DocketNumber: C.A. No. 09-908.
Judges: K. RODGERS, J.
Filed Date: 8/12/2010
Status: Precedential
Modified Date: 7/6/2016
This Court has jurisdiction pursuant to G.L. 1956 §
Defendants own and reside across Burgess Road and directly west of the Plaintiffs' home. Defendants have resided at 2A Burgess Road since approximately 1994. Their property is a 4.95-acre corner lot abutting Burgess Road to the east and Hartford Pike to the north. Defendants Louis J. Pezza and Isabelle C. Pezza are the parents of Defendant Louis J. Pezza, Jr. ("Louis Pezza"), and live in an in-law apartment within the two-story residence. Louis Pezza and his wife, Sarah Pezza, reside in the main part of the residence.
For health reasons, the elder Pezzas require the heat in their living area to be maintained at a higher temperature than the remainder of the house where Louis and Sarah Pezza reside. Defendants' property is currently serviced by an oil furnace that is over fifteen (15) years old. In an effort to save money on heating costs in the fall and winter months, and to avoid the costly replacement of the existing oil furnace, Defendants purchased and had installed the OWB on the eastern side of their property in the summer of 2008 at a cost of approximately $15,000. Louis Pezza expected that it would take three (3) years of operating the OWB to recoup the money spent on the OWB and its installation by not having to purchase home heating oil. The OWB is located 55' from the Defendants' own residence, 15' from the edge of Defendants' property, 30' *Page 3 from the edge of Plaintiffs' property, and less than 200' from Plaintiffs' house.2 Plaintiffs' property is at a grade seven feet (7') below Defendants' property.
Generally, an OWB is a wood-burning appliance that converts wood fuel to heat. More specifically, the OWB installed on Defendants' property is a Central Boiler, Inc., Classic Model 6048 ("Model 6048"), and is recognized in the industry as a mid-sized residential unit that is designed to be fueled by hand by loading wood through a door into the combustion chamber. When the wood burns, the heat from the combustion chamber in turn heats a water jacket surrounding the combustion chamber; the water jacket is attached to a series of pumps and piping which connect the device to an indoor heating system servicing Defendants' residence. The OWB releases steam and smoke from the combustion chamber through a metal smokestack attached to the structure; the top of the smokestack on Defendants' OWB measures 18' above the ground.
Twelve witnesses testified before the Court, including Plaintiffs, Defendant Louis Pezza, Sarah Pezza, and six (6) other Foster residents, four (4) of whom reside on Burgess Road and one being the Town Solicitor. Expert testimony was also presented on behalf of Plaintiffs as well as Defendants.
Mrs. Charette testified that she first observed emissions from Defendants' OWB in June or July, 2008. She experienced an odor while on the back deck of her home one afternoon and immediately went in to close the sliding doors. Plaintiffs also recalled a nighttime incident in August, 2008, during which their twin sons, then 3-years old, awoke crying and coughing due to smoke that had entered Plaintiffs' home.
The next business day following Mrs. Charette's first observations, Mrs. Charette visited Foster Town Hall to complain about the smoke from Defendants' OWB. She stated that the Town did not have any knowledge about OWBs. Mr. Charette testified that Town officials would not allow his wife to make a formal complaint. Mr. Charette subsequently contacted the Foster Building Official, the Rhode Island Department of Environmental Management, the Rhode Island Department of Health, and the Rhode Island Attorney General, with no official action taken by any entity or individual. According to Mr. Charette, Foster Town Solicitor John Bevilacqua advised Mr. Charette that the Town would shut down Defendants' OWB and create laws to regulate it. At trial, Mr. Bevilacqua disputed that he made such representations. To the contrary, Mr. Bevilacqua recognized that upwards of fifty (50) OWBs are in operation in Foster, some of which have been in operation for many years. *Page 5
Mrs. Charette testified that just after her visit to Town Hall, she observed Louis Pezza "barreling down the driveway beeping." She described him as irate and testified that he demanded that she inform Mr. Charette that he wanted to speak to him. Mrs. Charette testified that she was offended by how Mr. Pezza belittled her and she informed her husband that he was not to go over to speak with Louis Pezza.
