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How Oil Dispersants Work How Oil Dispersants Work Kenneth Lee - PowerPoint PPT Presentation

How Oil Dispersants Work How Oil Dispersants Work Kenneth Lee Photos\Lee_Ken\IMG_0530_ppt.JPG Kenneth Lee Kenneth Lee Centre for Offshore Oil, Gas and Energy Research (COOGER) Centre for Offshore Oil, Gas and Energy Research (COOGER)


  1. How Oil Dispersants Work How Oil Dispersants Work Kenneth Lee Photos\Lee_Ken\IMG_0530_ppt.JPG Kenneth Lee Kenneth Lee Centre for Offshore Oil, Gas and Energy Research (COOGER) Centre for Offshore Oil, Gas and Energy Research (COOGER) Fisheries and Oceans Canada Fisheries and Oceans Canada Bedford Institute of Oceanography Bedford Institute of Oceanography Dartmouth, Nova Scotia Dartmouth, Nova Scotia Canada B2Y 4A2 Canada B2Y 4A2 Ken.Lee@dfo- Ken.Lee@dfo -mpo.gc.ca mpo.gc.ca

  2. What Are Dispersants? • Dispersants are liquid solutions of detergent-like surfactants dissolved or suspended in solvent • The surfactants have two ends: one attracted to oil (lipophilic) and another attracted to water (hydrophilic) Water-compatible (Hydrophilic) Oil-compatible (Lipophilic) • The solvent enables the surfactants (active ingredients) to be applied and helps get them through the oil film to the water interface • At the interface the surfactants reduce the surface tension allowing the oil to enter the water as tiny droplets which are degraded by natural bacteria

  3. Activity of Chemical Dispersants Dispersant (surfactant) Dispersant sprayed onto oil slick Hydrophilic Oil Hydrophobic Surfactant locates at interface Surfactant-stabilized oil droplet (micelles) Oil slick broken into droplets The droplets dispersed by turbulence by mixing energy leaving low oil concentrations Surfactant reduces the oil-water interfacial tension by orienting the interaction of hydrophilic groups with the water phase and the hydrophobic groups with oil Reduced oil-water interfacial tension facilitates the formation of a large number of small oil droplets that can be entrained in the water column

  4. Orientation of surfactants at oil Surfactant coated dispersed water interface oil droplet in dispersed oil droplets x xxxxxxxxxx Oil phase B B A B A = sorbitan monooleate A (a.k.a, Span 80; HLB ~ 4.3) B = ethoxylated (E20) sorbitan monooleate (a.k.a, Tween 80; HLB ~ 15) HLB (hydrophile-lipophile balance) Predominantly hydrophilic surfactants (HLB >7) will favour oil-in water dispersions (entrained oil droplets in a water body)

  5. Chemical Constituents (Dispersant – Corexit) CAS # Name Common Day-to-Day Use Examples 1338-43-8 Sorbitan, mono-(9Z)-9- Skin cream, body shampoo, emulsifier octadecenoate in juice 9005-65-6 Sorbitan, mono-(9Z)-9- Baby bath, mouth wash, face lotion, octadecenoate, poly(oxy-1,2- emulsifier in food ethanediyl) derivs. 9005-70-3 Sorbitan, tri-(9Z)-9-octadecenoate, Body/Face lotion, tanning lotions poly(oxy-1,2-ethanediyl) derivs. 577-11-7 * Butanedioic acid, 2-sulfo-, 1,4- Wetting agent in cosmetic products, bis(2-ethylhexyl) ester, sodium salt gelatin, beverages (1:1) 29911-28-2 Propanol, 1-(2-butoxy-1- Household cleaning products methylethoxy) 64742-47-8 Distillates (petroleum), hydrotreated Air freshener, cleaner light 111-76-2 ** Ethanol, 2-butoxy Cleaners * Contains 2-Propanediol ** Ethanol, 2-butoxy-) is absent in the composition of COREXIT 9500

  6. Dispersant Activity t = 14 ms t = 28 ms t = 0 ms t = 38 ms 5 mm t = 48 ms t = 40 ms t = 42 ms t = 46 ms Extracted images from cinematic digital holography of turbulent break-up of crude oil mixed with dispersants into microdroplets Gopalan, B. and J. Katz (2010) Physical Review Letters 104, 054501

