BackgroundSevere Acute Respiratory Syndrome (SARS) was first described as a new disease in Mar. 2003. Its causative agent is a coronavirus named the SARS-associated coronavirus, SARS CoV. It is generally agreed that the main mode of transmission is from person to person in close proximity. Through outbreaks in Hong Kong SAR, the People's Republic of China, Viet Nam, Singapore and Canada, it rapidly achieved notoriety as a readily transmissible infectious disease with a significant mortality rate (currently estimated at 9.5%) and global economic consequences. The costs incurred by the 2003 outbreaks have been estimated at between US$30 and 150 billion.
At the time of the Consultation (Sept. 2003), the global epidemic was estimated to have resulted in 8,097 cases of clinical illness, with 774 deaths in 27 countries on six continents. There are no reliable estimates of low-severity or asymptomatic infections. In Jul. 2003 the World Health Organization declared the epidemic to have come to an end.
There remain considerable gaps in our understanding of the sources, transmission dynamics and routes of infection of the pathogen. These hamper our full understanding of how the epidemic evolved and, in particular, how and to what extent environmental factors contributed to the propagation of disease. As a result, we lack complete insight into the extent to which environmental control measures could play a role in containing future outbreaks of this disease and diseases caused by other pathogenic micro-organisms with similar routes of transmission. What is clear, however, is that in any outbreak situation effective disease control will be essential to contain and eliminate the epidemic, while preventive environmental measures will help reduce the risk of outbreaks, limit the extent of outbreaks when they occur and enhance the impact of control measures.
Available evidence suggests that SARS CoV originated from animal populations and that intensive human-animal contact was instrumental in its transfer to the human population. Such intensive contacts occur, for example, at marketplaces where live animals are traded and slaughtered. The SARS CoV responsible for the outbreak in humans in 2003 shows slight genetic differences from the virus found in animal populations (also referred to as SARS CoV). The latter appears to be responsible for sero-positivity among animal handlers. At the time of the Consultation, it was unclear whether the circulation of a SARS CoV in human populations had led to establishment of a modified virus in animal reservoirs that may be more infectious or virulent to humans.
This Consensus Statement addresses the risks of transmission of SARS CoV amongst human populations associated with the design and operation of sanitation facilities for the management of human excreta. It does not give further consideration to the transfer of the agent between animal and human populations; this issue is dealt with in another WHO publication under preparation: Water-borne zoonoses: understanding their identification, causes and control.
There is evidence that, once established in human populations, SARS CoV is excreted by symptomatic persons in feces, vomit, respiratory secretions and urine (ranked in the approximate order of quantity of virus shedding). Virus shedding peaks between days 7 and 10 after the onset of symptoms. The most severely affected cases have been associated with especially intense transmission, and have been referred to as "super-transmitters." This status is more likely linked to the innate capacity of the host to mount an immune response than to possible genetic differences between virus strains. Asymptomatic or mild disease appears to have occurred, yet there is no evidence that chronic infections or prolonged asymptomatic carrier states are part of the syndrome.
In most areas, disease transmission during the epidemics has been overwhelmingly across short distances, i.e. less than 1 meter. In a number of well-documented specific cases, however, there is compelling evidence of virus-containing droplets traveling over a longer distance (tens of metres) and leading to human infection. In one outbreak cluster (the Amoy Gardens in Hong Kong) this transmission route was associated with inadequate maintenance of bathroom plumbing and drainage systems combined with inappropriate ventilation of bathrooms. In another, the Metropole Hotel, transmission might have been associated with droplets generated by vomiting (a route that is well recognized in the transmission of other viruses such as norovirus). Data limitations prevent the exact determination of the fraction of transmission attributable to this route in other outbreaks where close-contact spread dominated. These two clusters may be considered important "
ContextSARS and SARS CoV have focused interest on some aspects of links between sewage/sewerage and health. This interest may usefully contribute to furthering the control of health risks associated with inadequate sewerage and especially of pathogenic viruses that are amenable to droplet transmission. Disease transmission via sewage droplets is, in general, likely to be a small but significant contributor to the overall burden of sewage-related disease (which includes disease associated with environmental contamination with untreated or under-treated sewage/excreta, as well as its introduction into the domestic environment). A large part of the burden of disease associated with inadequate water, sanitation and hygiene (an estimated 2,213,000 deaths and 82,196,000 DALYs lost annually) is borne by populations in developing countries (children in particular), with the lack of access to adequate sanitation a major determinant (Pruess et al., 2002). Approximately 1.9 billion people or 31% of the global population use water-based sanitation, both in developed and developing countries (WHO/UNICEF, 2000).
