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Evaluation of Indoor Air Quality Improvement by Formaldehyde Emission Rate in School Indoor Environment Using Mass Balance

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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-

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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

so

on. 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

so

on.

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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Outdoor

4.1

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Indoor

After remodehg

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1 day after coating

Outdoor Indoor Indoor

-

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(Japan 1

: 0.08ppm

(5)

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0 Before remodehg After remodeling 1 day after remodehg

-1

0

Fig. 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 O

o]-$z)q HCHO !g~J$q. 7 , F k 4

installation instalIation coating coating coating

5s

+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

(6)

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~1 1991;4: 31-38 kxa

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1 - 0 I - O L ,

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7d$q9

3

$9, elm, w f .

A ~ Q A ~

9

;?- 5)xq 44 2714 zhi 2 9 4 %

327).

q@qAJqqX]

2003;18(3):101-110

oJqa.4q27) 1 $ g $ q kg

" -

A3347).

q@f q2ht

f

g 4 4 0 0

q g ~ ] 2003;79:1(n-117

O~+e,qgf, 61719, 3 s a . 48

A I ~ , F ~ I

rdrs i - f f q q -17126

A13 1%41 a@ 97. @qg

$ ~ A J % L ~ x ]

2000;26(3):50-54

$*4,4~19, ol%Q, @I-%+, ",F

f-9. +-qz+h]+jq 421 2 4L# .4q41 qE Zsgrj]%]S

%LE @3+.

@qggxaqqzl

2 W ;30(3

)

:259 -263

5 q + , q q q 4 *JA)gq 413 *J q g ~ 1 5 9 5 q 04046650, 5 q 3 2 0 0 3 .

~ 7 j + . . ^ ? . q + 7 ] ~ ~ ; l j h ] ~ * J $ 2004 ;46 -5 1

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109-113

Daisey JM, Angell WJ and Apte MG.

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MeininghausR, Kouniali A, Mandin C and Cicolella A. Risk assessment of sensory initants in indoor air

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a case study in a French school. Environment International 2003;28: 553-557 NIOSH. NIOSH Manual of Analytical

Methods(NMAM).htIp J/www.cdcCgov /niosh/ nmam 2003.

Rosen KG and Richardson G. Would removing indoor air particulates in children's environments reduce

I-dte

of absenteeism - A hypothesis. the Science of Total Environment

1999;234: 87-93

Sekine Y and Nishimura A. Removal of formaldehyde from indoor air by passive type air-cleaning materials.

Atmospheric Environment 2001;35:

2001-2007

Yang W, L e e K a d Q l P l g U m . . on of indoor air quality using multiple measurements of nitrogen dioxide.

Indoor Air 2004;14: 105-111

수치

Fig. 1.  Sampling process for formaldehyde in schoolroom.
Table  1.  bstrumen t  and a.nalysis condition for HCHO  concentration  Sample site  Outdoor  4.1  Before  0.130  0.002  remodeling  Indoor  7.3  (R2=0.954  )  Indoor  After  remodehg  Outdoor Indoor  Indoor  1 day  after coating  Outdoor Indoor  Indoor  -
Fig. 2.  Comparison be tween indoor HCHO concentrations and  source emission rates of HCHO

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