provided at the dryer section to
help control heat and humidity in
the room. An exhaust rate slightly
greater than the supply rate results
in a negative room air pressure
which reduces the potential for air
contaminants and odors for
escaping from the photographic
processing area to any adjacent
areas.
Open-machine, general room
Supply Fresh Air
150 cfm
Figure 3
exhaust ventilation
1
should
Exhaust to Outdoors
170 cfm
Figure 4
Open-machine with a
slot hood ventilation
upply Fresh Air
150 cfm
Exhaust to Outdoors
170 cfm
If solution tanks are enclosed or covered, the fresh air supply rate may be
reduced to 90 cfm and the exhaust rate to 100 cfm per machine (Figure 5).
1. Means “uncontaminated air” which includes
the ASHRAE recommendation of 0.5 cfm/ft
2
.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG)8
Figure 5
Enclosed-machine
ventilat i on
Supply Fresh Air
90 cfm
Exhaust to Outdoors
100 cfm
In addition, it is important to
follow the processing equipment
manufacturer’s recommendations
regarding venting of the dryer
section of the processor. Whenever
possible, dryer vents should be
ducted to the outdoors to prevent
the build up of excessive
temperature and humidity in the
workplace.
Install all local exhaust systems
that vent to the outdoors in
accordance with local, state, and
federal regulations.
EFFECTIVE COVERS FOR PROCESSING EQUIPMENT AND CHEMICAL STORAGE TANKS
Covers on photographic processing
equipment and chemical storage
tanks can effectively minimize the
amount of gases, vapors or mists
that may enter the work area. In
addition, covers also reduce the
potential for contamination of the
processing solutions. Covers should
be fabricated from durable, nonreactive materials and should cover
as much of the open surface of the
tank as possible. In many cases,
effective tank covers combined with
good general room ventilation, and
proper operation and maintenance
may be all that is needed to control
odors and airborne exposure to
photographic processing chemicals.
In situations where local exhaust is
needed for a covered tank, 25 - 30
cubic feet per minute (cfm) per
square foot of tank area is adequate.
Work practices controls:
• Proper operation and
maintenance of photographic
processing equipment;
• Prudent techniques for handling
chemicals.
PROPER OPERATION AND MAINTENANCE OF PHOTOGRAPHIC PROCESSING EQUIPMENT
The level of airborne contamination
generated from photographic
processing solutions can be affected
by how the processing equipment is
operated. It is important to follow
the manufacturer’s recommended
operating procedures for operating
temperature, the agitation of
processing solutions, and
processing speeds.
In addition, draining and flushing
processing equipment tanks with
cold water prior to rack removal or
maintenance operations can also be
effective at controlling short-term
exposures to processing solutions.
The health, comfort, and
efficiency of personnel, as well as the
proper conditions for processing,
handling and storage of
photographic materials depends on
a suitable indoor air environment.
Modern ventilation techniques
include several factors: air supply,
air movement; air distribution; air
conditioning or control of
temperature and humidity; air
pressure adjustment; and air
cleaning or filtration. If you plan a
photographic plant of considerable
size, consult a ventilation and air
conditioning engineer as early as
possible in the planning stages. If the
designer has the opportunity to
make suggestions in the early stages
of planning, the result may be a
better overall design, and lower
installation and operating costs.
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 9
REGULATORY AND ASSOCIATED REFERENCES
Subject Resource
Exposure Standard OSHA, 29 CFR 1910.1000, Tab le Z1, Z2, and Z3
Formaldehyde Standa rd OSHA, 29 CFR, 11910.1000-1048
Design of Ventilation System s ACGIH Industrial Ventilat ion Manual (ACGIH 2001)
Design of Ventilation Systems
(Ventilation Recommendations)
Theshold Limit Values Threshold Limits Values (lat est edition), American Conferen ce of G ov ernmental Industrial Hygien ist s
Indoor Air Quality Building Air Quality, A Guide for Building Owners and Facility Managers, U.S. Environmental Protection
Indoor Air Quality Indoor Air Quali t y and H VAC Sy st em s, D av i d W. Bea rg , Lew is Publishers, 1993
American Society of Heating, R efr ig er at ion and Air Condition Engineers Sta ndard 62-1989
Agency
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 10
MORE INFORMATION
If you have environmental or safety questions about
Kodak products, services, or publications, contact
Kodak Environmental Services at 1-585-477-3194, or
visit KES on-line at www.kodak.com/go/kes.
Kodak also maintains a 24-hour health hotline to
answer questions about the safe handling of
photographic chemicals. If you need health-related
information about Kodak products, call
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For questions concerning the safe transportation of
Kodak products, call Kodak Transportation Services at
1-585-722-2400.
Additional information is available on the Kodak
website and through the Canada faxback system.
The products and services described in this
publication may not be available in all countries. In
countries other than the U.S., contact your local Kodak
representative, or your usual supplier of Kodak
products.
J-311 Hazard Communication for Photographic
Processing Facilities
J-312 Personal Protective Equipment Requirements in
Photographic Proces sing Facilities
J-313 Occupational Noise Exposure Requirem en ts for
Photographic Proces sing Facilities
J-315 Special Materials Management in Photograp hi c
Processing Facilities
J-316 Emergency Preparedness for Photographic
Processing Facilities
J-317 Injury and Illness Management for Photographic
Processing Facilities
Indoor Air Quality and Ventilation in Photographic Processing Facilities • J-314(ENG) 11
For more information about Kodak Environmental Services,
visit Kodak on-line at:
www.kodak.com/go/kes
Many technical suppo rt publications for
Kodak products can be se nt to you r f ax m ac hi ne
from the Kodak Information Center. Call:
Canada 1-800-295 -55 31
—Available 24 hours a day, 7 days a week—
If you have questions about KODAK product s, call Kodak.
In the U.S.A.:
1-800-242-2424, Ext . 19, Mo nday–Friday
9 a.m.–7 p.m. (Eastern time)
In Canada:
1-800-465-6325, Monday–Friday
8 a.m.–5 p.m. (Eastern time)
This publication is a guide to the Federal Health and Safety Regulations
that apply to a typical photographic processing fac ility . Local or state
requireme nt s ma y al so ap pl y . Ver i fy th e s pec if i c r eq ui re ment s fo r y our
facility with your legal counsel.
Indoor Air Quality and Ventilation in
Photographic Processing Facilities
KODAK Publication No. J-314(ENG)
CAT No. 184 9298
This publication is printed on recycled paper that contains
50 percent recycled fiber and 10 percent post-consumer material.
EASTMAN KODAK COMPANY • ROCHESTER, NY 14650
Kodak and “e" mark are trademarks.
Revised 9/02
Printed in U.S.A.
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