ILLINOIS POLLUTION CONTROL BOARD
August 5, 1999
LAWRENCE C. SWEDA,
Complainant,
v.
OUTBOARD MARINE CORPORATION
and the CITY OF WAUKEGAN,
Respondents.
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PCB 99-38
(Enforcement - Noise, Citizens)
LAWRENCE C. SWEDA APPEARED
PRO SE
;
THOMAS LUPO AND SUSANNAH A. SMETANA, OF SEYFARTH, SHAW, FAIRWEATHER & GERALDSON,
APPEARED ON BEHALF OF RESPONDENT OUTBOARD MARINE CORPORATION; and
HEIDI J. AAVANG, OF DIVER, GRACH, QUADE & MASSINI, APPEARED ON BEHALF OF RESPONDENT THE
CITY OF WAUKEGAN.
OPINION AND ORDER OF THE BOARD (by M. McFawn):
This case is before the Illinois Pollution Control Board on a complaint filed on August
21, 1998, by
complainant Lawrence C. Sweda against two respondents, Outboard Marine Corporation (OMC) and the City of
Waukegan (City). The complaint alleges noise pollution in violation of Sections 23 and 24 of the Illinois
Environmental Protection Act (Act) (415 ILCS 5/23, 24 (1998)) and two of the Board’s noise regulations, 35 Ill. Adm.
Code 900.102 and 901.104. The complaint is based on noise from propane cannons used by respondents to frighten
away seagulls that would otherwise nest at respondents’ facilities near Waukegan harbor.
The respondents each filed motions to dismiss this matter as fr
ivolous. In an order adopted on September
17, 1998, the Board dismissed the alleged violations of Section 23 of the Act but concluded that the other claims in
the complaint were not frivolous, and directed the parties to proceed to hearing. A hearing was held before Board
Hearing Officer John Knittle on April 19 and 20, 1999, in Waukegan, Lake County, Illinois. Respondents filed
posthearing briefs on May 28, 1999. Complainant did not file a posthearing brief or reply brief.
After reviewing the record, the Board concludes that respondents’ actions do not constitute a violation of
35 Ill. Adm. Code 900.102. The Board further finds the evidence insufficient to establish a violation of 35 Ill. Adm.
Code 901.104. Having found no violation of Section 900.102 or Section 901.104, the Board finds no violation of
Section 24 of the Act. Section 24 prohibits any person from emitting noise “beyond the boundaries of his property
. . . so as to violate any regulation or standard adopted by the Board .” (Emphasis added.)
MOTION TO EXCLUDE TESTIMONY
A procedural issue requires resolution before we turn to the merits of this case. On May 28, 1999, OMC
filed a motion with the Board seeking to exclude the opinion testimony of Greg
Zak. Zak, noise advisor for the
Illinois Environmental Protection Agency, was called by
Sweda and testified on his behalf. The basis of OMC’s
motion was that Sweda failed to disclose the opinions to which
Zak would testify by the discovery deadlines set by
the hearing officer, and consequently OMC was unable to prepare its defense. For the reasons that follow, the
Board grants OMC’s motion.
2
On December 22, 1998, the hearing officer issued an order setting hearing dates and a discovery schedule.
The hearing was originally scheduled for April 7 and 8, 1999. To accommodate this hearing date, the order
required all written discovery to be filed and served by January 11, 1999.
Responses were to be filed by February
11, 1999, with all discovery completed by March 1, 1999.
On December 24, 1998, OMC propounded its first set of interrogatories to Sweda. OMC’s Interrogatory 3
provided:
Identify each and every expert, including noise experts, with whom you have
communicated or consulted or whom you have retained. With regards to each
expert, state the following:
* * *
d.
Describe in detail the substance of all facts, assumptions, opinions, and
conclusions about which the expert is expected to testify; identify each
document (i.e., textbooks, treatises, articles) which support the
substance of the facts or opinions about which the expert witness is
expected to testify; identify the information and documents that were
provided to the expert for use in this matter; identify each document
the expert witness has prepared and which summarizes the facts or
opinions about which the expert is expected to testify and provide all
reports of the expert[.]
Sweda responded to OMC’s interrogatories on February 4, 1999, identifying
Zak as an expert with whom
he had communicated or consulted. For his specific response to item 3(d),
Sweda put “Do not know.”
Shortly thereafter, the respondents jointly moved to extend the discovery schedule for an additional 30
days, based on asserted deficiencies in Sweda’s discovery responses, including the failure to describe the nature of
Zak’s opinion testimony. “Motion to Extend Hearing Officer’s Discovery Schedule and Hearing Date” at 3.
Respondents argued that they needed this information to determine whether to depose Zak and, if so, regarding
what issues.
Id.
Sweda opposed the motion to extend. On March 9, 1999, the hearing officer issued an order
extending the deadline for completing discovery to March 26, 1999, and rescheduling the hearing to the week of
April 19, 1999. (These extensions were shorter than requested by respondents.) OMC’s posthearing motion
indicates that Zak was deposed on March 25, 1999. The deposition transcript is not part of the record.
By an order issued March 30, 1999, the hearing officer set additional deadlines for exchanging witness lists
and expert opinions (April 9, 1999) and filing motions
in limine
(April 13, 1999). Sweda filed “Complainant’s
Witness List and Expert Opinions” on April 7, 1999, but still did not disclose any specific opinions of
Zak. He
stated rather that Mr. Zak would testify as to “his knowledge of [PCB] 99-38 as Noise Advisor with [the Illinois
Environmental Protection Agency], including testing presented during the April 19 and 20, 1999 Hearing.” In a
subsequent motion
in limine
, OMC moved to exclude undisclosed opinion testimony of
Zak.
