A formal Environmental Management System (EMS), using the International Organization for Standardization (ISO) standard 14001 as the performance specification, has been developed and is being implemented in one of the largest teaching health care complexes in Canada. The Health Sciences Centre (HSC) consists of five hospitals and associated clinical and research laboratories, occupying a 32-acre site in central Winnipeg. Of the 32 segregated solid waste streams at the facility, hazardous wastes account for seven. This summary focuses on the hazardous waste disposal aspect of the hospital’s operations.

ISO 14000

The ISO 14000 standards system is a typical continuous improvement model based on a controlled management system. The ISO 14001 standard addresses the environmental management system structure exclusively. To conform with the standard, an organization must have processes in place for:

  • adopting an environmental policy that sets environmental protection as a high priority
  • identifying environmental impacts and setting performance goals
  • identifying and complying with legal requirements
  • assigning environmental accountability and responsibility throughout the organization
  • applying controls to achieve performance goals and legal requirements
  • monitoring and reporting environmental performance; auditing the EMS system
  • conducting management reviews/ identifying opportunities for improvement.

 

The hierarchy for carrying out these processes in the HSC is presented in table 1.

Table 1. HSC EMS documentation hierarchy

EMS level

Purpose

Governance document
Mission/strategic plan

Includes the Board’s expectations on each core performance category and its requirements for corporate competency in each category.

Level 1
Output requirements   

Prescribes the outputs that will be delivered in response to customer and stakeholder (C/S) needs (including government regulatory requirements).

Level 2
Corporate policy

Prescribes the methodologies, systems, processes and resources to be used for achieving C/S requirements; the goals, objectives and performance standards essential for confirming that the C/S requirements have been met (e.g., a schedule of required systems and processes including responsibility centre for each).

Level 3
System descriptions

Prescribes the design of each business system or process that will be operated to achieve the C/S requirements (e.g., criteria and boundaries for system operation; each information collection and data reporting point; position responsible for the system and for each component of the process, etc.).

Level 4
Work instructions

Prescribes detailed task instructions (specific methods and techniques), for each work activity (e.g., describe the task to be done; identify the position responsible for completing the task; state skills required for the task; prescribe education or training methodology to achieve required skills; identify task completion and conformance data, etc.).

Level 5
Records of work and  process compliance

Organizes and records measurable outcome data on the operation of systems, processes and tasks designed to verify completion according to specification. (e.g., measures for system or process compliance; resource allocation and budget compliance; effectiveness, efficiency, quality, risk, ethics, etc.).

Level 6
Performance reports 

Analyses records and processes to establish corporate performance in relation to standards set for each output requirement (Level 1) related to C/S needs (e.g., compliance, quality, effectiveness, risk, utilization, etc.); and financial and staff resources.

 

ISO standards encourage businesses to integrate all environmental considerations into mainstream business decisions and not restrict attention to concerns that are regulated. Since the ISO standards are not technical documents, the function of specifying numerical standards remains the responsibility of governments or independent expert bodies.

Management System Approach

Applying the generic ISO framework in a health care facility requires the adoption of management systems along the lines of those in table 1, which describes how this has been addressed by the HSC. Each level in the system is supported by appropriate documentation to confirm diligence in the process. While the volume of work is substantial, it is compensated by the resulting performance consistency and by the “expert” information that remains within the corporation when experienced persons leave.

The main objective of the EMS is to establish consistent, controlled and repeatable processes for addressing the environmental aspects of the corporation’s operations. To facilitate management review of the hospital’s performance, an EMS Score Card was conceived based on the ISO 14001 standard. The Score Card closely follows the requirements in the ISO 14001 standard and, with use, will be developed into the hospital’s audit protocol.

Application of the EMS to the Hazardous Waste Process

Facility hazardous waste process

The HSC hazardous waste process currently consists of the following elements:

  • procedure statement assigning responsibilities
  • process description, in both text and flowchart formats
  • Disposal Guide for Hazardous Waste for staff
  • education programme for staff
  • performance tracking system
  • continuous improvement through multidisciplinary team process
  • a process for seeking external partners.

 

The roles and responsibilities of the four main organizational units involved in the hazardous waste process are listed in table 2.

Table 2. Role and responsibilities

Organizational unit

Responsibility

S&DS
Supply and Distribution
Services

Operates the process and is the process owner/leader, and arranges responsible disposal of waste.

UD–User Departments
the source of waste materials

Identifies waste, selects packaging, initiates disposal activities.

DOEM
Department of Occupational and
Environmental Medicine

Provides specialist technical support in identifying risks and protective measures associated with materials used by HSC and identifies improvement opportunities.

EPE
Environmental Protection
Engineer

Provides specialist support in process performance monitoring and reporting, identifies emerging regulatory trends and compliance requirements, and identifies improvement opportunities.

ALL–All participants

Shares responsibility for process development activities.

 Process description

The initial step in preparing a process description is to identify the inputs (see table 3 ).

Table 3. Process inputs

Organizational unit

Examples of process inputs and supporting inputs

S&DS (S&DS)

Maintain stock of Hazardous Waste Disposal Requisition forms and labels
— order requisition forms and labels.

S&DS (UD, DOEM, EPE) (S&DS)

Maintain supply of packaging containers in warehouse for UDs
— determine appropriate packaging for each waste class
— build adequate stock of containers for requisitioning by UD.

DOEM

Produce SYMBAS Classification Decision Chart.

EPE

Produce the list of materials for which HSC is registered as a waste generator with regulatory department.

S&DS

Produce a database of SYMBAS classifications, packaging requirements, TDG classifications, and tracking information for each material disposed by HSC.

The next process component is the list of specific activities required for proper disposal of waste (see table 4 ).

Table 4. List of activities

Unit

Examples of activities required

UD

Order Hazardous Waste Disposal Requisition, label and packaging from S&DS as per standard stock ordering procedure.

S&DS     

Deliver Requisition, label and packaging to UD.

UD

Determine whether a waste material is hazardous (check MSDS, DOEM, and such considerations as dilution, mixture with other chemicals, etc.).

UD

Assign the Classification to the waste material using SYMBAS Chemical Decision Chart and WHMIS information. Classification can be checked with the S&DS Data Base for materials previously disposed by HSC. Call first S&DS and second DOEM for assistance if required.

UD

Determine appropriate packaging requirements from WHMIS information using professional judgement or from S&DS Data Base of materials previously disposed by HSC. Call first S&DS and second DOEM for assistance if required.

 

Communication

To support the process description, the hospital produced a Disposal Guide for Hazardous Waste to assist staff in the proper disposal of hazardous waste materials. The guide contains information on the specific steps to follow in identifying hazardous waste and preparing it for disposal. Supplemental information is also provided on legislation, the Workplace Hazardous Materials Information System (WHMIS) and key contacts for assistance.

A database was developed to track all relevant information pertaining to each hazardous waste event from originating source to final disposal. In addition to waste data, information is also collected on the performance of the process (e.g., source and frequency of phone calls for assistance to identify areas which may require further training; source, type, quantity and frequency of disposal requests from each user department; consumption of containers and packaging). Any deviations from the process are recorded on the corporate incident reporting form. Results from performance monitoring are reported to the executive and the board of directors. To support effective implementation of the process, a staff education programme was developed to elaborate on the information in the guide. Each of the core participants in the process carries specific responsibilities on staff education.

Continuous Improvement

To explore continuous improvement opportunities, the HSC established a multidisciplinary Waste Process Improvement Team. The Team’s mandate is to address all issues pertaining to waste management. Further to encourage continuous improvement, the hazardous waste process includes specific triggers to initiate process revisions. Typical improvement ideas generated to date include:

  • prepare list of high hazard materials to be tracked from time of procurement
  • develop material “shelf life” information, where appropriate, for inclusion in the materials classification database
  • review shelving for physical integrity
  • purchase spill containing trays
  • examine potential for spills entering sewer system
  • determine whether present storage rooms are adequate for anticipated waste volume
  • produce a procedure for disposing of old, incorrectly identified materials.

 

The ISO standards require regulatory issues to be addressed and state that business processes must be in place for this purpose. Under the ISO standards, the existence of corporate commitments, performance measuring and documentation provide a more visible and more convenient trail for regulators to check for compliance. It is conceivable that the opportunity for consistency provided by the ISO documents could automate reporting of key environmental performance factors to government authorities.

 

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Wednesday, 02 March 2011 16:38

Hospital Waste Management

An adaptation of current guidelines on the disposal of hospital wastes, as well as improvements in internal safety and hygiene, must be part of an overall plan of hospital waste management that establishes the procedures to follow. This should be done through properly coordinating internal and external services, as well as defining responsibilities in each of the management phases. The main goal of this plan is to protect the health of health care personnel, patients, visitors and the general public both in the hospital and beyond.

At the same time, the health of the people who come in contact with the waste once it leaves the medical centre should not be overlooked, and the risks to them should also be minimized.

Such a plan should be campaigned for and applied according to a global strategy that always keeps in mind the realities of the workplace, as well as the knowledge and the training of the personnel involved.

Stages followed in the implementation of a waste management plan are:

  • informing the management of the medical centre
  • designating those responsible at the executive level
  • creating a committee on hospital wastes made up of personnel from the general services, nursing and medical departments that is chaired by the medical centre’s waste manager.

 

The group should include personnel from the general services department, personnel from the nursing department and personnel from the medical department. The medical centre’s waste manager should coordinate the committee by:

  • putting together a report on the present performance of the centre’s waste management
  • putting together an internal plan for advanced management
  • creating a training programme for the entire staff of the medical centre, with the collaboration of the human resources department
  • launching the plan, with follow-up and control by the waste management committee.

 

Classification of hospital wastes

Until 1992, following the classical waste management system, the practice was to classify most hospital wastes as hazardous. Since then, applying an advanced management technique, only a very small proportion of the large volume of these wastes is considered hazardous.

The tendency has been to adopt an advanced management technique. This technique classifies wastes starting from the baseline assumption that only a very small percentage of the volume of wastes generated is hazardous.

Wastes should always be classified at the point where they are generated. According to the nature of the wastes and their source, they are classified as follows:

  • Group I: those wastes that can be assimilated into urban refuse
  • Group II: non-specific hospital wastes
  • Group III: specific hospital wastes or hazardous wastes
  • Group IV: cytostatic wastes (surplus antineoplastic drugs that are not fit for therapeutic use, as well as the single-use materials that have been in contact with them, e.g., needles, syringes, catheters, gloves and IV set-ups).

 

According to their physical state, wastes can be classified as follows:

  • solids: wastes that contain less than 10% liquid
  • liquids: wastes that contain more than 10% liquid

 

Gaseous wastes, such as CFCs from freezers and refrigerators, are not normally captured (see article “Waste anaesthetic gases”).

By definition, the following wastes are not considered sanitary wastes:

  • radioactive wastes that, because of their very nature, are already managed in a specific way by the radiological protection service
  • human cadavers and large anatomical parts which are cremated or incinerated according to regulations
  • waste water.

 

Group I Wastes

All wastes generated within the medical centre that are not directly related to sanitary activities are considered solid urban wastes (SUW). According to the local ordinances in Cataluna, Spain, as in most communities, the municipalities must remove these wastes selectively, and it is therefore convenient to facilitate this task for them. The following are considered wastes that can be assimilated to urban refuse according to their point of origin:

Kitchen wastes:

  • food wastes
  • wastes from leftovers or single-use items
  • containers.

 

Wastes generated by people treated in the hospital and non-medical personnel:

  • wastes from cleaning products
  • wastes left behind in the rooms (e.g., newspapers, magazines and flowers)
  • wastes from gardening and renovations.

 

Wastes from administrative activities:

  • paper and cardboard
  • plastics.

 

Other wastes:

  • glass containers
  • plastic containers
  • packing cartons and other packaging materials
  • dated single-use items.

 

So long as they are not included on other selective removal plans, SUW will be placed in white polyethylene bags that will be removed by janitorial personnel.

Group II Wastes

Group II wastes include all those wastes generated as a by-product of medical activities that do not pose a risk to health or the environment. For reasons of safety and industrial hygiene the type of internal management recommended for this group is different from that recommended for Group I wastes. Depending on where they originate, Group II wastes include:

Wastes derived from hospital activities, such as:

  • blood-stained materials
  • gauze and materials used in treating non-infectious patients
  • used medical equipment
  • mattresses
  • dead animals or parts thereof, from rearing stables or experimental laboratories, so long as they have not been inoculated with infectious agents.

 

Group II wastes will be deposited in yellow polyethylene bags that will be removed by janitorial personnel.

Group III Wastes

Group III includes hospital wastes which, due to their nature or their point of origin, could pose risks to health or the environment if several special precautions are not observed during handling and removal.

Group III wastes can be classified in the following way:

Sharp and pointed instruments:

  • needles
  • scalpels.

 

Infectious wastes. Group III wastes (including single-use items) generated by the diagnosis and treatment of patients who suffer from one of the infectious diseases are listed in table 1.

Table 1. Infectious diseases and Group III wastes

Infections

Wastes contaminated with

Viral haemorrhagic fevers
Congo-Crimean fever
Lassa fever
Marburg virus
Ebola
Junin fever
Machupo fever
Arbovirus
Absettarow
Hanzalova
Hypr
Kumlinge
Kiasanur Forest Disease
Omsk fever
Russian spring-summer
encephalitis

All wastes

Brucellosis

Pus

Diphtheria

Pharyngeal diphtheria: respiratory secretions
Cutaneous diphtheria: secretions from skin
lesions

Cholera

Stools

Creutzfelt-Jakob encephalitis

Stools

Borm

Secretions from skin lesions

Tularaemia

Pulmonary tularaemia: respiratory secretions
Cutaneous tularaemia: pus

Anthrax

Cutaneous anthrax: pus
Respiratory anthrax: respiratory secretions

Plague

Bubonic plague: pus
Pneumonic plague: respiratory secretions

Rabies

Respiratory secretions

Q Fever

Respiratory secretions

Active tuberculosis

Respiratory secretions

 

Laboratory wastes:

  • material contaminated with biological wastes
  • waste from work with animals inoculated with biohazardous substances.

 

Wastes of the Group III type will be placed in single-use, rigid, colour-coded polyethylene containers and hermetically sealed (in Cataluna, black containers are required). The containers should be clearly labelled as “Hazardous hospital wastes” and kept in the room until collected by janitorial personnel. Group III wastes should never be compacted.

To facilitate their removal and reduce risks to a minimum, containers should not be filled to capacity so that they can be closed easily. Wastes should never be handled once they are placed in these rigid containers. It is forbidden to dispose of biohazardous wastes by dumping them into the drainage system.

Group IV Wastes

Group IV wastes are surplus antineoplastic drugs that are not fit for therapeutic use, as well as all single-use material that has been in contact with the same (needles, syringes, catheters, gloves, IV set-ups and so on).

Given the danger they pose to persons and the environment, Group IV hospital wastes must be collected in rigid, watertight, sealable single-use, colour-coded containers (in Cataluna, they are blue) which should be clearly labelled “Chemically contaminated material: Cytostatic agents”.

Other Wastes

Guided by environmental concerns and the need to enhance waste management for the community, medical centres, with the cooperation of all personnel, staff and visitors, should encourage and facilitate the selective disposal (i.e., in special containers designated for specific materials) of recyclable materials such as:

  • paper and cardboard
  • glass
  • used oils
  • batteries and power cells
  • toner cartridges for laser printers
  • plastic containers.

 

The protocol established by the local sanitation department for the collection, transport and disposal of each of these types of materials should be followed.

Disposal of large pieces of equipment, furniture and other materials not covered in these guidelines should follow the directions recommended by the appropriate environmental authorities.

Internal transport and storage of wastes

Internal transport of all the wastes generated within the hospital building should be done by the janitorial personnel, according to established schedules. It is important that the following recommendations be observed when transporting wastes within the hospital:

  • The containers and the bags will always be closed during transport.
  • The carts used for this purpose will have smooth surfaces and be easy to clean.
  • The carts will be used exclusively for transporting waste.
  • The carts will be washed daily with water, soap and lye.
  • The waste bags or containers should never be dragged on the floor.
  • Waste should never be transferred from one receptacle to another.

 

The hospital must have an area specifically for the storage of wastes; it should conform to current guidelines and fulfil, in particular, the following conditions:

  • It should be covered.
  • It should be clearly marked by signs.
  • It should be built with smooth surfaces that are easy to clean.
  • It should have running water.
  • It should have drains to remove the possible spillage of waste liquids and the water used for cleaning the storage area.
  • It should be provided with a system to protect it against animal pests.
  • It should be located far away from windows and from the intake ducts of the ventilation system.
  • It should be provided with fire extinguishing systems.
  • It should have restricted access.
  • It should be used exclusively for the storage of wastes.

 

All the transport and storage operations that involve hospital wastes must be conducted under conditions of maximum safety and hygiene. In particular, one must remember:

  • Direct contact with the wastes must be avoided.
  • Bags should not be overfilled so that they may be closed easily.
  • Bags should not be emptied into other bags.

 

Liquid Wastes: Biological and Chemical

Liquid wastes can be classified as biological or chemical.

Liquid biological wastes

Liquid biological wastes can usually be poured directly into the hospital’s drainage system since they do not require any treatment before disposal. The exceptions are the liquid wastes of patients with infectious diseases and the liquid cultures of microbiology laboratories. These should be collected in specific containers and treated before being dumped.

It is important that the waste be dumped directly into the drainage system with no splashing or spraying. If this is not possible and wastes are gathered in disposable containers that are difficult to open, the containers should not be forced open. Instead, the entire container should be disposed of, as with Group III solid wastes. When liquid waste is eliminated like Group III solid waste, it should be taken into consideration that the conditions of work differ for the disinfection of solid and liquid wastes. This must be kept in mind in order to ensure the effectiveness of the treatment.

Liquid chemical wastes

Liquid wastes generated in the hospital (generally in the laboratories) can be classified in three groups:

  • liquid wastes that should not be dumped into the drains
  • liquid wastes that can be dumped into the drains after being treated
  • liquid wastes that can be dumped into the drains without being previously treated.

