Regl. 3215, art. 20
Interpretation. As used in this
Length: 28,000 wordsOfficial source
Cite as Reglamento Núm. 3215, Art. 20
Agreement, words in the singular include the
plural and words in the plural include the
singular. The descriptive headings for each
Section of this Agreement shall not affect the
interpretation or the legal efficacy of this
Agreement.
In Witness Whereof the parties have
caused this Agreement to be executed by
their respective officers duly authorized and
their corporate seals to be hereunto affixed
and attested as of the date first above
written: The parties below certify :hat the
wording of this Agreement is identical to the
wording specified in 40 CFR 264.151(a)(1) as
such regulations were constituted on the date
first above written.
[Signature of Grantor)
(Title]
Attest:
[Title]
[Seal]
[Signature of Trustee]
[Title]
[Seal]
(2) The following is an example of the
certification of acknowledgment which
must accompany the trust agreement for
a trust fund as specified in §§ 264.143(a)
and 264.145(a) or §§ 265.143(a) or
265.145(a) of this chapter. State
requirements may differ on the proper
content of this acknowledgment.
State of
County of
On this [date]. before me personally came
[owner or operator] to me known. who. being
by me duly sworn. did depose and say that
she/he resides at [address]. that she/he is
[title] of [corporation], the corporation
described in and which executed the above
instrument; that she/he knows the seal of
said corporation; that the seal affixed to such
instrument is such corporate seal: that it was
60 affixed by order of the Board of Directors
[Sec. 264.151(a)(2)]
200
PERMITTED FACILITIES STANDARDS
S-618
of said corporation. and that she/he signed
her/his name thereto by like order.
[Signature of Notary Public]
(b) A surety bond guaranteeing
payment into a trust fund. as specified in
§§ 264.143(b) or 264.145(b) or
§§ 265.143(b) or 265.145(b) of this
chapter, must be worded as follows,
except that instructions in brackets are
to be replaced with the relevant
information and the brackets deleted:
Financial Guarantee Bond
[Corrected by 47 FR 19995. May 10,
1982]
Date bond executed:
Effective date:
Principal: [legal name and business address
of owner or operator]
Type of organization: [insert "individual."
"joint venture," "partnership." or
"corporation"]
State of incorporation:
Surety(ies): [name(s) and business
address(es)]
EPA Identification Number, name. address.
and closure and/or post-closure amount(s)
for each facility guaranteed by this bond
[indicate closure and post-closure amounts
separately]:
Total penal sum of bond: $
Surety's bond number:
Know All Persons By These Presents. That
we, the Principal and Surety(ies) hereto are
firmly bound to the U.S. Environmental
Protection Agency (hereinafter called EPA).
in the above penal suni for the payment of
which we bind ourselves. our heirs.
executors. administrators. successors. and
assigns jointly and severally: provided that,
where the Surety(ies) are corporations acting
as co-sureties. we, the Sureties, bind
ourselves in such sum "jointly and severally"
only for the purpose of allowing a joint action
or actions against any or all of us. and for all
other purposes each Surety binds itself.
jointly and severally with the Principal, for
the payment of such sum only as is set forth
opposite the name of such Surety, but if no
limit of liability is indicated. the limit of
liability shall be the full amount of the penal
sum.
Whereas said Principal is required. under
the Resource Conservation and Recovery Act
85 amended (RCRA). to have a permit or
interim status in order to own or operate each
hazardous waste management facility
identified above, and
Whereas said principal is required to
provide financial essurance for closure, or
closure and post-closure care, 88 a condition
of the permit or interim status, and
Whereas said Principal shall establish a
standby trust fund as is required when a
surety bond is used to provide such financial
assurance:
Now, Therefore, the conditions of the
obligation are such that if the Principal shall
faithfully. before the beginning of final
closure of each facility identified above. fund
the standby trust fund in the amount(s)
identified above for the facility,
Or, if the Principal shall fund the standby
trust fund in such amount(s) within 15 days
after an order to begin closure is issued by an
EPA Regional Administrator or a U.S. district
court or other court of competent jurisdiction.
Or, if the Principal shall provide alternate
financial assurance, as specified in Subpart H
of 40 CFR Parts 264 or 265, 88 applicable, and
obtain the EPA Regional Administrator's
written approval of such assurance. within 90
days after the date notice of cancellation is
received by both the Principal and the EPA
Regional Administrator(s) from the
Surety(ies). then this obligation shall be null
and void, otherwise it is to remain in full
force and effect.
The Surety(ies) shall become liable on this
bond obligation only when the Principal has
failed to fulfill the conditions described
above. Upon notification by an EPA Regional
Administrator that the Principal has failed to
perform as guaranteed by this bond. the
Surety(ies) shall place funds in the amount
guaranteed for the facility(ies) into the
standby trust fund as directed by the EPA
Regional Administrator.
The liability of the Surety(ies) shall not be
discharged by any payment or succession of
payments hereunder. unless and until such
payment or payments shall amount in the
aggregate to the penal sum of the bond. but in
no event shall the obligation of the
Surrity(ies) hereunder exceed the amount of
said penal sum.
The Surety(ies) may cancel the bond by
sending notice of cancellation by certified
mail to the Principal and to the EPA Regional
Administrator(s) for the Region(s) in which
the facility(ies) is (are) located, provided,
however. that cancellation shall not occur
during the 120 days beginning on the date of
receipt of the notice of cancellation by both
the Principal and the EPA Regional
Administrator(s), as evidenced by the return
receipts.
The Principal may terminate this bond by
sending written notice to the Surety(ies).
provided. however, that no such notice shall
become effective until the Surety(ies)
receive(s) written authorization for
termination of the bond by the EPA Regional
Administrator(s) of the EPA Region(s) in
which the bonded facility(ies) is (are) located.
[The following paragraph is an optional
rider that may be included but is not
required.]
Principal and Surety (ies) hereby eyree to
adjust the penal sum of the bond yearly so
that it guarantees a new closure and/or postclosure amount. provided that the penal sum
does not increase by more than 20 percent in
any one year, and no decrease in the penal
sum takes place without the written
permission of the EPA Regional
Administrator(s).
In Witness Whereof. the Principal and
Surety(ies) have executed this Financial
Cuarantee Bond and have affixed their seals
on the date set forth above.
The persons whose signatures appear
below hereby certify that they are authorized
to execute this surety bond on behalf of the
Principal and Surety(ies) and that the
wording of this surety bond is identical to the
wording specified in 40 CFR 264.151(b) as
such regulations were constituted on the date
this bond was executed.
Principal
[Signature(s)]
[Name(s)]
[Title(s)]
[Corporate seal]
Corporate Surety(ies)
[Name and address)
State of incorporation:
Liability limit: $
[Signature(s)]
[Name(s) and title(s)]
[Corporate seal]
[For every co-surety, provide signature(s).
corporate seal. and other information in the
same manner as for Surety above.)
Bond premium: $
(c) A surety bond guaranteeing
performance of closure and/or postclosure care, as specified in
§§ 264.143(c) or 264.145(c). must be
worded as follows, except that the
instructions in brackets are to be
replaced with the relevant information
and the brackets deleted:
Performance Bond
[Corrected by 47 FR 19995, May 10,
1982]
Date bond executed:
Effective date:
Principal: [legal name and business address
of owner or operator]
Type of organization: [insert "individual"
"joint venture." "partnership." or
"corporation"]
State of incorporation:
Surety(ies):
[name(s)
and
business
address(es)]
EPA Identification/Number. name. address.
and closure and/or post-closure amount(s)
for each facility guaranteed by this bond
[indicate closure and post-closure amounts
separately]
Total penal sum of bond: $
Surety's bond number:
Know All Persons By These Presents. That
we, the Principal and Suraty(ies) hereto are
firmly bound to the U.S. Environmental
Protection Agency (hereinafter called EPA).
in the above penal sum for the payment of
which WE bind ourselves. our heirs,
executors. administrators. successors. and
assigns jointly and severally: provided that
where the Surety(ies) are corporations acting
as co-sureties, we. the Sureties: bind
[Sec. 264.151(c)]
161:2038
ourselves in such sum "jointly and severally"
only for the purpose of allowing a joint action
or actions against any or all of us. and for all
other purposes each Surety binds itself.
jointly and severally with the Principal, for
the payment of such sum only as is set forth
opposite the name of such Surety. but if no
limit of liability is indicated. the limit of
liability shall be the full amount of the penal
sum.
Whereas said Principal is required. under
the Resource Conservation and Recovery Act
as amended (RCRA), to have a permit in
order to own or operate each hazardous
waste management facility indentified above,
and
Whereas said Principal is required to
provide financial assurance for closure. or
closure and post-closure care. as 8 condition
of the permit. and
Whereas said Principal shall establish a
standby trust fund as is required when 8
surely bond is used to provide such financial
assurance;
Now, Therefore, the conditions of this
obligation are such that if the Principal shall
faithfully perform closure, whenever required
to do 60, of each facility for which this bond
guarantees closure, in accordance with the
closure plan and other requirements of the
permit 8$ such plan and permit may be
amended. pursuant to all applicable laws,
statutes, rules. and regulations, as such laws,
statutes, rules, and regulations may be
amended,
And. if the Principal shall faithfully perform
post-closure care of each facility for which
this bond guarantees post-closure care, in
accordance with the post-closure plan and
other requirements of the permit. as such plan
and permit may be amended, pursuant to all
applicable laws, statutes. rules. and
regulations, as such laws. statutes. rules. and
regulations may be amended,
Or, if the Principal shall provide alternate
financial assurance as specified in Subpart H
of 40 CFR Part 264, and obtain the EPA
Regional Administrator's written approval of
such assurance, within 90 days after the date
notice of cancellation is received by both the
Principal and the EPA Regional
Administrator(s) from the Surety(ies). then
this obligation shall be null and void,
otherwise it is to remain in full force and
effect.
The Surety(ies) shall become liable on this
bond obligation only when the Principal has
failed to fulfill the conditions described
above.
Upon notification by an EPA Regional
Administrator that the Principal has been
found in violation of the closure requirements
of 40 CFR Part 264, for a facility for which
this bond guarantees performance of
closure, the Surety(ies) shall either perform
closure in accordance with the closure plan
and other permit requirements or place the
closure amount guaranteed for the facility
into the standby trust fund as directed by the
EPA Regional Administrator.
Upon notification by an EPA Regional
Administrator that the Principal has been
found in violation of the post-closure
requirements of 40 CFR Part 264 for a facility
for which this bond guarantees performance
of post-closure care. the Surety(ies) shall
either perform post-closure care in
accordance with the post-closure plan and
other permit requirements or place the postclosure amount guaranteed for the facility
Into the standby trust fund as directed by the
EPA Regional Administrator.
Upon notification by an EPA Regional
Administrator that the Principal has failed to
provide alternate financial assurance as
specified in Subpart H of 40 CFR Part 264,
and obtain written approval of such
assurance from the EPA Regional
Administrator(s) during the 90 days following
receipt by both the Principal and the EPA
Regional Administrator(s) of a notice of
cancellation of the bond. the Surety(ies) shall
place funds in the amount guaranteed for the
facility(ies) into the standby trust fund as
directed by the EPA Regional Administrator.
The surety(ies) hereby waive(s) notification
of amendments to closure plans. permits,
applicable laws, statutes. rules, and
regulations and agrees that no such
amendment shall in any way alleviate its
(their) obligation on this bond.
The liability of the Surety(ies) shall not be
discharged by any payment or succession of
payments hereunder, unless and until such
payment or payments shall amount in the
aggregate to the penal sum of the bond. but in
no event shall the obligation of the
Surety(ies) hereunder exceed the amount of
said penal sum.
The Surety(ies) may cancel the bond by
sending notice of cancellation by certified
mail to the owner or operator and to the EPA
Regional Administrator(s) for the Region(s) in
which the facility(ies) is (are) located,
provided. however, that cancellation shall
not occur during the 120 days beginning on
the date of receipt of the notice of
cancellation by both the Principal and the
EPA Regional Administrator(s), as evidenced
by the return receipts.
The principal may terminate this bond by
sending written notice to the Surety(ies).
provided. however. that no such notice shall
become effective until the Surety(ies)
receive(s) written authorization for
termination of the bond by the EPA Regional
Administrator(s) of the EPA Region(s) in
which the bonded facility(ies) is (are) located.
[The following paragraph is an optional
rider that may be included but is not
required.)
Principal and Surety(ies) hereby agree to
adjust the penal sum of the bond yearly so
that it guarantees a new closure and/or postclosure amount. provided that the penal sum
does not increase by more than 20 percent in
any one year, and no decrease in the penal
sum takes place without the written
permission of the EPA Regional
Administrator(s).
in Witness Whereof, The Principal and
Surety(ies) have executed this Performance
Bond and have affixed their seals on the date
set forth above.
The persons whose signatures appear
below hereby certify that they are authorized
to execute this surety bond on behalf of the
Principal and Surety(ies) and that the
wording of this surety bond is identical to the
wording specified in 40 CFR 264.151(c) as
such regulation was constituted on the date
this bond was executed.
Principal
[Signature(s)]
[Name(s)]
[Title(s)]
(Corporate seal]
Corporate Surety(ies)
[Name and address]
State of incorporation:
Liability limit: $
[Signature(s)]
[Name(s) and title(s)]
Corporate seal:
[For every co-surely. provide signature(s),
corporate seal. and other information in the
same manner as for Surety above.]
Bond premium: $
(d) A letter of credit, as specified in
§§ 264.143(d) or 264.145(d) or
§§ 265.143(c) or 265.145(c) of this
chapter, must be worded as follows,
except that instructions in brackets are
to be replaced with the relevant
information and the brackets deleted:
Irrevocable Standby Letter of Credit
Regional Administrator(s)
Region(s)
U.S. Environmental Protection Agency
Dear Sir or Madam: We bereby establish
our Irrevocable Standby Letter of Credit
No. in your favor, at the request and for
the account of [owner's or operator's name
and address) up to the aggregate amount of
[in words] U.S. dollars S-. available.upon
presentation [insert, if more than one
Regional Administrator is a beneficiary. "by
any one of you") of
(1) your sight draft. bearing reference to
this letter of credit
and
(2) your signed statement reading as
follows: "I certify that the amount of the draft
is payable pursuant to regulations issued
under authority of the Resource Conservation
and Recovery Act of 1976 as amended."
This letter of credit is effective as of [date]
and shall expire on [date at least 1 year
later}. but such expiration date shall be
automatically extended for a period of [at
least 1 year] on [date] and on each successive
expiration date. unless, at least 120 days
before the current expiration date, we notify
both you and [owner's or operator's name] by
certified mail that we have decided not to
extend this letter of credit beyond the current
expiration date. In the event you are so
[Sec. 264.151(d)]
PERMITTED FACILITIES STANDARDS
notified. any unused portion of the credit
shall be available upon presentation of your
sight draft for 120 days after the date of
receipt by both you and (owner's or
operator's name]. as shown on the signed
return receipts.
Whenever this letter of credit is drawn on
under and In compliance with the terms of
this credit, we shall duly honor such draft
upon presentation to us, and we shall deposit
the amount of the draft directly into the
standby trust fund of [owner's or operator's
name] in accordance with your instructions.
We certify that the wording of this letter of
credit is identical to the wording specified in
40 CFR 264.151(d) as such regulations were
constituted on the date shown immediately
below.
[Signature[s] and title(s) of official(s) of
issuing institution] [Date]
This credit is subject to [insert "the most
recent edition of the Uniform Customs and
Practice for Documentary Credits. published
by the International Chamber of Commerce."
or "the Uniform Commercial Code"].
(e) A certificate of insurance, as
specified in §§ 264.143(e) or 264.145(e) or
§§ 265.143(d) or 265.145(d) of this
chapter. must be worded as follows,
except that instructions in brackets are
to be replaced with the relevant
information and the brackets deleted:
Certificate of Insurance for Closure or Post-
Closure Care
Name and Address of Insurer
(herein called the "Insurer"):
Name and Address of Insured
(herein called the "Insured"):
Facilities Covered: [List for each facility: The
EPA Identification Number, name, address,
and the amount of insurance for closure
and/or the amount for post-closure care
(these amounts for all facilities covered
must total the face amount shown below).]
Face Amount:
Policy Number:
Effective Date:
The Insurer hereby certifies that it has
issued to the Insured the policy of insurance
identified above to provide financial
assurance for [insert "closure" or "closure
and post-closure care" or "post-closure care"]
for the facilities identified above. The Insurer
further warrants that such policy conforms in
all respects with the requirements of 40 CFR
264.143(e). 264.145(e). 265.143(d). and
265.145(d). as applicable and as such
regulations were constituted on the date
shown immediately below. It is agreed that
any provision of the policy inconsistent with
such regulations is hereby amended to
eliminate such inconsistency.
Whenever requested by the EPA Regional
Administrator(s) of the U.S. Environmental
Protection Agency, the Insurer agrees to
furnish to the EPA Regional Administrator(s)
a duplicate original of the policy listed above.
including all endorsements thereon.
I hereby certify that the wording of this
certificate is identical to the wording
specified in 40 CFR 264.151(e) as such
regulations were constituted on the date
shown immediately below.
[Authorized signature for Insurer]
[Name of person signing]
[Title of person signing]
Signature of witness or notary:
[Date]
(f) A letter from the chief financial
officer, as specified in §§ 264.143(f) or
264.145(f) or §§ 265.143(e) or 265.145(e)
of this chapter, must be worded as
follows, except that instructions in
brackets are to be replaced with the
relevant information and the brackets
deleted:
Letter From Chief Financial Officer
[Address to Regional Administrator of every
Region in which facilities for which financial
responsibility is to be demonstrated through
the financial test are located.)
I am the chief financial officer of [name
and address of firm]. This letter is in support
of this firm's use of the financial test to
demonstrate financial assurance, as specified
in Subpart H of 40 CFR Parts 264 and 265.
(Fill out the following four paragraphs
regarding facilities and associated cost
estimates. If your firm has no facilities that
belong in a particular paregraph. write
"None" in the space indicated. For each
facility. include its EPA Identification
Number, name, address, and current closure
and/or post-closure cost estimates. Identify
each cost estimate as to whether it is for
closure or post-closure care.]
1. This firm is the owner or operator of the
following facilities for which financial
assurance for closure or post-closure care is
demonstrated through the financial test
specified in Subpart H of 40 CFR Parts 264
and 265. The current closure and/or postclosure cost estimates covered by the test are
shown for each facility:
2. This firm guarantees, through the
corporate guarantee specified in Subpart H of
40 CFR Parts 264 and 265. the closure or postclosure care of the following facilities owned
or operated by subsidiaries of this firm. The
current cost estimates for the closure or postclosure care so guaranteed are shown for
each facility:
3. In States where EPA is not administering
the financial requirements of Subpart H of 40
CFR Parts 264 or 265. this firm. as owner or
operator or guarantor. is demonstrating
financial assurance for the closure or postclosure care of the following facilities through
the use of a test equivalent or substantially
equivalent to the financial test specified in
Subpart H of 40 CFR Parts 264 and 265. The
current closure and/or post-closure cost
estimates covered by such a test are shown
for each facility:
4. This firm is the owner or operator of the
following hazardous waste management
facilities for which financial assurance for
closure or. if a disposal facility, post-closure
care, is not demonstrated either to LPA or a
State through the financial test or any other
financial assurance mechanism specified in
Subpart H of 40 CFR Parts 264 and 265 or
equivalent or substantially equivalent State
mechanisms. The current closure and/or
post-closure cost estimates not covered by
such financial assurance are shown for each
facility:
This firm [insert "is required" or "is not
required") to file a Form 10K with the
Securities and Exchange Commission (SEC)
for the latest fiscal year.
The fiscal year of this firm ends on [month.
day]. The figures for the following items
marked with an asterisk are derived from this
firm's independently audited. year-end
financial statements for the latest completed
fiscal year, ended [date].
[Fill in Alternative 1 If the criteria of
paragraph (f)(1)(i) of 11 264.143 or 254.145, or
of paragraph (e)(1)[i) of $$ 265.143 or 265.145
of this chapter are used. Fill in Alternative II
if the criteria of paragraph (f)(1)(ii) of
$1 264.143 or 264.145, or of paragraph (e){1)(ii)
of §§ 265.143 or 265.145 of this chapter are
used.]
