UNITED STATES GOVERNMENT MEMORANDUM

To: Public Information (MS 5030)

Plans Section, Office of Field Operations (MS 5231)

Public Information copy of Exploration Plan

Control # - N-09789

Type - Initial Exploration Plan

Lease(s) - OCS-G34467 Block - 943 Mississippi Canyon Area

Operator - Shell Offshore Inc.

Drill and suspend Wells A, B, C, and D

Not Found

Attached is a copy of the subject plan for public comments on issues that

should be addressed in an Environmental Assessment.

It has been deemed submitted as of this date and is under review for approval.

Ulunma Nwokeafor

Plan Coordinator Description -

Rig Type - Subject: From: April 28, 2014Shell Offshore Inc

. P. O. Box 61933
New Orleans, LA 70161

- 1933

United States of America

Tel +1 504 425 7215

Fax +1 504 425 6747 Email sylvia.bellone@shell.com

March 18, 2014 Public Information Copy

Ms. Michelle Uli, Plans Supervisor Bureau of Ocean Energy Management

1201 Elmwood Park Boulevard New Orleans, LA 70123-2394

Attn: Plans Group GMG 290103

SUBJECT: Initial Exploration Plan

– Mississippi Canyon Block 9 43

OCS- G 34467, Offshore Louisiana

Dear Ms. Uli:

In compliance with 30 CFR 550.211 and NTLs 2008-G04

, 2009-G27 and 2010-N06, giving Exploration Plan guidelines, Shell Offshore Inc. (Shell) requests your approval of this Initial Exploration Plan requesting approval to drill four wells in Mississippi Canyon Block 943. Target date to commence drilling

is July 2014.

This plan consists of a series of attachments describing our intended operations. The attachments we

desire to be exe mpted from disclosure under the Freedom of Information Act are marked “Proprietary”

and excluded from the Public Information c op y of this submittal. The cost recovery receipt is attached to the Proprietary copy of the plan.

We are providing the following report in support of this plan: Geologic, Stratigraphic and Archeological Assessment of Blocks 942 (OCS-G 24130) and 943 (OCS-G 34467) and Portions of Surrounding Blocks, Mississippi Canyon Area, Gulf of Mexico prepared by GEMS, Project No. 0513-2243a,b dated February 11, 2014

.

Should you require additional information, please contact Tracy Albert at 504.425.4652 or tracy.albert@shell.com

.

Sincerely,

Sylvia A. Bellone

## SHELL OFFSHORE INC.

INITIAL EXPLORATION PLAN

for



### MISSISSIPPI CANYON BLOCK 943

OCS- G 34 467

MARCH 2014



# PUBLIC INFORMATION COPY

PREPARED BY:



## Tracy W. Albert Regulatory Specialist

504.425 .4652

tracy.albert@shell.comREVISIONS TABLE

Date of Request Plan Section What was Corrected Date Resubmitted

3/24/2014 Section 2j

Section 7

Section 8

Section 9

Section 17 A dd Form 0 1 37 , pgs 3

- 4
Removed dup. entry & Added chemical product Updated AQR 2018 Requested statement

was in Plan Section 9.D

Add MS CZM 3/2 7 /2014

4/15/2014 Provided final copy of plan 4/16/2014INITIAL EXPLORATION PLAN

MISSISSIPPI CANYON BLOCK 943

OCS-G 34467

TABLE OF CONTENTS

1. PLAN CONTENTS

2. GENERAL INFORMATION

3. GEOLOGICAL AND GEOPHYSICAL

4. HYDROGEN SULFIDE - H 2 S

5. MINERAL RESOURCE CONSERVATION

6. BIOLOGICAL, PHYSICAL AND SOCIOECONOMIC INFORMATION

7. WASTE AND DISCHARGE INFORMATION

8. AIR EMISSION INFORMATION

9. OIL SPILL INFORMATION

10. ENVIRONMENTAL MONITORING

11. LEASE STIPULATIONS

12. ENVIRONMENTAL MITIGATION MEASURES

13. RELATED FACILITIES AND OPERATIONS INFORMATION

14. SUPPORT VESSELS AND AIRCRAFT

15. ONSHORE SUPPORT FACILITIES INFORMATION

16. SULPHUR OPERATIONS

17. COASTAL ZONE MANAGEMENT ACT INFORMATION

18. ENVIRONMENTAL IMPACT ANALYSIS

19. AD MINISTRATIVE INFORMATIONSECTION 1: PLAN CONTENTS

A. DESCRIPTION, OBJECTIVES & SCHEDULE

This Initial Exploration Plan (EP/Plan) describes the drilling activities Shell Offshore Inc. (Shell) plans to conduct with respect to Lease OCS- G 34467 located in Mississippi Canyon ( MC ) Block 943

.

Shell’s P lan, as detailed in this EP, is to use a either a dynamically positioned (DP) drillship, the M/V Noble Don Taylor or equivalent r ig or a DP semi-submersible, the Noble Jim day or equivalent. The initial drilling activities are planned to commence on or about July 2014 and drilling is expected to take approximately 187 days per well. The timeframe to complete the initial drilling activity is an estimate based on the best available information regarding downhole conditions likely to be encountered while drilling and is not intended to be a limitation. Once the wells are drilled, a dry hole tree will be installed. Shell will complete and commence production under a separate DOCD.

The selected rig will be equipped with state- of -the-art drilling and well control equipment. The rig will comply with the requirements in the Final Drilling Rules. The drilling activities will be supported by the vessels and aircraft as well as onshore support facilities as listed in Sections 14 and 15 of the EP. Shell has employed or contracted trained personnel to carry out its exploration activities. Shell is committed to local hire, contracting and purchasing to the maximum extent possible. Shell personnel and contractors are experienced at operating in the Gulf of Mexico and are well versed in all Federal and State laws regulating operations. Shell ’s employees and contractors share Shell’s deep commitment to operating in a safe and environmentally responsible manner.

Shell, through its parent and affiliate corporations, has extensive experience safely exploring for oil and gas in the Gulf of Mexico. Shell will draw upon this experience in organizing and carrying out its planned drilling program. Shell believes that the best way to manage blowouts is to prevent them from happening. Significant effort goes into the design and execution of wells and into building and maintaining staff competence. In the unlikely event of a spill, Shell’s Regional OSRP is designed to contain and respond to a spill that meets or

exceeds the WCD detailed in Section 9 of this EP. The WCD does not take into account potential flow mitigating factors such as well bridging, obstructions in wellbore, reservoir barriers, or early intervention. Shell continues to invest in Research and Development (R&D) to improve safety and reliability of our well systems. All operations will be conducted in accordance with applicable federal and state laws, regulations, and lease and permit requirements. Shell will have trained personnel and monitoring programs in place to ensure such compliance.

B. LOCATION

See attached Maps.

C. RIG SAFETY AND POLLUTION FEATURES :

The selected rig will comply with all of the regulations of the American Bureau of Shipping (ABS), International Maritime Organization (IMO) and the United States Coast Guard (USCG). All drilling operations will be conducted under the provisions of 30 CFR, Part 250, Subpart D, and other applicable regulations and notices, including those regarding the avoidance of potential drilling hazards and safety and pollution prevention control. Such measures as inflow detection and well control, monitoring for loss of circulation and seepage loss, and casing design will be our primary safety measures. Primary pollution prevention measures are contaminated and non-contaminated drain system, mud drain system, and oily water processing.DRAIN SYSTEM POLLUTION FEATURES

Drains are provided on the rig in all spaces and on all decks where water or oil can accumulate. The drains are divided into two categories, non-contaminated and contaminated. All deck drains are fitted with a removable strainer plate to prevent debris entering the system.

Deck drainage from rainfall, rig washing, deck washing, and runoff from curbs and gutters, including drippans and work areas, are discharged depending on if it comes in contact with the contaminated or noncontaminated areas of the rig.

1) Non-contaminated Drains

Non-contaminated drains are designated as drains that under normal circumstances do not contain hydrocarbons, and can be discharged directly overboard. These are mostly located around the main deck and outboard in places where it is unlikely that hydrocarbons will be found.

Drains within 50 feet of a designated chemical storage area which uses the weather deck as a primary containment means shall be designated “normally plugged.” An adequate number of drains around the rig shall be designated as “normally open” to allow run -off of rain water. Normally open drains shall have a plug located in a conspicuous area near the drain which can be easily installed in the event of a spill.

The rig’s drain plug program consists at a minimum of a weekly check of all deck drains leading to the sea to verify that their status is as designated. If normally open they shall verify that the drain is open and that the plug is available in the area. If normally closed they shall verify that the plug is securely installed in the

drain.

In the event a leak or spill is observed, the event shall be contained (drain plug installation and/or spill kit deployment as appropriate) and reported immediately.

Rig personnel shall ensure that the perimeter kick-plates on weather decks are maintained and drain plugs are in place as needed to ensure a proper seal.

2) Contaminated Drains

Contaminated drains are designated as drains that contain hydrocarbons and cannot be discharged

overboard. When oil -based mud is used for drilling it will be collected in portable tanks and sent to shore for processing.

3) Mud Drain System

None

4) Oily Water Processing

Oily water is collected in an oily water tank. It must be separated and not pumped overboard until oil

content is < 15 ppm. The separated oil is pumped to a dirty oil tank and has to be sent ashore for disposal. On board the MODU an oil record log has to be kept according to instructions included in the log. Any and all pollution pans are subjected to a sheen test before being pumped out. If the water passes the sheen test then it is pumped over board. If it does not pass the sheen test then the water/oil mixture is pumped to a dirty oil tank and sent to shore for disposal. All waste oil that is sent in to be disposed of is recorded in the MODU’s oil log book.

All discharges will be in accordance with applicable NPDES permits. See Section 18, EIA.5) Lower Hull Bilge System

• The main bilge system is designed to drain the pontoons. There are Goulds electrically driven, self priming centrifugal pumps - one for each main pump room. The aux pumps can pump out with the bilge pump but has to be lined up manually from the main pump room.

• Bilge water is pumped overboard after a sheen test has been completed.

• The pontoon bilge pumps are operable from the bridge, and have audible and visual bilge alarms set for high and low levels.

• Portable submersible pumps are carried onboard the rig to service all column void spaces and are also used for emergency bilge pump in the event of the main pump room flooding.

• Alternate means of pumping the bilges in each pontoon pump room include the use of:

• The ballast system emergency bilge valve which is operated from the control panel;

• Portable submersible pumps; and

• Emergency bilge suction line connected directly to the ballast manifold. (Main Pump rooms only.)

The bilge pumps are manual/automatic type pumps. They are equipped with sensors that give a high and a high-high alarm. They are set to activate when the water gets to a certain level they will automatically pump water out in order to keep flooding under control. The pumps are also capable of being put in manual mode in which they can be turned on by hand.

6) Emergency Bilge System

Main ballast pumps may also be used for emergency bilge pumping directly from the pump rooms via remotely actuated direct bilge suction valves on the ballast system. These valves will operate in a fully flooded compartment. The ballast pumps can be supplied from the emergency switchboard.

7) Oily Water Drain/Separation System

Oily water/engine room bilge water is collected in an oily water tank. It must be separated and not pumped overboard until oil content is < 15 ppm. The separated oil is pumped to a dirty oil tank and has to be sent ashore for disposal. On board all drilling units, an oil record log has to be kept according to instructions included in the log. The rig floor has two skimmer tanks and each is subjected to a sheen test before pumping overboard to ensure environmental safety. All three anchor winch windlasses have skimmer tanks and are subjected to sheen tests before discharge as well.

8) Drain, Effluent and Waste Systems

• The r ig’s drainage system is designed in line with our environmental and single point discharge policies. Drains are either hazardous, i.e. from a hazardous area as depicted on the Area Classification drawings, or non-hazardous drains from nonhazardous areas.

• To prevent migration of hazardous materials and flammable gas from hazardous to non-hazardous areas, the drainage systems are segregated.

• The rig drainage systems tie into oily water separators that take out elements in the drainage that could harm the environment. This is part of Noble’s initiative to be good stewards of the environment. The oily water separators divide the drainage system into these sections:

 Rig Floor Drainage

The Rig floor has been outfitted with a Facet International MAS 34-3 separator. The separator has coalescent plates that remove the solids from the drainage, and the remaining drainage goes

to a skimmer tank. From the skimmer tank it is drained to one of the column dirty oil tank systems where it is then sent through 2 separators and cleaned further to reduce oil content to less than 15 ppm. Columns #3 & 4

The drains on the decks and machinery spaces are separated at mid ship and directed to either the #3 or #4 columns. The separators in these columns go through three cycles of circulation and remove oil to less than 15ppm, then discharge the clean product to sea.

 Main Engine Rooms

• The engine rooms have their own drainage and handling system. The engine rooms are outfitted with a dirty oil tank and the drainage in the tank is processed through the separator, the waste from the separator goes back to the dirty oil tank and the clean water (less than 15ppm) goes overboard.

• The locations and models of the separators are as follows:

• Column #3

–

Westfalia WSD- 18

• Column #4

–

Westfalia WSD- 18

• Drill Floor

–

Facet International MAS 34-3

 Helideck Drains

The helideck has a dedicated drainage system around its perimeter to drain heli-fuel from a helicopter incident. The fuel can be diverted to the designated heli fuel recovery tank which is

located under the Helideck structure.

Operating configurations are as follows:

 The overboard piping valves and hydrocarbons take on valves are closed and locked. To unlock overboard or take on valves a permit has to be filled out.

 The oily water collection tank overflow valve is closed.

 The drill floor drains are lined-up to the drill floor skimmer tank. The Skimmer tanks have a high alarm which sounds by means of an air horn. Before tanks are pumped out a sheen test is performed. Water is pump out the skimmer tanks down the shunt line. Oil containment side is pumped out into 550 gal tote tanks.

 The BOP test area drains are normally lined-up to drain overboard.

 The oily water separator continuously circulates the oily water collection tank. Waste oil is discharged into the waste oil tank and oily water is re-circulated back into the oily water collection tank. Clean water is pumped overboard, which is controlled/monitored by the oil content detector, set at 15 ppm.

 The solids control system is capable of being isolated for cuttings collection.

 The bilge system is normally pumped directly overboard after a sheen test has been performed.

 The engine dirty oil sump can be drained down in Port column oily water separator which discharges water overboard from the water side and oil being pumped out into a 550 gal tote tank oil containment side. There is a high audible alarm on the ballast control panel.D. Storage Tanks

– Noble Don Taylor or similar DP Drillship:

Type of Storage

Tank Tank

Capacity (bbls) Number of

Tanks Total

Capacity (bbls) Fluid Gravity (Specific)

Fuel oil 2,889 4 11,556 Marine Diesel (0.91 SG)

Fuel oil 3,225 4 12,900 Marine Diesel (0.91 SG)

Fuel oil 2,887 4 11,548 Marine Diesel (0.91 SG)

Fuel oil 2,680 4 10,720 Marine Diesel (0.91 SG)

Fuel oil 178 8 1,424 Marine Diesel (0.91 SG)

Storage Tanks

–

Noble Jim Day DP (or similar Semi-Submersible)

Type of Storage

Tank Type of

Facility Tank

Capacity (Bbls) Number of

Tanks Total

Capacity (Bbls) Fluid Gravity (Specific)

Diesel Tank in
stbd 1 80% fill in

all hull tanks Drilling Rig 3597 1 Marine Diesel (0.91 SG)

Diesel Tank in

stbd 2 Drilling Rig 2713 1 Marine Diesel (0.91 SG)

Diesel Tank in

stbd 3 Drilling Rig 3456 1 Marine Diesel (0.91 SG)

Diesel Tank in

stbd 4 Drilling Rig 653 1 Marine Diesel (0.91 SG)

Diesel Tank in port 1 Drilling Rig 2090 1 Marine Diesel (0.91 SG)

Diesel Tank in port 2 Drilling Rig 1366 1 Marine Diesel (0.91 SG)

Diesel Tank in port 3 Drilling Rig 4787 1 Marine Diesel (0.91 SG)

Diesel Tank in port 4 Drilling Rig 3456 1 Marine Diesel (0.91 SG)

Total storage in

hull tanks Drilling Rig 22118 Marine Diesel (0.91 SG)

Diesel Settling

Tanks Drilling Rig 129 1 Marine Diesel (0.91 SG)

Diesel Settling

Tanks Drilling Rig 129 1 Marine Diesel (0.91 SG)

Diesel Settling

Tanks Drilling Rig 139 1 Marine Diesel (0.91 SG)

Diesel Settling

Tanks Drilling Rig 129 1 Marine Diesel (0.91 SG)E. Pollution Prevention Measures

Pursuant to NTL No. 2008-G04 the proposed operations covered by this EP do not require Shell to specifically address the discharges of oil and grease from the rig during rainfall or routine operations. Nevertheless, Shell has provided this information as part of its response in 1(c) above.

F. Additional Measures

 HSE (health safety and environment) are the primary topics in pre-tour and pre-job safety meetings. The discussion around no harm to people or environment is a key mindset. All personnel are reminded daily to inspect work areas for safety issues as well as potential pollution

issues.

 All tools that come to and from the rig have their pollution pans inspected, cleaned and confirmation of plugs installed prior to leaving dock and prior to loading on the boat.

 Preventive maintenance of rig equipment includes visual inspection of hydraulic lines and reservoirs

on routine scheduled basis.

 All pollution pans on rig are inspected daily.

 Containment dikes are installed around all oil containment, drum storage areas, fuel vents, and fuel storage tanks.

 All used oil and fuel is collected and sent in for recycling.

 Every drain on the rig is assigned a number on a checklist. The checklist is used daily to verify drain plugs are installed.

 All trash containers are checked and emptied daily. The trash containers are kept covered. Trash is disposed of in a compactor and shipped in via boat.

 The rig is involved in a recycling program for cardboard, plastic, paper, glass, and aluminum.

 Fuel hoses and SBM are changed on annual basis.

 TODO spill prevention fittings are installed on all liquid take on hoses.

 Waste paint thinner is recycled on board with a solvent still to reduce hazard of shipping and
storage.

 All equipment on board utilizes Envirorite hydraulic fluid as opposed to hydraulic oil.

 Shell has obtained ISO14001 certification.

 Shell uses low sulfur fuel.Attachment 1A Bathymetry and Surface LocationAttachment 1C



### U. S. Department of the Interior OMB Control Number: 1010-0151 

### Bureau of Ocean Energy Management OMB Approval Expires: 12/31 /2014



### OCS PLAN INFORMATION FORM

General Information

Type of OCS Plan: X Exploration Plan (EP) DOCD

Company Name: Shell Offshore Inc. BOEM Operator Number: 0689

Address: P. O. Box 61933 Contact Person: Tracy Albert

New Orleans, LA 70161

- 1933 Phone Number: (504) 425

- 4652

E

- Mail Address: tracy.albert@shell.com

Lease(s): G 34467 Area: MC Block(s): 943 Project Name (If Applicable): PowerNap

Objective(s): X Oil X Gas Sulphur Salt Onshore Base: Fourchon /Boothville Distance to Closest Land (Miles): 65



### Description of Proposed Activities (Mark all that apply)

X Exploration drilling Development drilling

Well completion Installation of production platform

Well test flaring (for more than 48 hours) Installation of production facilities

Installation of caisson or platform as well protection structure Installation of satellite structure

Installation of subsea wellheads and/or manifolds Commence production

Installation of lease term pipelines Other (Specify and describe) Pipeline appurtenance

Have you submitted or do you plan to submit a Conservation Information Document to accompany this plan? Yes X No

Do you propose to use new or unusual technology to conduct your activities? Yes X No

Do you propose any facility that will serve as a host facility for deepwater subsea development? Yes X No

Do you propose any activities that may disturb a BOEM

- designated high

- probability archaeological area? Yes X No

Have all of the surface locations of your proposed activities been previously reviewed and approved by BOEM ? Yes X No


### Tentative Schedule of Proposed Activities

Proposed Activity Start Date End Date No. of Days

Drill and suspend well A 0 7 /01/2014 01 / 0 4 /201 5 1 87

Drill and suspend well B 07/01/201 5 01 /0 4 /201 6 187

Drill and suspend well C 07/01/201 6 01/04 /201 7 187

Drill and suspend well D 07/01/201 7 01 /0 4 /201 8 187



### Description of Drilling Rig Description of Production Platform

Jackup X Drillship Caisson Tension leg platform

Gorilla Jackup Platform rig Well protector Compliant tower

Semisubmersible Submersible Fixed platform Guyed tower

X DP Semisubmersible Other (Attach Description) Subsea manifold Floating production system

Drilling Rig Name (If Known): Noble Don Taylor or similar
Noble Jim Day or similar Spar Other (Attach Description)



### Description of Lease Term Pipelines

From (Facility/Area/Block) To (Facility/Area/Block) Diameter (Inches) Length (Feet)


### N/A

Form BOEM- 0137 (December 2011-Supercedes all previous editions of form BOEM-0137 which may not be used.)

### Attachment 1D OCS PLAN INFORMATION FORM (CONTINUED)
Include one copy of this page for each proposed well/structure

Proposed Well/Structure Location

Well or Structure Name/Number (If renaming well or structure, reference previous name): A Subsea Completion

Anchor Radius (if applicable) in feet: NA x Yes No

Surface Location Bottom

- Hole Location (For Wells)

Lease No. OCS

- G 34467

Area Name Mississippi Canyon

Block No. 943

Blockline

Departures (in feet) N/S Departure: 986’ FSL

E/W Departure: 7,108’ FE L

Lambert X

- Y

coordinates X: 990,812’

Y: 10,170,266’

Latitude/
Longitude Latitude 28.0111767

Longitude

- 89.0137157

TVD (Feet ): MD (Feet): Water Depth (Feet): 4,211 ’



### Anchor Locations for Drilling Rig or Construction Barge ( If anchor radius supplied above, not necessary)

Anchor Name

or No. Area Block X Coordinate Y Coordinate Length of Anchor Chain on

Seafloor

Paperwork Reduction Act of 1995 Statement: The Paperwork Reduction Act of 1995 (44 U.S.C. 2501 et seq.) requires us to inform you that BOEM collects this information as part of an applicant’s Exploration Plan or Development Operations Coordination Document sub mitted for
BOEM approval. We use the i nformation to facilitate our review and data entry for OCS plans. We will protect proprietary data according to the
Freedom of Information Act and 30 CFR 550.197. An agency may not conduct or sponsor, and a person is not required to respond to, a collectio n of information unless it displays a currently valid Office of Management and Budget Control Number. Responses are mandatory ( 43 U.S.C. 1334).
The public reporting burden for this form is included in the burden for preparing Exploration Plans and Developm ent Operations Coordination
Documents. We estimate that burden to average 600 hours with an accompanying EP, or 700 hours with an accompanying DPP or DOC D, including the time for reviewing instructions, gathering and maintaining data, and completing and re viewing the forms associated with subpart
B. Direct comments regarding the burden estimate or any other aspect of this form to the Information Collection Clearance Off icer, Bureau of
Ocean Energy Management, 381 Elden Street, Herndon, VA 20170.

Form BOEM- 0137 (December 2011-Supercedes all previous editions of form BOEM-0137 which may not be used.)

### Attachment 1E OCS PLAN INFORMATION FORM (CONTINUED)
Include one copy of this page for each proposed well/structure

Proposed Well/Structure Location

Well or Structure Name/Number (If renaming well or structure, reference previous name): B Subsea Completion

Anchor Radius (if applicable) in feet: NA x Yes No

Surface Location Bottom

- Hole Location (For Wells)

Lease No. OCS

- G 34467

Area Name Mississippi Canyon

Block No. 9 43

Blockline

Departures (in feet) N/S Departure: 364’ FSL

E/W Departure: 2,612’ FEL

Lambert X

- Y

coordinates X: 99 5

, 308 ’

Y: 10,1 69 ,6 44 ’

Latitude/
Longitude Latitude 28.0096697

Longitude

- 89.9997538

TVD (Feet): MD (Feet): Water Depth (Feet): 4,227 ’



### Anchor Locations for Drilling Rig or Construction Barge ( If anchor radius supplied above, not necessary)

Anchor Name

or No. Area Block X Coordinate Y Coordinate Length of Anchor Chain on

Seafloor

Paperwork Reduction Act of 1995 Statement: The Paperwork Reduction Act of 1995 (44 U.S.C. 2501 et seq.) requires us to inform you that BOEM collects this information as part of an applicant’s Exploration Plan or Development Operations Coordination Document sub mitted for
BOEM approval. We use the i nformation to facilitate our review and data entry for OCS plans. We will protect proprietary data according to the
Freedom of Information Act and 30 CFR 550.197. An agency may not conduct or sponsor, and a person is not required to respond to, a collectio n of information unless it displays a currently valid Office of Management and Budget Control Number. Responses are mandatory ( 43 U.S.C. 1334).
The public reporting burden for this form is included in the burden for preparing Exploration Plans and Developm ent Operations Coordination
Documents. We estimate that burden to average 600 hours with an accompanying EP, or 700 hours with an accompanying DPP or DOC D, including the time for reviewing instructions, gathering and maintaining data, and completing and re viewing the forms associated with subpart
B. Direct comments regarding the burden estimate or any other aspect of this form to the Information Collection Clearance Off icer, Bureau of
Ocean Energy Management, 381 Elden Street, Herndon, VA 20170.

Form BOEM- 0137 (December 2011-Supercedes all previous editions of form BOEM-0137 which may not be used.)

### Attachment 1F OCS PLAN INFORMATION FORM (CONTINUED)
Include one copy of this page for each proposed well/structure

Proposed Well/Structure Location

Well or Structure Name/Number (If renaming well or structure, reference previous name): C Subsea Completion

Anchor Radius (if applicable) in feet: NA x Yes No

Surface Location Bottom

- Hole Location (For Wells)

Lease No. OCS

- G 34467

Area Name Mississippi Canyon

Block No. 9 43

Blockline

Departures (in feet) N/S Departure: 1,535’ FSL

E/W Departure: 861’ FEL

Lambert X

- Y

coordinates X: 997,059’

Y: 10,170,815’

Latitude/
Longitude Latitude 28.0129687

Longitude

- 89.9943880

TVD (Feet): MD (Feet): Water Depth (Feet): 4,276 ’



### Anchor Locations for Drilling Rig or Construction Barge ( If anchor radius supplied above, not necessary)

Anchor Name

or No. Area Block X Coordinate Y Coordinate Length of Anchor Chain on

Seafloor

Paperwork Reduction Act of 1995 Statement: The Paperwork Reduction Act of 1995 (44 U.S.C. 2501 et seq.) requires us to inform you that BOEM collects this information as part of an applicant’s Exploration Plan or Development Operations Coordination Document sub mitted for
BOEM approval. We use the i nformation to facilitate our review and data entry for OCS plans. We will protect proprietary data according to the
Freedom of Information Act and 30 CFR 550.197. An agency may not conduct or sponsor, and a person is not required to respond to, a collectio n of information unless it displays a currently valid Office of Management and Budget Control Number. Responses are mandatory ( 43 U.S.C. 1334).
The public reporting burden for this form is included in the burden for preparing Exploration Plans and Developm ent Operations Coordination
Documents. We estimate that burden to average 600 hours with an accompanying EP, or 700 hours with an accompanying DPP or DOC D, including the time for reviewing instructions, gathering and maintaining data, and completing and re viewing the forms associated with subpart
B. Direct comments regarding the burden estimate or any other aspect of this form to the Information Collection Clearance Off icer, Bureau of
Ocean Energy Management, 381 Elden Street, Herndon, VA 20170.

Form BOEM- 0137 (December 2011-Supercedes all previous editions of form BOEM-0137 which may not be used.)

### Attachment 1G OCS PLAN INFORMATION FORM (CONTINUED)
Include one copy of this page for each proposed well/structure

Proposed Well/Structure Location

Well or Structure Name/Number (If renaming well or structure, reference previous name): D Subsea Completion

Anchor Radius (if applicable) in feet: NA x Yes No

Surface Location Bottom

- Hole Location (For Wells)

Lease No. OCS

- G 34467

Area Name Mississippi Canyon

Block No. 9 43

Blockline

Departures (in feet) N/S Departure: 2,869’ FSL

E/W Departure: 3,587’ FEL

Lambert X

- Y

coordinates X: 994,333’

Y: 10,172,149’

Latitude/
Longitude Latitude 28.0165143

Longitude

- 89.0029022

TVD (Feet): MD (Feet): Water Depth (Feet): 4,270 ’



### Anchor Locations for Drilling Rig or Construction Barge ( If anchor radius supplied above, not necessary)

Anchor Name

or No. Area Block X Coordinate Y Coordinate Length of Anchor Chain on

Seafloor

Paperwork Reduction Act of 1995 Statement: The Paperwork Reduction Act of 1995 (44 U.S.C. 2501 et seq.) requires us to inform you that BOEM collects this information as part of an applicant’s Exploration Plan or Development Operations Coordination Document sub mitted for
BOEM approval. We use the i nformation to facilitate our review and data entry for OCS plans. We will protect proprietary data according to the
Freedom of Information Act and 30 CFR 550.197. An agency may not conduct or sponsor, and a person is not required to respond to, a collectio n of information unless it displays a currently valid Office of Management and Budget Control Number. Responses are mandatory ( 43 U.S.C. 1334).
The public reporting burden for this form is included in the burden for preparing Exploration Plans and Developm ent Operations Coordination
Documents. We estimate that burden to average 600 hours with an accompanying EP, or 700 hours with an accompanying DPP or DOC D, including the time for reviewing instructions, gathering and maintaining data, and completing and re viewing the forms associated with subpart
B. Direct comments regarding the burden estimate or any other aspect of this form to the Information Collection Clearance Off icer, Bureau of
Ocean Energy Management, 381 Elden Street, Herndon, VA 20170.

Form BOEM- 0137 (December 2011-Supercedes all previous editions of form BOEM-0137 which may not be used.)SECTION 2: GENERAL INFORMATION

A. Application and Permits

There are no individual or site-specific permits other than general NPDES Permit and rig move notification that

need to be obtained. Prior to beginning exploration operations, an Application for Permit to Drill will be submitted and approved by the Bureau of Safety and Environmental Enforcement (BSEE).

B. Drilling Fluids

See Section 7, Tables 7A and 7B.

C. Production

Information regarding production is not included in this EP as such information is only necessary in the case

of DOCDs.

D. Oil Characteristics

Information regarding oil characteristics is not included in this EP as such information is only necessary in the

case of DOCDs.

E. New Or Unusual Technology

Shell is not proposing to use new or unusual technology as defined in 30 CFR 250.200 to carry out the proposed

activities in this EP.

F. Bonding

The bond requirement for the activities proposed in this EP are satisfied by an area-wide bond furnished and maintained according to 30 CFR Part 256, subpart I; NTL No. 2000-G16, Guideline for General Lease Surety Bonds;” and additional security under National NTL No. 2008- N0 7 , “Supplemental Bond Proc ed ures.”

G. Oil Spill Financial Responsibility (OSFR)

Shell Offshore Inc.

, BOEM Operator Number 0689, has demonstrated oil spill financial responsibility for the facilities proposed in the EP according to 30 CFR Part 250 and 253, and NTL No. 2008- N05 , “Guidelines for Oil Spill Financial Responsibility for Covered Facilities.”

H. Deepwater well control statement

Shell Offshore Inc.

, BOEM Operator Number 0689, has the financial capability to drill a relief well and conduct other emergency well control operations.

I. Suspension of Production

Information regarding Suspension of Production is not included in this EP as such information is only necessary in the case of DOCDs.J. Summary

This Section 2j was prepared by Shell pursuant to the guidance provided in the BOEM’s NTL 2010 -N06 with respect to blowout and worst case discharge (WCD) scenario descriptions. Shell intends to comply with all applicable laws, regulations, rules and Notices to Lessees.

Shell focuses on an integrated, three-pronged approach to a blowout, including prevention, intervention

, containment, and recovery.

1. Shell believes that the best way to manage blowouts is to prevent them from happening. Significant effort goes into design and execution of wells and into building and maintaining staff competence. Shell continues to invest independently in R&D to improve safety and reliability of our well systems.

2. Shell is a founding member of the MWCC, which provides robust well containment (shut-in and controlled flow) capabilities. Additionally, Shell is investing in R&D to improve containment
systems.

3. As outlined in Shell’s OSRP, and detailed in EP Section 9a (ii), Shell has contracts with OSROs to provide the resources necessary to respond to this WCD scenario. The capabilities for on-water recovery, aerial and subsea dispersant application, in-situ burning, and nighttime monitoring and tracking have been significantly increased.

The WCD blowout scenario for this plan is calculated for the MC 943 Well A location penetration of the target interval and is based on the guidelines outlined in NTL 2010-N06 along with subsequent Frequently Asked Questions (FAQ). Shell’s Regional OSRP (April 2013) is based on MC-391 Well 1 as the WCD well. In the unlikely event of a spill, Shell’s Regional OSRP is designed to contain and respond to a spill that exceeds this WCD. This WCD does not take into account potential flow mitigating factors such as well bridging, obstructions in wellbore, reservoir barriers, and early intervention including containment capabilities.

Uncontrolled blowout (volume first day) 175,000 bbl oil

Uncontrolled blowout rate (first 30

- days average daily rate) 165 ,000 bopd Duration of flow (days) based on relief well 203 days

Total volume of spill (bbls) for 203 days 32 MMBO

Table 2.1. PowerNap Worst Case Discharge Summary

The exploration prospect is located approximately 65 statute miles south-southeast of the nearest Louisiana shoreline in the Gulf of Mexico, in water depths of 4186- 4708’ across the prospect. The MC943 A well is expected to have the highest flow rates. The alternate well locations (B, C, D) were also evaluated; however,

their flow rates are lower than the WCD calculated for the MC 943 A well.

1) Purpose

Pursuant to 30 CFR 250.213(g), 250.219, 250.250, and NTL 2010-N06, this document provides a blowout scenario description, further information regarding any potential oil spill, the assumptions and calculations used to determine the WCD and the measures taken to 1) enhance the ability to prevent a blowout and 2) respond and manage a blowout scenario if it were to occur. These calculations are based on best technical estimates of subsurface parameters that are derived from the regional formation of offset well data and seismic data. These parameters are better than or consistent with the estimates used by Shell to justify the investment. Therefore, these assumed parameters were used to calculate the WCD. They do not reflect probabilistic estimates.2) Background

This attachment has been developed to document the additional information requirements for EPs as requested by NTL No. 2010-N06 in response to the explosion and sinking of the MODU Deepwater Horizon and the resulting subsea well blowout and recovery operations of the exploration well at the MC-252

Macondo location.

3) Information Requirements

a) Blowout scenario

All well locations addressed in this EP were assessed for WCD. The MC -943 well from the A location represents the highest flow potential. The A well penetrates the Miocene objective interval as outlined in the Geological and Geophysical Information Section of the EP using a subsea wellhead system, conductor, surface and intermediate casing program, and using a DP MODU with a marine riser and subsea blowout preventer (BOP). A hydrocarbon influx and a well control event are modeled to occur from reservoirs in the objective interval. The modeled blowout results in unrestricted flow from the well at the seafloor, which represents the WCD (no restrictions in wellbore, failure/loss of the subsea BOP, and a blowout to the seabed).

b) Estimated flow rate of the potential blowout

Category EP

Type of Activity Drilling

Facility Location (area/block) MC

- 943

Facility Designation MODU

Distance to Nearest Shoreline (Statute miles) 65

Uncontrolled blowout (volume first day) 175,000 bbl oil

Uncontrolled blowout rate (first 30

- days average daily rate) 165,000 bopd

Table 2.2 Estimated Flow Rates of a Potential Blowout

c) Total volume and maximum duration of the potential blowout

Duration of flow (days) 203 days total duration to drill re lief well (14 days rig demobilization, 4 days rig mobilization, 155 days spud to TD, 30 days ranging). Total volume of spill (bbls) 32 MMBO based on 203 days flowing. Note: From GAP/Prosper/MBAL model

Table 2.3 Estimated Duration and Volume of a Potential Blowout

There is usually a decline in the discharge rate as time proceeds, which is illustrated by the differences between the first 24-hour volume and 30-day average rate. The total volume calculated until a well is killed in a potential blowout further demonstrates this decline. At very short times, e.g. during the first 24 hours, the pressure profile in the reservoir changes from the moment when a well first starts flowing to a pseudo-steady state pressure profile with time, and as a result the rate declines. At somewhat longer time scales, effects such as reservoir voidage and the impact of boundaries can cause the rate to drop continuously with production. Simulation and material balance models can include these effects and form the basis of the NTL 2010-N06 calculations for 24-hour and 30-day rates as well as maximum duration volumes.d) Assumptions and calculations used in determining the worst case discharge ( Proprietary )

e) Potential for the well to bridge over

Mechanical failure/collapse of the borehole in a blowout scenario is influenced by several factors including insitu stress, rock strength and fluid velocities at the sandface. Based on the nodal analysis and reservoir
simulation models outlined above, a seabed blowout would create a high drawdown at the sand face. Given
the substantial fluid velocities inherent in the worst case discharge, and the scenario as defined where the
formation is not supported by a cased and cemented wellbore, it is possible that the borehole may
fail/collapse/bridge over within the span of a few days, significantly reducing the outflow rates. However, this
WCD scenario does not include any bridging.

f) Likelihood for intervention to stop the blowout.

Safety of operations is our top priority. Maintaining well control at all times to prevent a blowout is the key focus of our operations. Our safe drilling record is based on our robust standards, conservative well design, prudent operations practices, competency of personnel, and strong HSE focus. Collectively, these constitute a robust system making blowouts extremely rare events.

Intervention Devices: Notwithstanding these facts, the main scenario for recovery from a blowout event is via intervention with the BOP attached to the well. There are built in redundancies in the BOP system to allow activation of selected components with the intent to seal off the well bore. As a minimum, the Shell contracted rig fleet in the GOM will have redundancies meeting the Final Drilling Safety Rule with respect to Remotely Operated Vehicle (ROV) hot stab capabilities, a deadman system, and an autoshear system.

The rig that will be used to drill the well will be equipped with BOP stack that complies with Shell and BSEE

standards.

Containment: The experience of gaining control over the Macondo well has resulted in a better understanding of the necessary equipment and systems for well containment. As a result, industry and government are better equipped and prepared today to contain an oil well blowout in deepwater. Shell is further analyzing these advances and incorporating them into its comprehensive approach to help prevent and, if needed, control another deepwater control incident.

Pursuant to NTL 2010-N10 Shell will provide additional information regarding our containment capabilities in a subsequent filing.

g) Availability of a rig to drill a relief well and rig package constraints

Blowout intervention can be conducted from an ROV equipped vessel, the existing drilling rig or from another drilling rig. Shell has an active portfolio of well operations in the GOM which will be supported by a total of four to six MODU rigs in 2014

– 2018 timeframe. The dynamically positioned rigs under contract, the Noble Jim Day, Noble Globetrotter I, and the Noble Bully I will be the preferred rigs for blowout intervention work. However, moored rigs, like the Transocean Deepwater Nautilus, can also be used in some scenarios. Additionally, in the event of a blowout, there is the distinct possibility that other non-contracted rigs in the GOM could be utilized whether for increased expediency or better suitability. All efforts will be made at the time to secure the appropriate rig.Shell’s current contracted rigs capable of operating at PowerNap water depths and reservoir depths without

constraints are in the following table:

Rig Name Rig Type

Noble Jim Day Dynamically positioned semisubmersible

Noble Globetrotter I Dynamically positioned drillship

Noble Bully I Dynamically positioned drillship

Transocean Deepwater Nautilus Moored semisubmersible

Table 2.4 Shell contracted rigs capable at PowerNap

Future modifications may change the rig’s capability. Rig capabilities need to be assessed on a work scope specific basis.

h) Time taken to contract a rig, move it onsite, and drill a relief well

Relief well operations will immediately take priority and displace any activity from Shell’s contracted rig fleet. Table 2.4 lists the Shell contracted rigs capable of operating at PowerNap. It is expected to take an average of 14 days to safely secure the well that the rig is working on up to the point the rig departs location, and an additional 4 days transit to mobilize to the relief well site depending on distance to the site. The relief well will take approximately 155 days to drill down to the last casing string above the blowout zone, plus approximately 30 days for precision ranging activity to intersect the blowout well bore. The total time to mobilize and drill a relief well would be 203 days for the Power Nap well

.

If a moored rig is chosen to conduct the relief well operations, anchor handlers would be prioritized to prepare mooring on the relief well site while the rig is being mobilized. This mooring activity is not expected to delay initiation of relief well drilling operations. Shell has deepwater anchor handlers on long term contract to support its moored rigs.

It is not possible to drill relief wells from any existing platforms due to the distance to reach the sub-surface.

i) Measures proposed to enhance ability to prevent blowout and to reduce likelihood of a

blowout.

Shell believes that the best way to manage blowouts is to prevent them from happening. Detailed below are the measures employed by Shell with the goal of no harm to people or the environment. The Macondo incident has highlighted the importance of these practices. The lessons learned from the investigation are, and will continue to be, incorporated into our operations.

Standards: Shell’s well design and operations adhere to internal corporate standards, the Code of FederalRegulations, and industry standards. A robust management of change process is in place to handle undefined or exception situations. Ingrained in the Shell standards for well control is the philosophy of multiple barriers in the well design and operations on the well.

Risk Management: Shell believes that prevention of major incidents is best managed through the systematic identification and mitigation process (Safety Case). All Shell contracted rigs in the GOM have been operating with a Safety Case and will continue to do so. A Safety Case requires both the owner and contractors to systematically identify the risks in drilling operations and align plans to mitigate those risks; an alignment which is critical before drilling begins.Well Design Workflow: The Well Delivery Process (WDP) is a rigorous internal assurance process with

defined decision gates. The WDP leverages functional experts (internal and external) to examine the well design at the conceptual and detailed design stages for robustness before making a recommendation to the management review board. Shell’s involvement in global deepwater drilling, starting in the GOM in the mid

1980’s, provides a sig nificant depth and breadth of internal drilling and operational expertise. Third party vendors and rig contractors are involved in all stages of the planning, providing their specific expertise. A Drill the Well On Paper (DWOP) exercise is conducted with rig personnel and vendors involved in execution of the well. This forum communicates the well plan, and solicits input as to the safety of the plan and procedures proposed.