At hearing, after argument by the parties, the hearing officer denied the motion
in limine
, but allowed the
respondents to object to any specific testimony of Zak. Tr. at 12. The hearing officer also pointed out to
respondents’ counsel that they could make their objection to the Board, as OMC has now done. Tr. at 17. Sweda did
not file a response.
OMC’s interrogatories and the hearing officer’s March 30, 1999, order placed Mr. Sweda under an
obligation to disclose the opinions of any expert witnesses by at the very latest April 9, 1999. It appears that
Sweda
was unable to disclose Zak’s opinions because Zak had not yet formed those opinions at the time of the disclosure
deadlines. According to OMC, at his deposition
Zak testified that he had formed no opinions. “Motion of
Respondent Outboard Marine Corporation to Exclude Opinion Testimony of Greg Zak” at 2. We note that
Sweda
3
has argued throughout these proceedings, with some success, for a fast track to hearing. See,
e.g.
, Sweda’s
“Pleading Regarding the Discovery Schedule,” filed on December 10, 1998. While such a fast track results in a
quicker resolution of the case, it also imposes a burden on the complainant, to prepare his own case more quickly.
OMC was entitled to know the substance of any opinion testimony to be offered by
Zak. By failing to
disclose this information as required by the hearing officer’s orders,
Sweda deprived OMC of the opportunity to
fully prepare its case. Without knowing what
Zak would say, OMC could not ensure that any necessary rebuttal
witnesses would be present, or that any necessary rebuttal documents would be available. In this case, since no
opinions were disclosed in discovery, no opinions should have been presented at hearing. Accordingly, the Board
grants OMC’s posthearing motion to exclude opinion testimony of
Zak.
STATUTES AND REGULATIONS
OMC and the City are alleged to have violated Section 24 of the Act (415 ILCS 5/24 (1998)) and Sections
900.102 and 901.104 of the Board’s noise regulations (35 Ill. Adm. Code 900.102 and 901.104). (As noted above,
alleged violations of Section 23 of the Act were dismissed on respondents’ motions.) Section 24 provides:
No person shall emit beyond the boundaries of his property any noise that
unreasonably interferes with the enjoyment of life or with any lawful business
or activity, so as to violate any regulation or standard adopted by the Board
under this Act.
Section 900.102 provides:
No person shall cause or allow the emission of sound beyond the boundaries of
his property . . . so as to cause noise pollution in Illinois, or so as to violate any
provision of this Chapter.
“Noise pollution” is defined in 35 Ill. Adm. Code 900.101 as “the emission of sound that unreasonably interferes
with the enjoyment of life or with any lawful business or activity.”
Section 901.104 establishes the following specific numerical noise standard:
Except as elsewhere in this Part provided, no person shall cause or allow the
emission of impulsive sound from any property-line-noise-source located on
any Class A, B or C land to any receiving Class A or B land which exceeds the
allowable A-weighted sound levels specified in the following table, when
measured at any point within such receiving Class A or B land, provided,
however, that no measurement of sound levels shall be made less than 25 feet
from such property-line-noise-source.
Classification of
Allowable A-weighted Sound Levels
Land on which
in Decibels of Impulsive Sound Emitted
Property-Line-
to Receiving Class A or B Land
Noise-Source
Class A Land
is Located
Class B Land
Daytime
Nighttime
Class A Land
50
50
45
Class B Land
57
50
45
Class C Land
61
56
46
4
FACTS
At hearing, two witnesses, John Neff and Greg Zak, testified on Sweda’s behalf. Sweda also presented his
own testimony. OMC presented ten witnesses; the City presented four.
Respondents’ Facilities
Outboard Marine Corporation was created in approximately 1936 when two existing companies, Johnson
Motors and Everett Motors, merged and combined operations. Tr. at 136. Prior to consolidation, Johnson Motors
had operated on a portion of the Waukegan lakefront since approximately 1925.
Id.
OMC’s operations currently are located in an industrial campus north and east of Waukegan harbor. The
OMC campus includes a vacant piece of property which was the former site of a
coking plant. Tr. at 146-47. The
site, approximately 30 acres of open field, is contaminated. Tr. at 373-74. The area is fenced, with access to the site
controlled by the United States Environmental Protection Agency (USEPA). Tr. at 180, 374. OMC’s use of the
property is limited to activities permitted by USEPA. Tr. at 180. The area is generally referred to as either the
“coke plant site” or the “ Superfund site.”
Several OMC buildings are located close to the coke plant site. East of the site is OMC’s Information
Technology building and its parking lot, and the OMC Environmental Health and Safety building. Tr. at 141; OMC
Exh. 2. South of the site is OMC Plant 1, which is separated from the site by a parking area.
Id
. The parking area is
used for transportation of goods, employee access, parking and training purposes. Tr. at 141. Approximately 600 to
700 OMC employees work in and around Plant 1. Tr. at 140-141.
To the south of OMC’s campus is the City of Waukegan’s water treatment plant. Tr. at 145; OMC Exh. 1.
The water treatment plant is located on Waukegan harbor, less than half a mile from the coke plant site. Tr. at 540.
Among the facilities at the plant are sedimentation basins, which are raised enclosures with grass on top. Tr. at
542. The sedimentation basins run parallel to the south wall of OMC’s Plant 1 building, separated from it by a
parking lot. Tr. at 543.
