A very important issue for all activities for better IAQ in Finland has been the introduction of theclassification guidelines for indoor air quality and climate. These guidelines, published by FISIAQ,including measurable target values, cleanliness requirements and emission criteria for buildingmaterials, have been in use in Finland since 1995 and were revised in 2001.An essential part of the successful IAQ classification has been the emission classification ofconstruction materials.
Building environmental performance evaluation should make use of a life cycle assessment(LCA) approach, by considering all building process phases: raw material acquisition,manufacture, transportation, construction, use or operation, decommissioning, disposal andre-use. Such an approach is intended to measure, not only impacts on natural and non-naturalresources but also building indoor environmental quality (IEQ).
The Environmental Protection Department conducted a territory-wide indoor air qualitysurvey in Hong Kong. The report released in 1997 confirmed that one-third of the sampledbuildings were classified as sick buildings. Many of the causes could be attributed tounacceptable indoor air quality (IAQ). In response to this, the Indoor Air Quality ManagementGroup distributed a Guidance Notes for the Management of Indoor Air Quality in Offices andPublic Places for public consultation. It includes an annual IAQ certification scheme.
Life-cycle costs of investments for improving air quality in an office building were comparedwith the resulting revenues from increased office productivity; benefits from reduced healthcosts and sickness absence were not included. The building was simulated in a cold, amoderate and a hot climate. It was ventilated by a constant air volume system with heatrecovery. The air quality was improved by increasing the outdoor air supply rate and byreducing the pollution loads.
This study calculates the effect of permeable hygroscopic structures on IAQ and thermalcomfort in a cold climate. Simulations are carried out for a detached house and application ofcriteria for assessment of indoor climate is given. The results show that hygroscopic structuressignificantly decreased the fluctuation of indoor relative humidity. In the winter,hygroscopicity had only minor effect on indoor climate, but in the summer, hygroscopicityhad some effect on thermal comfort, which was improved at lower ventilation rates.
The presence of high levels of urban pollution imposes at the international level the need tothink again about the type of ventilation systems in residential buildings. This has to be donein order to provide a better IAQ level. Natural ventilation cannot guarantee either the correctchange of air inside the buildings or a good IAQ level, as there is no possibility of checkingthe supply and extraction airflow rates in any thermo-hygrometric condition.
Indoor Air Quality (IAQ) in workplace and residential environments has been a concern ofpeople. Recently, Ministry of Environment in Korea has recognized the potential risk on thehealth effects related to indoor air pollution at home. Therefore, the purpose of this study wasto measure the indoor air pollutants of IAQ at different homes and investigate the perceptionof IAQ recognition at home through a questionnaire survey in Seoul.We estimated the IAQ of six selected homes based on site region and housing type.
Many workers in an office building complained about IAQ. No moisture damage was foundin the offices, which were, however, painted and carpeting was changed. Ventilation ductswere cleaned and the supply and exhaust air vents were installed in every room. Shortly afterthe repair the workers developed symptoms. A thorough survey of IAQ including microbesand particles and volatile organic compounds was conducted twice after the repair. Betweensurveys the rooms were cleaned for 2 months twice a week with more effective practices thanbefore.
Subjective experiments were conducted in summer and winter in order to clarify the effects ofhumidity and indoor chemical pollutants on subjective comfort and productivity, and evaluatethe seasonal differences in their reactions. Subjects were exposed to three levels of humidityconditions and 2 indoor air quality levels in a climate chamber performing the simulatedoffice works. For all conditions, SET* was constant. Subjects adapted to the indoor air qualityduring the 180-min exposures under the polluted conditions.
A new derivation of productivity calculation model based on pollution loads and contaminantremoval effectiveness is applied and the effect of the improved ventilation efficiency onproductivity is estimated. The findings show that the proportion dissatisfied could be asuitable predictor of productivity loss due to indoor air quality in different kinds of officework. The proportion dissatisfied is possible to calculate from olf and decipol units. In a caseof one person per 10 m2 (0.1 olf/m2) and low-emitted material (0.1 olf/m2), the total sensorypollution load is 0.2 olf/m2.
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