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Building and Environment
journal homepage: www.elsevier.com/locate/buildenv
Removal performance of formaldehyde by ceiling tiles as sorptive passive
panels
Mitra Bahri
∗
, Hans Schleibinger, William Render, Olga Naboka
Indoor Air Quality Group, Construction Research Center, National Research Council Canada (NRC), Ottawa, Canada
ARTICLEINFO
Keywords:
Indoor air quality
Formaldehyde
Sorptive passive panels
Removal efciency
Ceiling tiles
ABSTRACT
In this study a ceiling tile (CT) was selected as a sorptive passive panel, and the efect of environmental con-
ditionsonitsformaldehyderemovalefciencywasevaluated.Experimentswereperformedina0.4m
3
chamber
withtheairfowrateof0.2m
3
h
−1
,theairexchangerateofthe0.5h
−1
,andtheloadingratioof0.23m
2
m
-3
.The
range of temperature humidity levels varied between 21°C ± 2°C–26°C ± 2°C, and 30% ± 5%–75% ± 5%,
respectively, to simulate the indoor conditions for Canadian homes during most months of the year. Results
demonstrated formaldehyde removal efciencybetween40%and75%dependingontheappliedenvironmental
conditions. GC/MS and HPLC trace analyses revealed that only very low concentrations of by-products were
formed. The by-product formation increased slightly when exposing the ceiling tile to relatively high relative
humidity (RH=75%) and temperature (T=26°C). Given a loading factor of only 0.23m
2
m
−3
in our test
chamber, which in most scenarios underestimates the loading factor in real settings, our fndings suggest that
ceiling tiles used as passive removal panels have the potential to lower formaldehyde concentrations under the
Health Canada's guideline for residential settings under real-life conditions.
1. Introduction
Indoor air contains a variety of airborne pollutants emitted from
diferent sources. Their presence, depending on their concentrations,
may afect the health and wellbeing of building occupants [1–3].
Among those volatile pollutants, formaldehyde could be regarded as
onethemosthealth-relevantindoorairpollutants[4].Formaldehydeis
being emitted from many diferent indoor sources, including latex
paints, varnishes, and from oil-based paints that are applied on MDF
and HDF [5–9]. It also of-gasses from wooden, especially engineered
products and wood smoke [10–12]. The formation of formaldehyde is
also attributed to photo-catalytically decomposed paint binders
[13,14]. The presence of formaldehyde in indoor environment is of a
great concern, because elevated concentrations are linked to several
chronic and carcinogenic health efects, allergic reactions, and eye and
airway irritations [2,4,15–17]. Long term exposure to formaldehyde
increases the risk of respiratory symptoms (i.e. development of asthma)
in children between 6 and 36 months, when concentrations exceeds
60μgm
−3
[18,19].
WhileaccordingtoHealthCanada'sguidelineforresidentialsettings
the maximum level for an 8h exposure to formaldehyde is 50μgm
−3
[20], it was shown that the concentration of formaldehyde may
signifcantly exceed this level in residential buildings in Canada. For
instance,astudyof96homesinQuebecCity(Canada),showedthatthe
concentration of formaldehyde can reach 90μgm
−3
between Januar-
y–April, when windows are usually kept closed due to the cold climate
[6].Accordingtothisstudyanelevationinformaldehydeconcentration
was observed in homes built after 1970 [5]. A similar study conducted
in59homesinPrinceEdwardIsland(Canada)alsoshowedthelevelsof
formaldehyde as high as 87.5μgm
−3
. In both studies formaldehyde
concentrations in 20% of homes exceeded the Canadian target value of
60mgm
−3
.
So far, several methods have been proposed for the removal of
formaldehyde. Among those, increased mechanical ventilation, ad-
sorbent- and catalytic-based flters are the most frequently studied
[21–25]. However, using these methods requires additional mechanical
force which is associated with an increase in energy consumption [21].
Toovercomethisdisadvantage,theapplicationofindoorpassivepanels
has been proposed [26,27]. Passive panels (PPs), also known as passive
removal materials (PRMs), are emerging materials designed for the
removal of indoor pollutants without the requirement of any additional
energy input beyond normal building operations [28]. These materials
can be designed in diferent types and features including ceiling tiles,
wallboards, wallpapers, paint, fooring, etc.
https://doi.org/10.1016/j.buildenv.2019.106172
Received 12 March 2019; Received in revised form 16 May 2019; Accepted 29 May 2019
∗
Corresponding author. Indoor Air Quality (IAQ) Group, Construction Research Center, National Research Council of Canada (NRC), M-24, 1200 Montreal Road,
Ottawa, K1A 0R6, Canada.
E-mail address: mitra.bahri@nrc-cnrc.gc.ca (M. Bahri).
Building and Environment 160 (2019) 106172
Available online 31 May 2019
0360-1323/ Crown Copyright © 2019 Published by Elsevier Ltd. All rights reserved.
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