Respondents’ Use of Propane Cannons
In 1995, OMC began to experience problems related to the presence of a breeding colony of seagulls
located on the coke plant site. In the spring of 1998, at the suggestion of a bird control expert, OMC implemented a
program involving use of noisemaking propane cannons to drive the gulls off the site. During the nesting season,
the cannons were fired from approximately 7:00 or 8:00 a.m. until approximately 6:00 p.m., sometimes as late as
8:00 p.m. Tr. at 166. The program continued in 1999, beginning in early March. Tr. at 70.
The City began having its own problems with gulls nesting on the sedimentation basins in 1998. The City
consulted with OMC regarding its bird control program, and ultimately borrowed a propane cannon from OMC
for use on the sedimentation basin. Tr. at 545. The City fired the cannon from approximately 7:30 or 8:00 a.m. until
approximately 4:30 or 5:00 p.m. from mid-April to late May or early June. Tr. at 548. The City implemented an
alternative program in 1999, and is no longer using the cannon. Tr. at 551.
Cannon Noise Issues
Sweda claims that noise generated by respondents’ use of cannons has unreasonably interfered with the
use and enjoyment of his property and endangered his physical and emotional health and well-being. Beginning
in mid-March of 1998, Sweda was aware of the cannons firing, which he described as “comparable to a 4th of July
fireworks display,” “blasts,” or “loud booming noises.” Tr. at 31-32.
Sweda has lived at 923 N. County St. in
Waukegan, Illinois, for twenty-five years. Tr. at 30. He lives with his wife and two dogs.
Id
. His home is
approximately a mile northwest of the respondents’ sites. OMC Exh. 2. Between the Sweda home and the
respondents’ facilities are Waukegan Harbor, a railroad line, an expressway and Sheridan Road.
Id.
5
In addition to presenting his own testimony, at hearing
Sweda called John Neff as a witness. Neff has
lived for 30 years at 320 Stewart in Waukegan with his wife. Tr. at 97, 104. Neff’s house is several blocks from
Sweda’s house, and around two miles from the OMC site. Tr. at 97-98. He and his wife began noticing the cannon
noise in late March or April, 1998, when they began working outside in their gardens. Tr. at 104-05. He
characterized the cannon noise as sounding like a gunshot.
Id.
Adverse Impacts of Cannon Noise
Effects on Mr. Sweda. Sweda found the noise from the cannons very intrusive. He testified that the noise
prevented him from engaging in the following activities on and around his property: conversing, sitting outside,
reading, listening to music, talking on the phone, cooking outside, entertaining, picking up litter, playing with
dogs, playing with the neighbor’s child, starting the grill, gardening, thinking, resting, sleeping, napping, bird and
squirrel watching, cleaning his car, taking groceries out of the cars, getting the mail, taking the garbage out,
putting water out for the birds and squirrels, writing letters, making notes on wildlife behavior, cleaning the
garage, putting storms and screens in, having a cup of coffee or tea, cleaning up after the dogs, getting the
newspaper, picking up litter, moving lawn chairs, putting bird feed up, taking compost material out to the yard,
putting laundry on the line to dry, and taking laundry down, taking the dog out or in, working the dogs, watching
for sunrise or sunset, and watching and listening to a storm come and go. Tr. at 36; Sweda Exh. 2. Mr. Sweda
considers these activities necessary for well-balanced physical and emotional health. Sweda Exh. 2. After the
cannons stopped firing for the year, it took Mr. Sweda until late July to be able to go outside and relax, without
anticipating the disruption of cannon fire. Tr. at 42-43. The cannons began again on March 4, 1999, and varied in
volume from extremely loud (as last year) to less loud, as on sporadic days when it appeared respondents were
trying to mute the noise with barriers. Tr. at 70.
Effects on Mr. Neff. Neff considers the sound “a real annoyance.” Tr. at 117. He was most upset by the
repetitive nature of the sound, and its similarity to gunfire. Tr. at 105-06.
Neff is a high school football coach, and
testified that the noise is especially troublesome to him because he has lost several players to gunfire. Tr. at 106.
Neff testified that the noise disrupted the tranquility of his yard, and sometimes he and his wife had difficulty
carrying on conversations across their yard due to the noise. Tr. at 110. He admitted, however, that he and his wife
ate outside some days last spring and summer, and they continued to garden outside. Tr. at 116.
Comparison to Other Noise Sources. Sweda testified that the cannons were louder than a car starting in
the driveway, louder than a plane flying overhead, louder than trains (sometimes). Tr. at 81. (There is a train yard
several blocks from Sweda’s house. Tr. at 91.) Pounding and hammering noises from construction were
occasionally louder than the cannons, but they were not as upsetting to
Sweda because they were “normal” and
“acceptable” noises. Tr. at 83. Sweda explained the difference between “normal, acceptable” noises and other
noise:
Normal acceptable noises are that I’ve lived there for 25 odd years and it’s just
simply through observation of what acceptable noises are or what regular
kinds of noises are in terms of expectations of you know that you’re not
moving into a drop-forge area or you know you’re not moving into an O’Hare
Airport. You have reasonable assurances that in your own mind as—making a
decision as to a place of residence is one choice. And that’s what I’m saying in
terms of I chose the area. We chose the area because of its ambiance as well as
what the house and property was. Tr. at 91-92.
