Oil Spill Contingency Plan Issue 5. External Copy

Transcription

1 Issue 5 External Copy The Bristol Port Company, Marine Department, Avonmouth Docks, Bristol, BS11 9AT Tel marine.admin@bristolport.co.uk

2 Contents Preface Plan Custodian & Revision List 5 Distribution & Document Control 5 Abbreviations and Acronyms 7 Page Numbers 1 Introduction STRATEGY 1.1 Statutory Requirement Purpose of the Plan Scope of the Plan Interfacing Oil Pollution Contingency Plans Oil Terminal Plans County, District and Borough Council Plans Harbour Authority Plans National Contingency Plan Bristol Channel Standing Environment Group Risk Assessment Summary Classification of Oil Spills Incident Response Organisation Haven Master Oil Spill Management Team Tier One Incident Tier Two Incident Tier Three Incident Strategic and Tactical Co-ordinating Groups Marine Response Centre (MRC) Salvage Control Unit (SCU) 14 3 Call Out, Reporting and Logs ACTIONS AND OPERATIONS 3.1 Call Out Reporting Issue 5 31/03/15 Page 1 of 102

3 3.3 Oil Spill Incident Logs Personal Log Guidance Personal Log Incident Log Oil Spill Progress Report Oil Spill Contractor Briefing Report POLREP MCA Post Exercise/Incident Report 15 4 Action Cards& Checklists 4.1 Action Cards 24 Action Card 1 - Duty Assistant Haven Master Bristol VTS Action Card 2 - Marine Support Officer Action Card 3 Overall Incident Commander (Haven Master or Deputy) Action Card 4 On Scene Commander (5P) Action Card 5 Operator (1P) Checklists 30 Oil Spill Assessment Checklist Oil Spill Briefing Checklist Oil Spill Sampling Checklist 5 Response Guidelines 5.1 FlowchartTactical Response Plans 34 Tactical Response Plan 1 Impounded dock; Spirit Tactical Response Plan 2 Lock; Spirit Tactical Response Plan 3 River/Estuary; Spirit Tactical Response Plan 4 Impounded dock; Light Oil Tactical Response Plan 5 Lock; Light Oil Tactical Response Plan 6 Estuary/River; Light Oil Tactical Response Plan 7 Impounded Dock, Heavy Oil Tactical Response Plan 8 Lock; Heavy Oil Tactical Response Plan 9 Estuary/River; Heavy Oil Tactical Response Plan 10 Land Pipeline; Spirit Tactical Response Plan 11 Land Pipeline; Light Oil Tactical Response Plan 12 Land Pipeline; Heavy Oil 5.2 Oil Boom deployment Oil Boom deployment at Avonmouth Dock Oil Boom deployment at Portbury Dock Oil Boom deployment at other locations 5.3 Dispersants Notification, communications & media 6.1 Notifications Issue 5 31/03/15 Page 2 of 102

4 6.2 Communications Media 50 7 Health and Safety Introduction Legislation Site Hazards Site Emergency Plan 62 8 Waste Management Plan General Temporary Storage Disposal Methods 76 9 Contact Directory DATA DIRECTORY Training and Exercises Training Exercises Training / Exercise Records Risk Assessment Introduction Navigation risks Supplementary risks Chiksan arm failure Pipeline failure 11.4 Quantitative Risk Assessment Fate of Spilled Oil - General Fate of Spilled Oil Specific (Marine Diesel Oil) Oil Spill Quantification Oil Spill Movement Tidal Influence within the Estuary General Environmental 90 Issue 5 31/03/15 Page 3 of 102

5 12.1 Overview of the Severn Estuary Environment Nature Conservation Designations Environmental, social & economic sensitivities 13 Roles and Responsibilities 13.1 Responsibility Overview 13.2 Harbour Authority 13.3 Local Authorities 13.4 Maritime and Coastguard Agency(MCA) 13.5 Marine Management Organisation (MMO) 13.6 Natural England 13.7 The Environment Agency 13.8 Bristol Channel Environment Group Anti Pollution Resources Tier 1 Resources Oil Basin Berth Spill Kits Bristol Aviation Fuel Terminal/Portbury Berth 7 Spill Kit Haven Masters Office Oil Pollution Storeroom Oil Pollution Container Oil Booms Additional Resources Tier 2 Resources Rendezvous Site for Assembly of Equipment Manpower Availability 102 ANNEX 1 Tier 2 Contract 2 Figures 3 Notices of consultation agreement 4 MSDS Sheets 5 MMO Standing Approval for use of dispersants 6 MCA Stop Notice 4/ Letter of approval from MCA 8 Notification Form (Tier Two Contractor) 9 Emergency Contacts Directory (Internal Copy Only) Issue 5 31/03/15 Page 4 of 102

6 Preface Document administration Title Custodian Contributors Oil Spill Contingency Plan Deputy Haven Master (SMS) Deputy Haven Master (Shipping Operations) Deputy Haven Master (Conservancy) Marine Environment Manager Health & Safety Manager Status Final Date of publication 31 March 2015 Review Valid for 5 years from date of issue. The plan will undergo a full review, including agreement by consultees, prior to its fifth anniversary. Document history Issue 5 Distribution& Document Control The plan is a controlled document and the latest version is downloadable at Printed copies of the plan are held in the Haven Masters Office, Bristol VTS andthe Oil Basin Office (Avonmouth). The plan, and future amendments of it, will been sent electronically to the below organisations. When printed the document will be uncontrolled. Bristol City Council Bristol City Docks Bristol Channel Standing Environment Group Adler & Allan (Tier 2 Response) Devon & Severn IFCA Environment Agency Gloucester Harbour Trustees Marine Management Organisation (MMO) Maritime and Coastguard Agency Natural England North Somerset Council Pill Hobbler Marine Services (Tier 1 Response) South Gloucestershire Council Issue 5 31/03/15 Page 5 of 102

7 Amendments Amendment number Page(s) amended Authorised by 1 16/10/2015 Page 1-5 New contents &Tier Two Contractor, Page 6 Amendments Table, Page 20- Form withdrawn (new form Annex 8),Page (Section 9) withdrawn (see Annex 9), Page Tier Two Contractor change, Annex 1 - New Contract C. Jones - DHM(SMS) Consultation The following authorities and organisations have been consulted during the preparation of this plan: Bristol City Council Bristol City Docks Bristol Channel Standing Environment Group Devon & Severn IFCA Environment Agency Gloucester Harbour Trustees Marine Management Organisation (MMO) Natural England North Somerset Council South Gloucestershire Council The requirements of these authorities and organisations have been taken into account and they have individually confirmed their general agreement to the plan details. See Annex 3. Issue 5 31/03/15 Page 6 of 102

8 Acronym Table Acronym DAHM DHM (C) DHM (SMS) DHM (SO) EMC IFCA MCA MMO MRC MSDS NCP NERC OIC OMT OSC CPSO PPE SAC SCU SOSREP SPA SSHP SSSI STOp SCG TCG SUR2 TBPC Definition Duty Assistant Haven Master Deputy Haven Master (Conservancy) Deputy Haven Master (Safety Management System) Deputy Haven Master (Shipping Operations) Emergency Management Centre Inshore Fisheries & Conservation Authority Maritime and Coastguard Agency Marine Management Organisation Marine Response Centre Material Safety Data Sheet National Contingency Plan Natural Environment & Rural Communities Overall Incident Commander Oil Spill Management Team On Scene Commander Counter Pollution and Salvage Officer Personal Protective Equipment Special Area of Conservation Salvage Control Unit Secretary of State Representative Special Protection Area Site Health and Safety Plan Site of Special Scientific Interest Special Scientific Technical & Operational Advice Notice Strategic Co-ordinating Group Tactical Co-ordinating Group Shoreline Survey Report Form The Bristol Port Company Issue 5 31/03/15 Page 7 of 102

9 1 Introduction 1.1 Statutory Requirement This Oil Spill Contingency Plan has been developed to conform to the Merchant Shipping (Oil Pollution Preparedness, Response and Co-operation Convention) Regulations 1998, SI 1998 No. 1056, which entered into effect on the 15 th May The plan is approved by the MCA Annex Purpose of the Plan The plan is provided to assist The Bristol Port Company (TBPC) and other relevant organisations in dealing with an accidental discharge of oil into the waters TBPC s Harbour Area (Figure 1& 2). Its primary purpose is to set in motion the necessary actions to stop or minimise the discharge and to mitigate its effects. Effective planning ensures that the necessary actions are performed in a structured, logical and timely manner. This plan guides the Haven Master and his Duty Officers through the decisions that will be required in an incident response. The tables, figures and checklists provide a visible form of information, thus reducing the chance of oversight or error during the early stages of dealing with an emergency situation. It is the responsibility of the Deputy Haven Master (SMS) to update and amend the plan. For the plan to be effective, it must be: familiar to those with key response functions in the Port / Plan; regularly exercised; and reviewed and updated on a regular basis. This plan uses a tiered response to oil pollution incidents. The plan is designed to deal with Tier One and Tier Two incidents and also to provide guidance for the response to a Tier Three incident. Where a spillage is associated with a wider emergency, then additional factors involving the safety of personnel will take precedence over the pollution response. In this case, reference must be made to TBPC s Emergency Response Plan. The salvage and casualty management of any vessels, which pose a threat of pollution, is a priority consideration. During Oil Spill response activities account must be taken of the following: site hazard information adherence to permit procedures spill site pre-entry briefing boat safety COSHH Regulations material safety data sheets personal protective equipment needs heat stress, cold stress and hypothermia decontamination Issue 5 31/03/15 Page 8 of 102

10 1.3 Scope of the Plan Oil Spill Contingency Plan The plan details the contingency arrangements for responding to an actual or threatened oil pollution incident occurring within the statutory harbour limits and on land owned by TBPC. These limits can be found in various local Acts including the following: The Port of Bristol Harbour Revision Order 1993 (SI 1993 No.2974) The Bristol Port and Harbour Revision Order 1976 (SI 1976 No.1067) The Bristol Port and Harbour Revision Order 1972 (SI 1972 No.1931) The response strategy for TBPC Oil Spill Contingency Plan has been developed taking into account the spill risks and possible sources of spillage associated with the Port operations. The Plan consists of three elements: Strategy Plan: Describes statutory requirements and the purpose and scope of the plan, including the geographical coverage. It shows the relationship of the plan to the National Contingency Plan for Marine Pollution from Shipping (NCP) and plans of local organisations. Also included are perceived risks, the Incident Response Organisation and responsibilities of individuals for defined categories of spill. Action Plan: Sets out the emergency procedures that will allow rapid mobilisation of resources and an early response to the situation. Data Directory: Contains all supplementary information relevant to the performance of the plan such as, contact directory, training and exercise policy, risk assessment, sensitivity maps, roles and responsibilities of government and other agencies, resources directory and uncontrolled appendices. 1.4 Interfacing Oil Spill Contingency Plans Oil Terminal Plans Several Oil Companies operate within TBPC s jurisdictional area. Each of these facilities has their own Oil Spill Contingency Plan, designed to cover minor tier one spillages and define the procedure for notifying TBPC of a larger incident. The terminal plans designed to interface with TBPC Oil Spill Contingency Plan are list below are: ESSO Marine Terminal Valero Westway Terminals Costain (OPA) Q8 Issue 5 31/03/15 Page 9 of 102

11 1.4.2 County, District and Borough Council Plans In the event of actual or threatened shoreline impact, the appropriate Local or County Authority Oil Pollution Plan(s) will be implemented (Figure 3). The level of activation will be dictated by the incident classification (refer Section 1.6). The interfacing plans are: South Gloucestershire Council Coastal Pollution Emergency Plan North Somerset Council Oil Pollution Plan Bristol City Council Oil Pollution Plan Harbour Authority Plans TBPC s Harbour Area adjoins those of Gloucester Harbour Trustees and Bristol City Council (Figure 4) National Contingency Plan As a Party to the United Nations Convention on the Law of the Sea, the United Kingdom has an obligation to protect and preserve the marine environment. This National Contingency Plan (NCP) is one of the measures that the United Kingdom has taken to meet this obligation. This Plan provides a Strategic and Operational overview intended to inform Central Government Departments, Devolved Administrations, Local Authorities, Environmental Agencies, Port and Harbour Authorities and senior managers of response organisations - including those of industry Bristol Channel Standing Environment Group The Bristol Channel Standing Environment Group may be requested to convene by the MCA or other key respondents to act as a single point of environmental and public health advice. The Bristol Channel Standing Environment Group has an Activation Plan to be used in the event of an Oil Spill within the Bristol Channel. 1.5 Risk Assessment Summary(For full risk assessment details refer to Section 11) The following table shows the potential scenarios, credible release quantity, worst-case release quantity and probability of occurrence for each potential scenario. Scenario Collision underway Collision with fixed installation Description Collision between vessels underway in the estuary, river or docks Collision of a vessel in the locks or during berthing in the docks Worst Case Credible Potential Probability 12,000 m 3 2,400 m 3 Low 6,000 m 3 1,200 m 3 Low Grounding Grounding of a vessel in the estuary or river 5,000 m 3 1,000 m 3 Low Bunkering operations Chiksan arm failure Pipeline failure Refuelling of vessels in the docks usually by road tanker with marine diesel oil Failure of a marine loading arm during cargo transfer from ships in the Oil Basin/BAFT Failure of a pipeline between the Oil Basin/BAFT and relevant oil terminal 20 m 3 <1 m 3 Medium 5 m 3 <1 m 3 Low 40 m 3 8 m 3 Low Issue 5 31/03/15 Page 10 of 102

12 For the purpose of planning, the worst case scenarios have been based on the following assumptions: Vessel involved assumed to be 80,000 DWT Tanker All collisions assumed to hole two wing tanks All groundings assumed to hole centre tank Wing Tank capacity is 3,000m 3 Centre tank capacity is 5,000m 3 Vessel discharge rate is 2,500m 3 /hr Road Tanker Capacity is 20m 3 Chiksan arms assumed to hold 5m 3 Vessel shutdown procedure takes 30 seconds Pipelines assumed to hold 40m Classification of Oil Spills Oil spills will be categorised in accordance with the internationally recognised three-tier classification system: Response Tier 1 Tier 2 Tier 3 Description Small operational spills that may occur within a location as a result of daily activities. The level at which a response operation could be carried out successfully using individual resources and without assistance from others. Medium sized spills where immediate resources are insufficient to cope with the incident and further resources may be called in on a mutual aid basis. A Tier 2 incident may involve Local Government. A large spill where substantial further resources are required and support from a national (Tier 3) or international co-operative stockpile may be necessary. A Tier 3 incident is beyond the capability of both local and regional resources. This is an incident that requires national assistance through the implementation of the National Contingency Plan and will be subject to Government controls. Issue 5 31/03/15 Page 11 of 102

13 2 - Incident Response Organisation 2.1 Haven Master The Haven Master (or his nominated deputy) has overall responsibility for the conduct of spill response operations and for casualty/salvage management within TBPC s Harbour Area. He will be supported in his role by TBPC personnel and by the Oil Spill Management Team. 2.2 Oil Spill Management Team An Oil Spill Management Team (OMT) will be established, under the chairmanship of the Harbour Master, for Tier Two and Tier Three incidents. The OMT will meet at the Emergency Management Centre (EMC) which is located on the ground floor of the Haven Masters Office. Depending upon the circumstances of the incident an OMT may also be established for a Tier One Incident response. The OMT will provide the command and control structure to co-ordinate and direct the incident response. In the event of a Tier Two incident the OMT will liaise with national and regional bodies. In the event of a Tier Three incident and the implementation of the National Contingency Plan, the OMT will assist MCA. In the event of a Tier Three incident and the implementation of the National Contingency Plan (NCP), overall control would pass to the Secretary of State s Representative, SOSREP, or his appointed deputy. The OMT will assist SOSREP and appropriate members of the OMT will re-deploy to the SRC. The Haven Master will require the transfer of responsibility for managing the incident response to be formally documented prior to relinquishing overall control of at-sea counter pollution measures to MCA. Oil Spill Management Team The Bristol Port Company Haven Master Deputy Haven Master (SO) Deputy Haven Master (SMS) Marine Engineering Manager (or Deputy) Oil Spill Support Team The Bristol Port Company Marine Administration Finance Department Engineering Department Director of Communications Environment Manager Other Companies Oil Company (if appropriate) Vessel Owner / Agent External Organisations P & I Club MCA (if appropriate) Tier 2 Contractor Local Authority South Gloucestershire Council North Somerset Council Bristol City Council External Organisations The Bristol Channel Standing Environment Group Environment Agency Natural England Marine Management Organisation (MMO) Issue 5 31/03/15 Page 12 of 102

14 2.3 Tier One Incident The Harbour Master will decide whether or not to set up an OMT. Depending on the circumstances of the incident OMT may include representatives from the following organisations and authorities who will convene at TBPC s Emergency Management Centre: Harbour Authority Relevant Local Authority Emergency Team Oil Company (terminal spill) Environment Agency 2.4 Tier Two Incident An Oil Spill Management Team will be established, under the chairmanship of the Harbour Master, will be established at TBPC s Emergency Management Centre and will include representatives from the following organisations and authorities: Harbour Authority Relevant Local Authority Emergency Team Oil Company (terminal spill) Natural England Environment Agency MCA HM Coastguard Bristol Channel Standing Environment Group MMO Tier Two Contractor Vessel Owners/Agents P&I Club 2.5 Tier Three Incident An Oil Spill Management Team will be established, under the chairmanship of the Harbour Master, will be established at the TBPC s Emergency Management Centre and will include representatives from the following organisations and authorities: Harbour Authority Relevant Local Authority Emergency Team Oil Company (terminal spill) Natural England Bristol Channel Standing Environment Group Environment Agency MMO Tier Two Contractor Vessel Owners/Agents P&I Club MCA HM Coastguard MCA Principal Counter Pollution and Salvage Officer Issue 5 31/03/15 Page 13 of 102

15 2.6 Strategic and Tactical Co-ordinating Groups The Strategic (SCG) and Tactical Co-ordinating (TCG) Groups between them cover many of the functions previously carried out by the Shoreline Response Centre and may be established when pollution threatens the shoreline. The SCG will normally be chaired by a senior police officer during the response phase although on occasions, particularly where there is no immediate threat to life, a senior local authority official. When established it manages the overall on-shore response strategy, dovetailing when appropriate with the at sea response, develops the long term plan, and the policy and direction of the response. The Tactical Co-ordinating Groups usually comprise of the most senior officers of each agency committed within the area of operation and assume tactical command of the event or situation In order to maintain consistency throughout the incident response, TBPC will appoint a person to liaise with the groups. The SCG and/or TCG will be at the following locations as shown in the Local Authorities Plans: North Somerset Council Town Hall, Weston-Super-Mare South Gloucestershire Council Council Office, Yate Bristol City Council PBA Sport and Social Club, Avonmouth 2.7 Marine Response Centre (MRC) The Marine Response Centre considers and implements the most appropriate means to contain, disperse, and remove potential pollutants from the scene based on all the information available to them. In almost all cases involving a national response the MCA establishes a Marine Response Centre at the most appropriate location. For a shipping incident this location may be within the Marine Emergencies Information Room at the MCA s Southampton Headquarters, the nearest MRCC or suitably equipped port operations room. During a complex salvage operation, the Marine Response Centre may be co-located near the Salvage/Operations Control Unit. TBPC s Offices are available for a MRC to be established. 2.8 Salvage Control Unit (SCU) During a shipping incident, the primary role of the Salvage Control Unit is to monitor salvage operations and actions that are being taken and/or proposed relating to salvage activity and to ensure that such actions do not have an adverse effect on safety and the environment. The SOSREP determines the requirement for a Salvage Control Unit taking into consideration the nature and scale of the incident. The Unit operates close to the incident site. For incidents at sea the most appropriate MRCC or other MCA facilities may be considered. For incidents within port or harbour jurisdictions it is likely that a suitable location for the cell may have already been determined in the local contingency plan. However for at sea or harbour responses commercial facilities may be more appropriate or conveniently situated. TBPC s Offices are available for a SCU to be established. Issue 5 31/03/15 Page 14 of 102

16 3.1 Call Out 3 Call Out, Reporting and Logs The DAHM, based at Bristol VTS is most likely to receive the initial Oil Spill Report. Marine Operations Procedure 3.3 details the first and second contacts. Depending on the nature of the oil spill TBPC Emergency Plan may be activated. The Duty Shipping Manager will become the Overall Incident Commander (OIC). The On Scene Commander (OSC) must be MCA 5P accredited. He will liaise with the Duty Port Incident controller. The below table shows the call out protocol to be followed in the event of an oil spill being reported: Position Alerts Duty Assistant Haven Master Marine Support Officer Duty Port Incident Controller Port Police Duty Shipping Manager (OIC) Other Emergency Services (as appropriate) Overall Incident Commander (OIC) On Scene Commander (5P Trained) TBPC Directors External Authorities including MCA (as appropriate) On Scene Commander (OSC) 1P Operators (number as appropriate) Tier 2 Contractor (in consultation with OIC) Should the oil spill require the support of the Tier 2 Contractor the Oil Spill Contractor Briefing Report must be completed authorising this call out. 3.2 Reporting The OSC will complete the Oil Spill Progress Report. This is given to OIC at the end of each shift to ensure an accurate record is available of actions taken, equipment used and the amount of oil spilled and recovered. The On Scene Commander will complete a POLREP and forward this to the Coastguard having assessed the extent of the incident. 3.3 Oil Spill Incident Logs It is the responsibility of OIC to ensure an accurate Incident Log is completed. This may be delegated to the DAHM, Incident Controller or On Scene Commander as appropriate. Every person responding to the incident is expected to maintain a Personal Log. Issue 5 31/03/15 Page 15 of 102

17 Personal Log Guidance This guidance is designed to facilitate and provide consistency in the response teams log keeping, thereby providing accurate information in the final incident report. Safety Hazards Initial Notification Daily Activities Record all accidents / near miss incidents regardless of how / potentially how serious result. Record time of notification of oil spill incident and the name of the person informing you. Keep a daily record of all response activities undertaken, including time and location. Also include: Meetings attended Instructions received / given Site visits and movements Contacts with outside agencies Personal Contacts Photographic/Video records Oil Distribution Site Supervision Expenditure Incurred Generate a list of relevant contacts made, including contact details. Note time and location of any photographs / video taken. Make sketches of oiled areas with notes. Keep a record of all staff under supervision, including hours of work etc. List all equipment utilised. Record all expenditure and keep receipts. Issue 5 31/03/15 Page 16 of 102

18 Personal Log Incident Name Date Page Number Time Comment / Action / Detail Signed. Issue 5 31/03/15 Page 17 of 102

19 Incident Log Incident Name Date Page Number Time Comment / Action / Detail Signed. Issue 5 31/03/15 Page 18 of 102

20 Oil Spill Progress Report Incident Name: Updated by: Date: Time (local): Summary of Incident Response Operations: Summary of Incident Response Resource Utilisation: Dispersant Used litres Length of Booms in Use: m Number of Recovery Devices: Sorbent Used: Number of Personnel: Number of Storage Devices: kg Number of Vessels: Number of Vehicles: Specialist Equipment: Oil Spill Balance Sheet: Total amount of oil spilled: Total amount of oil recovered: Outstanding amount of spilled oil: litres/tonnes litres/tonnes litres/tonnes Mass balance: Estimated Natural Weathering: Mechanically agitated: Chemically dispersed Skimmer recovered Sorbent recovered: Manually recovered: Other.. litres/tonnes litres/tonnes litres/tonnes litres/tonnes litres/tonnes litres/tonnes litres/tonnes Issue 5 31/03/15 Page 19 of 102

21 Oil Spill Contractor Briefing Report See Annex 8 Issue 5 31/03/15 Page 20 of 102

22 CG77 POLREP Pollution Report Form Part 1: Information which should be provided in an initial pollution report A. Classification of report (i) doubtful (ii) probable (iii) confirmed (Delete as necessary) B. Date: Time: pollution observed Identity of observer/reporter C. Position of pollution: (by latitude and longitude if possible, state range and bearing from some prominent landmark) Extent of pollution: litres/barrels/tonnes Size of polluted area from: (from where sighted) (estimated amount of pollution, e.g. size of polluted area, number of tonnes of oil spilled or number of containers. When appropriate position of observer) D. Wind Speed knots; direction from: Tidal status at time pollution observed: after/before HW/LW E. Weather conditions and sea state: Sea state/ wave height metres F. Characteristics of pollution: Type: (E.g. oil, crude, diesel, packaged bulk chemicals UN number if known, garbage) Appearance: (E.g. liquids, floating solid, liquid oil etc.) G. Sources of pollution: (from vessel or other undertaking) Issue 5 31/03/15 Page 21 of 102

