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BEAM P

LUS FOR

N

EW

B

UILDINGS

I

NDOOR

E

NVIRONMENTAL

Q

UALITY

(I

EQ

)

V

ERSION

1.2

Copyright © 2012 BEAM Society Limited. All rights reserved.

Page 138

6.3 I

NDOOR

A

IR

Q

UALITY

I

EQ

5 C

ONSTRUCTION

IAQ M

ANAGEMENT

I

EQ

6 O

UTDOOR

S

OURCES OF

A

IR POLLUTION

I

EQ

7 I

NDOOR

S

OURCES OF

A

IR POLLUTION

I

EQ

8 IAQ

IN

C

AR

P

ARKS

B

ACKGROUND

Indoor air quality (IAQ) is defined by a list of the constituents, in both

solid and gaseous states, in air. Subjectively, IAQ is the human

perceived response to nasal irritants in the air. ASHRAE [5] defines

‘Acceptable Indoor Air Quality’ as “air in which there are no known

contaminants at harmful concentrations as determined by cognizant

authorities and with which a substantial majority (80% or more) of the

people exposed do not express dissatisfaction.”

A key factor in determining appropriate standards for IAQ is the duration

of exposure. Exposure to indoor pollutants for a matter of minutes (e.g.

car parks), hours (e.g. entertainment establishments), or over a working

day (e.g. offices, classrooms, etc) will be different for most parameters

depending on dose and response. For example, limits of the exposure

considered acceptable for the general public, include the young and

infirm, are different from exposures considered acceptable for the

sedentary workplace, and certainly, the industrial workplace.

Sources of indoor pollutants include outdoor pollutants, building fabric

materials, interior finishes, building systems and equipment, appliances,

consumer products, and the occupants and their activities. The selection

of building materials is important, as pollutants can be emitted for weeks,

months or even years after installation. The design of the building

envelope should consider moisture and vapour penetration, and

infiltration. Air intakes should be sited away from pollutant sources and

avoid short-circuiting with exhausts. Ventilation system design should not

introduce pollutants, and filtering should be effective in removing outdoor

pollutants.

6.4 V

ENTILATION

I

EQ

9 I

NCREASED

V

ENTILATION

I

EQ

10 B

ACKGROUND

V

ENTILATION

I

EQ

11 L

OCALISED

V

ENTILATION

I

EQ

12 V

ENTILATION IN

C

OMMON

A

REAS

B

ACKGROUND

The outside air ventilation to a centrally air-conditioned building should

be adequate for the intended levels of occupancy. The criteria often used

to indicate satisfactory provision of ventilation in occupied premises is

the level of carbon dioxide (CO

2

) at design occupancy. In Hong Kong, it

is usual that the minimum values for ventilation rate for various spaces

will be specified in accordance with an appropriate version of ASHRAE

62 [5], or an equivalent design standard. However, the amount of

ventilation supply reaching the breathing zone of occupants is critical to

the adequacy of the ventilation. Inadequate distribution within zones or

within rooms can result in dissatisfaction at a local level, even if the total

ventilation supplied to a space meets specification. It is not possible to

use CO

2

as a measure of satisfactory performance in unoccupied

premises, but it is possible to determine if ventilation will be satisfactory

through measurement of ventilation rate and ventilation effectiveness.

There are three basic requirements for ventilation of occupied rooms and

rooms used for habitation [6,7]; background ventilation, local exhaust,

5

American Society of Heating, Refrigeration and Air-conditioning Engineers. ASHRAE 62.1-2007: Ventilation for Acceptable

Indoor Air Quality. Atlanta 2007.

6

ASHRAE Standard 62.2. Ventilation and Acceptable Indoor Air Quality in Low-Rise Residential Buildings. Atlanta 2007.

7

UK Department of the Environment and Welsh Office. The Building Regulations Part F Ventilation.