1. MIC in Long Oil Pipelines: Diagnosis, Treatment and Monitoring ISMOS 3 Calgary, Alberta June 14, 2011 Gary Jenneman, Jennifer Harris and Robert Webb

2. 300 km70 km 7 km 5 km Organic Acids Acetic Propionic Butyric Inorganic Solids BaSO 4 FeS Produced Water Pitting in the first 70 Km 70 km 7 km 5 km Pitting Oil Pipeline Terminal Gases CO 2 H 2 S Bacteria 10°C Production Platform Problem

3. Is it MIC? Biological –Are environmental conditions conducive to microbial growth and metabolism? Chemical –Are environmental conditions such that abiotic mechanism could explain observed rates? Metallurgical –Are corrosion products and features characteristic of MIC present? Operational –Have changes occurred that may enhance the activity of microorganisms? MIC does not produce any unique type of corrosion and there are no definitive tests or specific observations that can be used to detect MIC. B. J. Little

4. Temperature Gradient Production Platform Oil Terminal Zone of active pitting Distance - Km

5. AnalyteUnits1/27/052/9/052/24/053/14/05 pH---- 5.96.25.5 6.0 Susp. Solids > 0.45 μmg/l 340490300 161 Total Organic Carbonmg/l 830852662 1370 Total Sulfidemg/l 0.50.7 <1 Soluble Femg/l 302643 28 Phosphorus as PO4mg/l 6.118.17.3 5.5 Calciummg/l 7108605660 1190 Potassiummg/l 340260410 390 Magnesiummg/l 160250400 530 Sodiummg/l 91001320016200 13900 Strontiummg/l 80120160 120 Ammoniummg/l 274251 48.4 Chloridemg/l 142002200029800 26400 Sulfatemg/l 90155280 610 Methanolmg/l 103080 1010 Ethanolmg/l 15549 145 Acetaldehydemg/l 1722 140 Acetic Acidmg/l 350760700 630 Propionic Acidmg/l 145240130 40 Butyric Acidmg/l 151114 9 Chemical analyses of water from pig runs.

6. Disc Pig

7. XRD of Pig Sludge Solids

9. Bacteria Analyses in PL Pig Water

10. Bacteria Analysis in Pig Sludge

11. Community Structure of PL Pig Sludge by PLFA Analyses Date BiomassCommunity Structure (% total PLFA) Cells/gFirmicutes Anaerobic Gram ( – ) (TerBrSats) Proteo- Bacteria (Monos) Anaerobic Metal Reducers (BrMonos) SRB/ Actino-mycetes (MidBrSats) General (Nsats) Eukaryotes (Polyenoics) 3-147.73x10 7 39.19.71.1 49.00.0 5-092.59x10 6 46.47.50.0 46.10.0

12. March 14 Sludge sample Sequence results from bands excised from Figure 5 (March 14). Similarity indices above.900 are considered excellent,.700-.800 are good, and below.600 are considered to be unique sequences. DGGE of PL Pig Sludge – Mar. 14

13. May 9 Sludge sample Sequence results from bands excised from Figure 5 (May 9). Similarity indices above.900 are considered excellent,.700-.800 are good, and below.600 are considered to be unique sequences. DGGE of PL Pig Sludge – May 9

14. Biometabolite Analysis 23 putative hydrocarbon biometabolites were identified. Biometabolites of the biodegradation of aromatic HC were especially prevalent (5 to 7 µM). Biometabolites for the anaerobic biodegradation of aromatic HC (e.g, BTEX) were also detectable. Evidence for anaerobic biodegradation of n-alkanes (e.g., fumarate addition products) were only weakly detectable.

15. Operational Considerations Soured reservoir History of MIC in upstream pipelines Velocity - < 1.5 m/s Presence of solids – scale, suspended solids Water slugging Oxygen 3 rd party lines

16. Is it MIC? Microbiological, chemical, metallurgical and operational evidence suggest that MIC is a likely mechanism.

17. Biocide/Mitigation Program

18. Glutaraldehyde residuals in pig envelope water by GC-ECD.

20. Synthetic seawater was amended with: -sodium bicarbonate - ammonium chloride - ethylene glycol - acetic acid - boric acid - *iron (0.58 mM) - *crude oil (50%) Water type[glut] 0, ppm T (  C) % degrad, 24h Field sample10006090 Field sample3006085 Synthetic PW10005080 from McGinley et al., SPE OFC Symposium (2011)

21. Screening of Components Water typeNH 4 +% degrad Synthetic PWNone10 Synthetic PW10 ppm40 Synthetic PW100 ppm81 Modified Synthetic PW, 55 ° C, 24h from McGinley et al., SPE OFC Symposium (2011)

22. Screening of Components * Complete Synthetic PW has 100 ppm ammonium Sample[NH 4 +]other% degrad 1,2,3--0, 0, 8 4100 ppm20 5--595 ppm EG0 6100 ppm595 ppm EG30 7--390 ppm AcOH12 8100 ppm390 ppm AcOH45 9--49 ppm boron14 Amended Instant Ocean, 55 °C, 24 hrs from McGinley et al., SPE OFC Symposium (2011)

23. Successful Mitigation Measures Increase CO 2 inhibitor concentration Remove sources of oxygen ingress. Increase continuous biocide concentration (GA/QAC) Batch biocide and batch corrosion inhibitor every 5 th week following aggressive pit cleaning tool. Scale inhibitor injection

24. Acknowledgments The authors would like to thank ConocoPhillips for the opportunity to present this work.