Location of the Spill
The release occurred on the northwestern corner of MIPC’s approximately 160-acre Chelsea Tank Farm, located at 920 Cherry Tree Road, Aston, PA. The specific area of focus is primarily to the west, south, and southwest of Tank 708.

Release Investigation and Response Actions
- Data and information collected as part of the ongoing investigation,
- Design, implementation, and monitoring of remedial system(s), and
- Final demonstration of attainment of the Pennsylvania Act 2 remediation standards as approved by the Department.
Public Information
Bottled Water
At this time, none of the over 40 residential wells that have been sampled indicate that they have been impacted by this release. None of the sample results exceed even the most stringent safe drinking water standards. In two instances to date, wells tested have detectable levels of gasoline-related compounds. These detections are below the state (PADEP) and federal (EPA) drinking water standards.
- At one property, concentrations of only a few gasoline-related compounds were detected in water samples collected from a private well on January 14 and 28, 2026. The detections are mostly estimated concentrations because they are below the lab reporting limit that can be confidently reported by the lab. Furthermore, all reported concentrations are at least an order of magnitude (i.e., 10 times or more) below the PADEP and EPA standards, as shown in the table below. Additionally, this well is located over 700 feet west-southwest of the site, and the results are inconsistent with other private water well and monitoring well results. Water sampling results from over 40 other private water wells, many of which are located nearer to the release than this well, indicate non-detectable levels of the same compounds detected in this well. As a precaution, routine monitoring is planned for this private well, and the property owner is being provided with bottled water.

- At another property, a low concentration of one gasoline-related compound (p/m-xylene) was detected during only the second round of sampling from a private well on January 29, 2026. This same compound was not detected in the duplicate sample (an additional sample taken at the same time). PADEP also collected a sample before the Langan samples were taken on this same date with the sample results being non-detect.
- Additionally, this compound was not detected in the first sample collected from this private well on January 7, 2026. The lone detection of total xylenes (0.56 micrograms per liter or ug/l) is not only inconsistent with these other sample results but is orders of magnitude below the PADEP and EPA drinking water standards, both of which are 10,000 ug/L.
As a precaution, routine monitoring is planned for this private well, and the property owner is being provided with bottled water.
If sampling shows that petroleum-related compounds have impacted a neighbor’s well water above Act 2 statewide health standards, per PADEP’s Order, MIPC will offer to install a point-of-entry water treatment system (“POET”) to ensure safe household water. Although not required by PADEP, MIPC will also offer to provide connection to public water as a second option if a resident would prefer. In both cases, the installation of these would come at no cost to the property owner.
In the case of a POET system, MIPC will increase the frequency of water testing at their home and closely monitor system performance.
Monitoring Wells/Residential Wells
EPA and PADEP are the federal and state entities charged with protecting health & the environment. These agencies set the standards for safe drinking water and these standards are used in evaluating the drinking water sample results for the tested gasoline-related compounds compared to their safe drinking water standards.
Private well sampling results are compared to U.S. EPA Safe Drinking Water Act (SDWA) Maximum Contaminant Levels (MCLs) for regulated gasoline-related compounds, where such values have been established. MCLs are enforceable standards for public water systems. For private drinking water supplies, PADEP routinely applies these criteria as conservative benchmarks.
Applicable MCLs include, but are not limited to:
- Benzene: 5 microgram per liter (µg/L)
- Toluene: 1,000 µg/L
- Ethylbenzene: 700 µg/L
- Total xylenes: 10,000 µg/L
These values represent concentrations protective of human health for lifetime consumption and serve as the primary drinking water criteria for constituents with established MCLs.
For petroleum-related constituents that do not have federal MCLs (e.g., MTBE, naphthalene, isopropylbenzene, trimethylbenzenes), analytical results are compared to Pennsylvania Act 2 Residential Statewide Health Standards for groundwater used as drinking water (Medium-Specific Concentrations, MSCs). Act 2 MSCs are risk-based criteria developed to protect residential potable groundwater use and are appropriate for evaluating private drinking water well data.
Where both an EPA MCL and an Act 2 MSC are available for a given compound, the more stringent value will be used as the screening benchmark.
