# Failure Report- Plains Pipeline, LP 5/19/15

- **operation:** document
- **citation:** PHMSA FIR, Plains Pipeline, LP, 2015-05-19
- **title:** Failure Report- Plains Pipeline, LP 5/19/15
- **source type:** incident
- **agency:** Pipeline and Hazardous Materials Safety Administration
- **status:** historical
- **official:** true
- **published on:** 2016-06-01
- **effective on:** 2015-05-19
- **summary:** Plains Pipeline, LP; Hazardous Liquid; CA; failure 2015-05-19; apparent cause: Corrosion External.
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- **app url:** https://regulus.evalyn.ai/document/phmsa-fir-failure-report-plains-pipeline-lp-51915
- **source url:** https://www.phmsa.dot.gov/safety-reports/failure-report-plains-pipeline-lp-51915
**body:**

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Failure Investigation Report
Plains Pipeline, LP, Line 901
Crude Oil Release, May 19, 2015
Santa Barbara County, California
May 2016

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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
Table of Contents
Executive Summary .......................................................................................................................... 3
Final Report Methodology ................................................................................................................ 4
Facility Background ......................................................................................................................... 4
Events Immediately Prior to and During the Crude Oil Release ...................................................... 6
Plains’ Field Response and National Response Center Notifications .............................................. 7
PHMSA’s Corrective Action Order ................................................................................................. 9
Pipeline Alignment ........................................................................................................................... 9
Las Flores Station to Gaviota Station Line 901 Elevation Description .......................................... 9
Gaviota to Pentland Station Line 903 Elevation Description ....................................................... 10
Post-Incident Investigation Results ................................................................................................ 11
Metallurgical Evaluation of Failed Pipe ....................................................................................... 11
In-Line Inspection Survey Review ............................................................................................... 12
Number of Anomalies ............................................................................................................ 13
Cathodic Protection Findings ........................................................................................................ 13
Spill Volume Estimate from Plains’ Third-Party Consultant ....................................................... 13
Investigation Findings and Conclusions ......................................................................................... 14
Proximate or Direct Cause ............................................................................................................ 14
Contributory Causes ...................................................................................................................... 14
PHMSA Post-Incident Action Chronology .................................................................................... 18
Appendices ..................................................................................................................................... 20
ii

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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
Executive Summary
At approximately 10:55 a.m. Pacific Daylight Time (PDT) on May 19, 2015, the Plains
Pipeline, LP (Plains), Line 901 pipeline in Santa Barbara County, CA, ruptured, resulting in the
release of approximately 2,934 barrels (bbl) of heavy crude oil.i An estimated 500 bbl of crude
oil entered the Pacific Ocean. Line 901 is a 24-inch diameter buried, insulated pipeline which
extends approximately 10.7 miles in length and transports heated crude oil from Exxon Mobil’s
storage tanks in Las Flores Canyon westward to Plains’ Gaviota Pumping Station. On May 21,
2015, the Pipeline and Hazardous Materials Safety Administration (PHMSA), a regulatory
agency within the U.S. Department of Transportation, issued a Corrective Action Order (CAO)
that required the operator to shut down Line 901. Concurrent with the issuance and
implementation of the CAO, PHMSA conducted an investigation to identify causal factors that
contributed to the occurrence and size of the crude oil release. As the failure investigation
progressed, the CAO was amended to address additional safety concerns that were identified.
On June 18, 2015, Line 901 was purged and filled with inert nitrogen to enhance safety during
the investigation and development of a remedial action plan.ii No fatalities or injuries occurred
as a result of this rupture and release. The spill resulted in substantial damage to natural
habitats and wildlife.
PHMSA’s findings indicate that the proximate or direct cause of the Line 901 failure was
external corrosion that thinned the pipe wall to a level where it ruptured suddenly and released
heavy crude oil. PHMSA’s investigation identified numerous contributory causes of the
rupture, including:
1) Ineffective protection against external corrosion of the pipeline
 The condition of the pipeline’s coating and insulation system fostered an
environment that led to the external corrosion.
 The pipeline’s cathodic protection (CP) system was not effective in preventing
corrosion from occurring beneath the pipeline’s coating/insulation system.
