Federal Register Vol. 82, No.167,

Section 702 of the Trade Agreements Act of 1979 (as amended) (the Act) requires the Department of Commerce (the Department) to determine, in consultation with the Secretary of Agriculture, whether any foreign government is providing a subsidy with respect to any article of cheese subject to an in-quota rate of duty, as defined in section 702(h) of the Act, and to publish quarterly updates to the type and amount of those subsidies. We hereby provide the Department's quarterly update of subsidies on articles of cheese that were imported during the periods January 1, 2017, through March 31, 2017.

The Department has developed, in consultation with the Secretary of Agriculture, information on subsidies, as defined in section 702(h) of the Act, being provided either directly or indirectly by foreign governments on articles of cheese subject to an in-quota rate of duty. The appendix to this notice lists the country, the subsidy program or programs, and the gross and net amounts of each subsidy for which information is currently available. The Department will incorporate additional programs which are found to constitute subsidies, and additional information on the subsidy programs listed, as the information is developed.

The Department encourages any person having information on foreign government subsidy programs which benefit articles of cheese subject to an in-quota rate of duty to submit such information in writing to the Assistant Secretary for Enforcement and Compliance, U.S. Department of Commerce, 1401 Constitution Ave. NW., Washington, DC 20230.

This determination and notice are in accordance with section 702(a) of the Act.

Background

On July 12, 2017, the Department of Commerce (Department) initiated a countervailing duty investigation on ripe olives from Spain.1 Currently, the preliminary determination is due no later than September 15, 2017.

Section 703(b)(1) of the Tariff Act of 1930, as amended (the Act), requires the Department to issue the preliminary determination in a countervailing duty investigation within 65 days after the date on which the Department initiated the investigation. However, section 703(c)(1) of the Act permits the Department to postpone the preliminary determination until no later than 130 days after the date on which the Department initiated the investigation if: (A) The petitioner 2 makes a timely request for a postponement; or (B) the Department concludes that the parties concerned are cooperating, that the investigation is extraordinarily complicated, and that additional time is necessary to make a preliminary determination. Under 19 CFR 351.205(e), the petitioner must submit a request for postponement 25 days or more before the scheduled date of the preliminary determination and must state the reasons for the request. The Department will grant the request unless it finds compelling reasons to deny the request.

On August 7, 2017, the petitioner submitted a timely request that we postpone the preliminary CVD determination.3 The petitioner stated that it requests postponement because the Department continues to gather “questionnaire responses from the Government of Spain, the European Union, and the mandatory respondents in this investigation. Thus, extra time is needed to permit the Department . . . to analyze fully the questionnaire responses, request any necessary clarifications, and determine the extent to which countervailable subsidies have been bestowed on the respondents.” 4 In accordance with 19 CFR 351.205(e), the petitioner has stated the reasons for requesting a postponement of the preliminary determination, and the Department finds no compelling reason to deny the request. Therefore, pursuant to section 703(c)(1)(A) of the Act, we are extending the due date for the preliminary determination to no later than 130 days after the date on which this investigation was initiated, i.e., to November 20, 2017.5 Pursuant to section 705(a)(1) of the Act and 19 CFR 351.210(b)(1), the deadline for the final determination will continue to be 75 days after the date of the preliminary determination.

This notice is issued and published pursuant to section 703(c)(2) of the Act and 19 CFR 351.205(f)(l).

The NCCP announces the reconstitution of its Federated Cloud Public Working Group (Working Group). The Working Group was formed to address Requirement #5 of NIST's US Government Cloud Computing Technology Roadmap (NIST SP 500-293) (Cloud Computing Roadmap), “Frameworks to Support Federated Community Clouds.” This requirement calls for “frameworks to support seamless implementation of federated community cloud environments.” The Working Group's activities will resume and initiate work to try and fully understand and describe the elements of federated cloud computing. Assorted topics include developing and gaining consensus on a common federated cloud computing vocabulary, as well as developing an underlying conceptual model of what federated cloud computing is, its major components, and users/stakeholders.

An initial teleconference will take place on Thursday, August 31, 2017, at 10:00 a.m. Eastern Time. The dial-in number is 1-877-953-0273, and the passcode is 456-4979. Members of the public who wish to participate in the teleconference should provide their name and email address to [email protected], no later than 5:00 p.m. Eastern Time on Thursday, August 24, 2017. Responses received after the deadline will also be added to the group's mailing list, but they may not receive initial documentation prior to the first meeting. Members of the public who provide their email addresses but who cannot participate in the initial teleconference will still be notified about subsequent meetings. It is anticipated that there will be subsequent monthly meetings by teleconference on the fourth Thursday of every month from either 11:00 a.m. to 1:00 p.m. Eastern Time or 1:30 p.m. to 3:00 p.m. Eastern Time. A schedule of meeting times will be provided to all participants who submit their name and email address as provided above. Participation in the Working Group is open to all interested parties; there is no fee to participate. Standing Rules Documents explaining how the group will be run will be made available at the first meeting to all Working Group members. Final technical recommendations from the Working Group will be made publicly accessible on the NIST Cloud Computing Portal, and NIST may make the results of this Working Group available to Standards Developing Organizations and other interested parties.

The Cloud Computing Roadmap is being used industry-wide to advance the rapid adoption of cloud computing. Two of the 10 requirements (numbers 5 and 8) in the Cloud Computing Roadmap point to the next generation of cloud computing which will be focused on the concept of federated clouds. Federated clouds represent a future where there is seamless integration between multiple cloud service providers. Fulfilling this vision of the future of cloud computing will require a foundational effort to understand all the technological and standards-based obstacles that will need to be addressed to build the necessary underlying architecture.

The scope of the project is to fully understand and describe the elements of federated cloud computing. This will involve developing and gaining consensus on a common federated cloud computing vocabulary, as well as developing an underlying conceptual model of what federated cloud computing is, its major components, and users/stakeholders. The Working Group will then use that conceptual model to map out an implementation strategy including a gap analysis to identify the missing technologies and standards needed to cultivate a seamless system of systems. The anticipated results are:

• Federated Cloud Computing Vocabulary;

• Conceptual Model of Federated Clouds; and

• Technology Gap Analysis.

The Working Group will also investigate and identify the needed technologies, tools, and standards to enable these environments. They will use material from NIST's Cloud Computing Reference Architecture (NIST SP 500-292) and materials located at the group's public twiki site: http://collaborate.nist.gov/twiki-cloud-computing/bin/view/CloudComputing/RATax_FedCommunity.

The Working Group will work in a coordinated effort with the IEEE ICWG/2302 WG—Intercloud Working Group to produce an implementation of this reference material and create a compliant technical standard. A list of NIST's Cloud Computing Working Groups can be found at http://collaborate.nist.gov/twiki-cloud-computing/bin/view/CloudComputing/WebHome#Working_Groups_of_NIST_Cloud_Com. The work of the NIST Cloud Computing Working Groups is interrelated, and this Working Group will also liaise with other working groups as needed.

In February 2013, DOJ and NIST announced a partnership that included the formation of the OSAC. As is stated in the OSAC Charter, the purpose of the OSAC is to strengthen the Nation's use of forensic science by: Providing technical leadership necessary to facilitate the development and promulgation of consensus-based documentary standards and guidelines for forensic science; promoting standards and guidelines that are fit-for-purpose and based on sound scientific principles; promoting the use of OSAC standards and guidelines by accreditation and certification bodies; and establishing and maintaining working relationships with other similar organizations. The OSAC Charter and Bylaws are available online at: https://www.nist.gov/topics/forensic-science/about-osac.

These purposes of the OSAC are achieved through the OSAC Registry, the repository for all standards and guidelines. A standard or guideline is posted on the OSAC Registry only after the validity of any methods it contains has been assessed by forensic practitioners, academic researchers, measurement scientists, and statisticians through a consensus development process that allows participation and comment from all relevant stakeholders. NIST retains ultimate authority over posting of standards and responsibility for support of the OSAC Registry.

The OSAC Charter states that the aims of the OSAC are to: Populate the OSAC Registry; develop and maintain the Principles of Professional Practice; compile and update the forensic science catalog of standards and related documents; maintain Priority Action Plan documents on OSAC strategic objectives and associated goals and intended actions; promote and improve the communication, dissemination and use of forensic science standards, accreditation, and personnel competencies; encourage forensic science service providers in the United States to implement guidelines and standards (e.g., ISO/IEC 17025, etc.) for quality and competency; provide insight on each forensic science discipline's research and measurement standard needs; and enlist stakeholder involvement from a broad community to provide public comment on OSAC outputs.

Under the OSAC Charter, NIST has primary responsibility to coordinate development of a quality infrastructure for forensic science standards development and to support the OSAC. NIST envisioned the OSAC as a multi-level organization consisting of five Scientific Area Committees (SACs) that report to a Forensic Science Standards Board (FSSB). Each of the five SACs oversees discipline-specific subcommittees. In addition, there are three Resource Committees that provide input to the FSSB, SACs, and SAC Subcommittees. DOJ funds the OSAC through appropriated funds that are transferred to NIST. While DOJ personnel participate as members of OSAC committees and subcommittees, DOJ itself does not review or approve OSAC standards prior to posting on the Registry.

Both NIST and DOJ recognized from the outset that the OSAC would be realigned over time to ensure continuous improvement and better realize its purpose and objectives. NIST has publicly announced its intention to transition the administration of the OSAC to another host within five to ten years. NIST's goals in this transition process are to establish the next generation of OSAC (OSAC 2.0) that strengthens forensics science, follows American National Standards Institute principles for standards development, and promotes a collaborative process that actively involves practitioners and researchers. NIST notes that, as a non-regulatory research and development agency, it does not contemplate undertaking any a regulatory or quasi-regulatory function in connection with OSAC 2.0. NIST is open to maintaining elements of the current OSAC structure, to modifications to the structure, as well as to substantially different structural concepts, including several examples of concepts at: https://www.nist.gov/topics/forensic-science/potential-concepts-osac-20. NIST notes its continuing commitment to the forensic science community, that OSAC 2.0 will promote the continued scientific integrity and stability of the organization.

NIST is now in the process of developing a process for the transition of OSAC 1.0 to an OSAC 2.0 structure that will accomplish these goals and safeguard the efficiency and effectiveness of the organization. To ensure that the transition plan is comprehensive and meets the needs of the community, NIST, in collaboration with DOJ, requests from the public, comments on the questions below, which will inform the approach to an OSAC 2.0 in the following six areas: (A) Purpose, (B) oversight and independence, (C) work product and aims, (D) structure, (E) participation, and (F) funding.

(A) Purpose: As stated above, the OSAC charter identifies four purposes. (See section 1.1: https://www.nist.gov/sites/default/files/documents/2017/03/16/fssb_osac_charter_and_bylaws_v_1.3.pdf). What is your opinion regarding whether the OSAC is fulfilling these purposes under the current structure? What is your opinion regarding whether these purposes/functions are appropriate for the OSAC and whether the purposes should be modified in any way? What is your opinion regarding what role, if any, the OSAC should be playing in addressing the recommendations of the 2009 National Academies of Sciences report, “Strengthening Forensic Science in the United States: A Path Forward” (https://www.nap.edu/read/12589/chapter/1)?

(B) Oversight and independence: Please provide your views regarding what type of entity should host the OSAC (e.g., governmental, professional association, etc.). What is your opinion about the preferred characteristics of a host organization for an effective OSAC? What are your views as to the type of organization that should provide oversight to the OSAC? Do you believe that the OSAC should have more/less independence from a host organization?

(C) Work products and aims: As stated above, the OSAC Charter identifies eight aims. (See section 1.2: https://www.nist.gov/sites/default/files/documents/2017/03/16/fssb_osac_charter_and_bylaws_v_1.3.pdf.) What is your opinion regarding whether the OSAC is fulfilling these aims as structured? Do you believe that the OSAC is addressing the correct aims? What are your views as to the type of work products the OSAC should produce? What do you believe are the essential elements of work products? Please provide your opinion as to whether there should be implementation/enforcement of the work products. Do you believe that the OSAC should develop “best practices” and other materials that are not formal “standards”?

(D) Structure: What are your views as to whether the current the OSAC structure works efficiently? Do you believe that another structure should be utilized? Please provide your opinion about whether there are any issues in the current work product development process that should be addressed structurally. In your view, does the reliance on standards development organizations function as intended (please include the reasons for your opinion)?

(E) Participation: What are your views as to the community the OSAC should serve? In your opinion, what stakeholders must be a part of the OSAC (e.g., practitioners, researchers, forensic science societies, accreditation bodies, scientific societies, human factors experts, metrologists, standards development organizations, legal practitioners)? If you think that any of these entities should be excluded, please explain why and identify other venues for the views of the excluded entities to be incorporated into forensic practice, if appropriate. In your view, should some stakeholders serve more limited roles and, if so, how and why?