23 Causes of pollution: (Apparent deliberate or casualty. If the latter give a brief description. Where possible name, type, size and nationally and Port of Registry or polluting vessel. If vessel underway gives course speed and destination if known). H. Details of other vessels in the area (to be given if the polluter cannot be identified and the spill is considered to be of recent origin) I. Photograph taken Yes / No Sample taken for analysis Yes / No J. Remedial action taken, intended to deal with spillage: K. Forecast of likely effect of pollution: L. Names of those informed other than addresses: M. Any other relevant information: (E.g. names of other witnesses, references to other instances of pollution) Issue 5 31/03/15 Page 22 of 102

24 MCA Post Exercise/Incident Report Exercise/Incident Report Scenario/Incident Location Date../../. Organisations or authorities List of equipment deployed Tactical response actioned Boom deployment actioned Observations/Outcome Details of amendments to be made to Contingency Plan I can confirm that the details on this form provide a realistic summary of the exercise. Any action points resulting from this exercise have been completed accordingly. On Scene Commander Signature Position/job title Date Issue 5 31/03/15 Page 23 of 102

25 4 Action Cards & Checklists The following section contains action cards and checklists for various members of the Bristol Port Company Oil Spill Management Team, for use during an Oil Spill incident. 4.1 Action Cards The action cards follow methodical checklist styles, in order that they effectively guide the person fulfilling the role through the actions that they are expected to take and also the responsibilities falling upon them during an oil spill response incident. The action cards are split into four sections: Alert - This section lists the different notifications that will be required, both internally and externally. Initial Actions - Those that will be required to be carried out immediately to initiate the response operation. Further Actions - Those that will be required to be carried out when the response operation is underway. Final Actions - Those that will be required to be completed before the response operation can be officially stood down. Action cards can be found for the following positions: Action Card 1 - Duty Assistant Haven Master Bristol VTS Action Card 2 - Marine Support Officer Action Card 3- Overall Incident Commander (Haven Master or Deputy) Action Card 4- On Scene Commander (5P) Action Card 5 Operator (1P) Issue 5 31/03/15 Page 24 of 102

26 Action Card 1 Duty Assistant Haven Master Bristol VTS Responsibilities Receive information/report of oil spill incident Maintain communication with all vessels in vicinity Carry out internal notifications Step Actions Additional Information Alert Initial Actions Further Actions Final Actions Duty Shipping Manager Marine Support Officer Duty Incident Controller Emergency Services (if required) Port Police 1P Operators (initial team of 4 persons) Initiate Personal Log Verify incident details Despatch MSO to scene Assign initial incident category (Checklist 1) Issue general warning to all vessels in vicinity Brief Overall Incident Commander Brief Duty Incident Controller Provide Co-ordination of the on water response Submit Personal Log to the Haven Master Attend debrief Duty Shipping manager assumes role of Overall Incident Commander (Action Card 3). Issue 5 31/03/15 Page 25 of 102

27 Action Card 2 Marine Support Officer Responsibilities Initially assess situation Verify classification Provide accurate situation reports to DAHM/OIC/OSC Collect evidence and/or statements in conjunction with Port Police Liaise with incident vessel regarding status of oil spill (if applicable) Step Actions Additional Information Initial Actions Further Actions Final Actions Proceed to incident location Investigate cause/ source of spill Communicate all information to the DAHM/ Duty Incident Controller Take samples of spilled oil (Checklist 3) Initiate Personal Log Take photographic evidence Collect evidence and take statements Track the leading edge of slick Provide detailed situation reports to the Duty Incident Controller Survey the shoreline if applicable Submit Personal Log to the Haven Master Attend debrief Issue 5 31/03/15 Page 26 of 102

28 Action Card 3 Overall Incident Commander (Haven Master or Deputy) Responsibilities Assume overall control of Tier Two/Three incidents Approve expenditure Approve Port Closure if appropriate Ensure Admin Support established record keeping procedure established Record all decisions made at the Oil Management Team meetings Record and keep a precise account of the use of resources which have a financial implication in conjunction with financial control/support Step Actions Additional Information Alert Initial Actions Further Actions Final Actions Bristol Port Company Directors On Scene Commander External Authorities as required Convene Oil Spill Management Team Initiate appropriate tactical response plan Initiate TBPC Emergency Plan if appropriate Close Port if required Initiate Incident log (Tier Two/Three) Initiate Personal Log Initiate Notification of external bodies Coastguard Constantly review strategy in use and change as appropriate Liaise with the MCA MRC and SRC if appropriate Authorise dispersant spraying in line with MMO approval Authorise termination of Tier Two clean up Approve re-opening of the Port if appropriate Collate Personal Logs Prepare the incident report Hold full debrief involving all members Amend Contingency Plan as appropriate Appoint On Scene Commander (5P Trained) Use Checklist 2 to assess/brief. Issue 5 31/03/15 Page 27 of 102

29 Action Card 4 On Scene Commander (5P Trained) Responsibilities Assume overall control of Tier One incidents Confirm/amend initial classification Mobilise Oil Spill Response contractor (if appropriate) Complete POLREP Brief Haven Master (or his deputy) Complete external reporting requirements Ensure a first aid post and evacuation procedure is established Step Actions Additional Information Alert Initial Actions Further Actions Final Actions Coastguard Oil Spill Response contractor (if required) Additional 1P Operators (if required) Test and establish communications Verify/amend spill classification Establish operational plan Initiate Personal Log Initiate Incident log (Tier One) Develop a site safety plan Ensure machinery pre-start checks carried out by operators Commence clean-up operation Constantly review the strategy being employed and advise of changes where necessary Provide regular briefs to Overall Incident Commander Liaise with to Duty Incident Controller For Tier 2/3 Incidents assist Overall Incident Commander Oversee the dispersant spraying (if appropriate), ensuring it is in line with MMO approval. Authorise termination of Tier One clean up Collect personal logs from operators Submit personal log/ incident report to the OIC Delegate to Duty Incident Controller where required. Use Checklist 2 to assess/brief. Consult with OIC and Duty Incident Controller as required Issue 5 31/03/15 Page 28 of 102

30 Action Card 5 Operator (1P) Responsibilities Provide accurate situation reports to the On Scene Commander Follow instructions of On Scene Commander Ensure safe working practice is carried out Step Actions Additional Information Initial Actions Further Actions Final Actions Proceed to spill site Attend safety brief Carry out a risk assessment Perform response operation Perform pre-start checks on equipment Monitor safety Submit Personal Log to On Scene Commander Attend debrief Under instruction of On Scene Commander in conjunction with oil spill response team Issue 5 31/03/15 Page 29 of 102

31 4.2 Oil Spill Incident Checklists The following checklists are designed to ensure consistency for all response personnel throughout the incident response. The checklists are as follows: Oil Spill Assessment Checklist 1 This checklist ensures that the initial assessment of the oil spill is accurate and all aspects likely to affect the classification, quantity and likely fate of the spilled oil are investigated thoroughly. Oil Spill Briefing Checklist 2 This checklist ensures that all personnel involved in the incident management are given a thorough briefing of the incident, and are then able to give a consistent and effective briefing to personnel falling under their management during the incident. Oil Spill Sampling Checklist 3 This checklist should be used a guidance for taking samples of the spilled oil that may be used legally at a later date. By following this checklist ensures that sufficient sample is taken and that it is packaged and labelled correctly. For further information regarding sampling, refer to STOp notice number 4/2001. Annex 6 Issue 5 31/03/15 Page 30 of 102

32 Checklist 1 Oil Spill Assessment Checklist This checklist is designed to assist those personnel who have the responsibility of initially assessing and subsequently assessing the oil spill incident. These personnel are likely to be: Duty Assistant Haven Master Marine Support Officer Duty Incident Controller Overall Incident Commander Actions Assess safety hazards Determine oil spill source Estimate quantity of oil released Assess weather conditions Can the spill be contained Predict oil fate Guidance Until otherwise established, assume oil spill is giving off potentially dangerous hydrocarbon vapours. ELIMINATE IGNITION SOURCES Approach Oil Spill from upwind to reduce effects of vapours. APPROACH ONLY IF CONSIDERED SAFE TO DO SO If source unknown, investigate with care. Instigate actions to stop spillage at source. ONLY IF CONSIDERED SAFE TO DO SO Estimate if exact quantity unknown. Determine the: Wind speed and direction State of tide and current speed Sea state Consider options available. Determine direction and speed of oil movement. Take weather forecast into account. Issue 5 31/03/15 Page 31 of 102

33 Checklist 2 Oil Spill Briefing Checklist This checklist is designed to facilitate an effective response team briefing and should be used by supervisory personnel and the OMT. Actions Guidance Location, specific hazards identified: Specify Safety Hazards Size of spillage, type of oil, source: Extent of Problem Tide and wind conditions: Slick trajectory Strategies to utilise: Response actions Equipment and personnel: Resource mobilisation Meetings schedule: Planning Cycle Communications, waste disposal, weather forecast: Additional Information Issue 5 31/03/15 Page 32 of 102

34 Checklist 3 Oil Spill Sampling Checklist Responsibilities This checklist is designed to give guidance on taking samples of spilled oil. By following this checklist, it will be possible to ensure that sufficient oil has been collected, packaged correctly, labelled correctly and handled in such a way that it may be used as part of a legal claim / prosecution. Sample gear, bottles, labels etc are available in the Marine Support Officers vehicle. Spares are available at the Marine Department office. Personnel designated to take samples, and procedure to be followed are detailed in Marine Support Officers Action Card 2 Step Number of samples required Sample frequency Sample size Method of sampling Sealing of sample containers Labelling of Samples Information Guidance According to law, a single sample of the spilled oil should be collected. However, it would be desirable to take at least three samples. Whenever an incident is ongoing, at least one sample of spilled oil should be taken per day, where the oil pollution is on the water. Where shoreline impact has occurred, then one sample per every 1km of impacted shoreline should be taken per day. Generally, at least 500ml of liquid should be taken or in the case of polluted shoreline, at least 50 grams. Where the oil is free floating, it is imperative that the oil is skimmed from the water surface, and that no excessive amount of water is recovered. Where oil has impacted on the shoreline then oil should be scraped from rocks etc and placed in the sample container. Samples should be placed in screw top bottles and the top sealed with a means of ensuring that it cannot be tampered with, such as an adhesive label placed over the top and bottle. Sample bottle should be labelled in accordance with STOp notice number 4/2001 The samples should be sent to the address given in the STOp notice. In addition to this, the MCA should be informed of the fact. Issue 5 31/03/15 Page 33 of 102

35 5 Response Guidelines The following section gives details of the strategies to employ for the various type of oil spill incident that could occur within The Bristol Port Company s harbour area. The section contains a flow chart that is designed to enable a swift decision to be made as to what strategy/tactics to employ in response to an incident dependent upon oil type and the location of the spillage. In addition to this, the section gives guidelines on how to obtain approval to use dispersants and the reports that should be made following dispersant use and also shows the different booming sites that may be used for oil spill response operations within the docks. 5.1 Flowchart& Tactical Response Plans By using the flow chart, it will be possible to determine which of the twelve tactical response plans to employ. These tactical response plans give details of what tactics should be employed and considerations/requirements that should be complied with or made before implementing the plan. OIL SPILL INCIDENT Where has the incident occurred? Land Impounded Dock Lock Estuary or River Avon What type of Oil has Spilled? What type of Oil has Spilled? What type of Oil has Spilled? What type of Oil has Spilled? SPIRIT Implement TRP10 SPIRIT Implement TRP1 SPIRIT Implement TRP2 SPIRIT Implement TRP3 LIGHT OIL LIGHT OIL LIGHT OIL LIGHT OIL Implement TRP11 Implement TRP4 Implement TRP5 Implement TRP6 HEAVY OIL Implement TRP12 HEAVY OIL Implement TRP7 HEAVY OIL Implement TRP8 HEAVY OIL Implement TRP9 Issue 5 31/03/15 Page 34 of 102

36 Tactical Response Plan 1 Location: Impounded Dock Primary Strategy: Monitor Oil Type: Spirit (Petroleum etc) Secondary Strategy: Agitation/Absorbents Introduction Safety Tactical Response Considerations/Requirements Spirit will spread rapidly over the water s surface. It is likely to evaporate rapidly in the first few hours after a spillage, due to the many light ends. Spirit spills in an enclosed environment pose an explosive hazard. There is little that can be done actively to recover spirit from the waters surface. The most acceptable strategy is usually to encourage the products to evaporate and disperse naturally. Stop all operations in the area Prohibit smoking and naked flames Evacuate the area DO NOT attempt to contain the spillage allow it to spread Call the Emergency Services Ban use of non-intrinsically safe equipment STOP ALLPORT OPERATIONS IN THE AFFECTED DOCK! The initial tactical response to this incident is to do nothing for the first few fours apart from considering the safety of life. The Emergency Services should take charge of the initial response effort. When considered to be safe, assist the dispersion of the product by agitating the spillage using water jets / fire hoses and possibly the propeller wash / bow waves of vessels. For large concentrations of spilled product, use absorbent pads to soak up the product. Upon arrival at the scene, the Emergency Services Primary Response is likely to be to smother the spillage with Foam to inhibit Fire and Explosion. If it is considered to be safe not to smother the spillage, this should be encouraged. The reasoning behind this is that up to 80% of a spirit spillage on water may evaporate rapidly. If the spillage is smothered, evaporation will not take place, and there will become a need for a major manual clean-up operation to be undertaken. Issue 5 31/03/15 Page 35 of 102

37 Tactical Response Plan 2 Location: Lock Primary Strategy: Monitor Oil Type: Spirit (Petroleum etc) Secondary Strategy: Agitation/Absorbents Introduction Safety Tactical Response Considerations/Requirements Spirit will spread rapidly over the water s surface. It is likely to evaporate rapidly in the first few hours after a spillage, due to the many light ends. Spirit spills in an enclosed environment pose an explosive hazard. There is little that can be done actively to recover spirit from the waters surface. The most acceptable strategy is usually to encourage the products to evaporate and disperse naturally. Stop all operations in the area Prohibit smoking and naked flames Evacuate the area DO NOT attempt to contain the spillage allow it to spread Call the Emergency Services Ban use of non intrinsically safe equipment STOP ALLPORT OPERATIONS IN THE AFFECTED LOCK! The initial tactical response to this incident is to do nothing for the first few fours apart from considering the safety of life. The Emergency Services should take charge of the initial response effort. When considered to be safe, assist the dispersion of the product by agitating the spillage using water jets / fire hoses and possibly the propeller wash / bow waves of vessels. For large concentrations of spilled product, use absorbent pads to soak up the product. Upon arrival at the scene, the Emergency Services Primary Response is likely to be to smother the spillage with Foam to inhibit Fire and Explosion. If it is considered to be safe not to smother the spillage, this should be encouraged. The reasoning behind this is that up to 80% of a spirit spillage on water may evaporate rapidly. If the spillage is smothered, evaporation will not take place, and there will become a need for a major manual clean-up operation to be undertaken. Issue 5 31/03/15 Page 36 of 102

38 Tactical Response Plan 3 Location: River/Estuary Primary Strategy: Monitor Oil Type: Spirit (Petroleum etc) Secondary Strategy: Agitation/Absorbents Introduction Safety Tactical Response Considerations/Requirements Spirit will spread rapidly over the water s surface. It is likely to evaporate rapidly in the first few hours after a spillage, due to the many light ends. There is little that can be done actively to recover spirit from the waters surface. The most acceptable strategy is usually to encourage the products to evaporate and disperse naturally, and where possible assist this. DO NOTHING TO ACTIVELY RESPOND TO THE INCIDENT FOR THE FIRST TWO HOURS. Stop all operations in the area Prohibit smoking and naked flames DO NOT attempt to contain the spillage allow it to spread DO NOT allow vessels to close to within 800 metres of the spillage Where possible, remain upwind of the spill Establish a vessel exclusion zone around the spillage be prepared to change the position of this exclusion zone as the spillage moves. If possible, arrange aerial surveillance to monitor the size and movement of the spillage. If this is not possible, monitor the spillage from a vessel When considered safe, approach the spillage by vessel from upwind and agitate the spillage by fire hose from vessels. It is also possible to use the vessels propeller wash and bow wave to assist dispersion. Specialist organisations are able to provide computer modelling of spillages to give indications of the likely time scale for the spillage to evaporate/disperse naturally. Information that will be required to do this is: water temperature, air temperature, wind speed, oil type, approximate size of spillage. Issue 5 31/03/15 Page 37 of 102

39 Tactical Response Plan 4 Location: Impounded Dock Primary Strategy: Containment Oil Type: Light Oil Secondary Strategy: Recovery/Absorbents Introduction Safety Tactical Response Considerations/Requirements Light oils (such as diesel) are not as volatile as spirit, but still evaporate and disperse quite rapidly in the correct environment. As these types of oil are not as volatile, it is possible to contain the spillage close to its source, thereby reducing the overall area where an active clean up is required. Recovery of the Gross oil may be undertaken by vacuum systems / trucks and final polishing by using absorbent pads. Absorbent booms may be used to sweep the spillage using small vessels. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels / working on the waters edge should use lifejackets. Boom across the entrance to the relevant dock Once oil spill contained, commence recovery using vacuum system / truck Use small boats and an absorbent boom sweep system to corral oil and move to the vacuum system / truck. For small patches of spilled oil, use absorbent pads to remove from the waters surface Given the fact that the impounded dock remains at approximately a constant level, there is no need to use running moorings for the booms, merely ensure that there is an effective seal with the dock wall. Given the fact that the dock is relatively still water, there is no need to angle the boom to the current to make it effective. It is essential that all recovered oil and absorbents be disposed of in the correct manner. If it is necessary to use temporary storage devices the Environment Agency should be consulted. Issue 5 31/03/15 Page 38 of 102

40 Tactical Response Plan 5 Location: Lock Primary Strategy: Containment Oil Type: Light Oil Secondary Strategy: Recovery/Absorbents Introduction Safety Tactical Response Considerations/Requirements Light oils (such as diesel) are not as volatile as spirit, but still evaporate and disperse quite rapidly in the correct environment. As these types of oil are not as volatile, it is possible to contain the spillage close to its source, thereby reducing the overall area where an active clean up is required. Recovery of the Gross oil may be undertaken by vacuum systems / trucks and final polishing by using absorbent pads. Absorbent booms may be used to sweep the spillage using small vessels. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels / working on the waters edge should use lifejackets. Close both lock gates and keep closed until recovery complete, provide additional protection with GP750 boom around gate. If possible contain vessel in inner lock in order to minimise affected area and provide a double barrier to the estuary Commence recovery using vacuum system / truck Use absorbent booms to corral oil into the vicinity of the vacuum system. For small patches of spilled oil, use absorbent pads to remove from the waters surface. It is essential that all recovered oil and absorbents are disposed of in the correct manner. If it is necessary to use temporary storage devices, the Environment Agency should be consulted. In order to facilitate a rapid clean up, the dock should be closed until the gross oil has been removed. Once the gross oil has been removed, the dock may reopen. Issue 5 31/03/15 Page 39 of 102

41 Tactical Response Plan 6 Location: Estuary/River Primary Strategy: Monitor Oil Type: Light Oil Secondary Strategy: Agitation/Absorbents Introduction Safety Tactical Response Considerations/Requirements Light oils (such as diesel) are not as volatile as spirit, but still evaporate and disperse quite rapidly in the correct environment. Due to the strong currents in the Severn Estuary / River Avon, there is little that can be done to actively recover the spilled oil. It is more acceptable to monitor the spillage and allow it to disperse / evaporate naturally. Shoreline protection will prove difficult due to the strong currents / tidal regime. It is also possible to assist the natural dispersion / evaporation by agitating the oil spill manually. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels should use lifejackets. Establish a vessel exclusion zone around the spillage be prepared to change the position of this exclusion zone as the spillage moves. If possible, arrange aerial surveillance to monitor the size and movement of the spillage. If this is not possible, monitor the spillage from a vessel If the oil spill does not appear to be approaching the shoreline, do not undertake an active response, merely monitor the situation on a regular basis. If the spillage appears to be approaching the shoreline, approach the spillage by vessel from upwind and agitate the spillage by fire hose from vessels. It is also possible to use the vessels propeller wash and bow wave to assist dispersion. For large concentrations that are not evaporating / dispersing, use either absorbent booms or pads to remove these concentrations from the waters surface. Specialist are able to provide computer modelling of spillages to give indications of the likely timescale for the spillage to evaporate / disperse naturally. Information that will be required to do this is: water temperature, air temperature, wind speed, oil type, approximate size of spillage. It is essential that all used absorbents are disposed of in the correct manner. The Environment Agency should be consulted with regard to this matter. Issue 5 31/03/15 Page 40 of 102

42 Tactical Response Plan 7 Location: Impounded Dock Primary Strategy: Containment Oil Type: Heavy Oil Secondary Strategy: Recovery/Dispersant Introduction Safety Tactical Response Considerations/Requirements Heavy oils do not evaporate and disperse as readily as light oils and spirits. It is for this reason that they are referred to as Persistent Oils. For oil spills like this, it is necessary to contain the oil near its source of spillage and then to actively recover the oil from the waters surface. For large amounts of oil spilled of this type, booming and mechanical recovery will take place. Chemical dispersants may then be used to disperse any residual amounts into the water column. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels / working on the waters edge should use lifejackets. Boom across the entrance to the relevant dock See Figure 5or Figure 6 Booming Sites Once oil spill contained, commence recovery using disc or weir skimmers, pumped to temporary storage tanks that should be located on the quayside. Use small boats and an absorbent boom sweep system to corral oil and move to the recovery device. For small patches of spilled oil, use absorbent pads to remove from the waters surface. If the oil spill is particularly large in size, it may be more appropriate to use chemical dispersants to disperse the spillage into the water column. If this is the case, the dock is covered by a standing approval for the use of dispersant, and the amount used must not exceed the amount stated in the approval. If dispersants are used, then the small amounts of oil that have not been dispersed should be removed by vacuum truck / system. Given the fact that the impounded dock remain at a relatively constant level, there is no need to use running moorings for the booms, merely ensure there is an effective seal with the dock wall. Given the fact that the dock is relatively still water, there is no need to angle the boom to the current to make it effective. It is essential that all recovered oil and absorbents are disposed of in the correct manner. If it is necessary to use temporary storage devices, then the Environment Agency should be consulted. The use of dispersants is strictly controlled by MMO. They should be consulted before its use. Issue 5 31/03/15 Page 41 of 102

43 Tactical Response Plan 8 Location: Lock Primary Strategy: Containment Oil Type: Heavy Oil Secondary Strategy: Recovery/Dispersant Introduction Safety Tactical Response Considerations/Requirements Heavy oils do not evaporate and disperse as readily as light oils and spirits. It is for this reason that they are referred to as Persistent Oils. For oil spills like this, it is necessary to contain the oil near its source of spillage and then to actively recover the oil from the waters surface. For large amounts of oil spilled of this type, booming and mechanical recovery will take place. Chemical dispersants may then be used to disperse any residual amounts into the water column. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels / working on the waters edge should use lifejackets. Close both lock gates to contain the spilled oil in the lock, provide additional protection with GP900 boom around gate. If possible contain vessel in the inner lock in order to minimise the affected area and to provide a double barrier to the estuary Once oil spill contained, commence recovery using disc or weir skimmers, pumped to temporary storage tanks that should be located on the quayside. Use small boats and an absorbent boom sweep system to corral oil and move to the recovery device. For small patches of spilled oil, use absorbent pads to remove from the waters surface. If recovery is not possible, it may be appropriate to use chemical dispersants to disperse the spillage into the water column. If this is the case the dock is covered by a Standing Approval for dispersant use, and the amount used must not exceed the amount stated in the Approval. If dispersants are used, then the small amounts of oil that have not been dispersed should be removed by other systems. It is essential that all recovered oil and absorbents are disposed of in the correct manner. If it is necessary to use temporary storage devices, then the Environment Agency should be consulted. The use of dispersants is strictly controlled by MMO. They should be consulted before its use. Issue 5 31/03/15 Page 42 of 102

44 Tactical Response Plan 9 Location: Estuary/River Primary Strategy: Dispersant Oil Type: Heavy Oil Secondary Strategy: Containment/Recovery Introduction Safety Tactical Response Considerations/Requirements Heavy oils do not evaporate and disperse as readily as light oils and spirits. It is for this reason that they are referred to as Persistent Oils. For oil spills like this in open water areas, the most appropriate strategy to employ is the use of chemical dispersant, if approved, to disperse the oil into the water column. If this strategy is not acceptable, then it is necessary to utilise specialist equipment to contain and recover the spilled oil. It should be noted that this strategy is unlikely to have a high success rate. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels / working on the waters edge should use lifejackets. If the oil spill is particularly large in size, then consideration should be given to the use of chemical dispersants to disperse the spillage into the water column. However, MMO must give approval before the use of dispersant in the estuary/river. Dispersants should be applied by specialist equipment from vessels. Record should be kept of the amount of dispersant used. Information and forms are appended to this section. If the use of dispersant is not approved, contact should be made with the Tier Two contractor who will be able to mobilise specialist containment, recovery and storage equipment. Establish a vessel exclusion zone around the spillage be prepared to change the position of this exclusion zone as the spillage moves. If possible, arrange aerial surveillance to monitor the size and movement of the spillage. If this is not possible, monitor the spillage from a vessel It is essential that all recovered oil is disposed of in the correct manner. If it is necessary to use temporary storage devices, then the Environment Agency should be consulted. The use of dispersants is strictly controlled by MMO. They should be consulted before its use. Issue 5 31/03/15 Page 43 of 102