2) Failure by Plains to detect and mitigate the corrosion
 The in-line inspection (ILI) tool and subsequent analysis of ILI data did not
characterize the extent and depth of the external corrosion accurately.
3) Lack of timely detection of and response to the rupture
 The pipeline supervisory control and data acquisition (SCADA) system did not
have safety-related alarms established at values sufficient to alert the control
room staff to the release at this location.
 Control room staff did not detect the abnormal conditions in regards to the
release as they occurred. This resulted in a delayed shutdown of the pipeline.
 The pipeline controller restarted the Line 901 pipeline after the release occurred.
 The pipeline’s leak detection system lacked instrumentation and associated
calculations to monitor line pack (the total volume of liquid present in a pipeline
section) along all portions of the pipeline when it was operating or shut down.
 Control room staff training lacked formalized and succinct requirements,
including emergency shutdown and leak detection system functions such as
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
alarms.
The consequences of the spill were additionally aggravated by an oil spill response plan that
did not identify the culvert near the release site as a spill pathway to the Pacific Ocean.
This report contains factual information and analysis regarding the events leading up to the
release, information collected during PHMSA’s failure investigation to date, and the technical
analysis of that information known at the time of the completion of this report. PHMSA used
this information to mandate remedial measures on Line 901, Line 903, and associated stations
and tankage. PHMSA will also use the information to determine whether violations of the
federal pipeline safety regulations occurred.
Final Report Methodology
PHMSA conducted relevant interviews, gathered and reviewed numerous historical documents
and available records, and performed a thorough review of the Plains Control Room in
Midland, TX. An ILI subject matter expert (SME) was hired to review the raw magnetic flux
leakage (MFL) data and final vendor reports from the MFL surveys, and evaluated Plains
actions as a result of their review of the vendor reports. PHMSA issued a CAO which in part
instructed Plains to have the failed pipe examined by a PHMSA-approved metallurgical
laboratory and to have a root cause failure analysis (RCFA) performed by a third party
independent consultant.
The factual evidence reviewed includes: the Plains Integrity Management Plan (IMP), CP
records, ILI reports, anomaly dig information, SCADA event and alarm logs, pressure and flow
trends, procedures and reports obtained from the pipeline operator and PHMSA SMEs.
The arrangement of this report provides a general description of the pipeline system, the events
that occurred on the day of the release, and acts or omissions of the operator that led to this
failure and release of crude oil. Specific evidence is supplied and pertinent statements from
each report are excerpted where appropriate.
Facility Background
Plains transports crude oil produced in federal and state waters off the coast of Santa Barbara,
CA to inland refineries. Plains’ pipeline is composed of two major pipeline sections: (1) Line
901, and (2) Line 903. Lines 901 and 903 were constructed in the late 1980s, hydrostatically
tested in 1990, and went into crude oil service in 1992 and 1991, respectively. The pipelines
are coated with coal tar urethane and covered with foam insulation which in turn is covered by
a tape wrap over the insulation. Shrink wrap sleeves, which provide a barrier between the
steel pipeline and soil for corrosion prevention, are present at all of the pipeline joints on Line
901 and multiple locations on Line 903. The pipelines carry high viscosity crude oil at a
temperature of approximately 135 degrees Fahrenheit to facilitate transport. Lines 901 and 903
are controlled from the Plains Control Room’s (PCR) California console in Midland, TX.
(1) Line 901 is a 24-inch diameter pipeline that extends approximately 10.7 miles in length
from the Las Flores Pump Station to the Gaviota Pump Station; and (2) Line 903 is a 30-inch
diameter pipeline that extends approximately 128 miles in length from the Gaviota Pump
Station to the Emidio Pump Station, with intermediate stations at Sisquoc Mile Post (MP) 38.5
and Pentland (MP 114.57). There is a delivery point into Line 901 from Venoco’s Line 96
located approximately 2 miles downstream of the Las Flores Station. All of Line 901 crude oil
throughput enters Line 903. Line 901 was manufactured of low carbon steel by Nippon Steel
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
in Japan in 1986. Line 901’s pipe specifications are API 5L, Grade X-65 pipe, 0.344-inch wall
thickness, with a high frequency-electric resistance welded (HF-ERW) long seam. The line
was hydrotested to 1,686 pounds per square inch gauge (psig) on November 25, 1990.