(F) Funding: What is your opinion as to the funding model that the OSAC should employ—Entirely funded by the Federal government, by non-Federal funds, or a combination of funding sources? (Please include your thoughts on the role of funding sources such as membership fees, certification fees, and meeting registration fees.) What are your views about the implications of funding models for the other traits, particularly oversight and independence?

Response to this request for information (RFI) is voluntary, and comments are not limited to the specific questions posed. Respondents need not reply to all questions; however, it is requested that they clearly indicate the letter of each question to which they are responding. All responses to this RFI must be submitted electronically through www.regulations.gov.

All responses received will be posted on www.regulations.gov without making any changes to the responses or redacting any information, including any personally identifiable information provided. It is the responsibility of the respondent to safeguard personally identifiable information. You are not required to submit personally identifying information in order to respond and it is recommended that respondents' personally identifiable information not be included. Responses may be provided anonymously, but those respondents who do share contact information are requested to include brief background information regarding the respondent's subject-matter experience and expertise. Responses submitted through www.regulations.gov will not include the email address of the respondent unless the respondent chooses to include that information as part of the response.

This request is for an extension and revision of a currently approved information collection under the Office of Management and Budget's (OMB) Control Number 0648-0551, Southeast Region IFQ (individual fishing quota) Programs. The NMFS Southeast Regional Office manages three commercial IFQ and individual transferable quota (ITQ) programs in the Southeast Region under the authority of the Magnuson-Stevens Fishery Conservation and Management Act (Magnuson-Stevens Act), 16 U.S.C. 1801 et seq. The IFQ programs for red snapper, and grouper and tilefish occur in Federal waters of the Gulf of Mexico, and the ITQ program for wreckfish occurs in Federal waters of the South Atlantic.

This collection of information tracks the transfer and use of IFQ and ITQ shares, and IFQ allocation and landings necessary to operate, administer, and review management of the IFQ and ITQ programs. Regulations for the IFQ and ITQ programs are located at 50 CFR part 622.

The NMFS Southeast Regional Office also proposes to revise parts of the information collection approved under OMB Control Number 0648-0551 to account for updates to burden time and cost estimates, as well as administrative updates to online and paper forms. NMFS intends the revisions would make instructions and data collection requirements clearer and easier to understand, resulting in more accurate and efficient information available for use by fishery managers.

Information for the Gulf red snapper, and grouper and tilefish IFQ programs is collected electronically via a web-based system, through satellite-linked vessel monitoring systems, through a 24-hour call line, and with paper form submission for landing corrections, closing an account, and account applications, as well as landing transactions under catastrophic circumstances.

The share transfer process in the wreckfish ITQ program requires the signatures of witnesses on paper forms. The ITQ program remains paper based until the South Atlantic Fishery Management Council and NMFS consider whether to implement an electronic system.

OMB Control Number: 0648-0551.

Form Number(s): None.

Type of Review: Regular submission (extension and revision of a currently approved information collection).

Affected Public: Business or other for-profit organizations.

Estimated Number of Respondents: 1,059.

Estimated Time per Response: Share Transfer Receipt form, Cost Recovery Fee Submission form, 1 minute; Share Transfer form, IFQ Close Account form, Cost Recovery Fee Submission form, Landing Transaction Correction Request form, Landing Location Submission form, Transfer Allocation form, Cost Recovery Fee payment through pay.gov, 3 minutes; Notification of Landing form, 5 minutes; Landing Transaction Report form, 6 minutes; IFQ Online Account Application form, 15 minutes; Wreckfish Quota Share Transfer form, 18 minutes.

Estimated Total Annual Burden Hours: 2,322.

Estimated Total Annual Cost to Public: $150 in recordkeeping/reporting costs.

Comments are invited on: (a) Whether the proposed collection of information is necessary for the proper performance of the functions of the agency, including whether the information shall have practical utility; (b) the accuracy of the agency's estimate of the burden (including hours and cost) of the proposed collection of information; (c) ways to enhance the quality, utility, and clarity of the information to be collected; and (d) ways to minimize the burden of the collection of information on respondents, including through the use of automated collection techniques or other forms of information technology.

Comments submitted in response to this notice will be summarized and/or included in the request for OMB approval of this information collection; they also will become a matter of public record.

The National Oceanic and Atmospheric Administration (NOAA) National Data Buoy Center (NDBC), a part of the National Weather Service (NWS), designs, develops, operates, and maintains a network of moored buoys and coastal stations throughout the world's oceans, seas, and lakes for the purpose of civil earth marine observations. NDBC has prepared a Programmatic Environmental Assessment (PEA) to analyze the continued operational activities of its network of moored buoys and coastal stations.

NDBC provides high quality ocean and coastal observations for public safety use in direct support of short range and extended range NWS forecasts, warnings, and watches. NDBC provides essential real-time oceanographic and meteorological observation data to stakeholders in key U.S. Economic Sectors, such as, Trade and Retail (i.e., maritime transportation) and Commercial sectors (i.e., energy, fishing, and agriculture). This valuable data provides users with up to the minute decision-making observations needed for safe commercial and marine recreation activities.

NDBC operates a network composed of four formal NOAA Observing Systems of Record: (1) Coastal Weather Buoys (CWB); (2) the land-based Coastal-Marine Automated Network (C-MAN); (3) Tropical Atmosphere Ocean Array (TAO) and (4) Deep-ocean Assessment and Reporting of Tsunamis (DART). Currently, NDBC's network consists of 200 buoys and 46 C-MAN stations that transmit observations and data (i.e., wind speed and direction, barometric pressure, air temperature; sea surface temperatures, wave height and period, water currents, and conductivity) via satellite that are processed and quality-controlled, and then disseminated for public release in near real-time.

In-situ real-time oceanographic and meteorological observations are critical to a wide variety of users such as federal, state, academic, and private industry stakeholders. These observations add value to a diverse spectrum of civil use applications including severe and routine weather forecasting; improved coastal ocean circulation models; commercial and recreational marine transportation and fishing; and environmental monitoring and research. The societal benefits of ocean observations are interconnected at local, regional, national, and international scales. The National Plan for Civil Earth Observations and the National Strategy for Sustained Network of Coastal Moorings identify the Societal Benefit Areas (SBAs) supported by NDBC ocean observations. These SBAs include scientific research, economic activities, and environmental and social domains. Many involve critical government functions, such as the protection of life and property (NSTC 2014). The nine SBAs that are applicable to NDBC are: Climate; Coastal and Marine Hazards and Disasters; Ocean and Coastal Energy and Mineral Resources; Human Health; Ocean and Coastal Resources and Ecosystems; Marine Transportation; Water Resources; Coastal and Marine Weather; and Reference Measurements.

Ocean observations are an indispensable component to measure and monitor our progress towards addressing societal challenges. Among the diverse sources of ocean observations, data buoys provide unique and invaluable information to support critical government functions, such as the protection of life and property. NDBC data are accessed on a daily basis, by millions of national and international stakeholders and assimilated into a myriad products and services.

Background

Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.) direct the Secretary of Commerce (as delegated to NMFS) to allow, upon request, the incidental, but not intentional, taking of small numbers of marine mammals by U.S. citizens who engage in a specified activity (other than commercial fishing) within a specified geographical region if certain findings are made and either regulations are issued or, if the taking is limited to harassment, a notice of a proposed authorization is provided to the public for review.

An authorization for incidental takings shall be granted if NMFS finds that the taking will have a negligible impact on the species or stock(s), will not have an unmitigable adverse impact on the availability of the species or stock(s) for subsistence uses (where relevant), and if the permissible methods of taking and requirements pertaining to the mitigation, monitoring and reporting of such takings are set forth.

NMFS has defined “negligible impact” in 50 CFR 216.103 as an impact resulting from the specified activity that cannot be reasonably expected to, and is not reasonably likely to, adversely affect the species or stock through effects on annual rates of recruitment or survival.

The MMPA states that the term “take” means to harass, hunt, capture, kill or attempt to harass, hunt, capture, or kill any marine mammal.

Except with respect to certain activities not pertinent here, the MMPA defines “harassment” as: Any act of pursuit, torment, or annoyance which (i) has the potential to injure a marine mammal or marine mammal stock in the wild (Level A harassment); or (ii) has the potential to disturb a marine mammal or marine mammal stock in the wild by causing disruption of behavioral patterns, including, but not limited to, migration, breathing, nursing, breeding, feeding, or sheltering (Level B harassment).

To comply with the National Environmental Policy Act of 1969 (NEPA; 42 U.S.C. 4321 et seq.) and NOAA Administrative Order (NAO) 216-6A, NMFS must review our proposed action (i.e., the issuance of an incidental harassment authorization) with respect to environmental consequences on the human environment.

This action is consistent with categories of activities identified in CE B4 of the Companion Manual for NOAA Administrative Order 216-6A, which do not individually or cumulatively have the potential for significant impacts on the quality of the human environment and for which we have not identified any extraordinary circumstances that would preclude this categorical exclusion. Accordingly, NMFS has determined that the issuance of the IHA qualifies to be categorically excluded from further NEPA review and signed a Categorical Exclusion memo in August 2017.

On May 3, 2017, NMFS received a request from WETA for an IHA to take marine mammals incidental to pile driving and removal in association with the Central Bay Operations and Maintenance Facility Project (Project) in Alameda, California. WETA's request is for take of seven species by Level A and Level B harassment. Neither WETA nor NMFS expect mortality to result from this activity and, therefore, an IHA is appropriate.

This is the second year of a 2-year project. In-water work associated with the second year of construction is expected to be completed within 22 days. This proposed IHA is for the second phase of construction activities (August 1, 2017 through November 30, 2017). WETA received authorization for take of marine mammals incidental to these same activities for the first phase of construction in 2016 (80 FR 10060; February 25, 2015). In addition, similar construction and pile driving activities in San Francisco Bay have been authorized by NMFS in the past. These projects include construction activities at the San Francisco Ferry Terminal (81 FR 43993, July 6, 2016); Exploratorium (75 FR 66065, October 27, 2010); Pier 36 (77 FR 20361, April 4, 2012); and the San Francisco-Oakland Bay Bridge (71 FR 26750, May 8, 2006; 72 FR 25748, August 9, 2007; 74 FR 41684, August 18, 2009; 76 FR 7156, February 9, 2011; 78 FR 2371, January 11, 2013; 79 FR 2421, January 14, 2014; and 80 FR 43710, July 23, 2015). This IHA is valid from August 1, 2017, through July 31, 2018.

WETA is constructing a Central Bay Operations and Maintenance Facility to serve as the central San Francisco Bay base for WETA's ferry fleet, Operations Control Center (OCC), and Emergency Operations Center (EOC). The Project will provide maintenance services such as fueling, engine oil changes, concession supply, and light repair work for WETA ferry boats operating in the central San Francisco Bay. In addition, the project will be the location for operational activities of WETA, including day-to-day management and oversight of services, crew, and facilities. In the event of a regional disaster, the facility will also function as an EOC, serving passengers and sustaining water transit service for emergency response and recovery. A detailed description of the planned construction project is provided in the Federal Register notice for the proposed IHA (82 FR 29486; June 29, 2017). Since that time, no changes have been made to the planned activities. Therefore, a detailed description is not provided here. Please refer to that Federal Register notice for the description of the specific activity.

A notice of NMFS's proposal to issue an IHA to WETA was published in the Federal Register on 82 FR 29486; June 29, 2017). That notice described, in detail, WETA's activity, the marine mammal species that may be affected by the activity, and the anticipated effects on marine mammals. During the 30-day public comment period, NMFS received a letter from the Marine Mammal Commission and a group of private citizens. The Marine Mammal Commission noted they look forward to working with NMFS regarding rounding in take estimation.

Comment 1: The group of private citizens recommend reviewing the construction process to ensure the maximum number of pilings is installed each day.

Response: NMFS has reviewed the number of pilings that were proposed by WETA and while the goal is to install as many piles per day as possible, it was determined that the duration and number of piles were the most realistic scenario for this project. A total of 22 days of construction is expected, which NMFS considers to be short and will not have excessive impacts to marine mammals.

Comment 2: The group of private citizens recommend that NMFS conduct more primary research on TTS and PTS thresholds in marine mammals using a study design that NMFS finds appropriate.

Response: As required, NMFS used the best available science available when determining acoustic impacts to marine mammals from WETA's construction project. Any new research on marine mammal TTS and PTS thresholds will be considered in future authorizations.

Comment 3: The group of private citizens recommend that NMFS require enhanced and continued monitoring even after pier construction and into ferry operations and further recommend that NMFS encourage WETA to install a second floating platform for harbor seals.