Like Sweda, Neff placed significance on the character of the noise, finding it incompatible with his
expectations:
I expect to hear certain noises when I go downtown. I expect to hear certain
noises in my front yard. You know, I expect to hear certain noises on the 4th of
July, but to go in your back yard—I think all of us understands [sic] what a
6
backyard is. And you go in your backyard, first of all, when you’re by yourself
and you’re raking and doing those things you want to do and you want some
quiet time, you want some privacy, you want some relaxation, this is totally
disrupted by that number 1. Number 2, to associate it as I do in my particular
experience with a community full of violence and gun problems, we lose a
number of teenagers every year to that. That’s the second factor. And then the
third thing, when my wife and myself are out in the yard, of course she’s on
one side of the yard. I’m in another part of the yard and there are times when
we try to carry on conversations. Sometimes you can’t hear each other, but
more than that, the serenity, the violation of privacy that takes place and can
you accept it? Maybe if you’re perfectly healthy and everything is right, you
can roll with it, but you shouldn’t have to.
* * *
There are other noises but, you know, there are other noises, but first of all, you
expect certain kinds of noises and they don’t take place all the time. And
they’re not connected with violence and they’re not—you know, you go out
[sic] your front yard, you expect to hear certain things. You go down, you
expect hear certain things. I don’t expect to hear something like this constantly
when I go in my backyard. Tr. at 109-111.
Respondents’ Evidence
In response to Sweda’s claims, OMC and the City introduced evidence regarding the problems which
prompted their attempts to control the gulls and the process that led to their use of the propane cannons.
Respondents also offered the testimony of witnesses who live or work in and around the area, concerning the
effects of the cannons on their lives. Finally, OMC offered the testimony of a sound expert who measured sound
levels near Sweda’s house.
OMC’s Program
Development of Gull Problems at OMC. The coke plant site was a nesting area for seagulls. Beginning in
1995, the number of birds on the site increased dramatically, and as the gull reproductive season wore on, OMC
began to get complaints from employees. Tr. at 149. Gull chicks were finding their way onto the roadways and
parking lots. Tr. at 150, 292. Nesting gulls were damaging roofs. Tr. at 151.
The number of gulls further increased in 1996. Tr. at 151. In spite of the use of gull distress noisemakers,
the problems continued. Tr. at 151, 153. The nature of the complaints now involved gulls bombarding cars with
feces and adult gulls, protective of chicks, “dive bombing” humans. Tr. at 153. Other complaints raised the health
hazard issue due to the amount of bird feces. Tr. at 153-54.
OMC began looking into different ways to control the gulls. Tr. at 377. In 1997, OMC put wire grids over
portions of the coke plant site. Tr. at 378. This moved the gulls off those areas, but they just moved east to another
part of the site. Tr. at 379. OMC contacted several agencies, including the U.S. Department of Agriculture, Animal
Damage Control, and the U.S. Fish and Wildlife Service. Animal Damage Control visited the site in the summer of
1997, and recommended applying to Fish & Wildlife for a permit to take (shoot) gulls, which OMC did. Tr. at 381.
In March of 1998, Fish & Wildlife issued a permit allowing OMC to take up to 100 ring-billed gulls, up to 20
herring gulls, and to destroy 500 nests and eggs. Tr. at 383-84.
Dr. Southern’s Survey and Recommendations. Also in 1997, OMC hired a bird control consultant, Dr.
William E. Southern. Tr. at 154-55. Southern is an animal behavior scientist specializing in ornithology, the study
7
of birds. Tr. at 191-92. He was a professor at Northern Illinois University from 1959 to 1990; since 1990 he has
worked as an environmental consultant, specializing in bird control programs. Tr. at 192-94.
In early June 1997, Southern made a site visit and found a “well-established” colony of around 2,500 pairs
of gulls nesting in the area known as the Superfund site. Tr. at 196-97. He prepared a report for OMC in which he
evaluated the problem and recommended possible solutions. OMC Exh. 3. He described the problem and the need
to relocate the gulls as follows:
Gulls nesting at this corporate location in
sizeable numbers are a definite
nuisance because they defecate on vehicles in parking lots adjacent to the
colony, chicks wander into traffic and are killed thereby causing public concern,
and the presence of nesting birds interrupts the required monitoring of wells
within the Superfund site on which they are nesting. Long-term nesting of
gulls in this location also raises concerns about employees possibly being
exposed to the fungus that causes histoplasmosis in humans. The spores of this
organism have been documented to develop in organically rich soils in some
gull colonies when soil conditions are optimal. A gull colony in close
proximity to a corporate facility such as this where hundreds of people work is
undesirable.
The presence of the gull colony at this location also complicates the proposed
remedial action for this Superfund site. Work on the site is expected during the
next year or so and continued gull use of the area could compromise work
schedules. Whatever work is done under Superfund guidelines undoubtedly
would alter the landscape thereby necessitating the gulls to move. The
question, therefore, is not if the gulls should be moved but when and how.
OMC Exh. 3 at 2 (emphasis in original).
Southern testified that, in general, gull colonies are not compatible with areas of human activity. Tr. at
197. Although he pointed out that gulls have educational value and in a proper location a gull colony would be an
asset, next to an industrial facility like OMC, he considered it a detriment.
Id
. He identified several factors
contributing to this conclusion and identified a number of potential adverse effects a gull colony can have. Many
of the adverse effects he mentioned were in fact experienced by OMC and other businesses near the gull colony.
Problems Associated with Gull Colonies.
The adverse effects a gull colony can have on nearby human
establishments, according to Southern, are numerous. Potential health risks associated with gull colonies stem
from the fact that gull fecal matter, highly concentrated around breeding colonies, carries high levels of
coliform
bacteria. Tr. at 198. Gulls also often carry salmonella.
