Sick building syndrome

Last updated
Sick building syndrome
Specialty Environmental medicine, immunology   OOjs UI icon edit-ltr-progressive.svg

Sick building syndrome (SBS) is a condition in which people develop symptoms of illness or become infected with chronic disease from the building in which they work or reside. [1]

Contents

The main identifying observation is an increased incidence of complaints of symptoms such as headache, eye, nose, and throat irritation, fatigue, dizziness, and nausea. The 1989 Oxford English Dictionary defines SBS in that way. [2] The World Health Organization created a 484-page tome on indoor air quality back in 1984 when SBS was attributed only to non-organic causes, and suggested that the book might form a basis for legislation or litigation. [3]

The outbreaks may or may not be a direct result of inadequate or inappropriate cleaning methods. [2] SBS has also been used to describe staff concerns in post-war buildings with misplanned building aerodynamics, defects in the construction materials or assembly process and-or inadequate maintenance. [2] Certain symptoms tend to increase in severity with the time people spend in the building; often improving over time or even disappearing when people are away from the building. [2] [4] SBS is also used interchangeably with "building-related symptoms", which orients the name of the condition around patients' symptoms rather than a "sick" building. [5]

Attempts have been made to connect sick building syndrome to various causes, such as contaminants produced by outgassing of some types of building materials, volatile organic compounds (VOC), improper exhaust ventilation of ozone (byproduct of some office machinery), light industrial chemicals used within, or lack of adequate fresh-air intake/air filtration (see minimum efficiency reporting value). [2] Sick building syndrome has also been attributed to heating, ventilation, and air conditioning (HVAC) systems. However, there have been inconsistent findings on whether air conditioning systems result in SBS or not. [6]

Signs and symptoms

An air quality monitor Portable Air Quality monitor Kong Qi Zhi Ce Ding Qi .jpg
An air quality monitor

Human exposure to aerosols has been documented to give rise to a variety of adverse health effects. [7] Building occupants complain of symptoms such as sensory irritation of the eyes, nose, or throat; neurotoxic or general health problems; skin irritation; nonspecific hypersensitivity reactions; infectious diseases; [8] and odor and taste sensations. [9] Exposure to poor lighting conditions has led to general malaise. [10]

Extrinsic allergic alveolitis has been associated with the presence of fungi and bacteria in the moist air of residential houses and commercial offices. [11] A study in 2017 correlated several inflammatory diseases of the respiration tract with objective evidence of damp-caused damage in homes. [12]

The WHO has classified the reported symptoms into broad categories, including: mucous membrane irritation (eye, nose, and throat irritation), neurotoxic effects (headaches, fatigue, and irritability), asthma and asthma-like symptoms (chest tightness and wheezing), skin dryness and irritation, gastrointestinal complaints and more. [13]

Several sick occupants may report individual symptoms which do not appear to be connected. The key to discovery is the increased incidence of illnesses in general with onset or exacerbation within a fairly close time frame – usually within a period of weeks. In most cases, SBS symptoms will be relieved soon after the occupants leave the particular room or zone. [14] However, there can be lingering effects of various neurotoxins, which may not clear up when the occupant leaves the building. In some cases – particularly in sensitive individuals – there can be long-term health effects. [15]

Cause

ASHRAE has recognized that polluted urban air, designated within the United States Environmental Protection Agency (EPA)'s air quality ratings as unacceptable, requires the installation of treatment such as filtration for which the HVAC practitioners generally apply carbon-impregnated filters and their likes. Different toxins will aggravate the human body in different ways. Some people are more allergic to mold, while others are highly sensitive to dust. Inadequate ventilation will exaggerate small problems (such as deteriorating fiberglass insulation or cooking fumes) into a much more serious indoor air quality problem. [10]

Common products such as paint, insulation, rigid foam, Particle Board, plywood, duct liners, exhaust fumes and other chemical contaminants from indoor or outdoor sources, and biological contaminants can be trapped inside by the HVAC AC system. As this air is recycled using fan coils the overall oxygenation ratio drops and becomes harmful. When combined with other stress factors such as traffic noise, poor lighting, inhabitants of buildings located in a polluted urban area can quickly become ill as their immune system is overwhelmed. [10]

Certain VOCs, considered toxic chemical contaminants to humans, are used as adhesives in all common building construction products. These aromatic carbon rings / VOCs can cause acute and chronic health effects on the occupants of a building, including cancer, paralysis, lung failure, and others. Bacterial spores, fungal spores, mold spores, pollen, and viruses are types of biological contaminants and can all cause allergic reactions or illness described as SBS. In addition, pollution from outdoors, such as motor vehicle exhaust, can infiltrate into poorly designed buildings and contribute to poor indoor air quality, high ppm of CO and CO2. [16] Adult SBS symptoms were associated with a history of allergic rhinitis, eczema and asthma. [17]

