5.3.15 Offshore oil & gas

All activity relating to off-shore oil and gas in the Irish sea is currently limited to exploration, rather than exploitation. Factors that could influence bottlenose dolphins within the cSAC in the exploratory and exploitation phases are considered here, although the latter is a wholly unknown area at present.

a.    Extent of activity

i.   Within the site

One block within the cSAC has been licensed for exploration for oil and gas by the DTI. Seismic survey was carried out by ARCO in the early 1990s who have subsequently relinquished their license. There is currently no exploitation of oil and gas resources in the southern Irish sea.

ii.  Adjacent to the site

All exploration activity has been or is being undertaken in blocks that lie to the north-west and south of the cSAC. Current levels of exploratory activity, ranging from seismic shooting to drilling in areas adjacent to the cSAC are low. Recently several oil companies holding exploration licenses for blocks within the bay have sought to surrender these to the DTI. In particular this means that whereas oil companies were previously required to conduct exploration drills as a condition of their license they are no longer required to do so where there are sufficient economic and geological reasons not to.

b.    Mechanisms for effects on the features

i.   Exploration

Seismic survey of the sea bed.

Seismic survey essentially involves the use of compressed air to generate high energy sounds, typically ranging between 10 and 200 Hz. Seismic shooting takes place via an array of air guns aimed at the sea bed. Intensive low frequency sounds penetrate the sea bed and are reflected back by different rock-types. The reflected sound waves are received by arrays of hydrophones, and reveal subsurface geological formations. During firing, high amplitude pulses lasting for ca. one second are emitted every 5-15 seconds. Water is an excellent conductor of sound, and sound (from man-made and natural sources) travels considerable distances through the water column. Seismic impulses travel large distances, beyond the area targeted for seismic survey. Small cetaceans have highly sensitive hearing, necessary for echolocation. Their hearing covers a very broad band width, and there is some overlap between sound frequencies emitted during the seismic activity and the hearing range of dolphins.

Research and monitoring carried out in the Irish sea and elsewhere suggests that seismic testing can adversely affect small cetaceans in the following ways:-

  • Direct effects: Possible damage to hearing, e.g. from a sudden burst of seismic activity at close range; disruption/disturbance to normal behaviour patterns e.g. temporary evacuation of the area effected by seismic testing [135] . See ‘Disturbance’.

  • Indirect effects: Possible impact on prey species (e.g. fish) resulting in temporary redistribution in or changes in the behaviour of shoaling fish [136] .

Since all seismic activity has been/is being conducted outside the cSAC boundary, any effects on bottlenose dolphins using the cSAC are likely to derive from exploration in licensed blocks adjacent to the cSAC. The significance of any such impacts would be determined (in part at least) by the distance between the animals and the point-source of activity during the seismic survey. See ‘Disturbance ’, page 55.

Shipping movements

In instances where exploratory activity moves beyond seismic survey, i.e. drilling, there is likely to be an increased level of localised shipping movements, associated with supplying the temporary drill rig (which could be on board a ship, or a "jack-up" rig). Activity may be highly localised, and of a temporary nature, whilst test drilling is in progress. It is unlikely that the area within the cSAC would be directly affected, however the dolphins could be indirectly affected by:-

Noise generated by shipping associated with drilling activity. See ‘Disturbance ’.

  • Pollution, e.g. from accidental spillages of fuel; rubbish; sewerage; bunkering/supply of drilling vessels/rigs with fuel (accidents during fuel transfer). See ‘Pollution’.

  • Collisions between shipping and dolphins. See ‘Collisions’.

Drilling

All exploratory drilling has been carried out, or is being carried out in areas to the west and south of the cSAC. Influences on bottlenose dolphins could arise from the following:

  • Pollution, e.g. oily water discharges, oil or fuel discharges/spillage's e.g. from rigs, well-heads or during bunkering operations (see above). Localised contamination of the sea bed as a result of disposal of drill cuttings and muds. Sewerage and litter. See ‘Pollution’ and ‘Entanglement & Ingestion’.

  • Noise from drills. Sustained noise pollution from drilling activities could possible induce changes in dolphin behaviour in the vicinity of the rig, and further a field. See ‘Disturbance ’.

ii.  Exploitation

The range of factors that could influence bottlenose dolphins within the cSAC should exploration be followed by development and exploitation of oil and/or gas reservoirs in the vicinity of the cSAC are broadly similar to those above. They include:

  • Pollution, from shipping associated with servicing of rigs, the rigs themselves, well-heads, pipelines and other infrastructure associated with extraction and movement of hydrocarbons, e.g.:

    • - Oil pollution e.g. bunkering accidents; collisions between ships and rigs; fractured pipelines.