Id
. There is also a health risk from histoplasmosis, which is
caused by a fungus that thrives in areas where there is a lot of fecal matter. Tr. at 198-99. The condition can cause
serious problems, and in some cases can be lethal. Tr. at 199. Southern additionally expressed concern over
potential contamination of water at the City’s water treatment plant. Tr. at 225.
Another problem is odor, caused by both accumulating fecal matter and decaying bodies of dead birds.
Tr. at 201. The odor intensifies on wet days and will carry on a breeze. Tr. at 201-02. Fecal matter can become very
slippery when wet, creating a hazard in parking lots. Tr. at 202. Dr. Southern also testified that gull chicks can
create problems. By wandering, they create a distraction in the parking lot. Tr. at 202-03. Many are hit by cars. Tr.
at 150, 292. Furthermore, adult gulls protecting the chicks create problems by dive bombing humans. Tr. at 200.
Even wearing head protection, a person can still get hit very hard. Tr. at 201.
Gulls can also cause property damage. On flat roofs they peck at the tar, pecking holes in the roofs. Tr. at
203. They also carry nesting material up onto roofs, which clogs up drain pipes and can cause associated water
damage. Tr. at 203-04. Thomas Elsen, manager of facilities operations and security at OMC, Tr. at 258, testified that
the gulls caused extensive damage to the roof of the Plant 1 building by pecking holes ranging from the diameter
8
of a beak up to two feet in diameter and six or seven inches deep; these holes allow water to penetrate the roof
membrane and leak into the building. Tr. at 262. He also noted that feathers drawn into air conditioning intakes
necessitated changing filters more often. Tr. at 265. Also, at the Information Technology building, OMC had to
purchase deodorant blocks to mask the odor coming into the building. Tr. at 265.
Other witnesses also testified regarding the problems experienced in fact around the coke plant site. John
Battisfore, who works in the Information Technology building at OMC, testified regarding the mess caused by bird
droppings on cars, stating that the prevalence of bird droppings required daily cleaning of his car, and that the bird
droppings had caused discoloration of the car’s paint. Tr. at 287-290.
Battisfore testified to being disturbed by the
presence of dead chicks in the parking lots, and that the birds dive bombed people, hitting their heads and clothing
with droppings. Tr. at 292. Gerald Larson, president of Larson Marine Services, Tr. at 422, also testified as to
problems from gull droppings, including the need to wash cars and boats. Tr. at 429-30.
Larson testified that gull
droppings made the docks around Larson Marine Services slippery when they were wet, necessitating washing of
the docks. Tr. at 430. (Larson Marine Services is located directly north of the coke plant site. Tr. at 423-24; OMC
Exh. 2.) Theresa Fisel, who works for OMC in a building near Plant 1, Tr. at 305, testified that the prevalence of gull
fecal matter and feathers in the area had aggravated her asthma. Tr. at 312-315.
Mark Pfister, an aquatic biologist with the Lake County Health Department in Waukegan, Tr. at 523-24,
testified that Waukegan South Beach was closed far more often due to fecal coliform bacteria in the water than
either of the other public beaches in the area. Tr. at 528-29. (Waukegan South Beach, including a boardwalk and a
parking area, is located to the east of the coke plant site and immediately across a road from OMC. Tr. at 142, 524;
OMC Exh. 1, 2.) Pfister believes the larger gull population near Waukegan South
Beach, and the corresponding
greater amount of fecal matter, was a factor behind the greater fecal coliform counts at the south beach. Tr. at 531.
Daniel Chamernik, in charge of overseeing the grounds at the beach, Tr. at 448-49, testified that during 1997 the
beach also had a problem with dead gulls and gull chicks “all over the place.” Tr. at 451-52. Mr.
Chamernik
testified that at one point beach personnel were picking up from 10 to 13 dead gulls a day. Tr. at 452. The beach
also had problems with gulls getting into picnic baskets and garbage cans. Tr. at 455.
Dr. Southern’s Recommendations.
Southern explained that a gull colony is established after gulls nest
on a property for a year or two. Tr. at 204-05. The attachment of gulls to an established colony is very strong. The
birds will tolerate extreme amounts of distraction or injury—almost anything short of death—before they will
leave a colony. Tr. at 205. The attachment to a site grows with each year of having nested there.
Id
. Gull colonies
grow from year to year; growth of 10 to 20 percent per year is not uncommon. Tr. at 206. The OMC site could
easily hold 20,000 birds or more. Tr. at 207. As the colony grows, the risk of contaminants reaching the public
beach via the gulls would increase also.
Id
.
The nesting season is approximately 11 or 12 weeks long; it takes that long for gulls to build a nest, lay
eggs, incubate the eggs and rear the young. If one prevents the gulls from actually starting the nesting process, it is
unlikely that any of them would continue to try to nest much after the early part of June. In fact, if the gulls do not
achieve a critical mass of birds on the ground, the colony may break up sooner than that. Tr. at 222-23.
Based on his visit to the site, Southern recommended a program emphasizing pyrotechnic noise-makers,
i.e.
, propane cannons supplemented by pistol-fired whistlers and “bird booms.” The pyrotechnics are the most
dependable way of moving gulls quickly. Tr. at 208-10. He figured that it would probably take around three years
to break the gulls’ nesting habit. Tr. at 209. Southern recommended a minimum of six propane cannons, supported
by hand-fired pyrotechnic devices. OMC Exh. 3 at 7.
Southern considered other methods of bird control, but, for various reasons, ruled them out.
