## BIOLOGICAL ASSESSMENT

FLORIDA POWER & LIGHT COMPANY PORT EVERGLADES NEXT GENERATION CLEAN ENERGY CENTER

Public Consultation Tracking System (PCTS) 2012/00657 Prepared for: National Oceanic & Atmospheric Administration

– National Marine Fisheries S ervice Southeast Regional Office 263 13 th 

### Avenue South St

. Petersburg, FL 33701 Prepared by Inwater Research Group on behalf of: United States Environmental Protection Agency Region 4 Atlanta Federal Center 61 Forsyth Street Atlanta, Georgia 30303

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1.0 BACKGROUND / HISTORY

................................ ................................ ................................ .. 1 1.1 Purpose

................................ ................................ ................................ ......................... 1 1.2 Existing an d Physical Conditions

................................ ................................ ................. 2 1.3 FPL’s Existing Environmental Programs

................................ ................................ ..... 4 2.0 DESCRIPTION OF THE A CTION AND ACTION ARE A

................................ ..................... 5 2.1 The Proposed Action

................................ ................................ ................................ .... 5 2.2 The Action Area

................................ ................................ ................................ ........... 8 2.3 Project Benefits

................................ ................................ ................................ .......... 10 3.0 LISTED SPECIES AND C RITICAL HABITAT IN T HE ACTION AREA

......................... 11 3.1 Loggerhead Sea Turtle ( Caretta caretta )

................................ ................................ ... 11 3.1.1 General Information

................................ ................................ ...................... 11 3.1.2 Plant Specific Information

................................ ................................ ............ 12 3.2 Green Sea Turtle ( Chelonia mydas )

................................ ................................ ........... 13 3.2.1 General Information

................................ ................................ ...................... 13 3.2.2 Plant Specific Information

................................ ................................ ............ 13 3.3 Lea therback Sea Turtle ( Dermochelys coriacea )

................................ ....................... 14 3.3.1 General Information

................................ ................................ ...................... 14 3.3.2 Plant Specific Information

................................ ................................ ............ 15 3.4 Hawksbill Sea Turtle ( Eretmochelys imbricata )

................................ ........................ 15 3.4.1 General Information

................................ ................................ ...................... 15 3.4.2 Pla nt Specific Information

................................ ................................ ............ 15 3.5 Kemp's Ridley Sea Turtle ( Lepidochelys kempii )

................................ ...................... 16 3.5.1 General Information

................................ ................................ ...................... 16 3.5.2 Plant Specific Information

................................ ................................ ............ 17 3.6 Smalltooth Sawfish ( Pristis pectinata )

................................ ................................ ....... 17 3.6.1 Gene ral Information

................................ ................................ ...................... 17 3.6.2 Plant Specific Information

................................ ................................ ............ 18 3.7 Johnson’s Seagrass ( Halophila johnsonii )

................................ ................................ . 18 3.7.1 General Information

................................ ................................ ...................... 18 3.7.2 Plant Specific Information

................................ ................................ ............ 18 3.8 Other Listed Species

................................ ................................ ................................ ... 19 4.0 ENVIRONMENTAL BASELI NE CONDITIONS

................................ ................................ . 19 4.1 Loggerhead Sea Turtle ( Caretta caretta )

................................ ................................ ... 19 4.2 Green Sea Turtle ( Chelonia mydas )

................................ ................................ ........... 20 4.3 Leatherback Sea Turtle ( Dermochelys coriacea )

................................ ....................... 22 4.4 Hawksbill Sea Turtle ( Eretmochelys imbricata )

................................ ........................ 22 4.5 Kemp's Ridley Sea Turtle ( Lepidochelys kempii )

................................ ...................... 23 4.6 Smalltooth Sawfish ( Pristis pectinata )

................................ ................................ ....... 24 4.7 Johnson’s Seagrass ( Halophila johnsonii )

................................ ................................ . 24 5.0 EFFECTS OF THE PROPO SED ACTION

................................ ................................ ............ 25 5.1 Overview of the Proposed Action

................................ ................................ .............. 25 5.1.1 Loggerhead Sea Turtle ( Caretta caretta )

................................ ...................... 26 5.1.2 Green Sea Turtle ( Chelonia mydas )

................................ .............................. 27 5.1.3 Leatherback Sea Turtle ( Dermochelys coriacea )

................................ .......... 27 5.1.4 Hawksbill Sea Turtle ( Eretmochelys imbricata )

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5.1.5 Kemp's Ridley Sea Turtle ( Lepidochelys kempii )

................................ ......... 27 5.1.6 Unidentified Sea Turtle Species

................................ ................................ .... 27 5.1.7 Smalltooth Sawfish ( Pristis pectinata )

................................ .......................... 27 5.1.8 Johnson’s Seagrass ( Halophila johnsonii )

................................ .................... 28 5.2 Changes in Pote ntial Effects Under the Proposed Action

................................ .......... 28 5.2.1 Changes During the Construction Phase of PEEC

................................ ........ 28 5.2.2 Changes During Operation of PEEC

................................ ............................. 28 5.3 Minimization of Potential Impacts and Conservation Efforts under the Proposed Action

................................ ................................ ................................ ......... 29 5.3.1 Minimization

................................ ................................ ................................ . 30 5.3.2 Conservation Efforts

................................ ................................ ..................... 30 6.0 CUMULATIVE EFFECTS

................................ ................................ ................................ ..... 31 7.0 CONCLUSIONS

................................ ................................ ................................ ..................... 32 8.0 LITERATURE CITED

................................ ................................ ................................ ............ 34

LIST OF TABLES Table 1 ENDANGERED AND THREATENED SPECIES UNDER THE JURISDICTION OF

THE NATIONAL MARINE FISHERIES SERVICE IN THE SOUTH ATLANT IC Table 2 SUMMARY OF SEA TURTLE ENCOUNTERS IN THE PORT EVERGLADES PLANT

INTAKE CANAL SYSTEM 1990 THROUGH 2012

LIST OF FIGURES Figure 1 General Location of the FPL Port Everglades Plant Figure 2 FPL Port Everglades Plant (PPE) Figure 3 Typical Intake Str ucture Figure 4 Typical “3 on 1” Combined Cycle Unit Figure 5 Action Area Boundary Figure 6 Broward County Sawfish Encounters 2001 through 2012 Figure 7 Port Everglades Submerged Aquatic Vegetation MapNovember 2012 iii 113

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- 12.doc ABBREVIATIONS AND ACRONYMS

BA Biological Assessmen t BTU British Thermal Unit
cm c entimeter CO 2 carbon dioxide CPUE Catch per Unit Effort EPA U. S. Environmental Protection Agency ESA Endangered Species Act FDEP Florida Department of Environmental Protection FDOT Florida Department of Transporta tion FLUCFCS Florida Land Use, Cover and Forms Classification System FPL Florida Power & Light Company fps feet per second ft feet FWC Florida Fish and Wildlife Conservation Commission ICW Intracoastal Waterway INBS Index Nesting Beach Survey IWW Industrial Wastewater IRG Inwater Research Group km kilometer MGD million gallons per day MW megawatt NO x nitrogen oxides NMFS National Marine Fisheries Service NOAA National Oceanic & Atmospheric Administration PCTS Public Consultation Tracking System PM particulate matter PM 10 particulate matter with an aerodynamic particle size of 10 μm or less PPE Port Everglades Plant PEEC Port Everglades Next Generation Clean Energy Center SAC Southport Access Channel SERMANAT 

### Secretariat of Environmen t and Natural Resources (in Spanish: Secretaría

del Medio Ambiente y Recursos Naturales ) SCL straight carapace length SO 2 sulfur dioxide STSSN Sea Turtle Stranding and Salvage Network TN Turning Notch ULSD ultra

- low sulfur distillate USACE U.S

. Army Corps of Engineers USFWS U.S

. Fish and Wildlife ServicesNovember 2012 1 113

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### 1.0 BACKGROUND / HISTORY
This section provides the Biological Assessment (BA) purpose and includes informal consultation history

. It also describes the existing facility to be modernized and a background on existing FPL environmental programs.

1.1 Purpose The purpose of this BA is to address the effect of the Florida Power & Light Company (FPL) Port Everglades Next Generation Clean Energy Center (PEEC) Project (the Project) on species listed as end angered or threatened under the Endangered Species Act (ESA) or their designated critical habitat

. The Project involves the modernization of the existing Port Everglades Plant into a highly efficient, lower emission next generation clean energy center usi ng the latest combined cycle technology

. Four existing primarily oil

- fired units will be replaced with a single nominal 1,250 megawatt (MW) 3

- on - 1 combined cycle unit fueled primarily by natural gas. The Project is located within the boundaries of the Ci ty of Hollywood in Broward County, Florida

. The lead federal agency for this Project is the U.S. Environmental Protection Agency (EPA) Region 4, under the authority of the Clean Air Act

. In a letter dated February 22, 2012, the EPA requested an informa l consultation with the National Marine Fisheries Service (NMFS) and the U.S

. Fish and Wildlife Service (FWS) under Section 7 of the ESA to address concerns regarding the potential effects of the proposed Project on listed species and their critical habit at

. On March 29, 2012, NMFS recommended that EPA prepare a BA on the listed species that may occur in the Action Area, as defined in Section 2.2 below

. EPA designated FPL as the non

- federal agent and asked FPL to prepare the BA on behalf of EPA

. FPL hir ed Inwater Research Group (IRG) to prepare the BA

. The following is the list of species, provided by NMFS, which may occur in the Action Area:

Green sea turtle ( Chelonia mydas ) Loggerhead sea turtle ( Caretta caretta ) Hawksbill sea turtle ( Eretmochelys im bricata ) Leatherback sea turtle ( Dermochelys corieca ) Kemp's Ridley sea turtle ( Lepidochelys kempii ) Smalltooth sawfish ( Pristis pectinata ) Johnson’s seagrass ( Halophila johnsonii ) Johnson’s seagrass has been identified to exist in the Action Area. Table 1 presents further detail and the comprehensive list of all species

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- 12.doc Early coordination with NMFS was conducted via a teleconference on June 7, 2012 with

re presentatives from NMFS, FPL and IRG

. FPL also hosted a visit to the Project site on July 17, 2012 attended by NMFS, FPL and IRG

. Early coordination with U .S. Fish & Wildlife Service (FWS) was facilitated by a follow

- up email from EPA dated April 25, 2012

. Based on responsive correspondence from FWS to EPA on May 3, 2012, no further action is require d regarding listed species under their jurisdiction

. This BA addresses the proposed action in compliance with Section 7(c) of the ESA of 1973, as amended

. Section 7 of the ESA assures that, through consulta tion with the NMFS and/or the FWS, federal action s do not jeopardize the continued existence of any threatened, endangered or proposed listed species, or result in the destruction or adverse modification of critical habitat.

