Literature DB >> 18187161

Oil persistence on beaches in Prince William Sound - a review of SCAT surveys conducted from 1989 to 2002.

Elliott Taylor1, Doug Reimer.   

Abstract

In 2002, 13 years after the Exxon Valdez oil spill (EVOS), 39 selected sites in Prince William Sound (PWS) were re-surveyed following established shoreline cleanup assessment team (SCAT) field observation procedures to document surface and sub-surface oiling conditions in shoreline sediments and to compare results with those from previous Shoreline Cleanup Assessment Team (SCAT) surveys and other surveys in PWS. The selected sites are locations where EVOS oil persisted in 1992, at the time the Federal and State On-Scene Coordinators determined that the cleanup was complete and that further cleanup activities would provide no net environmental benefit. These sites had been included in a 2001 NOAA survey of shoreline oiling conditions and account for 88% of the sub-surface oil residues (SSO) oil documented by that study. The 2002 field survey found isolated occurrences of residual EVOS surface oil residues (SO) in the form of weathered asphalt pavement at 15 of the 39 sites. This residual SO typically consisted of asphalt in mixed sand/gravel substrate, located within a wave shadow effect created by boulders or bedrock in the upper intertidal to supratidal zone. Residual SO, expressed as a continuous oil cover, was less than 200 m(2) within the approximately 111,120 m(2) surveyed. A total of 1182 pits were dug at locations where SSO residues were present in 1992. Six of the 39 sites and 815 (68%) of the pits contained no residual SSO. Eighty-three percent of pits with SSO residues were found primarily in middle to upper intertidal locations. SSO residues commonly occurred in a discontinuous approximately 3 cm thick band 5-10 cm below the boulder/cobble or pebble/gravel veneer. The SO and SSO occurrences in the 2002 survey closely match the locations where they were found in 1992 and earlier surveys; however, in 2002 residual SSO patches are more discontinuous and thinner than they were in the earlier surveys. These sites are biased toward SSO persistence; those that have SSO residues represent less than 0.5% of the originally oiled shorelines in PWS. Despite evidence of continued oil weathering, both at the surface and in the sub-surface, it is clear that the natural cleaning processes at these particular locations are slow. The slow weathering rates are a consequence of the oil residue being incorporated in finer sediments (fine sand, silt, mix) and isolated from active weathering processes as boulders and outcrops, shallow bedrock asperities, or boulder-armoring create wave shadows and limit effective physical action on shorelines.

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Year:  2008        PMID: 18187161     DOI: 10.1016/j.marpolbul.2007.11.008

Source DB:  PubMed          Journal:  Mar Pollut Bull        ISSN: 0025-326X            Impact factor:   5.553


  11 in total

1.  Beach geomorphic factors for the persistence of subsurface oil from the Exxon Valdez spill in Alaska.

Authors:  Yuqiang Xia; Michel C Boufadel
Journal:  Environ Monit Assess       Date:  2011-02-19       Impact factor: 2.513

2.  Monitoring of PAHs and alkylated PAHs in aquatic organisms after 1 month from the Solar I oil spill off the coast of Guimaras Island, Philippines.

Authors:  Seiichi Uno; Jiro Koyama; Emiko Kokushi; Harold Monteclaro; Sheryll Santander; J Orkuma Cheikyula; Shizuho Miki; Nathaniel Añasco; Ida G Pahila; Hilario S Taberna; Tatsuro Matsuoka
Journal:  Environ Monit Assess       Date:  2009-05-16       Impact factor: 2.513

3.  A Conceptual Model of Natural and Anthropogenic Drivers and Their Influence on the Prince William Sound, Alaska, Ecosystem.

Authors:  Mark A Harwell; John H Gentile; Kenneth W Cummins; Raymond C Highsmith; Ray Hilborn; C Peter McRoy; Julia Parrish; Thomas Weingartner
Journal:  Hum Ecol Risk Assess       Date:  2010-08-23       Impact factor: 5.190

4.  A Quantitative Ecological Risk Assessment of the Toxicological Risks from Exxon Valdez Subsurface Oil Residues to Sea Otters at Northern Knight Island, Prince William Sound, Alaska.

Authors:  Mark A Harwell; John H Gentile; Charles B Johnson; David L Garshelis; Keith R Parker
Journal:  Hum Ecol Risk Assess       Date:  2010-08-23       Impact factor: 5.190

5.  Long-Term Ecological Impacts from Oil Spills: Comparison of Exxon Valdez, Hebei Spirit, and Deepwater Horizon.

Authors:  Mace G Barron; Deborah N Vivian; Ron A Heintz; Un Hyuk Yim
Journal:  Environ Sci Technol       Date:  2020-04-15       Impact factor: 9.028

6.  Environmental management: integrating ecological evaluation, remediation, restoration, natural resource damage assessment and long-term stewardship on contaminated lands.

Authors:  Joanna Burger
Journal:  Sci Total Environ       Date:  2008-08-06       Impact factor: 7.963

7.  Quantitative Assessment of Current Risks to Harlequin Ducks in Prince William Sound, Alaska, from the Exxon Valdez Oil Spill.

Authors:  Mark A Harwell; John H Gentile; Keith R Parker; Stephen M Murphy; Robert H Day; A Edward Bence; Jerry M Neff; John A Wiens
Journal:  Hum Ecol Risk Assess       Date:  2012-03-16       Impact factor: 5.190

8.  Quantifying population-level risks using an individual-based model: sea otters, Harlequin Ducks, and the Exxon Valdez oil spill.

Authors:  Mark A Harwell; John H Gentile; Keith R Parker
Journal:  Integr Environ Assess Manag       Date:  2012-03-12       Impact factor: 2.992

9.  Oil biodegradation and bioremediation: a tale of the two worst spills in U.S. history.

Authors:  Ronald M Atlas; Terry C Hazen
Journal:  Environ Sci Technol       Date:  2011-07-08       Impact factor: 9.028

10.  Assessing Risks to Sea Otters and the Exxon Valdez Oil Spill: New Scenarios, Attributable Risk, and Recovery.

Authors:  Mark A Harwell; John H Gentile
Journal:  Hum Ecol Risk Assess       Date:  2014-02-06       Impact factor: 5.190

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