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HomeMy WebLinkAbout06_Annual Review of Hoag DA_PA2009-064CITY OF NEWPORT BEACH ZONING ADMINISTRATOR STAFF REPORT September 27, 2018 Agenda Item No. 6 SUBJECT: Annual Review of Hoag Development Agreement (PA2009-064) SITE LOCATION: 1 Hoag Drive APPLICANT: Hoag Memorial Hospital Presbyterian OWNER: Hoag Memorial Hospital Presbyterian PLANNER: Chelsea Crager, Associate Planner 949-644-3227, ccrager@newportbeachca.gov ZONING DISTRICT/GENERAL PLAN Coastal Land Use Category: PI-B Private Institutions (0.0 – 0.75 FAR) Coastal Zoning District: PC 38 (Hoag Hospital) General Plan: PI (Private Institutions) Zoning District : PC 38 (Hoag Hospital) PROJECT SUMMARY An annual review of Development Agreement No. 5 for Hoag Memorial Hospital Presbyterian, pursuant to Section 15.45.080 of the Municipal Code and Section 65865.1 of the California Government Code. RECOMMENDATION 1)Conduct a public hearing; 2)Find the annual review is exempt from the California Environmental Quality Act (“CEQA”) pursuant to Section 15321, Class 21 (Enforcement Actions by Regulatory Agencies) of the CEQA Guidelines, California Code of Regulations, Title 14, Chapter 3; 3)Receive and file the Annual Report of Development Agreement for Hoag Memorial Hospital Presbyterian (Attachment No. ZA 2); and 4)Find that the applicant has demonstrated good faith compliance with the terms of Development Agreement No. 5. DISCUSSION Section 15.45.080 of the Municipal Code requires the City to periodically review development agreements to determine if the applicant has complied with the terms of the 1 Annual Review of Development Agreement No. 5 (PA2009-064) Zoning Administrator, September 27, 2018 Page 2 Tmplt: 01/12/18 agreement. This review should be conducted at least once every 12 months and should occur in April pursuant to the development agreement. Consideration has been delayed to complete noise testing. The applicant is required to demonstrate good faith compliance with the terms of the agreement, and should the Zoning Administrator find that the applicant has not complied in good faith with the terms of the agreement; the Zoning Administrator should refer the matter to the City Council. Background Development Agreement No. 5 (DA) was signed in 1994, and it relates to the long-term development and expansion of Hoag Memorial Hospital Presbyterian (Hoag). In May 2008, the DA was amended to allow the hospital to increase the intensity of future development on the upper campus with a commensurate reductio n in intensity of future development on the lower campus. The Hoag Planned Community Development Plan was also amended in 2008 to reflect the amended DA and to require additional landscape screening improvements and noise mitigation. The term of the agreement has always been twenty-five (25) years and it expires in March 2019. The 1994 DA and the 2008 amendment are available online at: http://www.newportbeachca.gov/developmentagreements. The last annual review hearing was conducted on August 10, 2017. The Zoning Administrator found Hoag to be in good faith compliance with the Development Agreement. Annual Review On April 5, 2018, Hoag submitted its 2018 Development Agreement Annual Review Report (Attachment No. ZA 2) and a noise compliance report prepared by ARUP Noise Consultant. Staff reviewed and provided comments to Hoag. A revised noise report was submitted on August 14, 2018. On September 17, 2018, Hoag submitted a revised report to reflect noise measurements taken in September to account for additional noise mitigation installed after the first noise report. This most recent report, dated September 14, 2018, can be found as Attachment No. ZA 3. On September 17, 2018, Hoag and City staff met with representatives of the Villa Balboa and Versailles residential communities. Hoag provided a presentation summarizing landscape and noise abatement improvements over the past year. This presen tation is provided as Attachment No. ZA 4. A summary of the Development Agreement Annual Review Report is as follows. 2 Annual Review of Development Agreement No. 5 (PA2009-064) Zoning Administrator, September 27, 2018 Page 3 Tmplt: 01/12/18 1. Project Status Report (Section 1 of the Annual Review Report): A project status report includes various updates on the status of mitigation measure compliance and construction activities within the past year. Construction this past year has largely been limited to interior improvements with no significant new construc tion or expansion of buildings within the Hoag campus. A list of improvement projects and mitigation measure compliance is provided in the Project Status Report Section within Attachment No. ZA 3. 2. Lower Campus Landscaping Areas (Section 4 of the Annual Review Report): The submitted photos of the most recent annual review report show 2017 and 2018 conditions of various areas of the lower campus. On-going maintenance and increased watering has resulted in improved coverage and health of all the plantings. The Co-Gen green screen wall has been adequately implemented through a combination of the raised planters, additional vines, care, and watering. Staff found each of the landscape areas in compliance and has no ongoing concerns about landsca ping. Hoag shall continue their efforts going forward. Staff conducted a site inspection on May 3, 2018 , and verified the health and coverage of the plantings to be a significant improvement over the previous year’s condition. 3. 2018 Acoustical Measurement Test Report: A summary of the September 14, 2018, Annual Noise Report prepared by ARUP Noise Consultant is as follows: A. Nighttime noise measurements were taken at adjacent properties of Versailles and Villa Balboa to document the 2017/18 levels. Daytime measurements were not conducted as previous year’s measurements have suggested that mechanical equipment is not audible above ambient noise conditions. B. Nighttime measurements near both the main loading dock and dietary loading dock were taken and found to be in compliance with applicable standards. C. Co-Gen Plant in proximity to residences at Villa Balboa 1. The ARUP report shows that exterior noise measurements are in compliance with the 50 db(A) nighttime standard. 2. The ARUP report shows that interior noise to the most effected unit can exceed the nighttime 40 db(A) standard by one db(A). These levels were measured in an unfurnished dining room and with the window in the room open consistent with the interior noise measurement requirements of the Community Noise Control Ordinance. ARUP indicated that interior furnishings will reduce noise 3 Annual Review of Development Agreement No. 5 (PA2009-064) Zoning Administrator, September 27, 2018 Page 4 Tmplt: 01/12/18 levels. It is also important to note that the Co-Gen plant was operated at 100% during the testing, which is not the normal operating condition. During the previous year, there was only one week in July where Hoag was forced to operate the plant at 100% to maintain mandated climate controls for the hospital. Staff does believe the Co-Gen plant to be operated in violation understanding that the plant is normally operated close to 80% capacity and the unit in question is furnished. Staff recommends that noise from the plant be tested before the next review while operating under normal conditions within a furnished unit. It is important to note that there is a disagreement as to how interior noise measurements should be taken. The Community Noise Ordinance specifies that a window nearest the noise source be left in the open position when taking an interior noise measurement. Villa Balboa representatives suggest that the sliding glass door from the exterior balconies should be considered a window and left in an open position during testing. Staff’s position after conferring with the City Attorney’s office is that a sliding glass door is a door for the purposes of interior noise testing. D. Upper Central Plant near the residences at Versailles Condominiums: 1. Exterior noise measurements at the location representative of the nearest second floor balcony to the plant exceeds the exterior nighttime 50 db(A) standard by one db(A).This is consistent with 2017 measurements. The particular location is approximately 15 feet east of the south facing balcony and it is easterly of the building itself may not be entirely indicative of the sound of the southerly facing elevation of the building. Staff recommends that Hoag work more closely with Versailles before the next review to take a measurement from the balcony itself. 