Well and rig equipment qualification, certification, and quality assurance: All rigs will meet all applicable rules, regulations, and Notice to Lessees. Shell works closely with rig contractors to ensure proper upkeep of all rig equipment, which meets or exceeds the strictest of Shell, industry, or regulatory requirements. Well tangibles are governed by our internal quality assurance/control standards and industry

standards.

MWD/LWD/PWD Tools: Shell intends to use these tools at PowerNap. The MWD/LWD/PWD tools are run on the drill string so that data on subsurface zones can be collected as the well advances in real time instead of waiting until the drill string is pulled to run wireline logs. Data from the tools are monitored and interpreted real time against prognosis to provide early warning of abnormal pressures to allow measures to be taken to progress the well safely.

Mud Logger: Mud-logging personnel continually monitor returning drilling fluids for indications of hydrocarbons, utilizing both a hot wire and a gas chromatograph. An abrupt increase in gas or oil carried in the returning fluid can be an indication of an impending kick. The mud logger also monitors drill cuttings returned to the surface in the drilling fluid for changes in lithology that can be an indicator that the well has penetrated or is about to penetrate a hydrocarbon-bearing interval. Mud logging instruments also monitor penetration rate to provide an early indication of drilling breaks that show the bit penetrating a zone that could contain hydrocarbons. The mud logging personnel are in close communication with both the offshore drilling foremen and onshore Shell representative(s) to report any observed anomalies so appropriate action

can be taken.

Remote Monitoring: The Real Time Operating Center has been used by Shell to complement and support traditional rig-site monitoring since 2003. Well site operations are monitored 24/7 virtually by onshore teams consisting of geoscientists, petrophysicists, well engineers, and monitoring specialists. The same real time well control indicators monitored by the rig personnel are watched by the monitoring specialist for an added layer of redundancy.

Competency and Behavior: A structured training program for Well Engineers and Foremen is practiced, which includes internal professional examinations to verify competency. Other industry training in well control, such as by International Association of Drilling Contractors (IADC) and International Well Control Forum (IWCF) are also mandated. Progressions have elements of competency and Shell continues to have comprehensive internal training programs. The best systems and processes can be defeated by lack of knowledge and/or improper values. We believe that a combination of HSE tools (e.g. stop work, pre-job analysis, behavior based safety, DWOPs, audits), management HSE involvement and enforcement (e.g. compliance to life saving rules) have created a strong safety culture in our operations.

j) Measures to conduct effective and early intervention in the event of a blowout.

The response to a blowout is contained in our Well Control Contingency Plan (WCCP) which is a specific requirement of our internal well control standards. The WCCP in turn is part of the wider emergency response framework within Shell that addresses the overall organization response to an emergency situation. Resources are dedicated to these systems and drills are run frequently to test preparedness (security,medical, oil spill, and hurricane). This same framework is activated and tested during hurricane evacuations,

thereby maintaining a fresh and responsive team.

The WCCP specifically addresses implementing actions at the emergency site that will ensure personnel safety, organizing personnel and their roles in the response, defining information requirements, establishing protocols to mobilize specialists, pre-selecting sources, and developing mobilization plans for personnel, material and services for well control procedures. The plan references individual activity checklists, a roster of equipment and services, initial information gathering forms, a generic description of relief well drilling, strategy and guidelines, intervention techniques and equipment, site safety management, exclusion zones, and re-boarding.

As set forth in 2f of this document, Shell is currently analyzing recent advances in containment technology and equipment and will incorporate them as they become available.

k) Arrangements for drilling a relief well

The size of the Shell contracted rig fleet in the GOM from 2014-2018 ensures that there is adequate well equipment (e.g. casing and wellhead) available for relief wells. Rigs and personnel will also be readily available within Shell, diverted from their active roles elsewhere. Resources from other operators can also be leveraged should the need arise. Generally, relief well plans will mirror the blowout well, incorporating any learning on well design based on root cause analysis of the blowout. A generic relief well description is

outlined in the WCCP.

l) Assumptions and calculations used in Regional OSRP

All proposed PowerNap locations were evaluated and Location A was determined to have the greatest WCD volume. Shell has designed a response program (Regional OSRP) based upon a regional capability of responding to a range of spill volumes, from small operational spills up to and including the WCD from a well blowout. Shell’s program is developed to fully satisfy federal oil spill planning regulations. The Regional OSRP presents specific information on the response program that includes a description of personnel and equipment mobilization, the incident management team organization and the strategies and tactics used to implement effective and sustained spill containment and recovery operations.SECTION 3: GEOLOGICAL & GEOPHYSICAL INFORMATION

A. Geological Description

Proprietary Data

B. Structure contour map

Proprietary Data

C. Interpreted 2D and/or 3D Seismic line(s)

Proprietary Data

D. Geological Structure Cross-section(s)

Proprietary Data

E. Shallow Hazards Report

Geoscience Earth and Marine Services, Inc. (GEMS), Geologic, Stratigraphic and Archaeological Assessment of Blocks 942 (OCS G-24130), 943 (OCS G-34467), and Portions of Surrounding Blocks, Mississippi Canyon Area, Gulf of Mexico. Project No. 0513 -2243a,b, dated February 11, 2014.

C&C Technologies, Archaeological Assessment Report, Blocks 895-898, 939-942, & 983-986, MississippiCanyon Area. Project No. 072657-072954, dated October, 2007. Data: AUV Side Scan Sonar and SubBottom Profiler

F. Shallow Hazards Assessment

See Section 6 for Shallow Hazards Assessment.

G. High-Resolution Seismic Lines

Proprietary Data

H & I Stratigraphic Column with Time vs depth table

Proprietary DataSECTION 4: HYDROGEN SULFIDE

A. Concentration

0 ppm.

B. Classification

Based on 30 CFR 550.215, Shell requests that the Regional Supervisor, Field Operations, classify the area in the proposed drilling operations as an area where the absence of H 2 S is confirmed.

C. H 2 S Contingency Plan

Shell is not required to provide an H 2 S Contingency Plan with the Application for Permit to Drill before conducting the proposed activities.

D. Modeling Report

We do not anticipate to encounter or handle H 2 S at concentrations greater than 500 parts per million (ppm) and therefore have not included modeling for H 2 S. Attachment 3 B

– Structure Map : Middle Miocene 2SECTION 5: MINERALS RESOURCE CONSERVATION

Information regarding Mineral Resource Conservation is not included in this EP as such information is only necessary in the case of DOCDs..

SECTION 6: BIOLOGICAL, PHYSICAL AND SOCIOECONOMIC INFORMATION

Mississippi Canyon Blocks 943

Shallow Hazards Report and Data:

Geoscience Earth and Marine Services, Inc. (GEMS), Geologic, Stratigraphic and Archaeological Assessment of Blocks 942 (OCS G-24130), 943 (OCS G-34467), and Portions of Surrounding Blocks, Mississippi Canyon Area, Gulf of Mexico. Project No. 0513-2243a,b, dated February 11, 2014. Data: AUV Side Scan Sonar, Sub Bottom Profiler, and frequency enhanced 3-D Seismic

Archaeological Reports and Data:

Geoscience Earth and Marine Services, Inc., Geologic, Stratigraphic and Archaeological Assessment of Blocks 942 (OCS G-24130), 943 (OCS G-34467), and Portions of Surrounding Blocks, Mississippi Canyon Area, Gulf of Mexico. Project No. 0513-2243a,b, dated January 24, 2013. Data: AUV Side Scan Sonar, Sub Bottom Profiler, and frequency enhanced 3-D Seismic

C&C Technologies, Archaeological Assessment Report, Blocks 895-898, 939-942, & 983-986, MississippiCanyon Area. Project No. 072657-072954, dated October, 2007. Data: AUV Side Scan Sonar and SubBottom Profiler

Proposed Locations and Coordinates:

Proposed

Location X Coordinate Y coordinate FNL/FSL FEL/FWL Water Depth

MC 943 A 990,812 10,170,266 986 ’ FSL 7108’ FEL 4211’

MC 943 B 995,308 10,169,644 364’ FSL 2612’ FEL 4227’

MC 943 C 997,059 10,170,815 1535’ FSL 861’ FEL 4276’

MC 943 D 994,333 10,172,149 2869’ FSL 3587’ FEL 4270’ Coordinates are in UTM 16, NAD27

Site Assessment, MC 943, Proposed Location A

Mississippi Canyon 943, Proposed Location A is located in a water depth of approximately 4211 feet. Proposed Location A lies along the flank of a seafloor ridge. Buried faults are identified 195’ below the

mudline , seafloor offset is 950’ north of Proposed Location A. Proposed Location A will not intersect this or any faulting in the shallow stratigraphy. There is no other evidence of seafloor or near-surface faulting, slumping amplitudes or fluid expulsion features within 2000 feet of MC 943, Proposed Location A .

The stratigraphy at the site of MC 943, Proposed Location A consists of: • Unit 1 (Seafloor – 452’ BML) - 5’ transparent drape of very soft silty clays, 200’ of layered soft hemipelagic silty clays, 247’ stratified pelagic and hemipelagic muds with thin mud

- rich MTD’s • Unit 2 (452’ – 1194’ BML) – 416’ hemipelagic sediments layers with thin, discontinuous MTD’s, 326’

mud- rich MTD’s with possible sand pockets

• Unit 3 - Blue Unit (1194’ – 1929’ BML)

– 113’ layered turbidites of clay, silt and thin sand layers, 409’ Ursa Canyon

- fill sediments of silts, clays and thin sand layers and pockets, 213’ of MTD’s of sand, silt and clay • Unit 4 (1929’ – 2249’ BML) – 320’ discontinuous, mud

- rich MTD’s

• Unit 5 (2249’ – 2932’ BML) – 683’ discontinuous, mud

- rich MTD’s

• Unit 6 – Orange Unit (2932’ – 4205’ BML) – 298’ slope fan sequence of clays, silts with scattered sand layers and pockets, 283’ MTD’s with scattered small channels of sand, silt and clay, 692’ mud- rich MTD’s • Unit 7 (4205’ – 5503’ BML) – 1298’ layered turbidites inter -layered with clay, silt and sand

Shallow Water Flow Potential: Negligible Potential

– Seafloor

– 868’ BML

Low Potential

– 868’ – 1194’ BML High Potential

– 1194’ – 1929’ BMLLow Potential

– 1929’ – 2932’ BML

High Potential

– 2932’ – 3230’ BML

Moderate Potential

– 3230’ – 3513’ BML

Low Potential - 3513’ – 5503’ BML

Shallow Gas Potential Negligible Potential

– Seafloor

– 868’ BML

Low Potential

– 868’ – 5503’ BML

An ampl itude event in Unit 6 (Orange Unit, 2932’ – 4205’ BML) is identified 465’ north -northwest of Proposed Location A. Proposed Location A will not penetrate this amplitude.

Benthic/Anchor Assessment, MC 943, Proposed Location A (no anchors

– DP Vessel)

Miss issippi Canyon 943, Proposed Location A is located in a water depth of approximately 4211 feet. Proposed Location A lies along the flank of a subtle seafloor ridge.

A seafloor fault is identified 950’ north of Proposed Location A. There is no other evidence of seafloor or

near- surface faulting, slumping, amplitudes or fluid expulsion features within 2000’ of Proposed Location A. Proposed Location A will not disturb any high-density areas of benthic communities.

The following table consisting of 9 t argets is a listing of marine avoidance zones identified within 2000’ of MC 943, Proposed Location A.

Target No. X Coordinate Y Coordinate Distance to Target Direction

from Prop Loc A To Target Avoidance

2013

- 467 989569.73 10169766.76 1338.83’ Northeast 100’

2013

- 474 989872.25 10169151.92 1457.50’ Northeast 100’

2013

- 471 990641.40 10168799.28 1476.61’ Northeast 100’

2013

- 424 991265.98 10171677.51 1482.72’ Southwest 100’

2013

- 475 990159.18 10168646.73 1745.91’ Northeast 100’

2013

- 388 990336.26 10171972.46 1771.53’ Southeast 100’

2013

- 375 990301.76 10172034.60 1840.73’ Southeast 100’

2013

- 485 991130.85 10168446.82 1846.91’ Southwest 100’

2013

- 390 989873.59 10171963.69 1939.78’ Southeast 100’

Currently, there are no flowlines or umbilicals located within 2000’ of Proposed Location A.

Based on a high-resolution geophysical survey consisting of AUV Side-Scan Sonar and Sub-Bottom Profiler, frequency enhanced 3- D Seismic, Enhanced Surface Renderings (ESR’s) and ESR’s with amplitudes applied, MC 943, Proposed Location A appears suitable for the planned activity.

Site Assessment, MC 943, Proposed Location B

Mississippi Canyon 943, Proposed Location B is located in a water depth of approximately 4227 feet. Proposed Location B lies alo ng the flank of a subtle seafloor ridge. Buried faults are identified 100’ below the mud line, seafloor offset is 1300’ north of Proposed Location B. Proposed Location B will not intersect this or any faulting in the shallow stratigraphy. There is no other evidence of seafloor or near-surface faulting, slumping amplitudes or fluid expulsion features within 2000 feet of MC 943, Proposed Location B.

The stratigraphy at the site of MC 943, Proposed Location B consists of: • Unit 1 (Seafloor – 428’ BML) - 5’ transparent drape of very soft silty clays, 200’ layered soft hemipelagic silty clays, 223’ stratified pelagic and hemipelagic muds with thin mud

- rich MTD’s • Unit 2 (428’ – 1149’ BML) – 570’ hemipelagic sediments layers with thin, discontinuous MTD’s, 151’

mud- rich MTD’s with possible sand pockets

• Unit 3 - Blue Unit (1149’ – 1910’ BML) – 395’ Ursa Canyon -fill sediments of silts, clays and thin sand layers and pockets, 366’ of MTD’s of sand, silt and clay • Unit 4 (1910’ – 2079’ BML) – 169’ disco ntinuous, mud- rich MTD’s • Unit 5 (2079’ – 2692’ BML) – 613’ discontinuous, mud

- rich MTD’s• Unit 6 – Orange Unit (2692’ – 3948’ BML) – 662’ slope fan sequence of clays, silts with scattered

sand layers and pockets, 594’ mud

- rich MTD’s • Unit 7 (3948’ – 5436’ BML) – 1488’ layered turbidites inter -layered with clay, silt and sand.

Shallow Water Flow Potential: Negligible Potential

– Seafloor

– 998’ BML

Low Potential

– 998’ – 1149’ BML High Potential

– 1149’ – 1910’ BML

Low Potential

– 1910’ – 2692 ’ BML High Potential

– 2692’ – 3354’ BML

Low Potential

– 3354’ – 5436’ BML

Shallow Gas Potential Negligible Potential

– Seafloor

– 998’ BML

Low Potential

– 998’ - 5436’ BML

A buried amplitude in Unit 7 (3948’ – 5436’ BML) is identified 500’ southwes t of Proposed Location B. Proposed Location B will not penetrate this amplitude.

Benthic/Anchor Assessment, MC 943, Proposed Location B (no anchors

– DP Vessel)

Mississippi Canyon 943, Proposed Location B is located in a water depth of approximately 422 7 feet. Proposed Location B lies along the flank of a subtle seafloor ridge.

A seafloor fault is identified 1300’ north of Proposed Location B, approximately 100’ BML. There is no other evidence of seafloor or near-surface faulting, slumping, amplitudes or fluid expulsion features within 2000’ of Proposed Location B. Proposed Location B will not disturb any high-density areas of benthic communities.

The following table consisting of 5 targets is a listing of marine avoidance zones identified within 2000’ of MC 943, Proposed Location B.

Target No. X Coordinate Y Coordinate Distance to Target Direction

from Prop Loc B To Target Avoidance

2013

- 450 995375.92 10170383.69 742.80’ Southwest 100’

2013

- 468 995259.62 10168797.53 847.85’ Northeast 100’

2013

- 483 995816.99 10168443.56 1303.89’ Northwest 100’

2013

- 438 994687.32 10171051.54 1538.31’ Southeast 100’

2013

- 405 996336.25 10171355.84 1996.92’ Southwest 100’

Currently, there are no flowlines or umbilicals located within 2000’ of Proposed Location B.

Based on a high-resolution geophysical survey consisting of AUV Side-Scan Sonar and Sub-Bottom Profiler, frequency enhanced 3- D Seismic, Enhanced Surface Renderings (ESR’s) and ESR’s with amplitudes applied, MC 943, Proposed Location B appears suitable for the planned activity. Site Assessment, MC 943, Proposed Location C

Mississippi Canyon 943, Proposed Location C is located in a water depth of approximately 4276 feet. Proposed Location C lies along the flank of a subtle seafloor ridge. Buried faults are identified 50’

- 120’ below the mud line, seafloor offset is 1750’ east of Proposed Location C. Proposed Location C will not intersect these or any other faulting in the shallow stratigraphy. There is no other evidence of seafloor or near-surface faulting, slumping amplitudes or fluid expulsion features within 2000 feet of MC 943, Proposed Location C.

The stratigraphy at the site of MC 943, Proposed Location C consists of: • Unit 1 (Seafloor – 412’ BML) - 8’ transparent drape of very soft silty clays, 190’ layered soft hemipelagic silty clays, 214’ stratified pelagic and hemipelagic muds with thin mud

- rich MTD’s• Unit 2 (412’ – 1069’ BML) – 483’ hemipelagic sediments layers with thin, discontinuous MTD’s, 174’

mud- rich MTD’s with possible sand pockets

• Unit 3 - Blue Unit (1069’ – 1827’ BML) – 225’ MTD’s mixture of sand, silt and clay, 533’ Ursa Canyon-fill sediments of silts, clays and thin sand layers and pockets • Unit 4 (1827’ – 1931’ BML) – 104’ discontinuous, mud -r ich MTD’s • Unit 5 (1931’ – 2527’ BML) – 596’ discontinuous, mud

- rich MTD’s

• Unit 6 – Orange Unit (2527’ – 3698’ BML) – 575’ slope fan sequence of clays, silts with scattered sand layers and pockets, 596’ mud

- rich MTD’s with scattered small channels, mi x of sand, silt and clay • Unit 7 (3698’ – 5381’ BML) – 1683’ layered turbidites inter -layered with clay, silt and sand

Shallow Water Flow Potential: Negligible Potential

– Seafloor

– 895’ BML

Low Potential

– 895’ – 1069’ BML High Potential

– 1069’ – 1827’ BML

Low Potential

– 1827’ – 2527’ BML High Potential

– 2527’ – 3102’ BML

Moderate Potential

– 3102’ - 3698’ BML

Low Potential - 3698’ – 5381’ BML

Shallow Gas Potential Negligible Potential

– Seafloor

– 895’ BML

Low Potential

– 895’ - 5381’ BML

A buried amplitude in Unit 6 (Orange Unit 2527’ – 3698’ BML) is identified 300’ southwest of Proposed Location C. Proposed Location C will not penetrate this amplitude.

Benthic/Anchor Assessment, MC 943, Proposed Location C (no anchors

– DP Vessel)

Mississippi Canyon 943, Proposed Location C is located in a water depth of approximately 4276 feet. Proposed Location C lies along the flank of a subtle seafloor ridge.

A seafloor fault is identified 1750’east of Proposed Location C. There is no other evidence of seafloor or nearsurface faulting, slumping, amplitudes or fluid expulsion features within 2000’ of Proposed Location C. Proposed Location C will not disturb any high-density areas of benthic communities.

The following table consisting of 4 targets is a listing of marine avoidance zones identified within 2000’ of MC 943, Proposed Location C.

Target No. X Coordinate Y Coordinate Distance to Target Direction

from Prop Loc C To Target Avoidance

2013

- 400 997424.79 10171372.56 666.84’ Southwest 100’

2013

- 440 997872.94 10171028.93 841.58’ Southwest 100’

2013

- 405 996336.25 10171355.84 902.70’ Northeast 100’

2013

- 450 99375.92 10170383.69 1737.47’ Southeast 100’

Currently, there are no flowlines or umbilicals located within 2000’ of Proposed Location C.

Based on a high-resolution geophysical survey consisting of AUV Side-Scan Sonar and Sub-Bottom Profiler, frequency enhanced 3- D Seismic, Enhanced Surface Renderings (ESR’s) and ESR’s with amplitudes applied, MC 943, Proposed Location C appears suitable for the planned activity.

Site Assessment, MC 943, Proposed Location D

Mississippi Canyon 943, Proposed Location D is located in a water depth of approximately 4270 feet. Proposed Location D lies along the flank of a subtle seafloor ridge. Buried faults are identified 120- 190’below the mud line, seafloor offset is 825’ southwest of Proposed Location D. Proposed Location D will not

intersect these or any other faulting in the shallow stratigraphy. There is no other evidence of seafloor or near-surface faulting, slumping amplitudes or fluid expulsion features within 2000 feet of MC 943, Proposed

Location D.

The stratigraphy at the site of MC 943, Proposed Location D consists of: • Unit 1 (Seafloor – 439’ BML) - 5’ transparent drape of very soft silty clays, 200’ layered soft hemipelagic silty clays, 234’ stratified pelagic and hemipelagic muds with thin mud

- rich MTD’s • Unit 2 (439’ – 1053’ BML) –440’ hemipelagic sediments layers with thin, discontinuous MTD’s, 174’

mud- rich MTD’ s with possible sand pockets

• Unit 3 - Blue Unit (1053’ – 1919’ BML) – 866’ Ursa Canyon -fill sediments of silts, clays and thin sand layers and pockets, 153’ discontinuous mud

- rich MTD’s • Unit 4 (1919’ – 2072’ BML) – 153’ discontinuous, mud

- rich MTD’s • Unit 5 (2072’ – 2723’ BML) – 651’ discontinuous, mud

- rich MTD’s

• Unit 6 – Orange Unit (2723’ – 3947’ BML) – 650’ slope fan sequence of clays, silts with scattered sand layers and pockets, 574’ mud

- rich MTD’s with scattered small channels, mix of sand, silt and clay • Unit 7 (3947’ –5422’ BML) – 1475’ layered turbidites inter -layered with clay, silt and sand

Shallow Water Flow Potential: Negligible Potential

– Seafloor

– 879’ BML

Low Potential

– 879’ – 1053’ BML High Potential

– 1053’ – 1919’ BML

Low Potential

– 1919’ – 2723’ BML High Potential

– 2723’ – 3373’ BML

Low Potential - 3373’ – 5422’ BML

Shallow Gas Potential Negligible Potential

– Seafloor

– 879’ BML

Low Potential

– 879’ - 5422’ BML

A buried amplitude in Unit 7 (3947’ – 5422’ BML) is identified 700’ northwest of Proposed Location D. Proposed Location D will not penetrate this amplitude.

Benthic/Anchor Assessment, MC 943, Proposed Location D (no anchors

– DP Vessel)

Mississippi Canyon 943, Proposed Location D is located in a water depth of approximately 4270 feet. Proposed Location D lies along the flank of a subtle seafloor ridge.

A seafloor fault is identified 825’ southwest of Proposed Location D. There is no other evidence of seaflo or or

near- surface faulting, slumping, amplitudes or fluid expulsion features within 2000’ of Proposed Location D. Proposed Location D will not disturb any high-density areas of benthic communities.

The following table consisting of 10 targets is a listi ng of marine avoidance zones identified within 2000’ of MC 943, Proposed Location D.

Target No. X Coordinate Y Coordinate Distance to Target Direction

from Prop Loc D To Target Avoidance

2013

- 381 993989.42 10172424.86 440.62’ Southeast 100’

2013

- 371 994524.86 10172603.25 493.20’ Southwest 100’

2013

- 366 994359.46 10172649.65 501.35’ Southwest 100’`

2013

- 418 994948.00 10171714.14 753.21’ Northwest 100’

2013

- 421 995183.94 10171692.61 965.60’ Northwest 100’

2013

- 438 994687.32 1017105.54 1153.24’ Northwest 100’

2013

- 347 994674.39 10173358.12 1256.39’ Southwest 100’

2013

- 361 994362.99 10173634.16 1485.46’ Southwest 100’

2013

- 349 993365.33 10173352.60 1544.36’ Southeast 100’

2013

- 385 992474.37 10172209.41 1859.61’ Southeast 100’Currently, there are no flowlines or umbilicals located within 2000’ of Proposed Location D.

Based on a high-resolution geophysical survey consisting of AUV Side-Scan Sonar and Sub-Bottom Profiler, frequency enhanced 3-D Seismic, Enhanced Surface Renderin gs (ESR’s) and ESR’s with amplitudes applied, MC 943, Proposed Location D appears suitable for the planned activity.

B

– F

Pursuant to NTL No. 2008-G04 the proposed operations covered by this EP do not involve operations impacting the following: Topographic features map, Topographic features statement (shunting), Live bottoms, (Pinnacle Trend) map, Live bottoms (low relief) map, potentially sensitive biological features map.

G. Remotely Operated Vehicle (ROV) Monitoring Plan

In accordance with the provisions of NTL No. 2008-G06, Remotely Operated Vehicle Surveys in Deepwater, Walker Ridge Block 95 is located in Grid 13. Grid 13 is an area that has adequate ROV survey coverage; therefore we are not proposing to run the pre- an d post-ROV survey in accordance with the NTL.

H. Threatened and Endanger Species Information

There are 5 species of sea turtles that may be found in the Gulf of Mexico (see table). No critical habitat for these species has been designated in the Gulf of Mexico.

Common Name Scientific Name T/E Status

Hawksbill Turtle Eretmochelys imbricata E

Green Turtle Chelonia mydas T
Kemp's Ridley Turtle Lepidochelys kempii E

Leatherback Turtle Dermochelys coriacea E
Loggerhead Turtle Caretta caretta TThere are 28 species of marine mammals that may be found in the Gulf of Mexico (see table). Of the species

listed as Endangered, only the Sperm whale is commonly found in the project area. No critical habitat for these species has been designated in the Gulf of Mexico.

Common Name Scientific Name T/E Status
Atlantic Spotted Dolphin Stenella frontalis

Blainville's Beaked Whale Mesoplodon densirostris

Blue Whale Balaenoptera musculus E
Bottlenose Dolphin Tursiops truncatus
Bryde's Whale Balaenoptera edeni
Clymene Dolphin Stenella clymene

Cuvier's Beaked Whale Ziphius cavirostris
Dwarf Sperm Whale Kogia simus

False Killer Whale Pseudorca crassidens

Fin Whale Balaenoptera physalus E
Fraser's Dolphin Lagenodelphis hosei

Gervais' Beaked Whale Mesoplodon europaeus
Humpback Whale Megaptera novaeangliae E

Killer Whale Orcinus orca

Melon

- headed Whale Peponocephala electra

Minke Whale Balaenoptera acutorostrata
Northern Right Whale Eubalaena glacialis
Pantropical Spotted Dolphin Stenella attenuata
Pygmy Killer Whale Feresa attenuata
Pygmy Sperm Whale Kogia breviceps
Risso's Dolphin Grampus griseus
Rough

- toothed Dolphin Steno bredanensis

Sei Whale Balaenoptera borealis E

Short

- finned Pilot Whale Globicephala macrorhynchus
Sowerby's Beaked Whale Mesoplodon bidens
Sperm Whale Physeter macrocephalus E
Spinner Dolphin (Long

- snouted) Stenella longirostris
Striped Dolphin Stenella coeruleoalbaI. Archaeological Report

Arch Statements

2013 Report (GEMS)

The archaeological assessment identified 637 unidentified sonar contacts within the 2013 survey area and 106 unidentified sonar contacts within the 2007 survey area covered by the AUV data sets. The unidentified contacts are likely man-made debris. None of these targets is believed to have a cultural significance and no avoidance zones have been assigned. However, a disused Industrial Waste Dumpsite is northwest of the study area. Some of the debris within the AUV survey area may represent material intended the dumpsite. A

100 -ft (30.5 m) geohazard avoidance is recommended for all unidentified sonar contacts in the area.

2007 Report (C&C Technologies)

Data assessment of Blocks 895-898, 939-942, and 983-986, Mississippi Canyon Area for the Vito Prospect

re vealed 106 contacts. The unidentified contacts are interpreted as debris from modern shipping and lease activities or are geologic in origin. None of the unidentified contacts are recommended for an archaeological avoidance based on their acoustic signatures.

It is possible shipwrecks exist undetected or unidentified within the survey area. If wood beams, planking, ceramics, or other possible cultural materials are encountered during lease development, the MMS archaeologists must be contacted within 48 hours for an assessment of any antiquities. In this event, no activities should be conducted near the area of discovery until advised by the appropriate MMS personnel.

J. Air and Water Quality Information

Pursuant to NTL No. 2008-G04 the proposed operations covered by this EP do not require Shell to provide additional information relating to air and water quality information. For specific information relating to air and water quality information please refer to the EIA, Attachment 18

.

K. Socioeconomic Information

Pursuant to NTL No. 2008-G04 the proposed operations covered by this EP do not require Shell to provide additional information relating to air and water quality information. For specific information relating to socioeconomic information please refer to the EIA, Attachment 18

.ESR for MC 943 Well AESR for MC 943 Well BESR for MC 943 Well CESR for MC 943 Well DSECTION 7: WASTE AND DISCHARGE INFORMATIONA.Discharge to GOM or DownholeNote: Please specify if the amount reported is a total or per well amountPower NapType of Waste and CompositionCompositionProjected Amount Discharge rateDischarge MethodAnswer yes or noWill drilling occur ? If yes, you should list muds and cuttingsEXAMPLE: Cuttings wetted with ynthetic based fluidCuttings generatedwhile using syntheticbased drilling fluid. X bbl/well X bbl/day discharge pipe NoWater-based drilling fluid barite, additives, mud 30,000 bbls / well 3,500 bbls / dayOverboard and seafloor discharge prior tomarine riser installation NoCuttings wetted with water-based fluidcuttings coated with water based drillingmud1,590 bbls / well200 bbls / daySea bed during riserless drillingNoCuttings wetted with synthetic-based fluidCuttings generated while using syntheticbased drilling fluid.8,295 bbls / well165 bbs / dayOverboard discharge line below the waterlevelNoSynthetic based drilling fluid adhering to washed drillcuttingsSynthetic based drilling fluid adhering towashed drill cuttings290 bbls / well6 bbls / dayOverboard discharge line below the waterlevelNoWill humans be there? If yes, expect conventional wasteEXAMPLE: Sanitary waste waterX liter/person/dayNAchlorinate and dischargeNoDomestic waste (kitchen water, shower water) grey water39,000 bbls/well203 bbls / dayGrinded to less than 25 mm mesh size anddischarge overboardNoSanitary waste (toilet water)treated sanitary waste6,000 bbls/well30 bbls / dayTreated in the MSD** prior to discharge tomeet NPDES limitsNoIs there a deck? If yes, there will be Deck DrainageDeck DrainageWash and rainwater4,000 bbls/well20 bbls / day Drained overboard through deck scuppersNoWill you conduct well treatment, completion, or workover?well treatment fluidsNANANANANowell completion fluidsNANANANANoworkover fluidsNANANANANoMiscellaneous discharges. If yes, only fill in those associated with your activity.Chemical product wasteDrilling additives added to well50 bbls / well.5 bbls / dayTreated to meet NPDES limits anddischarged overboardNoDesalinization unit dischargeRejected water from watermaker unit72,000 bbls/well380 bbls /day Discharged overboard below waterline NoBlowout prevent fluidWater based400 bbls/well50 bbls/dayDisharge at seafloorNoBallast waterUncontaminated seawater374,000 bbls/well2,000 bbls / day Discharged overboard Just above waterlineNoBilge waterBilge and drainage water will be treated toMARPOL standards (< 15ppm oil in water). 374,000 bbls/well2,000 bbls / dayBilge and drainage water will be treated toMARPOL standards (< 15ppm oil in water). NoExcess cement at seafloorCement slurry1100 bbls/well (assumeplanned 100% excess isdischarged)1100 bbls / wellDischarged at the seafloor during riserlessdrillingNoFire waterTreated seawater13,000 bbls/well2,000 bbls / month Drained overboard through deck scuppersNoCooling waterTreated seawater27,120,000 bbls/well 145,000 bbls / dayDischarged overboard 40 feet belowwaterlineNoWill you produce hydrocarbons? If yes fill in for produced water.Produced waterNANANANANAWill you be covered by an individual or general NPDES permit ?GENERAL PERMITGMG290103NOTE: If you will not have a type of waste, enter NA in the row.TABLE 7A: WASTES YOU WILL GENERATE, TREAT AND DOWNHOLE DISPOSE OR DISCHARGE TOTHE GOMProjectedDownholeDisposalProjected generated wasteProjected ocean dischargesB. Landfill, inject, incinerate or recycle table

C. Modeling Report

Shell did not model the trajectory for discharges because it is not required in the GOM.SECTION 8: AIR EMISSIONS INFORMATION

A. Emissions Worksheet and Screening Questions

Screening Questions for EP’s Yes No

Is any calculated Complex Total (CT) Emission amount (in tons) associated with your proposed exploration activities more than 90% of the amounts calculated using the following formulas: CT = 3400D 2/3 for CO, and CT 33.3D for the other air pollutants (whe re D distance to shore in miles)? x

Do your emission calculations include any emission reduction measures or

modified emission factors? X*

Are your proposed exploration activities located east of 87.5° W longitude? x Do you expect to encounter H 2 S at concentrations greater than 20 parts per million (ppm)? x

Do you propose to flare or vent natural gas for more than 48 continuous hours From any proposed well? x

Do you propose to burn produced hydrocarbon liquids? x

*This plan includes fuel tracking reductions.

B. If you answer no to all of the above screening questions from the appropriate table, provide:

1) Summary information regarding the peak year emissions for both Plan Emissions and Complex Total Emissions, if applicable. This information is compiled on the summary form of the two sets of worksheets. You can submit either these summary forms or use the format below. You

do not need to include the entire set of worksheets.

Air Pollutant Plan Emission

Amounts (tons) Calculated

E xemption

Amounts (tons) Calculated

Complex Total

Emission

Amounts (tons)

PM

SO
x NOx

VOC

CO

2) Contact: Tracy Albert, 504.425.4652

, tracy.albert@shell.com

(1) Worksheets

Worksheets included. Shell is providing the Excel worksheet on the Proprietary CD for your review.COMPANY Shell Offshore Inc.

AREA Mississippi Canyon

BLOCK 943

LEASE OCS

- G 34467

PLATFORM Dynamically Positioned MODU

WELL A, B, C, D

COMPANY

CONTACT Jeff McMenis

TELEPHONE NO. 504

- 425

- 6021

REMARKS SEPCO Env File Name

- PowerNap_AQR_DPMODU_031114.xlsxCOMPANY AREA BLOCK LEASE PLATFORM WELL

Shell Offshore

Inc. Mississippi

Canyon 943 OCS

- G 34467 Dynamically Positioned
MODU A, B, C, D

Emitted Substance

Year

PM SOx NOx VOC CO

2014 43.60 26. 0 9 1477.24 44.32 322.85

2015

- 2017 44.52 26.62 1508.76 45.27 329.73

2018 3.32 2.99 92.43 2.78 20.71

Allowable 2164.50 2164.50 2164.50 2164.50 54965.20

Notes:

1

- Emissions for Calendar

- Years 2014, 2015, 2016, and 2017 account for reduced fuel usage. CY2018 activity accounts for only 4 days of operation and fuel reduction measures are not necessary to stay below the relevant BOEM exemption amounts.SECTION 9: OIL SPILL INFORMATION

A. Oil Spill Response Planning

All the proposed activities and facilities in this EP will be covered by the Regional OSRP filed by Shell Offshore Inc. (0689) in accordance with 30 CFR 550 and 254. Shell’s Regional OSRP was approved by BSEE on April 11, 2013.

Spill Response sites are as follows:

Primary Response Equipment Locations Preplanned Staging Location(s)
Venice, LA; Ft Jackson, LA; Harvey, LA; Stennis, MS; Pascagoula, MS Venice, LA; Pacagouls, MS ; Mobile, AL

Table 9.1

–

Response Equipment and Staging Areas

The names of the OSRO’s under contract include Clean Gulf Associates (CGA), Marine Spill Response Company (MSRC), Clean Caribbean America (CCA) and OSRL/EARL.

Category Regional OSRP EP

Type of Activity Subsea Drilling Exploratory Drilling

Facility Location (area/block) MC 391 MC 943

Facility Designation Subsea well 1 ◊ Subsea well A

Distance to Nearest Shoreline (miles) 70 65

Volume
Storage tanks (total)
Flowlines (on facility)
Pipelines
Uncontrolled blowout (volume per day)

Total Volume N/A
N/A
N/A
416,414* BOPD
416,414 Bbls N/A
N/A
N/A

175 ,000** BOPD

175 ,000 Bbls

Type of Oil(s)

- (crude oil, condensate, diesel) Crude oil Crude oil

API Gravity(s) 26o 2 8 o

*24 hour rate (3 91 ,808 BOPD 30 day average) **24 hour rate ( 165 ,000 BOPD 30 day average)

◊ This well was reviewed and accepted by BOEM in Plan S-7444 (May 2011) and corrected by BSEE on July 10, 2012 during the drilling of the well. The 30-day average was updated in OSRP in July 2012.

Since Shell Offshore Inc. has the capability to respond to the appropriate worst-case spill scenario included in its regional OSRP, approved by BSEE on April 11, 2013, and since the worst-case scenario determined for our Plan does not replace the appropriate worst-case scenario in our regional OSRP, I hereby certify that Shell Offshore Inc. has the capability to respond, to the maximum extent practicable, to a worst-case discharge, or a substantial threat of such a discharge, resulting from the activities proposed in our EP.

Modeling: Shell did not model a potential oil or hazardous substance spill for operations proposed in this plan.B. Oil Spill Response Discussion

1. Volume of the Worst Case Discharge
Please refer to Section 2j and 9(iv) of this EP

.

2. Trajectory Analysis

Trajectories of a spill and the probability of it impacting a land segment have been projected utilizing information in the B SE E Oil Spill Risk Analysis Model (OSRAM) for the Central and Western

Gulf of Mexico available on the B SE E website using 30 day impact. Offshore areas along the trajectory between the source and land segment contact could be impacted. The land segment contact probabilities are shown in Table 9.C.1.

Area/Block OCS

- G Launch

Area Land Segment Contact %

Exploratory

MC 943 34467 58 Galveston, TX 1
Jefferson, TX 1
Cameron, LA 3
Vermilion, LA 2
Iberia, LA 1
Terrebonne, LA 3
Lafourche, LA 3
Jefferson, LA 1
Plaquemines, LA 8
St. Bernard, LA 1 Okaloosa, FL 1

Table 9.C.1 Probability of Land Segment Impact C. Resource Identification

The locations identified in Table 9.C.1 are the highest probable land segments to be impacted using the BOEMRE Oil Spill Risk Analysis Model (OSRAM). The environmental sensitivities are identified using the appropriate National Oceanic and Atmospheric Administration (NOAA) Environmental Sensitivity Index (ESI) maps for the given land segment. ESI maps provide a concise summary of coastal resources that are at risk if an oil spill occurs nearby. Examples of at-risk resources include biological resources (such as birds and shellfish beds), sensitive shorelines (such as marshes and tidal flats), and human-use resources (such as public beaches and parks).

In the event an oil spill occurs, ESI maps can help responders meet one of the main response objectives: reducing the environmental consequences of the spill and the cleanup efforts. Additionally, ESI maps can be used by planners to identify vulnerable locations, establish protection priorities, and identify cleanup strategies.

The following is a list of resources of special economic or environmental importance that potentially could be impacted by the Mississippi Canyon 943 WCD scenario.Onshore/Nearshore: Plaquemines Parish has been identified as the most probable impacted

Parish within the Gulf of Mexico for the Greater than 10 Mile Worst Case Discharge and the Exploratory Worst Case Discharge. Plaquemines Parish has a total area of 2,429 square miles of which, 845 square miles of it is land and 1,584 square miles is water. Plaquemines Parish includes two National Wildlife Refuges: Breton National Wildlife Refuge and Delta National Wildlife Refuge. This area is also a nesting ground for the brown pelican, an endangered species. Examples of Environmental Sensitivity maps for Plaquemines Parish are detailed in the following pages. Example ESI maps for Plaquemines Parish and the legend are shown in Figures 9.C.1through 9.C.5.

Offshore: An offshore spill may require an Essential Fishing Habitat (EFH) Assessment. This assessment would include a description of the spill, analysis of the potential adverse effects on EFH and the managed species; conclusions regarding the effects on the EFH; and proposed mitigation, if applicable.

Significant pre-planning of joint response efforts was undertaken in response to provisions of the National Contingency Plan (NCP). Area Contingency Plans (ACPs) were developed to provide a well coordinated response to oil discharges and other hazardous releases. The One Gulf Plan is specific to the Gulf of Mexico to advance the unity of policy and effort in each of the Gulf Coast ACPs. Strategies used for the response to an oil spill regarding protection of identified resources are

detailed in the One Gulf Plan and relevant Gulf Coast ACP.

D. Worst Case Discharge Response

Shell will make every effort to respond to the MC 943 Worst Case Discharge as effectively as possible. Below is a table outlining the applicable evaporation and surface dispersion quantity:

Mississippi Canyon Block 943 Calculations

(BBLS)



### i. TOTAL WCD (based on 30 day average (per day)) ~165,000



### ii. Loss of volume of oil to natural surface dispersion and evaporation base (approximate bbls per day)*

(10% Natural surface evaporation and dispersion in 24 hrs) - 16,500

TOTAL REMAINING ~148,500

* As this scenario involves a surface blowout onboard the platform, an ADIOS 2 Model was ran to account for surface dispersion and evaporation.

