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ENVIRONMENTAL STATEMENT BARDOLINO DEVELOPMENT

ENVIRONMENTAL STATEMENT BARDOLINO DEVELOPMENT

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Bardolino Development Environmental Statement<br />

3.4.7 Cementing Chemicals<br />

Cement is used to secure the steel casing in the well bore, and the cementing chemicals are<br />

used to modify the technical properties of the cement slurry. During cementing operations,<br />

the majority of these chemicals are left downhole but a small quantity of cement may be<br />

discharged onto the seabed around the top of the casing. However, the chemicals used will<br />

be contained within inert cement and will therefore not pose a threat to the marine<br />

environment. Careful estimates of the final volume of the hole will be made during drilling,<br />

and the volume of cement used will be adjusted accordingly to minimise the risk of excess<br />

cement being squeezed out of the hole onto the seabed.<br />

A number of chemicals will need to be added to the cement. The exact chemical constituents<br />

required to formulate the cement will be confirmed during the final stages of well design.<br />

They will be included in the detailed chemical risk assessment of the PON 15B which will be<br />

submitted to BERR at least 28 days prior to commencement of drilling activities as required<br />

by the Offshore Chemical Regulations 2002.<br />

3.4.8 Contingency Chemicals<br />

Contingency chemicals will be held on the rig for use in unplanned events. Potential<br />

applications would be to free a stuck drill string, or seal highly porous or fractured zones to<br />

prevent the uncontrolled loss of drilling fluid. A detailed risk assessment for contingency<br />

chemical use will be submitted to BERR as required by the Offshore Chemical Regulations<br />

2002.<br />

3.4.9 Handling Mud and Cuttings<br />

Once on board the rig, drill cuttings are removed from the drilling mud by solids control<br />

equipment. Where LTOBM is used the mud and cuttings will be treated by the solids control<br />

equipment before being intercepted by a collection device. The cuttings will be transferred<br />

from the solids control equipment and then either dried and collected in skips ready for<br />

transfer to a supply vessel, or slurrified and pumped directly to the bulk tanks of a supply<br />

vessel for transport to shore. Once onshore the cuttings are processed until they have very<br />

low oil content and then disposed of. The base oil residue recovered during this process is<br />

returned to the mud company.<br />

Shell’s “Ship to Shore Cuttings Disposal Guidelines” will be followed during the planned<br />

LTOBM phase. In the event of unexpected hole conditions (e.g. faster than expected<br />

penetration rates), equipment breakdown or failure, or operational and logistics downtime due<br />

to adverse weather conditions, contingency arrangements will be in place to permit storage of<br />

cuttings on board the rig until normal operations are resumed. If necessary, unless personnel<br />

safety or installation integrity is threatened, drilling will cease in preference to the discharge of<br />

LTOBM-coated cuttings to sea. However, in the event of a major safety incident where no<br />

compromise on safety risks to personnel or asset can be made, the contingency will exist to<br />

divert limited quantities of cuttings overboard.<br />

3.4.10 Well Clean-up and Testing Operations<br />

Once drilling has been completed, the Bardolino well will be circulated clean prior to<br />

completion, and then tested. The exact chemicals required for these processes will be<br />

included in the chemical risk assessment of the PON 15B as required by the Offshore<br />

Chemical Regulations 2002. Hydrocarbons produced during the well flow clean-up and<br />

testing will be flared.<br />

The aim of well clean-up is to remove detritus from the well prior to running the completion. It<br />

also removes solids that could impair both mechanical operations in the well bore and<br />

reservoir performance once the well has been perforated.<br />

The potential emissions from well clean-up and testing of the development well have been<br />

calculated based on a total testing and clean-up period of 48 hours with a maximum of 15,000<br />

bbls of oil, with an expected GOR of 870 scf/bbl (<br />

Table 3.4). This represents a worst case for emissions. There is no intention to perform an<br />

extended well test, and it is likely that the quantity of oil flared during well clean-up and testing<br />

April 2008 Page 3-11

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