Louis Pezza testified that after installing the OWB in accordance with the instructions, he used the OWB in late August, 2008, only as a dry run before the colder weather set in. At that time, Mr. Pezza used unseasoned pine wood to fuel the OWB, which Mr. Pezza acknowledged created significant emissions and a pungent odor that the Charettes described on that first occasion. He has since used only seasoned, cut hardwood to fuel the OWB, which wood is stacked in the vicinity of the OWB for easy access.
Sharon Franco, a neighbor immediately south of Plaintiffs on Burgess Road, testified that she first observed smoke from Defendants' OWB in May or early June, 2008. She recalled thinking at that time that someone's house was on fire because of the concentrated smoke. She described the smell on that occasion as a "toxic odor," with an oil type of smell. She further described the smoke on that occasion as "like driving through a fog of darkness" which rolled onto Plaintiffs' property. Her husband, Anthony Franco, testified that he first observed significant smoke in the vicinity of Plaintiffs' home in early fall 2008 — not in the summer — when he drove home from work after 9 p.m. and saw smoke in the headlights of cars stopped on Burgess Road. He recalled that he thought there was a fire at Plaintiffs' house, but admittedly did not stop to inquire of anyone else that had been stopped what they knew to be happening. He testified that at that time the smoke was at or near ground level, and he recalled feeling bad for the people next door when he observed that smoke. *Page 6
From late August to late September, 2008, Defendants did not operate the OWB in any manner. The testimony further reveals that Defendants had not been ordered by any official or entity to cease operating the OWB during that time.
Plaintiffs each testified that the operation of the OWB forced them to close all their windows and they could no longer play with their children in their yard. Without air conditioning in their home that summer of 2008, the closed windows caused the inside of their home to become very hot in the warm weather. Mr. Charette further stated he was unable to lie in his hammock, rake leaves, shovel his driveway or clean out his barn because of the smell. Additionally, Plaintiffs could not build a snowman or sled on a small hill in their front yard with their young boys all winter.
Even with windows closed, Mrs. Charette testified that smoke permeates into the home daily. Mrs. Charette stated that even when she did not observe smoke, she would not open her windows out of fear that the smoke would suddenly return. For this reason, she would hurriedly *Page 7 close the doors quickly when she left or re-entered the house, and she would cover her face with clothing to avoid breathing the smoke. Although Mrs. Charette stated that she "got used to the smell," she continued to believe that the effects of the smoke were harmful. She described her life as being a prisoner in her own home. She testified that she was too uncomfortable and embarrassed to invite people to her home because of the emissions from Defendants' OWB.
On cross-examination, Mr. Charette acknowledged that many of the front-facing windows on Plaintiffs' home do not open, that they are less likely to open windows in the winter months and that their children are less likely to play outside in the winter due to the cold weather. For her part, Mrs. Charette testified that because her children were forced to stay indoors to avoid smoke from the OWB, they now "acted differently." In discussing her sons' past play outside, Mrs. Charette further commented that the noise of airplanes in Foster is disturbing.
Mrs. Charette expressed great concern with the safety of Defendants' OWB. Specifically, she stated that anyone could walk up to the OWB, open it up and put anything they wanted into the combustion chamber. She provided emotional testimony that a child could die if he or she opened Defendants' OWB because oxygen would be introduced and smoke would blast out.
Mrs. Charette maintained a journal detailing her observations regarding the OWB from September, 2008 to March, 2009. Although the journal was not marked as a full exhibit, the testimony elicited at trial revealed that Mrs. Charette strongly distrusted Foster Town officials and believed that Louis Pezza was intentionally creating more smoke. *Page 8
To demonstrate what Plaintiffs experienced "everyday," Plaintiffs videotaped several minutes on thirty-six (36) dates from September 23, 2008 through March 9, 2009. (See Defs.' Exs. A and B.) Plaintiffs contend that they could only film a limited number of days and just a few minutes at a time because of their work and childrearing responsibilities. On direct examination, Plaintiffs' testimony was streamlined to address the "worst" conditions that Plaintiffs experienced, utilizing abridged versions of the exhibits introduced in full by Defendants. (See Pls.' Exs. 4 and 5.) Only the video portions were introduced and marked as evidence; this Court denied entry of the audio portion as evidence and the parties complied with such limitations in presenting the respective DVDs3 to the Court. In Plaintiffs' Post-Hearing Response Memorandum, Plaintiffs characterize the video footage as "the most important evidence in this matter," and they rely heavily on the scenes depicted therein as conclusive proof that emissions from Defendants' OWB constitutes a private nuisance and a continuing trespass. (See Pls.' Post-Hearing Resp. Memo. at 5.)
