Standards of Performance for New Stationary Sources: Starch Production Plants, Cold Cleaning Machine Operations, and Organic Solvent Cleaners
Federal RegisterOct 18, 1996
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 60
[FRL-5637-5]
Standards of Performance for New Stationary Sources: Starch
Production Plants, Cold Cleaning Machine Operations, and Organic
Solvent Cleaners
AGENCY: Environmental Protection Agency (EPA).
ACTION: Withdrawal of proposed standards of performance, final action.
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SUMMARY: New source performance standards (NSPS) required by section
111 of the Clean Air Act (Act) were proposed on September 8, 1994 (59
FR 46381) for new, modified, and reconstructed starch production
plants, and on September 9, 1994 (59 FR 46602) for new, modified, and
reconstructed cold cleaning machines. After a thorough review and
analysis of the comments received during the public comment period, the
Administrator has concluded that the proposed NSPS for these two source
categories are not needed. The proposed NSPS are, therefore, being
withdrawn.
In the September 9, 1994 notice proposing the NSPS for cold
cleaning machines, the EPA proposed to withdraw the NSPS for organic
solvent cleaners proposed on June 11, 1980 (45 FR 39765). The NSPS for
organic solvent cleaners are also being withdrawn with this document.
DATE: These proposed rules are withdrawn as of October 18, 1996.
ADDRESSES: Docket. Docket No. A-94-18, containing supporting
information used in developing the proposed NSPS for starch production
plants and a detailed discussion of the comments received during the
public comment period; and Docket No. A-94-08, containing the same
information pertaining to the proposed cold cleaning machine operations
NSPS, are available for public inspection and copying at the following
address: U.S. Environmental Protection Agency, Air and Radiation Docket
and Information Center (6102), 401 M Street, S.W., Washington, D.C.
20460. The docket is located at the above address in room M-1500,
Waterside Mall (ground floor), and may be inspected from 8 a.m. to 4
p.m., Monday through Friday. The materials are available for review in
the docket center or copies may be mailed on request from the Air and
Radiation Docket and Information Center by calling (202) 260-7548 or
7549. The FAX number for the Center is (202) 260-4000. A reasonable fee
may be charged for copying docket materials.
FOR FURTHER INFORMATION CONTACT: For information concerning specific
aspects of this action, contact Mr. William Maxwell [(919) 541-5430],
Combustion Group [starch production facilities] or Mr. Daniel Brown
[(919) 541-5305], Coatings and Consumer Products Group [cold cleaning
machines]. Both contacts are at the Emission Standards Division (MD-
13), U.S. Environmental Protection Agency, Research Triangle Park,
North Carolina 27711.
SUPPLEMENTARY INFORMATION:
Starch
The Proposed Standards
The proposed NSPS for starch production plants would have limited
emissions of particulate matter from new, modified, and reconstructed
facilities that produce dry starch (including modified starches)
derived from corn, wheat, potatoes, tapioca, or other vegetable
sources, and facilities drying starch extracted from the wastewater at
snack food production facilities (e.g., potato chips, french fries).
Typically, starch production plants are components of larger facilities
that prepare a variety of products. For example, a corn wet milling
facility will normally produce a range of products that can include
animal feed, corn gluten, corn germ, germ meal, corn oil, starch, and
starch derivatives. Starch derivatives can include modified specialty
starches, dextrins, dextrose, corn syrup, high fructose corn syrup,
ethanol, and a variety of sweeteners. Similar ranges of products may be
derived from wheat, potatoes, or tapioca.
The starch facilities that would have been affected by the proposed
NSPS for starch production plants are new, modified, and reconstructed
starch dryers; dextrin roasters; and starch transfer, storage, and
loading facilities at which construction, reconstruction, or
modification commenced after September 8, 1994. The proposed NSPS would
not have applied to any existing starch production facility, unless
such a facility was subsequently modified or reconstructed. At the time
of proposal, 17 different companies owned and operated the 47 known
existing starch production facilities: 20 produced starch from corn; 3
from wheat; 21 from potatoes; 1 from tapioca; and 2 from other
vegetable sources. These existing facilities are concentrated in the
midwestern United States, but are found in 19 States across the
country.