2. Hoag installed a roll down door to cover a large opening to the upper campus equipment yard as an additional noise abatement measure in August 2018. Since installation, the exterior noise measurement at the property line between the Upper Central Plant and the Versailles tennis courts has dropped by 2 db(A) to 50 db(A). This is in compliance with the nighttime standard and represents a 3 db(A) decrease from 2017 measurements. 3. The ARUP report shows that all other exterior noise measurements are in compliance with the 50 db(A) nighttime standard. Since the last annual review, Code Enforcement staff has received one noise complaint in October 2017, related to property maintenance during permitted hours. Only one complaint during the past year is consistent with the previous year and an improvement over years prior and is evidence of Hoag’s ongoin g commitment to controlling their operations and vendors appropriately. 4 Annual Review of Development Agreement No. 5 (PA2009-064) Zoning Administrator, September 27, 2018 Page 5 Tmplt: 01/12/18 4. Co-Gen Weather Plume Report (Section 3 of the Annual Review Report): Hoag continues to operate the Co-Gen facility in concert with the weather station to reduce the water vapor plume from the cooling towers. Plume reduction protocols continue to operate between 7 a.m. and 7 p.m. starting November 1, 2017, through March 31, 2018. STAFF RECOMMENDATION After reviewing the attached annual report and its supplemental noise reports, Hoag’s willingness to continue to address its operational noise, and improvements to the planting and maintenance of the lower campus’s landscaping areas, staff believes that Hoag Memorial Hospital Presbyterian has remained in good faith compliance with the terms of Development Agreement No. 5. ENVIRONMENTAL REVIEW This annual review is exempt from the California Environmental Quality Act (“CEQA”) pursuant to Section 15321, Class 21 (Enforcement Actions by Regulatory Agencies) of the CEQA Guidelines, California Code of Regulations, Title 14, Chapter 3, because it has no potential to have a significant effect on the environment. This section exempts actions by regulatory agencies to enforce or revoke a lease, permit, license, certificate, or other entitlement for use issued, adopted, or prescribed by the regulatory agency or enforcement of a law, general rule, standard, or objective, administered or adopted by the regulatory agency. PUBLIC NOTICE Notice of this review was published in the Daily Pilot, mailed to all owners of property within 300 feet of the boundaries of the site (excluding intervening rights -of-way and waterways), including the applicant, and posted on the subject property at least 10 days before the scheduled hearing, consistent with the provisions of the Municipal Code. Additionally, the item appeared on the agenda for this meeting, which was posted at City Hall and on the City website. APPEAL PERIOD: An appeal or call for review may be filed with the Director of Community Development within 14 days following the date of action. For additional information on filing an appeal, contact the Planning Division at 949-644-3200. 5 Annual Review of Development Agreement No. 5 (PA2009-064) Zoning Administrator, September 27, 2018 Page 6 Tmplt: 01/12/18 Prepared by: JC/cc Attachments: ZA 1 Vicinity Map ZA 2 April 15, 2018 Hoag Development Agreement Annual Report ZA 3 September 14, 2018 Noise Compliance Report ZA 4 September 2018 Hoag Presentation 6 Attachment No. ZA 1 Vicinity Map 7 VICINITY MAP Annual Review Hoag Development Agreement Review (PA2009-064) 1 Hoag Drive Subject Property 8 Attachment No. ZA 2 April 15, 2018 Hoag Development Agreement Annual Report 9 Development Agreement Annual Review Hoag Memorial Hospital Presbyterian April 1, 2017 thru March 31, 2018 Prepared for: The City of Newport Beach 100 Civic Center Drive, Newport Beach, Calif. 92660 Prepared by: Hoag Memorial Hospital Presbyterian One Hoag Drive Newport Beach, CA 92663 10 Development Agreement Annual Review April 1, 2017 thru March 31, 2018 Hoag Memorial Hospital Presbyterian Prepared for: The City of Newport Beach 100 Civic Center Drive Newport Beach, CA 92660 Prepared by: Hoag Memorial Hospital Presbyterian One Hoag Drive Newport Beach, CA 92663 1. Project Status Report 2. Landscaping Photos (Attachment 1) 3. Acoustical Measurement Program Test Report (Attachment 2) 4. Co-Gen Weather Plume Reports (Attachment 3 and Flash drive) 11 3 Project Status Report Thru April 1, 2017 thru March 31, 2018 Tenth Annual Review of the Development Agreement Between the City of Newport Beach And Hoag Memorial Hospital Presbyterian Introduction & Overview On April 22, 2008, the City of Newport Beach (“City) approved an amended Development Agreement between the city of Newport Beach and Hoag Memorial Hospital Presbyterian (“Hoag”) which is known as the “Amendment to the Restated Development Agreement No. 6”. This Amended Development Agreement was adopted by Ordinance No. 2008-10 on May 13, 2008. Per Section 5.2 of the Amended Development Agreement: “The Annual Review shall be conducted at a public hearing noticed in accordance with the provisions of Chapter 15.45 of the Newport Beach Municipal Code. Annual Reviews should be scheduled in April of each year”. This Amended Development Agreement was part of Hoag’s Master Plan Update which included revised Development Agreement provisions, a revised Planned Community Text (“PC Text”) and associated standards, and certification of the Supplemental Environmental Impact Report (“SEIR”) with mitigation measures. The Supplemental Environmental Impact Report (SCH No. 1991071003) was certified by adoption of City Council Resolution No. 2008-27. As part of the SEIR adoption, a Mitigation Monitoring & Reporting Program was required which shall be utilized as the basis for the Development Agreement Updates as it relates to mitigation measures. For the purposes of this Development Agreement update, and those subsequent annual updates, this update shall serve as the Tenth Annual Review for the Amendment to the Restated Development Agreement No. 6 Project Status for the Tenth Development Agreement Annual Review As will be described in detail below, over the last year, Hoag has made a diligent, good faith effort in completing as many of the mitigation measures and associated requirements for both the Development Agreement & Planned Community Text as required in this timeframe. Development Agreement Specific Terms & Obligations In the separate terms of the Development Agreement requirements (not found in either Mitigation Measures of PC Requirements), the following have been completed: Section 5.4 “5.4 Mitigation Review – The annual review shall include a detailed report of compliance with the various conditions and mitigation measures contained with the mitigation monitoring plan. The report shall also include a noise regulation compliance assessment that includes noise measurements prepared by a qualified noise consultant on a yearly basis. The noise assessment shall identify noise regulation compliance issues 12 4 and recommended measures to abate any noncompliance. The report shall include an analysis of the view impacts of buildings constructed in comparison to the anticipated views depicted in the EIR. Hoag shall be found in compliance with this Agreement unless the City Council determines, based upon evidence presented at the Annual Review, that Hoag has not complied with all mitigation measures and conditions including those imposed as a