Analyzing a complex oil spill at an Ottawa hospital
Transcription
Analyzing a complex oil spill at an Ottawa hospital
Spill Management Analyzing a complex oil spill at an Ottawa hospital By Dan McNicoll, Mark McCalla, Kathy O’Neill and Philippe Marleau n January 2009, a large furnace oil spill occurred beneath the Montfort Hospital which is situated in the east end of Ottawa, Ontario. During a $300M expansion program, a 50,000 litre underground storage tank (UST) was installed just north of the “D Wing” building of the hospital complex. The UST supplies furnace oil to the hospital’s heating plant. A remote fill station was located approximately 20 m from the tank. During final construction activities, the remote fill pipe for the furnace oil tank was inadvertently severed without being repaired. In January 2009, during a period of peak demand, the tank was filled five times before strong petroleum odours were noticed by the basement staff. The hospital immediately evacuated the affected staff and retained exp Services Inc. (exp) to determine the source of the furnace oil odours and to direct emergency response measures. Emergency response As part of the emergency response program, indoor air samples were collected, portable air scrubbers were brought in, furnace oil fill procedures were immediately ceased, and an investigation was conducted to determine the source of the furnace oil odours. After some remote video camera work, a break in the pipe was confirmed. The furnace oil UST and piping was subsequently removed and 1,200 tonnes of furnace oil impacted soil were removed beneath the pipe break and around the UST. Unfortunately, a significant amount of furnace oil was determined to have migrated directly beneath D Wing. Interior sumps and sewers were inspected and temporary oil recovery/groundwater treatment measures were immediately implemented, where necessary. Subsurface Investigation Exp conducted a detailed forensic investigation to determine the most likely cause of the pipe break and calculated that approximately 22,000 L of furnace oil had leaked into the subsurface environment. Due to pending legal actions I 64 | September 2011 Aerial view of hospital. by the insurer, the cause of the pipe break cannot be disclosed at this time. A comprehensive subsurface investigation was performed to delineate the extent of the subsurface impact. In total, 28 interior and exterior overburden wells and 33 interior and exterior bedrock wells were constructed on the site, using both conventional and unconventional drilling techniques. The site was found to be underlain by approximately 1 - 2 m of granular fill material, overlying native silty clay, and silty glacial till. The till, in turn, is underlain by Ottawa Formation limestone bedrock at depths ranging from 4 m to 10 m below grade. A major geological fault also exists beneath the site and is thought to pass directly beneath the affected D Wing building. Bedrock groundwater flow direction was found to be from northeast to southwest, or from the neighbouring residential houses towards the hospital. The overburden groundwater regime was found to be discontinuous and, where present, was calculated to be flowing to the south under a gradient of approxi- mately 0.03 m/m. The furnace oil plume was found to have migrated beneath 75% of the D Wing building footprint and towards the adjacent off-site apartment building property, located approximately 50 m to the south. Large concrete earthquake ballast slabs situated beneath the building served to channel and funnel the oil, making its delineation (and subsequent recovery) very difficult. Stakeholders The hospital’s medical records, decision support, and medical affairs departments are located directly over the area affected by the spill. Health and safety issues for these departments and others located in the new wing needed to be addressed throughout the remediation process. Measures are still ongoing to ensure that all concerns are met. Hospital support services such as Facilities and Occupational Health and Safety were key partners in the management of the situation, as was the Montfort Hospital Governance. Another important stakeholder was the hospital’s major tencontinued overleaf... Environmental Science & Engineering Magazine Spill Management Tank removal. ant, the Department of National Defense. The hospital is surrounded by a neighbouring community whose residents have their own well and septic systems. Monitoring measures were put in place and regular community communication sessions were offered to address their concerns. A residential apartment building is located directly to the south of the hospital, so owner and resident concerns regarding the spread of the spill onto their property needed to be addressed on an ongoing basis. Regular communication with various ministries including Ontario Health and Long Term Care, the Ontario Ministry of the Environment (MOE), The Technical Standards and Safety Authority, the City of Ottawa and other governing bodies, had to be addressed. Because the project was not fully completed at the time of the spill event, coordination was needed with the general contractor and prime consultant. Finally, as the ultimate payer, the insurance company, the insurance adjuster, and their broker representative were included in all aspects of communication and overall management of the situation. Remedial options analysis Based on the findings of the subsurface investigation, a Remedial Options Analysis (ROA) was performed to select 66 | September 2011 the most appropriate solution. The ROA included a comprehensive review of available remedial technologies; the selection of four preferred technologies or options; preliminary cost estimates for each option; estimates of the anticipated operating period; and, an estimate of hospital staff displacement duration. The ROA focused on a phased approach to the overall site remediation program. The first phase was concentrated on the recovery of furnace oil product. The second phase consisted of the establishment of the final remediation objectives (i.e., background, potable/ non-potable water, or site specific criteria). The third phase, if required, would be to examine additional treatment technologies that could be used to reduce the length of time required to attain the desired final remediation objectives once all of the furnace oil product had been recovered (i.e., the addition of surfactants, oxygen releasing compounds, etc.). Based on the site conditions, it was agreed that the provincial potable groundwater criteria would be used as the remediation criteria. The four remedial options that were ultimately selected for more detailed costing were 1) natural