Elsevier

Toxicology Letters

Volume 128, Issues 1–3, 10 March 2002, Pages 55-68
Toxicology Letters

The wreckage of the oil tanker ‘Erika’—human health risk assessment of beach cleaning, sunbathing and swimming

Dedicated to the late Philip Chambers
https://doi.org/10.1016/S0378-4274(01)00533-1Get rights and content

Abstract

In December 1999 the oil tanker ‘Erika’, carrying approximately 30 tons of heavy fuel oil, wrecked before the coast of Brittany (France), polluting the local beaches and rocks over a distance of some 500 km. Also numerous birds were affected. During the first months of 2000 the coastal area and many birds were cleaned. The health risk for people involved in these cleaning activities and for tourists was evaluated with emphasis on the carcinogenic properties of this oil. The outcome indicates that the risks were limited to people who had been in bare-handed contact with the oil. Firstly they had an increased risk for developing skin irritation and dermatitis, however, these effects are in general reversible. Secondly they had an increased risk for developing skin tumours, but since the dermal contacts with the oil were of relative short duration, this risk is considered to be very limited.

Introduction

On Sunday December 12, 1999, the 30 000 ton Maltese oil tanker ‘Erika’ wrecked on the Atlantic Ocean about 65 km south of Penmarch (Brittany, France), causing a spillage of approximately 10 000 tons of oil, contaminating the French coast and its small islands from Southern Brittany to the Vendée over about 400–500 km (Fig. 1). For a large part, cleaning of the polluted coast had to be done by hand due to the rough and rocky nature of the coast; in addition numerous oil-contaminated birds were cleaned.

Early February 2000, the French Ministry of the Environment (Ministère de l'Aménagement du Territoire et de l'Environnement, Direction de la Prévention et des Risques, Paris) asked the Dutch National Institute of Public Health and the Environment (RIVM) for an independent risk assessment for humans involved in the beach-cleaning operations, at mid-April followed by a similar request dealing with tourist activities on these beaches.

Section snippets

General

In the assessment of the health risk for people involved in activities on the contaminated beaches, two types of risk associated with fuel oil #6 components have to be considered: the risk due to toxicity and the risk due to carcinogenicity. In assessing toxic risks the actual exposure levels are compared with limit values taken from the literature; in assessing carcinogenic risks the actual exposure levels are compared with the 1:104 lifetime excess risk for developing tumours.

Inhalation exposure

Regarding oil in

General

In cleaning an oil spillage the exposure routes of consideration are in general the inhalation and the dermal route; oral exposure is prevented by appropriate safety measures and safety instructions.

Estimation of the potential inhalation exposure in cases of oil spillage is very difficult due to the general lack of data and the highly varying composition of heavy fuel oils in general. However, due to the low volatility of fuel oils, human exposure to vapour concentrations of toxicological

Beach and bird cleaning

For people cleaning the beaches the actual inhalation after correction with a factor of (8/24)×(5/7) for continuous exposure time during at least a full week (except the inhalation of volatile organic compounds because this particular exposure is compared with a limit value for occupational health) is for the larger part well below the limit values (Table 7 part 1). For benzene (which is carcinogenic), however, the corrected inhalation for continuous exposure time during at least a full week

Conclusion

At first instance the health risks for people (among which many volunteers) cleaning the beaches and the birds immediately following the fuel oil #6 spillage resulting from the wreckage of the ‘Erika’ appeared to be considerable. Hence there was an urgent need for an evaluation of these risks to allow the local and national authorities to take proper measures. The risk estimation, however, was hampered by (1) a general lack of detailed chemical–analytical and exposure data of this particular

Acknowledgements

I thank Drs. Ada Knaap, Hans Könemann, Cees van Leeuwen and Moniek Pieters of the RIVM Centre for Substances and Risk Assessment for their valuable contributions and for critically reviewing the manuscripts of the reports on which this article is based. In addition I appreciate the valuable comments of Drs. Ada Knaap and Hans Könemann on this article's manuscript. I greatly valued the excellent co-operation with Dr. André Cicolella (Institut National de l'Environnement Industriel et des Risques

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    This article is based on RIVM-CSR report no. 000/383 CSR WK/tk dated 19 April 2000 and the addendum report (same number) dated 7 June 2000.

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