 

This classification is based on considerations related to the health and quality of life of the entire community. These include:

  • protection of the water supply
  • protection of the sewer system
  • protection of the waste water purification stations.

 

Liquid wastes that can pose a serious threat to people or to the environment because they are toxic, noxious, flammable, corrosive or carcinogenic should be separated and collected so that they can subsequently be recovered or destroyed. They should be collected as follows:

  • Each type of liquid waste should go into a separate container.
  • The container should be labelled with the name of the product or the major component of the waste, by volume.
  • Each laboratory, except the pathological anatomy laboratory, should provide its own individual receptacles to collect liquid wastes that are correctly labelled with the material or family of materials it contains. Periodically (at the end of each work day would be most desirable), these should be emptied into specifically labelled containers which are held in the room until collected at appropriate intervals by the assigned waste removal subcontractor.
  • Once each receptacle is correctly labelled with the product or the family of products it contains, it should be placed in specific containers in the labs.
  • The person responsible for the laboratory, or someone directly delegated by that person, will sign and stamp a control ticket. The subcontractor will then be responsible for delivering the control ticket to the department that supervises safety, hygiene and the environment.

 

Mixtures of chemical and biological liquid wastes

Treatment of chemical wastes is more aggressive than treatment of biological wastes. Mixtures of these two wastes should be treated using the steps indicated for liquid chemical wastes. Labels on containers should note the presence of biological wastes.

Any liquid or solid materials that are carcinogenic, mutagenic or teratogenic should be disposed of in rigid colour-coded containers specifically designed and labelled for this type of waste.

Dead animals that have been inoculated with biohazardous substances will be disposed of in closed rigid containers, which will be sterilized before being reused.

Disposal of Sharp and Pointed Instruments

Sharp and pointed instruments (e.g., needles and lancets), once used, must be placed in specifically designed, rigid “sharps” containers that have been strategically placed throughout the hospital. These wastes will be disposed of as hazardous wastes even if used on uninfected patients. They must never be disposed of except in the rigid sharps container.

All HCWs must be repeatedly reminded of the danger of accidental cuts or punctures with this type of material, and instructed to report them when they occur, so that appropriate preventive measures may be instituted. They should be specifically instructed not to attempt to recap used hypodermic needles before dropping them into the sharps container.

Whenever possible, needles to be placed in the sharps container without recapping may be separated from the syringes which, without the needle, can generally be disposed of as Group II waste. Many sharps containers have a special fitting for separating the syringe without risk of a needlestick to the worker; this saves space in the sharps containers for more needles. The sharps containers, which should never be opened by hospital personnel, should be removed by designated janitorial personnel and forwarded for appropriate disposal of their contents.

If it is not possible to separate the needle in adequately safe conditions, the whole needle-syringe combination must be considered as biohazardous and must be placed in the rigid sharps containers.

These sharps containers will be removed by the janitorial personnel.

Staff Training

There must be an ongoing training programme in waste management for all hospital personnel aimed at indoctrinating the staff on all levels with the imperative of always following the established guidelines for collecting, storing and disposing wastes of all kinds. It is particularly important that the housekeeping and janitorial staffs be trained in the details of the protocols for recognizing and dealing with the various categories of hazardous waste. The janitorial, security and fire-fighting staff must also be drilled in the correct course of action in the event of an emergency.

It is also important for the janitorial personnel to be informed and trained on the correct course of action in case of an accident.

Particularly when the programme is first launched, the janitorial staff should be instructed to report any problems that may hinder their performance of these assigned duties. They may be given special cards or forms on which to record such findings.

Waste Management Committee

To monitor the performance of the waste management programme and resolve any problems that may arise as it is implemented, a permanent waste management committee should be created and meet regularly, quarterly at a minimum. The committee should be accessible to any member of the hospital staff with a waste disposal problem or concern and should have access as needed to top management.

Implementing the Plan

The way the waste management programme is implemented may well determine whether it succeeds or not.

Since the support and cooperation of the various hospital committees and departments is essential, details of the programme should be presented to such groups as the administrative teams of the hospital, the health and safety committee and the infection control committee. It is necessary also to obtain validation of the programme from such community agencies as the departments of health, environmental protection and sanitation. Each of these may have helpful modifications to suggest, particularly with respect to the way the programme impinges on their areas of responsibility.

Once the programme design has been finalized, a pilot test in a selected area or department should permit rough edges to be polished and any unforeseen problems resolved. When this has been completed and its results analysed, the programme may be implemented progressively throughout the entire medical centre. A presentation, with audio-visual supports and distribution of descriptive literature, can be delivered in each unit or department, followed by delivery of bags and/or containers as required. Following the start-up of the programme, the department or unit should be visited so that any needed revisions may be instituted. In this manner, the participation and support of the entire hospital staff, without which the programme would never succeed, can be earned.

 

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A hospital is not an isolated social environment; it has, given its mission, very serious intrinsic social responsibilities. A hospital needs to be integrated with its surroundings and should minimize its impact upon them, thus contributing to the welfare of the people who live near it.

From a regulatory perspective, the health industry has never been considered to be on the same level as other industries when they are ranked according to the health risks they pose. The result is that specific legislation in this sphere has been non-existent until recently, although in the last few years this deficiency has been addressed. While in many other kinds of industrial activities, health and safety is an integral part of the organization, most health centres still pay little or no attention to it.

One reason for this could be the attitudes of HCWs themselves, who may be preoccupied more with research and the acquisition of the latest technologies and diagnostic and treatment techniques than with looking into the effects that these advances could have on their own health and on the environment.

New developments in science and health care must be combined with environmental protection, because environmental policies in a hospital affect the quality of life of HCWs within the hospital and those who live outside it.

Integrated Health, Safety and Environmental Programmes

HCWs represent a major group, comparable in size to the large enterprises of the private sector. The number of people who pass through a hospital every day is very large: visitors, inpatients, outpatients, medical and commercial representatives, subcontractors and so on. All of them, to a greater or lesser degree, are exposed to the potential risks posed by the activities of the medical centre and, at the same time, contribute on a certain level to the improvement or the worsening of the safety and the care of the centre’s surroundings.

Strict measures are needed in order to safeguard HCWs, the general public and the surrounding environment from the deleterious effects that may stem from hospital activities. These activities include the use of ever more sophisticated technology, the more frequent use of extremely powerful drugs (the effects of which can have a profound and irreparable impact on the people who prepare or administer them), the too-often uncontrolled use of chemical products and the incidence of infectious diseases, some of which are incurable.

The risks of working in a hospital are many. Some are easy to identify, while others are very hard to detect; the measures to be taken should therefore always be rigorous.

Different groups of health professionals are particularly exposed to risks common to the health care industry in general, as well as to specific risks related to their profession and/or to the activities they perform in the course of their work.

The concept of prevention, therefore, must of necessity be incorporated to the health care field and encompass:

  • safety in the broadest sense, including psychosociology and ergonomics as part of the programmes to improve the quality of life in the workplace
  • hygiene, minimizing as much as possible any physical, chemical or biological factor that may affect the health of people in the work environment
  • environment, following policies to protect nature and people in the surrounding community and decreasing the impact on the environment.

 

We should be aware that the environment is directly and intimately related to the safety and hygiene in the workplace, because natural resources are consumed at work, and because these resources are later reincorporated into our surroundings. Our quality of life will be good or bad depending on whether we make correct use of these resources and use appropriate technologies.

Everyone’s involvement is necessary in order to contribute to further:

  • nature conservancy policies, designed to guarantee the survival of the natural heritage that surrounds us
  • environmental improvement policies as well as policies to control indoor and environmental pollution in order to integrate human activity with the environment
  • environmental research and training policies to improve working conditions as well as to reduce environmental impact
  • planning organizational policies designed to set goals and develop norms and methodology for workers’ health and the environment.

 

Goals

Such a programme should endeavour to:

  • change the culture and habits of health professionals in order to stimulate behaviour more conducive to safeguarding their health
  • set goals and develop internal safety, hygiene and environmental guidelines through adequate planning and organization
  • improve the methods of work to avoid a negative impact on health and the environment through environmental research and education
  • increase the involvement of all personnel and have them take responsibility for health in the workplace
  • create an adequate programme to establish and publicize the guidelines as well as to monitor their continued implementation
  • correctly classify and manage the waste generated
  • optimize costs, avoiding added expenditures that cannot be justified by the increased levels of safety and health or environmental quality.

 

Plan

A hospital should be conceived as a system that, through a number of processes, generates services. These services are the main goal of the activities performed in a hospital.

For the process to begin, certain commitments of energy, investments and technology are needed, which in turn will generate their own emissions and wastes. Their only aim is to provide service.

In addition to these prerequisites, consideration should be given to the conditions of the areas of the building where these activities will take place, since they have been designed a certain way and built with basic construction materials.

Control, planning and coordination are all necessary for an integrated safety, health and environmental project to succeed.

Methodology

Because of the complexity and the variety of risks in the health care field, multidisciplinary groups are required if solutions to each particular problem are to be found.

It is important for health care workers to be able to collaborate with safety studies, participating in the decisions that will be made to improve their working conditions. This way changes will be seen with a better attitude and the guidelines will be more readily accepted.

The safety, hygiene and environmental service should advise, stimulate and coordinate the programmes developed at the health centre. Responsibility for their implementation should fall upon whoever heads up the service where this programme will be followed. This is the only way to involve the entire organization.

In each particular case, the following will be selected:

  • the system involved
  • the parameters of the study
  • the time needed to carry it out.

 

The study will consist of:

  • an initial diagnosis
  • analysis of the risk
  • deciding on the course of action.

 

In order to implement the plan successfully it will always be necessary to:

  • educate and inform people of the risks
  • improve the management of human resources
  • improve the channels of communication.

 

This type of study may be a global one encompassing the centre as a whole (e.g., internal plan for the disposal of hospital wastes) or partial, encompassing only one concrete area (e.g., where cancer chemotherapeutic drugs are prepared).

The study of these factors will give an idea of the degree to which safety measures are disregarded, as much from the legal as from the scientific point of view. The concept of “legal” here encompasses advances in science and technology as they occur, which requires the constant revision and modification of established norms and guidelines.

It would be convenient indeed if the regulations and the laws by which safety, hygiene and the environment are regulated were the same in all countries, something that would make the installation, management and use of technology or products from other countries much easier.

Results

The following examples show some of the measures that can be taken while following the aforementioned methodology.

Laboratories

An advisory service can be developed involving professionals of the various laboratories and coordinated by the safety and hygiene service of the medical centre. The main goal would be to improve the safety and health of the occupants of all the labs, involving and giving responsibility to the entire professional staff of each and trying at the same time to make sure that these activities do not have a negative impact on public health and the environment.

The measures taken should include:

  • instituting the sharing of materials, products and equipment among the different laboratories, in order to optimize resources
  • reducing the stocks of chemical products in laboratories
  • creating a manual of basic norms of safety and hygiene
  • planning courses to educate all laboratory workers on these matters
  • training for emergencies.

 

Mercury

Thermometers, when broken, release mercury into the environment. A pilot project has been started with “unbreakable” thermometers to consider eventually substituting them for the glass thermometers. In some countries, such as the United States, electronic thermometers have replaced mercury thermometers to a very great extent.

Training the workers

The training and the commitment of the workers is the most important part of an integrated safety, health and environment programme. Given enough resources and time, the technicalities of almost any problem can be solved, but a complete solution will not be achieved without informing the workers of the risks and training them to avoid or control them. The training and education must be continuous, integrating health and safety techniques into all the other training programmes in the hospital.

Conclusions

The results that have been achieved so far in applying this work model allow us so far to be optimistic. They have shown that when people are informed about the whys and wherefores, their attitude toward change is very positive.

The response of health care personnel has been very good. They feel more motivated in their work and more valued when they have participated directly in the study and in the decision-making process. This participation, in turn, helps to educate the individual health care worker and to increase the degree of responsibility he or she is willing to accept.

The attainment of the goals of this project is a long-term objective, but the positive effects it generates more than compensate for the effort and the energy invested in it.

 

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Wednesday, 02 March 2011 16:30

Buildings for Health Care Facilities

The health maintenance and enhancement, the safety and the comfort of people in health care facilities are seriously affected if specific building requirements are not met. Health care facilities are rather unique buildings, in which heterogeneous environments coexist. Different people, several activities in each environment and many risk factors are involved in the pathogenesis of a broad spectrum of diseases. Functional organization criteria classify health care facility environments as follows: nursing units, operating theatres, diagnostic facilities (radiology unit, laboratory units and so on), outpatients’ departments, administration area (offices), dietary facilities, linen services, engineering services and equipment areas, corridors and passages. The group of people which attends a hospital is composed of health personnel, staff personnel, patients (long-stay inpatients, acute inpatients and outpatients) and visitors. The processes include health care specific activities—diagnostic activities, therapeutic activities, nursing activities—and activities common to many public buildings—office work, technological maintenance, food preparation and so on. The risk factors are physical agents (ionizing and non-ionizing radiation, noise, lighting and microclimatic factors), chemicals (e.g., organic solvents and disinfectants), biological agents (viruses, bacteria, fungi and so on), ergonomics (postures, lifting and so on) and psychological and organizational factors (e.g., environmental perceptions and work hours). The illnesses related to the above-mentioned factors range from environmental annoyance or discomfort (e.g., thermal discomfort or irritative symptoms) to severe diseases (e.g., hospital-acquired infections and traumatic accidents). In this perspective, the risk assessment and control require an interdisciplinary approach involving physicians, hygienists, engineers, architects, economists and so on and fulfilment of preventive measures in the building planning, design, construction and management tasks. Specific building requirements are extremely important among these preventive measures, and, according to the guidelines for healthy buildings introduced by Levin (1992), they should be classified as follows:

  • site planning requirements
  • architectural design requirements
  • requirements for building materials and furnishings
  • requirements for heating, ventilation and air-conditioning systems and for microclimatic conditions.

 

This article focuses on general hospital buildings. Obviously, adaptations would be required for specialty hospitals (e.g., orthopaedic centres, eye and ear hospitals, maternity centres, psychiatric institutions, long-term care facilities and rehabilitation institutes), for ambulatory care clinics, emergency/urgent care facilities and offices for individual and group practices. These will be determined by the numbers and types of patients (including their physical and mental status) and by the number of HCWs and the tasks they perform. Considerations promoting the safety and well-being of both patients and staff that are common to all health care facilities include:

  • ambience, including not only decoration, lighting and noise control but also partitioning and placement of furniture and equipment that avoid entrapment of workers with potentially violent patients and visitors
  • ventilation systems that minimize exposure to infectious agents and potentially toxic chemicals and gases
  • storage facilities for clothing and effects of patients and their visitors that minimize potential contamination
  • lockers, changing rooms, wash-up facilities and rest rooms for staff
  • conveniently-located hand-washing facilities in each room and treatment area
  • doorways, elevators and toilets that accommodate wheel chairs and stretchers
  • storage and filing areas designed to minimize workers’ stooping, bending, reaching and heavy lifting
  • automatic and worker-controlled communication and alarm systems
  • mechanisms for collection, storage and disposition of toxic wastes, contaminated linens and clothing and so on.

 

Site Planning Requirements

The health care facility site must be chosen following four main criteria (Catananti and Cambieri 1990; Klein and Platt 1989; Decree of the President of Ministers Council 1986; Commission of the European Communities 1990; NHS 1991a, 1991b):

  1. Environmental factors. The terrain should be as level as possible. Ramps, escalators and elevators can offset sides of hills, but they hinder the access of elderly and handicapped people, adding both a higher cost to the project and an extra burden to fire departments and evacuation teams. Heavy wind sites should be avoided, and the area should be far from sources which create pollution and noise (especially factories and landfills). Radon and radon daughters levels should be assessed, and measures to reduce exposure should be taken. In colder climates, consideration should be given to embedding snow-melting coils in sidewalks, entrance ways and parking areas to minimize falls and other accidents. 
  2. Geological configuration. Earthquake-prone areas should be avoided, or at least anti-seismic construction criteria must be followed. The site must be chosen following an hydrogeological assessment, to avoid water infiltrations into the foundations. 
  3. Urbanistic factors. The site should be easily accessible to potential users, ambulances and service vehicles for goods supply and waste disposal. Public transportation and utilities (water, gas, electricity and sewers) should be available. Fire departments should be nearby, and fire-fighters and their apparatus should find ready access to all parts of the facility. 
  4. Space availability. The site should allow some scope for expansion and provision of adequate car parking.

 

Architectural Design

Health care facilities architectural design usually follows several criteria:

  • class of the health care facility: hospital (acute-care hospital, community hospital, rural hospital), large or small health care centre, nursing homes (extended care facilities, skilled nursing homes, residential care homes), general medical practice premise (NHS 1991a; NHS 1991b; Kleczkowski, Montoya-Aguilar and Nilsson 1985; ASHRAE 1987)
  • catchment area dimensions
  • management issues: costs, flexibility (susceptibility to adaptation)
  • ventilation provided: an air-conditioned building is compact and deep with as small an amount of external walls as possible, to reduce the heat transfer between outside and inside; a naturally ventilated building is long and thin, to maximize exposure to breezes and to minimize internal distances from windows (Llewelyn-Davies and Wecks 1979)
  • building/area ratio
  • environmental quality: safety and comfort are extremely relevant targets.

