The multicup pig arrived ashore Jan. 15, 2009, and two out of four bottles in the serial-dilution test yielded indications at least 100 microbes/ml. APS reductase methodology showed up to 10,000 microbes/ml. These collective results showed large microbial populations were still within the trunkline and there was a continuing potential for MIC occurrence.
Following Jan. 15 passage of the pig through the damaged lateral, attention shifted to returning other laterals, not damaged by Hurricane Ike, to production. Initial concerns again focused on preventing hydrate formation in either the laterals or the trunkline.
Pigs launched from laterals on Jan. 21 and 27, 2009, traveled to the trunkline and were then pushed to the onshore gas processing plant by a 30-in. multicup pig from EW-873 at the upstream end of the trunkline. Fluid samples were again collected at the onshore facility, and they provided positive indications for SRB, with 100 microbes/ml based on serial dilution studies and 10,000 microbes/ml using APS reductase studies.
THPS treatment
THPS biocide was injected into the upstream end of the trunkline and was first evident in sampling associated with the pig arriving Feb. 5. A sufficient volume of THPS was injected into the trunkline to provide 1,000 ppm of THPS residual at the end of the trunkline based on the estimated volume of seawater remaining in the trunkline at the time. The first measurement, however, yielded only 76 ppm of THPS at the onshore facility.
Biocide treatments and pig runs followed a rotating schedule treating all laterals on the pipeline system, including those unaffected by Hurricane Ike, and the trunkline. Through February 2009 THPS residuals increased to roughly 720-820 ppm. The delay in getting the biocide distributed through the pipeline is undoubtedly related to the frequency of the pigging and the vertical incline of the pipeline.
Serial dilution studies were negative, showing microbial populations of SRB were below detectable levels.
The biocide was effective as APS reductase readings mostly measured zero. Samples collected Feb. 22 and Feb. 27, however, had APS reductase readings as high as 10,000 microbes/ml. The APS reductase test cannot distinguish between live SRBs and those freshly killed by a biocide, explaining how there can be differences in results between the serial dilution and APS reductase techniques. Results from serial dilution studies were taken as the most definitive measure of microbial populations.
Once microbial populations were eradicated, a batch treatment of a tenacious oil-soluble corrosion was applied to the trunkline, quickly reestablishing a protective inhibitor film, helping ensure the trunkline's ongoing integrity.
18-in. lateral
The next major operational change was returning the 18-in. lateral to service. The multidisc pig used to dewater the 18-in. OD lateral arrived at the ST- 200 platform Mar. 10, 2009.
During initial dewatering elevated levels of
H2S levels
The concentration of
Throughout this period, each of the laterals received biocide treatments on a regular rotation, and
As the pH slowly increased to 7.3 from 6.5, concentrations of iron and manganese in the water samples gathered at Larose continued to slowly drop, suggesting corrosion was abating. Serial dilution studies throughout this period also showed microbial populations of SRB as below detectable limits; the microbiological processes were now being kept in check.
Continuing trend
Through the rest of 2009 and early 2010, continued serial dilution and APS reductase studies show microbial populations have remained below detectable levels, even after biocide residuals approached zero. The pH of the water removed from the system continues to be in the range 7.1-7.2, and the concentration of dissolved