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2007_6_Nr6_EEMJ

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Robu et al. /Environmental Engineering and Management Journal 6 (<strong>2007</strong>), 6, 573-592<br />

environmental competent authority to request a risk<br />

assessment with the aim at evaluating the probability<br />

of harm and at finding the possible prejudiced<br />

entities. Not every site affected by a certain pollutant<br />

will exhibit the same risk or will need the same level<br />

of remediation. The risk assessment is defined by the<br />

World Bank as being a process for identification,<br />

analysis and control of the danger appeared due to<br />

the presence of a hazardous substance into a plant.<br />

The Report from 1992 of the British Royal Society<br />

explains the sense of the definition given in the<br />

Directive European Commission 93/67/EEC,<br />

enlightening the components of risk assessment,<br />

meaning the risk estimation and calculus.<br />

In consequence, the risk assessment involves<br />

an estimation (including the identification of the<br />

hazards, the magnitude of the effects and the<br />

probability of occurrence) and a calculus of the risk<br />

(including the quantification of the danger importance<br />

and consequences for humans and/or environment).<br />

Risk assessment aims at controlling the risks<br />

produced on a site by identification of:<br />

• Pollutant agents or the most important<br />

hazards;<br />

• Resources and receptors exposed to the risk;<br />

• Mechanisms of risk accomplishment;<br />

• Important risks that emerge on the site;<br />

• General measures needed for reduction of<br />

the risk to an accepted level.<br />

The risk depends on the nature of impact<br />

upon the receptors but also on the probability of the<br />

occurrence of this impact. Identification of the critical<br />

factors that influence the relationship source-pathreceptor<br />

involves the detailed characterization of the<br />

site from physical and chemical point of views.<br />

Generally, the quantitative risk assessment<br />

encloses five stages:<br />

• description of the aim;<br />

• identification of the hazard;<br />

• identification of the consequences;<br />

• estimation of the magnitude of the<br />

consequences;<br />

• estimation of the probabilities of the<br />

consequences.<br />

Concordant to Order to 184/1997, the risk is<br />

the probability that a negative effect to occur in a<br />

specified period of time and is often described by the<br />

relation:<br />

Risk = Danger x Exposure<br />

The risk assessment implies the<br />

identification of the hazard and of consequences that<br />

may appear as a result of occurrence of the events<br />

considered as risk sources. In function of the<br />

importance of the consequences one may decide if<br />

there is necessary or not to take remediation<br />

measures. Concordant to the Order no. 184/1997, the<br />

risk quantification is based on a simple system of<br />

classification, where the probability and severity of an<br />

event are descendent distributed, being assigned with<br />

an arbitrary score:<br />

Simplified model<br />

Probability Severity<br />

3 = high 3 = major<br />

2 = medium 2 = medium<br />

1 = low 1 = insignificant<br />

This model is used not only for qualitative,<br />

but also for quantitative risk assessment. Thus, the<br />

risk may be calculated by multiplying the two factors<br />

(probability, severity) in order to obtain a<br />

comparative number, for example 3 (high probability)<br />

x 2 (medium severity) = 6 (high risk). This allows the<br />

comparison of different risks.<br />

The greater the results, the bigger the priority<br />

should be given to risk control. This basic technique<br />

may be developed for allowing more serious analysis<br />

by increasing the range of the scores for classification<br />

and by considering a bigger number of improved<br />

definitions for major severity, increased probability<br />

etc. When a big number of important pollutants are<br />

considered for assessment, an increased attention<br />

should be paid to a clearer manner of presentation. It<br />

is often necessary to summarize the information as a<br />

control list or matrix.<br />

4. Quantitative risk analysis for port hydrocarbon<br />

logistics<br />

4.1. Brief review<br />

Over the last few decades much experience<br />

has been gained in the field of risk analysis of<br />

standard chemical or petrochemical plants.<br />

Nowadays, this knowledge is being applied to a wide<br />

range of industrial activities involving hazardous<br />

materials handling, including ports (Crowl, 2002,<br />

Gavrilescu, 2003; Robu, 2005). Nevertheless, few<br />

works approached the application of QRA to<br />

navigational aspects and terminal operations are<br />

available, and this is to the role played by SEVESO II<br />

Directive. This method allows quantitative risk<br />

analysis (QRA) to be performed on marine<br />

hydrocarbon terminals sited in ports. A significant<br />

gap is identified in the technical literature on QRA for<br />

the handling of hazardous materials in harbors<br />

published prior to this work Ports are environments<br />

often overloaded with hazardous materials, both in<br />

bulk and containerized.<br />

The method described here is proposed<br />

within a Spanish project called FLEXRIS and applied<br />

to the premises of the port of Barcelona, one of the<br />

largest ports on the Mediterranean Sea (Ronza et.al.,<br />

2006). Several risk assessment reports, made<br />

available to the public, proved to be a valuable source<br />

of information. What these works lack is an attempt at<br />

standardizing the process of risk assessment of<br />

navigation and loading operations for a generic<br />

port/terminal.<br />

580

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