result of subsequent environmental analysis, applicable to the grading of, or building on, the Property as of the date of the Annual Review.” Hoag has complied with this section of the Amended Development Agreement with the submittal of this detailed report which demonstrates good faith compliance with the various conditions and mitigation measures contained within the mitigation monitoring plan, as noted below. Additionally, Hoag has complied with noise regulation compliance assessments. A noise analysis was performed at Versailles on March 12, 2018. As you will see in the report (Attachment 2), the Versailles sprinklers were on during the entire time of testing which affected the sound measurement. Although Hoag believes we would be meeting and below the 50dB threshold, Hoag has decided to reschedule another test, coordinating with Versailles to ensure the sprinklers and all other noise is turned off. For the cogeneration noise regulation compliance assessment, after several attempts to schedule with the Villa Balboa Home Owners’ Association and residents, starting on February 5, 2018, Hoag proceeded with the testing that was scheduled at Versailles only. On February 26, 2018, The Villa Balboa Home Owners’ Association verbally requested Hoag not to do sound testing this year, indicating that we have been acting in good faith compliance with the Development Agreement and that they had extenuating circumstances with coordinating the testing. This testing report will be known as Attachment 2. The subsequent report for a repeat test for Versailles will be submitted as soon as possible as an Addendum to the Development Agreement Annual Review. No view analysis was necessary for this Annual Development Agreement review, as only interior building remodels have occurred and there were no new additions on the Hoag Campus during this timeframe. 2018 Update Construction activities have been largely limited to interior tenant improvements with no new buildings or expansions taking place in this year. These improvements have included the following items: Central Plant Acoustical Louvers: Installed acoustical louvers at all air openings in the central plant to reduce sound travel from the inside of the central plant. The louvers reduced the noise level at the property line incrementally and was completed in June 2017. Cooling Tower Splash Attenuation Project: Installed a splash attenuation system in the central plant cooling tower basins, completed in August 2017. The attenuators greatly reduced the dB level around the plant and also contributed to the overall noise reduction for the Versailles neighbors. Mechanical/Facility/Infrastructure Upgrades: Various projects scheduled throughout the Newport Beach Campus addressing routine repairs and refurbishment of the infrastructure. Some projects include air handler upgrades, flooring replacements, and building management system upgrades. 13 5 Cancer Center CT Scanner Replacement: Tenant improvements to accommodate an upgrade of services. Project was completed June 2017. Main OR / PACU renovation- Provide 2 new ORs and the replacement of the 14 bay PACU with the latest technologies suited for Brain and Spine surgery and to build a new Recovery Room in an existing space in the hospital. PACU occupancy completion expected June 15, 2018. OR replacement will start July 2018 and is scheduled for completion in February 2019. Acute (Physical) Rehabilitation Unit- Provide a dedicated department for the acute physical therapy needs of our patients in an existing area of the hospital. Therapy garden is being built between the Women’s Pavilion and the North Building. Scheduled completion is for May 2018. Women’s Pavilion Cosmetic Interior Renovation: Refreshing all patient rooms and corridors in the Women’s Pavilion. Project is ongoing through July 2018. HHNB Nurse Call Replacement: Complete replacement of the Newport Beach nurse call system/tracking system. The project has been ongoing for about two years, and is expected to be complete by the end of 2018. Get Well TV Replacement: Replacement and upgrade of TV system from analog to digital with additional patient amenities. The project was completed in July 2017. HHNB Seismic Upgrades: Continue with the review of multiple on-campus buildings under the guidelines of the OSHPD SPC 4-D seismic model, enabling the extension of building use as acute care beyond 2030. In material testing phase until August 2018. North Building Restack: Complete remodel and repurposing of the 2nd and 3rd floor of the North Building. Project is currently in the design phase. Construction to start end of year 2018. Breast Center Renovation: Cosmetic upgrades and an MRI Replacement. Construction to start in August 2018. Completion expected in the 1st quarter of 2019. Cancer Center Infusion: Renovation of 2nd and 3rd floor of the Cancer Center. Currently is design phase. OSHPD review through 2019. Section 8.5 – Cogeneration Plant Energy Curtailment “8.5 Hoag shall install a weather station capable of identifying ambient conditions necessary in documenting cogeneration plant and cooling tower operations. The weather station shall be tied into the cogeneration plant controls in order to maximize automatic responses to prevailing weather conditions, assisting in managing the operation changes and load shifting, as well as to provide periodic reports on plant operations. Hoag shall not construct or erect additional cooling towers within the Hoag Lower Campus. Hoag shall reduce the effective heat rejection by 33% at the existing cooling towers and such reduction shall be measured from a baseline (to be measured at the cooling towers) of operating three existing generators and absorption chiller at 100% of design capacity. This reduced capacity operation shall be implemented daily between November 1st and April 14 6 30th, between the hours of 7:00 AM and 7:00 PM when the relative humidity is equal to or less than 55 degrees Fahrenheit.” 2018 Update: Hoag has complied with all requirements regarding the Cogeneration Plant Energy Curtailment and has attached a letter from Hoag’s chief engineer of record, Peter Moore, Yorke Engineering, which certifies the plant has been in operation in accordance with curtailment requirements as feasible. Daily Cogeneration Plant Reports for the dates of November 1, 2017 through March 29, 2018 are attached for your review. (Attachment 3 and Enclosed Flash Drive) Mitigation Measures and PC Text Requirements In that no new major construction or additions has occurred over the last year, Hoag’s focus is to fulfill the requirements that were oriented to noise mitigation and aesthetic improvement. For your reference, the relevant mitigation measures and PC Text requirements are addressed below. Mitigation Measure 3.4-9 Cogeneration Plant Noise Although the last sound testing showed compliance at the cogeneration plant, Hoag continues its diligence to operate and maintain the plant below the required sound levels. The Hoag team is focused on continually reducing the noise levels in and around the plant. Some of the ongoing improvements include:  A custom built sound enclosure has been installed around the flare blower.  Nightly rounds conducted by the operators outside the plant to ensure quiet operation.  Shutting down any excess cooling tower fans and motors on cooler nights.  Securing of engines when Hospital load decreases in the evenings.  Slowing down the engine room supply fan on cooler nights or when engines are secured.  Ensuring that scheduled maintenance is completed on time for all sound emitting equipment.  Ensuring that all cogen plant doors are properly sealed and closed tight. Note: On February 26, 2018, The Villa Balboa Home Owners’ Association verbally requested Hoag not to do sound testing this year, indicating that we have been acting in good faith compliance with the Development Agreement and that they had extenuating circumstances with coordinating the testing. Noise – West Hoag Drive Mitigation Measure: Reduce noise levels around the Central Plant In the last year no new structure or structures on the Upper Campus were constructed requiring the transfer of buildable square footage from the Lower Campus. 