Figure 1. Map of Plains’ Western Division Pipelines. The arrow points to the approximate
release site on Line 901.
At Sisquoc Station, crude oil can be pumped to one of two locations: a nearby refinery via a 12-
inch diameter pipeline operated by Phillips 66, or continue down Line 903 to Pentland Station.
There are additional crude oil lines coming in and out of Pentland Station with numerous tanks
at that station used to blend different crude oils for delivery further downstream. At Emidio
Station crude oil is delivered to above-ground storage tanks for future delivery to Los Angeles
refineries in a separate pipeline system.
Prior to the May 19, 2015 release, there had been four small releases meeting PHMSA
reportable criteria at pump stations on Lines 901 and 903. No releases were reported to
PHMSA on the pipelines outside of pump stations prior to 2015. The operator reported
maximum operating pressure (MOP) of Line 901 is 1,341 psig.
At the time of the spill, Plains All American Pipeline (PAAPL) operated Line 901 and Line 903
under a Federal Energy Regulatory Commission (FERC) certificate of economic regulatory
jurisdiction that was issued in 1987. Plains Pipeline, LP, is a subsidiary of PAAPL. Based on
the FERC filing, Lines 901 and 903 were classified as interstate pipelines, pursuant to 49
U.S.C. § 60101(7), as facilities used to transport hazardous liquid in interstate or foreign
commerce, and as such, were regulated by PHMSA as interstate pipelines. Plains cancelled the
FERC certificates for Lines 901 and 903 on February 12, 2016 and April 29, 2016,
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
respectively, stating that the transportation service was no longer available in interstate
commerce. Line 903 from Gaviota to Sisquoc to Pentland Stations was purged with nitrogen in
accordance with Amendment No. 2 to the CAO, and remains shut down between these stations.
The Pentland to Emidio segment of Line 903 is active and operating intermittently at low
pressures. This section of pipe between Pentland and Emidio is not directly connected to the
Gaviota to Pentland segment and is used to transport crude product from breakout tanks in
Pentland Station.
Events Immediately Prior to and During the Crude Oil Release
On the morning of May 19, 2015, Lines 901 and 903 were transporting crude oil with a flow
rate setpoint of 1,240 bbl per hour (BPH) leaving the Las Flores Station, and the discharge
pressure was approximately 575 psig. Pumps were operating at the Las Flores Station on Line
901 and Sisquoc Station on Line 903. A Plains instrumentation and electrical technician was
dispatched that morning to disconnect and remove a motor from a non-operational pump at the
Sisquoc Station. While the technician was performing his work, the operational pump (Pump
401) at the Sisquoc Station was shut down unintentionally (i.e., “uncommanded”). When
Pump 401 on Line 903 stopped operating, the pressure in Line 901 increased. The pressure rose
to a maximum of 696 psig at the Las Flores Station discharge. The controller shut down the
pump at Las Flores Station and the pressure remained at 677 psig. Approximately four minutes
later, the pump at Las Flores Station was restarted. At approximately 10:55 a.m. PDT, the flow
rate at Las Flores Station climbed from zero to 2,042 BPH. Concurrently, the line pressure rose
to a high of 721 psig, then dropped to 199 psig, and then slightly increased to approximately
210 psig until the Las Flores pump was shut down a second and final time. Generally, a
sudden increase in flow rate accompanied by a decrease in pressure is indicative of a release.
PHMSA has determined that Pump 401 going offline in an “uncommanded” manner on the
morning of May 19, 2015, was an abnormal event, but that this in itself should not have caused
Line 901 to rupture.