ALTERNATIVE I
$
1. Sum of current ciosure and post-ctosure cost
estimates [total of all cost estimates shown in
the lour paragraphs abovel
"2. Total liabilities (if any portion of the closure
or post-closure cost estimates is included in
total liabilities. you may deduct the amount of
that portion from this line and add that amount
to lines 3 and 4)
*3. Tangible net worth
"4. Net worth
*5. Current assets
"E. Current liabilities
7. Net working caprial fline 5 minus line 6]
"a. The sum of net income plus depreciation,
depletion. and emortization
*9. Total assets in U.S. (required only If less
than 80% of firm's assets are located in the
U.S.).
ALTERNATIVE II
Yes
No
10 Is line 3 at least $10 million?
11. Is line 3 at least 6 times line 1?
12. Is line 7 at least 6 times line 17
*13. Are at least 90% of firm's assets located in
the U S.? H not, complete line 14.
14. Is line 9 at least 6 times line 17
15. Is line 2 divided by line 4 less than 2.07
16. is line 8 divided by line 2 greater man 0.17
17. Is line 5 divided by line 6 greater than 1.57
1. Sum of current closure and post-closure cost
estimates [total of all cost estimates shown in
the four paragraphs above)
2. Current bond rating of most recent issuance
of this firm and name of rating service
3. Date of issuance of bond
4. Date of maturity of bond
$
[Sec. 264.151(f)]
161:2040
*5. Tangible nel worth [if any portion of the
closure and post-closure cost estimates is
included in "total liabilities" on your firm's
financial statements. you may add the amount
of that portion to this line)
$
"6. Total assets in U.S. (required only # less
than 90% of firm's assets are located in. the
U.S.)
Yes
No
7. is line 5 at least $10 miliion?
B. is line 5 at least 6 times line 17
*9. Are at least 90% of firm's assets located in
the U.S.7 If not complete line TO
10. Is line 6 at least 6 times line 1?
$
I hereby certify that the wording of this
letter is identical to the wording specified in
40 CFR 264.151(f) as such regulations were
constituted on the date shown immediately
below.
[Signature]
[Name]
[Title]
(Date)
[Editor's note: EPA July 1, 1982 (47
FR 28627) amended $264.151(g) to add
OMB Control No. 2000-0445.]
(g) A letter from the chief financial
officer, as specified in 264.147(f) or
265.147(f) of this chapter. must be
worded as follows. except that
instructions in brackets are to be
replaced with the relevant information
and the brackets deleted:
Letter from Chief Financial Officer (10
demonstrate liability coverage or to
demonstrate both liability coverage and
assurance of closure or post-closure care).
[Address to Regional Administrator of
every Region in which facilities for which
financial responsibility is to be demonstrated
through the financial test are located.)
I am the chief financial officer of [owner's
or operator's name and address]. This letter
is in support of the use of the financial test to
demonstrate financial responsibility for
liability coverage [insert "and closure and/or
post-closure care" if applicable] as specified
in Subpart H of 40 CFR Parts 264 and 265.
[Fill out the following paragraph regarding
facilities and liability coverage. For each
facility. include its EPA Identification
Number. name, and address.]
The owner or operator identified above is
the owner or operator of the following
facilities for which liability coverage is being
demonstrated through the financial test
specified in Subpart H of 40 CFR Parts 264
and 265:
(If you are using the financial test to
demonstrate coverage of both liability and
closure and post-closure care, fill in the
following four paragraphs regarding facilities
and associated closure and post-closure cost
estimates. If there are no facilities that belong
in a particular paragraph, write "None" in the
space indicated. For each facility. include its
EPA Identification Number, name. address,
and current closure and/or post-closure cost
estimates. Identify each cost estimate as to
whether it is for closure or post-closure care.]
1. The owner or operator identified above
owns or operates the following facilities for
which financial assurance for closure or postclosure care is demonstrated through the
financial test specified in Subpart H of 40
CFR Parts 264 and 265. The current closure
and/or post-closure cost estimates covered
by the test are shown for each facility:
2. The owner or operator identified above
guarantees. through the corporate guarantee
specified in Subpart H of 40 CFR Parts 264
and 205, the closure and post-closure care of
the following facilities owned or operated by
its subsidiaries. The current cost estimates
for the closure or post-closure care so
guaranteed are shown for each facility:
3. in States where EPA is not administering
the financial requirements of Subpart H of 40
CFR Parts 264 and 265, this owner or operator
is demonstrating financial assurance for the
closure or post-closure care of the following
facilities through the use of a test equivalent
or substantially equivalent to the financial
test specified in Subpart H of 40 CFR Parts
264 and 265. The current closure and/or postclosure cost estimates covered by such a test
are shown for each facility:
4. The owner or operator identified above
owns or operates the following hazardous
waste management facilities for which
financial assurance for closure or. if a
disposal facility. post-closure care. is not
demonstrated either to EPA or a State
through the financial test or any other
financial assurance mechanism specified in
Subpart H of 40 CFR Parts 264 and 265 or
equivalent or substantially equivalent State
mechanisms. The current closure and/or
post-closure cost estimates not covered by
such financial assurance are shown for each
facility:
This owner or operator [insert "is required"
or "is not required"] to file a Form 10K with
the Securities and Exchange Commission
(SEC) for the latest fiscal year.
The fiscal year of this owner or operator
ends on [month. day]. The figures for the
following items marked with an asterisk are
derived from this owner's or operator's
independently audited. year-end financial
statements for the latest completed fiscal
year, ended [date].
[Fill in part A if you are using the financial
test to demonstrate coverage only for the
liability requirements.]
Part A. Liability Coverage for Accidental
Occurrences
(Fill in Alternative I if the criteria of
paragraph (f)(1)(i) of $ $ 264.147 or 265.147 are
used. Fill in Alternative II if the criteria of
paragraph (f)(1)(ii) of §§ 264.147 or 265.147
are used.]
ALTERNATIVE I
1. Amount of annual aggregate hability
coverage to be demonstrated
$
"2. Current assets
$
*3. Current habilities
$
4. Net working capital (line 2 minus line
3)
$
*5. Tangible net worth
$
*6. If less than 90% of assets are localed in the U.S., give total U.S. assets
$
YES
NO
7. is line 5 at least $10 million?
8. is line 4 at least 6 times line 17
9. Is line 5 at least 6 times line 17
*10. Are a1 least 90% of assets located
in the U.S.? If not complete line 11.
11. Is line 6 at least 6 times line 17
ALTERNATIVE II
[Corrected by 47 FR 17989, April 27,
1982]
1. Amount of annual aggregate liability
coverage to be demonstrated
$
2. Current bond rating of most recent
issuance and name of rating service
3. Date of issuance of bond
4. Date of maturity of bond
"5. Tengible net worth
$
"6. Total assets in U.S. (required only if
less than 90% of assets are located in
the U.S.)
$
YES
NO
7. Is line 5 at least $10 million?
a. is line 5 at least 6 times line 1?
*9. Are at least 90% of assets located in
the U.S.? If not, complete line 10.
10. Is line 6 at least 6 times line 17
[Fill in part B if you are using the financial
test to demonstrate assurance of both
liability coverage and closure or post-closure
care.]
Port B. Closure or Post-Closure Care and
Liability Coverage
[Fill in Alternative I if the criteria of
paragraphs (f)(1)(i) of $5 264.143 or 264.145
and (f)(1)(i) of § 264.147 are used or if the
criteria of paragraphs (e)(1)(i) of §§ 265.143 or
265.145 and (f)(1)(i) of § 265.147 are used. Fill
in Alternative II if the criteria of paragraphs
[f)(1)(ii) of 11 264.143 or 264.145 and (f)(1)(ii)
of $ 254.147 are used or if the criteria of
paragraphs (e)(1)(ii) of §§ 265.143 or 265.145
and (f)(1)[ii) of 265.147 are used.]
ALTERNATIVE I
1. Sum of current closure and post-closure cost estimates (total of all cost
estimates listed above)
$
2. Amount of annual aggregate liability
coverage to be demonstrated
$
3 Sum of lines 1 and 2
$
"4. Total liabilities (if any portion of your
closure or post-closure cost estimates
is included in your total liabilities, you
may deduct that portion from this line
and add that amount to lines 5 and 6)
$
*5. Tangible net worth
$
*6. Net worth
$
"7. Current assets
$
"6. Current liabilities
$
9. Net working capital (line 7 minus line
B)
$
'10. The sum of net income plus deprectation, depletion, and amortization
$
"11. Total assets in U.S. (required only if
less than 90% of assets are located in
the U.S.)
$
YES
NO
12. is line 5 at least $10 million?
13. is line 5 at least 6 times line 37
[Sec. 264.151(g)]
PERMITTED FACILITIES STANDARDS
S-616
ALTERNATIVE I-Continued
14. is line 9 at least 6 times line 37
-
"15. Are at least 90% of assets located
in the U.S.? If not complete line 16
-
1
16. is line 11 at least 6 times line 37
17. is line 4 divided by line 6 less than
2.07
18. is line 10 divided by line 4 greater
than 0.17
19. is line 7 divided by line 6 greater than
1.57
-
ALTERNATIVE II
" offected In 47 IK 17989. April 27. 19821
1. Sum or current closure and post-closure cost estimates (total of all cost
estimates listed above)
$
2. Amount of annual aggregate liability
coverage to be demonstrated
$
3. Sum of lines 1 and 2
$
4. Current bond rating of most recent
issuance and name of rating service
5. Date of issuance of bond
6. Date of maturity of bond
*7. Tangible net worth (if any portion of
the closure or post-closure cost estmales is included in "total liabilities"
on your financial statements you may
add that portion to this line)
$
*8 Total assets in the U.S. (required only
if less than 90% of assets are located
in the U.S.)
$
YES
NO
9. is line 7 at least $10 million?
10. is line 7 at least 6 times line 3?
"11. Are at least 90% of assets located
in the U.S.? If not. complete line 12
12. Is line B at least 6 times line 3?
I hereby certify that the wording of this
letter is identical to the wording specified in
40 CFR 264.151(g) as such regulations were
constituted on the date shown immediately
below.
[Signature]
[Name]
[Title]
[Date]
[264.151(g) revised by 47 FR 16554,
April 16, 1982]
(h) A corporate guarantee, as
specified in §§ 264.143(f) or 264.145(f) or
§§ 265.143(e) or 265.145(e) of this
chapter, must be worded as follows,
except that instructions in brackets are
to be replaced with the relevant
information and the brackeis deleted:
Corporate Cuarantee for Closure or Post-
Closure Care
Guarantee made this [date] by [name of
guaranteeing entity]. a business corporation
organized under the laws of the State of
[insert name of State]. herein referred to as
guarantor. to the United States
Environmental Protection Agency (EPA).
obligee. on behalf of our subsidiary [owner or
operator) of [business address).
Recitals
1. Guarantor meets or exceeds the financial
test criteria and agrees to comply with the
reporting requirements for guarantors as
specified in 40 CFR 264.143(f). 264.145(f).
265.143(e). and 265.145(e).
2. [Owner or operator] owns or operates
the following hazardous waste management
facility(ies) covered by this guarantee: [List
for each facility: EPA Identification Number,
name, and address. Indicate for each whether
guarantee is for closure. post-closure care. or
both.]
3. "Closure plans" and "post-closure plans"
85 used below refer to the plans maintained
as required by Subpart G of 40 CFR Parts 264
and 265 for the closure and post-closure care
of facilities as identified above.
4. For value received from [owner or
operator], guarantor guarantees to EPA that
in the event that {owner or operator] fails to
perform [insert "closure," "post-closure care"
or "closure and post-closure care"] of the
above facility(ies) in accordance with the
closure or post-closure plans and other
permit or interim status requirements
whenever required to do so, the guarantor
shall do so or establish & trust fund as
specified in Subpart H of 40 CFR Parts 264 or
265, as applicable, in the name of [owner or
operator] in the amount of the current closure
or post-closure cost estimates as specified in
Subpart H of 40 CFR Parts 204 and 265.
5. Guarantor agrees that if, at the end of
any fiscal year before termination of this
guarantee, the guarantor fails to meet the
financial test criteria, guarantor shall send
within 90 days. by certified mail, notice to the
EPA Regional Administrator(s) for the
Region(s) in which the facility(ies) is (are)
located and to [owner or operator] that he
intends to provide alternate financial
assurance as specified in Subpart H of 40
CFR Parts 264 or 265, as applicable, in the
name of (owner or operator]. Within 120 days
after the end of such fiscal year, the
guarantor shall establish such financial
assurance unless [owner or operator] has
done so.
6. The guarantor agrees to notify the EPA
Regional Administrator by certified mail. of a
voluntary or involuntary proceeding under
Title 11 (Bankruptcy). U.S. Code. naming
guarantor as debtor. within 10 days after
commencement of the proceeding.
7. Guarantor agrees that within 30 days
after being notified by an EPA Regional
Administrator of a determination that
guarantor no longer meets the financial test
criteria or that he is disallowed from
continuing as a guarantor of closure or postclosure care, he shall establish alternate
financial assurance 85 specified in Subpart H
of 40 CFR Parts 264 or 265. as applicable, in
the name of [owner or operator] unless
[owner or operator] has done so.
8. Guarantor agrees to remain bound under
this guarantee notwithstanding any or all of
the following: amendment or modification of
the closure or post-closure plan, amendment
or modification of the permit, the extension
or reduction of the time of performance of
closure or post-closure. or any other
modification or alteration of an obligation of
the owner or operator pursuant to 40 CFR
Parts 264 or 265.
9. Guarantor agrees to remain bound under
this guarantee for so long as [owner or
operator] must comply with the applicable
financial assurance requirements of Subpart
H of 40 CFR Parts 264 and 265 for the abovelisted facilities, except that guarantor may
cancel this guarantee by sending notice by
certified mail to the EPA Regional
Administrator(s) for the Region(s) in which
the facility(ies) is (are) located and to [owner
or operator]. such cancellation to become
effective no earlier than 120 days after
receipt of such notice by both EPA and
[owner or operator]. as evidenced by the
return receipts.
10. Cuarantor agrees that if [owner or
operator] fails to provide alternate financial
assurance as specified in Subpart H of 40
CFR Parts 264 or 265, as applicable. and
obtain written approval of such assurance
from the EPA Regional Administrator(s)
within 90 days after a notice of cancellation
by the guarantor is received by an EPA
Regional Administrator from guarantor,
guarantor shall provide such alternate
financial assurance in the name of [owner or
operator].
11. Guarantor expressly waives notice of
acceptance of this guarantee by the EPA or
by [owner or operator]. Guarantor also
expressly waives notice of amendments or
modifications of the closure and/or postclosure plan and of amendments or
modifications of the facility permit(s).
I hereby certify that the wording of this
guarantee is identical to the wording
specified in 40 CFR 264.151(h) as such
regulations were constitituted on the date
first above written.
Effective date:
[Name of guarantor]
(Authorized signature for guarantor]
[Name of person signing]
[Title of person signing]
Signature of witness or nolary:
[264.151(h) added by 47 FR 15047, April
7, 1982]
[264.151(i) and (j) added by 47 FR
16554, April 16. 1982]
[Editor's note: EPA July 1, 1982 (47
FR 28627) amended $264.151(i) to add
OMB Control No. 2000-0445.]
(i) A hazardous waste facility liability
endorsement as required in §§ 264.147
or 265.147 must be worded as follows.
except that instructions in brackets are
to be replaced with the relevant
information and the brackets deleted:
Hazardous Waste Facility Liability
Endorsement
1. This endorsement certifies that the
policy to which the endorsement is attached
provides liability insurance covering bodily
injury and property damage in connection
with the insured's obligation to demonstrate
financial responsibility under 40 CFR 264.147
or 265.147. The coverage applies at [list EPA
Identification Number. name, and address for
each facility] for [insert "sudden accidental
occurrences." "nonsudden accidental
Published by THE BUREAU OF NATIONAL AFFAIRS INC., Washington. D.C. 20037
[Sec. 264.151(i)]
161:2042
occurrences." or "sudden and nonsudden
accidental occurrences"; If coverage is for
multiple facilities and the coverage is
different for different facilities, indicate
which facilities are insured for sudden
accidental occurrences. which are insured for
nonsudden accidental occurrences, and
which are insured for both). The limits of
liability are [insert the dollar amount of the
"each occurrence" and "annual aggregate"
limits of the Insurer's liability), exclusive of
legal defense costs.
2. The insurance afforded with respect to
such occurrences is subject to all of the terms
and conditions of the policy: provided,
however, that any provisions of the policy
inconsistent with subsections (a) through (e)
of this Paragraph 2 are hereby amended to
conform with subsections (a) through (e):
(a) Bankruptcy or insolvency of the insured
shall not relieve the Insurer of its obligations
under the policy to which this endorsement is
attached.
(b) The Insurer is liable for the payment of
amounts within any deductible applicable to
the policy. with a right of reimbursement by
the insured for any such payment made by
the Insurer. This provision does not apply
with respect to that amount of any deductible
for which coverage is demonstrated as
specified in 40 CFR 264.147(f) or 285.147(f).
(c) Whenever requested by a Regional
Administrator of the U.S. Environmental
Protection Agency (EPA). the Insurer agrees
to furnish to the Regional Administrator a
signed duplicate original of the policy and all
endorsements.
(d) Cancellation of this endorsement,
whether by the Insurer or the insured. will be
effective only upon written notice and only
after the expiration of sixty (60) days after a
copy of such written notice is received by the
Regional Administrator(s) of the EPA
Region(s) in which the facility(ies) is (are)
located.
(e) Any other termination of this
endorsement will be effective only upon
written notice and only after the expiration of
thirty (30) days after a copy of such written
notice is received by the Regional
Administrator(s) of the EPA Region(s) in
which the facility(ies) is (are) located.
Attached to and forming part of policy No.
issued by [name of Insurer]. herein
called the Insurer. of [address of Insurer] to
[name of insured] of [address] this - day of
19- The effective date of said policy
is - day of 19-
I hereby certify that the wording of this
endorsement is identical to the wording
specified in 40 CFR 264.151(i) as such
regulation was constituted on the date first
above written, and that the Insurer is
licensed to transact the business of
insurance. or eligible to provide insurance as
an excess or surplus lines insurer. in one or
more States.
[Signature of Authorized Representative of
Insurer]
[Type name]
[Title]. Authorized Representive of [name of
Insurer]
[Address of Representative]
[Editor's note: EPA July 1, 1982 (47 FR 28627)
amended $264.151(j) to add OMB Control No. 2000-
0445.]
(j) A certificate of liability insurance
as required in §§ 264.147 or 265.147 must
be worded as follows, except that the
instructions in brackets are to be
replaced with the relevant information
and the brackets deleted:
Hazardous Waste Facility Certificate of
Liability Insurance
1. [Name of Insurer]. (the "Insurer"), of
[address of Insurer] hereby certifies that it
has issued liability insurance covering bodily
injury and property damage to (name of
insured]. (the "insured"). of [address of
insured) in connection with the insured's
obligation to demonstrate financial
responsibility under 40 CFR 264.147 or
265.147. The coverage applies at [list EPA
Identification Number, name, and address for
each facility] for [insert "sudden accidental
occurrences." "nonsudden accidental
occurrences." or "sudden and nonsudden
accidental occurrences"; if coverage is for
multiple facilities and the coverage is
different for different facilities, indicate
which facilities are insured for sudden
accidental occurrences, which are insured for
nonsudden accidental occurrences. and
which are insured for both]. The limits of
liability are (insert the dollar amount of the
"each occurrence" and "annual aggregate"
limits of the Insurer's liability]. exclusive of
legal defense costs. The coverage is provided
under policy number issued on [date].
The effective date of said policy is [date].
2. The Insurer further certifies the following
with respect to the insurance described in
Paragraph 1:
(a) Bankruptcy or insolvency of the insured
shall not relieve the Insurer of ils obligations
under the policy.
(b) The Insurer is liable for the payment of
amounts within any deductible applicable to
the policy, with 8 right of reimbursement by
the insured for any such payment made by
the Insurer. This provision does not apply
with respect to that amount of any deductible
for which coverage is demonstrated as
specified in 40 CFR 264.147(f) or 265.147(f).
(c) Whenever requested by a Regional
Administrator of the U.S. Environmental
Protection Agency (EPA). the Insurer agrees
to furnish to the Regional Administrator a
signed duplicate original of the policy and all
endorsements.
(d) Cancellation of the insurance, whether
by the Insurer or the insured. will be effective
only upon written notice and only after the
expiration of sixty (60) days after a copy of
such written notice is received by the
Regional Administrator(s) of the EPA
Region(s) in which the facility(ies) is (are)
located.
(c) Any other termination of the insurance
will be effective only upon written notice and
only after the expiration of thirty (30) days
after a copy of such written notice is received
by the Regional Administrator(s) of the EPA
Region(s) in which the facility(ies) is (are)
located.