Response: NMFS believes that the monitoring proposed by WETA is sufficient to not only document take, but to also increase our knowledge of the species during project activities. Additional research on harbor seal use of the haul out or associated harbor seal activities, or construction of a second is not required for the WETA Central Bay project.

There are seven marine mammal species that may inhabit or may likely transit through the waters nearby the project area, and are expected to potentially be taken by the specified activity. These include the Pacific harbor seal (Phoca vitulina), California sea lion (Zalophus californianus), northern elephant seal (Mirounga angustirostris), northern fur seal (Callorhinus ursinus), harbor porpoise (Phocoena phocoena), gray whale (Eschrichtius robustus), and bottlenose dolphin (Tursiops truncatus). Multiple additional marine mammal species may occasionally enter the activity area in San Francisco Bay but would not be expected to occur in shallow nearshore waters of the action area. Guadalupe fur seals (Arctocephalus philippii townsendi) generally do not occur in San Francisco Bay, however, there have been recent sightings of this species due to an El Niño event. Only single individuals of this species have occasionally been sighted inside San Francisco Bay, and their presence near the action area is considered unlikely. No takes are requested for this species, and a shutdown zone will be in effect for this species if observed approaching the Level B harassment zone. Although it is possible that a humpback whale (Megaptera novaeangliae) may enter San Francisco Bay and find its way into the project area during construction activities, their occurrence is unlikely, since humpback whales very rarely enter the San Francisco Bay area. No takes are requested for this species, and a delay and shutdown procedure will be in effect for this species if observed approaching the Level B harassment zone.

Table 1 lists all species with expected potential for occurrence in San Francisco Bay near Alameda Point and summarizes information related to the population or stock, including potential biological removal (PBR), where known. For taxonomy, we follow Committee on Taxonomy (2016). PBR is defined by the MMPA as the maximum number of animals, not including natural mortalities, that may be removed from a marine mammal stock while allowing that stock to reach or maintain its optimum sustainable population (as described in NMFS's SARs). While no mortality is anticipated or authorized here, PBR and annual serious injury and mortality are included here as gross indicators of the status of the species and other threats.

A detailed description of the of the species likely to be affected by WETA's project, including brief introductions to the species and relevant stocks as well as available information regarding population trends and threats, and information regarding local occurrence, were provided in the Federal Register notice for the proposed IHA (82 FR 29486; June 29, 2017); since that time, we are not aware of any changes in the status of these species and stocks; therefore, detailed descriptions are not provided here. Please refer to that Federal Register notice for these descriptions. Please also refer to NMFS' Web site (www.nmfs.noaa.gov/pr/species/mammals/) for generalized species accounts.

Species that could potentially occur in the proposed survey areas, but are not expected to have reasonable potential to be harassed by in-water construction, include extralimital species, which are species that do not normally occur in a given area but for which there are one or more occurrence records that are considered beyond the normal range of the species (e.g., humpback whales and Guadalupe fur seal). All other species in Table 1 may occur in the project area and we therefore have authorized take for them.

The effects of underwater noise from WETA's pile driving and removal activities for the Central Bay Operations and Maintenance Project have the potential to result in behavioral harassment of marine mammals in the vicinity of the action area. The Federal Register notice for the proposed IHA (82 FR 29486; June 29, 2017) included a discussion of the effects of anthropogenic noise on marine mammals, therefore that information is not repeated here; please refer to that Federal Register notice for that information.

This section provides an estimate of the number of incidental takes authorized through this IHA, which informed both NMFS' consideration of whether the number of takes is “small” and the negligible impact determination.

Harassment is the only type of take expected to result from these activities. Except with respect to certain activities not pertinent here, section 3(18) of the MMPA defines “harassment” as any act of pursuit, torment, or annoyance which (i) has the potential to injure a marine mammal or marine mammal stock in the wild (Level A harassment); or (ii) has the potential to disturb a marine mammal or marine mammal stock in the wild by causing disruption of behavioral patterns, including, but not limited to, migration, breathing, nursing, breeding, feeding, or sheltering (Level B harassment).

Authorized takes are by Level A and Level B harassment, in the form of disruption of behavioral patterns for individual marine mammals resulting from exposure to vibratory and impact pile driving and removal, and potential permanent threshold shift (PTS) for harbor seals that may transit through the Level A zone to their haulout. Based on the nature of the activity and the anticipated effectiveness of the mitigation measures (i.e., bubble curtain, soft start, etc.—discussed in detail below in Mitigation section), Level A harassment is neither anticipated nor proposed to be authorized for all other species.

As described previously, no mortality is anticipated or authorized for this activity. Below we describe how the take is estimated.

Described in the most basic way, we estimate take by considering: (1) Acoustic thresholds above which NMFS believes the best available science indicates marine mammals will be behaviorally harassed or incur some degree of permanent hearing impairment; (2) the area or volume of water that will be ensonified above these levels in a day; (3) the density or occurrence of marine mammals within these ensonified areas; and, (4) and the number of days of activities. Below, we describe these components in more detail and present the proposed take estimate.

Using the best available science, NMFS has developed acoustic thresholds that identify the received level of underwater sound above which exposed marine mammals would be reasonably expected to be behaviorally harassed (equated to Level B harassment) or to incur PTS of some degree (equated to Level A harassment).

Level B Harassment for non-explosive sources—Though significantly driven by received level, the onset of behavioral disturbance from anthropogenic noise exposure is also informed to varying degrees by other factors related to the source (e.g., frequency, predictability, duty cycle), the environment (e.g., bathymetry), and the receiving animals (hearing, motivation, experience, demography, behavioral context) and can be difficult to predict (Southall et al., 2007, Ellison et al., 2011). Based on what the available science indicates and the practical need to use a threshold based on a factor that is both predictable and measurable for most activities, NMFS uses a generalized acoustic threshold based on received level to estimate the onset of behavioral harassment. NMFS predicts that marine mammals are likely to be behaviorally harassed in a manner we consider Level B harassment when exposed to underwater anthropogenic noise above received levels of 120 decibels (dB) re 1 microPascal (μPa) (root mean square (rms)) for continuous (e.g., vibratory pile-driving, drilling) and above 160 dB re 1 μPa (rms) for non-explosive impulsive (e.g., seismic airguns) or intermittent (e.g., scientific sonar) sources.

WETA's proposed activities include the use of continuous (vibratory pile driving) and impulsive (impact pile driving) sources, and therefore the 120 and 160 dB re 1 μPa (rms) are applicable.

Level A harassment for non-explosive sources—NMFS' Technical Guidance for Assessing the Effects of Anthropogenic Sound on Marine Mammal Hearing (Technical Guidance 2016) identifies dual criteria to assess auditory injury (Level A harassment) to five different marine mammal groups (based on hearing sensitivity) as a result of exposure to noise from two different types of sources (impulsive or non-impulsive). WETA's proposed activity includes the use of impulsive (impact pile driving) and non-impulsive (vibratory pile driving) sources.

These thresholds were developed by compiling and synthesizing the best available science and soliciting input multiple times from both the public and peer reviewers to inform the final product, and are provided in the table below. The references, analysis, and methodology used in the development of the thresholds are described in NMFS 2016 Technical Guidance, which may be accessed at http://www.nmfs.noaa.gov/pr/acoustics/guidelines.htm.

Here, we describe operational and environmental parameters of the activity that will feed into identifying the area ensonified above the acoustic thresholds.

Pile driving and removal generates underwater noise that can potentially result in disturbance to marine mammals in the project area. Transmission loss (TL) is the decrease in acoustic intensity as an acoustic pressure wave propagates out from a source. TL parameters vary with frequency, temperature, sea conditions, current, source and receiver depth, water depth, water chemistry, and bottom composition and topography. The general formula for underwater TL is:

Underwater Sound—The intensity of pile driving and removal sounds is greatly influenced by factors such as the type of piles, hammers, and the physical environment in which the activity takes place. A number of studies, primarily on the west coast, have measured sound produced during underwater pile driving projects. These data are largely for impact driving of steel pipe piles and concrete piles as well as vibratory driving of steel pipe piles.

In order to determine reasonable source levels and their associated effects on marine mammals that are likely to result from vibratory or impact pile driving or removal at the Project area, we considered existing measurements from similar physical environments (e.g., substrate of bay mud and water depths ranging from 14 to 38 feet).

The values used to calculate distances at which sound would be expected to exceed the Level A thresholds for impact driving of and 36-inch (in) and 42-in piles include peak values of 210 dB and anticipated SELs for unattenuated impact pile-driving of 183 dB, and peak values of 203 dB and SEL values of 177 for 24-in piles (Caltrans 2015a). Bubble curtains will be used during the installation of these piles, which is expected to reduce noise levels by about 10 dB rms (Caltrans 2015a), which are the values used in Table 3. Vibratory driving source levels include 175 dB RMS for 42-in piles, 170 dB RMS for 36-in piles, 160 dB RMS for 24-in piles, and 150 dB RMS for 14-in H piles (Caltrans 2015a). The inputs for the user spreadsheet from NMFS' Guidance are as follows: For impact driving, 450 strikes per pile with 3 piles per day for 24-in piles, and 600 strikes per pile with 2 piles per day for 36-in and 42-in piles. The total duration for vibratory driving of 14-in, 24-in, 36-in, and 42-in piles were all approximately 10 minutes (0.166666, 0.1708333 hours, 0.16666 hours, and 0.177777 hours, respectively).

Approximately 15 steel piles, 42-in in diameter, will be installed, with approximately 2 installed per day over 8 days. The source level for this pile size during impact driving came from the Caltrans summary table (Caltrans 2015a) for “loudest” values for 36 in piles at approximately 10 m depth.

Approximately 6 steel piles, 36-in in diameter, will be installed, with approximately 2 installed per day over 3 days. The source level for this pile size during impact driving came from the Caltrans summary table (Caltrans 2015a) for “typical” values for 36 in piles at approximately 10 m depth.

Approximately 8 steel piles, 24-in in diameter, will be installed, with approximately 3 installed per day over 3 days. The source level for this pile size during impact driving came from the Caltrans summary table (Caltrans 2015a) for 24 in piles at approximately 5 meter depth. The source level for this pile size during vibratory driving came from the Caltrans table for the Trinidad Pier Reconstruction project (Caltrans 2015a).

Approximately 20 14-in H piles (10 temporary and 10 permanent), with approximately 5 installed or removed per day over 8 days. The source level for this pile size during impact and vibratory driving came from the Caltrans summary table (Caltrans 2015a) for 10 in H piles.

Tables 3 and 4 show the expected underwater sound levels for pile driving activities and the estimated distances to the Level A (Table 3) and Level B (Table 4) thresholds.

When NMFS Technical Guidance (2016) was published, in recognition of the fact that ensonified area/volume could be more technically challenging to predict because of the duration component in the new thresholds, we developed a User Spreadsheet that includes tools to help predict a simple isopleth that can be used in conjunction with marine mammal density or occurrence to help predict takes. We note that because of some of the assumptions included in the methods used for these tools, we anticipate that isopleths produced are typically going to be overestimates of some degree, which will result in some degree of overestimate of Level A take. However, these tools offer the best way to predict appropriate isopleths when more sophisticated 3D-modeling methods are not available, and NMFS continues to develop ways to quantitatively refine these tools, and will qualitatively address the output where appropriate. For stationary sources (such as WETA's Project), NMFS User Spreadsheet predicts the closest distance at which, if a marine mammal remained at that distance the whole duration of the activity, it would not incur PTS. Inputs used in the User Spreadsheet, and the resulting isopleths are reported below.

Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.) direct the Secretary of Commerce (as delegated to NMFS) to allow, upon request, the incidental, but not intentional, taking of small numbers of marine mammals by U.S. citizens who engage in a specified activity (other than commercial fishing) within a specified geographical region if certain findings are made and either regulations are issued or, if the taking is limited to harassment, a notice of a proposed authorization is provided to the public for review.

An Incidental Take Authorization (ITA) shall be granted if NMFS finds that the taking will have a negligible impact on the species or stock(s), will not have an unmitigable adverse impact on the availability of the species or stock(s) for subsistence uses (where relevant), and if the permissible methods of taking and requirements pertaining to the mitigation, monitoring and reporting of such takings are set forth.

NMFS has defined “negligible impact” in 50 CFR 216.103 as an impact resulting from the specified activity that cannot be reasonably expected to, and is not reasonably likely to, adversely affect the species or stock through effects on annual rates of recruitment or survival.

The MMPA states that the term “take” means to harass, hunt, capture, kill or attempt to harass, hunt, capture, or kill any marine mammal.

Except with respect to certain activities not pertinent here, the MMPA defines “harassment” as any act of pursuit, torment, or annoyance which (i) has the potential to injure a marine mammal or marine mammal stock in the wild (Level A harassment); or (ii) has the potential to disturb a marine mammal or marine mammal stock in the wild by causing disruption of behavioral patterns, including, but not limited to, migration, breathing, nursing, breeding, feeding, or sheltering (Level B harassment).