PHMSA performed a detailed review of the SCADA event and alarm logs, and pressure and
flow records. The review indicated that there was information reported by the SCADA system
that indicated a release had occurred by approximately 10:58 a.m., and an alarm was generated
on low pressure. The alarm was not set at an appropriate value. The alarm also did not have a
major priority/severity or safety-related alarm status. The controller did not recognize the
information he received as indicative of an abnormal operation. Evidence indicates that the
controller was focused on the events at Sisquoc Station (i.e., restarting the Sisquoc pump that
had gone down once uncommanded, and a second time on high case temperature along with
other duties).iii
Due to the Sisquoc Station maintenance activity resulting in an unplanned pump shutdown, the
controller anticipated alarms would be activated from the pipeline leak monitoring (PLM)
system. According to interviews and a review of the alarm log, the PLM inhibit was requested
by the controller to the step-up shift supervisor between 11:15 and 11:22 a.m.iv The step-up
shift supervisor then inhibited (shut off) the PLM system alarms.v Also, during this time, the
controller started an investigation of the SCADA data in an attempt to understand the
operational abnormalities that were occurring. After attempting to restart the Sisquoc pump
twice, the controller shut down the pipeline. PHMSA requested the operator review the flow
imbalance calculations and provide a time when the PLM system would have generated an
alarm if not inhibited, and it was determined that alarms would have been generated
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
approximately two minutes before the controller shut down the pipeline.vi
Figure 2. Schematic of Plains Pipeline, LP, Line 901 and spill path.
Plains’ Field Response and National Response Center Notifications
The following is a timeline of Plains and emergency responder activities conducted
immediately prior to locating the leak site:vii
 At 11:42 a.m. a call reporting a petroleum smell was received at Santa Barbara Fire
Department (SBFD) Station 18. Engine 18 left the station to investigate the odor
complaint near Refugio State Beach.
 At approximately 12:15 p.m., prior to a scheduled tabletop spill drill required by federal
regulations 49 C.F.R. §194, the pre-drill meeting was completed and adjourned. A
representative from the Santa Barbara Office of Emergency Management (SB-OEM)
received a call from the SBFD reporting that there was oil on Refugio Beach. The SB-
OEM representative and the Plains representatives left the spill drill and drove
separately to Highway 101 at Refugio Beach.
 The Santa Barbara Dispatch notified the National Response Center (NRC #1116950) at
12:43 p.m. PDT of an unknown sheen in the ocean at Highway 101 and Refugio
Beach.viii
 At approximately 12:55 p.m., the two Plains representatives arrived at the south side of
Highway 101 where the SBFD personnel were. They noted oil in the ocean but could
not determine the source of the oil. One of the Plains representatives told the assembled
group that he did not think the oil was coming from Line 901 because the pipeline is
located on the other side of Highway 101, and there would be oil flowing across
Highway 101 if Line 901 was leaking.
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
 The Plains representatives drove to the company’s pipeline right-of-way (ROW). At
approximately 1:27 p.m., the Plains representatives located the leak site on the Plains
ROW. They called the controller to report the leak and to tell the controller to leave
Line 901 shut down and to close the Refugio gate valve. The Plains representatives
used their cell phones to contact other Plains personnel, the landowner where the leak
occurred, Plains’ oil spill response contractors, and others. The Plains representatives
noted that crude oil from the release site had entered a culvert that crosses under the
Highway 101 and railroad tracks and discharges to Refugio Beach. The Plains
representatives, along with Fire Department personnel, attempted to stop the flow of oil
into the culvert. However, the culvert was too large to stop the flow with shovels, and
sand bags were not readily available, so their immediate efforts were unsuccessful. At
approximately 3:00 p.m., additional equipment and personnel arrived, the culvert was
dammed and oil was prevented from entering the culvert.
 At 2:56 p.m., a representative from Plains called the NRC to report (NRC #1116972)
the release of crude oil at 2:56 p.m. PDT. This report indicated that the release was at
Latitude: 34° 27' 43" N; and Longitude: 120° 05' 24" W. This NRC report was made
89 minutes after the release site was found by Plains field personnel.ix
Figure 3. Spill location relative to Refugio Beach in Santa Barbara County, CA. Photo: John L.
Wiley http://flickr.com/jw4pix
Federal pipeline safety regulations, (49 C.F.R. § 195.52), require that the NRC be notified at
the earliest practicable moment following discovery of a release of a hazardous liquid,
including “[a]ny failure that resulted in pollution of any stream, river, lake, reservoir, or other
similar body of water that violated applicable water quality stands, caused a discoloration of the
surface of the water or adjoining shoreline, or deposited a sludge or emulsion beneath the
surface of the water or upon adjoining shorelines.” On January 30, 2013, PHMSA issued an
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
Advisory Bulletin clarifying that this was to be interpreted as within one hour of
discovery. Plains reported the rupture to the NRC approximately 89 minutes after discovery,
thus notifying the NRC 29 minutes late.