 

The listed criteria lead health care facilities planners to choose the best building shape for each situation, ranging essentially from an extended horizontal hospital with scattered buildings to a monolithic vertical or horizontal building (Llewelyn-Davies and Wecks 1979). The first case (a preferable format for low-density buildings) is normally used for hospitals up to 300 beds, because of its low costs in construction and management. It is particularly considered for small rural hospitals and community hospitals (Llewelyn-Davies and Wecks 1979). The second case (usually preferred for high-density buildings) becomes cost-effective for hospitals with more than 300 beds, and it is advisable for acute-care hospitals (Llewelyn-Davies and Wecks 1979). The internal space dimensions and distribution have to cope with many variables, among which one can consider: functions, processes, circulation and connections to other areas, equipment, predicted workload, costs, and flexibility, convertibility and susceptibility of shared use. Compartments, exits, fire alarms, automatic extinction systems and other fire prevention and protection measures should follow local regulations. Furthermore, several specific requirements have been defined for each area in health care facilities:

1.       Nursing units. Internal layout of nursing units usually follows one of the following three basic models (Llewelyn-Davies and Wecks 1979): an open ward (or “Nightingale” ward)—a broad room with 20 to 30 beds, heads to the windows, ranged along both walls; the “Rigs” layout—in this model beds were placed parallel to the windows, and, at first, they were in open bays on either side of a central corridor (as at Rigs Hospital in Copenhagen), and in later hospitals the bays were often enclosed, so that they became rooms with 6 to 10 beds; small rooms, with 1 to 4 beds. Four variables should lead the planner to choose the best layout: bed need (if high, an open ward is advisable), budget (if low, an open ward is the cheapest one), privacy needs (if considered high, small rooms are unavoidable) and intensive care level (if high, the open ward or Rigs layout with 6 to 10 beds are advisable). The space requirements should be at least: 6 to 8 square metres (sqm) per bed for open wards, inclusive of circulation and ancillary rooms (Llewelyn-Davies and Wecks 1979); 5 to 7 sqm/bed for multiple bedrooms and 9 sqm for single bedrooms (Decree of the President of Ministers Council 1986; American Institute of Architects Committee on Architecture for Health 1987). In open wards, toilet facilities should be close to patients’ beds (Llewelyn-Davies and Wecks 1979). For single and multiple bedrooms, handwashing facilities should be provided in each room; lavatories may be omitted where a toilet room is provided to serve one single-bed room or one two-bed room (American Institute of Architects Committee on Architecture for Health 1987). Nursing stations should be large enough to accommodate desks and chairs for record keeping, tables and cabinets for preparation of drugs, instruments and supplies, chairs for sit-down conferences with physicians and other staff members, a wash-up sink and access to a staff toilet.

2.       Operating theatres. Two main classes of elements should be considered: operating rooms and service areas (American Institute of Architects Committee on Architecture for Health 1987). Operating rooms should be classified as follows:

  • general operating room, needing a minimum clear area of 33.5 sqm.
  • room for orthopaedic surgery (optional), needing enclosed storage space for splints and traction equipment
  • room for cardiovascular surgery (optional), needing a minimum clear area of 44 sqm. In the clear area of the surgical suite, nearby the operating room, an additional pump room should be designed, where extracorporeal pump supplies and accessories are stored and serviced.
  • room for endoscope procedures, needing a minimum clear area of 23 sqm
  • rooms for waiting patients, induction of anaesthesia and recovery from anaesthesia.

 

Service areas should include: sterilizing facility with high-speed autoclave, scrub facilities, medical gas storage facilities and staff clothing change areas.

3.       Diagnostic facilities: Each radiology unit should include (Llewelyn-Davies and Wecks 1979; American Institute of Architects Committee on Architecture for Health 1987):

  • appointment desk and waiting areas
  • diagnostic radiographic rooms, needing 23 sqm for fluoroscopic procedures and about 16 sqm for radiographic ones, plus a shielded control area, and rigid support structures for ceiling-mounted equipment (where necessary)
  • dark room (where necessary), needing almost 5 sqm and appropriate ventilation for the developer
  • contrast media preparation area, clean-up facilities, film quality control area, computer area and film storage area
  • viewing area where films can be read and reports dictated.

 

The wall thickness in a radiology unit should be 8 to 12 cm (poured concrete) or 12 to 15 cm (cinder block or bricks). The diagnostic activities in health care facilities may require tests in haematology, clinical chemistry, microbiology, pathology and cytology. Each laboratory area should be provided with work areas, sample and material storage facilities (refrigerated or not), specimen collection facilities, facilities and equipment for terminal sterilization and waste disposal, and a special facility for radioactive material storage (where necessary) (American Institute of Architects Committee on Architecture for Health 1987).

4.       Outpatient departments. Clinical facilities should include (American Institute of Architects Committee on Architecture for Health 1987): general-purpose examination rooms (7.4 sqm), special-purpose examination rooms (varying with the specific equipment needed) and treatment rooms (11 sqm). In addition, administrative facilities are needed for the admittance of outpatients.

5.       Administration area (offices). Facilities such as common office building areas are needed. These include a loading dock and storage areas for receiving supplies and equipment and dispatching materials not disposed of by the separate waste removal system.

6.       Dietary facilities (optional). Where present, these should provide the following elements (American Institute of Architects Committee on Architecture for Health 1987): a control station for receiving and controlling food supplies, storage spaces (including cold storage), food preparation facilities, handwashing facilities, facility for assembling and distributing patients’ meals, dining space, dishwashing space (located in a room or an alcove separated from the food preparation and serving area), waste storage facilities and toilets for dietary staff.

7.       Linen services (optional). Where present, these should provide the following elements: a room for receiving and holding soiled linen, a clean-linen storage area, a clean-linen inspection and mending area and handwashing facilities (American Institute of Architects Committee on Architecture for Health 1987).

8.       Engineering services and equipment areas. Adequate areas, varying in size and characteristics for each health care facility, have to be provided for: boiler plant (and fuel storage, if necessary), electrical supply, emergency generator, maintenance workshops and stores, cold-water storage, plant rooms (for centralized or local ventilation) and medical gases (NHS 1991a).

9.       Corridors and passages. These have to be organized to avoid confusion for visitors and disruptions in the work of hospital personnel; circulation of clean and dirty goods should be strictly separated. Minimum corridor width should be 2 m (Decree of the President of Ministers Council 1986). Doorways and elevators must be large enough to allow easy passage of stretchers and wheelchairs.

Requirements for Building Materials and Furnishings

The choice of materials in modern health care facilities is often aimed to reduce the risk in accidents and fire occurrence: materials must be non-inflammable and must not produce noxious gases or smokes when burnt (American Institute of Architects Committee on Architecture for Health 1987). Trends in hospital floor-covering materials have shown a shift from stone materials and linoleum to polyvinyl chloride (PVC). In operating rooms, in particular, PVC is considered the best choice to avoid electrostatic effects that may cause explosion of anaesthetic flammable gases. Up to some years ago, walls were painted; today, PVC coverings and fibreglass wallpaper are the most used wall finishes. False ceilings are today built mainly from mineral fibres instead of gypsum board; a new trend appears to be that of using stainless steel ceilings (Catananti et al. 1993). However, a more complete approach should consider that each material and furnishing may cause effects in the outdoor and indoor environmental systems. Accurately chosen building materials may reduce environmental pollution and high social costs and improve the safety and comfort of building occupants. At the same time, internal materials and finishes may influence the functional performance of the building and its management. Besides, the choice of materials in hospitals should also consider specific criteria, such as ease of cleaning, washing and disinfecting procedures and susceptibility to becoming a habitat for living beings. A more detailed classification of criteria to be considered in this task, derived from the European Community Council Directive No. 89/106 (Council of the European Communities 1988), is shown in table 1 .

Table 1. Criteria and variables to be considered in the choice of materials

Criteria

Variables

Functional performance

Static load, transit load, impact load, durability, construction requirements

Safety

Collapse risk, fire risk (reaction to fire, fire resistance, flammability), static electric charge (explosion risk), disperse electric power (electric shock risk), sharp surface (wound risk), poisoning risk (hazardous chemical emission), slip risk, radioactivity

Comfort and pleasantness

Acoustic comfort (features related to noise), optical and visual comfort (features related to light), tactile comfort (consistence, surface), hygrothermal comfort (features related to heat), aesthetics, odour emissions, indoor air quality perception

Hygienicity

Living beings habitat (insects, moulds, bacteria), susceptibility to stains, susceptibility to dust, easiness in cleaning, washing and disinfecting, maintenance procedures

Flexibility

Susceptibility to modifications, conformational factors (tile or panel dimensions and morphology)

Environmental impact

Raw material, industrial manufacturing, waste management

Cost

Material cost, installation cost, maintenance cost

Source: Catananti et al. 1994.

On the matter of odour emissions, it should be observed that a correct ventilation after floor or wall-coverings installation or renovation work reduces exposure of personnel and patients to indoor pollutants (especially volatile organic compounds (VOCs)) emitted by building materials and furnishings.

Requirements for Heating, Ventilation and Air-Conditioning Systems and for Microclimatic Conditions

The control of microclimatic conditions in health care facilities areas may be carried out by heating, ventilation and/or air-conditioning systems (Catananti and Cambieri 1990). Heating systems (e.g., radiators) permit only temperature regulation and may be sufficient for common nursing units. Ventilation, which induces changes of air speed, may be natural (e.g., by porous building materials), supplementary (by windows) or artificial (by mechanical systems). The artificial ventilation is especially recommended for kitchens, laundries and engineering services. Air-conditioning systems, particularly recommended for some health care facility areas such as operating rooms and intensive-care units, should guarantee:

  • the control of all microclimatic factors (temperature, relative humidity and air speed)
  • the control of air purity and concentration of micro-organisms and chemicals (e.g., anaesthetic gases, volatile solvents, odours and so on). This target may be achieved by adequate air filtration and air changes, right pressure relationships among adjacent areas and laminar airflow.

 

General requirements of air-conditioning systems include outdoor intake locations, air filter features and air supply outlets (ASHRAE 1987). Outdoor intake locations should be far enough, at least 9.1 m, from pollution sources such as exhaust outlets of combustion equipment stacks, medical-surgical vacuum systems, ventilation exhaust outlets from the hospital or adjoining buildings, areas that may collect vehicular exhaust and other noxious fumes, or plumbing vent stacks. Besides, their distance from ground level should be at least 1.8 m. Where these components are installed above the roof, their distance from roof level should be at least 0.9 m.

Number and efficiency of filters should be adequate for the specific areas supplied by air conditioning systems. For example, two filter beds of 25 and 90% efficiency should be used in operating rooms, intensive-care units and transplant organ rooms. Installation and maintenance of filters follow several criteria: lack of leakage between filter segments and between the filter bed and its supporting frame, installation of a manometer in the filter system in order to provide a reading of the pressure so that filters can be identified as expired and provision of adequate facilities for maintenance without introducing contamination into the air flow. Air supply outlets should be located on the ceiling with perimeter or several exhaust inlets near the floor (ASHRAE 1987).

Ventilation rates for health care facility areas permitting air purity and comfort of occupants are listed in table 2 .

Table 2. Ventilation requirements in health care facilities areas

Areas

Pressure relationships to adjacent areas

Minimum air changes of outdoor air per hour supplied to room

Minimum total air changes per hour supplied to room

All air exhausted directly to outdoors

Recirculated within room units

Nursing units

         

Patient room

+/–

2

2

Optional

Optional

Intensive care

P

2

6

Optional

No

Patient corridor

+/–

2

4

Optional

Optional

Operating theatres

         

Operating room (all outdoor system)

P

15

15

Yes1

No

Operating room (recirculating system)

P

5

25

Optional

No2

Diagnostic facilities

         

X ray

+/–

2

6

Optional

Optional

Laboratories

         

Bacteriology

N

2

6

Yes

No

Clinical chemistry

P

2

6

Optional

No

Pathology

N

2

6

Yes

No

Serology

P

2

6

Optional

No

Sterilizing

N

Optional

10

Yes

No

Glasswashing

N

2

10

Yes

Optional

Dietary facilities

         

Food preparation centres3

+/–

2

10

Yes

No

Dishwashing

N

Optional

10

Yes

No

Linen service

         

Laundry (general)

+/–

2

10

Yes

No

Soiled linen sorting and storage

N

Optional

10

Yes

No

Clean linen storage

P

2 (Optional)

2

Optional

Optional

P = Positive. N = Negative. +/– = Continuous directional control not required.

1 For operating rooms, use of 100% outside air should be limited to these cases where local codes require it, only if heat recovery devices are used; 2 recirculating room units meeting the filtering requirement for the space may be used; 3 food preparation centres shall have ventilation systems that have an excess of air supply for positive pressure when hoods are not in operation. The number of air changes may be varied to any extent required for odour control when the space is not in use.

Source: ASHRAE 1987.

Specific requirements of air-conditioning systems and microclimatic conditions regarding several hospital areas are reported as follows (ASHRAE 1987):

Nursing units. In common patient rooms a temperature (T) of 24 °C and a 30% relative humidity (RH) for winter and a T of 24 °C with 50% RH for summer are recommended. In intensive-care units a variable range temperature capability of 24 to 27 °C and a RH of 30% minimum and 60% maximum with a positive air pressure are recommended. In immunosuppressed patient units a positive pressure should be maintained between patient room and adjacent area and HEPA filters should be used.

In full-term nursery a T of 24 °C with RH from 30% minimum to 60% maximum is recommended. The same microclimatic conditions of intensive-care units are required in special-care nursery.

Operating theatres. Variable temperature range capability of 20 to 24 °C with RH of 50% minimum and 60% maximum and positive air pressure are recommended in operating rooms. A separate air-exhaust system or special vacuum system should be provided in order to remove anaesthetic gas traces (see “Waste anaesthetic gases” in this chapter).

Diagnostic facilities. In the radiology unit, fluoroscopic and radiographic rooms require T of 24 to 27 °C and RH of 40 to 50%. Laboratory units should be supplied with adequate hood exhaust systems to remove dangerous fumes, vapours and bioaerosols. The exhaust air from the hoods of the units of clinical chemistry, bacteriology and pathology should be discharged to the outdoors with no recirculation. Also, the exhaust air from infectious disease and virology laboratories requires sterilization before being exhausted to the outdoors.

Dietary facilities. These should be provided with hoods over the cooking equipment for removal of heat, odours and vapours.

Linen services. The sorting room should be maintained at a negative pressure in relation to adjoining areas. In the laundry processing area, washers, flatwork ironers, tumblers, and so on should have direct overhead exhaust to reduce humidity.

Engineering services and equipment areas. At work stations, the ventilation system should limit temperature to 32 °C.

Conclusion

The essence of specific building requirements for health care facilities is the accommodation of external standard-based regulations to subjective index-based guidelines. In fact, subjective indices, such as Predicted Mean Vote (PMV) (Fanger 1973) and olf, a measure of odour (Fanger 1992), are able to make predictions of the comfort levels of patients and personnel without neglecting the differences related to their clothing, metabolism and physical status. Finally, the planners and architects of hospitals should follow the theory of “building ecology” (Levin 1992) which describes dwellings as a complex series of interactions among buildings, their occupants and the environment. Health facilities, accordingly, should be planned and built focusing on the whole “system” rather than any particular partial frames of reference.

 

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Wednesday, 02 March 2011 16:27

Health Care Workers and Latex Allergy

With the advent of the universal precautions against bloodborne infections which dictate the use of gloves whenever HCWs are exposed to patients or materials that might be infected with hepatitis B or HIV, the frequency and severity of allergic reactions to natural rubber latex (NRL) have zoomed upward. For example, the Department of Dermatology at the Erlangen-Nuremberg University in Germany reported a 12-fold increase in the number of patients with latex allergy between 1989 and 1995. More serious systemic manifestations increased from 10.7% in 1989 to 44% in 1994-1995 (Hesse et al. 1996).

It seems ironic that so much difficulty is attributable to rubber gloves when they were intended to protect the hands of nurses and other HCWs when they were originally introduced toward the end of the nineteenth century. This was the era of antiseptic surgery in which instruments and operative sites were bathed in caustic solutions of carbolic acid and bichloride of mercury. These not only killed germs but they also macerated the hands of the surgical team. According to what has become a romantic legend, William Stewart Halsted, one of the surgical “giants” of the time who is credited with a host of contributions to the techniques of surgery, is said to have “invented” rubber gloves around 1890 to make it more pleasant to hold hands with Caroline Hampton, his scrub nurse, whom he later married (Townsend 1994). Although Halsted may be credited with introducing and popularizing the use of rubber surgical gloves in the United States, many others had a hand in it, according to Miller (1982) who cited a report of their use in the United Kingdom published a half century earlier (Acton 1848).

Latex Allergy

Allergy to NRL is succinctly described by Taylor and Leow (see the article “Rubber contact dermatitis and latex allergy” in the chapter Rubber industry) as “an immunoglobulin E-mediated, immediate, Type I allergic reaction, most always due to NRL proteins present in medical and non-medical latex devices. The spectrum of clinical signs ranges from contact urticaria, generalized urticaria, allergic rhinitis, allergic conjunctivitis, angioedema (severe swelling) and asthma (wheezing) to anaphylaxis (severe, life-threatening allergic reaction)”. Symptoms may result from direct contact of normal or inflamed skin with gloves or other latex-containing materials or indirectly by mucosal contact with or inhalation of aerosolized NRL proteins or talcum powder particles to which NRL proteins have adhered. Such indirect contact can cause a Type IV reaction to the rubber accelerators. (Approximately 80% of “latex glove allergy” is actually a Type IV reaction to the accelerators.) The diagnosis is confirmed by patch, prick, scratch or other skin sensitivity tests or by serological studies for the immune globulin. In some individuals, the latex allergy is associated with allergy to certain foods (e.g., banana, chestnuts, avocado, kiwi and papaya).

While most common among health care workers, latex allergy is also found among employees in rubber manufacturing plants, other workers who habitually use rubber gloves (e.g., greenhouse workers (Carillo et al. 1995)) and in patients with a history of multiple surgical procedures (e.g., spina bifida, congenital urogenital abnormalities, etc.) (Blaycock 1995). Cases of allergic reactions after the use of latex condoms have been reported (Jonasson, Holm and Leegard 1993), and in one case, a potential reaction was averted by eliciting a history of an allergic reaction to a rubber swimming cap (Burke, Wilson and McCord 1995). Reactions have occurred in sensitive patients when hypodermic needles used to prepare doses of parenteral medications picked up NRL protein as they were pushed through the rubber caps on the vials.