    • - Sewerage

    • - Litter from rigs and ships

  • Contamination of the sea bed by drill cuttings and muds.

  • Noise from shipping associated with servicing of rigs; drilling operations

  • Collisions between dolphins and shipping.

  • Catastrophic events: it is possible that a "blow-out" on a rig could have an effect on bottlenose dolphins in the cSAC, e.g. through initial noise and/or any resultant pollution and cleanup operation.

Any actual impacts from the factors listed above would depend on a number of variablese.g. the distance between the drilling operations and the seaward boundary of the cSAC, the locations of dolphins at the time of any incident likely to impact on them, and their subsequent behaviour, as well as the nature of individual incidents such as pollution.

c.    Management response

The mechanisms by which oil and gas exploration/exploitation could affect the feature are, for the most part, reasonably well understood. There is, however, no evidence to suggest that oil and gas exploration is having an effect at present.

i.   Rationale

The absence of oil and gas exploration within the cSAC, together with the relatively low levels of activity in neighbouring "blocks" that have been licensed by the DTI for exploration suggest that, at present, this is not a significant factor influencing the feature in the cSAC. This would appear likely to decrease following recent exploration pull outs by Marathon and Chevron the two companies with the largest holdings in the southern Irish Sea.

The bottlenose dolphins that use the cSAC are highly mobile, and (probably) range throughout the Cardigan Bay/southern Irish Sea areas. Oil and gas exploration & exploitation together with associated activities, e.g. shipping could have a significant influence on the dolphins that use the cSAC, even though these activities are/would be taking place outside the cSAC. Bottlenose dolphins are potentially "at risk" from disturbance caused by noise (seismic shooting in particular, but also noise caused by shipping and drilling) and from oil and other forms of pollution. Increases in shipping movements may also put individual animals at risk from collisions.

Oil and gas exploration (and any subsequent exploitation) in waters adjacent to the cSAC could give rise to concern: risks of disturbance, direct effects on individual animals from pollution, collisions etc. and degradation of the habitat could become significant. Future licensing rounds and seismic surveys proposals should be monitored, and competent Authorities should ensure that all potential impacts on the feature and the habitat within the cSAC are properly addressed in EIAs and via the significance/appropriate assessment provisions in the 1994 Habitats Regulations (see ‘Plans and Projects’,). Competent Authorities should also satisfy themselves that oil spill and other emergency contingency plans adequately address the sensitivity of the cSAC and the requirement to protect the habitat as well as the feature of European importance. Surveillance and/or monitoring of the influences of this factor can only be carried out on a reactive basis, i.e. when exploratory or exploitative activities are notified/planned and then carried out. General surveillance of dolphin activity numbers and distribution within and adjacent to the cSAC should be established. Data collected will help to provide the information required for impact assessment.

ii.  Type of response

F1 : The activity constitutes a plan or project.

iii.      Actions, including links to other policies/plans/measures

  • Ensure, that EIAs and appropriate assessments under the 1994 Habitats Regulations are carried out, of all potential direct and indirect impacts of off-shore oil and gas exploration/exploitation.

  • Ensure that oil spill and other emergency contingency plans adequately address the requirement to protect the bottlenose dolphin and its habitat in so far as they can.

  • In the event of a marine pollution incident within the cSAC, or which could threaten the cSAC, ensure that appropriate consideration is given by the Environment Group to the requirements/sensitivities of bottlenose dolphins, and that this is reflected in the advice give to any marine or other response centre(s).

[135] Goold, J.C. 1996. Acoustic assessment of populations of common dolphin Delphinus delphis in conjunction with seismic surveying. J. Mar.Biol.Ass. UK 76:811-820.

[136] Dalen, J. and Knutsen, G.M. 1987. Scaring effects on fish and harmful effects on eggs, larvae and fry by offshore seismic exploration. In Merklinger, H.M. (Ed). Progress in Underwater Acoustics. Plenum Publishing Corp.

Engas, A., Lokkeborg, S. , Ona, E. & Soldal, A.V. 1993. Effects of seismic shooting on catch availability of cod and haddock. Institute of Marine Research, Norway Fisken og Havet, No. 9.