To comply with the National Environmental Policy Act (NEPA) of 1969 (NEPA; 42 U.S.C. 4321 et seq.) and NOAA Administrative Order (NAO) 216-6A, NMFS must review our proposed action (i.e., the issuance of an incidental harassment authorization) with respect to environmental consequences on the human environment.

This action is consistent with categories of activities identified in CE B4 of the Companion Manual for NOAA Administrative Order 216-6A, which do not individually or cumulatively have the potential for significant impacts on the quality of the human environment and for which we have not identified any extraordinary circumstances that would preclude this categorical exclusion. Accordingly, NMFS has preliminarily determined that the issuance of the proposed IHA qualifies to be categorically excluded from further NEPA review.

We will review all comments submitted in response to this notice prior to concluding our NEPA process or making a final decision on the IHA request.

On March 31, 2017, NMFS received a request from the FAA for an IHA to take marine mammals incidental to pile driving and removal and down the hole (DTH) drilling in association with the Biorka Island Dock Replacement Project (Project) in Symonds Bay, Alaska. The FAA's request is for take of five species by Level A and Level B harassment. Neither the FAA nor NMFS expect mortality to result from this activity and, therefore, an IHA is appropriate.

In-water work associated with the in-water construction is expected to be completed within 70 days. This proposed IHA is for the 2018 construction window (May 1, 2018 through September 30, 2018). This IHA would be valid from May 1, 2018, through April 30, 2019.

The FAA is constructing a replacement dock on Biorka Island in Symonds Bay near Sitka, Alaska. The purpose of the Project is to improve and maintain the sole point of access to Biorka Island and the navigational and weather facilities located on the Island. The existing dock is deteriorated and has reached the end of its useful life. Regular and repetitive heavy surging seas, along with constant use have destroyed the face of the existing floating marine dock, and have broken cleats making it difficult to tie a vessel to the existing dock. In its present condition, small vessels cannot use the dock to provide supplies to facilities on the Island. The existing barge landing area is reinforced seasonally by adding fill to the landing at the shoreline, which is periodically washed away by storms and wave action. The Project would reconstruct the deteriorated existing dock and construct an improved barge landing area.

The total Project is expected to require a maximum of 70 days of in-water construction activities. In-water activities are limited to occurring between May 1 and September 30 of any year to minimize impacts to special-status and commercially and biologically important fish species. This proposed authorization would be effective from May 1, 2018 through April 30, 2019.

The Project is located approximately 15 miles (24 kilometers (km)) southwest of Sitka on the northern shore of Biorka Island on land owned by the FAA (see Figure 1-1 of the FAA's application). Biorka Island is the most westerly and largest of the Necker Island group on the west coast of Baranof Island.

Symonds Bay is approximately 0.4 miles wide (east to west direction). Water depths are less than 66 feet (ft) within 1,300 ft of the dock (see Figure 1-2 of the FAA's application). The outer dolphin (see Figure 1-4 of the application) would be located in about 20 ft of water at mean high water. This is the deepest water depth for all piles and, as a precautionary measure, was used as the water depth input for acoustic modeling described later in this document.

On shore at the Project site, bedrock is exposed in many places. The overburden varies from zero to about 15 ft deep and consists of highly fractured weathered bedrock and includes seams of very soft rock or soil. Due to the fractures and seams, it is possible to drive piles into this top layer “Category 1 intensely fractured bedrock.” Beneath the top layer, the rock becomes more intact “Category II intensely to moderately fractured bedrock.” The seabed composition is important in this Project because it determines the pile-driving methods needed to achieve the required pile penetration.

The Project consists of removing the existing dock and associated infrastructure and constructing a new, modern structure to provide continued safe access to Biorka Island facilities. The existing dock is a T-shaped, pile-supported structure consisting of a 170-ft long by 16-ft wide approach trestle with a 51-ft wide by 35-ft long end section. The existing infrastructure also includes a 30-ft by 32-ft floating dock that is accessed by a 5-ft wide by 50-ft long steel gangway, a small 10-ft by 10-ft pre-fabricated building, and an electric hydraulic pedestal crane.

A total of 46 existing piles would be removed (Table 1). The steel and timber piles would be pulled out of the substrate directly with a crane and sling, by using a vibratory hammer, or with a clamshell bucket. The three concrete piles that are located above the high tide were cast in place. The concrete piles are set in bedrock and will be removed at low tide using standard excavation equipment. Therefore, removal of these piles will not produce underwater noise. The construction contractor would determine the exact method for concrete pile removal.

The existing deck and other associated infrastructure would also be disassembled and removed. The existing 4-ton pedestal crane would be salvaged for relocation on the new dock. As necessary, portions of the existing rubble mound/breakwater would be removed to provide enough clearance for construction and then replaced once the dock has been constructed.

Facilities for the new dock consist of three main structures: A barge landing platform, a dock/trestle, and two dolphin fenders located near the dock outer corners (Figure 1-4 of the FAA's application). For these structures, temporary piles would be installed to form a scaffold system (i.e., a template) that permits the permanent piles to be aligned and controlled. With the exception of the temporary piles, which are driven exclusively by vibratory pile driving, the installation of all permanent piles requires a combination of pile driving methods.

Construction of the new dock would begin with the erection of a temporary template. The construction contractor would determine the specific type and size of template piles based on site conditions and availability of materials. The template piles would be driven into the overburden by vibratory hammer and removed after the permanent piles are installed. Table 2 shows the anticipated number of template piles for the Project.

The new trestle approach would be up to 25-ft wide. An 80-ft aluminum gangway connecting to a 15-ft wide by 32-ft long small craft berthing float would also be constructed (see Figure 1-4 of the FAA's application). The face of the dock would be approximately 54-ft long and 35-ft wide. Similar to the trestle, steel pipe pilings would support a precast concrete deck. Two berthing dolphin fenders would be installed, one at each end section of the new dock. These dolphins each consist of one 30-in diameter plumb pile and two 18-in diameter batter piles. Some piles would require internal tension anchors for increased support. A wave barrier, consisting of Z-sheet piles in between steel H piles, would be installed at the face of the dock. Pile counts, sizes, and other details are shown in Table 2.

All permanent pipe piles would be installed using a combination of vibratory and impact hammering methods to drive the pile into the overburden. Pipe piles would then be drilled and socketed into the underlying bedrock using DTH hammering/drilling techniques. DTH equipment breaks up the rock below the pile while simultaneously installing the pile through rock formation. The pile is then set/confirmed with a few strikes of an impact hammer. Sheet piles would be driven into the overburden and set into the top layer of bedrock using a combination of vibratory and impact hammering.

Certain piles would require internal tension anchors. Up to eight of the dock piles and all six piles for the dolphins would require these internal tension anchors. Each pile with a tension anchor would first be drilled, socketed into bedrock, and proof driven with an impact hammer as described above for permanent piles. Then a separate smaller drill would be used to complete an approximately 5-in diameter hole extending about 30- to 40-ft into bedrock below the tip of the pile. A steel bar would be grouted into this hole. Once the grout sets, a jack would be applied to the top of the bar and the tensioned rod would be locked off to plates at the top of the pile.

The wave barrier consisting of steel H piles with Z sheets in between is located at the face of the dock. The H piles and Z sheets would be initially driven through overlying sediment with a vibratory hammer, and set into the bedrock with an impact hammer. The wave barrier sheet piling would be driven either singly or in preassembled pairs.

The current barge landing is located northwest of the existing dock and is comprised of gravel and cobbles with no formal structure. The uplands area on the west end of the trestle would be slightly graded into the existing terrestrial approach. The existing barge landing would be upgraded to a 30-ft by 90-ft precast concrete plank landing placed over fill, with a perimeter constructed of concrete, sheet piles, and 18-in steel piles (see Table 2). Similar to the wave barrier, the sequence for installing the permanent barge ramp pipe piles would begin with advancement through overlying sediment with a vibratory hammer, followed by use of an impact hammer to drive the piles into bedrock.

Vibratory hammers are commonly used in steel pile driving or removal where sediments allow. Generally, the pile is placed into position using a choker and crane, and then vibrated between 1,200 and 2,400 vibrations per minute. The vibrations liquefy the sediment surrounding the pile allowing it to penetrate to the required seating depth, or to be removed.

Impact hammers are used to install plastic/steel core, wood, concrete, or steel piles. An impact hammer is a steel device that works like a piston. The pile is first moved into position and set in the proper location using a choker cable or vibratory hammer. The impact hammer is held in place by a guide (lead) that aligns the hammer with the pile. A heavy piston moves up and down, striking the top of the pile and driving it into the substrate. Once the pile is set in place, pile installation with an impact hammer can take less than 15 minutes under good substrate conditions. However, under poor conditions, such as glacial till and bedrock or exceptionally loose material, piles can take longer to set.

The DTH drill/hammer acts on a shoe at the bottom of the pile and uses a pulsing mechanism to break up rock below the pile while simultaneously installing the pile through the rock formation. Rotating bit wings extend below the pile and remove the broken rock fragments as the pile advances. The pulsing sounds produced by the DTH hydro-hammer method reduces sound attenuation because the noise is primarily contained within the steel pile and below ground rather than impact hammer driving methods which occur at the top of the pile (R&M 2016). Therefore, the pulsing sounds produced by this method are considered less harmful than those produced by impact hammer driving. Table 3 provides a summary of the six methods of construction (“scenarios”) used in the modeling of the zone of influence (ZOI)s for the Biorka Project.

Proposed mitigation, monitoring, and reporting measures are described in detail later in this document (please see Proposed Mitigation and Proposed Monitoring and Reporting).

There are five marine mammal species that may likely transit through the waters nearby the Project area, and are expected to potentially be taken by the specified activity. These include the Steller sea lion (Eumetopias jubatus), harbor seal (Phoca vitulina), harbor porpoise (Phocoena phocoena), killer whale (Orcinus orca), and humpback whale (Megaptera noviaeangliae). Multiple additional marine mammal species may occasionally enter Sitka sound but would not be expected to occur in shallow nearshore waters of the action area.

Sections 3 and 4 of the FAA's application summarize available information regarding status and trends, distribution and habitat preferences, and behavior and life history, of the potentially affected species. Additional information regarding population trends and threats may be found in NMFS's Stock Assessment Reports (SAR; www.nmfs.noaa.gov/pr/sars/) and more general information about these species (e.g., physical and behavioral descriptions) may be found on NMFS's Web site (www.nmfs.noaa.gov/pr/species/mammals/).

Table 4 lists all species with expected potential for occurrence in Symonds Bay and Sitka Sound and summarizes information related to the population or stock, including potential biological removal (PBR), where known. For taxonomy, we follow Committee on Taxonomy (2016). PBR is defined by the MMPA as the maximum number of animals, not including natural mortalities, that may be removed from a marine mammal stock while allowing that stock to reach or maintain its optimum sustainable population (as described in NMFS's SARs). While no mortality is anticipated or authorized here, PBR and annual serious injury and mortality are included here as gross indicators of the status of the species and other threats.

Species that could potentially occur in the proposed survey areas, but are not expected to have reasonable potential to be harassed by in-water construction, are described briefly but omitted from further analysis. These include extralimital species, which are species that do not normally occur in a given area but for which there are one or more occurrence records that are considered beyond the normal range of the species. Gray whales are observed in and outside of Sitka Sound during their northward spring migration; however, they occur generally north and west of the Project area in outer shelf waters of Sitka Sound near Kruzof Island during the construction window. Dall's porpoise are observed in mid- to outer-shelf coastal waters of Sitka Sound ranging to the Gulf of Alaska and are not expected to occur in the Project area during the construction window. Pacific white-sided dolphins occur in the outer-shelf slope in the Gulf of Alaska, which is outside of the Project area. During the construction window, they are considered rare in Sitka Sound. Sperm whales generally occur in deeper waters in the Gulf of Alaska, which is outside of the Project area. We do not anticipate gray whales, Dall's porpoise, Pacific white-sided dolphins, or sperm whales to be affected by Project activities; therefore, we do not discuss these species further. For status of species, we provide information regarding U.S. regulatory status under the MMPA and Endangered Species Act (ESA).

Marine mammal abundance estimates presented in this document represent the total number of individuals that make up a given stock or the total number estimated within a particular study area. NMFS's stock abundance estimates for most species represent the total estimate of individuals within the geographic area, if known, that comprises that stock. For some species, this geographic area may extend beyond U.S. waters. All managed stocks in this region are assessed in NMFS's U.S. Pacific SARs (Muto et al., 2017). All values presented in Table 4 are the most recent available at the time of publication and are available in the 2016 SARs (Muto et al., 2017).