A 2015 study concerning the association of SBS and indoor air pollutants in office buildings in Iran found that, as carbon dioxide levels increase in a building, symptoms like nausea, headaches, nasal irritation, dyspnea, and throat dryness have also been shown to increase. [10] Certain work conditions have been found to be correlated with specific symptoms. For example, higher light intensity was significantly related to skin dryness, eye pain, and malaise. [10] Higher temperature has also been found to correlate with symptoms such as sneezing, skin redness, itchy eyes and headache, while lower relative humidity has been associated with sneezing, skin redness, and pain of the eyes. [10]

In 1973, in response to the oil crisis and conservation concerns, ASHRAE Standards 62-73 and 62-81 reduced required ventilation from 10 cubic feet per minute (4.7 L/s) per person to 5 cubic feet per minute (2.4 L/s) per person, but this was found to be a contributing factor to sick building syndrome. [18] As of the 2016 revision, ASHRAE ventilation standards call for 5 to 10 cubic feet per minute of ventilation per occupant (depending on the occupancy type) in addition to ventilation based on the zone floor area delivered to the breathing zone. [19]

Workplace

Excessive work stress or dissatisfaction, poor interpersonal relationships and poor communication are often seen to be associated with SBS, recent[ when? ] studies show that a combination of environmental sensitivity and stress can greatly contribute to sick building syndrome. [15] [ citation needed ]

Greater effects were found with features of the psycho-social work environment including high job demands and low support. The report concluded that the physical environment of office buildings appears to be less important than features of the psycho-social work environment in explaining differences in the prevalence of symptoms. However, there is still a relationship between sick building syndrome and symptoms of workers regardless of workplace stress. [20]

Specific work-related stressors are related with specific SBS symptoms. Workload and work conflict are significantly associated with general symptoms (headache, abnormal tiredness, sensation of cold or nausea). While crowded workspaces and low work satisfaction are associated with upper respiratory symptoms. [21] Work productivity has been associated with ventilation rates, a contributing factor to SBS, and there's a significant increase in production as ventilation rates increase, by 1.7% for every two-fold increase of ventilation rate. [22] Printer effluent, released into the office air as ultra-fine particles (UFPs) as toner is burned during the printing process, may lead to certain SBS symptoms. [23] [24] Printer effluent may contain a variety of toxins to which a subset of office workers are sensitive, triggering SBS symptoms. [25]

Specific careers are also associated with specific SBS symptoms. Transport, communication, healthcare, and social workers have highest prevalence of general symptoms. Skin symptoms such as eczema, itching, and rashes on hands and face are associated with technical work. Forestry, agriculture, and sales workers have the lowest rates of sick building syndrome symptoms. [26]

From the assessment done by Fisk and Mudarri, 21% of asthma cases in the United States were caused by wet environments with mold that exist in all indoor environments, such as schools, office buildings, houses and apartments. Fisk and Berkeley Laboratory colleagues also found that the exposure to the mold increases the chances of respiratory issues by 30 to 50 percent. [27] Additionally, studies showing that health effects with dampness and mold in indoor environments found that increased risk of adverse health effects occurs with dampness or visible mold environments. [28]

Milton et al. determined the cost of sick leave specific for one business was an estimated $480 per employee, and about five days of sick leave per year could be attributed to low ventilation rates. When comparing low ventilation rate areas of the building to higher ventilation rate areas, the relative risk of short-term sick leave was 1.53 times greater in the low ventilation areas. [29]

Home

Sick building syndrome can also occur due to factors of the home. Laminate flooring can cause more exposure to chemicals and more resulting SBS symptoms compared to stone, tile, and cement flooring. [17] Recent redecorating and new furnishings within the last year were also found to be associated with increased symptoms, along with dampness and related factors, having pets, and the presence of cockroaches. [17] The presence of mosquitoes was also a factor related to more symptoms, though it is unclear whether it was due to the presence of mosquitoes or the use of repellents. [17]

Mold

Some studies have found that sick building syndrome may be associated with indoor mould or mycotoxin contamination. However, the attribution of sick building syndrome to mould is controversial and supported by little evidence. [30] [31] [32]

Indoor temperature

Indoor temperature under 18 °C (64 °F) has been shown to be associated with increased respiratory and cardiovascular diseases, increased blood levels, and increased hospitalization. [33]

Diagnosis

While sick building syndrome (SBS) encompasses a multitude of non-specific symptoms, building-related illness (BRI) comprises specific, diagnosable symptoms caused by certain agents (chemicals, bacteria, fungi, etc.). These can typically be identified, measured, and quantified. [34] There are usually 4 causal agents in BRI; 1.) Immunologic, 2.) Infectious, 3.) toxic, and 4.) irritant. [34] For instance, Legionnaire's disease, usually caused by Legionella pneumophila , involves a specific organism which could be ascertained through clinical findings as the source of contamination within a building. [34]