Notably, of the thirty-six (36) dates filmed over the course of 5½ months of operation, a number of days videotaped reveal a "trickle" of smoke, (see, e.g., Defs.' Ex. A, at 9/28/08, 10/11/08; Defs.' Ex. B, at 3/9/08), smoke blowing in an easterly direction and away from *Page 9 Plaintiffs' property (see, e.g., Defs.' Ex. B, at 1/30/09), or dark smoke lifting into the air from Defendants' OWB with no documented or discernable effect on Plaintiffs' property. (See, e.g., Defs.' Ex. A, at 9/23/08, 9/24/08, 9/25/08, 10/7/08, 11/2/08, 12/21/08; Defs.' Ex. B, at 1/21/09.) Further, the quality of the video on many days was compromised and made it difficult at best to observe smoke from Defendants' OWB or the effect on Plaintiffs' property due to what appears to be sun glare (see, e.g., Defs.' Ex. A, at 10/13/08, 10/20/08, 10/26/08, 11/21/08, 11/29/08, 12/13/08, 12/23/08; Defs.' Ex. B, at 1/14/09, 1/16/09, 1/17/09, 2/15/09), dark conditions (see, e.g., Defs.' Ex. A, at 9/26/08, 9/29/08, 11/20/08; Defs.' Ex. B, at 1/26/09), or overcast conditions (see,e.g., Defs.' Ex. A, at 9/30/08, 10/1/08, 10/3/08, 10/9/08; Defs.' Ex. B, at 2/19/09).
In addition to the video evidence prepared by Plaintiffs for the purpose of this litigation, Mrs. Charette took two (2) pictures which were introduced into evidence. (Pls.' Exs. 8 and 9.) According to Mrs. Charette, these pictures were taken in late September, 2008, because Defendants had just started operating the OWB again. The pictures reveal sun glare from the south and what Mrs. Charette described as smoke; she also testified that there was an intense smell associated with that smoke. According to Mrs. Charette and using Mr. Charette's scale of 1 to 10, the depiction in Plaintiffs' Exhibits 8 and 9 would be a "7."
Defendants introduced twelve (12) photographs into evidence. (Defs.' Ex. I.) Sarah Pezza testified that she took these photographs on August 2 — 4, 2009, when this trial was underway and when Defendants' OWB was not in operation, and indeed the pictures are date stamped accordingly. Those photographs display some sun glare but, importantly, also reveal a hazy, low-lying denseness in and around Plaintiffs' property. The hazy, low-lying denseness appears to the Court to be similar in several respects to the denseness depicted in Plaintiffs' two photographs (Pls.' Exs. 8 and 9) and to many days of video filmed by Plaintiffs, namely, the lowlying *Page 10 nature, color, thickness and location in and around the side yard and brush area to the west and southwest of the Plaintiffs' residence. (See, e.g., Defs.' Ex. I; cf., e.g., Defs. Ex. A, at 10/2/08, 10/9/08, 10/13/08, 10/20/08, 10/26/08, 11/9/08, 11/21/08, 11/29/08, 12/13/08; Defs.' Ex. B, at 1/14/09, 1/17/09, 1/30/09, 2/15/09, 2/19/09, 3/9/09.)
On cross-examination, it was revealed that there was another reason that Plaintiffs kept their dog inside rather than in the outside dog kennel. Specifically, Plaintiffs' dog had been the subject of an appeal to Sixth Division District Court following a vicious dog hearing before the Town of Foster. Town Solicitor John Bevilacqua testified that Mr. Charette was represented by counsel on that appeal and that restrictions were imposed on the dog after conference with the District Court Justice. Mrs. Charette acknowledged on cross-examination that their dog was not permitted to be off-leash outside of Plaintiffs' property, was limited to just 10-15 minutes per day outside, and was to be fenced in or under the supervision of the owner while outside on Plaintiffs' property.
