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11. TRANSBOUNDARY IMPACTS

11.1 Introduction

The DAN project refers to the platform Dan F, Dan B, Dan E, Kraka and Regnar. An

environmental and social impact assessment (EISA-16) is undertaken for the remaining lifetime of the ongoing projects, and the entire life time from exploration to decommissioning for planned projects. The ESIA-16 shall replace the EIA conducted in 2010 “Environmental impact

assessment from additional oil and gas activities in the North Sea, July 2011” which is valid for the period 1st January 2010 to 31st December 2015.

Notifications for the DAN project were forwarded to the relevant German authorities in

accordance with article 3.1 of the Espoo convention. The German authorities have expressed the wish to participate in the hearing for the ESIS DAN.

In this section, a summary of the DAN project and its likely significant transboundary impacts is provided. The section is focused on providing sufficient information to facilitate the identification of possible transboundary impacts. The rationale and support for the attributed level of

significance and spatial extent can be found in detail in the relevant sections of the ESIS (section 6 and 7).

11.2 ESPOO convention

The ESPOO convention states that the concerned parties likely to be affected by transboundary adverse significant impacts are to be informed of and provided with possibilities for making comments or objections on the proposed activity.

The DAN project can be found as item 15 (offshore hydrocarbon production) on the list of activities in appendix I to the convention, that are likely to cause a significant adverse transboundary impact.

11.3 The DAN project

11.3.1 Existing production and processing facilities

The DAN project, including the three platforms Dan F, Dan B and Dan E as well as the satellite platform Kraka and the subsea wellhead Regnar. Production was initiated at Dan B in 1972, then later at Dan Dan E (1977), Dan F (1987), Kraka (1991) and Regnar (1993). The total production peaked in 2000 and has been on a natural decline since. Maersk Oil has the license to explore for and produce oil and gas was extended until 8 July 2042.

Dan F is primarily an oil producing and oil processing platform that receives, processes and sends the Dan field production to Gorm (oil) and Tyra (gas). Regnar is an unmanned subsea wellhead, while Kraka is an unmanned satellite wellhead platform.

The processing facilities include hydrocarbon processing equipment (oil stabilisation, gas processing and processing of production water), auxiliary safety systems such as an emergency shutdown system, emergency blow-down system, fire and gas detection system, firewater system, etc.

Figure 11-1 Maersk Oil North Sea projects TYRA, HARALD, DAN, GORM and HALFDAN.

11.3.2 Planned development activities

The following main activities are planned to continue and optimise the production for the DAN project and potentially access new hydrocarbon resources:

 Seismic investigations to provide information to interpret the geological structure of the subsurface and to identify the location and volume of remaining and potential new

hydrocarbon reserves. Seismic data is also acquired as part of drilling hazard site surveys to map and identify potential hazards to the installation of drilling rigs and to the drilling operation. Seismic data are also acquired as part of seabed and shallow geophysical surveys to map seabed and shallow soil conditions for the design and installation of pipelines, platforms and other structures.

 Construction of up to five new platforms (four wellhead platforms and an accommodation platform), along with connecting pipelines

 Drilling of up to 57 wells (43 new wells, and 14 redrilling from existing wells) can be expected as part of the DAN project. Drilling is performed from a drilling rig, which is placed on the seabed. Different types of drilling mud will be used based on the well and reservoir

properties. Water-based mud and cuttings will be discharged to the sea, whereas oil-based mud and cuttings will be brought onshore to be dried and incinerated.

 Well stimulation will be performed to facilitate hydrocarbon extraction (for a production well) or water injection (for an injection well).

 Decommissioning will be done in accordance with technical capabilities, industry experience, relevant international conventions and under the legal frameworks at the time of

decommissioning.

11.3.3 Accidental events

As part of the production, accidental spills of oil, gas or chemical may occur. There is a risk of accidents that could lead to major significant environmental and social impacts, such as vessels collisions, large pipeline rupture or a well blow out. The risk of a well blowout is very unlikely.