Prevention

Management

SBS, as a non specific blanket term, does not have any specific cause or cure. Any known cure would be associated with the specific eventual disease that was cause by exposure to known contaminants. In all cases, alleviation consists of removing the affected person from the building associated. BRI, on the other hand, utilizes treatment appropriate for the contaminant identified within the building (e.g., antibiotics for Legionnaire's disease).[ citation needed ]

In most cases, simply improving the indoor air quality (IAQ) of a particular building will attenuate, or even eliminate, the continued exposure to toxins. For the individual, the recovery may be a process involved with targeting the acute symptoms of a specific illness, as in the case of mold toxins. [44] Treating various building-related illnesses is vital to the overall understanding of SBS. Careful analysis by certified building professionals and Medical Doctors can help to identify the exact cause of the BRI, and help to illustrate a causal path to infection. With this knowledge one can, theoretically, remediate a building of contaminants and rebuild the structure with new materials. Office BRI may more likely than not be explained by three events: "Wide range in the threshold of response in any population (susceptibility), a spectrum of response to any given agent, or variability in exposure within large office buildings." [45]

Isolating any one of the three aspects of office BRI can be a great challenge, which is why those who find themselves with BRI should take three steps, history, examinations, and interventions. History describes the action of continually monitoring and recording the health of workers experiencing BRI, as well as obtaining records of previous building alterations or related activity. Examinations go hand in hand with monitoring employee health. This step is done by physically examining the entire workspace and evaluating possible threats to health status among employees. Interventions follow accordingly based on the results of the Examination and History report. [45]

Epidemiology

Some studies have found that women have higher reports of SBS symptoms than men. [17] [10] It is not entirely clear, however, if this is due to biological, social, or occupational factors.

A 2001 study published in the Journal Indoor Air, gathered 1464 office-working participants to increase the scientific understanding of gender differences under the Sick Building Syndrome phenomenon. [46] Using questionnaires, ergonomic investigations, building evaluations, as well as physical, biological, and chemical variables, the investigators obtained results that compare with past studies of SBS and gender. The study team found that across most test variables, prevalence rates were different in most areas, but there was also a deep stratification of working conditions between genders as well. For example, men's workplaces tend to be significantly larger and have all-around better job characteristics. Secondly, there was a noticeable difference in reporting rates, specifically that women have higher rates of reporting roughly 20% higher than men. This information was similar to that found in previous studies, thus indicating a potential difference in willingness to report. [46]

There might be a gender difference in reporting rates of sick building syndrome, because women tend to report more symptoms than men do. Along with this, some studies have found that women have a more responsive immune system and are more prone to mucosal dryness and facial erythema. Also, women are alleged by some to be more exposed to indoor environmental factors because they have a greater tendency to have clerical jobs, wherein they are exposed to unique office equipment and materials (example: blueprint machines, toner-based printers), whereas men often have jobs based outside of offices. [47]

History

In the late 1970s, it was noted that nonspecific symptoms were reported by tenants in newly constructed homes, offices, and nurseries. In media it was called "office illness". The term "sick building syndrome" was coined by the WHO in 1986, when they also estimated that 10–30% of newly built office buildings in the West had indoor air problems. Early Danish and British studies reported symptoms.

Poor indoor environments attracted attention. The Swedish allergy study (SOU 1989:76) designated "sick building" as a cause of the allergy epidemic as was feared. In the 1990s, therefore, extensive research into "sick building" was carried out. Various physical and chemical factors in the buildings were examined on a broad front.

The problem was highlighted increasingly in media and was described as a "ticking time bomb". Many studies were performed in individual buildings.

In the 1990s "sick buildings" were contrasted against "healthy buildings". The chemical contents of building materials were highlighted. Many building material manufacturers were actively working to gain control of the chemical content and to replace criticized additives. The ventilation industry advocated above all more well-functioning ventilation. Others perceived ecological construction, natural materials, and simple techniques as a solution.

At the end of the 1990s came an increased distrust of the concept of "sick building". A dissertation at the Karolinska Institutet in Stockholm 1999 questioned the methodology of previous research, and a Danish study from 2005 showed these flaws experimentally. It was suggested that sick building syndrome was not really a coherent syndrome and was not a disease to be individually diagnosed, but a collection of as many as to dozen semi related diseases. In 2006 the Swedish National Board of Health and Welfare recommended in the medical journal Läkartidningen that "sick building syndrome" should not be used as a clinical diagnosis. Thereafter, it has become increasingly less common to use terms such as "sick buildings" and "sick building syndrome" in research. However, the concept remains alive in popular culture and is used to designate the set of symptoms related to poor home or work environment engineering. "Sick building" is therefore an expression used especially in the context of workplace health.