Below, for those species that are likely to be taken by the activities described, we offer a brief introduction to the species and relevant stock. We also provide information regarding population trends and threats, and describe any information regarding local occurrence.

In Southeast Alaska, marine mammal distributions and seasonal increases in their abundance are strongly influenced by seasonal pre-spawning and spawning aggregations of forage fish, particularly Pacific herring (Clupea pallasii), eulachon (Thaleichthys pacificus) and Pacific salmon (Onchorynchus spp.) (Marston et al., 2002, Sigler et al., 2004, Womble et al., 2005; USACE 2013). All five species of salmon are found in Sitka Sound and are preyed upon by Steller sea lions, harbor seals, and killer whales. However, there are no salmon spawning streams in the vicinity of the Project or presence of eulachon or herring during the construction time period that would tend to aggregate foraging marine mammals.

Herring are the keystone species in Southeast Alaska, especially Sitka Sound, serving as a vital link between lower trophic levels, including crustaceans and small fish, and higher trophic levels (NMFS 2014a). Foraging studies of Steller sea lions suggest that during their non-breeding season, they forage on seasonally densely aggregated prey (Sinclair and Zepplin 2002). In southeast Alaska, Pacific herring typically spawn from March to May and attract large numbers of predators (Marston et al., 2002, Womble 2003). The relationship between humpback whales and Steller sea lions and these ephemeral fish runs is so strong in Sitka Sound that the seasonal abundance and distribution of marine mammals reflects the distribution of pre-spawning and spawning herring, and overwintering aggregations of adult herring in Sitka Sound. The largest aggregations of several species of marine mammals in the Action Area target Pacific herring during spring and again in late fall through the winter. Pacific herring are largely absent from Sitka Sound and the Action Area from May, following spawning season, until at least October, prior to adult overwintering in Sitka Sound (NMFS 2014a).

Steller sea lions are divided in to two distinct population segments (DPSs): The western DPS (wDPS) and the eastern DPS (eDPS). The wDPS is listed as endangered under the ESA. The wDPS breeds on rookeries located west of 144° W. in Alaska and Russia, whereas the eDPS breeds on rookeries in southeast Alaska through California. The majority of Steller sea lions are part of the non-listed eDPS. The best available information indicates the eDPS has increased at a rate of 4.18 percent per year between 1979 and 2010 (Allen and Angliss 2014). Steller sea lions range from the North Pacific Rim from northern Japan to California, with centers of abundance located in the Gulf of Alaska and Aleutian Islands. Large numbers of individuals disperse widely outside of the breeding season (late May to early July), thus potentially intermixing with animals from other areas to access seasonally important prey resources (Allen and Angliss 2014). The distinction between western and eastern DPS individuals cannot be confirmed unless an animal has been marked, and since guidance on how to otherwise distinguish between the two DPSs is not available, for this IHA it is assumed that 50 percent of the Steller sea lions observed in the Project area are from each DPS.

Critical habitat for Steller sea lions includes designated haulouts within the range of the eDPS, and all marine waters within 20 nautical miles of rookeries and haulouts within the breeding range of the wDPS and within three special aquatic foraging areas in Alaska (NMFS 1993). In identifying aquatic habitats as part of critical habitat, NMFS specifically highlighted several components of such habitats: Nearshore waters around rookeries and haulouts; traditional rafting sites; food resources; and foraging habitats. Adequate food resources are an essential feature of the Steller sea lion's aquatic habitat (NMFS 1993). The closest haulout/rookery to the Project area that has been designated as a Steller sea lion critical habitat is listed as “Biorka Island” in the critical habitat descriptions. However, the haulout is actually on Kaiuchali Island, a three-acre rocky islet located slightly less than one mile southwest of Biorka Island, outside of the ZOI for this project.

This species occurs in coastal and nearshore habitats of Sitka Sound, and forage on herring and salmon throughout the Sound. Both DPSs occur in the Project area on a year-round basis. Kaiuchali Island is used as a sea lion rookery in spring-summer and as a haulout during the non-breeding seasons (Fritz et al. 2016). Based on results of recent aerial surveys, there has been an increase of sea lions that use Kaiuchali Island during both the breeding and non-breeding seasons. In June 2013, Fritz et al., (2016) documented 22 individuals, none of which were pups. In June 2015, the same study recorded 77 Steller sea lions, including one pup. This limited information shows an increase in the numbers of animals at this location and indicates that the site has become a recently-established eDPS rookery.

The breeding season for Steller sea lions does not overlap with proposed summer construction activity at the Project site, and the location of the rookery at Kaiuchali Island is outside the Project area, opposite Biorka Island. The late fall and overwintering aggregation of adult herring results in hundreds of animals using Kaiuchali Island as a haulout during this period; however, the construction period for the proposed Project would not overlap with the overwintering aggregations of sea lions. Steller sea lions are present in Sitka Sound in very low numbers over the summer months when construction is planned, during the interval between herring spawning and the return of adult herring to Sitka Sound. Prey availability for Steller sea lions in Sitka Sound is limited during this period as compared to other seasons, and they are generally only observed by the whale watch industry as individuals or in small groups of three to five animals. During this period, sea lions tend to forage in the vicinity of recreational and commercial fishing vessels, or scavenge in very shallow waters near the Sitka town docks when the vessels return from fishing.

Harbor seals inhabit coastal and estuarine waters off Alaska. Harbor seals in Southeast Alaska are considered non-migratory with local movements attributed to factors such as prey availability, weather, and reproduction. In 2010, NMFS identified 12 stocks of harbor seals in Alaska based on genetic structure (Allen and Angliss 2015). The Sitka/Chatham (S/C) stock is genetically distinct and believed to be year-round residents of the region. Although generally solitary in the water, harbor seals congregate at haulouts to rest, socialize, breed, and molt. Habitats used as haul-out sites include tidal rocks, bayflats, sandbars, and sandy beaches (Zeiner et al., 1990).

Harbor seals are opportunistic feeders that forage on fish and invertebrates and often adjust their distribution to take advantage of locally and seasonally abundant prey. Aggregations of adult herring during spring pre-spawning and spawning runs, and again from October throughout the winter, are a very important seasonal prey species for harbor seals in Sitka Sound. The minimum count of harbor seals within Sitka Sound during the 2011 aerial survey was approximately 900 individuals occupying 25 haulout locations (unpublished data from MML dataset). The largest count of seals in Sitka Sound (n = 745) during the 2011 survey occurred at several adjacent rocky outcroppings and islands (Vitskari Rocks, Vitskari Island and Low Island) located approximately 15 miles (24 km) north of the Project site in northcentral Sitka Sound inside Kruzof Island. This is outside of the Project Area. Prey species moving into Sitka Sound from the Gulf of Alaska move past these islands so pinnipeds aggregate at these rocks to forage. There are six haul-out locations identified in the extreme southern portion of the Sitka Sound, and potentially in the Project Area, including rocky outcroppings near Biorka Island, where seals have been observed in low numbers. Prey resources inside Symonds Bay are limited, particularly when compared to the northern coastal areas of Sitka Sound. While individual seals may occur in Symonds Bay, it is unlikely that seals would be attracted to Symonds Bay to forage. While their occurrence in the Action Area is possible, it is infrequent to uncommon and only small numbers of approximately five animals per day are expected to potentially be in the Project area during the construction window.

In the Pacific, harbor porpoise are found in coastal and inland waters from Point Conception, California to Alaska and across to Kamchatka and Japan (Gaskin 1984). Harbor porpoise appear to have more restricted movements along the western coast of the continental U.S. than along the eastern coast. In the Gulf of Alaska and Southeast Alaska they are observed most frequently in waters less than 350 ft (107 m) deep (Dahlheim et al., 2009). There are three harbor porpoise stocks in Alaska: The Bering Sea Stock; the Southeast Alaska Stock; and the Gulf of Alaska Stock (Angliss and Allen 2015). Only the Southeast Alaska stock occurs in the Project area. The mean group size of harbor porpoise in Southeast Alaska is estimated at two to three individuals (Dahlheim et al., 2009).

This species can be found in Sitka Sound throughout the year but individuals are infrequently observed during the summer months by the whale watching industry. Harbor porpoise are infrequently observed in nearshore Sitka Sound areas in summer by hikers on the coastal trails that parallel the coastline near Sitka. At times throughout the year, they likely forage exclusively on herring and may be more abundant when herring are present. During surveys for seabirds, marine mammals and forage fish conducted in Sitka Sound during July 2000, relatively few marine mammals were observed during this period. However, one harbor porpoise was observed in coastal/shelf waters of northeast Sitka Sound (Piatt and Dragoo 2005).

Killer whales are found throughout the North Pacific. Along the west coast of North America, killer whales occur along the entire Alaskan coast, in British Columbia and Washington inland waterways, and along the outer coasts of Washington, Oregon, and California (Allen and Angliss 2014). Seasonal and year-round occurrence has been documented for killer whales throughout Alaska and in the intra-coastal waterways of British Columbia and Washington State.

Killer whales that are observed in Southeast Alaska could belong to one of three different stocks: Eastern North Pacific Northern Resident Stock (Northern residents); Gulf of Alaska, Aleutian Islands, and Bering Sea Transient Stock (Gulf of Alaska transients); or West Coast Transient Stock. The Gulf of Alaska Transient Stock occupies a range that includes southeastern Alaska. Resident killer whales do not occur in Sitka Sound. However, transient killer whales from either the Gulf of Alaska transient group or West Coast Transient Stock have been observed in the sound. These whales are observed infrequently during summer months with five to six sightings noted throughout the summer by the whale-watching industry. Dahlheim et al. (2009) found that transient killer whale mean group size ranged from four to six individuals in Southeast Alaska. Generally, transient killer whales follow movements of, and prey on, Steller sea lions and harbor seals. Killer whales have been observed in the waters outside of Sitka Sound near the haulouts at Kaiuchali Island and outside of Kruzof Island when sea lions are present. This behavioral distribution is characteristic of killer whales and consistent with killer whale sightings around other Steller sea lion haul-out locations in southeast Alaska (Dahlheim et al., 2009). Given the low numbers of Steller sea lions in Sitka Sound during summer, it is consistent that transient killer whales would be considered infrequent to uncommon in the Project area during these months.

Humpback whales were listed as endangered under the ESA in 1970. As a result of the ESA listing, the central North Pacific Stock of humpback whale was also designated as depleted under the MMPA. The humpback whale is also considered a strategic stock under the MMPA. NMFS proposed a revised species-wide listing of the humpback whale in 2015 and a revision to the status of humpback whale DPSs was finalized by NMFS on September 8, 2016 (NMFS 2016b), effective October 11, 2016. In the final decision, NMFS recognized the existence of 14 DPSs, classified four of those as endangered and one as threatened, and determined that the remaining nine DPSs do not warrant protection under the ESA. Three DPSs of humpback whales occur in waters off the coast of Alaska: The endangered Western North Pacific (WNP) DPS, the threatened Mexico DPS, and the Hawaii DPS, which is not listed under the ESA. Humpback whales in Southeast Alaska are most likely to be from the Hawaii DPS (93.9 percent probability) (Wade et al., 2016).

The humpback whales of Southeast Alaska and Northern British Columbia form a genetically discrete feeding aggregation and return to specific feeding locations in southeast Alaska including Sitka Sound. Humpback whale seasonal distribution varies from infrequent (very low in number during summer), to common (very abundant during late fall through spring). Humpback whales are most abundant in Sitka Sound from late fall through April when they forage on large densities of herring (Liddle et al., 2015a). The seasonal increase in whale abundance corresponds to increases in Pacific herring biomass during pre-spawning, spawning and overwintering periods (Liddle et al., 2015b). Whales feed on large schools of adult, over-wintering herring throughout winter, and on pre-spawning and spawning aggregations of herring in spring. Sitka Sound is believed to be a last feeding stop for humpback whales as they migrate to winter breeding and calving waters in Hawaii. During winter months, groups of 30 to 40 humpback whales have been observed by the whale watching industry from the coastline of Sitka Sound. However, humpback whales stagger their departure from the feeding grounds, suggesting they also stagger their return. This could create the impression that whales had been present throughout the entire winter in the sound when it is unlikely that any individual whale remains in Sitka Sound throughout the entire winter (Heintz et al., 2010). The abundance of humpbacks in Sitka Sound changes by several orders of magnitude from one season to another in response to dense schools of herring in the sound (Liddle et al., 2015b). They are generally present in large numbers from late fall-early winter through mid- to late-spring, but are infrequent to uncommon during the mid-summer months when herring are absent. During mid-summer, tour boat operators generally observe four to five whales per day near rocky islets in the middle of Sitka Sound.