  7. Oil Droplet Size Distribution - Dispersant + Dispersant 1.0 0.5 t = 1 min t = 1 min 0.5 0.0 t = 10 min 0.0 1.0 Particle Concentration ( μ l/L) t = 10 min Particle Concentration ( μ l/L) 0.5 0.5 0.0 0.0 t = 30 min t = 30 min 0.5 0.5 0.0 0.0 t = 60 min t = 60 min 0.5 0.5 0.0 0.0 10 100 10 100 Mean Diameter ( μ m) Mean Diameter ( μ m)

  8. Small Oil Droplets Rise Slower than Large Oil Droplets STOKES LAW ∆ h / t = D 2 ( ρ w – ρ o )g 18 η w Where: ∆ h / t = rise velocity D = drop diameter ρ w = aqueous density ρ o = oil density g = gravitational constant η w = aqueous viscosity

  9. Dispersion of Oil In the open sea currents distribute oil over a large area 1 st Hour 2-5 Hours Top 10 meters of the Water Column 2 – 180 ppm Less than 1 ppm Oil is diluted to concentrations below toxicity threshold limits

  10. Fate of Oil Components in Oil Droplets Entrained in the Water Column Rate of loss of volatile and water Solubles soluble components (chemical partitioning) and microbial 20µm oil droplet surrounded by degradation are influenced by surfactant molecules surface-to-volume ratios (Area 5x10 3 Volume 3.3x10 4 ) Sphere surface area: 4 π r 2 Sphere volume: 4/3 π r 3 Solubles For two orders of magnitude Increase in diameter: Surface area increases by 10,000x Volume increases by 1,000,000x 2000µm entrained oil droplet (Area 5x10 7 Volume 3.3x10 10 )

  11. Fate of Dispersed Oil Droplets 4 weeks 1-2 days Applying Dispersant S E A S U R F A C E Initial Dispersion Bacterial colonization of dispersant and dispersed oil droplets Bacterial degradation Colonization of of oil and dispersant bacterial aggregates by protozoans and nematodes Source: http://www.response.restoration.noaa.gov

  12. Application of Oil Dispersants • In addition to (mechanical recovery techniques (skimming and booming) and in situ burning, oil dispersants were used to prevent landfall of the oil in the Deepwater Horizon Spill • Beginning in early May responders began injecting dispersants at the source of the release (~1500m depth) to reduce oil from reaching the surface • Advantages of subsurface injection: • Reduced VOCs (volatile organic compounds) • Reduced Oil Emulsification • Volume of dispersant needed

  13. Dispersant Monitoring and Assessment for Subsurface Dispersant Application • Directive issued by US EPA and USCG required BP to implement a monitoring and assessment plan for subsurface and surface use of dispersants • Shutdown Criteria • Significant reduction in dissolved oxygen (< 2 mg/L) • Rotifer acute toxicity tests • Later addenda to implement SMART Tier 3 Monitoring Program • Droplet size distribution (LISST) • CTD instrument equipped with CDOM fluorometer • Discreet sample collection to measure fluorometry (FIR) • Eliminate surface application altogether • Subsea limited to < 15,000 gpd

  14. Joint Analysis Group (JAG) for Surface and Subsurface Oceanographic, Oil, and Dispersant Data • Working group of scientists from EPA, NOAA, OSTP and DFO • Analyze an evolving database of sub-surface oceanographic data by BP, NOAA, and academic scientists • Near term actions: • Integrate the data • Analyze the data to describe the distribution of oil and the oceanographic processes affecting its transport • Issue periodic reports

  15. Vertical Profile of O 2 Depressions Coincident with Fluorescence Peaks

  16. aaa CDOM (Colored Dissolved Organic Matter Fluorescence) a Normalized Mean CDOM Fluorescence (1000-1300 m) vs. Distance from Wellhead 14 Brooks McCall 12 Normalized CDOM Fluorescence Walton Smith 10 Ocean Veritas Gordon Gunter 8 Thomas Jefferson 6 4 2 0 0 10000 20000 30000 40000 50000 60000 Distance from wellhead, m FOR INTERNAL USE ONLY

  17. Preliminary Conclusions • Fluorometry shows recurring anomaly at 1000 to 1300 m • Strongest near wellhead, decreases with distance • Trending WS to NE direction consistent with water movement along isobath isobath • Natural Organic Matter contribute to fluorescence signal • Spatial and temporal variability in fluorometric anomalies • Active natural seeps mapped ~12 km SW and 17 km NE of wellhead • Minimum detection limit of CDOM fluorometers ~1 ppm oil • CTD DO anomalies seen at 1000 to 1300 m • Interpretation to be refined and data validated by Winkler O 2 titrations against electronic sensor data

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