Sick building syndrome made a rapid journey from media to courtroom where professional engineers and architects became named defendants and were represented by their respective professional practice insurers. Proceedings invariably relied on expert witnesses, medical and technical experts along with building managers, contractors and manufacturers of finishes and furnishings, testifying as to cause and effect. Most of these actions resulted in sealed settlement agreements, none of these being dramatic. The insurers needed a defense based upon Standards of Professional Practice to meet a court decision that declared that in a modern, essentially sealed building, the HVAC systems must produce breathing air for suitable human consumption. ASHRAE (American Society of Heating, Refrigeration and Air Conditioning Engineers, currently with over 50,000 international members) undertook the task of codifying its indoor air quality (IAQ) standard.

ASHRAE empirical research determined that "acceptability" was a function of outdoor (fresh air) ventilation rate and used carbon dioxide as an accurate measurement of occupant presence and activity. Building odors and contaminants would be suitably controlled by this dilution methodology. ASHRAE codified a level of 1,000 ppm of carbon dioxide and specified the use of widely available sense-and-control equipment to assure compliance. The 1989 issue of ASHRAE 62.1-1989 published the whys and wherefores and overrode the 1981 requirements that were aimed at a ventilation level of 5,000 ppm of carbon dioxide (the OSHA workplace limit), federally set to minimize HVAC system energy consumption. This apparently ended the SBS epidemic.

Over time, building materials changed with respect to emissions potential. Smoking vanished and dramatic improvements in ambient air quality, coupled with code compliant ventilation and maintenance, per ASHRAE standards have all contributed to the acceptability of the indoor air environment. [48] [49]

See also

Related Research Articles

<span class="mw-page-title-main">Mold health issues</span> Harmful effects of molds

Mold health issues refer to the harmful health effects of moulds and their mycotoxins. However, recent research has shown these adverse health effects are caused not exclusively by molds, but also other microbial agents and biotoxins associated with dampness, mold, and water-damaged buildings, such as gram-negative bacteria that produce endotoxins, as well as actinomycetes and their associated exotoxins. Approximately 47% of houses in the United States have substantial levels of mold, with over 85% of commercial and office buildings found to have water damage predictive of mold. As many as 21% of asthma cases may result from exposure to mold. Substantial and statistically significant increases in the risks of both respiratory infections and bronchitis have been associated with dampness in homes and the resulting mold.

<span class="mw-page-title-main">Heating, ventilation, and air conditioning</span> Technology of indoor and vehicular environmental comfort

Heating, ventilation, and air conditioning (HVAC) is the use of various technologies to control the temperature, humidity, and purity of the air in an enclosed space. Its goal is to provide thermal comfort and acceptable indoor air quality. HVAC system design is a subdiscipline of mechanical engineering, based on the principles of thermodynamics, fluid mechanics, and heat transfer. "Refrigeration" is sometimes added to the field's abbreviation as HVAC&R or HVACR, or "ventilation" is dropped, as in HACR.

<span class="mw-page-title-main">Indoor air quality</span> Air quality within and around buildings and structures

Indoor air quality (IAQ) is the air quality within and around buildings and structures. Poor indoor air quality due to indoor air pollution is known to affect the health, comfort, and well-being of building occupants. It has also been linked to sick building syndrome, reduced productivity, and impaired learning in schools. Common pollutants of indoor air include: secondhand tobacco smoke, air pollutants from indoor combustion, radon, molds and other allergens, carbon monoxide, volatile organic compounds, legionella and other bacteria, asbestos fibers, carbon dioxide, ozone and particulates. Source control, filtration, and the use of ventilation to dilute contaminants are the primary methods for improving indoor air quality.

<span class="mw-page-title-main">Ventilation (architecture)</span> Intentional introduction of outside air into a space

Ventilation is the intentional introduction of outdoor air into a space. Ventilation is mainly used to control indoor air quality by diluting and displacing indoor pollutants; it can also be used to control indoor temperature, humidity, and air motion to benefit thermal comfort, satisfaction with other aspects of the indoor environment, or other objectives.

<span class="mw-page-title-main">Air purifier</span> Device that removes contaminants from the air in a room

An air purifier or air cleaner is a device which removes contaminants from the air in a room to improve indoor air quality. These devices are commonly marketed as being beneficial to allergy sufferers and asthmatics, and at reducing or eliminating second-hand tobacco smoke.