The estimated costs reported by the operator as of December 23, 2015, were $142,931,884.
This figure includes all costs the operator spent as a result of this release through the date
reported, including commodity lost, the operator’s property damage and repairs, operator’s
emergency response, environmental remediation, and estimated other costs spent including
government agency costs and media relations expenses.x
PHMSA’s Corrective Action Order
On May 21, 2015, PHMSA issued a CAO, CPF No. 5-2015-5011H, to Plains. The CAO
required Plains to purge Line 901; review the pipeline’s construction, operating, maintenance,
and integrity management history; expedite the review of data from the May 5, 2015, ILI tool
run; conduct metallurgical evaluation of the failed pipe; repair any integrity-threatening
anomalies identified by the ILI survey; and conduct a root cause failure analysis. The CAO
requires Plains to purge Line 901 and to keep Line 901 shut down until PHMSA approves the
restart of the pipeline. Plains’ Line 901 was purged and filled with an inert nitrogen gas on
June 18, 2015.
On June 3, 2015, PHMSA issued Amendment No. 1 to the CAO. The amendment was issued
to address preliminary findings from the early stages of PHMSA’s investigation, and the
possibility that the conditions on Line 901 also existed on Plains Line 903. The amendment to
the CAO required Plains to conduct additional non-destructive testing of ILI anomalies on
Lines 901 and 903; review the construction, operating, maintenance, integrity management,
and ILI history of Line 903; and reduce the operating pressure of Line 903 to 80% of the
highest pressure sustained for a continuous 8-hour period during the month before the May 19
failure. This pressure reduction was intended to enhance safety until all facets of the line’s
integrity could be evaluated.
On November 12, 2015, PHMSA issued Amendment No. 2 to the CAO. The amendment
required Plains to empty and purge Line 903 between Gaviota and Pentland Stations and fill it
with an inert gas. Line 903 was purged between Gaviota and Pentland Stations and filled with
inert nitrogen. The complex purging operations began in December 2015, and were completed
on April 18, 2016. Both Line 901 and the purged sections of Line 903 will remain shut down
until all actions required by PHMSA’s CAO and subsequent amendments have been
completed. PHMSA may continue to issue additional amendments to the CAO as necessary.
Pipeline Alignment
Las Flores Station to Gaviota Station Line 901 Elevation Description
To fully understand the Line 901 release, it is vital to understand the elevation profile of Line
901 and Line 903 from the Las Flores Canyon to Pentland Station. Line 901 starts at the Las
Flores Station at an elevation of approximately 180 feet. There are two large hills downstream
of the originating pump station. The first hill has a peak elevation of approximately 740 feet
and the second hill has an elevation of approximately 600 feet. The release occurred
downstream of the second hill at an elevation of approximately 80 feet. Immediately
downstream of the release point, the pipeline rises slightly and then runs relatively level
approaching the Gaviota station. This fact is important because as soon as the pump at Las
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
Flores Pump Station was turned off the second time, the only crude oil that could be released
was the height of oil in the pipeline above the release site and not the amount located between
the two aforementioned hills.
Gaviota to Pentland Station Line 903 Elevation Description
Line 903 receives all of the crude oil delivered by Line 901. The line elevation at Gaviota is
approximately 150 feet. The elevation at Sisquoc is approximately 880 feet. Downstream of
Sisquoc, Line 903 rises to 2,420 feet and then to a height of approximately 2,750 feet and
ultimately to an elevation of close to 3,000 feet before dropping into Pentland Station at an
elevation of approximately 690 feet. Line 903 exhibits many of the same construction and
operation conditions as Line 901 and was addressed by the amendments to the CAO. Pump 401
at Sisquoc Station has adequate capacity to push the oil up and over the downstream hills and
into Pentland Station but only if it has full suction pressure and full flow coming into the pump.
Because of the release, the pump could not push the oil over the downstream hills, and so the
oil in the pump became hot and the pump shut down to prevent overheating.
