Hydraulic fracturing chemical spills on agricultural land need scrutiny
Hydraulic fracturing, a widely used method for extracting oil and gas from otherwise impenetrable shale and rock formations, involves not only underground injections composed mostly of water, but also a mixture of chemical additives. These chemicals range from toxic biocides and surfactants, to corrosion inhibitors and slicking agents, and many are also used by other industries.
A Colorado State University research team desired a deeper understanding of the fate of these chemicals when they are spilled accidentally during either transportation or production in oil and gas operations. These spills, especially in Colorado, often take place on or near agricultural lands.
The researchers set out to discover whether the degradation of these chemicals in agricultural soil are affected by co-contamination. The team consisted of Thomas Borch, a professor in the Department of Soil and Crop Sciences in the College of Agricultural Sciences, with joint appointments in civil and environmental engineering and chemistry; Jens Blotevogel, a research assistant professor in civil and environmental engineering; and their graduate student Molly McLaughlin.
Their results are online in the journal Environmental Science and Technology, published by the American Chemical Society (ACS).
In the paper, Borch, Blotevogel and McLaughlin cite 838 total hydraulic fracturing fluid spills in Colorado, reported to the Colorado Oil and Gas Conservation Commission in 2014. These spills only include those larger than five barrels of fluid when they happen within a well pad, and larger than one barrel when outside a well pad.
For their proof-of-concept experiments, the researchers used reactors to simulate chemical reactions and biodegradation of hydraulic fracturing additives spilled on agricultural soil. Later, they plan to test their conclusions at actual spill sites.
They tested three well-known organic chemicals: polyethylene glycol (PEG), a commonly used surfactant; glutaraldehyde, a biocide that prevents pipe corrosion from microbial activity; and polyacrylamide, a slicking agent that allows hydraulic fracturing fluid to better penetrate shale. They looked at how these chemicals interact both with each other, and with naturally occurring salts underground.
They found that the PEG (surfactant) by itself completely biodegrades within about 70 days, but that in combination with glutaraldehyde (biocide), the PEG stayed in the soil much longer. That biodegradation was fully inhibited by salt concentrations typical for oil and gas extraction activities.
"Our motivation for doing this is because the chemicals often come up as mixtures," Borch said. "While you may see biodegradation of a surfactant under normal circumstances, if you spill that together with a biocide that kills bacteria, maybe you don't break that surfactant down as quickly. And that's exactly what we see. If chemicals don't degrade as quickly, it gives them more time to be transported to groundwater or sensitive surface water."
They also looked at the degradation cycle of glutaraldehyde (biocide), which occurred within about two months. While polyacrylamide stuck around in the soil for six months, it covalently bonded with the glutaraldehyde, effectively lowering the toxicity of the biocide.
The bottom line is that more science is needed around how spilled chemicals interact with each other and the underground chemical environment - and this applies not just to oil and gas extraction, but to many industrial processes, the researchers say. Such follow-up studies could lead to better understanding of the potential uptake of pollutants in crops, or contamination of groundwater and surface water, with the ultimate goal of helping improve human health risk assessment of spills.
"We cannot say our findings are valid for all the different chemicals used worldwide in hydraulic fracturing," Blotevogel said. "There are probably 1,000 different chemicals used globally, and they all behave very differently with respect to how they are broken down."
Borch and Blotevogel previously published a comprehensive review of the biocide toxicity in hydraulic fracturing fluids and have worked together for almost nine years. The ES&T study was supported primarily by CSU's School of Global and Environmental Sustainability (SoGES), a grant from the CSU Water Center, and by the Borch-Hoppess Fund for Environmental Contaminant Research.
Hydraulic fracturing frequently occurs on agricultural land. Yet the extent of sorption, transformation, and interactions among the numerous organic frac fluid and oil and gas wastewater constituents upon environmental release is hardly known. Thus, this study aims to advance our current understanding of processes that control the environmental fate and toxicity of commonly used hydraulic fracturing chemicals. Poly(ethylene glycol) surfactants were completely biodegraded in agricultural topsoil within 42–71 days, but their transformation was impeded in the presence of the biocide glutaraldehyde and was completely inhibited by salt at concentrations typical for oil and gas wastewater. At the same time, aqueous glutaraldehyde concentrations decreased due to sorption to soil and were completely biodegraded within 33–57 days. While no aqueous removal of polyacrylamide friction reducer was observed over a period of 6 months, it cross-linked with glutaraldehyde, further lowering the biocide's aqueous concentration. These findings highlight the necessity to consider co-contaminant effects when we evaluate the risk of frac fluid additives and oil and gas wastewater constituents in agricultural soils in order to fully understand their human health impacts, likelihood for crop uptake, and potential for groundwater contamination.