He testified
that lethal control methods are not necessarily effective. Tr. at 214, 220. He also discussed use of more wires across
the site. In this case, however, due to the environmental contamination at the coke plant site, wires could not be
erected. Tr. at 238-39. In any event, barriers such as overhead wires become less effective over time due to the
birds’ attachment to the site: the gulls walk under the wires. Furthermore, even when wires are used, this solution
would normally be buttressed by use of pyrotechnics. Tr. at 218. Finally, Southern concluded that use of other
9
animals to control the bird population would not work at the OMC site. While dogs have been used at some sites
to chase birds off, Southern ruled out this method at the OMC site because it is too large, and it is contaminated.
Id.
Southern further testified that use of birds of prey is not considered an effective method of driving gulls off a
colony site: when the bird of prey leaves, the gulls return.
Id
.
Procedures Implemented by OMC and Results. Rather than the six cannons recommended by Southern,
OMC purchased four cannons. Three were set up, and one was held in reserve. Tr. at 165. The cannons and
pyrotechnics were effective: very few nests were built after the program began, and by the middle of June 1998,
the birds were no longer returning to the site. Tr. at 391-92. There were virtually no chicks in 1998. Tr. at 168.
OMC turned the cannons off in early June 1998 because the birds were not nesting on the site. Tr. at 392-93. As of
the date of Southern’s testimony (April 19, 1999), there were no gulls at the OMC site. Tr. at 227.
He opined,
however, that if OMC ceased its use of pyrotechnics that day, birds would start nesting again almost immediately.
Tr. at 224.
Other witnesses testified that since the cannon program was instituted the problems associated with the
gulls have lessened. Thomas Elsen testified that since the cannon program started damage to the buildings has
been minimal. Tr. at 268. Mark Pfister testified that in 1998, there were only seven beach closures at Waukegan
South. Tr. at 531-32. Pfister credits the relocation of the gulls with the reduction in bacteria. Tr. at 532. Daniel
Chamernik likewise testified that in 1998 the problems at the beach were not as bad. Tr. at 460.
City of Waukegan Program
Jeffrey Musinski, director of the water division for the City of Waukegan, testified regarding the
City’s
gull removal efforts. Tr. at 539-40. In the spring of 1998, Musinski noticed a significant increase in the number of
gulls nesting on the water treatment plant’s settling basin. The number of birds increased from approximately a
dozen pairs to over a hundred pairs in 1998. Tr. at 541-44. The water plant borrowed a propane cannon from OMC
and set it up on the basin. Tr. at 545. Almost overnight the gulls were gone. Tr. at 546.
The City considered other alternatives, but determined that they could not be implemented at the time.
Musinski testified that the City could not use wires because of the need for access to the area. Tr. at 547. He also
testified that repairs and improvements were necessary before dogs could be brought into the area, and that this
prevented the City from using the dogs during the 1998 nesting season. Tr. at 550. This year the City did put a dog
out on the fenced grounds, which has been 100% effective. Tr. at 551-52. The City is no longer using the cannon.
Tr. at 554.
Reactions of Other Waukegan Residents
OMC and the City, in rebuttal of Sweda’s claims, introduced a number of witnesses who lived or worked
around the OMC campus and/or Sweda’s house but were not bothered by the noise.
Daniel Hirsch lives at 527 N. Sheridan Rd. in Waukegan. Tr. at 399-400. He owns an engineering company,
Lakewise, Inc., and has his office in his home. He works from roughly 7:00 a.m. to around 6:00 p.m. Tr. at 401.
Hirsch’s house is approximately 900 yards from OMC’s facility, considerably closer than
Sweda’s house. Tr. at 403;
OMC Exh. 1. Hirsch first noticed the cannon noise from OMC’s gull removal operation in March of 1998. Tr. at 416.
He can hear the cannons on his deck and occasionally in his house. Tr. at 415. He described the noise as sounding
like small arms discharge, or a firecracker in the distance. Tr. at 416. He can converse outside in a normal tone
while the cannons are firing. Tr. at 416. The noise does not interfere with activities either outdoors or inside the
house, such as watching television, listening to the radio, or talking on the phone. Tr. at 417-18. If anything else is
making noise (
i.e.
, TV, radio, conversation) it drowns out the noise of the cannons. Tr. at 418. Hirsch found noise
from the gulls themselves, the railroad, the highway, and the civil defense siren “considerably louder and more
disruptive” than the cannons. Tr. at 419.
10
William Noff lives at 928 N. County St. in Waukegan; he has lived there for seven years. Tr. at 436. He
lives across the street from Sweda. Tr. at 438. He hears the cannons in his house and yard, and described the sound
as like the popping of a paper bag. Tr. at 443-44. Noff entertains, barbecues, and does yard work in his yard. Tr. at
442. The noise from the cannons has not interfered with any of Noff’s outdoor activities, or with talking on the
phone inside. Tr. at 444.
Similarly, Craig
Linn lives at 915 Sheridan Road in Waukegan, within three or four blocks of Mr. Sweda.
Tr. at 556, 561. Although he can hear the cannons from his yard, they blend in to other noise from the nearby
expressway or railroad, so he did not remember a specific date when he first noticed them. Tr. at 558. He has
never had any trouble conversing with his wife or children in the back yard while the cannons were firing. Tr. at
559.
People working in the vicinity of the cannons also reported no problems from the noise.