1.2 Existing and Physical Conditions

The FPL Port Everglades Plant (PPE) sits on 92. 5 acres of land in Broward County located in the mid

- port section within the jurisdictional area of Port Everglades (the Port) ( Figures 1 and 2)

. The Plant has convenient access to State Road 84 and Interstate

- 595 and is locally accessible by Eller Drive to the south

. Roadways that surround the Plant include S.E

. 14 th Avenue to the eas t, Eisenhower Drive to the west and S.E

. 26 th Street to the north

. The Port entrance channel and the Intracoastal Waterway (ICW) are approximately 0.5 miles to the east of the FPL property

. Prior to the development of the Port for its current activities (power generation, fuel storage and distribution, intermodal shipping, milit ary and homeland security and tourism), a majority of the Port Everglades property was submerged l ands and required extensive civil modifications to reach its current operating capacity

. The current design and capacity of the Port is under modification and has a number of civil activities planned to further redesign and retrofit the Port to accommodat e a greater number of ships and to increase the types/sizes of ships

. These activities include modifications of the existing piers and berths , addition of new piers and berths , as well as deepening of the ICW, inlet and turning basin . The Port is a major commercial shipping port located immediately west of the Port Everglades Inlet

. Cargo statistics for 2011 include a total of 4,183 ship visits, 5,787,961 tons of container cargo and 15,325,199 tons of petroleum products

. It is also a major passenger cru ise port, where 3,952,843 single and multi

- day passengers embarked in 2011 ( Broward County, 2011 )

. Operations and activities at the Port have the potential to impact organisms and influence environmental conditions encountered at PPE

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- 12.doc PPE is a series of f

our 1960s vintage oil and natural gas

- fired steam electric units consisting of two nominal 200 MW and two nominal 400 MW units (Units 1 through 4)

. Units 1 and 2 began operation in 1960 and 1961, respectively

. The commercial in

- service dates for Units 3 and 4 were 1964 and 1965, respectively

. All four units have remained in service since these dates

. Units 1 through 4 are authorized pursuant to Florida Department of Environmental Protection (FDEP) Final Title V Permit 0110036

- 009

- AV to operate on natura l gas, No

. 6 fuel oil, No

. 2 fuel oil, propane and, on specification, used oil from FPL operations

. The air emissions from each unit are exhausted through four separate approximately 343 foot (ft) tall stacks

. PPE currently has fueling infrastructure on FPL property (piping and storage) and on Port property through offsite linear facilities (piping and loading infrastructure)

. From 2000 through 2012, a total of 274 vessels made fuel deliveries to PPE under the currently reduced operational capacity

. Th is equates to the requirement of over 22 fuel barges per year entering and leaving the Port for the purposes of maintaining the necessary fuel for reliable operations.

PPE utilizes once

- through cooling water for condenser and auxiliary cooling. PPE withdr aws and discharges to the waters influenced by Port activities. The once

- through cooling water system is currently authorized to operate under FDEP Industrial Wastewater (IWW) Permit No

. FL0001538 and Broward County Permit IW

- 2010

- 0150

. FPL has submitted a substantial revision application to modify the IWW Permit for PEEC. The Broward County permit is being incorporated into the state license that will be issued by FDEP under the Power Plant Siting Act. The cooling water system has several components tha t allow for the withdrawal of marine water from Port Slip No. 3 and discharging that same water through the existing dischar ge canal into the ICW (Figure 2)

. Portions of the intake and discharge canals are located on Port property which limits accessibili ty

. Port Slip No

. 3 is connected to the Port Everglades Turning Basin

. The slip is dredged to approximately 38 ft and has bulkheads along three sides

. There is no submerged aquatic vegetation or emergent wetland habitat in the Port Everglades Turning Ba sin or Slip No

. 3

. These areas do not provide significant spawning sites, food production, nursery areas, or migratory pathways for aquatic organisms

.
At t he p oint where the intake withdraw s cooling water at Port Slip No

. 3 are four, 12 ft diameter, 2 44 ft long reinforced concrete pipes with centerlines seven ft below mean low water. The velocity at the point of withdrawal for PPE is approximately 4.4 feet per second (fps). The intake pipes are connected to a 2,100 ft canal that guides the water to t he existing intake structures. The intake canalNovember 2012 4 113

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- 12.doc average velocity is approximately 2.1 fps. The average velocity at the intake screens is approximately 2.9 fps.

The intake structure has se veral compo nents (Figure 3)

. The concrete structure s that separat e the cool ing water flow for each unit have four intake wells

. Within each intake well, vertical coarse bar racks allow water to flow into the cooling system but stop any large debris

. A series of rakes that move along the coarse bar racks are utilized t o remove the large debris

. Prior to activating the rakes to clean the racks, the intake wells and racks are visually inspected by PPE personnel for the presence of turtles. Beyond the bar racks, there are stop logs and sluice gates for access to the cent er portion of the intake well, and an automated traveling screen that collects and removes the smaller debris as the water passes through. These collection systems ensure that debris that could be potentially harmful to operations is removed from the coo ling water

. The authorized average flow for the existing units is 1,296 million gallons per day (MGD) and is split between intake wells that are dedicated to each of the existing units . PPE has operated at this location for over 45 years using a once - th rough cooling system. Once through the facility , the approximately 14 degree Fahrenheit warmer water enters the 4,850 ft long discharge canal that connects to the ICW

. Since the PPE thermal discharge existed on July 1, 1972, it is subject to the thermal surface water criteria established by FDEP Rule 62

- 302.520(1)

. Previous biological studies (Envirosphere 1987; Applied Biology Inc. , 1987) have found no adverse impact from the existing thermal discharge on fish, shellfish, or plankton from operation of U nits 1 through 4 , and the studies found no impact to benthos outside the discharge canal

. Within the discharge canal , the impacts were seasonal and temporary

. Where the discharge enters the ICW, the water is relatively deep and the channel is maintained by dredging. The shoreline is protected with bulkheads and armoring. Consequently, there is no significant submerged aquatic vegetation or wetlands along the western shoreline of the ICW, where the heated water enters the ICW. Also, this area does not p rovide significant spawning sites, food production, nursery areas or migratory pathways for aquatic organisms. Previous thermal discharge modeling showed that the heated water, as it enters the ICW, stratifies and remains at the surface. This reduces pot ential impacts to benthic communities and provides passage for fish and other aquatic organisms.

1.3 FPL’s Existing Environmental Programs

To enhance its commitment to sustainable operations, FPL adopts environmental policies and programs at the local level, w here it can monitor the impact of existing operations and the potential impact of future operations on wildlife

. FPL has an avian protection plan, manatee protection plans, aNovember 2012 5 113

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- 12.doc crocodile monitoring program, corporate endangered species management procedures and a scrub

- jay habitat vegetation management plan

. At this and other facilities, FPL has a demonstrated history of environmental stewardship that has supported the rehabilitation of injured sea turtles

. Sea turtles in various conditions of fitness have been observed in the PPE intake canal over the years

. The current intake monitoring procedure at the existing facility has been successful at minimizing impacts to sea turtles. The procedure requires that all intake wells are monitored four times in a 2 4 hour period for the presence of sea turtles. If a dead or injured turtle is found in the intake system, FPL notifies Florida Fish and Wildlife Conservation Commission (FWC) via the emergency hotline. Once FWC personnel or a member of the Sea Turtle Str anding and Salvage Network (STSSN) arrives at the site, the turtle is removed from the intake system. If FWC is unable to respond to the call, FPL waits for further direction from FWC. For each encounter, site personnel record the location, species, size , and condition of the sea turtle. During the years where FPL has a recorded history of sea turtle encounters (1990 to 2012) there were 29 documented turtles recovered from the intake canal. Twelve of those were determined to be dead prior to arrival in the intake system, with most being moderately to severely decomposed. Eight of the turtles recovered were found with pre

- existing injuries requiring rehabilitation. T hese injured turtles benefited from PPE’s operation because they were able to escape the Port area, be transport ed to a rehabilitation facility and get the veterinary attention they needed to improve their chance for survival

. Nine turtles were captured, evaluated and found to have no si gnificant injury or abnormality and were released back to the environment on the same day.



### 2.0 DESCRIPTION OF THE A CTION AND ACTION ARE A
This Section provides a description of the proposed action, P roject features that reduce or eliminate environmental impacts, key P roject components and their operation and P rojec t benefits

. The Action Area is also defined in this Section as PPE , its circulating water system, the receiving water body in fluenced by the plant discharge and the adjacent aquatic and shoreline habitats.

2.1 The Proposed Action The proposed action is the di smantlement of the four existing units at PPE and the construction and operation of the new PEEC , a nominal 1250 MW “3 on 1” combined cycle unit (Figure 4)

. The

e xisting infrastructure at PPE, including access roads, right s - of

- way for fueling infrastructu re, natural gas transportation to PPE , potable water supplies, phone and fiber infrastructure, access to the FPL transmission system and cooling

- water intake and discharge structures , will be utilized in theNovember 2012 6 113

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- 12.doc development of PEEC while min imizing environmen tal, land use and cost impacts

. There are no planned activities that will require shallow water dredging or may potentially impact mangroves.

Pre

- Dismantlement Phase: Prior to the dismantlement of PPE, FPL will install a Manatee Temporary Heating System. The system w ill include a 12 million BTU per hour heating system to continue to provide a manatee refuge by discharging warm water

. The manatee refuge will be located within the existing cooling water discharge canal

. Dismantlement and Construction Phases : During the dismantlement of the existing units there will be a number of activities at the PEEC site and the surrounding FPL property to prepare for construction and eventually commercial operation

. These activities include the removal of the existing p ower block and associated facilities (tanks, piping, support buildings, etc .). During the dismantlement and the majority of the construction phase, the existing withdrawal of cooling water system will not be operational. The condenser cooling water will begin testing and commissioning in the fourth quarter of 2015. Plant Operational Phase: Primary water uses at the new PEEC will be for cooling water and process makeup water

. Cooling water is required for condenser cooling and auxiliary equipment cooling

. Condenser cooling for PEEC will be accomplished using the existing infrastructure of the Units 3 and 4 once

- through cooling system intake and discharge structures which withdraw from Port Slip No. 3 and discharge through a canal connected to the ICW. T he average flow for PEEC will be 635 MGD once the plant is fully commissioned and in operation , while the flow for the existing units is authorized for 1,296 MGD

. Because the design intake flow for PEEC will be approximately one

- half of PPE’s intake flow, the existing intake infrastructure can be used for PEEC with lower cooling water requirements

. Therefore, the point of intake velocity and the intake canal flow velocity will be approximately 51 percent lower at the 635 MGD flow rate

. The velocity at th e culverts will be approximately 2.17 fps and the average velocity within the intake canal is approximately 1.0 fps

. The velocity at the intake screen is unchanged at approximately 2.9 fps. The flow reduction will decrease potential impingement and entr ainment of small fish, shellfish and larvae by approximately 50 percent. To further mitigate possible effects of the PEEC cooling water withdrawals, FPL will install state

- of

- the

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- 12.doc in the existing Unit 3 and 4 intake structures to minimize small fish and shellfish impingement mortality

. The traveling screens will incorporate protective measures including modified Ristroph

type screens with collection buckets (or equivalent) designed to minimize tu rbulence to small aquatic organisms and a guard rail or barrier to prevent loss of aquatic organisms from the collection bucket

. The screen panels will use smooth woven mesh (or equivalent) to prevent abrasion of the aquatic organisms

. The screen wash will use a dual spray system (or equivalent) with a low pressure wash to remove organisms prior to a high pressure wash to remove trash

. The aquatic organism return system will return the organisms to the source water in a manner that min imizes predation or re

impingement. The temperature rise across the PEEC condensers will be approximately the same as the current plant operations

. However, PEEC will decrease the thermal loading to the aquatic environment by approximately 50 percent, due to reduced heat rejection and cooling water flows

. Therefore, the size of the thermal discharge in the ICW will be significantly reduced

. The cooling water discharge canal lies within an area designated as essential habitat for the Florida manatee

. Man atees are known to use the area around PPE as a thermal refuge

. PEEC will continue to provide a thermal refuge for manatees pursuant to the facility’s Manatee Protection Plan that is incorporated by reference in the IWW Permit No

. FL0001538

. FPL has sub mitted a substantial revision application to modify the current permit to authorize PEEC operations

. The revised permit is anticipated to be issued in 2013.