According to a recent study of 63 patients with NRL allergy, it took an average of 5 years of working with latex products for the first symptoms, usually a contact urticaria, to develop. Some also had rhinitis or dyspnoea. It took, on average, an additional 2 years for the appearance of lower respiratory tract symptoms (Allmeers et al. 1996).

Frequency of latex allergy

To determine the frequency of NRL allergy, allergy tests were performed on 224 employees at the University of Cincinnati College of Medicine, including nurses, laboratory technicians, physicians, respiratory therapists, housekeeping and clerical workers (Yassin et al. 1994). Of these, 38 (17%) tested positive to latex extracts; the incidence ranged from 0% among housekeeping workers to 38% among dental staff. Exposure of these sensitized individuals to latex caused itching in 84%, a skin rash in 68%, urticaria in 55%, lachrymation and ocular itching in 45%, nasal congestion in 39% and sneezing in 34%. Anaphylaxis occurred in 10.5%.

In a similar study at the University of Oulo in Finland, 56% of 534 hospital employees who used protective latex or vinyl gloves on a daily basis had skin disorders related to the usage of the gloves (Kujala and Reilula 1995). Rhinorrhoea or nasal congestion was present in 13% of workers who used powdered gloves. The prevalence of both skin and respiratory symptoms was significantly higher among those who used the gloves for more than 2 hours a day.

Valentino and colleagues (1994) reported latex induced asthma in four health care workers in an Italian regional hospital, and the Mayo Medical Center in Rochester Minnesota, where 342 employees who reported symptoms suggestive of latex allergy were evaluated, recorded 16 episodes of latex-related anaphylaxis in 12 subjects (six episodes occurred after skin testing) (Hunt et al. 1995). The Mayo researchers also reported respiratory symptoms in workers who did not wear gloves but worked in areas where large numbers of gloves were being used, presumably due to air-borne talcum powder/latex protein particles.

Control and Prevention

The most effective preventive measure is modification of standard procedures to replace the use of gloves and equipment made with NRL with similar items made of vinyl or other non-rubber materials. This requires involvement of the purchasing and supply departments, which should also mandate the labelling of all latex-containing items so that they may be avoided by individuals with latex sensitivity. This is important not only to the staff but also to patients who may have a history suggestive of latex allergy. Aerosolized latex, from latex powder, is also problematic. HCWs who are allergic to latex and who do not use latex gloves may still be affected by the powdered latex gloves used by co-workers. A significant problem is presented by the wide variation in content of latex allergen among gloves from different manufacturers and, indeed, among different lots of gloves from the same manufacturer.

Glove manufacturers are experimenting with gloves using formulations with smaller amounts of NRL as well as coatings that will obviate the need for talcum powder to make the gloves easy to put on and take off. The goal is to provide comfortable, easy to wear, non-allergenic gloves that still provide effective barriers to the transmission of the hepatitis B virus, HIV and other pathogens.

A careful medical history with a particular emphasis on prior latex exposures should be elicited from all health care workers who present symptoms suggestive of latex allergy. In suspect cases, evidence of latex sensitivity may be confirmed by skin or serological testing. Since there is evidently a risk of provoking an anaphylactic reaction, the skin testing should only be performed by experienced medical personnel.

At the present time, allergens for desensitization are not available so that the only remedy is avoidance of exposure to products containing NRL. In some instances, this may require a change of job. Weido and Sim (1995) at the University of Texas Medical Branch at Galveston suggest advising individuals in high-risk groups to carry self-injectable epinephrine to use in the event of a systemic reaction.

Following the appearance of several clusters of latex allergy cases in 1990, the Mayo Medical Center in Rochester, Minnesota, formed a multidisciplinary work group to address the problem (Hunt et al. 1996). Subsequently, this was formalized in a Latex Allergy Task Force with members from the departments of allergy, preventive medicine, dermatology and surgery as well as the Director of Purchasing, the Surgical Nursing Clinical Director and the Director of Employee Health. Articles on latex allergy were published in staff newsletters and information bulletins to educate the 20,000 member workforce to the problem and to encourage those with suggestive symptoms to seek medical consultation. A standardized approach to testing for latex sensitivity and techniques for quantifying the amount of latex allergen in manufactured products and the amount and particle size of air-borne latex allergen were developed. The latter proved to be sufficiently sensitive to measure the exposure of individual workers while performing particular high-risk tasks. Steps were initiated to monitor a gradual transition to low-allergen gloves (an incidental effect was a lowering of their cost by concentrating glove purchases among the fewer vendors who could meet the low allergen requirements) and to minimize exposures of staff and patients with known sensitivity to NLR.

To alert the public to the risks of NLR allergy, a consumer group, the Delaware Valley Latex Allergy Support Network has been formed. This group has created an Internet website (http://www.latex.org) and maintains a toll-free telephone line (1-800 LATEXNO) to provide up-to-date factual information about latex allergy to persons with this problem and those who care for them. This organization, which has a Medical Advisory Group, maintains a Literature Library and a Product Center and encourages the exchange of experiences among those who have had allergic reactions.

Conclusion

Latex allergies are becoming an increasingly important problem among health care workers. The solution lies in minimizing contact with latex allergen in their work environment, especially by substituting non-latex surgical gloves and appliances.

 

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Wednesday, 02 March 2011 16:24

Waste Anaesthetic Gases

The use of inhaled anaesthetics was introduced in the decade of 1840 to 1850. The first compounds to be used were diethyl ether, nitrous oxide and chloroform. Cyclopropane and trichloroethylene were introduced many years later (circa 1930-1940), and the use of fluoroxene, halothane and methoxiflurane began in the decade of the 1950s. By the end of the 1960s enflurane was being used and, finally, isoflurane was introduced in the 1980s. Isoflurane is now considered the most widely used inhalation anaesthetic even though it is more expensive than the others. A summary of the physical and chemical characteristics of methoxiflurane, enflurane, halothane, isoflurane and nitrous oxide, the most commonly used anaesthetics, is shown in table 1 (Wade and Stevens 1981).

Table 1. Properties of inhaled anaesthetics

 

Isoflurane,
Forane

Enflurane,
Ethrane

Halothane,
Fluothane

Methoxyflurane,
Penthrane

Dinitrogen oxide,
Nitrous oxide

Molecular weight

184.0

184.5

197.4

165.0

44.0

Boiling point

48.5°C

56.5°C

50.2°C

104.7°C

Density

1.50

1.52 (25°C)

1.86 (22°C)

1.41 (25°C)

Vapour pressure at 20 °C

250.0

175.0 (20°C)

243.0 (20°C)

25.0 (20°C)

Smell

Pleasant, sharp

Pleasant, like ether

Pleasant, sweet

Pleasant, fruity

Pleasant, sweet

Separation coefficients:

Blood/gas

1.40

1.9

2.3

13.0

0.47

Brain/gas

3.65

2.6

4.1

22.1

0.50

Fat/gas

94.50

105.0

185.0

890.0

1.22

Liver/gas

3.50

3.8

7.2

24.8

0.38

Muscle/gas

5.60

3.0

6.0

20.0

0.54

Oil/gas

97.80

98.5

224.0

930.0

1.4

Water/gas

0.61

0.8

0.7

4.5

0.47

Rubber/gas

0.62

74.0

120.0

630.0

1.2

Metabolic rate

0.20

2.4

15–20

50.0

 

All of them, with the exception of nitrous oxide (N2O), are hydrocarbons or chlorofluorinated liquid ethers that are applied by vapourization. Isoflurane is the most volatile of these compounds; it is the one that is metabolized at the lowest rate and the one that is least soluble in blood, in fats and in the liver.

Normally, N2O, a gas, is mixed with a halogenated anaesthetic, although they are sometimes used separately, depending on the type of anaesthesia that is required, the characteristics of the patient and the work habits of the anaesthetist. The normally used concentrations are 50 to 66% N2O and up to 2 or 3% of the halogenated anaesthetic (the rest is usually oxygen).

The anaesthesia of the patient is usually started by the injection of a sedative drug followed by an inhaled anaesthetic. The volumes given to the patient are in the order of 4 or 5 litres/minute. Parts of the oxygen and of the anaesthetic gases in the mixture are retained by the patient while the remainder is exhaled directly into the atmosphere or is recycled into the respirator, depending among other things on the type of mask used, on whether the patient is intubated and on whether or not a recycling system is available. If recycling is available, exhaled air can be recycled after it is cleaned or it can be vented to the atmosphere, expelled from the operating room or aspirated by a vacuum. Recycling (closed circuit) is not a common procedure and many respirators do not have exhaust systems; all the air exhaled by the patient, including the waste anaesthetic gases, therefore, ends up in the air of the operating room.

The number of workers occupationally exposed to waste anaesthetic gases is high, because it is not only the anaesthetists and their assistants who are exposed, but all the other people who spend time in operating rooms (surgeons, nurses and support staff), the dentists who perform odontological surgery, the personnel in delivery rooms and intensive care units where patients may be under inhaled anaesthesia and veterinary surgeons. Similarly, the presence of waste anaesthetic gases is detected in recovery rooms, where they are exhaled by patients who are recovering from surgery. They are also detected in other areas adjacent to operating rooms because, for reasons of asepsis, operating rooms are kept at positive pressure and this favours the contamination of surrounding areas.

Health Effects

Problems due to the toxicity of anaesthetic gases were not seriously studied until the 1960s, even though a few years after the use of inhaled anaesthetics became common, the relationship between the illnesses (asthma, nephritis) that affected some of the first professional anaesthetists and their work as such was already suspected (Ginesta 1989). In this regard the appearance of an epidemiological study of more than 300 anaesthetists in the Soviet Union, the Vaisman (1967) survey, was the starting point for several other epidemiological and toxicological studies. These studies—mostly during the 1970s and the first half of the 1980s—focused on the effects of anaesthetic gases, in most cases nitrous oxide and halothane, on people occupationally exposed to them.

The effects observed in most of these studies were an increase in spontaneous abortions among women exposed during or before pregnancy, and among women partners of exposed men; an increase in congenital malformations in children of exposed mothers; and the occurrence of hepatic, renal and neurological problems and of some types of cancer in both men and women (Bruce et al. 1968, 1974; Bruce and Bach 1976). Even though the toxic effects of nitrous oxide and of halothane (and probably its substitutes as well) on the body are not exactly the same, they are commonly studied together, given that exposure generally occurs simultaneously.

It appears likely that there is a correlation between these exposures and an increased risk, particularly for spontaneous abortions and congenital malformations in children of women exposed during pregnancy (Stoklov et al. 1983; Spence 1987; Johnson, Buchan and Reif 1987). As a result, many of the people exposed have expressed great concern. Rigorous statistical analysis of these data, however, casts doubt on the existence of such a relationship. More recent studies reinforce these doubts while chromosomal studies yield ambiguous results.

The works published by Cohen and colleagues (1971, 1974, 1975, 1980), who carried out extensive studies for the American Society of Anaesthetists (ASA), constitute a fairly extensive series of observations. Follow-up publications criticized some of the technical aspects of the earlier studies, particularly with respect to the sampling methodology and, especially, the proper selection of a control group. Other deficiencies included lack of reliable information on the concentrations to which the subjects had been exposed, the methodology for dealing with false positives and the lack of controls for factors such as tobacco and alcohol use, prior reproductive histories and voluntary infertility. Consequently, some of the studies are now even considered invalid (Edling 1980; Buring et al. 1985; Tannenbaum and Goldberg 1985).

Laboratory studies have shown that exposure of animals to ambient concentrations of anaesthetic gases equivalent to those found in operating rooms does cause deterioration in their development, growth and adaptive behaviour (Ferstandig 1978; ACGIH 1991). These are not conclusive, however, since some of these experimental exposures involved anaesthetic or subanaesthetic levels, concentrations significantly higher than the levels of waste gases usually found in operating room air (Saurel-Cubizolles et al. 1994; Tran et al. 1994).

Nevertheless, even acknowledging that a relationship between the deleterious effects and exposures to waste anaesthetic gases has not been definitively established, the fact is that the presence of these gases and their metabolites is readily detected in the air of operating rooms, in exhaled air and in biological fluids. Accordingly, since there is concern about their potential toxicity, and because it is technically feasible to do so without inordinate effort or expense, it would be prudent to take steps to eliminate or reduce to a minimum the concentrations of waste anaesthetic gases in operating rooms and nearby areas (Rosell, Luna and Guardino 1989; NIOSH 1994).

Maximum Allowable Exposure Levels

The American Conference of Governmental Industrial Hygienists (ACGIH) has adopted a threshold limit value-time weighted average (TLV-TWA) of 50 ppm for nitrous oxide and halothane (ACGIH 1994). The TLV-TWA is the guideline for the production of the compound, and the recommendations for operating rooms are that its concentration be kept lower, at a level below 1 ppm (ACGIH 1991). NIOSH sets a limit of 25 ppm for nitrous oxide and of 1 ppm for halogenated anaesthetics, with the additional recommendation that when they are used together, the concentration of halogenated compounds be reduced to a limit of 0.5 ppm (NIOSH 1977b).

With regard to values in biological fluids, the recommended limit for nitrous oxide in urine after 4 hours of exposure at average ambient concentrations of 25 ppm ranges from 13 to 19 μg/L, and for 4 hours of exposure at average ambient concentrations of 50 ppm, the range is 21 to 39 μg/L (Guardino and Rosell 1995). If exposure is to a mixture of a halogenated anaesthetic and nitrous oxide, the measurement of the values from nitrous oxide is used as the basis for controlling exposure, because as higher concentrations are used, quantification becomes easier.

Analytical Measurement

Most of the procedures described for measuring residual anaesthetics in air are based on the capture of these compounds by adsorption or in an inert bag or container, later to be analysed by gas chromatography or infrared spectroscopy (Guardino and Rosell 1985). Gas chromatography is also employed to measure nitrous oxide in urine (Rosell, Luna and Guardino 1989), while isoflurane is not readily metabolized and is therefore seldom measured.

Common Levels of Residual Concentrations in the Air of Operating Rooms

In the absence of preventive measures, such as the extraction of residual gases and/or introducing an adequate supply of new air into the operating suite, personal concentrations of more than 6,000 ppm of nitrous oxide and 85 ppm of halothane have been measured (NIOSH 1977). Concentrations of up to 3,500 ppm and 20 ppm, respectively, in the ambient air of operating rooms, have been measured. The implementation of corrective measures can reduce these concentrations to values below the environmental limits cited earlier (Rosell, Luna and Guardino 1989).

Factors that Affect the Concentration of Waste Anaesthetic Gases

The factors which most directly affect the presence of waste anaesthetic gases in the environment of the operating room are the following.

Method of anaesthesia. The first question to consider is the method of anaesthesia, for example, whether or not the patient is intubated and the type of face mask being used. In dental, laryngeal or other forms of surgery in which intubation is precluded, the patient’s expired air would be an important source of emissions of waste gases, unless equipment specifically designed to trap these exhalations is properly placed near the patient’s breathing zone. Accordingly, dental and oral surgeons are considered to be particularly at risk (Cohen, Belville and Brown 1975; NIOSH 1977a), as are veterinary surgeons (Cohen, Belville and Brown 1974; Moore, Davis and Kaczmarek 1993).

Proximity to the focus of emission. As is usual in industrial hygiene, when the known point of emission of a contaminant exists, proximity to the source is the first factor to consider when dealing with personal exposure. In this case, the anaesthetists and their assistants are the persons most directly affected by the emission of waste anaesthetic gases, and personal concentrations have been measured in the order of two times the average levels found in the air of operating rooms (Guardino and Rosell 1985).

Type of circuit. It goes without saying that in the few cases in which closed circuits are used, with reinspiration after the cleansing of the air and the resupply of oxygen and the necessary anaesthetics, there will be no emissions except in the case of equipment malfunction or if a leak exists. In other cases, it will depend on the characteristics of the system used, as well as on whether or not it is possible to add an extraction system to the circuit.

The concentration of anaesthetic gases. Another factor to take into account is the concentrations of the anaesthetics used since, obviously, those concentrations and the amounts found in the air of the operating room are directly related (Guardino and Rosell 1985). This factor is especially important when it comes to surgical procedures of long duration.

Type of surgical procedures. The duration of the operations, the time elapsed between procedures done in the same operating room and the specific characteristics of each procedure—which often determine which anaesthetics are used—are other factors to consider. The duration of the operation directly affects the residual concentration of anaesthetics in the air. In operating rooms where procedures are scheduled successively, the time elapsed between them also affects the presence of residual gases. Studies done in large hospitals with uninterrupted use of the operating rooms or with emergency operating rooms that are used beyond standard work schedules, or in operating rooms used for prolonged procedures (transplants, laryngotomies), show that substantial levels of waste gases are detected even before the first procedure of the day. This contributes to increased levels of waste gases in subsequent procedures. On the other hand, there are procedures that require temporary interruptions of inhalation anaesthesia (where extracorporeal circulation is needed, for example), and this also interrupts the emission of waste anaesthetic gases into the environment (Guardino and Rosell 1985).

Characteristics specific to the operating room. Studies done in operating rooms of different sizes, design and ventilation (Rosell, Luna and Guardino 1989) have demonstrated that these characteristics greatly influence the concentration of waste anaesthetic gases in the room. Large and non-partitioned operating rooms tend to have the lowest measured concentrations of waste anaesthetic gases, while in small operating rooms (e.g., paediatric operating rooms) the measured concentrations of waste gases are usually higher. The general ventilation system of the operating room and its proper operation is a fundamental factor for the reduction of the concentration of waste anaesthetics; the design of the ventilation system also affects the circulation of waste gases within the operating room and the concentrations in different locations and at various heights, something that can be easily verified by carefully taking samples.

Characteristics specific to the anaesthesia equipment. The emission of gases into the environment of the operating room depends directly on the characteristics of the anaesthesia equipment used. The design of the system, whether it includes a system for the return of excess gases, whether it can be attached to a vacuum or vented out of the operating room, whether it has leaks, disconnected lines and so on are always to be considered when determining the presence of waste anaesthetic gases in the operating room.

