http://www.crrc.unh.edu/news/kinner_house_testimony.pdfThe Gulf of Mexico Contingency Plan allows dispersant use, without preauthorization, a minimum distance of 3 nautical miles from the shore and a water depth of at least 33 feet. As of May 18th, 2010 an unprecedented 590,000 gallons of chemical dispersant have been applied to the oil on the surface of the Gulf. Responders are also experimenting with injecting dispersants into the oil as it is being released from the damaged riser pipe ~5,000 feet below the surface. Beginning on May 3rd, a series of trial injections began and 3,000 gallons of dispersant were injected into the oil plume at a depth of approximately 5,000 feet. Visual observations indicate this was successful in reducing the volume of oil reaching the surface. US EPA and USCG recently approved the use of dispersants in the subsurface by the damaged riser pipe.
The Deepwater Horizon blowout marks the largest volume of dispersants ever used, domestically and internationally. . While dispersants have proven to be successful at reducing oiling of shorelines, numerous questions remain regarding the fate of the dispersed oil and the chemical dispersant. Application of dispersants at this depth is unprecedented, and the fate and potential effects have never been investigated. ...
Little is known about the long-term fate of dispersed oil. The National Research Council (NRC) published two studies in 1989 and 2005 reviewing the state of dispersant use and knowledge in the United States. Both reports indicated there was a lack of understanding on the fate and potential impacts of large quantities of dispersed oil. ...
Biodegradation is often cited as the most likely fate of dispersed oil, however, little research has been done on the likelihood of this scenario. Biodegradation, while potentially able to completely degrade the oil, is a complex and often misunderstood process. The majority of the studies that have examined biodegradation of dispersed oil have focused on droplets in the mixed layer, and found that biodegradation was often incomplete (i.e., some compounds remained), and significant degradation took weeks to months to occur (Harayama, 2004; Stewart et al., 1993; Lindstrom et al., 1999). No research has been done on the potential for biodegradation of dispersed oil at depths approaching those of the Deepwater Horizon, and the high pressures and different microbial communities at this depth may severely restrict or prevent any biodegradationfrom occurring. ...
Many marine biota, including copepods, shrimp, and oysters, feed on microplankton and other very small organisms that are similar in size to some dispersed oil droplets (0.1 to 1 mm), and it is possible that these organisms may consume smaller dispersed oil droplets (Gyllenberg, 1981; Andrews and Floodgate, 1974). These smaller organisms are the foundation of the marine food web, and reduced body weight, population, or mortality may occur. In addition, the oil can bioaccumulate, impacting larger species, including commercially important species such as shellfish, tuna, and shrimp. Many organisms in aquatic environments transfer dissolved gasses via special organs (i.e., gills) that can lead to increased exposure to dissolved chemicals through absorption (Barnett and Toews, 1978). While difficult to quantify, the large surface area to volume ratio of oil droplets will result in rapid dissolution of soluble chemicals, and potential exposure to biota. ...
The major gaps in dispersant knowledge arise in the link between the fate of dispersed oil and the biological endpoints. The key question that remains unanswered is: What is the most likely fate of the dispersed oil and dispersant in the marine environment? In 2009, CRRC held an R&D needs workshop that brought together members of the oil spill community and stakeholders to identify the top research needs to enhance spill response. Not surprisingly, understanding long-term fate of chemically dispersed oil was a top research priority. The Deepwater Horizon incident response has used significantly more dispersants than any other spill in U.S. history. The endpoint and effects from this huge quantity of dispersed oil cannot be confidently predicted because of lack of understanding of the potential pathways and effects. ...
However, when winds and storms created waves and currents preventing booming, skimming and burning, the method of choice became application of chemical dispersants. With more than 590,000 gallons delivered by aircraft and now with approved injection at 5,000 feet, the oil is not reaching shorelines, but is submerged in the water. The concerted effort by responders to prevent oil from reaching the marshes and beaches has to date prevented some of the images many associate with the Exxon Valdez, including oiled birds, sea otters, as well as blackened shorelines and huge floating oil slicks. Questions abound as to whether the worst is yet to come, and if there will there be long term effects of dispersing millions of gallons of oil, and if so, how fast will the natural resources rebound.
Unfortunately, I do not believe that anyone knows the answers to these questions. As data is collected by scientists to determine the amount of oil contamination in the water at various depths, we can begin to predict what the potential impacts may be. The basic risk equation is: Chemical Exposure ? Toxicological Response. Exposure is a function of the rate of uptake by the organism, the concentration of the contaminant, the duration of the exposure, and the bioavailability, absorption and metabolic reaction related to the contaminant. The toxicity can be acute (lethal) or chronic (affecting growth, reproduction, behavior or population level parameters). There have been scientific studies done that examine some constituents of oil and mimic certain environmental exposures, but there is a relatively limited database and some of it does not withstand the rigors of peer-review. None of it addresses the magnitude and extent of exposure that the Deepwater Horizon spill represents.