The proposed NSPS would also not have applied to small dryers;
small dextrin roasters; or certain starch transfer, storage, and
loading facilities located at snack food processing facilities.
Specifically, drum dryers and dryers located at snack food processing
facilities having a manufacturer's listed dry starch capacity of 907
kilograms per hour (kg/hr) (2,000 pounds per hour [lb/hr]) or less
would have been exempt, because of the low level of emissions from
these dryers. Similarly, dextrin roasters and starch transfer, storage,
and loading facilities at snack food processing facilities would have
been exempt if the dry starch capacity of any of the individual
facilities was 454 kg/hr (1,000 lb/hr) or less, because of the low
level of emissions from these facilities.
A starch dryer is the equipment used to remove uncombined (free)
water from starch slurry through direct or indirect heating. There are
several types of dryers used at starch production plants, including
single-pass (also known as one-pass) flash dryers, ring (also known
[[Page 54378]]
as loop) flash dryers, spray dryers, drum dryers, and belt (also known
as conveyor, tunnel, or apron) dryers. A dextrin roaster is a reactor
vessel, or a series of vessels, in which starch is reacted, through the
addition of heat and/or chemicals, to form the modified starch
``dextrin'' (or ``polydextrin''). Starch transfer, storage, and loading
facilities include any facility used to blend, mix, mill, grind,
screen, convey, transfer, store, or load for shipment (into any
container for shipment, including, but not limited to, bag, truck, and
rail car) dry starch.
Specifically, the proposed NSPS would have limited particulate
matter emissions from ring flash dryers to 45 mg/dscm (0.02 gr/dscf);
from single-pass flash dryers to 25 mg/dscm (0.01 gr/dscf); and from
spray dryers, drum dryers, and belt dryers to 10 mg/dscm (0.05 gr/
dscf). The proposed NSPS would also have limited visible emissions from
dextrin roasters and starch transfer, storage, and loading facilities
to zero percent opacity.
Rationale for Withdrawing the Proposed NSPS
The Agency is withdrawing the proposed NSPS for new, modified, or
reconstructed starch production plants because it has concluded that
promulgation of such standards of performance would achieve little or
no emission reduction from starch facilities and, therefore, that
promulgation of NSPS is unnecessary, not cost effective, and will not
serve the purposes of the Act. After reviewing comments on the
September 8, 1994 proposed NSPS, the EPA believes that new, modified,
or reconstructed starch facilities that would be subject to the
emission standards will employ the best demonstrated technological
system of continuous emission reduction (BDT) necessary to meet such
standards and, hence, will, or already do, meet the performance
standards without additional regulatory requirements.
Although starch production facilities are one of the source
categories on the priority list of major source categories for the
development of NSPS pursuant to section 111 of the Act (section 60.16),
in promulgating the priority list the Agency reserved the right to
remove a source category from the priority list if it subsequently
determined that promulgating NSPS for a particular source category
would have little or no effect on emissions. Indeed, not only is it
likely that promulgating NSPS for new or modified starch facilities
would achieve little or no emission reduction, but currently available
information about the relative size and operating practices of the
starch industry suggests the industry does not pose the environmental
concern that the Agency originally believed existed over 14 years ago
when it listed starch production facilities on the priority list of
major source categories.
Starch processing and production plants were listed in 1982 as one
of 59 source categories on the priority list of major source categories
because of the concern about particulate matter, a criteria pollutant,
that is emitted from starch processing and production facilities in the
form of starch dust. Significantly, starch facilities were initially
identified in the late 1970's as a source of particulate matter for
inclusion on the priority list of major source categories based on the
potential for uncontrolled emissions of starch dust from a facility. It
is, however, not the current practice of the starch industry, if indeed
it ever was, to allow uncontrolled emissions of starch. As discussed
below, starch facilities have an economic incentive to minimize losses
of their product, starch, by recapturing emissions of starch dust to
the extent possible in order to remain competitive. Accordingly, after
issuing today's notice that withdraws the proposed NSPS for starch
facilities, the Agency may remove the starch industry from the priority
list of major source categories for which NSPS are to be promulgated.