Factors specific to the anaesthetist and his or her team. The anaesthetist and his or her team are the last element to consider, but not necessarily the least important. Knowledge of the anaesthesia equipment, of its potential problems and the level of maintenance it receives—both by the team and by the maintenance staff in the hospital—are factors that affect very directly the emission of waste gases into the air of the operating room (Guardino and Rosell 1995). It has been clearly shown that, even when using adequate technology, the reduction of the ambient concentrations of anaesthetic gases cannot be achieved if a preventive philosophy is absent from the work routines of anaesthetists and their assistants (Guardino and Rosell 1992).

Preventive Measures

The basic preventive actions required to reduce occupational exposure to waste anaesthetic gases effectively can be summarized in the following six points:

  1. Anaesthetic gases should be thought of as occupational hazards. Even if from a scientific standpoint it has not been conclusively shown that anaesthetic gases have a serious deleterious effect on the health of people who are occupationally exposed, there is a high probability that some of the effects mentioned here are directly related to the exposure to waste anaesthetic gases. For that reason it is a good idea to consider them toxic occupational hazards.
  2. Scavenger systems should be used for waste gases. Scavenger systems are the most effective technical hardware for the reduction of waste gases in the air of the operating room (NIOSH 1975). These systems must fulfil two basic principles: they must store and/or adequately eliminate the whole volume of air expired by the patient, and they must be designed to guarantee that neither the respiration of the patient nor the proper functioning of the anaesthesia equipment will be affected—with separate safety devices for each function. The techniques most commonly employed are: a direct connection to a vacuum outlet with a flexible regulating chamber that allows for the discontinuous emission of gases of the respiratory cycle; directing the flow of the gases exhaled by the patient to the vacuum without a direct connection; and directing the flow of gases coming from the patient to the return of the ventilation system installed in the operating room and expelling these gases from the operating room and from the building. All these systems are technically easy to implement and very cost-efficient; the use of installed respirators as part of the design is recommended. In cases where systems that eliminate waste gases directly cannot be used because of the special characteristics of a procedure, localized extraction can be employed near the source of emission as long as it does not affect the general ventilation system or the positive pressure in the operating room.
  3. General ventilation with a minimum of 15 renewals/hour in the operating room should be guaranteed. The general ventilation of the operating room should be perfectly regulated. It should not only maintain positive pressure and respond to the thermohygrometric characteristics of the ambient air, but should also provide a minimum of 15 to 18 renewals per hour. Also, a monitoring procedure should be in place to ensure its proper functioning.
  4. Preventive maintenance of the anaesthesia circuit should be planned and regular. Preventive maintenance procedures should be set up that include regular inspections of the respirators. Verifying that no gases are being emitted to the ambient air should be part of the protocol followed when the equipment is first turned on, and its proper functioning with regard to the safety of the patient should be checked. The proper functioning of the anaesthesia circuit should be verified by checking for leaks, periodically replacing filters and checking the safety valves.
  5. Environmental and biological controls should be used. The implementation of environmental and biological controls provides information not only about the correct functioning of the various technical elements (extraction of gases, general ventilation) but also about whether the working procedures are adequate for curtailing the emission of waste gases into the air. Today these controls do not present technical problems and they can be implemented economically, which is why they are recommended.
  6. Education and training of the exposed personnel is crucial. Achieving an effective reduction of occupational exposure to waste anaesthetic gases requires educating all operating room personnel about the potential risks and training them in the required procedures. This is particularly applicable to anaesthetists and their assistants who are most directly involved and those responsible for the maintenance of the anaesthesia and air-conditioning equipment.

 

Conclusion

Although not definitively proven, there is enough evidence to suggest that exposures to waste anaesthetic gases may be harmful to HCWs. Stillbirths and congenital malformations in infants born to female workers and to the spouses of male workers represent the major forms of toxicity. Since it is technically feasible at a low cost, it is desirable to reduce the concentration of these gases in the ambient air in operating rooms and adjacent areas to a minimum. This requires not only the use and correct maintenance of anaesthesia equipment and ventilation/air conditioning systems but also the education and training of all personnel involved, especially anaesthetists and their assistants, who generally are exposed to higher concentrations. Given the work conditions peculiar to operating rooms, indoctrination in the correct work habits and procedures is very important in trying to reduce the amounts of anaesthetic waste gases in the air to a minimum.

 

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Wednesday, 02 March 2011 16:21

Managing Chemical Hazards in Hospitals

The vast array of chemicals in hospitals, and the multitude of settings in which they occur, call for a systematic approach to their control. A chemical-by-chemical approach to prevention of exposures and their deleterious outcome is simply too inefficient to handle a problem of this scope. Moreover, as noted in the article “Overview of chemical hazards in health care”, many chemicals in the hospital environment have been inadequately studied; new chemicals are constantly being introduced and for others, even some that have become quite familiar (e.g., gloves made of latex), new hazardous effects are only now becoming manifest. Thus, while it is useful to follow chemical-specific control guidelines, a more comprehensive approach is needed whereby individual chemical control policies and practices are superimposed on a strong foundation of general chemical hazard control.

The control of chemical hazards in hospitals must be based on classic principles of good occupational health practice. Because health care facilities are accustomed to approaching health through the medical model, which focuses on the individual patient and treatment rather than on prevention, special effort is required to ensure that the orientation for handling chemicals is indeed preventive and that measures are principally focused on the workplace rather than on the worker.

Environmental (or engineering) control measures are the key to prevention of deleterious exposures. However, it is necessary to train each worker correctly in appropriate exposure prevention techniques. In fact, right-to-know legislation, as described below, requires that workers be informed of the hazards with which they work, as well as of the appropriate safety precautions. Secondary prevention at the level of the worker is the domain of medical services, which may include medical monitoring to ascertain whether health effects of exposure can be medically detected; it also consists of prompt and appropriate medical intervention in the event of accidental exposure. Chemicals that are less toxic must replace more toxic ones, processes should be enclosed wherever possible and good ventilation is essential.

While all means to prevent or minimize exposures should be implemented, if exposure does occur (e.g., a chemical is spilled), procedures must be in place to ensure prompt and appropriate response to prevent further exposure.

Applying the General Principles of Chemical Hazard Control in the Hospital Environment

The first step in hazard control is hazard identification. This, in turn, requires a knowledge of the physical properties, chemical constituents and toxicological properties of the chemicals in question. Material safety data sheets (MSDSs), which are becoming increasingly available by legal requirement in many countries, list such properties. The vigilant occupational health practitioner, however, should recognize that the MSDS may be incomplete, particularly with respect to long-term effects or effects of low-dose chronic exposure. Hence, a literature search may be contemplated to supplement the MSDS material, when appropriate.

The second step in controlling a hazard is characterizing the risk. Does the chemical pose a carcinogenic risk? Is it an allergen? A teratogen? Is it mainly short-term irritancy effects that are of concern? The answer to these questions will influence the way in which exposure is assessed.

The third step in chemical hazard control is to assess the actual exposure. Discussion with the health care workers who use the product in question is the most important element in this endeavour. Monitoring methods are necessary in some situations to ascertain that exposure controls are functioning properly. These may be area sampling, either grab sample or integrated, depending on the nature of the exposure; it may be personal sampling; in some cases, as discussed below, medical monitoring may be contemplated, but usually as a last resort and only as back-up to other means of exposure assessment.

Once the properties of the chemical product in question are known, and the nature and extent of exposure are assessed, a determination could be made as to the degree of risk. This generally requires that at least some dose-response information be available.

After evaluating the risk, the next series of steps is, of course, to control the exposure, so as to eliminate or at least minimize the risk. This, first and foremost, involves applying the general principles of exposure control.

Organizing a Chemical Control Programme in Hospitals

The traditional obstacles

The implementation of adequate occupational health programmes in health care facilities has lagged behind the recognition of the hazards. Labour relations are increasingly forcing hospital management to look at all aspects of their benefits and services to employees, as hospitals are no longer tacitly exempt by custom or privilege. Legislative changes are now compelling hospitals in many jurisdictions to implement control programmes.

However, obstacles remain. The preoccupation of the hospital with patient care, emphasizing treatment rather than prevention, and the staff’s ready access to informal “corridor consultation”, have hindered the rapid implementation of control programmes. The fact that laboratory chemists, pharmacists and a host of medical scientists with considerable toxicological expertise are heavily represented in management has, in general, not served to hasten the development of programmes. The question may be asked, “Why do we need an occupational hygienist when we have all these toxicology experts?” To the extent that changes in procedures threaten to have an impact on the tasks and services provided by these highly skilled personnel, the situation may be made worse: “We cannot eliminate the use of Substance X as it is the best bactericide around.” Or, “If we follow the procedure that you are recommending, patient care will suffer.” Moreover, the “we don’t need training” attitude is commonplace among the health care professions and hinders the implementation of the essential components of chemical hazard control. Internationally, the climate of cost constraint in health care is clearly also an obstacle.

Another problem of particular concern in hospitals is preserving the confidentiality of personal information about health care workers. While occupational health professionals should need only to indicate that Ms. X cannot work with chemical Z and needs to be transferred, curious clinicians are often more prone to push for the clinical explanation than their non-health care counterparts. Ms. X may have liver disease and the substance is a liver toxin; she may be allergic to the chemical; or she may be pregnant and the substance has potential teratogenic properties. While the need to alter the work assignment of particular individuals should not be routine, the confidentiality of the medical details should be protected if it is necessary.

Right-to-know legislation

Many jurisdictions around the world have implemented right-to-know legislation. In Canada, for example, WHMIS has revolutionized the handling of chemicals in industry. This country-wide system has three components: (1) the labelling of all hazardous substances with standardized labels indicating the nature of the hazard; (2) the provision of MSDSs with the constituents, hazards and control measures for each substance; and (3) the training of workers to understand the labels and the MSDSs and to use the product safely.

Under WHMIS in Canada and OSHA’s Hazard Communications requirements in the United States, hospitals have been required to construct inventories of all chemicals on the premises so that those that are “controlled substances” can be identified and addressed according to the legislation. In the process of complying with the training requirements of these regulations, hospitals have had to engage occupational health professionals with appropriate expertise and the spin-off benefits, particularly when bipartite train-the-trainer programmes were conducted, have included a new spirit to work cooperatively to address other health and safety concerns.

Corporate commitment and the role of joint health and safety committees

The most important element in the success of any occupational health and safety programme is corporate commitment to ensure its successful implementation. Policies and procedures regarding the safe handling of chemicals in hospitals must be written, discussed at all levels within the organization and adopted and enforced as corporate policy. Chemical hazard control in hospitals should be addressed by general as well as specific policies. For example, there should be a policy on responsibility for the implementation of right-to-know legislation that clearly outlines each party’s obligations and the procedures to be followed by individuals at each level of the organization (e.g., who chooses the trainers, how much work time is allowed for preparation and provision of training, to whom should communication regarding non-attendance be communicated and so on). There should be a generic spill clean-up policy indicating the responsibility of the worker and the department where the spill occurred, the indications and protocol for notifying the emergency response team, including the appropriate in-hospital and external authorities and experts, follow-up provisions for exposed workers and so on. Specific policies should also exist regarding the handling, storage and disposal of specific classes of toxic chemicals.

Not only is it essential that management be strongly committed to these programmes; the workforce, through its representatives, must also be actively involved in the development and implementation of policies and procedures. Some jurisdictions have legislatively mandated joint (labour-management) health and safety committees that meet at a minimum prescribed interval (bimonthly in the case of Manitoba hospitals), have written operating procedures and keep detailed minutes. Indeed in recognizing the importance of these committees, the Manitoba Workers’ Compensation Board (WCB) provides a rebate on WCB premiums paid by employers based on the successful functioning of these committees. To be effective, the members must be appropriately chosen—specifically, they must be elected by their peers, knowledgeable about the legislation, have appropriate education and training and be allotted sufficient time to conduct not only incident investigations but regular inspections. With respect to chemical control, the joint committee has both a pro-active and a re-active role: assisting in setting priorities and developing preventive policies, as well as serving as a sounding board for workers who are not satisfied that all appropriate controls are being implemented.

The multidisciplinary team

As noted above, the control of chemical hazards in hospitals requires a multidisciplinary endeavour. At a minimum, it requires occupational hygiene expertise. Generally hospitals have maintenance departments that have within them the engineering and physical plant expertise to assist a hygienist in determining whether workplace alterations are necessary. Occupational health nurses also play a prominent role in evaluating the nature of concerns and complaints, and in assisting an occupational physician in ascertaining whether clinical intervention is warranted. In hospitals, it is important to recognize that numerous health care professionals have expertise that is quite relevant to the control of chemical hazards. It would be unthinkable to develop policies and procedures for the control of laboratory chemicals without the involvement of lab chemists, for example, or procedures for handling anti-neoplastic drugs without the involvement of the oncology and pharmacology staff. While it is wise for occupational health professionals in all industries to consult with line staff prior to implementing control measures, it would be an unforgivable error to fail to do so in health care settings.

Data collection

As in all industries, and with all hazards, data need to be compiled both to help in priority setting and in evaluating the success of programmes. With respect to data collection on chemical hazards in hospitals, minimally, data need to be kept regarding accidental exposures and spills (so that these areas can receive special attention to prevent recurrences); the nature of concerns and complaints should be recorded (e.g., unusual odours); and clinical cases need to be tabulated, so that, for example, an increase in dermatitis from a given area or occupational group could be identified.

Cradle-to-grave approach

Increasingly, hospitals are becoming cognizant of their obligation to protect the environment. Not only the workplace hazardous properties, but the environmental properties of chemicals are being taken into consideration. Moreover, it is no longer acceptable to pour hazardous chemicals down the drain or release noxious fumes into the air. A chemical control programme in hospitals must, therefore, be capable of tracking chemicals from their purchase and acquisition (or, in some cases, synthesis on site), through the work handling, safe storage and finally to their ultimate disposal.

Conclusion

It is now recognized that there are thousands of potentially very toxic chemicals in the work environment of health care facilities; all occupational groups may be exposed; and the nature of the exposures are varied and complex. Nonetheless, with a systematic and comprehensive approach, with strong corporate commitment and a fully informed and involved workforce, chemical hazards can be managed and the risks associated with these chemicals controlled.

 

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Wednesday, 02 March 2011 16:17

Overview of Chemical Hazards in Health Care

Exposure to potentially hazardous chemicals is a fact of life for health care workers. They are encountered in the course of diagnostic and therapeutic procedures, in laboratory work, in preparation and clean-up activities and even in emanations from patients, to say nothing of the “infrastructure” activities common to all worksites such as cleaning and housekeeping, laundry, painting, plumbing and maintenance work. Despite the constant threat of such exposures and the large numbers of workers involved—in most countries, health care invariably is one of the most labour-intensive industries—this problem has received scant attention from those involved in occupational health and safety research and regulation. The great majority of chemicals in common use in hospitals and other health care settings are not specifically covered under national and international occupational exposure standards. In fact, very little effort has been made to date to identify the chemicals most frequently used, much less to study the mechanisms and intensity of exposures to them and the epidemiology of the effects on the health care workers involved.

This may be changing in the many jurisdictions in which right-to-know laws, such as the Canadian Workplace Hazardous Materials Information Systems (WHMIS) are being legislated and enforced. These laws require that workers be informed of the name and nature of the chemicals to which they may be exposed on the job. They have introduced a daunting challenge to administrators in the health care industry who must now turn to occupational health and safety professionals to undertake a de novo inventory of the identity and location of the thousands of chemicals to which their workers may be exposed.

The wide range of professions and jobs and the complexity of their interplay in the health care workplace require unique diligence and astuteness on the part of those charged with such occupational safety and health responsibilities. A significant complication is the traditional altruistic focus on the care and well-being of the patients, even at the expense of the health and well-being of those providing the services. Another complication is the fact that these services are often required at times of great urgency when important preventive and protective measures may be forgotten or deliberately disregarded.

Categories of Chemical Exposures in the Health Care Setting

Table 1 lists the categories of chemicals encountered in the health care workplace. Laboratory workers are exposed to the broad range of chemical reagents they employ, histology technicians to dyes and stains, pathologists to fixative and preservative solutions (formaldeyde is a potent sensitizer), and asbestos is a hazard to workers making repairs or renovations in older health care facilities.

Table 1. Categories of chemicals used in health care

Types of chemicals

Locations most likely to be found

Disinfectants

Patient areas

Sterilants

Central supply
Operating theatres
Physician offices
Rehabilitation centres

Medicines

Patient areas
Pharmacy

Laboratory reagents

Laboratories

Housekeeping/maintenance chemicals

Hospital-wide

Food ingredients and products

Kitchen
Cafeteria

Pesticides

Hospital-wide

 

Even when liberally applied in combating and preventing the spread of infectious agents, detergents, disinfectants and sterilants offer relatively little danger to patients whose exposure is usually of brief duration. Even though individual doses at any one time may be relatively low, their cumulative effect over the course of a working lifetime may, however, constitute a significant risk to health care workers.

Occupational exposures to drugs can cause allergic reactions, such as have been reported over many years among workers administering penicillin and other antibiotics, or much more serious problems with such highly carcinogenic agents as the antineoplastic drugs. The contacts may occur during the preparation or administration of the dose for injection or in cleaning up after it has been administered. Although the danger of this mechanism of exposure had been known for many years, it was fully appreciated only after mutagenic activity was detected in the urine of nurses administering antineoplastic agents.

Another mechanism of exposure is the administration of drugs as aerosols for inhalation. The use of antineoplastic agents, pentamidine and ribavarin by this route has been studied in some detail, but there has been, as of this writing, no report of a systematic study of aerosols as a source of toxicity among health care workers.

Anaesthetic gases represent another class of drugs to which many health care workers are exposed. These chemicals are associated with a variety of biological effects, the most obvious of which are on the nervous system. Recently, there have been reports suggesting that repeated exposures to anaesthetic gases may, over time, have adverse reproductive effects among both male and female workers. It should be recognized that appreciable amounts of waste anaesthetic gases may accumulate in the air in recovery rooms as the gases retained in the blood and other tissues of patients are eliminated by exhalation.