45 Tactical Response Plan 10 Location: Land Pipeline Primary Strategy: Safety Oil Type: Spirit (Petroleum etc) Secondary Strategy: Containment/Recovery Introduction Safety Tactical Response Considerations/Requirements Spirit will spread quickly depending on the type of surface. It is likely to evaporate rapidly in the first few hours after a spillage, due to the many light ends. Spirit spills pose a highly explosive/ flammable atmosphere hazard depending on location and weather. The primary activity is to establish an exclusion zone around the spill site and to exclude all ignition sources. Entry into water courses or drains will extend the hazardous area and must be minimised or prevented if at all possible. Stop all operations on vessel & in the immediate and surrounding areas Call the Emergency Services Establish an exclusion zone Prohibit smoking and naked flames Evacuate the area Ban use of non intrinsically safe equipment Close all roads in spill area Provide safe access and egress for responders to area Assess any drains or water courses nearby and dam if required Prevent discharge(third party) into these water courses for period of clean up Set up atmospheric monitoring at spill site Ensure all personnel wear full PPE STOP ALLPORT OPERATIONS IN THE AFFECTED AREA! The initial tactical response to this incident is to do nothing apart from considering the safety of life. The Emergency Services should take charge of the initial response effort. For large concentrations of spilled product, the use of appropriate vacuum tankers and absorbent materials will be employed to recover the product. Removal of oil soaked waste requires the same safety precautions to be in place as the clean-up operation. Upon arrival at the scene, the Emergency Services Primary Response is likely to be to smother the spillage with foam to inhibit fire and explosion. If the spillage is smothered, evaporation will be reduced, and there will be a need for a major manual clean-up operation to be undertaken. Issue 5 31/03/15 Page 44 of 102

46 Tactical Response Plan 11 Location: Land Pipeline Primary Strategy: Containment Oil Type: Light Oil Secondary Strategy: Recovery/Absorbents Introduction Safety Tactical Response Considerations/Requirements Light oils (such as diesel and Kerosene) are not as volatile as spirit, but still evaporate and disperse quite rapidly in certain environments. As these types of oil are not as volatile, it is preferable to contain the spillage close to its source, thereby reducing the overall area where an active clean up is required. The areas that could be affected include paved, rough ground, salt marsh and water courses may be nearby. Recovery of the Gross oil may be undertaken by vacuum systems / trucks and final polishing by using absorbent pads. Absorbent booms may be used to sweep or contain the spillage. Stop all operations on vessel & in the area and establish an exclusion zone Prohibit smoking and naked flames Provide safe access and egress for responders to area Assess any drains or water courses nearby and dam if required Prevent discharge(third party) into these water courses for period of clean up Ensure all personnel wear full PPE Contain spill area using resources available Dams may be required for water courses, absorbent boom for small areas or temporary earth or plate dams for larger areas. Once oil spill contained, commence recovery using vacuum system / truck Absorbent boom sweep system to corral oil and move to the vacuum system / truck when on water. For small patches of spilled oil, use absorbent pads to remove from the surface. Drawings of water courses are available from the Port Engineers, and these must be consulted to prevent or minimise escape of any oil into the water. It is essential that all recovered oil and absorbents be disposed of in the correct manner. If it is necessary to use temporary storage devices, then the Environment Agency should be consulted. Issue 5 31/03/15 Page 45 of 102

47 Tactical Response Plan 12 Location: Land Pipeline Primary Strategy: Containment Oil Type: Heavy Oil Secondary Strategy: Recovery/Absorbents Introduction Safety Tactical Response Considerations/Requirements Heavy oils do not evaporate and disperse as readily as light oils and spirits. It is for this reason that they are referred to as Persistent Oils. For oil spills like this, it is necessary to contain the oil near its source of spillage and then to actively recover the oil from the surface. For large amounts of oil spilled of this type, temporary bunds or booming will be required and mechanical recovery will take place. Stop all operations in the area Prohibit smoking and naked flames Ensure all personnel wear full PPE Persons using vessels / working on the waters edge should use lifejackets. Provide bunds or booms to contain spill. Once oil spill contained, commence recovery using vacuum tanker/ disc or weir skimmers, pumped to temporary storage tanks that should be located in suitable area. If oil escapes into water see appropriate TRP for that area. For small patches of spilled oil, use absorbent pads to remove from the surface. To prevent the oil spreading, bunds or booms should be used to contain the oil. The building of temporary bunds using earth moving vehicles may be the quickest means of containing the spill. It is essential that all recovered oil and absorbents are disposed of in the correct manner. If it is necessary to use temporary storage devices, then the Environment Agency should be consulted. Dispersant may be used to clean surfaces and equipment after the bulk oil has been removed, provided there is no run off into water. The use of dispersants is strictly controlled by MMO. They should be consulted before its use. Issue 5 31/03/15 Page 46 of 102

48 5.2 Oil Boom deployment TBPC own two hydraulic boom reels loaded with Troilboom 750. A boom reel is located at both Portbury (240m) and Avonmouth (200m) Docks. These booms are fitted with ASTM connections and compatible with each other. The booms are fitted with a tow end to enable quick deployment from the reel. The ends of the boom must be tight alongside the wall. This is best achieved by attaching the boom ends (fitted with tow ends) then placing a weighted line over the boom approx. 10 metres from the end. The running of a boom around a curved dock wall will also aid making a seal. Absorbent booms can be placed between the Troilboom and wall to ensure there is minimal oil breaching the seal. The dock water level remains at a near constant level so tidal boom compensators are not required. Issue 5 31/03/15 Page 47 of 102

49 Additional booms are located at both inner lock entrances. These can be used to seal off the lock entrances and will lead around the entrance knuckles providing a close fitting to the wall Oil boom Deployment at Avonmouth Dock The design of Avonmouth Dock lends itself well to oil spill containment. There are 6 principle boom deployment options. See Figure Oil boom Deployment at Portbury Dock The booming of this dock requires careful consideration. The quay wall at berths 1 to 6 are suspended with the deck soffit at 18m (0.9m above normal dock level). At Bollard 14 on 1/2, 3/4 and 5/6 a solid support enables the boom to close off an area of the dock when the dock level is below 18m. Consideration should be given to pumping the dock up to maintain a level above that of the deck soffit thus preventing oil from going under the quay wall where it will be difficult to recover. There are 7 principle boom deployment options. With the exception of option A both of TBPC booms will need to be joined together to achieve the desired boom deployment. See Figure Oil boom Deployment at other locations Due to the strong tidal flows in the estuary and River Avon it is not considered practical to boom in these areas, particularly across the water flow however consideration should be given to booming off creeks and pills. Consideration should also be given to areas where the deployment of deflector booms may be effective. The booming off of a ship in dock can be achieved easily and an assessment should be carried out by an On Scene Commander how best to achieve this. If the ship is still suffering a loss of oil it is important to allow room for the spill to expand. Issue 5 31/03/15 Page 48 of 102

50 5.3 Dispersants The use of dispersants can be an effective method of combating oil spills. The use of dispersants is strictly controlled by the MMO and conditions are imposed on its use. TBPC has derogation for the use of up to 200 gallons (884 litres) of Dasic Slickgone NS Dispersant within Avonmouth and Portbury Docks and the River Avon however themmo should be informed of its use. Approval from MMO must be sought prior to dispersant use in excess of the quantity shown in the Standing Approval or for any dispersant use in waters such as the Severn Estuary which are not included in the scope of the Standing Approval. MMO will consider all the relevant implications associated with dispersant and formally approve any use. Note: the use of dispersants if not totally successful, might affect the ability to use certain other response strategies. In order to obtain approval a telephone call should be made to the MMO who are available 24/7. The MMO official who takes the call will require certain key items of information so that an informed decision can be taken on whether use of the product is appropriate. Approval will normally be given within 1 hour. A formal record of the approval will then be sent as an to confirm MMO s verbal agreement. If MMO decides not to approve the use of the product, the reasons for this will be explained and another option discussed. MMO will require a report on any use of oil treatment products that has taken place within 72 hours of the spill whether under the terms of a standing approval or otherwise. Issue 5 31/03/15 Page 49 of 102

51 6 NOTIFICATION, COMMUNICATIONS & MEDIA 6.1 Notifications The below notification matrix advised which external organisations must be informed following an oil spill. It should be noted that spills within the impounded docks of Portbury and Avonmouth trigger a different response to a spill in tidal waters. Oil Spill Tier Dock Oil Spill Tier Estuary or River Avon Organisation Comments Milford Haven CGOC (Coastguard) X X X X X X Information will be required on Oil Spill Report Form. Coastguard will inform their Pollution Response Unit Natural England X X X Contact if spill exceeds one tonne South Gloucestershire X X X Contact only if oil is likely to contaminate land. County Council Bristol City Council X X X Contact only if oil is likely to contaminate land. North Somerset Council X X X Contact only if oil is likely to contaminate land. Environment Agency X X X X X X Contact if spill is from a land based source. MMO/South West Area X X X X X X Contact regarding dispersant Adjoining Harbour and Port Authorities X X X X Contact if oil is likely to move into their area. 6.2 Communications 6.3 Media Wherever possible, private VHF/UHF radio channels and telephones (either mobile or fixed) should be used as the primary means of incident communication. This can prevent eavesdropping by nonincident personnel and greatly reduce the potential of information being misinterpreted. Oil spill incidents generally rouse public and media attention. In order that the incident response operations can be undertaken efficiently without hindrance from the media and also that the correct information is passed onto the public at the correct time. Under no circumstances should any person connected with the incident response speculate to the press as to the cause of the incident, nor comment on any aspect of the response operation. All media enquiries should be directed to TBPC s Director of Communications, rather than to the OMT. This allows the OMT to undertake their roles without interruption. The Director of Communications will be able to pass on approved information through the Media Holding Statement or details of press conference timings. In the event of a Tier three incident TBPC s Director of Communications will liaise with the MCA Public Relations Officer. For further information on Media Procedures please see TBPC s Emergency Plan Issue 4 Section 8. Issue 5 31/03/15 Page 50 of 102

52 7- Health and Safety 7.1 Introduction This guide is intended to help in developing a Site Health and Safety Plan (SSHP). The SSHP can be used for both small and large spill responses and can be completed rapidly stat responders can begin clean-up operations as soon as possible. It is intended that the SSHP should be completed prior to work commencement in conjunction with the Shoreline Survey Report Form SUR2. Initial Steps for Effective use of this Plan A. Complete the Shoreline Survey Report Form SUR2 and the Site Safety Health Plan Assessment Form. In each category check/ complete all that apply. Separate checklists should be prepared for each site and a master list maintained by planning and operations teams. B. Complete or provide the Site Safety and Health Plan Site Map. The map may include: Work zone Evacuation routes Assembly points First aid locations Staging areas Command post locations C. Provide hazard information on the spilled product, such as MSDS or other data. D. Revise the site plan, site map and any attachments as conditions at the site change. Attach these revisions to the original plan and date them to ensure currency. 7.2 Legislation Employers Duties The principal duty of an employer is that imposed by the Health and Safety at Work Act The Act states, the employer is to ensure, as far as is reasonably practicable, the health, safety and welfare of their employees and anyone else who may be affected by their business activities whilst at work. The Management of Health and Safety at Work Regulations 1992 impose specific duties on employers to: carry out a risk assessment of their work activities in order to identify protective and preventative measures - significant findings must be recorded if there are five or more employees; make arrangements for the planning, organisation, control, monitoring and review of the preventive and protective measures. When there are five or more employees these arrangements must be recorded; provide employees with appropriate health surveillance, where this is shown to be necessary by risk assessment; Issue 5 31/03/15 Page 51 of 102

53 appoint a competent person(s) to help ensure compliance with health and safety law; set up emergency procedures; only allow persons with sufficient health and safety instructions to have access to restricted areas; provide employees with comprehensive health and safety information relating to the details above; full co-operation with other employers sharing the workplace; provide the relevant health and safety information to any outside employer working within their premises, including relevant instruction and information; provide the relevant health and safety training to employees; and provide all temporary workers with relevant information on health and safety requirements appropriate to their position within the company Employees Duties All employees have a duty under The Health and Safety at Work Act 1974, to take reasonable care for the health and safety of themselves and their colleagues at work who may be affected by their acts or omissions. Under the Health and Safety at Work Act 1974 employees have a duty to co-operate with their employer and colleagues enabling them to comply with statutory duties and requirements. Additionally, the Health and Safety at Work Act 1974 states that employees must not intentionally or recklessly misuse any equipment and the like provided for them in the interests of health, safety or welfare. The Management of Health and Safety at Work Regulations 1992, further oblige employees to: use any of the equipment etc, provided in the interests of safety; follow health and safety instructions; report any problem they consider to be a danger; and report any shortcomings in the protection arrangements for health and safety. 7.3 SITE HAZARDS BIRD HANDLING Handling of birds must be carried out by properly trained personnel to ensure the protection of both bird and handler. Wild birds have no understanding of human intentions. Even a greatly weakened bird can inflict serious injury to handlers, especially to human eyes. Open wounds on hands and arms from such injuries can present opportunities for oily contaminants and disease to enter the handler's blood system. Issue 5 31/03/15 Page 52 of 102

54 Bird Handling is usually best left to experts, or to volunteers who have had some training. It is easy to put the birds under more stress by chasing and man handling them. If you see an oiled bird notify the Beach Master who will provide advice on what action to take. If a decision is taken to catch an oiled bird take the following actions: Equipment: Thick gloves (able to withstand nasty pecks) Overalls Safety footwear Cardboard Box with lid of a suitable size to give the bird some room for movement Goggles to protect eyes Optional long- handled net to help catch bird. Procedures: Do not let the bird get close to your head, as it may try to peck your eyes. Catch the bird by hand or with the aid of a long-handled net. Do not put the birds under any more stress than necessary. Only attempt to capture the bird if it can be done quickly and efficiently. Hold the bird with both hands, holding the wings in. Put the bird in a cardboard box lined with absorbent material (e.g. newspaper), with a lid. Do not wrap the bird up in anything - it may get too hot and will cause additional stress. Take the bird to a cleaning station as soon as possible. Let them know where and when the bird was caught. Keep a note of all birds caught and sent to cleaning station. Make a note of species if possible. BOAT SAFETY Boat operators must familiarise themselves and passengers with safety features and equipment on their boats. Qualified individuals must operate boats. Personnel on boats must wear Lifejackets. Use of cold water immersion suits is particularly critical under conditions of cold stress. Boats should generally not be used after sunset for oil recovery. If this is required or boat use poses minimal risk, areas of operation should be carefully prescribed. Individual boat operators should maintain a communication schedule with a shore base. Each boat should be fully equipped with appropriate navigation lights. Distress signals should be carried on all vessels. Boat operators must keep their supervisors informed on their area of operation, especially when they change their work area (i.e. if plans call for a boat to move to another location during a shift, the operator should advise the supervisor of his actual time of departure). Issue 5 31/03/15 Page 53 of 102

55 Portable fuel tanks should be filled outside of the boat. All sources of ignition in the area of refuelling should be isolated. Personnel working in or operating boats should wear appropriate non-slip footwear. Fixed ladders or other substantial access/egress should be provided at boat transfer locations from low water line to platform. Workers should be cautioned about using their arms or legs to fend off during berthing, or getting their hands, arms, or legs between vessels and docks or fixed structures. CHEMICAL HAZARDS Attach appropriate Material Safety Data Sheets for all hazardous substances likely to be used at a spill site. COLD STRESS Cold stress can occur among responders as a result of prolonged exposure to low environmental air temperatures or from immersion in low temperature water. It can lead to a number of adverse effects including: frostbite; chilblains; and hypothermia. The single most important aspect of life-threatening hypothermia is a fall in the deep core temperature of the body. Workers shall be provided with warm clothing, rest opportunities, exposure protection, and warm and / or sweet fluids. Boat crew personnel need to wear immersion suits in the water where temperatures are below 15 o, or the combined water and air temperature is less than 48 o Celsius. WIND CHILL CHART Strength Speed Temperature Celsius Calm Okm ¹-34 ¹-40 ¹-45 Breeze 16km ¹-44 ¹-51 ¹-51 ¹-57 ²-64 Moderate 32km ¹-32 ¹-40 ¹-48 ¹-55 ²-64 ²-72 ²-80 Near Gale 48km ¹-36 ¹-45 ¹-53 ²-62 ²-71 ²-79 ²-88 Gale 64km ¹-38 ¹-48 ¹-57 ²-66 ²-74 ²-83 ²-92 Little danger to properly dressed personnel ¹Danger of freezing exposed flesh ²Greatest Danger Issue 5 31/03/15 Page 54 of 102

56 DRUM HANDLING / MANUAL HANDLING Drum handling at a spill site primarily involves drums of waste and contaminated clothing. Several types of drums and containers may be used. These range from 25 to 200 litres in size. All drums and containers must be properly labelled. If in doubt as to the contents of a drum - seek advice. Manual lifting and movement of drums should be kept to a minimum. A guide to manual handling is as follows: Wear gloves. Assess the weight of the load and get help if it is beyond your capacity. Where appropriate use mechanical aids provided. Size up the job - remove any obstructions, note any snags and make sure there is a clear space where the load is to be set down. Ensure that you can see over the load whilst carrying it. Look out for any splinters, projecting nails, sharp edges or wire. Stand close to the object with your feet 20 to 30cm apart, place one-foot in advance of the other, pointing in the direction you intend to move. Hold your chin inwards - avoid moving your head backwards or forwards. Bend your knees to a crouch position, keeping your back straight. Get a firm grip at opposite corners of the load with the palm of the hand and the roots of the fingers. Arms should be as close to the body as possible. Lift with your thigh muscles and extend body/straighten your legs. Apply the above principles, to any movement such as pushing, pulling, digging, shovelling etc. Use the reverse procedure when setting down the load. EQUIPMENT OPERATIONS Heavy Equipment Operators of heavy equipment, such as front-end loaders, graders, and bulldozers must be trained and qualified in their safe operation. The operator and banksman must be familiar with agreed signalling techniques. Where appropriate, the banksman should use protective headgear. Buckets must not be used for personnel transport. FORKLIFTS Only trained and authorised operators shall be allowed to operate forklifts. Only stable or safely arranged loads that do not exceed the capacity of the truck shall be handled. Operators are expected to carry out daily checks of the forklift to be operated. All Inspection defects are to be corrected prior to its operation. If it cannot be rectified immediately, the truck should be taken out of service. Issue 5 31/03/15 Page 55 of 102

57 ELECTRICAL HAZARDS Electrical hazards shall be identified and marked with suitable placards, barricades, or warning tape as necessary. FATIGUE Working long hours without rest may be required, especially during the early phase of response. This coupled with the stress of the situation and wearing required PPE, can contribute to fatigue. Symptoms include: loss of concentration; errors in judgement; irritability; sleepiness; and soreness and stiffness in joints and muscles. Rest and sleep are the primary treatments for fatigue. Stress can be addressed by relaxation techniques, such as deep breathing, stretching and taking breaks. TBPC Operations department has in the region of 150 personnel which will allow a shift pattern to be established allowing adequate periods of rest. FIRE AND EXPLOSION Flammable and combustible materials may be encountered at the spill site. These may be fuels for vehicles and equipment or the spilled material itself. However other chemicals may be encountered during the response. Refer to the container label and MSDS for more information on these materials. Precautions should be taken when working with either flammables or combustibles: No smoking Store in approved, labelled containers Provide fire extinguishers in areas where these materials are used. HEAT STRESS Heat stress can result whilst responders perform heavy labour work in protective and/or impermeable clothing. This clothing does not breathe or allow for the normal dissipation of body heat. Heat build up can lead to a number of adverse health effects including, heat rash, heat cramps, dehydration, heat exhaustion or heat stroke. The incidence of heat stress is dependent on a number of factors such as temperature, humidity, a person's fitness, age, weight and clothing worn. Therefore supervisors should continually monitor their employees when workloads are heavy and temperatures and/or humidity are high. Fluids shall be available at all times and personnel will be encouraged to drink these during rest periods. Shaded rest areas will be made available where feasible. Issue 5 31/03/15 Page 56 of 102

58 HEAT INDEX AIR TEMPERATURE CELSIUS Relative Humidity 21º 24º 26º 30º 32º 35º 38º 40º 44º 46º 20% 19º 22º 25º 28º 31º 34º 37º *41º *45º *49º 40% 20º 24º 26º 30º 34º 39º *44º *51º **58º **66º 60% 21º 25º 28º 32º 38º *46º **56º **65º 80% 22º 26º 30º 36º *45º **58º * Heat cramps or exhaustion likely. Heat-stroke possible. ** Heat-stroke highly likely. AIR MONITORING MONITORING PLAN Air monitoring at the spill site and surrounding areas will be carried out by response personnel in the event of a tier two oil pollution incident to ensure site worker and community safety. 1. Air monitoring will be done during site characterisation, and on each work shift during clean-up activities until results indicate no further monitoring is required. 2. All monitoring done at the clean-up site will be documented and the data maintained by qualified personnel on site. INITIAL SITE MONITORING 1. Monitoring will be done during initial site entry. This monitoring is to include checking for: Oxygen (O 2 ) deficiency using a direct reading oxygen meter; flammable atmospheres (% Lower Explosive Limit [LEL]) using a combustible gas indicator; benzene, hydrogen sulphide and other gases as needed using direct reading instruments, indicator tubes or other accepted methods. 2. Competent personnel will carry out tests. 3. Instrument calibrations will be carried out prior to use 4. All monitoring will be documented ( refer Attachment 1 for example) ON GOING MONITORING Monitoring for oxygen deficiency and flammable atmospheres will be made if confined spaces are encountered, or as required. Monitoring for benzene, hydrogen sulphide or other identified gases will be done at work shift start as needed. Results of site monitoring will be made available to interested parties. Issue 5 31/03/15 Page 57 of 102

59 NB. If a Gas cloud is developing which could lead to a hazard off site, the involvement of the Public Health Consultant, and Environmental Health Officer may be required. MOTOR VEHICLES Drivers shall maintain a safe speed at all times, and shall not be allowed to operate vehicles in a reckless manner. NOISE Appropriate hearing protection shall be used in designated high noise areas where personnel noise exposure exceeds 85 dba, time weighted average over an 8 hour work shift/ period. Additionally, no person shall be exposed to greater than 115 dba at any time without the use of appropriate hearing protection. OVERHEAD AND BURIED UTILITIES If work has to be carried out near overhead lines, consultation with the organisation that operates the supply system should be undertaken. A safe working distance from these overhead lines should be determined and the area cordoned off. The estimated location of buried utilities such as sewer, telephone, fuel, electric or water should be predetermined before work begins. Utility companies or owners must be contacted, advised of the proposed work and informed of the urgency of the situation. PUMPS AND HOSES Pumps and hoses may be used at the spill site to apply water, steam or chemical for clean up and/or decontamination. They may also be used for transfer of liquid waste. Caution should be used when working in these areas where hoses are being used as they represent a tripping hazard. Additionally when using pumps and hoses determine their last contents to avoid unnecessary contamination. SLIPS, TRIPS AND FALLS Slips, trips and falls on oily surfaces are the major cause of injuries at an oil spill site. Many of these injuries occur in the first few minutes of work before workers are totally familiar with the conditions and before precautionary measures have been taken. When entering a spill site, walk slowly and carefully in oil coated areas. Be especially careful when walking on oil covered rocks. Oil resistant safety footwear with non-slip soles should be worn. It is best to clear an access/egress route than walk through oiled areas. HELICOPTER OPERATIONS Helicopter Operations may be in use at the spill site for: overflight surveillance; site characterisation; personnel/equipment transport; and rescue/medical transport. Safe working practices for passengers and other personnel include: Passengers must receive a safety briefing from the pilot prior to takeoff. The briefing shall include, safety features and equipment location on the aircraft, helicopter underwater escape procedures when appropriate and emergency information. Issue 5 31/03/15 Page 58 of 102