2018 update: As noted in the project section above, the Upper Campus central utility plant has installed acoustical sound attenuation louvers at the air openings and splash attenuators in the cooling tower basin. A noise analysis was performed at Versailles on March 12, 2018. The results of the analysis can be found in Attachment 2. Hoag believes that the numerous modifications made to the plant have been effective in achieving the city ordinance noise requirements. 15 7 Planned Community Requirements – Landscaping Lower Campus Area 7a – West Parking Area Islands 2018 update: The additional trees and increased island groundcover areas installed in the Sunset View Lot has substantially increased the visual quality of this area. They continue to flourish and are in good health. However, Hoag has recognized that there is one tree below standard in the Sunset View Lot which is slated to be replaced in April 2018 (See photos Attachment 1). Area 9 – North Slope above Retaining Wall 2018 Update: On-going maintenance of this area continues and remains compliant (See photos Attachment 1). Area 12 Pacific Coast Highway Green Screen This mitigation measure has been completely satisfied per the 2012 Development Agreement Update. 2018 Update: On-going maintenance of this area continues and has remained compliant (See photos Attachment 1). Area 13 – Future Parking Lot at base of Wall behind ATP Building 2018 Update: The grid arrangement of canopy shade trees intermixed with plant squares of drought tolerant shrubs continues to thrive, while on-going maintenance of this area continues, this area remains compliant (See photos Attachment 1). Hoag has found a colony of gophers so has initiated pest management and will replace a few damaged plants. Cogeneration Plant 2018 Update: On-going improvements in the growth and coverage of the vines and the trees that were planted last year have taken hold. The vines and trees are reaching full maturity and are providing optimal coverage. A continued maintenance and monitoring program is in place, which will continue to ensure the full maturity of the vines (See photos Attachment 1). 16 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 1 Hoag DA Update 2018 Picture # 1: Sunset Lower Parking Lot Landscape (2017) Picture # 2: Sunset Lower Parking Lot Landscape (2018) 17 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 2 Hoag DA Update 2018 Picture #3: Sunset Lower Parking Lot Re-Landscaping (2016) Picture # 4: Sunset Lower Parking Lot Re-Landscaping (2017) 18 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 3 Hoag DA Update 2018 Picture # 5: Lower Sunset Lot Tree Island (2017) Picture # 6: Lower Sunset Lot Tree Island (2018) 19 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 4 Hoag DA Update 2018 Picture # 7: Behind ATP Re-Landscaping (2017) Picture # 8: Behind ATP Re-Landscaping (2018) 20 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 5 Hoag DA Update 2018 Picture # 9: Cogen Upper Bluff / Green Screen (2017) Picture # 10: Cogen Upper Bluff / Green Screen (2017) 21 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 6 Hoag DA Update 2018 Picture # 11: Cogen Screen Wall (2017) Picture # 12: Cogen Screen Wall (2018) 22 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 7 Hoag DA Update 2018 Picture # 13: Cogen Planter (2017) Picture # 14: Cogen Planter (2018) 23 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 8 Hoag DA Update 2018 Picture # 15: 2nd Cogen Planter (2017) Picture # 16 2nd Cogen Planter (2018) 24 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 9 Hoag DA Update 2018 Picture # 17: 3rd Cogen Planter (2017) Picture # 18: 3rd Cogen Planter (2018) 25 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 10 Hoag DA Update 2018 Picture # 19: Upper Cogen Bluff (2017) Picture # 20: Upper Cogen Bluff (2018) 26 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 11 Hoag DA Update 2018 Picture # 21: Lower Cogen, Slope Replanted (2017) Picture # 22: Lower Cogen, Slope Replanted (2018) 27 2018 HOAG DA UPDATE – LANDSCAPING PHOTOS Attachment # 1 Created March 26th, 2018 12 Hoag DA Update 2018 Picture # 23: Infill Shrubs Upper Cogen Slope (2017) Picture # 24: Infill Shrubs Upper Cogen Slope (2018) 28 LOS ANGELES/ORANGE COUNTY/RIVERSIDE/VENTURA/FRESNO/OAKLAND/BAKERSFIELD 31726 Rancho Viejo Road, Suite 218 ▼ San Juan Capistrano, CA 92675 ▼ Tel: (949) 248-8490 ▼ Fax: (949) 248-8499 April 2, 2018 Erik Lidecis Manager of Utilities/Operations Hoag Memorial Hospital Presbyterian One Hoag Drive Newport Beach, CA 92658 E-mail: erik.lidecis@hoag.org Subject: City Mitigation Measure – Cogen Plume Review Monitoring Period: November 1, 2017 – March 31, 2018 Hoag Memorial Hospital Presbyterian (Hoag), Newport Beach, CA Dear Mr. Lidecis: Yorke Engineering, LLC (Yorke) reviewed the meteorological data and cooling tower operating data for the subject period to evaluate Hoag’s compliance with Section 8.5 of the Development Agreement (“Agreement”). SUMMARY Meteorological data was collected from the weather station located at the cogeneration plant for the period starting November 1, 2017 and ending March 31, 2018 (“Monitoring Period”). Cooling tower operating data is available for the period November 1, 2017 – March 31, 2018. The data for this period shows that whenever the ambient temperature was less than or equal to 55 F and humidity was greater than or equal to 60%, cooling tower heat rejection was reduced at least 33% from the maximum heat rejection capacity. According to graphed data (see attachments), there were no instances during which the temperature and humidity reached plume conditions and the cooling towers exceeded 46.4 MMBtu/hr (67%) heat rejection. Cooling tower heat rejection data was unavailable for the period starting at 4 PM on February 6th to 11 AM on February 7th. However, meteorological data was available and confirmed plume conditions were not reached. Based on the available data, Hoag complied with the Agreement. BACKGROUND Hoag is party to a Development Agreement with the City of Newport Beach entitled Cogeneration Plant Energy Curtailment in which it agrees to curtail cogeneration plant operations when certain meteorological conditions exist that may result in the formation of a visible plume from the cooling towers. Section 8.5 of the agreement requires Hoag to install a weather station and monitor temperature and humidity. Between November 1 and April 30, between the hours of 7:00 AM and 7:00 PM, whenever the relative humidity is greater than or equal to 60% and ambient temperature is less than or equal to 55 F, Hoag shall reduce the effective heat rejection at the cooling towers by 33% from maximum design capacity. 29 Erik Lidecis, Hoag Hospital April 2, 2018 Page 2 of 3 Cooling Tower Heat Rejection Calculation Heat rejection for the cooling towers is calculated as follows: Q = 500 x (Flow 11 + Flow 12 + Flow 13 + Flow 14) x (Temperature In – Temperature Out) Where:  Q = heat rejection rate (Btu/hr)  Flows 11 – 14 are the water pump flow rates (gal/hour) for each of the four cooling towers;  Temperature In is the water inlet temperature (F) to the cooling towers;  Temperature Out is the water outlet temperature (F) from the cooling towers. Cooling Tower Maximum Capacity Maximum cooling capacity is calculated assuming all four water pumps operate at 3,150 gallons per minute, and the maximum difference between inlet and outlet temperatures is 11 F. Qmax = 500 (3150 + 3150 + 3150 + 3150) (11)/1,000,000 = 69.3 MMBtu/hour Heat Rejection Percentage Heat rejection is calculated on an ongoing basis as the combined heat rejection of the four cooling towers. The percentage reduction from maximum is calculated as: Q% reduction = (Q - Qmax)/Qmax CONCLUSION 1. Hoag operated weather stations that collected temperature and humidity data during the Monitoring Period. 