PEEC will use clean fuel sources such as natural gas as the primary fuel with ultra

- low sulfur dis tillate (ULSD) oil used as the backup fuel . Natural gas will be transported to PEEC via an existing natural gas pipeline. New infrastructure will be built to accommodate ULSD storage, delivery and unloading from Port unloading facilities. During normal operations, i t is anticipated that an average of less than one ship per year will be sufficient to maintain the necessary levels of ULSD for reliable and continuous service . This is a significant reduction from the 22 plus ships per year necessary under c urrent operations. D uring emergency situations such as periods of disrupted natural gas supply additional ships may be required. The reduction in shipping traffic will further reduce the environmental impacts of electrical generation at this Plant by dec reasing the potential for spills, propeller strikes and other potentially harmful effects of shipping traffic on local and regional species

. The operation of PEEC will result in reduced air emissions

. The use of clean fuels (natural gas and ULSD), combust ion controls and air pollution control equipment will minimize air emissions and ensure compliance with applicable emission limiting standards

. Using clean fuels will minimize emissions of sulfur dioxide (SO 2 ), particulate matter (PM), particulate matter with an aerodynamic particle size of 10 μm or less (PM 10 ), and other fuel

- bound contaminants

. Nitrogen oxide s (NO x )November 2012 8 113

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- 12.doc emissions will be reduced by approximately 3900 tons per year (an 85 percent reduction), SO 2 emissions will be reduced by approximately 900 0 tons per year (a 95 percent reduction), and particulate emissions (PM and PM 10 ) will be reduced by approximately 350 tons per year (a 50 percent reduction)

. Due to increased generation capacity and utilization, greenhouse gas emissions at PEEC will incr ease despite a carbon dioxide (CO 2 ) emissions rate that is approximately 50 percent lower than the existing Units 1 through 4 . However, with power from PEEC replacing power generated from other less efficient plants, total greenhouse gas emissions (primar ily CO 2 ) for the FPL generating system are expected to decrease by approximately 22 million tons over the life of the Project (FPL, 2012).

2.2 The Action Area For the purposes of this assessment, the “Action Area” (Figure 5) includes the upland area of PPE whe re dismantlement and construction will occur, the once

- through cooling water system (intake and discharge canals and structures) and the areas of the Port and ICW adjacent to the intake and discharge canal terminal

. Under current operating characteristics , that includes an area from just south of the discharge canal at approximately 26.07784 degrees north latitude and 80.11513 degrees west longitude north to a point in the ICW just south of the turning basin near the Coast Guard Station at approximately 26 .08855 degrees north latitude and 80.11432 degrees west longitude (Envirosphere , 1987; Applied Biology Inc. , 1987)

. The Action Area includes this area of direct influence and also the adjacent aquatic habitats that may experience indirect impacts and is h ere defined as PPE and the adjacent waterways and shoreline habitats between the Port Everglades Turning Basin entrance channel midline south to a point approximately 370 meters south of the mouth of the discharge canal (Figure 5 )

. The Action Area boundar ies are defined conservatively, as they include areas well outside the area of direct influence of PPE operations even under the current operating conditions, and the area of direct influence of the PEEC will be considerably smaller due to the reduced cool ing water volume requirements and lower thermal loading to the aquatic environment

. The corner coordinates for the portions of the Port and the ICW included in the Action Area are:

Northwest Corner: 26.09352° North and 80.12384° West

Northeast Corner: 26 .09360° North and 80.11240° West Southwest Corner: 26.07514° North and 80.11551° West Southeast Corner: 26.07518° North and 80.11352° West Terrestrial and aquatic habitats within the Action Area are briefly described below, following the Florida Land Use, Cover and Forms Cl assification System (FLUCFCS ) (FDOT, 1999)

. The majorityNovember 2012 9 113

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- 12.doc of the upland land use in the Action Area is comprised of facilities related to electric power generation at PPE (FLUCFCS Code 831)

. The existing electric power facilities do no t include areas of significant natural vegetative habitats

. Within the existing PPE property boundary there is an area of open land on the northern side of the cooling water discharge canal (FLUCFCS Code 190)

. This area is generally a mowed and maintaine d lawn with a small number of cabbage palm ( Sabal palmetto )

. The ground cover is a mix of grasses and ruderal species. The cooling

- water intake (north side) and discharge (south side) canals are upland cut ditches (FLUCFCS Code 512)

. The banks of the can als are overgrown primarily with Brazilian pepper ( Schinus terebinthifolius ) and Australian pine ( Casuarina equisetifolia ) with scattered Mexican fireplant ( Poinsettia heterophylla ), painted leaf ( Poinsettia cyathophora ), Durban crowfoot grass ( Dactylocten ium aegyptium ), Virginia creeper ( Parthenocissus quinquefolia ) and prickly pear cactus ( Opuntia humifusa )

. Natural terrestrial vegetative communities are scarce within the urban environment surrounding the PPE p roperty

. Areas of mangrove wetlands and are as dominated by melaleuca ( Melaleuca quinquenervia 

### ) and Australian pine occur in the Action Area, in particular on the tract south of the discharge canal and at John U

. Lloyd State Recreation Area on the eastern shore of the ICW across from PPE.
The on ly aquatic env ironments that occur within PEEC are the cooling

- water intake and discharge canals (FLUCFCS Code 512)

. Previous studies have found sparse seagrass coverage with low density of coverage, within the canals

. No listed seagrasses were identifie d in the canals. Aquatic environments within the Action Area adjacent to the PEEC p roperty include the ICW and the Port slips and turning basin (FLUCFCS Code 512)

. The entire area of the ICW and turning basin contained within the Action Area have been dr edged to depths greater than ten meters to accommodate deep draft

. However, studies conducted for the U.S

. Army Corps of Engineers (USACE) in support of the Port Everglades E xpansion Project have documented Halophila johnsonii and other non

- listed seagra sses ( Halophila decipiens , Halodule wrightii and Syringodium filiforme ) within the Action Area (DC&A , 2009)

. Biological studies conducted in the area have reported a very depauperate benthic fauna, attributed to the deep dredging and to impacts from the a djacent industrial uses (Applied Biology, 1987)

. As previously noted in Section 1.2 above, due to the proximity of PEEC to Port Everglades, operations and activities at the Port will have the potential to impact organisms and influence environmental condi tions encountered at PEEC

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- 12.doc 2.3 Project Benefits

PEEC is strategically located to serve FPL’s customers in an area of concentrated demand

. Locating generation sources as close to the load as possible reduces the reliance upon the transmission system and also reduces overall costs of service . PEEC has multiple advantages including (1) reuse of an existing developed site with adequate land size and zoning, (2) access to existing fuel transportation infrastructure (gas pipeline), (3) e xisting transmission facil ities and (4) excellent access to water supply and transportation

. Since the existing Units 1 through 4 are older and less efficient; they are used less often and the system relies on imported power via the transmission system

. The Project will add base load generation close to the load and thereby reduce the need for new transmission investments projected to cost hundreds of millions of dollars in the next decade

. FPL estimates that the proposed Project will create 650 direct construction jobs at its pe ak and provide more than $20 million in new tax revenue to local governments and school districts

. The Project will also result in significant environmental benefits compared to the existing Units 1 through 4

. In addition, the use o f the existing site, f

acilities and committed resources such as water, should not result in additional land use impacts such as impact s on wetlands associated with locating new gas pipelines or transmission facilities

. Thus, the Project will provide benefits beyond the provisi on of electric service. The Project will provide needed reliable base load capacity near FPL’s load center to improve the power generation efficiency at PEEC by approximately 35 percent

. PEEC will improve several other existing conditions such as the disc harge water quality , reduction of both the volume of cooling water flow and the therma l loading into the local waters, local air quality by reducing system

- wide greenhouse gas emissions by 22 million to ns over the life of the Project and providing economic stimulus locally and nationally through direc t and indirect job creation, material procurement and increased tax basis

. The above benefits will be achieved with no need for additional linear facilities like transmission lines, natural gas transmission, f uel piping or water transmission

. In addition, the Project will result in more than $400 million in savings c ompared to the continued operation of the existing units and over $800 million in savings o ver the construction of a green field site of the same

c apacity or any other options identified

. The Project will also provide economic and environmental benefits derived from greater fuel efficiency of the new unit, reduced emissions, lower ope rating and maintenance expenses and enhanced unit availability.

Be cause of the long list of benefits derived from PEEC, especially the economic benefits to FPL customers, the Florida Public Service Commission and FPL have identified th e P roject to be the most prudent strategy for meeting its customer’s future energy requ irements

. The decision is also based upon FPL’s assumption that because of these benefits, permitting PEEC could be achieved in a timelyNovember 2012 11 113

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- 12.doc and efficient manner

. Without certainty of receiving these permits , PEEC will not be pursued and the continued operat ion of PPE will be the next best alternative to meet FPL customers’ demands

. 

### 3.0 LISTED SPECIES AND C RITICAL HABITAT IN T HE ACTION AREA
A current listing of threatened and endangered species in the South Atlantic area under the jurisdiction of the National M arine Fisheries Service is found in Table 1. The loggerhead, green, hawksbill, Kemp's Ridley and leatherback sea turtles, the smalltooth sawfish and Johnson's seagrass are discussed in detail below and other species are discussed briefly in Section 3. 8

. 3.1 L oggerhead Sea Turtle ( Caretta caretta )

3.1.1 General Information The loggerhead sea turtle has been federally listed as a threatened species since 1978

. Loggerheads are circumglobal in distribution in tropical and temperate waters

. The southeast U.S

. coast, an d particularly Florida, is considered to be the most important rookery in the western he misphere for loggerheads (NMFS & USFWS , 2008)

. Recent studies have revealed three genetically distinct nesting populations in the southeast U.S.: the northern nesting population (North Carolina to Cape Canaveral), the South Florida population (Ca pe Canaveral to Collier County) and the Florida Panhandle population (Franklin to Escambia Counties, Florida) (Bowen et al. , 1993)

. Trends in Florida nesting were assessed by Witherington et al

. (2009), who analyzed loggerhead nesting for thirty nesting beach sites in Florida included in the Florida Index Nesting Beach Survey (INBS) program . This assessment concluded that following a 24 percent increase in nesting between 198 9 through 1998, loggerhead nesting declined 16 percent from 1999 through 2007

. An examination of INBS loggerhead nesting data through the 2011 nesting season shows an overall 3.6 percent increase in loggerhead nesting over the entire period from 1989 thro ugh 2011, a figure that does not dif fer significantly from zero ( Witherington, 2012 ). Loggerheads nest in the southeast U.S

. from April through September, with the peak nesting in June and July (NMFS and USFWS , 1991a)

. The nesting process is remar kably st ereotyped and is described in Bustard et al

. (1975)

. Hatch lings emerge primarily at night and swim offshore in a “frenzy” until they arrive at offshore weed and debris lines (Carr , 1986) (Wyneken & Salmon , 1992)

. Post hatchling turtles from the Florida c oast enter the currents of the North Atlantic Gyre, eventually returning to the western Atlantic coastal waters (Bowen et al. , 1993).November 2012 12 113

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- 12.doc When loggerheads reach a carapace length of approximately 40 to 60 centimeters (cm), they leave the pelagic environment an d move into various nearshore habitats (Carr , 1986)

. In the U.S. , developmental habitats for loggerheads are found from Texas to Nova Scotia (Turtle Expert Working Group , 1998)

. As they approach adult size of about 83 cm carapace length (Ehrhart et al. , 1996), loggerheads leave the developmental habitats

. Adult loggerhead foraging grounds for the South Florida nesting population are found in the Cari bbean basin, the Gulf of Mexico and along the eastern seaboard of the U.S

. (Meylan et al. , 1983)

. Abundan ces of adult loggerheads in Florida coastal waters are much lower in months outside of the nesting season (Magnuson et al. , 1990).

3.1.2 Plant Specific Information A review of research projects on in

- water sea turtle populations in Florida (Eaton et al. , 2008)

r evealed no current or historical surveys on sea turtle populations in the inshore waters of Broward County that include the Action Area

. There have been two in

- water research projects on nearshore and offshore reef habitats in oceanic waters adjacent to a nd connected to the inshore waters of the Action Area . Makowski et al. (2005) conducted towed diver surveys in the immediate nearshore area along a 30 kilometer (km) strip roughly centered on the Port entrance channel to evaluate sea turtle abundance as a part of environmental monitoring for beach restoration projects. These surveys sighted 370 green turtles (presumably mostly juveniles, although life stage was not reported) and no sea turtles of any other species.

