BLUE RIDGE ENVIRONMENTAL DEFENSE LEAGUE
www.BREDL.org
~ PO Box 88 Glendale Springs, North Carolina
28629 ~ Phone (336) 982-2691 ~ Fax (336) 982-2954
~ Email: BREDL@skybest.com
January 27, 2004
Scott Miller
Air Permits Section, APTMD
U.S. EPA Region 4
61 Forsyth Street, SW
Atlanta, GA 30303
Fax: 404-562-9019
E-mail: Miller.Scott@epamail.epa.gov
Re: International Paper-Riegelwood Mill,
Site Number: 2400036, Air Permit No. 03138T20
Dear Mr. Miller:
On behalf of the Board of Directors of the
Blue Ridge Environmental Defense League and our
members in the Columbus, Bladen, Pender,
Brunswick, and New Hanover county area, I write
to provide comments on the air permits for
International Paper-Riegelwood.
Request
We ask that the EPA comment period be extended
two weeks so that additional oral and written
remarks may be included in the record for this
permit. As you know, upon the denial of requests
for public hearing by NC DAQ Director Keith
Overcash, we planned to have a grassroots
organized Peoples Hearing for Columbus
County residents and other interested citizens.
The hearing was to have been held tonight in Lake
Waccamaw but winter weather, downed telephone
lines and power outages in coastal NC counties
have forced us to postpone the hearing until
February 12th. Therefore, we hereby
request that the EPA comment period be extended
from January 30 to February 13, 2004.
Overview
International Paper-Riegelwood is a bleached
kraft paper mill (SIC 2631, NAICS 32213) which
manufactures paperboard from wood fiber. Wood
chips are cooked in digesters with white liquor:
sodium sulfide and sodium hydroxide, Na2S
and NaOH. Spent liquor and lignin are removed
from the mixture, leaving a brown cellulose pulp.
Turpentine is also removed from the resulting
mixture when softwoods are used. The pulp is then
bleached with chlorine dioxide to make paper.
To reduce water pollution, paper mill
operators burn waste products from the paper
process in the power boilers. International
Paper-Riegelwoods draft permit lists 5
power boilers, 3 recovery boilers, 4 smelt tanks,
2 lime slakers, 2 lime kilns, and many other
sources of air pollutants. The plant is a major
source of HAPs and must comply with Title III
maximum achievable control technology (MACT)
standards for paper mills (40 CFR Part 63,
Subparts S and MM).
International Paper seeks a case-by-case MACT
determination for two of the power boilers under
the Industrial, Commercial, Institutional Boiler
source category (Section 112j of the 1990 Clean
Air Act Amendments). Case-by-case MACT allows the
operator of a major pollution source to satisfy
air quality standards based on a risk assessment,
that is, an estimate of the hazard to public
health. Three of the power source boilers for the
paper mill burn fuel oil (No. 4 or No. 6). The
other two boilers burn a variety of fuels
including coal, wood bark, paper making sludge,
and oil residue; these are the two boilers for
which IP seeks a case-by-case MACT . A risk
assessment and computer air modeling analysis was
performed by International Paper and were
submitted to the NC Division of Air Quality.
Riegelwood mill is a major source, with annual
emissions of:
| PM |
2192 tons/year |
| SO2 |
2830 tons/year |
| VOC |
1,40 tons/year (sic) |
| NOx |
5408 tons/year |
| CO |
6214 tons/year |
| HAP |
1106 tons/year |
Total reduced sulfur (TRS) air
emissions are regulated by NSPS CAA section 111.
National Emission Standards for Hazardous Air
Pollutants (NESHAP) Subparts S, MM, BB and Kb
apply to emission sources at IP-Riegelwood.