Summary of Public Comments
None of the five commentors to the proposed standards supported the
need for the standards. One commentor challenged the need for the NSPS
and the remaining commentors addressed the technical aspects of the
proposed standards. The comments that address the technical validity of
the standards are not discussed in today's notice because they are not
relevant to the Agency's decision to withdraw the proposed NSPS. A
summary and analysis of these comments has been placed in the docket
for the proposed rule.
The commentor that opposes the proposed NSPS argues that the
standards are unnecessary, because (1) starch facilities are minor
sources of particulate matter, (2) the proposed NSPS would not reduce
emissions from new, modified, or reconstructed starch facilities as
these facilities will employ BDT that would be required by the
regulations to meet the proposed emission standards for particulate
matter, (3) the proposed NSPS would impose significant additional
administrative and reporting costs with no commensurate environmental
benefits. The Agency agrees with the comments for the reasons discussed
below.
Analysis of Comments
The EPA's analysis indicates that promulgation of NSPS for starch
production plants would achieve little or no emission reduction from
starch facilities. Owners and operators of starch facilities have a
very significant economic incentive to recover as much of the starch
particulate emissions from their facilities as possible. Unlike other
facilities where particulate emissions are typically an unwanted by-
product that not only has no economic value but would, in fact, be
expensive for a facility to capture and dispose of properly,
particulate emissions at starch facilities are made up of starch, which
is of course, the very product of economic value that such facilities
produce for sale. To the extent, therefore, that a starch facility
captures and minimizes the amount of starch particulates released to
the environment, it will have that much more starch product for sale
and, hence, be that much more profitable. Indeed, a starch facility
that allows the starch that it produces to be wasted as particulate
emissions to the environment would be less efficient than a competitor
that does not waste its product and would become less competitive and,
hence, less profitable than its cleaner and more efficient competitor.
Pursuant to the proposed NSPS, new, modified, and reconstructed
starch dryers; dextrin roasters; and starch transfer, storage, and
loading facilities would have had to use wet scrubbers or fabric
filters, which is the BDT for starch facilities, in order to meet the
required emission levels. The EPA's investigations, however, show that
existing facilities already collect particulate matter from the exhaust
ducts or vents of the affected facilities for the reasons discussed
above. Specifically, while most existing starch dryers are, at a
minimum, equipped with cyclonic collectors, the newer starch dryers are
equipped with low energy wet scrubbers or fabric filters, either alone
or in combination with one or more cyclones. Waste water from the
scrubbers and collected dust from the fabric filters are returned to
the process and not sent to disposal. Similarly, dextrin roasters and
starch transfer, storage, and loading facilities employ fabric filters
to recover starch emissions in dry form for immediate recycle to the
process. (See docket A-94-18, entry II-A-8, pp. 4+).
The fact that existing newer starch facilities already employ BDT
(even
[[Page 54379]]
though they are not required to do so) supports the conclusion that
promulgating NSPS for new or modified starch facilities would achieve
little or no emission reduction. Not only would this appear to confirm
that existing starch facilities must minimize losses of their product
to remain economically competitive, but it further suggests that any
new or modified starch facilities, which must function at least as
efficiently as existing facilities in order to compete with such
facilities, must equal, if not exceed, the amount of starch recaptured
by existing facilities and, thereby, effectively control emissions of
particulate matter at or below the levels of emissions contemplated by
the proposed NSPS.
