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Abstract
Hydraulic fracturing of oil and gas wells requires high volumes of water.
Often these waters originate from rivers, lakes, ponds, and recovered water
from previous fracturing treatments. These waters are often infested with
aerobic and anaerobic bacteria that can cause multiple problems. These include
degradation of fracturing chemicals, down-hole corrosion, biological-based
H2S generation, and down-hole flow-impairment due to slime producing
bacteria. Historically, these waters have been treated with biocides such as
tetrakis (hydroxymethyl) phosphonium sulfate (THPS), glutaraldhyde or
quaternary ammonium-based surfactants. Lately, oxidizing biocides such as
peracetic acid, chlorine dioxide and hypochlorous acid have been used as
environmental alternatives.
Recently, tetrahydro-3,5-dimethyl-1,3,5-thiadiazine-2-thione (Dazomet) has
been used as a biocide with good results in the Barnett, Marcellus, Eagle Ford
and Haynesville gas shale basins in the US. This biocide is effective against
most aerobic and anaerobic bacteria encountered in water sourced for fracturing
applications. Although not a fast-killing biocide, it is effective for
long-term maintenance of the formation and well with loadings normally about
0.4 L/m3 of 24% active solutions.
Further investigation has now discovered that the combination of this
biocide with others has significantly reduced necessary loadings of these
biocides to values less than 0.2 L/m3. These Dazomet-combinations
also tend to show much higher degrees of efficacy, showing superior bacteria
management over the single or oxidizing biocides. This enhanced performance
also allows for reduced chemical exposure to the environment. The performance
of these Dazomet biocide-combinations and field trials will be presented and
discussed.
Introduction
Multi-stage fracturing treatments of horizontal wells in shale formations
require very large volumes of water, often exceeding 38,000 m3. This
fluid volume is needed to create the fracture network for optimum reservoir
contact. The source of this water is rarely municipal treated water; rather
this resource is taken from surface waters such as rivers, lakes, reservoirs
and frac ponds. Recently, mine-back waters, well flow-back water and produced
water have become other viable sources of water, either to minimize disposal
costs or to overcome water shortages. Blends of fresh water and produced water
have become common practice to reduce the consumption of fresh, surface
water.
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