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
Post-Incident Investigation Results
Metallurgical Evaluation of Failed Pipe
The failed pipe segment has been analyzed by third-party metallurgical experts, Det Norske
Veritas (U.S.A.), Inc.’s (DNV-GL) in Dublin, OH. The failed pipe assessment and testing was
witnessed by PHMSA, the California Department of Fish and Wildlife, and the U.S.
Department of Justice.
Figure 4. The failed pipe and surrounding insulation and coating.
Figure 5. Pipe External Surface at the Line 901 failure site after cleaning.
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
DNV-GL’s draft report was completed and disseminated to Plains and PHMSA on August 6,
2015. The draft report was reviewed by PHMSA engineers, and a number of comments and
clarification requests were made. DNV-GL reviewed the comments and revised the report.
The Final Report was issued on September 18, 2015.
The Final Report provides a summary of findings, including the following excerpt:
“The results of the metallurgical analysis indicate that the leak occurred at an area of external
corrosion that ultimately failed in ductile overload under the imposed operating pressure. The
morphology of the external corrosion observed on the pipe section is consistent with corrosion
under insulation facilitated by wet-dry cycling.”xi
In-Line Inspection Survey Review
Plains conducted ILI surveys on Line 901 (10.7 miles in length) to assess the integrity of the
pipeline in accordance with PHMSA regulations in 2007, 2012, and 2015. According to 49
C.F.R. § 195.452(j)(3), the pipeline is required to be surveyed at intervals commensurate with
the pipeline’s risk of integrity threats, but at least every 5 years. Plains changed Line 901 from
a 5-year assessment cycle to a 3-year assessment cycle after the 2012 ILI survey.
The data collected during these surveys must be fully evaluated within 180 days of the ILI, and
an operator must take action upon discovery of any “immediate repair conditions” as defined in
49 C.F.R. § 195.452(h) unless the operator can demonstrate that the 180-day period is
impracticable.
The most recent ILI survey for Line 901 was completed on May 6, 2015. The 2015 ILI survey
data for the first 2 miles of Line 901, as measured from the Las Flores Station, was found to be
incomplete and not useable for ILI analysis. For the rest of the ILI survey, the correlation
digs, which are used to gauge survey data accuracy in the ILI vendor’s preliminary report, had
not been finished at the time of the May 19, 2015 failure.
PHMSA’s independent third-party ILI SME also performed an analysis of the data from past
ILI surveys of Line 901. Preliminary data from the results of each of the ILI surveys are
summarized below and show a growing number of corrosion anomalies on Line 901.
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
Number of Anomalies
Metal loss June 19, 2007 July 3, 2012 May 6, 2015
Greater than 80% 0 0 2
60-79% 2 5 12
12 54 80
40-59% The May 6, 2015 ILI survey data and subsequent analysis by the ILI vendor predicted external
corrosion at the failure site with an area of 5.38 inches by 5.45 inches, and a maximum depth of
47% of the original pipe wall thickness. After the failure, the DNV-GL metallurgical
investigators physically measured external corrosion at the failure site to have a maximum
depth of 89%.xii The dimensions of the corrosion feature were 12.1 inches axially by 7.4 inches
in circumference. The maximum depth, as measured using laser scan data, was 0.318 inches or
89% of the measured wall thickness (0.359 inches).
The ILI summary report prepared by PHMSA’s SME also examined the “as-called” (ILI-
predicted) versus as-found (field measured) lengths, widths and area for the excavated
anomalies on Line 901. The report demonstrates that the lengths and widths of the anomalies
were under-called (underestimated) in many cases, however many were also over-called.
Plains submitted little documentation concerning their analysis of how the field measured
anomalies compared to the ILI vendor analysis. Furthermore, Plains did not provide
documentation showing that discrepancies between the originally reported anomaly sizes
predicted by the ILI vendor and Plain’s actual field-measured sizing of the corrosion anomalies
were subsequently discussed with the ILI vendor, as required by Plains’ IMP.xiii
Cathodic Protection Findings
According to 49 C.F.R. § 195.563, CP is required under the federal Pipeline Safety Regulations
to prevent external corrosion of buried pipelines. Historical CP records for line 901 have been
reviewed and reveal protection levels that typically are sufficient to protect non-insulated,
coated steel pipe. Line 901 and Line 903, however, are insulated. An increasing frequency and
extent of corrosion anomalies were noted on both Lines 901 and 903 in ILI survey results,
anomaly excavations, and repairs. PHMSA inspectors noted moisture entrained in the
insulation at four excavations performed by Plains on Line 901 after the May 19 spill and prior
to the PHMSA-mandated purging of the pipelines.