For the reasons discussed above, the Agency anticipates little or
no reduction in particulate matter emissions from starch facilities by
mandating maximum emission levels. Arguably, any emission reductions
achieved by promulgating NSPS would result from improved operation and
maintenance of starch facilities as a result of the proposed monitoring
requirements for such facilities. However, it is the EPA's judgement
that the potential marginal reduction in particulate matter emission
levels from starch facilities does not justify the additional
administrative costs (primarily related to monitoring and recordkeeping
and estimated at approximately $1.6 million nationwide) that would be
required by the standards of performance.
Cold Cleaning Machine Operations and Organic Solvent Cleaners
The Proposed Standards
The NSPS for organic solvent cleaners, which were proposed on June
11, 1980, would have limited emissions of volatile organic compounds
(VOC) and trichloroethylene, perchloroethylene, methylene chloride,
1,1,1-trichloroethane, and trichlorotrifluoroethane from new, modified,
and reconstructed organic solvent cleaners. On December 2, 1994,
national emission standards for hazardous air pollutants (NESHAP) were
promulgated for halogenated solvent cleaners (40 CFR Part 63, Subpart
T), and on September 9, 1994, the NSPS for cold cleaning machine
operations was proposed. The halogenated solvent cleaner NESHAP and the
proposed NSPS for cold cleaning machine operations eliminated the need
for the duplicative standards proposed in the NSPS for organic solvent
cleaners (45 FR 39766). Therefore, the EPA proposed withdrawal of the
NSPS for organic solvent cleaners when the NSPS for cold cleaning
machines was proposed.
The proposed NSPS for cold cleaning machine operations would have
limited emissions of VOC from new, modified, and reconstructed cold
cleaning machines. Specifically, the proposed NSPS would have limited
VOC emissions from cold cleaning machines with a solvent-air interface
greater than or equal to 1.8 square meters (19 square feet) by
requiring equipment standards and work practices considered to be BDT.
Rationale for Withdrawing the Proposed NSPS
The decision to withdraw the proposed NSPS is based on the Agency's
finding that all cold cleaning machines likely to become subject to the
NSPS would employ BDT, even in the absence of the NSPS. The EPA
believes that existing regulations are adequate to protect the public
health and welfare, and promulgation of the NSPS for cold cleaning
machines would impose additional administrative burdens without
providing significant emission reductions. In making this decision, the
Administrator has concluded that withdrawal of the proposed NSPS is
consistent with the purposes of section 111 of the Act in light of
current (and expected future) control patterns for cold cleaning
machine operations.
The proposed standards were all pollution prevention techniques
that minimize the solvent vapor loss from the machine and encourage
reuse of solvent. The proposed equipment standards for cold cleaning
machines included covers, drain rack, raised freeboard, visible fill
line, solvent pump pressure design limits, and a label stating required
work practices. The proposed work practices included not exceeding the
tank solvent fill line, flushing performed in the freeboard area with
continuous stream, operating the agitator without observable splashing,
closing the machine's cover when it is not in use or when the agitator
is being used, guarding against air drafts when the machine cover is
open, draining cleaned parts, storing waste solvent in closed
containers, and cleaning up spills. Finally, the proposed NSPS
contained reporting requirements including an initial notification
report demonstrating equipment compliance and an annual report
demonstrating continued equipment compliance. The Office of Management
and Budget (OMB) did not find sufficient justification for the annual
reporting requirement; therefore, that provision would have been
dropped from the proposed NSPS.
Notwithstanding that there is currently no NSPS for cold cleaning
machines, these units are already subject to many, if not all, of the
regulatory requirements that would be mandated by the NSPS. Cold
cleaning machines, for example, that use halogenated solvents are
subject to the NESHAP for halogenated solvent cleaning. Furthermore,
cold cleaning machines located in non-attainment areas, regardless of
whether they use halogenated or non-halogenated solvents, are subject
to reasonably available control technology (RACT) rules established
pursuant to section 182 of the Act and the 1977 Control Techniques
Guideline (CTG) for the Control of VOC Emissions from Solvent Metal
Cleaning. The EPA, therefore, believes that the proposed NSPS
requirements would be duplicative of existing requirements for cold
cleaning machines that are already subject to the 1994 NESHAP for
halogenated solvent cleaning and/or RACT rules based on the 1977
solvent metal cleaning CTG.