60 Passengers and ground crew should approach/depart from the FRONT of the helicopter only when signalled by the pilot and shall never walk under or around the tail rotor or exhaust. Loose fitting clothing, hats or other gear which might be caught in the rotor down wash, must be secured or removed within 100 feet of operating helicopters. Passengers shall wear seat belts at all times and personal flotation devices when flying over water. Passengers and ground crew shall wear hearing protection (which may include communication headsets) at all times around operating helicopters. During emergency landing on water, do not exit until instructed to do so by the pilot after rotor blades stop turning or pilot signals all clear, do no inflate personal flotation devices until outside of the helicopter. LIFTING Cranes must be operated in accordance with the manufacturer s instructions and established construction practices. Only trained and authorised operators shall be allowed to operate cranes. Outriggers must be fully extended to assure maximum stability of the equipment. Cranes must only be operated where the ground provides adequate support. Rigging components must be inspected daily. Only certified wire rope slings or web strops shall be used. Each sling or strop must be clearly marked or tagged with its rated capacity and must not be used in excess of this rating. Personnel should not be allowed under the jib or load except for the minimum time necessary to hook or unhook the load. STEAM AND HOT WATER Steam and hot water may be used during the spill clean-up. Use caution when working with these since they can cause severe burns. Wear glove and eye/ face protection when handling and be careful not to spray in the direction of other personnel. TIDES Tidal information can be sought from nautical almanacs and tide tables. These tidal heights are predicted for average meteorological conditions or barometric pressure and winds. Higher than average barometric pressure results in tide heights lower than predicted and vice-versa. Strong winds can also affect tidal levels and may alter the predicted time of high or low water. The effect is very variable and is strongly influenced by local topography. TRENCHES AND EXCAVATIONS Open manholes, pits, trenches or similar hazards are to be noted on the updated map as they are constructed. The Beach Master shall ensure that these locations are periodically checked during the day and adequate warning signs are posted around these hazards. Keep a map record of these excavations. UV RADIATION Ultra violet radiation from sunlight can be a significant hazard at a spill site. Sunblocks with the appropriate protection factor and tinted safety glasses maybe needed. Issue 5 31/03/15 Page 59 of 102

61 VISIBILITY Fixed or portable lighting shall be maintained for dark areas or work areas after sunset to ensure that sufficient illumination is provided. WEATHER Weather forecasts should be available for the next work period prior to work commencing. Severe weather warnings should be taken into account as to the possibility of work having to be terminated during the operational period or not starting at all. WORK NEAR WATER All personnel working in boats, on docks, or generally within three metres of water deeper than one metre, shall wear a life jacket. Dangerous mud flats posing a hazard shall be designated on the site map as areas off limits to personnel. Mark these locations with hazard tape, barricades, or other marking equipment. Where tides are unpredictable, or where there is a danger of being cut off by the tide, personnel should be briefed to be extra vigilant. Personnel should be withdrawn from areas where being cut off is a possibility well before the incoming tide poses a threat to safe exit route. GAS MONITORING INFORMATION Oxygen Oxygen must be equal to or greater to 19.5% and less than or equal to 22%. There should be no unexplained defection from the calibrated setting for ambient air typically 20.9% Atmospheres less than 19.5% should be treated as Immediately Dangerous to Life or Health (IDLH) atmospheres for purposes of respiratory protection selection. Atmospheres greater than 22% should be treated as a flammable atmosphere hazard. Combustible Atmospheres Where flammable/ combustible gases and vapours may be present, the instrument reading should be less than 10% LEL. There should be no unexplained deflection from the calibrated zero setting without the assessment of potential toxic hazards associated with the atmosphere. PERSONAL PROTECTIVE EQUIPMENT (PPE) Personal protective equipment selection should be based upon the hazards expected to be encountered at the spill site. To assist with selection refer to the appendix figure. SITE FACILITIES SANITATION AND PERSONAL HYGIENE Potable water, non-potable water, toilets and personal hygiene facilities shall be readily available. Location of hygiene facilities are contained on the Site Safety Map. FIRST AID Each site shall have a member of the response team identified as a first aider. This person shall have been trained in first aid techniques for likely medical incidents during a response. Additional medical advice and support should be identified for this person e.g. doctor, hospital and ambulance/ medevac support. DECONTAMINATION Contaminated personnel and equipment shall be decontaminated in accordance with the instructions of the Beach Master, who must prepare a decontamination plan which should include the following things: Issue 5 31/03/15 Page 60 of 102

62 A description of the location and layout of potential decontamination stations for the facility. A list of the decontamination equipment needed for the possible hazards. The appropriate PPE for persons assisting with decontamination. Appropriate procedures for specific materials that may be encountered. Methods and procedures for preventing contamination of clean areas. Methods and procedures for minimising worker contact with contaminants during removal of PPE. Safe disposal methods for clothing and equipment which are not completely decontaminated. Revisions whenever the type of PPE or equipment changes, the site conditions change, or the facility hazards are reassessed based on the new information. Recommended PPE Donning Procedures Inspect PPE to ensure it is in proper working condition before each use. Close zips, buttons and snaps fully. Tuck gloves under the sleeves with a second pair of tough outer gloves over the sleeves. Tuck boots under the legs of the outer clothing. Wear hoods, if not attached, outside the collar. Tape all seals to prevent contaminants from running inside the gloves, boots and jackets. The Decontamination Line The decontamination line is an organised series of procedures performed in a specific sequence to reduce levels of contamination on personnel, PPE and equipment until no contaminant is present. Each procedure is performed at a separate station. The stations are arranged in order of decreasing contamination, preferably in a straight line. Hot Zone Warm Zone Cold Zone Tool/ equipment drop Rubbish drop Wash outer garments Rinse outer garments Remove outer garments Wash/ rinse inner garments Wash boots Face piece drop Inner glove drop Shower/ changing area Issue 5 31/03/15 Page 61 of 102

63 7.4 SITE EMERGENCY PLAN After the Site Safety and Health Plan Assessment Form and Site Map have been completed in conjunction with the site Operational Plan, a site Emergency Plan should be produced. This plan should include the following elements: Site emergency responder supervisors Work plan Site facilities Site alerting/alarm system Evacuation plan Emergency medical facilities Guidance for completion of these elements can be drawn from preceding information. Issue 5 31/03/15 Page 62 of 102

64 Site Specific Health and Safety Plan Assessment 1. APPLIES TO SITE : 2. DATE : 3. TIME : 4. INCIDENT : 5. PRODUCT(S) : (Attach MSDS) 6. Site Characterisation 6a. Area Open water Inshore water River Saltmarsh Mudflats Shoreline Sand Shingle Docks 6b. Use Commercial Industrial Public Government Recreational Residential Other 7. Site Hazards Boat safety Fire, explosion, in-situ burn Slips, trips and falls Chemical hazards Heat stress Steam and hot water Cold stress Helicopter operations Tides Drum handling Lifting Trenches, excavations Equipment operations Motor vehicles Visibility Electrical hazards Noise Weather Fatigue Overhead/buried utilities Work near water Others Pumps and hoses 8. Air Monitoring (Oil company incident) O 2 LEL Benzene H 2 S Other 9. Personal Protective Equipment Foot Protection Coveralls Head Protection Impervious suits Eye Protection Personal Floatation Ear Protection Respirators Hand Protection Other 10. Site Facilities Sanitation First Aid Decontamination 11. Contact details : Doctor Phone Hospital Phone Fire Phone Police Phone Other Phone 12. Date Plan Completed 13. Plan Completed by Issue 5 31/03/15 Page 63 of 102

65 Site Health and Safety Plan Site Emergency Plan Safe 1 Site Name Location/ Map Ref. Site Supervisors (list roles and names) Work Plan Site Facilities Issue 5 31/03/15 Page 64 of 102

66 Site alerting/ Alarm system Evacuation Plan Emergency Medical Facilities: First Aid: Doctor: Hospital: Ambulance Prepared by: Date: Issue 5 31/03/15 Page 65 of 102

67 Site Health and Safety Plan Assessment Form Site Name Location/ map Reference Include Work Zones, First Aid Locations, Primary and Secondary Escape Routes, Assembly Points, Staging Area and Command Post Locations. Issue 5 31/03/15 Page 66 of 102

68 Site Health and Safety Plan Site Gas Monitoring Initial Test Follow Up Tests Gas Test Limits Results Date/ Time Results Date/ Time Results Date/ Time Results Date/ Time % O 2 >19.5%<22% % LEL <10% H 2 S STEL 15 ppm PEL 10 ppm Benzene STEL 1 ppm PEL 0.1 ppm #1 #2 #3 #4 #5 O 2 = Oxygen, LEL = Lower Explosive Limit, H 2 S = Hydrogen Sulphide, STEL = Short Term Exposure Limit, PEL = Personal Exposure Limit #1 = #2 = #3 = #4 = #5 = Tests completed by Initial test 1 st follow up 2 nd follow up 3 rd follow up Name Signature Issue 5 31/03/15 Page 67 of 102

69 Site Health and Safety Plan Site Briefing Incident Site Name Date Project Code Location/Map Ref. Time Briefing Conducted by. Topics Covered: Weather Conditions Injuries and Illnesses Corrective actions/precautions First Aid Site emergency plan Site hazards Oil/chemical hazards PPE to be worn Decontamination procedures Other topics (list below) Comments Issue 5 31/03/15 Page 68 of 102

70 Shoreline Survey Report Form A Site Details A1 Incident A2 Project Code A3 Date A4 Time Survey Started A5 Site Name No. A6 Map/Chart ref. Grid reference/ lat long A7 Photos Yes No Roll No. A8 Video Yes No Tape No. A9 Surveyed By Foot Boat Air A 10 Completed by Signature B Weather Conditions B1 Wind Speed B2 Direction B3 Sea State B4 Time HW B5 Time LW B6 Current C Shoreline Features C1 Shore Type % C2 Shore Access Cliffs Metalled Road Bedrock Track Boulders (>10cm) Pathway Pebbles (1-10cm) Steps Gravel (2mm-1cm) Slipway Sandy Car park Mud Boat Man-made Other Marsh/ Mangrove Other C3 Load Bearing Firm Will support any vehicle Good 4 wheel drive Soft Tracked vehicles Very soft Will not support vehicles Issue 5 31/03/15 Page 69 of 102

71 D Shoreline Usage D1 Industry Sea Water Intake Fisheries Docks Other Unknown Details D2 Recreational Bathing Marina Watersports Hotel Moorings Other Details D Ecological Important Habitat Rare Species Birds Dunes Wildlife Casualties Unknown Details E Suitability for Parking/ Equipment Storage E1 Area Available Yes No E2 Security needed? Yes No Details F Storage Facilities for oil/oiled solids F1 Facilities for oil Available (add details below) Not available F2 Facilities for oiled Available (add details below) Not available solids Details Forwarded to: Planning Issue 5 31/03/15 Page 70 of 102

72 G Sketch Map of Area ( Plan view and shore profile/s) Site Have you included the following? Band A, B, C Scale North Arrow Pits Boom anchorpoints % Cover Photo location Key landmarks Access points Oil distribution Likely disposal sites Slope Position H/L tide Access restrictions Backshore features Issue 5 31/03/15 Page 71 of 102

73 H Surface Oiling (see key below and visual aid) H1 Band H2 Area H3 Dist. H4 Thickness H5 Character H6 Zone Length m Width m % F M T C R P D US M S LS A B C D E F H1 Band: Delineated on sketch map. Use identifiers A, B, C. bands to be chosen to have a fairly even oil distribution and thickness. H2 Area: Length and width of the oiled area at each zone. If multiple bands of oil across shore, width represents the sum of them. H3 Distribution: The % of the surface within an area covered by oil (see visual estimation chart below. H4 Thickness: Average or dominant oil thickness within an area. 1 = Pooled oil > 1 cm thick 2 = Cover 1mm 1cm thick 3 = Coat 0.1 mm 1 mm thick (can be scratched off rock with fingernail) 4 = Stain <0.1 mm thick (cannot be scratched off easily) 5 = Film Transparent or translucent film or sheen H5 Character: F = Fresh M = Mousse T = Tar balls or patties C = Tar Coat R = Surface residue P = Asphalt pavement D = Debris Unweathered, low viscosity Emulsified Balls <10cm, Patties > 10cm Weathered coat or cover Non-cohesive, oiled surface sediments Cohesive mix of oil and sediment Seaweed, rubbish etc.. H6 Zone: Refers to height on shoreline US = Upper shore MS = Middle shore LS = Lower shore Issue 5 31/03/15 Page 72 of 102

74 J Subsurface Oiling J1 Pit J2 Penetration Depth J3 Concentration and Range (cm) AP OP PP OR OS TR NO #1 #2 #3 #4 #5 AP = Asphalt pavement cohesive sediment/ weathered oil mixture OP = Oil-filled pores pore spaces in the sediment matrix completely filled with oil PP = Partially filled pores pore spaces filled with oil (oil flows out of pores when disturbed) OR = Cover (>0.1 1 cm) or Coat ( <0.1cm) of oil residue on sediments OS = Stain (<0.01 cm) or film oil residue on the sediment surfaces. Non cohesive. TR = Trace discontinuous film or spots of oil on sediments or tackiness with no visible evidence of oil NO = No visible or apparent trace of oil Have samples been taken? Yes No Have all the samples been labelled? Yes No Summary of Proposed Action (After on site evaluation) Clean up Strategy Approval Authorised by (print name) Authorised by (signature) Issue 5 31/03/15 Page 73 of 102

75 8.1 General 8 - Waste Management Plan Oil spills generate a lot of oily waste, often in amounts far in excess of the original oil spillage. If not managed properly, large quantities of hazardous oily wastes can have adverse impacts on the environment and can cause logistical problems, delays and great expense for clean-up operations. Types of waste that may arise during/after a clean-up operation include the following: recovered oil, seawater and oil mixtures/emulsions, seawater and oil mixtures/emulsions treated with dispersant, lumps of thick weathered oil, oiled sands, shingles and other sediments, oiled vegetation and shorelinedebris, oiled fauna, cleaning products, and used sorbent materials, personal protection equipment, containers and other contaminated solids (e.g. plastics, textiles, metal). The waste management strategy adopted when responding to an oil spill incident must consider the Waste Hierarchy laid out in the EU Waste Framework Directive. Management options under the waste hierarchy comprise prevention/minimisation, re-use, recycle, other recovery, and disposal. In accordance with this hierarchy, amounts of waste generated during clean-up operations should be minimised and wherever possible oily wastes should be recovered for recycling and re-use. Disposal is the last waste management option considered. All oily wastes must be handled, stored, transported and disposed of as hazardous waste in accordance with the legislative requirements. The generation of oily waste during clean-up operations can be minimised in a number of ways, including the use of oil and water separators to reduce amounts of liquid waste; using selective cleanup techniques so that clean substrate/material is not picked up along with the contaminated; and good site management during the response. Where possible, equipment and resources should be washed and re-used. Wastes should be segregated into different types in order for it to be managed effectively and to enable the waste to enter the appropriate treatment, recycling or disposal method. Separation of wastes should be done according to their physical state (e.g. solid or liquid) and the type of oily waste (e.g. plastic, mineral, organic). Responsibility for waste management arrangements for shoreline pollution lies with the local authorities. TBPC will arrange for the disposal of oily waste from clean-up operations within the docks, on harbour waters and on land owned by the Port, in conjunction with the local authorities and the Environment Agency as appropriate. For large incidents including shore-line clean-up operations co-operation across authorities will be required to ensure that waste is managed in a timely and efficient manner. The Oil Spill Plans of adjacent local authorities describe procedures for the disposal of wastes from shoreline clean-up in situations where an Emergency Management Team is established under the control of the County Council s Chief Executive or Emergency Planning Officer. These plans contain details of temporary waste storage sites in the vicinity of the port. Copies of these plans are held in the Marine Response Centre. In the event of an oil spill the Environment Agency would be able to provide advice and guidance on waste management matters. Issue 5 31/03/15 Page 74 of 102

76 8.2 Temporary Storage Clean-up activities may produce quantities of oil and oily debris at a fast rate, generally resulting in larger quantities of waste than can be disposed of immediately. Therefore, temporary storage is likely to be necessary. For example, an oil spill in harbour waters may require quantities of recovered oil to be held in fast tanks (or similar storage container) in the Port area awaiting disposal. For an oil spill not involving an oil company, the Harbour Authority may provide a bunded lay down area as temporary storage for drums and skips in consultation with the Environment Agency. Suitable sites for temporary storage must be identified in the vicinity of the clean-up operation. Selection of suitable sites requires consideration of a number of factors including access by vehicles, firm ground, environmental sensitivities, risk of flooding, space required to segregate wastes and other operational requirements. The sites for any temporary storage areas would be agreed prior to use with the Environment Agency. Storage areas need to be isolated, bunded and lined with an impermeable barrier (e.g. thick plastic sheeting) to prevent contamination of groundwater and the surrounding area. Care must be taken to keep different types of waste separate and to prevent the spread of oil contamination. A range of temporary storage methods can be used, including the following: Storage Facility Type of Waste Comments Suitable for initial storage following clean-up on water. Barges Road tankers Pits Bunds Liquid Liquid Liquid & liquid/solid mixture Liquid & liquid/solid mixture HM Customs and Excise must be notified of intention to land recovered oil by barge. Suitable for initial storage and ideal for transport to final disposal site. Can be excavated in substrates that are reasonably firm. Must be lined with sand and heavy duty plastic sheets. Cheaper than pits. Must be lined with heavy duty plastic sheets. Skips Drums Plastic containers Heavy duty plastic bags Liquid & liquid/solid mixture Liquid & liquid/solid mixture Liquid & liquid/solid mixture Solids Versatile, robust and cheap. Difficult to handle when full. Quick deployment. Useful for inaccessible areas. Ideal for manual clean up. Cheap & easy to deploy. Should be used to transport waste rather than store it for any length of time. Hard standing Solids Preferably a bunded level site. Issue 5 31/03/15 Page 75 of 102

77 Details of temporary storage sites for wastes arising from shoreline clean-up are held in the Local Authority Oil Spill Plans. For a major incident temporary storage sites may be established at a regional level and waste recovered in the Port may be transported to this regional storage facility prior to final disposal. 8.3 Disposal Methods All oily wastes must be disposed of as hazardous waste in accordance with the specific legislative requirements for its movement, recovery and disposal. All waste contractors must be appropriately licensed. The Port Waste Management Plan contains details of approved waste disposal contractors for oily wastes. These wastes must only be disposed of at a suitably authorised waste management facility. A hazardous waste consignment note must be produced and retained for each movement of hazardous waste. In addition, HM Customs and Excise must be notified if recovered oil is brought ashore by barge and provided with information on the quantity and nature of the recovered oil by the operator. Arrangements for the disposal of small amounts of oily waste are made by the Port or the Port s responders, larger quantities would be arranged in consultation with the Environment Agency and other relevant authorities. The treatment and disposal option selected will depend upon the nature and volume of the oily waste, the availability of suitable sites and facilities, costs and regulatory controls. Possible disposal options will include the following: Recycling or reprocessing of oily liquid waste- The best waste management option is to recover as much liquid oil as possible to be taken to an oil refinery or a repossessing/treatment centre. A number of specialist waste contractors provide waste oil recovery and treatment services where recovered oil is reintroduced to the market for its original use or is recycled as a fuel oil for industrial use. Transport to an appropriate disposal site - Controlled landfill may be suitable for disposal of lightly oiled (hazardous) waste with agreement of Environment Agency/Local Authorities. Noncontaminated general wastes can be disposal of at landfill by approved contractor. Treat, stabilise and reuse oily waste can be treated or stabilised to enable its reuse. Contaminated material can be stabilised using a binding agent such as quicklime, cement, clay or asphalt. Contaminated soils can be mixed with soil bulking agents and nutrients and then spread on the earth under controlled conditions (a process called land farming). Treatment of waste comes under the waste permitting system and would be developed in close liaison with the Environment Agency and other relevant authorities. Controlled combustion/incineration- may be suitable for small quantities of waste such as heavily oiled vegetation or debris. In the event of an oil spill the Environment Agency would be able to provide advice and guidance on waste disposal and treatment options. Issue 5 31/03/15 Page 76 of 102

78 9 - Contact Directory See Annex 9 Emergency Contacts Directory Issue 5 31/03/15 Page 77 of 102

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83 10 - TRAINING AND EXERCISES 10.1 Training The importance of training for harbour personnel who may become involved in the response to oil spill incidents is recognised and acknowledged. All members of the Oil Management Team and undergo periodic training in line with the following matrix. Course TBPC Personnel Role in Response Team Notes Oil Spill Equipment Operators Course 1P MCA Accredited x5 Dredge Crew x17 Pill Hobblers Operators All staff who operate with Adler & Allan equipment must be fully conversant with correct and safe deployment techniques. Valid for 3 years. Oil Spill Management Course 5P MCA Accredited DHM (SO) DHM (SMS) DMEM On Scene Commanders A training course providing in-depth knowledge of the main functions of an oil spill management team. Valid for 3 years 10.2 Exercises A series of annual exercises should take place within the Port in line with the type and frequency shown in the exercise matrix. Exercise Frequency Notes Notification Exercise Quarterly Test communication systems, check availability of personnel, evaluate travel options and the speed at which travel arrangements can be made. Table Top Exercise 6 monthly Consist of interactive discussions of a simulated scenario among members of a response team but do not involve the mobilisation of personnel or equipment. Equipment Deployment Exercise 6 monthly Test the capability of a local team to respond to a Tier 1 or 2 type spill. Incident Management Exercise Once every 3 years Demonstrate spill response management capabilities, integration of roles of different parties, focus on overall incident management aspects. Issue 5 31/03/15 Page 82 of 102

84 10.3 Training / Exercise Records Training records are held by The Deputy Haven Master (SMS) who will be responsible for the upkeep of these records. An Exercise Report must be completed and any amendments actioned. It is the responsibility of the Exercises On Scene Commander to complete this form and any amendments to the plan. Exercise Report Scenario Location Date../../. Participating organisations or authorities List of equipment deployed Tactical response actioned Boom deployment actioned Observations Details of amendments to be made to Contingency Plan I can confirm that the details on this form provide a realistic summary of the exercise. Any action points resulting from this exercise have been completed accordingly. On Scene Commander Signature Position/job title Date Issue 5 31/03/15 Page 83 of 102

85 11. Risk Assessment 11.1 Introduction The Port of Bristol is a large, deep, lock-protected, general cargo, multi user port located on the Severn Estuary. The Port comprises of two fully enclosed docks, Royal Portbury Dock on the southern side of the River Avon, capable of handling post-panamax vessels up to 300m loa, 40m beam and 14.5m draught, and Avonmouth Docks to the North capable of handling handy size vessels up to 200m loa, 30m beam and 11m draught. The Bristol City Docks are located on the River Avon and Sharpness Dock on the River Severn, and although not part of the Bristol Port Company, vessels using these docks navigate through TBPC s Harbour Area. In the region of 3000 shipping movements occur annually carrying over 10,000,00 tons of cargo. The upper Bristol Channel forms the Severn Estuary and provides a deep water approach to the entrance of the docks, with 17m below CD at Portishead Point and a tidal range of up to 14m. The associated tidal currents flow at speeds of up to 5kts, self-scouring the approach channels, and providing wide docking windows for deep-draught vessels. Entrance locks provide access to the impounded waters of the docks, where periodic dredging maintains depths in excess of the maximum advertised. Berths 1 to 4 at Portbury can each handle Panamax length vessels, 1 and 2 providing general cargo and gantry crane facilities, 3 and 4 general cargo, and 4 molasses and self-discharge gypsum. Berths 5 and 6 are dedicated to the bulk discharge and grain-loading of up to post-panamax dry bulk vessels, whilst 7 is a dedicated jet fuel facility. Avonmouth has 6 liquid product berths within the Oil Basin, and 23 general cargo berths with a range of fixed and mobile facilities. Dry bulk cargos include coal, animal feedstuffs, grain, aggregates, fertilizer and wood pellet/chip, break-bulk cargo include steel, aluminium and paper, liquid bulk cargos include jet fuel, DERV, spirit, molasses and orange juice, and both docks handle containers. All liquid product berths are managed by the Bristol Port Company and pollution equipment for these berths is highlighted in section Basic repair and maintenance functions can be supported by prior arrangement, but the dry-dock is not currently in commission. Towage is provided by a third party contractor, Svitzer, who maintain a fleet of five c40 tonne bollard pull harbour tugs in the port. Pilotage is provided by the Bristol Pilots Limited Liability Partnership. Due to the prevailing currents and the lack of suitable anchorages within the Statutory Harbour Area, no anchorages or sheltered areas are designated. Sand dredging operations is the only other industrial commercial activity conducted within the area, whilst a variety of commercial pleasure craft operate on the Avon and in the Estuary. Avonmouth and Royal Portbury Docks are both capable of offering Places of Refuge, but suffer from limitations which may make them less attractive than other ports. From a navigational safety perspective, the diversion up the Severn Estuary will take any vessel seeking refuge a significant distance from the open sea, and there are very limited anchorages and swinging opportunities once committed to the last 20 miles of approach channel. The locks are less easy to negotiate in a vessel which is in any way not under command or restricted in its ability to manoeuvre, and any vessel limitations may demand delays whilst awaiting the right tidal conditions. The proximity of residential housing may render Bristol unsuitable to provide refuge for any vessel suffering leakage of noxious cargos. Relatively deep and sheltered waters are available once safely within the docks, which by their nature will contain any spillages. A broad range of cargo handling equipment is available to discharge cargo as required. Issue 5 31/03/15 Page 84 of 102