I hereby certify that the wording of this
instrument is identical to the wording
specified in 40 CFR 264.151(j) as such
regulation was constituted on the date first
above written, and that the Insurer is
licensed to transact the business of
insurance, or eligible to provide insurance as
an excess or surplus lines insurer, in one or
more States.
[Signature of authorized representative of
Insurer]
[Type name]
[Title]. Authorized Representative of Iname
of Insurer]
[Address of Representative]
Subpart I-Use and Management of
Containers
[Interim final]
[Subpart I added by 46 FR 2847,
January 12, 1981)
$ 264.170 Applicability.
The regulations in this Subpart apply
to owners and operators of all
hazardous waste facilities that store
containers of hazardous waste, except
as § 264.1 provides otherwise.
[Comment: Under § 261.7 and
$ 261.33(c). if 8 hazardous waste is
(Sec. 264.170]
206
ANEJO B12
29 CFR 1910.94
Ventilation
Subparte G-Occupational Health
and Environmental Control
§ 1910.69
Anejo B12
Manlifts found to be unsale shall not
be operated until properly repaired.
(2) Items covered. This periodic inspection shall cover but is not limited
to the following items:
Steps.
Step Fastenings.
Rails.
Rail Supports and Pastenings.
Rollers and Slides.
Belt and Belt Tension.
Handholds and Fastenings.
Floor Landings.
Guardrails.
Lubrication.
Limit Switches.
Warning Signs and Lights.
Illumination.
Drive Pulley.
Bottom (boot) Pulley and Clearance.
Pulley Supports.
Motor.
Driving Mechanism.
Brake.
Electrical Switches.
Vibration and Misalignment.
"Skip" on up or down run when mounting
step (indicating worn gears).
(3) Inspection log. A written record
shall be kept of findings at each inspection. Records of inspection shall
be made available to the Assistant Secretary of Labor or his duly authorized
representative.
(SOURCE ANSI A90.1-1969 Safety Code for
Manlifts.)
OMB CONTROL No. 1218-0055, paragraph (e)(3). (47 FR 14706, Apr. 6,
1982)
(Secs. 4(b)(2). 6(b) and 8(c), 84 Stat. 1592.
1593, 1596, 29 U.S.C. 653, 655, 657; Secretary
of Labor's Order No. 8-76 (41 FR 25059); 29
CFR Part 1911)
139 FR 23502. June 27. 1974. as amended at
43 FR 49746. Oct. 24, 1978; 47 FR 14706,
Apr. 6. 1982)
$ 1910.69 Sources of standards.
$ 1910.70 Standards organizations.
Sec
Source
1910 66
ANSI A120.1-1970 Safety Code for Powered
Platforms for Exterior Building Mainte.
nance
1910.67
ANSI A92 2-1969 American National Stand.
and for Vehicle-Mounted Elevaling and Rotaking Work Platforms
1910 68
ANSI A90 1-1969 Safety Code for Manlifts
Specific standards of the following
organizations have been referenced In
this subpart. Copies of the standards
may be obtained from the issuing organization.
American National Standards Institute
1430 Broadway
New York. New York 10018
Subport G-Occupational Health and
Environmental Control
American Welding Society
2501 NW. 7th Street
Miami, Florida 33125
139 FR 23502. June 27. 1974. as amended at
40 FR 13440. Mar. 26, 1975)
$ 1910.94 Ventilation.
(a) Abrasive blasting-(1) Definitions applicable to this paragraph-(i)
Abrasive. A solid substance used in an
abrasive blasting operation.
(ii) Abrasive-blasting respirator. A
continuous flow air-line respirator constructed so that it will cover the wearer's head, neck. and shoulders to protect him from rebounding abrasive.
(iii) Blast cleaning barrel. A complete enclosure which rotates on an
axis, or which has an internal moving
tread to tumble the parts, in order to
expose various surfaces of the parts to
the action of an automatic blast spray.
(iv) Blast cleaning room. A complete
enclosure in which blasting operations
are performed and where the operator
works inside of the room to operate
the blasting nozzle and direct the flow
of the abrasive material.
(v) Blasting cabinet. An enclosure
where the operator stands outside and
operates the blasting nozzle through
an opening or openings in the enclosure.
(vi) Clean air. Air of such purity
that it will not cause harm or discomfort to an individual if it is inhaled for
extended periods of time.
(vii) Dust collector. A device or combination of devices for separating dust
from the air handled by an exhaust
ventilation system.
(viii) Exhaust ventilation system. A
system for removing contaminated air
from a space, comprising two or more
of the following elements (a) enclosure or hood, (b) duct work, (c) dust
collecting equipment, (d) exhauster,
and (e) discharge stack.
(ix) Particulate-filter respirator. An
air purifying respirator, commonly referred to as a dust or a fume respirator, which removes most of the dust or
fume from the air passing through the
device.
(x) Respirable dust. Airborne dust in
sizes capable of passing through the
upper respiratory system to reach the
lower lung passages.
(xi) Rotary blast cleaning table. An
enclosure where the pieces to be
cleaned are positioned on a rotating
table and are passed automatically
through a series of blast sprays.
(xii) Abrasive blasting. The forcible
application of an abrasive to a surface
by pneumatic pressure, hydraulic pressure, or centrifugal force.
sides away from any occupied area, to
provide for pressure relief in case of
explosion, following the principles set
forth in the National Fire Protection
Association Explosion Venting Guide.
NFPA 68-1954.
(3) Blast-cleaning enclosures. (i)
Blast-cleaning enclosures shall be exhaust ventilated in such a way that a
continuous inward flow of air will be
maintained at all openings in the enclosure during the blasting operation.
(a) All air inlets and access openings
shall be baffled or so arranged that by
the combination of inward air flow
and baffling the escape of abrasive or
dust particules into an adjacent work
area will be minimized and visible
spurts of dust will not be observed.
(b) The rate of exhaust shall be suf.
ficient to provide prompt clearance of
the dust-laden air within the enclosure
after the cessation of blasting.
(c) Before the enclosure is opened,
the blast shall be turned off and the
exhaust system shall be run for a sufficient period of time to remove the
dusty air within the enclosure.
(d) Safety glass protected by screening shall be used in observation windows, where hard deep-cutting abrasives are used.
(e) Slit abrasive-resistant baffles
shall be installed in multiple sets at all
small access openings where dust
might escape, and shall be inspected
regularly and replaced when needed.
(1) Doors shall be flanged and tight
when closed.
(2) Doors on blast-cleaning rooms
shall be operable from both inside and
outside, except that where there is a
small operator access door, the large
work access door may be closed or
opened from the outside only.
(4) Exhaust ventilation systems. (i)
The construction, installation, inspection. and maintenance of exhaust systems shall conform to the principles
and requirements set forth in American National Standard Fundamentals
Governing the Design and Operation
of Local Exhaust Systems, Z9.2-1960,
and ANSI Z33.1-1961.
(a) When dust leaks are noted, repairs shall be made as soon as possible.
(b) The static pressure drop at the
exhaust ducts leading from the equipment shall be checked when the in-
(2) Dust hazards from abrasive blasting. (i) Abrasives and the surface coatings on the materials blasted are shattered and pulverized during blasting
operations and the dust formed will
contain particles of respirable size.
The composition and toxicity of the
dust from these sources shall be considered in making an evaluation of the
potential health hazards.
(ii) The concentration of respirable
dust or fume in the breathing zone of
the abrasive-blasting operator or any
other worker shall be kept below the
levels specified in § 1910.1000.
(iii) Organic abrasives which are
combustible shall be used only in automatic systems. Where flammable or
explosive dust mixtures may be
present, the construction of the equipment, including the exhaust system
and all electric wiring. shall conform
to the requirements of American National Standard Installation of Blower
and Exhaust Systems for Dust, Stock,
and Vapor Removal or Conveying
Z33.1-1961 (NFPA 91-1961), and the
National Electrical Code, NFPA 70-
1971; ANSI C1-1971 (Rev. of C1-1968).
The blast nozzle shall be bonded and
grounded to prevent the build up of
static charges. Where flammable or
explosive dust mixtures may be
present, the abrasive blasting enclosure, the ducts, and the dust collector
shall be constructed with loose panels
or explosion venting areas, located on
91910.94
stallation is completed and periodically thereafter to assure continued satisfactory operation. Whenever an appreciable change in the pressure drop indicates a partial blockage, the system
shall be cleaned and returned to
normal operating condition.
(ii) In installations where the abrasive is recirculated, the exhaust ventilation system for the blasting enclosure shall not be relied upon for the
removal of fines from the spent abrasive instead of an abrasive separator.
An abrasive separator shall be provided for the purpose.
(iii) The air exhausted from blastcleaning equipment shall be discharged through dust collecting equipment. Dust collectors shall be set up so
that the accumulated dust can be emptied and removed without contaminat-
Ing other working areas.
(5) Personal protective equipment.
(i) Only respiratory protective equipment approved by the Bureau of
Mines, U.S. Department of the Interior (see 30 CFR Part 11) shall be used
for protection of personnel against
dusts produced during abrasive-blasting operations.
(ii) Abrasive-blasting respirators
shall be worn by all abrasive-blasting
operators:
(a) When working inside of blast.
cleaning rooms, or
(b) When using silica sand in manual
blasting operations where the nozzle
and blast are not physically separated
from the operator in an exhaust ventilated enclosure, or
(c) Where concentrations of toxic
dust dispersed by the abrasive blasting
may exceed the limits set in
§ 1910.1000 and the nozzle and blast
are not physically separated from the
operator in an exhaust-ventilated enclosure.
(III) Particulate filter respirators,
commonly referred to as dust-filter
respirators, properly fitted, may be
used for short, intermittent, or occasional dust exposures such as cleanup,
dumping of dust collectors, or unloading shipments of sand at a receiving
point, when It is not feasible to control
the dust by enclosure, exhaust ventilation, or other means. Respirators used
shall be approved (see 30 CFR Part 11)
for protection against the specific type
of dust encountered.
(a) Dust-filter respirators may be
used to protect the operator of outside
abrasive-blasting operations where
nonsilica abrasives are used on materials having low toxicities.
(b) Dust-filter respirators shall not
be used for continuous protection
where silica sand is used as the blasting abrasive, or toxic materials are
blasted.
(iv) A respiratory protection program as defined and described in
§ 1910.134 (a) and (b), shall be estab.
lished wherever it is necessary to use
respiratory protective equipment.
(v) Operators shall be equipped with
heavy canvas or leather gloves and
aprons or equivalent protection to protect them from the impact of abrasives. Safety shoes shall be worn to
protect against foot injury where
heavy pieces of work are handled.
(a) Safety shoes shall conform to
the requirements of American National Standard for Men's Safety-Toe
Footwear, Z41.1-1967.
(b) Equipment for protection of the
eyes and face shall be supplied to the
operator when the respirator design
does not provide such protection and
to any other personnel working in the
vicinity of abrasive blasting operations. This equipment shall conform
to the requirements of § 1910.133.
(6) Air supply and air compressors.
The air for abrasive-blasting respirators shall be free of harmful quantities of dusts, mists, or noxlous gases,
and shall meet the requirements for
air purity set forth in ANSI Z9.2-1960.
The air from the regular compressed
air line of the plant may be used for
the abrasive-blasting respirator if (1) a
trap and carbon filter are installed
and regularly maintained, to remove
oil, water, scale, and odor, (ii) a pressure reducing diaphragm or valve is Installed to reduce the pressure down to
requirements of the particular type of
abrasive-blasting respirator, and (III)
an automatic control is provided to
either sound an alarm or shut down
the compressor in case of overheating.
(7) Operational procedures and general safety. Dust shall not be permitted to accumulate on the floor or on
ledges outside of an abrasive-blasting
enclosure, and dust spills shall be
cleaned up promptly. Aisles and walkways shall be kept clear of steel shot
or similar abrasive which may create a
slipping hazard.
(8) Scope. This paragraph (a) applies
to all operations where an abrasive is
forcibly applied to a surface by pneumatic or hydraulic pressure, or by centrifugal force. It does not apply to
steam blasting, or steam cleaning, or
hydraulic cleaning methods where
work is done without the aid of abrasives.
(b) Grinding, polishing, and buffing
operations-(1) Definitions applicable
to this paragraph-(i) Abrasive cutling-off wheels. Organic-bonded
wheels, the thickness of which is not
more than one forty-eighth of their diameter for those up to, and including,
20 inches in diameter, and not more
than one-sixtieth of their diameter for
those larger than 20 inches in diameter, used for a multitude of operations
variously known as cutting. cutting
off, grooving, slotting. coping, and
jointing, and the like. The wheels may
be "solld" consisting of organic-bonded
abrasive material throughout, "steel
centered" consisting of a steel disc
with a rim of organic-bonded material
moulded around the periphery. or of
the "inserted tooth" type consisting of
a steel disc with organic-bonded abrasive teeth or inserts mechanically secured around the periphery.
(ii) Belts. All power-driven, flexible,
coated bands used for grinding, polishing. or buffing purposes.
(iii) Branch pipe. The part of an ex.
haust system piping that is connected
directly to the hood or enclosure.
(iv) Cradle. A movable fixture, upon
which the part to be ground or polished is placed.
(v) Disc wheels. All power-driven rotatable discs faced with abrasive materials, artificial or natural, and used for
grinding or polishing on the side of
the assembled disc.
for separating solid contaminants
from the air flowing in the system,
and a discharge stack to outside.
(vi) Entry loss. The loss In static
pressure caused by air flowing into a
duct or hood. It is usually expressed In
inches of water gauge.
(vii) Exhaust system. A system consisting of branch pipes connected to
hoods or enclosures, one or more
header pipes, an exhaust fan, means
(viii) Grinding wheels. All powerdriven rotatable grinding or abrasive
wheels, except disc wheels as defined
in this standard, consisting of abrasive
particles held together by artificial or
natural bonds and used for peripheral
grinding.
(ix) Header pipe (main pipe). A pipe
into which one or more branch pipes
enter and which connects such branch
pipes to the remainder of the exhaust
system.
(x) Hoods and enclosures. The par.
tial or complete enclosure around the
wheel or disc through which air enters
an exhaust system during operation.
(xi) Horizontal double-spindle disc
grinder. A grinding machine earrying
two power-driven, rotatable, coaxial,
horizontal spindles upon the inside
ends of which are mounted abrasive
disc wheels used for grinding two sur.
faces simultaneously.
(xii) Horizontal single-spindle disc
grinder. A grinding machine carrying
an abrasive disc wheel upon one or
both ends of a power-driven, rotatable
single horizontal spindle.
(xiii) Polishing and buffing wheels
All power-driven rotatable wheels
composed all or in part of textile fabrics, wood, felt, leather. paper. and
may be coated with abrasives on the
periphery of the wheel for purposes of
polishing, buffing. and light grinding.
(xiv) Portable grinder. Any powerdriven rotatable grinding. polishing, or
buffing wheel mounted in such
manner that it may be manually manipulated.
(xv) Scratch brush wheels. All powerdriven rotatable wheels made from
wire or bristles, and used for scratch
cleaning and brushing purposes.
(xvi) Swing-frame grinder. Any
power-driven rotatable grinding, polishing, or buffing wheel mounted in
such a manner that the wheel with its
supporting framework can be manipulated over stationary objects.
(xvil) Velocity pressure (vp). The kinetic pressure in the direction of flow
necessary to cause a fluid at rest to
flow at a given velocity. It is usually
expressed in inches of water gauge.
§ 1910.94
(xvili) Vertical spindle disc grinder.
A grinding machine having a vertical,
rotatable power-driven spindle carrying a horizontal abrasive disc wheel.
(2) Application. Wherever dry grinding. dry polishing or buffing is performed, and employee exposure, without regard to the use of respirators,
exceeds the permissible exposure
limits prescribed in § 1910.1000 or
other sections of this part, a local exhaust ventilation system shall be provided and used to maintain employee
exposures within the prescribed limits.
(3) Hood and branch pipe requirements. (i) Hoods connected to exhaust
systems shall be used, and such hoods
shall be designed, located, and placed
so that the dust or dirt particles shall
fall or be projected into the hoods in
the direction of the air flow. No
wheels, discs, straps, or belts shall be
operated in such manner and in such
direction as to cause the dust and dirt
particles to be thrown into the operator's breathing zone.
(ii) Grinding wheels on floor stands,
pedestals, benches, and special-purpose grinding machines and abrasive
cutting-off wheels shall have not less
than the minimum exhaust volumes
shown in Table G-4 with a recommended minimum duct velocity of
4,500 feet per minute in the branch
and 3,500 feet per minute in the main.
The entry losses from all hoods except
the vertical-spindle disc grinder hood,
shall equal 0.65 velocity pressure for a
straight takeoff and 0.45 velocity pressure for a tapered takeoff. The entry
loss for the vertical-spindle disc grinder hood Is shown in figure G-1 (follow-
Ing § 1910.94(b)).
TABLE G-4-GRINDING AND ABRASIVE
CUTTING-OFF WHEELS
For any wheel wider than wheel diameters shown in Table G-4, Increase the
exhaust volume by the ratio of the
new width to the width shown.
Minimum
Wheel
exhaust
Wheel diameter (inches)
width
volume
(inches)
fleat "
min.)
To
1%
220
Over 9 to 16
2
390
Over 16 10 19
3
500
Over 19 to 24
4
610
Over 24 to 30
5
880
Over 30 to 36
6
1,200
Example:
If wheel width=4% inches, then
4.5+4x610=686 (rounded to 690).
(iii) Scratch-brush wheels and all
buffing and polishing wheels mounted
on floor stands, pedestals, benches, or
special-purpose machines shall have
not less than the minimum exhaust
volume shown in Table G-5.
TABLE G-5-BUFFING AND POLISHING WHEELS
Minimum
Wheel
exhaust
Wheel diameter (inches)
width
volume
(inches)
(feel V
min.)
To 9
2
300
Over 9 to 16
3
500
Over 16 to 19
4
610
Over 19 to 24
5
740
Over 24 10 30
6
1,040
Over 30 to 36
6
1,200
(iv) Grinding wheels or discs for
horizontal single-spindle disc grinders
shall be hooded to collect the dust or
dirt generated by the grinding operation and the hoods shall be connected to branch pipes having exhaust volumes as shown in Table G-6.
TABLE G-6-HORIZONTAL SINGLE-SPINDLE
Disc GRINDER
Exhaust
Disc diameter (inches)
volume
(n. 1/min.)
Up to 12
220
Over 12 to 19
390
Over 19 to 30
610
Over 30 to 36
680
Chapter XVII-Occupational Safety and Health Administration
(v) Grinding wheels or discs for hortzontal double-spindle disc grinders
shall have a hood enclosing the grinding chamber and the hood shall be
connected to one or more branch pipes
having exhaust volumes as shown in
Table G-7.
TABLE G-7-HORIZONTAL DOUBLE-SPINDLE
DISC GRINDER
Exhaust
Disc diameter (inches)
volume
(11. 1/min.)
up 10 19
610
Over 19 to 25
880
Over 25 to 30
1,200
Over 30 to 53
1,770
Over 53 to 72
6,280
(vi) Grinding wheels or discs for vertical single-spindle disc grinders shall
be encircled with hoods to remove the
dust generated in the operation. The
hoods shall be connected to one or
more branch pipes having exhaust volumes as shown in Table G-8.
TABLE G-8-VERTICAL SPINDLE DISC GRINDER
One-half or more
Disc not covered
of disc covered
Disc diameter
Ex-
Ex-
(inches)
Numhaust
Numhaust
ber
foot "
ber
foot "
min.
min
Up to 20
1
500
2
780
Over 20 to 30
2
780
2
1,480
Over 30 to 53
2
1,770
4
3,530
Over 53 to 72
2
3,140
5
6,010
Number of exhaust outlets around periphery of hood, OF
equal distribution provided by other means
(vii) Grinding and polishing belts
shall be provided with hoods to
remove dust and dirt generated in the
operations and the hoods shall be connected to branch pipes having exhaust
volumes as shown in Table G-9.
TABLE G-9-GRINDING AND POLISHING BELTS
Exhaust
Belts width (inches)
volume
(ft. 1/min.)
Up to 3
220
Over to 5
300
Over to 7
390
Over to 9
500
Over to 11
610
Over 11 to 13
740
(viii) Cradles and swing-frame grinders. Where cradles are used for handling the parts to be ground, polished,
or buffed, requiring large partial enclosures to house the complete operation, a minimum average air velocity
of 150 feet per minute shall be maintained over the entire opening of the
enclosure. Swing-frame grinders shall
also be exhausted in the same manner
as provided for cradles. (See fig. G-3)
(ix) Where the work is outside the
hood, air volumes must be increased as
shown in American Standard Fundamentals Governing the Design and
Operation of Local Exhaust Systems.