Chemical disinfecting and sterilizing agents are another important category of potentially hazardous chemical exposures for health care workers. Used primarily in the sterilization of non-disposable equipment, such as surgical instruments and respiratory therapy apparatus, chemical sterilants such as ethylene oxide are effective because they interact with infectious agents and destroy them. Alkylation, whereby methyl or other alkyl groups bind chemically with protein-rich entities such as the amino groups in haemoglobiin and DNA, is a powerful biological effect. In intact organisms, this may not cause direct toxicity but should be considered potentially carcinogenic until proven otherwise. Ethylene oxide itself, however, is a known carcinogen and is associated with a variety of adverse health effects, as discussed elsewhere in the Encyclopaedia. The potent alkylation capability of ethylene oxide, probably the most widely-used sterilant for heat-sensitive materials, has led to its use as a classic probe in studying molecular structure.

For years, the methods used in the chemical sterilization of instruments and other surgical materials have carelessly and needlessly put many health care workers at risk. Not even rudimentary precautions were taken to prevent or limit exposures. For example, it was the common practice to leave the door of the sterilizer partially open to allow the escape of excess ethylene oxide, or to leave freshly-sterilized materials uncovered and open to the room air until enough had been assembled to make efficient use of the aerator unit.

The fixation of metallic or ceramic replacement parts so common in dentistry and orthopaedic surgery may be a source of potentially hazardous chemical exposure such as silica. These and the acrylic resins often used to glue them in place are usually biologically inert, but health care workers may be exposed to the monomers and other chemical reactants used during the preparation and application process. These chemicals are often sensitizing agents and have been associated with chronic effects in animals. The preparation of mercury amalgam fillings can lead to mercury exposure. Spills and the spread of mercury droplets is a particular concern since these may linger unnoticed in the work environment for many years. The acute exposure of patients to them appears to be entirely safe, but the long-term health implications of the repeated exposure of health care workers have not been adequately studied.

Finally, such medical techniques as laser surgery, electro-cauterization and use of other radiofrequency and high-energy devices can lead to the thermal degradation of tissues and other substances resulting in the formation of potentially toxic smoke and fumes. For example, the cutting of “plaster” casts made of polyester resin impregnated bandages has been shown to release potentially toxic fumes.

The hospital as a “mini-municipality”

A listing of the varied jobs and tasks performed by the personnel of hospitals and other large health care facilities might well serve as a table of contents for the commercial listings of a telephone directory for a sizeable municipality. All of these entail chemical exposures intrinsic to the particular work activity in addition to those that are peculiar to the health care environment. Thus, painters and maintenance workers are exposed to solvents and lubricants. Plumbers and others engaged in soldering are exposed to fumes of lead and flux. Housekeeping workers are exposed to soaps, detergents and other cleansing agents, pesticides and other household chemicals. Cooks may be exposed to potentially carcinogenic fumes in broiling or frying foods and to oxides of nitrogen from the use of natural gas as fuel. Even clerical workers may be exposed to the toners used in copiers and printers. The occurrence and effects of such chemical exposures are detailed elsewhere in this Encyclopaedia.

One chemical exposure that is diminishing in importance as more and more HCWs quit smoking and more health care facilities become “smoke-free” is “second hand” tobacco smoke.

Unusual chemical exposures in health care

Table 2 presents a partial listing of the chemicals most commonly encountered in health care workplaces. Whether or not they will be toxic will depend on the nature of the chemical and its biological proclivities, the manner, intensity and duration of the exposure, the susceptibilities of the exposed worker, and the speed and effectiveness of any countermeasures that may have been attempted. Unfortunately, a compendium of the nature, mechanisms, effects and treatment of chemical exposures of health care workers has not yet been published.

There are some unique exposures in the health care workplace that substantiate the dictum that a high level of vigilance is necessary to protect workers fully from such risks. For example, it was recently reported that health care workers had been overcome by toxic fumes emanating from a patient under treatment from a massive chemical exposure. Cases of cyanide poisoning arising from patient emissions have also been reported. In addition to the direct toxicity of waste anaesthetic gases to anaesthetists and other personnel in operating theatres, there is the often unrecognized problem created by the frequent use in such areas of high-energy sources which can transform the anaesthetic gases to free radicals, a form in which they are potentially carcinogenic.

Table 2. Chemicals cited Hazardous Substances Database (HSDB)

The following chemicals are listed in the HSDB as being used in some area of the health care environment. The HSDB is produced by the US National Library of Medicine and is a compilation of more than 4,200 chemicals with known toxic effects in commercial use. Absence of a chemical from the list does not imply that it is not toxic, but that it is not present in the HSDB.

Use list in the HSDB

Chemical name

CAS number*

Disinfectants; antiseptics

benzylalkonium chloride
borax
boric acid
cetyl pyridinium chloride
m-cresol
2-chlorophenol
4-chlorophenol
hexachlorophene
methyl ethyl ketone
phenol
tri-m-cresyl phosphate (lysol)

0001-54-5
1303-96-4
10043-35-3
123-03-5
95-57-8
106-48-9
70-30-4
108-39-4
78-93-3
108-95-2
563-04-2

Sterilants

beta-propiolactone
crotonaldehyde
ethylene oxide
formaldehyde
glutaraldehyde

57-57-8
4170-30-3
75-21-8
50-00-0
111-30-8

Laboratory reagents:
Biological stains

2,4-xylidine (magenta-base)
acridine-red
basic parafuchsine
basic-magenta
CI-acid-blue-9
CI-acid-green-3
CI-acid-red-14
CI-direct-blue-1
CI-direct-red-28
CI-direct-yellow-11
CI-acid-green-3
curcumin
Heamtoxylin
hexamethyl-p-rosaniline
chloride (violet)
malachite green
osmiun tetroxide
ponceau 3R

3248-93-9
2465-29-4
569-61-9
3248-93-9
129-17-9
4680-78-8
3567-69-9
2429-74-5
573-58-0
1325-37-7
4680-78-8
458-37-7
517-28-2

548-62-9
569-64-2
20816-12-0
3564-09-8

* Chemical Abstracts identification number.

 

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Transmission of Mycobacterium tuberculosis is a recognized risk in health care facilities. The magnitude of the risk to HCWs varies considerably by the type of health care facility, the prevalence of TB in the community, the patient population served, the HCW’s occupational group, the area of the health care facility in which the HCW works and the effectiveness of TB infection-control interventions. The risk may be higher in areas where patients with TB are provided care before diagnosis and initiation of TB treatment and isolation precautions (e.g., in clinic waiting areas and emergency departments) or where diagnostic or treatment procedures that stimulate coughing are performed. Nosocomial transmission of M. tuberculosis has been associated with close contact with persons who have infectious TB and with the performance of certain procedures (e.g., bronchoscopy, endotracheal intubation and suctioning, open abscess irrigation and autopsy). Sputum induction and aerosol treatments that induce coughing may also increase the potential for transmission of M. tuberculosis. Personnel in health care facilities should be particularly alert to the need for preventing transmission of M. tuberculosis in those facilities in which immunocompromised persons (e.g., HIV-infected persons) work or receive care—especially if cough-inducing procedures, such as sputum induction and aerosolized pentamidine treatments, are being performed.

Transmission and Pathogenesis

M. tuberculosis is carried in airborne particles, or droplet nuclei, that can be generated when persons who have pulmonary or laryngeal TB sneeze, cough, speak or sing. The particles are an estimated 1 to 5 μm in size and normal air currents can keep them airborne for prolonged time periods and spread them throughout a room or building. Infection occurs when a susceptible person inhales droplet nuclei containing M. tuberculosis and these droplet nuclei traverse the mouth or nasal passages, upper respiratory tract and bronchi to reach the alveoli of the lungs. Once in the alveoli, the organisms are taken up by alveolar macrophages and spread throughout the body. Usually within two to ten weeks after initial infection with M. tuberculosis, the immune response limits further multiplication and spread of the tubercle bacilli; however, some of the bacilli remain dormant and viable for many years. This condition is referred to as latent TB infection. Persons with latent TB infection usually have positive purified protein derivative (PPD)-tuberculin skin-test results, but they do not have symptoms of active TB, and they are not infectious.

In general, persons who become infected with M. tuberculosis have approximately a 10% risk for developing active TB during their lifetimes. This risk is greatest during the first two years after infection. Immunocompromised persons have a greater risk for the progression of latent TB infection to active TB disease; HIV infection is the strongest known risk factor for this progression. Persons with latent TB infection who become co-infected with HIV have approximately an 8 to 10% risk per year for developing active TB. HIV-infected persons who are already severely immunosuppressed and who become newly infected with M. tuberculosis have an even greater risk for developing active TB.

The probability that a person who is exposed to M. tuberculosis will become infected depends primarily on the concentration of infectious droplet nuclei in the air and the duration of exposure. Characteristics of the TB patient that enhance transmission include:

  • disease in the lungs, airways or larynx
  • presence of cough or other forceful expiratory measures
  • presence of acid-fast bacilli (AFB) in the sputum
  • failure of the patient to cover the mouth and nose when coughing or sneezing
  • presence of cavitation on chest radiograph
  • inappropriate or short duration of chemotherapy
  • administration of procedures that can induce coughing or cause aerosolization of M. tuberculosis (e.g., sputum induction).

 

Environmental factors that enhance the likelihood of transmission include:

  • exposure in relatively small, enclosed spaces
  • inadequate local or general ventilation that results in insufficient dilution and/or removal of infectious droplet nuclei
  • recirculation of air containing infectious droplet nuclei.

 

Characteristics of the persons exposed to M. tuberculosis that may affect the risk for becoming infected are not as well defined. In general, persons who have been infected previously with M. tuberculosis may be less susceptible to subsequent infection. However, reinfection can occur among previously infected persons, especially if they are severely immunocompromised. Vaccination with Bacille of Calmette and Guérin (BCG) probably does not affect the risk for infection; rather, it decreases the risk for progressing from latent TB infection to active TB. Finally, although it is well established that HIV infection increases the likelihood of progressing from latent TB infection to active TB, it is unknown whether HIV infection increases the risk for becoming infected if exposed to M. tuberculosis.

Epidemiology

Several TB outbreaks among persons in health care facilities have been reported recently in the United States. Many of these outbreaks involved transmission of multidrug-resistant strains of M. tuberculosis to both patients and HCWs. Most of the patients and some of the HCWs were HIV-infected persons in whom new infection progressed rapidly to active disease. Mortality associated with those outbreaks was high (with a range of 43 to 93%). Furthermore, the interval between diagnosis and death was brief (with a range of median intervals of 4 to 16 weeks). Factors contributing to these outbreaks included delayed diagnosis of TB, delayed recognition of drug resistance and delayed initiation of effective therapy, all of which resulted in prolonged infectiousness, delayed initiation and inadequate duration of TB isolation, inadequate ventilation in TB isolation rooms, lapses in TB isolation practices and inadequate precautions for cough-inducing procedures and lack of adequate respiratory protection.

Fundamentals of TB infection control

An effective TB infection-control programme requires early identification, isolation and effective treatment of persons who have active TB. The primary emphasis of the TB infection-control plan should be on achieving these three goals. In all health care facilities, particularly those in which persons who are at high risk for TB work or receive care, policies and procedures for TB control should be developed, reviewed periodically and evaluated for effectiveness to determine the actions necessary to minimize the risk for transmission of M. tuberculosis.

The TB infection-control programme should be based on a hierarchy of control measures. The first level of the hierarchy, and that which affects the largest number of persons, is using administrative measures intended primarily to reduce the risk for exposing uninfected persons to persons who have infectious TB. These measures include:

  • developing and implementing effective written policies and protocols to ensure the rapid identification, isolation, diagnostic evaluation and treatment of persons likely to have TB
  • implementing effective work practices among HCWs in the health care facility (e.g., correctly wearing respiratory protection and keeping doors to isolation rooms closed)
  • educating, training and counselling HCWs about TB
  • screening HCWs for TB infection and disease.

 

The second level of the hierarchy is the use of engineering controls to prevent the spread and reduce the concentration of infectious droplet nuclei. These controls include:

  • direct source control using local exhaust ventilation
  • controlling direction of airflow to prevent contamination of air in areas adjacent to the infectious source
  • diluting and removing contaminated air via general ventilation
  • air cleaning via air filtration or ultraviolet germicidal irradiation (UVGI).

 

The first two levels of the hierarchy minimize the number of areas in the health care facility where exposure to infectious TB may occur, and they reduce, but do not eliminate, the risk in those few areas where exposure to M. tuberculosis can still occur (e.g., rooms in which patients with known or suspected infectious TB are being isolated and treatment rooms in which cough-inducing or aerosol-generating procedures are performed on such patients). Because persons entering such rooms may be exposed to M. tuberculosis, the third level of the hierarchy is the use of personal respiratory protective equipment in these and certain other situations in which the risk for infection with M. tuberculosis may be relatively higher.

Specific measures to reduce the risk for transmission of M. tuberculosis include the following:

1.    Assigning to specific persons in the health care facility the supervisory responsibility for designing, implementing, evaluating and maintaining the TB infection-control programme.

2.    Conducting a risk assessment to evaluate the risk for transmission of M. tuberculosis in all areas of the health care facility, developing a written TB infection-control programme based on the risk assessment and periodically repeating the risk assessment to evaluate the effectiveness of the TB infection-control programme. TB infection-control measures for each health care facility should be based on a careful assessment of the risk for transmission of M. tuberculosis in that particular setting. The first step in developing the TB infection-control programme should be to conduct a baseline risk assessment to evaluate the risk for transmission of M. tuberculosis in each area and occupational group in the facility. Appropriate infection-control interventions can then be developed on the basis of actual risk. Risk assessments should be performed for all inpatient and outpatient settings (e.g., medical and dental offices). Classification of risk for a facility, for a specific area and for a specific occupational group should be based on the profile of TB in the community, the number of infectious TB patients admitted to the area or ward, or the estimated number of infectious TB patients to whom HCWs in an occupational group may be exposed and the results of analysis of HCW PPD test conversions (where applicable) and possible person-to-person transmission of M. tuberculosis. Regardless of risk level, the management of patients with known or suspected infectious TB should not vary. However, the index of suspicion for infectious TB among patients, the frequency of HCW PPD skin testing, the number of TB isolation rooms and other factors will depend on the level of risk for transmission of M. tuberculosis in the facility, area or occupational group.

3.    Developing, implementing and enforcing policies and protocols to ensure early identification, diagnostic evaluation and effective treatment of patients who may have infectious TB. A diagnosis of TB may be considered for any patient who has a persistent cough (i.e., a cough lasting for longer than 3 weeks) or other signs or symptoms compatible with active TB (e.g., bloody sputum, night sweats, weight loss, anorexia or fever). However, the index of suspicion for TB will vary in different geographic areas and will depend on the prevalence of TB and other characteristics of the population served by the facility. The index of suspicion for TB should be very high in geographic areas or among groups of patients in which the prevalence of TB is high. Appropriate diagnostic measures should be conducted and TB precautions implemented for patients in whom active TB is suspected.

4.    Providing prompt triage for and appropriate management of patients in the outpatient setting who may have infectious TB. Triage of patients in ambulatory-care settings and emergency departments should include vigorous efforts to identify promptly patients who have active TB. HCWs who are the first points of contact in facilities that serve populations at risk for TB should be trained to ask questions that will facilitate identification of patients with signs and symptoms suggestive of TB. Patients with signs or symptoms suggestive of TB should be evaluated promptly to minimize the amount of time they are in ambulatory-care areas. TB precautions should be followed while the diagnostic evaluation is being conducted for these patients. TB precautions in the ambulatory-care setting should include placing these patients in a separate area apart from other patients and not in open waiting areas (ideally, in a room or enclosure meeting TB isolation requirements), giving these patients surgical masks to wear and instructing them to keep their masks on and giving these patients tissues and instructing them to cover their mouths and noses with the tissues when coughing or sneezing. Surgical masks are designed to prevent the respiratory secretions of the person wearing the mask from entering the air. When not in a TB isolation room, patients suspected of having TB should wear surgical masks to reduce the expulsion of droplet nuclei into the air. These patients do not need to wear particulate respirators, which are designed to filter the air before it is inhaled by the person wearing the mask. Patients suspected of having or known to have TB should never wear a respirator that has an exhalation valve, because the device would provide no barrier to the expulsion of droplet nuclei into the air.

5.    Promptly initiating and maintaining TB isolation for persons who may have infectious TB and who are admitted to the inpatient setting. In hospitals and other inpatient facilities, any patient suspected of having or known to have infectious TB should be placed in a TB isolation room that has currently recommended ventilation characteristics (see below). Written policies for initiating isolation should specify the indications for isolation, the person(s) authorized to initiate and discontinue isolation, the isolation practices to follow, the monitoring of isolation, the management of patients who do not adhere to isolation practices and the criteria for discontinuing isolation.

6.    Effectively planning arrangements for discharge. Before a TB patient is discharged from the health care facility, the facility’s staff and public health authorities should collaborate to ensure continuation of therapy. Discharge planning in the health care facility should include, at a minimum, a confirmed outpatient appointment with the provider who will manage the patient until the patient is cured, sufficient medication to take until the outpatient appointment and placement into case management (e.g., directly observed therapy (DOT)) or outreach programmes of the public health department. These plans should be initiated and in place before the patient’s discharge.

7.    Developing, installing, maintaining and evaluating ventilation and other engineering controls to reduce the potential for airborne exposure to M. tuberculosis. Local exhaust ventilation is a preferred source control technique, and it is often the most efficient way to contain airborne contaminants because it captures these contaminants near their source before they can disperse. Therefore, the technique should be used, if feasible, wherever aerosol-generating procedures are performed. Two basic types of local exhaust devices use hoods: the enclosing type, in which the hood either partially or fully encloses the infectious source, and the exterior type, in which the infectious source is near but outside the hood. Fully enclosed hoods, booths or tents are always preferable to exterior types because of their superior ability to prevent contaminants from escaping into the HCW’s breathing zone. General ventilation can be used for several purposes, including diluting and removing contaminated air, controlling airflow patterns within rooms and controlling the direction of airflow throughout a facility. General ventilation maintains air quality by two processes: dilution and removal of airborne contaminants. Uncontaminated supply air mixes with the contaminated room air (i.e., dilution), which is subsequently removed from the room by the exhaust system. These processes reduce the concentration of droplet nuclei in the room air. Recommended general ventilation rates for health care facilities are usually expressed in number of air changes per hour (ACH).