Table 9.D.1 Oil Remaining After Subsurface and Surface Dispersion

Shell has contracted OSROs to provide equipment, personnel, materials and support vessels as well as temporary storage equipment to be considered in order to cope with a WCD spill. Under adverse weather conditions, major response vessels and Transrec skimmers are still effective and safe in sea states of 6-8 ft. If sea conditions prohibit safe mechanical recovery efforts, then natural dispersion and airborne chemical dispersant application (visibility & wind conditions permitting) may be the only safe and viable recovery option.

MSRC OSRV 8 foot seas VOSS System 4 foot seas Expandi Boom 6 foot seas, 20 knot winds Dispersants Winds more than 25 knots, Visibility less than 3 nautical miles, or Ceiling less than 1,000 feet.

Table 9.D.2 Operational Limitations of Response EquipmentUpon notification of the spill, Shell would request a partial or full mobilization of contracted

resources, including, but not limited to, skimming vessels, oil storage vessels, dispersant aircraft, subsea dispersant, shoreline protection, wildlife protection, and containment equipment. Following is a list of the contracted resources including de-rated recovery capacity, personnel, and estimated response times (procurement, load out, travel time to the site, and deployment). The Incident Commander or designee may contact other service companies if the Unified Command deems such services necessary to the response efforts.

Based on the anticipated worst case discharge scenario, Shell can be onsite with dedicated, contracted on water oil spill recovery equipment with adequate response capacity to contain and recover surface oil, and prevent land impact, within 34 hours (based on the equipment’s Estimated Daily Response Capacity (EDRC)). Shell will continue to ramp up additional on-water mechanical recovery resources as well as apply dispersants and in-situ burning as needed and as approved under the supervision of the USCG Captain of the Port (COTP) and the Regional Response Team (RRT).

Subsea Control and Containment: Shell, as a founding member of the MWCC, will have access to the IRCS that can be rapidly deployed through the MWCC. The IRCS is designed to contain oil flow in the unlikely event of an underwater well blowout, and is designed, constructed, tested, and

ava ilable for rapid response. Shell’s specific containment response for MC 943 will be addressed in
Shell’s NTL 2010-N10 submission at the time the APD is submitted.

Table 9.D.9 Control, Containment, and Subsea Dispersant Package Activation List

Mechanical Recovery (skimming): Response strategies include skimming utilizing available OSROs Oil Spill Response Vessels (OSRVs), Oil Spill Response Barges (OSRBs), ID Boats, and Quick Strike OSRVs. There is a combined de-rated recovery rate capability of approximately 529,000 barrels/day. Temporary storage associated with the identified skimming and temporary storage equipment equals approximately 317,000 barrels.

De

- rated Recovery Rate (bopd) Storage (bbls) Offshore Recovery and Storage 295,339 305,285 Nearshore Recovery and Storage 233,856 12,516

Total 529,195 317,801

Table 9.D.3 Mechanical Recovery Combined De-Rated Capability

Table 9.D.4 Offshore On-Water Recovery and Storage Activation List Table 9.D.5 Nearshore On-Water Recovery and Storage Activation List

Oil Storage: The strategy for transferring, storing and disposing of oil collected in these recovery zones is to utilize two 150,000-160,000 ton (dead weight) tankers mobilized by Shell (or any other tanker immediately available). The recov ered oil would be transferred to Motiva’s Norco, LA storage and refining facility, or would be stored at Delta Commodities, Inc. Harvey, LA facility.

Aerial Surveillance: Aircraft can be mobilized to detect, monitor, and target response to oil spills. Aircraft and spotters can be mobilized within hours of an event.

Table 9.D.6 Aerial Surveillance Activation List

Aerial Dispersant: Depending on proximity to shore and water depth, dispersants may be a viable response option. If appropriate and approved, 4 to 5 sorties from three DC- 3’s can be made within the first 12 hour operating day of the response. These aerial systems could disperse approximately 7,704 to 9,630 barrels of oil per day. Additionally, 3 to 4 sorties from the BE90 King Air and 3 to 4 sorties from the Hercules C-130A within the first 12 hour operating day of the response could disperse 4,600 to 6,100 barrels of oil pe r day. For continuing dispersant operations, the CCA’s Aerial Dispersant Delivery System (ADDS) would be mobilized. The ADDS has a dispersant spray capability of 5,000 gallons per sortie.Table 9.D.7 Offshore Aerial Dispersant Activation List

Vessel Dispersant: Vessel dispersant application is another available response option. If appropriate, vessel spray systems can be installed on offshore vessels of opportunity using inductor nozzles (installed on fire-water monitors), skid mounted systems, or purpose-built boom arm spray systems. Vessels can apply dispersant within the first 12-24 hours of the response and continually as

directed.

Table 9.D.8 Offshore Boat Spray Dispersant Activation List

Subsea Dispersant: Shell has contracted with MWCC and Wild Well Control for a subsea dispersant packages. Subsea dispersant application has been found to be highly effective at reducing the amount of oil reaching the surface. Additional data collection, laboratory tests and field tests will help in facilitating the optimal application rate and effectiveness numbers. For planning purposes, the se system has the potential to disperse approximately 24,500 to 34,000 barrels of oil per day.

Table 9.D.9 Control, Containment, and Subsea Dispersant Package Activation List

In -Situ Burning: Open-water in-situ burning (ISB) also may be used as a response strategy, depending on the circumstances of the release. ISB services may be provided by the primary OSRO contractors. If appropriate conditions exist and approvals are granted, one or multiple ISB task forces could be deployed offshore. Task forces typically consist of two to four fire teams, each withtwo vessels capable of towing fire boom, guide boom or tow line with either a handheld or aeriallydeployed oil ignition system. At least one support/safety boat would be present during active burning operations to provide logistics, safety and monitoring support. Depending upon a number of factors, up to 4 burns per 12-hour day could be completed per ISB fire team. Most fire boom systems can be used for approximately 8-12 burns before being replaced. Fire intensity and weather will be the main determining factors for actual burns per system. Although the actual amount of oil that will be removed per burn is dependent on many factors, recent data suggests that a typical burn might eliminate approximately 750 barrels. For planning purposes and based on the above assumptions, a single task force of four fire teams with the appropriate weather and safety conditions could complete four burns per day and remove up to ~12,000 bbls/day. In-situ burning nearshore and along shorelines may be a possible option based on several conditions and with appropriate approvals, as outlined in Section 19, In-situ Burn Plan (OSRP). In-situ burning along certain types of shorelines may be used to minimize physical damage where access is limited or if it is determined that mechanical/manual removal may cause a substantial negative impact on the environment. All safety considerations will be evaluated. In addition, Shell will assess the situation and can make notification within 48 hours of the initial spill to begin ramping up fire boom production through contracted OSRO(s). There are potential limitations that need to be assessed prior to ISB operations. Some limitations include atmospheric and sea conditions; oil weathering; air quality impacts; safety of response workers; and risk of secondary fires.

Table 9.D.10 In -Situ Burn Equipment Activation List

Shoreline Protection: If the spill went unabated, shoreline impact in Plaquemines Parish, LA would depend upon existing environmental conditions. Nearshore response may include the deployment of shoreline boom on beach areas, or protection and sorbent boom on vegetated areas. Strategies would be based upon surveillance and real time trajectories provided by The Response Group that depict areas of potential impact given actual sea and weather conditions. Strategies from the New Orleans, Louisiana Area Contingency Plan, Unified Command would be consulted to ensure that environmental and special economic resources would be correctly identified and prioritized to ensure optimal protection. Shell has access to shoreline response guides that depict the protection response modes applicable for oil spill clean-up operations. Each response mode is schematically represented to show optimum deployment and operation of the equipment in areas of environmental concern. Supervisory personnel have the option to modify the deployment and operation of equipment allowing a more effective response to site-specific circumstances.

Table 9.D.11 Shoreline Protection and Wildlife Support ListWildlife Protection: If wildlife is threatened due to a spill, the contracted OSRO’s have resources

available to Shell, which can be utilized to protect and/or rehabilitate wildlife. The resources under contract for the protection and rehabilitation of affected wildlife are in Table 9.D.11.

New or unusual technology in regards to spill, prevention, control and clean-up: Shell will use our normal well design and construction processes with multiple barrier approach as well as new stipulations mandated by NTL 05. Response techniques will utilize new learnings from Macondo response to include in-situ burning and subsea dispersant application. Mechanical recovery advancements are continuing to be made to incorporate utilization of Koseq arms outfitted on barges, conversion of Platform Support Vessels for Oil Spill Response, and inclusion of nighttime spill detection radar to improve tracking capabilities (X-Band radar, Infrared sensing, etc.). In addition, new response technologies/techniques are continuing to be considered by Shell and the appropriate government organizations for incorporation into our planned response. Any additional response technologies/techniques presented at the time of response will be used at the discretion of

the Unified Command and USCG.Figure 9.C.1 Environmental Sensitivity Index Map LegendFigure 9.C.2 South Pass ESI MapFigure 9.C.3 Garden Island Pass ESI Map.

Figure 9.C.4 Pass a Loutre West ESI MapFigure 9.C.5 Main Pass ESI MapTable 9.D.4 Offshore On-Water Recovery and Storage Activation ListTable 9.D.4 Offshore On-Water Recovery and Storage Activation List (continued)Table 9.D.4 Offshore On-Water Recovery and Storage Activation List (continued)Table 9.D.5 Nearshore On-Water Recovery Activation ListTable 9.D.5 Nearshore On-Water Recovery Activation List (continued)Table 9.D.5 Nearshore On-Water Recovery Activation List (continued)Table 9.D.5 Nearshore On-Water Recovery Activation List (continued)

Table 9.D.6 Aerial Surveillance Activation ListTable 9.D.7 Offshore Aerial Dispersant Activation ListTable 9.D.7 Offshore Aerial Dispersant Activation List (continued)

Table 9.D.8 Offshore Boat Spray Dispersant Activation ListTable 9.D.9 Control, Containment, and Subsea Dispersant Package Activation ListTable 9.D.10 In-Situ Burn Equipment Activation ListTable 9.D.10 In -Situ Burn Equipment Activation List (continued)Table 9.D.10 In-Situ Burn Equipment Activation List (continued)Table 9.D.10 In-Situ Burn Equipment Activation List (continued)Table 9.D.10 In-Situ Burn Equipment Activation List (continued)Table 9.D.11 Shoreline Protection and Wildlife Support ListTable 9.D.11 Shoreline Protection and Wildlife Support List (continued)Table 9.D.11 Shoreline Protection and Wildlife Support List (continued)Table 9.D.11 Shoreline Protection and Wildlife Support List (continued)SECTION 10 : ENVIRONMENTAL MONITORING INFORMATION

A. Monitoring Systems

A rig based Acoustic Doppler Current Profiler (ADCP) is used to continuously monitor the current beneath the rig. Metocean conditions such as sea states, wind speed, ocean currents, etc. will also be continuously monitored. Shell will comply with NTL 2009-G02.

B. Incidental Takes

No incidental takes are anticipated. Although marine mammals may be seen in the area, Shell does not believe that its operations proposed under this EP will result Shell implements the mitigation measures and monitors for incidental takes of protected species according to the following notices to lessees and operators from the BOEM/BSEE:

NTL 2012- BS EE -G01 “Marine Trash and Debris Awareness and Elimination”

NTL 2012-Joint-G01 “Vessel Strike Avoidance and Injured/Dead Protected Species Reporting”

NTL 2012-Joint-G02 “Implementation of Seismic Survey Mitigation Measures & Protected Species

Observer Program”

C. Flower Garden Banks National Marine Sanctuary

The operations proposed in this plan will not be conducted within the Protective Zones of the Flower Garden

Banks and Stetson Bank.SECTION 11 : LEASE STIPULATIONS INFORMATION

OCS- G 34467, MC 943, was part of Lease Sale #222 held on June 20, 2012. The lease has an expected expiration date of October 31, 2019. The lease is owned by Anadarko US Offshore Corporation (50%) and Shell Offshore Inc. (50%) and Shell is designated operator. The lease is not a part of any Biological Sensitive Area, Military Warning Area, high Archeological probability area, or Shipping Fairway.

Lease Stipulation No. 8, Protected Species, is applicable to this lease and is addressed in the following sections of this plan:

Section 6h, Threatened or endangered species, critical habitat, and marine mammal information Section 10b, Environmental Monitoring Information, Incidental takes Section 12b, Environmental Mitigation Measures Information, Incidental takes Section 18, Environmental Impact Assessment

SECTION 12 : ENVIRONMENTAL MITIGATION MEASURE INFORMATION

 Impacts to Marine and coastal environments

The proposed action will implement mitigation measures required by laws and regulations, including all applicable Federal & State requirements concerning air emissions, discharges to water and solid waste disposal, as well as any additional permit requirements and Shell policies. Project activities will be conducted in accordance with the Regional OSRP. Section 18 of this plan discusses impacts and mitigation measures, including Coastal Habitats and

Protected Areas.

 Incidental Takes

We do not anticipate any incidental takes related to the proposed operations. Shell implements the mitigation measures and monitors for incidental takes of protected species according to the following notices to lessees and operators from the BOEM/BSEE:

NTL 2012-BSEE-G01 “Marine Trash and Debris Awareness and Elimination”

NTL 2012-Joint-G01 “Vessel Strike Avoidance and Injured/Dead Protected Species Reporting”

NTL 2012-Joint-G02 “ NTL 2012

- Joint

- G02 “Implementation of Seismic Survey Mitigation Measures & Protected Species Observer Program”

SECTION 13 : RELATED FACILITIES AND OPERATIONS INFORMATION

Information regarding Related Facilities and Operations Information, transportation systems, & produced liquid hydrocarbon transportation vessels are not included in this EP as such information is only necessary in the case of

DOCDs.SECTION 14 : SUPPORT VESSELS AND AIRCRAFT INFORMATION

A. General

Type Maximum Fuel Tank

Storage Capacity ( Gals ) Maximum No. In Area at Any Time Trip Frequency or

Duration

Crew Boats 8,000 1 Twice per week Offshore Support Vessels 120,000 2 Twice per week Helicopter 760 1 Once per day

B. Diesel Oil Supply Vessels

Size of Fuel Supply

Vessel Capacity of Fuel Supply

Vessel Frequency of Fuel

Transfers Route Fuel Supply Vessel Will

Take

280 foot length 100,000 gals 1 week Port Fourchon to MC 943

C. Drilling Fluids Transportation

According to NTL 2008-G04, this information in only required when activities are proposed in the State

of Florida.

D. Solid and Liquid Wastes Transportation

See Section 7, Table 7B.

E. Vicinity Map

See Attachment 14A for Vicinity Map.Attachment 14A

– Vicinity MapSECTION 15 : ONSHORE SUPPORT FACILITIES INFORMATION

A. General

Name Location Existing/New/Modified

Boothville PHI Heliport Boothville, LA Existing

C

- Port II Fourchon, LA Existing

The existing onshore support base for air transportation will be PHI Heliport in Boothville, LA located at 38963 Highway 23. The existing onshore base for installation water traffic will be the C-Port II located at Port Fourchon Terminal located on Bayou LaFourche, south of Leeville, LA approximately three miles from the Gulf

of Mexico.

B. Support Base Construction or Expansion

This section does not apply to this EP as Shell does not plan to construct a new onshore support base or expand an existing one to accommodate the activities proposed in this EP.

C. Support Base Construction or Expansion Timetable

This Section does not apply to this EP as Shell does not plan to construct a new onshore support base or expand an existing one to accommodate the activities proposed in this EP.

D. Waste Disposal

See Table 7B.

SECTION 16 : SULPHUR OPERATIONS INFORMATION

Information regarding Sulfur Operations Information is not included in this EP as such information is only necessary in the case of DOCDs.SECTION 17 : COASTAL ZONE MANAGEMENT ACT (CZMA) INFORMATION

LOUISIANA

COASTAL ZONE MANAGEMENT

CONSISTENCY CERTIFICATION

INITIAL EXPLORATION PLAN Type of Plan

MISSISSIPPI CANYON BLOCK 9 43

OCS- G 34467

The proposed activities described in detail in this Plan will comply with Louisiana's State and Local Coastal Resources Management Act of 1978, Coastal Resources Program, and Coastal Area Management Enforceable

Policies.

We have considered all of Louisiana's Enforceable Policies in making this certification of consistency.

SHELL OFFSHORE INC.

Operator

_____________________________________________

Sylvia A. Bellone Certifying Official

0 3 / 18 /201 4

DateMISSISSIPPI

COASTAL ZONE MANAGEMENT

CONSISTENCY CERTIFICATION

INITIAL EXPLORATION PLAN Type of Plan

MISSISSIPPI CANYON BLOCK 943

OCS-G 34467

The proposed activities described in detail in this Plan will comply with Mississippi’s approved Coastal Resources Program and Coastal Area Management Program Policies.

We have considered all of Mississippi’s Enforceable Policies in making this certification of consistency.

SHELL OFFSHORE INC.

Operator

_____________________________________________

Sylvia A. Bellone Certifying Official

3/18/2014

_____________________________________________ DateCoastal Zone Management Consistency Information

For the State of Mississippi

Goal 1. To provide for reasonable industrial expansion in the Coastal Area and to insure the efficient utilization of waterfront industrial sites so that suitable sites are conserved for the water dependent industry.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 2. To favor the preservation of the coastal wetlands and ecosystems, except where a specific alternation of specific coastal wetlands would serve a higher public interest in compliance with the public purposes of the public

trust in which the coastal wetlands are held.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 3. To protect, propagate, and conserve the State’s seafood and aquatic life in connection with the revitalization, and conserve the State’s seafood and aquatic life in connection with the revitalization of the seafloor industry of the State of Mississippi.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 4. To conserve the air and waters of the State, and to protect, maintain and improve the quality thereof for public use, for the prorogation of wildlife, fish and aquatic life, and for domestic, agricultural, industrial, recreational and other legitimate beneficial uses.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 5. To put the benefit use to the fullest extent of which they are capable to water resources of the State, and to prevent the waste, unreasonable use, or unreasonable method of use of water.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 6. To preserve the State’s historical and archaeological resources, to prevent their destruction, and to enhance these resources whenever possible.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 7. To encourage the preservation of natural scenic qualities in the coastal area.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.

Goal 8. To assist local government in the provision of public facilities services in a manner consistent with the coastal program.

The proposed activities are located in OCS Federal Waters, Gulf of Mexico, approximately 65 miles from the nearest Louisiana shoreline. Shell will utilize existing facilities in Fourchon, Louisiana; therefore, there should not be any adverse impacts to the Mississippi coastal areas.SECTION 18: ENVIRONMENTAL IMPACT ANALYSIS (EIA)

Environmental Impact Analysis

INITIAL EXPLORATION PLAN Mississippi Canyon Block 943 (OCS -G 34467)

Offshore Louisiana

March 2014

Prepared for:

Shell Offshore Inc.

P.O. Box 61933 New Orleans, Louisiana 70161 Telephone: (504) 425-6021

Prepared by:

CSA Ocean Sciences Inc.

8502 SW Kansas Avenue Stuart, Florida 34997 Telephone: (772) 219-3000

# Acronyms and Abbreviations

AUV autonomous underwater vehicle ADIOS Automated Data Inquiry for Oil Spills

bbl barrel
BOEM Bureau of Ocean Energy Management
BOEMRE Bureau of Ocean Energy Management,

Regulation and Enforcement
BOP blowout preventer BOPD barrels of oil per day (bbl/d)
BSEE Bureau of Safety and Environmental

Enforcement
C&C C&C Technologies, Inc.

CH 4 methane

CO carbon monoxide

CO 2 carbon dioxide

DP dynamically positioned
DPS distinct population segment

EFH Essential Fish Habitat
EIA Environmental Impact Analysis
EIS Environmental Impact Statement

EP Exploration Plan
ESA Endangered Species Act

FAD fish-attracting device

FR Federal Register
GEMS Geoscience Earth and Marine Services,

Inc. GMFMC Gulf of Mexico Fishery Management

Council

H 2 S hydrogen sulfide

HAPC Habitat Area of Particular Concern

IPF impact-producing factor

MARPOL International Convention for the

Prevention of Pollution from Ships

MC Mississippi Canyon

MMC Marine Mammal Commission

MMPA Marine Mammal Protection Act MMS Minerals Management Service
MWCC Marine Well Containment Company
NAAQS National Ambient Air Quality Standards
NEPA National Environmental Policy Act

NMFS National Marine Fisheries Service
NOAA National Oceanic and Atmospheric

Administration

NO

x nitrogen oxides
NPDES National Pollutant Discharge Elimination

System

NRC National Research Council
NTL Notice to Lessees and Operators
NWR National Wildlife Refuge

OCS Outer Continental Shelf

OCSLA Outer Continental Shelf Lands Act
OSAT Operational Science Advisory Team
OSRA Oil Spill Risk Analysis
OSRP Oil Spill Response Plan
PAH polycyclic aromatic hydrocarbons

PM particulate matter
ROV remotely operated vehicle

SBM synthetic-based mud
SEA Site-Specific Environmental Assessment

Shell Shell Offshore Inc.

SO

x sulfur oxides
SWIM Surface Water Improvement and

Management UME Unusual Mortality Event

USCG U.S. Coast Guard
USDOI U.S. Department of the Interior
USEPA U.S. Environmental Protection Agency

USFWS U.S. Fish and Wildlife Service
VOC volatile organic compound
WCD worst case discharge WMA Wildlife Management AreaINTRODUCTION

Project Summary

Shell Offshore Inc. (Shell) is submitting an Initial Exploration Plan (EP) for Mississippi Canyon Block 943 (MC 943) for four (4) exploration wells to be drilled using either a dynamically positioned (DP) drillship or DP semisubmersible drilling rig. This EP is for proposed well locations A, B, C, and D. All surface hole locations will be in MC 943, in the Central Planning Area of the

Gulf of Mexico.

The lease area is 65 miles (105 km) from the nearest shoreline (Louisiana), 106 miles (171 km) from the onshore support base at Port Fourchon, Louisiana, and 89 miles (143 km) from the helicopter base at Boothville, Louisiana. All miles in this Environmental Impact Analysis (EIA) are statute miles. Water depths at the wellsites range from approximately 4,211 to 4,276 ft (1,284 to 1,303 m).

The following types of exploratory drilling rigs are available for this project:

 Noble Don Taylor or a similar DP drillship; and

 Noble Jim Day

or a similar DP semisubmersible rig.

The EIA is structured to address environmental impacts from both types of drilling rigs. Spudding for the proposed wells is scheduled for July 1, 2014, with an estimated timeline of

187 days per well and one well drilled each year.

Purpose of the EIA

This EIA was prepared pursuant to the requirements of the Outer Continental Shelf Lands Act (OCSLA), 43 U.S.C. §§ 1331-1356, as well as regulations including 30 CFR 550.212(o) and 550.227. The EIA is a project- and site- specific analysis of Shell’s planned activities under this

EP 1 . The EIA presents data, analyses, and conclusions to support BOEM reviews as required by the National Environmental Policy Act (NEPA) and other relevant federal laws, including the Endangered Species Act (ESA) and Marine Mammal Protection Act (MMPA). It also identifies some of the mitigation measures Shell will implement in connection with the planned activities.

The EIA is a project-specific analysis that focuses on the impacts of a specific plan. This EIA addresses the impact-producing factors (IPFs), resources, and impacts associated with the activities proposed in this EP. The EIA also analyzes the potential environmental impacts of the revised blowout scenario and worst case discharge (WCD) information.

BOEM has performed numerous environmental evaluations of oil and gas activities on the Gulf of Mexico Outer Continental Shelf (OCS). Potential impacts were analyzed at a broader level in the

1 On October 1, 2011, the Bureau of Ocean Energy Management, Regulation and Enforcement (BOEMRE)
reorganized into two separate agencies: Bureau of Ocean Energy Management (BOEM) and Bureau of Safety and Environmental Enforcement (BSEE). Shell understands that BOEM will review this EIA and prepare a Site-Specific
Environmental Assessment (SEA) for the project. This EIA complies with guidance provided in existing Notices to Lessees and Operators (NTLs) issued by the former Minerals Management Service ( MMS ) and BOEMRE, including
NTL 2008-G04 (recently extended by NTL 2014-G03). Throughout this EIA, when existing guidance and general agency activities are referred to, “BOEM” is mea nt to subsume the former agencies and to represent the continuous regulatory entity now called BOEM. The former agency names (MMS and BOEMRE) are used when
referring to particular historical documents published under those names. In addition, until NTLs are reissued
under BOEM or BSEE, the EIA will refer to the former BOEMRE as BOEM when addressing NTLs issued by BOEMRE

or MMS.Programmatic Environmental Impact Statements (EISs) for the OCS Oil and Gas Leasing Program (MMS, 2007a; BOEM 2012a) and in lease sale EISs for the Western and Central Gulf of Mexico Planning Areas (MMS, 2007b; BOEM, 2012b,c, 2013).

These studies generated critical data and advanced the large body of existing knowledge on the Gulf of Mexico OCS. They analyze potential impacts on the natural environment, the socioeconomic effects of exploration and development activities, and other regional resources. Numerous technical studies address the likely trajectory of spilled oil, the effects of underwater noise on threatened and endangered species, and other IPFs. The studies inform agency decision-making on lease offerings, mitigation measures and lease stipulations, operational requirements, and permit restrictions. This substantial body of work, which in part, forms the basis for the evaluation presented here, will allow the BOEM and other regulatory agencies to evaluate Shell’s EP and ensure that oil and gas exploration and development activities are performed in an environmentally sound manner, with minimal impacts on the environment. Shell has incorporated these comprehensive environmental analyses by reference and built on them with project- and site-specific analyses, where applicable.

OCS Regulatory Framework

The regulatory framework for OCS activities in the Gulf of Mexico was summarized in MMS (2010) and BOEM (2012b). Under the OCSLA, the U.S. Department of the Interior (USDOI) is responsible for the administration of mineral exploration and development of the OCS. Within the USDOI, BOEM and BSEE are charged with the responsibility of managing and regulating the development of OCS oil and gas resources in accordance with the provisions of the OCSLA. The BSEE offshore regulations are in 30 CFR Chapter II, Subchapter B. BOEM offshore regulations

are in 30 CFR Chapter V, Subchapter B.

In implementing its responsibilities under the OCSLA and NEPA, the BOEM consults numerous federal departments and agencies that have authority to govern and maintain ocean resources pursuant to other federal laws. Among these are the U.S. Coast Guard (USCG), U.S. Environmental Protection Agency (USEPA), U.S. Fish and Wildlife Service (USFWS), and the National Oceanic and Atmospheric Administration (NOAA) through the National Marine Fisheries Service (NMFS). Federal regulations establish consultation and coordination processes with federal, state, and local agencies (e.g., the ESA, MMPA, Coastal Zone Management Act of 1972, and the Magnuson-Stevens Fishery Conservation and Management Act).

NTLs are formal documents issued by the BOEM and BSEE that provide clarification, description, or interpretation of a regulation or standard. Table 1 lists and summarizes the NTLs applicable

to this EIA.

### Table 1. Notices to Lessees and Operators (NTLs) that are applicable to this Environmental Impact Analysis (EIA).

NTL Title Summary

2014

- G03 Extension of Prior Notices to Lessees Extends the effective date of NTL 2008

- G04 (and two other NTLs) until

June 30, 2014.

BSEE

2012

- N06 Guidance to Owners and Operators of

Offshore Facilities Seaward of the

Coast Line Concerning Regional Oil
Spill Response Plans Provides clarification, guidance, and information for preparation of regional
Oil Spill Response Plans. Recommends description of response strategy for
WCD scenarios to ensure capability to respond to oil discharges is both

efficient and effective.

2012

- JOINT

- G01 Vessel Strike Avoidance and

Injured/Dead Protected Species
Reporting Recommends protected species identification training; recommends that
vessel operators and crews maintain a vigilant watch for marine mammals
and slow down or stop their vessel to avoid striking protected species; and
requires operators to report sightings of any injured or dead protected
species.

2012

- BSEE

- G01 Marine Trash and Debris Awareness

and Elimination Instructs operators to exercise caution in the handling and disposal of small
items and packaging materials; requires the posting of placards at prominent

locations on offshore vessels and structures; and mandates a yearly marine
trash and debris awareness training and certification process.

2011

- JOINT

- G01 Revisions to the List of OCS Blocks

Requiring Archaeological Resource
Surveys and Reports Provides new information on which Outer Continental Shelf (OCS) blocks
require archaeological surveys and reports and line spacing required in each
block. This NTL augments NTL 2005

- G07.

2010

- N10 Statement of Compliance with

Applicable Regulations and Evaluation
of Information Demonstrating Adequate
Spill Response and Well Containment

Resources Informs operators using subsea blowout preventers (BOPs) or surface BOPs
on floating facilities that applications for well permits must include a
statement signed by an authorized company official stating that the operator

will conduct all activities in compliance with all applicable regulations,
including the increased safety measures regulations (75 Federal Register
[ FR ] 63346). Informs operators that the BOEM will be evaluating whether
each operator has submitted adequate inf ormation demonstrating that it has
access to and can deploy containment resources to promptly respond to a

blowout or other loss of well control.

2010

- N06 Information Requirements for

Exploration Plans, Development and
Production Plans, and Development
Op erations Coordination Documents on

the OCS Rescinds the limitations set forth in NTL 2008

- G04 regarding a blowout
scenario and WCD scenario, and provides guidance regarding the
information required in blowout scenario and WCD scenario descriptions.

2009

- G 40 Deepwater Benthic Communities Guidance for avoiding and protecting high

- density deepwater benthic
communities (including chemosynthetic and deepwater coral communities)
from damage caused by OCS oil and gas activities in water depths greater

than 984 ft (300 m). Prescribes separation distances of 2,000 ft (610 m) from
each mud and cuttings discharge location and 250 ft (76 m) from all other

seafloor disturbances.

2009

- G39 Biologically Sensitive Underwater

Features and Areas Guidance for avoiding and pr otecting biologically sensitive features and
areas (i.e., topographic features, pinnacles, low

- relief live bottom areas, and
other potentially sensitive biological features) when conducting OCS
operations in water depths less than 984 ft (300 m) in the Gul f of Mexico.

2008

- G04 Information Requirements for

Exploration Plans and Development
Operations Coordination Documents Guidance on the information requirements for OCS plans, including

EIA requirements and information regarding compliance with the provisions
of the Endangered Species Act and Marine Mammal Protection Act.

2005

- G07 Archaeological Resource Surveys and

Reports Provides guidance on regulations regarding archaeological discoveries,
specifies requirements for archaeological resource surve ys and reports, and
outlines options for protecting archaeological resources.

## Oil Spill Prevention and Contingency Planning

Shell’s Gulf of Mexico Regional Oil Spill Response Plan (OSRP) approved by BSEE is a fundamental component of the planned drillin g program that certifies Shell’s capability to respond to the maximum extent practicable to a WCD (30 CFR 254.2) (see EP Section 9 ). The OSRP demonstrates Shell’s capabilities to rapidly and effectively manage oil spills that may result from drilling operations. Despite the extremely low likelihood of a large oil spill occurring during the project, Shell has designed its response program based upon a regional capability of responding to a range of spill volumes that increase from small operational spills to a WCD from a well blowout. Shell’s program is intended to meet the response planning requirements of the relevant coastal states and federal oil spill planning regulations. The OSRP includes information regarding Shell’s regional oil spill organizatio n and dedicated response assets, potential spill risks, and local environmental sensitivities. The OSRP presents specific information on the response program that includes a description of personnel and equipment mobilization, the incident management team organization, and the strategies and tactics used to implement effective and sustained spill containment and recovery operations.



## EIA Organization

The EIA is organized into Sections A through I corresponding to the information required by NTL 2008-G04, which provides guidance regarding information required by 30 CFR Part 550 for EPs. The main impact-related discussions are in Section A (Impact-Producing Factors) and

Section C (Impact Analysis).

# A. IMPACT-PRODUCING FACTORS

Table 2 is a matrix of IPFs and potentially affected environmental resources adapted from

Form BOEM- 142. An “X” indicates that an IPF could reasonably be expected to affect a certain resource, and a dash (

-- ) indicates no impact or negligible impact. Where there may be an effect, an analysis is provided in Section C . Potential IPFs for the proposed activity are listed below and briefly discussed in the following subsections:

 Drilling rig presence (including noise and lights);

 Physical disturbance to the seafloo r;

 Air pollutant emissions;

 Effluent discharges;

 Water intake;

 Onshore waste disposal;

 Marine debris;

 Support vessel and helicopter traffic; and

 Accidents.



## A.1 Drilling Rig Presence (including noise and lights)

The wells will be drilled using a DP drillship or DP semisubmersible rig, which will be on site for an estimated 187 days per well. DP drillships and DP semisubmersible rigs are self-propelled and maintain position using a global positioning system, specific computer software, and sensors in conjunction with a series of thrusters. Offshore support vessels will be used during the drilling program, and there will likely be at least one vessel in the field at all times. Potential impacts to marine resources from the drilling rig include the physical presence of the DP vessel in the ocean, increased light from working and safety lighting on the vessel, and noise audible above and

below the water surface.

The physical presence of a DP drillship or DP semisubmersible rig in the ocean can attract pelagic fishes and other marine life, as discussed in Section C.5.1 . Drilling vessels also maintain exterior lighting for working at night and navigational and aviation safety in accordance with federal regulations. Artificial lighting may attract and directly or indirectly impact natural resources, particularly birds, as discussed in Section C.4

.

Drilling operations produce noise that includes strong tonal components at low frequencies, including infrasonic frequencies in at least some cases (MMS, 2000). DP drillships and DP semisubmersible rigs can be expected to produce noise from both drilling and maintenance operations. Potential impacts of noise produced during drilling operations and vessel positioning

are discussed in Section C.3 (threatened, endangered, and protected species) and Section C.4 (coastal and marine birds).

### Table 2. Matrix of impact-producing factors and affected environmental resources. X = potential impact; dash (

-- ) = no impact or
negligible impact.

Environmental Resources Impact

- producing Factors
Drilling Rig Presence (incl. noise & lights) Physical

Disturbance to Seafloor Air

Pollutant Emissions Effluent

Discharges Water

Intake Onshore

Waste Disposal Marine

Debris Support

Vessel/Helo Traffic Accidents

Small Fuel Spill Large Oil

Spill Physical/Chemical Environment Air quality

-- -- X

-- -- -- -- -- X (6) X (6) Water quality

-- -- -- X

-- -- -- -- X (6) X (6)

Seafloor Habitats and Biota
Soft bottom benthic communities

-- X

-- X

-- -- -- -- -- X (6) High

- density deepwater benthic communities

-- -- (4)

-- -- (4)

-- -- -- -- -- X (6) Designated topographic features

-- -- (1)

-- -- (1)

-- -- -- -- -- -- Pinnacle trend area live bottoms

-- -- (2)

-- -- (2)

-- -- -- -- -- -- Eastern Gulf live bottoms

-- -- (3)

-- -- (3)

-- -- -- -- -- -- Threatened, Endangered, and Protected Species and Critical Habitat Sperm whale (endangered) X (8)

-- -- -- -- -- -- X (8) X (6,8) X (6,8)
West Indian manatee (endangered)

-- -- -- -- -- -- -- X (8)

-- X (6,8) Endangered mysticete whales

-- -- -- -- -- -- -- -- -- -- Non

- endangered marine mammals (protected) X

-- -- -- -- -- -- X X (6) X (6) Sea turtles (endangered/threatened) X (8)

-- -- -- -- -- -- X (8) X (6,8) X (6,8) Piping Plover (threatened)

-- -- -- -- -- -- -- -- -- X (6) Whooping Crane (endangered)

-- -- -- -- -- -- -- -- -- X (6) Gulf sturgeon (threatened)

-- -- -- -- -- -- -- -- -- X (6) Beach mice (endangered)

-- -- -- -- -- -- -- -- -- X (6)

Coastal and Marine Birds Marine and pelagic birds X

-- -- -- -- -- -- X X (6) X (6) Shorebirds and coastal nesting birds

-- -- -- -- -- -- -- X

-- X (6)

Fisheries Resources Pelagic communities and ichthyoplankton X

-- -- X X

-- -- -- X (6) X (6)

Essential Fish Habitat X

-- -- X X

-- -- -- X (6) X (6) Archaeological Resources Shipwreck sites

-- -- (7)

-- -- -- -- -- -- -- X (6) Prehistoric archaeological sites

-- -- (7)

-- -- -- -- -- -- -- X (6)

Coastal Habitats and Protected Areas
Beaches

-- -- -- -- -- -- -- -- -- X (6) Wetlands and seagrass beds

-- -- -- -- -- -- -- X

-- X (6) Coastal wildlife refuges and wilderness areas

-- -- -- -- -- -- -- -- -- X (6)

Socioeconomic and Other Resources Recreational and commercial fishing X

-- -- -- -- -- -- -- X (6) X (6) Public health and safety

-- -- -- -- -- -- -- -- X (6) X (6) Employment and infrastructure

-- -- -- -- -- -- -- -- X (6) X (6)

Recreation and tourism

-- -- -- -- -- -- -- -- X (6) X (6)

Land use

-- -- -- -- -- -- -- -- -- X (6)
Other marine uses

-- -- -- -- -- -- -- -- -- X (6)

### Table 2 Footnotes and Applicability:

(1) Activities that may affect a marine sanctuary or topographic feature. Specifically, if the well, platform site, or
any anchors will be on the seafloor within the following: (a) 4- mi le zone of the Flower Garden Banks, or the 3- mi le zone of Stetson Bank;
(b) 1,000-m, 1- mi le

, or 3- mi le zone of any topographic feature (submarine bank) protected by the
Topographic Features Stipulation attached to an Outer Continental Shelf (OCS) lease;
(c) Essential Fish Habitat (EFH) criteria of 500 ft from any no-activity zone; or (d) Proximity of any submarine bank (500-ft buffer zone) with relief greater than 2 m that is not protected by
the Topographic Features Stipulation attached to an OCS lease.

 Not applicable. The lease is not within the given ranges (buffer zone) of any marine sanctuary,
topographic feature, or no-activity zone. There are no submarine banks in the lease block.

(2) Activities with any bottom disturbance within an OCS lease block protected through the Live Bottom (Pinnacle Trend) Stipulation attached to an OCS lease.

 The Live Bottom (Pinnacle Trend) Stipulation is not applicable to the lease area.

(3) Activities within any Eastern Gulf OCS block and portions of Pensacola and Destin Dome area blocks in the Central Planning Area where seafloor habitats are protected by the Live Bottom (Low-Relief) Stipulation

attached to an OCS lease.

 The Live Bottom (Low-Relief) Stipulation is not applicable to the lease area.

(4) Activities on blocks designated by the BOEM as being in water depths 300 m or greater.

 No impacts on high-density deepwater benthic communities are anticipated because no features
indicative of high-density chemosynthetic communities or coral communities are located within 2,000 ft (610 m) of mud or cuttings discharge locations.

(5) Exploration or production activities where hydrogen sulfide (H 2 S) concentrations greater than 500 ppm might

be encountered.

 EP Section 4 contains Shell’s request for classification as an area absent of H 2 S.

(6) All activities that could result in an accidental spill of produced liquid hydrocarbons or diesel fuel that you
determine would impact these environmental resources. If the proposed action is located a sufficient distance
from a resource that no impact would occur, the EIA can note that in a sentence or two.

 Accidental hydrocarbon spills could affect the resources marked (X) in the matrix, and impacts are
analyzed in Section C

. (7) All activities that involve seafloor disturbances, including anchor emplacements, in any OCS block designated
by the BOEM as having high-probability for the occurrence of shipwrecks or prehistoric sites, including such
blocks that will be affected that are adjacent to the lease block in which your planned activity will occur. If the
proposed activities are located a sufficient distance from a shipwreck or prehistoric site that no impact would
occur, the EIA can note that in a sentence or two.

 No impacts on archaeological resources are expected. Although the lease area is on the list of archaeology survey blocks (BOEM

, 2012d )

, the archaeological survey did not detect any potential submerged cultural resources within 2,000 ft (610 m) of the wellsites. The lease area is beyond the 60- m (197 -ft) depth contour; therefore, prehistoric archaeological sites are not likely. A dynamically positioned
drillship or semisubmersible rig will be used; therefore, no seafloor disturbances due to anchoring will

occur.

(8) All activities that you determine might have an adverse effect on endangered or threatened marine mammals

or sea turtles or their critical habitats.

 IPFs that may affect marine mammals or sea turtles include drilling rig presence and emissions, support
vessel and helicopter traffic, and accidents. See Section C

. (9) Production activities that involve transportation of produced fluids to shore using shuttle tankers or barges.

 Not applicable.Underwater marine sounds associated with drilling operations are not particularly intense and include strong tonal components at low frequencies (averaging 10 to 500 Hz) and infrasonic frequencies in at least some cases (Richardson et al., 1995; MMS, 2000). From a drillship or semisubmersible, sound and vibration associated with drilling operations are transmitted to the water either through the air or the risers (MMS, 2000). Marine sounds emitted by drilling rigs were found to be dominated by a mix of tones believed to be related to the drill string rotation rate. When drilling, the drill string represents a long vertical sound source (McCauley, 1998). The DP thrusters add another component to the marine sound signature from a drillship or semisubmersible drilling rig. DP thrusters can produce intermittent or continuous marine sound that varies depending on thruster type, operating efficiency, ship size, engine load, duty cycle,

and weather or current conditions.

The response of marine mammals, sea turtles, and fishes to a perceived marine sound depends on a range of factors, including 1) the sound pressure level, frequency, duration, and novelty of the sound; 2) the physical and behavioral state of the animal at the time of perception; and 3) the ambient acoustic features of the environment (Hildebrand, 2004).



## A.2 Physical Disturbance to the Seafloor

The wells will be drilled with a DP drillship or DP semisubmersible rig, which do not use anchors. There will be minimal disturbance to the seafloor and soft bottom communities during positioning of the wellbore and blowout preventers. Physical disturbance of the seafloor will be limited to the proximal area where the wellbore penetrates the substrate and where mud and drill cuttings will be deposited.



