semi合集-English.pdf - 第7033页
SEMI S14-0704 © SEMI 2000, 2004 12 RELATED INFORMATION 2 SMOKE MANAGEMENT IN CLEANROOMS NOTICE : This related information is not an o fficial part of SEMI S14 and was deri ved from the work of a mem ber of the Fire Pr ot…

SEMI S14-0704 © SEMI 2000, 2004 11
RELATED INFORMATION 1
TEST PROTOCOL FOR WET BENCH MATERIALS PROCESS
COMPATIBILITY
NOTICE: This related information is not an official part of SEMI S14 and is not intended to modify or supersede the official
guideline. It has been derived from the cited work. Publication is authorized by vote of the responsible committee. Determination
of the suitability of this material is solely the responsibility of the user.
R1-1 SEMATECH has published the results of a study
on testing of polymeric materials for use in wet
benches. The Abstract and citation are provided as
Related Information 1 to SEMI S14, Safety Guidelines
for Fire Risk Assessment and Mitigation for
Semiconductor Manufacturing Equipment as the
responsible committee believes the information in this
document may be of use in identifying materials that
are appropriate for the described applications and
consistent with appropriate management of fire risks.
R1-2 The report, SEMATECH Document ID #:
98123623A-ENG, entitled Process Compatibility
Parameters for Wet Bench Plastic Materials, was
written by Archibald Tewarson, Avtar S. Jassal, Latif
Ahmed, and Mark Camenzind and published 30
December 1998.
R1-3 SEMATECH retains the copyright to the
document, but has granted SEMI permission to include
the Abstract and citation in this Safety Guideline. The
complete document (90 pages) is available from
SEMATECH' s web site:
http://www.sematech.org/public/docubase/abstract/tech
-5.htm.
R1-4 Abstract
R1-4.1 This report presents a test protocol of accepted
analytical procedures to determine the process
compatibility parameters for commonly used wet bench
plastic materials (PP, FRPP, and PVC) and proposed
plastic materials (CPVC, ECTFE, and PVDF) that may
be used for wet bench construction. Three industry
standard test methods were used to determine the
outgassing, leaching, and extraction parameters, defined
in combination as the process compatibility parameters.
To supplement them, the presence of critical elements
at the surface of the materials and the condition of the
surface were examined before and after exposure to
water and chemicals. Changes in the mass of plastic
materials as a result of outgassing, leaching, and
extraction were also used to supplement the parameters.
The report includes details of the test procedures, data
analysis, surface topography of the plastic materials,
before and after exposure to water and chemicals, and
discussion of the results.

SEMI S14-0704 © SEMI 2000, 2004 12
RELATED INFORMATION 2
SMOKE MANAGEMENT IN CLEANROOMS
NOTICE: This related information is not an official part of SEMI S14 and was derived from the work of a member
of the Fire Protection Task Force of the North American Environmental, Health, and Safety Committee. This
related information was approved for publication by 2/3 committee vote on July 17, 2003.
R2-1 Introduction
R2-1.1 Semiconductor cleanrooms are operationally
sensitive to products of a fire. A fire will result in
smoke and corrosive particle contamination to the
cleanroom, process equipment, and work in process. A
properly designed, installed, and maintained smoke
detection and control system will not prevent
contamination, but will limit the spread and
concentration of the contaminant. The basis of the
smoke control system design should be aligned with the
organization’s risk management objectives.
R2-1.2 This Related Information deals with smoke
management systems for cleanrooms themselves, not
for equipment. Smoke removal from a cleanroom may
be performed by ventilation systems that are in place
for other purposes (e.g., process exhaust systems of
equipment) or by equipment designed and installed
specifically to remove smoke from the room. These
may both be parts of the protection for a cleanroom and
may differ in how they are activated.
R2-2 Actuation
R2-2.1 Automatic actuation of dedicated smoke control
systems is preferable; however, many facilities prefer
manual activation. If the system is manually activated,
the following should be done.
R2-2.1.1 The smoke detection system should be
monitored by qualified personnel 24 hours per day.
R2-2.1.2 Emergency response teams (ERT) or other
personnel authorized to actuate the manual smoke
control system should be capable of prompt
notification.
R2-2.1.3 Detailed smoke control emergency
procedures should be documented and practiced. These
procedures can include hazardous gas shutdowns and
shutdowns of appropriate air recirculation fans as well
as activating the smoke control exhaust fans.
R2-2.2 A secondary means of manual actuation of the
smoke/contaminant control system should be provided
in a clearly marked and accessible area outside the
cleanroom.
R2-3 Capacity
R2-3.1 The smoke control system capacity needed is
directly related to the design fire size which depends
upon the type, amount and arrangement of combustible
materials in the cleanroom. In order to achieve a
system that is economically feasible, the maximum
design fire size should be limited to the fire size at
sprinkler operation. For a typical cleanroom
configuration, the fire size at sprinkler operation is in
the range of 600 to 800 kilowatts.
R2-3.2 Smoke removal system capacity can be
designed based on an integrated system approach. The
total capacity can include the fume exhaust system
capacity and dedicated smoke removal system capacity.
R2-4 Design Considerations
R2-4.1 When the fume exhaust system is used for
smoke removal, the following design parameters should
be followed.
R2-4.1.1 The fume exhaust system ductwork should be
of non-combustible construction or should be
listed/approved for smoke removal and not incorporate
the use of fire dampers or interrupters.
R2-4.1.2 It should be confirmed that sufficient fume
exhaust system intake points exist throughout the clean
room. If not, additional intake points should be
provided and incorporate the use of normally closed
dampers. These dampers should be opened either
automatically by activation of the smoke detection
system or by manual means.
R2-4.1.3 When the fume exhaust system is used for
smoke removal, it can incorporate the use of variable
speed fan(s). During the smoke removal mode, fire
dampers on supplemental intake points will open and
the fan speed will be increased. The design capture
velocity at the tool(s) could be affected, and this should
be reviewed. Necessary balancing changes should be
made to ensure the design capture velocity is
maintained.
R2-4.2 The ventilation system make-up air fans should
be sized such that under full smoke and process
exhaust, the fabrication area maintains a positive
pressure relative the adjacent areas.

SEMI S14-0704 © SEMI 2000, 2004 13
R2-4.3 Smoke removal system intake locations are
dependent on the fabrication area design. Design
alternatives should be addressed with a competent fire
protection engineering design firm. For example, for
open manufacturing areas, smoke removal system
intake sequencing should be designed such that
individual zones can be activated to prevent
contaminant migration to adjacent clean areas of the
fab. From a smoke removal perspective, ducted returns
are a better option than open attic plenum
configurations.
R2-5 Testing
R2-5.1 The smoke/contaminant control system should
have a functional test done annually of all detection and
control systems including system dampers and fans.
The system should be designed so that operational and
functional testing can be done without interruption to
the normal clean room air handling.
R2-5.2 The smoke/contaminant control system for new
semiconductor facilities should be fully tested during
mechanical system tests done near the end of the
construction process. Testing should consist of a
complete functional test of detection and control
systems, plus activation of smoke/contaminant removal
fan and damper systems. The performance of the
smoke/contaminant removal system should be verified
using either sulfur hexafluoride (SF
6
) or another tracer
gas method.