In the same area but somewhat farther of fshore, conducted between 1986 and 1991, Wershoven and Wershoven (1992) conducted aerial surveys and scuba diving hand capture efforts. Although the research was focused on green turtles, the authors did include 14 observations of loggerhead turtles

over nearshore reef habitat. The best data source on sea turtle presence available for the inshore waters of Broward County that include the Action Area is the database of sea turtle strandings maintained by the STSSN. A review of that database for Broward Cou nty inshore waters for the ten

- year period from 2002 through 2011 conducted by Dr. Allen Foley of the Florida Fish and Wildlife Conservation Commission revealed loggerhead turtles to be the dominant species found stranded in Broward County inshore waters, w ith 26 loggerheads recorded out of a total of 4 2 strandings for the ten

- year period. Of the turtles for which carapace length data are available, most (12 out of 15) were subadults with a carapace length less than 85 cm. Curved carapace lengths of strand ed loggerheads ranged from 64 to 101 cm, with a mean of 76 cm. The greatest number of strandings occurred in October throughNovember 2012 13 113

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- 12.doc December (38 percent) and April through July (35 percent), with lesser numbers occurring in July through September (15 percent) an d January through March (11 percent).

FPL records for sea turtles encountered at PPE over the same ten

- year period from 2002 through 201 1 indicate that 12 loggerhead turtles have been recorded within the intake system.

3.2 Green Sea Turtle ( Chelonia mydas )

3.2.1 Gen eral Information The green turtle was listed under the ESA in 1978 and the Florida nesting population is currently listed as endangered

. Green turtles are found worldwide in tropical and subtropical waters

. Major green turtle rookeries in the Western Hem isphere occur on South Atlantic islands and the Caribbean basin

. Most continental U.S

. nesting of the green turtle takes place on the Florida East Coast south of Cape Canaveral (NMFS & USFWS , 1991)

. Green turtles show a similar life history pattern as lo ggerheads, but they leave the pelagic phase and enter developmental habitats at a considerably smaller size, about 20 to 25 cm carapace length (Magnuson et al. , 1990)

. Typical developmental habitats are shallow, protected waters where seagrasses are preva lent (Carr et al. , 1978), but small green turtles are also commonly found in reef environments where attached algae are present (Ehrhart et al. , 1996; Coyne , 1994)

. It has been suggested that green turtles in foraging habitats may tend to specialize in ei ther algae or seagrass forage, as individual turtles with intestinal microbial flora adapted to aid in seagrass digestion woul d digest algae less efficiently and vice versa (Bjorndal , 1985). Green turtles nesting in Florida have a minimum size of 83 cm car apace length, but they appear to leave Florida developmental habitats by about 60 to 65 cm carapace length (Witherington & Ehrhart , 1989), perhaps migrating to the southeastern Caribbean

. The majority of green turtle nesting in Flor ida takes place in July , August and early September, and green turtle nesting is concentrated in southeast and east central Florida

. A review of the INBS nesting data for green turtles in Florida over the period from 1989 through 2011 shows a marked and steady increase in nesti ng
. Ther e has been an approximately ten

- fold increase in green turtle nesting on Florida Index beaches from 1989 through 2011, and the 2011 nesting total was highest on record ( Witherington, 2012 ).

3.2.2 Plant Specific Information A review of research projects on in

- water sea turtle populations in Florida (Eaton et al. , 2008) revealed no current or historical surveys on sea turtle populations in the inshore waters of Broward County that include the Action Area

. There have been two in

- water research projects on nearshoreNovember 2012 14 113

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- 12.doc and offshore reef habitats in oceanic waters adjacent to and connected to the inshore waters of the Action Area . Makowski et al. (2005) conducted towed diver surveys in the immediate nearshore area along a 30 km strip roughly centered on the Po rt entrance channel to evaluate sea turtle abundance as a part of environmental monitoring for beach restoration projects

. These surveys sighted 370 green turtles (presumably mostly juveniles, although life stage was not reported) and no sea turtles of an y other species.
In the same area but somewhat farther offshore, between 1986 and 1991 Wershoven and Wershoven (1992) conducted aerial surveys and scuba diving hand capture efforts. In this study, 187 green turtles were captured. All individuals were ner itic stage juveniles, with curved carapace lengths ranging from 27 to 67 cm, with a mean curved carapace length of 43 cm. Seasonal abundance differences were noted in the study, with the greatest number of captures occurring in April, May, June and August and the lowest number of captures in September and December. A review of the STSSN database for Broward County inshore waters for the ten

- year period from 2002 through 2011 conducted by Dr. Allen Foley of the FWC revealed 16 green turtle strandings for th e ten

- year period. All stranded green turtles were juveniles. Curved carapace lengths of stranded green turtles ranged from 29 to 46 cm, with a mean of 38 cm. A majority of the strandings (11 out of 16) occurred in the months of October through March.

F PL records for sea turtles encountered at PPE over the same ten

- year period from 2002 through 2011indicate that three green turtles have been recorded within the intake system.

3.3 Leatherback Sea Turtle ( Dermochelys coriacea )

3.3.1 General Information
The leatherba ck sea turtle was federally listed as endangered in 1970

. Leatherbacks are found worldwide in pelagic waters from the tropics to near the Arctic and Antarctic Circles

. Nesting primarily occurs on the Pacific coast of Mexico and the Caribbean coast of Sou th America, with some continental U

. S

. nesting in Florida

. During the period from 1979 through 1992, over 90 percent of Florida leatherback nesting occurred in St. Lucie, Martin and Palm Beach counties (Meylan et al. , 1995)

. An analysis of Florida INBS d ata indicates a statistically significant increase in Florida leatherback nesting over the period from 1989 through 1998 (Witherington & Koppel , 2000)

. That increase has continued for the period from 1998 through 2011.November 2012 15 113

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- 12.doc 3.3.2 Plant Specific Information
With the exception of nesting females, leatherback turtles occur almost exclusively in offshore waters

. None of the nearshore in

- water studies conducted in the waters of Broward County documented any leatherback turtles

. The STSSN stranding database contains no r ecords of leatherback turtle strandings in inshore Broward County waters in the last ten years, and FPL records do not contain any encounters with leatherback turtles in the intake system over the same period (2002 through 2011). The presence of leatherba ck turtles in the Action Area is considered extremely unlikely.

3.4 Hawksbill Sea Turtle ( Eretmochelys imbricata )

3.4.1 General Information
The hawksbill turtle was listed as en dangered in 1970 and critical habitat has been established at the islands of Mona and Mon ita in Puerto Rico (NMFS & USFWS , 1993)

. Hawksbills are the rarest of the five species of marine turtles found in Florida waters (Meylan & Redlow , 2006)

. Hawksbill turtles are known to occur in appropriate habitats in Florida (generally in association wi th coral reef environments), although much of the information available on their distribution has been inferred from stranding and incidental capture data (Meylan & Redlow , 2006)

. Early reports mention southeast Florida and the Florida Keys as having both the greatest abundance of hawksbills in the state an d appropriate hawksbill habitat (DeSola , 1935; Carr , 1940)

. It is assumed that nesting beaches in the Caribbean Basin are the recruitment source for hawksbills in these developmental habitats

. Nesting in Florida by hawksbill turtles is extremely rare

. Major nesting beaches for hawksbill turtles in the Caribbean and western Atlantic include a large nesting aggregation in the Yucatan Peninsula and smaller mainland nesting beach aggregations in Panama an d Nicaragua, as well as island beaches in Puerto Rico and the U

. S . Virgin Islands, Cuba and Barbados (Meylan & Redlow , 2006).

3.4.2 Plant Specific Information
There have been two in

- water research projects involving hawksbill turtles in the nearshore ocean water s of Broward County that are adjacent to and connected to the Action Area. The green turtle project conducted by Wershoven and Wershoven (1992) cited in Section 3.2.2 above documented and captured three hawksbill turtles on the Broward County nearshore re ef. The turtles ranged between 34 to 60 cm curved carapace lengths. A similar but more extensive project is being conducted by Larry Wood with the Palm Beach Zoo on the offshore reef tract in Palm Beach County. This work has morphometric data from 138 i ndividuals and shows a size class distribution with a mean straight carapace length (SCL) of 56 cm and a peak in the 51 to 60 cm SCL size class. There are noNovember 2012 16 113

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- 12.doc observations of turtles with an SCL of less than 40 cm (Wood et al., in press). The STSSN databa se for the inshore waters of Broward County that includes the Action Area for the period from 2002 through 2011 has no records of hawksbill strandings.

FPL records for sea turtles encountered at PPE over the same ten

- year period from 2002 through 2011 indi cate that no hawksbill turtles have been recorded within the intake system.

3.5 Kemp's Ridley Sea Turtle ( Lepidochelys kempii )

3.5.1 General Information Kemp's Ridley turtles inhabit sheltered coastal areas and frequent larger estuaries, bays, and lagoon s in the tem

perate, subtropical and tropical waters of the northwestern Atlantic Ocean and Gulf of Mexico (Mager , 1985)

. The foraging range of adult Kemp's Ridley turtles appears to be restricted to the Gulf of Mexico

. However, juveniles and subadults occur througho ut the warm coastal waters of the U.S

. Atlantic coast (Hopkins & Richardson , 1984; Pritchard & Marquez , 1973)

. Juveniles and subadults travel northward with vernal warming to feed in the productive coastal waters of Georgia through New England, but return southward with the onset of winter to escape the cold (Henwood & Ogren , 1987; Lutcavage & Musick , 1985; Ogren , 1989). Nesting of Kemp's Ridleys is mainly restricted to a stretch of beach near Rancho Nuevo, Tamaulipas, Mexico (Pritchard & Marquez , 1973; Ho pkins & Richardson , 1984)

. An estimated 40,000 females nested on a single day in 1947, but between 1978 and 1990 there were less than 1000 nests per

season
. More recently, nesting levels at the key Mexican beaches have recovered significantly, with

over 20,000 nests recorded at Rancho Nuevo in 2009 (NMFS, USFWS, & SEMARNAT , 2010)

. Occasional nesting has also historically occurred at Padre Island, Texas and Veracruz, Mexico (Mager , 1985; Turtle Expert Working Group , 2000)

. Kemp's Ridley nesting in Texas has also increased significantly in recent years (NMFS, USFWS, & SEMARNAT , 2010). Population estimates of immature Kemp's Ridleys are difficult to develop

. Increases have been noted in the number of juvenile captures during the late 1980s and early 1990s in long

- term tagging studies in the northeast Gulf of Mexico (Ogren, unpublished data)

. If this increase is indicative of an overall increase in the juvenile population, more recruitment into the adult population should occur in the future (NMFS & FWS , 19 92). An analysis of the size of stranded Kemp's Ridleys indicated that many more large immature individuals were stranded during the 1990s relative to the 1980s (Turtle Expert Working Group ,November 2012 17 113

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. These results also suggest that juvenile mortality has de creased and that the population is increasing

. Despite these improvements, the data suggest that this population remains at critically low levels

. This species was listed as endangered in 1970 and is considered the most endangered of all sea turtles (NMF S & FWS , 1992; Burke et al. , 1994).

3.5.2 Plant Specific Information
A review of active and inactive in

- water sea turtle research projects in Florida (Eaton et al. , 2008) found no Kemp's Ridley turtles captured or sighted in any project closer to the Action Area than Florida Bay in Everglades National Park

. The STSSN database for the inshore waters of Broward County that includes the Action Area for the period from 2002 through 2011 has no records of Kemp's Ridley strandings. FPL records do not contain any enco unters with Kemp's Ridley turtles in the cooling water intake system over the same ten

- year period. The presence of Kemp's Ridley turtles in the Action Area is considered possible but unlikely.