This section includes a summary and discussion of the ways that components of the specified activity (e.g., sound produced by pile driving and removal) may impact marine mammals and their habitat. The Estimated Take by Incidental Harassment section later in this document will include a quantitative analysis of the number of individuals that are expected to be taken by this activity. The Negligible Impact Analysis section will consider the content of this section, the Estimated Take by Incidental Harassment section and the Proposed Mitigation section, to draw conclusions regarding the likely impacts of these activities on the reproductive success or survivorship of individuals and how those impacts on individuals are likely to impact marine mammal species or stocks.

Sound travels in waves, the basic components of which are frequency, wavelength, velocity, and amplitude. Frequency is the number of pressure waves that pass by a reference point per unit of time and is measured in hertz (Hz) or cycles per second. Wavelength is the distance between two peaks of a sound wave; lower frequency sounds have longer wavelengths than higher frequency sounds. Amplitude is the height of the sound pressure wave or the `loudness' of a sound and is typically measured using the decibel (dB) scale. A dB is the ratio between a measured pressure (with sound) and a reference pressure (sound at a constant pressure, established by scientific standards). It is a logarithmic unit that accounts for large variations in amplitude; therefore, relatively small changes in dB ratings correspond to large changes in sound pressure. When referring to sound pressure levels (SPLs; the sound force per unit area), sound is referenced in the context of underwater sound pressure to 1 microPascal (μPa). One pascal is the pressure resulting from a force of one newton exerted over an area of one square meter. The source level (SL) represents the sound level at a distance of 1 m from the source (referenced to 1 μPa). The received level is the sound level at the listener's position. Note that all underwater sound levels in this document are referenced to a pressure of 1 µPa and all airborne sound levels in this document are referenced to a pressure of 20 µPa.

Root mean square (rms) is the quadratic mean sound pressure over the duration of an impulse. Rms is calculated by squaring all of the sound amplitudes, averaging the squares, and then taking the square root of the average (Urick 1983). Rms accounts for both positive and negative values; squaring the pressures makes all values positive so that they may be accounted for in the summation of pressure levels (Hastings and Popper 2005). This measurement is often used in the context of discussing behavioral effects, in part because behavioral effects, which often result from auditory cues, may be better expressed through averaged units than by peak pressures.

When underwater objects vibrate or activity occurs, sound-pressure waves are created. These waves alternately compress and decompress the water as the sound wave travels. Underwater sound waves radiate in all directions away from the source (similar to ripples on the surface of a pond), except in cases where the source is directional. The compressions and decompressions associated with sound waves are detected as changes in pressure by aquatic life and man-made sound receptors such as hydrophones.

Even in the absence of sound from the specified activity, the underwater environment is typically loud due to ambient sound. Ambient sound is defined as environmental background sound levels lacking a single source or point (Richardson et al., 1995), and the sound level of a region is defined by the total acoustical energy being generated by known and unknown sources. These sources may include physical (e.g., waves, earthquakes, ice, atmospheric sound), biological (e.g., sounds produced by marine mammals, fish, and invertebrates), and anthropogenic sound (e.g., vessels, dredging, aircraft, construction). A number of sources contribute to ambient sound, including the following (Richardson et al., 1995):

• Wind and waves: The complex interactions between wind and water surface, including processes such as breaking waves and wave-induced bubble oscillations and cavitation, are a main source of naturally occurring ambient noise for frequencies between 200 Hz and 50 kilohertz (kHz) (Mitson 1995). In general, ambient sound levels tend to increase with increasing wind speed and wave height. Surf noise becomes important near shore, with measurements collected at a distance of 8.5 km from shore showing an increase of 10 dB in the 100 to 700 Hz band during heavy surf conditions.

• Precipitation: Sound from rain and hail impacting the water surface can become an important component of total noise at frequencies above 500 Hz, and possibly down to 100 Hz during quiet times.

• Biological: Marine mammals can contribute significantly to ambient noise levels, as can some fish and shrimp. The frequency band for biological contributions is from approximately 12 Hz to over 100 kHz.

• Anthropogenic: Sources of ambient noise related to human activity include transportation (surface vessels and aircraft), dredging and construction, oil and gas drilling and production, seismic surveys, sonar, explosions, and ocean acoustic studies. Shipping noise typically dominates the total ambient noise for frequencies between 20 and 300 Hz. In general, the frequencies of anthropogenic sounds are below 1 kHz and, if higher frequency sound levels are created, they attenuate rapidly (Richardson et al., 1995). Sound from identifiable anthropogenic sources other than the activity of interest (e.g., a passing vessel) is sometimes termed background sound, as opposed to ambient sound.

The sum of the various natural and anthropogenic sound sources at any given location and time—which comprise “ambient” or “background” sound—depends not only on the source levels (as determined by current weather conditions and levels of biological and shipping activity) but also on the ability of sound to propagate through the environment. In turn, sound propagation is dependent on the spatially and temporally varying properties of the water column and sea floor, and is frequency-dependent. As a result of the dependence on a large number of varying factors, ambient sound levels can be expected to vary widely over both coarse and fine spatial and temporal scales. Sound levels at a given frequency and location can vary by 10-20 dB from day to day (Richardson et al., 1995). The result is that, depending on the source type and its intensity, sound from the specified activity may be a negligible addition to the local environment or could form a distinctive signal that may affect marine mammals.

In-water construction activities associated with the Project would include impact pile driving, vibratory pile driving and removal, and DTH drilling. The sounds produced by these activities fall into one of two general sound types: Pulsed and non-pulsed (defined in the following). The distinction between these two sound types is important because they have differing potential to cause physical effects, particularly with regard to hearing (e.g., Ward 1997 in Southall et al., 2007). Please see Southall et al., (2007) for an in-depth discussion of these concepts.

Pulsed sound sources (e.g., explosions, gunshots, sonic booms, impact pile driving) produce signals that are brief (typically considered to be less than one second), broadband, atonal transients (ANSI 1986; Harris 1998; NIOSH 1998; ISO 2003; ANSI 2005) and occur either as isolated events or repeated in some succession. Pulsed sounds are all characterized by a relatively rapid rise from ambient pressure to a maximal pressure value followed by a rapid decay period that may include a period of diminishing, oscillating maximal and minimal pressures, and generally have an increased capacity to induce physical injury as compared with sounds that lack these features.

Non-pulsed sounds can be tonal, narrowband, or broadband, brief or prolonged, and may be either continuous or non-continuous (ANSI 1995; NIOSH 1998). Some of these non-pulsed sounds can be transient signals of short duration but without the essential properties of pulses (e.g., rapid rise time). Examples of non-pulsed sounds include those produced by vessels, aircraft, machinery operations such as drilling or dredging, vibratory pile driving, and active sonar systems (such as those used by the U.S. Navy). The duration of such sounds, as received at a distance, can be greatly extended in a highly reverberant environment.

Impact hammers operate by repeatedly dropping a heavy piston onto a pile to drive the pile into the substrate. Sound generated by impact hammers is characterized by rapid rise times and high peak levels, a potentially injurious combination (Hastings and Popper 2005). Vibratory hammers install piles by vibrating them and allowing the weight of the hammer to push them into the sediment. Vibratory hammers produce significantly less sound than impact hammers. Peak SPLs may be 180 dB or greater, but are generally 10 to 20 dB lower than SPLs generated during impact pile driving of the same-sized pile (Oestman et al., 2009). Rise time is slower, reducing the probability and severity of injury, and sound energy is distributed over a greater amount of time (Nedwell and Edwards 2002; Carlson et al., 2005).

Hearing is the most important sensory modality for marine mammals, and exposure to sound can have deleterious effects. To appropriately assess these potential effects, it is necessary to understand the frequency ranges marine mammals are able to hear. Current data indicate that not all marine mammal species have equal hearing capabilities (e.g., Richardson et al., 1995; Wartzok and Ketten, 1999; Au and Hastings, 2008). To reflect this, Southall et al. (2007) recommended that marine mammals be divided into functional hearing groups based on measured or estimated hearing ranges on the basis of available behavioral data, audiograms derived using auditory evoked potential techniques, anatomical modeling, and other data. The lower and/or upper frequencies for some of these functional hearing groups have been modified from those designated by Southall et al. (2007). The marine mammal hearing groups and the associated frequencies are indicated below in Table 5 (note that these frequency ranges do not necessarily correspond to the range of best hearing, which varies by species).

As mentioned previously in this document, five marine mammal species (three cetaceans and two pinnipeds) may occur in the Project area. Of these three cetaceans, one is classified as a low-frequency cetacean (i.e. humpback whale), one is classified as a mid-frequency cetacean (i.e., killer whale), and one is classified as a high-frequency cetacean (i.e., harbor porpoise) (Southall et al., 2007). Additionally, harbor seals are classified as members of the phocid pinnipeds in water functional hearing group, while Steller sea lions are grouped under the Otariid pinnipeds in water functional hearing group. A species' functional hearing group is a consideration when we analyze the effects of exposure to sound on marine mammals.

Please refer to the information given previously (Description of Sound Sources) regarding sound, characteristics of sound types, and metrics used in this document. Anthropogenic sounds cover a broad range of frequencies and sound levels and can have a range of highly variable impacts on marine life, from none or minor to potentially severe responses, depending on received levels, duration of exposure, behavioral context, and various other factors. The potential effects of underwater sound from active acoustic sources can potentially result in one or more of the following; temporary or permanent hearing impairment, non-auditory physical or physiological effects, behavioral disturbance, stress, and masking (Richardson et al., 1995; Gordon et al., 2004; Nowacek et al., 2007; Southall et al., 2007; Gotz et al., 2009). The degree of effect is intrinsically related to the signal characteristics, received level, distance from the source, and duration of the sound exposure. In general, sudden, high level sounds can cause hearing loss, as can longer exposures to lower level sounds. Temporary or permanent loss of hearing will occur almost exclusively for noise within an animal's hearing range. We first describe specific manifestations of acoustic effects before providing discussion specific to the FAA's construction activities.

Richardson et al. (1995) described zones of increasing intensity of effect that might be expected to occur, in relation to distance from a source and assuming that the signal is within an animal's hearing range. First is the area within which the acoustic signal would be audible (potentially perceived) to the animal, but not strong enough to elicit any overt behavioral or physiological response. The next zone corresponds with the area where the signal is audible to the animal and of sufficient intensity to elicit behavioral or physiological responsiveness. Third is a zone within which, for signals of high intensity, the received level is sufficient to potentially cause discomfort or tissue damage to auditory or other systems. Overlaying these zones to a certain extent is the area within which masking (i.e., when a sound interferes with or masks the ability of an animal to detect a signal of interest that is above the absolute hearing threshold) may occur; the masking zone may be highly variable in size.

We describe the more severe effects (i.e., permanent hearing impairment, certain non-auditory physical or physiological effects) only briefly as we do not expect that there is a reasonable likelihood that the FAA's activities may result in such effects (see below for further discussion). Marine mammals exposed to high-intensity sound, or to lower-intensity sound for prolonged periods, can experience hearing threshold shift (TS), which is the loss of hearing sensitivity at certain frequency ranges (Kastak et al., 1999; Schlundt et al., 2000; Finneran et al., 2002, 2005b). TS can be permanent (PTS), in which case the loss of hearing sensitivity is not fully recoverable, or temporary (TTS), in which case the animal's hearing threshold would recover over time (Southall et al., 2007). Repeated sound exposure that leads to TTS could cause PTS. In severe cases of PTS, there can be total or partial deafness, while in most cases the animal has an impaired ability to hear sounds in specific frequency ranges (Kryter 1985).

When PTS occurs, there is physical damage to the sound receptors in the ear (i.e., tissue damage), whereas TTS represents primarily tissue fatigue and is reversible (Southall et al., 2007). In addition, other investigators have suggested that TTS is within the normal bounds of physiological variability and tolerance and does not represent physical injury (e.g., Ward 1997). Therefore, NMFS does not consider TTS to constitute auditory injury.

Relationships between TTS and PTS thresholds have not been studied in marine mammals—PTS data exists only for a single harbor seal (Kastak et al., 2008)—but are assumed to be similar to those in humans and other terrestrial mammals. PTS typically occurs at exposure levels at least several dB above a 40-dB threshold shift approximates PTS onset; (e.g., Kryter et al., 1966; Miller, 1974) that inducing mild TTS (a 6-dB threshold shift approximates TTS onset; e.g., Southall et al., 2007). Based on data from terrestrial mammals, a precautionary assumption is that the PTS thresholds for impulse sounds (such as impact pile driving pulses as received close to the source) are at least 6 dB higher than the TTS threshold on a peak-pressure basis and PTS cumulative sound exposure level thresholds are 15 to 20 dB higher than TTS cumulative sound exposure level thresholds (Southall et al., 2007). Given the higher level of sound or longer exposure duration necessary to cause PTS as compared with TTS, it is considerably less likely that PTS could occur.