## A.3 Air Pollutant Emissions

Estimates of air pollutant emissions are provided in EP Section 8 . Offshore air pollutant emissions will result from operations of thee drillships or DP semisubmersible rigs as well as service vessels and helicopters. These emissions occur mainly from combustion of diesel fuel. Primary air pollutants typically associated with OCS activities are suspended particulate matter (PM), sulfur oxides (SO

x ), nitrogen oxides (NO

x ), volatile organic compounds (VOCs), and carbon monoxide (CO).

MC 943 is located westward of 87.5° W longitude; thus, air quality is under BOEM jurisdiction as explained in NTL 2009-N11. The BOEM implementing regulations are provided in 30 CFR 550 Subpart C. The Air Quality Emissions Report (see EP Section 8 ) prepared in accordance with BOEM requirements shows that the projected emissions from emission sources associated with the proposed activities meet the BOEM exemption criteria and are therefore exempt from further air quality review pursuant to 30 CFR 550.303(d). Based on calculated emissions and the wells’ location relative to shore, it can be concluded that project emissions will not significantly affect onshore air quality for any of the criteria pollutants. No further analysis or control measures ar e required.



## A.4 Effluent Discharges

Effluent discharges from the drillship vessel are summarized in EP Section 7 . Discharges from the drilling vessel are required to be in compliance with and monitored as required by the National Pollutant Discharge Elimination System (NPDES) permit for oil and gas activities (GMG290000). Support vessel discharges are expected to be in accordance with USCG regulations and, as applicable, the NPDES Vessel General Permit and, therefore, are not expected to cause significant impacts on water quality.Water-based drilling muds and cuttings will be released at the seafloor during the initial well intervals before the marine riser is set, which allows their return to the surface. Excess cement slurry will also be released at the seafloor during casing installation for the riserless portion of the drilling operations.

A synthetic-based mud (SBM) system will be used for drilling activities after the marine riser is installed that allows recirculation of the SBM fluids and cuttings. Unused or residual SBM will be collected and transported to Port Fourchon, Louisiana, for recycling. Drill cuttings will be discharged overboard via a downpipe below the water surface, after treatment that complies with the NPDES permit limits for synthetic fluid retained on cuttings. The estimated volume of drill cuttings to be discharged is provided in EP Section 7

.

Other effluent discharges from the drilling vessel and support vessel are expected to include excess cement, non-contact cooling water, treated sanitary and domestic wastes, deck drainage, desalination unit brine, uncontaminated fire water, and ballast water. Drilling vessel and support vessel discharges are expected to be in accordance with NPDES permit and USCG regulations, as applicable, and therefore are not expected to cause significant impacts on water quality.



## A.5 Water Intake

Seawater will be drawn from several meters below the ocean surface for various services, including firewater and once-through non-contact cooling of machinery on the drilling vessel ( EP Table 7a ).

Section 316(b) of the Clean Water Act requires NPDES permits to ensure that the location, design, construction, and capacity of cooling water intake structures reflect the best technology available to minimize adverse environmental impact from impingement and entrainment of aquatic organisms. The NPDES General Permit No. GMG290000 specifies requirements for new facilities for which construction commenced after July 17, 2006, with a cooling water intake structure having a design intake capacity of greater than 2 million gallons of water per day, of which at least 25% is used for cooling purposes.

The wells will be drilled using either the Noble Don Taylor or a similar DP drillship, or the Noble Jim Day

or a similar DP semisubmersible rig. If the drilling vessel selected for this project meets the described applicability for new facilities, the vessel’s water intakes are expected to be in compliance with the design, monitoring, and recordkeeping requirements of the NPDES permit.



## A.6 Onshore Waste Disposal

Wastes generated during exploration activities are tabulated in EP Section 7 . Non-hazardous trash and debris and non-recyclable waste will be transported to Republic/BFI landfill in Sorrento, Louisiana, or to the parish landfill in Avondale, Louisiana. Recyclable trash and debris will be recycled at Omega Waste Management in Patterson, Louisiana, or at ARC of New Iberia, Louisiana. Used oil will be sent to Omega Waste Management in Patterson, Louisiana, or to ARC of New Iberia, Louisiana. Hazardous waste will be sent to Safety Kleen in Denton, Texas. At the respective onshore facilities, wastes will be recycled or disposed of according to applicable regulations.



## A.7 Marine Debris

Trash and debris released into the marine environment can harm marine animals through entanglement and ingestion. Shell will adhere to the International Convention for the Prevention of Pollution from Ships (MARPOL 73/78) Annex V requirements, USEPA and USCG regulations, and BSEE regulations and NTLs regarding solid wastes. BSEE regulations at 30 CFR 250.300(a)and (b)(6) prohibit operators from deliberately discharging containers and other similar materials (e.g., trash and debris) into the marine environment, and 30 CFR 25 0.300(c) requires durable identification markings on equipment, tools and containers (especially drums), and other material. USCG and USEPA regulations require operators to become proactive in avoiding accidental loss of solid waste items by developing waste management plans, posting informational placards, manifesting trash sent to shore, and using special precautions such as covering outside trash bins to prevent accidental loss of solid waste. Shell complies with NTL 2012-BSEE-G01, which instructs operators to exercise caution in the handling and disposal of small items and packaging materials, requires the posting of placards at prominent locations on offshore vessels and structures, and mandates a yearly marine trash and debris awareness training and certification process. Shell’s compliance with applicable laws, regulations, and NTL 2012-BSEE-G01 will avoid significant impacts on the environment.



## A.8 Support Vessel and Helicopter Traffic

Shell will use existing shore-based facilities at Port Fourchon and Boothville, Louisiana, for onshore support for water and air transportation, respectively. No terminal expansion or construction is planned at either location.

The supply base at Port Fourchon is operated by Shell and located on Bayou Lafourche, approximately 3 miles (5 km) from the Gulf of Mexico. There will likely be at least one support vessel in the field at all times during drilling activities. The supply vessels will normally move to the project area via the most direct route from the shorebase. Helicopters transporting personnel and small supplies will normally take the most direct route of travel between the helicopter base and the lease area when air traffic and weather conditions permit. Helicopters typically maintain a minimum altitude of 700 ft (213 m) while in transit offshore; 1,000 ft (305 m) over unpopulated areas or across coastlines; and 2,000 ft (610 m) over populated areas and sensitive habitats such as wildlife refuges and park properties. Additional guidelines and regulations specify that helicopters maintain an altitude of 1,000 ft (305 m) within 300 ft (91 m) of marine mammals (BOEM, 2012a).

Vessel noise is one of the main contributors to overall noise in the sea (National Research Council [NRC], 2003a; Jasny et al., 2005). Offshore supply and service vessels associated with the proposed project would contribute to the overall noise environment by transmitting noise through both air and water. Vessel noise is a combination of narrow-band (tonal) and broadband sound (Richardson et al., 1995). Tones typically dominate up to about 50 Hz, whereas broadband sounds may extend to 100 kHz. The primary sources of vessel noise are propeller cavitation, propeller singing, and propulsion; other sources include auxiliary engine noise, flow noise from water dragging along the hull, and bubbles breaking in the vessel’s wake while moving through the water (Richardson et al., 1995). Propeller cavitation is usually the dominant underwater noise source. The intensity of noise from service vessels is roughly related to ship size and speed. Broadband source levels for smaller boats (a category that would include supply and other service vessels) are in the range of 150 to 170 dB re 1 μPa at 1 m (Richardson et al., 1995).

Helicopters used for offshore oil and gas operation support are a potential source of noise to the marine environment. Helicopter noise is generated from their jet turbine engines, airframe, and rotors. The dominant tones for helicopters are generally below 500 Hz (Richardson et al., 1995). Richardson et al. (1995) reported received sound pressure levels in water of 109 dB re 1 μPa from a Bell 212 helicopter flying at an altitude of 152 m (500 ft). Penetration of aircraft noise below the sea surface is greatest directly below the aircraft; at angles greater than 13 degrees from vertical, much of the sound is reflected from the sea surface and so does not penetrate into the water (Richardson et al., 1995). The duration of underwater sound from passing aircraft is much shorter in water than air; for example, a helicopter passing at an altitude of 152 m (500 ft)that is audible in air for 4 minutes may be detectable under water for only 38 seconds at 3 m (10 ft) depth and for 11 seconds at 18 m (59 ft) depth (Richardson et al., 1995).



## A.9 Accidents

A.9.1 Types of Accidents Evaluated

The analysis in this EIA focuses on two types of potential accidents:

 a small fuel spill, which is the most likely type of spill during OCS exploration activities;

and

 an oil spill resulting from an uncontrolled blowout. A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures detailed in EP Section 2j

.

The following subsections summarize assumptions about the sizes and fates of these spills as well as Shell’s spill response plans. Impacts are analyzed in Section C

.

Lease sale EISs (MMS, 2007b; BOEM, 2012b,c) analyzed other types of accidents, including chemical spills, vessel collisions, and loss of well control. These accidents are discussed briefly in

Section A.9.4

.



### A.9.2 Small Fuel Spill

Spill Size . According to the analysis in BOEM (2012b), the most likely type of small spill (<1,000 barrels [bbl]) as a result of OCS activities is a minor diesel fuel spill. Historically, most diesel spills have been <1 bbl, and this size is predicted to be the most common in ongoing and future OCS activities in the Western and Central Gulf of Mexico Planning Areas (BOEM, 2012b). The median size for spills <1 bbl is <0.024 bbl, and the median size for spills of 1 to 10 bbl is 3 bbl (BOEM, 2012b). For this analysis, a small diesel fuel spill of 3 bbl is assumed. Operational experience suggests that the most likely cause of such a spill would be a hose rupture resulting in the loss of the contents of a fuel transfer hose, which is less than 3 bbl.

Spill Fate . The fate of a small fuel spill in the lease area would depend on meteorological and oceanographic conditions at the time, as well as the effectiveness of spill response activities. However, given the open ocean location of the lease area and the short duration of a small spill, the opportunity for impacts to occur would be very brief.

The water-soluble fractions of diesel are dominated by two- and three-ringed polycyclic aromatic hydrocarbons (PAHs), which are moderately volatile (NRC, 2003b). The constituents of these oils are light to intermediate in molecular weight and can be readily degraded by aerobic microbial oxidation. Diesel density is such that it will not sink to the seafloor. Diesel dispersed in the water column can adhere to suspended sediments, but this generally occurs only in coastal areas with high-suspended solids loads (NRC, 2003b) and would not be expected to occur to any appreciable degree in offshore waters of the Gulf of Mexico. Diesel oil is readily and completely degraded by naturally occurring microbes (NOAA, 2006).

The fate of a small diesel fuel spill was estimated using NOAA’s Automated Data Inquiry for Oil Spills (ADIOS) 2 model. This model uses the physical properties of oils in its database to predict the rate of evaporation and dispersion over time, as well as changes in the density, viscosity, and water content of the product spilled. It is estimated that more than 90% of a small diesel spill would be evaporated or naturally dispersed within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather

conditions.The ADIOS 2 results, coupled with spill trajectory information discussed in the next section for a large spill, indicate that a small fuel spill would not affect coastal or shoreline resources. The lease area is 65 miles (105 km) from the nearest shoreline (Louisiana). Modeling results indicate that a surface spill in the lease area would have an 8% probability of contacting the nearest Louisiana shorelines within 30 days after a spill. Slicks from spills are expected to persist for relatively short periods of time ranging from minutes (<1 bbl) to hours (<10 bbl) to a few days (10 to 1,000 bbl) and rapidly spread out, evaporate and disperse into the water column (BOEM, 2012b). Because of the distance of these potential spills on the OCS and their lack of persistence, it is unlikely that a small diesel spill would make landfall prior to dissipation (BOEM, 2012b).

Spill Response . In the unlikely event of a fuel spill, response equipment and trained personnel would be available to ensure that spill effects are localized and would result only in short-term, localized environmental consequences. EP Section 9b provides a detailed discussion of Shell’s response to a spill.



### A.9.3 Large Oil Spill

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures detailed in

EP Section 2j . Blowouts are rare events and most do not result in oil spills (BOEM, 2012a).

Spill Size . Shell has calculated a WCD for this EP using the requirements prescribed by NTL 2010-N06. The WCD is a 30-day average of 165,000 barrels of oil per day (BOPD). The detailed analysis of this calculation can be found in EP Section 2j . The WCD scenario for this EP has a low probability of being realized. Some of the factors that are likely to reduce rates and volumes, which are not included in the WCD calculation, include, but are not limited to, obstructions or equipment in the wellbore, well bridging, and early intervention such as

containment.

Shell has a robust system in place to prevent blowouts. Included in EP Sections 2j and 9b is Shell’s response to NTL 2010-N06, which includes descriptions of measures to prevent a blowout, reduce the likelihood of a blowout, and conduct effective and early intervention in the event of a blowout. Shell will also comply with NTL 2010-N10 and the Final Drilling Safety Rule, which specify additional safety measures for OCS activities.

Spill Trajectory . The fate of a large oil spill in the lease area would depend on meteorological and oceanographic conditions at the time. The Oil Spill Risk Analysis (OSRA) model is a computer simulation of oil spill transport that uses realistic data for winds and currents to predict spill fate. The OSRA report by Ji et al. (2004) provides conditional contact probabilities for shoreline segments.

The results for Launch Area 58 (the launch area nearest to the lease area) are presented in

Table 3 . The model predicts no shoreline contact within 3 days. After 10 days, Plaquemines Parish, Terrebonne Parish, and Lafourche Parish in Louisiana may be contacted; after 30 days, 8 other counties and parishes from Texas to Florida may be contacted. Plaquemines Parish, Louisiana, has the greatest probability of shoreline contact, with a 4% chance within 10 days and an 8% chance within 30 days. Other parishes and counties ranging from Texas to Florida have a 3% or less probability of shoreline contact within 30 days.

### Table 3. Conditional probabilities of a spill in the lease area contacting shoreline segments (From: Ji et al., 2004). Values are conditional probabilities that a hypothetical spill in the lease area (represented by OSRA Launch Area 58 ) could contact shoreline
segments within 3, 10, or 30 days.

Shoreline Segment County or Parish, State Conditional Probability of Contact 1 (%)
3 Days 10 Days 30 Days

C10 Galveston, TX

- - 1

C12 Jefferson, TX

- - 1

C13 Cameron, LA

- - 3

C14 Vermilion, LA

- - 2

C15 Iberia, LA

- - 1

C17 Terrebonne, LA

- 1 3

C18 Lafourche, LA

- 2 3

C19 Jefferson, LA

- - 1

C20 Plaquemines, LA

- 4 8

C21 St. Bernard, LA

- - 1

C28 Okaloosa, FL

- - 1

1 Conditional probability refers to the probability of contact within the stated time period, assuming that a spill has occurred (- indicates less than 0.5%).

The OSRA model does not evaluate the fate of a spill over time periods longer than 30 days, nor does it predict the fate of a release that continues over a period of weeks or months. Also as noted in Ji et al. (2004), the OSRA model does not take into account the chemical composition or biological weathering of oil spills, the spreading and splitting of oil spills, or spill response activities. The model does not assume a particular spill size but has generally been used by BOEM to evaluate contact probabilities for spills greater than 1,000 bbl.

Weathering . Following an oil spill, several physical, chemical, and biological processes, collectively called weathering, interact to change the physical and chemical properties of the oil, and thereby influence its harmful effects on marine organisms and ecosystems. The most important weathering processes include spreading, evaporation, dissolution, dispersion into the water column, formation of water- in -oil emulsions, photochemical oxidation, microbial degradation, adsorption to suspended PM, and stranding on shore or sedimentation to the seafloor (NRC, 2003b).

Weathering decreases the concentration of oil and produces changes in its chemical composition, physical properties, and toxicity. The more toxic, light aromatic and aliphatic hydrocarbons are lost rapidly by evaporation and dissolution from the slick on the water surface. Evaporated hydrocarbons are degraded rapidly by sunlight. Biodegradation of oil on the water surface and in the water column by marine bacteria removes first the n-alkanes and then the light aromatics from the oil. Other petroleum components are biodegraded more slowly. Photooxidation attacks mainly the medium and high molecular weight PAHs in the oil on the water surface.

Spill Response . Shell is a founding member of the Marine Well Containment Company (MWCC) and has access to an integrated subsea well control and containment system that can be rapidly deployed through the MWCC. The MWCC is a non-profit organization that assists with the subsea containment system during a response. The near-term containment response capability will be specifically addressed in Shell’s NTL 2010-N10 submission at the time an Application for Permit to

Drill is submitted and will include equipment and services available to Shell through MWCC’s development of near-term capability and other industry sources. Shell is a member of Clean Caribbean & Americas, Marine Spill Response Corporation, Clean Gulf Associates, and Oil SpillResponse Limited, organizations that are committed to providing the resources necessary to respond to a spill as outlined in Shell’s OSRP.

Mechanical recovery capabilities are addressed in the OSRP. The mechanical recovery response equipment that could be mobilized to the spill location in normal and adverse weather conditions is included in the Offshore On-Water Recovery Activation List in the OSRP.

Chemical dispersion capabilities are also readily available from resources identified in the OSRP. Available equipment for surface and subsea application of dispersants, response times, and support resources are identified in the OSRP.

Open-water in situ

burning may also be used as a response strategy, depending on the circumstances of the release. If appropriate conditions exist and approval from the Unified Command is received, one or multiple in situ burning task forces could be deployed offshore.

See EP Section 9b for a detailed description of spill response measures.



### A.9.4 Other Accidents Not Analyzed in Detail

The lease sale EISs (BOEM, 2012b,c, 2013) discuss four other types of accidents: chemical spills, pipeline failures, vessel collisions, and loss of well control. Three of these types of accidents considered relevant to this EP are briefly discussed in this section. Other than the presence of hydrogen sulfide (H 2 S), which is addressed below, no other site-specific issues have been identified for this EP. The analysis in the lease sale EISs for these topics is incorporated by

reference.

Chemical Spill . Chemicals are used in drilling and producing operations to achieve technical goals in the drilling process, improve the efficiency and safety of drilling, and protect associated equipment. Chemicals used during drilling include surfactants, bentonite clays, olefins, inorganic salts, glycols, polymers, barite, and calcium carbonate. Supplies are renewed on a regular basis by transfer in containers from supply boats (Boehm et al., 2001). In addition to chemicals used in drilling fluids, the following chemicals are likely to be used on the rig: ethylene glycol (blowout prevention control fluid, used in closed cooling loops for crane and main engines and brake coolers), cement (used to cement casing in place), solvents (used in painting operations), hydraulic fluids (used in cranes and other hydraulic rig equipment), lubricating oil and grease (used in reciprocating and electrical equipment), and sodium hypochlorite (dilute, used as laundry bleach and disinfectant).

A study of environmental risks of chemical products used in OCS activities determined that only two chemicals could potentially affect the marine environment in the concentrations typically used: zinc bromide and ammonium chloride (Boehm et al., 2001). The project addressed by this EP does not anticipate the use of either zinc bromide or ammonium chloride. Most other chemicals are either nontoxic or used in small quantities (BOEM, 2012b,c, 2013). No significant impacts are expected from chemical spills.

Vessel Collisions . As summarized in MMS (2007b) and BOEM (2012b,c, 2013), vessel collisions occasionally occur during routine operations. Most collision mishaps are the result of service vessels colliding with platforms or vessel collisions with pipeline risers. About 10% of these collisions have caused spills of diesel fuel or chemicals (BOEM, 2012b,c). Shell will comply with USCG and BOEM-mandated safety requirements to minimize the potential for vessel collisions.

Loss of Well Control . A loss of well control is the uncontrolled flow of a reservoir fluid that may result in the release of gas, condensate, oil, drilling fluids, sand, or water. Loss of well control is a broad term that includes minor to serious well control incidents, while blowouts, discussed in

Section A.9.3 , are considered to be a more serious subset of loss of well control incidents withgreater risk of oil spill or human injury (MMS, 2007b). Not all loss of well control events result in blowouts (BOEM, 2012b,c, 2013). In addition to the potential release of gas, condensate, oil, sand, or water, the loss of well control can also resuspend and disperse bottom sediments (BOEM, 2012b). BOEM (2012b,c, 2013) noted that most OCS blowouts have resulted in the release of gas.

Shell has a robust system in place to prevent loss of well contr ol. Included in this EP is Shell’s response to NTL 2010-N06, which includes descriptions of measures to prevent a blowout, reduce the likelihood of a blowout, and conduct effective and early intervention in the event of a blowout. Shell will also comply with NTL 2010-N10 and the Final Drilling Safety Rule, which specify additional safety measures for OCS activities. See EP Sections 2j and 9b for further

information.

H 2 S Release

. EP Section 4 contains Shell’s request for classification as an area absent of H 2 S.



# B. AFFECTED ENVIRONMENT

The lease area is in the central Gulf of Mexico, 65 miles (105 km) from the nearest shoreline,

106 miles (171 km) from the onshore support base at Port Fourchon, Louisiana, and 89 miles (143 km) from the helicopter base at Boothville, Louisiana.

Water depths at the proposed wellsites range from approximately 4,211 to 4,276 ft (1,284 to 1,303 m). The proposed wellsites range from 825 to 1,750 ft (91 to 209 m) from the nearest seafloor faults and 300 to 700 ft (91 to 213 m) from the nearest buried amplitudes (Geoscience Earth and Marine Services, Inc. [GEMS], 2013). No fault or amplitude penetration is expected at any of the proposed wellsites.

The geologic, stratigraphic, and archaeological assessment detected marine avoidance targets within 2,000 ft (610 m) of the proposed wellsites (C&C Technologies, Inc. [C&C], 2007; GEMS, 2013). Each of these targets will be avoided by 100 ft (31 m) or more. Each target wil l be assigned an Avoidance Zone Number, and exact geographic coordinates of the targets will be plotted to allow the drilling subcontractor to avoid them. There are no existing wells, flowlines, or umbilicals in the vicinity of any of the proposed wellsites (C&C , 2007; GEMS, 2013).

The archaeological assessment confirmed the existence of modern debris primarily associated with prior industrial waste disposal or field development activities. A discontinued industrial waste disposal site is located northwe st of the lease area. Shell’s procedure “Waste Barrel Avoidance and Release Response in the Mississippi Canyon Area,” which was approved by

MMS and BOEM 2 , applies to operations that could cause a disturbance of a seafloor barrel. Shell’s overarching poli cy is to avoid barrel contact. In the unlikely case that contact is suspected or has been made with any wastes from a barrel, the plan specifies actions to be taken for the topside safety of personnel handling the equipment. The plan also outlines barrel impact reporting procedures.

A detailed description of the regional affected environment is provided in MMS (2007b) and BOEM (2012b,c), including meteorology, oceanography, geology, air and water quality, benthic

2 MMS approval of West Boreas Supplemental Exploration Plan, MS 5231 December 16, 2008, Control No. S-07273,
Mississippi Canyon Area Block 762, Lease OCS-G 07957; Mississippi Canyon Area Block 806, Lease OCS-G 07962
and BOEM approval of the Supplement to the Conceptual Deepwater Operations Plan for Mars B project,

August 12, 2010, MS 5220.communities, threatened and endangered species, biologically sensitive resources, archaeological resources, socioeconomic conditions, and other marine uses. These regional descriptions are based on extensive literature reviews and are incorporated by reference. General background information is presented in the following sections, and brief descriptions of each potentially affected resource are presented in Section C , including site-specific and/or new information if

available.

The local environment in the lease area is not known to be unique with respect to physical/chemical, biological, or socioeconomic conditions. Baseline environmental conditions in the lease area are expected to be consistent with the regional description of continental slope locations evaluated in MMS (2007b) and BOEM (2012b,c).



# C. IMPACT ANALYSIS

This section analyzes the potential direct and indirect impacts of routine activities and accidents; cumulative impacts are discussed in Section C.9

.

Impacts have been analyzed extensively in lease sale EISs for the Western and Central Gulf of Mexico Planning Areas (MMS, 2007b; BOEM, 2012b,c, 2013). Site-specific issues are addressed in this section as appropriate.



## C.1 Physical/Chemical Environment

C.1.1 Air Quality

Due to the distance from shore-based pollution sources, offshore air quality is expected to be good. The attainment status of federal OCS waters is unclassified because there is no provision in the Clean Air Act for classification of areas outside state waters (MMS, 2007b).

In general, ambient air quality on coastal counties along the Gulf of Mexico is relatively good (BOEM, 2012a). As of December 5, 2013, Louisiana, Mississippi, Alabama, and Florida coastal counties and parishes are in attainment of the National Ambient Air Quality Standards (NAAQS) for all criteria pollutants (USEPA, 2013). One coastal metropolitan area in Texas (Houston-Galveston-Brazoria) is a nonattainment area for 8-hour ozone. One coastal metropolitan area in Florida (Tampa) is a nonattainment area for lead based on the

2008 Standard.

Winds in the region are driven by the clockwise circulation around the Bermuda High (BOEM, 2012b). The Gulf of Mexico is located to the southwest of this center of circulation, resulting in a prevailing southeasterly to southerly flow, which is conducive to transporting emissions toward shore. However, circulation is also affected by tropical cyclones (hurricanes) during summer and fall and by extratropical cyclones (cold fronts) during winter.

IPFs that could potentially affect air quality are air pollutant emissions and two types of accidents

– a small fuel spill and a large oil spill.

Impacts of Air Pollutant Emissions

Air pollutant emissions are the only routine IPF likely to affect air quality. Offshore air pollutant emissions will result from the operation of the drilling rig as well as helicopters and service

vessels as described in Section A.3 . These emissions occur mainly from combustion or burningof diesel fuel. Primary air pollutants typically associated with OCS activities are suspended PM,

SO
x , NO
x , VOCs, and CO.

Due to the distance from shore, routine operations in the project area are not expected to impact air quality along the coast. As noted in the lease sale EISs (MMS, 2007b; BOE M, 2012b,c, 2013), emissions of air pollutants from routine activities in the Gulf of Mexico Central Planning Area are projected to have minimal impacts on onshore air quality because of the prevailing atmospheric conditions, emission heights, emission rates, and the distance of these emissions from the

coastline.

MC 943 is located westward of 87.5° W longitude; thus, air quality is under BOEM jurisdiction as explained in NTL 2009-N11. The BOEM implementing regulations are provided in 30 CFR 550 Subpart C. The Air Quality Emissions Report (see EP Section 8 ) prepared in accordance with BOEM requirements shows that the projected emissions from emission sources associated with the proposed activities meet the BOEM exemption criteria. This EP is therefore exempt from further air quality review pursuant to 30 CFR 550.303(d).

The Breton Wilderness Area, which is part of the Breton National Wildlife Refuge (NWR), is designated under the Clean Air Act as a Prevention of Significant Deterioration Class I air qualit y area. The BOEM coordinates with the USFWS if emissions from proposed projects may affect the Breton Class I area. The lease area is approximately 99 miles (160 km) from the Breton Wilderness Area. Shell will comply with emissions requirements as directed by the BOEM.

Carbon dioxide (CO 2 ) and methane (CH 4 ) emissions from the project would constitute a negligible contribution to greenhouse gas emissions from all OCS activities. According to Programmatic and OCS lease sale EISs (BOEM, 2012a,b), estimated CO 2 emissions from OCS oil and gas sources are 0.4% of the U.S. total. OCS activities in the Central and Western Planning Areas contribute approximately 0.005% to total global CO 2 emissions (BOEM 2012b). Greenhouse gas emissions from this proposed project represent a negligible contribution to the total greenhouse gas emissions from reasonably foreseeable activities in the Gulf of Mexico area and would not significantly alter any of the climate change impacts evaluated in the Programmatic EIS (BOEM, 2012a).

Impacts of a Small Fuel Spill

Potential impacts of a small spill on air quality are expected to be consistent with those analyzed and discussed in MMS (2007b) and BOEM (2012b,c, 2013). The probability of a small spill would be minimized by Shell’s pre ventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the extent and duration of air quality impacts from a small spill would not be significant.

A small fuel spill would likely affect air quality near the spill site by introducing VOCs through evaporation. The ADIOS 2 model (see Section A.9.2 ) indicates that more than 90% of a small diesel spill would be evaporated or dispersed within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather

conditions.

A small fuel spill would not affect coastal air quality because the spill would not be expected to make landfall or reach coastal waters prior to breaking up (see Section A.9.2 ).

Impacts of a Large Oil Spill

Potential impacts of a large oil spill on air quality are expected to be consistent with those analyzed and discussed in MMS (2007b) and BOEM (2012b,c, 2013).A large oil spill would likely affect air quality by introducing VOCs through evaporation from the slick. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Additional air quality impacts could occur if response measures approved by the Unified Command included in situ burning of the floating oil. In situ burning would generate a plume of

black smoke offshore and result in emissions of NO

x , SO
x , CO, and PM, as well as greenhouse

gases.

Due to the lease area location (65 miles [105 km] from the nearest shoreline), most air quality impacts would occur in offshore waters. Depending on the spill trajectory and the effectiveness of spill response measures, coastal air quality could also be affected. Based on the OSRA modeling predictions ( Table 3 ), Plaquemines Parish, Terrebonne Parish, and Lafourche Parish, Louisiana, are the coastal areas most likely to be affected.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention meas ures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on air quality are expected.



### C.1.2 Water Quality

Deepwater areas in the Gulf of Mexico are relatively homogeneous with respect to temperature, salinity, and oxygen (MMS, 2007b). IPFs that could potentially affect water quality are effluent discharges and two types of accidents

– a small fuel spill and a large oil spill.

Impacts of Effluent Discharges

Discharges of treated SBM cuttings will produce temporary, localized increases in suspended solids in the water column around the drilling rig. NPDES permit limits and requirements will be met. After discharge, SBM retained on cuttings would be expected to adhere tightly to the cuttings particles and, consequently, would not produce much turbidity as the cuttings sink through the water column (Neff et al., 2000). Recent EISs have concluded that the discharge of treated SBM cuttings will not cause persistent impacts on water quality in the lease area (BOEM 2012b,c, 2013).

Treated sanitary and domestic wastes may have a slight transient effect on water quality in the immediate vicinity of these discharges. NPDES permit limits and requirements will be met, and little or no impact on water quality is anticipated.

Deck drainage includes effluents resulting from rain, deck washings, and runoff from curbs, gutters, and drains, including drip pans in work areas. Rainwater that falls on uncontaminated areas of the drilling rig will flow overboard without treatment. However, rainwater that falls on the drilling rig deck and other areas such as chemical storage areas and places where equipment is exposed will be collected and oil and water separated to meet NPDES permit requirements. Negligible impact on water quality is anticipated.

Other discharges from the proposed drilling rig will be in accordance with the NPDES permit. Discharges include desalination unit brine and uncontaminated cooling water, fire water, and ballast water and are expected to be diluted rapidly and have little or no impact on water quality.

Support vessels will discharge treated sanitary and domestic wastes. These will have a slight effect on water quality in the immediate vicinity of the discharges. Support vessel discharges are subject to USCG regulations and therefore are not expected to cause significant impacts on water quality.Impacts of a Small Fuel Spill

Potential impacts of a small spill on water quality are expected to be consistent with those analyzed and discussed in MMS (2007b) and BOEM (2012b,c, 2013). The probability of a small spill would be minimized by Shell’s preventative measures durin g routine operations, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the extent and duration of water quality impacts from a small spill would not be significant.

A small fuel spill in offshore waters would increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. However, it is estimated that more than 90% of a small diesel spill would be evaporated or dispersed within 24 hours (see Section A.9.2 ). The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather

conditions.

The water-soluble fractions of diesel are dominated by two- and three-ringed PAHs, which are moderately volatile (NRC, 2003b). The constituents of these oils are light to intermediate in molecular weight and can be readily degraded by aerobic microbial oxidation. Diesel’s density is such that it will not sink and pool on the seafloor. Diesel dispersed in the water column can adhere to suspended sediments, but this generally occurs only in coastal areas with high suspended solids loads (NRC, 2003b) and would not be expected to occur to any appreciable degree in offshore waters of the Gulf of Mexico. Diesel oil is readily and completely degraded by naturally occurring microbes (NOAA, 2006).

A small fuel spill would not affect coastal water quality because the spill would not be expected to make landfall or reach coastal waters prior to breaking up (see Section A.9.2 ).

Impacts of a Large Oil Spill

Potential impacts of a large oil spill on water quality are expected to be consistent with those analyzed and discussed in MMS (2007b) and BOEM (2012b,c, 2013). A large spill would likely affect water quality by producing a slick on the water surface and increasing the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Most of the oil would be expected to form a slick at the surface, although observations following the Macondo spill indicate that plumes of submerged oil droplets can be produced when subsea dispersants are applied at the wellhead (Camilli et al., 2010; Hazen et al., 2010; Joint Analysis Group, 2010a,b,c). Recent analyses of the full set of samples associated with the Macondo spill have confirmed that the application of subsurface dispersants resulted in subsurface hydrocarbon plumes (Spier et al., 2013). A report by Kujawinski et al. (2011) indicates that chemical components of subsea dispersants used during the Macondo spill persisted for up to 2 months and were detectable up to 186 miles (300 km) from the wellsite at a water depth of 3,280 to 3,937 ft (1,000 to 1,200 m). While dispersants were detectable in 353 of the 4,114 total water samples, concentrations in the samples were significantly below the chronic screening level for dispersants (BOEM, 2012c).

Once oil enters the ocean, a variety of physical, chemical, and biological processes act to disperse the oil slick. These processes include spreading, evaporation of the more volatile constituents, dissolution into the water column, emulsification of small droplets, agglomeration sinking, microbial modification, photochemical modification, and biological ingestion and excretion (NRC, 2003b). Marine water quality would be temporarily affected by the dissolved components and small oil droplets that do not rise to the surface or are mixed down by surface turbulence.Dispersion by currents and microbial degradation removes the oil from the water column or dilutes the constituents to background levels.

A large oil spill could result in a release of gaseous hydrocarbons that could affect water quality.

Du ring the Macondo spill, large volumes of CH 4 were released, causing localized oxygen depletion as methanotrophic bacteria rapidly metabolized the hydrocarbons (Joye et al., 2011; Kessler et al., 2011). However, a broader study of the deepwater Gulf of Mexico found that although some stations showed slight depression of dissolved oxygen concentrations relative to climatological background values, the findings were not indicative of hypoxia (<2.0 mg/L) (Operational Science Advisory Team [OSAT], 2010). Stations revisited around the Macondo wellhead in October 2010 showed no measurable oxygen depressions (OSAT, 2010).

Due to the lease area location, most water quality impacts would occur in offshore waters. Depending on the spill trajectory and the effectiveness of spill response measures, coastal water quality could be affected. Based on the OSRA modeling predictions ( Table 3 ), nearshore waters and embayments of Plaquemines Parish, Terrebonne Parish, and Lafourche Parish, Louisiana, are the coastal areas most likely to be affected.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures detailed in

EP Section 2j . In the unlikely event o f a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on water quality are expected.



## C.2 Seafloor Habitats and Biota

Water depths at the proposed well surface locations range from approximately 4,211 to 4,276 ft (1,284 to 1,303 m). See EP Section 6a for further information.

According to BOEM (2012b,c, 2013), existing information for the deepwater Gulf of Mexico indicates that the seafloor is composed primarily of soft sediments; hard bottom communities are rare. In accordance with the guidance of NTL 2008-G04, a remotely operated vehicle (ROV) Monitoring Survey Plan is one of several requirements to accompany the EP when there is a potential to disturb seafloor areas in deepwater (>400 m). The specific requirements of the ROV Survey Plan are detailed in NTL 2008-G06. The BOEM (2011) has subdivided the Gulf of Mexico Region (Western Planning Area, Central Planning Area, and parts of Eastern Planning Area) into grids. MC 943 is within deepwater Grid 13 where remotely operated vehicle coverage of the seafloor is considered adequate to characterize the area (BOEM, 2011), and as such an ROV Monitoring Survey Plan is not necessary to accompany the EP. An autonomous underwater vehicle (AUV) survey consisting of side-scan sonar, multibeam bathymetry, and subbottom profiler data collection was conducted (GEMS, 2013).



### C.2.1 Soft Bottom Benthic Communities

Data from the Northern Gulf of Mexico Continental Slope Habitats and Benthic Ecology study (Wei, 2006; Rowe and Kennicutt, 2009) can be used to describe typical benthic communities in

the area. Table 4 summarizes data from two nearby stations in similar water depths to the proposed MC 943 wells (approximately 1,294 m water depth). Sediments at these two stations were similar, predominantly clay (45.5% at MT4 and 52.6% at MT3) and silt (45.5% at MT4 and 41.5% at MT3) (Rowe and Kennicutt, 2009).



### Table 4. Benthic community data from stations nearest to the lease area in similar water depths sampled during the Northern Gulf of Mexico Continental Slope Habitats and Benthic Ecology Study (From: Wei, 2006; Rowe and Kennicutt, 2009).Station Location

Relative to

Lease Area Water Depth

(m) Abundance

Meiofauna (individuals/m 2 ) Macroinfauna

(individuals/m 2 ) Megafauna

(individuals/ha)

MT4 17 miles SSW 1,401 246,058 3,262 1,548

MT3 32 miles WNW 990 885,995 4,924 1,034

Meiofaunal and megafaunal abundance from Rowe and Kennicutt (2009); macroinfaunal abundance from Wei (2006).

Meiofauna (animals passing through a 0.5-mm sieve but retained on a 0.062-mm sieve) densities in water depths representative of the lease area typically range from about 250,000 to 890,000 individuals/m 2 (Rowe and Kennicutt, 2009). Nematodes, nauplii, and harpacticoid copepods were the three dominant groups in the meiofauna, accounting for about 90% of total abundance.

The benthic macroinfauna is characterized by small mean individual sizes and low densities, both of which are a reflection of the meager primary production in Gulf of Mexico surface waters (Wei, 2006). Densities decrease exponentially with water depth. Based on an equation presented by Wei (2006), macroinfaunal densities in the water depth of the wellsites are expected to be about 2,600 individuals/m 2 , lower than the values in Table 4

.

Polychaetes are typically the most abundant macroinfaunal group on the northern Gulf of Mexico continental slope, followed by amphipods, tanaids, bivalves, and isopods. Wei (2006) recognized four depth-dependent faunal zones (1 through 4), two of which are divided horizontally. The lease area is in Zone 2E. Zone 2E consists of stations ranging in depth from 2,831 to 5,315 ft (625 to 1,828 m), covering mid Texas-Louisiana Slope, the west flank of the Mississippi Fan, the mid Mississippi Canyon, the head of De Soto Canyon, and the mid West Florida Terrace. The five most abundant species in Zone 2E were the polychaetes Aricidea suecica, Exogone sp. A., Paralacydonia paradoxa, and Tharyx annulosus (Wei, 2006).

Megafaunal density from nearby station MT4 was 1,548 individuals/ha ( Table 4 ). Densities of 195 to 2,941 individuals/ha were reported from other stations in a similar depth range. Common megafauna included motile groups such as decapods, ophiuroids, holothurians, and demersal fishes, as well as sessile groups such as sponges and anemones.

Bacteria are the foundation of deep-sea chemosynthetic communities (Ross et al., 2012) and are an important component in terms of biomass and cycling of organic carbon (Cruz-Kaegi, 1998). Bacterial biomass at the depth range of the lease area typically is about 1 to 1.5 grams of carbon per square meter (g C m

− 2 ) in the top 6 in. (15 cm) of sediments (Rowe and Kennicutt, 2009).

IPFs that could potentially affect benthic communities are physical disturbance, effluent discharges (drilling mud and cuttings), and a large oil spill resulting from a well blowout at the seafloor. A small fuel spill would not affect benthic communities because the diesel fuel would float and dissipate on the sea surface.

Impacts of Physical Disturbance to the Seafloor

In water depths such as those that are encountered in the lease area, DP drillships or

DP semisubmersible rigs disturb the seafloor only around the wellbore (surface hole location) where the bottom template and blowout preventer are located. Depending upon the specific well configuration, this area is generally about 0.62 ac (0.25 ha) (BOEM, 2012b).

The areal extent of these impacts from the drilling rig will be small compared to the lease area itself. Soft bottom communities are ubiquitous along the northern Gulf of Mexico continental slope (Gallaway et al., 2003; Rowe and Kennicutt, 2009). Physical disturbance to the seafloor during this project will have no significant impact on soft bottom benthic communities on a regional basis.Impacts of Effluent Discharges

Drilling mud and cuttings are the only effluents likely to affect benthic communities. During initial well interval(s) before the marine riser is set, cuttings and seawater- based “spud mud” will be released at the seafloor. Excess cement slurry will also be released at the seafloor during casing installation for the riserless portion of the drilling operations. Cement slurry components typically include cement mix and some of the same chemicals used in water-based drilling mud (Boehm et al., 2001). The main impacts will be burial and smothering of benthic organisms within several meters to tens of meters around the wellbore. Soft bottom sediments disturbed by cuttings, drilling mud, and cement slurry will eventually be recolonized through larval settlement and migration from adjacent areas. Because some deep-sea biota grow and reproduce slowly, recovery may require several years.

Discharges of treated SBM cuttings from the rig may affect benthic communities, primarily within several hundred meters of the wellsites. The fate and effects of SBM cuttings have been reviewed by Neff et al. (2000), and monitoring studies have been conducted in the Gulf of Mexico by Continental Shelf Associates, Inc. (2004, 2006). In general, cuttings with adhering SBM tend to clump together and form thick cuttings piles close to the drillsite. Areas of SBM cuttings deposition may develop elevated organic carbon concentrations and anoxic conditions (Continental Shelf Associates, Inc., 2006). Where SBM cuttings accumulate and concentrations exceed approximately 1,000 mg/kg, benthic infaunal communities may be adversely affected due to both the toxicity of the base fluid and organic enrichment (with resulting anoxia) (Neff et al., 2000). Infaunal numbers may increase and diversity may decrease as opportunistic species that tolerate low oxygen and high H 2 S predominate (Continental Shelf Associates, Inc., 2006). As th e base synthetic fluid is decomposed by microbes, the area will gradually return to pre-drilling conditions. Disturbed sediments will be recolonized through larval settlement and migration from adjacent areas.