Spill Volume Estimate from Plains’ Third-Party Consultant
Plains initially estimated the volume of spilled crude oil to be approximately 2,400 bbl, of
which 500 bbl was estimated to have reached the ocean. On August 4, 2015, Plains reported
to the Unified Command that the 2,400 bbl release estimate was still accurate. However, after
Plains completed the PHMSA-mandated purge, the company’s calculations indicated that up to
3,400 bbl had possibly been released from the pipeline. Plains notified the Unified Command
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
that RPS Knowledge Reservoir (RPS), a third-party investigator hired by Plains, was still trying
to reconcile the difference.
On November 24, 2015, Plains informed PHMSA that RPS had completed their analysis
regarding the release volume and produced a report of findings. RPS used the OLGA
simulation software tool to model the behavioral dynamics of the pipeline prior to, during, and
immediately after the May 19, 2015 leak. The report concluded that the discharge leak volume
was 2,934 bbl. The RPS report was dated November 11, 2015. Plains has reported 1,100 bbl
of crude oil have been recovered.
Investigation Findings and Conclusions
Line 901 pipeline ruptured at approximately 56% of the MOP. Although the operational events
that occurred on the morning of the release were abnormal, this should not have caused the
release if the pipeline’s integrity had been maintained to federal standards.
Proximate or Direct Cause
PHMSA determined that the proximate or direct cause of the release was progressive external
corrosion of the insulated, 24-inch diameter steel pipeline. The corrosion occurred under the
pipeline’s coating system, which consisted of a urethane coal tar coating applied directly to the
bare pipe, covered by foam thermal insulation with an overlying Polyken tape wrap. Water has
been noted in the foam insulation at a number of digs, indicating that the integrity of the
coating system had been compromised. The external corrosion was facilitated by the
environment’s wet/dry cycling, as determined by the PHMSA-approved, third-party
metallurgical laboratory. The release was a single event caused at an area where external
corrosion had thinned the pipeline wall. There is no evidence that the pipeline leaked before
the rupture. There was a telltale “fish mouth” (a split due to over-pressurization) at the release
site indicating the line failed in a single event.
PHMSA’s investigation identified numerous contributory causes of the rupture. The
contributory causes can be grouped into three categories: 1) ineffective protection against
external corrosion of the pipeline; 2) failure by Plains to detect and mitigate the corrosion;, and
3) lack of timely detection of the rupture. Below is a summary of the key contributory causes:
Contributory Causes
1) Ineffective protection against external corrosion of the pipeline
 Plains’ CP system was ineffective in protecting thermally insulated underground
pipeline systems from external corrosion. Industry practices recognize that an
impressed current system like the one utilized on Line 901 cannot protect an insulated
steel pipeline should the coating (tape wrap over insulation) become compromised.
The external coating in the area of the rupture had allowed moisture to enter the
insulation adjacent to the steel pipe.xiv Corrosion under insulation (CUI) cannot be
prevented on insulated lines where the coating system has been compromised.xv
2) Failure by Plains to detect and mitigate external corrosion
 Plains did not identify CUI as a risk-driving threat in their federally-mandated
integrity management program (IMP).
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
 Plains’ did not fully implement their IMP.
o Plains did not perform suitable analysis of the field measurements of the
excavated corrosion anomalies that occurred after ILI surveys were completed
in 2007 and 2012.
o The data reported by the ILI vendor were inconsistent (and did not meet the
published accuracy of the ILI tools of +/- 10%, 80% of the time for depth)
when compared to the results of the field-measured corrosion anomalies.
o Plains’ as-found field measurements of corrosion anomalies were inconsistent
with the as-called vendor-provided ILI data and analytical reports. ILI surveys
conducted in 2007 and 2012 revealed inconsistencies in the character of the
anomalies. In both of these cases, Plains did not consult the ILI vendor to help
resolve the inconsistency.
o Plains failed to follow written procedures directing the IMP group to perform
appropriate statistical analysis after the anomaly dig reports were received
from the field, and to discuss any inconsistencies with the ILI vendor.xvi
 Plains’ Pipeline Integrity group created a unity plot for depth after the
2012 ILI survey and anomaly digs. There is no documentation
detailing what was done with the information from the unity plot.
o Plains incorrectly added the over-called anomalies in the close-out reports.