3.6 Smalltooth Sawfish ( Pristis pectinata )

3.6.1 General Information
In the U.S. , smalltooth sawfish are generally a shallow water fish of inshore bars, mangrove edges and seagrass beds, but are occasionally found in deeper coastal waters The smalltooth sawfish was said to be commonly found in shallow water throughout the nor thern Gulf of Mexico, especially near river mouths and in large bays and was common in peninsular Florida (Walls, 1975)

. Historical records indicate that smalltooth sawfish have been found in the lower reaches of the Mississippi and St

. Johns Rivers and t he Indian River Lagoon system

. Individuals have also historically been reported to migrate northward along the Atlantic seaboard in the warmer months

. Estimating from the latitudinal limits within which they are year

- round residents and from the summer

- w inter temperatures of the Carolinian waters that they visit during the warmer half of the year, the lower thermal limit to their normal range is probably about 16 to 18 o Celsius

. Over the past century the population has been reduced by fishing and habitat alteration and degradation, and currently smalltooth sawfish are primarily found in southern Florida in the Everglades and Florida Keys (NMFS , 2006). The smalltooth sawfish has been extirpated from much of its former range in Florida

. The U.S

. region tha t has always harbored the largest numbers of smalltooth sawfish lies in south and southwest Florida from Charlotte Harbor through the Dry Tortugas

. There has been a continuous and frequent record of occurrences of sawfish in the Everglades since the first report in 1834 and the vicinity nowNovember 2012 18 113

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- 12.doc serves as the last U.S

. stronghold for the species

. Long

- term abundance data are not available, but there are recent (1989 through 1999) recreational catch per unit effort (CPUE) data for the Everglades (NMFS , 2006)

. This species typically inhabits shallow waters, but may occur in deeper waters of the continental shelf, and shallow waters are important nursery habitat for this species (NMFS , 2006)

. No critical habitat for the Smalltooth sawfish has been designated wit hin the Action Area or adjacent waters. It was federally listed as endangered in 2003.

3.6.2 Plant Specific Information A summary of sawfish records (NMFS , 2000) contains one record of a sawfish (not positively identified as a smalltooth sawfish, listed only as Pectinata sp .) from Broward County waters in September of 1998

. A more recent publication (Simpendorfer & Wiley , 2006) contains a figure showing smalltooth sawfish sightings in the Broward area in 2006, but specific location information was not provid ed. A search of the National Sawfish Encounter Database revealed a number of recent encounters in Broward County (Figure 6) including two encounters in the Action Area in 2006 and 2008 (Norton, 2012). There have not been any recorded sawfish encounters in t he PPE intake system.

3.7 Johnson’s Seagrass ( Halophila johnsonii )

3.7.1 General Information Halophilia johnsonii (Johnson’s seagrass) was listed as a threatened species by NMFS on September 14, 1998 (Federal Register Volume 63, p

. 49035) and the final rule for crit ical habitat designation for H

. johnsonii was published April 5, 2000 (Federal Register, Vol . 65, p
. 66)

. H

. johnsonii has one of the most limited geographic ranges of all seagrass species

. It is known to occur only from 21.5 km north of Sebastian Inle t (near Palm Bay in Brevard County) south to northern Biscayne Bay (near North Miami) on the east coast of Florida (Kenworthy , 1997; Virnstein & Hall , 2009)

. Johnson’s seagrass is thought to support fisheries as habitat and foraging grounds for fish and i nvertebrates

.
3.7.2 Plant Specific Information A review of current information on Johnson’s seagrass distribution in the Action Area revealed a number of studies c onducted from the 1990s to 2009 for USACE in support of the Port expansion project (DC&A , 2000, 2001, 2006, 2009)

. Since 1999, Johnson's seagrass has been documented in the Action Area and adjacent waters

. Johnson's seagrass in the area occurs in single and mixed beds with its congener, H

. decipiens

. Johnson's seagrass is generally found in sha l low water, less than one meter , but does occur in water up to three m eters in the Action Area

. Johnson's seagrass distribution as of 2009 is shown in Figure 7.November 2012 19 113

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- 12.doc 3.8 Other Listed Species Other listed species under the jurisdiction of NMFS listed in Table 1 are either not found in habitats included in the Action Area or do not have the potential to be affected by the proposed action and so will not be discussed in detail.



### 4.0 ENVIRONMENTAL BASELI NE CONDITIONS

This section discusses human

- induced impacts other t han the proposed action in the Action Area to the listed species discussed in Section 3 above

. Since the Action Area does not include any nesting habitat for the species in question, impacts to nesting beaches such as artificial lighting and beach restora tion are not included in the discussion

. Information specific to the Action Area and the surrounding Broward County inshore waters from the STSSN was provided by Dr. Allen Foley of FWC and will be discussed for each species below.

4.1 Loggerhead Sea Turtle ( C aretta caretta ) The loggerhead turtle recovery plan (NMFS & USFWS , 2008) lists the following threats to loggerhead turtles that may potentially occur in the Action Area:


### Vessel strikes Marine debris entanglement Hook and line fisheries Oil pollution and ch emical pollution Dredging Marina an d dock development Given its setting in the highly urbanized and heavily utilized inshore waterway of Broward County, vessel strikes can reasonably be expected to be a significant threat in the Action Area . The recovery plan (NMFS & USFWS, 2008) notes that vessel strike injuries are particularly prevalent in the Southeast Florida region from Palm Beach through Dade Counties, and 60 percent of all loggerhead strandings in this region show signs of vessel strike injury. A review of STSSN records for inshore strandings in Broward County from 2002 through 2011 show eight out of 23 loggerhead strandings (35 percent) had codes or comments indicating a vessel strike injury. Entanglement in marine debris and hook and line fishi ng gear may also reasonably be expected to be significant in such a heavily used marine area. A review of STSSN records for inshore strandings inNovember 2012 20 113

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- 12.doc Broward County from 2002 through 2011 show three out of 23 loggerhead strandings (13 percent) had codes or co mments indicating entanglement in debris or fishing gear. The area including and surrounding the Action Area has a very high potential for impacts from oil and chemical pollution, as the Port is a major shipping hub , and has significant commerce in petrol eum, with over 128 million barrels transshipped through the Port in 2005, including h eavy fuel oil, diesel, gasoline and jet fuel (Broward County , 2011 ). A review of STSSN records for inshore strandings in Broward County from 2002 through 2011 show one ou t of 23 loggerhead strandings (four percent) had codes or comments indicating oil or tar impacts. Dredging activities occur periodically in the Action Area to maintain suitable navigational depths. Hopper dredges have historically been used for this act ivity, which do have the potential to cause sea turtle mortalities. In the Environmental Assessment for the Port maintenance dredging in 2005, USACE concluded that: "the project may adversely affect sea turtles below mean high water if a hopper dredge is used" (USACE, 2005). A search of the USACE Sea Turtle Data Warehouse (USACE, 2005b) revealed no takes of loggerhead turtles were recorded for the 2005 maintenance dredging. Dredging, along with marina and dock development, may also affect turtles less di rectly by degrading habitat quality. The Action Area is currently very intensively developed and the potential for new dock and marina development in the Action Area appears to be very slight, given that the only remaining areas of natural shoreline and s hallow water habitat are protected within the boundaries of the John U. Lloyd State Recreation Area. The Action Area includes a portion of the Port facility. The Port Everglades Master Plan document (Broward County, 2012) outlines plans for expansion and continued development of the Port facilities in conjunction with the Federal channel deepening and widening project currently under review.

4.2 Green Sea Turtle ( Chelonia mydas ) The green turtle recovery plan (NMFS & USFWS , 1991) lists the following threats t o green turtles that may potentially occur in the Action Area:


### Vessel strikes Marine debris entanglement Hook and line fisheries Oil and gas exploration, development and transportation Dredging Marina and dock development Seag rass degradationNovember 2012 21 113

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- 12.doc Given its se tting in the highly urbanized and heavily utilized inshore waterway of Broward County, vessel strikes can reasonably be expected to be a significant threat in the Action Area. The recovery plan (NMFS & USFWS, 1991) states that from 1986 through 1988 an av erage of 7.4 percent of U.S. waters strandings showed injuries consistent with vessel strikes, and that these types of injury were more common in areas of intense vessel traffic, including South Florida. A review of STSSN records for inshore strandings in Broward County from 2002 through 2011 show three out of 11 green turtle strandings (27 percent) had codes or comments indicating a vessel strike injury. Entanglement in marine debris and hook and line fishing gear may also reasonably be expected to be si gnificant in such a heavily used marine area. A review of STSSN records for inshore strandings in Broward County from 2002 through 2011 show two out of 11 green turtle strandings (18 percent) had codes or comments indicating entanglement or other injuries from recreational fishing gear. The area including and surrounding the Action Area has a very high potential for impacts from oil and chemical pollution, as Port Everglades is a major shipping port and has significant commerce in petroleum, with over 128 million barrels transshipped through the Port in 2005, including heavy fuel oil, diesel, gasoline and jet fuel (Broward County, 2012). There are no records in the recent STSSN data for inshore Broward County waters indicating oil or tar impacts to green turtles. Dredging activities occur periodically in the Action Area to maintain suitable navigational depths. Hopper dredges have historically been used for this activity, which do have the potential to cause sea turtle mortalities. In the Environmental Assessment for the Port maintenance dredging in 2005, the U.S. Army Corps of Engineers (USACE) concluded that: "the project may adversely a ffect sea turtles below mean high water if a hopper dredge is used" (USACE , 2005)

. A search of the USACE Sea Turtle Data Warehouse (USACE, 2005b) revealed no takes of green turtles were recorded for the 2005 maintenance dredging. Dredging, along with marina and dock development, may also affect turtles less directly by degrading habitat quality. The Action Area is cur rently very intensively developed, and the potential for new dock and marina development in the Action Area appears to be very slight, given that the only remaining areas of natural shoreline and shallow water habitat are protected within the boundaries of the John U. Lloyd State Recreation Area. Of particular concern for green turtles is the loss of shallow seagrass and other submerged aquatic vegetation resulting from dredging and dock and marina development. The majority of the Action Area is currently dredged to a depth of at least ten meters, except for shoreline vegetation and shallow water habitats within John U

. Lloyd State Recreation Area, and there is thus little potential for further degradation of green turtle foraging habitat in the Action Ar ea
. The Action Area includes a portion of the Port facility

. The Port Everglades Master Plan document (Broward C ounty, 2012) outlines plans for expansion andNovember 2012 22 113

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- 12.doc continued development of the Port facilities in conjunction with the Federal channel deepening a nd widening project currently under review.

4.3 Leatherback Sea Turtle ( Dermochelys coriacea ) The leatherback turtle recovery plan (NMFS & USFWS , 1992) lists the following threats to leatherback turtles that may potentially occur in the Action Area:


### Vessel str ikes Marine debris entanglement and ingestion Oil and gas exploration, development and transportation
Given its setting in the highly urbanized and heavily utilized inshore waterway of Broward County, vessel strikes can reasonably be expected to be a sign ificant threat in the Action Area

. The recovery plan (NMFS & USFWS , 1992) notes that vessel strike injuries were noted in 17 percent of leatherback strandings in Florida

. Entanglement in marine debris and hook and line fishing gear may also reasonably be expected to be significant in such a heavily used marine area

. The area including and surrounding the Action Area has a very high potential for impacts from oil and chemical pollution, as the Port is a major shipping hub and has significant commerce in p etroleum, with over 128 million barrels transshipped through the Port in 2005, including h eavy fuel oil, diesel, gasoline and jet fuel (Broward County , 2012 )

. It is very unlikely, however, that an almost exclusively pelagic species such as the leatherback would be found in the inshore waters of the Action Area, and records from the Florida STSSN show no strandings of leatherbacks at all in the inshore waters of Broward County from 2002 through 2011 (Foley, 2012).

4.4 Hawksbill Sea Turtle ( Eretmochelys imbric ata ) The hawksbill turtle recovery plan (NMFS & USFWS , 1993) lists the following threats to hawksbill turtles that may potentially occur in the Action Area:


### Vessel strikes Marine debris entanglement and ingestion Oil and gas exploration, development and tr ansportation
G iven its setting in the highly urbanized and heavily utilized inshore waterway of Broward County, vessel strikes can reasonably be expected to be a significant threat in the Action Area

. Entanglement in marine debris and hook and line fishin g gear may also reasonably be expected to be significant in such a heavily used marine area

. The area including and surrounding the Action Area has a very highNovember 2012 23 113

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- 12.doc potential for impacts from oil and chemical pollution, as the Port is a major shipping hub and has significant commerce in petroleum, with over 128 million barrels transshipped through the Port in 2005, including h eavy fuel oil, diesel, gasoline and jet fuel (Broward County , 2012 ). There are no records of hawksbill turtle strandings in the STSSN d atabase for inshore Broward County waters that include the Action Area for the period from 2002 through 2011.