The areal extent of impacts from drilling discharges will be small; the typical effect radius is 1,640 ft (500 m) around each wellsite. For the four surface locations in this exploration drilling program, the total impact area would be 776 ac (314 ha). In light of the proximity of the proposed wells to each other, the overall impact area could be reduced. Soft bottom communities are ubiquitous along the northern Gulf of Mexico continental slope (Gallaway, 1988; Gallaway et al., 2003; Rowe and Kennicutt, 2009). Impacts from drilling discharges during this project will have no significant impact on soft bottom benthic communities on a regional basis.

Impacts of a Large Oil Spill

Potential impacts of a large oil spill on the benthic community are expected to be consistent with those analyzed and discussed in MMS (2007b) and BOEM (2012b,c, 2013). Likely impacts from a subsea blowout include smothering and exposure to toxic hydrocarbons from oiled sediment settling to the seafloor. The most likely effects of a subsea blowout on benthic communities would be within a few hundred meters of the wellsites. The MMS (2007b) estimates that a severe subsurface blowout could resuspend and disperse sediments within a 984-ft (300-m) radius. While coarse sediments (sands) would probably settle at a rapid rate within 1,312 ft (400 m) from the blowout site, fine sediments (silts and clays) could be resuspended for more than 30 days and dispersed over a much wider area. A previous study characterized surface sediments in the vicinity of the site as about 53% clay and 42% silt (Rowe and Kennicutt, 2009).

Previous analyses (MMS, 2007a, 2008) concluded that oil spills would be unlikely to affect benthic communities beyond the immediate vicinity of the wellhead (i.e., due to physical impacts of a blowout) because the oil would rise quickly to the sea surface directly over the spill location. However, during the Macondo spill, subsurface plumes were reported at a water depth of about 3,600 ft (1,100 m), extending at least 22 miles (35 km) from the wellsite and persisting for more than a month (Camilli et al., 2010). The subsurface plumes apparently resulted from the use ofdispersants at the wellhead (Joint Analysis Group, 2010c; Spier et al., 2013). Chemical components of subsea dispersants used during the Macondo spill persisted for up to 2 months and were detected up to 186 miles (300 km) from the wellsite at a water depth of 3,280 to 3,937 ft (1,000 to 1,200 m) (Kujawinski et al., 2011). However, estimated dispersant concentrations in the subsea plume were below levels known to be toxic to marine life. While the behavior and impacts of subsurface plumes are not well known, a subsurface plume could contact the seafloor and affect benthic communities beyond the 984-ft (300-m) radius estimated in MMS (2007a, 2008), depending on its extent, trajectory, and persistence (Spier et al., 2013). This contact could result in smothering and/or toxicity to benthic organisms. The affected area would be recolonized by benthic organisms over a period of months to years (NRC, 2003b).

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementa tion of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on soft bottom communities are expected.



### C.2.2 High-Density Deepwater Benthic Communities

As defined in NTL 2009-G40, high-density deepwater benthic communities are features or areas that could support high-density chemosynthetic communities, high-density deepwater corals, or other associated high-density hard bottom communities. Chemosynthetic communities were discovered in the central Gulf of Mexico in 1984 and have been studied extensively (MacDonald, 2002). Deepwater coral communities are also known from numerous locations in the Gulf of Mexico (Brooke and Schroeder, 2007; CSA International, Inc., 2007; Brooks et al., 2012). These communities occur almost exclusively on authigenic carbonates created by chemosynthetic communities, and on shipwrecks.

Monitoring programs on the Gulf of Mexico continental slope have shown that benthic impacts from drilling discharges typically are concentrated within about 1,640 ft (500 m) of the wellsites, although detectable deposits may extend beyond this distance (Continental Shelf Associates, Inc., 2004, 2006; Neff et al., 2005). The nearest known high-density deepwater benthic community site is located approximately 54 miles (88 km) west of the lease area in MC 969 (Brooks et al., 2009). The site clearance survey by GEMS (2013) did not identify any features that could support high-density deepwater benthic communities within 2,000 ft (610 m) of the proposed drilling mud/cuttings discharge locations.

The only IPF identified for this project that could potentially affect high-density deepwater benthic communities is a large oil spill from a well blowout at the seafloor. A small fuel spill would not affect benthic communities because the diesel fuel would float and dissipate on the

sea surface.

Impacts of a Large Oil Spill

BOEM (2012a) concluded that oil spills would be unlikely to affect benthic communities beyond the immediate vicinity of the wellhead (i.e., due to physical impacts of a blowout) because the oil would rise quickly to the sea surface directly over the spill location. However, during the Macondo spill, subsurface plumes were reported at a water depth of about 3,600 ft (1,100 m), extending at least 22 miles (35 km) from the wellsite and persisting for more than a month (Camilli et al., 2010). The subsurface plumes apparently resulted from the use of dispersants at the wellhead (Joint Analysis Group, 2010c). Chemical components of subsea dispersants used during the Macondo spill persisted for up to 2 months and were detectable up to 186 miles (300 km) from the wellsite at a water depth of 3,280 to 3,937 ft (1,000 to 1,200 m) (Kujawinski et al., 2011). However, estimated dispersant concentrations in the subsea plume were below levels known to be toxic to marine life. While the behavior and impacts of subsurface plumes arenot well known, a subsurface plume could have the potential to contact high-density deepwater benthic communities beyond the 984-ft (300-m) radius estimated in BOEM (2012a), depending on its extent, trajectory, and persistence. Oil plumes that contact sensitive benthic communities before degrading could potentially impact the resource (BOEM, 2012b). Potential impacts on sensitive resources would be an integral part of the decision and approval process for the use of dispersants. The site clearance assessment by GEMS (2013) did not identify high-density deepwater benthic communities within 2,000 ft (610 m) of the proposed drilling mud/cuttings discharge locations. Potential impacts of oil on high-density deepwater benthic communities are discussed in MMS (2007b) and BOEM (2012b).

Although chemosynthetic communities live among hydrocarbon seeps, natural seepage occurs at a relatively constant low rate compared with the potential rates of oil release from a blowout. In addition, seep organisms require unrestricted access to oxygenated water at the same time as exposure to hydrocarbon energy sources (MacDonald, 2002). Oil droplets or oiled sediment particles could come into contact with chemosynthetic organisms or deepwater corals.

As discussed in MMS (2007b), impacts could include loss of habitat, biodiversity, and live coral coverage; destruction of hard substrate; change in sediment characteristics; and reduction or loss of one or more commercial and recreational fishery habitats. Sublethal effects could be long lasting and affect the resilience of coral colonies to natural disturbances (e.g., elevated water temperature and diseases) (BOEM, 2012c).

The potential for a spill to affect deepwater corals was observed during an October 2010 survey of deepwater coral habitats in water depths of 4,600 ft (1,400 m) approximately 7 miles (11 km) southwest of the Macondo wellhead. Much of the soft coral observed in a location measuring about 50 by 130 ft (15 by 40 m) was covered by a brown flocculent material (BOEMRE, 2010) with signs of stress, including varying degrees of tissue loss and excess mucous production (White et al., 2012a,b). Researchers concluded, based on hopanoid petroleum biomarker analysis of the flocculent material, that it contained oil from the Macondo spill. The injured and dead corals were in an area where a subsea plume of oil had been documented during the spill in June 2010. The deepwater coral at this location showed signs of tissue damage that was not observed elsewhere during these surveys or in previous deepwater coral studies in the Gulf of Mexico. The team of researchers concluded that the observed coral injuries likely resulted from exposure to the subsurface oil plume (White et al., 2012a,b).

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an

event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Potential impacts on sensitive resources would be an integral part of the decision and approval process for the use of dispersants. Therefore, no significant spill impacts on deepwater benthic communities are expected.



### C.2.3 Designated Topographic Features

The block is not within or near a designated topographic feature or a no-activity zone as identified in NTL 2009-G39. The nearest designated topographic feature stipulation block is Sackett Bank in West Delta Block 147, located 52 miles (83 km) northwest of the lease area.

There are no IPFs associated with either routine operations or accidents that could cause impacts to designated topographic features due to the distance from the lease area.

### C.2.4 Pinnacle Trend Area Live Bottoms

The lease area is not covered by the Live Bottom (Pinnacle Trend) Stipulation. As defined in NTL 2009-G39, the nearest pinnacle trend blocks are located about 91 miles (146 km)

north-northeast of the lease area in Main Pass Block 290.

There are no IPFs associated with either routine operations or accidents that could cause impacts to pinnacle trend area live bottoms due to the distance from the lease area.



### C.2.5 Eastern Gulf Live Bottoms

The lease area is not covered by the Live Bottom (Low-Relief) Stipulation, which pertains to seagrass communities and low-relief hard-bottom reef within the Gulf of Mexico Eastern Planning Area blocks in water depths of 328 ft (100 m) or less and portions of Pensacola and Destin Dome Area Blocks in the Central Planning Area. The nearest blocks covered by the live bottom stipulation, as defined in NTL 2009-G39, are about 121 miles (195 km) northeast of the project

area.

There are no IPFs associated with either routine operations or accidents that could cause impacts

to eastern Gulf of Mexico live bottom areas due to the distance from the lease area.



## C.3 Threatened, Endangered, and Protected Species and Critical Habitat

This section discusses species listed as endangered or threatened under the ESA. In addition, it includes all marine mammal species in the region that are protected under the MMPA.

Endangered, threatened, or species of concern that may occur in the project area and/or along

the northern and eastern Gulf Coast are listed in Table 5 . The table also indicates the location of designated critical habitat in the Gulf of Mexico. Critical habitat is defined as (1) specific areas within the geographical area occupied by the species at the time of listing, if they contain physical or biological features essential to conservation, and those features may require special management considerations or protection; and (2) specific areas outside the geographical area occupied by the species if the agency determines that the area itself is essential for conservation. The NMFS has jurisdiction over ESA-listed cetaceans and fishes in the Gulf of Mexico. The USFWS has jurisdiction over ESA-listed birds and the West Indian manatee. These two agencies share federal jurisdiction over sea turtles, with NMFS having lead responsibility at sea and USFWS on nesting beaches.

Table 5. Listed endangered and threatened species in the lease area and along the northern and

eastern Gulf Coast.

Species Scientific Name Status Potential Presence Critical Habitat Designated in

Gulf of Mexico Lease

Area Coastal

Marine Mammals

Sei whale Balaenoptera borealis E X a

-- None

Blue whale Balaenoptera musculus E X a

-- None

Fin whale Balaenoptera physalus E X a

-- None
North Atlantic right whale Eubalaena glacialis E X a

-- None
Humpback whale Megaptera novaeangliae E X a

-- None
Sperm whale Physeter macrocephalus E X

-- None

West Indian manatee Trichechus manatus latirostris E

-- X Florida (Peninsular)

Sea Turtles
Loggerhead turtle Caretta caretta T, E b X X Proposed b

Green turtle Chelonia mydas T, E c X X None

### Table 5. (Continued).

Species Scientific Name Status Potential Presence Critical Habitat Designated in

Gulf of Mexico Lease

Area Coastal

Leatherback turtle Dermochelys coriacea E X X None

Hawksbill turtle Eretmochelys imbricata E X X None Kemp’s ridley turtle Lepidochelys kempii E X X None

Birds

Piping P lover Charadrius melodus T

-- X Coastal Texas, Louisiana, Mississippi, Alabama, and Florida (Panhandle)

Whooping C rane Grus americana E

-- X Coastal Texas (Aransas National Wildlife Refuge)

Fishes

Gulf sturgeon Acipenser oxyrinchus desotoi T

-- X Coastal Louisiana, Mississippi, Alabama, and Florida (Panhandle)

Terrestrial Mammals
Beach mouse (Alabama, Choctawhatchee,

Perdido Key, St. Andrew) Peromyscus polionotus E

-- X Alabama and Florida (Panhandle) beaches

Abbreviations: E = Endangered; T = Threatened. a The blue, fin, humpback, North Atlantic right, and sei whales are rare or extralimital in the Gulf of Mexico and are
unlikely to be present in the lease area.

b The loggerhead turtle is composed of nine distinct population segments (DPS) that are considered “species.” The
only DPS that may occur in the project area (Northwest Atlantic DPS) is listed as threatened ( 76 Federal Register
[ FR ] 58868; September 22, 2011). The National Marine Fisheries Service and U.S. Fish and Wildlife Service hav e proposed to designate critical habitat for this DPS, including beaches in Jackson County, Mississippi; Baldwin
County, Alabama; and Bay, Gulf, and Franklin Counties in the Florida panhandle, as well as several counties in southwest Florida and the Florida Keys (78 FR 18000).
c The green sea turtle is threatened except for the Florida breeding population, which is listed as endangered.

The sperm whale and five species of sea turtles are the only endangered or threatened species likely to occur at or near the lease area. No critical habitat has been designated for these species

in the Gulf of Mexico.

Five endangered mysticete whales (blue whale, fin whale, humpback whale, North Atlantic right whale, and sei whale) have also been reported from the Gulf of Mexico but are considered rare or extralimital there (Würsig et al., 2000). No critical habitat has been designated for these species

in the Gulf of Mexico.

Coastal endangered or threatened species include the West Indian manatee, Piping Plover, Whooping Crane, Gulf sturgeon, and four subspecies of beach mouse. Critical habitat has been designated for all of these species as indicated in Table 5 and discussed in individual sections.

Two other coastal species (Bald Eagle and Brown Pelican) discussed in MMS (2007b) and BOEM (2012b) are no longer federally listed as endangered or threatened; these species are

discussed in Section C.4.2

, Shorebirds and Coastal Nesting Birds

.

There are no other endangered animals or plants in the Gulf of Mexico that are reasonably likely to be affected by either routine or accidental events. Other species occurring at certain locations in the Gulf of Mexico such as the smalltooth sawfish ( Pristis pectinata ), elkhorn coral (

Acropora palmata ), staghorn coral ( Acropora cervicornis ), and Florida salt marsh vole( Microtus pennsylvanicus dukecampbelli ) are remote from the lease area and highly unlikely to be

affected.



### C.3.1 Sperm Whale (Endangered)

The only endangered marine mammal likely to be present at or near the project area is the sperm whale ( Physeter macrocephalus ). Resident populations of sperm whales occur within the Gulf of Mexico. A species description is presented in MMS (2007b). Gulf of Mexico sperm whales are classified as an endangered sp ecies and a “strategic stock” (defined as a stock that may have unsustainable human-caused impacts) by NMFS (Waring et al., 2013). No critical habitat for the sperm whale has been designated in the Gulf of Mexico.

The distribution of sperm whales in the Gulf of Mexico is correlated with mesoscale physical features such as eddies associated with the Loop Current (Jochens et al., 2008). Sperm whale populations in the north-central Gulf of Mexico are present there throughout the year (Davis et al., 2000). Results of a multi-year tracking study show female sperm whales typically concentrated along the upper continental slope between the 656- and 3,280-ft (200- and 1,000-m) depth contours (Jochens et al., 2008). Male sperm whales were more variable in their movements and were documented in water depths greater than 9,843 ft (3,000 m). Generally, groups of sperm whales sighted in the Gulf of Mexico during the MMS-funded Sperm Whale Seismic Study consisted of mixed-sex groups comprising adult females and immatures, and groups of bachelor males. Typical group size for mixed groups was 10 individuals (Jochens et al., 2008). A review of sighting reports from seismic mitigation surveys in the Gulf of Mexico conducted over a 6-year period found a mean group size for sperm whales of 2.5 individuals (Barkaszi et al., 2012).

In these mitigation surveys, sperm whales were the most common cetacean encountered (Barkaszi et al., 2012). Results of the Sperm Whale Seismic Study showed that sperm whales transit through the vicinity of the lease area. Movements of satellite-tracked individuals suggest that this area of the Gulf continental slope is within the home range of the Gulf of Mexico population (within the 95% utilization distribution) (Jochens et al., 2008).

Current threats to sperm whale populations worldwide are discussed in a final recovery plan for the sperm whale published by NOAA (NMFS, 2010a). Threats are defined as “any factor that could represent an impediment to recovery,” and include fisheries interactions , anthropogenic noise, vessel interactions, contaminants and pollutants, disease, injury from marine debris, research, predation and natural mortality, direct harvest, competition for resources, loss of prey base due to climate change and ecosystem change, and cable laying. In the Gulf of Mexico, the impacts from many of these threats are identified as either low or unknown (BOEMRE, 2011; BOEM, 2012c).

IPFs that could potentially affect sperm whales include drilling rig presence, noise, and lights; support vessel and helicopter traffic noise; support vessel strikes; and two types of accidents

– a small fuel spill and a large oil spill. Effluent discharges are likely to have negligible impacts on sperm whales due to rapid dispersion, the small area of ocean affected, the intermittent nature of the discharges, and the mobility of these marine mammals. Compliance with NTL 2012-BSEE-G01 will minimize the potential for marine debris-related impacts on sperm whales.

Impacts of Drilling Rig Presence, Noise, and Lights

Some sounds produced by the drilling rig may be emitted at levels that could potentially disturb individual whales or mask the sounds animals would normally produce or hear. Noise associated with drilling is relatively weak in intensity, and an indi vidual animal’s noise exposure would betransient. As discussed in Section A.1 , the bandwidth of sounds generated by the drilling rig is approximately 10 to 500 Hz.

Sperm whales appear to have good low-frequency hearing, with variable responses to anthropogenic noise (Jochens et al., 2008). The sperm whale may possess better low-frequency hearing than some of the other odontocetes, although not as low as many baleen whale species that produce sounds within a bandwidth between 30 Hz and greater than 5 kHz (Wartzok and Ketten, 1999). Southall et al. (2007) lists sperm whales in the same hearing group (i.e., mid-frequency cetaceans) as dolphins, toothed whales, beaked whales, and bottlenose whales (estimated hearing range from 150 Hz to 160 kHz). Generally, most of the acoustic energy from sperm whales is present at frequencies below 4 kHz, although diffuse energy up to and past 20 kHz has been reported, with source levels up to 236 dB re 1 μPa at 1 m. Other studies indicate sperm whales’ wideband clicks contain energy between 0.1 and 20 kHz (Weilgart and Whitehead, 1993; Goold and Jones, 1995). Most observations of behavioral responses of marine mammals to anthropogenic sounds, in general, have been limited to short-term behavioral responses, which included the cessation of feeding, resting, or social interactions (NMFS, 2009a).

Observations of sperm whales near offshore oil and gas operations suggest an inconsistent response to anthropogenic marine sound (Jochens et al., 2008). Sounds produced during drilling operations are generally constant (rather than pulsed or intermittent) and at levels that may be louder than, and of a similar frequency to, the auditory signal received by sperm whales. Animals can determine the direction from which a sound arrives based on cues, such as difference in arrival times, sound levels, and phases at the two ears. Thus, an animal’s directional hearing capabilities have a bearing on its vulnerability to masking (NRC, 2003a). Behavioral changes for marine mammals such as the sperm whale to auditory masking sounds may include producing more calls, longer calls, or shifting the frequency of the calls (NMFS, 2009a; Holt et al., 2009).

In addition, there are other OCS facilities and activities near the lease area, and the region as a whole has a large number of similar sound sources. Drilling-related noise associated with this project will contribute to increases in the ambient noise environment of the Gulf of Mexico, but it is not expected in amplitudes sufficient enough to cause either hearing or behavioral effects to sperm whales.

The drilling rig used during the proposed activity will be located within a deepwater, open ocean environment and will maintain position during drilling operations. Sounds generated by the rig and by drilling operations will be generally continuous with some variability in sound level. This analysis assumes that the continuous nature of sounds produced by the drilling rig will provide individual whales with cues relative to the direction and relative distance (sound intensity) of the sound source, and the fixed position of the drilling rig will provide multiple options for active avoidance of potential physical impacts.

NMFS analyzed the potential for impacts of drilling-related noise on sperm whales in its Biological Opinion for the Five-Year Oil and Gas Leasing Program in the Central and Western Planning Areas of the Gulf of Mexico (NMFS, 2007). The analysis noted that drilling rigs show low sound source levels and concluded that drilling is not expected to produce amplitudes sufficient to cause hearing or behavioral effects in sperm whales; therefore, these effects are insignificant (NMFS, 2007).

Although offshore lighting and presence of drilling rigs and OCS vessels were considered potential factors affecting sperm whales , NMFS’s 2007 Biological Opinion and lease sale EISs (MMS, 2007b; BOEM, 2012b,c, 2013) did not identify these as IPFs for sperm whales. Therefore, no significant impacts are expected.Impacts of Support Vessel and Helicopter Traffic

Support vessel traffic has the potential to disturb sperm whales. There is also a risk of vessel strikes, which are identified as a threat in the recovery plan for this species (NMFS, 2010a). Data concerning the frequency of vessel strikes are presented in the lease sale EIS (MMS, 2007b).

To reduce the potential for vessel strikes, the BOEM has issued NTL 2012-JOINT-G01, which recommends protected species identification training and that vessel operators and crews maintain a vigilant watch for marine mammals and slow down or stop their vessel to avoid striking protected species, and requires operators to report sightings of any injured or dead protected species. When whales are sighted, vessel operators and crews are required to attempt to maintain a distance of 300 ft (91 m) or greater whenever possible. Vessel operators are required to reduce vessel speed to 10 knots or less, when safety permits, when mother/calf pairs, pods, or large assemblages of cetaceans are observed near an underway vessel. Compliance

with this NTL will minimize the likelihood of vessel strikes as well as reduce the chance for disturbing sperm whales.

NMFS (2007) analyzed the potential for vessel strikes and harassment of sperm whales in its Biological Opinion for the Five-Year Oil and Gas Leasing Program in the Central and Western Planning Areas of the Gulf of Mexico (NMFS, 2007). With implementation of the mitigation measures in NTL 2012-JOINT-G01, NMFS concluded that the likelihood of collisions between vessels and sperm whales would be reduced to insignificant levels. NMFS concluded that the observed avoidance of passing vessels by sperm whales is an advantageous response to avoid a potential threat and is not expected to result in any significant effect on migration, breathing, nursing, breeding, feeding, or sheltering to individuals, or have any consequences at the level of the population. With implementation of the vessel strike avoidance measures requirement to maintain a distance of 295 ft (90 m) from sperm whales, NMFS concluded that the potential for harassment of sperm whales would be reduced to discountable levels.

Helicopter traffic also has the potential to disturb sperm whales. Smultea et al. (2008) documented responses of sperm whales offshore Hawaii to fixed wing aircraft flying at an altitude of 800 ft (245 m). A reaction to the initial pass of the aircraft was observed during 3 (12%) of

24 sightings. All three reactions consisted of a hasty dive and occurred at less than 1,180 ft (360 m) lateral distance from the aircraft. Additional reactions were seen when aircraft circled certain whales to make further observations. Based on other studies of cetacean responses to sound, the authors concluded that the observed reactions to brief overflights by the aircraft were short-term and probably of no long-term biological significance.

Helicopters maintain altitudes above 700 ft (213 m) during transit to and from the offshore working area. In the event that a whale is seen during transit, the helicopter will not approach or circle the animal(s). In addition, guidelines and regulations specify that helicopters maintain an altitude of 1,000 ft (305 m) within 300 ft (91 m) of marine mammals (BOEM, 2012a,b). Although whales may respond to helicopters (Smultea et al., 2008), NMFS (2007) and BOEM (2012a) concluded that this altitude would minimize the potential for disturbing sperm whales. Therefore, no significant impacts are expected.

Impacts of a Small Fuel Spill

Potential spill impacts on marine mammals including sperm whales are discussed in MMS (2007b) and BOEM (2012b,c, 2013) and the Biological Opinion for the Five-Year Oil and Gas Leasing Program in the Central and Western Planning Areas of the Gulf of Mexico (NMFS, 2007). Oil impacts on marine mammals are discussed by Geraci and St. Aubin (1990). For this EP, there are no unique site-specific issues with respect to spill impacts on these animals.

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation ofShell’s OSRP will mitigate and reduce the potential for impacts on sperm whales. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area and the duration of a small spill, the opportunity for impacts to occur would be very brief.

A small fuel spill in offshore waters would produce a slick on the water surface and increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Section A.9.2 discusses the likely fate of a small fuel spill and indicates that more than 90% would be evaporated or dispersed naturally within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions.

Direct physical and physiological effects of exposure to diesel fuel could include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes; ingestion of oil directly or via contaminated prey; and stress from the activities and noise of response vessels and aircraft (Marine Mammal Commission [MMC], 2011). However, due to the limited areal extent and short duration of water quality impacts from a small fuel spill, as well as the mobility of sperm whales, no significant impacts are expected.

Impacts of a Large Oil Spill

Potential spill impacts on marine mammals including sperm whales are discussed in

MMS (2007b), BOEM (2012a,b,d), and in NMFS (2007). Oil impacts on marine mammals are discussed by Geraci and St. Aubin (1990). For this EP, there are no unique site-specific issues with respect to spill impacts on these animals.

Impacts of oil spills on sperm whales can include direct impacts from oil exposure, as well as indirect impacts due to response activities and materials (e.g., vessel traffic, noise, and dispersants) (MMC, 2011). Direct physical and physiological effects can include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes; ingestion of oil (and dispersants) directly or via contaminated prey; and stress from the activities and noise of response vessels and aircraft. The level of impact of oil exposure depends on the amount, frequency, and duration of exposure; route of exposure; and type or condition of petroleum compounds or chemical dispersants (Waring et al., 2013). Complications of the above may lead to dysfunction of immune and reproductive systems, physiological stress, declining physical condition, and death. Behavioral responses can include displacement of animals from prime habitat, disruption of social structure, changing prey availability and foraging distribution and/or patterns, changing reproductive behavior/productivity, and changing movement patterns or migration (MMC, 2011). Ackleh et al. (2012) hypothesized that sperm whales may have temporarily relocated away from areas near the Macondo spill in 2010.

In the event of a large spill, the level of vessel and aircraft activity associated with spill response could disturb sperm whales and potentially result in vessel strikes, entanglement, or other injury or stress. Response vessels would operate in accordance with NTL 2012-JOINT-G01 to reduce the potential for striking or disturbing these animals.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Se ction 9b provides detail on spill response measures. Therefore, no significant spill impacts on sperm whales are expected.

### C.3.2 West Indian Manatee (Endangered)

Most of the Gulf of Mexico manatee population is located in peninsular Florida (USFWS, 2001). Manatees regularly migrate farther west of Florida in the warmer months (Wilson, 2003) into Alabama and Louisiana coastal environs, with some individuals traveling as far west as Texas (Fertl et al., 2005). A species description is presented in MMS (2007b) and in the recovery plan for this species (USFWS, 2001).

IPFs that could potentially affect manatees include support vessel and helicopter traffic and a large oil spill. A small fuel spill in the lease area would be unlikely to affect manatees, as the lease area is approximately 65 miles (105 km) from the nearest shoreline (Louisiana).

As explained in Section A.9.2 , a small fuel spill would not be expected to make landfall or reach coastal waters prior to breaking up. Compliance with NTL 2012-BSEE- G0 1 will minimize the potential for marine debris-related impacts on manatees. Consistent with the analysis in BOEM (2012a), impacts of routine project-related activities on the manatee would be negligible.

Impacts of Support Vessel and Helicopter Traffic

Support vessel traffic has the potential to disturb manatees, and there is also a risk of vessel strikes, which are identified as a threat in the recovery plan for this species (USFWS, 2001).

To reduce the potential for vessel strikes, the BOEM has issued NTL 2012-JOINT-G01, which recommends protected species identification training and that vessel operators and crews maintain a vigilant watch for marine mammals and slow down or stop their vessel to avoid striking protected species, and requires operators to report sightings of any injured or dead protected species. Compliance with NTL 2012-JOINT-G01 will minimize the likelihood of vessel strikes, and no significant impacts on manatees are expected.

Helicopter traffic, if present, also has the potential to disturb manatees. Rathbun (1988) reported that manatees were disturbed more by helicopters than by fixed-wing aircraft; however, the helicopter was flown at relatively low altitudes of 66 to 525 ft (20 to 160 m). Helicopters used in support operations maintain a minimum altitude of 700 ft (213 m) while in transit offshore, 1,000 ft (305 m) over unpopulated areas or across coastlines, and 2,000 ft (610 m) over populated areas and sensitive habitats such as wildlife refuges and park properties. In

addition

, guidelines and regulations specify that helicopters maintain an altitude of 1,000 ft (305 m) within 300 ft (91 m) of marine mammals (BOEM, 2012a,b). This mitigation measure will minimize the potential for disturbing manatees, and no significant impacts are expected.

Impacts of a Large Oil Spill

The OSRA results summarized in Table 3 predict that some Texas, Louisiana, and Florida shorelines could be contacted by a large oil spill within 30 days. There is no critical habitat designated in these areas, and the number of manatees potentially present is a small fraction of the population in peninsular Florida.

In the event that manatees were exposed to oil, effects could include direct impacts from oil exposure, as well as indirect impacts due to response activities and materials (e.g., vessel traffic, noise, and dispersants) (MMC, 2011). Direct physical and physiological effects can include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes; ingestion of oil (and dispersants) directly or via contaminated prey (or contaminated vegetation, in the case of manatees); and stress from the activities and noise of response vessels and aircraft. Complications of the above may lead to dysfunction of immune and reproductive systems, physiological stress, declining physical condition, and death. Behavioral responses can include displacement of animals from prime habitat, disruption of social structure, changing prey availability and foraging distribution and/or patterns, changing reproductive behavior/productivity, and changing movement patterns or migration (MMC, 2011).In the event that a large spill reached coastal waters where manatees were present, the level of vessel and aircraft activity associated with spill response could disturb manatees and potentially result in vessel strikes, entanglement, or other injury or stress. Response vessels would operate in accordance with NTL 2012-JOINT-G01 to reduce the potential for striking or disturbing these animals, and therefore no significant impacts are expected.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementat ion of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on manatees are expected.



### C.3.3 Endangered Mysticete Whales

Five endangered mysticete whales (blue whale, fin whale, humpback whale, North Atlantic right whale, and sei whale) have also been reported from the Gulf of Mexico, but are considered rare or extralimital there (Würsig et al., 2000). No critical habitat has been designated for these species in the Gulf of Mexico.

Due to the rare occurrence of these whales in the Gulf of Mexico, it is unlikely that any endangered mysticete would come into contact with any project activities, either routine operations or accidents.

Mysticete whales were not included as affected species in the Biological Opinion for the Five-Year Oil and Gas Leasing Program in the Central and Western Planning Areas of the Gulf of Mexico (NMFS, 2007). Potential impacts analyzed in MMS (2007b) and BOEM (2012a,b,d) are incorporated by reference. If any of these whales were present in the area, potential impacts

would be the same as those discussed in Section C.3.4

.



### C.3.4 Non-Endangered Marine Mammals (Protected)

In addition to the seven endangered species that have been cited previously, 22 additional species of marine mammals may be found in the Gulf of Mexico, including 2 species of mysticete whales, the dwarf and pygmy sperm whales, 4 species of beaked whales, and

14 species of delphinids (see EP Section 6h ). All marine mammals are protected species under the MMPA. The most common non-endangered cetaceans in the deepwater environment are odontocetes such as the pantropical spotted dolphin, spinner dolphin, and Clymene dolphin. A brief summary is presented in this section, and additional information on these groups is presented in MMS (2007b).

Mysticete whales . Two species of non-endangered mysticete whales are known from the Gulf of

Mexico: the Bryde’s whale ( Balaenoptera edeni ) and minke whale ( Balaenoptera acutorostrata ).

The Bryde’s whale ( Balaenoptera edeni ) has been sighted most frequently along the 328-ft (100- m) isobath (Davis and Fargion, 1996; Davis et al., 2000). Most sightings have been made in the DeSoto Canyon region and off western Florida, although there have been some in the west-central portion of the northeastern Gulf. The minke whale is considered rare in the Gulf of Mexico, with the only confirmed records coming from strandings (Würsig et al., 2000). Based on the available data, it is possible that Bryde’s whales could occur in the lease area.

Dwarf and pygmy sperm whales . At sea, it is difficult to differentiate dwarf sperm whales ( Kogia sima

) from pygmy sperm whales ( Kogia breviceps ), and sightings are often grouped together as “ Kogia spp.” Both species have a worldwide distribution in temperate to tropical waters. In the Gulf of Mexico, both species occur primarily along the continental shelf edge and in deeper waters off the continental shelf (Mullin et al., 1991; Mullin, 2007; Waring et al., 2013). Either species could occur in the lease area.Beaked whales . Four species of beaked whales are known from the Gulf of Mexico. They are Blainville’s beaked whale ( Mesoplodon densirostris ), Cuvier’s beaked whale ( Ziphius cavirostris ),

S owerby’s beaked whale ( Mesoplodon bidens ), and Gervais’ beaked whale ( Mesoplodon europaeus ). Stranding records in the Gulf of Mexico suggest that Gervais’ beaked whale is the most common, and Sowerby’s beaked whale is extralimital. Due to the difficultie s of

at

- sea identification, beaked whales in the Gulf of Mexico are identified either as Cuvier’s beaked whales or are grouped into an undifferentiated complex ( Mesoplodon spp. and Ziphius

spp.).

In the northern Gulf of Mexico, they are broadly distributed in waters greater than 3,281 ft (1,000 m) over lower slope and abyssal landscapes (Davis et al., 2000). Any of these species could occur in the lease area (Waring et al., 2013).

Delphinids . Fourteen species of delphinids are known from the Gulf of Mexico, including Atlantic spotted dolphin ( Stenella frontalis ), bottlenose dolphin ( Tursiops truncatus

), Clymene dolphin ( Stenella clymene

), false killer whale ( Pseudorca crassidens ), Fraser’s dolphin ( Lagenodelphis

hosei ), killer whale ( Orcinus orca ), melon-headed whale ( Peponocephala electra ), pantropical spotted dolphin ( Stenella attenuata ), pygmy killer whale ( Feresa attenuata ), short-finned pilot whale ( Globicephala macrorhynchus ), Risso’s dolphin ( Grampus griseus ), rough-toothed dolphin ( Steno bredanensis

), spinner dolphin ( Stenella longirostris ), and striped dolphin ( Stenella

coeruleoalba

). The most common non-endangered cetaceans in the deepwater environment are the pantropical spotted dolphin, spinner dolphin, and Clymene dolphin. However, any of these species could occur in the lease area (Waring et al., 2013)

.

The bottlenose dolphin ( Tursiops truncatus

) is a common inhabitant of the northern Gulf of Mexico, particularly within continental shelf waters. There are two ecotypes of bottlenose dolphins, a coastal form and an offshore form, which are genetically isolated from each other (Waring et al., 2013). The offshore form of the bottlenose dolphin may occur within the lease area. Inshore populations of coastal bottlenose dolphins in the northern Gulf of Mexico are separated by the NMFS into 37 geographically distinct population units, or stocks, for management purposes (Waring et al., 2013). NMFS (2013) has proposed to classify the Gulf of Mexico Northern Coastal Stock, Western Coastal Stock, and all 32 of the Bay, Sound, and Estuarine Stocks as strategic stocks. A “strategic” stock is defined by the MMPA as a marine

mammal stock.

 for which the level of direct human-caused mortality exceeds the potential biological removal level;

 which, based on the best available scientific information, is declining and is likely to be listed as a threatened species under the ESA within the foreseeable future; or

 which is listed as a threatened or endangered species under the ESA, or is designated as depleted under the MMPA.

The strategic stock designation in this case was based primarily on the occurrence of an “Unusual Mortality Event” (UME) of unprecedented size and duration that has affected these stock areas. This UME began in February 2010 and, as of late 2013, the event was still considered to be ongoing (NOAA, 2013; Waring et al., 2013). Carmichael et al. (2012) hypothesized that the unusual number of bottlenose dolphin strandings in the northern Gulf of Mexico during this time may have been associated with environmental perturbations, including sustained cold weather and the Macondo spill in 2010, as well as large volumes of cold freshwater discharge in the early

months of 2011.

IPFs that could potentially affect non-endangered marine mammals include drilling rig presence, noise, and lights; support vessel and helicopter traffic; and two types of accidents (a small fuel spill and a large oil spill). Effluent discharges are likely to have negligible impacts on marine mammals due to rapid dispersion, the small area of ocean affected, the intermittent nature of thedischarges, and the mobility of marine mammals. Compliance with NTL 2012-BSEE-G01 will minimize the potential for marine debris-related impacts on marine mammals.

Impacts of Drilling Rig Presence, Noise, and Lights

Noise from routine drilling activities has the potential to disturb marine mammals. Most odontocetes (toothed whales and dolphins) use higher frequency sounds than those produced by OCS drilling activities (Richardson et al., 1995). Noise associated with drilling is relatively weak in intensity, and an individual animal’s noise exposure would be transient. Stronger noise levels will occur during thruster use in dynamic positioning. Thruster noise impacts would be expected at greater distances than vessel noise alone (LGL Ecological Research Associates, Ltd., 2006) but are dependent on variables relating to thruster type and usage. It is expected that marine mammals within or near the lease area would be able to detect the presence of the drilling rig and avoid exposure to higher energy sounds, particularly within an open ocean environment.

Some odontocetes have shown increased feeding activity around lighted platforms at night (Todd et al., 2009). Even temporary drilling rigs present an attraction to pelagic food sources that may attract cetaceans (and sea turtles). Therefore, prey congregation could pose an attraction to protected species that exposes them to higher levels or longer durations of noise that might

otherwise be avoided.

There are other OCS facilities and activities near the lease area, and the region as a whole has a large number of similar sources. Due to the limited scope, timing, and geographic extent of drilling activities, this project would represent a small temporary contribution to the overall noise regime, and any short-term impacts are not expected to be biologically significant to marine mammal populations.

Drilling rig lighting and presence are not identified as IPFs for marine mammals in MMS (2007b) or BOEM (2012a,b,c). Therefore, no significant impacts are expected.

Impacts of Support Vessel and Helicopter Traffic

Support vessel traffic has the potential to disturb marine mammals, and there is also a risk of vessel strikes. Data concerning the frequency of vessel strikes are presented in the lease sale EIS (MMS, 2007b). To reduce the potential for vessel strikes, the BOEM and BSEE have issued NTL 2012-JOINT-G01, which recommends protected species identification training and that vessel operators and crews maintain a vigilant watch for marine mammals and slow down or stop their vessel to avoid striking protected species, and requires operators to report sightings of any injured or dead protected species. Vessel operators and crews are required to attempt to maintain a distance of 300 ft (91 m) or greater when whales are sighted and 150 ft (45 m) when small cetaceans are sighted. When cetaceans are sighted while a vessel is underway, vessels must attempt to remain parallel to the animal’s course and avoid exce ssive speed or abrupt changes in direction until the cetacean has left the area. Vessel operators are required to reduce vessel speed to 10 knots or less when mother/calf pairs, pods, or large assemblages of cetaceans are observed near an underway vessel, when safety permits. Compliance with this NTL will minimize the likelihood of vessel strikes as well as reduce the chance for disturbing marine mammals, and therefore no significant impacts are expected.

Aircraft traffic also has the potential to disturb marine mammals (Würsig et al., 1998). However, while flying offshore, helicopters maintain altitudes above 700 ft (213 m) during transit to and from the working area. In addition, guidelines and regulations specify that helicopters maintain an altitude of 1,000 ft (305 m) within 300 ft (91 m) of marine mammals (BOEM, 2012a,b). This altitude will minimize the potential for disturbing marine mammals, and no significant impacts are expected (BOEM, 2012a,b).Impacts of a Small Fuel Spill

Potential spill impacts on marine mammals are discussed in MMS (2007b) and BOEM (2012a,b,d), and oil impacts on marine mammals in general are discussed in Geraci and St. Aubin (1990). For this EP, there are no unique site-specific issues with respect to spill impacts on these animals.

The probability of a fuel spill will be minimized by Shell’s preventative measures, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP is expected to mitigate and reduce the potential for impacts on marine mammals. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area and the duration of a small spill, the opportunity for impacts to occur would be very brief.

A small fuel spill in offshore waters would produce a slick on the water surface and increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Section A.9.2 discusses the likely fate of a small fuel spill and indicates that over 90% would be evaporated or dispersed naturally within

24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions.

Direct physical and physiological effects of exposure to diesel fuel could include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes; ingestion of oil directly or via contaminated prey; and stress from the activities and noise of response vessels and aircraft (MMC, 2011). However, due to the limited areal extent and short duration of water quality impacts from a small fuel spill, as well as the mobility of marine mammals, no significant impacts would be expected.

Impacts of a Large Oil Spill

Potential spill impacts on marine mammals are discussed in MMS (2007b), BOEM (2012a,b,d), and in Geraci and St. Aubin (1990). For this EP, there are no unique site-specific issues.

Impacts of oil spills on marine mammals can include direct impacts from oil exposure, as well as indirect impacts due to response activities and materials (e.g., vessel traffic, noise, and dispersants) (MMC, 2011). Direct physical and physiological effects can include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes; ingestion of oil (and dispersants) directly or via contaminated prey (or contaminated vegetation, in the case of manatees); and stress from the activities and noise of response vessels and aircraft. Complications of the above may lead to dysfunction of immune and reproductive systems, physiological stress, declining physical condition, and death. Behavioral responses can include displacement of animals from prime habitat; disruption of social structure; changing prey availability and foraging distribution and/or patterns; changing reproductive behavior/productivity; and changing movement patterns or migration (MMC, 2011).

In the event of a large spill, the level of vessel and aircraft activity associated with spill response could disturb marine mammals and potentially result in vessel strikes, entanglement, or other injury or stress. Response vessels would operate in accordance with NTL 2012-JOINT-G01 to reduce the potential for striking or disturbing these animals, and therefore no significant impacts are expected. A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention

measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of
Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on marine mammals are expected.

### C.3.5 Sea Turtles (Endangered/Threatened)

As listed in EP Section 6h , five species of endangered or threatened sea turtles may be found near the lease area. Endangered species are the leatherback ( Dermochelys coriacea ), Kemp's ridley ( Lepidochelys kempii ), and hawksbill ( Eretmochelys imbricata ) turtles. The distinct population segment (DPS) of loggerhead turtle ( Caretta caretta ) that occurs in the Gulf of Mexico is listed as threatened, although other DPSs are endangered. The green turtle ( Chelonia mydas ) is listed as threatened, except for the Florida breeding population, which is listed as endangered. Species descriptions are presented in MMS (2007b).