Non-auditory physiological effects or injuries that theoretically might occur in marine mammals exposed to high level underwater sound or as a secondary effect of extreme behavioral reactions (e.g., change in dive profile as a result of an avoidance reaction) caused by exposure to sound include neurological effects, bubble formation, resonance effects, and other types of organ or tissue damage (Cox et al., 2006; Southall et al., 2007; Zimmer and Tyack 2007). The FAA's activities do not involve the use of devices such as explosives or mid-frequency active sonar that are associated with these types of effects.

When a live or dead marine mammal swims or floats onto shore and is incapable of returning to sea, the event is termed a “stranding” (16 U.S.C. 1421h(3)). Marine mammals are known to strand for a variety of reasons, such as infectious agents, biotoxicosis, starvation, fishery interaction, ship strike, unusual oceanographic or weather events, sound exposure, or combinations of these stressors sustained concurrently or in series (e.g., Geraci et al., 1999). However, the cause or causes of most strandings are unknown (e.g., Best 1982). Combinations of dissimilar stressors may combine to kill an animal or dramatically reduce its fitness, even though one exposure without the other would not be expected to produce the same outcome (e.g., Sih et al., 2004). For further description of stranding events see, e.g., Southall et al., 2006; Jepson et al., 2013; Wright et al., 2013.

1. Temporary threshold shift—TTS is the mildest form of hearing impairment that can occur during exposure to sound (Kryter 1985). While experiencing TTS, the hearing threshold rises, and a sound must be at a higher level in order to be heard. In terrestrial and marine mammals, TTS can last from minutes or hours to days (in cases of strong TTS). In many cases, hearing sensitivity recovers rapidly after exposure to the sound ends. Few data on sound levels and durations necessary to elicit mild TTS have been obtained for marine mammals.

Marine mammal hearing plays a critical role in communication with conspecifics, and interpretation of environmental cues for purposes such as predator avoidance and prey capture. Depending on the degree (elevation of threshold in dB), duration (i.e., recovery time), and frequency range of TTS, and the context in which it is experienced, TTS can have effects on marine mammals ranging from discountable to serious. For example, a marine mammal may be able to readily compensate for a brief, relatively small amount of TTS in a non-critical frequency range that occurs during a time where ambient noise is lower and there are not as many competing sounds present. Alternatively, a larger amount and longer duration of TTS sustained during a time when communication is critical for successful mother/calf interactions could have more serious impacts.

Currently, TTS data only exist for four species of cetaceans (bottlenose dolphin (Tursiops truncatus), beluga whale (Delphinapterus leucas), harbor porpoise, and Yangtze finless porpoise (Neophocoena asiaeorientalis)) and three species of pinnipeds (northern elephant seal, harbor seal, and California sea lion) exposed to a limited number of sound sources (i.e., mostly tones and octave-band noise) in laboratory settings (e.g., Finneran et al., 2002; Nachtigall et al., 2004; Kastak et al., 2005; Lucke et al., 2009; Popov et al., 2011). In general, harbor seals (Kastak et al., 2005; Kastelein et al., 2012a) and harbor porpoises (Lucke et al., 2009; Kastelein et al., 2012b) have a lower TTS onset than other measured pinniped or cetacean species. Additionally, the existing marine mammal TTS data come from a limited number of individuals within these species. There are no data available on noise-induced hearing loss for mysticetes. For summaries of data on TTS in marine mammals or for further discussion of TTS onset thresholds, please see Southall et al. (2007) and Finneran and Jenkins (2012).

2. Behavioral effects—Behavioral disturbance may include a variety of effects, including subtle changes in behavior (e.g., minor or brief avoidance of an area or changes in vocalizations), more conspicuous changes in similar behavioral activities, and more sustained and/or potentially severe reactions, such as displacement from or abandonment of high-quality habitat. Behavioral responses to sound are highly variable and context-specific and any reactions depend on numerous intrinsic and extrinsic factors (e.g., species, state of maturity, experience, current activity, reproductive state, auditory sensitivity, time of day), as well as the interplay between factors (e.g., Richardson et al., 1995; Wartzok et al., 2003; Southall et al., 2007; Weilgart, 2007; Archer et al., 2010). Behavioral reactions can vary not only among individuals but also within an individual, depending on previous experience with a sound source, context, and numerous other factors (Ellison et al., 2012), and can vary depending on characteristics associated with the sound source (e.g., whether it is moving or stationary, number of sources, distance from the source). Please see Appendices B-C of Southall et al. (2007) for a review of studies involving marine mammal behavioral responses to sound.

Habituation can occur when an animal's response to a stimulus wanes with repeated exposure, usually in the absence of unpleasant associated events (Wartzok et al., 2003). Animals are most likely to habituate to sounds that are predictable and unvarying. It is important to note that habituation is appropriately considered as a “progressive reduction in response to stimuli that are perceived as neither aversive nor beneficial,” rather than as, more generally, moderation in response to human disturbance (Bejder et al., 2009). The opposite process is sensitization, when an unpleasant experience leads to subsequent responses, often in the form of avoidance, at a lower level of exposure. As noted, behavioral state may affect the type of response. For example, animals that are resting may show greater behavioral change in response to disturbing sound levels than animals that are highly motivated to remain in an area for feeding (Richardson et al., 1995; NRC 2003; Wartzok et al., 2003). Controlled experiments with captive marine mammals have showed pronounced behavioral reactions, including avoidance of loud sound sources (Ridgway et al., 1997; Finneran et al., 2003). Observed responses of wild marine mammals to loud-pulsed sound sources (typically seismic airguns or acoustic harassment devices) have been varied but often consist of avoidance behavior or other behavioral changes suggesting discomfort (Morton and Symonds 2002; see also Richardson et al., 1995; Nowacek et al., 2007).

Available studies show wide variation in response to underwater sound; therefore, it is difficult to predict specifically how any given sound in a particular instance might affect marine mammals perceiving the signal. If a marine mammal does react briefly to an underwater sound by changing its behavior or moving a small distance, the impacts of the change are unlikely to be significant to the individual, let alone the stock or population. However, if a sound source displaces marine mammals from an important feeding or breeding area for a prolonged period, impacts on individuals and populations could be significant (e.g., Lusseau and Bejder 2007; Weilgart 2007; NRC 2005). However, there are broad categories of potential response, which we describe in greater detail here, that include alteration of dive behavior, alteration of foraging behavior, effects to breathing, interference with or alteration of vocalization, avoidance, and flight.

Changes in dive behavior can vary widely, and may consist of increased or decreased dive times and surface intervals as well as changes in the rates of ascent and descent during a dive (e.g., Frankel and Clark 2000; Costa et al., 2003; Ng and Leung 2003; Nowacek et al., 2004; Goldbogen et al., 2013a,b). Variations in dive behavior may reflect interruptions in biologically significant activities (e.g., foraging) or they may be of little biological significance. The impact of an alteration to dive behavior resulting from an acoustic exposure depends on what the animal is doing at the time of the exposure and the type and magnitude of the response.

Disruption of feeding behavior can be difficult to correlate with anthropogenic sound exposure, so it is usually inferred by observed displacement from known foraging areas, the appearance of secondary indicators (e.g., bubble nets or sediment plumes), or changes in dive behavior. As for other types of behavioral response, the frequency, duration, and temporal pattern of signal presentation, as well as differences in species sensitivity, are likely contributing factors to differences in response in any given circumstance (e.g., Croll et al., 2001; Nowacek et al.; 2004; Madsen et al., 2006; Yazvenko et al., 2007). A determination of whether foraging disruptions incur fitness consequences would require information on or estimates of the energetic requirements of the affected individuals and the relationship between prey availability, foraging effort and success, and the life history stage of the animal.

Variations in respiration naturally vary with different behaviors and alterations to breathing rate as a function of acoustic exposure can be expected to co-occur with other behavioral reactions, such as a flight response or an alteration in diving. However, respiration rates in and of themselves may be representative of annoyance or an acute stress response. Various studies have shown that respiration rates may either be unaffected or could increase, depending on the species and signal characteristics, again highlighting the importance in understanding species differences in the tolerance of underwater noise when determining the potential for impacts resulting from anthropogenic sound exposure (e.g., Kastelein et al., 2001, 2005b, 2006; Gailey et al., 2007).

Marine mammals vocalize for different purposes and across multiple modes, such as whistling, echolocation click production, calling, and singing. Changes in vocalization behavior in response to anthropogenic noise can occur for any of these modes and may result from a need to compete with an increase in background noise or may reflect increased vigilance or a startle response. For example, in the presence of potentially masking signals, humpback whales and killer whales have been observed to increase the length of their songs (Miller et al., 2000; Fristrup et al., 2003; Foote et al., 2004), while right whales (Eubalaena glacialis) have been observed to shift the frequency content of their calls upward while reducing the rate of calling in areas of increased anthropogenic noise (Parks et al., 2007b). In some cases, animals may cease sound production during production of aversive signals (Bowles et al., 1994).

Avoidance is the displacement of an individual from an area or migration path as a result of the presence of a sound or other stressors, and is one of the most obvious manifestations of disturbance in marine mammals (Richardson et al., 1995). For example, gray whales (Eschrictius robustus) are known to change direction—deflecting from customary migratory paths—in order to avoid noise from seismic surveys (Malme et al., 1984). Avoidance may be short-term, with animals returning to the area once the noise has ceased (e.g., Bowles et al., 1994; Goold, 1996; Stone et al., 2000; Morton and Symonds, 2002; Gailey et al., 2007). Longer-term displacement is possible, however, which may lead to changes in abundance or distribution patterns of the affected species in the affected region if habituation to the presence of the sound does not occur (e.g., Blackwell et al., 2004; Bejder et al., 2006; Teilmann et al., 2006).

A flight response is a dramatic change in normal movement to a directed and rapid movement away from the perceived location of a sound source. The flight response differs from other avoidance responses in the intensity of the response (e.g., directed movement, rate of travel). Relatively little information on flight responses of marine mammals to anthropogenic signals exist, although observations of flight responses to the presence of predators have occurred (Connor and Heithaus 1996). The result of a flight response could range from brief, temporary exertion and displacement from the area where the signal provokes flight to, in extreme cases, marine mammal strandings (Evans and England 2001). However, it should be noted that response to a perceived predator does not necessarily invoke flight (Ford and Reeves 2008), and whether individuals are solitary or in groups may influence the response.

Behavioral disturbance can also impact marine mammals in more subtle ways. Increased vigilance may result in costs related to diversion of focus and attention (i.e., when a response consists of increased vigilance, it may come at the cost of decreased attention to other critical behaviors such as foraging or resting). These effects have generally not been demonstrated for marine mammals, but studies involving fish and terrestrial animals have shown that increased vigilance may substantially reduce feeding rates (e.g., Beauchamp and Livoreil 1997; Fritz et al., 2002; Purser and Radford 2011). In addition, chronic disturbance can cause population declines through reduction of fitness (e.g., decline in body condition) and subsequent reduction in reproductive success, survival, or both (e.g., Harrington and Veitch, 1992; Daan et al., 1996; Bradshaw et al., 1998). However, Ridgway et al. (2006) reported that increased vigilance in bottlenose dolphins exposed to sound over a five-day period did not cause any sleep deprivation or stress effects.

Many animals perform vital functions, such as feeding, resting, traveling, and socializing, on a diel cycle (24-hour cycle). Disruption of such functions resulting from reactions to stressors such as sound exposure are more likely to be significant if they last more than one diel cycle or recur on subsequent days (Southall et al., 2007). Consequently, a behavioral response lasting less than one day and not recurring on subsequent days is not considered particularly severe unless it could directly affect reproduction or survival (Southall et al., 2007). Note that there is a difference between multi-day substantive behavioral reactions and multi-day anthropogenic activities. For example, just because an activity lasts for multiple days does not necessarily mean that individual animals are either exposed to activity-related stressors for multiple days or, further, exposed in a manner resulting in sustained multi-day substantive behavioral responses.

3. Stress responses—An animal's perception of a threat may be sufficient to trigger stress responses consisting of some combination of behavioral responses, autonomic nervous system responses, neuroendocrine responses, or immune responses (e.g., Seyle 1950; Moberg 2000). In many cases, an animal's first and sometimes most economical (in terms of energetic costs) response is behavioral avoidance of the potential stressor. Autonomic nervous system responses to stress typically involve changes in heart rate, blood pressure, and gastrointestinal activity. These responses have a relatively short duration and may or may not have a significant long-term effect on an animal's fitness.

Neuroendocrine stress responses often involve the hypothalamus-pituitary-adrenal system. Virtually all neuroendocrine functions that are affected by stress—including immune competence, reproduction, metabolism, and behavior—are regulated by pituitary hormones. Stress-induced changes in the secretion of pituitary hormones have been implicated in failed reproduction, altered metabolism, reduced immune competence, and behavioral disturbance (e.g., Moberg 1987; Blecha 2000). Increases in the circulation of glucocorticoids are also equated with stress (Romano et al., 2004).