The permit approved by the NC Division of Air
Quality sets the following state-only enforceable
acceptable ambient limits (AAL) for toxic air
pollutants which may be emitted annually by
IP-Riegelwood (in pounds of emissions per year):
toxic air pollutant pounds
per year
| Acetaldehyde |
7,513,452
|
| Acrylonitrile |
436
|
| Carbon
disulfide |
986,376
|
| Carbon
tetrachloride |
23,125
|
| Chlorine |
100,338
|
| Chloroform |
38,051
|
| Chromium
VI |
80
|
| Cresol |
91,104
|
| Fluorides |
75,701
|
| Formaldehyde |
72,708
|
| Hexachlorocyclopentadiene |
1,569
|
| Mercury
compounds |
137,386
|
| Methylene
chloride |
18,150,346
|
| Pentachlorophenol |
2,299
|
| Phenol |
7,884
|
| Sulfuric
acid |
1,337,104
|
| Total |
28,537,963
|
General Comments
Air pollutants emitted by IP-Riegelwood
include compounds which cause serious
neurological damage, carcinogens, and many other
health problems in plant workers and mill
neighbors. The pollutants include large amounts
of toxic formaldehyde, hydrogen sulfide,
hydrochloric acid, sulfuric acid, mercury, dioxin
and many others. Because they emit large amounts
of hazardous air pollutants (HAP) to the air,
paper mills are regulated by Title III of the
federal Clean Air Act.
Neurotoxicants
Paper mills are well known for their
distinctive, rotten-egg odor caused by sulfur
compounds. Medical data continues to mount
revealing serious and long-term negative health
impacts from these pollutants. Reduced sulfur
compounds such as hydrogen sulfide and carbon
disulfide have devastating effects even at levels
previously thought to be acceptable. A study
published in Archives of Environmental Health on
these compounds effects (below) on
residents living near a paper mill indicates that
that adverse health effects of malodorous
sulfur compounds occur at lower concentrations
than reported previously. The total reduced
sulfur exposure levels in this study were in the
2 to 3 microgram/cubic meter range which is two
to three orders of magnitude lower than the North
Carolina AALs for such compounds.
| Arch Environ Health.
1996 Jul-Aug;51(4):315-20
The South Karelia Air Pollution Study:
effects of low-level exposure to
malodorous sulfur compounds on symptoms.
Partti-Pellinen K,
Marttila O, Vilkka V, Jaakkola JJ,
Jappinen P, Haahtela T.
South Karelia Allergy
and Environmental Institute, Tiuruniemi,
Finland.
Exposure to very low
levels of ambient-air malodorous sulfur
compounds and their effect on eye
irritation, respiratory-tract symptoms,
and central nervous system symptoms in
adults were assessed. A cross-sectional
self-administered questionnaire (response
rate = 77%) was distributed during March
and April 1992 to adults (n = 336) who
lived in a neighborhood that contained a
pulp mill and in a nonpolluted reference
community (n = 380). In the exposed
community, the measured annual mean
concentrations of total reduced sulfur
compounds and sulfur dioxide measured in
two stations were 2 to 3 micrograms/m3
and 1 micrograms/m3, respectively. In the
reference community, the annual mean
concentration of sulfur dioxide was 1
micrograms/m3. The residents of the
community near the pulp mill reported an
excess of cough, respiratory infections,
and headache during the previous 4 wk, as
well as during the preceding 12 mo. The
relative risk for headache was increased
significantly in the exposed community,
compared with the reference area: the
adjusted odds ratio (aOR) was 1.83 (95%
confidence interval [95% CI] = 1.06-3.15]
during the previous 4 wk and 1.70 (95% CI
= 1.05-2.73) during the preceding 12 mo.
The relative risk for cough was also
increased during the preceding 12 mo (aOR
= 1.64, 95% CI = 1.01-2.64). These
results indicated that adverse health
effects of malodorous sulfur compounds
occur at lower concentrations than
reported previously.
PMID: 8757412 [PubMed -
indexed for MEDLINE]
|
Carbon disulfide is a potent
neurotoxicant which affects the nervous system;
even low levels of may result in headaches, loss
of energy, altered behavior, sleep disturbances,
memory loss, depression and suicide. Research
indicates that negative health effects occur at
lower levels of exposure. Abstracts of two
studies are reproduced below:
| Neurobehavioral
toxicity of carbon disulfide. Neurobehav Toxicol Teratol. 1981
Winter;3(4):397-405
Wood RW.