86 11.2 Navigation risks Navigation Risks are identified in the Navigation Risk Assessment, and cover the full spectrum of collision, grounding, and contact events. These Risks are itemised and reduced to ALARP through a range of control measures, the details of which are formalised as Marine Procedures Supplementary risks Chiksan arm failure The risk of a structural failure of the Chiksan arms located in the Oil Basin, and RPD Berth 7 during pumping operations is mitigated by a planned maintenance regime and permanent supervision during operations Pipeline Failure There are numerous pipelines situated within the port, between the Oil Basin and the relevant oil terminal, RP Berth 7 and the OPA pipeline. A pipeline failure could give rise to an oil spill incident occurring. Measures have been taken to reduce this by implementing an efficient maintenance and monitoring system on the pipelines and also by the addition of manual isolation valves in the pipelines Bunkering Vessels receive bunkers at the port by road tanker or bunker barge. In the region of 6000 ton is delivered by bunker barge with transfer taking place within the enclosed dock. Road tankers deliver a similar figure annually. Bunkers taken at the port are either Heavy Fuel Oil or Marine Gas Oil Quantitative Risk Assessment. The following table shows the potential scenarios, credible release quantity, worst-case release quantity and probability of occurrence for each potential scenario. For the purpose of planning, the worst case scenarios have been based on the following assumptions: Vessel involved assumed to be a 70,000 dwt Tanker. All collisions assumed to hole two wing tanks All groundings assumed to hole centre tank Wing Tank capacity is 3000 m 3 Centre tank capacity is 5000 m 3 Vessel discharge rate is 2500 m 3 /h Road Tanker Capacity is 40 m 3 Chiksan arms assumed to hold 5m 3 Pipelines assumed to hold up to 300 m 3 Scenario Worst Case Qty Credible Qty Potential Probability Collision underway 3000 m m 3 Low Collision with fixed installation 3000 m m 3 Low Grounding 2500 m m 3 Low Bunkering Operation from Road Tanker 20 m 3 <1 m 3 Medium Chiksan Arm failure 5 m 3 <1 m 3 Low Pipeline failure 300 m 3 20 m 3 Low Bunkering Operation from Barge 25 m 3 <1 m 3 Medium Issue 5 31/03/15 Page 85 of 102

87 11.5 Fate of Spilled Oil General. In considering the fate of oil on the water a distinction is frequently made between non-persistent oils, which tend to dissipate rapidly from the sea s surface and persistent oils, which do not. Non persistent oils are commonly referred to as white oils and have an API > 45. Persistent oils are commonly referred to as black oils and have an API < 45. The physical and chemical changes which spilled oil undergoes are collectively known as weathering (see figure below). Knowledge of these processes and how they interact to alter the nature and composition of the oil with time is valuable in preparing and implementing this contingency plan for effective oil spill response. evaporation fragmentation spread stranding emulsification biodegradation dispersion sedimentation Combined weathering process of spilled oil 11.6 Fate of Spilled Oil Specific (Marine Diesel Oil). The Bristol Port Company operations involve both the handling of non-persistent oils and persistent oils. A computer model, ADIOS 1.1, was used to give an indication of the likely fate of an oil spill of both Marine Diesel and Heavy Fuel Oil. The parameters used for model run one were: Water temperature: 9 0 c Wind Speed: 8 knots Oil Type: Marine Diesel Quantity of Oil Spilled: 20 cu.m. Issue 5 31/03/15 Page 86 of 102

88 The results of the computer model run were as follows: Time Elapsed (hours) Volume Dispersed (%) Volume Evaporated (%) The parameters used for model run two were: Water temperature: 9 0 c Wind Speed: 8 knots Oil Type: heavy Fuel Oil Quantity of Oil Spilled: 20 cu.m. The results of the computer model run were as follows: Time Elapsed (hours) Volume Dispersed (%) Volume Evaporated (%) Oil Spill Quantification. Estimating the initial release volume of an oil spillage is notoriously difficult to establish, unless accurate information regarding flow rates, exact time of spillage and duration of spillage are all known. The simplest method of quantifying on water oil slicks is by visual appearance. The colour of the oil slick gives an indication of the thickness and type of oil. However, it should be borne in mind that oil slicks do not spread uniformly and as such, the estimate of oil remaining at sea is open to potentially large errors. The table in section 3.5 should be used in the estimation of oil spill quantity. Issue 5 31/03/15 Page 87 of 102

89 Oil Spill Quantification Table. Colour Oil Type Thickness (mm) Volume (m 3 /km 2 ) Silvery Light Sheen Iridescent Sheen Light Brown Thick Sheen / FO Brown Fuel Oil / Crude Oil Black Crude Oil Orange Emulsion (Mousse) Oil Spill Movement Spilled oil on water moves as a function of the current and wind. The current has a 100% effect on the speed and direction of an oil slicks movement, for example, if the current heads north at 3 knots, then the oil slick will travel north at a rate of 3 knots. Wind, on the other hand, has only a 3% influence on the movement of the oil slick. This is shown in the following diagram. 3% wind marina time A time B 100% current Oil movement on sea surface 11.9 Tidal Influence within the Estuary - General Any movement of spilt oil upon the water will be influenced by the above. However, oil migration within the Severn Estuary is also dependent upon the initial release location of the spill. After basic analysis the following details illustrate the rates and directions of tidal streams within the estuary. Rate and set have been identified and are recorded below: Issue 5 31/03/15 Page 88 of 102

90 Outgoing Tide (Ebb) Incoming Tide (Flood) Speed Direction Speed Direction Spring Tide Neap Tide 3.2 knots (5 hrs after HW) 1.7 knots (5 hrs after HW) 4.6 knots (3 hrs before HW) 2.4 knots (3 hrs before HW) Issue 5 31/03/15 Page 89 of 102

91 12. Environmental 12.1 Overview of the Severn Estuary Environment Avonmouth and Royal Portbury Docks are located on either side of the mouth of the River Avon where it flows into the Severn Estuary. Bristol s Harbour Area stretches from north of Avonmouth Docks down to Steep Holm Island in the Lower Severn Estuary and up the River Avon to the entrance to Bristol City Docks (Figure 1). The shoreline within the harbour area between Chittening Warth to the south of Avonmouth Docks and Ladye Point in Clevedon falls within the jurisdiction of South Gloucestershire, Bristol City and North Somerset Councils (Figure 3). Areas of the foreshore in the immediate vicinity of Avonmouth and Royal Portbury Docks and to the north in the vicinity of Chittening Warth are owned/leased by the Port (Figure 2). Physical environment The Severn Estuary is one of the largest estuaries in the UK, with the third highest tidal range in the world. It is characterised by its strong tidal currents, mud laden waters and extensive mudflats, saltmarshes and sandbanks. The Estuary s sheer scale and extreme dynamic physical environment shapes its ecology and sets it apart from other UK and European estuaries. Key aspects of the physical environment of the Severn Estuary are as follows: There is a 14.8m difference between the highest and lowest astronomical tides at Avonmouth, with a mean spring tidal range of around 12m. The neap tidal range at Avonmouth is 6m which is larger than the spring tidal range in many locations around the UK. The large tidal range propagates into the River Avon over 17km to its normal tidal limit at Netham Dam. Strong tidal currents occur throughout the area. Currents in the approaches to Bristol Port (Bristol Deep and King Road) are around 4 or 5 knots. The highest currents of around 8 knots are recorded upstream of Avonmouth at the Shoots by the Severn Bridge Crossings. The estuary is a tidally dominated system, in contrast to the wave dominated environment of the wider Bristol Channel to the west. There is significant variation on tidal regimes from year to year. At Avonmouth there are about five hours of flood and seven hours of ebb tide. Winds and waves from the west and south west are prevalent in the approaches to Bristol Port. The high energy associated with the tides in the estuary has a large effect on the suspension and deposition of sediments. During spring tides very large volumes of suspended sediments can be found throughout the water column (over 30 million tonnes in the estuary s waters on a spring tide). During slack water and neap tides when there is less energy in the estuary system the sediments settle out to form mobile layers of mud on the bed of the estuary. Subtidal sands cover a large proportion of the middle and outer estuary. In the approaches to Bristol Port there are extensive intertidal and subtidal sandbanks of Welsh Grounds and the Denny Shoal. Highly mobile sands form sand waves (mega ripples) which, for example, are up to 4m high in the deep water channel off Portishead Point. In the scoured deepwater channels sands can form a relatively thin veneer over the underlying bedrock, which is exposed in large areas. The estuary coastline within Bristol Port s harbour area is a high energy environment, comprising mostly of rocky shores, tidal flats, saltmarshes and shingle banks. The more sheltered environment of the River Avon up to the Bristol City Docks is characterised by mudflats and salt marshes. Intertidal mudflats are exposed by the tide twice a day and are subject to significant changes in bed levels as a result of variations in tidal range, season and wave conditions. The dynamic physical environment of the Severn Estuary and River Avon means that any oil spills in harbour waters would be expected to spread and disperse over large distances in relatively short periods of time. A spill in the mouth of the estuary will travel around 35km upstream on an incoming spring tide and about half that distance on a neap tide. Issue 5 31/03/15 Page 90 of 102

92 Habitats and species The Estuary has extensive intertidal mudflats, sand flats and saltmarsh habitats which support large numbers of invertebrate animals, with high densities of ragworm, lugworm, snails and other invertebrates. These prey species in turn support large populations of nationally and internationally important migratory waterfowl that visit each winter. Fringing saltmarsh contains several notable and nationally scarce saltmarsh plant species. The saltmarsh in the vicinity of Avonmouth and Royal Portbury Docks is not grazed. There are also areas of shingle with rocky outcrops and rock platforms, some covered in sea weed. Much of the subtidal habitats of the Severn Estuary support a relatively impoverished fauna and flora, characterised by low diversity and biomass communities due to the harsh physical environment. Subtidal sediments are generally inhabited by a few species of marine worm and amphipods. The tube-building honeycomb worm, Sabellaria alveolata, inhabits rocky and gravel substrates in the estuary and can form extensive sub-tidal reefs, largely in the outer estuary. Intertidal reefs can be found on the gravel banks upstream of Avonmouth and the rocky shores between Portishead and Clevedon. The Severn Estuary is an important migratory route for a number of designated and protected fish species, including shad, lamprey, salmon, sea trout and eels. The estuary is also an important nursery and feeding area for a wider fish assemblage, comprised of over 100 species. Many of these fish species move between the estuary and the open sea on a seasonal basis or at different life history stages. Marine mammals, such as seal or harbour porpoise, are very rare visitors to the estuary. Phytoplankton and macroalgal growth is reduced in the Severn Estuary due to the high turbidity, rapid mixing of the water column and scouring. The extensive intertidal habitats of the Severn Estuary, particularly the mud and sand flats, provide feeding habitat for large numbers of wintering and passage migratory wildfowl and waders. The estuary regularly supports internationally important populations of over 60,000 water-birds over the winter months, with a five year mean peak of around 78,000 total birds between 2007/8 and 2011/12 (WeBS, 2014). The most important sites for waders in the estuary include Bridgwater Bay, Clevedon (Woodspring Bay), Severn Beach and the Welsh Coast between Rhymney and Nash. Portbury Wharf and the extensive intertidal habitats to the north of Avonmouth Docks support good numbers of wildfowl and waders in the winter month and autumn passage periods. Important bird species found in significant numbers in the vicinity of Bristol Port include, dunlin, redshank, curlew, ringed plover, teal, gadwall and mallard. The banks of the River Avon are mainly comprised of steep intertidal mudflats, backed by a narrow fringe of saltmarsh. There are a number of sheltered pills and creeks along the river, including Crockerne Pill, Chapel Pill and Sea Mills. The saltmarsh at Horseshoe Bend, Shirehampton, is backed by a wooded cliff, which contains a number of rare and notable plant and tree species. The intertidal and coastal habitats support a variety of waterbirds, including waders, gulls and duck species Nature Conservation Designations The importance and conservation value of the marine and coastal wildlife and habitats of the Severn Estuary and the mouth of the River Avon are well documented and recognised in its designation and protection under international, European and national law. The location of sites designated for their nature conservation value in the vicinity of TBPC s harbour area are shown in Figure 7. Issue 5 31/03/15 Page 91 of 102

93 The intertidal habitat of the Severn Estuary supports populations of birds that are of European importance and in recognition of this the estuary is classified as a Special Protection Area (SPA) under the EC Birds Directive. The Estuary is also designated as a Special Area of Conservation (SAC) under the EC Habitats Directive because it contributes to the range and variation of estuaries in the UK, as an example of a large turbid-water estuary with an exceptional tidal range.theimportant marine conservation features in the estuary includesubtidal sandbanks, intertidal sand and mudflats, Atlantic salt meadows, biogenic reef and three species of migratory fish. The intertidal and subtidal areas of the estuary designated as SAC and SPA are together known as the Severn Estuary European Marine Site (EMS).The Severn Estuary is also a designated Ramsar site as a Wetland of International Importance. This designation is based on its physical features, estuarine communities, migratory fish and bird populations. Further information on the conservation features and objectives of the Severn Estuary SAC, SPA and Ramsar site can be found in the Regulation 33 advice produced by Natural England and Natural Resources Wales. This advice is currently under review. The intertidal areas of the Severn Estuary are designated as a Site of Special Scientific Interest Special (SSSI) under national environmental legislation. The Severn Estuary SSSI covers around 16,000ha of intertidal habitat, including saltmarsh, sandbanks, mudflats, rocky platforms and grazing marsh. The estuary is designated for its estuarine fauna, including important bird and fish populations, and its diverse geology and wide range of geomorphological features. Outside TBPC s harbour area there are two further Estuary SSSIs covering the upper estuary and Bridgwater Bay, the latter of which is also a National Nature Reserve. Located within the estuary itself are three island SSSI s. These sites namely, Sully, Flat Holm and Steep Holm are of geomorphological, geological and biological importance. The intertidal SAC, SPA and SSSI units in the vicinity of the Avonmouth and Royal Portbury Docks are generally in favourable condition. The exception is two units of saltmarsh in the vicinity of Pill and Chittening Warth which are in unfavourable and declining condition primarily due to the loss of grazing in these areas. Adjacent to TBPC s harbour area along the shore of the River Avon there are a number of terrestrial sites of nature conservation importance (Figure 8), including: Horseshoe Bend, Shirehampton, SSSI; Avon Gorge Woodlands SAC and SSSI; and Leigh Woods National Nature Reserve. These sites are designated primarily for their geology and woodland habitats containing rare fauna and flora, including species that are unique to the area, such as the Bristol and Wilmott s whitebeam trees in the Avon Gorge. There are no Areas of Outstanding Natural Beauty (AONB), Heritage Coasts or National Parks within TBPC s Harbour Area. The nearest of these coastal designations are located further seaward in the Bristol Channel at the Quantock Hills, Exmoor and the Vale of Glamorgan Environmental, social and economic sensitivities The impact of oil spills on coastal and marine habitats and species in the Bristol Channel and the sensitivity of different shoreline types to oils spills are discussed in the following reports: Issue 5 31/03/15 Page 92 of 102

94 The Bristol Channel Counter Pollution Association Shoreline Environmental Sensitivity Manual (ECOS, 2002) Feasibility study on the use of dispersants in the Bristol Channel in the event of an oil spill incident (CCW, 2002). An Atlas of Coastal and Marine Resources Sensitive to Oil Pollution (CCW, 2009). Intertidal saltmarshes and mudflats of international and national importance are the most sensitive habitats to oil pollution within TBPC s land ownership and harbour area. The smothering and toxic effects of oil are likely to greatest in these more sheltered intertidal habitats, and on any sensitive animals, birds and plants they support. The breakdown of oil tends to be slowest in intertidal areas, which leads to higher concentrations of oils which may persist for years. The effects of oil spills on waterbirds are likely to be greatest in the winter months when greater numbers of birds are present in the estuary. Attempts at clean-up of oiled mudflats and saltmarsh are likely to drive oil into the sediments and can be more damaging to these sensitive habitats than the effects of the oil alone. The main priority for oil spill response is therefore to prevent these areas from becoming contaminated with oil where possible. If oil reaches an area of mudflat, if it is not collected it is likely to be spread further along the estuary with the next tides. Therefore, loose oil, particularly from the margins of the mudflat habitat should be removed if access allows, minimising the risk of other habitats being impacted. Once oil has contaminated saltmarsh areas it should be left to degrade naturally. Rocky shore and sandflat habitats are generally less sensitive to oil pollution effects, having a shorter recovery time and greater successful clean-up potential than saltmarsh and mudflat areas. Avonmouth and Royal Portbury Docks are man-made structures and are considered to be of low conservation value and environmental sensitivity. The Severn Estuary supports an important coastal tourism and recreation industry. There are a number of popular resorts and attractions in the vicinity of TBPC s harbour area, including the traditional seaside resorts of Weston-super-Mare and Clevedon. There are no bathing waters within TBPC s harbour area, the nearest is Clevedon Beach located just outside the harbour. Recreational boating is a popular activity all year round, with higher numbers of boats present in the harbour area during weekends, particularly in the Easter and summer holidays. The greatest numbers of moorings in the estuary are located in Portishead Marina, Bristol City Docks and Cardiff Bay (all outside TBPC s harbour area). There are smaller numbers of moorings for recreational craft in the sheltered pills and creeks of the River Avon. There are popular coastal footpaths adjacent to the harbour area in the vicinity of Portishead, Clevedon, Severn Beach and along the River Avon. There is no public access in Avonmouth and Royal Portbury Docks, including most of the shoreline immediately adjacent to the docks. The estuary is important for a number of commercial fish species, including eels, salmon, sea trout, cod, whiting, bass, sole, plaice and mullet. The sandflats, mudflats and saltmarshes of the Severn Estuary provide important feeding areas for many juvenile fish. Overall, commercial fishing occurs at a relatively low level within TBPC s harbour area, with a few of small fishing vessels operating out of the North Somerset and South Wales coastal areas. There are no commercial shellfisheries within the harbour. A number of charter vessels operate sea-angling trips out of Portishead Marina, together with many personal sea angling boats and large active clubs, such as the Portishead Small Boat and Sea Angling Club. Recreational angling occurs in numerous places along the coast adjacent to the harbour area, with Battery Point, Portishead Pier, Clevedon Pier and Aust being popular angling locations. Angling is restricted in the immediate vicinity of Avonmouth and Royal Portbury Docks. Issue 5 31/03/15 Page 93 of 102

95 Although of low conservation value, the docks are of regional and national importance for trade and any disruption of operations and possible closure of Royal Portbury and/or Avonmouth Docks in response to an oil spill incident would have significant socio-economic impacts. Access for clean-up in the docks is good and recovery times short. The harbour s deep waters provide important shipping lanes for vessels visiting the commercial ports of Bristol, Cardiff, Newport and Sharpness all year round. There are maintenance dredging sites within Avonmouth and Royal Portbury Docks and their entrances and the main licensed disposal sites located nearby off the Avonmouth and Portishead coasts. The environmental, social and economic sensitivities and considerations for oil spill response within the following four areas of TBPC s harbour are summarised in the table below: The enclosed waters of Avonmouth and Royal Portbury Docks Harbour waters within the Severn Estuary & mouth of River Avon to Pill (i.e. to the inland limit of the Severn Estuary SAC/SPA in the River Avon) Harbour waters within the River Avon - Pill to the entrance to Bristol City Docks Foreshore in TBPC ownership in the vicinity of Avonmouth and Royal Portbury Docks Issue 5 31/03/15 Page 94 of 102

96 Summary of environmental, social and economic sensitivities and considerations for oil spill response in TBPC s harbour area: Environmental features Environmental Sensitivity Socio-economic features Socio-economic sensitivity Environmental considerations for oil spill response Natural England will be consulted over any oil spill response options in the Severn Estuary and River Avon in order to safeguard internationally and nationally designated sites Enclosed waters of Avonmouth and Royal Portbury Docks Man-made structures of low conservation value No designated marine habitats or species Harbour waters - Severn Estuary & mouth of River Avon Severn Estuary SAC, SPA, Ramsar & SSSI Designated features include: o Intertidal mud & sand flats o Saltmarsh (Atlantic salt meadow) o Migratory birds o Migratory fish o Estuary, subtidal sandbank & reef habitats Harbour waters - River Avon (Pill to Bristol City Docks) No designated marine habitats or species Predominantly intertidal mudflats and saltmarsh habitats Important adjacent woodland habitats at Horseshoe Bend and Avon Gorge Low High Moderate High Commercial vessels and significant port infrastructure Dredge/disposal areas No public access/ recreation/fishing Commercial shipping Recreational boating Dredge/disposal areas Commercial and recreational fishing Adjacent coastal resorts, amenity &recreation areas Small commercial craft and recreational boating Moorings for recreational craft in creeks and pills Dredge/disposal area Low level commercial and recreational fishing Adjacent coastal amenity &recreation areas High Moderate Moderate Low Enclosed artificial environment of little ecological significance. Access for clean-up is good and recovery time short. Priority for action is containment and recovery of any floating oil, preventing it from entering the estuary and river where possible (with three pairs of lock gates at each dock, oil booms and other oil recovery equipment). Standing approval is in place for the use of small quantities of dispersant in dock under appropriate conditions. Manual cleaning of man-made structures may include the use of high pressure hoses on quay walls and other structures where there is little marine growth. Where possible, safe and estuary conditions allow, any floating oil on the water surface should be removed physically. Removal of oil should particularly be attempted where this may reduce the possibility of oil coming ashore in sensitive areas. Given the dynamic environment there may be little that can practically be done to prevent the spread of oil to the shoreline. Loose oil on mudflats should be collected where possible, oil contamination in saltmarsh should be left to degrade naturally. No chemical dispersants should be used. Consider the need for emergency call-out of oiled bird rescue services/rspca Where possible, safe and river conditions allow, any floating oil on the water surface should be removed physically. Given the dynamic environment of the River Avon there may be little that can practically be done to prevent the spread of oil to the shoreline. It may be possible to use booms to protect creeks and pills. Loose oil on mudflats should be collected where possible, oil contamination in saltmarsh should be left to degrade naturally. Standing approval is in place for the use of small quantities of dispersant in the River Avon under appropriate conditions. Consider the need for emergency call-out of oiled bird rescue services/rspca Avonmouth and Portbury foreshore in TBPC ownership Severn Estuary SAC, SPA, Ramsar & SSSI Designated features include: o Intertidal mudflats o Saltmarsh (Atlantic salt meadow) o Migratory birds o Migratory fish o Estuary habitat Some port infrastructure (e.g. piers, flood defences) No public access, recreation& fishing Oil on mudflats and saltmarsh should be left to degrade naturally. No dispersants should be used. Consider the need for emergency call-out of oiled bird rescue services /RSPCA. Manual cleaning of man-made structures may be possible. Care should be taken during any clean-up operations to minimise disturbance and damage in or adjacent to intertidal areas. Advice would be sought from Natural England regarding possible clean-up operations in the vicinity of designated habitats. Issue 5 31/03/15 Page 95 of 102

97 13 - Roles and Responsibilities 13.1 RESPONSIBILITY OVERVIEW The owners and masters of ships, the operators of offshore installations, oil handling facilities, and the harbour masters/operators of ports/harbours bear the primary responsibility for operating in a manner that avoids marine pollution. They are equally responsible for ensuring that they have the means at their disposal to respond to pollution incidents within the limits of their stipulated area of jurisdiction. The following table provides guidance on who would assume the lead: Location of pollution On the water, jetties, wharves, structures, beach or shoreline owned by the harbour authority within the port/harbour area. Shoreline (including land exposed by falling tide). Jetties, wharves, structures, beach or shoreline which is privately owned. All other areas at sea (inside the UK Pollution Control Zone and the UK Continental Shelf). Responsibility for ensuring clean up Harbour authority Local authority Owner of the property/land MCA 13.2 HARBOUR AUTHORITY The Merchant Shipping (Oil Pollution Preparedness, Response and Co-operation Convention) Regulations 1998 came into force on 15 May 1998 (SI 1998 No. 1056). Regulations apply to any harbour for which there is a statutory harbour authority having an annual turnover, as defined in the schedule in the regulations, of more than 1 million. Every harbour authority of a harbour to which these regulations apply shall have an oil pollution emergency plan in accordance with the regulations. There may be joint plans between the harbour authority and the operators of oil handling facilities within an area. The obligation in the Regulations relates to pollution by oil spilt in harbour areas from vessels. The requirement is to plan to remove oil pollution from the harbour waters; and structures and shoreline owned by the harbour authority. Cleaning other shoreline areas is assigned to local authorities and the landowners. The Statutory Harbour Authority has a responsibility under Section 133 of the Merchant Shipping Act 1995 for bringing prosecutions for the offences of discharge of oil, or a mixture containing oil, into the waters of the harbour. Issue 5 31/03/15 Page 96 of 102