This number is the ratio of the volume of air entering the room per hour to the room volume and is equal to the exhaust airflow (Q, in cubic feet per minute) divided by the room volume (V, in cubic feet) multiplied by 60 (i.e., ACH = Q / V x 60). For the purposes of reducing the concentration of droplet nuclei, TB isolation and treatment rooms in existing health care facilities should have an airflow of greater than 6 ACH. Where feasible, this airflow rate should be increased to at least 12 ACH by adjusting or modifying the ventilation system or by using auxiliary means (e.g., recirculation of air through fixed HEPA filtration systems or portable air cleaners). New construction or renovation of existing health care facilities should be designed so that TB isolation rooms achieve an airflow of at least 12 ACH. The general ventilation system should be designed and balanced so that air flows from less contaminated (i.e., more clean) to more contaminated (less clean) areas. For example, air should flow from corridors into TB isolation rooms to prevent spread of contaminants to other areas. In some special treatment rooms in which operative and invasive procedures are performed, the direction of airflow is from the room to the hallway to provide cleaner air during these procedures. Cough-inducing or aerosol-generating procedures (e.g., bronchoscopy and irrigation of tuberculous abscesses) should not be performed in rooms with this type of airflow on patients who may have infectious TB. HEPA filters may be used in a number of ways to reduce or eliminate infectious droplet nuclei from room air or exhaust. These methods include placement of HEPA filters in exhaust ducts discharging air from booths or enclosures into the surrounding room, in ducts or in ceiling- or wall-mounted units, for recirculation of air within an individual room (fixed recirculation systems), in portable air cleaners, in exhaust ducts to remove droplet nuclei from air being discharged to the outside, either directly or through ventilation equipment, and in ducts discharging air from the TB isolation room into the general ventilation system. In any application, HEPA filters should be installed carefully and maintained meticulously to ensure adequate functioning. For general use areas in which the risk for transmission of M. tuberculosis is relatively high, ultraviolet lamps (UVGI) may be used as an adjunct to ventilation for reducing the concentration of infectious droplet nuclei, although the effectiveness of such units has not been evaluated adequately. Ultraviolet (UV) units can be installed in a room or corridor to irradiate the air in the upper portion of the room, or they can be installed in ducts to irradiate air passing through the ducts.

8.    Developing, implementing, maintaining and evaluating a respiratory protection programme. Personal respiratory protection (i.e., respirators) should be used by persons entering rooms in which patients with known or suspected infectious TB are being isolated, persons present during cough-inducing or aerosol-generating procedures performed on such patients and persons in other settings where administrative and engineering controls are not likely to protect them from inhaling infectious airborne droplet nuclei. These other settings include transporting patients who may have infectious TB in emergency transport vehicles and providing urgent surgical or dental care to patients who may have infectious TB before a determination has been made that the patient is non-infectious.

9.    Educating and training HCWs about TB, effective methods for preventing transmission of M. tuberculosis and the benefits of medical screening programmes. All HCWs, including physicians, should receive education regarding TB that is relevant to persons in their particular occupational group. Ideally, training should be conducted before initial assignment and the need for additional training should be re-evaluated periodically (e.g., once a year). The level and detail of this education will vary according to the HCW’s work responsibilities and the level of risk in the facility (or area of the facility) in which the HCW works. However, the programme may include the following elements:

  • the basic concepts of M. tuberculosis transmission, pathogenesis and diagnosis,
    including information concerning the difference between latent TB infection and active
    TB disease, the signs and symptoms of TB and the possibility of reinfection
  • the potential for occupational exposure to persons who have infectious TB in the
    health care facility, including information concerning the prevalence of TB in the
    community and facility, the ability of the facility to properly isolate patients who have
    active TB, and situations with increased risk for exposure to M. tuberculosis
  • the principles and practices of infection control that reduce the risk for transmission of
    M. tuberculosis, including information concerning the hierarchy of TB infection-control
    measures and the written policies and procedures of the facility. Site-specific control
    measures should be provided to HCWs working in areas that require control
    measures in addition to those of the basic TB infection-control programme.
  • the importance of proper maintenance for engineering controls (e.g., cleaning UVGI lamps and ensuring negative pressure in TB isolation rooms)
  • the purpose of PPD skin testing, the significance of a positive PPD test result and the importance of participating in the skin-test programme
  • the principles of preventive therapy for latent TB infection; these principles include the indications, use, effectiveness and the potential adverse effects of the drugs
  • the HCW’s responsibility to seek prompt medical evaluation if a PPD test conversion
    occurs or if symptoms develop that could be caused by TB. Medical evaluation will
    enable HCWs who have TB to receive appropriate therapy and will help to prevent
    transmission of M. tuberculosis to patients and other HCWs.
  • the principles of drug therapy for active TB
  • the importance of notifying the facility if the HCW is diagnosed with active TB so that contact investigation procedures can be initiated
  • the responsibilities of the facility to maintain the confidentiality of the HCW while
    ensuring that the HCW who has TB receives appropriate therapy and is non-
    infectious before returning to duty
  • the higher risks associated with TB infection in persons who have HIV infection or
    other causes of severely impaired cell-mediated immunity, including (a) the more
    frequent and rapid development of clinical TB after infection with M. tuberculosis, (b)
    the differences in the clinical presentation of disease and (c) the high mortality rate associated with multiple drug resistant-TB in such persons
  • the potential development of cutaneous anergy as immune function (as measured by CD4+ T-lymphocyte counts) declines
  • information regarding the efficacy and safety of BCG vaccination and the principles of PPD screening among BCG recipients
  • the facility’s policy on voluntary work reassignment options for immunocompromised HCWs.

 

10.    Developing and implementing a programme for routine periodic counselling and screening of HCWs for active TB and latent TB infection. A TB counselling, screening and prevention programme for HCWs should be established to protect both HCWs and patients. HCWs who have positive PPD test results, PPD test conversions or symptoms suggestive of TB should be identified, evaluated to rule out a diagnosis of active TB and started on therapy or preventive therapy if indicated. In addition, the results of the HCW PPD screening programme will contribute to evaluation of the effectiveness of current infection-control practices. Because of the increased risk for rapid progression from latent TB infection to active TB in human immunodeficiency virus, HIV-infected or otherwise severely immunocompromised persons, all HCWs should know if they have a medical condition or are receiving a medical treatment that may lead to severely impaired cell-mediated immunity. HCWs who may be at risk for HIV infection should know their HIV status (i.e., they should be encouraged to voluntarily seek counselling and testing for HIV antibody status). Existing guidelines for counselling and testing should be followed routinely. Knowledge of these conditions allows the HCW to seek the appropriate preventive measures and to consider voluntary work reassignments.

11.    ll HCWs should be informed about the need to follow existing recommendations for infection control to minimize the risk for exposure to infectious agents; implementation of these recommendations will greatly reduce the risk for occupational infections among HCWs. All HCWs should also be informed about the potential risks to severely immunocompromised persons associated with caring for patients who have some infectious diseases, including TB. It should be emphasized that limiting exposure to TB patients is the most protective measure that severely immunosuppressed HCWs can take to avoid becoming infected with M. tuberculosis. HCWs who have severely impaired cell-mediated immunity and who may be exposed to M. tuberculosis may consider a change in job-setting to avoid such exposure. HCWs should be advised of the legal option in many jurisdictions that severely immunocompromised HCWs can choose to transfer voluntarily to areas and work activities in which there is the lowest possible risk for exposure to M. tuberculosis. This choice should be a personal decision for HCWs after they have been informed of the risks to their health.

12.    Employers should make reasonable accommodations (e.g., alternative job assignments) for employees who have a health condition that compromises cell-mediated immunity and who work in settings where they may be exposed to M. tuberculosis. HCWs who are known to be immunocompromised should be referred to employee health professionals who can individually counsel the employees regarding their risk for TB. Upon the request of the immunocompromised HCW, employers should offer, but not compel, a work setting in which the HCW would have the lowest possible risk for occupational exposure to M. tuberculosis.

13.    All HCWs should be informed that immunosuppressed HCWs should have appropriate follow-up and screening for infectious diseases, including TB, provided by their medical practitioner. HCWs who are known to be HIV-infected or otherwise severely immunosuppressed should be tested for cutaneous anergy at the time of PPD testing. Consideration should be given to retesting, at least every 6 months, those immunocompromised HCWs who are potentially exposed to M. tuberculosis because of the high risk for rapid progression to active TB if they become infected.

14.    Information provided by HCWs regarding their immune status should be treated confidentially. If the HCW requests voluntary job reassignment, the privacy of the HCW should be maintained. Facilities should have written procedures on confidential handling of such information.

15.    Promptly evaluating possible episodes of M. tuberculosis transmission in health care facilities, including PPD skin-test conversions among HCWs, epidemiologically associated cases among HCWs or patients and contacts of patients or HCWs who have TB and who were not promptly identified and isolated. Epidemiological investigations may be indicated for several situations. These include, but are not limited to, the occurrence of PPD test conversions or active TB in HCWs, the occurrence of possible person-to-person transmission of M. tuberculosis and situations in which patients or HCWs with active TB are not promptly identified and isolated, thus exposing other persons in the facility to M. tuberculosis. The general objectives of the epidemiological investigations in these situations are as follows:

  • to determine the likelihood that transmission of and infection with M. tuberculosis has occurred in the facility
  • to determine the extent to which M. tuberculosis has been transmitted
  • to identify those persons who have been exposed and infected, enabling them to receive appropriate clinical management
  • to identify factors that could have contributed to transmission and infection and to implement appropriate interventions
  • to evaluate the effectiveness of any interventions that are implemented and to ensure that exposure to and transmission of M. tuberculosis have been terminated.

 

16.    Coordinating activities with the local public health department, emphasizing reporting and ensuring adequate   discharge follow-up and the continuation and completion of therapy. As soon as a patient or HCW is known or suspected to have active TB, the patient or HCW should be reported to the public health department so that appropriate follow-up can be arranged and a community contact investigation can be performed. The health department should be notified well before patient discharge to facilitate follow-up and continuation of therapy. A discharge plan coordinated with the patient or HCW, the health department and the inpatient facility should be implemented.

 

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Prevention of occupational transmission of bloodborne pathogens (BBP) including the human immunodeficiency virus (HIV), hepatitis B virus (HBV) and more recently hepatitis C virus (HCV), has received significant attention. Although HCWs are the primary occupational group at risk of acquisition of infection, any worker who is exposed to blood or other potentially infectious body fluids during the performance of job duties is at risk. Populations at risk for occupational exposure to BBP include workers in health care delivery, public safety and emergency response workers and others such as laboratory researchers and morticians. The potential for occupational transmission of bloodborne pathogens including HIV will continue to increase as the number of persons who have HIV and other bloodborne infections and require medical care increases.

In the US, the Centers for Disease Control and Prevention (CDC) recommended in 1982 and 1983 that patients with the acquired immunodeficiency syndrome (AIDS) be treated according to the (now obsolete) category of “blood and body fluid precautions” (CDC 1982; CDC 1983). Documentation that HIV, the causative agent of AIDS, had been transmitted to HCWs by percutaneous and mucocutaneous exposures to HIV-infected blood, as well as the realization that the HIV infection status of most patients or blood specimens encountered by HCWs would be unknown at the time of the encounter, led CDC to recommend that blood and body fluid precautions be applied to all patients, a concept known as “universal precautions” (CDC 1987a, 1987b). The use of universal precautions eliminates the need to identify patients with bloodborne infections, but is not intended to replace general infection control practices. Universal precautions include the use of handwashing, protective barriers (e.g., goggles, gloves, gowns and face protection) when blood contact is anticipated and care in the use and disposal of needles and other sharp instruments in all health care settings. Also, instruments and other reusable equipment used in performing invasive procedures should be appropriately disinfected or sterilized (CDC 1988a, 1988b). Subsequent CDC recommendations have addressed prevention of transmission of HIV and HBV to public safety and emergency responders (CDC 1988b), management of occupational exposure to HIV, including the recommendations for the use of zidovudine (CDC 1990), immunization against HBV and management of HBV exposure (CDC 1991a), infection control in dentistry (CDC 1993) and the prevention of HIV transmission from HCWs to patients during invasive procedures (CDC 1991b).

In the US, CDC recommendations do not have the force of law, but have often served as the foundation for government regulations and voluntary actions by industry. The Occupational Health and Safety Administration (OSHA), a federal regulatory agency, promulgated a standard in 1991 on Occupational Exposure to Bloodborne Pathogens (OSHA 1991). OSHA concluded that a combination of engineering and work practice controls, personal protective clothing and equipment, training, medical surveillance, signs and labels and other provisions can help to minimize or eliminate exposure to bloodborne pathogens. The standard also mandated that employers make available hepatitis B vaccination to their employees.

The World Health Organization (WHO) has also published guidelines and recommendations pertaining to AIDS and the workplace (WHO 1990, 1991). In 1990, the European Economic Council (EEC) issued a council directive (90/679/EEC) on protection of workers from risks related to exposure to biological agents at work. The directive requires employers to conduct an assessment of the risks to the health and safety of the worker. A distinction is drawn between activities where there is a deliberate intention to work with or use biological agents (e.g., laboratories) and activities where exposure is incidental (e.g., patient care). Control of risk is based on a hierarchical system of procedures. Special containment measures, according to the classification of the agents, are set out for certain types of health facilities and laboratories (McCloy 1994). In the US, CDC and the National Institutes of Health also have specific recommendations for laboratories (CDC 1993b).

Since the identification of HIV as a BBP, knowledge about HBV transmission has been helpful as a model for understanding modes of transmission of HIV. Both viruses are transmitted via sexual, perinatal and bloodborne routes. HBV is present in the blood of individuals positive for hepatitis B e antigen (HBeAg, a marker for high infectivity) at a concentration of approximately 108 to 109 viral particles per millilitre (ml) of blood (CDC 1988b). HIV is present in blood at much lower concentrations: 103 to 104 viral particles/ml for a person with AIDS and 10 to 100/ml for a person with asymptomatic HIV infection (Ho, Moudgil and Alam 1989). The risk of HBV transmission to a HCW after percutaneous exposure to HBeAg-positive blood is approximately 100-fold higher than the risk of HIV transmission after percutaneous exposure to HIV-infected blood (i.e., 30% versus 0.3%) (CDC 1989).

Hepatitis

Hepatitis, or inflammation of the liver, can be caused by a variety of agents, including toxins, drugs, autoimmune disease and infectious agents. Viruses are the most common cause of hepatitis (Benenson 1990). Three types of bloodborne viral hepatitis have been recognized: hepatitis B, formerly called serum hepatitis, the major risk to HCWs; hepatitis C, the major cause of parenterally transmitted non-A, non-B hepatitis; and hepatitis D, or delta hepatitis.

Hepatitis B. The major infectious bloodborne occupational hazard to HCWs is HBV. Among US HCWs with frequent exposure to blood, the prevalence of serological evidence of HBV infection ranges between approximately 15 and 30%. In contrast, the prevalence in the general populations averages 5%. The cost-effectiveness of serological screening to detect susceptible individuals among HCWs depends on the prevalence of infection, the cost of testing and the vaccine costs. Vaccination of persons who already have antibodies to HBV has not been shown to cause adverse effects. Hepatitis B vaccine provides protection against hepatitis B for at least 12 years after vaccination; booster doses currently are not recommended. The CDC estimated that in 1991 there were approximately 5,100 occupationally acquired HBV infections in HCWs in the United States, causing 1,275 to 2,550 cases of clinical acute hepatitis, 250 hospitalizations and about 100 deaths (unpublished CDC data). In 1991, approximately 500 HCWs became HBV carriers. These individuals are at risk of long-term sequelae, including disabling chronic liver disease, cirrhosis and liver cancer.

The HBV vaccine is recommended for use in HCWs and public safety workers who may be exposed to blood in the workplace (CDC 1991b). Following a percutaneous exposure to blood, the decision to provide prophylaxis must include considerations of several factors: whether the source of the blood is available, the HBsAg status of the source and the hepatitis B vaccination and vaccine-response status of the exposed person. For any exposure of a person not previously vaccinated, hepatitis B vaccination is recommended. When indicated, hepatitis B immune globulin (HBIG) should be administered as soon as possible after exposure since its value beyond 7 days after exposure is unclear. Specific CDC recommendations are indicated in table 1 (CDC 1991b).

Table 1. Recommendation for post-exposure prophylaxis for percutaneous or permucosal exposure to hepatitis B virus, United States

Exposed person

When source is

 

HBsAg1 positive

HBsAg negative

Source not tested or
unknown

Unvaccinated

HBIG2´1 and initiate
HB vaccine3

Initiate HB vaccine

Initiate HB vaccine

Previously
vaccinated

Known
responder

No treatment

No treatment

No treatment

Known non-
responder

HBIG´2 or HBIG´1 and
initiate revaccination

No treatment

If known high-risk source
treat as if source were
HBsAg positive

Response
unknown

Test exposed for anti-HBs4
1. If adequate5, no
treatment
2. If inadequate, HBIGx1
and vaccine booster

No treatment

Test exposed for anti-HBs
1. If adequate, no
treatment
2. If inadequate, vaccine
booster

1 HBsAg = Hepatitis B surface antigen. 2 HBIG = Hepatitis B immune globulin; dose 0.06 mL/kg IM. 3 HB vaccine = hepatitis B vaccine.  4 Anti-HBs = antibody to hepatitis B surface antigen. 5 Adequate anti-HBs is ≥10 mIU/mL.