Carbon disulfide is an
exceptionally potent neurotoxicant. In
industrial settings its effects are
pernicious, producing symptoms and
behavioral alterations in the absence of
frank poisoning; affective disorders are
common, and exposure is associated with
an elevated incidence of suicide. With
more severe exposure, sensory
disturbances are commonplace, as are
alterations in sensory and motor nerve
function. Alterations in behavior and
central nervous system function can be
readily produced in the laboratory with
acute or chronic carbon disulfide
exposure. Profound morphological changes,
especially in the basal ganglia, can be
produced with intense exposure. Dopamine
beta-hydroxylase inhibition has been
demonstrated in vivo and in vitro.
Despite prolonged interest in its health
effects, the toxic sequelae of exposure
have not been adequately described using
modern techniques of neurobehavioral
toxicology, nor have the mechanisms of
action been adequately elucidated.
Publication Types:
Review
PMID: 7038525 [PubMed -
indexed for MEDLINE]
Carbon disulfide and
the central nervous system: a 15-year
neurobehavioral surveillance of an
exposed population.
Environ Res. 1993
Nov;63(2):252-63
Cassitto MG,
Camerino D, Imbriani M, Contardi T,
Masera L, Gilioli R.
Institute of
Occupational Health, University of Milan,
Italy.
Carbon
disulfide-induced neurobehavioral effects
are well known and do not need further
evidence. Carbon disulfide vasculopathy
and the syndromic complex resulting in
depression, loss of memory and
concentration, and behavior disturbances
have been widely demonstrated. Less known
is the evolution of the symptomatology
when the environmental conditions are
consistently improved, that is, the
reversibility or the progression of the
dysfunctions observed. This paper reports
on a neurobehavioral follow-up in a
viscose rayon factory carried out, in
intervals, from 1974 to 1990. Several
successive improvements were implemented
in the plant through the years, until
finally, the most radical changes were
made at the end of the Seventies and
these resulted in exposure levels far
below the current Threshold Limit Values.
A total of 493 subjects were examined and
some of them were reexamined up to six
times. The last examination was completed
in September, 1990. In this paper,
studies by our group over the 15 years of
monitoring are discussed. The results
show that the general mental state, as
measured by neurobehavioral methods,
reflects past and current exposure. This
point was explored by dividing the
subjects into six groups on the basis of
their length of exposure and year of
examination and by comparing their
performances. The results show that even
exposure to levels of carbon disulfide
not exceeding 8 mg/m3 may induce
absentmindedness and difficulties in
perceptive abilities.
PMID: 8243419 [PubMed -
indexed for MEDLINE]
|
Other studies indicate that
negative effects are increased when women of
child-bearing age who are taking oral
contraceptives are exposed to carbon disulfide.
The researchers state, oral contraceptive
users are at increased risk of experiencing
adverse psychological disorders, including
irritability and depression, when exposed to
elevated levels of carbon disulfide. The
study concludes: These effects are thought
to occur at exposure levels below those normally
associated with adverse effects.
| Does use of oral
contraceptives enhance the toxicity of
carbon disulfide through interactions
with pyridoxine and tryptophan
metabolism? Med
Hypotheses. 1980 Jan;6(1):21-33
Calabrese EJ.
It is proposed that
oral contraceptive (OC) users are at
increased risk to experiencing adverse
psychological disorders (e.g.
irritability, depression) from exposures
to elevated levels of carbon disulfide
(CS2). This theory is based on studies
indicating that both OCs and CS2 induce
either a vitamin B6 deficiency and/or
enhance its requirement. Since
disruptions of B6 metabolism are thought
to explain, at least in part, the adverse
psychological effects of OCs and CS2, it
is speculated that joint exposure to
these substances may result in an
exaggerated disruption of B6 metabolism
with the development of CS2 induced
adverse psychological effects occurring
at exposure levels below those normally
associated with adverse effects.