98 13.3 LOCAL AUTHORITIES There are three Unitary Authorities, which have coastline adjoining their boundaries; Bristol City, South Gloucestershire and North Somerset Councils. Although the councils work independently of each other they do provide mutual aid when required or requested. There is no lead County Council. If an incident occurs the lead authority becomes the one in which the incident is centred. Unitary Authorities have the responsibility for dealing with oil on the shoreline and beaches within the limits of their resources. Their role would be to carry out both County and District Authority functions, which includes; assuming responsibility for co-ordinating the appropriate Unitary Authority action plan in the event of widespread pollution which affects more than one district; assisting with oil on beaches in terms of providing districts with additional resources for clean-up activities; and remaining responsible for physical clearance in respective areas of jurisdiction MARITIME AND COASTGUARD AGENCY (MCA) In the event of a Tier three incident causing, or threatening to cause, significant pollution the MCA will mobilise its resources in response. Depending upon the nature of the incident the MCA will set up a Salvage Control Unit (SCU) and /or a Marine Response Centre (MRC). The SCU will be led by the Secretary of States Representative (SOSREP) who will monitor the salvage operation. TBPC and the Salvage Company will be represented in the SCU. All salvage plans will need to be cleared through the SOSREP before implementation. In exceptional circumstances SOSREP may choose to exercise powers of intervention. The MCA or the Port of Bristol, if within Port limits, will also set up a MRC to facilitate the at-sea response to pollution. This could involve spraying aircraft, oil pollution recovery vessels, deployment of booms, cargo transfer, etc. The MRC will be led by Port of Bristol, if within Port limits, or a MCA Counter Pollution and Salvage Officer (CPSO), if outside Port limits. In the latter case TBPC will still be represented in the MRC. Where the threat of pollution to the shoreline exceeds the capability of the most affected local authority they may request the assistance of the MCA. It will be for the local authority most concerned by the incident to designate whom, if not the Chief Executive, should act as the head of the SRC. The MCA s Chief Scientist will advise the SRC MARINE MANAGEMENT ORGANISATION (MMO) The MMO plays a major role in the protection of the marine environment, including fisheries resources, and in ensuring the safety of the aquatic food chain, including the safety of consumers of fish and shellfish. MMO is also the marine licencing authority and is responsible for approving deposits in the sea. Under the terms of the Marine Licensing (Exempted Activities) Order 2011 and the Marine and Coastal Access Act 2009, it is a legal requirement that oil treatment products may only be used in English waters if they have been formally approved for this purpose by MMO. In addition, specific permission from MMO must be obtained before any such products are used in shallow waters these are defined as any area of the sea which is less than 20 metres deep, or within one nautical mile of such an area. This includes any use in tidal docks, locks and on beaches, shorelines or structures such Issue 5 31/03/15 Page 97 of 102

99 as piers and breakwaters. The dispersant must be used in accordance with any conditions to which the approval was subject.themmo aims to approve or refuse oil spill treatment product use within 1 hour of being asked to authorise dispersant use. MMO can also give advice on the type of product most suitable for dealing with a particular incident. The MMO aims to ensure that damage caused by the oil or oil spill treatment product is minimised and consults on the implications for fisheries and marine fauna and flora with a variety of organisations including Cefas, Natural England and the Food Safety Agency. MMO coastal offices are also representatives of the Bristol Channel Standing Environment Group NATURAL ENGLAND Natural England is the body responsible for advising Government on nature conservation in England. Natural England s purpose as outlined in the Natural Environment and Rural Communities (NERC) Act is to ensure that the natural environment is conserved, enhanced and managed for the benefit of present and future generations, thereby contributing to sustainable development. At the time of an oil pollution incident, Natural England is responsible for providing advice on how best to respond in the interests of natural environment and threatened wildlife and habitats. Natural England is a member of the Bristol Channel Environment Group THE ENVIRONMENT AGENCY The Environment Agency is a non-departmental public body with statutory duties and powers in relation to water resources, pollution control, flood defence, fisheries, recreation, conservation and navigation in England. The Environment Agency is responsible for the control of pollution and water quality in all controlled waters; which include groundwater, fresh water, estuaries and relevant territorial waters (these extend 3 miles seaward from specific baselines).the Environment Agency is also the competent authority for waste management licensing, including the enforcement of Hazardous Waste Regulations. In the event of an oil spill incident, the Environment Agency would advise on waste related matters as a result of clean-up operations. The Environment Agency is a member of the Bristol Channel Environment Group BRISTOL CHANNEL ENVIRONMENT GROUP This group provides a single advisory line on environmental and public health issues for marine pollution incidents in the Severn Estuary and Inner Bristol Channel. The composition of the group includes Natural England, Natural Resources Wales, the Environment Agency, Marine Management Organisation, Welsh Government (Fisheries), Devon and Severn Inshore Fisheries and Conservation Authority (IFCA) and the Health Protection Agency. The membership can be expanded to include representatives of other organisations, such as the RSPCA, RSPB, Wildlife Trusts and National Trust. The Bristol Channel Environment Group have developed an Activation Plan (2012) which provides a framework within which member organisations can function quickly and efficiently to provide advice to National Contingency Plan Response Units. The Activation Plan is invoked and the Environment Group set up for an incident at the request of the MCA, SOSREP or other National Contingency Plan Responder, such as a Local Authority or Harbour Authority with an approved oil spill plan. The group will automatically be activated in response to a Tier 3 incident and may be activated to a lesser extent to a Tier 1 or 2 incident. The group may be set up as a precautionary approach when there is the possibility of an incident escalating or as a virtual group providing advice to minor incidents. Issue 5 31/03/15 Page 98 of 102

100 The main function of the Group is to provide advice and guidance on all environmental and public health aspects of a pollution incident. This includes the assessment of environmental risks and potential impacts arising from an incident, as well as the implications of any clean up or salvage operations. The Environment Group s remit is advisory and it has no powers of direction or enforcement. Regulatory functions of individual members are exercised outside the Group. Issue 5 31/03/15 Page 99 of 102

101 14 - Anti-Pollution Resources 14.1 Tier 1 Resources Tier 1 Equipment is located at strategic locations in Avonmouth and Portbury Docks as shown below Oil Basin Berth Spill Kits The following equipment is held on each of the following Oil Basin berths, 1,3,5,6 and 7A. Item Description Qty Spill Container (Medium Size) 1 Bag of Absorbent Granules 1 Plastic Shovel 1 Absorbent Pads (48 x 48) 100 Large Absorbent Boom 4m 2 Small Absorbent Booms 6 Waste Disposal Bags 20 Warning Tape (Roll) 1 Warning Sign 1 Paper Oversuit 1 Gauntlets (Pairs) Bristol Aviation Fuel Terminal/Portbury Berth 7 Spill Kit The following equipment is held in the spill container situated at berth 7 platform Item Description Qty Absorbent Pads (48 x 48) 100 Large Absorbent Boom 4m 2 Small Absorbent Booms 6 Waste Disposal Bags 200 Paper Oversuit 1 Gauntlets (Pairs) 1 Issue 5 31/03/15 Page 100 of 102

102 Haven Masters Office Oil Pollution Storeroom Item Description Qty Absorbent Pads (48 x 48) 600 Absorbent Boom 4m 8 Small Absorbent Booms 10 Waste Disposal Bags 230 Dispersant (20 litres drums) 8 Portable Sprayer 2 Rolls of Twine 4 Rags (Bag) 3 Warning Sign 4 Paper Suits 12 Gauntlets 12 Paper Oversuit 10 Large Absorbent Booms 8 Paper Oversuit Oil Pollution Container (Located at Portbury Lock) Item Description Qty Absorbent Pads (48 x 48) 600 Large Absorbent Booms 8 Small Absorbent Booms? Waste Disposal Bags litres Dispersant 8 Issue 5 31/03/15 Page 101 of 102

103 Oil Booms Inner knuckle Portbury lock metrestroil Boom on reel. R Berth Avonmouth - 200metres Troil Boom on reel. Oil Pollution Container 50 metres Troil Boom (Portbury lock gate protection) Oil Pollution Storeroom 45 metres (Avonmouth lock gate protection) Additional Resources In addition to the above dedicated anti-pollution equipment, TBPC also have the following resources that may be utilised during an oil spill response incident: Item Description Qty Survey Boat Isambard Brunel 2 Pilot Boat Bristol Interceptor 1 Workboat with deck cranes 2 Line Handling Boats (Pill Hobbler Marine Services Ltd) 3 Tugs (Svitzer Marine Ltd) 5 Cranes / Forklifts Various 14.2 Tier 2 Resources Adler & Allan Ltd have been appointed as TBPC s Tier Two response contractor. Details of the resources held by Adler & Allan Ltd can be found in the current contract along with the current scale of fees (Internal Issue Only). The contracted maximum response time is 4 hours (within working hours) and 6 hours (outside working hours) Rendezvous Site for Assembly of Equipment In the event of any Tier 3 incident it would be difficult to formally identify the location for the assembly point of a national stockpile of equipment. It is the responsibility of TBPC and the respective callout authority to stipulate the appropriate laydown area for equipment during this event dependent upon spill location Manpower Availability Pill Hobbler Marine Services Ltd provides 1P Responders for TBPC. Additional 1P trained personnel are available from within TBPC s Marine Staff. Further manpower may be sourced from within TBPC Operations Department, this department has in the region of 150 personnel. Issue 5 31/03/15 Page 102 of 102

104 Annex 1 Tier 2 Contract

105

106

107 Annex 2 Figures

108 Newport <Double-click here to enter title> Severn Beach Avonmouth Docks Key The Bristol Port Company Portishead Royal Portbury Docks River Avon Inland limit of TBPC Severn Estuary Bristol City Docks Clevedon Ashton Swing Bridge Notes Notes Miles Boundaries shown are indicative The Harbour Area is defined in: - The Bristol Port and Harbour Revision Order The Bristol Port and Harbour Revision Order The Port of Bristol Harbour Revision Order 1993 Contains Ordnance Survey data Crown copyright and database right 2014 Steep Holm Weston-super-Mare Figure 1. Limits of the Port of Bristol (Statutory Harbour Authority Area) September 2014

109 Severn Estuary Avonmouth Docks Royal Portbury Docks River Avon Key Bristol Port Company Land Notes Boundaries shown are indicative Figure 2. The Bristol Port Company Land Contains Ordnance Survey data Crown copyright and database right 2014 September Miles

110 <Double-click here to enter title> Newport Severn Beach South Gloucestershire Council Key <all other values> Local Authorities: LAD12NM City of Bristol North Somerset Severn Estuary Clevedon North Somerset Council Avonmouth Docks Royal Bristol City Council Portbury Docks River Avon Notes Notes South Gloucestershire Boundaries shown are indicative Contains Ordnance Survey data Crown copyright and database right 2014 Weston-super-Mare Miles Steep Holm Figure 3. Adjacent Local Authorities September 2014

111 Newport <Double-click here to enter title> Gloucester Harbour Trustees Severn Beach Avonmouth Docks Key The Bristol Port Company Severn Estuary Portishead Docks Royal Portbury Docks River Avon Bristol City Docks Gloucester Harbour Trustees Bristol City Docks The Bristol Port Company Clevedon Notes Notes Boundaries shown are indicative Contains Ordnance Survey data Crown copyright and database right Miles Steep Holm Weston-super-Mare Figure 4. Adjacent Harbour Authorities September 2014

112 !!!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!(!( E A B F C D H J L M N A B C D X W V U R O S P Q T WW5 WW4 WW2 WW1 OB1 OB8 OB2 OB7 K WW3 OB6 OB3 Key Avonmouth Oil Boom Options 40m 40m 75m 125m 125m 150m Oil Basin Eastern Arm Swinging Basin Figure 5. Oil Boom Options in Avonmouth Docks September 2014 Notes Locations of oil booms shown are indicative Contains Ordnance Survey data Crown copyright and database right 2014 South Dock 75m Meters

113 !( m G 1!( E F m 20 A 400m m B D 6!( 2 3!(!( m 400m C 440m 5!( !( Key Portbury Oil Boom Options Notes Locations of oil booms shown are indicative Figure 6. Oil Boom Options in Royal Potrbury Docks Contains Ordnance Survey data Crown copyright and database right 2014 September 2014 Meters

114 Newport River Usk SAC <Double-click here to enter title> Severn Estuary SAC, SPA & Ramsar sites Severn Beach Severn Estuary SAC Portishead Royal Portbury Docks Avonmouth Docks River Avon Key The Bristol Port Company Harbour Area Special Area of Conservation (SAC) Special Protection Area (SPA) Ramsar Site Bristol City Docks Clevedon Notes Notes Boundaries shown are indicative Contains Ordnance Survey data Crown copyright and database right Miles Steep Holm Weston-super-Mare Figure 7. European and International Marine Nature Conservation Designations September 2014

115 Severn Estuary SAC <Double-click here to enter title> Severn Estuary SAC, SPA, Ramsar site & SSSI Key Severn Estuary SAC, SPA, Ramsar site & SSSI Royal Portbury Docks Avonmouth Docks Severn Estuary SAC, SPA, Ramsar site & SSSI River Avon Horseshoe Bend, Shirehampton SSSI Ham Green SSSI Notes Notes The Bristol Port Company Harbour Area Special Area of Conservation (SAC) Special Protection Area (SPA) Ramsar site National Nature Reserve Site of Special Scientific Interest (SSSI) Boundaries shown are indicative Contains Ordnance Survey data Crown copyright and database right 2014 Leigh Woods National Nature Reserve Avon Gorge Woodlands SAC & SSSI Bristol City Docks Miles Figure 8. Nature Conservation Designations near Bristol Port and River Avon September 2014 Ashton Court SSSI

116 Annex 3 Notices of consultation agreement

117 ed received Thu 12/02/ :20 Dear Chris, Thank you for consulting the Severn Estuary Partnership on the draft contingency plan in November The Partnership provide secretariat services for the Bristol Channel Standing Environment Group (BCSEG) and on its behalf, we are pleased to confirm that BCSEG formally agree with the Plan content in its current form. Kind regards, Lucy Taylor Lucy Taylor Severn Estuary Partnership c/o School of Earth and Ocean Sciences Main Building. Cardiff University. Park Place. CARDIFF CF10 3AT. Tel: +44(0) Fax: +44(0) Website: Facebook: Severn Estuary Partnership

118 received Mon 16/02/ :25 Hi Chris, Happy to agree the final document, Many thanks, Libby Libby Ross Senior Environment Officer Devon and Severn Inshore Fisheries and Conservation Authority phone: website:

119 received Thu 26/02/ :39 Hi Chris. Further to our phone call. I confirm that there are no further consultation comments that I can add to the Oil Spill Contingency Plan. I note that the comment on burning/incineration of waste is taken from a higher level plan and that, in the event, there is always the option for the Environment Agency to advise on best practice. I hope these comments are sufficient response. Regards, Steve George. Steve George. Environment Officer, Bristol Avon Land & Water

120 received on Tue 17/02/ :27 Dear Chris, Thank you for providing the opportunity to review the final version of the Bristol Port Company Oil Spill Contingency Plan. I am pleased to advise that the Trustees agree with the contents of the plan. Kind regards Mike -- Mike Johnson Marine Officer/Harbourmaster Gloucester Harbour Trustees

121 received on Mon 16/02/ :34 Hi Chris, I have reviewed the plan and can confirm we are happy with the content. I can now renew the standing approval. Currently it is made out to James Clark, Assistant Haven Master. Is this still the correct person or would your name be more appropriate? Kind regards Katherine Morton, Katherine (MMO) <Katherine.Morton@marinemanagement.org.uk>

122 received on Thu 19/02/ :29 Chris, I have now had the opportunity to review the contingency plan. Apologies for the delay in our response. We consider the plan good and comprehensive. There are a few outstanding points that we do not feel were addressed following our initial review, however, these are not significant enough to insist upon. We are happy to give our approval to the final document. Kind regards, Lizy Lizy Gardner Marine Adviser (Severn Estuary EMS) Avon Wiltshire Somerset Team Natural England Floor 1, Temple Quay House, 2 The Square Bristol, BS1 6EB...><((((º> `. Landline no Mobile no Ways you can help us improve our service

123 received on Wed 18/02/ :27 Chris, Apologies, we are happy with the plan. Kind regards, Ian Ian M Wilson Emergency Manager North Somerset Council Tel: Fax: Post : Emergency Management Unit, North Somerset Council, Floor 2, Castlewood, Tickenham Road, Clevedon, BS21 6FW Web: < Community Resilience North Somerset: a community's capacity to cope with an emergency

124 Annex 4 MSDS Sheets

125 MATERIAL SAFETY DATA SHEET UNLEADED PETROL Reference 6 REVISION 1 Page 1 of 5 1. IDENTIFICATION OF SUBSTANCE OR PREPARATION PRODUCT ULTRA LOW SULPHUR PETROL/LOW SULPHUR LEAD REPLACEMENT PETROL/LOW SULPHUR SUPER UNLEADED APPLICATION Motor Vehicle Fuel COMPANY Thomas Silvey Limited Roundway House Newfoundland Road Bristol BS2 9LU Telephone EMERGENCY TELEPHONE DAY: FAX: NIGHT: COMPOSITION / INFORMATION ON INGREDIENTS CHEMICAL DESCRIPTION HAZARDOUS COMPONENTS A complex combination of hydrocarbons consisting primarily of paraffins, napthlenes, aromatic and olefinic hydrocarbons having carbon numbers predominantly between C4 and C12. Name % CAS EINEC SYMBOL RISK PHRASES BENZENE 1.0 max T R45,R11,R48,R23,R24,R25 GASOLINE BULK V/V F+,T,Xi,Xn R12,R38,R45,R65,R67,R51,R53 3. HAZARDS IDENTIFICATION Extremely flammable. Explosive mixtures may form at ambient temperatures. May cause irritation in contact with eyes and skin. Harmful if swallowed. Aspiration into the lungs caused by vomiting is harmful and can be fatal. Contains benzene: prolonged or repeated exposure to benzene may cause anaemia and other blood diseases including leukemia. Classified as a category 2 carcinogen. Toxic to aquatic organisms, may cause long-term adverse effects in the aquatic environment. 4. FIRST AID MEASURES EYE CONTACT SKIN CONTACT INGESTION Immediately wash with fresh water for at least 15 minutes. Obtain medical advice if pain or redness develops. Remove contaminated clothing as soon as possible. Wash exposed skin thoroughly with soap and water. If irritation persists, seek medical attention. If this material is swallowed, DO NOT INDUCE VOMITING. If unconscious, place in recovery position and protect airway. Seek immediate medical attention. INHALATION If over exposure occurs, remove to fresh air. Administer artificial respiration if breathing stops. Seek immediate medical attention.

126 UNLEADED PETROL Reference 6 REVISION 1 Page 2 of 5 5. FIRE FIGHTING MEASURES EXTINGUISHING MEDIA FIRE AND EXPLOSION HAZARDS PROTECTIVE MEASURES Use carbon dioxide, dry powder or foam. DO NOT USE WATER JETS. For small fires sand or earth may also be used. Forms extremely flammable vapour air mixture. Do not enter confined spaces without proper protective equipment including respirator. Use waterfog or spray to cool containers exposed to fire. 6. ACCIDENTAL RELEASE MEASURES (SPILLAGE) PERSONAL PRECAUTIONS ENVIRONMENTAL PRECAUTIONS RECOVERY In the event of a major spillage, only trained personnel wearing self contained breathing apparatus. Any spillage or leak should be treated as a major fire/explosion hazard. Alert fire brigade. Eliminate all sources of ignition. If vehicles present, switch off engines. Contain spillage. Recovery of large spillages should be effected by specialist personnel. Soak up residual fluids using sand, sawdust, earth. 7. STORAGE AND HANDLING (IN NORMAL USE) STORAGE VENTILATION Gasoline storage is subject to legistrative controls. Storage tanks must be suitably designed and installed, in accordance with legislation. Storage must be remote from all sources of heat, ignition and open flame. The vapours in tank head spaces should be considered highly flammable at all times. Use spark proof tools. Ensure adequate ventilation. HANDLING DO NOT SMOKE, EAT OR DRINK WHILST HANDLING. Avoid breathing vapours and/or mist. Launder contaminated clothing before re-use. Do not siphon product by mouth 8. EXPOSURE CONTROLS/PERSONAL PROTECTION (NORMAL USE) OCCUPATIONAL EXPOSURE LIMITS Name 8Hr TWA 15 min Type Ref BENZENE MEL EH40/02 1 ppm GASOLINE the following limits are recommended 900 mg/m mg/m3 TLV ACGIH 300 ppm 500 ppm ENGINEERING MEASURES Ensure adequate ventilation. Avoid flames and excessive temperatures. PERSONAL PROTECTIVE EQUIPMENT RESPIRATORY HAND EYE Unlikely to be required in normal use. If exposed to vapours or mist use organic vapour mask. Impervious gloves of nitrile rubber or PVC. Use goggles if risk of eye contact. OTHER Coveralls.

127 UNLEADED PETROL Reference 6 REVISION 1 Page 3 of 5 9. PHYSICAL/CHEMICAL PROPERTIES APPEARANCE Clear liquid. Pale yellow. ODOUR Characteristic odour. BOILING POINT (or RANGE) C FLASH POINT < -40 C AUTO-IGNITION TEMP 380 C EXPLOSIVE LIMITS UPPER LIMIT 8% LOWER LIMIT 1% VAPOUR PRESSURE bars VAPOUR DENSITY 3 4 (air = 1) 15 C kg/m³ SOLUBILITY Negligible, < 0.1% 10. STABILITY AND REACTIVITY STABILITY CONDITIONS TO AVOID MATERIALS TO AVOID HAZARDOUS DECOMPOSITION PRODUCTS Stable at ambient temperatures. Burning can be easily started. Avoid exposure to heat and flame. Avoid strong oxidising materials. Incomplete combustion will generate carbon monoxide, carbon dioxide and other hazardous gases. Thermal decomposition products will vary with conditions. 11. TOXICOLOGICAL INFORMATION ACUTE EFFECTS EYES SKIN INGESTION INHALATION Exposure to mist or direct splashing may cause irritation. Will remove natural fats from the skin. Prolonged or repeated exposure may cause irritation or possibly dermatitis. Unlikely to occur in normal use. Spontaneous vomiting is common with consequent risk of aspiration resulting in a potentially fatal chemical pneumonitis. Exposure to high levels of vapour result in central nervous system and respiratory depression with subsequent loss of consciousness. Where ventilation is poor or temperatures high vapour production may be a hazard. Inhalation of oil mists may cause irritation to the upper respiratory tract. CHRONIC EFFECTS This product contains Benzene ( < 1%) which is classified as a carcinogen. Exposure to benzene may result in blood disorders such as anaemia and leukemia.

128 UNLEADED PETROL Reference 6 REVISION 1 Page 4 of ECOLOGICAL INFORMATION MOBILITY PERSISTENCE & DEGRADABILITY BIO-ACCUMULATION AQUATIC TOXICITY OTHER Spillages may penetrate the soil causing ground water contamination. Ground spillage in large quantities may be of concern as the high mobility of the product could cause it to enter soil sub-strata, long term ground and ground water contamination may result. This product is inherently biodegradable. Not determined. Toxic to aquatic organisms, may cause long-term adverse effects in the aquatic environment. Any films formed on water may effect oxygen transfer and damage organisms. The vapours emitted are V.O.C s and may contribute to the formation of low level ozone. 13. DISPOSAL Dispose of in accordance with local authority/national regulations relating to hazardous waste. Materials contaminated with product should be treated as highly flammable. 14. TRANSPORT INFORMATION (REGULATIONS) PACKAGING (Size & Description) TRANSPORT CLASSIFICATION FLAMMABLE LIQUID UN NUMBER 1203 PROPER SHIPPING NAME Petrol or Motor Spirit or Gasoline. ICAO/IATA/IMDG CLASS 3 SUBSIDIARY RISK -- PACKING GROUP II ADR CLASS 3 TRANSPORT HAZARD SYMBOL Black flame on red. HAZARD IDENT. NUMBER 33 EMERGENCY ACTION CODE 3YE OTHER

129 UNLEADED PETROL Reference 6 REVISION 1 Page 5 of REGULATORY INFORMATION (Supply & Labelling) SUPPLY CLASSIFICATION LABELLING SYMBOLS RISK PHRASES Extremely Flammable. Cat 2 Carcinogen.Harmful. Irritant. Dangerous for the environment. Black flame on orange square Black skull and crossbones on orange square. Dead tree & fish. R12 Extremely flammable. R38 Irritating to skin. R45 May cause cancer. R51/R53 Toxic to aquatic organisms, may cause long-term adverse effects in the aquatic environment. R65 Harmful: May cause lung damage if swallowed. R67 Vapours may cause drowsiness and dizziness. SAFETY PHRASES S23 Do not breathe vapour. S24 Avoid contact with skin. S16 Keep away from sources of ignition. S33 Take precautionary measures against static discharge. S2 Keep out of the reach of children. S29 Do not empty into drains. S43 In case of fire, use foam/dry powder/ CO2. Never use water jets. S61 Avoid release to the environment. Refer to special instructions/ safety data sheets. S62 If swallowed, do not induce vomiting seek medical advice immediately and show this container or label. 16. OTHER INFORMATION Fuel for spark ignition engines primarily, for automotive and commercial use but used in industrial and marine applications. DO NOT siphon by mouth. DO NOT use as fuel for aircraft. REVISION 2 ISSUE DATE: January 2003 The information given in this data sheet is presented as guidance only for the purpose of determining health, safety and environmental measures. No warranty or representation express or implied is made as to the accuracy of completeness of the data and information contained in this data sheet. It is the users responsibility to evaluate this product and its intended use and to ensure compliance with applicable laws and regulations.