Larson Marine
Services, located directly north of OMC and the gull colony site, has approximately 50 employees, and a large
number of them work outside from March through November. Tr. at 423-426. Larson Marine employees have
never complained about the noise from the cannons. Tr. at 433. Mr. Larson’s office is approximately 300 to 400
yards from the cannons, and he cannot hear the cannons inside his office. Tr. at 432. He can hear them if he is
outside, but can talk in a normal voice with the cannons firing. Tr. at 432, 433. John
Battisfore and Lisa
Bongiovanni, who work at OMC in close proximity to the cannons, testified that they had had conversations
outside in a normal tone of voice while the cannons were firing. Tr. at 294, 397.
Bongiovanni also testified that the
noise of the cannons has never interfered with her phone conversations in her office. Tr. at 398.
Numerical Testing
After Sweda filed his complaint, OMC retained Brian
Homans to measure and assess the noise from the
cannons at a point near Sweda’s house and compare those results with the Board’s regulatory standards. Tr. at 471.
Homans is an accoustical engineer with Shiner & Associates, Inc. Tr. at 462-63. He is an expert in environmental
acoustics with considerable experience taking sound level measurements, including field testing impulsive sound.
Tr. at 467-68. Mr. Homans took measurements from a site close to Sweda’s house, between Sweda’s house and the
OMC site, and approximately the same distance from Sheridan Road as
Sweda’s house. Tr. at 471-72. He took
measurements on March 4, 1999, and again on
March 15, 1999. Tr. at 475.
The A-weighted level measured by Homans was less than the Section 901.104 daytime limits by 11 dB (45
dB versus 56 dB). Tr. at 499-500; OMC Ehx. 10. Homans determined that the cannons have a slight effect (1dB) on
ambient noise levels. Tr. at 503; OMC Exh. 10. The noise from airplanes was louder than the noise of the cannons.
Tr. at 504-05.
DISCUSSION
Any violation of Section 24 of the Act must be predicated on a violation of one of the Board’s noise
regulations. We thus consider whether the evidence establishes either of the alleged violations of regulations.
35 Ill. Adm. Code 900.102
The Board’s inquiry in cases alleging noise pollution is two-part. First, the Board determ
ines whether
there has been interference with enjoyment of life or with any lawful business or activity. If interference is found,
the Board then decides whether the interference is unreasonable. Regarding the first part of the inquiry, the Board
has held:
The threshold issue in any noise enforcement proceeding is whether the sounds
have caused some type of interference with the complainant’s enjoyment of life
or lawful business or activity. If there is no interference, no “nuisance noise”
11
violation is possible. Interference is more than an ability to distinguish sounds
attributable to a particular source. Rather, the sounds must objectively affect
the complainant’s life or business activities.
Zivoli v. Prospect Dive & Sport
Shop, Ltd. (March 14, 1991), PCB 89-205, slip op. at 9.
Interference
Although the law does not protect a person from noise which is merely a source of aggravation,
Kochanski v. Hinsdale Golf Club
(July 13, 1989), PCB 88-16, slip op. at 14, in this case we conclude that the irritation
experienced by Sweda and Neff rises to the level of interference with their enjoyment of life. We therefore
examine whether such interference is unreasonable.
Reasonableness
In determining whether interference is unreasonable, the Board weighs the factors listed in Section 33(c) of
the Act (415 ILCS 5/33(c) (1998)), to the extent the record contains evidence relevant to those factors. Scarpino v.
Henry Pratt Co. (April 3, 1997), PCB 96-110, slip op. at 15; Charter Hall Homeowners’ Assoc. v. Overland
Transportation Systems, Inc. (October 1, 1998), PCB 98-81, slip op. at 21.
Section 33(c) provides:
c.
In making its orders and determinations, the Board shall take into
consideration all the facts and circumstances bearing upon the
reasonableness of the emissions, discharges or deposits involved
including, but not limited to:
i.
the character and degree of injury to, or interference with the
protection of the health, general welfare and physical
property of the people;
ii.
the social and economic value of th e pollution source;
iii.
the suitability or unsuitability of the pollution source to the
area in which it is located, including the question of priority
of location in the area involved;
iv.
the technical practicability and economic reasonableness of
reducing or eliminating the emissions, discharges or deposits
resulting from such pollution source; and
v.
any subsequent compliance.
Section 33(c)(i): Character and Degree of Injury. An important inquiry in examining the character of any
interference is objectivity. The Illinois Supreme Court, in
Processing and Books, Inc. v. Pollution Control Board , 64
Ill. 2d 68, 351 N.E.2d 865 (1976), interpreted the word “unreasonably,” as used in the Act, to impose an element of
objectivity on the analysis of interference:
There is little that any person can do which does not in some degree “interfere
with the enjoyment of life or property” of other persons. The very act of
breathing consumes oxygen. In our opinion the word “unreasonably” . . . was
intended to introduce into the statute something of the objective quality of the
common law, and thereby exclude trifling inconvenience, petty annoyance or
minor discomfort. *** [I]t removes the possibility that a defendant’s conduct
12
may be measured by its effect upon those who are inordinately timorous or
belligerent. 351 N.E.2d at 869.
Although the court in Processing and Books was interpreting the air pollution provisions of the Act, based on the
analogous language in the definition of noise pollution we have consistently found this analysis applicable in
noise pollution cases as well. See,
e.g.
, D’Souza v. Marraccini (May 2, 1996), PCB 96-22; Village of Matteson v.
World Music Theater
(February 25, 1993), PCB 90-146; Zarlenga v. Partnership Concepts (May 9, 1991), PCB 89-169 (all citing Wells
Manufacturing Co. v. Pollution Control Board , 73 Ill.2d 226, 232, 383 N.E.2d 148, 150 (1978), which in turn cites
Processing and Books).