The existing regulatory requirements establish four levels of
coverage for cold cleaning machines; the relative stringency of the
regulatory requirements applicable to each category depends on the type
of solvent (halogenated, non-halogenated, or mixture of both) used in
the operation, and whether the operation takes place in an area
designated as attainment or non-attainment of the national ambient air
quality standards for ozone.
The first level of coverage would affect cold cleaning machines
that (1) use both halogenated and non-halogenated solvents and (2) are
located in a non-attainment area. These units are subject to both the
NESHAP and RACT requirements. The existing regulatory requirements
applicable to machines in this situation not only meet, but exceed, the
regulatory requirements of the proposed NSPS. The combination of the
NESHAP and RACT requirements provide for the same five equipment
standards and nine work practices that would be required by the
proposed NSPS. Furthermore, cold cleaning machines in this situation
are also subject to monitoring, recordkeeping, and annual reporting
requirements that the proposed NSPS would not require.
The second level of coverage would affect cold cleaning machines
that (1) use both halogenated and non-halogenated solvents and (2) are
operated in an attainment area. These units are subject to the NESHAP
requirements only. The NESHAP requires the same work practices as the
proposed NSPS and the same
[[Page 54380]]
equipment standards with the exception of the drain rack, the label
stating the work practices, and the solvent pump pressure design
limits. As discussed in the Response to Comments Section below, the
solvent pump pressure design limit as proposed in the NSPS would have
been deleted if the NSPS had been promulgated. Furthermore, although a
drain rack is not specified as an equipment standard in the NESHAP,
draining of cleaned parts is a work practice requirement that
inherently requires a drain rack, or something of equal utility, to be
present. Accordingly, the EPA believes that the existing regulatory
requirements applicable to machines in this situation would provide for
the same work practices and equipment standards that would be required
in a final NSPS. Again, cold cleaning machines in this situation are
also subject to monitoring, recordkeeping, and annual reporting
requirements that a final NSPS would not have required.
The third level of coverage would affect cold cleaning machines
that (1) use only non-halogenated solvents and (2) are located in a
non-attainment area. These units are subject to RACT requirements only.
The RACT requirements include several of the work practices proposed in
the NSPS and all of the equipment standards with the exception of a
visible fill line. The work practice requirements included in the
proposed NSPS, but not required by RACT, include not exceeding the
solvent fill line, flushing to be performed in the freeboard area with
continuous stream, operating the agitator without observable splashing,
guarding against air drafts when the machine cover is open, and
cleaning up spills. It is difficult to verify continued compliance for
these and all other work practices proposed in the NSPS and required by
RACT. The work practices, however, are common sense pollution
prevention techniques that minimize solvent loss and are beneficial to
the operators of cold cleaning machines. Accordingly, the EPA believes
the existing regulatory requirements applicable to machines in this
situation would provide for the work practices and the equipment
standards (with the exception of a visible fill line) included in a
final NSPS. A final NSPS would have required an initial notification
demonstrating compliance with all equipment standards, including a
visible fill line. Although the absence of a final NSPS in this
situation could result in cold cleaning machines without a visible fill
line, as discussed below, the EPA believes all cold cleaning machines
will be constructed with visible fill lines.
