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SPE International Symposium on Oilfield Chemistry | 2011

Case Study: Evaluation of an Oxidative Biocide During and After a Hydraulic Fracturing Job in the Marcellus Shale

Shawn McCleskey Rimassa; Paul R. Howard; Bruce Mackay; Kristel A. Blow; Noel Coffman

Effective microbiological control is an important aspect of a successfully executed fracturing job. Control of bacterial growth is often accomplished through the use of biocides such as glutaraldehyde, particularly in the multi-stage, high-volume fracturing of unconventional shale gas reservoirs. Biocidal additives, which are toxic by necessity, can persist in flowback water, so their use in shale fracturing has come under increasing scrutiny since high biocide concentrations in flowback water increase fluid cost and limit the options for disposal. The case for designing a bactericide program to match, and not exceed, the required amount of bacterial control is clear, but rarely is the bacterial load determined during and after the job to verify this balance. Herein, we report a case study undertaken to evaluate the bacterial load of field mix water and flowback water during and after a large hydraulic fracturing job in the Marcellus Shale. A novel oxidative biocide product was used during the fracturing job that has both an effective fast kill and a low toxicity profile (e.g. HMIS rating of 1,0,0). Because of its rapid biodegradability, there was concern that the effective kill of this biocide would not persist beyond a few days. Industry standard techniques (NACE Std. TMO194-94) for quantifying bacteria were applied to water samples taken during the job and over several weeks of production. The biocide was also evaluated for compatibility with common fracturing additives and for its corrosivity to surface equipment and tubular goods. This study determines that the new biocide does not persist in flowback water beyond a few days. However, analysis of flowback water samples reveals that the bacteria count stays low (less than 10 cells/mL) for up to 81 days after application of this biocide in a slickwater fluid. Additionally, genetic fingerprinting using Denaturing Gradient Gel Electrophoresis Analysis (DGGE) was applied to the bacteria in the initial field mix water to allow comparison to any bacteria detected in the flowback samples. This paper will describe the details of this case study. Since the completion of this case study, we have successfully deployed this technology on treatments in the Barnett, Haynesville, Marcellus, and Granite Wash shale regions. This paper reveals details of a field test and of the efficacy of this biocide as tested in flowback waters from the Piceance and Marcellus Shale basin. The results of the bacteria enumerated from each job site sample are presented. Finally, dosage requirements for biocidal efficacy were optimized for slickwater hydraulic fracturing applications are described. Introduction Control of microbial growth is an essential consideration in the design of fracturing fluids. (Brandon, et al., 1995) Because of their ability to rapidly degrade biopolymers such as guar, bacterial enzymes can seriously affect the rheology of traditional gels. Slickwater fracturing fluids, where viscosity is not critical and the (typically synthetic) drag-reducing polymers are unaffected by bacterial enzymes, also require a biocide strategy to prevent well damage. The re-use of produced water (PW) in slickwater campaigns raises the risk of introducing anaerobic bacteria to the well, because PW is generally less oxygenated (Seright, et al., 2009) and is often rich with inorganic nutrients. Acid-producing bacteria (APB), and sulfate-reducing bacteria (SRB) can cause problematic localized corrosion to completions and tubular goods. (Nemati and Voordouw, 2000) The latter can also be responsible for well souring and iron sulfide precipitation in the low-oxygen wellbore environment. (Carpenter and Nalepa, 2005) These and other general heterotrophic bacteria (GHB) can form biofilms that damage proppant packs and impair production flow, and can be problematic for surface equipment and even pipelines. (Bottero, et al., 2010). * BASF Corporation, Oilfield and Mining Division, as of 2010


Archive | 2007

Fluid loss control and well cleanup methods

Shawn McCleskey Rimassa; Mehmet Parlar


Archive | 2009

METHOD FOR TREATING FRACTURING WATER

Syed Ali; Shawn McCleskey Rimassa; Francois M. Auzerais; Leiming Li


Archive | 2010

Aqueous solution for controlling bacteria in the water used for fracturing

Kristel A. Blow; Syed Ali; Paul R. Howard; Shawn McCleskey Rimassa; Bruce Mackay; Leiming Li; Noel Coffman; Richard D. Hutchins


trustworthy global computing | 2009

Optimizing Fracturing Fluids From Flowback Water

Shawn McCleskey Rimassa; Paul R. Howard; Kristel A. Blow


Archive | 2010

ENVIRONMENTALLY FRIENDLY COMPOSITION FOR SLICKWATER APPLICATION

Paul R. Howard; Shawn McCleskey Rimassa; Syed Ali


Archive | 2011

BACTERIAL CONTROL OF WATER BASED FLUIDS DURING SUBSURFACE INJECTION AND SUBSEQUENT RESIDENCE TIME IN THE SUBTERRANEAN FORMATION

Gregory Kubala; Iain Cooper; Shawn McCleskey Rimassa; Robert Seth Hartshorne


Archive | 2009

Method of installing sand control screens in wellbores containing synthetic or oil-based drilling fluids

Mehmet Parlar; Balkrishna Gadiyar; Sudhir Shenoy; Shawn McCleskey Rimassa


Archive | 2007

Temperature-Extended Enzyme Systems

Shawn McCleskey Rimassa; Mathew Samuel; Steve Mason


SPE Hydraulic Fracturing Technology Conference | 2009

Are You Buying Too Much Friction Reducer Because of Your Biocide

Shawn McCleskey Rimassa; Paul R. Howard; Michael O. Arnold

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