Underlying trends--most importantly population growth, urbanization, increasing affluence and a general preference for water-borne sanitation--suggest that the total population exposed to sewage/sewerage-related risks will increase in numbers and as a proportion of the total global population.
The majority of the world's population uses some form of dry sanitation, and this dominates amongst the rural poor and poor populations in peri-urban and slum areas of cities in developing countries. There is insufficient evidence, however, to support meaningful statements on the risk of SARS transmission through the environment in areas with dry sanitation; it appears that the principal environmental risk is associated with water-borne sanitation.
Lessons LearnedThere is limited reliable information available concerning SARS CoV. There is a need, therefore, to combine information from different sources in order to arrive at useful conclusions. Relevant sources of information include our knowledge and experience with other viruses known to be transmitted via the fecal droplet route; it also includes our knowledge of the characteristics and behavior of virus particles, experience with other droplet or aerosol-transmitted infections such as legionellosis and validated mathematical models that allow a systematic analysis and synthesis of all available information.
Sources, Transmission and Routes of InfectionIt can be reasonably assumed that, in general, in the 2003 SARS outbreaks more than one source-transmission-exposure combination contributed to the total disease outcome. It is therefore appropriate to consider all reasonably credible routes and to assess the controls acting on them.
The principal sources of human derived SARS CoV in the built environment appear to be respiratory secretions, human excreta (feces and urine) and vomitus. The role of animal-human exchange is recognised but not considered here.
The principal potential transmission routes for SARS CoV in the environment include droplets and aerosols generated from secretions and excreta, sewage and perhaps vectors. These routes may interact with one another--droplet deposition on surfaces is an example.
Plausible routes of infection include inhalation and mucosal/conjunctival contact--the latter especially through hand contact. Available evidence does not support ingestion as a route of infection.
Objectives and Control MeasuresControl of transmission of SARS CoV (and of viruses with related transmission patterns) in human populations depends on interrupting source-transmission-infection route combinations. In connection with fecal droplet transmission, four principal objectives are:
To effectively remove suspended fecal droplets containing viruses from the built environment;
To prevent (re-)entry of fecal droplets (from sewage) to the human/built environment;
To minimize inhalation of air from occupied rooms;
To remove virus contamination from (human contact) surfaces (i.e. cleaning);
To prevent entry of fecal droplets from sewage into the human/built environment.
Principal barriers include effective sealing of all connections to sewerage from the dwelling. Water seals in toilets are highly effective, but leaks enabling droplets to escape may occur in pipes routing through buildings and from vent stacks without evidence of liquid leakage and are a matter of concern. Pressure differences caused by ventilation or air-conditioning between rooms or between the inside and outside of an apartment may exacerbate the risks associated with such leaks. Whenever possible, venting systems should be free of mechanical devices.
Suspended droplets containing virus may arise in the built environment from a variety of sources in addition to excreta/sewage droplet formation. These include respiratory secretions and vomitus. The role of these in disease transmission has been highlighted for other viruses (e.g. Norovirus). There is a generic set of interventions that is effective against droplets regardless of source. These will contribute to the interruption of transmission and are of concern primarily in environments where virus-containing droplets are most likely to be generated. This focuses attention on healthcare facilities and toilets/bathrooms. Removal of potentially virus-containing droplets from the built environment must be accompanied by measures to ensure that the exhausted droplets are not then reintroduced to the built environment. This phenomenon appears to have played a critical role in the Amoy Gardens outbreak. In this connection, a number of effective building design and management measures can be readily identified, such as vertical separation of vents and separating inlet from outlet vents. Some of these measures may be costly, and there is generally little evidence to define exact standards for design parameters. This area has been identified as a research priority. While lessons may be learned from experience with legionellosis outbreaks, virions are about one hundredth the size of Legionella bacteria and could therefore behave differently under similar conditions. In high risk settings, such as healthcare facilities with symptomatic individuals, it may be appropriate to treat exhaust air to reduce the potential viral load, e.g. through heat, filtration and/or impact. The extent to which these control measures would be effective in reducing viral load is, however, still inadequately understood and requires further investigation.
The importance of inhalation of (potentially virus-contaminated) air exhausted from rooms will depend on infectious virus loads and therefore prevailing sources and environmental conditions. Air originating from toilets/bathrooms used by and other spaces occupied by symptomatic persons is of specific concern. Limited evidence suggests that this mechanism has contributed to SARS CoV transmission in some circumstances, and it is likely to be relevant for several other viruses. The principal prevention and control measures include re-entrant and light well design, separation of inlet and outlets to and from built environments and effective dispersal of exhaust air. The building and design specifications are to be supported by regular sanitary inspection and proper maintenance, and by cleaning and disinfection of installations.