Table 2. Provisional US Public Health Service recommendations for chemoprophylaxis after occupational exposure to HIV, by type of exposure and source of material, 1996

Type of exposure

Source material1

Antiretroviral
prophylaxis2

Antiretroviral regimen3

Percutaneous

Blood
Highest risk4
Increased risk4
No increased risk4
Fluid containing
visible blood, other
potentially infectious
fluid6, or tissue
Other body fluid
(e.g., urine)


Recommend
Recommend
Offer
Offer
Not offer


ZDV plus 3TC plus IDV
ZDV plus 3TC, ± IDV5
ZDV plus 3TC
ZDV plus 3TC

Mucous membrane

Blood
Fluid containing
visible blood, other
potentially infectious
fluid6, or tissue
Other body fluid
(e.g., urine)

Offer
Offer
Not offer

ZDV plus 3TC, ± IDV5
ZDV, ± 3TC5

Skin, increased risk7

Blood
Fluid containing
visible blood, other
potentially infectious
fluid6 , or tissue
Other body fluid
(e.g., urine)

Offer
Offer
Not offer

ZDV plus 3TC, ± IDV5
ZDV, ± 3TC5

1 Any exposure to concentrated HIV (e.g., in a research laboratory or production facility) is treated as percutaneous exposure to blood with highest risk.  2 Recommend—Postexposure prophylaxis (PEP) should be recommended to the exposed worker with counselling. Offer—PEP should be offered to the exposed worker with counselling. Not offer—PEP should not be offered because these are not occupational exposures to HIV.  3 Regimens: zidovudine (ZDV), 200 mg three times a day; lamivudine (3TC), 150 mg two times a day; indinavir (IDV), 800 mg three times a day (if IDV is not available, saquinavir may be used, 600 mg three times a day). Prophylaxis is given for 4 weeks. For full prescribing information, see package inserts. 4 Risk definitions for percutaneous blood exposure: Highest risk—BOTH larger volume of blood (e.g., deep injury with large diameter hollow needle previously in source patient’s vein or artery, especially involving an injection of source-patient’s blood) AND blood containing a high titre of HIV (e.g., source with acute retroviral illness or end-stage AIDS; viral load measurement may be considered, but its use in relation to PEP has not been evaluated). Increased risk—EITHER exposure to larger volume of blood OR blood with a high titre of HIV. No increased risk—NEITHER exposure to larger volume of blood NOR blood with a high titre of HIV (e.g., solid suture needle injury from source patient with asymptomatic HIV infection).  5 Possible toxicity of additional drug may not be warranted. 6 Includes semen; vaginal secretions; cerebrospinal, synovial, pleural, peritoneal, pericardial and amniotic fluids.  7 For skin, risk is increased for exposures involving a high titre of HIV, prolonged contact, an extensive area, or an area in which skin integrity is visibly compromised. For skin exposures without increased risk, the risk for drug toxicity outweighs the benefit of PEP.

Article 14(3) of EEC Directive 89/391/EEC on vaccination required only that effective vaccines, where they exist, be made available for exposed workers who are not already immune. There was an amending Directive 93/88/EEC which contained a recommended code of practice requiring that workers at risk be offered vaccination free of charge, informed of the benefits and disadvantages of vaccination and non-vaccination, and be provided a certificate of vaccination (WHO 1990).

The use of hepatitis B vaccine and appropriate environmental controls will prevent almost all occupational HBV infections. Reducing blood exposure and minimizing puncture injuries in the health care setting will reduce also the risk of transmission of other bloodborne viruses.

Hepatitis C. Transmission of HCV is similar to that of HBV, but infection persists in most patients indefinitely and more frequently progresses to long-term sequelae (Alter et al. 1992). The prevalence of anti-HCV among US hospital-based health care workers averages 1 to 2% (Alter 1993). HCWs who sustain accidental injuries from needlesticks contaminated with anti-HCV-positive blood have a 5 to 10% risk of acquiring HCV infection (Lampher et al. 1994; Mitsui et al. 1992). There has been one report of HCV transmission after a blood splash to the conjunctiva (Sartori et al. 1993). Prevention measures again consist of adherence to universal precautions and percutaneous injury prevention, since no vaccine is available and immune globulin does not appear to be effective.

Hepatitis D. Hepatitis D virus requires the presence of hepatitis B virus for replication; thus, HDV can infect persons only as a coinfection with acute HBV or as a superinfection of chronic HBV infection. HDV infection can increase the severity of liver disease; one case of occupationally acquired HDV infection hepatitis has been reported (Lettau et al. 1986). Hepatitis B vaccination of HBV-susceptible persons will also prevent HDV infection; however, there is no vaccine to prevent HDV superinfection of an HBV carrier. Other prevention measures consist of adherence to universal precautions and percutaneous injury prevention.

HIV

The first cases of AIDS were recognized in June of 1981. Initially, over 92% of the cases reported in the United States were in homosexual or bisexual men. However, by the end of 1982, AIDS cases were identified among injection drug users, blood transfusion recipients, haemophilia patients treated with clotting factor concentrates, children and Haitians. AIDS is the result of infection with HIV, which was isolated in 1985. HIV has spread rapidly. In the United States, for example, the first 100,000 AIDS cases occurred between 1981 and 1989; the second 100,000 cases occurred between 1989 and 1991. As of June 1994, 401,749 cases of AIDS had been reported in the United States (CDC 1994b).

Globally, HIV has affected many countries including those in Africa, Asia and Europe. As of 31 December 1994, 1,025,073 cumulative cases of AIDS in adults and children had been reported to the WHO. This represented a 20% increase from the 851,628 cases reported through December 1993. It was estimated that 18 million adults and about 1.5 million children have been infected with HIV since the beginning of the pandemic (late 1970s to early 1980s) (WHO 1995).

Although HIV has been isolated from human blood, breast milk, vaginal secretions, semen, saliva, tears, urine, cerebrospinal fluid and amniotic fluid, epidemiological evidence has implicated only blood, semen, vaginal secretions and breast milk in the transmission of the virus. The CDC has also reported on the transmission of HIV as the result of contact with blood or other body secretions or excretions from an HIV-infected person in the household (CDC 1994c). Documented modes of occupational HIV transmission include having percutaneous or mucocutaneous contact with HIV-infected blood. Exposure by the percutaneous route is more likely to result in infection transmission than is mucocutaneous contact.

There are a number of factors which may influence the likelihood of occupational bloodborne pathogen transmission, including: the volume of fluid in the exposure, the virus titre, the length of time of the exposure and the immune status of the worker. Additional data are needed to determine precisely the importance of these factors. Preliminary data from a CDC case-control study indicate that for percutaneous exposures to HIV-infected blood, HIV transmission is more likely if the source patient has advanced HIV disease and if the exposure involves a larger inoculum of blood (e.g., injury due to a large-bore hollow needle) (Cardo et al. 1995). Virus titre can vary between individuals and over time within a single individual. Also, blood from persons with AIDS, particularly in the terminal stages, may be more infectious than blood from persons in earlier stages of HIV infection, except possibly during the illness associated with acute infection (Cardo et al. 1995).

Occupational exposure and HIV infection

As of December 1996, CDC reported 52 HCWs in the United States who have seroconverted to HIV following a documented occupational exposure to HIV, including 19 laboratory workers, 21 nurses, six physicians and six in other occupations. Forty-five of the 52 HCWs sustained percutaneous exposures, five had mucocutaneous exposures, one had both a percutaneous and a mucocutaneous exposure and one had an unknown route of exposure. In addition, 111 possible cases of occupationally acquired infection have been reported. These possible cases have been investigated and are without identifiable non-occupational or transfusion risks; each reported percutaneous or mucocutaneous occupational exposures to blood or body fluids, or laboratory solutions containing HIV, but HIV seroconversion specifically resulting from an occupational exposure was not documented (CDC 1996a).

In 1993, the AIDS Centre at the Communicable Disease Surveillance Centre (UK) summarized reports of cases of occupational HIV transmission including 37 in the United States, four in the UK and 23 from other countries (France, Italy, Spain, Australia, South Africa, Germany and Belgium) for a total of 64 documented seroconversions after a specific occupational exposure. In the possible or presumed category there were 78 in the United States, six in the UK and 35 from other countries (France, Italy, Spain, Australia, South Africa, Germany, Mexico, Denmark, Netherlands, Canada and Belgium) for a total of 118 (Heptonstall, Porter and Gill 1993). The number of reported occupationally acquired HIV infections is likely to represent only a portion of the actual number due to under-reporting and other factors.

HIV post-exposure management

Employers should make available to workers a system for promptly initiating evaluation, counselling and follow-up after a reported occupational exposure that may place a worker at risk of acquiring HIV infection. Workers should be educated and encouraged to report exposures immediately after they occur so that appropriate interventions can be implemented (CDC 1990).

If an exposure occurs, the circumstances should be recorded in the worker’s confidential medical record. Relevant information includes the following: date and time of exposure; job duty or task being performed at the time of exposure; details of exposure; description of source of exposure, including, if known, whether the source material contained HIV or HBV; and details about counselling, post-exposure management and follow-up. The source individual should be informed of the incident and, if consent is obtained, tested for serological evidence of HIV infection. If consent cannot be obtained, policies should be developed for testing source individuals in compliance with applicable regulations. Confidentiality of the source individual should be maintained at all times.

If the source individual has AIDS, is known to be HIV seropositive, refuses testing or the HIV status is unknown, the worker should be evaluated clinically and serologically for evidence of HIV infection as soon as possible after the exposure (baseline) and, if seronegative, should be retested periodically for a minimum of 6 months after exposure (e.g., six weeks, 12 weeks and six months after exposure) to determine whether HIV infection has occurred. The worker should be advised to report and seek medical evaluation for any acute illness that occurs during the follow-up period. During the follow-up period, especially the first six to 12 weeks after the exposure, exposed workers should be advised to refrain from blood, semen or organ donation and to abstain from, or use measures to prevent HIV transmission, during sexual intercourse.

In 1990, CDC published a statement on the management of exposure to HIV including considerations regarding zidovudine (ZDV) post-exposure use. After a careful review of the available data, CDC stated that the efficacy of zidovudine could not be assessed due to insufficient data, including available animal and human data (CDC 1990).

In 1996, information suggesting that ZDV post-exposure prophylaxis (PEP) may reduce the risk for HIV transmission after occupational exposure to HIV-infected blood (CDC 1996a) prompted a US Public Health Service (PHS) to update a previous PHS statement on management of occupational exposure to HIV with the following findings and recommendations on PEP (CDC 1996b). Although failures of ZDV PEP have occurred (Tokars et al. 1993), ZDV PEP was associated with a decrease of approximately 79% in the risk for HIV seroconversion after percutaneous exposure to HIV-infected blood in a case-control study among HCWs (CDC 1995).

Although information about the potency and toxicity of antiretroviral drugs is available from studies of HIV-infected patients, it is uncertain to what extent this information can be applied to uninfected persons receiving PEP. In HIV-infected patients, combination therapy with the nucleosides ZDV and lamivudine (3TC) has greater antiretroviral activity than ZDV alone and is active against many ZDV-resistant HIV strains without significantly increased toxicity (Anon. 1996). Adding a protease inhibitor provides even greater increases in antiretroviral activity; among protease inhibitors, indinavir (IDV) is more potent than saquinavir at currently recommended doses and appears to have fewer drug interactions and short-term adverse effects than ritonavir (Niu, Stein and Schnittmann 1993). Few data exist to assess possible long-term (i.e., delayed) toxicity resulting from use of these drugs in persons not infected with HIV.

The following PHS recommendations are provisional because they are based on limited data regarding efficacy and toxicity of PEP and risk for HIV infection after different types of exposure. Because most occupational exposures to HIV do not result in infection transmission, potential toxicity must be carefully considered when prescribing PEP. Changes in drug regimens may be appropriate, based on factors such as the probable antiretroviral drug resistance profile of HIV from the source patient, local availability of drugs and medical conditions, concurrent drug therapy and drug toxicity in the exposed worker. If PEP is used, drug-toxicity monitoring should include a complete blood count and renal and hepatic chemical function tests at baseline and two weeks after starting PEP. If subjective or objective toxicity is noted, drug reduction or drug substitution should be considered, and further diagnostic studies may be indicated.

Chemoprophylaxis should be recommended to exposed workers after occupational exposures associated with the highest risk for HIV transmission. For exposures with a lower, but non-negligible risk, PEP should be offered, balancing the lower risk against the use of drugs having uncertain efficacy and toxicity. For exposures with negligible risk, PEP is not justified (see table 2 ). Exposed workers should be informed that knowledge about the efficacy and toxicity of PEP is limited, that for agents other than ZDV, data are limited regarding toxicity in persons without HIV infection or who are pregnant and that any or all drugs for PEP may be declined by the exposed worker.

PEP should be initiated promptly, preferably with 1 to 2 hours post-exposure. Although animal studies suggest that PEP probably is not effective when started later than 24 to 36 hours post-exposure (Niu, Stein and Schnittmann 1993; Gerberding 1995), the interval after which there is no benefit from PEP for humans is undefined. Initiating therapy after a longer interval (e.g., 1 to 2 weeks) may be considered for the highest risk exposures; even if infection is not prevented, early treatment of acute HIV infection may be beneficial (Kinloch-de-los et al. 1995).

If the source patient or the patient’s HIV status is unknown, initiating PEP should be decided on a case-by-case basis, based on the exposure risk and likelihood of infection in known or possible source patients.

Other Bloodborne Pathogens

Syphilis, malaria, babesiosis, brucellosis, leptospirosis, arboviral infections, relapsing fever, Creutzfeldt-Jakob disease, human T-lymphotropic virus type 1 and viral haemorrhagic fever have also been transmitted by the bloodborne route (CDC 1988a; Benenson 1990). Occupational transmission of these agents has only rarely been recorded, if ever.

Prevention of Transmission of Bloodborne Pathogens

There are several basic strategies which relate to the prevention of occupational transmission of bloodborne pathogens. Exposure prevention, the mainstay of occupational health, can be accomplished by substitution (e.g., replacing an unsafe device with a safer one), engineering controls (i.e., controls that isolate or remove the hazard), administrative controls (e.g., prohibiting recapping of needles by a two-handed technique) and use of personal protective equipment. The first choice is to “engineer out the problem”.

In order to reduce exposures to bloodborne pathogens, adherence to general infection control principles, as well as strict compliance with universal precaution guidelines, is required. Important components of universal precautions include the use of appropriate personal protective equipment, such as gloves, gowns and eye protection, when exposure to potentially infectious body fluids is anticipated. Gloves are one of the most important barriers between the worker and the infectious material. While they do not prevent needlesticks, protection for the skin is provided. Gloves should be worn when contact with blood or body fluids is anticipated. Washing of gloves in not recommended. Recommendations also advise workers to take precautions to prevent injuries by needles, scalpels and other sharp instruments or devices during procedures; when cleaning used instruments; during disposal of used needles; and when handling sharp instruments after procedures.

Percutaneous exposures to blood

Since the major risk of infection results from parenteral exposure from sharp instruments such as syringe needles, engineering controls such as resheathing needles, needleless IV systems, blunt suture needles and appropriate selection and use of sharps disposal containers to minimize exposures to percutaneous injuries are critical components of universal precautions.

The most common type of percutaneous inoculation occurs through inadvertent needlestick injury, many of which are associated with recapping of needles. The following reasons have been indicated by workers as reasons for recapping: inability to properly dispose of needles immediately, sharps disposal containers too far away, lack of time, dexterity problems and patient interaction.

Needles and other sharp devices can be redesigned to prevent a significant proportion of percutaneous exposures. A fixed barrier should be provided between hands and the needle after use. Worker’s hands should remain behind the needle. Any safety feature should be an integral part of the device. The design should be simple and little or no training should be required (Jagger et al. 1988).

Implementing safer needle devices must be accompanied by evaluation. In 1992, the American Hospital Association (AHA) published a briefing to assist hospitals with the selection, evaluation and adoption of safer needle devices (AHA 1992). The briefing stated that “because safer needle devices, unlike drugs and other therapies, do not undergo clinical testing for safety and efficacy before they are marketed, hospitals are essentially ‘on their own’ when it comes to selecting appropriate products for their specific institutional needs”. Included in the AHA document are guidance for the evaluation and adoption of safer needle devices, case studies of the use of safety devices, evaluation forms and listing of some, but not all, products on the US market.

Prior to implementation of a new device, health care institutions must ensure that there is an appropriate needlestick surveillance system in place. In order to accurately assess the efficacy of new devices, the number of reported exposures should be expressed as an incidence rate.

Possible denominators for reporting the number of needlestick injuries include patient days, hours worked, number of devices purchased, number of devices used and number of procedures performed. The collection of specific information on device-related injuries is an important component of the evaluation of the effectiveness of a new device. Factors to be considered in collecting information on needlestick injuries include: new product distribution, stocking and tracking; identification of users; removal of other devices; compatibility with other devices (especially IV equipment); ease of use; and mechanical failure. Factors which may contribute to bias include compliance, subject selection, procedures, recall, contamination, reporting and follow-up. Possible outcome measures include rates of needlestick injuries, HCW compliance, patient care complications and cost.

Finally, training and feedback from workers are important components of any successful needlestick prevention programme. User acceptance is a critical factor, but one that seldom receives enough attention.

Elimination or reduction of percutaneous injuries should result if adequate engineering controls are available. If HCWs, product evaluation committees, administrators and purchasing departments all work together to identify where and what safer devices are needed, safety and cost effectiveness can be combined. Occupational transmission of bloodborne pathogens is costly, both in terms of money and the impact on the employee. Every needlestick injury causes undue stress on the employee and may affect job performance. Referral to mental health professionals for supportive counselling may be required.

In summary, a comprehensive approach to prevention is essential to maintaining a safe and healthy environment in which to provide health care services. Prevention strategies include the use of vaccines, post-exposure prophylaxis and prevention or reduction of needlestick injuries. Prevention of needlestick injuries can be accomplished by improvement in the safety of needle-bearing devices, development of procedures for safer use and disposal and adherence to infection control recommendations.

Acknowledgements: The authors thank Mariam Alter, Lawrence Reed and Barbara Gooch for their manuscript review.

 

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