ASHRAE FUNDAMENTALS SI CH 10-2013 Indoor Environmental Health.pdf
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1、10.1CHAPTER 10INDOOR ENVIRONMENTAL HEALTHBackground 10.1Descriptions of Selected Health Sciences 10.3Hazard Recognition, Analysis, and Control . 10.4AIRBORNE CONTAMINANTS 10.4Particles . 10.4Gaseous Contaminants 10.10Outdoor Air Ventilation and Health. 10.16PHYSICAL AGENTS 10.17Thermal Environment.
2、10.17Electrical Hazards 10.19Mechanical Energies 10.19Electromagnetic Radiation. 10.22Ergonomics. 10.24NDOOR environmental health comprises those aspects of hu-I man health and disease that are determined by factors in theindoor environment. It also refers to the theory and practice ofassessing and
3、controlling factors in the indoor environment that canpotentially affect health. The practice of indoor environmentalhealth requires consideration of chemical, biological, physical andergonomic hazards.Diseases are caused by genetics and exposures. Despite a hugeinvestment in DNA research in recent
4、decades, few diseases can besolely explained by our genes. An interaction between genes andenvironmental exposures is needed, and understanding indoorenvironmental exposures is essential in this respect. Over a 70-yearlifespan in a developed region, indoor air (in homes, schools, daycares, offices,
5、shops, etc.) constitutes around 65% of the totallifetime exposure (in mass), whereas air in industry, outdoor air, airduring transportation, food, and liquid makes up the rest. For themost vulnerable population, newborns, indoor air in homes makesup around 80% of the exposure.It is essential for eng
6、ineers to understand the fundamentals ofindoor environmental health because the design, operation, andmaintenance of buildings and their HVAC systems significantlyaffect the health of building occupants. In many cases, buildings andsystems can be designed and operated to reduce the exposure ofoccupa
7、nts to potential hazards. Unfortunately, neglecting to considerindoor environmental health can lead to conditions that create orworsen those hazards.This chapter provides general background information and intro-duces important concepts of hazard recognition, analysis, and con-trol. It also presents
8、 information on specific hazards, and describessources of exposure to each hazard, potential health effects, relevantexposure standards and guidelines, and methods to control expo-sure.This chapter is introductory in nature, and indoor environmentalhealth is a very broad and dynamic field. Thus, des
9、criptions ofpotential hazards (and especially their controls) presented are not acomprehensive, state-of-the-art review. Additional detail is availableon many important topics in other ASHRAE Handbook chapters,including Chapter 9, Thermal Comfort, of this volumeChapter 11, Air Contaminants, of this
10、volumeChapter 12, Odors, of this volumeChapter 16, Ventilation and Infiltration, of this volumeChapter 29, Air Cleaners for Particulate Contaminants, of the2012 ASHRAE HandbookHVAC Systems and EquipmentChapter 31, Ventilation of the Industrial Environment, of the 2011ASHRAE HandbookHVAC Applications
11、Chapter 46, Control of Gaseous Indoor Air Contaminants, of the2011 ASHRAE HandbookHVAC ApplicationsOther important sources of information from ASHRAE includethe building ventilation and related requirements in Standards 62.1and 62.2. Additional details are available from governmental andprivate sour
12、ces, including the U.S. Department of Health andHuman Services Centers for Disease Control and Prevention, U.S.Environmental Protection Agency, Occupational Safety and HealthAdministration, American Conference of Governmental IndustrialHygienists, National Institute for Occupational Safety and Healt
13、h,parallel institutions in other countries, and the World Health Orga-nization.BACKGROUNDEvaluation of exposure incidents and laboratory studies withhumans and animals have generated reasonable consensus on safeand unsafe workplace exposures for about 1000 chemicals and par-ticles. Consequently, man
14、y countries regulate exposures of workersto these agents. However, chemical and dust contaminant concentra-tions that meet occupational health criteria usually exceed levelsacceptable to occupants in nonindustrial spaces such as offices,schools, and residences, where exposures often last longer and
15、mayinvolve mixtures of many contaminants and a less robust population(e.g., infants, the elderly, the infirm) (NAS 1981).The generally accepted definition of health is that in the constitu-tion of the World Health Organization (WHO): “Health is a state ofcomplete physical, mental, and social well-be
16、ing and not merely theabsence of disease or infirmity.”Another, more narrowly focused definition of health by theAmerican Thoracic Society (ATS 1999) takes into account broader,societal decision-making processes in defining what constitutes anadverse health effect of air pollution. Key points of the
17、 ATS defini-tion of adverse effects are as follows:Biomarkers, or biological indicators (e.g., in blood, exhaled air,sputum) of environmental effects. Because few markers have yetbeen sufficiently validated for use in defining thresholds, not allchanges in biomarkers related to air pollution should
18、be consideredadverse effects.Quality of life. Adverse effects of air pollution can range fromwatering, stinging eyes to cardiopulmonary symptoms, and evenpsychiatric conditions.Physiological impact. Physical effects of pollution can be transi-tory or permanent, and appear alone or accompanied by oth
19、ersymptoms. The ATS minimum requirement for considering pollu-tion to have an adverse effect is reversible damage accompaniedby other symptoms (reversible damage alone is not sufficient).Also, effects such as developmental damage to lungs, or exacer-bation of age-related decay in function, must be c
20、onsidered.The preparation of this chapter is assigned to the Environmental HealthCommittee.10.2 2013 ASHRAE HandbookFundamentals (SI)Symptoms. Not all increased occurrences of symptoms are con-sidered adverse effects of air pollution: only those diminishing anindividuals quality of life or changing
21、a patients clinical statusshould be considered adverse.Clinical outcomes. Detectable effects of air pollution on clinicaltests should be considered adverse.Mortality. Any effect on mortality should be judged adverse.Population health versus individual risk. Any change in therisk of an exposed popula
22、tion should be considered adverse, evenif there is no immediate, outright illness.Definitions of comfort vary. Comfort encompasses perception ofthe environment (e.g., hot/cold, humid/dry, noisy/quiet, bright/dark)and a value rating of affective implications (e.g., too hot, too cold).Rohles et al. (1
23、989) noted that acceptability may represent a moreuseful concept of evaluating occupant response, because it allowsprogression toward a concrete goal. Acceptability is the foundationof a number of standards covering thermal comfort and acoustics.Nevertheless, acceptability varies between climatic re
24、gions and cul-tures, and may change over time as expectations change.Concern about the health effects associated with indoor air datesback several hundred years, and has increased dramatically in recentdecades. During the 1970s and 1980s, this attention was mainly aresult of concerns about radon and
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