4.5 Kemp's Ridley Sea Turtle ( Lepidochelys kempii ) The most recent revision of the recovery plan for the Kemp's Ridley sea turtle (NMFS, USFWS & SEMAR NAT , 2010) lists the following threats that may potentially occur in the Action Area:


### Vessel strikes Marine debris entanglement and ingestion Hook and line fisheries Oil, fu el, tar and chemical pollution Dredging Given its setting in the highly urbanized and heavily utilized inshore waterway of Broward County, vessel strikes can reasonably be expected to be a significant threat in the Action Area

. The recovery plan (NMFS, USFWS, & SEMARNAT , 2010) notes that vessel strike injuries were found in approximate ly 13 percent of Kemp's Ridley strandings from 1997 through 2001

. Entanglement in marine debris and hook and line fishing gear may also reasonably be expected to be significant in such a heavily used marine area

. From 1980 through 2006, there were 354 Ke mp’s Ridleys stranded along the U.S

. Atlantic and Gulf of Mexico coast with evidence of interactions with recreational or commercial hook and line fisheries, based on the internal and/or external presence of hook and line gear (NMFS STSSN , unpublished dat a )

. The area including and surrounding the Action Area has a very high potential for impacts from oil and chemical pollution, as the Port is a major shipping hub and has significant commerce in petroleum, with over 128 million barrels transshipped through the Port in 2005, including h eavy fuel oil, diesel, gasoline and jet fuel (Broward County , 2012 )

. Dredging activities occur periodically in the Action Area to maintain suitable navigational depths

. Hopper dredges have historically been used for this act ivity, which do have the potential to cause sea turtle mortalities

. In the Environmental Assessment for the Port m aintenance dredging in 2005, USACE concluded that: "the project may adversely affect sea turtles below mean high water if a hopper dredge is used" (USACE, 2005)

. A search of the USACE Sea Turtle Data Warehouse (USACE , 2005b) revealed no takes of Kemp's Ridley turtles were recorded for the 2005 maintenance dredging

. Dredging, along with marina and dock development, may also affect turtles less directly by degrading habitat quality

. The Action Area is curre ntly very intensively developed and the potentialNovember 2012 24 113

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- 12.doc for new dock and marina development in the Action Area appears to be very slight, given that the only remaining areas of natural shoreline an d shallow water habitat are protected within the boundaries of the John U

. Lloyd State Recreation Area . There are no records of Kemp's Ridley turtle strandings in the STSSN database for inshore Broward County waters that include the Action Area for the pe riod from 2002 through 2011.

4.6 Smalltooth Sawfish ( Pristis pectinata ) The smalltooth sawfish draft recovery plan (NMFS , 2006) lists the following threats to the smalltooth sawfish that may potentially occur in the Action Area: 

### Urban development Commercial ac tivities Channel dredging Boating activities Many of these threats are particularly widespread in the highly urbanized marine environment of southeast Florida

. The Action Area is curre ntly very intensively developed and the potential for new dock and mari na development in the Action Area appears to be very slight, given that the only remaining areas of natural shoreline and shallow water habitat are protected within the boundaries of the John U

. Lloyd State Recreation Area

. The Action Area includes a port ion of the Port facility

. The Port Everglade s Master Plan document (Broward County , 2012) outlines plans for expansion and continued development of the Port facilities in conjunction with the Federal channel deepening and widening project currently under review.

4.7 Johnson’s Seagrass ( Halophila johnsonii ) The Johnson’s seagrass recovery plan (NMFS , 2002) lists the following threats to Johnson’s seagrass that may potentially occur in the Action Area: 

### Dredging and filling Construction and shading f rom in and ov erwater structures P rop scarring and anchor mooring Trampling Altered water quality (such as s tormwater runoff and turbidity) Storms SiltationNovember 2012 25 113

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- 12.doc Dredging and filling occur regularly to maintain suitable navigational depths in the Action Area

. Due to the hig hly urbanized character, the existence of docks and Port structures in the Action Area, construction and shading from in and overwater structures may occur

. Prop scarring and anchor mooring may also occur in the Action Area

. The area waterways are heavil y used by commercial and recreational vessels

. Trampling is less likely, since the waterways are used primarily for navigation

. Water quality in the area varies due to tidal influence, stormwater run

- off from th e surrounding urban environment and fuel fr om high boat usage

. Storms affect the area on a seasonal basis, in cluding hurricanes, nor’easters and seasonal thunderstorms that occur during the summer

. Siltation may occur associated with construction projects and large pulses of freshwater due to rai n events

. Despite all of these potential effects , Johnson’s seagrass expanded its cover from 1999 through 2009 (DC&A , 2009).



### 5.0 EFFECTS OF THE PROPO SED ACTION
This section discusses the effects of the proposed action on the listed species discussed in Secti on 3 above . No indirect, interrelated, or interdependent effects were identified for the proposed action; thus the discussion is limited to direct effects.

5.1 Overview of the Proposed Action The proposed action involves the modernization and continued op eration of a facility that has been in operation at PPE since the early 1960s. Therefore, an examination of the recent history of the effects of the operation of the facility provides the best predictor of potential impacts from the proposed action, takin g into account the positive influence the proposed action will have on the potential for impacts to listed species. Available information on the history of sea turtle encounters at PPE from 1990 to 2012 was provided by FPL. Additional information on thos e encounters was obtained from a review of STSSN, rehabilitation facility and necropsy records. This information is summarized in Table 2 and will be discussed for each species below. In evaluating both the historical effects of the operation of PPE and the potential effects of the operation of PEEC, the beneficial role that encounters at PPE have had in recovering sick and injured turtles and transferring them to rehabilitation facilities should be considered. An examination of the data in Table 2 rev eals encounters with turtles that were recovered from PPE with vessel strike, entanglement, or other infirmities sustained outside the intake canal system that were successfully rehabilitated and released. Had these turtles not been encountered in the int ake system, it is very likely they would have continued to decline in condition in the wild and eventually succumb.November 2012 26 113

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- 12.doc PPE has operated in the Port area since the early 1960s

. At this and other facilities, FPL has a demonstrated history of environmental st ewardship that has supported the rehabilitation of injured sea turtles

. Sea turtles in various conditions of fitness have been observed in the PPE intake canal over the years

. The intake canal connects to the open Port waters and supports the PPE cooling system

. When PPE is operating, there is a unidirectional flow from the Port area (where multiple hazards exist including Port shipping traffic) into the intake canal

. During the years where FPL has a recorded histories (1990 to 2012), there were 29 docu mented turtles recovered from the intake canal. Twelve of those were found dead prior to arrival in the intake system, with most being severely decomposed. Eight of the turtles recovered were found with pre

- existing injuries requiring rehabilitation. Th ese injured turtles benefited from PPE’s operation because they were able to escape the Port area. They were recovered and received the veterinary attention they needed to improve their chances for survival. Nine turtles were captured and released back t o the environment on the same day.

The modernized PEEC will use the same intake canal as PPE. Because PEEC is more efficient than PPE, it will use less water and thus there will be a n approximately 5 0 percent reduction in flow at the point where the intak e canal water meets the open Port. This reduced flow is expected to result in fewer turtles entering the intake canal than occurs at PPE (already a small number on average of 1.26 turtles per year, ranging from zero to four turtles per year). Historical data indicates that 75 percent of the turtles recovered from the intake canal will be dead or have pre

- existing injuries. The beneficial properties of the intake canal described above will be maintained at PEEC. FPL will continue to monitor the intake ca nal for injured turtles. Any injured turtles that are encountered will be recovered and transported to a rehabilitation facility. FPL believes the reduced flow and the benefit to injured animals that the intake canal provides will further mitigate the al ready small number of encounters with these animals.

5.1.1 Loggerhead Sea Turtle ( Caretta caretta ) Loggerhead turtles were the species most often encountered at PPE. There were 19 encounters with loggerhead turtles in the intake system from 1990 through 2012. Ten loggerheads were recovered or observed alive and nine loggerheads were recovered dead

. Of the ten live loggerheads, four were transported to a rehabilitation facility, five had no apparent injury and appeared healthy and active and so were released th e same day and one was observed to swim out of the intake well area on its own. Based on a review of the available information, it does not appear that any of the injuries or mortalities was likely to have been causal to the operation of PPE.November 2012 27 113

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- 12.doc 5.1.2 Green Sea Turtle ( Chelonia mydas ) There were four encounters with green turtles in the intake system of PPE from 1990 through 2012. Three green turtles were recovered or observed alive and one was recovered dead. All three of the live green turtles were transporte d to a rehabilitation facility. Based on a review of the available information, it does not appear that any of the injuries or mortalities was likely to have been causal to the operation of PPE.

5.1.3 Leatherback Sea Turtle ( Dermochelys coriacea ) There have not been any encounters with leatherback turtles recorded at the PPE.

5.1.4 Hawksbill Sea Turtle ( Eretmochelys imbricata ) There were two encounters with hawksbill turtles in the intake system of PPE from 1990 through 2012. Both turtles were recovered alive. One hawksbill was transported to a rehabilitation facility and one was apparently uninjured and released the same day. Based on a review of available information, it does not appear the injuries of the hawksbill transported to a rehabilitation facility

were likely to have been causal to PPE operation.

5.1.5 Kemp's Ridley Sea Turtle ( Lepidochelys kempii ) There have not been any encounters with Kemp's Ridley turtles recorded at PPE.

5.1.6 Unidentified Sea Turtle Species There have been seven encounters with sea turtles rec orded at PPE where the species could not be determined or were not recorded. Five encounters involved live turtles that were either captured and released the same day (three individuals) or that swam out of the intake well area on their own (two individua ls). Two individuals that were not identified to species were recovered dead from the intake canal system. Based on a review of the available information, it does not appear that any of the injuries or mortalities were likely to have been causal to the o peration of PPE.

5.1.7 Smalltooth Sawfish ( Pristis pectinata ) There have not been any encounters with smalltooth sawfish recorded at PPE. The proposed action will not result in any dredging, shoreline armoring, or clearing of aquatic vegetation. A low level th reat to smalltooth sawfish identified in the draft recovery plan (NMFS, 2006) is warm water discharge from power stations, which is believed to interfere with natural movement patterns, as evidenced by the large number of smalltooth sawfish sightings near power station discharges. TheNovember 2012 28 113

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- 12.doc sawfish recovery plan bases the potential impact on indirect evidence of effects on bull sharks and the number of sawfish sightings near power plant discharges. The evidence for the threat is indirect and circumstantial and the severity is low; under the proposed action the potential for effects will be substantially reduced due to the lower flow and heat rejection rates for PEEC.

5.1.8 Johnson’s Seagrass ( Halophila johnsonii ) The proposed action will not result in any perturbation s of the bottom or deleteriously affect water quality

. The proposed action will reduce the volume of cooling water discharged and the extent of the thermal discharge as compared to the current characteristics. No adverse impacts to Johnson’s seagrass are anticipated.

5.2 Changes in Potential Effects Under the Proposed Action Under the proposed action, portions of the physical structures of the PPE cooling water intake and discharge systems will be refurbished and reused

. These modernized structures and the reduced cooling water volume requirements will result in lower water flow velocities and a reduction in the extent of the thermal discharge

. In combination, the above factors may reasonably be expected to significantly reduce the potential for impacts to listed species.

5.2.1 Changes During the Construction Phase of PEEC

While the Project is under construction for a period of approximately three years, ther e will be no cooling water used and thermal discharges will be limited to the operation of the Manatee Temp orary Heating System described in Section 2.1

. During this phase, there will be no potential impacts to listed species.