Finally, the fourth level of coverage would affect cold cleaning
machines that are (1) located in an attainment area and (2) operated
with only non-halogenated solvents. These units are subject to neither
the NESHAP nor the RACT requirements. Although machines in this
situation are not necessarily subject to RACT rules or the NESHAP, to
the extent that cold cleaning machines are built to a single standard
with BDT, the EPA believes that such machines will meet both the RACT
and NESHAP equipment standards. Based on information available to the
Administrator, the EPA believes that cold cleaning machines are built
to a single standard that reflects BDT as specified in the CTG and
NESHAP such that a machine design can be constructed for sale and/or
distribution throughout the United States regardless of the machines
ultimate location in an attainment or non-attainment area. Similarly,
cold cleaning machines built to a single standard reflecting BDT allows
the machine operators flexibility in choosing the type of cleaning
solvent used (halogenated, non-halogenated, or a mixture). Accordingly,
the EPA believes that machines in this situation would meet the
equipment standards that a final NSPS would require. The EPA also
believes that operators of machines in this situation would meet the
work practices that would be included in a final NSPS. The EPA expects
that the regulated community would follow such work practices as a
matter of course to the extent that such practices are pollution
prevention techniques which benefit the operator and reflect prudent,
if not standard, operating practices already employed in the industry.
Under a separate action, the Agency may proceed to revise the
priority list of major source categories for which NSPS are required by
deleting the ``organic solvent cleaners'' listing. In finalizing this
priority list, the Agency indicated that a subsequent finding that any
NSPS would have little or no effect on emissions would be sufficient
grounds for removing that source category from the priority list (44 FR
49223).
Summary of Public Comments
Ten comment letters were received during the public comment period
following proposal. Two commenters advised the Agency that there was
redundancy and duplicative requirements in the proposed NSPS that were
already required in the NESHAP and the RACT; the other commenters
addressed various technical aspects of the proposed NSPS. After
reviewing all the comments, the EPA has concluded that the proposed
NSPS is not needed. A summary and analysis of the ten comment letters
received appears in the docket; only those comments pertinent to the
decision to withdraw the NSPS are discussed here.
The comment regarding the duplicative requirements in the proposed
NSPS and NESHAP suggested that cold cleaning machines could be subject
to both standards which would require unnecessary compliance burden
with no additional air quality benefit. The comment regarding
duplicative requirements in the proposed NSPS and RACT rules suggested
that some State RACT rules are more stringent than the proposed NSPS
and specific language should be included in the final NSPS stating that
more stringent RACT rules take precedence over the NSPS. Two of the
technical comments received were in regard to solvent pump pressure
design limits stating that certain cleaning operations could only be
conducted with high pressure solvents and the final NSPS should not
prohibit these operations. These comments are discussed in the
following paragraphs.
Analysis of Comments
The EPA's analysis indicates that the proposed NSPS would achieve
little or no emission reduction. At proposal, the Agency acknowledged
that promulgation of the NESHAP for halogenated solvent cleaners
eliminated the need for the NSPS for organic solvent cleaners and
proposed withdrawal of that NSPS. The EPA now believes that existing
regulations for cold cleaning machines in the NESHAP and RACT rules are
adequate to protect public health and welfare and the proposed NSPS for
cold cleaning machines is also unnecessary. If the EPA moved forward
with promulgation of the NSPS, the equipment standard for solvent pump
pressure would have been eliminated so as not to prohibit necessary
cleaning operations for some sectors of industry. With the absence of
this equipment standard, the NESHAP equipment standards are essentially
the same as the NSPS equipment standards (see rationale for withdrawing
the NSPS).
After reviewing its analysis and the submitted comments, it is the
Agency's judgment that compliance with the NSPS in this instance would
achieve little or no VOC emission reductions; therefore, the benefits
of the proposed standards do not justify the additional administrative
costs that would be required by an NSPS.
[[Page 54381]]
Economic and Regulatory Impacts
Today's withdrawal of three proposed rules is not a rulemaking; it
does not impose or relieve any regulatory requirements or costs on the
regulated community or the national economy.
List of Subjects in 40 CFR Part 60
Environmental protection, Air pollution control, Intergovernmental
Relations, Reporting and recordkeeping requirements, Starch production
plants, Cold cleaning operations, Organic solvent cleaners.
Dated: October 11, 1996.
Carol M. Browner,
Administrator.
[FR Doc. 96-26816 Filed 10-17-96; 8:45 am]
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