Leatherbacks and loggerheads are the most likely species to be present near the lease area as adults. Green, hawksbill, and Kemp’s ridley turtles are typically inner shelf and nearshore species, unlikely to occur near the lease area as adults. Hatchlings or juveniles of any of the sea turtles may be present in deepwater areas, including the lease area, where they may be

associated with Sargassum and other flotsam.

All five sea turtle species in the Gulf of Mexico are migratory and use different marine habitats according to their life stage. These habitats include high-energy beaches for nesting females and emerging hatchlings and pelagic convergence zones for hatchling and juvenile turtles. As adults, green, hawksbill, and loggerhead turtles forage primarily in shallow, benthic habitats. Leatherbacks are the most pelagic of the sea turtles, feeding primarily on jellyfish.

Sea turtle nesting in the northern Gulf of Mexico can be summarized by species as follows:

 Loggerhead turtles

– Loggerhead turtles nest in significant numbers along the Florida Panhandle and, to a lesser extent, from Texas through Alabama (NMFS and USFWS, 2008). The nearest significant nesting area of loggerhead turtles is found in Louisiana, on beaches within the Breton NWR;

 Green and leatherback turtles

– Green and leatherback turtles infrequently nest on Florida Panhandle beaches (Florida Fish and Wildlife Conservation Commission, 2013a,b);

 Kemp’s ridley turtles – The main nesting site of the Kemp’s ridley turtle is Rancho Nuevo beach, Tamaulipas, Mexico (NMFS et al., 2011). Approximately 200 Kemp’s ridley turtles nested on Texas beaches in 2009 (Sea Turtle Restoration Project, 2011). Kemp’s ridley turtles typically do not nest anywhere near the project area, although there have been occasional reports of nesting in Alabama (Share the Beach,2014); and

 Hawksbill turtles

–

Hawksbill turtles typically do not nest anywhere near the project area (USFWS, 2013).

IPFs that could potentially affect sea turtles include drilling rig presence, noise, and lights; support vessel and helicopter traffic; and two types of accidents

– a small fuel spill and a large oil spill. Effluent discharges are likely to have negligible impacts on sea turtles due to rapid dispersion, the small area of ocean affected, and the intermittent nature of the discharges. Compliance with NTL 2012-BSEE-G01 will minimize the potential for marine debris-related impacts on sea turtles.

Impacts of Drilling Rig Presence, Noise, and Lights

Offshore drilling activities produce a broad array of sounds at frequencies and intensities that may be detected by sea turtles (Geraci and St. Aubin, 1987). Potential impacts may include behavioral disruption and temporary or permanent displacement from the area near the sound source. Certain sea turtles, especially loggerheads, may be attracted to offshore structures (Lohoefener et al., 1990) and, thus, may be more susceptible to impacts from sounds produced during routine operations. Helicopters and service vessels may also affect sea turtles due to machinery noise and/or visual disturbances. The most likely impacts would be short-term behavioral changes such as diving and evasive swimming, disruption of activities, or departurefrom the area. Due to the limited scope, timing, and geographic extent of drilling activities, these short-term impacts are not expected to be biologically significant to sea turtle populations.

Artificial lighting can disrupt the nocturnal orientation of sea turtle hatchlings (Witherington, 1997; Tuxbury and Salmon, 2005). However, hatchlings may rely less on light cues when they are offshore than when they are emerging on the beach (Salmon and Wyneken, 1990). NMFS (2007) concluded that the effects of lighting from offshore structures on sea turtles are insignificant. Therefore, no significant impacts are expected.

Impacts of Support Vessel and Helicopter Traffic

Support vessel traffic has the potential to disturb sea turtles, and there is also a risk of vessel strikes. Data show that vessel traffic is one cause of sea turtle mortality in the Gulf of Mexico (Lutcavage et al., 1997). While adult sea turtles are visible at the surface during the day and in clear weather, they can be difficult to spot from a moving vessel when resting below the water surface, during nighttime, or during periods of inclement weather. To reduce the potential for vessel strikes, the BOEM and BSEE have issued NTL 2012-JOINT-G01, which recommends protected species identification training and that vessel operators and crews maintain a vigilant watch for sea turtles and slow down or stop their vessel to avoid striking protected species, and requires operators to report sightings of any injured or dead protected species. When sea turtles are sighted, vessel operators and crews are required to attempt to maintain a distance of 150 ft (45 m) or greater whenever possible. Compliance with this NTL will minimize the likelihood of vessel strikes as well as reduce the chance for disturbing sea turtles (NMFS, 2007). Therefore, no significant impacts are expected.

Helicopter traffic also has the potential to disturb sea turtles. However, while flying offshore, helicopters maintain altitudes above 700 ft (213 m) during transit to and from the working area. This altitude will minimize the potential for disturbing sea turtles, and no significant impacts are expected.

Impacts of a Small Fuel Spill

Potential spill impacts on sea turtles are discussed in MMS (2007b), BOEM (2012b,c, 2013), and in NMFS (2007) in its Biological Opinion for the Five-Year Oil and Gas Leasing Program in the Central and Western Planning Areas of the Gulf of Mexico. For this EP, there are no unique site-specific issues with respect to spill impacts on these animals.

The probability of a fu el spill will be minimized by Shell’s preventative measures, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP is expected to mitigate and reduce the potential for impacts on sea turtles. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the duration of a small spill and opportunity for impacts to occur would be very brief.

A small fuel spill in offshore waters would produce a slick on the water surface and increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Secti on A.9.2 discusses the likely fate of a small fuel spill and indicates that more than 90% would be evaporated or dispersed naturally within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions.

Direct physical and physiological effects of exposure to diesel fuel could include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes; ingestion of oil directly or via contaminated prey; and stress from the activities and noise of response vessels and aircraft (MMS, 2007b; NMFS, 2010b; BOEM, 2012b,c, 2013).However, due to the limited areal extent and short duration of water quality impacts from a small

fue l spill, no significant impacts would be expected.

A small fuel spill in the lease area would be unlikely to affect sea turtle nesting beaches because the lease area is 65 miles (105 km) from the nearest shoreline (Louisiana). As explained in

Section A.9.2 , a small fuel spill would not be expected to make landfall or reach coastal waters prior to breaking up.

Impacts of a Large Oil Spill

Impacts of oil spills on sea turtles can include direct impacts from oil exposure, as well as indirect impacts due to response activities and materials (e.g., vessel traffic, noise, dispersants, and beach cleanup activities). Direct physical and physiological effects can include skin irritation, inflammation, or necrosis; chemical burns of skin, eyes, and mucous membranes; inhalation of toxic fumes and smoke (e.g., from in situ burning of oil); ingestion of oil (and dispersants) directly or via contaminated food; and stress from the activities and noise of response vessels and aircraft. Complications of the above may lead to dysfunction of immune and reproductive systems, physiological stress, declining physical condition, and death. Behavioral responses can include displacement of animals from prime habitat, disruption of social structure, changing food availability and foraging distribution and/or patterns, changing reproductive behavior/productivity, and changing movement patterns or migration (MMS, 2007b; NMFS, 2010c). In the unlikely event of a spill, implementation of Shell’s OSRP is expected to mitigate and reduce the potential for these types of impacts on sea turtles. EP Section 9b provides detail on spill response measures.

Studies of oil effects on loggerheads in a controlled setting (Lutcavage et al., 1995) suggest that sea turtles show no avoidance behavior when they encounter an oil slick, and any sea turtle in an affected area would be expected to be exposed. Sea turtles’ diving behaviors also put them at risk. Sea turtles rapidly inhale a large volume of air before diving and continually resurface over time, which may result in repeated exposure to volatile vapors and oiling (NMFS, 2007).

The OSRA results summarized in Table 3 predict that some shorelines that support sea turtle nesting could be contacted within 30 days. The nearest significant nesting area of loggerhead turtles is found on beaches within the Breton NWR. Spilled oil reaching sea turtle nesting beaches could have effects on nesting sea turtles and egg development (NMFS, 2007). An oiled beach could affect nest site selection or result in no nesting at all (e.g., false crawls). Upon hatching and successfully reaching the water, hatchlings are subject to the same types of oil spill exposure hazards as adults. Hatchlings that contact oil residues while crossing a beach can exhibit a range of effects, from acute toxicity to impaired movement and normal bodily functions (NMFS, 2007).

NOAA’s Office of Response and Restoration prepared guidelines in 2007 to minimize impacts to nesting activities and existing nests due to beach cleanup activities (Shigenaka et al., 2010). Oil spill cleanup activities on the beach (e.g., raking, shoveling, use of mechanical equipment) may adversely affect sea turtle nesting activity or existing beach nests. Response workers and vehicles may crush eggs and compact beach sand, making it difficult or impossible for hatchlings to emerge or for females to use for nesting (Shigenaka et al., 2010). Nighttime human activity can prevent sea turtles from coming ashore, may cause females to stop nesting and return to the ocean, disorient or impede emerging hatchlings, and crush hatchlings attempting to reach the

ocean.

Impacts to sea turtles from a large oil spill and associated cleanup activities would be dependent upon spill extent, duration, and season (relative to turtle nesting season); the amount of oil reaching the shore; the importance of specific beaches to sea turtle nesting; and the level of cleanup vessel and beach crew activity required. A blowout resulting in a large oil spill is anextremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP would mitigate and reduce direct and indirect impacts to turtles from oil exposure and response activities and materials. EP Section 9b provides detail on spill response measures.



### C.3.6 Piping Plover (Threatened)

The Piping Plover ( Charadrius melodus ) is a migratory shorebird that overwinters along the southeastern U.S. and Gulf of Mexico coasts. This threatened species is in decline as a result of hunting, habitat loss and modification, predation, and disease (USFWS, 2003). Critical overwintering habitat has been designated, including beaches in Texas, Louisiana, Mississippi, Alabama, and Florida ( Figure 1 ). Piping Plovers inhabit coastal sandy beaches and mudflats, feeding by probing for invertebrates at or just below the surface. They use beaches adjacent to foraging areas for roosting and preening (USFWS, 2010a). A species description is presented in MMS (2007b).

A large oil spill is the only IPF that could potentially affect Piping Plovers. There are no IPFs associated with routine project activities that could affect these birds. A small fuel spill in the lease area would be unlikely to affect Piping Plovers because a small fuel spill would not be expected to make landfall or reach coastal waters prior to breaking up (see explanation in

Section A.9.2 ).

Impacts of a Large Oil Spill

The lease area is 67 miles (108 km) from the nearest shoreline inhabited by Piping Plovers. The

OSRA results summarized in Table 3 predict that Texas, Louisiana, and Florida shorelines designated as critical habitats for the wintering Piping Plover could be contacted by a spill within

30 days. Plaquemines Parish, Louisiana, which has the highest probability of contact for the

30 -day interval (8%), includes critical habitat of Piping Plovers.

### Figure 1. Location of selected environmental features in relation to the lease area. (EFH = Essential Fish Habitat; HAPC = Habitat Area of Particular Concern.)Plovers could become externally oiled while foraging on oiled shores or be exposed internally through ingestion of oiled intertidal sediments and prey (MMS, 2007b). Plovers congregate and feed along tidally exposed banks and shorelines, following the tide out and foraging at the water’s edge. It is possible that some deaths of Piping Plovers could occur, especially if spills occur during winter months when plovers are most common along the coastal Gulf or if spills contacted critical habitat. Impacts could also occur from vehicular traffic on beaches and other activities associated with spill cleanup. Shell has extensive resources available to protect and rehabilitate wildlife in the event of a spill reaching the shoreline, as detailed in the OSRP.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on Piping Plovers are expected.



### C.3.7 Whooping Crane (Endangered)

The Whooping Crane ( Grus americana ) is an omnivorous wading bird and an endangered species. There are three wild populations in North America (National Wildlife Federation, 2012). One population winters along the Texas coast at Aransas NWR and summers at Wood Buffalo National Park in Canada. This population represents the majority of the world’s populatio n of free-ranging Whooping Cranes and reached a record population of 278 at Aransas/Wood Buffalo National Park in August 2011 (Whooping Crane Eastern Partnership, 2013). A non-migrating population has been reintroduced in central Florida, and another reintroduced population summers in Wisconsin and migrates to the southeastern U.S. for the winter. Whooping Cranes breed, migrate, winter, and forage in a variety of habitats, including coastal marshes and estuaries, inland marshes, lakes, ponds, wet meadows and rivers, and agricultural fields (USFWS, 2007). About 22,240 ac (9,000 ha) of salt flats on Aransas NWR and adjacent islands comprise the principal wintering grounds of the Whooping Crane. Aransas NWR is designated as critical habitat for the species ( Figure 1 ). A species description is presented in MMS (2007b) and BOEM (2012b,c).

A large oil spill is the only IPF that could potentially affect Whooping Cranes due to the distance

from Aransas NWR.

Impacts of a Large Oil Spill

A large oil spill has a low probability of affecting Whooping Cranes because the lease area is approximately 454 miles (730 km) from its critical habitat (Aransas NWR, Texas) and the likelihood of contact with the habitat is extremely low (BOEM, 2012b).

In the event of oil exposure, Whooping Cranes could become externally oiled while foraging in oiled areas or internally exposed to oil through ingestion of contaminated shellfish, frogs, and fishes. It is possible that some death of Whooping Cranes could occur. Shell has extensive resources available to protect and rehabilitate wildlife in the event of a spill reaching the shoreline, as detailed in the OSRP.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on Whooping Cranes are expected.

### C.3.8 Gulf Sturgeon (Threatened)

The Gulf sturgeon (

Acipenser oxyrinchus desotoi ) is a threatened fish species that inhabits major rivers and inner shelf waters from the Mississippi River to the Suwannee River, Florida (Barkuloo, 1988; Wakeford, 2001). An anadromous fish that migrates from the sea upstream into coastal rivers to spawn in freshwater, it historically ranged from the Mississippi River to Charlotte Harbor, Florida (Wakeford, 2001). Today, this range has contracted to encompass major rivers and inner shelf waters from the Mississippi River to the Suwannee River, Florida. Populations have been depleted or even extirpated throughout this range by fishing, shoreline development, dam construction, water quality changes, and other factors (Barkuloo, 1988; Wakeford, 2001). These declines prompted the listing of the Gulf sturgeon as a threatened species in 1991. The best known populations occur in the Apalachicola and Suwannee Rivers in Florida (Carr, 1996; Sulak and Clugston, 1998), the Choctawhatchee River in Alabama (Fox et al., 2000), and the Pearl River in Mississippi/Louisiana (Morrow et al., 1998). Critical habitat in the Gulf extends from Lake Borgne, Louisiana (St. Bernard Parish), to Suwannee Sound, Florida (Levy County) (NMFS, 2010d) ( Figure 1 ). A species description is presented in MMS (2007b) and in the recovery plan for this species (USFWS and Gulf States Marine Fisheries Commission, 1995).

A large oil spill is the only IPF that could potentially affect Gulf sturgeon. There are no IPFs associated with routine project activities that could affect this species. A small fuel spill in the lease area would be unlikely to affect Gulf sturgeon, because a small fuel spill would not be expected to make landfall or reach coastal waters prior to breaking up (see explanation in

Section A.9.2 ).

Impacts of a Large Oil Spill

Potential spill impacts on Gulf sturgeon are discussed in MMS (2007b), BOEM (2012b,c, 2013), and in NMFS (2007) in its Biological Opinion for the Five-Year Oil and Gas Leasing Program in the Central and Western Planning Areas of the Gulf of Mexico. For this EP, there are no unique site-specific issues with respect to this species.

The lease area is about 132 miles (212 km) from the nearest Gulf sturgeon critical habitat. OSRA modeling ( Table 3 ) predicts that a spill in the lease area would have a 1% chance of contacting Gulf sturgeon critical habitat in coastal areas of Okaloosa County, Florida, within

30 days. In the event of oil reaching Gulf sturgeon habitat, the fish could be affected by direct ingestion, ingestion of oiled prey, or the absorption of dissolved petroleum products through the gills. Based on the life history of this species, subadult and adult Gulf sturgeon would be most vulnerable to a marine oil spill, and would be vulnerable only during winter months (from September 1 through April 30) when this species is foraging in estuarine and marine habitats (NMFS, 2007).

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. Shell has extensive resources available to protect coastal and estuarine wildlife and habitats in the event of a spill reaching the shoreline, as detailed in the OSRP.

EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on Gulf sturgeon are expected.



### C.3.9 Beach Mice (Endangered)

Four subspecies of endangered beach mouse ( Peromyscus polionotus ) occur on the barrier islands of Alabama and the Florida Panhandle. They are the Alabama, Choctawhatchee, Perdido Key, and St. Andrew beach mouse. Critical habitat has been designated for all foursubspecies; Figure 1 shows the critical habitat combined for all four subspecies. Species descriptions are provided in MMS (2007b).

A large oil spill is the only IPF that could potentially affect subspecies of beach mouse. There are no IPFs associated with routine project activities that could affect these animals due to the distance from shore and the lack of onshore support activities near their habitat.

Impacts of a Large Oil Spill

Potential spill impacts on beach mice are discussed in MMS (2007b) and BOEM (2012b,c, 2013). For this EP, there are no unique site-specific issues with respect to these species.

The lease area is about 163 miles (262 km) from the nearest beach mouse critical habitat. OSRA modeling predicts that a spill in the lease area would have a 1% chance of contacting beach mouse critical habitat in Okaloosa County, Florida, within 30 days. In the event of oil contacting these beaches, beach mice could experience several types of direct and indirect impacts. Contact with spilled oil could cause skin and eye irritation and subsequent infection; matting of fur; irritation of sweat glands, ear tissues, and throat tissues; disruption of sight and hearing; asphyxiation from inhalation of fumes; and toxicity from ingestion of oil and contaminated food. Indirect impacts could include reduction of food supply, destruction of habitat, and fouling of nests. Impacts could also occur from vehicular traffic and other activities associated with spill cleanup.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementat ion of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on beach mice are expected.



## C.4 Coastal and Marine Birds

C.4.1 Marine and Pelagic Birds

A variety of seabirds may occur in the pelagic environment of the project areas (Clapp et al., 1982a,b, 1983; Peake, 1996; Hess and Ribic, 2000). Seabirds spend much of their lives offshore over the open ocean, except during breeding season when they nest along the coast. In addition, other birds such as waterfowl, marsh birds, and shorebirds may occasionally be present over open ocean areas. No endangered or threatened bird species are likely to occur at the project area due to the distance from shore. For a discussion of shorebirds and coastal nesting birds, see Section C.4.2

.

Seabirds of the northern Gulf of Mexico were surveyed from ships during the GulfCet II program. Hess and Ribic (2000) reported that terns, storm-petrels, shearwaters, and jaegers were the most frequently sighted seabirds in the deepwater area. From these surveys, four ecological categories of seabirds were documented in the deepwater areas of the Gulf: summer migrants (shearwaters, storm petrels, boobies); summer residents that breed in the Gulf (Sooty Tern, Least Tern, Sandwich Tern, Magnificent Frigatebird); winter residents (gannets, gulls, jaegers); and permanent resident species (Laughing Gull, Royal Tern, Bridled Tern) (Hess and Ribic, 2000).

Common seabird species include Wilson’s S torm-Petrel ( Oceanites oceanicus ), Magnificent Frigatebird ( Fregata magnificens ), Northern Gannet ( Morus bassanus ), Masked Booby ( Sula dactylatra

), Brown Booby ( Sula leucogaster ), Cory’s Shearwater ( Calonectris diomedea ), Greater Shearwater ( Puffinus gravis ), and Audubon Shearwater ( Puffinus lherminieri ). Seabirds are distributed Gulf-wide and are not specifically associated with the lease area.Relationships with hydrographic features were found for several seabird species, possibly due to effects of hydrography on nutrient levels and productivity of surface waters where birds forage. GulfCet II did not estimate bird densities; however, Powers (1987) indicates that seabird densities over the open ocean typically are <10 birds/km 2

.

Trans-Gulf migrant birds including shorebirds, wading birds, and terrestrial birds may also be present in the lease area. Migrant birds may use offshore structures and platforms for resting, feeding, or as temporary shelter from inclement weather (Russell, 2005). Some birds may be attracted to offshore structures because of the lights and the fish populations that aggregate

around these structures.

IPFs that could potentially affect marine and pelagic birds include drilling rig presence, noise, and lights; support vessel and helicopter traffic; and two types of accidents

– a small fuel spill and a large oil spill. Effluent discharges permitted under the NPDES general permit are likely to have negligible impacts on the birds due to rapid dispersion, the small area of ocean affected, the intermittent nature of the discharges, and the mobility of these animals. Compliance with NTL 2012-BSEE-G01 will minimize the potential for marine debris-related impacts on birds.

Impacts of Drilling Rig Presence, Noise, and Lights

Birds that frequent platforms may be exposed to contaminants including air pollutants and routine discharges, but significant impacts are unlikely due to rapid dispersion of effluents and air pollutants. Birds migrating over water have been known to strike offshore structures, resulting in death or injury (Wiese et al., 2001; Russell, 2005). Mortality of migrant birds at tall towers and other land-based structures has been reviewed extensively, and the mechanisms involved in platform collisions appear to be similar. In some cases, migrants simply do not see a part of the platform until it is too late. In other cases, navigation may be disrupted by noise (Russell, 2005). Conversely, offshore structures are suitable stopover habitats for most trans-Gulf migrant species, and most of the migrants that stop over on platforms probably benefit from their stay, particularly in spring (Russell, 2005).

Overall, potential negative impacts to birds from drilling rig lighting, potential collisions, or other adverse effects are highly localized, relatively short term and temporary in nature, and may be expected to affect only individual birds during migration periods. Therefore, these potential impacts are not expected to affect birds at the population or species level and are not significant (BOEM, 2012b, 2013).

Impacts of Support Vessel and Helicopter Traffic

Support vessels and helicopters are unlikely to significantly disturb pelagic birds in open, offshore waters. It is likely that individual birds would experience, at most, only short-term behavioral disruption, and the impact would not be significant.

Impacts of a Small Fuel Spill

Potential spill impacts on marine birds are discussed in MMS (2007b) and BOEM (2012b,c, 2013). For this EP, there are no unique site-specific issues with respect to spill impacts on these animals.

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of

Shell’s OSRP will mitigate and reduce the potential for impacts on marine and pelagic birds.

EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area and the short duration of a small spill, the potential exposure for pelagic marine birds

would be brief.A small fuel spill in offshore waters would produce a slick on the water surface and increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Section A.9.2 discusses the likely fate of a small fuel spill and indicates that more than 90% would be evaporated or dispersed naturally within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions.

Birds exposed to oil on the sea surface could experience direct physical and physiological effects including skin irritation; chemical burns of skin, eyes, and mucous membranes; and inhalation of VOCs. Because of the limited areal extent and short duration of water quality impacts from a small fuel spill, secondary impacts due to ingestion of oil via contaminated prey or reductions in prey abundance are unlikely. Due to the low densities of birds in open ocean areas, the small area affected, and the brief duration of the surface slick, no significant impacts on marine and pelagic birds would be expected.

Impacts of a Large Oil Spill

Potential spill impacts on marine and pelagic birds are discussed in MMS (2007b) and BOEM (2012b,c, 2013). For this EP, there are no unique site-specific issues with respect to spill impacts

on these animals.

Pelagic seabirds could be exposed to oil from a spill at the project area. Hess and Ribic (2000) reported that terns, storm-petrels, shearwaters, and jaegers were the most frequently sighted seabirds in the deepwater Gulf of Mexico (>656 ft [>200 m]). Powers (1987) indicates that seabird densities over the open ocean typically are <10 birds/km 2 . The number of pelagic birds that could be affected in open, offshore waters would depend on the extent and persistence of

the oil slick.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on marine and pelagic birds are expected.



### C.4.2 Shorebirds and Coastal Nesting Birds

Threatened and endangered bird species (Piping Plover and Whooping Crane) are discussed in

Section C.3 . Various species of non-endangered birds are also found along the northern Gulf Coast, including diving birds, shorebirds, marsh birds, wading birds, and waterfowl. Gulf Coast marshes and beaches also provide important feeding grounds and nesting habitats. Species that nest on beaches, flats, dunes, bars, barrier islands, and similar coastal and nearshore habitats include the Sandwich Tern, Wilson’s Plover, Black Skimmer, Forster’s Tern, Gull -Billed Tern, Laughing Gull, Least Tern, and Royal Tern (USFWS, 2010b). Additional information is presented in MMS (2007b) and BOEM (2012b).

The Brown Pelican ( Pelecanus occidentalis ) was delisted from federal endangered status in 2009 (USFWS, 2010c). However, this species remains listed as endangered by the State of Louisiana (State of Louisiana Department of Wildlife and Fisheries, 2013), is listed as a species of greatest conservation need by the State of Mississippi (Mississippi Department of Wildlife, Fisheries and Parks, 2005), and is designated as a species of special concern by the State of Florida (Florida Fish and Wildlife Conservation Commission, 2013c). Brown Pelicans inhabit coastal habitats and forage within both coastal waters and waters of the inner continental shelf. Aerial and shipboard surveys, including GulfCet and GulfCet II, indicate that Brown Pelicans do not occur over deep offshore waters (Fritts and Reynolds, 1981; Peake, 1996; Hess and Ribic, 2000). Nearly half thesoutheastern population of Brown Pelicans lives in the northern Gulf Coast, generally nesting on protected islands (USFWS, 2010b).

IPFs that could potentially affect shorebirds and coastal nesting birds include support vessel and helicopter traffic and a large oil spill. As explained in Section A.9.2 , a small fuel spill would not be expected to make landfall or reach coastal waters prior to breaking up. Compliance with NTL 2012-BSEE-G01 will minimize the potential for marine debris-related impacts on shorebirds.

Impacts of Support Vessel and Helicopter Traffic

Support vessels and helicopters will transit coastal areas near Port Fourchon and Boothville, Louisiana, where shorebirds and coastal nesting birds may be found. These activities could periodically disturb individuals or groups of birds within sensitive coastal habitats (e.g., wetlands that may support feeding, resting, or breeding birds).

Vessel traffic may disturb some foraging and resting birds. Flushing distances vary among species and individuals (Rodgers and Schwikert, 2002). The disturbances will be limited to flushing birds away from vessel pathways; known distances are from 65 to 160 ft (20 to 49 m) for personal watercraft and 75 to 190 ft (23 to 58 m) for outboard-powered boats (Rodgers and Schwikert, 2002). Flushing distances may be similar or less for the support vessels to be used for Shell’s project, and some species such as gulls are attracted to boats. Support vessels will not approach nesting or breeding areas on the shoreline, so nesting birds, eggs, and chicks will not be disturbed. Vessel operators will use designated navigation channels and comply with posted speed and wake restrictions while transiting sensitive inland waterways. Due to the limited scope, duration, and geographic extent of drilling activities, any short-term impacts are not expected to be significant to coastal bird populations.

Aircraft traffic can cause some disturbance to birds on shore and off shore. Responses are highly dependent on the type of aircraft, bird species, activities that animals were previously engaged in, and previous exposures to overflights (Efroymson et al., 2000). Helicopters seem to cause the most intense responses over other human disturbances for some species (Bélanger and Bédard, 1989). However, Federal Aviation Administration Advisory Circular No. 91 -36D recommends that pilots maintain a minimum altitude of 2,000 ft (610 m) when flying over noise-sensitive areas such as wildlife refuges, parks, and areas with wilderness characteristics. This is greater than the distance (slant range) at which aircraft overflights have been reported to cause behavioral effects on most species of birds studied in Efroymson et al. (2000). With these guidelines in effect, it is likely that individual birds would experience, at most, only short-term behavioral disruption. The potential impacts are not expected to be significant to bird populations or species in the project area.

Impacts of Large Oil Spill

Coastal birds can be exposed to oil as they float on the water surface, dive during foraging, or

wade in oiled coastal waters. The OSRA results summarized in Table 3 predict that shorelines of Texas, Louisiana, and Florida that include habitat for shorebirds and coastal nesting birds could be affected within 30 days.

Studies concerning the Macondo spill provide additional information regarding impacts on shorebirds and coastal nesting birds that may be affected in the event that a large oil spill reaches coastal habitats. Although the Macondo spill had direct and indirect impacts to coastal and marine birds, it is premature to conclude impacts over a long period (BOEM, 2012b). A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate andreduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on shorebirds and coastal nesting birds are expected.



## C.5 Fisheries Resources

C.5.1 Pelagic Communities and Ichthyoplankton

Biggs and Ressler (2000) reviewed the biology of pelagic communities in the deepwater environment of the northern Gulf of Mexico. The biological oceanography of the region is dominated by the influence of the Loop Current, whose surface waters are among the most oligotrophic in the world’s oce ans. Superimposed on this low-productivity condition are productive “hot spots” associated with entrainment of nutrient -rich Mississippi River water and mesoscale oceanographic features. Anticyclonic and cyclonic hydrographic features play an important role in determining biogeographic patterns and controlling primary productivity in the northern Gulf of Mexico (Biggs and Ressler, 2000).

Most fishes inhabiting shelf or oceanic waters of the Gulf of Mexico have planktonic eggs and larvae (Ditty, 1986; Ditty et al., 1988; Richards et al., 1989, 1993). Pelagic eggs and larvae become part of the planktonic community for various lengths of time (10 to 100 days, depending on the species) (MMS, 2007b). A study by Ross et al. (2012) on midwater fauna to characterize vertical distribution of mesopelagic fishes in selected deepwater areas in the Gulf of Mexico substantiated high species richness, but general domination by relatively few families and species.

IPFs that could potentially affect pelagic communities and ichthyoplankton include drilling rig presence, noise, and lights; effluent discharges; water intakes; and two types of accidents

– a small fuel spill and a large oil spill.

Impacts of Drilling Rig Presence, Noise, and Lights

The drilling rig, as a floating structure in the deepwater environment, will act as a fish-attracting device (FAD). In oceanic waters, the FAD effect would be most pronounced for epipelagic fishes such as tunas, dolphin, billfishes, and jacks, which are commonly attracted to fixed and drifting surface structures (Holland et al., 1990; Higashi, 1994; Relini et al., 1994). This FAD effect could possibly enhance the feeding of epipelagic predators by attracting and concentrating smaller fish species. Because the drilling rig is a single, temporary structure, impacts on fish populations, whether beneficial or adverse, are considered minor.

Impacts of Effluent Discharges

Discharges of treated SBM cuttings will produce temporary, localized increases in suspended solids in the water column around the drilling rig. In general, turbid water can be expected to extend between a few hundred meters and several kilometers down current from the discharge point (NRC, 1983; Neff, 1987). NPDES permit limits and requirements will be met.

Treated sanitary and domestic wastes may have a slight effect on the pelagic environment in the immediate vicinity of these discharges. These wastes may have elevated levels of nutrients, organic matter, and chlorine, but will be diluted rapidly to undetectable levels within tens to hundreds of meters from the source. Minimal impacts on water quality, plankton, and nekton are anticipated.

Deck drainage may have a slight effect on the pelagic environment in the immediate vicinity of these discharges. Deck drainage from contaminated areas will be passed through an oil and water separator prior to release, and discharges will be monitored for visible sheen. The discharges may have slightly elevated levels of hydrocarbons but will be diluted rapidly toundetectable levels within tens to hundreds of meters from the source. Minimal impacts on water quality, plankton, and nekton are anticipated.

Other discharges in accordance with the NPDES permit, such as desalination unit brine and uncontaminated cooling water, fire water, and ballast water, are expected to be diluted rapidly and have little or no impact on water column biota.

Impacts of Water Intakes

Seawater will be drawn from several meters below the ocean surface for various services including firewater and once-through non-contact cooling of machinery on the drilling rig ( EP Table 7a ). Section 316(b) of the Clean Water Act requires NPDES permits to ensure that the location, design, construction, and capacity of cooling water intake structures reflect the best technology available to minimize adverse environmental impact from impingement and entrainment of aquatic organisms. The current general NPDES Permit No. GMG290000 specifies requirements for new facilities for which construction commenced after July 17, 2006 with a cooling water intake structure having a design intake capacity of greater than two million gallons of water per day, of which at least 25% is used for cooling purposes.

The wells will be drilled using either a drillship or DP semisubmersible rig. If the drilling vessel selected for this project meets the described applicability for new facilities, the vessel’s water intakes are expected to be in compliance with the design, monitoring, and recordkeeping requirements of the NPDES permit.

Impacts of a Small Fuel Spill

Potential spill impacts on fisheries resources are discussed in MMS (2007b) and BOEM (2012a,b,d). For this EP, there are no unique site-specific issues with respect to spill impacts.

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of
Shell’s OSRP will mitigate and reduce the potential for impacts on pelagic communities, including ichthyoplankton. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the duration of a small spill and opportunity for impacts to occur would be very brief.

A small fuel spill in offshore waters would produce a slick on the water surface and increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and persistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Section A.9.2 discusses the likely fate of a small fuel spill and indicates that more than 90% would be evaporated or dispersed naturally within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions.

A small fuel spill could have localized impacts on phytoplankton, zooplankton, ichthyoplankton, and nekton. Due to the limited areal extent and short duration of water quality impacts, a small fuel spill would be unlikely to produce detectable impacts on pelagic communities.

Impacts of a Large Oil Spill

Potential spill impacts on pelagic communities and ichthyoplankton are discussed in BOEM (2012a,b,d). For this EP, there are no unique site-specific issues.

A large oil spill could affect water column biota including phytoplankton, zooplankton, ichthyoplankton, and nekton. A large spill that persisted for weeks or months would be morelikely to affect these communities. While adult and juvenile fishes may actively avoid a large spill, planktonic eggs and larvae would be unable to avoid contact. Eggs and larvae of fishes in the upper layers of the water column are especially vulnerable to oiling; certain toxic fractions of spilled oil may be lethal to these life stages. Impacts would be potentially greater if local scale currents retained planktonic larval assemblages (and the floating oil slick) within the same water

mass.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on pelagic communities and ichthyoplankton are expected.



### C.5.2 Essential Fish Habitat

Essential Fish Habitat (EFH) is defined as those waters and substrate necessary to fish for spawning, breeding, feeding, and growth to maturity. Under the Magnuson-Stevens Fishery Conservation and Management Act, as amended, federal agencies are required to consult on activities that may adversely affect EFH designated in Fishery Management Plans developed by the regional Fishery Management Councils.

The Gulf of Mexico Fishery Management Council (GMFMC) has prepared Fishery Management Plans for corals and coral reefs, shrimps, stone crab, spiny lobster, reef fishes, coastal migratory pelagic fishes, and red drum. In 2005, the EFH for these managed species was redefined in Generic Amendment No. 3 to the various Fishery Management Plans (GMFMC, 2005). The EFH for most of these GMFMC-managed species is on the continental shelf in waters shallower than

600 ft (183 m). The shelf edge is the outer boundary for coastal migratory pelagic fishes, reef fishes, and shrimps. EFH for corals and coral reefs includes some shelf-edge topographic features on the Texas-Louisiana OCS, the nearest of which is located 53 miles (85 km) northwest

of the lease area.

EFH has been identified in the deepwater Gulf of Mexico for highly migratory pelagic fishes, which occur as transients in the lease area. Species in this group, including tunas, swordfishes, billfishes, and sharks, are managed by NMFS. Highly migratory species with EFH at or near the lease area include the following (NMFS, 2009b):

 Atlantic bluefin tuna (spawning, eggs, larvae, adults)

 Atlantic skipjack tuna (spawning, adults)

 Atlantic swordfish (larvae, juveniles, adults)

 Atlantic yellowfin tuna (spawning, juveniles, adults)

 Bigeye thresher shark (all)

 Bigeye tuna (juveniles, adults)  Blue marlin (juveniles, adults)

 Longbill spearfish (juveniles, adults)

 Longfin mako shark (all)

 Oceanic whitetip shark (all)

 Sailfish (adults)

 Silky shark (all)

 White marlin (juveniles, adults)

Research indicates the central and western Gulf of Mexico may be important spawning habitat for Atlantic bluefin tuna, and NMFS (2009b) has designated a Habitat Area of Particular Concern (HAPC) for this species. The HAPC covers much of the deepwater Gulf of Mexico, including the lease area ( Figure 1 ). The areal extent of the HAPC is approximately 115,830 mi 2
(300,000 km 2 ). The prevailing assumption is that Atlantic bluefin tuna follow an annual cycle of foraging in June through March off the eastern United States and Canadian coasts, followed by migration to the Gulf of Mexico to spawn in April, May, and June (NMFS, 2009b).Other HAPCs have been identified in the Gulf of Mexico by the GMFMC (2005). These include the Florida Middle Grounds, Madison-Swanson Marine Reserve, Tortugas North and South Ecological Reserves, Pulley Ridge, and several individual reefs and banks of the northwestern Gulf of Mexico ( Figure 1 ). The nearest of these is Jakkula Bank, located 155 miles (250 km) west of the lease

area.

Routine IPFs that could potentially affect EFH and fisheries resources include drilling rig presence, noise, and lights; effluent discharges; and water intakes. In addition, two types of accidents

– a small fuel spill and a large oil spill may potentially affect EFH and fisheries resources.

Impacts of Drilling Rig Presence, Noise, and Lights

The drilling rig, as a floating structure in the deepwater environment, will act as an FAD.

In oceanic waters, the FAD effect would be most pronounced for epipelagic fishes such as tunas, dolphin, billfishes, and jacks, which are commonly attracted to fixed and drifting surface structures (Holland et al., 1990; Higashi, 1994; Relini et al., 1994). This FAD effect would possibly enhance feeding of epipelagic predators by attracting and concentrating smaller fish species. Any impacts on EFH for highly migratory pelagic fishes are considered minor.

Impacts of Effluent Discharges

Other effluent discharges affecting EFH by diminishing ambient water quality include drilling mud and cuttings, treated sanitary and domestic wastes, deck drainage, and miscellaneous discharges such as desalination unit brine and uncontaminated cooling water, fire water, and ballast water. Impacts on EFH from effluent discharges are anticipated to be similar to those described in

Section C.5.1 for pelagic communities. No significant impacts on EFH for highly migratory pelagic fishes are expected from these discharges.

Impacts of Water Intakes

As noted previously, cooling water intake will cause entrainment and impingement of plankton, including fish eggs and larvae (ichthyoplankton). Due to the limited scope, timing, and geographic extent of drilling activities, any short-term impacts on EFH for highly migratory pelagic fishes are not expected to be biologically significant.

Impacts of a Small Fuel Spill

Potential spill impacts on EFH are discussed in MMS (2007b) and BOEM (2012a,b,d). For this EP, there are no unique site-specific issues with respect to spill impacts.

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of

Shell’s OSRP will mitigate and reduce the potential for impacts on EFH. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the duration of a small spill and opportunity for impacts to occur would be very brief.

A small fuel spill in offshore waters would produce a slick on the water surface and increase the concentrations of petroleum hydrocarbons and their degradation products. The extent and

pe rsistence of impacts would depend on the meteorological and oceanographic conditions at the time and the effectiveness of spill response measures. Section A.9.2 discusses the likely fate of a small fuel spill and indicates that more than 90% would be evaporated or dispersed naturally within 24 hours. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions.A small fuel spill could have localized impacts on EFH for highly migratory pelagic fishes, including tunas, swordfishes, billfishes, and sharks. These species occur as transients in the lease area. A spill would also produce short-term impact on water quality in the HAPC for spawning Atlantic bluefin tuna, which covers much of the deepwater Gulf of Mexico. The affected area would represent a negligible portion of the HAPC, which covers approximately 115,830 mi 2 (300,000 km 2 ) of the Gulf of Mexico. Therefore, no significant spill impacts on EFH for highly migratory pelagic fishes are expected.

A small fuel spill would not affect EFH for corals and coral reefs; the nearest coral EFH is located

53 miles (85 km) northwest of the lease area. A small fuel spill would float and dissipate on the

sea surface and would not contact these features. Therefore, no significant spill impacts on EFH for corals and coral reefs are expected.

Impacts of a Large Oil Spill

Potential spill impacts on EFH are discussed in MMS (2007b) and BOEM (2012a,b,d). For this EP

, there are no unique site-specific issues with respect to EFH.

An oil spill in offshore waters would temporarily increase hydrocarbon concentrations on the water surface and potentially the subsurface as well. Given the extent of EFH designations in the Gulf of Mexico (GMFMC, 2005; NMFS, 2009b), some impact on EFH would be unavoidable.

A large spill could affect the EFH for many managed species including shrimps, stone crab, spiny lobster, corals and coral reefs, reef fishes, coastal migratory pelagic fishes, red drum, and highly migratory pelagic fishes. It would result in adverse impacts on water quality and water column biota including phytoplankton, zooplankton, ichthyoplankton, and nekton. In coastal waters, sediments could be contaminated and result in persistent degradation of the seafloor habitat for managed demersal fish and invertebrates.

The lease area is within the HAPC for spawning Atlantic bluefin tuna (NMFS, 2009b). A large spill could temporarily degrade the HAPC due to increased hydrocarbon concentrations in the water column, with the potential for lethal or sublethal impacts on spawning tuna and their offspring. Potential impacts would depend in part on the timing of a spill, as this species migrates to the Gulf of Mexico to spawn in April, May, and June (NMFS, 2009b).

The nearest feature designated as EFH for corals is located 53 miles (85 km) northwest of the lease area. An accidental spill would be unlikely to reach or affect this feature. Near-bottom currents in the region are expected to flow along the isobaths (Nowlin et al., 2001) and typically would not carry a plume up onto the continental shelf edge.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on EFH are expected.