5.2.2 Changes During Operation of PEEC Once PEEC is constructed and operational, potential impacts to listed species will be significantly

re duced in comparison to the current operation of PPE. The intake structure will maintain the four 12 ft diameter intake pipes drawing water from Port Slip No. 3

. However, due to increased efficiencies in power generation, the volume of cooling water draw n through the intake pipes will be considerably reduced, from approximately 1300 MGD to approximately 635 MGD. This reduction in flow volume will be accompanied by a n approximately 5 0 percent reduction in intake velocities at the point of intake in Slip N o. 3. This change is expected to have a significant effect in reducing the number of encounters of sea turtles in the intake system,November 2012 29 113

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- 12.doc the residence time of healthy turtles in the intake system and the potential for injury or mortality at the intake wells.

Under PPE operating characteristics, intake velocities are not sufficient to cause entrainment of a strong swimming animal such as a sea turtle

- the turtles must actively swim into and through the intake pipes, although the current flow in the pipes make s it more likely that a turtle entering the intake structure will continue through the pipes and enter the intake canal

. With the reduced flows characteristic of the proposed action, it is expected that fewer turtles wil l enter the intake canal itself and potential for entrainment of injured or dead sea turtles on the vertical coarse bar racks is expected to be reduced

. In addition, the reduced flow will facilitate the egress of healthy turtles

. Lastly and perhaps most significantly, a n approximately 50 percent reduction in current velocity entering the culverts and within the intake canal will make it easier for a sick or injured turtle with compromised swimming ability to avoid the area of the intake wells, where there is a small potential for drowning on the intake grate and/or mechanical injury from the intake rakes that keep the intake grate clear of debris. It should be noted, however, that based on a review of the available information, it does not appear that any of the historical injuries or mor talities were likely to have been causal to the operation of PPE. The extent of the thermal discharge will be significantly reduced when PEEC is in operation compared to the current operation of PPE. The temperature rise of the cooling water at discharge will remain approximately the same at PEEC as compared to PPE, but the significant reduction in cooling water volume requirements will reduce the extent of the thermal discharge in the ICW adjacent to the discharge canal by approximately 50 percent. This reduction will reduce any potential effects to the smalltooth sawfish and Johnson's seagrass. In combination, the above factors may reasonably be expected to significantly reduce the potential for impacts to listed species, although the magnitude of the re duction is difficult to predict and will not necessarily have a linear relationship to the reduction in flow volume, velocities, or thermal discharges

. 5.3 Minimization of Potential Impacts and Conservation Efforts under the Proposed Action

This subsection d escribes how impacts to listed species are minimized by the operation of PEEC and also outlines proposed conservation efforts to be undertaken by FPL in the operation of PEEC.November 2012 30 113

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- 12.doc 5.3.1 Minimization As mentioned in Section 2.1, PEEC will use natural gas as the prima ry fuel with ULSD oil used as the backup fuel

. Natural gas will be transported to PEEC via an existing natural gas pipeline

. New infrastructure will be built to accommodate ULSD storage, delivery and unloading from Port unloading facilities

. It is antic ipated that less than one ship on average per year will be sufficient to maintain the necessary levels of ULSD for reliable and continuous service even during periods of disrupted natural gas supply, a significant reduction from the 22 plus ships per year necessary under current operations

. The reduction in shipping traffic will further reduce the environmental impacts of electrical generation at PEEC by decreasing the potential for spills, propeller strikes and other potentially harmful effects of shippin g traffic on listed species potentially occurring in the Action Area. PEEC will reuse portions of the existing cooling water intake system, specifically the PPE Units 3 and 4 cooling water intake structures after refurbishment and the addition of an Aquati c Organism Return System

. Therefore future operations of PEEC will involve half the number of intake bays and screens, with a resulting 50 percent reduction in operations and maintenance activities that have the potential for impact to sea turtles. This will also create an area near the intake wells that is relatively calm, providing greater opportunity for sick or injured turtles that enter the intake canal to avoid the intake wells

. In addition, the approximately 50 percent lower velocities at the poin t of intake and within the intake canal, combined with an approximately 50 percent reduction in cooling water flows, will minimize the potential impact to sea turtles. As mentioned previously, the extent of the thermal discharge will be significantly reduc ed when PEEC is in operation compared to PPE. The temperature elevation of the cooling water at discharge will remain about the same at the PEEC as compared to PPE , but the significant reduction in the extent of the thermal discharge and decrease in cooli ng water withdrawals will reduce the extent of the thermal discharge in the ICW adjacent to the discharge canal. This reduction will minimize any potential effects to the smalltooth sawfish and Johnson's seagrass.

5.3.2 Conservation Efforts

PEEC will be more ef

ficient than PPE, so it will use less water. Thus, there will be a reduction in flow at the point of withdrawal at Port Slip No. 3. This reduced flow is expected to result in fewer turtles entering the intake canal than occurs at PPE (already a small nu mber on average of 1.26 turtles per year, ranging from zero to four per year)

. In an attempt to provide further protection to the sea turtles in the area, FPL would like to propose additional conservation measures

.November 2012 31 113

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- 12.doc The record demonstrates that the intak e system at PPE has a history of collecting sea turtles that are predominantly weak, lethargic, or injured due to injuries or infirmities sustained outside of Plant operations. As discussed in Sections 1.3 and 5.0 above, when collected by trained staff an d treated at a rehabilitation center, the impacts to the animals have been minimized because they are given care they would otherwise not receive in the wild. The procedures currently in place at PPE have resulted in appropriate and effective responses to sea turtle encounters in the intake system

. Although the current procedures have been successful at minimizing impacts, a more comprehensive procedure would have the potential to provide better and more complete information on turtles that enter the intak e canal system and further reduce the potential for injury or mortality.
As part of the revised procedure, FPL will increase the monitoring frequency of the intake well s to every 4 hours (6 times in a 24 hour period)

. Personnel conduct ing the monitor ing would be trained to observe and record data on each turtle. If a turtle is observed that appears to be weak, lethargic, or injured, a permitted , experienced , on - call sea turtle biologist would be mobilized to the PEEC

. The biologist would capture and evaluate the turtle

. F WC has a Sea Turtle Stranding and Salvage Network (STSSN) that standardized the format for reporting captured or stranded turtles. FPL ’s revised procedure will incorporate the same format used in the STSSN ’s Stranding Report

. After evaluating the sea turtle, the biologist will either release the turtle or transport it to a rehabilitation facility , as appropriate. Annual reports with a summary of sea turtle records at PEEC would be submitted to NMFS and FWC . This additional informat ion will be used by FPL to identify trends and inform future decision

- making. The conservation measures proposed would allow for a quicker response to each incident and increased data collection. The revised procedure would be submitted to NMFS and FWC for review and approval prior to the operation of PEEC.



### 6.0 CUMULATIVE EFFECTS

This section addresses non

- federal actions other than the proposed P roject reasonably certain to occur that have the potential to affect listed spec ies in the Action Area

. There is one non

- federal project expected to occur in the waters south of the Action Area, The Dania Cut

- off Canal Deepening Project and one federal project that will involve the northern segment of the Action Area, the Port Everg lades Expansion Project.

The Dania Cut

- off Canal is permitted to b e dredged along 4,763 linear ft , beginning at the southwestern end of the Port , extending west to U

. S

. Highway 1

. This portion of the canal will beNovember 2012 32 113

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- 12.doc dredged to

- 17 feet mean low water (proj ect depth of

- 15 ft mean low water and two ft of overdredging) in order to create a uniform depth throughout this portion of the canal

. The project will be managed by the Florida Inland Navigation District. The Port Everglades Federal Channel Project wil l deepen and widen the outer entrance channel, deepen the inner entrance channel, deepen the main turning basin, widen the rectangular shoal region to the southeast of the main turning basin by about 300 ft and deepen to 50 ft; widen the Southport Access C hannel (SAC) in the proximity of berths 23 to 26 by about 250 ft and relocate the U.S

. Coast Guard facility to the east; shift the existing 400

- ft wide SAC about 65 ft to the east from approximately berth 26 to the south end of berth 29 to provide a trans ition back to the existing f ederal channel limits; deepen the SAC from about berth 23 to the south end of berth 32 to 50 ft; deepen the Turning Notch (TN) (following local

- sponsor - dredging of same area to 42 f t) to 50 ft with an additional 100

- ft north

- sou th widening parallel to the SAC on the eastern edge of the SAC over a length of about 1,845 ft; and widen the western edge of the SAC for access to the TN from the existing f ederal channel edge near the south end of bert h 29 to a width of about 130 f t at t he north edge of the TN

. The entire Action Area is currently developed and built out, other than the shoreline and uplands in the John U

. Lloyd State Recreation Area, which is protected under the Florida State Park System

. The activities anticipated in the vicinity of the Action Area are not expected to affect listed species in the Action Area. N o cumulative effects upon listed species under the ESA are anticipated.


### 7.0 CONCLUSIONS
In conclusion, the proposed action will have no e ffect on the following listed species and/or their critical habitats:

blue whale ( Balaenoptera musculus ) finback whale ( Balaenoptera physalus ) humpback whale ( Megaptera novaeangliae ) North Atlantic right whale ( Eubalaena glacialis ) sei whale ( Balaenoptera boreal is ) sperm whale ( Physeter macrocephalus ) Kemp's Ridley sea turtle ( Lepidochelys kempii ) leatherback sea turtle ( Dermochelys coriacea ) shortnose sturgeon ( Acipenser brevirostrum ) smalltooth sawfish ( Pristis pectinata ) elkhorn coral ( Acrop ora palmata )November 2012 33 113

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- 12.doc staghorn coral ( Acropora cervicornis ) Johnson’s seagrass ( Halophila johnsonii ) Although the velocity and flow rate at the point of withdrawal as well as the number of intake bays will be reduced by approximately 50 percent, operation of the Project is likely to continue to result in sea turtles entering the intake system. Capture and release or rehabilitation of these individuals will be required. Section 9 of the Endangered Species Act and Federal regulation pursuant to section 4(d) of the Act prohibits the take of endangered and threatened species without special exemption. The definition of a “take” under the Act is “to harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect or attempt to engage in any such condu ct” (FWS, 1973). Although it is expected that the PEEC operations will have a positive impact on sea turtles by saving weak or injured animals, that benefit requires the Plant to “capture” or “collect”. Based on this definition, it was concluded that the proposed action may affect and is likely to adversely affect the following listed species and/or their critical habitats: loggerhead sea turtle ( Caretta caretta ) green sea turtle ( Chelonia mydas ) hawksbill sea turtle ( Eretmochelys imbricata )
Th e Project is likely to continue to observe sea turtles entering the intake system. Even though there is the determination that the Project “may affect, is likely to adversely affect” the three species listed above, the EPA believes the Project will not je opardize the continued existence of those species. It is recommended that NMFS and EPA engage in a formal consultation and prepare a Biological Opinion. The Biological Opinion should address incidental take. It is anticipated that an average of five tur tles per year may enter the wells and the incidental take statement should be based on a five

- year rolling average. This measure would allow PEEC to operate as designed while still providing an opportu nity for weak , injured and/or stranded turtles to be c aptured and sent for rehabilitation, if possible.November 2012 34 113

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Applied Biology, Inc. (ABI). May 1987

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statistics/ Broward County, 2012. Retrieved from: http://www.broward.org/Port/MasterPlan/Pages/2009Elements.aspx Burke, V

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. Marine Seagrass Survey of Port Ever glades, Final Report, January 28, 2000

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Dial Cordy and Associates Inc (DC&A)

. 2006

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. A study of the population ecology of inwater marine turtle populations on the east central coast of Florida

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- Site Certification Application. FPL Group, Inc. Juno Beach, FL. Foley, A. 2012. Personal communication. Henwood, T

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. 1987

. Distribution and migrations of immature Kemp's R idley turtles ( Lepidochelys kempii ) and green turtles ( Chelonia mydas ) off Florida, Georgia, and South Carolina