Surfaces may be contaminated by viruses through droplet deposition, contact with infected persons and through vectors and fomites. Such viruses become a cause of health concern when carried to a site of infection; apparently transmission by hand contact from contaminated surfaces to, for example, conjunctivae is of particular importance. Measures described above will contribute to minimising droplet presence in the built environment and general vector/vermin control will further contribute to minimizing contamination and pathogen spread. Of primary importance, however, is surface cleaning (and where appropriate disinfection). Moreover, such hygiene measures contribute to the control of a variety of pathogens causing gastrointestinal and respiratory infections. Control of infection arising from surface contamination also depends significantly on personal hygiene behaviour. Uninterrupted access to water in sufficient quantities for hygiene purposes is necessary for effective control of a wide range of infections including interruption of SARS transmission from surfaces to sites of infection.
SettingsThe selection of appropriate control measures will depend on the settings in which they are to be applied. The principal settings of interest include the health care environment (including residential care) and multi-story residential accommodation (which, for all practical purposes, also reflects the concerns over other multi-story buildings). Local or national characteristics, such as cultural practices, will also determine which control measures are likely to be effective and feasible to implement. The development of control strategies should take full account of these. Where public health policies prescribe the isolation of potential SARS patients in residential settings, consideration must be given to applying prevention and control measures designed for health care setting to affected household settings, as appropriate.
In the countries affected by SARS in 2003, infections acquired in health care settings figured significantly and health care workers constituted an important vulnerable group. Some association has been reported between the implementation of procedures involving the generation of infectious droplets and transmission risk, but there are insufficient data to verify and firmly establish the fraction of risk attributable to this mode of transmission as compared to the predominant close-range spread. In health care settings aspects of concern include sluice rooms, the handling of soiled surfaces and linen, the ventilation of toilets and bathrooms (including the proximity of ventilation outlets to air intakes including windows) and the role of humidifiers in droplet transmission. Training and explicit infection control strategies (including "
Effective Supportive Regulation and Good PracticeMany of the interventions/controls that will contribute to the reduction or elimination of the spread of virus-laden droplets are long term in nature. Their deployment is best achieved through interventions in design, construction, operation, licensing and certification, and these are important components of overall national strategies.
Design interventions center upon review of designs for compliance with health-based regulations and standards, and subsequent approval. This procedure is supported by the existence of regulations and standards and by the inclusion of disease control in the training of architects and engineers.
In many countries there are procedures for building inspection at various stages of construction or rehabilitation, as well as at final commissioning. These provide opportunities to ensure that construction work has complied with design and followed health-based regulations and standards. Such procedures are supported by the existence of corresponding regulations and standards and by the existence of appropriately trained professionals charged with conducting the inspections.
Responsibility for building safety should be assigned to a specified authority (e.g. owner, manager) under appropriate legislation. While specific arrangements will respond to local/national circumstances, it would normally be appropriate for public and multi-occupancy buildings to require a declared "
Priority Research Issues for Effective ManagementA limited number of issues were identified where targeted research is necessary to provide information of immediate relevance to increasing the effectiveness of controls and minimising likelihood of costly over-engineering:
The degree of separation between air inlet and outlet structures and vertical separation to sewer vents or building exhausts may be usefully studied through air movement modelling combined with information on pathogen infectivity. The costs associated with amending guidance on this could be significant and research could contribute to rapidly refining standards of good practice appropriate for health protection
It is unclear whether the presence or use of toilet lids contributes to or reduces overall risk. It is not relevant in cultures where squat plates are used and in some countries lids are discouraged in public buildings. Given the risk of droplet generation by the act of toilet flushing insight into designs or measures that would reduce this and/or minimise dispersal of droplets would provide useful clarification.
Research into disease transmission through virus-contaminated droplets has been very limited and simple questions such as the range over which droplets from a flushed toilet spread and deposit remain unclear.
Much of the available information concerning SARS CoV and indeed concerning other viruses transmitted through droplets is qualitative in nature (e.g. infectivity, inactivation), and this inhibits the application of quantitative methods to assess the effectiveness of actual and potential control measures.
The pros and cons of toilet bowl disinfection by means of additives to flush water and its potential contribution to reducing droplet infectivity would merit research because it is frequently advocated without a clear and reliable evidence base.
ReferencesPruess, A., Kay, D., Fewtrell, L., and Bartram, J. (2002). "Estimating the Burden of Disease from Water, Sanitation and Hygiene at a Global Level," Environmental Health Perspectives 110 (5): 537-542
WHO/UNICEF, 2000. "Global Water Supply and Sanitation Assessment 2000 Report," WHO/UNICEF Joint Monitoring Programme, Geneva/New York.