<span class="mw-page-title-main">Building science</span>

Building science is the science and technology-driven collection of knowledge in order to provide better indoor environmental quality (IEQ), energy-efficient built environments, and occupant comfort and satisfaction. Building physics, architectural science, and applied physics are terms used for the knowledge domain that overlaps with building science. In building science, the methods used in natural and hard sciences are widely applied, which may include controlled and quasi-experiments, randomized control, physical measurements, remote sensing, and simulations. On the other hand, methods from social and soft sciences, such as case study, interviews & focus group, observational method, surveys, and experience sampling, are also widely used in building science to understand occupant satisfaction, comfort, and experiences by acquiring qualitative data. One of the recent trends in building science is a combination of the two different methods. For instance, it is widely known that occupants' thermal sensation and comfort may vary depending on their sex, age, emotion, experiences, etc. even in the same indoor environment. Despite the advancement in data extraction and collection technology in building science, objective measurements alone can hardly represent occupants' state of mind such as comfort and preference. Therefore, researchers are trying to measure both physical contexts and understand human responses to figure out complex interrelationships.

Displacement ventilation (DV) is a room air distribution strategy where conditioned outdoor air is supplied at a low velocity from air supply diffusers located near floor level and extracted above the occupied zone, usually at ceiling height.

<span class="mw-page-title-main">Center for the Built Environment</span> Research center at the University of California, Berkeley

The Center for the Built Environment (CBE) is a research center at the University of California, Berkeley. CBE's mission is to improve the environmental quality and energy efficiency of buildings by providing timely, unbiased information on building technologies and design techniques. CBE's work is supported by a consortium of building industry leaders, including manufacturers, building owners, contractors, architects, engineers, utilities, and government agencies. The CBE also maintains an online newsletter of the center's latest activities called Centerline.

<span class="mw-page-title-main">Thermal comfort</span> Satisfaction with the thermal environment

Thermal comfort is the condition of mind that expresses satisfaction with the thermal environment and is assessed by subjective evaluation. The human body can be viewed as a heat engine where food is the input energy. The human body will release excess heat into the environment, so the body can continue to operate. The heat transfer is proportional to temperature difference. In cold environments, the body loses more heat to the environment and in hot environments the body does not release enough heat. Both the hot and cold scenarios lead to discomfort. Maintaining this standard of thermal comfort for occupants of buildings or other enclosures is one of the important goals of HVAC design engineers.

<span class="mw-page-title-main">Passive ventilation</span> Ventilation without use of mechanical systems

Passive ventilation is the process of supplying air to and removing air from an indoor space without using mechanical systems. It refers to the flow of external air to an indoor space as a result of pressure differences arising from natural forces.

Infiltration is the unintentional or accidental introduction of outside air into a building, typically through cracks in the building envelope and through use of doors for passage. Infiltration is sometimes called air leakage. The leakage of room air out of a building, intentionally or not, is called exfiltration. Infiltration is caused by wind, negative pressurization of the building, and by air buoyancy forces known commonly as the stack effect.

<span class="mw-page-title-main">Indoor mold</span> Fungal growth that develops on wet materials

Indoor mold or indoor mould, also sometimes referred to as mildew, is a fungal growth that develops on wet materials in interior spaces. Mold is a natural part of the environment and plays an important part in nature by breaking down dead organic matter such as fallen leaves and dead trees; indoors, mold growth should be avoided. Mold reproduces by means of tiny spores. The spores are like seeds, but invisible to the naked eye, that float through the air and deposit on surfaces. When the temperature, moisture, and available nutrient conditions are correct, the spores can form into new mold colonies where they are deposited. There are many types of mold, but all require moisture and a food source for growth.

Air changes per hour, abbreviated ACPH or ACH, or air change rate is the number of times that the total air volume in a room or space is completely removed and replaced in an hour. If the air in the space is either uniform or perfectly mixed, air changes per hour is a measure of how many times the air within a defined space is replaced each hour. Perfectly mixed air refers to a theoretical condition where supply air is instantly and uniformly mixed with the air already present in a space, so that conditions such as age of air and concentration of pollutants are spatially uniform.

Indoor bioaerosol is bioaerosol in an indoor environment. Bioaerosols are natural or artificial particles of biological origin suspended in the air. These particles are also referred to as organic dust. Bioaerosols may consist of bacteria, fungi, viruses, microbial toxins, pollen, plant fibers, etc. Size of bioaerosol particles varies from below 1 µm to 100 µm in aerodynamic diameter; viable bioaerosol particles can be suspended in air as single cells or aggregates of microorganism as small as 1–10 µm in size. Since bioaerosols are potentially related to various human health effects and the indoor environment provides a unique exposure situation, concerns about indoor bioaerosols have increased over the last decade.

<span class="mw-page-title-main">Underfloor air distribution</span>

Underfloor air distribution (UFAD) is an air distribution strategy for providing ventilation and space conditioning in buildings as part of the design of a HVAC system. UFAD systems use an underfloor supply plenum located between the structural concrete slab and a raised floor system to supply conditioned air to supply outlets, located at or near floor level within the occupied space. Air returns from the room at ceiling level or the maximum allowable height above the occupied zone.