Z9.2-1960 (section 4, exhaust hoods).
(4) Exhaust systems. (i) Exhaust systems for grinding, polishing. and buffing operations should be designed in
accordance with American Standard
Fundamentals Governing the Design
and Operation of Local Exhaust Sys.
tems, Z9.2-1960.
(ii) Exhaust systems for grinding.
polishing, and buffing operations shall
be tested in the manner described in
American Standard Fundamentals
Governing the Design and Operation
of Local Exhaust Systems, Z9.2-1960.
(iii) All exhaust systems shall be
provided with suitable dust collectors.
(5) Hood and enclosure design. (i) (a)
It is the dual function of grinding and
abrasive cutting-off wheel hoods to
protect the operator from the hazards
of bursting wheels as well as to provide a means for the removal of dust
and dirt generated. All hoods shall be
not less in structural strength than
specified in the American National
Standard Safety Code for the Use,
Care, and Protection of Abrasive
Wheels. B7.1-1970.
(b) Due to the variety of work and
types of grinding machines employed,
it is necessary to develop hoods adaptable to the particular machine in question, and such hoods shall be located
as close as possible to the operation.
(ii) Exhaust hoods for floor stands.
pedestals, and bench grinders shall be
designed in accordance with figure G-
2. The adjustable tongue shown in the
figure shall be kept in working order
and shall be adjusted within onefourth inch of the wheel periphery at
all times.
(iii) Swing-frame grinders shall be
provided with exhaust booths as Indicated in figure G-3.
(iv) Portable grinding operations,
whenever the nature of the work permits, shall be conducted within a partial enclosure. The opening in the enclosure shall be no larger than is actu-
§ 1910.94
ally required in the operation and an
average face air velocity of not less
than 200 feet per minute shall be
maintained.
(v) Hoods for polishing and buffing
and scratch-brush wheels shall be constructed to conform as closely to
figure G-4 as the nature of the work
will permit.
(vi) Cradle grinding and polishing
operations shall be performed within a
partial enclosure similar to figure G-5.
The operator shall be positioned outside the working face of the opening
of the enclosure. The face opening of
the enclosure should not be any greater in area than that actually required
for the performance of the operation
and the average air velocity into the
working face of the enclosure shall not
be less than 150 feet per minute.
(vii) Hoods for horizontal singlespindle disc grinders shall be constructed to conform as closely as possible to the hood shown in figure G-6. It
is essential that there be a space between the back of the wheel and the
hood, and a space around the periphery of the wheel of at least 1 inch in
order to permit the suction to act
around the wheel periphery. The
opening on the side of the disc shall be
no larger than is required for the
grinding operation, but must never be
less than twice the area of the branch
outlet.
(viii) Horizontal double-spindle disc
grinders shall have a hood encircling
the wheels and grinding chamber similar to that illustrated in figure G-7.
The openings for passing the work
into the grinding chamber should be
kept as small as possible. but must
never be less than twice the area of
the branch outlets.
(ix) Vertical-spindle disc grinders
shall be encircled with a hood so constructed that the heavy dust is drawn
off a surface of the disc and the lighter dust exhausted through a continuous slot at the top of the hood as
shown in figure G-1.
(x) Grinding and polishing belt
hoods shall be constructed as close to
the operation as possible. The hood
should extend almost to the belt, and
1-inch wide openings should be provided on either side. Figure G-8 shows
a typical hood for a belt operation.
30°
OF
DISC
DIRECTION
ROTATION
ANGLE OF SLOT
TO BE IN RELATION
TO ROTATION
D
1/2"
10P Of GRINDER DISC
E
E
Fig. G-1
Vertical Spindle Disc Grinder Exhaust Hood and Branch Pipe Connections
Dia D. inches
Exhaust E
Volume
Exhausted
Note
No
al 4,500
Min.
Max
Dia
11/min 11 1/
Pipes
min
20
1
4%
500
When one-hall or more of the disc can be
hooded, use exhaust ducts as shown at the
left
Over 20
30
2
4
780
Over 30
72
2
6
1,770
Over 53
72
2
8
3,140
20
2
4
780
When no hood can be used over disc, use
exhaust ducts as shown at left
Over 20
20
2
4
780
Over 30
30
2
5%
1,480
Over 53
53
4
6
3,530
Dia D inches
Exhaust E
Volume
Exhausted
Min
Max
No
at 4,500
Note
Pipes
Dia
n/min ny
min
72
5
7
6,010
Entry loss 10 siol velocity pressure 05 branch velocity pressure.
Minimum slot velocity 2,000 ft/min-3/2-inch stot width
THIS SPACE 10
GUARD VERTICAL
BE 't
ADJUSTABLE SLIDE
If
ROBBER HEL TING
**** STRIPPER
COLLAR PIMMED 10
ADJUSTING SCREP
CLEARANCE TO FACE
-
AND BIDES OF WHEEL
DOOR CLAMP
1
"
DIAME
GUARD FOR WHEEL
&
MINIMUM USEABLE
PLANCE AND NOT
THE DIAME TEA
PLANGE
WHE FLANCE
CLEARANCE
MARIMUM
RUCCED TOP NINCE
TO MATCH BOTTOM
NINCE CENTERLINES
WHEEL WIDEH
WORK REST
PLUS V*
MARIMUM
ALTERNATE
HEAL
TRANSITION
10 CLOSE HOOD
=
ARRANGEMENTS
OPENING AS
*CRK REST
MOVES INWARD
E
0008 CLAMP STUD
to SUIT
ILIDING DIRT
DIRT BOX
BOX WITH
NOT -
SAFFLE FRONT
THAN &
LIP
Flg. G-2
Standard Grinder Hood
Wheel dimension, inches
Exhaust
Volume of
Diameter
air at
Width.
outlet,
4,500 h/
Min d
Max D
Max
inches E
min
9
1 1/2
3
220
Over 9
16
2
4
390
Over 16
19
3
4½
500
Over 19
24
4
5
510
Over 24
30
5
6
880
Over 30
36
6
7
1,200
Entry loss 0 45 velocity pressure for sapered takeolf 0.65 velocity pressure for straight takeoff
- " - - - tax or
VEL = 150F TAMIN
DID SUSPENSION
DIRECTION OF
BAFFLE
ROTATION
E
STOCK
SWING FRAME CRINDER
STOCK REST
Flg. 0-3
A Method of Applying an Exhaust Enclosure to Swing-Frame Grinders
NOTE: Baffie to reduce froat opening as much 83 possible
159
Title 29-Lobor
11"FOR HARD WHEELS
FOR SOFT WHEELS
0.25D
ADJUSTABLE TONGUE
as
HINGED DOOR REIN.
in
KEEP AS CLOSE TO
WHEEL AS POSSIBLE
FORCED FOR STIFFNESS
DIRECTION OF
ROTATION
D
D
0.75D
4
LATCH
:- FOR HARD WHEELS
11" FOR SOFT WHEELS
E
D
PO
KNEE CLEARANCE
0.750
TRAP WITH CL EANOUT
WHEN DESIRED
Fig. G-4
Standard Butting and Polishing Hood
Wheel dimension, inches
Volume of
Exhaust
Diameter
air at
outlet
Width.
inches E
4,500 n/
Min= d
Max D
Max
min
9
2
3½
300
Over 9
16
3
4
500
Over 16
19
4
5
610
Over 19
24
5
5½
740
Over 24
30
6
6½
1.040
Over 30
36
6
7
1.200
Entry loss = 0.15 velocity pressure for lapered takeoft, 0.65 velocity pressure for straight takeoff
TO sure TIPE are OF *0**
700
MINIMUM VELOCITY IN E 3,000 , T/MIN
€
BENGES
i 1541 10
x
SWIVEL BAIL
TROLLEY
DRIVE
CRINDING
WHITE
DIRECTION OF
ROTATION
o
o
CRIMDER FRAME
SWIVEL
CRADLE
CLEANOUT DOORS
FLOOR ****
BD
DO
.
MINIMUM VELOCITY AT ENCLOSURE FACE 15 130 FT/MIN
Fig. G-5
Cradle Polishing or Grinding Enclosure
Eatry loss - 0.45 velocity pressure for tapered takeoff
TABLE H-12-MAXIMUM ALLOWABLE SIZE OF CONTAINERS AND PORTABLE TANKS
Flammable liquids
Combustible liquids
Container type
Class IA
Class IB
Class IC
Class II
Class 01
Glass or approved plastic
pl
91
gal
gal
gal.
Metal (other than DOT drums)
, gat
5 gal
gal
gal
gal.
Safety cans
2 gat
5 ga!
5 gal
5 gal
$ gal
Metal drums (DOT spec.
60 gal
60 gal
60 gal
60 gal
60 gal
Approved portable tanks
660 gal
660 gat
660 gal
660 gal
660 gal
Container exemptions (a) Medicines beverages. foodstuffs, cosmetics. and other common consumer items, when packaged
according to commonly accepted practices, shall be exempt from the requirements of $ 1910.106(d)(2) (1) and (ii)
161
Chapler XVII-Occupational Safety and Health Administration
W 2
D
2
+1"
0
+1°
2
W
DIRECTION OF
ROTATION
0
OP ENING TO
HINGE
SUIT WORK
0/4
D/2
THE MINIMUM
AREA OF
OPENING SHALL
E
NOT BE LESS
THAN TWICE THE
AREA OF THE
OUTLET "E"
HINCE
LOCKING HOOKS
Fig. G-6
Horizontal Single-Spindle Disc Grinder Exhaust Hood and Branch Pipe Connections
Dia D. Inches
Volume
Exhaust E
exhausted
Min
Max
die inches
at 4,500 N/
min 1/min
12
3
220
Over 12
19
4
390
Over 19
30
5
610
Over 30
36
6
880
described HT 91.
NOTE: If grinding wheels are used for disc grinding purposes. hoods must conform to structural strength and materials as
Entry loss - 0.45 velocity pressure for tapered takeoff.
a
OF SPINDLE
FACE OF GRINDING DISCS
W
A-A
E
DIRECTION OF ROTATION
WORK
CONVEYOR
A
DIRECTION OF CONVEYOR
0
D+ 2
ANY METHOD OF
FEEDING PARTS TO
BE GROUND MAY
BE USED.
E
Flg: C-7
Horizontal Double-Spindle Disc Grinder Exhaust Hood and Branch Pipe Connections
Disc die inches
Exhaust E
Volume
exhaust at
4,500 n/
Note
Min.
Max.
No Pipes
Dia
min. n y
min
19
1
5
610
Over 19
25
1
6
880
When width "W" permits. exhaust ducts
should be as near heaviest grinding
as possible
Over 25
30
1
7
1,200
Over 30
53
2
6
1,770
Over 53
72
4
8
6,280
Entry loss = 0 45 velocity pressure for a takeoff
163
Studing tangue
1/14"
Flange
Bels tension
Side hinged
FIGURE G-8 -A Typical Hood for a Bell Operation
FIGURE G-8.-A TYPICAL HOOD FOR A BELT OPERATION
Exhaust
Bell width W. Inches
volume
n. 1/min
Up to 3
220
3 10 5
300
5 to 7
390
7 9
500
9 10 11.
610
" to 13
740
Minimum duct velocity = 4,500 h/min branch, 3,500 ft/min
main
Entry loss = 0.45 velocity pressure for tapered takeoff;
065 velocity pressure for straight takeoft.
(6) Scope. This paragraph (b), prescribes the use of exhaust hood enclosures and systems in removing dust,
dirt, fumes, and gases generated
through the grinding, polishing, or
buffing of ferrous and nonferrous
metals.
(c) Spray finishing operations-
(1) Definitions applicable to this paragraph-(1) Spray-finishing operations.
Spray-finishing operations are employment of methods wherein organic
or inorganic materials are utilized in
dispersed form for deposit on surfaces
to be coated, treated, or cleaned. Such
methods of deposit may involve either
automatic, manual, or electrostatic
deposition but do not include metal
spraying or metallizing. dipping, flow
coating. roller coating, tumbling. centrifuging, or spray washing and degreasing as conducted in self-contained washing and degreasing machines or systems.
(ii) Spray booth. Spray booths are
defined and described in § 1910.107(a).
(See sections 103, 104, and 105 of the
Standard for Spray Finishing Using
Flammable and Combustible Materials, NFPA No. 33-1969).
(iii) Spray room. A spray room is a
room in which spray-finishing operations not conducted in a spray booth
are performed separately from other
areas.
(iv) Minimum maintained velocity.
Minimum maintained velocity is the
velocity of air movement which must
be maintained in order to meet minimum specified requirements for
health and safety.
(2) Location and application. Spray
booths or spray rooms are to be used
to enclose or confine all operations.
Spray-finishing operations shall be located as provided in sections 201
through 206 of the Standard for Spray
Finishing Using Flammable and Combustible Materials, NFPA No. 33-1969.
(3) Design and construction of spray
booths. (1) Spray booths shall be designed and constructed in accordance
with § 1910.107(b) (1)-(4) and (6)-(10)
(see sections 301-304 and 306-310 of
the Standard for Spray Finishing
Using Flammable and Combustible
Materials, NFPA No. 33-1969). for general construction specifications. For a
more detailed discussion of fundamentals relating to this subject, see ANSI
Z9.2-1960
Chapter XVII-Occupational Safety and Health Administration
(a) Lights, motors, electrical equipment, and other sources of ignition
shall conform to the requirements of
§ 1910.107 (b)(10) and (c). (See section
310 and chapter 4 of the Standard for
Spray Finishing Using Flammable and
Combustible Materials NFPA No. 33-
1969.)
(b) In no case shall combustible materia) be used in the construction of a
spray booth and supply or exhaust
duct connected to it.
(ii) Unobstructed walkways shall not
be less than 6½ feet high and shall be
maintained clear of obstruction from
any work location in the booth to a
booth exit or open booth front. In
booths where the open front is the
only exit, such exits shall be not less
than 3 feet wide. In booths having
multiple exits, such exits shall not be
less than 2 feet wide, provided that
the maximum distance from the work
location to the exit is 25 feet or less.
Where booth exits are provided with
doors, such doors shall open outward
from the booth.
(iii) Baffles, distribution plates, and
dry-type overspray collectors shall
conform to the requirements of
§ 1910.107(b) (4) and (5). (See sections
304 and 305 of the Standard for Spray
Finishing Using Flammable and Combustible Materials, NFPA No. 33-
1969.)
(a) Overspray filters shall be installed and maintained in accordance
with the requirements of § 1910.107
(b)(5), (see section 305 of the Standard
for Spray Finishing Using Flammable
and Combustible Materials, NFPA No.
33-1969). and shall only be in a location easily accessible for inspection,
cleaning, or replacement.
(b) Where effective means, independent of the overspray filters, are
installed which will result in design air
distribution across the booth cross
section, it is permissible to operate the
booth without the filters in place.
(iv) (a) For wet or water-wash spray
booths, the water-chamber enclosure,
within which intimate contact of contaminated air and cleaning water or
other cleaning medium is maintained,
If made of steel, shall be 18 gage or
heavier and adequately protected
against corrosion.
(b) Chambers may include scrubber
spray nozzles, headers, troughs. or
other devices. Chambers shall be provided with adequate means for creating and maintaining scrubbing action
for removal of particulate matter from
the exhaust air stream.
(v) Collecting tanks shall be of
welded steel construction or other
suitable non-combustible material. If
pits are used as collecting tanks, they
shall be concrete, masonry, or other
material having similar properties.
(a) Tanks shall be provided with
weirs, skimmer plates, or screens to
prevent sludge and floating paint from
entering the pump suction box. Means
for automatically maintaining the
proper water level shall also be provided. Fresh water inlets shall not be
submerged. They shall terminate at
least one pipe diameter above the
safety overflow level of the tank.
(b) Tanks shall be SO constructed as
to discourage accumulation of hazardous deposits.
(vi) Pump manifolds, risers, and
headers shall be adequately sized to
Insure sufficient water flow to provide
efficient operation of the water chamber.
(4) Design and construction of spray
rooms. (i) Spray rooms, including
floors, shall be constructed of masonry, concrete, or other noncombustible
material.
(ii) Spray rooms shall have noncombustible fire doors and shutters.
(iii) Spray rooms shall be adequately
ventilated so that the atmosphere in
the breathing zone of the operator
shall be maintained in accordance
with the requirements of subparagraph (6)(ii) of this paragraph.
(iv) Spray rooms used for production
spray-finishing operations shall conform to the requirements for spray
booths.
(5) Ventilation. (i) Ventilation shall
be provided in accordance with provisions of § 1910.107(d) (see chapter 5 of
the Standard for Spray Finishing
Using Flammable or Combustible Materials, NFPA No. 33-1969), and in accordance with the following:
(a) Where a fan plenum is used to
equalize or control the distribution of
exhaust air movement through the
booth, it shall be of sufficient strength
or rigidity to withstand the differential air pressure or other superficially
imposed loads for which the equipment is designed and also to facilitate
cleaning. Construction specifications
shall be at least equivalent to those of
subdivision (iii) of this subparagraph.
(ii) Inlet or supply ductwork used to
transport makeup air to spray booths
or surrounding areas shall be constructed of noncombustible materials.
(a) If negative pressure exists within
inlet ductwork. all seams and joints
shall be sealed if there is a possibility
of infiltration of harmful quantities of
noxious gases. fumes, or mists from
areas through which ductwork passes.
(b) Inlet ductwork shall be sized in
accordance with volume flow requirements and provide design air requirements at the spray booth.
(c) Inlet ductwork shall be adequately supported throughout its length to
sustain at least its own weight plus
any negative pressure which is exerted
upon it under normal operating conditions.
(iii) (Reserved)
(a) Exhaust ductwork shall be adequately supported throughout its
length to sustain its weight plus any
normal accumulation in interjor
during normal operating conditions
and any negative pressure exerted
upon it.
(b) Exhaust ductwork shall be sized
in accordance with good design practice which shall include consideration
of fan capacity, length of duct,
number of turns and elbows, variation
in size, volume, and character of materials being exhausted. See American
National Standard Z9.2-1960 for further details and explanation concerning elements of design.
(c) Longitudinal joints in sheet steel
ductwork shall be either lock-seamed,
riveted, or welded. For other than
steel construction, equivalent securing
of joints shall be provided.
(d) Circumferential joints In
ductwork shall be substantially fastened together and lapped in the direction of airflow. At least every
fourth joint shall be provided with
connecting flanges, bolted together, or
of equivalent fastening security.
(e) Inspection or clean-out doors
shall be provided for every 9 to 12 feet
of running length for ducts up to 12
inches in diameter, but the distance
between cleanout doors may be greater for larger pipes. (See 8.3.21 of
American National Standard Z9.1-
1951.) A clean-out door or doors shall
be provided for servicing the fan. and
where necessary. a drain shall be provided.
(f) Where ductwork passes through a
combustible roof or wall, the roof or
wall shall be protected at the point of
penetration by open space or fire-resistive material between the duct and the
roof or wall. When ducts pass through
firewalls, they shall be provided with
automatic fire dampers on both sides
of the wall, except that three-eighthinch steel plates may be used in lieu of
automatic fire dampers for ducts not
exceeding 18 inches in diameter.
(g) Ductwork used for ventilating
any process covered in this standard
shall not be connected to ducts ventilating any other process or any chimney or flue used for conveying any
products of combustion.
(6) Velocity and air flow requirements. (i) Except where a spray booth
has an adequate air replacement
system, the velocity of air into all
openings of a spray booth shall be not
less than that specified in Table G-10
for the operating conditions specified.
An adequate air replacement system is
one which introduces replacement air
upstream or above the object being
sprayed and is so designed that the velocity of air in the booth cross section
is not less than that specified in Table
G-10 when measured upstream or
above the object being sprayed.
TABLE G-10-MINIMUM MAINTAINED VELOCITIES INTO SPRAY BOOTHS
Arflow velocities. t.p.m.
Operating conditions for objects completely inside booth
Crossdrah, I.p.m.
Design
Range
Electrostatic and automatic airless operation contained in
Negligible
50 large booth
50-75
booth without operator.