Mr. Bevilacqua confirmed such restrictions, among others, and further testified that the restrictions were imposed on Plaintiffs' dog after Defendant began to use the OWB. Nonetheless, Mr. Bevilacqua testified that based on several telephone conversations he has had with Mr. Charette, Mr. Charette was under the belief that Louis Pezza was the cause of Plaintiffs' dog problems. Louis Pezza testified that although his father was bitten by Plaintiffs' *Page 11 dog, neither Louis Pezza nor anyone in his family called any Town official concerning that dog bite, and therefore the Pezzas were not responsible for the vicious dog hearing or, consequently, the restrictions imposed on Plaintiffs' dog.
Steven Young, an 8-plus-year resident of 2 Burgess Road, directly west of Plaintiffs' barn area and south of Defendants' property, testified to the conversations that Mr. Charette attempted to initiate with him. After Mr. Charette left a note in Mr. Young's mailbox asking him to call, Mr. Young recalled from that conversation that Mr. Charette stated that he was "sick of hearing Lou talk about [Plaintiffs'] dog" and that Mr. Charette then complained about Defendants' OWB. Mr. Young also described the conversation as Mr. Charette's attempt to persuade him that OWBs were pollutants and that operating Defendants' OWB was the equivalent of leaving fifty (50) cars running on Defendants' property. *Page 12
Anthony Franco testified that he walks on Burgess Road everyday, that he frequently observed smoke on Plaintiffs' property, and that the smoke was always low lying. His daily walks occur at different times of the day, and he has seen other OWBs operating on the 1½ mile-long Burgess Road. On cross-examination, he testified that even after Defendants ceased operating the OWB in March, 2009, he still smelled wood burning and noticed smoke from units servicing other properties, including his own woodstove. He acknowledged that he could not definitively say that when he did not see smoke but smelled it or tasted it, that it emanated from Defendants' OWB. He further stated on cross-examination that Burgess Road does get low lying fog, but he observed that low lying fog doesn't smell and that emissions do smell. Mr. Franco stated that sometimes the smell he experienced on Burgess Road was objectionable, but other times it was not.
Defendants presented the testimony of three neighbors on or near Burgess Road, including Defendants' immediate neighbor to the south, Steven Young. Mr. Young testified that many people in the area burn wood, including himself. The Youngs utilize a woodstove to heat their entire house in the winter months and refuel the stove four to five times daily; the *Page 13 smokestack to that woodstove is 16'-17' above grade and is directly west of the barn area on Plaintiffs' property. At times when Mr. Young has observed smoke emanating from Defendants' OWB smokestack, he experienced a smell that was similar to the smell of wood from a woodstove, a smell with which he is familiar. When asked to describe the difference in smoke emissions from Defendants' OWB and his own woodstove, Mr. Young testified that in his opinion, there was little difference and that Defendants' unit probably emitted less smoke than his own woodstove.
Myra Mercier, a resident of 3½ Burgess Road, southwest of Plaintiffs' property and south of Defendants' property, testified that everyone she knows in the area burns wood, including herself. She walks to her mailbox daily, drives her car frequently on Burgess Road past Plaintiffs' and Defendants' properties, and has observed Defendants' OWB in operation. Mrs. Mercier testified that she never observed smoke entering Plaintiffs' property. Mrs. Mercier testified that the area of Burgess Road frequently experiences ground fog.
Finally, Donald Knox, Jr., a resident of a corner lot on Shippee School House Road approximately ½ mile away from Plaintiffs' and Defendants' properties on Burgess Road, testified that three of five properties adjacent to his are serviced by OWBs, including his own being serviced by an OWB. His own home serves as a daycare for six pre-schoolers, ages 3-4, and he is not aware of any complaints having been made concerning the health of these children. Mr. Knox testified that he has observed Defendants' OWB in operation and testified that the smoke output is similar to the amount of smoke from his own OWB and that of his neighbors' OWBs. Further, he testified that he has never observed smoke from Defendants' OWB crossing over Burgess Road to Plaintiffs' property. *Page 14
Mr. Leston testified that the firebox, or combustion chamber, of the Model 6048 is thirty (30) to sixty (60) times the size of the firebox of a standard approved woodstove, which is only one (1) or two (2) cubic feet in size. He had studied the Model 6048 in use in two other settings outside of Rhode Island. He further testified that the OWB emits considerably more grams of particulate and gaseous matter per hour than does a woodstove. Mr. Leston testified that woodstoves operate at a much higher rate of efficiency than an OWB so there are less emissions *Page 15 from a woodstove than an OWB. Per Mr. Leston's testimony, lower efficiency translates into incomplete combustion, greater emissions and higher particulate matter. Further, the effects of incomplete combustion, as experienced in the operation of an OWB, leads to the formation of creosote that builds up in the combustion chamber and smokestack, creating a different quality of smoke and odor in an OWB as compared to in a woodstove, which goes through a complete combustion cycle.