<span class="mw-page-title-main">Dedicated outdoor air system</span>

A dedicated outdoor air system (DOAS) is a type of heating, ventilation and air-conditioning (HVAC) system that consists of two parallel systems: a dedicated system for delivering outdoor air ventilation that handles both the latent and sensible loads of conditioning the ventilation air, and a parallel system to handle the loads generated by indoor/process sources and those that pass through the building enclosure.

Airflow, or air flow, is the movement of air. The primary cause of airflow is the existence of air. Air behaves in a fluid manner, meaning particles naturally flow from areas of higher pressure to those where the pressure is lower. Atmospheric air pressure is directly related to altitude, temperature, and composition.

<span class="mw-page-title-main">ASHRAE</span> American HVAC professional association

The American Society of Heating, Refrigerating and Air-Conditioning Engineers is an American professional association seeking to advance heating, ventilation, air conditioning and refrigeration (HVAC&R) systems design and construction. ASHRAE has over 50,000 members in more than 130 countries worldwide.

Demand controlled ventilation (DCV) is a feedback control method to maintain indoor air quality that automatically adjusts the ventilation rate provided to a space in response to changes in conditions such as occupant number or indoor pollutant concentration. The most common indoor pollutants monitored in DCV systems are carbon dioxide and humidity. This control strategy is mainly intended to reduce the energy used by heating, ventilation, and air conditioning (HVAC) systems compared to those of buildings that use open-loop controls with constant ventilation rates.

Healthy building refers to an emerging area of interest that supports the physical, psychological, and social health and well-being of people in buildings and the built environment. Buildings can be key promoters of health and well-being since most people spend a majority of their time indoors. According to the National Human Activity Pattern Survey, Americans spend "an average of 87% of their time in enclosed buildings and about 6% of their time in enclosed vehicles."

