Country Case Study: Wakashio Oil Spill in Mauritius | |
Module 7 | |
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Overview | |
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Case study location | |
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Past incident | |
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MV Angel in August 2011 | |
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Past incident | |
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MV Benita in July 2016 | |
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Vessel had onboard around 145 MT HFO (380 CST), 42 MT diesel oil and 19 000 L Lube Oil.
Recent incident | |
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MV Wakashio in July 2020 | |
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25 July 2020: Grounding of MV Wakashio | |
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No oil spill was observed at that time.
Oil spill response structure | |
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provides the organisational structure and procedures for preparedness and response to oil spills.
responsible for coordination of the NOSCP.
coastal sensitive areas which required special protection. | |
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Identification of Environmentally Sensitive Areas | |
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Environmentally Sensitive Areas (ESAs) | |
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06 August 2020: Oil spill occurred from MV Wakashio | |
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Around 841 tons of LSFO spilled out
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Mahebourg waterfront | |
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Riviere des Creoles area | |
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Riviere des Creoles area | |
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Bambous Virieux Area | |
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Degree of shoreline contamination within affected areas | |
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Segmentation of affected shoreline | |
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Overview of affected shoreline | |
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(i) Fringe mangrove: Mangrove dominates most contaminated sites within the affected area. This ecologically sensitive habitat was typically found in the form of a relatively narrow fringe on the lower and mid-shore. The sites were sheltered, with a substrate of mud, sand, and scattered basalt boulders in places. | |
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Overview of affected shorelines | |
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Overview of affected shoreline | |
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Overview of affected shoreline | |
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Site prioritization | |
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Clean-up techniques | |
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The following shoreline clean-up techniques were applied to the affected sites, depending on the following key criteria: • Substrate and shoreline type • Environmental sensitivity • Amenity value / public use / tourism • Access and safety for workers | |
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Clean-up techniques | |
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Manual cleaning This technique is typically the first one to be applied to a site, for the removal of oil accumulations and oily debris. This will include all sites, but particularly those with mangrove, rip-rap and other substrates (natural or not) that can create traps for oil and debris, and that have not already been cleaned by the various local teams. | |
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Clean-up techniques | |
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High-Volume Low-Pressure Flushing Flushing consists of rinsing the oily substrate by applying large volumes of seawater at low pressure and ambient temperature using pumps to dislodge trapped oil, lift oil out of the sediment and re-float it before containing and recovering it using either skimmers or sorbents. | |
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Clean-up techniques | |
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Skimming This technique involves recovering oil from the water surface with the help of skimmers floating on the surface of the water. | |
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Clean-up techniques | |
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Hot-Water High-Pressure Washing Once the oil layers have been removed, high pressure cleaning is used on low sensitivity "hard" substrates such as rip-rap, concrete walls or natural rocks where a high level of cleanliness is required. | |
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Determinants of clean-up end points | |
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Determinants of clean-up end points | |
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Determinants of clean-up end points | |
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Determinants of clean-up end points | |
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Determinants of clean-up end points | |
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Outcomes of clean-up endpoints site visits | |
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Waste management | |
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Waste management | |
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Waste management | |
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Thank you | |
UNEP-Norway Partnership | |
United Nations Avenue, Gigiri PO Box 30552 – 00100 GPO Nairobi, Kenya | www.unep.org |