Mr. Leston discussed how an operator of an OWB can affect its efficiency. The timing of refueling, placement of logs, and the condition, size and type of wood used can all affect the efficiency of the unit. Refueling — or restacking wood in the combustion chamber — interrupts the combustion cycle and generates significantly greater amount of particulate matter.
However, he also acknowledged that the federal air quality standards, with which he was familiar, measure particulate matter inconcentration, or micrograms per cubic meter (µg/m3), to determine health effects from such particulate matter, and not by quantity of emissions measured by total grams of emissions per hour. The EPA has set a numerical limit of 35 µg/m3 over a 24hour period as a safe concentration of particulate matter (PM2.5).
Mr. Leston reviewed Plaintiffs' videotaped depiction of smoke from Defendants' OWB while in operation, as set forth on Defendants' Exhibits A and B, and conducted two site visits to the property in question. He observed Defendants' OWB in operation and testified that the smoke and odor were comparable to other OWBs he had observed. He noted that the human nose is generally sensitive to the smell of wood smoke, causing some people to find it unpleasant.
Mr. Leston opined that the emissions from Defendants' OWB impacted Plaintiffs' property from August, 2008 to March, 2009. His opinion was based on the following factors: *Page 16 relative locations of the OWB and Plaintiffs' residence; obstructions between those structures; topography; height of the OWB smokestack; and the upwind obstructions of the OWB, namely, Defendants' residence. Without objection by Defendants' counsel as being beyond the scope of his expertise, Mr. Leston testified that the prevailing winds from August, 2008 through March, 2009 was from west to east. Because Plaintiffs' residence was due west of the OWB and because Defendants' own home obstructed winds blowing from the west from allowing such winds to dissipate the emissions from the OWB, a region of turbulence (or wake cavity effect) was created. (Pls.' Ex. 12.) Mr. Leston testified that this region of turbulence created a situation by which the emissions from the OWB would be pushed toward the ground, west of the OWB and, consequently, into Plaintiffs' yard. In light or variable wind conditions (as opposed to a westerly wind), emissions would move in different directions and accumulate generally in the area of the OWB.
On cross-examination, Mr. Leston admitted that he did not research the weather, wind direction, or reports of ground fog on any of the days depicted on video. Further, he admitted that he had taken no measurements, collected no data, performed no air monitoring or meteorological research, and conducted no testing of any kind which would support his opinion that the air quality — or the concentration of particulate matter — was negatively impacted by the operation of Defendants' OWB. He did state on direct examination, however, that his opinion would not have changed because of the close proximity between the structures, the prevailing winds and the location of Defendants' residence upwind from the OWB. In sum, Mr. Leston relied wholly on the wake cavity effect and the westerly winds to support his conclusion that Plaintiffs' property was negatively affected by the operation of Defendants' OWB. *Page 17
Mr. Guldberg explained the two methods recommended by the EPA to determine whether air quality is acceptable. The first is monitoring the air at the receiver using an instrument that is certified as the Federal Reference Method for PM2.5. Alternatively, air dispersion modeling using EPA's computer model known as AERMOD, in conjunction with five (5) years of weather data, is an EPA-recommended method for determining PM2.5 particulate matter. For PM2.5, EPA has set a limit of 35 µg/m3 over a 24-hour period as safe ambient air quality.
Mr. Guldberg performed dispersion modeling in this case using EPA's AERMOD model, which stimulates transport, dispersion and dilution of PM2.5 emissions in the air. According to Mr. Guldberg, based on the dispersion model, the predicted maximum PM2.5 concentration is 7.8 µg/m3 and occurs on Defendants' property. At the front of Plaintiffs' home, the maximum PM2.5 concentration is between 4 — 5 µg/m3, significantly below the 35 µg/m3 health standard set by EPA. Mr. Guldberg concluded that the emissions from Defendants' OWB were very easily in compliance with the EPA health standard, and that based on that compliance, such emissions were not at a concentration high enough to cause harm. *Page 18
Although the Model 6048 has a much larger combustion chamber than a woodstove, Mr. Guldberg testified that a larger chamber did not correspond with a negative impact on air quality, and he discounted the significance of the amount of emissions generated from an OWB. The critical question, according to Mr. Guldberg, is concentration of the emissions rather than quantity. Like Mr. Leston, Mr. Guldberg testified that the manner in which the OWB is operated could impact emissions, but he further noted that no formal training beyond reviewing the manual would be necessary to safely operate the Model 6048.