2. Temperature and humidity data were provided to the cogeneration system operators who are directed to reduce heat rejection from the cooling towers by at least 33% from maximum capacity during the hours of 7:00 AM to 7:00 PM whenever temperature is less than or equal to 55 F, and humidity is greater than or equal to 60%. 3. For the period of available cooling tower data, November 1, 2017 – March 31, 2018, there were no incidents in which the cooling tower heat rejection was less than 33% reduced from maximum when temperature and humidity both exceeded their trigger thresholds. 30 Erik Lidecis, Hoag Hospital April 2, 2018 Page 3 of 3 Should you have any questions or concerns, please contact me at (949) 248-8490 x226. Sincerely, Corina Chang Senior Engineer Yorke Engineering, LLC CChang@YorkeEngr.com cc: Peter Moore, Yorke Engineering, LLC Corey Luth, Yorke Engineering, LLC Attachments: 1) Section 8.5, Restated Development Agreement, Cogeneration Plant Energy Curtailment 2) Daily Reports: Temperature & Humidity & Cooling Tower Heat Rejection (November 1, 2017 – March 31, 2018) 31 Attachment No. ZA 3 September 14, 2018 Noise Compliance Report 32 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 1 Your ref Our ref File ref 12777 West Jefferson Boulevard Suite 100 Building D Los Angeles CA 90066 United States of America t +1 310 578 4400 d +1 310 578 4592 f +1 310 861 9029 matthew.wilkinson@arup.com www.arup.com Roxanna Bryant Hoag Memorial Hospital Presbyterian One Hoag Drive, Newport Beach, CA 92658 14 September 2018 Dear Roxanna Hoag Hospital Newport Beach Annual Noise Reporting As requested, please find attached a summary report detailing the recent nighttime noise measurements at Hoag Hospital. Please do not hesitate to contact us with any queries. Yours sincerely Matt Wilkinson Senior Consultant cc Douglas Nordham Erik Lidecis 33 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 2 Executive Summary • As part of their development agreement with the city of Newport Beach, Hoag Hospital performs yearly monitoring of the noise levels from the hospital property. • Arup has conducted nighttime noise measurements at the Hoag Memorial Hospital Presbyterian and at adjacent properties (Versailles and Villa Balboa Communities) in Newport Beach, CA to document the 2018 levels. Daytime measurements were not conducted as previous year’s measurements (by others) have suggested that mechanical equipment is not audible above traffic noise and other sources during the day. • Originally measurements were performed on March 12th 2018, however, the measurements at Versailles were affected by sprinklers at the condo development. In addition, it was originally understood that measurements at Villa Balboa may not be required, however, these have been requested by the city. Further noise level measurements were made on April 17th and June 19th 2018. • At Villa Balboa, measurements were conducted on the balcony and the interior of a residence (#313) located on the façade facing the CoGen Plant. (This was a different location from previous years, the bedroom balcony was not accessible due to construction). • The external level measured at Villa Balboa was 47dBA Leq and compliant with the standards established by the City of Newport Beach Municipal Code. • The interior noise level measured at Villa Balboa marginally exceeded the City noise level requirement. This level was measured in the dining room of the unoccupied unit which was unfurnished, and with the large sliding window fully open. There was no window in the bedroom and therefore a measurement with a window open in that space was not possible. • At the Upper Central Plant, measurements were made at the property line and at an elevated location at approximately 20ft above the raised planter area representative of a 2nd floor balcony at the Versailles property. This location was chosen as it was similar to the previous year’s measurements. The level measured at this elevated position at Versailles was 51dBA Leq. This overall level is the same as the levels measured in 2017. However, the upgrades to the central plant have reduced the noise levels at frequencies above 1000Hz and therefore the overall character of the noise has changed. • Noise measurements were also made in the loading dock and these measurements were found to be compliant. 34 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 3 • A roll up door with seals has been installed at the Upper Central Plant to provide acoustic screening between mechanical equipment and the adjacent Versailles property. Follow up measurements were performed on September 5th, 2018 at the property line location directly opposite and at the façade location at Versaille. The measured noise levels at each location were 50dBA at the property line and 51dBA at the façade. 35 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 4 1 Introduction This report was prepared by Arup North America Ltd (“Arup”) at the request of and for the benefit of Hoag Memorial Hospital Presbyterian (“Hoag”) in Arup’s contractual capacity as Acoustic Consultant to conduct nighttime noise measurements at the adjacent residences for the purposes of Hoag’s annual reporting obligation to the City of Newport Beach (“the Report”). The limited purpose of this Report is to present a summary of recent ambient noise surveys conducted by Arup at Hoag Memorial Hospital Presbyterian in Newport Beach, CA on March 12th, April 17th, June 19th and September 5th 2018. The Report takes into account Hoag’s particular instructions, requirements and priorities at this time and is meant to be read as a whole. As part of the development agreement (DA) between the hospital and the adjacent residential developments, Hoag monitors the noise levels yearly from mechanical equipment noise. The DA states that noise from the Hoag Hospital property must not exceed the code requirements from Newport Beach City Municipal code. The two most significant noise generating sources on the Hoag Hospital Campus are the Upper Central Utility Plant Building and the CoGen Plant Building. As shown in Figure 1 below, the Upper Central Plant building is located at the Northeast of the Hoag Hospital Campus. It is bounded by Hospital Road to the North and the Hoag Road to the West. The Versailles community is located to the west of Hoag Road and the nearest residential building is highlighted below. 36 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 5 Figure 1 - Location of the Upper Central Utility Plant Building (highlighted blue) and the nearest noise sensitive receiver (highlighted in red). The red-dotted line shows the approximate location of the property line. [Source: Google Earth] The CoGen Plant is located to the southeast of the Hoag Hospital Campus adjacent to Superior Avenue, Pacific Coast Highway. The most southeasterly building located at the Villa Balboa development is the nearest noise sensitive receiver in this case. The relative locations are shown in Figure 2 below. 37 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 6 Figure 2 - Location of the CoGen Plant Building (highlighted blue) and the nearest noise sensitive receiver (highlighted in red). The red-dotted line shows the approximate location of the property line. [Source: Google Earth] 2 City of Newport Beach Noise Standards The most recent amendment to the development agreement between Hoag Hospital and the City of Newport Beach states in clause 1.17 that the noise generated and originating from the property be governed by the City Municipal Code. The relevant sections of Chapter 10.26 of the City Municipal Code are quoted or described in Section 2.1 below. 