INDUSTRIAL HYGIENE
 The 3 definite elements in industrial hygiene
 are the recognition, evaluation and control
       of occupational health hazards.
       The recognition of health hazards has
primacy, since it must take place before proper
   evaluation or (if needed) control can take
place. Upon recognition of a health hazard, the
industrial hygienist should be able to identify
 measures necessary for proper evaluation.
Upon completion of the evaluation, the industrial
hygienist then is in a position – in consultation with
 other members of the occupational health safety
team – to recommend controls needed to reduce
           exposures to tolerable limits.
  -1). Recognition of health hazards in the
                    workplace
 This is the first step in the process leading to
     evaluation and control and entails the
  identification of materials and processes
that have the potential for causing harm to
                     workers.
Sources of information about health
 hazards include clinical data about
     health problems in exposed
populations; information in scientific
 journals and reports of government
agencies; direct reports from workers,
union representatives, supervisors, or
              employers.
Inspection of the workplace is the best
 source of directly relevant data about health
                   hazards.
  There is no substitute for observation of
    work practices, use of chemical and
physical agents, and apparent effectiveness
            of control measures.
  The physician should be able to recognize
    major and obvious health hazards and
     distinguish those that require formal
    evaluation by the industrial hygienist.
The “walk through survey” in the
    company of the occupational health
  physician is the first and most important
 technique for recognition of occupational
               health hazards.
   The survey should begin with a proper
   introduction to plant management and
discussion of the purpose of the survey and
      inquiry about any relevant recent
                 complains.
Following the process flow through the
       plant is most productive.
  The survey might thus begin at the
    loading dock, where materials
entering the plant can be examined.
 Warning labels, descriptive language
  about the chemical composition of
   materials, and the packing of the
 incoming materials should be noted.
Questions should then be asked
  regarding the handling of unknown
  materials or materials about which
insufficient information is available.
        The incoming materials should
 then be followed into the process flow
   stream, and each of the process of
     interest in the plant should be
          observed in action.
Of interest throughout the survey
   will be the methods used for
material handling, particularly at
    the places where they are
transferred from manufacturers’
  containers into vessels for use
         within the plant.
Observations to be made.
  At each point in the process, the industrial
     hygienist should observe handling
    procedures as well as any protective
     measures that are employed. Use of
respiratory protection and protective clothing
should be recorded, as well as other common
   sense observations such as the apparent
  effectiveness of engineering controls – as
   indicated by absence of characteristic
odors, visible dust accumulations, and loud
                    noise.
The survey should continue through
to the final product produced by the
        plant and its packing.

 The industrial hygienist should also
  follow the pathway of any waste
materials and determine their disposal
                 sites.
The number of employees at each step
should be noted, as well as any relevant
  data on gender, ethnicity, or age that
  might affect employees’ sensitivity to
        chemicals in the workplace.
 It is also important to look for obvious
stigmas such as drying of skin, as might
   expected where exposure to solvents
                  occurs.
Data review.
Important part of the industrial hygienist’s
role in recognition of health hazards in the
      workplace will be data review.
   Such data may include reports from
physicians on clinical findings that may
be related to exposures in the workplace
 as well as a review of company records
 on materials coming into the workplace
   that may present significant hazards.
A common-sense duty of the employer is
    to inform workers of the nature and
hazards of materials to which they may be
                   exposed.
 In some cases, the industrial hygienist must
assess the potential for harm of chemicals for
 which no reliable human toxicological data
 are available. This need arises most often in
 research and development settings but also
    wherever chemical intermediates are
                 produced.
An important consideration is that the worker
  must be protected at all cost. If uncertainty
exists, it should be resolved in favor of highest
               standard of concern.

 Upon competition of the walk-through survey,
  the industrial hygienist will ordinary have a
closing conference with the plant management,
    at which time obvious concerns can be
  discussed and follow-up measures agreed
                     upon.
2).Evaluation of health hazards

Evaluation of health hazards within
the plant will include measurements
 of exposures, comparison of those
exposures to existing standards, and
  recommendations of controls, if
                needed.
Exposure measurements.

They are intended to be determinations
of doses delivered to the individual.