Mr. Guldberg performed a site inspection on two separate occasions — once when the OWB was in operation and once in the summer of 2009. He considered the height of the peaks on Plaintiffs' residence (or the two different rooflines) in relation to the height of the OWB's smokestack, took into consideration the change in grade between the structures, and concluded that the smokestack was at the same height of the higher peak and 8' higher than the lower peak of Plaintiffs' residence. Mr. Guldberg noted that manufacturer guidelines for the Model 6048 recommend the stack on the OWB be 2' above the roof peak of any non-serviced property within 300'.
Mr. Guldberg also reviewed the video footage prepared by Plaintiffs. Unlike Mr. Leston, he did research weather conditions on the days that were depicted on video and testified that a number of those days had reports of ground fog. He testified that the videos depicting Defendants' smokestack most often showed that smoke moved upward out of the smokestack, which is ideal for greater dispersion, and that the smoke from the smokestack was consistent with that from a properly operating OWB. Immediately after refueling, the smoke released will be heavier and thicker than the plume that was frequently observed. *Page 19 On cross-examination, Mr. Guldberg acknowledged that as recently as the spring of 2009 he served as a consultant to Central Boiler, the manufacturer of the Model 6048. In or about 2006, he provided scientific expertise to assist Central Boiler in responding to a report that had been issued by the Northeast States for Coordinated Air Use Management ("NESCAUM") concerning OWBs. NESCAUM is a quasi-governmental group comprised of state-level environmental officials in New England, New York and New Jersey, and addressed air quality issues. Mr. Guldberg admitted that he disagreed with many of the conclusions about OWB emissions contained in the NESCAUM report, which report was not admitted into evidence at trial.
Mr. Leston testified that prevailing winds is one factor in the manufacturers' recommendations for where the Model 6048 should be placed. It is not, however, a requirement. Mr. Leston further testified both on direct and cross-examination that there was no other place on *Page 20 Defendants' property where the OWB could be sited that would not affect Plaintiffs' property because the prevailing westerly winds will always carry emissions from any location on Defendants' property to Plaintiffs' property. In Plaintiffs' Post-Hearing Response Memorandum, Plaintiffs also agree with Defendants that there was no other feasible location on Defendants' property for the placement of the OWB which would not affect Plaintiffs' property. (Pls.' Post-Hearing Resp. Memo. at 2, 6-7.) Defendants' expert, Mr. Guldberg, testified that factors to be considered in siting an OWB include stack height. Given that he had determined that the smokestack on the OWB was at the same height as the higher roofline and 8' higher than the lower roofline on Plaintiffs' residence, he testified that the location of the OWB complied with the manufacturer guidelines for the Model 6048, which recommend the stack be 2' above the roof peak of any non-serviced property within 300'.
Mr. Bevilacqua testified that at the time of trial there were approximately fifty (50) OWBs in the Town. Many of these units have been in operation for several years but they have only recently become controversial because of complaints made. The Town now requires *Page 21 mechanical, electrical and building permits for an OWB that is being secured to a permanent structure, i.e., a slab foundation on which the OWB is placed. Zoning compliance is required for permanent fixtures. An OWB is not treated as an accessory structure. A site plan is also now required by the Town so the Town is aware of the exact location of OWBs, in the same manner that a site plan would be required to do most anything on one's property.