In this case, there is considerable evidence, in the form of testimony of local residents and OMC
employees, that the noise from the cannons did not generally interfere with enjoyment of life or lawful business or
activities in the noise-impacted community as a whole. The fact that not everyone in the vicinity of a noise source
is bothered by that noise source will not
ipso facto
prevent a finding of noise pollution.
Discovery South Group,
Ltd. v. Illinois Pollution Control Board
, 275 Ill. App. 3d 547, 554-55, 656 N.E.2d 51, 57 (1st Dist. 1995). There comes a
point, however, at which the evidence establishes that, whatever the complainant’s subjective experience, there is
no unreasonable interference when the noise source is evaluated objectively. We conclude that this point has been
reached in this case. Because the evidence indicates that most people in the affected area are not significantly
bothered by the cannon noise, the Board concludes that this factor supports a finding that the interference
experienced is not unreasonable. See Bolender v. Monticello Bus Service
(May 21, 1992), PCB 91-136.
Section 33(c)(ii): Social and Economic Value of the Source.
The Board finds the social and economic value
of the source in this case to be high. By dispersing the gull colony that formerly nested on the coke plant site, the
cannons prevent or mitigate a wide variety of negative effects of the colony’s presence. The positive effects of the
cannon program inure to the benefit of the general public as well as local businesses such as OMC and
Larson
Marine and their employees, inasmuch as bacterial contamination at the public beach is reduced, as is the risk of
contamination of the public water supply. The Board accordingly concludes that this factor also supports a finding
that the interference experienced is not unreasonable.
Section 33(c)(iii): Suitability of the Source and Priority of Location.
Sweda and Neff clearly have priority
of location. They lived in their current homes long before the propane cannon program was initiated in 1998. The
cannons do not, however, appear to bother other people, including people who live and work closer to the noise
source than Sweda or Neff, which suggests that the noise source is not unsuitable to its location. From the
evidence in this case, it appears that the cannons are separated from the residential areas of Waukegan by (a) the
width of Waukegan Harbor, (b) the railroad, (c) the expressway, and (d) Sheridan Road. Thus, both distance and
intervening noise sources lessen the impact of the cannons on local residents. The Board finds that the cannons are
suitable for their location, and concludes that this factor supports a finding that interference is not unreasonable.
Section 33(c)(iv): Technical Practicability and Economic Reasonableness of Reducing Emissions.
The
testimony of Southern established that the cannons are the most efficient and effective method of dispersing the
gulls, and explained why other programs would be ineffective. See
supra
, pp. 12-13. Based upon this testimony,
and the complications created by the environmental contamination at the gull colony site, the Board finds that
alternatives to the cannon program are not technically practicable or economically reasonable at the OMC site.
This factor therefore supports a finding that interference is not unreasonable.
The City has now implemented a new program—use of dogs—which has obviated the need for the
cannon. Musinski testified, however, that repairs and improvements were necessary before dogs could be brought
on to the property, and that this prevented the City from using the dogs during the 1998 nesting season. He also
testified that the City could not use wires because of the need for access to the area. Based on this testimony, the
Board finds that, pending the repairs and improvements necessary to accommodate dogs at the water treatment
plant, other bird control measures were not technically practicable. Accordingly the Board concludes that this
factor supports a finding that interference was not unreasonable with respect to the City as well.
13
Section 33(c)(v): Subsequent Compliance. This factor is not relevant to a determination about whether the
interference experienced by Sweda or Neff was unreasonable. Unless such interference is determined to be
unreasonable, there can be no violation and thus no “subsequent compliance.” Nevertheless, we note that the City
stopped using the cannons after 1998 when dogs were introduced at the water treatment plant site, and that OMC
projects that the cannon program will be finite in duration, and presumably will cease once the gulls’ attachment to
the site has been broken and they have relocated elsewhere.
After evaluating the Section 33(c) factors, the Board finds that the interference caused by OMC’s or the
City’s use of propane cannons to displace gull colonies is not unreasonable.
Conclusion.
Based on the foregoing analysis, the Board concludes that neither OMC nor the City has violated Section
900.102.
35 Ill. Adm. Code 901.104
Sweda presented no evidence that the impulsive sound from the propane cannons exceeded the decibel
levels set in Section 901.104. The only evidence on this subject is the testimony of
Homans, who determined that
the noise from the cannons, when measured near Sweda’s house, did not exceed the daytime limits for sound
emitted from class C to class A land. Tr. at 499-500. The Board finds no violation of Section 901.104 based on the
evidence in this record.
CONCLUSION
Upon review of the record in this case, the Board finds no violations of 35 Ill. Adm. Code 900.102 or
901.104. Having found no violation of a noise regulation or standard, the Board finds no violation of Section 24 of
the Act.
This opinion constitutes the Board’s findings of fact and conclusions of law in this matter.
ORDER
The Board finds no violation of 35 Ill. Adm. Code 900.102 or 901.104, and accordingly no violation of 415
ILCS 5/24, by either Outboard Marine Corporation or the City of Waukegan.
IT IS SO ORDERED.
Section 41 of the Environmental Protection Act (415 ILCS 5/41 (1998)) provides for the appeal of final
Board orders to the Illinois Appellate Court within 35 days of service of this order. Illinois Supreme Court Rule
335 establishes such filing requirements. See 172 Ill. 2d R. 335; see also 35 Ill. Adm. Code 101.246, Motions for
Reconsideration.
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, hereby certify that the above opinion
and order was adopted on the 5th day of August 1999 by a vote of 7-0.
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board