The mere existence of chemicals in the
 workplace – or even in the workplace
atmosphere – does not necessary imply
 that the chemicals are being delivered
       to a sensitive organ system.
The effective dose will depend upon such
things as particle sizes of dusts in the air,
the use of protective devices (respirators,
 protective clothing), and the existence of
   other contaminants in the workplace.
The task of determining the dose delivered
 to the worker may be complicated by the
     existence of multiple pathways of
        absorption and metabolism.
Such contaminants as lead are absorbed
   readily both through inhalation and
 ingestion, and both routes of intake must
be considered in evaluation of the potential
                  for harm.
   Similarly, many solvents are readily
  absorbed through the skin, and mere
 determination of airborne levels is not
   sufficient to determine the complete
      range of potential exposures.
Inhalation of airborne contaminants is the
      major route of entry for systemic
intoxicants. Thus, evaluation and control of
 airborne contaminants is an important part
     of any occupational health program.
    Sampling and analysis of airborne
contaminants is the definite function of the
    industrial hygienist. The methods for
      sampling and analysis of airborne
 contaminants have been already discussed.
Evaluation of physical agents
requires specialized equipment that
   is often not routinely available
  (except for sound level meters).

  Evaluation of ionizing or non-
   ionizing radiation requires
      specialized training.
3).Control of health hazards
Upon completion of evaluation, the industrial
   hygienist should recommend appropriate
              controls, if needed.
 Recommendations should take into account
  not only the conditions found during the
survey but also those that may be expected
 to prevail in the future. Controls should be
  adequate to prevent unnecessary exposure
during accidents and emergencies as well as
         during normal conditions.
Engineering controls
    Engineering controls to toxic
    exposures consist mainly of:

    - enclosure – building structures
     around the sources of emissions
- isolation – placing hazardous process
    components in areas with limited
           human contact and
           - VENTILATION
Local exhaust ventilation confirms to the
 principle that control should be implemented
as near to the source as practically possible.


Thus, application of a local exhaust inlet on
 a specific tool (such as grinder) would be
more desirable than performing the grinding
operation in a ventilated hood, which in turn
  would be more desirable than installing
 general ventilation in the room where the
           grinding is performed.
In a situation where a very toxic substance
is being manipulated in such a way that the
    exposure is possible, all 3 ventilation
   systems might be reasonable to use.
 Thus, the operator would be protected by
 the ventilation of the specific tool, nearby
workers (as well as the operator) would be
 protected by the hood and the reminder of
   the building would be protected by the
        general ventilation system.
Design of ventilation systems for
contamination control should ordinarily
   not to be left to engineers without
  specific background or experience.

Similarly, an industrial hygienist without
 engineering training and experience in
the process to be controlled may produce
        an unsatisfactory design.
 Substitution

 All possibilities for substitution of a nontoxic
     for a toxic material or agent should be
                    explored.
 If a toxic material can be dispersed with a
      less harmful, that should be done.
Substitution can be done, of course, if a useful
 substitute is available – one that is suitable
for existing processes or for which the process
        can be relatively easily adapted.
 Controls on human behavior –
   these can be subdivided into the
 general categories of administrative c
  ontrols and work practice controls.

   - Administrative controls – includes
 such things as establishment of prohibited
 areas, areas where smoking and eating are
   either prohibited or allowed, and safe
 pathways through the work environment.
Administrative controls will also include
 work scheduling in such a way that
 dangerous operations are carried out
  when fewest workers are present.

    Less desirable is the practice of
   scheduling individual workers to
perform tasks for short periods, where
    excessive exposures would be
              incurred.
This practice was at one time common in
nuclear power industry, where temporary
 employees (“jumpers”) were employed
and paid by the day, although their actual
work period may have been as short as 15
minutes. Such practices, where exposure
  to carcinogenic or genotoxic agent is
 spread across a larger population group
although individual exposures are lower,
        is entirely unacceptable.
- Work practices control – implies
 control over the behavior of individual
           workers on the job.

Such details as handling of contaminated
           tools are included.
Education (on the hazards to be avoided)
 and training (on the desired practices)
              are required.
Controls on work practices are
    particularly important where
engineering controls are either not
adequate or not possible and where
  there is significant potential for
       generation of airborne
contaminants outside of controlled
               places.
 Personal protection
  Personal protective equipment use,
though often essential, is less desirable
 than other approaches because of the
  difficulty in ensuring that it is both
           used and effective.
  Examples on construction sites are
    “hard hats” and “safety shoes”.
In laboratory environments, the use
 of protective eyewear is common,
as is the use of protective garments,
       such as laboratory coats.
   However, there are significant
  complexities in both design and
 function of the protective devices
      used to reduce exposures.

