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Environmental Statement - Maersk Oil

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5.2.2. DISCHARGES TO SEA<br />

5‐ 8<br />

Balloch Field Development <strong>Environmental</strong> <strong>Statement</strong><br />

Section 5 Assessment of Potential Impacts and Controls<br />

Routine discharges from vessels such as sewage are considered to have a negligible environmental<br />

impact and are therefore not considered here. Discharges assessed during the installation of the<br />

subsea infrastructure are associated with pipeline hydrotesting.<br />

Hydrotesting<br />

After installation and prior to being stabilised the lines will be flushed and hydrotested. It is<br />

anticipated that the lines will be tested using potable water and chemicals of the lowest possible<br />

Hazard Quotient (HQ). At the end of the testing operations, the hydrotest fluids will be discharged to<br />

sea.<br />

Concern over the impact of hydrotest water is due to the volume and types of chemicals discharged<br />

and the potential impact of chemicals on the marine environment. It is anticipated that only a single<br />

pipeline volume will be required for hydrotesting and, as such, chemical discharge will be a one‐off<br />

discharge; therefore, any effects from the discharge will be temporary. Based on the infrastructure<br />

listed in Table 2‐9 and assuming a tie‐in spool length of 20 m, a production spool inner diameter of 6”<br />

and a gas lift spool inner diameter of 3”,< 3m 3 of hydrotest water will be discharged during the testing<br />

operations of the production and gas lift jumpers and tie‐in spools at each well.<br />

The chemicals to be used are yet to be finalised; however, the dose and quantities will be in<br />

accordance with the manufacturer’s specifications and chemical permits will be sought prior to any<br />

chemical use or discharge using the relevant PON15 applications. Given the small volumes, the<br />

hydrotest fluids are expected to rapidly dilute in the marine environment.<br />

Proposed control measures for impacts associated with discharges to sea during the installation<br />

phase<br />

Control measures to mitigate impacts from discharges to sea associated with the installation phase<br />

are presented below.<br />

5.2.3. PHYSICAL PRESENCE<br />

The physical presence of the subsea infrastructure was assessed as being of low environmental risk;<br />

however, given the potential for impacts on other sea users and the seabed it was further assessed.<br />

Section 5.1.3 discusses the potential environmental impacts associated with the physical presence of<br />

vessels on other sea users and the marine environment. This section will therefore concentrate on<br />

the physical impacts of the subsea infrastructure.<br />

Subsea infrastructure<br />

Proposed Control Measures<br />

Chemicals of the lowest possible HQ will be used.<br />

Chemical use and discharge will be regulated under PON15C.<br />

The subsea infrastructure is likely to disturb the mobile benthic fauna and smother the mixed flora<br />

and fauna beneath. The structures could also cause a nuisance to fishing operations because of the<br />

potential snag risk. To mitigate against this, the X‐mas trees and cooling spools will be of a fishing<br />

friendly design.<br />

Table 5‐6 shows the area impacted by the subsea infrastructure using a worst case of three wells,<br />

with each at least 80 m from the DC2 manifold. The option chosen means that the area impacted is<br />

minimised as the only additional flow lines are the short jumpers required to connect the wellheads<br />

to the DC2 manifold. The maximum area impacted is anticipated to be 0.0008 km 2 .

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