Applicable Act 2 MSCs include, but are not limited to:
- Isopropylbenzene (Cumene): 840 µg/L
- MTBE: 20 µg/L
- Naphthalene: 100 µg/L
- 1,2,4-Trimethylbenzene: 130 µg/L
- 1,3,5-Trimethylbenzene: 130 µg/L
First and foremost, MIPC provides the results of private well sampling to each respective property owner(s). MIPC then shares these results with PADEP in each weekly report. Private well results are typically treated as the homeowners’ personal information and may include personal identifiers or property-specific details. To protect the privacy of our neighbors, MIPC does not publish the sampling results of individual properties.
The weekly report that MIPC provides on this website does include the aggregate findings of private well sampling.
Yes, MIPC has developed a continuing groundwater supply well monitoring program to confirm safe drinking water and, over time, to assess potential changes in water quality. Monitoring frequencies are based on the proximity of the groundwater supply well to the western boundary of the impact area and the baseline sampling results. The private drinking water well sampling plan is available on this website under the Remedial Action Plans and Other Technical Documents page.
Monitoring frequency and well selection may be adjusted over time based on cumulative results. Any modifications to the monitoring program would be submitted to PADEP for review and concurrence.
Air Monitoring
PHMSA Investigation
As required, Tank 708 was subject to an industry inspection in the Spring of 2025, which demonstrated the integrity of the tank was in excellent condition. During the initial investigation period, multiple onsite tests and leak detection efforts were conducted to evaluate Tanks 708 and 709 to identify a potential release. These efforts included static hold and pressure tests, pothole digs and excavations, gas testing performed on underground test stations, and more. MIPC also uses a FLIR camera, which is a specialized infrared camera that allows the user to see volatile organic compound vapors through the lens. None of these tests demonstrated that there was a release occurring from Tank 708.
In practical terms, every time product is transferred into or out of a tank, there are small measurement variances due to:
- Gauge precision limitations
- Temperature fluctuations affecting volume readings
- A single degree temperature drop (from 80°F to 79°F) causes the tank level to change by approximately 3/16 of an inch.
- The leak was causing a level drop of only 1/100th of an inch per hour.
This means the temperature effect from a one-degree change is roughly 18 times greater than the hourly loss from the leak. Normal daily temperature swings would create level changes that completely masked the existence of a leak.
Release detection is evaluated using multiple lines of evidence, and investigations may take time to confirm a source, timing, and pathway – especially where subsurface conditions are complex. So, while the loss is detectable in hindsight now that we know a hole existed, there were so many of these variables that it was not apparent at the time. The data was further complicated because other evidence (proximity and sampling) initially pointed toward a different tank as the potential source.
Government Oversight
PHMSA is a federal agency focused on certain safety and integrity aspects under its jurisdiction. PADEP is the primary Pennsylvania agency overseeing environmental investigation and remediation, including requirements for site characterization, monitoring, and cleanup standards (including Act-2).
The primary differences between a PHMSA Corrective Action Order (CAO) and a PADEP Act-2 order lay in their scope, focus, and jurisdiction. PHMSA CAOs are federal enforcement actions focused on immediate, urgent safety risks for operating pipelines & storage tanks, while PADEP Act-2 is a Pennsylvania state program primarily focused on environmental remediation, cleaning up contaminated soil and groundwater to agency-set standards.
Other Environmental Events
No.
In August 2025, a significant fish kill occurred in the West Branch of Chester Creek in Aston Township. As confirmed by Delaware County Emergency Services, this event was traced to a Chester Water Authority (CWA) pump station. Hazmat crews and officials identified the pollutant as a likely chlorine-based substance, not petroleum, affecting the creek near Mount Road.
Source: https://www.cbsnews.com/philadelphia/news/dead-fish-aston-pennsylvania-chester-creek/
MIPC personnel have continued conducting routine weekly inspections of multiple outfalls, the tributary of Marcus Hook Creek known as Bezer’s Run, and Marcus Hook Creek. No indications of impacts to surface water (e.g., sheen, odors, pooled product, stressed vegetation) have been identified to date.
No.
The P66 release occurred along Cherry Tree Road in December 2009. This event is unrelated to the current investigation and happened prior to MIPC’s ownership of the Chelsea Tank Farm. There is no known comingling between the P66 release and the current release. P66 is responsible for all remedial actions stemming from the 2009 release. Specific questions on the 2009 release are best directed to PADEP.