Industrial hygiene № 28

  • 1.
    INDUSTRIAL HYGIENE The3 definite elements in industrial hygiene are the recognition, evaluation and control of occupational health hazards. The recognition of health hazards has primacy, since it must take place before proper evaluation or (if needed) control can take place. Upon recognition of a health hazard, the industrial hygienist should be able to identify measures necessary for proper evaluation.
  • 2.
    Upon completion ofthe evaluation, the industrial hygienist then is in a position – in consultation with other members of the occupational health safety team – to recommend controls needed to reduce exposures to tolerable limits. -1). Recognition of health hazards in the workplace This is the first step in the process leading to evaluation and control and entails the identification of materials and processes that have the potential for causing harm to workers.
  • 3.
    Sources of informationabout health hazards include clinical data about health problems in exposed populations; information in scientific journals and reports of government agencies; direct reports from workers, union representatives, supervisors, or employers.
  • 4.
    Inspection of theworkplace is the best source of directly relevant data about health hazards. There is no substitute for observation of work practices, use of chemical and physical agents, and apparent effectiveness of control measures. The physician should be able to recognize major and obvious health hazards and distinguish those that require formal evaluation by the industrial hygienist.
  • 5.
    The “walk throughsurvey” in the company of the occupational health physician is the first and most important technique for recognition of occupational health hazards. The survey should begin with a proper introduction to plant management and discussion of the purpose of the survey and inquiry about any relevant recent complains.
  • 6.
    Following the processflow through the plant is most productive. The survey might thus begin at the loading dock, where materials entering the plant can be examined. Warning labels, descriptive language about the chemical composition of materials, and the packing of the incoming materials should be noted.
  • 7.
    Questions should thenbe asked regarding the handling of unknown materials or materials about which insufficient information is available. The incoming materials should then be followed into the process flow stream, and each of the process of interest in the plant should be observed in action.
  • 8.
    Of interest throughoutthe survey will be the methods used for material handling, particularly at the places where they are transferred from manufacturers’ containers into vessels for use within the plant.
  • 9.
    Observations to bemade. At each point in the process, the industrial hygienist should observe handling procedures as well as any protective measures that are employed. Use of respiratory protection and protective clothing should be recorded, as well as other common sense observations such as the apparent effectiveness of engineering controls – as indicated by absence of characteristic odors, visible dust accumulations, and loud noise.
  • 10.
    The survey shouldcontinue through to the final product produced by the plant and its packing. The industrial hygienist should also follow the pathway of any waste materials and determine their disposal sites.
  • 11.
    The number ofemployees at each step should be noted, as well as any relevant data on gender, ethnicity, or age that might affect employees’ sensitivity to chemicals in the workplace. It is also important to look for obvious stigmas such as drying of skin, as might expected where exposure to solvents occurs.
  • 12.
    Data review. Important partof the industrial hygienist’s role in recognition of health hazards in the workplace will be data review. Such data may include reports from physicians on clinical findings that may be related to exposures in the workplace as well as a review of company records on materials coming into the workplace that may present significant hazards.
  • 13.
    A common-sense dutyof the employer is to inform workers of the nature and hazards of materials to which they may be exposed. In some cases, the industrial hygienist must assess the potential for harm of chemicals for which no reliable human toxicological data are available. This need arises most often in research and development settings but also wherever chemical intermediates are produced.
  • 14.
    An important considerationis that the worker must be protected at all cost. If uncertainty exists, it should be resolved in favor of highest standard of concern. Upon competition of the walk-through survey, the industrial hygienist will ordinary have a closing conference with the plant management, at which time obvious concerns can be discussed and follow-up measures agreed upon.
  • 15.
    2).Evaluation of healthhazards Evaluation of health hazards within the plant will include measurements of exposures, comparison of those exposures to existing standards, and recommendations of controls, if needed.
  • 16.
    Exposure measurements. They areintended to be determinations of doses delivered to the individual. The mere existence of chemicals in the workplace – or even in the workplace atmosphere – does not necessary imply that the chemicals are being delivered to a sensitive organ system.
  • 17.