PIP: This paper argues,
hypothetically, that oral contraceptive
(OC) users are at increased risk of
experiencing adverse psychological
disorders, including irritablitity and
depression, when exposed to elevated
levels of carbon disulfide. The theory is
based on studies that indicated that both
OCs and carbon disulfide are capable of
inducing either a vitamin B6 deficiency
or an enhancement of the requirement for
the vitamin. B6 metabolism alterations
are thought to be associated with
psychological effects; therefore, joint
exposure to OCs and carbon disulfide
would probably result in an exaggerated
disruption of that vitamin's metabolism
leading to carbon disulfide-induced
adverse psychological effects. These
effects are thought to occur at exposure
levls below those normally associated
with adverse effects.
PMID: 7382884 [PubMed -
indexed for MEDLINE]
|
Carcinogens
Acrylonitrile, methylene chloride, and dioxin
are three cancer-causing compounds emitted by the
IP-Riegelwood mill. Acrylonitrile, also known as
vinyl cyanide, is reasonably
anticipated to cause cancer in humans
(ATSDR, http://www.atsdr.cdc.gov/tfacts125.html).
Methylene chloride, according to the EPA, is a
probable cancer-causing toxin (ATSDR,
http://www.atsdr.cdc.gov/tfacts14.html). Dioxins
and furans are known to cause cancer in humans. A
study of paper mill workers found elevated levels
of stomach cancer and leukemia which were related
to their exposure to pollutants on the job. (Galson, S. K., Hazard Evaluation and
Technical Assistance Report: Boise Cascade,
published by National Institute of Occupational
Safety and Health, 1990.)
In 2003 an analysis of the US EPAs
Dioxin Reassessment found that there is no
evidence of a safe threshold for exposure to
dioxin. The report states, We have
reexamined the threshold analysis and found that
the data have been incorrectly weighted by cohort
size. In our reanalysis, without the incorrect
weighting, the threshold effect disappears.
In other words, there is no safe level of dioxin.
The use of chlorine dioxide in the bleaching
process inevitably creates dioxin and should be
phased out as soon as possible and replaced with
safer processes. The abstract of the researched
paper published in Environmental Health
Perspectives is reproduced below:
| No Evidence of
Dioxin Cancer Threshold Environmental
Health Perspectives Volume
111, Number 9 , July 2003
David Mackie, Junfeng
Liu, Yeong-Shang Loh, and Valerie Thomas
http://ehpnet1.niehs.nih.gov/docs/2003/5730/abstract.html
Abstract
The U.S. Environmental
Protection Agency (EPA) has developed an
estimate of the human cancer risk from
dioxin, using the standard low-dose
linear extrapolation approach. This
estimate has been controversial because
of concern that it may overestimate the
cancer risk. An alternative approach has
been published and was presented to the
U.S. EPA Science Advisory Board's Dioxin
Review Panel in November 2000. That
approach suggests that dioxin is a
threshold carcinogen and that the
threshold is an order of magnitude above
the exposure levels of the general
population. We have reexamined the
threshold analysis and found that the
data have been incorrectly weighted by
cohort size. In our reanalysis, without
the incorrect weighting, the threshold
effect disappears.
Environ Health
Perspect 111:1145-1147 (2003).
doi:10.1289/ehp.5730
available via http://dx.doi.org/
|
EPA and the State of North
Carolina must do more to reduce toxic air and
water emissions from kraft paper mills. The costs
of medical treatment, hospitalization, and lost
work days which are borne by the workers and
their families and neighbors who live near the
mill are not factored into International
Papers bottom line. These costs are
externalized. The resultant human misery cannot
be calculated in terms of dollars alone.
Specific Comments
Recovery Boiler No. 5 Upgrade Project
On June 6, 2003 IP submitted an application
which requested permission to modify its permit
to allow increased burning of black liquor solids
(BLS) in Recovery Boiler No. 5 from 115 TPH to
140 TPH, an increase of 21%. The increase was to
be offset by the closure of three other emission
sources: Recovery Boiler No. 3, Smelt Tank No. 3
and Power Boiler No. 1. The change qualifies as a
major modification and requires new source review
(NSR) because it has the potential to increase
emissions of nitrogen oxides and carbon monoxide
in excess of PSD Significant Emission Rates.