## C.6 Archaeological Resources

C.6.1 Shipwreck Sites

MC 943 is on the list of archaeological survey blocks determined to have a high potential for containing archaeological properties (BOEM, 2012d). A geologic, stratigraphic, and archaeological assessment detected marine avoidance targets within 2,000 ft (610 m) of each of the proposed wellsites, but none were identified as shipwrecks (GEMS, 2013; C&C, 2007).Because there are no historic shipwreck sites in the lease area (see EP Section 6 ), there are no routine IPFs that are likely to affect these resources. A small fuel spill would not affect shipwrecks in adjoining blocks because the oil would float and dissipate on the sea surface. The impact of a large oil spill that could contact shipwrecks in other areas is considered below a level

of concern.

Impacts of a Large Oil Spill

Previous analyses (MMS, 2007a, 2008) concluded that oil spills would be unlikely to affect archaeological sites beyond the immediate vicinity of the wellhead (i.e., due to physical impacts of a blowout) because the oil would rise quickly to the sea surface directly over the spill location. However, during the Macondo spill, subsurface plumes were reported at a water depth of about 3,600 ft (1,100 m), extending at least 22 miles (35 km) from the wellsite and persisting for more than a month (Camilli et al., 2010). The subsurface plumes apparently resulted from the use of dispersants at the wellhead (Joint Analysis Group, 2010c). While the behavior and impacts of subsurface plumes are not well known, a subsurface plume could contact shipwreck sites beyond the 984-ft (300-m) radius estimated by MMS (2007a, 2008), depending on its extent, trajectory, and persistence.

BOEM (2012b) reexamined the analyses for archaeological resources presented in MMS (2007a, 2008) based on additional information available since the publication of these two documents and in consideration of the Macondo oil spill. Substantial new information that alters the initial impact conclusion for archaeological resources has come to light as a result of BOEM-sponsored studies and industry surveys. Specifically, evidence of damage to significant cultural resources (i.e., historic shipwrecks) has been shown to have occurred because of an incomplete knowledgeof seafloor conditions in lease areas >200 m (>656 ft) deep that have been exempted from highresolution surveys. Since significant historic shipwrecks have been recently discovered outside the previously designated high-probability areas (some of which show evidence of impacts from permitted activities prior to their discovery), BOEM now requires that operators submit an archaeological survey for exploration and development projects.

There are no known historic shipwrecks in the lease area and a spill entering shallow coastal waters could conceivably contaminate an undiscovered or known historic shipwreck site. The OSRA modeling summarized in Table 3 predicts that Texas, Louisiana, and Florida shorelines could be contacted by a spill within 30 days.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on historic shipwrecks are expected. Also as noted in MMS (2007b), should an oil spill contact a coastal historic site, such as a fort or a lighthouse, the major impact would be a temporary, reversible visual impact from oil contact and contamination of the site and its environment. However, more recent studies suggest that the impacts could be longer term and not easily reversible (BOEM, 2012b,c).

C.6.2 Prehistoric Archaeological Sites

With water depths ranging from approximately 4,211 to 4,276 ft (1,284 to 1,303 m), the wellsites are well beyond the 60-m (197-ft) depth contour used by the BOEM as the seaward extent for prehistoric archaeological site potential in the Gulf of Mexico. A geologic, stratigraphic, and archaeological assessment detected marine avoidance targets within 2,000 ft (610 m) of the proposed wellsites (GEMS, 2013; C&C, 2007) but none were suggestive of submerged cultural resources. Because prehistoric archaeological sites are not found in the lease area, the onlyrelevant IPF is a large oil spill that would reach coastal waters within the 60-m (197-ft) depth

contour.

Impacts of a Large Oil Spill

Because prehistoric archaeological sites are not found in the lease area, they would not be affected by the physical effects of a subsea blowout. MMS (2007b) estimates that a severe subsurface blowout could resuspend and disperse sediments within a 984-ft (300-m) radius.

Along the northern Gulf Coast, prehistoric sites occur frequently along the barrier islands and mainland coast and along the margins of bays and bayous (MMS, 2007b). The OSRA modeling

summarized in Table 3 predicts that Texas, Louisiana, and Florida shorelines could be contacted by a spill within 30 days. A spill reaching a prehistoric site along these shorelines could coat fragile artifacts or site features and compromise the potential for radiocarbon dating organic materials in a site (although other dating methods are available and it is possible to decontaminate an oiled sample for radiocarbon dating). Coastal prehistoric sites could also be damaged by spill cleanup operations (e.g., by destroying fragile artifacts and disturbing the provenance of artifacts and site features). BOEM (2012b) notes that some unavoidable direct and indirect impacts on coastal historic resources could occur, resulting in the loss of information.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shel l’s well control and blowout prevention measures as detailed in

EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on archaeological resources are expected.



## C.7 Coastal Habitats and Protected Areas

Coastal habitats in the northern Gulf of Mexico that may be affected by oil and gas activities are described in previous EISs (MMS, 2007b; BOEM, 2012a,b,d, 2013) and in a literature review by Collard and Way (1997). Sensitive coastal habitats are also tabulated in the OSRP. Coastal habitats inshore of the project area include barrier beaches and dunes, wetlands, and submerged seagrass beds. Generally, most of the northern Gulf is fringed by barrier beaches, with wetlands and/or submerged seagrass beds occurring in sheltered areas behind the barrier islands and in

estuaries.

Due to the distance from shore, there are no IPFs associated with routine activities occurring in the lease area that are likely to affect beaches and dunes, wetlands, seagrass beds, coastal wildlife refuges, wilderness areas, or any other managed or protected coastal area. The support bases at Port Fourchon and Boothville, Louisiana, are not located in a wildlife refuge or a wilderness area. Potential impacts of support vessel traffic are briefly addressed in this section.

A small fuel spill in the lease area would be unlikely to affect coastal habitats, because it would not be expected to make landfall or reach coastal waters prior to breaking up (see explanation in

Section A.9.2 ).

Impacts of Support Vessel Traffic

For OCS activities in general, support operations, including the crew boat and supply boats, may have a minor incremental impact on coastal habitats. Over time with a large number of vessel trips, vessel wakes can erode shorelines along inlets, channels, and harbors. Support operations, including the crew boat and supply boats as detailed in EP Section 14 , may have a minor incremental impact on coastal habitats or protected areas. Impacts will be minimized by following the speed and wake restrictions in harbors and channels.Impacts of a Large Oil Spill

Potential spill impacts on coastal habitats are discussed in MMS (2007b) and BOEM (2012a,b,d). Coastal habitats inshore of the project area include barrier beaches and dunes, wetlands, and submerged seagrass beds. For this EP , there are no unique site-specific issues with respect to

coastal habitats.

The OSRA results summarized in Table 3 predict that shorelines of Texas, Louisiana, and Florida could be affected within 30 days. Nearshore waters and embayments of Plaquemines Parish, Terrebonne Parish, and Lafourche Parish, Louisiana, have the highest probability of contact within 30 days. After 30 days, 11 counties or parishes may be contacted from Texas to Florida.

The shorelines within the geographic range predicted by the OSRA modeling include extensive barrier beaches and wetlands, with submerged seagrass beds occurring in sheltered areas behind the barrier islands and in estuaries. NWRs and other protected areas along the coast are discussed in the lease sale EISs (MMS, 2007b; BOEM, 2012b) and Shell’s OSRP. Coastal wildlife refuges, wilderness areas, and state and national parks within the geographic range of the potential shoreline contacts after 30 days include the following:

 Anahuac NWR

 Apalachicola Bay Aquatic Preserve Outstanding Florida Water

 Apalachicola National Estuarine

Research Reserve

 Apalachicola River and Bay Surface Water Improvement and Management (SWIM) Area

 Apalachicola River Wildlife and

Environmental Area

 Apffel Park

 Aransas NWR

 Atchafalaya Delta Wildlife Management Area (WMA)

 Atkinson Island WMA

 Bayou Portage Coastal Preserve

 Bayou Sauvage NWR

 Bayou Teche NWR

 Bellefontaine Point Coastal

Reserve

 Big Boggy NWR

 Big Branch Marsh NWR

 Big Lagoon State Recreation Area

 Biloxi Marshes State Coastal

Preserve

 Biloxi River Coastal Reserve

 Biloxi WMA

 Bon Secour NWR

 Brazoria NWR

 Breton NWR

 Buccaneer State Park

 Cameron Prairie NWR

 Candy Abshier WMA

 Choctawatchee Bay SWIM Area

 Christmas Bay Coastal Preserve  Christmas Bay State Park

 Cypremort Point State Park

 Davis Bayou Coastal Preserve

 Deer Island State Coastal Preserve

 Deer Lake State Park

 Delta NWR

 Fort Pickens State Park Aquatic

Preserve

 Fort Anahuac Park

 Galveston Island State Park

 Goose Island State Park

 Grand Bay National Estuarine

Research Reserve

 Grand Bay NWR

 Grand Bay Savannah Coastal

Preserve

 Grand Bayou Coastal Preserve

 Grand Isle State Park

 Graveline Bay Coastal Reserve

 Grayton Beach State Park Outstanding Florida Water

 Guadalupe Delta WMA

 Gulf Islands National Seashore

 Gulf State Park

 Hancock County Marsh Coastal

Reserve

 Henderson State Park

 Isles Dernieres Barrier Islands Refuge

 Jean Lafitte National Historical

Park and Preserve

 Jourdan River Coastal Reserve

 Lacassine NWR

 Lafitte Woods NA Laguna Madre Estuarine and

Coastal Marine Area

 Lake Corpus Christi SP

 Lillian Swamp Mitigation Area

 Little Pecan Island NA

 Lower Neches WMA

 Mad Island WMA

 Mandalay NWR

 Meaher State Park

 Marsh Island WMA

 Matagorda Island State Park

 Mcfaddin NWR

 Meaher State Park

 Mission -Aransas National Estuarine

Research Reserve

 Mississippi Sandhill Crane NWR

 J.D. Murphree WMA

 Mustang Island SP

 Old Fort Bayou Coastal Reserve

 Old Fort Travis Park

 Padre Island National Seashore

 Pascagoula River Coastal Reserve

 Pass A Loutre WMA

 Paul J. Rainey WMA

 Peach Point WMA

 Pearl River WMA

 Penalver State Park

 Pensacola Bay SWIM Area

 Perdido Key State Recreation Area

 Peveto Woods NA

 Point Au Chein WMA

 Point Washington Outstanding

Florida Water

 Salvador WMA

 San Bernard NWR

 Sea Rim State Park

 Seawolf Park

 Shell Keys NWR

 St. Andrew Bay Watershed SWIM

Area

 St. Andrews State Park

 St. Andrews State Park Aquatic

Preserve

 St. Bernard State Park

 St. George Island State Park

 St. Joseph Bay State Buffer

Preserve

 St. Joseph Peninsula State Park

 St. Vincent NWR

 Tarkiln Bayou State Preserve

 Texas Point NWR

 The Grand Bay Savanna Tract

 W.L. Holland WMA  Weeks Bay National Estuarine

Research Reserve

 Welder Flats Coastal Preserve

 Winser WMA

 Wolf River Coastal Reserve

 Yellow River WMA Port Aransas Park

 Rockefeller WMA

 Sabine NWR

The OSRA results in Table 3 include only shoreline segments with contact probabilities greater than 0.5% within 30 days; other coastal areas could be affected at lower contact probabilities within

30 days, or from a spill persisting for more than 30 days. Additional NWRs and managed wildlife areas occur along the Gulf Coast. These areas include habitats such as barrier beach and dune systems, wetlands, and submerged seagrass beds that support diverse wildlife, including endangered or threatened species.

The level of impacts from oil spills on coastal habitats depends on many factors, including the oil characteristics, the geographic location of the landfall, and the weather and oceanographic conditionsat the time (MMS, 2007b). Oil that makes it to beaches may be either liquid weathered oil, an oil-andwater mousse, or tarballs (MMS, 2007b). Oil is generally deposited on beaches in lines defined by

wave action at the time of landfall. Oil that remains on the beach will thicken as its volatile components are lost. Thickened oil may form tarballs or aggregations that incorporate sand, shell, and other materials into its mass. Tar may be buried to varying depths under the sand. On warm days, both exposed and buried tarballs may liquefy and ooze. Oozing may also serve to expand the size of a mass as it incorporates beach materials. Oil on beaches may be cleaned up manually, mechanically, or both. Some oil can remain on the beach at varying depths and may persist for several years as it slowly biodegrades and volatilizes.

Coastal wetlands are highly sensitive to oiling and can be significantly impacted because of the inherent toxicity of hydrocarbon and non-hydrocarbon components of the spilled substances (Mendelssohn, 2012). The MMS (2007b) predicted that for every 50 bbl of oil contacting wetlands, approximately 6.7 ac (2.7 ha) of wetland vegetation will experience dieback. Thirty percent of these damaged wetlands are assumed to recover within 4 years, and 85% within 10 years. About 15% of the contacted wetlands are expected to be converted permanently to open-water habitat. The critical concentration of oil is that concentration above which impacts to wetlands will be long term and recovery will take longer than two growing seasons, and which causes plant mortality and some permanent wetland loss. Critical concentrations of various oils are expected to vary broadly for wetland types and wetland plant species. Louisiana wetlands are assumed to be more sensitive to oil contact than elsewhere in the Gulf because of high cumulative stress (MMS, 2007b). In addition to the direct impacts of oil, cleanup activities in marshes may accelerate rates of erosion and retard recovery rates (MMS, 2007b).

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowo ut prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on coastal habitats are expected.



## C.8 Socioeconomic and Other Resources

C.8.1 Recreational and Commercial Fishing

BOEM has reexamined the analysis for recreational and commercial fishing presented in MMS (2007b, 2008) based on additional information and in consideration of the Macondo spill. No new information was found that would alter the potential impacts on commercial fishing (BOEMRE, 2011; BOEM, 2012c). The main commercial fishing activity in deep waters of the northern Gulf of Mexico is pelagic longlining for tunas, swordfishes, and other billfishes (Continental Shelf Associates, Inc., 2002). Pelagic longlining has occurred historically in the project area, primarily during spring and summer.

It is unlikely that any commercial fishing activity other than longlining occurs at or near the project area. Benthic species targeted by commercial fishers occur on the upper continental slope, well inshore of the project area. Royal red shrimp ( Pleoticus robustus ) are caught by trawlers in water depths of about 820 to 1,804 ft (250 to 550 m). Tilefishes (primarily Lophalotilus chamaeleonticeps ) are caught by bottom longlining in water depths from about 540 to 1,476 ft (165 to 450 m) (Continental Shelf Associates, Inc., 2002). The proposed project is in 4,211 to 4,276 ft (1,284 to 1,303 m) of water. No conflict with commercial fishing activity other than longlining is expected to

occur.Most recreational fishing activity in the region occurs in water depths less than 656 ft (200 m)

(Continental Shelf Associates, Inc., 1997, 2002). In deeper water, the main attraction to recreational fishers would be petroleum platforms in offshore waters of Texas and Louisiana.

The only routine IPF that could potentially affect fisheries is drilling rig presence (including noise and lights). Two types of potential accidents are also addressed in this section

– a small fuel spill and a large oil spill.

Impacts of Drilling Rig Presence

There is a slight possibility of pelagic longlines becoming entangled in the drilling rig. For example, in January 1999, a portion of a pelagic longline snagged on the acoustic Doppler current profiler of a drillship working in the Gulf of Mexico (Continental Shelf Associates, Inc., 2002). The line was removed without incident. Generally, longline fishers use radar and are aware of offshore structures and ships when placing their sets. Therefore, little or no impact on pelagic longlining is expected.

No adverse impacts on fishing activities are anticipated. Other factors such as effluent discharges are likely to have negligible impacts on commercial or recreational fisheries due to rapid dispersion, the small area of ocean affected, and the intermittent nature of the discharges.

Impacts of a Small Fuel Spill

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the potential for impacts. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the duration of a small spill and opportunity for impacts to occur would be very brief.

Pelagic longlining activities in the lease area, if any, could be interrupted in the event of a small fuel spill. The area of diesel fuel on the sea surface would range from 1.2 to 12 ac (0.5 to 5 ha), depending on sea state and weather conditions. Fishing activities could be interrupted due to the activities of response vessels operating in the lease area. A small fuel spill would not affect coastal water quality because the spill would not be expected to make landfall or reach coastal waters prior to breaking up (see Section A.9.2 ).

Impacts of a Large Oil Spill

Potential spill impacts on fishing activities are discussed in MMS (2007b) and BOEM (2012b,c, 2013).

For this EP , there are no unique site-specific issues with respect to this activity.

Pelagic longlining activities in the lease area and other fishing activities in the northern Gulf of Mexico could be interrupted in the event of a large oil spill. A spill may or may not result in fishery closures, depending on the duration of the spill, the oceanographic and meteorological conditions at the time, and the effectiveness of spill response measures. A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on fishing activities are expected.



### C.8.2 Public Health and Safety

There are no IPFs associated with routine operations that are expected to affect public health and safety. Impacts of a small fuel spill and a large oil spill are addressed in this section.

Impacts of a Small Fuel Spill

The probability of a fue l spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the potential for impacts. EP Section 9b provides detail on spill response

measures.

A small fuel spill would not have impacts on public health and safety because it would likely affect only a small area of the open ocean 65 miles (105 km) from the nearest shoreline and nearly all of the diesel fuel would evaporate or disperse naturally within 24 hours. Response crews would be equippedwith appropriate safety equipment to avoid injury and health effects. A small fuel spill would not be

expected to make landfall or reach coastal waters prior to breaking up ( see Section A.9.2 ).

Impacts of a Large Oil Spill

In the event of a large spill from a blowout, the main safety and health concerns are those of the offshore personnel involved in the incident and those responding to the spill. The proposed activities will be covered by the OSRP, and, in addition, the drilling rig maintains a Shipboard Oil Pollution Emergency Plan as required under MARPOL 73/78.

Depending on the spill rate and duration, the physical/chemical characteristics of the oil, the meteorological and oceanographic conditions at the time, and the effectiveness of spill response measures, the public could be exposed to oil on the water and along the shoreline, through skin contact or inhalation of VOCs. Crude oil is a highly flammable material, and any smoke or vapors from a crude oil fire can cause irritation. Exposure to large quantities of crude oil may pose a health

hazard.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event

will be minimized b y Shell’s well control and blowout prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on public health and safety are expected.



### C.8.3 Employment and Infrastructure

There are no IPFs associated with routine operations that are expected to affect employment and infrastructure. The project involves drilling with support from existing shore-based facilities in Louisiana. No new or expanded facilities will be constructed, and no new employees are expected to move permanently into the area. The project will have a negligible impact on socioeconomic conditions such as local employment, existing offshore and coastal infrastructure (including major sources of supplies, services, energy, and water), and minority and lower income groups. Impacts of a small fuel spill and a large oil spill are addressed in this section.

Impacts of a Small Fuel Spill

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the potential for impacts. EP Section and 9b provides detail on spill response measures. Given the open ocean location of the lease area and the duration of a small spill, the opportunity for impacts to occur would be very brief.

A small fuel spill that is dissipated within a few days would have little or no economic impact, as the spill response would use existing facilities, resources, and personnel.

Impacts of a Large Oil Spill

Potential socioeconomic impacts of an oil spill are discussed in MMS (2007b) and BOEM (2012b,c, 2013). For this EP, there are no unique site-specific issues with respect to employment and coastal infrastructure. A large spill could cause several types of economic impacts: extensive fishery closures could put fishermen out of work; temporary employment could increase as part of the response effort; adverse publicity could reduce employment in coastal recreation and tourism industries; and OCS drilling activities, including service and support operations that are an important part of local economies, could be suspended.

The lease area is 65 miles (105 km) from the nearest shoreline. Based on the OSRA modeling predictions ( Table 3 ), coastal areas of Texas, Louisiana, and Florida are the most likely to be contacted by a spill.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on employment and infrastructure are expected.

### C.8.4 Recreation and Tourism

BOEM has reexamined the analyses for recreation and tourism presented in MMS (2007b, 2008) based on additional information and in consideration of the Macondo oil spill event. No new information was found that would alter the potential impacts on recreation and tourism (BOEMRE, 2011; BOEM,

2012c ).

There are no known recreational uses of the lease area. Recreational resources and tourism in coastal areas would not be affected by routine activities due to the distance from shore. Compliance with NTL 2012-BSEE-G01 will minimize the chance of trash or debris being lost overboard from the drilling rig and subsequently washing up on beaches.

Impacts of a Small Fuel Spill

The probability of a fuel spill will be minimized by Shell’s preventative measures during routine operations, including fuel transfer. In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the potential for impacts. EP Section 9b provides detail on spill response measures. Given the open ocean location of the lease area, the duration of a small spill and opportunity for impacts to occur would be very brief.

A small fuel spill in the lease area would be unlikely to affect recreation and tourism. There are no known recreational or tourism activities occurring in the lease area, and as explained in

Section A.9.2 , a small fuel spill would not be expected to make landfall or reach coastal waters prior to breaking up.

Impacts of a Large Oil Spill

Potential impacts of an oil spill on recreation and tourism are discussed in MMS (2007b) and BOEM (2012a,b,d). For this EP , there are no unique site-specific issues with respect to these impacts.

Impacts on recreation and tourism would vary depending on the duration of the spill and its fate including the effectiveness of response measures. A large spill that reached coastal waters and shorelines could adversely affect recreation and tourism by contaminating beaches and wetlands,

re sulting in negative publicity that encourages people to stay away. The OSRA results summarized in

Table 3 predict that shorelines of Texas, Louisiana, and Florida could be affected within 30 days. Nearshore waters and embayments of Plaquemines Parish, Terrebonne Parish, and Lafourche Parish, Louisiana, have the highest probability of contact within 30 days.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control an d blowout prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on recreation and tourism are expected.



### C.8.5 Land Use

Land use along the northern Gulf Coast is discussed in MMS (2007b) and BOEM (2012b,c, 2013). There are no routine IPFs potentially affecting land use. The project will use existing onshore support facilities in Louisiana. The land use at the existing shorebase sites is industrial. The project will not involve new construction or changes to existing land use and, therefore, will not have any impacts. Levels of boat and helicopter traffic, as well as demand for goods and services, including scarce coastal resources, will represent a small fraction of the level of activity occurring at the shorebases.

A large oil spill is the only relevant accident IPF. A small fuel spill would not have impacts on land use, as the response would be staged out of existing shorebases and facilities.

Impacts of a Large Oil Spill

The initial response for a large oil spill would be staged out of existing facilities, with no effect on land use. A large spill could have limited temporary impacts on land use along the coast if additional staging areas were needed. For example, during the Macondo spill, 25 temporary staging areas were established in Louisiana, Mississippi, Alabama, and Florida for spill response and cleanup efforts (BOEM, 2012b). In the event of a large spill in the lease area, similar temporary staging areas could be needed. These areas would eventually return to their original use as the response is demobilized.A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event

will be minimized by Shell’s well control and blowout prevention measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on land use are expected.



### C.8.6 Other Marine Uses

The lease area is not located within any USCG-designated fairway or shipping lane and MC 943 is not in a designated Military Warning Area. Shell will comply with BOEM requirements and lease stipulations to avoid impacts on uses of the area by military vessels and aircraft. There are no existing wells, flowlines, or umbilicals in the vicinity of the proposed wellsites (GEMS, 2013).

The geologic, stratigraphic, and archaeological assessment detected marine avoidance targets within 2,000 ft (610 m) of all of the proposed wellsites. A discontinued industrial waste disposal site is

located no rthwest of the lease area. Shell’s procedure “Waste Barrel Avoidance and Release Response in the Mississippi Canyon Area,” which was approved by MMS and BOEM, applies to operations that could cause a disturbance of a seafloor barrel. Shell’s overarching policy is to avoid barrel contact. In the unlikely case that contact is suspected or has been made with any wastes from a barrel, the plan specifies actions to be taken for the topside safety of personnel handling the equipment. The plan also outlines barrel impact reporting procedures.

There are no IPFs from routine project activities that are likely to affect shipping or other marine uses. A large oil spill is the only relevant accident IPF. A small fuel spill would not have impacts on other marine uses, as the spill and response activities would be mainly within the lease area, and the

duration would be brief.

Impacts of a Large Oil Spill

An accidental spill would be unlikely to significantly affect shipping or other marine uses. The block is not located within any USCG-designated fairway or shipping lane. In the event of a large spill requiring numerous response vessels, coordination would be required to manage the vessel traffic for safe operations. Shell will comply with BOEM requirements and lease stipulations to avoid impacts on uses of the area by military vessels and aircraft.

A blowout resulting in a large oil spill is an extremely rare event, and the probability of such an event will be minimized by Shell’s well control and blowout preventio n measures as detailed in EP Section 2j . In the unlikely event of a spill, implementation of Shell’s OSRP will mitigate and reduce the impacts. EP Section 9b provides detail on spill response measures. Therefore, no significant spill impacts on other marine uses are expected.



## C.9 Cumulative Impacts

For purposes of NEPA, cumulative impact is defined as “the impact on the environment which results from the incremental impact of the action when added to other past, present, and reasonably foreseeable future actions regardless of what agency (federal or non-federal) or person undertakes such other actions” (40 CFR 1508.7). Any single activity or action may have a negligible impact(s) by itself, but when combined with impacts from other activities in the same area and/or time period, substantial impacts may result.

Prior Studies . Prior to the lease sales, MMS prepared a multi-sale EIS in which it analyzed the environmental impact of activities that might occur in the multi-lease-sale area. The MMS also recently analyzed the cumulative impacts of OCS exploration activities similar to those planned in this EP in several documents. The level and types of activities planned in Shell's EP are within the range of

activities described and evaluated in the Final EIS for Gulf of Mexico OCS Oil and Gas Lease Sales 2007-2012 (MMS, 2007b), as updated by a 2012 Final EIS for Gulf of Mexico OCS Oil and Gas Lease Sales 2012-2017 (BOEM, 2012b), the Final Supplemental EIS for Gulf of Mexico Lease Sale OCS Oil and Gas Sale: 2012 (BOEM, 2012c), and the Final Supplemental EIS for Gulf of Mexico OCS Oil and Gas Lease Sales 2013-2014 (BOEM, 2013).

Past, present, and reasonably foreseeable activities were identified in the cumulative effects scenario of these documents, which are incorporated by reference. The proposed action will not result in anyadditional impacts beyond those evaluated in the multi-sale and Final EISs (MMS, 2007b; BOEM,

2012b,c, 2013).

Description of Activities Reasonably Expected to Occur in the Vicinity of Project Area . Other exploration and development activities may occur in the vicinity of lease block MC 943. Shell does not anticipate other projects in the vicinity of the project area beyond the types of projects analyzed in the lease sale and Supplemental EISs (MMS, 2007b, 2008; BOEMRE, 2011; BOEM, 2012b,c, 2013).

Cumulative Impacts of Activities in the EP . The MMS (2007b) lease-sale EIS and BOEM (2012b,c, 2013) Final EISs included a lengthy discussion of cumulative impacts, which analyzed the environmental and socioeconomic impacts from the incremental impact of the 11 proposed lease sales, in addition to all activities (including non-OCS activities) projected to occur from past, proposed, and future lease sales during the 40-year period of 2007 to 2046 (see MMS, 2007b; BOEM, 2012b). The EISs considered exploration, delineation, and development wells; platform installation; service-vessel trips; and oil spills. The EISs examined the potential cumulative effects on each specific

resource for the entire Gulf of Mexico.

The level and type of activity proposed in Shell’s EP are within the range of activities described and evaluated in the recent lease-sale EISs. This EIA incorporates and builds on these analyses by examining the potential impacts on physical, biological, and socioeconomic resources from the work planned in this EP, in conjunction with the other reasonably foreseeable activities expected to occur in the Gulf of Mexico. Thus, for all impacts, the incremental contribution of Shell’s pro posed actions to the cumulative impacts analysis in these prior analyses is not significant.

C.9.1 Cumulative Impacts to Physical/Chemical Resources

The work planned in this EP is limited in geographic scope and duration, and the impacts on the physical/chemical environment will be correspondingly limited.

Air Quality

. Emissions from pollutants into the atmosphere from activities are not projected to have significant effects on onshore air quality because of the prevailing atmospheric conditions, emission rates and heights, and resulting pollutant concentrations. As BOEM found in the multi-lease-sale EISs, the incremental contribution of activities similar to Shell’s proposed activities to the cumulative impacts is not significant and will not cause or contribute to a violation of NAAQS (MMS, 2007b; BOEM, 2012b,c, 2013). In addition, the cumulative contribution to visibility impairment is also very small (MMS, 2007b; BOEM, 2012b,c, 2013). As mentioned in previous sections, projected emissions meet the BOEM exemption criteria and would not contribute to cumulative impacts on air quality.

Climate Change . CO 2 and CH 4 emissions from the project would constitute a negligible contribution to greenhouse gas emissions from all OCS activities. According to BOEM (2013), greenhouse gas emissions from all OCS oil and gas activities make up a very small portion of national CO 2 emissions and BOEM does not believe that emissions directly attributable to OCS activities are a significant contributor to global greenhouse gas levels. Greenhouse gas emissions identified in the EP represent a negligible contribution to the total greenhouse gas emissions from reasonably foreseeable activities in the Gulf of Mexico area and would not significantly alter any of the climate change impacts evaluated in the previous EISs. Globally, Shell is taking action in four areas: producing more natura l gas, the cleanest burning fossil fuel; helping to develop technologies to capture and store CO 2 ; producing low-carbon biofuel; and working to improve the energy efficiency of our operations (Shell, 2012).

Water Quality . Shell’s project will result in so me minor water quality impacts due to the NPDES-permitted discharge of SBM cuttings, treated sanitary and domestic wastes, excess cement, non-contact cooling water, deck drainage, desalination unit brine, uncontaminated fire water and ballast water. These effects are expected to be minor (localized to the area within a few hundred meters of the drilling rig), and temporary (lasting only hours longer than the disturbance or discharge). Any cumulative effects to water quality are expected to be negligible.

Archaeological Resources . MC 943 is on the list of archaeology survey blocks (BOEM, 2012d). A geologic, stratigraphic, and archaeological assessment by GEMS (2013) and C&C (2007) identified no sonar contacts suggestive of significant submerged cultural or archeological resources. Also, the lease area is well beyond the 60-m (197-ft) depth contour used by the BOEM as the seaward extent for prehistoric archaeological site potential in the Gulf of Mexico. Therefore, Shell’s operations will have no cumulative impacts on historic shipwrecks or prehistoric archaeological resources.New Information . New information included in the most recent Programmatic, Supplemental, and

Final EISs (BOEM, 2012a,b,d) has been incorporated into the EIA, where applicable.



### C.9.2 Cumulative Impacts to Biological Resources

The work planned in this EP is limited in geographic scope and duration, and the impacts on biological resources will be correspondingly limited.

Seafloor Habitats and Biota . Effects on seafloor habitats and biota from discharges of drilling mud and cuttings are expected to be minor and limited to a small area. White et al. (2012a,b) observed dead and damaged deepwater corals approximately 7 miles (11 km) southwest of the Macondo wellhead. The researchers concluded, based on hopanoid petroleum biomarker analysis of the flocculent material, that it contained oil from the Macondo spill. The impacted corals are located approximately 55 miles (89 km) northeast of MC 943, in deeper water (4,600 ft [1,400 m]) than is found at the proposed wellsites (4,211 to 4,276 ft [1,284 to 1,303 m]). It is unlikely that there would be cumulative impacts to those corals even in the unlikely event of a large spill associated with the

activities discussed in this EIA.

Areas that may support high-density deepwater benthic communities will be avoided as required by NTL 2009-G40. Soft bottom communities are ubiquitous along the northern Gulf of Mexico continental slope, and the extent of benthic impacts during this project is insignificant regionally. As noted in the

multi-lease- sale EISs, the incremental contributions of activities similar to Shell’s proposed activities to the cumulative impacts is not significant (MMS, 2007b; BOEM, 2012b,c, 2013).

Threatened, Endangered, and Protected Species . Threatened and endangered species reasonably likely to occur in the lease area include the sperm whale and five species of sea turtles. Potential impact sources include drilling rig presence including noise and lights, marine debris, and support vessel and aircraft traffic. Potential effects for these species would be limited and temporary, and would be reduced by Shell’s compliance with BOEM -required mitigation measures, including NTLs 2012-BSEE-G01 and 2012-JOINT-G01. No significant cumulative impacts are expected.

Coastal and Marine Birds . Birds may be exposed to contaminants, including air pollutants and routine discharges, but significant impacts are unlikely due to rapid dispersion. Shell’s c ompliance with NTL 2012-BSEE-G01 will minimize the likelihood of debris-related impacts on birds. Support vessel and helicopter traffic may disturb some foraging and resting birds; however, it is likely that individual birds would experience, at most, only short-term behavioral disruption.

Due to the limited scope, timing, and geographic extent of drilling activities, collisions or other adverse effects are unlikely, and no significant cumulative impacts are expected.

Fisheries Resources . Exploration and production structures occur in the vicinity of the lease area. The additional effect of the proposed drilling activity would be negligible.

Coastal Habitats . Due to the distance of the wellsites from shore, routine activities are not expected to have any impacts on beaches and dunes, wetlands, seagrass beds, coastal wildlife refuges, wilderness areas, or any other managed or protected coastal area. The support bases at Port Fourchon and Boothville, Louisiana, are not in wildlife refuge or wilderness areas. Support operations, including the crew boat and supply boats, may have a minor incremental impact on coastal habitats. Over time with a large number of vessel trips, vessel wakes can erode shorelines along inlets, channels, and harbors. Impacts will be minimized by following the speed and wake restrictions

in harbors and channels.

New Information . New information included in the most recent Programmatic, Supplemental, and Final EISs (BOEM, 2012a,b,c) has been incorporated into the EIA, where applicable.

C.9.3 Cumulative Impacts to Socioeconomic Resources

The work planned in this EP is limited in geographic scope and duration, and the impacts on socioeconomic resources will be correspondingly limited.

The multi-lease-sale and Supplemental and Final EISs analyzed the cumulative impacts of oil and gas exploration and development in the lease area, in combination with other impact-producing activities, on commercial fishing, recreational fishing, recreational resources, historical and archaeological resources, land use and coastal infrastructure, demographics, and environmental justice (MMS, 2007b;BOEM, 2012b,c, 2013). BOEM also analyzed the economic impact of oil and gas activities on the Gulf

States, finding only minor impacts in most of Texas, Mississippi, Alabama, and Florida, more significant impacts in parts of Texas, and substantial impacts on Louisiana.

Shell’s proposed activities will have negligible cumulative impacts on socioeconomic resources. There are no IPFs associated with routine operations that are expected to affect public health and safety, employment and infrastructure, recreation and tourism, land use, or other marine uses. Due to the distance from shore, it is unlikely that any recreational fishing activity is occurring in the project area, and it is unlikely that any commercial fishing activity other than longlining occurs at or near the project area. The project will have negligible impacts on fishing activities.

New Information . New information included in the most recent Programmatic, Supplemental, and Final EISs (BOEM, 2012a,b,c, 2013) has been incorporated into the EIA, where applicable.



# D. ENVIRONMENTAL HAZARDS

D.1 Geologic Hazards

The shallow hazards assessment included in this EP concludes that the wellsites are suitable for the planned activities. Proposed wellsites A, B, C, and D are located 950, 1,300, 1,750, and 825 ft (290, 396, 533, and 251 m), respectively, from the nearest seafloor faults (GEMS, 2013). No fault penetration is expected at any of the proposed wellsites. Based on results of a high-resolution geophysical survey consisting of frequency-enhanced three-dimensional seismic, subbottom profiling, (AUV) surveys, multibeam bathymetry, and side-scan sonar, these locations appear suitable for the planned activities (GEMS, 2013).

See EP Section 6a for supporting geological and geophysical information.

D.2 Severe Weather

Under most circumstances, weather is not expected to have any effect on the proposed activities. Extreme weather, including high winds, strong currents, and large waves, was considered in the design criteria for the drilling rig. High winds and limited visibility during a severe storm could disrupt communication and support activities (vessel and helicopter traffic) and make it necessary to suspend some activities on the drilling rig for safety reasons until the storm or weather event passes. In the event of a hurricane, procedures in Shell’s Hurricane Evacuation Plan would be followed.

D.3 Currents and Waves

A rig-based acoustic Doppler current profiler will be used to continuously monitor the current beneath the rig. Metocean conditions such as sea states, wind speed, ocean currents, etc., will also be continuously monitored. Under most circumstances, physical oceanographic conditions are not expected to have any effect on the proposed activities. Strong currents (caused by Loop Current eddies and intrusions) and large waves were considered in the design criteria for the drilling rig. High waves during a severe storm could disrupt support activities (i.e., vessel and helicopter traffic) and make it necessary to suspend some activities on the drilling rig for safety reasons until the storm or weather event passes.



# E. ALTERNATIVES

No formal alternatives were evaluated in this EIA. However, various technical and operational options, including the location of the wellsites and the selection of a drilling unit, were considered by Shell in developing the proposed action. There are no other reasonable alternatives to accomplish the goals of this project.

# F. MITIGATION MEASURES

The proposed action includes numerous mitigation measures required by laws, regulations, and BOEM lease stipulations and NTLs. The project will comply with applicable federal, state, and local requirements concerning air pollutant emissions, discharges to water, and solid waste disposal. Project activities will be conducted under Shell’s OSRP and will include the measures described in

EP Section 2f

.



# G. CONSULTATION

No persons or agencies were consulted regarding potential impacts associated with the propose d activities during the preparation of this EIA.



# H. PREPARERS

Th is EIA was prepared at the direction of Shell Offshore Inc. by its contractor, CSA Ocean Sciences Inc.
Contributors included the following:

 Tracy Albert (Regulatory Specialist, Regulatory Compliance Consultants of LA, LLC);

 Jeffrey McMenis (Environmental Engineer, Shell Exploration & Production Co.);

 John Baird (Reservoir Engineer, Shell Exploration & Production Co.);

 Megan Henley (Drilling Engineer, Shell International Exploration and Production );

 Saurabh Jain (Well Engineer, Shell International Exploration and Production);

 Phil Weatherill (Geologist, Shell Exploration & Production Co.);

 June Mire, Ph.D. (Senior Ecologist and Project Manager, Tetra Tech, Inc.);

 Neal Phillips, Ph.D. (Senior Scientist, CSA Ocean Sciences Inc.);

 Cindy Chandool, Ph.D. (Senior Scientist, CSA Ocean Sciences Inc.);

 Deborah Fawcett (Project Scientist III, CSA Ocean Sciences Inc.);

 Keith VanGraafeiland (GIS/Remote Sensing Specialist, CSA Ocean Sciences Inc.); and

 Kim Dunleavy (Senior Technical Editor, CSA Ocean Sciences Inc. ).



# I. REFERENCES

Ackleh, A., G.E. Loup, J.W. Loup, B. Ma, J.J. Newcomb, N. Pal, N.A. Sidorovskaia, and C. Tiemann. 2012. Assessing the
Deepwater Horizon oil spill impact on marine mammal population through acoustics: Endangered sperm whales. J.
Acoust. Soc. Am. 131(3): 2306-2314.

Barkuloo, J.M. 1988. Report on the conservation status of the Gulf of Mexico sturgeon, Acipenser oxyrinchus desotoi.
U.S. Department of the Interior, U.S. Fish Wildlife Service, Panama City, FL. 33 pp.

Barkaszi, M.J., M. Butler, R. Compton, A. Unietis, and B. Bennet. 2012. Seismic survey mitigation measures and marine mammal observer reports. U.S. Dept. of the Interior, Bureau of Ocean Energy Management, Gulf of Mexico OCS
Region, New Orleans, LA. OCS Study BOEM 2012-015. 53 pp.

Bélanger, L. and J. Bédard. 1989. Responses of Staging Greater Snow Geese to Human Disturbance. Journal of Wildlife
Management 53:713-719.

Biggs, D.C. and P.H. Ressler. 2000. Water column biology, pp. 141-187. In: Continental Shelf Associates, Inc. Deepwater
Program: Gulf of Mexico Deepwater Information Resources Data Search and Literature Synthesis. Volume I:
Narrative Report. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New
Orleans, LA. OCS Study MMS 2000- 049.Boehm, P., D. Turton, A. Raval, D. Caudle, D. French, N. Rabalais, R. Spies, and J. Johnson. 2001. Deepwater program:

Literature review, environmental risks of chemical products used in Gulf of Mexico deepwater oil and gas
operations. Volume I: Technical report. U.S. Department of the Interior, Minerals Management Service, Gulf of
Mexico OCS Region, New Orleans, LA. OCS Study MMS 2001-011. 326 pp. Brooke, S., and W.W. Schroeder. 2007. State of deep coral ecosystems in the Gulf of Mexico region: Texas to the Florida Straits, pp. 271-306. In: S.E. Lumsden, T.F. Hourigan, A.W. Bruckner, and G. Dorr (eds.), The State of Deep
Coral Ecosystems of the United States. NOAA Tech. Memo. CRCP-3. Silver Spring, MD. 365 pp. Brooks, J.M., C. Fisher, H. Roberts, B. Bernard, I. McDonald, R. Carney, S. Joye, E. Cordes, G. Wolff, and E. Goehring.
2009. Investigations of chemosynthetic communities on the lower continental slope of the Gulf of Mexico: Interim
Report 2. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans,
LA. OCS Study MMS 2009-046.

Brooks, J.M., C. Fisher, H. Roberts, E. Cordes, I. Baums, B. Bernard, R. Church, P. Etnoyer, C. German,E. Goehring,

I. McDonald, Harry Roberts, T. Shank, D. Warren, S. Welsh, and G. Wolff. 2012. Exploration and research of
northern Gulf of Mexico deepwater natural and artificial hard-bottom habitats with emphasis on coral communities:
Reefs, rigs, and wrecks

— “ Lophelia II” Interim report. U.S. Dept. of the Interior, Bureau of Ocean Energy
Management, Gulf of Mexico OCS Region, New Orleans, LA. OCS Study BOEM 2012-106. 135 pp.
Bureau of Ocean Energy Management. 2011. Grid EA and ROV survey status report. Website accessed on

March 5, 2014 ; updated on October 1, 2012 at: https://www.data.boem.gov/homepg/data_center/other/ea_grid/ea_grid.asp

. Bureau of Ocean Energy Management. 2012a. Outer Continental Shelf Oil and Gas Leasing Program: 2012-2017. Final
Programmatic Environmental Impact Statement. U.S. Department of the Interior, Bureau of Ocean Energy Management. OCS EIS/EA BOEM 2012- 030.

