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Comment submitted by Paul R. Tourangeau, Director, Colorado Air Pollution Control Division, Colorado Department of Public Health and Environment (CDPHE)
Document ID: EPA-HQ-OAR-2004-0083-0098
Document Type: Public Submission
Agency: Environmental Protection Agency
Received Date: October 22 2007, at 02:56 PM Eastern Daylight Time
Date Posted: October 24 2007, at 12:00 AM Eastern Standard Time
Comment Start Date: September 20 2007, at 12:00 AM Eastern Standard Time
Comment Due Date: October 22 2007, at 11:59 PM Eastern Standard Time
October 22, 2007
National Emission Standards for Hazardous Air Pollutants for Area Sources
Electric Arc Furnace Steelmaking Facilities Docket
Environmental Protection Agency
Air and Radiation Docket and Information Center
Mailcode: 2822T
1200 Pennsylvania Avenue, NW
Washington, DC 20460
Re: State of Colorado Comments on the Electric Arc Furnace NESHAP
Docket ID No. EPA-HQ-OAR-2004-0083
To Whom It May Concern:
This letter provides written comments from the Colorado Department of Public Health
and Environment (CDPHE) on the Proposed Rule for the National Emission Standards
for Hazardous Air Pollutants for Electric Arc Furnace Steelmaking Facilities. Thank you
in advance for considering these comments.
Mercury pollution is a serious environmental and public health threat in Colorado and
throughout the United States. In Colorado alone, 17 reservoirs are impaired for fish
consumption due, in part, to atmospheric deposition of mercury. To address this
extensive issue, Colorado has appropriately implemented one of the nation?s more
stringent mercury-reduction programs.
Although CDPHE commends the innovative pollution prevention approach that EPA is
taking in the proposed regulation, CDPHE believes the proposal is deficient in several
respects. Generally, CDPHE noted the rule?s lack of enforceable accountability and
emissions monitoring requirements to assess and verify mercury pollution reductions.
We also note that the limited scope of the proposed regulation does not address other
potential contributors of mercury to scrap metal.
Through these comments, Colorado respectfully highlights the following issues.
Accountability
While the proposed rule relies heavily on the effectiveness of pollution prevention plans
to reduce mercury emissions, states have little or no say in approving such site-
specific plans. States and/or local agencies should have more authority over such
approvals. In addition, states have previously called upon EPA to include in its
regulations an approach to verify the effectiveness of mercury source reduction
programs such as the National Vehicle Mercury Switch Recovery Program (NVMSRP )
and/or alternative switch removal efforts. This verification should be achieved through
written documentation and audits of program participants, evaluation of switch recovery
rates, and mercury emissions testing/monitoring requirements. Such accountability
measures were not adequately addressed in the proposed rule. For example, the
proposed rule includes no enforceable measures or mechanisms to ensure effective
participation or compliance with NVMSRP or other switch removal programs. Thus, the
proposed rule provides no mechanism to improve switch collection should the NVMSRP
fail to achieve its collection targets. Quantifiable performance measures, such as the
fraction of switches collected from end-of-life vehicles, should be included in the rule.
Enforceability
Metallic scrap restrictions exemptions, as proposed, are vague and therefore make the
restrictions and exemptions difficult and practically unenforceable. For example, the
proposed rule commonly uses the phrase "to the extent practicable". 40CFR63:10685
(a)(1)(i) requires that scrap materials must be depleted "to the extent practicable" of
undrained used oil filters, chlorinated plastics, and free organic liquids. This phrase is
also associated with the removal of lead-containing components. Additionally, the
proposed rule defers to removal of lead-containing components from scrap according
to "standard industry practice." While the intent is clear, it is nearly impossible to
ensure 100% removal. It is suggested that EPA define these above-mentioned terms
(or at least set boundaries/criteria), set a particular standard, or make these
requirements voluntary. Also, exemptions from pollution prevention plans allowing the
charging of recycled "baghouse bags or other internal process or maintenance
materials in the furnace" should not be allowed unless specifically identified in the
pollution prevention plan and approved by the Administrator. If not, these exemptions
create a potential loophole for sources to charge otherwise unacceptable materials in
the EAF.
The proposed rule sets an 80% switch removal goal but is silent on what happens if
these goals are not met. The rule should include a ?date final? when the goal(s) will be
met and identify the emission standards to be met (instead of the 80% switch removal
goal). In addition, the Administrator should specifically consider the participation rate of
scrap suppliers to an area steel mill and the collection rate of the largest scrap
suppliers prior to approving the goals, measuring the progress towards those goals, and
in setting emission standards.
Also, the proposed rule identifies opacity standards for the melt shop exclusive to the
EAF or ladle metallurgy operations, but not to other sources. Based on CDPHE?s
experiences, many different operations occur within the melt shop, including ladle
preheating, slag handling, diesel vehicle operation, etc. As currently written, this
standard will be extremely difficult to enforce. Thus, CDPHE suggests removing the
proposed rule?s exclusivity to EAF or ladle metallurgy operations.
Monitoring/ Evaluation of Program
It is suggested that EPA set specific mercury emission standards and use a tiered
approach towards demonstrating compliance rather than merely setting an 80%
collection ?goal.? For example, sources that emit less than a certain amount of mercury
per year might be allowed to comply with the proposed rule's work practice standards,
along with some sort of mercury emissions monitoring requirement. However, for more
significant emitters, more stringent monitoring should be required and done so with the
understanding that if a certain mercury emission standard is not achieved in a given
timeframe (e.g., three to four years), the source should install mercury emissions
controls and implement associated monitoring. Although the rule dismisses the
feasibility of emissions testing, monitoring technologies do exist that might be adaptable
for use by this industry.
Information regarding a residual risk determination is absent in the rule and should be
included. Since there are no set mercury emission standards, it would appear very
difficult for EPA to conduct its residual risk determination.
In closing, Colorado has gone to great lengths to adopt one of most encompassing
mercury programs in the nation. Given Colorado's strong commitment to minimizing the
release of and impacts from mercury, Colorado respectfully requests that EPA?s rule
for Electric Arc Furnaces be crafted to ensure such emissions are similarly minimized.
If Colorado can be of any assistance in this matter, please contact Theresa Amoroso of
my staff at 303-692-3111.
Sincerely,
Paul R. Tourangeau
Director, Colorado Air Pollution Control Division
Comment submitted by Paul R. Tourangeau, Director, Colorado Air Pollution Control Division, Colorado Department of Public Health and Environment (CDPHE)
This is comment on Proposed Rule
Revision of Source Category Lists for Standards Under Sections 112(c) and 112(k) of the Clean Air Act; and National Emission Standards for Hazardous Air Pollutants for Area Sources: Electric Arc Furnace Steelmaking Facilities
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