Abstract

Indoor vegetation is often proposed as a passive approach for improving indoor air quality. While studies of outdoor environments indicate that vegetation can be an important sink of outdoor ozone, there is scant data in the literature concerning the dynamics of ozone uptake by indoor plants. This study determined ozone deposition velocities (vd) for five common indoor plants (Peace Lily, Ficus, Calathia, Dieffenbachia, Golden Pothos). The transient vd was calculated, using measured leaf areas for each plant, for exposures mimicking three diurnal cycles where ozone concentrations in chamber tests were elevated for 8 h followed by 16 h in the absence of ozone. Estimates of vd at the end of the first exposures ranged from 5.6 m h−1 for Golden Pothos to 0.9 m h−1 for Peace Lily. Values of vd were approximately 50% and 66% lower at the end of a second exposure and third exposure, respectively. Estimates of vd were also made for a range of photosynthetic active radiation (PAR) levels typically observed indoors. An increase in PAR from 0.6 to 41.2 μmol m−2 sec−1 resulted in increases in vd ranging from a factor of 1.7 (Diffenbachia) to 4.7 (Peace Lily). For deposition velocities measured in this study, the ozone removal effectiveness ranges from 0.9% to 9% for leaf surface area to room volume ratio of 0.06 m−1 (approximately one plant for every 1.8 m2 of floor area) when accounting for values of air exchange and background loss typical of a residential environment.

Highlights

  • Ozone is a strong oxidant gas with known adverse health effects

  • Five different popular indoor plants have been tested for their ability to passively remove indoor ozone

  • The indoor plants tested had moderate ozone deposition velocity values ranging from about 0.5 to 5.5 m/h depending on period of time exposed to ozone, and number of exposures to ozone

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Summary

Introduction

Ozone is a strong oxidant gas with known adverse health effects. The predominant source of indoor ozone is outdoor air, where ozone is formed through photochemistry. Ozone may be generated indoors by, e.g., photocopiers or air-cleaners using UV light or corona discharge, the transport of outdoor ozone to indoor spaces through ventilation and infiltration is the predominant indoor source. Ozone can react with different surfaces indoor such as flooring, paints, and metals [2]. While these reactions suppress indoor concentrations of ozone, they may result in the production of byproducts that may be more harmful than ozone itself [3]

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