The effects of spilled oil on coastal ecosystems: lessons from the Exxon Valdez spill

2014 ◽  
pp. 311-346 ◽  
Author(s):  
James L. Bodkin ◽  
Dan Esler ◽  
Stanley D. Rice ◽  
Craig O. Matkin ◽  
Brenda E. Ballachey
1991 ◽  
Vol 1991 (1) ◽  
pp. 453-460 ◽  
Author(s):  
Miles O. Hayes ◽  
Jacqueline Michel ◽  
David C. Noe

ABSTRACT Several major oil spills of record (including the 1974 Metula spill, the 1978 Amoco Cadiz spill, and the 1989 Exxon Valdez spill) occurred along shorelines with abundant gravel beaches. Observations of these spills help in understanding factors controlling the initial deposition and long-term fate of spilled oil in such locations. Gravel beaches are most common on rocky, glaciated coasts (Holocene and/or Pleistocene). For example, leading-edge coastlines in subpolar to polar regions, of which the Alaska coast is a prime example, may have gravel beach deposits along more than 50 percent of their length. Spilled oil coming onshore in such gravel areas is likely to remain for a long time (up to decades), because of the potential for deep penetration and burial of the oil in the coarse sediments. The detailed, three-dimensional configuration of gravel beach deposits is affected by the internal characteristics of the waves shaping the beach (reflective or dissipative). Reflective waves typically produce steep, coarse, cuspate berms, which allow for deep penetration and burial in the beach face/berm areas. Dissipative waves typically build intertidal swash bars that may move landward and bury oil deposits, such as asphalt pavements. It would be useful for future contingency mapping projects to include this distinction on maps of gravel beaches. The formation of armoring (structural strengthening) of a gravel beach surface impedes erosion and sediment transport. Therefore, such beaches are likely to retain buried oil longer than those without armoring. Gravel beaches, because they are commonly located along plate margins, are usually subject to tectonic readjustment. The Exxon Valdez spill occurred along a shoreline out of equilibrium as a result of the 1964 earthquake. Uplift and downwarp is on the order of 1 to 3 meters throughout most of the area of the spill. Almost every coastal location affected by the spill is undergoing readjustment, causing many site-specific interpretive problems related to burial, penetration, and hydraulic flushing. For example, in many areas, a thin gravel veneer of armor overlies uplifted rock platforms and/or fine-grained bay bottom, or downwarped soil horizons, which served as either zones of oil accumulation or pathways of hydraulic flushing, depending on local conditions.


1990 ◽  
Vol 8 (3) ◽  
pp. 228-230 ◽  
Author(s):  
S. Harvey ◽  
I. Elashvili ◽  
J. J. Valdes ◽  
D. Kamely ◽  
A. M. Chakrabarty

Author(s):  
Verónica Lango-Reynoso ◽  
Karla Teresa González-Figueroa ◽  
Fabiola Lango-Reynoso ◽  
María del Refugio Castañeda-Chávez ◽  
Jesús Montoya-Mendoza

Objective: This article describes and analyzes the main concepts of coastal ecosystems, these as a result of research concerning land-use change assessments in coastal areas. Design/Methodology/Approach: Scientific articles were searched using keywords in English and Spanish. Articles regarding land-use change assessment in coastal areas were selected, discarding those that although being on coastal zones and geographic and soil identification did not use Geographic Information System (GIS). Results: A GIS is a computer-based tool for evaluating the land-use change in coastal areas by quantifying variations. It is analyzed through GIS and its contributions; highlighting its importance and constant monitoring. Limitations of the study/Implications: This research analyzes national and international scientific information, published from 2007 to 2019, regarding the land-use change in coastal areas quantified with the digital GIS tool. Findings/Conclusions: GIS are useful tools in the identification and quantitative evaluation of changes in land-use in coastal ecosystems; which require constant evaluation due to their high dynamism.


Author(s):  
Hideki Kokubu ◽  
Hideki Kokubu

Blue Carbon, which is carbon captured by marine organisms, has recently come into focus as an important factor for climate change initiatives. This carbon is stored in vegetated coastal ecosystems, specifically mangrove forests, seagrass beds and salt marshes. The recognition of the C sequestration value of vegetated coastal ecosystems provides a strong argument for their protection and restoration. Therefore, it is necessary to improve scientific understanding of the mechanisms that stock control C in these ecosystems. However, the contribution of Blue Carbon sequestration to atmospheric CO2 in shallow waters is as yet unclear, since investigations and analysis technology are ongoing. In this study, Blue Carbon sinks by Zostera marina were evaluated in artificial (Gotenba) and natural (Matsunase) Zostera beds in Ise Bay, Japan. 12-hour continuous in situ photosynthesis and oxygen consumption measurements were performed in both areas by using chambers in light and dark conditions. The production and dead amount of Zostera marina shoots were estimated by standing stock measurements every month. It is estimated that the amount of carbon storage as Blue Carbon was 237g-C/m2/year and 197g-C/m2/year in the artificial and natural Zostera marina beds, respectively. These results indicated that Zostera marina plays a role towards sinking Blue Carbon.


Sign in / Sign up

Export Citation Format

Share Document