However, no Title V permit application update was
submitted. Further, both draft Permit No. 3138R20
(Case-by-case MACT under CVAA 112j for which an
application was received by DAQ on August 6,
2003) and draft Permit No. 3138T20 (Title V
permit which went to notice October 10, 2003)
still list all three sources and seek permitting
for continued operation for recovery boiler 3 (ID
No. RB3), smelt tank 3 (ID No. ST3), and power
boiler 1 (ID No. PB1). The draft Title V permit
must be revised to eliminate the three sources
proposed for closure by International Paper in
its June 6th request.
Federal Regulations
NSPS standards for fossil-fuel fired steam
generators, ICI steam generating units, and kraft
pulp mills (40CFR60 Subparts D, Db, and BB) were
deemed by IP to be met without new pollution
controls. As we have stated above, we object to
the shifting of costs from IP to local residents
and plant personnel. Nowhere in their documents
submitted to NCDAQ is this externalization
addressed by International Paper.
IP would have had to meet the NESHAP standards
for kraft mills (40CFR63 Subpart MM) for chemical
recovery combustion under MACT II of the
cluster rule published in January
2001. Under this standard, the emissions of PM
would be limited to 0.10 g/dscm at 8% oxygen,
0.15 g/dscm at 10% oxygen, or 0.1 kg/mg BLS
fired. IP would have had to comply with this MACT
by March 2004, but NC DENR has granted IP a
one-year compliance deadline extension for MACT
II. Further, NC DENR has granted a separate
extension of six months for IP to meet the pulp
and paper MACT I, Phase 2 rule. On what basis can
NC DAQ or EPA justify this delay? The federal
Clean Air Act provides ample means to allow a
duly diligent plant operator to comply with all
air quality standards. This unjustified extension
should be cancelled.
IP utilized a top-down approach in
its determination of best available control
technology (BACT) for its boiler recovery upgrade
project. According to IP, BACT, is based on
the maximum degree of emissions limitation
achievable
but equal emphasis is
placed on the words maximum
and achievable. The
applicants explanation of what BACT means
defies accepted definitions. For example, the
state of California defines BACT without the
qualifiers posed by IP:
| Definition of Best
Available Control Technology 40405. (a) As used in this
chapter, "best available control
technology" means an emission
limitation that will achieve the lowest
achievable emission rate for the source
to which it is applied. H&S 40405, California
Air Pollution Control Laws, 2003
|
For control of NOx
and carbon monoxide, IP dismisses as technically
infeasible selective catalytic
reduction/selective non-catalytic reduction and
catalytic oxidation, respectively, settling on
proper design and good combustion control. One
performance test is proposed, but no continuous
monitoring, reporting or recordkeeping is
outlined. Without periodic monitoring, it is
impossible to determine if a facility is
violating air quality standards or emission
limits for best available control technology.
North Carolina Regulations
NC regulations are incorporated in the State
Implementation Plan approved by EPA. In its
application for the Recovery Boiler Upgrade
Project, IP asserts that particulates from
recovery boiler 5 would remain within previous
permit limits required under 15A NCAC 2D .0508 (3
lbs. per equivalent ton of air dried pulp). But
no actual testing is proposed to support this
claim. In a similar way, SO2, NOx,
and toxic air pollutant emissions limits are set
aside. For TAPs, net emissions changes were
calculated based on emission factors and/or
engineering judgments instead of
site-specific measurements and test data.
Typically, North Carolinas TAP program uses
computer estimates of pollution levels when
permit applications are submitted before a new
source is constructed. However, the IP Riegelwood
plant has been in operation since 1951. Computer
modeling is no substitute for real world testing.