Bureau of Ocean Energy Management. 2012b. Gulf of Mexico OCS Oil and Gas Lease Sales: 2012-2017. Western
Planning Area Lease Sales 229, 233, 238, 246 and 248. Central Planning Area Lease Sales 227, 231, 235, 241, and
247. Final Environmental Impact Statement. U.S. Department of the Interior, Bureau of Ocean Energy Management, Gulf of Mexico OCS Region. OCS EIS/EA BOEM 2012-019. 3 vols.

Bureau of Ocean Energy Management. 2012c . Gulf of Mexico OCS Oil and Gas Lease Sale: 2012. Central Planning Area Lease Sale 216/222. Final Supplemental Environmental Impact Statement. U.S. Department of the Interior, Bureau of Ocean Energy Management, Gulf of Mexico OCS Region. OCS EIS/EA BOEM 2012-058. 2 vols.

Bureau of Ocean Energy Management. 2012d . Archaeology Survey Blocks. Accessed on March 5, 2014 at: http://www.boem.gov/Environmental-Stewardship/Archaeology/surveyblocks-pdf.aspx

. Bureau of Ocean Energy Management. 2013. Gulf of Mexico OCS Oil and Gas Lease Sales: 2013-2014. Western
Planning Area Lease Sale 233. Central Planning Area Lease Sale 231. Final Supplemental Environmental Impact Statement. U.S. Department of the Interior, Bureau of Ocean Energy Management, Gulf of Mexico OCS Region. OCS EIS/EA BOEM 2013- 0118.

Bureau of Ocean Energy Management, Regulation and Enforcement. 2010. Federal & Academic Scientists Return from
Deep-sea Research Cruise in Gulf of Mexico: Scientists Observe Damage to Deep-sea Corals. Press release dated

4 November 2010. Accessed on March 5, 2014 at: http://www.noaanews.noaa.gov/stories2010/20101104_coralcruise.html

. Bureau of Ocean Energy Management Regulation and Enforcement. 2011. Gulf of Mexico OCS Oil and Gas Lease Sale:
2011. Western Planning Area Lease Sale 218. Final Supplemental Environmental Impact Statement.
U.S. Department of the Interior, Bureau of Ocean Energy Management, Regulation and Enforcement Gulf of Mexico OCS Region. OCS EIS/EA BOEMRE 2011-018. 801 pp.

C&C Technologies, Inc.. 2007. Archaeological Assessment Report, Blocks 895-898, 939-942, & 9 83 -986, Mississippi
Canyon Area. Project No. 072657-072954.

Carmichael, R.H., W.M. Graham, A. Aven, G.Worthy, and S. Howden. 2012. Were multiple stressors a ‘ perfect s torm’ for
northern Gulf of Mexico bottlenose dolphins ( Tursiops truncatus ) in 2011? PLoS ONE 7(7): e41155. Accessed on

March 5, 2014 at: http://www.plosone.org/article/info%3Adoi%2F10.1371%2Fjournal.pone.0041155

. Camilli, R., C.M. Reddy, D.R. Yoerger, B.A.S. Van Mooy, M.V. Jakuba, J.C. Kinsey, C.P. McIntyre, S.P. Sylva, and
J.V. Maloney. 2010. Tracking hydrocarbon plume transport and biodegradation at Deepwater Horizon . Science DOI: 10.1126/science.1195223.

Carr, A. 1996. Suwannee River sturgeon, pp. 73-83. In: M.H. Carr (ed.), A Naturalist in Florida. Yale University Press,

New Haven, CT.

Clapp, R.B., R.C. Banks, D. Morgan-Jacobs, and W.A. Hoffman. 1982a. Marine birds of the southeastern United States
and Gulf of Mexico. Part I. Gaviiformes through Pelicaniformes. U.S. Fish and Wildlife Service, Office of Biological Services, Washington, DC. FWS/OBS-82/01. 637 pp.Clapp, R.B., D. Morgan-Jacobs, and R.C. Banks. 1982b. Marine birds of the southeastern United States and Gulf of

Mexico. Part II. Anseriformes. U.S. Fish and Wildlife Service, Office of Biological Services, Washington, DC. FWS/OBS-82/20. 492 pp.

Clapp, R.B., D. Morgan-Jacobs, and R.C. Banks. 1983. Marine birds of the southeastern United States and Gulf of
Mexico. Part III. Charadriiformes. U.S. Fish and Wildlife Service, Office of Biological Services, Washington, DC. FWS/OBS-83/30. 853 pp.

Collard, S.B. and C. Way. 1997. Chapter 5

– The biological environment. In: Science Applications International Corporation (ed.), Northeastern Gulf of Mexico Coastal and Marine Ecosystem Program: Data Search and Synthesis;
Synthesis Report. U.S. Department of the Interior, U.S. Geological Survey, Biological Resources Division and Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, LA. USGS/BRD/CR- 1997 -0005. OCS Study

MMS 96-0014. 313 pp. Continental Shelf Associates, Inc. 1997. Characterization and trends of recreational and commercial fishing from the
Florida Panhandle. U.S. Department of Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, LA. USGS/BRD/CR-1997-0001 and OCS Study MMS 97 -0020. 333 pp.

Continental Shelf Associates, Inc. 2002. Deepwater Program: Bluewater fishing and OCS activity, interactions between
the fishing and petroleum industries in deepwaters of the Gulf of Mexico. U.S. Department of the Interior, Minerals
Management Service, Gulf of Mexico OCS Region, New Orleans, LA. OCS Study MMS 2002-078.

Continental Shelf Associates, Inc. 2004. Final Report: Gulf of Mexico Comprehensive Synthetic Based Muds Monitoring
Program. Report prepared for SBM Research Group, Houston, TX. October 2004. 3 volumes.

Continental Shelf Associates, Inc. 2006. Effects of oil and gas exploration and development at selected continental
slope sites in the Gulf of Mexico. Volume II: Technical report. U.S. Department of the Interior, Minerals
Management Service, Gulf of Mexico OCS Region, New Orleans, LA. OCS Study MMS 2006-045.

Cruz-Kaegi, M.E. 1998. Latitudinal variations in biomass and metabolism of benthic infaunal communities.
Ph.D. dissertation, Texas A&M University, College Station, TX.

CSA International, Inc. 2007. Characterization of northern Gulf of Mexico deepwater hard- bottom communities with
emphasis on Lophelia coral. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS
Region, New Orleans, LA. OCS Study MMS 2007-044. 169 pp. + app.

Davis, R.W. and G.S. Fargion. 1996. Distribution and abundance of cetaceans in the north-central and western Gulf of
Mexico: Final report. U.S. Dept. of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New
Orleans, LA. Accessed on March 5, 2014 at: http://www.getcited.org/pub/100201353

. Davis, R.W., J.G. Ortega-Ortiz, C.A. Ribic, W.E. Evans, D.C. Biggs, P.H. Ressler, J.H. Wormuth, R.R. Leben, K.D. Mullin, and
B. Würsig. 2000. Cetacean habitat in the northern Gulf of Mexico, pp. 217-253. In: R.W. Davis, W.E. Evans, and B. Würsig (eds.), Cetaceans, sea turtles, and seabirds in the northern Gulf of Mexico: Distribution, abundance and
habitat associations. Volume II: Technical report. U.S. Geological Survey, Biological Resources Division, USGS/BRD/CR-1999-0006 and U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS
Region, New Orleans, LA. OCS Study MMS 2000-003. 346 pp. Accessed on March 5, 2014 at: http://www.data.boem.gov/PI/PDFImages/ESPIS/3/3153.pdf

. Ditty, J.G. 1986. Ichthyoplankton in neretic waters of the northern Gulf of Mexico off Louisiana: Composition, relative abundance, and seasonality. Fish. Bull. 84(4):935- 946.

Ditty, J.G., G.G. Zieske, and R.F. Shaw. 1988. Seasonality and depth distribution of larval fishes in the northern Gulf of

Mexico above 26°00’N. Fish. Bull. 86:811

- 823.

Efroymson, R.A., W.H. Rose, S. Nemeth, and G.W. Suter II. 2000. Ecological risk assessment framework for low altitude
overflights by fixed-wing and rotary-wing military aircraft. Report prepared by Oak Ridge National Laboratory, Oak Ridge, TN. ORNL/TM-2000/289: ES-5048.

Fertl, D., A. Schiro, G. Regan, C. Beck, N. Adimey, L. Price-May, A. Amos, G. Wother, and R. Crossland. 2005. Manatee

occurrence in the Northern Gulf of Mexico west of Florida. Gulf and Caribbean Research 17: 69- 94.

Florida Fish and Wildlife Conservation Commission. 201 3a . Green turtle nesting in Florida. Accessed on March 5, 2014

at: http://myfwc.com/research/wildlife/sea-turtles/nesting/green-turtle/

. Florida Fish and Wildlife Conservation Commission. 201 3b . Leatherback nesting in Florida. A cce ssed on March 5, 2014

at: http://myfwc.com/research/wildlife/sea-turtles/nesting/leatherback/

. Florida Fish and Wildlife Conservation Commission. 201 3c . Florida's endangered and threatened species. Website
accessed on October 31, 2013. http://myfwc.com/media/1515251/Threatened_Endangered_Species.pdf

Fox, D.A., J.E. Hightower, and F.M. Paruka. 2000. Gulf sturgeon spawning migration and habitat in the Choctawhatchee
River system, Alabama-Florida. Trans. Am. Fish. Soc. 129:811-826.

Fritts, T.H. and R.P. Reynolds. 1981. Pilot study of the marine mammals, birds, and turtles in OCS areas of the Gulf of Mexico. U.S. Department of the Interior, Fish and Wildlife Service, Biological Services Program. FWS/OBS-81/36.Gallaway, B. (ed.). 1988. Northern Gulf of Mexico continental slope study, final report: Year 4. Volume II: Synthesis

report. Final report submitted to the Minerals Management Service, New Orleans, LA.

Contract No. 14

- 12 -0001-30212.

Gallaway, B.J., J.G. Cole, and R.G. Fechhelm. 2003. Selected Aspects of the Ecology of the Continental Slope Fauna of
the Gulf of Mexico: A Synopsis of the Northern Gulf of Mexico Continental Slope Study, 1983-1988.
U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, LA.
OCS Study MMS 2003-072.

Geoscience Earth and Marine Services, Inc. 2013. Geologic, Stratigraphic and Archaeological Assessment of Blocks 942 (OCS G-24130), 943 (OCS G-34467), and Portions of Surrounding Blocks, Mississippi Canyon Area, Gulf of Mexico.
Project No. 0513-2243a,b.

Geraci, J.R. and D.J. St. Aubin. 1987. Effects of offshore oil and gas development on marine mammals and turtles, pp.

587 -617. In: D.F. Boesch and N.N. Rabalais (eds.), Long Term Environmental Effects of Offshore Oil and Gas
Development. Elsevier Applied Science Publ. Ltd., London and New York.

Geraci, J.R. and D.J. St. Aubin. 1990. Sea Mammals and Oil: Confronting the Risks. Academic Press, San Diego, CA.

239 pp.
Goold, J.C. and S.E. Jones. 1995. Time and frequency domain characteristics of sperm whale clicks. J. Acoust. Soc. Am

. 98:1,279

– 1,291.

Gulf of Mexico Fishery Management Council. 2005. Generic Amendment Number 3 for addressing Essential Fish
Habitat Requirements, Habitat Areas of Particular Concern, and adverse effects of fishing in the following Fishery
Management Plans of the Gulf of Mexico: Shrimp fishery of the Gulf of Mexico, United States waters red drum fishery of the Gulf of Mexico, reef fish fishery of the Gulf of Mexico coastal migratory pelagic resources (mackerels)
in the Gulf of Mexico and South Atlantic, stone crab fishery of the Gulf of Mexico, spiny lobster in the Gulf of Mexico
and South Atlantic, coral and coral reefs of the Gulf of Mexico. Gulf of Mexico Fishery Management Council, Tampa,

FL.

Hazen, T.C., E.A. Dubinsky, T.Z. DeSantis, G.L. Andersen, Y.M. Piceno, N. Singh, J.K. Jansson, A. Probst, S.E. Borglin, J.L.
Fortney, W.T. Stringfellow, M. Bill, M.S. Conrad, L.M. Tom, K.L. Chavarria, T.R. Alusi, R. Lamendella, D.C. Joyner, C.
Spier, J. Baelum, M. Auer, M.L. Zemla, R. Chakraborty, E.L. Sonnenthal, P. D’haeseleer, H.N. Holman, S. Osman, Z. Lu,
J.D. Van Nostrand, Y. Deng, J. Zhou, and O.U. Mason. 2010. Deep-sea oil plume enriches indigenous oil-degrading

bacteria. Science DOI: 10.1126/science.1195979.

Hess, N.A. and C.A. Ribic. 2000. Seabird ecology, pp. 275-315. In: R.W. Davis, W.E. Evans, and B. Würsig (eds.),
Cetaceans, sea turtles, and seabirds in the northern Gulf of Mexico: Distribution, abundance and habitat
associations. Volume II: Technical report. U.S. Geological Survey, Biological Resources Division, USGS/BRD/CR-1999-0006 and U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS
Region, New Orleans, LA. OCS Study MMS 2000 -003. 346 pp.

Higashi, G.R. 1994. Ten years of fish aggregating device (FAD) design and development in Hawaii. Bull. Mar. Sci. 55(2-
3):651-666.

Hildebrand, J . 2004. Impacts of anthropogenic sound on cetaceans

. Unpublished paper submitted to the International
Whaling Commission Scientific Committee

. SC/56 E 13

. Holland, K.R., R.W. Brill, and R.K.C. Chang. 1990. Horizontal and vertical movements of yellowfin and bigeye tuna
associated with fish aggregating devices. Fish. Bull. 88:493- 507.

Holt, M. M., D.P. Noren, V. Veirs, C.K. Emmons, and S. Veirs. 2009. Speaking up: Killer whales ( Orcinus orca ) increase
their call amplitude in response to vessel noise. The Journal of the Acoustical Society of America

, 125 (1): 27

- 32.

Jasny, M., J. Reynolds, C. Horowitz, and A. Wetzler. 2005. Sounding the Depths II: The Rising Toll of Sonar, Shipping and
Industrial Ocean Noise on Marine Life. Natural Resources Defense Council, New York, NY. Vii + 76 pp.

Ji, Z-G., W.R. Johnson, C.F. Marshall, and E.M. Lear. 2004. Oil-Spill Risk Analysis: Contingency Planning Statistics for Gulf
of Mexico OCS Activities. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS
Region. OCS Report MMS 2004-026.

Jochens, A., D. Biggs, K. Benoit-Bird, D. Engelhaupt, J. Gordon, C. Hu, N. Jaquet, M. Johnson, R. Leben, B. Mate, P. Miller,
J. Ortega-Ortiz, A. Thode, P. Tyack, and B. Würsig. 2008. Sperm whale seismic study in the Gulf of Mexico:
Synthesis report. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New
Orleans, LA. OCS Study MMS 2008-006. 341 pp. Joint Analysis Group. 2010a. Joint Analysis Group (JAG) review of preliminary data to examine subsurface oil in the
vicinity of MC252#1 May 19 to June 19, 2010. Accessed on March 5, 2014 at: http://gomex.erma.noaa.gov/layerfiles/7229/files/JAG_Data_Report_2_Subsurface%20Oil_Final.pdf

. Joint Analysis Group. 2010b. Joint Analysis Group (JAG) review of R/V Brooks McCall data to examine subsurface oil.

Accessed on March 5, 2014 at: http://www.noaa.gov/sciencemissions/PDFs/JAG_Report_1_BrooksMcCall_Final_June20.pdf

.Joint Analysis Group. 2010c. Joint Analysis Group (JAG) review of preliminary data to examine oxygen levels in the

vicinity of MC252#1 May 8 to August 9, 2010. Accessed on March 5, 2014 at: http://www.noaa.gov/sciencemissions/PDFs/JAG_Oxygen_Report%20%28FINAL%20090410%29.pdf

. Joye, S.B., I.R. MacDonald, I. Leifer, and V. Asper. 2011. Magnitude and oxidation potential of hydrocarbon gases

released from the BP oil well blowout. Nature Geoscience 4: 160- 164. Accessed on March 5, 2014 at: http://www.nature.com/ngeo/journal/v4/n3/abs/ngeo1067.html

. Kessler, J.D., D. L. Valentine, M.C. Redmond, M. Du, E.W. Chan, S.D. Mendes, E.W. Quiroz, C.J. Villanueva, S.S. Shusta,
L.M. Werra, S.A. Yvon-Lewis, and T.C. Weber. 2011. A persistent oxygen anomaly reveals the fate of spilled
methane in the deep Gulf of Mexico. Science 331: 312-315

. Kujawinski, E.B., M.C. Kido Soule, D.L. Valentine, A.K. Boysen, K. Longnecker, and M.C. Redmond. 2011. Fate of
dispersants associated with the Deepwater Horizon oil spill. Environ. Sci. Technol. 45(4): 1298- 1306

. LGL Ecological Research Associates, Ltd. 2006. Assessment o f the effects of underwater noise from the proposed

Neptune L NG Project - Supplementary biological effects report to Ecology and Environment, Inc.

, LGL Report No.

4200

- 2a

, 8 August 2006. 11 pp.

Lohoefener, R., W. Hoggard, K. Mullin, C. Roden, and C. Rogers. 1990. Association of sea turtles with petroleum
platforms in the north-central Gulf of Mexico. U.S. Department of the Interior, Minerals Management Service, Gulf
of Mexico OCS Region, New Orleans, LA. OCS Study MMS 90 -0025. 90 pp.
Lutcavage, M.E., P.L. Lutz, G.D. Bossart, and D.M. Hudson. 1995. Physiologic and clinicopathologic effects of crude oil
on loggerhead sea turtles. Arch. Environ. Contam. Toxicol. 28:417- 422.

Lutcavage, M.E., P. Plotkin, B. Witherington, and P.L. Lutz. 1997. Human impacts on sea turtle survival, pps. 387 -409. In: Lutz, P.L. and J.A. Musick (eds.), The Biology of Sea Turtles. CRC Press, Boca Raton, FL.

MacDonald, I.R. (ed.). 2002. Stability and Change in Gulf of Mexico Chemosynthetic Communities. Volume II: Technical
Report. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans,
LA. OCS Study MMS 2002-036. 456 pp. Marine Mammal Commission. 2011. Assessing the long-term effects of the BP Deepwater Horizon oil spill on marine

mammals in the Gulf of Mexico: A statement of research needs. Accessed on March 5, 2014 at: http://www.mmc.gov/reports/workshop/pdf/longterm_effects_bp_oilspil.pdf

. McCauley, R. 1998. Radiated underwater noise measured from the drilling rig Ocean General , rig tenders Pacific Ariki

and Pacific Frontier

, fishing vessel Reef Venture and natural sources in the Timor sea, northern Australia. Prepared
for Shell Australia, Melbourne. 52pp. Accessed on March 11, 2014 at: http://cmst.curtin.edu.au/local/docs/pubs/1998-19.pdf

. Mendelssohn, I.A., G.L. Andersen, D.M. Baltz, R.H. Caffey, K.R. Carman, J.W. Fleeger, S.B. Joye, Q. Lin, E. Maltby, E.B.
Overton, and L. P. Rozas. 2012. Oil Impacts on Coastal Wetlands: Implications for the Mississippi River Delta
Ecosystem after the Deepwater Horizon Oil Spill. BioScience, 62(6):562-574.

Accessed on March 5, 2014 at: http://www.jstor.org/discover/10.1525/bio.2012.62.6.7?uid=3739600&uid=2129&uid=2&uid=70&uid=4&uid=3739

256&sid=21102052664157

. Minerals Management Service. 2000. Gulf of Mexico Deepwater Operations and Activities: Environmental Assessment.
U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, LA. OCS EIS/EA MMS 2000-001.

Minerals Management Service. 2007a. Outer Continental Shelf Oil & Gas Leasing Program: 2007-2012 Final
Environmental Impact Statement. U.S. Department of the Interior, Minerals Management Service, Herndon, VA. OCS EIS/EA MMS 2007-003. April 2007.

Minerals Management Service. 2007b. Gulf of Mexico OCS Oil and Gas Lease Sales: 2007-2012. Western Planning Area
Sales 204, 207, 210, 215, and 218; Central Planning Area Sales 205, 206, 208, 213, 216, and 222. Final Environmental Impact Statement. U.S. Dept. of the Interior, Minerals Management Service, Gulf of Mexico OCS Region. OCS EIS/EA MMS 2007-018. April 2007.

Minerals Management Service. 2008. Gulf of Mexico OCS Oil and Gas Lease Sales: 2009-2012; Central Planning Area
Sales 208, 213, 216, and 222; Western Planning Area Sales 210, 215, and 218. Final Supplemental Environmental
Impact Statement. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, LA. OCS EIS/EA MMS 2008-041. September 2008.

Minerals Management Service. 2010. OCS Regulatory Framework for the Gulf of Mexico Region. U.S. Department of
the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New Orleans, LA. OCS Report 2010-019.

May 2010.

Mississippi Department of Wildlife, Fisheries and Parks. 2005 . Mississippi’s species of greatest conservation need by
ecoregion. In: Mississippi's Comprehensive Wildlife Conservation Strategy 2005

– 2015, App. VIII pp. 375 -380.

Accessed on March 5, 2014 at: http://www.mdwfp.com/media/63792/cwcs.pdf

.Morrow, J.V., Jr., J.P. Kirk, K.J. Killgore, H. Rugillio, and C. Knight. 1998. Status and recovery of Gulf sturgeon in the Pearl

River system, Louisiana-Mississippi. North American Journal of Fisheries Management 18:798-808.

Mullin, K., W. Hoggard, C. Roden, R. Lohoefener, C. Rogers, and B. Taggart. 1991. Cetaceans on the upper continental slope in the north-central Gulf of Mexico. OCS Study/MMS 910027. U.S. Department of the Interior, Minerals
Management Service, Gulf of Mexico OCS Regional Office, New Orleans, LA. 108 pp.

Mullin, K.D. 2007. Abundance of cetaceans in the oceanic Gulf of Mexico based on 2003-2004 ship surveys. Available
from: National Marine Fisheries Service, Southeast Fisheries Science Center, Pascagoula, MS. 26 pp.
National Marine Fisheries Service. 2007. Endangered Species Act, Section 7 Consultation

– Biological Opinion. Gulf of
Mexico Oil and Gas Activities: Five-Year Leasing Plan for Western and Central Planning Areas 2007-2012. 29 June

2007.

National Marine Fisheries Service. 2009a. Final Amendment 1 to the Consolidated Atlantic Highly Migratory Species
Fishery Management Plan Essential Fish Habitat. Highly Migratory Species Management Division, Office of
Sustainable Fisheries, Silver Spring, MD. June 2009. Accessed on March 5, 2014 at: http://www.nmfs.noaa.gov/sfa/hms/EFH/Final/FEIS_Amendment_Total.pdf

. National Marine Fisheries Service. 2009b. Sperm Whale ( Physeter macrocephalus ) 5-Year Review: Summary and
Evaluation. National Marine Fisheries Service, Office of Protected Resources, Silver Spring, MD. January 2009. 44

pp.
National Marine Fisheries Service. 2010a. Sea turtles, dolphins, and whales and the Gulf of Mexico oil spill. Accessed

on March 5, 2014 at: http://www.nmfs.noaa.gov/pr/health/oilspill.htm

. National Marine Fisheries Service. 2010b. Final recovery plan for the sperm whale ( Physeter macrocephalus ). Silver
Spring, MD. 165 pp. Accessed on March 5, 2014 at: http://www.nmfs.noaa.gov/pr/pdfs/recovery/final_sperm_whale_recovery_plan_21dec.pdf

. National Marine Fisheries Service. 2010c. Impacts of oil on marine mammals and sea turtles. Accessed on

March 5, 2014 at: http://www.nmfs.noaa.gov/pr/pdfs/health/oil_impacts.pdf

. National Marine Fisheries Service. 2010d. Gulf sturgeon ( Acipenser oxyrinchus desotoi ). Website accessed on

March 5, 2014 ; updated on February 27, 2013 at: http://www.nmfs.noaa.gov/pr/species/fish/gulfsturgeon.htm

. National Marine Fisheries Service. 2013. Draft marine mammal stock assessment reports (SARs). Website accessed on

March 5, 2014; updated on February 6, 2014 at: http://www.nmfs.noaa.gov/pr/sars/draft.htm

. National Marine Fisheries Service and U.S. Fish and Wildlife Service. 2008. Recovery plan for the Northwest Atlantic population of the loggerhead sea turtle ( Caretta caretta ), second revision. National Marine Fisheries Service, Silver
Spring, MD. Accessed on March 5, 2014 at: http://www.nmfs.noaa.gov/pr/pdfs/recovery/turtle_loggerhead_atlantic.pdf

. National Marine Fisheries Service, U.S. Fish and Wildlife Service, and SEMARNAT. 2011. Bi -National Recovery Plan for the Kemp‘s Ridley Sea Turtle ( Lepidochelys kempii ), Second Revision. National Marine Fisheries Service. Silver
Spring, MD. Accessed on March 5, 2014 at: http://www.fws.gov/kempsridley/Finals/kempsridley_revision2.pdf

. National Oceanic and Atmospheric Administration. 2006. Fact Sheet: Small Diesel Spills (500-5,000 gallons). NOAA
Scientific Support Team, Hazardous Materials Response and Assessment Division, National Oceanic and
Atmospheric Administration, Seattle, WA. 2 pp.
National Oceanic and Atmospheric Administration. 2013. 2010-2013 Cetacean Unusual Mortality Event in Northern

Gulf of Mexico. Website accessed March 5, 2014; updated on March 4, 2014 at: http://www.nmfs.noaa.gov/pr/health/mmume/cetacean_gulfofmexico.htm

. National Research Council. 1983. Drilling Discharges in the Marine Environment. National Academy Press, Washington,

DC. 180 pp.

National Research Council. 2003a. Ocean noise and marine mammals. Ocean Studies Board, National Academies Press,
Washington, DC. 204 pp.

National Research Council. 2003b. Oil in the Sea III: Inputs, Fates, and Effects. National Academies Press, Washington,

DC. 182 pp. + app.

National Wildlife Federation. 2012. Wildlife library. Whooping Crane. Accessed on March 5, 2014 at: http://www.nwf.org/wildlife/wildlife-library/birds/whooping-crane.aspx

. Neff, J.M. 1987. Biological effects of drilling fluids, drill cuttings and produced waters, pp. 469-538. In: D.F. Boesch and N.N. Rabalais (eds.), Long-Term Effects of Offshore Oil and Gas Development. Elsevier Applied Science Publishers,

London.

Neff, J.M., S. McKelvie, and R.C. Ayers, Jr. 2000. Environmental impacts of synthetic based drilling fluids. Prepared by
Robert Ayers & Associates, Inc. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS
Region, New Orleans, LA. OCS Study MMS 2000-064. 118 pp.Neff, J.M., A.D. Hart, J.P. Ray, J.M. Limia, and T.W. Purcell. 2005. An assessment of seabed impacts of synthetic-based

drilling-mud cuttings in the Gulf of Mexico. 2005 SPE/EPA/DOE Exploration and Production Environmental
Conference, 7-9 March 2005, Galveston, Texas, USA. SPE 94086.

Nowlin, W.D., Jr., A.E. Jochens, S.F. DiMarco, R.O. Reid, and M.K. Howard. 2001. Deepwater Physical Oceanography
Reanalysis and Synthesis of Historical Data: Synthesis Report. U.S. Department of the Interior, Minerals
Management Service, Gulf of Mexico OCS Region, New Orleans, LA. OCS Study MMS 2001-064. 528 pp. Operational Science Advisory Team. 2010. Summary report for sub-surface and sub-sea oil and dispersant detection:
Sampling and monitoring. Prepared for Paul F. Zukunft, U.S. Coast Guard Federal On-Scene Coordinator, Deepwater
Horizon MC252. December 17, 2010. Accessed on March 5, 2014 at: http://www.restorethegulf.gov/sites/default/files/documents/pdf/OSAT_Report_FINAL_17DEC.pdf

. Peake, D.E. 1996. Bird surveys, pp. 271-304. In: R.W. Davis and G.S. Fargion (eds.), Distribution and abundance of
cetaceans in the north-central and western Gulf of Mexico, Final report. Volume II: Technical report. Prepared by
the Texas Institute of Oceanography and the National Marine Fisheries Service. U.S. Department of the Interior,
Minerals Management Service, Gulf of Mexico OCS Region Office, New Orleans, LA. OCS Study MMS 96-0027. 357

pp. Powers, K. 1987. Seabirds, pp. 194-201. In: J.D. Milliman and W.R. Wright (eds.), The Marine Environment of the U.S. Atlantic Continental Slope and Rise. Jones and Bartlett Publ., Inc. Boston/Woods Hole, MA. 275 pp.

Rathbun, G.B. 1988. Fixed-wing airplane versus helicopter surveys of manatees. Mar. Mamm. Sci. 4(1):71- 75.

Relini, M., L.R. Orsi, and G. Relini. 1994. An offshore buoy as a FAD in the Mediterranean. Bull. Mar. Sci. 55(2-3):1,099-

1,105.

Richards, W.J., T. Leming, M.F. McGowan, J.T. Lamkin, and S. Kelley-Farga. 1989. Distribution of fish larvae in relation to
hydrographic features of the Loop Current boundary in the Gulf of Mexico. Rapp. P.-v. Reun. Cons. Int. Explor. Mer.

191:169-176.

Richards, W.J., M.F. McGowan, T. Leming, J.T. Lamkin, and S. Kelley. 1993. Larval fish assemblages at the Loop Current boundary in the Gulf of Mexico. Bull. Mar. Sci. 53(2):475-537.

Richardson, W.J., C.R. Greene, Jr., C.I. Malme, and D.H. Thomson. 1995. Marine Mammals and Noise. Academic Press,
San Diego, CA. 576 pp.

Rodgers, J., Jr, and S. Schwikert. 2002. Buffer Zone Distances to Protect Foraging and Loafing Waterbirds from
Disturbances by Personal Watercraft and Outboard-Powered Boats. Conservation Biology 16:216- 224.

Ross, S.W., A.W.J. Demopoulos, C.A. Kellogg, C.L. Morrison, M.S. Nizinski, C.L. Ames, T.L. Casazza, D. Gualtieri, K. Kovacs,
J.P. McClain, A.M. Quattrini, A.Y. Roa-Varón, and A.D. Thaler. 2012. Deepwater Program: Studies of Gulf of Mexico
lower continental slope communities related to chemosynthetic and hard substrate habitats: U.S. Geological Survey
Open-File Report 2012-1032. 301 pp.

Rowe, G.T. and M.C. Kennicutt II. 2009. Northern Gulf of Mexico Continental Slope Habitats and Benthic Ecology Study.
Final Report. U.S. Department of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New
Orleans, LA. OCS Study MMS 2009-039. 456 pp.

Russell, R.W. 2005. Interactions between migrating birds and offshore oil and gas platforms in the northern Gulf of
Mexico: Final Report. U.S. Dept. of the Interior, Minerals Management Service, Gulf of Mexico OCS Region, New
Orleans, LA. OCS Study MMS 2005-009. 348 pp.

Salmon, M. and J. Wyneken. 1990. Do swimming loggerhead sea turtles ( Caretta caretta ) use light cues for offshore
orientation? Marine and Freshwater Behaviour and Physiology 17(4): 233- 246.

Sea Turtle Restoration Project. 20 11. Kemp’s ridley protection campaign. Accessed on March 5, 2014 at: http://www.seaturtles.org/article.php?list=type&type=41

. Share the Beach. 2014. Nesting season statistics. Accessed on March 5, 2014 at: http://www.alabamaseaturtles.com/nesting-season-statistics

. Shell. 2012. Greenhouse Gas Emissions. Accessed on March 5, 2014 at: http://www.shell.com/global/environmentsociety/environment/climate-change/greenhouse-gas-emissions.html

. Shigenaka, G., S. Milton, P. Lutz, R. Hoff, R. Yender, and A. Mearns. 2010. Oil and Sea Turtles: Biology, Planning and
Response. NOAA. National Ocean Service. Office of Restoration and Response. 111 pp. Accessed on March 5, 2014

at: http://archive.orr.noaa.gov/book_shelf/35_turtle_complete.pdf

. Smultea, M.A., J.R. Mobley, Jr., D. Fertl, and G.L. Fulling. 2008. An unusual reaction and other observations of sperm
whales near fixed wing aircraft. Gulf and Caribbean Research 20:75- 80.

Southall, B.L., A.E. Bowles, W.T. Ellison, J.J. Finneran, R.L. Gentry, C.R. Greene

, Jr.

, D. Kastak, D.R. Ketten, J.H. Miller, P.E.
Nachtigall, W.J. Richardson, J.A. Thomas, and P.L.Tyack. 2007. Marine mammal noise exposure criteria: initial
scientific recommendation. Aquatic Mammals 33:411- 521.

Spier, C., W. T. Stringfellow, T.C. Hazen, and M. Conrad. 2013. Distribution of hydrocarbons released during the 2010
MC252 oil spill in deep offshore waters. Environmental Pollution 173: 224- 230.State of Louisiana Department of Wildlife and Fisheries. 2013. Species by parish list. Accessed on March 5, 2014 at:

http://www.wlf.louisiana.gov/wildlife/species-parishlist?order=field_com_name_value&sort=asc&tid=All&type_1=All

. Sulak, K.J. and J.P. Clugston. 1998. Early life history stages of Gulf sturgeon in the Suwannee River, Florida. Trans. Am.

Fish. Soc. 127:758- 771.

Todd, V. L. G., W.D. Pearse, N.C. Tregenza, P.A. Lepper, and I.B. Todd. 2009. Diel echolocation activity of harbour porpoises ( Phocoena phocoena ) around North Sea offshore gas installations. ICES Journal of Marine Science, 66:

734 -745.

Tuxbury, S.M. and M. Salmon. 2005. Competitive interactions between artificial lighting and natural cues during
seafinding by hatchling marine turtles. Biol. Conserv. 121: 311-316.

U.S. Environmental Protection Agency. 2013 . The green book nonattainment areas for criteria pollutants. Website
accessed on March 5, 2014; updated on December 5, 2013 at: http://www.epa.gov/air/oaqps/greenbk

. U.S. Fish and Wildlife Service. Conservation Science and Policy Training. n.d. Sea Turtle Nest Protection Protocols for
Clean-up Crews on Beaches in Florida, Alabama, Mississippi, and Louisiana. 14 pp. Accessed on March 5, 2014 at: http://training.fws.gov/csp/oilspill/training/orientation/turtles/Sea_Turtle_Nest_Protection.pdf

. U.S. Fish and Wildlife Service. 2001. Florida manatee recovery plan ( Trichechus manatus latirostris ), Third Revision.
U.S. Fish and Wildlife Service, Southeast Region, Atlanta, GA.

U.S. Fish and Wildlife Service. 2003. Recovery plan for the Great Lakes Piping Plover ( Charadrius melodus ).
Fort Snelling, Minnesota. September 2003.

U.S. Fish and Wildlife Service. 2007. International Recovery Plan: Whooping Crane ( Grus americana ), Third Revision.
Albuquerque, New Mexico. March 2007.

U.S. Fish and Wildlife Service. 2010a. All about Piping Plovers. Accessed on March 5, 2014 at: http://www.fws.gov/plover/facts.html

. U.S. Fish and Wildlife Service. 2010b. FWS Deepwater Horizon oil spill response. Accessed on March 5, 2014 at: http://www.fws.gov/home/dhoilspill/pdfs/DHBirdsOfTheGulf.pdf

. U.S. Fish and Wildlife Service. 2010c. Species information, threatened and endangered animals and plants. Website

accessed on March 5, 2014 ; updated on October 29, 2013 at: http://www.fws.gov/endangered

. U.S. Fish and Wildlife Service. 2013. Hawksbill sea turtle ( Eretmochelys imbricata ). Accessed on March 5, 2014 at: http://www.fws.gov/northflorida/SeaTurtles/Turtle%20Factsheets/hawksbill-sea-turtle.htm

. U.S. Fish and Wildlife Service and Gulf States Marine Fisheries Commission. 1995. Gulf Sturgeon Recovery Plan.
Atlanta, Georgia. 170 pp. Accessed on March 5, 2014 at: http://www.nmfs.noaa.gov/pr/pdfs/recovery/sturgeon_gulf.pdf

. Wakeford, A. 2001. State of Florida conservation plan for Gulf sturgeon ( Acipencer oxyrinchus desotoi ). Florida Marine
Research Institute Technical Report TR-8. St. Petersburg, FL.

Waring, G.T., E. Josephson, K. Maze-Foley, and P.E. Rosel (eds .) . 2013. U.S. Atlantic and Gulf of Mexico Marine Mammal

Stock Assessments

–

2012. NOAA Tech Memo NMFS NE 223; 419 pp. Website accessed on March 5, 2014; updated
on February 10, 2014 at: http://www.nefsc.noaa.gov/nefsc/publications

. Wartzok, D. and D. Ketten. 1999

. Marine mammal sensory systems, pp. 117 -175. In : J.E. Reynolds and S. Rommel
(e ds .), Biology of Marine Mammals. Smithsonian Institution Press, Washington, DC.

Wei, C-L. 2006. The bathymetric zonation and community structure of deep-sea macrobenthos in the northern Gulf of
Mexico. M.S. thesis, Texas A&M University. Accessed on March 5, 2014 at: http://repository.tamu.edu/handle/1969.1/4927

. Weilgart, L. and H. Whitehead. 1993. Coda communication by sperm whales ( Physeter macrocephalus ) off the
Galapagos Islands. Can. J. Zool. 71:744

– 752.

White, H.K., P. Hsing, W. Cho, T.M. Shank, E.E. Cordes, A.M. Quattrini, R.K. Nelson, R. Camilli, A.W.J. Demopoulous, C.R.
German, J.M. Brooks, H.H. Roberts, W. Shedd, C.M. Reddy and C.R. Fisher. 2012a. Impact of the Deepwater
Horizon oil spill on a deep-water coral community in the Gulf of Mexico. Proceedings of the National Academy of

Sciences (Early Edition). doi: 10.1073/pnas.1118029109. Accessed on March 5, 2014 at: http://www.pnas.org/content/early/2012/03/23/1118029109.full.pdf+html?sid=56e8cdfe-2830-43f8-9d08-

8eca0efd27e2

. White, H.K., P. Hsing, W. Cho, T.M. Shank, E.E. Cordes, A.M. Quattrini, R.K. Nelson, R. Camilli, A.W.J. Demopoulous, C.R.
German, J.M. Brooks, H.H. Roberts, W. Shedd, C.M. Reddy, and C.R. Fisher. 2012b. Reply to Boehm and Carragher:
Multiple lines of evidence link deep-water coral damage to Deepwater Horizon oil spill. Proc. Nat. Acad. Sci

. 109 (40): E2648.

Whooping Crane Eastern Partnership. 2013. Whooping Crane Numbers 2002 thru 2013

. Accessed on March 5, 2014 at: http://www.bringbackthecranes.org/technicaldatabase/recovery/wc_nos_02to11.html

.Wiese, F.K., W.A. Montevecchi, G.K. Davoren, F. Huettmann, A.W. Diamond, and J. Linke. 2001. Seabirds at risk around

offshore oil platforms in the north-west Atlantic. Mar. Poll. Bull. 42(12):1,285-1,290.

Wilson, J. 2003. Manatees in Louisiana. Louisiana Conservationist. July/August 2003, pp. 4-7. Accessed on

March 5, 2014 at: http://lamer.lsu.edu/pdfs/Manatees_LaConservArticle.pdf

. Witherington, B.E. 1997. The problem of photopollution for sea turtles and other nocturnal animals, pp. 303 -328. In: J.R. Clemmons and R. Buchholz (eds.), Behavioral Approaches to Conservation in the Wild. Cambridge University
Press, Cambridge, England.

Würsig, B., S.K. Lynn, T.A. Jefferson, and K.D. Mullin. 1998. Behaviour of cetaceans in the northern Gulf of Mexico
relative to survey ships and aircraft. Aquatic Mammals 24:41-50.

Würsig, B., T.A. Jefferson, and D.J. Schmidly. 2000. The Marine Mammals of the Gulf of Mexico. Texas A&M University
Press, College Station, TX. 232 pp.SECTION 19 : Administrative Information

A. Exempted Information Description (Public Information Copies Only)

The following attachments are excluded from the public information copies of typical plans:

1b. OCS Plan Information form

– Bottom hole location & proposed total depth 2j. Blowout Scenario

–

confidential information for NTL 2010 N06 calculation 3a. Geologic Description 3b. Structure Contour Maps 3c. Interpreted 2D or 3D seismic line(s) 3d. Cross Section(s) 3e. Shallow Hazards Report 3g. High-Resolution Seismic Line & Top Hole Prog 3h. & 3i. Stratigraphic Column with Time vs. depth table

B. Bibliography

 Geoscience Earth and Marine Services, Inc. (GEMS), Geologic, Stratigraphic and Archaeological Assessment of Blocks 942 (OCS G-24130), 943 (OCS G-34467), and Portions of Surrounding Blocks, Mississippi Canyon Area, Gulf of Mexico. Project No. 0513-2243a,b, dated February 11,

2014.

 C&C Technologies, Archaeological Assessment Report, Blocks 895-898, 939-942, & 983-986, Mississippi Canyon Area. Project No. 072657 -072954, dated October, 2007. Data: AUV Side Scan
Sonar and Sub-Bottom Profiler

 Shell Regional OSRP

 Environmental Impact Assessment, CSA March 2014