2.1 Noise Criteria Noise level criteria for external and internal areas of noise sensitive spaces established by the City of Newport Beach Municipal Code are quoted below: Section 10.26.025 - Exterior Noise Standards The following noise standards, unless otherwise specifically indicated, shall apply to all property with a designated noise zone: 38 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 7 NOISE ZONE TYPE OF LAND USE ALLOWABLE EXTERIOR NOISE LEVEL (Equivalent Noise Level, Leq) 7 a.m. to 10 p.m. 10 p.m. to 7 a.m. I Single-, two-or multiple-family residential 55 dBA 50 dBA II Commercial 65 dBA 60 dBA III Residential portions of mixed-use properties 60 dBA 50 dBA IV Industrial or manufacturing 70 dBA 70 dBA If the ambient noise level exceeds the resulting standard, the ambient shall be the standard. B. It is unlawful for any person at any location within the incorporated area of the City to create any noise, or to allow the creation of any noise on property owned, leased, occupied or otherwise controlled by such person, which causes the noise level when measured on any other property, to exceed either of the following: 1. The noise standard for the applicable zone for any fifteen-minute period; 2. A maximum instantaneous noise level equal to the value of the noise standard plus twenty (20) dBA for any period of time (measured using A-weighted slow response). C. In the event the ambient noise level exceeds the noise standard, the maximum allowable noise level under said category shall be increased to reflect the maximum ambient noise level. D. The Noise Zone III standard shall apply to that portion of residential property falling within one hundred (100) feet of a commercial property, if the intruding noise originates from that commercial property. E. If the measurement location is on boundary between two different noise zones, the lower noise level standard applicable to the noise zone shall apply. (Ord. 95-53 § 1, 1995; Ord. 95-38 § 11 (part), 1995) Section 10.26.030 Interior Noise Standards. A. The following noise standard, unless otherwise specifically indicated, shall apply to all residential property within all noise zones: NOISE ZONE TYPE OF LAND USE ALLOWABLE INTERIOR NOISE LEVEL (Equivalent Noise Level, Leq) 7 a.m. to 10 p.m. 10 p.m. to 7 a.m. I Residential 45 dBA 40 dBA III Residential portions of mixed-use properties 45 dBA 40 dBA 39 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 8 If the ambient noise level exceeds the resulting standard, the ambient shall be the standard. B. It shall be unlawful for any person at any location within the incorporated area of the City to create any noise or to allow the creation of any noise on property owned, leased, occupied or otherwise controlled by such a person which causes the noise level when measured on any other property, to exceed either of the following: 1. The noise standard for the applicable zone for any fifteen-minute period; 2. A maximum instantaneous noise level equal to the value of the noise standard plus twenty (20) dBA for any period of time (measured using A-weighted slow response). C. In the event the ambient noise level exceeds the noise standard, the noise standard applicable to said category shall be increased to reflect the maximum ambient noise level. D. The Noise Zone III standard shall apply to that portion of residential property falling within one hundred (100) feet of a commercial property, if the intruding noise originates from that commercial property. E. If the measurement location is on a boundary between two different noise zones, the lower noise level standard applicable to the noise zone shall apply. (Ord. 95-53 § 2, 1995; Ord. 95-38 § 11 (part), 1995) The measurement methodology described in the municipal code states that ‘the location selected for measuring interior noise levels shall be made within the affected residential unit. The measurements shall be made at a point at least four feet from the wall, ceiling or floor, or within the frame of a window opening, nearest the noise source. The measurements shall be made with windows in an open position. (Ord. 95-38 § 11 (part), 1995)’ 10.26.015 Decibel Measurement Criteria. Any decibel measurement made pursuant to the provisions of this chapter shall be based on a reference sound pressure of twenty (20) micropascals as measured with a sound level meter using the A-weighted network (scale) at slow response. (Ord. 95-38 § 11 (part), 1995). The ratio of sound pressures which we can hear is a ratio of 106:1 (one million:one). For convenience, therefore, a logarithmic measurement scale is used. The resulting parameter is called the ‘sound pressure level’ (Lp) and the associated measurement unit is the decibel (dB). As the decibel is a logarithmic ratio, the laws of logarithmic addition and subtraction apply. dBA is the unit used to define a weighted sound pressure level, which correlates well with the subjective response to sound. The ‘A’ weighting follows the frequency response of the human ear, which is less sensitive to low and very high frequencies than it is to those in the range 500Hz to 4kHz. In some statistical descriptors the ‘A’ weighting forms part of a subscript, such as LAeq for the ‘A’ weighted equivalent continuous noise level. 40 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 9 The Newport City Code uses a typical index for assessment for overall noise exposure, this is the equivalent continuous sound level, Leq. This is a notional steady level which would, over a given period of time, deliver the same sound energy as the actual time- varying sound over the same period. Hence fluctuating levels can be described in terms of a single figure level. 2.2 Site Ambient Noise Level In section 10.26.010 of the city code, the ambient noise level is defined as ‘the all- encompassing noise level associated with a given environment, being a composite of sounds from all sources, excluding the alleged offensive noise, at the location and approximate time at which a comparison with the alleged offensive noise is to be made.’ In this case the ambient noise level would be affected by sources such as traffic, aircraft and mechanical services equipment (from all buildings other than those located on the Hoag Hospital Campus). In order to determine the ‘ambient noise’ level representative measurements would need to be made at locations with representative levels of traffic and other such noise sources but with minimal contribution from hospital equipment and operations. Site ambient noise measurements were conducted (by others) during the 2016 measurements (‘2016 Acoustical Measurement Test Report’ - RS Acoustics). Locations were chosen to minimize the contribution from hospital equipment. The locations are shown in Figure 3 below together with the locations of the CUP and CoGen Plant buildings. Figure 3 - Locations for Ambient Noise Measurements (Measurements conducted by others, March 2016). 1 2 3 41 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 10 Location No. Location description Measured Noise Level, dBA Leq, 15min Daytime Nighttime 1 Superior Ave & Sunset View Park 58 50 2 Hoag Rd & Sunset View Park 62 54 3 Old Newport Blvd & Catalina Dr 69 54 Table 1 - Measured 'Ambient' Noise levels dBA Leq (by RS Acoustics) Section 10.26.025 of the municipal code states that the ambient noise level shall be the highest measured noise level if this exceeds the prescriptive code noise level. The representative noise levels measured at location 1 closest to the CoGen plant building suggest that the daytime level criterion shall be 58dBA and the nighttime level at this location shall be 50dBA. Similar measurements were not conducted during this year’s measurements. As the main noise generating source affecting the ambient level is likely to be traffic and the traffic systems have not been materially altered to change the flow of traffic, these levels can be assumed to be representative of the ambient levels for 2017. A representative ambient noise level was not measured in 2016 close to the location of the Upper Central plant, therefore the prescriptive levels from section 10.26.025 will be used as the criteria in this report at this location. 3 Survey Methodology 3.1 Dates and Times 3.1.1 Daytime Noise Levels Noise levels measured by others during the 2016 noise assessment note that they ‘observed the majority of ambient noise was due to traffic on Superior Avenue and Pacific Coast Highway, ocean waves, and noise from the underground transformer on Superior Avenue was also slightly audible. Noise from the cooling towers and cogeneration facility were inaudible during the daytime tests.’ (‘2016 Acoustical Measurement Test Report’ - RS Acoustics) The contribution from the mechanical equipment could not be effectively isolated from the ambient noise sources during daytime measurements. As the traffic systems do not appear to have been altered since these measurements were made, it is assumed that the contribution from traffic, the most dominant source, remains the same. In addition, the typical operation of the central plant has not increased over the 42 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 11 last year, and all efforts have been made to reduce noise levels where possible. It was therefore concluded that the mechanical equipment could still not be isolated from the daytime ambient noise, and the focus of the noise measurements should be limited to the nighttime noise levels. 3.1.2 Nighttime Noise Levels The most recent nighttime measurements were conducted by Jacqueline Le and Joey Panlertkitsakul from Arup on Wednesday, September 5th 2018 from 12am to 2:30am, with previous measurements at the loading dock and along west road measured during the same time periods on March 12th 2018. This is typically the time period with the lowest expected ambient/background noise (from traffic activity and other sources) to isolate equipment noise. 3.2 Survey Locations and Methodology 3.2.1 Upper Central Plant measurements Figure 4 - Nighttime measurement locations at Upper Central Plant [Source: Google Earth]. Attended measurements were conducted around the Upper Central Plant site (see Figure 4) at the property line. These locations were chosen to be representative of the property line measurement locations measured in previous years. Measurements were also made at an elevated position near the center of the façade of the nearest residential building in the adjacent Versailles gated community. This measurement location is representative of the levels which may be experienced at the nearest balcony area. These measurements were at least 15 minutes or more in duration, in order to extract the background noise levels of Hoag Hospital equipment without the contribution from transient events such as ambulance and traffic passbys. Location 1- Elevated at approx. 20’ above raised planter area, representative of 2nd flr balcony, 3-4ft from façade. Location 2 – Measured with microphone at approx. 5’ above ground level, at the approximate property line Location 3 – Measured with microphone at approx. 5’ above ground level, at the approximate property line Location 4 – Measured with microphone at approx. 5’ above ground level, at the approximate property line 43 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 12 3.2.2 CoGen Plant Measurements Attended measurements were made in accordance with the guidance in the City of Newport Beach Municipal Code Section 10.26.030 at Unit #313 in the Villa Balboa complex. A measurement was made at the balcony and within the li (as directed by the resident representative) in the unoccupied unit on the façade facing the CoGen Plant Building and representative of the unit with the worst case exposure to noise. Closest façade at Unit #313. 44 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 13 3.2.3 West Road/Loading Dock Measurements Figure 5 - Measurement locations on the West Road Attended measurements were made along the west road at the hospital to measure the noise levels generated by mechanical equipment associated with the loading docks and the hospital buildings. Locations were chosen to be in line with the measurements made in 2016 by RS Acoustics. Elevated positions were used to measure at a location closer to the elevation of the noise source. Location 8 – Microphone at elevated position close to the Hospital property line. Approximately 5-6ft from the Noise Barrier opposite loading dock. Location 7 – Microphone at elevated position close to the Hospital property line. Approximately 5-6ft from the Noise Barrier opposite west tower. Location 6 – Microphone at elevated position close to the Hospital property line. Approximately 5-6ft from the Noise Barrier opposite ancillary building. Location 5 – Microphone at 5ft above floor level opposite the dietary loading dock 45 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 14 3.3 Equipment Settings The following settings were applied to the equipment at each site during the measurements: CoGen Plant. • 4 Cooling Towers running, with 3 fans running. The fans were set to manual during the measurement period and the drives set to full speed. These operating conditions would only occur at extreme conditions and not typical. Upper Central Plant • The following equipment was operational during the tests. These operating conditions are representative of all year round conditions and will not be exceeded barring emergencies. These are the maximum nighttime operating conditions which were adopted as a result of the previous hearings. o 2 Chillers o 2 Cooling Towers – Fans set to manual at 80% speed o 3 Condenser pumps at 80% duty o Sand Filter off o Boiler room door closed 3.4 Equipment The equipment used for the measurements was as follows: • Rion NL-52 Sound Level Meter • Rion Preamplifier NH-21 • Rion Microphone UC-59 • Rion Calibrator type NC-74 • Rion Microphone Extension Cable EC-04B (30ft.) • Rion AS-70 waveform software The sound level meters and microphones used for these measurements were calibrated before and after use, to confirm there was no significant drift in meter response. The meters are regularly calibrated and this calibration is traceable to international standards. The noise levels were recorded as real time calibrated uncompressed audio (*.wav files) and post processed using the ‘Slow’ weighting required by the Newport Beach Municipal code. 46 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 15 4 Sound Level Results 4.1 Post Processing In order to isolate the steady noise levels generated by the equipment, measurements were taken to be longer than the required 15 mins and post processed to determine the level without transient events such as traffic. This is effectively the same process as manually “pausing” the measurement during these events but reduces the influence of manual measurement error to better isolate the steadier mechanical equipment noise source. Figure 5(i) below shows an example un-processed measurement with the transient events in the time history. The time history shown in Figure 5(ii) below is the same measurement with the transient events removed. Once the transient events have been removed the equivalent sound level (dBA Leq) is re- calculated to determine the noise level generated by the mechanical equipment. 47 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 16 =` Figure 6 – Villa Balboa Unit #313 Balcony measurement - before and after transient events (marked with red circles) have been removed (i) (ii) Transient events such as traffic pass-bys temporarily produce high noise levels Mechanical noise is a steady noise source and makes up the background noise level Mechanical noise is a steady noise source and still can be identified after transient events have been removed 48 Hoag Memorial Hospital Presbyterian Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 17 Figure 7 - Elevated measurement at Versailles approximately 20ft above raised planter area before and after transient events (marked with red circles) have been removed (i) (ii) 49 14 September 2018 Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 18 4.2 Subjective Observations The ambient noise levels during the measurement periods were dominated by the noise from mechanical services in both the CoGen plant area and the Upper Central Plant area. As can be seen from Figure 5 and 6 there were several traffic passbys during measurements. The dominant noise source along the west road was mechanical noise from hospital buildings. Other noise sources included distant aircraft noise, hospital activity and occasional distant site traffic. 