Environmental Vulnerability of the Coastal Environments of Western Perak to Oil Spills

Author(s):  
C.W. Sum ◽  
B.J. Pierson ◽  
A.A. Kadir ◽  
Z.Z.T. Harith ◽  
U. Teknologi
2008 ◽  
Author(s):  
Chow Weng Sum ◽  
Bernard J. Pierson ◽  
Askury A. Kadir ◽  
Zuhar Zahir Tuan Harith

2008 ◽  
Author(s):  
Chow Weng Sum ◽  
Bernard J. Pierson ◽  
Askury A. Kadir ◽  
Zuhar Zahir Tuan Harith

2020 ◽  
Author(s):  
Olga Kalinka

The analytical review was prepared to assess coefficients of priority protection the features of special significance for mapping the vulnerability of marine coastal zones from oil pollution. Nowadays, this issue is a rather complex scientific problem, because there is no consensus on how to evaluate, calculate and how to present them. In most cases, such coefficients are given by one or more parameters in relative units (points, ranks). As a rationale, only criteria are given, taking into account which it is determined how much one object is more important for protection than another, and specific values are based mainly on the subjective expert’s opinion and are therefore ambiguous. At the same time, the availability of maps showing the environmental vulnerability of marine coastal zones is very important in case of emergency oil spills, as it facilitates the indicating of priorities for cleaning, especially at the initial stages of spill response and minimizes potential damage to the natural and man-made environment. This paper proposes approaches, where the basis for obtaining quantitative standardizable indicators of priority protection the features of special significance presented with minimal subjectivity and maximum generality.


2020 ◽  
Vol 267 ◽  
pp. 115238
Author(s):  
Caroline Barbosa Monteiro ◽  
Phelype Haron Oleinik ◽  
Thalita Fagundes Leal ◽  
Wiliam Correa Marques ◽  
João Luiz Nicolodi ◽  
...  

1979 ◽  
Vol 1979 (1) ◽  
pp. 193-198 ◽  
Author(s):  
Miles O. Hayes ◽  
Erich R. Gundlach ◽  
Laurent D'Ozouville

ABSTRACT Between 60,000 and 65,000 tons of the Amoco Cadiz oil came ashore along approximately 70 km of the shoreline of Brittany during the first few weeks of the spill (March 16–30, 1978). A prevailing westerly wind pushed the oil against west-facing headlands and into shoreline embayments as it moved east. A wind reversal in early April moved the oil in the opposite direction, contaminating previously untouched areas and transporting the oil as far southwest as Pointe du Raz (southwest of Brest). At the end of April, the total volume of oil onshore was reduced to approximately 10,000 tons but by that time more than 300 km of shoreline had been contaminated. The details of oil erosion and burial were determined by resurveying 19 permanent beach profiles established during the first few days of the spill. These stations, plus an additional 147 beach observation stations, were revisited one month after the spill. Coastal processes and geomorphology played a major role in the dispersal and accumulation of the oil once it came onshore. For example, oil accumulated at the heads of crenulate bays and on tombolos (sand spits formed in the lee of offshore islands). Local sinks, such as scour pits around boulders, bar troughs (runnels), marsh pools, and joints and crevasses in rocks, tended to trap oil. Classification of the coastal environments of the Amoco Cadiz oil spill site, according to an oil spill vulnerability index (scale of 1–10 on basis of potential oil spill damage), revealed a good correlation with earlier findings at the Metula and Urquiola oil spill sites. For example, exposed rocky coasts and wave-cut platforms (stations 1 and 2) were cleaned of extremely heavy doses of oil within a few days. Sheltered rocky coasts (station 8), sheltered tidal flats (station 9) and estuarine marsh systems (station 10) proved to be the most vulnerable of all coastal environments to oil spill damage. These observations provide encouragement and incentive to continue to apply the vulnerability index to areas in the United States threatened by potential oil spills. The Brittany coastline is particularly analogous to the coastline of Maine and parts of southern Alaska.


2017 ◽  
Vol 2017 (1) ◽  
pp. 1806-1818 ◽  
Author(s):  
Diana Ibarra-Mojica ◽  
Ágata Romero ◽  
Crisóstomo Barajas-Ferreira ◽  
Viatcheslav Kafarov ◽  
Crisóstomo Barajas-Solano

ABSTRACT 2017-397 Rivers have been a major part in the development of human activities since the beginning of civilization. Globally, increased navigation in rivers and construction of oil storage infrastructure along its banks has increased the risk of spillage of these substances in freshwater bodies. Mitigation associated with such incidents impact depends largely on the formulation and implementation of adequate contingency plans. To make this possible the vulnerability assessment is a tool of primary information which integrates the identification of possible sources of hydrocarbon’s spills and the respective dispersion patterns (evaluation of susceptibility); as well as analysis of areas that could be more seriously affected by the presence of those spills (sensitivity testing). There are known methodologies and study cases for assessing vulnerability to oil spills in marine and coastal environments; however, for rivers there are not references of this type of work. This paper presents a methodological adaptation for assessing environmental vulnerability for oil spills in rivers, from the integration of known methodologies for evaluation of sensitivity and susceptibility in coastal marine and river environments. Given its standardization and wide use, the ESI (NOAA) method was selected for river sensitivity assessment. It was not considered necessary to have a standardized method for trajectory modeling and hydrocarbons spill degradation (susceptibility analysis), but it was established that in each case of study the selected tool must analyze the determinant processes as advection, adhesion to the edges, mechanical dispersion, evaporation, dissolution, and vertical mixing. Finally, an adaptation of the Index of Environmental Vulnerability to Oil (IEVO) was proposed. At the moment, the application of the methodology is being carried out in a river of Colombia, however the results still unfinished will not be part of the discussion of the work below.


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