Further, in addressing a request for permanent injunction, the trial justice must determine that "the merits of the case call for an order forbidding or compelling particular conduct." 1 Kent Rules of Civil Procedure § 65:1 (2006). "The issuance of an injunction and the scope and quantum of injunctive relief rests in the sound discretion of the trier of fact." DeNucci v.Pezza,
The burden of proving a nuisance is on the party alleging such nuisance to demonstrate the existence of the nuisance and that an injury was caused by the nuisance. Citizens forPreservation,
In the instant case, the parties agreed to sever liability on the permanent injunction and trial on the merits from damages. At this juncture, then, Plaintiffs had the burden of demonstrating the existence of the private nuisance without yet having to establish any injury caused by the nuisance. However, in establishing the existence of the private nuisance, Plaintiffs were required to demonstrate the harm or risk of harm caused to Plaintiffs from the operation of Defendants' OWB is greater than they ought to bear under the circumstances. Id. For the following reasons, Plaintiffs have failed to sustain that burden.
By contrast, Defendants presented reliable and thorough expert testimony that the emissions from Defendants' OWB were well within the air quality standards set by EPA. Specifically, Mr. Guldberg performed dispersion modeling, an EPA-accepted method for determining compliance with federal air quality standards, which revealed that the concentration of emissions from Defendants' OWB at the front of Plaintiffs' residence at between 4 — 5 µg/m3, well within the EPA health standard of 35 µg/m3. Further, this Court is unmoved by Plaintiffs' attempt to discredit Mr. Guldberg's testimony by demonstrating his consultant arrangement with Central Boiler, the manufacturer of the OWB at issue, and his disagreement with the NESCAUM report.
While the expert testimony presented by the parties was lengthy, the credible testimony supported by scientific principles and standards can be summarized as follows: the quality of emissions from an OWB is measured by the concentration of emissions and not the quantity of emissions. An EPA-approved method of calculating the concentration of emissions from Defendants' OWB was utilized by Defendants' expert; Plaintiffs' expert simply failed to perform any other testing or recognized manner of calculating the concentration of emissions and relied instead on the physics theory known as the wake cavity effect. This Court finds Defendants' expert testimony to be more credible than Plaintiffs' expert testimony, which this Court finds to be sorely lacking based upon Plaintiffs' apparent decision to avoid further litigation costs. In short, the weight of the credible evidence before this Court demonstrated that the emissions created by Defendants' OWB were not unreasonable and indeed were well within EPA air quality measurements on Defendants' property as well as on Plaintiffs' property. *Page 27
Even if Plaintiffs' testimony was not exaggerated or biased, such testimony, at a minimum, evidences that Plaintiffs are not
persons of ordinary habits or sensibilities. To move to Foster and be disturbed by airplane noise or wood smoke is not within a normal range of sensibilities. Simply put, Plaintiffs' own testimony leads this Court to find that Plaintiffs cannot *Page 28
sustain their burden of proving that the alleged private nuisance exists based on the effects upon a person of ordinary habits and sensibilities. DeNucci,
By contrast to Plaintiffs' testimony, Louis Pezza and Sarah Pezza testified without motive or bias, but rather to present their reasons why their OWB is needed, how it operates, and the emissions they observe from their OWB. Similarly, Defendants' witnesses, including neighbors and another nearby OWB operator, generally appeared credible and unbiased. On balance, the weight of the credible evidence lies with Defendants and not Plaintiffs.
Based upon the foregoing analysis of private nuisance and the credibility determinations made therein, this Court finds that Plaintiffs are not entitled to relief based upon a continuing trespass. Plaintiffs did not sustain their burden of demonstrating that the haze and denseness depicted in video and in Plaintiffs' pictures were solely or even partially caused by the emissions from Defendants' OWB, or that any emissions were continuously flowing from Defendants' OWB and not from other wood burning units. Accordingly, this Court cannot find that Defendants would be under a duty to remove emissions from Plaintiffs' property. Finally, in the *Page 29 absence of such credible proof that the haze and low-lying denseness in the video and pictoral evidence was from Defendants' OWB, this Court cannot find that Defendants wrongfully interfered with the legal rights of Plaintiffs.
Liability for nuisance is distinguishable from negligence liability. The former, as discussed supra, is predicated upon unreasonable injury, and the latter is predicated upon unreasonable conduct. Weida,
With respect to neighboring land owners or users, the Rhode Island Supreme Court has analyzed the existence of a legal duty and found that "as a general proposition, each possessor of land owes to those outside the premises a duty to use reasonable care to prevent them from being *Page 30
injured as a result of activities on their property."Volpe,
As this Court finds that there was no breach of duty, proximate cause or damages to Plaintiffs need not be addressed.
Counsel for the prevailing party shall submit an appropriate judgment for entry in accordance with this decision.