. No rtheast Gulf Science, 9(2):153

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. and J.A

. Musick

. 1985

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. Florida Marine Research Pu blicat ions.
National Marine Fisheries Service

. 2000

. Status review of the smalltooth sawfish ( Pristis pectinata ).November 2012 36 113

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National Marine Fisheries Service and US 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

. Washington D.C.
National Marine Fisheries Service and US Fish and Wildlife Service. 1991. Recovery plan for the U

. S

. population of Atlantic green turtle

. National Marine Fisheries Service. Washing ton D.C.
National Marine Fisheries Service and U.S

. Fish and Wildlife Service (NMFS and FWS). 1992. Recovery plan for the Kemp's Ridley sea turtle ( Lepidochelys kempii )

. National Marine Fisheries Service, Washington, D.C

. 40 pp.
National Marine Fishe ries Service and U.S

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. Petersburg, Florida.
National Marine Fisheries Service

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. Prepared by the Johnson's Seagrass Recovery Team for the National Marine Fisheries Service, Silver Spring, Maryland

. 134 pages. National Marine Fisheries Service, US Fish and Wildlife Service and SEMARNAT. 2010. Bi

National recovery plan for the Kemp's Ridley sea turtle ( Lepidochyles kempii ). Second Revision. NMFS, Silver Springs, MD. Norton, S. 2012. Personal communication. Ogren, L

. H

. 1989

. Distribution of juvenile and su b

- adult Kemp's R idley sea turtle: Preliminary results from 1984

- 1987 surveys

. In Caillouet, C

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. First International Symposium on Kemp's Ridley Sea Turtle Biology, Conservation and Management

. Texas A & M Univ., Galveston, TX , Oct

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. 1973

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. IUCN Monog

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- n ational smalltooth sawfish encounter database. Mote Marine Laboratory technical report 1134. Sarasota, Florida. Turtle Expert Working Group

. 1998

. An assessment of the Kemp’s R idley and loggerhead sea turtle populations in the western North Atlantic

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- Port Everglades, Broward County, Florida. Final environmental assessment and finding of no significant impact. USACE, Jacksonville District. 208pg.
USACE 2005b. USACE Sea Turtle Data Warehouse. Retrieved from: http://el.erdc.usace.army.mil/seaturtles/project.cfm?Id=442&Code=Project U.S. Fish & Wildlife Service (FWS), 1973. Endangered Species Act of 1973, Depa rtment of the Interior, Washington, D.C. Retrieved from: http://www.fws.gov/endangered/esa

library/pdf/ESAall.pdf Virnstein, R.W and L.M. Hall. 2009. Northern Range extension of th e seagrasses Halophilia johnsonii and Halophilia decipiens along the east coast of Florida, USA. Aquatic Botany 90:89

- 92. Walls, Jerry G., Fishes of the Northern Gulf of Mexico., T.F.H., 1975. Wershoven, R. and J.L. Wershoven. 1992. Juvenile green turtles in their offshore habitat in Broward County, Florida: a five year review. In: Salmon, M. and J. Wyneken (compilers). Proceedings of the eleventh annual workshop on sea turtle biology and conservation. NOAA Technical Memo. NMFS

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. and L.M

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## TABLESNovember 2012 39 113

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- 12.doc TABLE 1 . ENDANGERED AND THREATENED SPECIES UNDER THE JURISDICTION OF THE NATIONAL MARINE FISHERIE S SERVI CE IN THE SOUTH ATLANTIC


### Listed Species Scientific Name 

### Status Date Listed Marine Mammals 

### blue whale Balaenoptera musculus 

### Endangered 12/02/70 finback whale Balaenoptera physalus 

### Endangered 12/02/70 humpback whale Megaptera novaeangliae 

### End angered 12/02/70 North Atlantic right whale Eubalaena glacialis 

### Endangered 12/02/70 sei whale Balaenoptera borealis 

### Endangered 12/02/70 sperm whale Physeter macrocephalus 

### Endangered 12/02/70 Turtles 

### green sea turtle Chelonia mydas 

### End angered 07/28/78 hawksbill sea turtle Eretmochelys imbricata 

### Endangered 06/02/70 Kemp's Ridley sea turtle Lepidochelys kempii 

### Endangered 12/02/70 leatherback sea turtle Dermochelys coriacea 

### Endangered 06/02/70 loggerhead sea turtle Carett a caretta 

### Threatened 09/22/11 Fish 

### shortnose sturgeon Acipenser brevirostrum 

### Endangered 03/11/67 smalltooth sawfish Pristis pectinata 

### Endangered 04/01/03 Invertebrates 

### elkhorn coral Acropora palmata 

### Threatened 0 5/ 0 9/06 staghorn coral Acropora cervicornis 

### Threatened 0 5/ 0 9/06 Seagrasses 

### Johnson’s seagrass Halophila johnsonii 

### Threatened 09/14/98November 2012 40 113

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- 12.doc TABLE 2. SUMMARY OF SEA TURTLE ENCOUNTERS IN THE PORT EVERGLADES PLANT INTAKE CANAL SYSTEM 1990 THROUGH 2012 (D ata from FPL, STS SN, rehabilitation facility, and necropsy report records )

DATE SPECIES LIFE STAGE ALIVE/

DEAD DESCRIPTION

6/23/1991 Caretta

caretta Subadult Alive Removed alive from intake canal

. Carapace and flipper injuries consistent with vessel strike

. Transported to Ocean World for re habilitation, released 7/25/91. STSSN file # KCF1991062301.

2/11/1991 Eretmochelys

imbricata Juvenile Alive Removed alive from intake canal

. Old, healed flipper injury

. Transported to Ocean World for rehabilitation, released 9/8/199 1. STSSN file # CXO1991021101

.

4/07/1992 Caretta

caretta Adult

female Alive Removed alive from intake canal

. Plastron and flipper damage

. Transported to Ocean World for rehabilitation, released 4/15/92 at Fort Lauderdale Beach

. STSSN file # REM1992040 701.

1/29/1993 Chelonia

mydas Juvenile Alive Removed alive from intake canal

. Entangled in debris

. Old, healed flipper damage

. Transported to rehabilitation facility, released 2/15/93 one mile offshore of Port Everglades

. STSSN file # SXG1993012901.
1/14/1994 Unidentified Unidentified Dead Removed dead from the intake canal

. Found moderately decomposed

. STSSN file # JRW1994011401.
2/21/1994 Eretmochelys

imbricata Unidentified Alive Recovered alive and uninjured from the intake canal

. Released ne ar Plant same day

. STSSN file # JRW1994022101.

4/24/2000 Caretta

caretta Adult

female Alive Recovered alive and uninjured from the intake well area
. Released same day at Frank C

. Tootie Adler Park

. STSSN file # MJB2000042401

.
4/07/2003 Caretta

caret ta Subadult Dead Recovered dead from intake canal

. Moderately decomposed

. Slightly emaciated with apparent propeller wounds from probable boat strike

. STSSN file # SXO2003040701.

7/16/2004 Caretta

caretta Subadult Alive Recovered alive from the intake canal

. Old, healed wounds consistent with constriction injuries

. Oil and tar stains on turtle

. Released same day

. STSSN file # EPD2004071601.
10/20/2005 Caretta

caretta Subadult Dead Recovered dead from intake canal

. Found severely decomposed

. ST SSN file # SXO2005102001.

12/28/2005 Caretta

caretta Subadult Dead Recovered dead from intake canal

. Found severely decomposed

. Evidence of injury consistent with vessel strike

. STSSN file # KXW2005122801.November 2012 41 113

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- 12.doc DATE SPECIES LIFE STAGE ALIVE/

DEAD DESCRIPTION

5/27/2006 Caretta

caretta Subadult Alive Rec overed alive from intake canal

. Fresh propeller wound to carapace

. Transported to Center for Rehabilitation of Wildlife (CROW) in Sanibel Island Florida

. Released 8/17/06

. STSSN file # MXB2006052701.
10/30/2006 Caretta

caretta Adult

female Dead Recov ered dead from intake canal

. Found severely decomposed

. STSSN file # SXR2006103001.

7/11/2007 Caretta

caretta Subadult Dead Recovered dead from the intake canal

. Thought to have floated in dead

. Moderately decomposed, emaciated, with old, healed inju ries

. STSSN file # KFS2007071101.
7/13/2007 Unidentified Unidentified Alive Recovered alive and uninjured from intake canal, released by plant staff at discharge canal

. STSSN file # KFS2007071301

. 7/13/2007 Unidentified Unidentified Alive Recovered al ive and uninjured from intake canal, released by plant staff at discharge canal

. STSSN file # KFS2007071302

. 7/13/2007 Unidentified Unidentified Alive Recovered alive and uninjured from intake canal, released by plant staff at discharge canal

. STSSN fil e # KFS2007071303

. 7/17/2008 Unidentified Unidentified Dead Recovered dead from intake wells

. Severe decomposition, only pieces of carapace and bone recovered

. STSSN file #JXW2008071701.

10/8/2008 Caretta

caretta Unidentified Alive Recovered alive from the intake canal by St

. Lucie power plant staff

. Fresh injuries consistent with entanglement in rope and/or net

. Old, partially healed amputation of right front flipper

. Transferred to Loggerhead Marinelife Center for rehabilitation

. Released at Juno Beach 5/13/2010

. STSSN file # MJB2008100101. 5/25/2009 Caretta

caretta Unidentified Alive Recovered alive and uninjured by FWCC staff

. Released same day

. No STSSN report found. 8/31/2009 Caretta

caretta Unidentified Alive Recovered alive and uninjure d by FWCC staff

. Released same day

. No STSSN report found.

12/14/2009 Chelonia

mydas Adult

female Dead Recovered dead from the intake wells

. Extensive crushing injury to carapace, neck, and plastron

. Salvaged and transported to Dr

. Brian Stacy at Uni versity of Florida for necropsy

. Necropsy concluded that cause of death could not be conclusively determined, and traumatic injuries were most likely sustained postmortem

. STSSN file # MXW2009121401

. Necropsy report file # ST09

- 173.

10/9/2010 Cheloni a

mydas Juvenile Alive Recovered alive from the intake canal

. Carapace injury consistent with a boat strike

. Transported to Miami Seaquarium for rehabilitation

. STSSN file # NMT2010100901.

10/24/2010 Chelonia

mydas Juvenile Alive Recovered alive from intake canal

. No external injuries but significant fibropapilloma tumors

. Transported to Mote Marine Lab for rehabilitation

. STSSN file # CFG2010102401.November 2012 42 113

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- 12.doc DATE SPECIES LIFE STAGE ALIVE/

DEAD DESCRIPTION

10/25/2010 Caretta

caretta Unidentified Alive Observed in intake canal

. Turtle swam out of well a rea independdently

. No visible injury

. No STSSN report found

12/31/2010 Caretta

caretta Subadult Dead Recovered dead from intake canal

. No apparent injury

. Documented by Broward County environmental staff . S TSSN file # TXK2010123101.
1/27/2011 Unide ntified Unidentified Alive Observed in intake canal

. Turtle swam out of intake well area on its own

. No visible injury

. No STSSN report found.
5/26/2011 Unidentified Unidentified Alive Observed in intake canal

. Turtle swam out of intake well area on i ts own

. No visible injury

. No STSSN report found.
4/16/2012 Caretta

caretta Unidentified Dead Recovered dead from intake canal with apparent post

- mortem injury to head, neck, and carapace

. No STSSN report found.

4/21/2012 Caretta

caretta Subadult Dead Recovered dead from intake canal with injury to head and carapace consistent with a vessel strike

. Moderately decomposed

. STSSN file # SXW2012042101.
5/7/2012 Caretta

caretta Unidentified Alive Recovered alive from intake canal

. No apparent injury

. Released same day

. No STSSN report found.

6/12/2012 Caretta

caretta Adult

female Dead Recovered dead from intake canal by Nova University staff

. No apparent injury or abnormality

. Severely decomposed

. STSSN file # EJS2012061201November 2012 43 113

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## FIGURES