130 MATERIAL SAFETY DATA SHEET MSDS: 941 Jet Fuel REVISION DATE: 2/26/2009 SECTION 1: PRODUCT AND COMPANY IDENTIFICATION PRODUCT NAME: SYNONYMS: Jet Fuel Jet Fuel, Kerosene, Jet A, Jet A-1, JP-8, Petroleum Distillate Fuel PRODUCT CODE: Jet A (212110) Jet A-1 (212212) Jet A-1 (50) (212211) JP-8 (212130) This Material Safety Data Sheet applies to the listed products and synonym descriptions for Hazard Communication purposes only. Technical specifications vary greatly depending on the product and are not reflected in this document. Consult specification sheets for technical information. This product contains ingredients that are considered to be hazardous as defined by the OSHA Hazard Communication Standard (29 CFR ). IMPORTANT: Read this MSDS before handling or disposing of this product. Pass this information on to employees, customers and product users. MANUFACTURER: U. S. OIL & REFINING CO. ADDRESS: 3001 Marshall Ave., Tacoma, WA EMERGENCY PHONE: (253) FAX PHONE: (253) CHEMTREC PHONE: (800) NATIONAL RESPONSE: (800) CHEMICAL FAMILY: PRODUCT USE: PREPARED BY: Hydrocarbon Jet Fuel is a complex blend of hydrocarbons derived from various refinery streams, This product is intended for us as a fuel or for use in an engineered process. Use in other applications may result in higher exposures and require additional controls, such as local exhaust ventilation and personal protective equipment. U.S. OIL & REFINING CO. CAS #: SECTION 2: COMPOSITION/INFORMATION ON INGREDIENTS NAME CAS NUMBER CONCENTRATION % Kerosene/Hydrocarbon mixture % Cyclohexane % 1,2,4 Trimethylbenzene % Benzene % Toluene % Xylene % Naphthalene % Ethylbenzene % PAGE 1 OF 12

131 SECTION 3: HAZARDS IDENTIFICATION Warning! Combustible! Mist or vapors can cause a flash fire. Liquid, mist or vapors can cause eye, skin and respiratory tract irritation. Ingestion of liquid and aspiration into the lungs can result in chemical pneumonia. PHYSICAL STATE: Color: Odor: Liquid Water white to light amber Faint petroleum odor ROUTES OF ENTRY: Dermal Contact. Eye Contact. Inhalation. Ingestion. POTENTIAL HEALTH EFFECTS EYES: SKIN: INGESTION: INHALATION: Eye irritation may result from contact with liquid, mists and/or vapors. In severe cases, permanent eye damage may occur. Contact with the skin may cause irritation. Skin irritation leading to dermatitis may occur upon prolonged or repeated contact. Symptoms include redness, itching and dermatitis. Repeated contact may cause harmful effects in other parts of the body. This material can irritate the mouth, throat, and/or stomach. Aspiration into the lungs may cause chemical pneumonia. Symptoms include burning sensation of the mouth, nausea and vomiting. In severe cases loss of consciousness may occur. Vapors or mists can irritate the nose, throat and/or lungs and can cause central nervous system depression. Symptoms include headache, nausea, fatigue and dizziness. In severe cases loss of consciousness or death may occur. MEDICAL CONDITIONS GENERALLY AGGRAVATED BY EXPOSURE: This product contains petroleum distillates similar to those shown to produce skin tumors on laboratory animals. Avoid prolonged or repeated skin contact. Caution is recommended for personnel with pre-existing central nervous system diseases. Personnel with pre-existing central nervous system diseas, skin disorders, or chronic respiratory diseases should avoid exposure to this product. OVER-EXPOSURE SIGNS/SYMPTOMS: Headache, nausea, vomiting, dizziness, central nervous system- respiratory depression, convulsions, loss of consciousness, coma or death. Eye or skin irritation. See toxicological information (section 11) PAGE 2 OF 12

132 SECTION 4: FIRST AID MEASURES EYES: SKIN: INGESTION: INHALATION: Flush eyes with plenty of water for a minimum of 15 minutes. Seek medical care if irritation persists. Flush skin with plenty of water for at least 15 minutes while removing contaminated clothing and shoes. Get medical attention if irritation or pain persists. Launder or dry-clean clothing prior to re-use. Discard contaminated leather goods. WARNING! DO NOT INDUCE VOMITING. If aspirated into the lungs, may cause chemical pneumonitis. Seek medical attention promptly. If inhaled, remove to fresh air. If breathing is difficult, give oxygen. If not breathing, give artificial respiration. Get immediate medical attention if breathing is difficult or stops. NOTES TO PHYSICIANS OR FIRST AID PROVIDERS: Ingestion/Inhalation of this product or subsequent vomiting may lead to aspiration, which may cause pneumonitis. PAGE 3 OF 12

133 SECTION 5: FIRE-FIGHTING MEASURES FLAMMABILITY OF THE PRODUCT: Combustible liquid FLAMMABLE LIMITS IN AIR, LOWER: Approx 0.7 (% BY VOLUME): UPPER: Approx 5.0 FLASH POINT: Closed Cup >38 C, (100 F) AUTOIGNITION TEMPERATURE: PRODUCTS OF COMBUSTION: Not determined Normal combustion forms water vapor and carbon dioxide. Incomplete burning can produce carbon monoxide and particulate matter. FIRE/EXPLOSION HAZARDS IN THE PRESENCE OF VARIOUS SUBSTANCES: FIRE-FIGHTING MEDIA AND INSTRUCTIONS: Combustible liquid. When heated above the flash point, this material will release vapors that can ignite when exposed to open flame, sparks and static discharge. Mists or sprays may be flammable at temperatures below the normal flash point. Keep away from heat and open flame. Combustible Liquid. Use dry chemical, foam or carbon dioxide to extinguish the fire. Consult foam manufacturer for appropriate media, application rates and water/foam ratio. If a leak or spill has not ignited, ventilate area and use water spray to disperse gas or vapor and to protect personnel attempting to stop a leak. Use water to flush spills away from sources of ignition. Do not flush down public sewers. Collect contaminated fire-fighting water separately. It must not enter the municipal sewage system. Dike area of fire to prevent runoff. Decontaminate emergency personnel and equipment with soap and water. Combustible liquid and vapor. Vapor may cause flash fire. Vapors may accumulate in low or confined areas or travel a considerable distance to a source of ignition and flashback. Runoff to sewer may create fire or explosion hazard. SPECIAL FIRE FIGHTING EQUIPMENT: UNUSUAL FIRE AND EXPLOSION HAZARDS: Fire-fighters should wear appropriate protective equipment and selfcontained breathing apparatus (SCBA) with a full face-piece operated in positive pressure mode. Cool tanks, containers and exposed structures with water. Moderately combustible. When heated above the flash point, this material will release flammable vapors which if exposed to a source of ignition can burn or be explosive in confined spaces. Mists or sprays may be flammable at temperatures below the normal flash point. Keep away from heat and open flame. PAGE 4 OF 12

134 SECTION 6: ACCIDENTAL RELEASE MEASURES PERSONAL PRECAUTIONS: Immediately contact emergency personnel. Eliminate all ignition sources. Keep unnecessary personnel away. Use suitable protective equipment (section 8). Do not touch or walk through spilled material. Tanks, vessels or other confined spaces which have contained product should be freed of vapors before entering. The container should be checked to ensure a safe atmosphere before entry. Empty containers may contain toxic, flammable/combustible or explosive residues or vapors. Do not cut, grind, drill, weld or reuse empty containers that contained this product. Do not transfer this product to another container unless the container receiving the product is labeled with proper DOT shipping name, hazard class and other information that describes the product and its hazards. ENVIRONMENTAL PRECAUTIONS: Avoid dispersal of spilled material and runoff and contact with soil, waterways, drains and sewers. If facility or operation has an "oil or hazardous substance contingency plan", activate its procedures. Stay upwind and away from spill. Wear appropriate protective equipment including respiratory protection as conditions warrant. Do not enter or stay in area unless monitoring indicates that it is safe to do so. Isolate hazard area and restrict entry to emergency crew. Review Fire Fighting Measures section before proceeding with clean up. Keep all sources of ignition (flames, smoking, flares, etc.) away from release. Contain spill in smallest possible area. Recover as much product as possible (e.g., by vacuuming). Stop leak if it can be done without risk. Use water spray to disperse vapors. Spilled material may be absorbed by an appropriate absorbent, and then handled in accordance with environmental regulations. Prevent spilled material from entering sewers, storm drains, other unauthorized treatment or drainage systems and natural waterways. Contact fire authorities and appropriate federal, state and local agencies. If spill of any amount is made into or upon navigable waters, the contiguous zone, or adjoining shorelines, contact the National Response Center at For highway or railway spills, contact Chemtrec at METHODS FOR CLEANING UP: If emergency personnel are unavailable, contain spilled material. For small spills, add absorbent (soil may be used in the absence of other suitable materials) and use a nonsparking or explosion-proof means to transfer material to a sealable, appropriate container for disposal. For large spills, dike spilled material or otherwise contain it to ensure runoff does not reach a waterway. Place spilled material in an appropriate container for disposal. Water spill: Eliminate sources of ignition and warn other ships in the area to stay clear. Notify the proper authorities. Confine with skimming equipment if available or set booms to recover the spill. PAGE 5 OF 12

135 SECTION 7: HANDLING AND STORAGE HANDLING Do not ingest. Do not get in eyes, on skin or on clothing. Keep container closed. Use only with adequate ventilation. Avoid breathing vapor or mist. Keep away from heat, sparks and flame. To avoid fire or explosion, dissipate static electricity during transfer by grounding and bonding containers and equipment before transferring material. Use explosion-proof electrical (ventilating, lighting and material handling) equipment. Wash thoroughly after handling. In case of fire, use water spray, foam, dry chemical or carbon dioxide as described in the Fire Fighting Measures section of the MSDS. Do not pressurize, cut, weld, braze, solder, drill on or near this container. "Empty" container contains residue (liquid and/or vapor) and may explode in heat of a fire. Use good personal hygiene practices. After handling this product, wash hands before eating, drinking or using toilet facilities. Keep out of reach of children. Failure to use caution may cause serious injury or illness. Do not use as a cleaning solvent or for other nonfuel uses. To prevent ingestion and exposure - Do not siphon by mouth to transfer product between containers. STORAGE: Store in a segregated and approved area. Keep container in a cool, wellventilated area. Keep container tightly closed and sealed until ready for use. Avoid all possible sources of ignition (spark or flame). For information regarding transferring material refer to OSHA Standard 29 CFR , Flammable and Combustible Liquids, National Fire Protection Association (NFPA) 77, Recommended Practice on Static Electricity, and/or the American Petroleum Institute (API) Recommended Practice 2003, Protection Against Ignitions Arising Out of Static, Lightning, and Stray Currents. PAGE 6 OF 12

136 SECTION 8: EXPOSURE CONTROLS/PERSONAL PROTECTION ENGINEERING CONTROLS: Provide exhaust ventilation or other engineering controls to keep the airborne concentrations of vapors below their respective occupational exposure limits. Special ventilation may be required for handling conditions at elevated temperatures. Ensure that eyewash stations and safety showers are close to the workstation location. PERSONAL PROTECTION SKIN: RESPIRATORY: HANDS: Eye: Other: PROTECTIVE CLOTHING OR EQUIPMENT: Personal protective equipment for the body should be selected based on the task being performed and the risks involved and should be approved by a specialist before handling this product. Flame retardant clothing is recommended. In case of skin contact, wash with mild soap and water or a waterless hand cleaner. Immediately remove soiled clothing and wash thoroughly before reuse. Discard oil-soaked leather goods. Use a properly fitted, air-purifying or air-fed respirator complying with an approved standard if a risk assessment indicates this is necessary. Respirator selection must be based on known or anticipated exposure levels, the hazards of the product and the safe working limits of the selected respirator. Chemical-resistant, impervious gloves complying with an approved standard should be worn at all times when handling chemical products if a risk assessment indicates this is necessary. Eye protection (chemical-type goggles and/or face shield) should be worn whenever there is a likelihood of splashing or spraying liquid. Contact lenses should not be worn. Eye wash water should be provided. Use good personal hygiene practices. Gloves, Hardhat, Face Shield, Boots, Safety Glasses, Respirator, Fire Retardant Clothing PERSONAL PROTECTIVE EQUIPMENT IN CASE OF A LARGE SPILL: Splash goggles. Full suit. Vapor respirator. Boots. Gloves. Suggested protective clothing might not be adequate. Consult a specialist before handling this product. PAGE 7 OF 12

137 SECTION 8: EXPOSURE CONTROLS/PERSONAL PROTECTION (Continued) Established Occupational Exposure Limits SUBSTANCE VALUE TIME/TYPE SOURCE 500 ppm 8 Hour PEL OSHA Stoddard Solvent 60 ppm 8 Hour PEL NIOSH Cyclohexane 300 ppm 98 Hour PEL OSHA Benzene 1 ppm 5 ppm 8 Hour PEL STEL OSHA OSHA Toluene 50 ppm 8 Hour TWA ACGIH 100 ppm 8 Hour TWA OSHA Xylene 150 ppm STEL OSHA Napthalene 10 ppm 15 ppm 8 Hour TWA STEL Consult local authorities for acceptable exposure limits. OSHA NIOSH PAGE 8 OF 12

138 SECTION 9: PHYSICAL AND CHEMICAL PROPERTIES PHYSICAL STATE: COLOR: ODOR: BOILING POINT: FREEZING POINT: SPECIFIC GRAVITY: VISCOSITY: VAPOR PRESSURE: Liquid Water white to light amber Faint Petroleum Odor 160 to 300 C (320 to 572 F) -50 to -40 C to (Water = 1) (@ 60 F) F (D-445) 2.2 C (100F) VAPOR DENSITY: >1 (Air = 1) VOLATILITY: EVAPORATION RATE: MATERIALS TO AVOID: Not Determined Not Available Reacts with strong oxidizing material and strong acids HAZARDOUS DECOMPOSITION PRODUCTS: Burning or excessive heating may produce carbon monoxide and other harmful gases and vapors including oxides and/or other compounds of sulfur and nitrogen. SECTION 10: STABILITY AND REACTIVITY STABILITY AND REACTIVITY: INCOMPATIBILITY WITH VARIOUS SUBSTANCES: HAZARDOUS DECOMPOSITION PRODUCTS: HAZARDOUS POLYMERIZATION: CONDITIONS TO AVOID (STABILITY): The product is stable Reactive with strong oxidizing agents and strong acids None known Will not occur Heat, sparks and open flame. Strong oxidizers. Strong acids. PAGE 9 OF 12

139 SECTION 11: TOXICOLOGICAL INFORMATION TOXICITY DATA Jet Fuel/Straight-run Kerosene CAS CARCINOGENICITY: Application of petroleum hydrocarbons of similar composition and boiling range to mouse skin resulted in an increased incidence of skin tumors in some studies. Potential components which are listed by IARC as carcinogens or potential carcinogens are: benzene and ethylbenzene. Risk of cancer depends on duration and level of exposure. TARGET ORGANS: Potential components which have demonstrated developmental and or target organ issues are: benzne, toluene, xylenes, naphthalene and ethylbenzene. SECTION 12: ECOLOGICAL INFORMATION ECOLOGICAL INFORMATION: This product is potentially toxic to aquatic organisms and should be kept out of sewage and drainage systems and all bodies of water. SECTION 13: DISPOSAL CONSIDERATIONS WASTE DISPOSAL: The generation of waste should be avoided or minimized wherever possible. Avoid dispersal of spilled material and runoff and contact with soil, waterways, drains and sewers. Consult your local or regional authorities. This material, if discarded as produced, is not a RCRA listed hazardous waste. However, conditions of use which results in chemical, physical changes or contamination, may subject it to regulation as a hazardous waste. Transportation, treatment, storage and disposal of waste material must be conducted in accordance with federal, state and local regulations. SECTION 14: TRANSPORT INFORMATION REGULATORY INFORMATION UN NUMBER EMERGENCY RESPONSE GUIDEBOOK PROPER SHIPPING NAME CLASS PACKING GROUP DOT Classification UN1863 Guide 128 Fuel, Aviation, Turbine Engine 3 III Note: This material may be re-classified as a combustible liquid for domestic land transportation under 49 CFR (f) PAGE 10 OF 12

140 SECTION 15: REGULATORY INFORMATION U.S. FEDERAL REGULATIONS: EPA SARA Sections 302, 304 & 313 and CERCLA : This material contains the following chemicals subject to the reporting requirements of SARA 302, SARA 304, SARA 313, CERCLA and 40 CFR 372: Chemical Name CAS Number Material Concentration CERCLA/SARA Section 302 TPQ (lbs.) CERCLA/SARA Section 304 RQ (lbs.) BENZENE % 10 1,2,4 TRIMETHYLBENZENE % N/A NAPHTHALENE % 100 XYLENES % 100 Carcinogen Identification: This mixture may contain chemicals that have been identified as a carcinogen by NTP, IARC, or OSHA. Extremely Hazardous Substances for Emergency Response and Planning 40 CFR 355 & 40 CFR 370: None. EPA SARA 311/312 Title III Hazard Categories: Acute Health Hazard: YES Chronic Health Hazard: YES Fire Hazard: YES Pressure Hazard: NO Reactive Hazard: NO PAGE 11 OF 12

141 SECTION 16: OTHER INFORMATION HAZARDOUS MATERIAL INFORMATION SYSTEM (U.S.A.) HEALTH HMIS III FLAMMABILITY * 1 2 PHYSICAL HAZARD PERSONAL PROTECTION 0 NATIONAL FIRE PROTECTION ASSOCIATION (U.S.A.) Health * Chronic Health Hazard Flammability Reactivity Specific Hazard DISCLAIMER The information in this MSDS was obtained from sources which we believe are reliable. HOWEVER, THE INFORMATION IS PROVIDED WITHOUT ANY REPRESENTATION OR WARRANTY, EXPRESS OR IMPLIED, REGARDING ITS ACCURACY OR CORRECTNESS. The conditions or methods of handling, storage, use and disposal of the product are beyond our control and may be beyond our knowledge. FOR THIS AND OTHER REASONS, WE DO NOT ASSUME RESPONSIBILITY AND EXPRESSLY DISCLAIM LIABILITY FOR LOSS, DAMAGE OR EXPENSE ARISING OUT OF OR IN ANY WAY CONNECTED WITH THE HANDLING, STORAGE, USE OR DISPOSAL OF THE PRODUCT. PAGE 12 OF 12

142 MATERIAL SAFETY DATA SHEET 1. IDENTIFICATION OF THE SUBSTANCE / PREPARATION AND OF THE COMPANY PRODUCT NAME AUTO DIESEL / DERV SYNONYMS : G.O.R.V., Ultra-Low Sulphur Diesel, AD10 Sheet 1 of 6 Revision No : 10 Last Revision Date : January 2006 This is an uncontrolled copy NAME AND ADDRESS OF MANUFACTURER/SUPPLIER ConocoPhillips Ltd, Humber Refinery, South Killingholme, North Lincolnshire, DN40 3DW. Telephone No Facsimile No EMERGENCY CONTACT ConocoPhillips Ltd. Humber Refinery, South Killingholme, Immingham, North Lincolnshire DN40 3DW. Health and Safety Emergency Telephone No (24 hours) APPLICATION For use as a fuel in diesel engines only. Any other use implies a processing operation which may change its essential characteristics and liability for safety of the product will transfer to the processor. 2. COMPOSITION / INFORMATION ON INGREDIENTS Petroleum Hydrocarbons >99% Saturated olefinic and aromatic - C 10 to C 26 - may contain Polycyclic Aromatic Hydrocarbons - PAHs. CAS No EINECS No , R40. Additives 1. Middle distillate flow improvers (various) up to 1000ppm. (Dispersion of Ethylene vinyl acetate in an organic solvent). 2. Cetane improvers (Alkyl Nitrates) - up to 500ppm. CAS No , EINECS No May contain Dye and Chemical Marker - Gas Oil Marker Concentrate. CAS No Antistatic Additive 1-3 ppm 5. May contain a multifunctional detergent

143 Sheet 2 of 6 PRODUCT NAME Revision No : 10 AUTO DIESEL / DERV Last Revision Date : January 2006 This is an uncontrolled copy 3. HAZARDS IDENTIFICATION Health Hazards: This product contains amounts of Polycyclic Aromatic Hydrocarbons, some of which are known from experimental animal studies to be skin carcinogens. Prolonged and repeated exposure may therefore cause dermatitis and there is a risk of skin cancer. The risk of skin cancer will be very low, providing the handling precautions are such that prolonged and repeated skin contact is avoided and good personal hygiene is observed. Aspiration of liquid into the lungs directly or as a result of vomiting following ingestion of the liquid can cause severe lung damage and death. Safety Hazards: Product can accumulate static charges, which may be a possible ignition source (see Section 7). However product does contain an antistatic additive. Environmental Hazards: Dangerous for the environment. Toxic to aquatic organisms. May cause long-term adverse effects in the environment. 4. FIRST AID MEASURES Eyes : Skin : Inhalation : Ingestion : Pressure Injection : Rinse immediately with plenty of water until irritation subsides. If irritation persists, obtain medical attention. Immediate flush with large amounts of water, using soap if available. Remove contaminated clothing, including shoes, after flushing has begun. If irritation persists, get medical attention. In emergency situations use proper respiratory protection to immediately remove the affected victim from exposure. Administer artificial respiration if breathing has stopped. Keep at rest. Call for prompt medical attention. DO NOT INDUCE VOMITING, since it is important that no amount of the material should enter the lungs (aspiration). Keep at rest. Get prompt medical attention. ALWAYS OBTAIN IMMEDIATE MEDICAL ATTENTION EVEN THOUGH THE INJURY MAY APPEAR MINOR. 5. FIRE-FIGHTING MEASURES Extinguishing Media : Fire and Explosion Hazards : Special Fire-Fighting Procedures : Hazardous Combustion Products : Foam, dry chemical powder, carbon dioxide. Flammable liquid, moderate hazard. Liquid can release vapours that readily form flammable mixtures at or above the flash point. Static discharge; material can accumulate static charges which may cause an incendiary electrical discharge. However, this product does contain an antistatic additive. Water fog or spray to cool fire exposed surfaces (e.g. containers) and to protect personnel, should only be used by personnel trained in firefighting. Cut off "fuel"; depending on circumstances, either allow the fire to burn out under controlled conditions or use foam or dry chemical powder to extinguish the fire. Respiratory and eye protection required for fire-fighting personnel exposed to fumes or smoke. Smoke, sulphur oxides and carbon monoxide in the event of incomplete combustion.