 The close-out reports should have only reported the anomalies that
were within the reported accuracy of the ILI tool. The reported tool
accuracy is +/- 10 %, 80 % of the time. Adding the overcalled
anomalies outside of the tool accuracy skews the data.
 Plains’ Pipeline Integrity group was historically focused on pitting corrosion under
“shrink sleeves” at the pipeline girth welds (circumferential welds to join pipe
segments).
o The release location was within 6 feet of a corrosion anomaly that was exposed
and repaired after the 2012 ILI survey. There was evidence of corrosion and
degraded coating systems between the 2012 repair site and the 2015 rupture
site.
o The anomaly that ruptured was called out by the ILI tool at 45% depth in 2012.
Plains’ IMP specified adding 10% to all anomalies (55% depth in this case)
then “growing them” to predicted failure using an anticipated corrosion growth
rate. This analysis would provide a predicted failure time. Plains did not
excavate the anomaly that failed.
3) Lack of timely detection of and response to the rupture
 The controller did not have information communicated from the SCADA system in
such a manner to be successful in detecting abnormal operations. The pipeline
SCADA system did not have safety-related alarms on low pressure configured at the
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Plains Pipeline, LP - Failure Investigation Report
Santa Barbara County, California Crude Oil Release - May 19, 2015
correct value or priority to alert the control room staff of the rupture. When this
alarm was provided to the controller, the discharge pressure at Las Flores was 199
psig but, within a minute, pressure elevated above 210 psig, the alarm status cleared,
and the discharge pressure remained above 200 psig (approximately 210-211 psig)
until the pipeline was purged. The pipeline was still leaking when the discharge
pressure at Las Flores was above 200 psig, and continued to do so without additional
alarm indications. When the pipeline was down, isolated but still leaking, the
minimum pipeline discharge pressure at Las Flores remained at 210-211 psig. The
low discharge pressure alarm setpoint value was not set properly as it should have
been above 211 psig. This type of alarm should be identified as a high priority safety
related alarm. While the controllers and shift supervisors can access historical trend
data or continue to monitor a given pressure or flow, when the pipeline was
ultimately shut down at 11:30 a.m., neither the controller nor step-up shift supervisor
detected any drop of pressure at the specific failure location that would indicate that
oil was being released.
 Neither the pipeline controller nor step-up shift supervisor detected the initial
abnormal conditions as the release occurred. There was an indication of decreased
pressure and increased flow between 10:53 and 10:58 a.m., which is consistent with a
pipeline release. This resulted in a delayed shutdown of the pipeline. Adequate alarm
setpoint values with correct priorities are essential to controller and shift supervisor
recognition of abnormal operations, especially when many pipeline systems are
operated from the same console.
 The pipeline controller restarted Line 901 after the release occurred.
 The pipeline leak detection system lacked instrumentation and associated
calculations to monitor line pack.
o The function of the PLM system was a simple line balance calculation based
on flow meter values without line pack considerations. The PLM relies on
comparing “meter in – meter out” calculations over time. This type of leak
detection system without the use of safety-related, high-priority, low-pressure
alarms does not provide the controller or shift supervisors with adequate
information when the pipeline is down.
o When the pipeline is not running, even if only due to scheduling and not
required maintenance activities, flows will be close to zero and the imbalance
calculation will provide little if any value as currently configured. Leak
detection on a down pipeline requires a robust system of planned and accurate
high-priority alarm types and alarm setpoint values in order for response to
occur on critical low pressures.
o The leak detection system for Lines 901 and 903 consists of two leak
detection segments. Additional instrumentation such as pressure and
temperature transmitters located at Refugio Gate and Cuyama valve settings
(both transmitter types on e
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