attenuation; 2) multi-phase extraction (MPE); 3) partial excavation and MPE; and 4) complete excavation. The preferred remedial option that was ultimately selected was MPE. MPE remediation system Exp designed the multi-phase extraction system to recover free phase furnace oil; petroleum impacted groundwater; petroleum vapours beneath the building; and to enhance biological degradation of the residually impacted soil beneath the building that could not be removed. The MPE system involved the installation of 16 interior recovery wells within the basement of the building and 13 exterior recovery wells along the southern property boundary to prevent off-site contaminant migration. All of the recovery wells are equipped with pneumatic submersible pumps, which recover oil, water and vapours from beneath the building and direct them to an exterior, on-site facility for treatment. Piping from each recovery well is directed beneath portions of the floor, within wall cavities, and above the ceiling. Installation of this piping distribution system within an operating hospital required extensive planning, coordination, security, installation of elaborate infection control barriers, and testing to demonstrate containment and treatment of petroleum vapours within the barriers prior to their removal. Pilot and full scale remediation Prior to the design of the full scale MPE system, a readily available, small packaged MPE unit was used on-site in order to provide some immediate control of the subfloor vapour emissions; collect and recover some of the furnace oil product; confirm the appropriateness of using MPE at this location; obtain site specific hydraulic conductivity and air permeability measurements; assist in sizing of the vacuum blowers, water pumps, oil/water separator, etc.; and, assist in determining the volumes of water and air that needed to be withdrawn from the subsurface for regulatory permitting purposes. The pilot test successfully demonstrated that a full scale MPE system would be effective at this location. Sitespecific soil parameters were calculated and used in the design of a full scale, permanent MPE system. The final design included three large vacuum blowcontinued overleaf... Environmental Science & Engineering Magazine Spill Management Treatment System. ers, 29 pneumatic submersible pumps, a large compressor, an elaborate sediment filtration system, liquid and vapour phase granular activated carbon, an oil/water separator, and a sophisticated control system with remote access and alarm capabilities. The full scale MPE remediation system was activated in January 2011 and has proven to be very effective. To date, approximately 60% of the 22,000 L of furnace oil product spilled has been recovered and petroleum vapour concentrations within the hospital have been reduced to acceptable levels. Initial capital costs for the remediation system and emergency response measures were in the range of $8 to $10 M, and the monitoring and maintenance costs for the anticipated 10 to 15 years of operation are expected to be in the range of $10 to $15 M. Indoor air quality Immediately after learning of the spill event, hospital staff became very concerned over their exposure to potentially hazardous air contaminants associated with the oil. In order to ensure their health and safety, the hospital engaged exp to conduct indoor air quality monitoring and provide recommendations on other mitigative measures that could be employed. 68 | September 2011 An indoor air monitoring program was implemented and is presently being conducted on an ongoing basis, including the regular collection of indoor air samples for laboratory analyses of volatile petroleum hydrocarbons (PHC) and real time, direct read, monitoring of total volatile organic compound (TVOC) levels. In addition, two sophisticated, real time TVOC monitors were installed in the D Wing basement, which provide continuous readings and record all readings on a data logger. These two units are equipped with audio/visible alarms in the event of elevated readings. Although, at present, there are no Canadian or US standards for TVOC, the Health Canada guideline indicates target and action levels of 1,000 and 5,000 µg/m3, respectively, are being discussed. The European Community indicates that, at a TVOC exposure over 3,000 µg/m3, symptoms such as odours, irritation, and discomfort may occur and complaints may be expected. Since the operation of the pilot, and subsequent full scale, remediation system, concentrations of TVOC have decreased and have remained stable in what is considered to be a normal range. In addition to the field measurements, indoor air samples are collected for laboratory analyses at nine locations every three months. Sample locations are in rooms where there were previous complaints of odours, in unoccupied rooms awaiting occupancy, and in areas situated above the oil plume. Analytical results are compared to Ontario Ministry of Labour (MOL) Occupational Exposure Limits and calculated MOE risk based target levels for the tested parameters. Over the last year, all measured parameters were below these levels. Benzene concentrations ranged from <1 µg/m3 to 3.6 µg/m3, which is much less than the MOL permissible occupational exposure limit of 1,600 ug/m3. Lastly, exp recommended that the ventilation system in the basement of the D Wing be adjusted to increase the air pressure so that it is positive with respect to the subfloor. With the negative subfloor pressure created by the MPE system, air flow within the basement is in a downward direction. This prevents potential vapours from migrating upwards into the hospital environment. To monitor air flow direction, there are currently four manometers installed within the basement floor that record and log the pressure difference between the office environment and the subfloor regime. MOL investigation and findings The local Ministry of Labour office conducted a comprehensive investigation in order to determine whether the remediation system and monitoring programs were sufficient to safeguard staff from being exposed to unacceptable health risks associated with the oil spill. After their review, the MOL concluded that the site remediation system has proven to be effective and worker exposure to airborne petroleum hydrocarbons is acceptable. There is no evidence to indicate that a chemical hazard presently exists for workers at the hospital, due to exposure to airborne petroleum hydrocarbons associated with the fuel oil spill. Dan McNicoll and Mark McCall are with exp Services Inc. Kathy O’Neill and Philippe Marleau are with the Montfort Hospital For more information, E-mail: [email protected] Environmental Science & Engineering Magazine