Chapter XVII-Occupational Safety and Health Administration
TABLE G-10-MINIMUM MAINTAINED VELOCITIES INTO SPRAY BOOTHS-Continued
Authow velocities, 1pm
Operating conditions for objects completely inside booth
Crossdraft, Lp
Design
Range
100 small booth
75-125
Air-operated guns, manual or automatic
Up to 50
100 large booth
75-125
150 small booth
125-175
Air-operated guns, manual or automatic
Up to 100
150 large booth
125-175
200 small booth
150-250
NOTES
(1) Attention IS invited to the fact that the effectiveness of the spray booth 15 dependent upon the relationship of the depth
of the booth to its height and width
(2) Crossdrafts can be eliminated through proper design and such design should be sought. Crossdrafts in excess of
1001pm (leet per minute) should not be permitted
(3) Excessive Bir pressures result in loss of both efficiency and material waste in addition to creating a backiash that may
carry overspray and lumes into adjacent work areas
(4) Booths should be designed with velocities shown in the column headed "Design." However, booths operating with
velocities shown in the column headed "Range" are in compliance with this standard
(ii) In addition to the requirements
in subdivision (i) of this subparagraph
the total air volume exhausted
through a spray booth shall be such as
to dilute solvent vapor to at least 25
percent of the lower explosive limit of
the solvent being sprayed. An example
of the method of calculating this
volume is given below.
Example: To determine the lower explosive limits of the most common solvents
used in spray finishing. see Table G-11.
Column 1 gives the number of cubic feel of
vapor per gallon of solvent and column 2
gives the lower explosive limit (LEL) in percentage by volume of air. Note that the
quantity of solvent will be diminished by
the quantity of solids and nonflammables
contained in the finish.
To determine the volume of air in cubic
feet necessary to dilute the vapor from 1
gallon of solvent to 25 percent of the lower
explosive limit, apply the following formula:
Dilution volume required per gallon of solvent=4 (100-LEL) (cubic feet of vapor
per gallon)- LEL
Using toluene as the solvent.
(1) LEL of toluene from Table G-11,
column 2, is 1.4 percent.
(2) Cubic feet of vapor per gallon from
Table G-11, column 1. Is 30.4 cuble feet per
gallon.
(3) Dilution volume required=
4 (100-1.4) 30.4 ÷ 1.4=8,564 cubic feet.
(4) To convert to cubic feet per minute of
required ventilation. multiply the dilution
volume required per gallon of solvent by the
number of gallons of solvent evaporated per
minute.
TABLE G-11-LOWER EXPLOSIVE LIMIT OF
SOME COMMONLY USED SOLVENTS
Lower
Cubic feet
explosive
per gallon
know in
Solvent
of vapor of
percent by
liquid at
volume of
70' F.
air at 70'
F
Column 1
Column 2
Acetons
44.0
26
Amyl Acetate (iso)
21.6
'1.0
Amyl Alcohol (n)
296
1.2
Amyl Alcohol (iso)
296
1.2
Benzene
36 6
11.4
Butyl Acelate (n)
248
17
Bulyl Alcohol (n)
35.2
1.4
Butyl Cellosolve
24.8
1.1
Cellosoive
336
1.8
Cellosolve Acetate
23.2
1.7
Cyclohexanone
312
1.1
1,1 Dichloroethylene
42.4
59
1,2 Dichloroethylene
42.4
97
Ethyl Acetate
32 8
2.5
Ethyl Alcohol
55.2
43
Ethy: Lactate
280
11.5
Melhyl Acetate
400
3.1
Methyl Alcohol
80.8
7.3
Methyl Cellosolve
40.8
2.5
Methyl Ethyl Ketone
360
1.0
Methy) n-Propyl Kelone
30 4
1.5
Naphina (VM&P) (76* Naphtha).
22.4
0.9
Naphtha (100' Fiash) Salety Solvent-Stoddard Solvent
23.2
1.0
Propyl Acetate (n)
27.2
28
Propyl Acelate (iso)
26.0
1.1
Propyl Alcohol (n)
448
2.1
Propyl Alcohol (iso)
440
2.0
Toluene
30 4
1.4
Turpentine
20.8
0.8
Xylene (o)
26.4
1.0
'A1 212' F.
(iii) (a) When an operator must position himself in a booth downstream of
the object being sprayed, an air supplied respirator or other type of respi-
13-091 0-13-13
rator approved by the Bureau of
Mines, U.S. Department of the Interior or specified in ANSI Z88.2-1969 for
the material being sprayed should be
used by the operator.
(b) Where downdraft booths are provided with doors, such doors shall be
closed when spray painting.
(7) Make-up air. (i) Clean fresh air,
free of contamination from adjacent
industrial exhaust systems, chimneys,
stacks, or vents. shall be supplied to a
spray booth or room in quantities
equal to the volume of air exhausted
through the spray booth.
(ii) Where a spray booth or room receives make-up air through self-closing
doors, dampers, or louvers, they shall
be fully open at all times when the
booth or room is in use for spraying.
The velocity of air through such
doors, dampers, or louvers shall not
exceed 200 feet per minute. If the fan
characteristics are such that the required air flow through the booth will
be provided, higher velocities through
the doors, dampers, or louvers may be
used.
(iii) (a) Where the air supply to a
spray booth or room is filtered, the
fan static pressure shall be calculated
on the assumption that the filters are
dirty to the extent that they require
cleaning or replacement.
(b) The rating of filters shall be governed by test data supplied by the
manufacturer of the filter. A pressure
gage shall be installed to show the
pressure drop across the filters. This
gage shall be marked to show the pressure drop at which the filters require
cleaning or replacement. Filters shall
be replaced or cleaned whenever the
pressure drop across them becomes excessive or whenever the air flow
through the face of the booth falls
below that specified in Table G-10.
(iv) (a) Means for heating make-up
air to any spray booth or room, before
or at the time spraying is normally
performed, shall be provided in all
places where the outdoor temperature
may be expected to remain below 55*
F. for appreciable periods of time
during the operation of the booth
except where adequate and safe means
of radiant heating for all operating
personnel affected is provided. The replacement air during the heating seasons shall be maintained at not less
than 65' F. at the point of entry into
the spray booth or spray room. When
otherwise unheated make-up air would
be at a temperature of more than 10'
F. below room temperature. its tem.
perature shall be regulated as provided in section 3.6.3 of ANSI Z9.2-
1960.
(b) As an alternative to an air replacement system complying with the
preceding section, general heating of
the building in which the spray room
or booth is located may be employed
provided that all occupied parts of the
building are maintained at not less
than 65* F. when the exhaust system
is in operation or the general heating
system supplemented by other sources
of heat may be employed to meet this
requirement.
(c) No means of heating make-up air
shall be located in a spray booth.
(d) Where make-up air is heated by
coal or oil, the products of combustion
shall not be allowed to mix with the
make-up air, and the products of combustion shall be conducted outside the
building through a flue terminating at
a point remote from all points where
make-up air enters the building.
(e) Where make-up air is heated by
gas, and the products of combustion
are not mixed with the make-up air
but are conducted through an independent flue to a point outside the
building remote from all points where
make-up air enters the building, it is
not necessary to comply with paragraph S of this subdivision.
S Where make-up air to any manually operated spray booth or room is
heated by gas and the products of
combustion are allowed to mix with
the supply air, the following precautions must be taken:
(1) The gas must have a distinctive
and strong enough odor to warn workmen in a spray booth or room of its
presence if in an unburned state in the
make-up air.
(2) The maximum rate of gas supply
to the make-up air heater burners
must not exceed that which would
yield in excess of 200 p.p.m. (parts per
million) of carbon monoxide or 2,000
p.p.m. of total combustible gases in
the mixture if the unburned gas upon
the occurrence of flame failure were
mixed with all of the make-up air supplied.
(3) A fan must be provided to deliver
the mixture of heated air and products of combustion from the plenum
chamber housing the gas burners to
the spray booth or room.
(8) Scope. Spray booths or spray
rooms are to be used to enclose or confine all spray finishing operations covered by this paragraph (c). This paragraph does not apply to the spraying
of the exteriors of buildings, fixed
tanks, or similar structures, nor to
small portable spraying apparatus not
used repeatedly in the same location.
(d) Open surface tanks-(1) General.
(i) This paragraph applies to all operations involving the immersion of materials in liquids, or in the vapors of
such liquids, for the purpose of cleaning or altering the surface or adding to
or imparting a finish thereto or changing the character of the materials, and
their subsequent removal from the
liquid or vapor, draining, and drying.
These operations include washing,
electroplating, anodizing, pickling.
quenching, dying. dipping, tanning,
dressing, bleaching, degreasing, alkaline cleaning, stripping. rinsing, digesting. and other similar operations.
(ii) Except where specific construction specifications are prescribed in
this section, hoods, ducts, elbows, fans.
blowers, and all other exhaust system
parts, components, and supports
thereof shall be so constructed as to
meet conditions of service and to facilitate maintenance and shall conform in construction to the specifications contained in American National
Standard Fundamentals Governing
the Design and Operation of Local Exhaust Systems, Z9.2-1960.
(2) Classification of open-surface
tank operations. (i) Open-surface tank
operations shall be classified into 16
classes, numbered A-1 to D-4, inclusive.
(ii) Determination of class. Class Is
determined by two factors, hazard potential designated by a letter from A
to D. inclusive, and rate of gas. vapor,
or mist evolution designated by a
number from 1 to 4, inclusive (for example, B.3).
(iii) Hazard potential is an index, on
a scale of from A to D, inclusive, of the
severity of the hazard associated with
the substance contained in the tank
because of the toxic, flammable, or explosive nature of the vapor, gas, or
mist produced therefrom. The toxic
hazard is determined from the concentration, measured in parts by volume
of a gas or vapor, per million parts by
volume of contaminated air (p.p.m.),
or in milligrams of mist per cubic
meter of air (mg./m.3), below which ill
effects are unlikely to occur to the exposed worker. The concentrations
shall be those in $ 1910.1000.
(iv) The relative fire or explosion
hazard Is measured in degrees Fahrenhelt in terms of the closed-cup flash
point of the substance in the tank. Detailed information on the prevention
of fire hazards in dip tanks may be
found in Dip Tanks Containing Flammable or Combustible Liquids, NFPA
No. 34-1966, National Fire Protection
Association. Where the tank contains
a mixture of liquids, other than organic solvents, whose effects are additive,
the hygienic standard of the most
toxic component (for example, the one
having the lowest p.p.m. or mg./m.³)
shall be used, except where such substance constitutes an insignificantly
small fraction of the mixture. For mixtures of organic solvents, their combined effect. rather than that of
either individually, shall determine
the hazard potential. In the absence of
information to the contrary. the effects shall be considered as additive. If
the sum of the ratios of the airborne
concentration of each contaminant to
the toxic concentration of that contaminant exceeds unity, the toxic concentration shall be considered to have
been exceeded. (See Note A to subdivision (v) of this subparagraph.)
(v) Hazard potential shall be determined from Table G-12, with the
value indicating greater hazard being
used. When the hazardous material
may be either a vapor with a threshhold limit value (TLV) in p.p.m. or a
mist with a TLV in mg./m.,, the TLV
indicating the greater hazard shall be
used (for example, A takes precedence
over B or C; B over C: C over D).
NOTE A:
168
Title 29-Labor
TLV 1
where:
-Concentration measured at the operation in p.p.m.
TABLE G-12-DETERMINATION OF HAZARD
POTENTIAL
Toxicity group
Hazard potential
Gas or
Flash
Mist
vapor
point (in
(p.p.m.)
(mg
degrees
F)
A
0-10
0-0.1
B
11-100
0.11-1.0
Under 100
C
101-500
1.1-10
100-200
D
Over 500
Over 10
Over 200
(vi) Rate of gas, vapor, or mist evolution is a numerical index, on a scale of
from 1 to 4, inclusive, both of the relative capacity of the tank to produce
gas, vapor, or mist and of the relative
energy with which it is projected or
carried upwards from the tank. Rate is
evaluated in terms of
(a) The temperature of the liquid in
the tank in degrees Fahrenheit;
(b) The number of degrees Fahrenhelt that this temperature is below the
boiling point of the liquid in degrees
Fahrenheit;
(c) The relative evaporation of the
liquid in still air at room temperature
In an arbitrary scale-fast, medium,
slow, or nil; and
(d) The extent that the tank gases
or produces mist in an arbitrary
scale-high, medium, low, and nil. (See
Table G-13, Note 2.) Gassing depends
upon electrochemical or mechanical
processes, the effects of which have to
be individually evaluated for each Installation usee Table G-13, Note 3).
(vii) Rate of evolution shall be determined from Table G-13. When evaporation and gassing yield different
rates, the lowest numerical value shall
be used.
TABLE G-13-DETERMINATION OF RATE OF
GAS, VAPOR, OR MIST EVOLUTION
Liquid
Degrees
Rate
tempera
below
Relative
boiling
evapora
Gassing
two," F.
point
tion
1
Over 200
0-20
Fast
High
2
150-200
21-50
Medium
Medium.
3
94-149
51-100
Slow
Low.
4
Under 94
Over 100
Nil
Nil.
in certain classes of equipment specifically vapor degreasers, an internal condenser or vapor level thermostal is
used to prevent the vapor from leaving the tank dunng
normal operation In such cases, rate of vapor evolution from
the tank into the workroom is not dependent upon the
factors listed in the table, but rather upon abnormations of
operating procedure, such as carryout of vapors from excessively last action, dragout of liquid by entrainment in parts,
contamination of solvent by water and other materials, or
improper heat balance When operating procedure is excel.
leni, effective rate of evolution may be taken as 4. When
operating procedure IS average, the effective rate of evolu.
lon may be taken as 3 When operation is poor, B rate of 2
or 1 IS indicated. depending upon observed conditions.
Relative evaporation rate IS determined according to the
methods described by A. K. Doolitile in Industrial and Engineering Chemistry, vol 27, P 1169. (3) where time for 100-
percent evaporation is as follows. Fast. 0-3 hours; Medium:
3-12 hours, Slow 12-50 hours; Nd: more than 50 hours.
Gassing means the formation by chemical or electrochemical action of minute bubbles of gas under the surface
solutions. of the figuid in the tank and is generally limited to aqueous
(3) Ventilation. Where ventilation is
used to control potential exposures to
workers as defined in subparagraph
(2)(iii) of this paragraph, it shall be
adequate to reduce the concentration
of the air contaminant to the degree
that a hazard to the worker does not
exist. Methods of ventilation are discussed in American National Standard
Fundamentals Governing the Design
and Operation of Local Exhaust Systems, Z9.2-1960.
(4) Control requirements. (j) Control
velocities shall conform to Table G-14
in all cases where the flow of air past
the breathing or working zone of the
operator and into the hoods is undisturbed by local environmental conditions, such as open windows, wall fans,
unit heaters, or moving machinery.
(11) All tanks exhausted by means of
hoods which
(a) Project over the entire tank;
(b) Are fixed in position in such a location that the head of the workman,
In all his normal operating positions
while working at the tank, is in front
of all hood openings; and
(c) Are completely enclosed on at
least two sides, shall be considered to
Chapter XVII-Occupational Safety and Health Administration
§ 1910.94
be exhausted through an enclosing
hood.
(d) The quantity of air in cuble feet
per minute necessary to be exhausted
through an enclosing hood shall be
not less than the product of the control velocity times the net area of all
openings in the enclosure through
which air can flow into the hood.
TABLE G-14-CONTROL VELOCITIES IN FEET PER MINUTE (F.P.M.) FOR UNDISTURBED LOCATIONS
Enclosing hood
Canopy hood
Lateral
Class
One open
Two open
exhaust
Three
Four open
side
sides
open sides
sides
0-1 and A-2
100
150
150
Do not use
Do not use
A-3' B-1. B-2, and C-1
75
100
100
125
175
A-3. C-2, and D-1
65
90
75
100
150
B-42 C-3, and D-2'
50
75
50
75
125
A-4, C-4, D-3ª, and D-4'
See Table G-15 for computation of ventilation rate
Do not use canopy hood for Hazard Potential A processes
Where complete control of not water IS desired, design as next highest class.
General room ventilation required.
(iii) All tanks exhausted by means of
hoods which do not project over the
entire tank, and in which the direction
of air movement into the hood or
hoods Is substantially horizontal, shall
be considered to be laterally exhausted. The quantity of air in cubic feet
per minute necessary to be laterally
exhausted per square foot of tank area
in order to maintain the required control velocity shall be determined from
Table G-15 for all variations in ratio
of tank width (W) to tank length (L).
The total quantity of air in cubic feet
per minute required to be exhausted
per tank shall be not less than the
product of the area of tank surface
times the cubic feet per minute per
square foot of tank area, determined
from Table G-15.
(a) For lateral exhaust hoods over 42
inches wide, or where it is desirable to
reduce the amount of air removed
from the workroom, air supply slots or
orifices shall be provided along the
side or the center of the tank opposite
from the exhaust slots. The design of
such systems shall meet the following
criteria:
(1) The supply air volume plus the
entrained air shall not exceed 50 percent of the exhaust volume.
(2) The velocity of the supply airstream as it reaches the effective control area of the exhaust slot shall be
less than the effective velocity over
the exhaust slot area.
TABLE G-15-MINIMUM VENTILATION RATE IN Cusic FEET OF AIR PER MINUTE PER SQUARE FOOT
OF TANK AREA FOR LATERAL EXHAUST
C.I.m. per sq. ft. to maintain required minimum velocities al
Required minimum control velocity, I.p.m. (Nom Table G-
following ratios (tank width (W)/tank length (i)) '.
14)
0.0-0.09
0.1-0.24
0.25-0.49
0.5-0.99
1.0-2.0
Hood slong one side or two parallel sides of tank when one hood is against a wall or baltie."
Also for a manitold along tank centerine
50
50
60
75
90
100
75
75
90
110
130
150
100
100
125
150
175
200
150
150
190
225
260
300
Hood along one side or two parallel sides of Iree standing tank not against was or battle
50
75
90
100
110
125
75
110
130
150
170
190
170
1910.94
Title 29-Labor
TABLE G-15-MINIMUM VENTILATION RATE IN CUBIC FEET OF AIR PER MINUTE PER SQUARE Foor
OF TANK AREA FOR LATERAL EXHAUST-Continued
§ 1910.94
C.f.m. per sq n to maintain required minimum velocities at
Required minimum control velocity. Ip m. (from Table G-
following ratios (tank width (W)/lank length (L)).',
14)
0.0-0 09
0.1-0 24
0.25-0.49
0 5-0.99
1.0-2.0
100
150
175
200
225
150
250
225
260
300
340
375
" 16 not practicable to ventilate across the long dimension of a tank whose (atio W/L exceeds 20.
use WIL 1.0; for over one-half the circumference use W/L 05.
0 IS undesirable 10 do so when WIL exceeds 1.0 For circular tanks with lateral exhaust along up to 1/2 the circumference,
Battle IS a vertical plate the same length as the lank. and with the lop of the plate as high as the tank IS wide If he
exhaust hood IS on the side of a tank against a building wall or close 10 it, rt 15 perfectly baffled
lank Use W/2 as tank width in computing when manifold is along centerline, or when hoods are used on two parallel sides of a
Tank Width (W) means the effective width over which the hood must pull all to operate (for example, where the hood face
15 set back from the edge of the lank, this sel back must be added in measuring tank width) The surface area of tanks can
upper edges of the stois toward the center of the lank.
frequently be reduced and better control obtained (particularly on conveyorized systems) by using covers extending from the
(3) The vertical height of the receiving exhaust hood, including any
baffle. shall not be less than one-quarter the width of the tank.
(4) The supply airstream shall not
be allowed to impinge on obstructions
between It and the exhaust slot in
such a manner as to significantly interfere with the performance of the
exhaust hood.
(5) Since most failure of push-pull
systems result from excessive supply
air volumes and pressures, methods of
measuring and adjusting the supply
air shall be provided. When satisfactory control has been achieved, the adjustable features of the hood shall be
fixed SO that they will not be altered.
cal means are used to disperse a liquid
above an open-surface tank, control
must be provided for the airborne
spray. Such operations shall be enclosed as completely as possible. The
inward air velocity into the enclosure
shall be sufficient to prevent the discharge of spray into the workroom.
Mechanical baffles may be used to
help prevent the discharge of spray.
Spray painting operations are covered
by paragraph (c) of this section.
(iv) All tanks exhausted by means of
hoods which project over the entire
tank, and which do not conform to the
definition of enclosing hoods, shall be
considered to be overhead canopy
hoods. The quantity of air in cubic
feet per minute necessary to be ex.
hausted through a canopy hood shall
be not less than the product of the
control velocity times the net area of
all openings between the bottom edges
of the hood and the top edges of the
tank.