Pulp and Paper Mill NESHAP
Under the Clean Air Act Section 112, the EPA
must regulate emissions of HAPs to protect public
health. Emission standards for new or existing
sources of hazardous air pollutants must result
in the maximum degree of reduction in
emissions of the hazardous air pollutants subject
to this section (including a prohibition on such
emissions where achievable)... [CAA 112
(d)(2)] To certify compliance under Section 112j
of the Clean Air Act, IP must certify compliance
with the terms and conditions of the MACT
including the format and frequency of the
certification. Each Title V permit and Notice of
MACT Approval must contain sufficient testing,
monitoring, reporting, and recordkeeping
requirements to assure compliance with the MACT
emission limitation.
Under the pulp and paper NESHAP Subpart S,
paper mill operators must conduct an initial
performance test to demonstrate compliance and
establish performance parameters. Thereafter,
continuous monitoring of air pollution control
devices or operating parameters or CEM must be
done. Exceeding a monitoring limit must be
reported and constitutes a violation of NAAQS.
Yet no testing is required by the draft Title V
permit. Throughout the draft the DAQ uses the
following language: If emissions testing is
required, the testing shall be performed in
accordance with
(NC or federal
regulations)
. If the results of this test
are above the limit given above, the Permittee
shall be deemed in noncompliance with
(regulation)
. In order to
determine if a given facility is complying with
the law, adequate periodic monitoring,
recordkeeping, and reporting is required to be
stipulated in the Title V permit. In addition to
production limits and other measures, the
operating permit must require the facility to
monitor emissions. This is the only means
available to assure the public that the facility
is complying with its permit.
Paper mill operators must comply with Subpart
S by April 16, 2001 except for HVLC systems which
must comply by April 17, 2006. Operators at mills
which implement a Voluntary Advanced Technology
Incentives Program for bleaching systems must
comply by April 15, 2004. To qualify for VATIP,
the operator must meet three conditions: 1) no
increase in rates of chlorine use in bleaching
systems, 2) submit control strategy report by
April 1999, and 3) submit updated control
strategy status reports every two years until in
compliance. We can find no such restrictions in
the draft Title V permit for the requirement to
limit chlorine use.
A Title V permit may not sanction
non-compliance. However, according to DAQ
records, the plant is not fully in compliance
with all state and federal regulations. The DAQ
Permit Review for the R20 permit states:
| VIII. Statement of
Compliance Based
on the latest inspection of August 25,
2003, by Lynette Bryan of the Wilmington
Regional
Office, the facility
was found to be in compliance with all
applicable air quality regulations.
|
However, the October 2003 Title
V Permit Review states that International
Paper-Riegelwood Mill does not meet two NESHAP
requirements: 1) for pulp & paper mills and
2) for chemical recovery combustion sources:
| The DAQ has reviewed
the compliance status of this facility.
During the last inspection performed in
August 2003, the facility appeared to be
operating in compliance with all permit
conditions. The applicant has certified
compliance with all applicable
requirements. The facility is subject to
two NESHAP requirements: Subpart S
(National Emission Standards for
Hazardous Air Pollutants from the Pulp
and Paper) and Subpart MM (National
Emission Standards for Hazardous Air
Pollutants for Chemical Recovery
Combustion Sources at Kraft, Soda,
Sulfite, and Stand-Alone Semichemical
Pulp Mills). The applicant is not
fully in compliance with either
requirement but has indicated that
the units will meet the requirements by
the specified compliance dates. The
applicant has also certified that the
facility will be in compliance with any
applicable requirements taking effect
during the term of the permit and will
meet such requirements on a timely basis.
(TV Permit Review, Section IV. Statement
of Compliance) [emphasis
added] |
The ongoing Title V process
contemporaneous with the 2Q .0300 permit process
may allow important issues to be overlooked or
poorly addressed. We believe that a public
hearing and further public comments would be in
the best interest of the people in eastern North
Carolina.
Respectfully submitted,
Louis Zeller, Clean Air Campaign Coordinator
Cc:
Keith Overcash
Laura Butler
Gary L.. Saunders
Mark Cuilla
>>download a .pdf version of
comments
IP-Riegelwood
BE SAFE NC Campaign
|