    The effective dosewill depend upon such things as particle sizes of dusts in the air, the use of protective devices (respirators, protective clothing), and the existence of other contaminants in the workplace. The task of determining the dose delivered to the worker may be complicated by the existence of multiple pathways of absorption and metabolism.
  • 18.
    Such contaminants aslead are absorbed readily both through inhalation and ingestion, and both routes of intake must be considered in evaluation of the potential for harm. Similarly, many solvents are readily absorbed through the skin, and mere determination of airborne levels is not sufficient to determine the complete range of potential exposures.
  • 19.
    Inhalation of airbornecontaminants is the major route of entry for systemic intoxicants. Thus, evaluation and control of airborne contaminants is an important part of any occupational health program. Sampling and analysis of airborne contaminants is the definite function of the industrial hygienist. The methods for sampling and analysis of airborne contaminants have been already discussed.
  • 20.
    Evaluation of physicalagents requires specialized equipment that is often not routinely available (except for sound level meters). Evaluation of ionizing or non- ionizing radiation requires specialized training.
  • 21.
    3).Control of healthhazards Upon completion of evaluation, the industrial hygienist should recommend appropriate controls, if needed. Recommendations should take into account not only the conditions found during the survey but also those that may be expected to prevail in the future. Controls should be adequate to prevent unnecessary exposure during accidents and emergencies as well as during normal conditions.
  • 22.
    Engineering controls Engineering controls to toxic exposures consist mainly of: - enclosure – building structures around the sources of emissions - isolation – placing hazardous process components in areas with limited human contact and - VENTILATION
  • 23.
    Local exhaust ventilationconfirms to the principle that control should be implemented as near to the source as practically possible. Thus, application of a local exhaust inlet on a specific tool (such as grinder) would be more desirable than performing the grinding operation in a ventilated hood, which in turn would be more desirable than installing general ventilation in the room where the grinding is performed.
  • 24.
    In a situationwhere a very toxic substance is being manipulated in such a way that the exposure is possible, all 3 ventilation systems might be reasonable to use. Thus, the operator would be protected by the ventilation of the specific tool, nearby workers (as well as the operator) would be protected by the hood and the reminder of the building would be protected by the general ventilation system.
  • 25.
    Design of ventilationsystems for contamination control should ordinarily not to be left to engineers without specific background or experience. Similarly, an industrial hygienist without engineering training and experience in the process to be controlled may produce an unsatisfactory design.
  • 26.
     Substitution Allpossibilities for substitution of a nontoxic for a toxic material or agent should be explored. If a toxic material can be dispersed with a less harmful, that should be done. Substitution can be done, of course, if a useful substitute is available – one that is suitable for existing processes or for which the process can be relatively easily adapted.
  • 27.
     Controls onhuman behavior – these can be subdivided into the general categories of administrative c ontrols and work practice controls. - Administrative controls – includes such things as establishment of prohibited areas, areas where smoking and eating are either prohibited or allowed, and safe pathways through the work environment.
  • 28.
    Administrative controls willalso include work scheduling in such a way that dangerous operations are carried out when fewest workers are present. Less desirable is the practice of scheduling individual workers to perform tasks for short periods, where excessive exposures would be incurred.
  • 29.
    This practice wasat one time common in nuclear power industry, where temporary employees (“jumpers”) were employed and paid by the day, although their actual work period may have been as short as 15 minutes. Such practices, where exposure to carcinogenic or genotoxic agent is spread across a larger population group although individual exposures are lower, is entirely unacceptable.
  • 30.
    - Work practicescontrol – implies control over the behavior of individual workers on the job. Such details as handling of contaminated tools are included. Education (on the hazards to be avoided) and training (on the desired practices) are required.
  • 31.
    Controls on workpractices are particularly important where engineering controls are either not adequate or not possible and where there is significant potential for generation of airborne contaminants outside of controlled places.
  • 32.
     Personal protection Personal protective equipment use, though often essential, is less desirable than other approaches because of the difficulty in ensuring that it is both used and effective. Examples on construction sites are “hard hats” and “safety shoes”.
  • 33.
    In laboratory environments,the use of protective eyewear is common, as is the use of protective garments, such as laboratory coats. However, there are significant complexities in both design and function of the protective devices used to reduce exposures.