(v) The rate of vapor evolution (including steam or products of combustion) from the process shall be estimated. If the rate of vapor evolution is
equal to or greater than 10 percent of
the calculated exhaust volume required, the exhaust volume shall be increased in equal amount.
(6) Control means other than venti.
lation. Tank covers, foams, beads,
chips, or other materials floating on
the tank surface so as to confine gases,
mists, or vapors to the area under the
cover or to the foam, bead, or chip
layer; or surface tension depressive
agents added to the liquid in the tank
to minimize mist formation, or any
combination thereof, may all be used
as gas, mist, or vapor control means
for open-surface tank operations, provided that they effectively reduce the
concentrations of hazardous materials
in the vicinity of the worker below the
limits set in accordance with subparagraph (2) of this paragraph.
(5) Spray cleaning and degreasing
Wherever spraying or other mechani-
(7) System design. (i) The equipment
for exhausting air shall have sufficient capacity to produce the flow of
air required in each of the hoods and
openings of the system.
(ii) The capacity required in subdivision (i) of this subparagraph shall be
obtained when the airflow producing
equipment is operating against the following pressure losses, the sum of
which is the static pressure:
Chapter XVII-Occupational Safety and Health Administration
(a) Entrance losses into the hood.
(b) Resistance to airflow in branch
pipe including bends and transformations.
(c) Entrance loss into the main pipe.
(d) Resistance to airflow in main
pipe including bends and transformations.
(e) Resistance of mechanical equipment; that is, filters, washers, condensers, absorbers, etc., plus their entrance and exit losses.
(f) Resistance in outlet duct and discharge stack.
(iii) Two or more operations shall
not be connected to the same exhaust
system where either one or the combination of the substances removed may
constitute a fire, explosion, or chemical reaction hazard in the duct system.
Traps or other devices shall be provided to insure that condensate in
ducts does not drain back into any
tank.
(iv) The exhaust system, consisting
of hoods, ducts, air mover, and discharge outlet. shall be designed in accordance with American National
Standard Fundamentals Governing
the Design and Operation of Local Exhaust Systems, Z9.2-1960, or the
manual, Industrial Ventilation, published by the American Conference of
Governmental Industrial Hygienists
1970. Airflow and pressure loss data
provided by the manufacturer of any
air cleaning device shall be included in
the design calculations.
(8) Operation. (i) The required air.
flow shall be maintained at all times
during which gas, mist, or vapor is
emitted from the tank, and at all
times the tank, the draining, or the
drying area is in operation or use.
When the system Is first installed, the
airflow from each hood shall be measured by means of a pitot traverse in
the exhaust duct and corrective action
taken if the flow is less than that required. When the proper flow is obtained, the hood static pressure shall
be measured and recorded. At intervals of not more than 3 months operation, or after a prolonged shutdown
period, the hoods and duct system
shall be inspected for evidence of cor.
rosion or damage. In any case where
the airflow is found to be less than required, it shall be increased to the required value. (Information on airflow
and static pressure measurement and
calculations may be found in American National Standard Fundamental
Governing the Design and Operation
of Local Exhaust Systems, Z9.2-1960,
or in the manual, Industrial Ventilation, published by the American Conference of Governmental Industrial
Hygienists.)
(ii) The exhaust system shall discharge to the outer air in such a
manner that the possibility of its ef.
fluent entering any building is at a
minimum. Recirculation shall only be
through a device for contaminant removal which will prevent the creation
of a health hazard in the room or area
to which the air is recirculated.
(iii) A volume of outside air in the
range of 90 percent to 110 percent of
the exhaust volume shall be provided
to each room having exhaust hoods.
The outside air supply shall enter the
workroom in such a manner as not to
be detrimental to any exhaust hood.
The airflow of the makeup air system
shall be measured on installation. Periodically, thereafter, the airflow
should be remeasured, and corrective
action shall be taken when the airflow
is below that required. The makeup
air shall be uncontaminated.
(9) Personal protection. (i) All employees working in and around opensurface tank operations must be instructed as to the hazards of their respective jobs, and in the personal protection and first aid procedures applicable to these hazards.
(il) All persons required to work in
such a manner that their feet may
become wet shall be provided with
rubber or other impervious boots or
shoes, rubbers, or wooden-soled shoes
sufficient to keep feet dry.
(lii) All persons required to handle
work wet with a liquid other than
water shall be provided with gloves Impervious to such a liquid and of a
length sufficient to prevent entrance
of liquid into the tops of the gloves.
The interior of gloves shall be kept
free from corrosive or irritating contaminants.
(iv) All persons required to work in
such a manner that their clothing may
become wet shall be provided with
such aprons, coats, jackets, sleeves, or
$ 1910.94
Title 29-Labor
other garments made of rubber, or of
other materials impervious to liquids
other than water. as are required to
keep their clothing dry. Aprons shall
extend well below the top of boots to
prevent liquid splashing into the
boots. Provision of dry, clean, cotton
clothing along with rubber shoes or
short boots and an apron impervious
10 liquids other than water shall be
considered a satisfactory substitute
where small parts are cleaned, plated,
or acid dipped in open tanks and rapid
work is required.
(v) Whenever there is a danger of
splashing. for example, when additions
are made manually to the tanks, or
when acids and chemicals are removed
from the tanks, the employees SO engaged shall be required to wear either
tight-fitting chemical goggles or an effective face shield. See § 1910.133.
(vi) When, during emergencies as described in paragraph (d)(11)(v) of this
section, workers must be in areas
where concentrations of air contaminants are greater than the limit set by
paragraph (d)(2)(iii) of this section, or
oxygen concentrations are less than
19.5 percent, they shall be required to
wear respirators adequate to reduce
their exposure to a level below these
limits, or to provide adequate oxygen.
Such respirators shall also be provided
in marked, quickly accessible storage
compartments built for the purpose,
when there exists the possibility of accidental release of hazardous concentrations of air contaminants. Respirators shall be approved by the U.S.
Bureau of Mines, U.S. Department of
the Interior and shall be selected by a
competent Industrial hygienist or
other technically qualified source.
Respirators shall be used in accordance with $ 1910.134, and persons who
may require them shall be trained in
their use.
(vii) Near each tank containing a
liquid which may burn, irritate, or
otherwise be harmful to the skin if
splashed upon the worker's body,
there shall be a supply of clean cold
water. The water pipe (carrying a pressure not exceeding 25 pounds) shall be
provided with a quick opening valve
and at least 48 inches of hose not
smaller than three-fourths inch. so
that no time may be lost in washing
off liquids from the skin or clothing.
Alternatively, deluge showers and eye
flushes shall be provided in cases
where harmful chemicals may be
splashed on parts of the body.
(viii) Operators with sores, burns, or
other skin lesions requiring medical
treatment shall not be allowed to work
at their regular operations until so authorized by a physician. Any small
skin abrasions, cuts, rash, or open
sores which are found or reported
shall be treated by a properly designated person so that chances of exposures to the chemicals are removed.
Workers exposed to chromic acids
shall have a periodic examination
made of the nostrils and other parts of
the body, to detect incipient ulceration.
(ix) Sufficient washing facilities, in.
cluding soap, individual towels, and
hot water. shall be provided for all
persons required to use or handle any
liquids which may burn, irritate, or
otherwise be harmful to the skin, on
the basis of at least one basin (or its
equivalent) with a hot water faucet for
every 10 employees. See § 1910.141(d).
(x) Locker space or equivalent cloth.
ing storage facilities shall be provided
to prevent contamination of street
clothing.
(xi) First aid facilities specific to the
hazards of the operations conducted
shall be readily available.
(10) Special precautions for cyanide.
Dikes or other arrangements shall be
provided to prevent the possibility of
intermixing of cyanide and acid in the
event of tank rupture.
(11) Inspection, maintenance, and
installation.
(i) Floors and platforms around
tanks shall be prevented from becoming slippery both by original type of
construction and by frequent flushing.
They shall be firm. sound, and of the
design and construction to minimize
the possibility of tripping.
Chapter XVII-Occupational Safety and Health Administration
(ii) Before cleaning the interior of
any tank, the contents shall be
drained off, and the cleanout doors
shall be opened where provided. All
pockets In tanks or pits, where it is
possible for hazardous vapors to collect, shall be ventilated and cleared of
such vapors.
(iii) Tanks which have been drained
to permit employees to enter for the
purposes of cleaning. inspection, or
maintenance may contain atmospheres which are hazardous to life or
health, through the presence of flammable or toxic air contaminants, or
through the absence of sufficient
oxygen. Before employees shall be permitted to enter any such tank. appropriate tests of the atmosphere shall be
made to determine if the limits set by
paragraph (d)(2)(iii) of this section are
exceeded, or if the oxygen concentration is less than 19.5 percent.
(iv) If the tests made in accordance
with paragraph(d)(11)(ii) of this
section indicate that the atmosphere
in the tank is unsafe, before any employee is permitted to enter the tank,
the tank shall be ventilated until the
hazardous atmosphere is removed, and
ventilation shall be continued so as to
prevent the occurrence of a hazardous
atmosphere as long as an employee is
in the tank.
(v) If, in emergencies, such as rescue
work, It is necessary to enter a tank
which may contain a hazardous atmosphere, suitable respirators. such as
self-contained breathing apparatus;
hose mask with blower. if there is a
possibility of oxygen deficiency: or a
gas mask, selected and operated in accordance with paragraph (d)(9)(vi) of
this section, shall be used. If a contaminant in the tank can cause dermatitis, or be absorbed through the skin.
the employee entering the tank shall
also wear protective clothing. At least
one trained standby employee, with
suitable respirator, shall be present in
the nearest uncontaminated area. The
standby employee must be able to
communicate with the employee in
the tank and be able to haul him out
of the tank with a lifeline If necessary.
(vi) Maintenance work requiring
welding or open flame, where toxic
metal fumes such as cadmium, chromium, or lead may be evolved, shall be
done only with sufficient local exhaust
ventilation to prevent the creation of a
health hazard, or be done with respirators selected and used in accordance
with paragraph (d)(9)(vi) of this
section. Welding, or the use of open
flames near any solvent cleaning
equipment shall be permitted only
after such equipment has first been
thoroughly cleared of solvents and
vapors.
(12) Vapor degreasing tanks. (1) In
any vapor degreasing tank equipped
with a condenser or vapor level thermostat, the condenser or thermostat
shall keep the level of vapors below
the top edge of the tank by a distance
at least equal to one-half the tank
width, or at least 36 inches, whichever
is shorter.
(ii) Where gas is used as a fuel for
heating vapor degreasing tanks, the
combustion chamber shall be of tight
construction, except for such openings
as the exhaust flue, and those that are
necessary for supplying air for combustion. Flues shall be of corrosion-resistant construction and shall extend
to the outer air. If mechanical exhaust
is used on this flue, a draft diverter
shall be used. Special precautions
must be taken to prevent solvent
fumes from entering the combustion
air of this or any other heater when
chlorinated or fluorinated hydrocarbon solvents (for example, trichloroethylene, Freon) are used.
(iii) Heating elements shall be so designed and maintained that their surface temperature will not cause the
solvent or mixture to decompose,
break down, or be converted into an
excessive quantity of vapor.
(iv) Tanks or machines of more than
4 square feet of vapor area, used for
solvent cleaning or vapor degreasing,
shall be equipped with suitable cleanout or sludge doors located near the
bottom of each tank or still. These
doors shall be so designed and gasketed that there will be no leakage of solvent when they are closed
(13) Scope. (i) This paragraph (d) ap.
plies to all operations involving the
immersion of materials in liquids, or in
the vapors of such liquids, for the purpose of cleaning or altering their surfaces, or adding or imparting a finish
thereto, or changing the character of
the materials, and their subsequent removal from the liquids or vapors.
draining, and drying. Such operations
include washing, electroplating. anodizing. pickling, quenching, dyeing,
dipping. tanning, dressing. bleaching,
degreasing, alkaline cleaning. stripping, rinsing, digesting, and other sim-
175
§ 1910.95
ilar operations. but do not include
molten materials handling operations,
or surface coating operations.
(ii) "Molten materials handling operations" means all operations, other
than welding. burning. and soldering
operations, involving the use, melting,
smelting, or pouring of metals, alloys.
salts, or other similar substances in
the molten state. Such operations also
include heat treating baths, descaling
baths, die casting stereotyping, galvanizing. tinning, and similar operations.
(lii) "Surface coating operations"
means all operations involving the application of protective, decorative, adhesive, or strengthening coating or impregnation to one or more surfaces, or
into the interstices of any object or
material, by means of spraying,
spreading, flowing. brushing, roll coat-
Ing. pouring. cementing, or similar
means; and any subsequent draining
or drying operations, excluding opentank operations.
(Secs. 4(b)(2), 6(b) and 8(c), 84 Stat. 1592,
1593, 1596; 29 U.S.C. 653, 655, 657; Sec. of
Labors Order No. 8-76 (41 FR 25059); 29
CFR 1911)
139 FR 23502, June 27. 1974, as amended at
40 FR 23073. May 28, 1975: 40 FR 24522,
June 9. 1975; 43 FR 49746. Oct. 24, 1978)
$ 1910.95 Occupational noise exposure.
(a) Protection against the effects of
noise exposure shall be provided when
the sound levels exceed those shown
in Table G-16 when measured on the
A scale of a standard sound level
meter at slow response. When noise
levels are determined by octave band
analysis, the equivalent A-weighted
sound level may be determined as follows:
Title 29-Labor
140
130
125
OCTAVE BAND SOUND PRESSURE LEVEL
120
120
115
DECIBELS
110
110
105
IN
100
100
95
EQUIVALENT A.WEIGHTED SOUND LEVEL
90
90
80
100
200
500
1000
2000
4000
8000
BAND CENTER FREQUENCY IN CYCLES PER SECOND
FIGURE G-9
Equivalent sound level contours. Octave
band sound pressure levels may be converted to the equivalent A-weighted sound level
by plotting them on this graph and noting
the A-weighted sound level corresponding to
the point of highest penetration into the
sound level contours. This equivalent A-
weighted sound level. which may differ
from the actual A-weighted sound level of
the noise, is used 10 determine exposure
limits from Table 1.G-16.
(b) (1) When employees are subjected to sound exceeding those listed in
Table G-16, feasible administrative or
engineering controls shall be utilized.
If such controls fail to reduce sound
levels within the levels of Table G-16,
personal protective equipment shall be
provided and used to reduce sound
levels within the levels of the table.
(2) If the variations in noise level involve maxima at intervals of 1 second
or less, it is to be considered continuous.
TABLE G-16-PERMISSIBLE NOISE
EXPOSURES
Sound
Duration per day. hours
level dBA
slow
response
8
90
6
92
4
95
3
97
2
100
1%
102
1
105
½
110
Chapter XVII-Occupational Safety and Health Administration
§ 1910.95
TABLE G-16-PERMISSIBLE NOISE
EXPOSURES'-Continued
Sound
level dBA
Duration per day, hours
slow
response
% or less
115
When the daily noise exposure is composed of two or
more periods of noise exposure of different levels. their
combined effect should be considered, rather than the individual effect of each it the sum of the following tractions:
C,IT, CJT C.IT. exceeds unity, then, the mixed exposure
should be considered to exceed the limit value. Cn indicates
the total time of exposure at & specified noise level, and Tn
indicates the total time of exposure permitted at that level
Exposure to impulsive or impact noise should not exceed
140 dB peak sound pressure level.
(c) Hearing conservation program.
(1) The employer shall administer a
continuing, effective hearing conservation program, as described in paragraphs (c) through (o) of this section,
whenever employee noise exposures
equal or exceed an 8-hour time-weighted average sound level (TWA) of 85
decibels measured on the A scale (slow
response) or, equivalently, a dose of
fifty percent. For purposes of the
hearing conservation program. employee noise exposures shall be computed in accordance with Appendix A
and Table G-16a, and without regard
to any attenuation provided by the use
of personal protective equipment.
(2) For purposes of paragraphs (c)
through (n) of this section, an 8-hour
time-weighted average of 85 decibels
or a dose of fifty percent shall also be
referred to as the action level.
(d) Monitoring. (1) When information indicates that any employee's exposure may equal or exceed an 8-hour
time-weighted average of 85 decibels,
the employer shall develop and Implement a monitoring program. (i) The
sampling strategy shall be designed to
identify employees for inclusion in the
hearing conservation program and to
enable the proper selection of hearing
protectors.
(ii) Where circumstances such as
high worker mobility. significant variations in sound level, or a significant
component of impulse noise make area
monitoring generally inappropriate,
the employer shall use representative
personal sampling to comply with the
monitoring requirements of this paragraph unless the employer can show
that area sampling produces equivalent results.
(2)(i) All continuous, intermittent
and impulsive sound levels from 80
decibels to 130 decibels shall be integrated into the noise measurements.
(li) Instruments used to measure employee noise exposure shall be callbrated to ensure measurement accuracy.
(3) Monitoring shall be repeated
whenever a change in production,
process, equipment or controls increases noise exposures to the extent
that:
(i) Additional employees may be exposed at or above the action level: or
(ii) The attenuation provided by
hearing protectors being used by employees may be rendered inadequate
to meet the requirements of paragraph (j) of this section.
(e) Employee notification. The employer shall notify each employee exposed at or above an 8-hour timeweighted average of 85 decibels of the
results of the monitoring.
(f) Observation of monitoring. The
employer shall provide affected employees or their representatives with
an opportunity to observe any noise
measurements conducted pursuant to
this section.
(g) Audiometric testing program. (1)
The employer shall establish and
maintain an audiometric testing program as provided in this paragraph by
making audiometric testing available
to all employees whose exposures
equal or exceed an 8-hour time-weighted average of 85 decibels.
(2) The program shall be provided at
no cost to employees.
(3) Audiometric tests shall be performed by a licensed or certified audiologist, otolaryngologist, or other
physician, or by a technician who is
certified by the Council of Accreditation in Occupational Hearing Conservation, or who has satisfactorily demonstrated competence in administering
audiometric examinations, obtaining
valid audiograms, and properly using,
maintaining and checking calibration
and proper functioning of the audiometers being used. A technician who
operates microprocessor audiometers
does not need to be certified. A technician who performs audiometric tests
ANEJO B13
40 CFR 260.11
References
161:1804
Anejo B13
FEDERAL REGULATIONS
wastewater treatment plant, water
supply treatment plant, or air pollution
control facility exclusive of the treated
effluent from a wastewater treatment
plant.
"Solid waste" means a solid
waste as defined in § 261.2 of this
Chapter.
"Spill" [Removed]
[Removed by 48 FR 2511, January 19, 1983]
"State" means any of the several
States, the District of Columbia, the
Commonwealth of Puerto Rico. the
Virgin Islands, Guam, American Samoa.
and the Commonwealth of the Northern
Mariana Islands.
"Storage" means the holding of
hazardous waste for a temporary period.
at the end of which the hazardous waste
is treated, disposed of. or stored
elsewhere.
"Surface impoundment" or
"impoundment" means a facility or part
of a facility which is a natural
topographic depression. man-made
excavation, or diked area formed
primarily of earthen materials (although
il may be lined with man-made
materials). which is designed to hold an
accumulation of liquid wastes or wasles
containing free liquids. and which is not
an injection well. Examples of surface
impoundments are holding. storage,
settling, and aeration pits, ponds, and
lagoons.
"Tank" means a stationary
device. designed to contain an
accumulation of hazardous waste which
is constructed primarily of non-earthen
materials (e.g., wood, concrete, steel.
plastic) which provide structural
support.
"Thermal treatment" means the
treatment of hazardous waste in a
device which uses elevated
temperatures as the primary means to
change the chemical, physical. or
biological character or composition of
the hazardous waste. Examples of
thermal treatment processes are
incineration, molten salt. pyrolysis.
calcination. wet air oxidation. and
microwave discharge. (See also
"incinerator" and "open burning".)
"Totally enclosed treatment
facility" means a facility for the
treatment of hazardous waste which is
directly connected to an industrial
production process and which is
constructed and operated in a manner
which prevents the release of any
hazardous waste or any constituent
thereof into the environment during
treatment. An example is a pipe in
which waste acid is neutralized.
"Transportation" means the
movement of hazardous waste by air.
rail. highway. or water.
engaged in the offsite transportation of
hazardous waste by air. rail, highway,
or water.
"Transporter" means a person
"Treatment" means any method,
technique, or process, including
neutralization, designed to change the
physical. chemical. or biological
character or composition of any
hazardous waste so as to neutralize
such waste, or so as to recover energy or
material resources from the waste, or so
as to render such waste non-hazardous,
or less hazardous: safer to transport.
store, or dispose of: or amenable for
recovery, amenable for storage, or
reduced in volume.
