gt+qqhJS+q 7(1 xj1153 4]38(2005* 12%) J Korean Soc Occup Environ Hyg 2005;15(3):16@165
(HCHO) ~flsq 434 451
l-%q%7)9 714 937)
Evaluation of Indoor Air Quality Improvenlent by Formaldehyde Emission Rate in School Indoor Environment Using Mass Balance
Won-Ho Yangt . Bu-Soon Son1)
.
Dae-Won Kim2).
Young-Hee Kim . Jae-Cheol Byeon . Soon-won Jungl)Department of Occupational Health, Catholic University of Daegu .
"Department of Environmental Health Science, Soonchyunhyang University . Z'Department of Environmental Science, Catholic University of Daegu .
Schools have significant and serious indoor environmental health problem, of which indoor air quality (IAQ) in school building may affect the health of the students and indirectly affect learning performance. Schools are of special concern when regarding indoor exposure to air pollutants, because students are particularly sensitive to pollutants and spend a significant amount of time in that environment. Therefore researches for improvement of indoor air quality have been developed such as installation of air cleaning device, ventilation system, titanium dioxide(X02) coating and
soon. However, it is cult to evaluate the magnitude of improvement of indoor air quality in field study because indoor air quality can be affected by source generation, outdoor air level, ventilation, decay by reaction, temperature, humidity, mixing condition and
soon.
In this study, evaluation of reduction of formaldehyde emission rate in school indoor environments by far-Infixed ray
coating material was carried out using mass balance model in indoor environment. we proposed the evaluation method of magnitude of improvement in indoor air quality, considering outdoor level and ventilation. Since simple indoor concentration measuements could not properly evaluate the indoor air quality, outdoor level and ventilation should be considered when evaluate the indoor air quality.
Key Words
:school, indoor air quality, evaluation,
forrnaldehyde(HCHO), ventilation
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UV Detector ( W a t e ~ 2487), 360 nm
Column C8(Symme&y HPLC column), Reversed-phase Effluent Acetonitn1e:DW
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Outdoor
4.1Before 0.130 0.002
remodeling Indoor 7.3 (R2=0.954
)Indoor
After remodehg
Outdoor Indoor Indoor
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Outdoor Indoor Indoor
-
Mmisq of Education
(Japan 1
: 0.08ppm
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$5 51.9
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A1 i l 4 4 q @& q-qg 3 q q .
0 Before remodehg After remodeling 1 day after remodehg-1
0Fig. 2. Comparison be tween indoor HCHO concentrations and source emission rates of HCHO.
4% q * q *
BJA\3q+k42
O Beforenew desk Afternew desk 1 day after 2dayafter 3day after Oo]-$z)q HCHO !g~J$q. 7 , F k 4
installation instalIation coating coating coating5s
+j4%71"?Z P ~ 4 % ~ Fig. 3. Comparison between indoor HCHO concentrations and
% 7 \ 5 ) 3 d r . 341 W$-'6FollA-l 4 4 source em ission rates of HCHO.
Table 3. Source emission rate of HCHO in library with new purchased desk sampling
. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . , . . . . . . . . . . . . . . . . . . , . . . . . . . , . .
Conc. ACH SER
sampling Sample site i l h ) (&I Standard
ipdm3
Before Outdoor
new desk Indoor
installation Indoor
After Outdoor 7.0 0.49
-Mitustry of
new desk Indoor 3830.58
(R2=0.99
)Environment
mtdation Indoor 36.5 (Korea 1
1 day Outdoor 5.2 : 0.lppm
0.27
after Indoor 3341.39
51.9 (Rd.89)
coating Indoor
-Ministry of
2 d a ~ Outdoor 7.5 0.24 Education
after Indoor 2811.12
(R'9.95
)(Japan 1
coating Indoor 51.7 : 0.08ppm
3 day Outdoor 7.5 0.23
after Indoor 2130.20
coating 42.45 (R2=0.97
)Indoor
REFERENCES
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