4.3 Noise measurements 4.3.1 Upper Central Plant Location Date/Time Measured Noise Level, dBA Leq Newport City Code Requirement, dBA Leq Location 1, Elevated microphone position at 20ft above raised planter area, 3-4ft from the façade, representative of the nearest 2nd floor balcony. 6/19/18 - 4:16am 51 50 Location 4 – microphone 5ft above ground level at the property line between the tennis courts and the Upper Central plant. 6/19/18 - 1.29am 52 50 Location 3 – microphone 5ft above ground level at the property line location located between the façade of the Versailles condominiums and the Upper Central Plant. 3/12/18 - 2.22am 46 50 Location 2 – microphone 5ft above ground level at the property line close to the intersection of Hoag Rd and Hospital Road. 6/19/18 4.56am 48 50 Location 1, Elevated microphone position at 20ft above raised planter area, 3-4ft from the façade, representative of the nearest 2nd floor 9/5/18 2:22am 51 50 50 14 September 2018 Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 19 Location Date/Time Measured Noise Level, dBA Leq Newport City Code Requirement, dBA Leq balcony. – After installation of roll up door. Location 4 – microphone 5ft above ground level at the property line between the tennis courts and the Upper Central plant. – After installation of roll up door. 9/5/18 1:00am 50 50 Table 2 - Measured Noise Levels, 15 minute dBA Leq (re 20µPa) 4.3.2 CoGen Plant Building Location Date/Time Measured Noise Level, dBA Leq Newport City Code Requirement, dBA Leq Villa Balboa, Unit #313, Outdoor Balcony 6/19/18 - 2:17am 47 50 Villa Balboa, Unit #313, Inside dining room with large sliding window fully open (microphone at 4ft from window opening) 6/19/18 - 3.04am 41 40 Table 3- Measured and Predicted Noise Levels in Unit #313, 15 minute Leq , dBA (re 20µPa) 4.3.3 West Road/Loading Dock Measurements Location Date/Time Measured Noise Level, dBA Leq Development Agreement Requirement, dBA Leq Location 5, microphone 5ft above ground level opposite the dietary loading dock 3/12/18 – 1.20am 48 55 51 14 September 2018 Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 20 Location Date/Time Measured Noise Level, dBA Leq Development Agreement Requirement, dBA Leq Location 6 – Microphone located at elevated position on telescoping tripod opposite the ancillary building 3/12/18 - 1.02am 52 55 Location 7 – Microphone located at elevated position on telescoping tripod opposite West Tower 3/12/18 - 12.39am 48 55 Location 8 – Microphone located at elevated position on telescoping tripod opposite the main loading dock 3/12/18 - 12.15am 50 55 4.4 Discussion 4.4.1 CoGen Plant Noise levels measured at the external location at Villa Balboa are below the 50dBA Leq nighttime criterion required by the Newport Beach City Noise Code. Noise levels measured at the interior location at Villa Balboa exceed the nighttime internal noise code requirements by 1dB. It should be noted that these measurements were taken in an unfurnished dining room and with the large sliding window in this area fully open. This measurement was made at the minimum required distance from the window. Noise levels further from the opening are likely to be below this level and compliant with the noise code requirements. If this apartment was fully furnished with a carpeted floor, this could potentially halve the reverberation time. Although the level at 4ft from the open window may be dominated by the direct noise level, the reverberant noise level build up would be reduced with the soft furnishings and it is reasonable to expect that a 1dB reduction could be achieved. In our experience, both the exterior and interior measurements would not both be measured to determine compliance. The external measurement is generally set to ensure that the internal level can be achieved. 4.4.2 Upper Central Plant Noise levels from the Upper Central Plant measured at the Versailles property line adjacent to the residential façade at street level are below the 50dBA Leq nighttime criterion required by the Newport Beach City Noise Code. The Noise level measured opposite the entrance to the Upper Central plant and adjacent to the tennis courts exceeded the nighttime levels by 2dB. It is assumed that, as per the 52 14 September 2018 Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 21 definition of exterior noise level measurement locations being ‘a private yard, patio, deck or balcony normally used for human activity’, this location is not representative of any of these areas. The Noise level measured at the elevated position at the Versailles façade exceeds the nighttime requirements by 1dB. This 1dB exceedance of City of Newport Beach Municipal Code, is not subjectively audible. The human ear does not generally perceive decibel differences of less than 3dB. Hoag Hospital has made significant material changes at the Upper Central Plant to reduce noise levels at the property line and façade. These upgrades have been completed since last years’ measurements. These include: • Adding acoustically attenuating louvers at the boiler room openings • Mechanical intervention to reduce noise from falling water. The subjective character of the noise has changed as a result of the acoustic interventions at the CUP, however overall noise levels have not significantly reduced. The low frequency noise levels, predominantly from the operation of the Cooling Tower fans, remain at a similar level. A comparison of the noise levels measured at the Versailles façade location in 2016, 2017 and 2018 is shown in Figure 8 below (It should be noted that the operating conditions for the 2016 values was slightly different from the following years, the CTs were both running at 75%). The noise levels above 1000Hz have reduced as a result of the work performed at the central plant. 53 14 September 2018 Hoag Hospital Newport Beach Annual Noise Reporting CoGen Plant and Upper Central Plant Noise Measurements R03 | Rev B | 14 September 2018 | Arup North America Ltd \\GLOBAL.ARUP.COM\AMERICAS\JOBS\L-A\250000\251950-00\4_INTERNAL_PROJECT_DATA\4-05_REPORTS_NARRATIVES\2018-06-19_2018 NOISE TESTING\2018-09- 14_R03_HOAGHOSPITAL_COGENCENTRALPLANTNOISETESTING_REV_C_ISSUE.DOCX Page 22 Figure 8 - Spectral noise levels measured at the Versailles façade There is still a noticeable low frequency element audible at the Versailles location due to the line of sight to the CT fans. Testing has been performed previously at equipment settings which are understood to be representative of the estimated maximum operation during the year. Testing was performed on 17 April 2018 with only a single CT operational due to the weather conditions on that day. This measurement achieved the Newport City Code noise requirement which suggests that the requirements may be achievable when the operational duties are less than the maximum settings. Further to these tests, Hoag Hospital has installed a roll down door near the entrance of the Upper Central Plant to provide further acoustic screening from mechanical equipment. Noise levels were measured after the installation of this door. As a result, the noise level at the property line location has reduced by 2dB, meeting Code requirements. 4.5 Clarifications Arup’s services are performed within the limits of the project as prescribed by Hoag Memorial Hospital Presbyterian in a manner consistent with the level of skill and care currently exercised by members of the same profession practicing in similar conditions in the same locality. No other warranty, either expressed or implied, is included hereunder. The Report has been prepared for the exclusive benefit of Hoag and no other party. No responsibility is undertaken to any third party in relation to the Report and Arup assumes no liability to third parties with respect to the use of any information, opinions or findings disclosed in the Report. END OF REPORT 54 Attachment No. ZA 4 September 2018 Hoag Presentation 55 56 57 58 59 60 61 62 63 64 65