"Treatment Zone" means a soil area of
the unsaturated zone of a land treatment
unit within which hazardous constituents
are degraded, transformed, or
immobilized.
[Added by 47 FR 32349, July 26, 1982]
"Underground injection" means
the subsurface emplacement of fluids
through a bored. drilled or driven well;
or through a dug well, where the depth
of the dug well is greater than the
largest surface dimension. (See also
"injection well".)
"Unsaturated zone" or "zone of
aeration" means the zone between the
land surface and the water table.
"United States" means the 50
States, the District of Columbia, the
Commonwealth of Puerto Rico, the U.S.
Virgin Islands. Guam. American Samoa,
and the Commonwealth of the Northern
Mariana Islands.
"Uppermost aquifer" means the geologic formation nearest the natural ground
surface that is an aquifer, as well as lower
aquifers that are hydraulically interconnected with this aquifer within the facili-
1y's property boundary.
[Added by 47 FR 32349, July 26, 1982]
"Wastewater treatment unit"
means a device which:
(1) Is part of a wastewater treatment
facility which is subject to regulation
under either Section 402 or Section
307(b) of the Clean Water Act; and
(2) Receives and treats or stores an
influent wastewater which is a
hazardous waste as defined in $261.3 of
this chapter, or generates and
accumulates a wastewater treatment
sludge which is a hazardous waste as
defined in $261.3 of this chapter, or
treats or stores a wastewater treatment
sludge which is a hazardous waste as
fined in $261.3 of this chapter; and
3) Meets the definition of tank in
-0.10 of this chapter.
Added by 45 FR 76075, November 17,
1980]
or bored into the earth. generally of a
cylindrical form, and often walled with
bricks or lubing to prevent the earth
from caving in.
[260.10(a) was amended by 45 FR 86968.
December 31, 1980, to add the following
definition:]
"Water (bulk shipment)" means
the bulk transportation of hazardous
waste which is loaded or carried on
board a vessel without containers or
labels.
"Well injection": (See
"underground injection".)
"Well" means any shaft or pit dug
"Transfer facility" means any
transportation related facility including
loading docks, parking areas, storage
areas and other similar areas where
shipments of hazardous waste are held
during the normal course of
transportation.
(260.10(a) was amended by 45 FR 72028,
October 30, 1980, to add the following
definition:)
"Transport vehicle" means a motor
vehicle or rail car used for the transportation of cargo by any mode. Each
cargo-carrying body (trailer, railroad freight car, etc.) is a separate
transport vehicle. "Vessel' includes
every description of watercraft, used
or capable of being used as a means of
transportation on the water.
§ 260.11 References.
[260.11 added by 46 FR 35247, July 7,
1981)
(a) When used in Parts 260 through
265 of this chapter, the following
publications are incorporated by
reference:
"ASTM Standard Test Methods for
Flash Point of Liquids by Setaflash
Closed Tester." ASTM Standard D-
3278-78. available from American
Society for Testing and Materials. 1916
Race Street. Philadelphia, Pa. 19103.
"ASTM Standard Test Methods for
Flash Point by Pensky-Martens Closed
Tester," ASTM Standard D-93-79 or D-
93-80. D-93-80 is available from
American Society for Testing and
Materials. 1916 Race Street,
Philadelphia, Pa. 19103.
"Flammable and Combustible Liquids
Code" (1977 or 1981). available from the
National Fire Protection Association,
470 Atlantic Avenue. Boston.
Massachusetts 02210.
"Test Methods for Evaluating Solid
Waste. Physical/Chemical Methods."
EPA Publication SW-846 (First Edition.
1980. as updated by Revisions A
[August. 1980). B (July, 1981). and C
(February. 1982)) or (Second Edition,
1982). The first edition of SW-846 is no
longer in print. Revisions A and B are
available from EPA. Office of Solid
Waste. (WH-565B). 401 M Street. S.W.,
Washington. D.C. 20400. Revision C is
available from NTIS, 5285 Port Royal
Road. Springfield. Virginia 22161. The
second edition of SW-846 includes
material from the first edition and
Revisions A. B. and C in a reorganized
format. It is available from the
Superintendent of Documents, U.S.
Government Printing Office.
[Sec. 260.11(a)]
GENERAL HAZARDOUS WASTE RULES
S-655
Washington, D.C. 20402, (202) 783-3238,
on a subscription basis, and future updates
will automatically be mailed to the
subscriber.
[260.11(a) amended by 47 FR 41563,
September 21, 1982]
(b) The references listed in paragraph
(a) of this section are also available for
inspection at the Office of the Federal
Register. 1100 L Street. NW,
Washington. D.C. 20408. These
incorporations by reference were
approved by the Director of the Federal
Register. These materials are
incorporated as they exist on the date of
approval and a notice of any change in
these materials will be published in the
Federal Register.
Subpart C-Rulemaking Petitions
[Interim Final]
§ 260.20 General.
(a) Any person may petition the
Administrator to modify or revoke any
provision in Parts 260 through 265 of this
Chapter. This section sets forth general
requirements which apply to all such
petitions. Section 260.21 sets forth
additional requirements for petitions to
add a testing or analytical method to
Parts 261, 264 or 265. Section 260.22 sets
forth additional requirements for
petitions to exclude a waste at a
particular facility from § 261.3 of this
Chapter or the lists of hazardous wastes
in Subpart D of Part 261.
(b) Each petition must be submitted to
the Administrator by certified mail and
must include:
(1) The petitioner's name and address;
(2) A statement of the petitioner's
interest in the proposed action:
(3) A description of the proposed action,
including (where appropriate)
suggested regulatory language: and
(4) A statement of the need and
justification for the proposed action,
including any supporting tests,
studies. or other information.
(c) The Administrator will make a
tentative decision to grant or deny a
petition and will publish notice of such
tentative decision. either in the form of
an advanced notice of proposed
rulemaking. a proposed rule, or a
tentative determination to deny the
petition. in the Federal Register for
written public comment.
(d) Upon the written request of any
interested person. the Administrator
may, at his discretion. hold an informal
public hearing to consider oral
comments on the tentative decision. A
person requesting a hearing must state
the issues to be raised and explain why
written comments would not suffice to
communicate the person's views. The
Administrator may in any case decide
on his own motion to hold an informal
public hearing.
comments the Administrator will make
a final decision by publishing in the
Federal Register a regulatory
amendment or a denial of the petition.
(e) After evaluating all public
§ 260.21 Petitions for equivalent testing or
analytical methods.
(a) Any person seeking to add a
testing or analytical method to Parts 261,
264, or 265 of this Chapter may petition
for a regulatory amendment under this
section and § 260.20. To be successful.
the person must demonstrate to the
satisfaction of the Administrator that
the proposed method is equal to or
superior to the corresponding method
prescribed in Parts 261. 264, or 265 of
this Chapter. in terms of its sensitivity,
accuracy, and precision (i.e.,
reproducibility).
(b) Each petition must include, in
addition to the information required by
§ 260.20(b):
(1) A full description of the proposed
method. including all procedural steps
and equipment used in the method;
(2) A description of the types of wastes
or waste matrices for which the
proposed method may be used:
(3) Comparative results obtained from
using the proposed method with those
obtained from using the relevant or
corresponding methods prescribed in
Parts 261, 264, or 265 of this Chapter:
(4) An assessment of any factors which
may interfere with. or limit the use of,
the proposed method: and
(5) A description of the quality control
procedures necessary to ensure the
sensitivity. accuracy and precision of
the proposed method.
(c) After receiving a petition for an
equivalent method, the Administrator
may request any additional information
on the proposed method which he may
reasonably require to evaluate the
method.
(d) If the Administrator amends the
regulations to permit use of a new
testing method. the method will be
incorporated in "Test Methods for the
Evaluation of Solid Waste: Physical/
Chemical Methods," SW-846. U.S.
Environmental Protection Agency,
Office of Solid Waste. Washington. D.C.
20460.
[Comment: This manual will be
provided to any person on request, and
will be available for inspection or
copying at EPA headquarters or any
EPA Regional Office.]
$ 260.22 Petitions to amend Part 261 to
exclude a waste produced at a particular
facility.
(a) Any person seeking to exclude a
waste at a particular generating facility
from the lists in Subpart D of Part 261
may petition for a regulatory
amendment under this section and
§ 260.20. To be successful, the petitioner
must demonstrate to the satisfaction of
the Administrator that the waste
produced by a particular generating
facility does not meet any of the criteria
under which the waste was listed as a
hazardous waste and. in the case of an
acutely hazardous waste listed under
§ 261.11(a)(2). that it also does not meet
the criterion of § 261.11(a)(3). A waste
which is so excluded may still. however,
be a hazardous waste by operation of
Subpart C of Part 261.
(b} The procedures in this section and
§ 260.20 may also be used to petition the
Administrator for a regulatory
amendment to exclude from
§ 261.3(a)(2)(ii) or (c), a waste which is
described in those sections and is either
a waste listed in Subpart D. contains a
waste listed in Subpart D. or is derived
from a waste listed in Subpart D. This
exclusion may only be issued for a
particular generating. storage, treatment.
or disposal facility. The petitioner must
make the same demonstration as
required by paragraph (a) of this section.
except that where the waste is a mixture
of solid waste and one or more listed
hazardous wastes or is derived from one
or more hazardous wastes, his
demonstration may be made with
respect to each constituent listed waste
or the waste mixture as a whole. A
waste which is so excluded may still be
a hazardous waste by operation of
Subpart C of Part 261.
(c) If the waste is listed with codes
"I", "C", "R", or "E" in Subpart D. the
petitioner must show that demonstration
samples of the waste do not exhibit the
relevant characteristic defined in
§§ 261.21, 261.22. 261.23, or 261.24 using
any applicable test methods prescribed
therein.
(d) If the waste is listed with code "T"
in Subpart D. the petitioner must
demonstrate that:
(1) Demonstration samples of the waste
do not contain the constituent (as
defined in Appendix VII) that caused
the Administrator to list the waste.
using the appropriate test methods
prescribed in Appendix III: or
(2) The waste does not meet the
criterion of § 261.11(a)(3) when
considering the factors in
$ 261.11(a)(3) (i) through (xi).
(e) If the waste is listed with the code
"H" in Subpart D. the petitioner must
demonstrate that the waste does not
meet both of the following criteria:
(1) The criterion of $ 261.11(a)(2).
(2) The criterion of § 261.11(a)(3) when
considering the factors listed in
§ 261.11(a)[3] (i) through (xi).
(f) [Reserved for listing radioactive
wastes.]
(g) [Reserved for listed infectious
wastes.)
5-13-83
Published by THE BUREAU OF NATIONAL AFFAIRS. INC WASHINGTON DC 20037 [Sec. 250.22(g)]
ANEJO B14
Apéndice VII, 40 CFR Parte 261
Basis for Listing Hazardous Waste
161:1868
Anejo B14
FEDERAL REGULATIONS
Appendix VII.-Basis for Listing Hazardous Wastes
[Appendix VII amended by 45 FR 47833,
July 16, 1980; revised by 45 FR 74890.
November 12. 1980; 46 FR 4617, January
16. 1981]
Appendix VII-Basis for Listing Hazardous
Waste
EPA hazardous
waste No.
Hazardous constituents for which listed
F001
Tetrachioroethylene, methylene chloride
trichloroethylene, t,1,1-trichiorosthane,
carbon tetrachloride, chlorinated fluoracarbons.
F002
Telrachioroethylene, methylene chloride,
trichioroethylene, 1,1,1-trichloroethane,
chiorobenzene, 1.1,2-tnichloro-1,2,2-m
fluoroethane,
ortho-dichlorobenzene,
tichiorofluoromethane.
F003
N.A.
F004
Cresols and cresylic acid, nitrobenzene.
FOOS
Toluene, methyl ethyl kelone, carbon disul.
fide, isobutanol, pyridine.
F006
Cadmium hexavalent chromium, nickel,
cyanide (complexed).
F007
Cyanide (salts).
F008
Cyanide (salts).
F009
Cyanide (salts).
F010
Cyanide (salts).
F011
Cyanide (salts).
F012
Cyanide (complexed).
F019
Hexavalent chromium, cyanide (complexed).
K001
Pentachlorophenol. phenol. 2-chiorophenol,
p-chloro-m-cresol, 2,4-dimethylpherryl,
2,4-dinitrophenol, bichtorophenols, totrachiorophenols. 2.4-dinvtrophenol, cresosole. chrysene, naphthalene. fluoranthene,
benzo(b)fluoranthene,
benzo(a)pyrene, indeno(1.2.3-cd)pyrene.
benz(a)anthracene, dibanz(a)anthracene,
acenaphthalene
K002
Hexavalent chromium, lead
K003
Hexavelent chromium. lead.
K004
Hexavalent chromium
K005
Hexavalent chromium lead
K006
Hexavelent chromium.
K007
Cyanide (complexed). hexavalent chromium
K008
Mexavalent chromium
K009
Chlorotorm, formaldehyde. methylene chionde. methyl chloride, paraidehyde, formic
acid.
K010
Chlorolorm formaldehyde, methylene chionoe. methyl chloride paraidehyde, formic
acid, chloroacetaidehyde.
K011
acetonitrile, hydrocyanic acid
K013
Hydrocyanic acid. acrylonitrile, acetonitrie
K014
Acetonitrile acrylamide
K015
Benzyl chionds, chlorobenzene, toluene,
benzotnchloride.
KG:3
Hexachlorpbenzene, hexachlorobutadiene,
carbon tetrachloride, hexachloroethane,
perchioroethyiene.
K017
Epichiorohydrin
chlorosthers
[bis(chioromethy]) ether and bis (2-chioroethyl) ethers]. trichloropropane, dichlarapropanols.
Appendix VII-Basis for Listing Hazardous
Waste-Continued
EPA hezardous
Hazardous constituents for which listed
waste No.
K018
1.2-dichloroethane, trichioroethylene, hexachiorobutadiene, hexachiorobenzene.
K019
Ethylene dichloride, 1,1,1-trichloroethane,
1.1.2-trichiorosthane tetrachloroethanes
(1.1.2.2-lelrachloroethane and 1.1.1.2-18
trachioroethane), trichloroethylene, 10-
trachloroethylene, carbon tetrachloride.
chioroform viryl chloride, vinylidens
chioride,
K020
Ethylene dichloride, 1,1,1-trichloroethane,
1.1.2-trichloroethane, tetrachioroethanes
(1.1.2,2-tetrachlorpethane and 1,1,1,2-to
trachloroethane). trichiorosthylene, totrachkoroethylene. carbon tetrachloride.
chloroform, vinyl chloride, vinylidene
chioride.
K021
Antimony, carbon tetrachloride, chloroform.
K022
Phenol, Lers (polycyclic aromatic hydrocar.
bons).
K023
Phthalic anhydride, maleic anhydride.
K024
Phthalic anhydride, 1,4-naphthoquinane,
K025
Meta-dinitroberizene,
K026
Paraldehyde. pyridines, 2-picoline.
K027
Toluene disocyanate, toluene-2. 4-diamine.
K028
1,1,1-tnchloroethane, viryl chloride.
K029
1.2-dichiorosthane,
a chionde, vinylidene chloride, chioroform.
K030
Hexachlorobenzene. hexachlorobutadiene.
hexachloroethane
1,1,1,2-letrachicroathane. ethylene dichloride.
K031
Arsenic
K032
Hexachlorocyclopentadiene
K033
Hexachlorocyclopentadiene
K034
Hexachlorocyclopentadiene.
K035
Creosote, chrysene, naphthalene, fluoranthene benzo(b) fluoranthene,
benzo(a)pyrene. indeno(1,2,3-cd) pyrene,
benzo(a)antivacene,
dibenzo(a)anthracene. acenaphthalene
K036
Toluene,
phosphorodithidic
and
phosphare-thic acid esters.
K037
Toluene,
phosphorodithic
and
phosphoro-thioic acid esters.
K038
Phorate, formaldehyde. phosphorodithicic
and phosphorothicie acid esters.
K039
Phosphorodithic and phosphorothioic acid
esters.
K040
Phorate formaldehyde, phosphorodithic
and phosphorothioic acid esters.
K041
Toxaphene
K042
Hexachlorobenzene,
ortho-dichiorobenzene.
K043
2.4-dichtorophenol,
2,6-dichlorpphendl,
2.4,6-trichlorophenal
K044
N.A.
K045
N.A.
K048
Lead
Appendix VII-Basis for Listing Hazardous
-Continued
EPA hazardous
Hazardous constituents for which listed
waste No.
K047
N.A.
K046
Hexevelent chromium. lead.
K049
Hexavalent chromium, lead
K050
Hexavalent chromium
K051
Hexavalent chromium, leed.
K052
Lead.
K060
Cyanide, napthalene, phenolic compounds,
arsenic
K061
Hexavelent chromium, lead. cadmium
KO62
Hexavalent chromium, lead.
K069
Hexavalent chromium, lead, cadmium
K071
Mercury.
K073
Chioroform, carbon tetrachloride hexacholroethane, trichloroethane, tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachioroethane.
K083
Aniline. diphenylamine, nitrobenzene, phenylenediamina.
K084
Arsenic.
K085
Benzane, dichiorobehzenes, trichiorobenzenes. tetrachiarobenzenes, pentachlorobenzene. hexachlorobenzene, benzyl
chioride
K086
Lead. hexavalent chromium.
K087
Phenol, naphthalene.
K093
Phthalic anhydride, maleic anhydride.
K094
Phthatic anhydride
K095
ane, $.1.2.2-tetrachloroethene
K096
1,2-dichloroethane 1.1.1-Brichloroethane,
K097
Chlordane, heptachlor.
K098
Toxaphene
K099
2,4-dichloraphenol, 2,4,6-Irichlorophenol.
K100
Hexavalent chromium, lead, cadmium
K101
Arsenic.
K102
Arsenic.
K103
Aniline, nitrobonzene. phenylenediamine
K104
Aniline, benzene, diphenylamine, nivoben.
zene, phenylenediamine.
K105
Benzene, monochiorobenzene, dichiarobenzenes, 2,4,6-trichlorophenol
K106
Mercury.
N.A-Waste IS hazardous because it fails the test for the
characterishc of ignitability, corrosmly. OF reactivity.
[Appendix VII)
ANEJO B15
Apéndice A (Método 3), 40 CFR Parte 60
Gas Analysis for Carbon Dioxide, Oxigen,
Excess Air, and Dry Molecular Weight
121:1572.2
Anejo B15
and carbon monoxide (CO) concentrations
are measured at the outlet. Then the ratio of
total carbon at the incinerator inlet and outlet
is multiplied by the inlet volume to determine
the exhaust volume and volume flow rate.
2. Apparatus.
2.1 Volume Meter. Equipment described
in Method 2A.
2.2 Organic Analyzer (2). Equipment
described in Method 25A or 25B.
2.3 CO Analyzer. Equipment described in
Method 10.
2.4 CO2 Analyzer. A nondispersive
infrared (NDIR) CO2 analyzer and supporting
equipment with comparable specifications as
CO analyzer described in Method 10.
3. Procedure.
3.1 Inlet Installation. Install a volume
meter in the vapor line to incinerator inlet
according to the procedure in Method 2A. At
the volume meter inlet, install a sample probe
as described in Method 25A. Connect to the
probe a leak-tight. heated (if necessary to
prevent condensation) sample line [Stainless
steel or equivalent) and an organic analyzer
system 88 described in Method 25A or 25B.
3.2 Exhaust Installation. Three sample
analyzers are required for the incinerator
exhaust: CO2. CO, and organic analyzers. A
sample manifold with a single sample probe
may be used. Install a sample probe as
described Method 25A. Connect a leak-tight
heated sample line to the sample probe. Heat
the sample line sufficiently to prevent any
condensation.
3.3 Recording Requirements. The output
of each analyzer must be permanently
recorded on an analog strip chart. digital
recorder, or other recording device. The chart
speed or number of readings per time unit
must be similar for all analyzers so that data
can be correlated. The minimum data
recording requirement for each analyzer is
one measurement value per minute.
3.4 Preparation. Prepare and calibrate all
equipment and analyzers according to the
procedures in the respective methods. For the
CO2 analyzer. follow the procedures
described in Method 10 for CO analysis
substituting CO₂ calibration gas where the
method calls for CO calibration gas. The span
value for the CO2 analyzer shall be 15 percent
by volume. All calibration gases must be
introduced at the connection between the
probe and the sample line. If a manifold
system is used for the exhaust analyzers. all
the analyzers and sample pumps must be
operating when the calibrations are done.