References

  1. "Sick Building Syndrome" (PDF). World Health Organization. n.d.
  2. 1 2 3 4 5 Passarelli, Guiseppe Ryan (2009). "Sick building syndrome: An overview to raise awareness". Journal of Building Appraisal. 5: 55–66. doi: 10.1057/jba.2009.20 .
  3. European Centre for Environment and Health, WHO (1983). WHO guidelines for indoor air quality: selected pollutants (PDF). EURO Reports and Studies, no 78. Bonn Germany Office: WHO Regional Office for Europe (Copenhagen).
  4. Stolwijk, J A (1991-11-01). "Sick-building syndrome". Environmental Health Perspectives. 95: 99–100. doi:10.1289/ehp.919599. ISSN   0091-6765. PMC   1568418 . PMID   1821387.
  5. Indoor Air Pollution: An Introduction for Health Professionals (PDF). Indoor Air Division (6609J): U.S. Environmental Protection Agency. c. 2015.{{cite book}}: CS1 maint: location (link)
  6. Shahzad, Sally S.; Brennan, John; Theodossopoulos, Dimitris; Hughes, Ben; Calautit, John Kaiser (2016-04-06). "Building-Related Symptoms, Energy, and Thermal Control in the Workplace: Personal and Open Plan Offices". Sustainability. 8 (4): 331. doi: 10.3390/su8040331 .
  7. Sundell, J; Lindval, T; Berndt, S (1994). "Association between type of ventilation and airflow rates in office buildings and the risk of SBS-symptoms among occupants". Environ. Int. 20 (2): 239–251. doi:10.1016/0160-4120(94)90141-4.
  8. Rylander, R (1997). "Investigation of the relationship between disease and airborne (1P3)-b-D-glucan in buildings". Med. Of Inflamm. 6 (4): 275–277. doi:10.1080/09629359791613. PMC   2365865 . PMID   18472858.
  9. Godish, Thad (2001). Indoor Environmental Quality. New York: CRC Press. pp. 196–197. ISBN   1-56670-402-2
  10. 1 2 3 4 5 6 7 Jafari, Mohammad Javad; Khajevandi, Ali Asghar; Mousavi Najarkola, Seyed Ali; Yekaninejad, Mir Saeed; Pourhoseingholi, Mohammad Amin; Omidi, Leila; Kalantary, Saba (2015-01-01). "Association of Sick Building Syndrome with Indoor Air Parameters". Tanaffos. 14 (1): 55–62. ISSN   1735-0344. PMC   4515331 . PMID   26221153.
  11. Teculescu, D. B. (1998). "Sick Building Symptoms in office workers in northern France: a pilot study". Int. Arch. Occup. Environ. Health. 71 (5): 353–356. doi:10.1007/s004200050292. PMID   9749975. S2CID   25095874.
  12. Pind C. Ahlroth (2017). "Patient-reported signs of dampness at home may be a risk factor for chronic rhinosinusitis: A cross-sectional study". Clinical & Experimental Allergy. 47 (11): 1383–1389. doi:10.1111/cea.12976. PMID   28695715. S2CID   40807627.
  13. Apter, A (1994). "Epidemiology of the sick building syndrome". J. Allergy Clin. Immunol. 94 (2): 277–288. doi:10.1053/ai.1994.v94.a56006. PMID   8077580.
  14. "Sick Building Syndrome". NSC.org. National Safety Council. 2009. Retrieved April 27, 2009.
  15. 1 2 Joshi, Sumedha M. (August 2008). "The sick building syndrome". Indian Journal of Occupational and Environmental Medicine. 12 (2): 61–64. doi: 10.4103/0019-5278.43262 . ISSN   0973-2284. PMC   2796751 . PMID   20040980.
  16. "Indoor Air Facts No.4: Sick Building Syndrome" (PDF). United States Environmental Protection Agency (EPA). 1991. Retrieved 2009-02-19.
  17. 1 2 3 4 5 6 Wang, Juan; Li, BaiZhan; Yang, Qin; Wang, Han; Norback, Dan; Sundell, Jan (2013-12-01). "Sick building syndrome among parents of preschool children in relation to home environment in Chongqing, China". Chinese Science Bulletin. 58 (34): 4267–4276. Bibcode:2013ChSBu..58.4267W. doi: 10.1007/s11434-013-5814-2 . ISSN   1001-6538.
  18. Joshi S. M. (2008). "The sick building syndrome". Indian J. Occup. Environ. Med. 12 (2): 61–4. doi: 10.4103/0019-5278.43262 . PMC   2796751 . PMID   20040980. in section 3 "Inadequate ventilation".
  19. ANSI/ASHRAE Standard 62.1-2016.
  20. Bauer R. M., Greve K. W., Besch E. L., Schramke C. J., Crouch J., Hicks A., Lyles W. B. (1992). "The role of psychological factors in the report of building-related symptoms in sick building syndrome". Journal of Consulting and Clinical Psychology. 60 (2): 213–219. doi:10.1037/0022-006x.60.2.213. PMID   1592950.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  21. Azuma K., Ikeda K., Kagi N., Yanagi U., Osawa H. (2014). "Prevalence and risk factors associated with nonspecific building-related symptoms in office employees in Japan: Relationships between work environment, Indoor Air Quality, and occupational stress". Indoor Air. 25 (5): 499–511. doi: 10.1111/ina.12158 . PMID   25244340.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  22. 1 2 Wargocki P., Wyon D. P., Sundell J., Clausen G., Fanger P. O. (2000). "The Effects of Outdoor Air Supply Rate in an Office on Perceived Air Quality, Sick Building Syndrome (SBS) Symptoms and Productivity". Indoor Air. 10 (4): 222–236. Bibcode:2000InAir..10..222W. doi: 10.1034/j.1600-0668.2000.010004222.x . PMID   11089327.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  23. Morimoto, Yasuo; Ogami, Akira; Kochi, Isamu; Uchiyama, Tetsuro; Ide, Reiko; Myojo, Toshihiko; Higashi, Toshiaki (2010). "[Continuing investigation of effect of toner and its by-product on human health and occupational health management of toner]". Sangyo Eiseigaku Zasshi = Journal of Occupational Health. 52 (5): 201–208. doi: 10.1539/sangyoeisei.a10002 . ISSN   1349-533X. PMID   20595787.