144 Sheet 3 of 6 PRODUCT NAME Revision No : 10 AUTO DIESEL / DERV Last Revision Date : January 2006 This is an uncontrolled copy 6. ACCIDENTAL RELEASE MEASURES Personal Precautions : See Section 8. Environmental Precautions : Land Spill : Water Spill : Eliminate sources of ignition. Shut off source taking normal safety precautions. Prevent liquid from entering sewers, watercourses or low lying areas; advise the relevant authorities if it has, or if it contaminates soil/vegetation. Take measures to minimise the effects of groundwater. Eliminate the spill immediately with booms. Warn shipping. Notify port and other relevant authorities. Decontamination Procedures : Recover by skimming or pumping using explosion-proof equipment, or contain spilled liquid with booms, sand or other suitable absorbent and remove mechanically into containers. If necessary, dispose of absorbed residues as directed in Section HANDLING AND STORAGE Store product in cool, well ventilated surroundings, well away from sources of ignition. Provide suitable mechanical equipment for the safe handling of drums and heavy packages. Electrical equipment and fittings must comply with local regulations regarding fire prevention with this class of product. Load/unload temperature : Ambient to 40 o C Storage temperature : Ambient to 40 o C Special Precautions Use the correct grounding procedure. Store and handle in closed or properly vented containers. Ensure compliance with statutory requirements for storage and handling. Check for and prevent potential leaks from containers. 8. EXPOSURE CONTROLS / PERSONAL PROTECTION Workplace Substance 8-hour TWA STEL Source / Other Information Exposure Limit : Mineral Oil Mist 5 mgm mgm -3 HSE Guidance: not listed in EH 40) Personal Protection : In open systems where contact is likely, wear safety goggles (EN 166), chemical-resistant overalls, and chemically impervious gloves (EN 374). Where only incidental contact is likely, wear safety glasses with side shields. No other special precautions are necessary provided skin/eye contact is avoided. Where concentrations in air may exceed the OES approved respirators may be required (EN 405). Monitoring Methods: Health & Safety Executive (HSE), Methods for the determination of Hazardous Substances (MHDS); MDHS 84

145 Sheet 4 of 6 Revision No : 10 AUTO DIESEL / DERV Last Revision Date : January 2006 This is an uncontrolled copy 9. PHYSICAL AND CHEMICAL PROPERTIES Appearance : Clear straw Odour : Pungent petroleum coloured liquid Density at 15 o C : 0.82 g/ml ph : Not applicable Vapour Pressure at 20 o C : < 0.3 Kpa Vapour Density (air=1) : < air Boiling point, o C : o C Pour Point o C : -24 o C Flash Point (Closed Cup), o C : > 55 o C Auto-ignition Temperature, o C : 250 o C o C Flammability Limit, in Air, % by Volume : LEL : 0.5 UEL : 6.0 Kinematic Viscosity at 20 o C, mm 2 s -1 : 4.8 Kinematic Viscosity at 40 o C, mm 2 s -1 : 3.0 Solubility : Negligible PLEASE NOTE THAT THESE PROPERTIES DO NOT CONSTITUTE A SPECIFICATION. 10. STABILITY AND REACTIVITY Stability : Conditions to avoid : Materials to avoid : Hazardous Decomposition Products : The product is stable and not subject to polymerisation. Avoid exposure to extreme heat. Avoid contact with strong oxidising agents such as liquid chlorine. Product does not decompose at ambient temperature. 11. TOXICOLOGICAL INFORMATION The following toxicological assessment is based on a knowledge of the toxicity of the product's component's HEALTH EFFECTS On eyes : On skin : By inhalation : Slightly irritating but does not damage eye tissue. Low order of acute toxicity. Irritating. Prolonged or repeated contact may also lead to more serious skin disorders, including skin cancer. Certain components present in this material may be absorbed through the skin, possibly in toxic quantities. In high concentrations and/or at elevated temperatures, vapour or mist is irritating to mucous membranes, may cause headaches and dizziness, may be anaesthetic and may cause other central nervous system effects. Elevated temperatures or mechanical action may form vapours, mists or fumes, which may be irritating to the eyes, nose, throat and lungs. Avoid breathing vapours, mists or fumes.

146 Sheet 5 of 6 AUTO DIESEL / DERV Revision No : 10 Last Revision Date : January 2006 This is an uncontrolled copy 11. TOXICOLOGICAL INFORMATION CONTINUED... By ingestion : Chronic : Acute : Low order of acute/systemic toxicity. Minute amounts aspirated into the lungs during ingestion or vomiting may cause sever pulmonary injury and death. Contains Polycyclic Aromatic Hydrocarbons (PAH's). Prolonged and/or repeated skin contact with certain PAH's has been shown to cause skin cancer. Prolonged and/or repeated exposure by inhalation of certain PAH's may also cause cancer of the lung and of other sites of the body. Based upon animal test data from similar materials and products, the acute toxicity of this product is expected to be : ORAL LD50 > 5000 mg/kg DERMAL LD50 > 2000 mg/kg 12. ECOLOGICAL INFORMATION In the absence of specific environmental data for this product, this assessment is based on information developed with various other crude oils. Gas oils released into the environment will float on water and spread on the surface; on release to soils, gas oils show some mobility, but absorption is the predominant physical process. Ecotoxicity: Mobility: Dangerous for the environment. Toxic to most invertebrates and slightly toxic to fish. Some mobility in soils. Persistence and Degradability : Lighter components volatilise and in air undergo photolysis to give half-lives of less than a day. Photoxidation of liquid hydrocarbons on the water surface also contributes to the loss process. Slow to moderate degradation in water and soil. Bioaccumulation Potential: Potential to bioaccumulate, but metabolic processes may reduce this tendency. 13. DISPOSAL CONSIDERATIONS The product contains hazardous ingredients listed in Section 2. Collects and dispose of it at an authorised disposal facility, in conformance with national and local; regulations and in accordance with EEC Directives on hazardous waste. 14. TRANSPORT INFORMATION Classification for Transport : Shipping Name : Rails cars, tank trucks, tankers, barges, drum. Diesel Fuel UN Number : 1202 Packaging Group : III UN Class : 3 Marine Pollutant: See Section 6 ADR/RID : Class 3 ICAO/IATA : Class 3 Emergency Action Code: 3Y

147 Sheet 6 of 6 Revision No : 10 AUTO DIESEL / DERV Last Revision Date : January 2006 This is an uncontrolled copy 15. REGULATORY INFORMATION Hazard Label Data : Xn Harmful N Dangerous for the Environment R & S Phrases : R40 Limited evidence of carcinogenic effect. R51/53 Toxic to aquatic organisms, may cause long-term adverse effects in the aquatic environment S2 Keep our of reach of children S36/37 Wear suitable protective clothing and gloves S61 Avoid releases into the environment, see Section 6 EC Directives : EC Directive 91 / 155 / EEC Waste Oil Directive 87 / 101/ EEC Statutory Information : The Health and Safety at Work Act OTHER INFORMATION Consumer Protection Act 1987 Environmental Protection Act 1990 Control of Substances Hazardous to Health Regulations 2002 (as amended) Chemicals (Hazard Information and Packaging) Regulations 2002 Dangerous Substances and Explosive Atmospheres Regulations 2002 The data and advice given apply when the product is sold for the stated application or applications. The product is not sold as suitable for any other application. Use of the product for applications other than as stated in this sheet may give rise to risks not mentioned in this Sheet. You should not use the product other than for the stated application or applications. If you have purchased the product for supply to a third party for use at work, it is your duty to take all necessary steps to ensure that any person handling or using the product is provided with the information in this sheet. If you are an employer, it is your duty to tell your employees and others or may be affected of any hazards described in this sheet and of any precautions that should be taken. This data sheet has been revised in sections 1, 8

148 Annex 5 MMO Standing Approval

149 Mr Chris Jones Deputy Haven Master Bristol Port Company Marine Department Avonmouth Docks Bristol BS11 9AT Date 16 February 2015 Marine Conservation and Enforcement Team Lancaster House Hampshire Court Newcastle upon Tyne NE4 7YH T +44 (0) F +44 (0) Dear Mr Jones, ARTICLE 15 OF THE MARINE LICENSING (EXEMPTED ACTIVITIES) ORDER 2011 STANDING APPROVAL FOR USE OF DISPERSANTS AND LOOSE FIBRE ON OIL SPILLS OCCURRING IN THE SEA WATERS WITHIN THE ADMINISTRATION OF THE BRISTOL PORT COMPANY On behalf of the Marine Management Organisation (MMO) I am writing to confirm that the MMO has agreed TO APPROVE the use by: The Bristol Port Company In its response to an oil spill in: AREA 1: the Impounded waters of Avonmouth, Royal Edward and Royal Portbury Docks within the control of the Bristol Port Company (Area 1 of the relevant waters ) Of a maximum quantity of: 200 gallons of approved oil dispersant and any quantity of loose absorbent fibre and the MMO has agreed to approve the use by: The Bristol Port Company In its response to an oil spill in: AREA 2: the estuarial waters of the River Avon between a line running from the East Pier at the entrance of the River Avon to the first and second piers on the western band and a line straight across the river from the southern wall of the Cumberland Basin

150 Entrance Lock within the control of Bristol Port Company (Area 2 of the relevant waters ) of a maximum quality of: 200 gallons of approved oil dispersant a) without prior notification to MMO; and b) without approval from MMO in accordance with the procedures outlined in the Bristol Port Company Oil Spill contingency Plan 2009 ( the Plan ). This Standing Approval shall be subject to the terms and conditions outlined in the attached schedule. A failure to comply with these terms and conditions will constitute an offence under the Marine and Coastal Access Act 2009, on which basis a prosecution may be brought. It shall have effect from 16 February 2015 and shall remain in force for a period of 5 years. It shall replace the standing approval sent to Bristol Port Company 28 October Yours sincerely, Katherine Morton Marine Conservation Officer

151 SCHEDULE OF TERMS AND CONDITIONS Application of the Standing Approval to the relevant waters The deposit of approved dispersants is permitted only within relevant waters. The deposit of oil treatment products other than dispersants is not covered by this Standing Approval. Any use of dispersants (approved or otherwise) outside the relevant waters is not covered by this standing approval. Such use is permitted only where prior agreement is obtained from MMO that chemical treatment of oil outside the relevant waters is appropriate. Treatments operations excluded from the scope of this Standing Approval 1. Dispersants (approved or otherwise) must not be used to treat spills of diesel, gas oil, or other light oil types which normally disperse readily by evaporation. 2. Dispersants (approved or otherwise) must not be used to treat spills of heavy oils which have a viscosity beyond the maximum specified by the manufacturers of the dispersants. 3. Dispersants (approved or otherwise) must not be used to treat oil on any saltmarsh or mudflat areas within the relevant waters. Advice on handerling oil spill impact in such habitats should be sought from Natural England in the first instance.

152 MMO approval must be obtained before any dispersants are applied to any such oil type or in any such sensitive areas. Further conditions under which this standing Approval is granted 1. When it is proposed to respond to an oil spill by using dispersants, a telephone call must be made to inform MMO as soon as possible (regardless of hour of day) of either the nature of the spill and the intended treatment or that the a fax or containing such information has been sent. 2. A report (as described in Annex F of the MMO`s Marine Pollution Contingency Plan) must be made in writing to MMO HQ on any use of dispersant by the Port of Workington within 72 hours of the discovery of the oil spill. 3. Only products approved by the MMO at time of manufacture may be used under the terms of this Standing Approval. Furthermore, any deposits which were manufactured more than 5 years previous to use, must have been retested for efficacy as specified in paragraph I.21 of Appendix I of the Maritime and Coastguard Agency booklet Contingency planning for Marine Pollution Preparedness and Response: Guidelines for Ports. 4. MMO may withdraw this Standing Approval without redress at any time, but will provide an explanation for such action. 5. Port of Workington must take full responsibility for the actions of others who are delegated by it to undertake oil treatment within the terms of this Standing Approval. Exemptions 1. The use of oil treatment products outside the terms of this standing approval is not normally allowed without specific agreement from MMO. However, under exceptional `force majeure` circumstances, where there is, for example, an immediate threat to human health or the safety of a vessel or wharf, such products may be used without obtaining MMO`s agreement in advance. In any such case, details of the incident should be notified to MMO as soon as possible. 2. Formal MMO agreement is required for any use of oil treatment products, including dispersants, in an area of sea of a depth of less than 20 meters, or within one mile of such an area or under the surface of the sea anywhere in English and Welsh waters where not covered by this standing approval. MMO`s agreement is not formally required for use of such products to treat oil on the surface of the sea more than one nautical mile from the 20 meter contour as long as the products were approved by MMO at time of manufacture, and have been retested for efficacy if required by the terms of paragraph I.21 of Appendix I of the Maritime and Coastguard Agency booklet Contingency planning for Marine Pollution Preparedness and Response: Guidelines for Ports. However, MMO and Natural England would nonetheless wish to be consulted about any proposed use of products in such deeper waters so that fisheries and environmental sensitivities can be fully taken into account.

153 3. Article 15 of the Marine Licensing (Exempted Activities) Order 2009 only requires MMO approval for the use of substances to treat oil on the surface of the sea. This means that approval is not needed for the use of equipment to control, contain or recover oil. You do not need to approach us before using items of equipment like recoverable absorbent booms and absorbent cushions. However, items like chemicals or loose absorbent granules which would be classified as substances rather than equipment are covered by the Order and their use does therefore require MMO specific approval where not approved by this Standing Approval.

154 Annex 6 MCA STOp Notice 4/2001

155 SCIENTIFIC, TECHNICAL AND OPERATIONAL ADVICE NOTE - STOp 4/2001 IMPORTANT This STOp notice replaces STOp 2/98, please destroy your copy of STOp 2/98 ADVICE TO LOCAL AUTHORITIES ON THE COLLECTION AND HANDLING OF OIL SAMPLES 1. Background 2. Sampling From The Sea And Shoreline 3. Size Of Samples 4. Methods Of Collecting Samples 5. Bottling, Sealing, Packaging And Boxing Of Samples 6. Labelling And Addressing Of Samples 7. Transportation Of Samples 8. Handling Of Samples For Bonn Agreement States Note: This document should be read in conjunction with: STOp 1/ The Environment Group and Maritime pollution response in the UK. STOp 2/ The Establishment, Management Structure, Roles and Responsibilities of a Shoreline Response Centre during a Maritime Pollution Incident in the United Kingdom. The National Contingency Plan for Marine Pollution from Shipping and Offshore Installations (NCP). All extant MCA STOp notices may be found on the MCA web site: and all enquires regarding this and other MCA STOp notices should be directed to meor_meor@mcga.gov.uk STOP 4_01.doc 1 December 2001

156 1. BACKGROUND Where an oil pollution incident is thought to have arisen from an illegal operational discharge an effort should be made to collect a sample of the pollutant and, if possible, matching samples from the suspect ship or other source for analysis, comparison, and possible subsequent use in legal proceedings. Samples of the pollutant may need to be taken from the sea or coastline. When beach pollution has occurred, local authorities or HM Coastguard would usually take the necessary samples. For advice on sampling at sea, contact the Counter Pollution Branch of the Maritime and Coastguard Agency (MCA) on This notice sets out the procedures to be followed when collecting and handling oil samples. The MCA s Enforcement Unit will collect evidence concerning pollution incidents from shipping at sea, upon which a decision will be made as to prosecute or not. In England, Wales and Northern Ireland the MCA will conduct prosecutions. In Scotland the case will be presented to the Procurator Fiscal for action. If samples are likely to be used in connection with legal proceedings then the following procedures should be implemented: In England and Wales Although a single sealed sample of each type of pollutant is required by law, MCA would prefer three samples to be collected. In Scotland There is no longer a legal requirement for three sealed samples of each type of pollutant in Scotland but as in England MCA recommend three samples: one for analysis, a second to be handed to the owner or master of the suspect vessel for retention and any appropriate action, and the third for production in court, where the prosecution will be handled by the local Procurator Fiscal. In Northern Ireland Although the law in Northern Ireland concerning this matter is the same as that in England and Wales, the Director of Public Prosecutions, who is responsible for handling prosecutions in Northern Ireland has asked that for the sake of safety, three sealed samples of each type of pollutant should be provided on the same basis as in Scotland. Responsibility for the collection of oil samples in Northern Ireland rests with Environment and Heritage Service, Department of the Environment (Northern Ireland). Samples will usually be requested by a scientist/mariner in the MCA s Counter Pollution Branch or one of the Principal Counter Pollution and Salvage Officers as part of the response to a reported incident. Once a sample has been taken, agreement must be obtained from the Counter Pollution Branch before it is analysed Please remember that analysis of samples will only be carried out and paid for by the MCA if authorised by the Counter Pollution Branch. Please note that organisations such as Ports and Harbours or the Environmental Regulator may be taking independent samples as part of their own individual responsibilities for oil spill response and pollution regulation. The analysis of the samples and the cost of analysis of such samples will be the responsibility of the organisation taking the sample and not the MCA. 2. SAMPLING FROM THE SEA & SHORELINE When a large oil slick exists at sea or on a coastline, the number of samples that MCA may require is: offshore spill - minimum of 1 sample / slick / day where possible, STOP 4_01.doc 2 December 2001

157 onshore spill - representative samples from the shoreline, following discussion with Counter Pollution Branch. Following an incident, attempts may be made to infer that not all the oil pollution came from one vessel, and that some of it may have come from other sources. Where therefore an oiled beach is being sampled, a careful and detailed examination of the beach should be made to determine the uniformity of the oil deposit and the extent to which it is polluted by more than one type of oil. In particular, if there are any tarry, semisolid lumps or wet tarry patches, their presence should be recorded and some idea of their quantity and extent obtained. In addition, samples of such pollution should be retained and an attempt should be made to estimate costs expended on the clean up of different oils. In cases where samples have been taken at intervals along the beach, these should be clearly identified (see section 6 on labelling) as sequential samples of what might be an oil slick. Material is thus available for examination at a later stage, and the analytical laboratory does not get overburdened with an unnecessary number of analysis reports of the same material. It is desirable that samples of oil are taken in the area where the oil is first washed ashore. This is necessary as the fresher the oil the easier it is to identify by laboratory techniques. 3. SIZE OF SAMPLES Modern analytical methods mean that very little original pollutant material is required to carry out most chemical analyses. However, a larger sample is likely to be more representative. Detailed analyses are often hampered by either contamination or the loss of the oil s lighter fractions. A larger undisturbed sample may consist of a weathered oil crust covering a less weathered (holding a greater percentage of lighter fractions) and therefore more valuable core. The recommended minimum quantities required for a detailed programme of analyses are: Unweathered oils that are liquid and substantially free of water Oil exposed to seas surface and forming water-in-oil emulsion chocolate mousse Overside water discharge where contravention of 100ppm or 15ppm is suspected Tarry lumps as found on beaches 10ml 10ml 1 litre of the discharge 10 grammes A sample should not be withheld because the recommended quantity cannot be obtained, since much smaller samples can give useful results. In cases of pollution within UK territorial waters, when it is only necessary to prove that some oil has been discharged, a relatively small sample may be acceptable. Larger samples may be useful to carry out a range of tests to determine the most appropriate response/clean-up strategy. MCA can advise when and why such an approach is desirable 4. METHODS OF COLLECTING SAMPLES When liquid samples are skimmed off the surface of the sea, care should be taken to ensure that the sample contains sufficient oil. Various techniques may be adopted to skim thin layers of oil from the waters surface such as using a bucket with a hole. Care should be taken to minimise contamination of liquid samples by solid matter. Oil deposited on rocks or other impervious materials should be scraped off and placed directly into the sample container. Lumps of tarry or waxy pollutant should be placed directly into sample containers; no attempt should be made to heat or melt these samples to enable them to flow into a container. STOP 4_01.doc 3 December 2001

158 Oil adhering to seaweed, small pieces of wood, sand, plastic, material, cloth, vegetation or other debris should be dealt with by placing the complete specimen comprising oil and support material into the sample container. 5. BOTTLING, SEALING, PACKAGING AND BOXING OF SAMPLES All samples should be securely packed and sealed, using screwtopped containers and UN approved fibreboard boxes to ensure safe carriage of the sample. These have been supplied to HM Coastguard Stations and MCA Marine Offices for use by MCA Staff. In consultation with CPB, MCA sampling bottles may be made available to local authorities. As proof against unauthorised opening, the sample container should be sealed with wire and a lead or sealing wax seal. Alternatively, adhesive labels with a signature on the paper stuck on the bottle top in such a way that they have to be broken to open the bottle are acceptable. The bottle should then be placed inside a plastic bag, which should be sealed with a further adhesive label in the same way as for the sample bottle to ensure that it is not tampered with. If it is necessary to take an oil sample where one of the standard containers above is not available the receptacle should be of glass with a screw-cover and a seal which would not be affected by the oil. Small (100ml) and medium (500ml) glass bottles are readily obtainable from chemists or hardware shops. The use of closed metal receptacles or plastic jars is strongly discouraged as contact with metal or plastic can, in some cases, interfere with the analysis. Avoid the use of any metal tool made of nickel or vanadium based alloys, as these metals occur naturally in crude oils and refined products and their levels may assist in the identification of the oil source. When boxing the sealed samples for transport, the Peters and May (Dangerous Goods) Ltd. Packing instructions should be followed, to ensure the integrity of the package for transport under Dangerous Goods conditions. Vermiculite should be used to surround the sample(s) in the box for added protection and to absorb any possible seepage. Make sure that the dangerous goods documentation is completed. Whenever possible, samples should be stored in refrigerators or cold rooms at less than 5 degrees C in the dark. These precautions are particularly important for samples containing water or sediment, but less so for bulk oil samples. When ordering sample bottles it is important to consider the following: 1. Wide necked bottles make sampling easier. 2. Sample security can be achieved with locking cap seal. 3. Ensure that no components of the bottle can interfere with analysis, e.g. waxed cap inserts. 6. LABELLING AND ADDRESSING OF SAMPLES Care should be taken to ensure that every sample bottle is not only suitably sealed but also clearly labelled before being submitted to the MCA contractor s laboratory. It is important that a sample is positively identified, particularly where more than one is taken during an incident. It is of vital importance to maintain continuity in the chain of evidence, MCA recommend that each sample is labelled and is accompanied by more detailed information set out on a standard proforma. The form accompanying each container should therefore provide the following details: - a. An identifying number: year 2 digits month 2 digits day 2 digits and the initials of the official in charge of taking the samples. For example 02/04/17/JS = Sample taken on 17 th April 2002 by John Smith STOP 4_01.doc 4 December 2001

159 b. Description of samples. c. Position from which sample was taken, grid reference if possible. d. Date and time of sampling. e. Purpose for which sample was taken. f. If known, suspected source, e.g. name of tanker or ship. g. Whether or not dispersants have been used and, if known, their type and make. h. Method of sampling (description of sampling device). h. Name, address and telephone no. of person taking the samples and of anyone witnessing the taking of it. If possible the following information would also be helpful: j. Wind direction and velocity. k. Air and water temperature. l. Sample descriptions, i.e. viscosity, colour and contaminants. m. Description of the oil spill, i.e. distribution and consistency. An example of the recommended form and label are appended to this notice. To assist with any subsequent investigations it is important that a letter is sent to MCA quite independently of the sample (but a copy should be sent with the samples), setting out details a. to m. 7. TRANSPORTATION OF SAMPLES If a sample needs to be analysed the Counter Pollution Branch will contact their analysis contractor to arrange for the sample to be collected by courier and analysed. Please ensure that the samples in question are labelled correctly and securely packed in UN approved boxes to avoid breakage. It is important that the standard proforma described in section 6 should also be included with the sample along with all carriage documentation. To facilitate sample transportation, clear information on the number of samples to be collected, the location they need to be collected from and a contact name and phone number need to be given to the Counter Pollution Branch. 8. HANDLING OF SAMPLES FOR BONN AGREEMENT STATES In cases where samples are taken at the request of a contracting member of the Agreement for Co-operation in Dealing with Pollution of the North Sea by Oil, the BONN Agreement, the Counter Pollution Branch would be the focal point for processing the samples for either analysis or onward transmission to the requesting member state. The results of such tests would not be made public until the contracting party involved was informed. STOP 4_01.doc 5 December 2001

160 OIL POLLUTION SAMPLE STANDARD LABEL ID No. Date/Time Location) Name and Address of (Grid Ref) person taking sample OIL POLLUTION SAMPLE - STANDARD LABEL ID No. Date/Time Location) Name and Address of (Grid Ref) person taking sample... For continuity of evidence: Please complete clearly Sample passed to: Date Name Address Signature... For continuity of evidence: Please complete clearly Sample passed to: Date Name Address Signature OIL POLLUTION SAMPLE STANDARD LABEL ID No. Date/Time Location) Name and Address of (Grid Ref) person taking sample OIL POLLUTION SAMPLE - STANDARD LABEL ID No. Date/Time Location) Name and Address of (Grid Ref) person taking sample... For continuity of evidence: Please complete clearly Sample passed to: Date Name Address Signature... For continuity of evidence: Please complete clearly Sample passed to: Date Name Address Signature STOP 4_01.doc 6 December 2001

161 Collection of oil samples - This form to be completed by person taking sample If in doubt please refer to MCA STOp Notice on sampling. Remember to complete sample jar label and sign A ID Number - YY/MM/DD - with initials of person taking sample B Sample description C Location of sample OS Grid Ref or Lat/Long if possible D Date and time of sample collection E Purpose for which sample was taken F If known, suspected source G Were dispersants used? H Method of sampling (device?) I Name, address, address & Tel No of person taking sample and any witnesses J Wind speed and direction K Air and Sea Temperature L M Sample description, viscosity, colour, any contaminants? Description of the oil spill, distribution and consistency If possible the following information would also be helpful Original form to be kept with sample - please send copy of the form to the Counter Pollution Branch of the MCA - Bay 1/11, Spring Place, 105 Commercial Road, Southampton, SO15 1EG Tel: STOP 4_01.doc 7 December 2001

162 Annex 7 Letter of Approval from MCA

163

164 Annex 8 Notification Form (Tier Two Contractor)

165