DAN

11.3.4 Alternatives Project alternative

The 0 alternative (zero alternative) is a projection of the anticipated future development without project realization, and describes the potential result if nothing is done. For the DAN project, this would mean that the production would cease. If no production is undertaken by Maersk Oil for the DAN project area in the North Sea, there will be no contribution from the DAN project to the Danish economy or security of hydrocarbon supply and employment.

Tehcnical alternatives

Best environmental practice for the different type of activities planned for the DAN project (seismic, pipelines and structures, production, drilling, well stimulation, transport and decommissioning) is continuously monitored and applied when feasible.

Alternative location

The DAN project is a continuation of production and activities at existing facilities. As such, there is no alternative location for the project.

11.4 Identified impacts – planned activities

Potential impacts to environmental and social receptors during planned activities at the DAN project have been assessed in section 6. A summary of the potential worst case impacts is presented in Table 11-1.

Table 11-1 Summary of potential impacts on environmental and social receptors from planned activities at the DAN project. The impact with the largest overall significance is provided for each receptor (without mitigating measures).

Receptor Worst case potential impact

Extent Overall significance of impact

Hydrography Local Minor negative

Climate and air quality Transboundary Moderate negative

Water quality Local Minor negative

Sediment type and quality Local Minor negative

Plankton Local Minor negative

Benthic communities Local Minor negative

Fish Local Minor negative

Marine mammals Local or regional Moderate negative

Seabirds Local Minor negative

Cultural heritage None None

Protected areas (UNESCO, nature reserve) None None

Natura 2000 No significant environmental effects

Marine spatial use Local Negligible negative

Fishery Local Negligible negative

Tourism None None

Employment and tax revenue Local or national Positive Oil and gas dependency Local or national Positive

Transboundary adverse impacts have been identified for climate and air quality, where the emissions from the DAN project may have a minor contribution to climate change and air pollution. Maersk Oil has implemented a structured energy efficiency process and conduct a comprehensive review to identify ways to improve energy efficiency offshore. The production has become more energy efficient over the years, and in 2013 the environmental management system at Maersk Oil was ISO-14001 certified.

No other significant adverse transboundary impacts have been identified for the planned activities at the DAN project.

A Natura 2000 screening is presented for the planned activities. It is assessed that the planned activities will have no significant environmental effects on the conservation objectives of the habitat types or species in the national and international Natura 2000 sites (section 10).

11.5 Identified impacts – accidental events

Potential impacts to environmental and social receptors during accidental events from the DAN project have been assessed in section 7. A summary of the worst case potential impacts (without mitigating measures) is presented in Table 11-2.

Table 11-2 Summary of potential impacts on environmental and social receptors for accidental events at the DAN project. The impact with the largest overall significance is provided for each receptor (without mitigating measures).

Receptor Worst case potential impact

Extent Overall significance of impact Climate and air quality Transboundary Moderate negative

Water quality Transboundary Moderate negative

Sediment type and quality Transboundary Moderate negative

Plankton Transboundary Minor negative

Benthic communities Transboundary Major negative

Fish Transboundary Major negative

Marine mammals Transboundary Major negative

Seabirds Transboundary Major negative

Cultural heritage National Moderate negative

Protected areas (UNESCO, nature reserve) Transboundary Major negative

Marine spatial use Transboundary Moderate negative

Fishery Transboundary Major negative

Tourism Transboundary Major negative

If a major oil spill occurs, there is a risk of major negative transboundary impacts. The risk of a major oil spill is very unlikely, but could potentially have significant, adverse transboundary impacts. Oil released could cross maritime boundaries with Norway, Germany, the Netherlands and the UK. The oil spill modelling identified the north and west of Denmark and south Norway as most vulnerable to oil beaching, although Germany, UK and the Netherlands could also be

affected.

Maersk Oil acts according to the zero tolerance for spills policy. Measures are introduced to reduce the volume and number of spillage, and Maersk Oil follows industrial best practices for prevention of accidents based on identification of major hazards assessed through risk assessment. Emergency response and contingency planning are also developed to limit the consequences of a major accident related to its projects