Note: For the purposes of this test. methane
should not be used as an organic calibration
gas.
3.5 Sampling At the beginning of the test
period. record the initial parameters for the
inlet volume meter according to the
procedures in Method 2A and mark all of the
recorder strip charts to indicate the start of
the test. Continue recording inlet organic and
exhaust CO2. CO, and organic concentrations
throughout the test. During periods of process
interruption and halting of gas flow, stop the
timer and mark the recorder strip charts so
that data from this interruption are not
included in the calculations. At the end of the
test period. record the final parameters for
the inlet volume meter and mark the end on
all of the recorder strip charts.
3.6 Post Test Calibrations. At the
conclusion of the sampling period. introduce
the calibration gases as specified in the
respective reference methods. If an analyzer
output does not meet the specifications of the
method. invalidate the test data for the
period. Alternatively. calculate the volume
results using initial calibration data and using
final calibration data and report both
resulting volumes. Then, for emissions
calculations. use the volume measurement
resulting in the greatest emission rate or
concentration.
4. Calculations.
Carry out the calculations, retaining at
least one extra decimal figure beyond that of
the acquired data. Round off figures after the
final calculation.
4.1 Nomenclature
CO, Mean carbon monoxide concentration
in system exhaust. ppmv.
CO2. Mean carbon dioxide concentration in
system exhaust. ppmv.
HC, = Mean organic concentration in system
exhaust as defined by the calibration
gas. ppmv.
HC, Mean organic concentration in system
inlet 85 defined by the calibration gas.
ppmv.
=Calibration gas factor for ethane
calibration gas.
for propane calibration gas.
4 for butane calibration gas.
= Appropriate response factor for other
calibration gas.
V.=Exhaust gas volume, M'.
Vₗ Inlet gas volume, M³.
Q. Exhaust gas volume flow rate, m3/min.
Qu=Inlet gas volume flow rate, m3/min.
=Sample run time, min.
=Standard Conditions: 20°C. 760 mm Hg.
00=Estimated concentration of ambient
CO2. ppmv. (CO₂ concentration in the
ambient air may be measured during the
test period using an NDIR and the mean
value substituted into the equation.)
determined on a parts per million by volume
(ppmv) basis.
4.3 Exhaust Gas Volume. Calculate the
exhaust gas volume as follows:
K(HC,)
V-
a
V.
K(HC.) +
4.2 Concentrations. Determine mean
concentration of inlet organics. outlet CO2,
outlet CO. and outlet organics according to
the procedures in the respective methods and
the analyzers' calibration curves. and for the
time intervals specified in the applicable
regulations. Concentrations should be
Eq. 2B-1
4.4 Exhaust Gas Volume Flow Rate.
Calculate the exhaust gas volume flow rate
as follows:
Q-=V~
Eq. 2B-2
5. Bibliography.
5.1 Measurement of Volatile Organic
Compounds. U.S. Environmental Protection
Agency. Office of Air Quality Planning and
Standards. Research Triangle Park. N.C.
27711. Publication No. EPA-450/2-78-041.
October 1978. p. 55.
METHOD 3-GAS ANALYSIS FOR CARBON DIOXIDE,
OXYGEN, Excess AIR, AND Day MOLECULAR WEIGHT
1.1 Principle. A gas sample is extracted from a stack,
by one of the following methods: (1) single-point, grab
sampling: (2) single-point, integrated sampllug; or (3)
multi-point, integrated sampling. The gas sample is
analyzed for percent carbon dioxide (CO2), percent oxygen (0:). and, if necessary, percent carbon monoxide
(CO). If a dry molecular weight determination is to be
made, either an Orsat or 8 Fyrite analyzer may be used
for the analysis; for excess air or emission rate correction
factor determination, an Orsat analyzer must be used.
1.2 Applicability. This method is applicable for determining CO2 and O, concentrations, excess air, and
dry molecular weight of a sample from a gas stream of 8
fossil-fuel combustion process. The method may also be
applicable toother processes where it hasbeen del termined
that compounds other than CO2, O2. CO, and nitrogen
(N,) are not present in concentrations sufficient to
affect the results.
Other methods, as well as modifications to the procedure described herein, are also applicable for some or all
of the above determinations. Examples of specific methods and modifications include: (1) a multi-point sampling method using an Orsat analyzer to analyze Individual grab samples obtained at each point: (2) a method
using CO, or O₂ and stoichiometric calculations to determine dry molecular weight and excess air; (3) assigning B
value of 30.0 for dry molecular weight, in lieu of actual
measurements, for processes burning natural gas, coal, or
oil. These methods and modifications may be used, but
are subject to the approval of the Administrator. U.S.
Environmental Protection Agency
2. Apparatus
As an alternative to the sampling apparatus and systems described herein, other sampling systems (e.g.,
Liquid displacement) may be used provided such systems
are capable of obtaining A representative sample and
maintaining a constant sampling rate, and are otherwise
capable of yielding acceptable results. Use of such
systems is subject 10 the approval of the Administrator.
2.1 Grab Sampling (Figure 3-1).
2.1.1 Probe. The probe should be made of stainless
steel or borosilicate glass tubing and should be equipped
with an in-stack or -stack futer to remove particulate
matter (a plug of glass wool is satisfactory for this purpose). Any other material inert to O2. CO: CO, and N,
and resistant to temperal ure AL sampling conditions may
be used for the probe; examples of such material are
aluminum, copper, quartz glass and Teflon,
2.1.2 Pump. A. one-way squeeze bulb, or equivalent,
is used to transport the gas sample to the analyzer.
2.2 Integrated Sampling (Figure 3-2).
2.2.1 Probe. A probe such as that described in Section
2.1.1 is suitable.
1. Principle and Applicability
I Mention of trade names or specific products does not
constitute endorsement by the Environmental Protection Agency.
[Appendix A, Method 3]
S-668
121:1572.3
PROBE
FLEXIBLE TUBING
TO ANALYZER
FILTER (GLASS WOOL)
SQUEEZE BULB
Figure 3.1. Grab-sampling train.
RATE METER
VALVE
SURGE TANK
AIR-COOLED
CONDENSER
PROBE
PUMP
FILTER
(GLASS WOOL)
QUICK DISCONNECT
JB
VALVE
BAG
RIGID CONTAINER
Figure 32. Integrated gas-sampling train.
[43 FR 1495, January 10, 1978)
[Appendix A, Method 3]
9-9-83
within
121:1573
S-676
2.2.2 Condenser. An air-cooled or watercooled condenser. or other condenser that
will not remove O1, CO., CO, and N, may be
used to remove excess moisture which
would interfere with the operation of the
pump and flow meter.
2.2.3 Valve. A needle valve is used to
adjust sample gas flow rate.
2.2.4 Pump. A leak-free. diaphragm-type
pump, or equivalent, is used to transport
sample gas to the flexible bag. Install a
small surge tank between the pump and
rate meter to eliminate the pulsation effect
of the diaphragm pump on the rotameter.
2.2.5 Rate Meter. The rotameter, or
equivalent rate meter. used should be capa.
ble of measuring flow rate to within ±2 percent of the selected flow rate. A flow rate
range of 500 to 1000 cm'/min is suggested.
2.2.6 Flexible Bag. Any leak-free plastic
(e.g., Tedlar, Mylar. Teflon) or plasticcoated aluminum (e.g., aluminized Mylar)
bag. or equivalent. having a capacity consistent with the selected flow rate and time
length of the test run. may be used. A capacity in the range of 55 to 90 liters is sug.
gested.
To leak-check the bag. connect it to a
water manometer and pressurize the bag to
5 to 10 cm H2O (2 to 4 In. H,O). Allow to
stand for 10 minutes. Any displacement in
the water manometer indicates a leak. An
alternative leak-check method is to pressurize the bag to 5 to 10 cm H.O (2 to 4 in. H,O)
and allow to stand overnight. A deflated bag
indicates a leak.
2.2.7 Pressure Gauge. A water-filled U.
tube manometer. or equivalent. of about 28
cm (12 in.) is used for the flexible bag leakcheck.
2.2.8 Vacuum Gauge. A mercury manometer. or equivalent. of at least 760 mm Hg
(30 in. Hg) is used for the sampling train
leak-check.
2.3 Analysis. For Orsat and Fyrite analyzer maintenance and operation procedures. follow the instructions recommended
by the manufacturer, unless otherwise specified herein.
2.3.1 Dry Molecular Weight Determination. An Orsat analyzer or Fyrite type combustion gas analyzer may be used.
2.3.2 Emission Rate Correction Factor or
Excess Air Determination. An Orsat analyzer must be used. For low CO, (less than 4.0
percent) or high O2 (greater that 15.0 percent) concentrations, the measuring burette
of the Orsat must have at least 0.1 percent
subdivisions.
3. Dry Molecular Weight Determination
Any of the three sampling and analytical
procedures described below may be used for
determining the dry molecular weight.
3.1 Single-Point. Grab Sampling and
Analytical Procedure.
3.1.1 The sampling point in the duct
shall either be at the centroid of the cross
section or at a point no closer to the walls
than 1.00 m (3.3 ft), unless otherwise specified by the Administrator.
3.1.2 Set up the equipment as shown in
Figure 3-1, making sure all connections
ahead of the analyzer are tight and leak.
free. If and Orsat analyzer is used. it is recommended that the analyzer be leakedchecked by following the procedure in Section 5; however, the leak-check is optional.
3.1.3 Place the probe in the stack. with
the tip of the probe positioned at the sampling point: purge the sampling line. Draw a
sample into the analyzer and immediately
analyze it for percent CO, and percent O,
Determine the percentage of the gas that is
N, and CO by subtracting the sum of the
percent CO, and percent O, from 100 percent. Calculate the dry molecular weight as
indicated in Section 6.3.
3.1.4 Repeat the sampling, analysis. and
calculation procedures, until the dry molecular weights of any three grab samples
differ from their mean by no more than 0.3
g/g-mole (0.3 16/1b-mole). Average these
three molecular weights, and report the results to the nearest 0.1 g/g-mole (lb/lbmole).
3.2 Single-Point, Integrated Sampling
and Analytical Procedure.
3.2.1 The sampling point in the duct
shall be located as specified in Section 3.1.1.
3.2.2 Leak-check (optional) the flexible
bag as in Section 2.2.6. Set up the equipment as shown in Figure 3-2. Just prior to
sampling, leak-check (optional) the train by
placing a vacuum gauge at the condenser
inlet. pulling a vacuum of at least 250 mm
Hg (10 in. Hg). plugging the outlet at the
quick disconnect. and then turning off the
pump. The vacuum should remain stable for
at least 0.5 minute. Evacuate the flexible
bag. Connect the probe and place it in the
stack. with the tip of the probe positioned
at the sampling point: purge the sampling
line. Next. connect the bag and make sure
that all connections are tight and leak free.
3.2.3 Sample at a constant rate. The sampling run should be simultaneous with. and
for the same total length of time as. the pol.
lutant emission rate determination. Collection of at least 30 liters (1.00 ft1) of sample
gas is recommended: however. smaller vol.
umes may be collected, if desired.
3.2.4 Obtain one integrated flue gas
sample during each pollutant emission rate
determination. Within 8 hours after the
sample is taken. analyze it for percent CO,
and percent O, using either an Orsat analyz.
er or a Fyrite-type combustion gas analyzer.
If an Orsat analyzer is used, it is recommended that the Orsat leak-check described
in Section 5 be performed before this deter.
mination: however, the check is optional.
Determine the percentage of the gas that is
N, and CO by subtracting the sum of the
percent CO, and percent O, from 100 percent. Calculate the dry molecular weight as
indicated in Section 6.3.
3.2.5 Repeat the analysis and calculation
procedures until the individual dry molecular weights for any three analyses differ
from their mean by no more than 0.3 8/8.
mole (0.3 lb/lb-mole). Average these three
molecular weights. and report the results to
the nearest 0.1 g/g-mole (0.1 1b/lb-mole).
3.3 Multi-Point. Integrated Sampling and
Analytical Procedure.
3.3.1 Unless otherwise specified by the
Administrator. a minimum of eight traverse
points shall be used for circular stacks
having diameters less than 0.61 m (24 in.). a
minimum of nine shall be used for rectangu.
lar stacks having equivalent diameters less
than 0.61 m (24 in.). and a minimum of
twelve traverse points shall be used for all
other cases. The traverse points shall be 10.
cated according to Method 1. The use of
fewer points is subject to approval of the
Administrator.
3.3.2 Follow the procedures outlined in
sections 3.2.2 throught 3.2.5. except for the
following: traverse all sampling points and
sample at each point for an equal length of
time. Record sampling data as shown in
Figure 3-3.
4. Emission Rate Correction Factor or
Excess Air Determination
NOTE: A Fyrite-type combustion gas analyzer is not acceptable for excess air or emission rate correction factor determination.
unless approved by the Administrator. If
both percent CO, and percent O, are meas.
ured, the analytical results of any of the
three procedures given below may also be
used for calculating the dry molecular
weight.
Each of the three procedures below shall
be used only when specified in an applicable
subpart of the standards. The use of these
procedures for other purposes must have
specific prior approval of the Administrator.
11-25-83
Published by THE BUREAU OF NATIONAL AFFAIRS INC., Washington D.C. 20037
121:1574
4.1 Single Point. Grab Sampling and
Analytical Procedure.
4.1.1 The sampling point in the duct
shall either be at the centroid of the crosssection or at a point no closer to the walls
than 1.00 m (3.3 ft). unless otherwise specified by the Administrator.
4.1.2 Set up the equipment as shown in
Figure 3-1. making sure all connections
ahead of the analyzer are tight and leakfree. Leak-check the Orsal analyzer according to the procedure described in Section 5.
This leak-check is mandatory.
TIME
TRAVERSE
a
PT.
% DEV.ᵃ
1pm
AVERAGE
a
DEV
11
(
)
100
avg
(MUST BE 10%)
Figure 3-3. Sampling rate data.
4.1.3 Place the probe in the stack, with
the tip of the probe positioned at the sampling point: purge the sampling line. Draw a
sample into the analyzer. For emission rate
correction factor determination. immediately analyze the sample. as outlined in Sections 4.1.4 and 4.1.5. for percent CO, or percent O, If excess air is desired. proceed as
follows: (1) immediately analyze the sample,
as in Sections 4.1.4 and 4.1.5. for percent
CO2, O2. and CO; (2) determine the percentage of the gas that is N, by subtracting the
sum of the percent CO., percent On and percent CO from 100 percent: and (3) calculate
percent excess air as outlined in Section 6.2.
4.1.4 To insure complete absorption of
the CO., O2, or if applicable, CO. make repeated passes through each absorbing solution until two consecutive readings are the
same. Several passes (three or four) should
be made between readings. (If constant
readings cannot be obtained after three consecutive readings. replace the absorbing solution.)
4.1.5 After the analysis is completed.
leak-check (mandatory) the Orsat analyzer
once again. as described in Section 5. For
the results of the analysis to be valid. the
Orsat analyzer must pass this leak test
before and after the analysis.
NOTE: Since this single-point, grab sampling and analytical procedure in normally
conducted in conjunction with a singlepoint. grab sampling and analytical procedure for a pollutant. only one analysis is ordinarily conducted. Therefore, great care
must be taken to obtain a valid sample and
analysis. Although in most cases only CO.
or O. is required. it is recommended that
both CO, and O₂ be measured, and that
stant rate. or as
specified by the Administrator. The sampling run must be simultaneous with, and
for the same total lengh of time as, the pollutant emission rate determination. Collect
at least 30 liters (1.00 ft') of sample gas.
Smaller volumes may be collected, subject
to approval of the Administrator.
4.2.4 Obtain one integrated flue gas
sample during each pollutant emission rate
determination. For emission rate correction
factor determination, analyze the sample
within 4 hours after it is taken for percent
CO, or percent O, (as outlined in Sections
4.2.5 through 4.2.7). The Orsat analyzer
must be leak-check (see Section 5) before
the analysis. If excess air is desired. proceed
as follows: (1) within 4 hours after the
sample is taken, analyze it (as in Sections
4.2.5 through 4.2.7) for percent CO2. O,, and
CO: (2) determine the percentage of the gas
that is N, by subtracting the sum of the percent CO., percent O., and percent CO from
100 percent: (3) calculate percent excess air,
as outlined in Section 6.2.
4.2.5 To insure complete absorption of
the CO2. O,, or if applicable, CO. make repeated passes through each absorbing solution until two consecutive readings are the
same. Several passes (three of four) should
be make between readings. (If constant
readings cannot be obtained after three consecutive readings. replace the absorbing SO.
lution.)
4.2.6 Repeat the analysis until the following criteria are met:
4.2.6.1 For percent CO2. repeat the analytical procedure until the results of any
three analyses differ by no more that (a) 0.3
percent by volume when CO2 is greater than
4.0 percent or (b) 0.2 percent by volume
when CO. is less than or equal to 4.0 percent. Average the three acceptable values of
percent CO, and report the results to the
nearest 0.1 percent.
121:1574.1
4.2.6.2 For percent O,, repeat the analytical procedure until the results of any three
analyses differ by no more than (a) 0.3 percent by volume when O, is less than 15.0
percent or (b) 0.2 percent by volume when
O2 is greater than or equal to 15.0 percent.
Average the three acceptable values of percent O, and report the results to the nearest
0.1 percent.
4.2.6.3 For percent CO. repeat the analytical procedure until the results of any
three analyses differ by no more than 0.3
percent. Average the three acceptable
values of percent CO and report the results
to the nearest 0.1 percent.
4.2.7 After the analysis is completed.
leak-check (mandatory) the Orsat analyzer
once again. as described in Section 5. For
the results of the analysis to be valid, the
Orsat analyzer must pass this leak test
before an after the analysis.
NOTE: Although in most instances only
CO, or O2 is required, it is recommended
that both CO2 and O, be measured, and that
Section 4.4 to be used to validate the
analytical data.
[4.2.7 Note amended by 48 FR 49459,
October 25, 1983]
4.3 Multi-Point. Integrated Sampling and
Analytical Procedure.
4.3.1 Both the minimum number of sampling points and the sampling point location
shall be as specified in Section 3.3.1 of this
method. The use of fewer points than specified is subject to the approval of the Administrator.
4.3.2 Follow the procedures outlined in
Sections 4.2.2 through 4.2.7. except for the
following: Traverse all sampling points and
sample at each point for an equal length of
time. Record sampling data as shown in
Figure 3-3.
[Section 4.4 added by 48 FR 49459, October 25, 1983]
4.4 Quality Control Procedures.
4.4.1 Data Validation When Both CO2 and
O2 Are Measured. Although in most
instances, only CO2 or O2 measurement is
required. it is recommended that both CO2
and O2 be measured to provide a check on
the quality of the data. The following quality
control procedure is suggested.
Note-Since the method for validating the
CO2 and O2 analyses is based on combustion
of organic and fossil fuels and dilution of the
gas stream with air. this method does not
apply to sources that (1) remove CO2 or O2
through processes other than combustion. (2)
add O2 (e.g., oxygen enrichment) and N, in
proportions different from that of air. (3) add
CO2 (e.g., cement or lime kilns). or (4) have no
fuel factor. For values obtainable (e.g.,
extremely variable waste mixtures). This
S-676
method validates the measured proportions
of CO2 and O2 for the fuel type. but the
method does not detect sample dilution
resulting from leaks during or after sample
collection. The method is applicable for
samples collected downstream of most lime
or limestone fiue-gas desulfurization units as
the CO2 added or removed from the gas
stream is not significant in relation to the
total CO2 concentration. The CO2
concentrations from other types of scrubbers
using only water or basic slurry can be
significantly affected and would render the F,
check minimally useful.
4.4.1.1 Calculate 8 fuel factor, Fo. using
the following equation:
20.9-%O₂
F.-
%CO₂
Eq. 3-3
Where:
%O2=Percent O2 by volume (dry basis).
%CO₂=Percent CO2 by volume (dry basis).
Percent O2 by volume in ambient air.
If CO is present in quantities measurable
by this method. adjust the O2 and CO2 values
before performing the calculation for F. as
follows:
%CO:(adj)=%CO₂+%CO
Where: %CO=Percent CO by volume (dry
basis).
4.4.1.2 Compare the calculated F. factor
with the expected F. values. The following
table may be used in establishing acceptable
ranges for the expected F. if the fuel being
burned is known. When fuels are burned in
combination. calculate the combined fuel F.
and F, factors (as defined in Method 19)
according to the procedure in Method 19