  24. Pirela, Sandra Vanessa; Martin, John; Bello, Dhimiter; Demokritou, Philip (September 2017). "Nanoparticle exposures from nano-enabled toner-based printing equipment and human health: state of science and future research needs". Critical Reviews in Toxicology. 47 (8): 678–704. doi:10.1080/10408444.2017.1318354. ISSN   1547-6898. PMC   5857386 . PMID   28524743.
  25. McKone, Thomas, et al. "Indoor Pollutant Emissions from Electronic Office Equipment, California Air Resources Board Air Pollution Seminar Series". Presented January 7, 2009. https://www.arb.ca.gov/research/seminars/mckone/mckone.pdf Archived 2017-02-07 at the Wayback Machine
  26. Norback D., Edling C. (1991). "Environmental, occupational, and personal factors related to the prevalence of sick building syndrome in the general population". Occupational and Environmental Medicine. 48 (7): 451–462. doi:10.1136/oem.48.7.451. PMC   1035398 . PMID   1854648.
  27. Weinhold, Bob (2007-06-01). "A Spreading Concern: Inhalational Health Effects of Mold". Environmental Health Perspectives. 115 (6): A300–A305. doi:10.1289/ehp.115-a300. PMC   1892134 . PMID   17589582.
  28. Mudarri, D.; Fisk, W. J. (June 2007). "Public health and economic impact of dampness and mold". Indoor Air. 17 (3): 226–235. Bibcode:2007InAir..17..226M. doi:10.1111/j.1600-0668.2007.00474.x. ISSN   0905-6947. PMID   17542835. S2CID   21709547.
  29. Milton D. K., Glencross P. M., Walters M. D. (2000). "Risk of Sick Leave Associated with Outdoor Air Supply Rate, Humidification, and Occupant Complaints". Indoor Air. 10 (4): 212–221. Bibcode:2000InAir..10..212M. doi: 10.1034/j.1600-0668.2000.010004212.x . PMID   11089326.{{cite journal}}: CS1 maint: multiple names: authors list (link)
  30. Straus, David C. (2009). "Molds, mycotoxins, and sick building syndrome". Toxicology and Industrial Health. 25 (9–10): 617–635. Bibcode:2009ToxIH..25..617S. doi:10.1177/0748233709348287. PMID   19854820. S2CID   30720328.
  31. Terr, Abba I. (2009). "Sick Building Syndrome: Is mould the cause?". Medical Mycology. 47: S217–S222. doi: 10.1080/13693780802510216 . PMID   19255924.
  32. Norbäck, Dan; Zock, Jan-Paul; Plana, Estel; Heinrich, Joachim; Svanes, Cecilie; Sunyer, Jordi; Künzli, Nino; Villani, Simona; Olivieri, Mario; Soon, Argo; Jarvis, Deborah (2011-05-01). "Lung function decline in relation to mould and dampness in the home: the longitudinal European Community Respiratory Health Survey ECRHS II". Thorax. 66 (5): 396–401. doi: 10.1136/thx.2010.146613 . ISSN   0040-6376. PMID   21325663. S2CID   318027.
  33. WHO Housing and health guidelines. World Health Organization. 2018. pp. 34, 47–48. ISBN   978-92-4-155037-6.
  34. 1 2 3 Seltzer, J. M. (1994-08-01). "Building-related illnesses". The Journal of Allergy and Clinical Immunology. 94 (2 Pt 2): 351–361. doi: 10.1016/0091-6749(94)90096-5 . ISSN   0091-6749. PMID   8077589.
  35. nasa techdoc 19930072988
  36. "Sick Building Syndrome: How indoor plants can help clear the air | University of Technology Sydney".
  37. Wolverton, B. C.; Johnson, Anne; Bounds, Keith (15 September 1989). Interior Landscape Plants for Indoor Air Pollution Abatement (PDF) (Report).
  38. Joshi, S. M (2008). "The sick building syndrome". Indian Journal of Occupational and Environmental Medicine. 12 (2): 61–64. doi: 10.4103/0019-5278.43262 . PMC   2796751 . PMID   20040980.
  39. "Benefits of Office Plants – Tove Fjeld (Agri. Uni. Of Norway)". 2018-05-13.
  40. "NASA: 18 Plants Purify Air, Sick Building Syndrome". 2016-09-20. Archived from the original on 2020-10-26.
  41. "Sick Building Syndrome – How Plants Can Help".
  42. How to deal with sick building syndrome: Guidance for employers, building owners and building managers. (1995). Sudbury: The Executive.
  43. Scungio, Mauro; Vitanza, Tania; Stabile, Luca; Buonanno, Giorgio; Morawska, Lidia (2017-05-15). "Characterization of particle emission from laser printers" (PDF). Science of the Total Environment. 586: 623–630. Bibcode:2017ScTEn.586..623S. doi:10.1016/j.scitotenv.2017.02.030. ISSN   0048-9697. PMID   28196755.
  44. Indoor Air Facts No. 4 (revised) Sick building syndrome. Available from: .
  45. 1 2 Menzies, Dick; Bourbeau, Jean (1997-11-20). "Building-Related Illnesses". New England Journal of Medicine. 337 (21): 1524–1531. doi:10.1056/NEJM199711203372107. ISSN   0028-4793. PMID   9366585.
  46. 1 2 Brasche, S.; Bullinger, M.; Morfeld, M.; Gebhardt, H. J.; Bischof, W. (2001-12-01). "Why do women suffer from sick building syndrome more often than men?--subjective higher sensitivity versus objective causes". Indoor Air. 11 (4): 217–222. Bibcode:2001InAir..11..217B. doi: 10.1034/j.1600-0668.2001.110402.x . ISSN   0905-6947. PMID   11761596. S2CID   21579339.
  47. Godish, Thad (2001). Indoor Environmental quality. New York: CRC Press. pp. 196–197. ISBN   1-56670-402-2
  48. "Sick Building Syndrome – Fact Sheet" (PDF). United States Environmental Protection Agency . Retrieved 2013-06-06.
  49. "Sick Building Syndrome". National Health Service, England. Retrieved 2013-06-06.

Further reading