The primary distinction between stress (which is adaptive and does not normally place an animal at risk) and “distress” is the cost of the response. During a stress response, an animal uses glycogen stores that can be quickly replenished once the stress is alleviated. In such circumstances, the cost of the stress response would not pose serious fitness consequences. However, when an animal does not have sufficient energy reserves to satisfy the energetic costs of a stress response, energy resources must be diverted from other functions. This state of distress will last until the animal replenishes its energetic reserves sufficient to restore normal function.

Relationships between these physiological mechanisms, animal behavior, and the costs of stress responses are well-studied through controlled experiments and for both laboratory and free-ranging animals (e.g., Holberton et al., 1996; Hood et al., 1998; Jessop et al., 2003; Krausman et al., 2004; Lankford et al., 2005). Stress responses due to exposure to anthropogenic sounds or other stressors and their effects on marine mammals have also been reviewed (Fair and Becker 2000; Romano et al., 2002b) and, more rarely, studied in wild populations (e.g., Romano et al., 2002a). For example, Rolland et al. (2012) found that noise reduction from reduced ship traffic in the Bay of Fundy was associated with decreased stress in North Atlantic right whales. These and other studies lead to a reasonable expectation that some marine mammals will experience physiological stress responses upon exposure to acoustic stressors and that it is possible that some of these would be classified as “distress.” In addition, any animal experiencing TTS would likely also experience stress responses (NRC, 2003).

4. Auditory masking—Sound can disrupt behavior through masking, or interfering with, an animal's ability to detect, recognize, or discriminate between acoustic signals of interest (e.g., those used for intraspecific communication and social interactions, prey detection, predator avoidance, navigation) (Richardson et al., 1995). Masking occurs when the receipt of a sound is interfered with by another coincident sound at similar frequencies and at similar or higher intensity, and may occur whether the sound is natural (e.g., snapping shrimp, wind, waves, precipitation) or anthropogenic (e.g., shipping, sonar, seismic exploration) in origin. The ability of a noise source to mask biologically important sounds depends on the characteristics of both the noise source and the signal of interest (e.g., signal-to-noise ratio, temporal variability, direction), in relation to each other and to an animal's hearing abilities (e.g., sensitivity, frequency range, critical ratios, frequency discrimination, directional discrimination, age or TTS hearing loss), and existing ambient noise and propagation conditions.

Under certain circumstances, marine mammals experiencing significant masking could also be impaired from maximizing their performance fitness in survival and reproduction. Therefore, when the coincident (masking) sound is man-made, it may be considered harassment when disrupting or altering critical behaviors. It is important to distinguish TTS and PTS, which persist after the sound exposure, from masking, which occurs during the sound exposure. Because masking (without resulting in TS) is not associated with abnormal physiological function, it is not considered a physiological effect, but rather a potential behavioral effect.

The frequency range of the potentially masking sound is important in determining any potential behavioral impacts. For example, low-frequency signals may have less effect on high-frequency echolocation sounds produced by odontocetes but are more likely to affect detection of mysticete communication calls and other potentially important natural sounds such as those produced by surf and some prey species. The masking of communication signals by anthropogenic noise may be considered as a reduction in the communication space of animals (e.g., Clark et al., 2009) and may result in energetic or other costs as animals change their vocalization behavior (e.g., Miller et al., 2000; Foote et al., 2004; Parks et al., 2007b; Di Iorio and Clark 2009; Holt et al., 2009). Masking can be reduced in situations where the signal and noise come from different directions (Richardson et al., 1995), through amplitude modulation of the signal, or through other compensatory behaviors (Houser and Moore 2014). Masking can be tested directly in captive species (e.g., Erbe 2008), but in wild populations it must be either modeled or inferred from evidence of masking compensation. There are few studies addressing real-world masking sounds likely to be experienced by marine mammals in the wild (e.g., Branstetter et al., 2013).

Masking affects both senders and receivers of acoustic signals and can potentially have long-term chronic effects on marine mammals at the population level as well as at the individual level. Low-frequency ambient sound levels have increased by as much as 20 dB (more than three times in terms of SPL) in the world's ocean from pre-industrial periods, with most of the increase from distant commercial shipping (Hildebrand 2009). All anthropogenic sound sources, but especially chronic and lower-frequency signals (e.g., from vessel traffic), contribute to elevated ambient sound levels, thus intensifying masking.

Potential Effects of DTH drilling and Pile Driving and Removal Sound—The effects of sounds from DTH drilling and pile driving and removal might include one or more of the following: Temporary or permanent hearing impairment, non-auditory physical or physiological effects, behavioral disturbance, and masking (Richardson et al., 1995; Gordon et al., 2003; Nowacek et al., 2007; Southall et al., 2007). The effects of pile driving and removal or drilling on marine mammals are dependent on several factors, including the type and depth of the animal; the pile size and type, and the intensity and duration of the pile driving/removal or drilling sound; the substrate; the standoff distance between the pile and the animal; and the sound propagation properties of the environment. Impacts to marine mammals from pile driving and removal and DTH drilling activities are expected to result primarily from acoustic pathways. As such, the degree of effect is intrinsically related to the frequency, received level, and duration of the sound exposure, which are in turn influenced by the distance between the animal and the source. The further away from the source, the less intense the exposure should be. The substrate and depth of the habitat affect the sound propagation properties of the environment. In addition, substrates that are soft (e.g., sand) would absorb or attenuate the sound more readily than hard substrates (e.g., rock), which may reflect the acoustic wave. Soft porous substrates would also likely require less time to drive the pile, and possibly less forceful equipment, which would ultimately decrease the intensity of the acoustic source.

In the absence of mitigation, impacts to marine species could be expected to include physiological and behavioral responses to the acoustic signature (Viada et al., 2008). Potential effects from impulsive sound sources like pile driving can range in severity from effects such as behavioral disturbance to temporary or permanent hearing impairment (Yelverton et al., 1973).

Hearing Impairment and Other Physical Effects—Marine mammals exposed to high intensity sound repeatedly or for prolonged periods can experience hearing threshold shifts. PTS constitutes injury, but TTS does not (Southall et al., 2007). Based on the best scientific information available, the SPLs for the construction activities in this Project are below the thresholds that could cause TTS or the onset of PTS (Table 6).

Non-auditory Physiological Effects—Non-auditory physiological effects or injuries that theoretically might occur in marine mammals exposed to strong underwater sound include stress, neurological effects, bubble formation, resonance effects, and other types of organ or tissue damage (Cox et al., 2006; Southall et al., 2007). Studies examining such effects are limited. In general, little is known about the potential for pile driving or removal to cause auditory impairment or other physical effects in marine mammals. Available data suggest that such effects, if they occur at all, would presumably be limited to short distances from the sound source and to activities that extend over a prolonged period. The available data do not allow identification of a specific exposure level above which non-auditory effects can be expected (Southall et al., 2007) or any meaningful quantitative predictions of the numbers (if any) of marine mammals that might be affected in those ways. Marine mammals that show behavioral avoidance of pile driving, including some odontocetes and some pinnipeds, are especially unlikely to incur auditory impairment or non-auditory physical effects.

Responses to continuous sound, such as vibratory pile installation, have not been documented as well as responses to pulsed sounds. With both types of pile driving, it is likely that the onset of pile driving could result in temporary, short term changes in an animal's typical behavior and/or avoidance of the affected area. These behavioral changes may include (Richardson et al., 1995): Changing durations of surfacing and dives, number of blows per surfacing, or moving direction and/or speed; reduced/increased vocal activities; changing/cessation of certain behavioral activities (such as socializing or feeding); visible startle response or aggressive behavior (such as tail/fluke slapping or jaw clapping); avoidance of areas where sound sources are located; and/or flight responses (e.g., pinnipeds flushing into water from haul-outs or rookeries). Pinnipeds may increase their haul-out time, possibly to avoid in-water disturbance (Thorson and Reyff 2006). If a marine mammal responds to a stimulus by changing its behavior (e.g., through relatively minor changes in locomotion direction/speed or vocalization behavior), the response may or may not constitute taking at the individual level, and is unlikely to affect the stock or the species as a whole. However, if a sound source displaces marine mammals from an important feeding or breeding area for a prolonged period, impacts on animals, and if so potentially on the stock or species, could potentially be significant (e.g., Lusseau and Bejder 2007; Weilgart 2007).

The biological significance of many of these behavioral disturbances is difficult to predict, especially if the detected disturbances appear minor. However, the consequences of behavioral modification could be expected to be biologically significant if the change affects growth, survival, or reproduction. Significant behavioral modifications that could potentially lead to effects on growth, survival, or reproduction include:

• Drastic changes in diving/surfacing patterns (such as those thought to cause beaked whale stranding due to exposure to military mid-frequency tactical sonar);

• Longer-term habitat abandonment due to loss of desirable acoustic environment; and

• Longer-term cessation of feeding or social interaction.

The onset of behavioral disturbance from anthropogenic sound depends on both external factors (characteristics of sound sources and their paths) and the specific characteristics of the receiving animals (hearing, motivation, experience, demography) and is difficult to predict (Southall et al., 2007).

Natural and artificial sounds can disrupt behavior by masking. The frequency range of the potentially masking sound is important in determining any potential behavioral impacts. Because sound generated from in-water pile driving and removal and DTH drilling is mostly concentrated at low frequency ranges, it may have less effect on high frequency echolocation sounds made by porpoises. The most intense underwater sounds in the proposed action are those produced by impact pile driving. Given that the energy distribution of pile driving covers a broad frequency spectrum, sound from these sources would likely be within the audible range of marine mammals present in the Project area. Impact pile driving activity is relatively short-term, with rapid pulses occurring for approximately fifteen minutes per pile. The probability for impact pile driving resulting from this proposed action masking acoustic signals important to the behavior and survival of marine mammal species is low. Vibratory pile driving is also relatively short-term, with rapid oscillations occurring for approximately one and a half hours per pile. It is possible that vibratory pile driving resulting from this proposed action may mask acoustic signals important to the behavior and survival of marine mammal species, but the short-term duration and limited affected area would result in insignificant impacts from masking. Any masking event that could possibly rise to Level B harassment under the MMPA would occur concurrently within the zones of behavioral harassment already estimated for DTH drilling and vibratory and impact pile driving, and which have already been taken into account in the exposure analysis.

Acoustic Effects, Airborne—Pinnipeds that occur near the Project site could be exposed to airborne sounds associated with pile driving and removal and DTH drilling that have the potential to cause behavioral harassment, depending on their distance from pile driving activities. Cetaceans are not expected to be exposed to airborne sounds that would result in harassment as defined under the MMPA.

Airborne noise will primarily be an issue for pinnipeds that are swimming or hauled out near the Project site within the range of noise levels elevated above the acoustic criteria. We recognize that pinnipeds in the water could be exposed to airborne sound that may result in behavioral harassment when looking with their heads above water. Most likely, airborne sound would cause behavioral responses similar to those discussed above in relation to underwater sound. For instance, anthropogenic sound could cause hauled-out pinnipeds to exhibit changes in their normal behavior, such as reduction in vocalizations, or cause them to temporarily abandon the area and move further from the source. However, these animals would previously have been `taken' as a result of exposure to underwater sound above the behavioral harassment thresholds, which are in all cases larger than those associated with airborne sound. Thus, the behavioral harassment of these animals is already accounted for in these estimates of potential take. Multiple instances of exposure to sound above NMFS' thresholds for behavioral harassment are not believed to result in increased behavioral disturbance, in either nature or intensity of disturbance reaction. Therefore, we do not believe that authorization of incidental take resulting from airborne sound for pinnipeds is warranted, and airborne sound is not discussed further here.

The proposed activities at the Project area would not result in permanent negative impacts to habitats used directly by marine mammals, but may have potential short-term impacts to food sources such as forage fish and may affect acoustic habitat (see masking discussion above). There are no known foraging hotspots or other ocean bottom structure of significant biological importance to marine mammals present in the marine waters of the Project area during the construction window. Therefore, the main impact issue associated with the proposed activity would be temporarily elevated sound levels and the associated direct effects on marine mammals, as discussed previously in this document. The primary potential acoustic impacts to marine mammal habitat are associated with elevated sound levels produced by vibratory and impact pile driving and removal and DTH drilling in the area. However, other potential impacts to the surrounding habitat from physical disturbance are also possible.

Construction activities would produce continuous (i.e., vibratory pile driving and DTH drilling) and pulsed (i.e., impact driving) sounds. Fish react to sounds that are especially strong and/or intermittent low-frequency sounds. Short duration, sharp sounds can cause overt or subtle changes in fish behavior and local distribution. Hastings and Popper (2005) identified several studies that suggest fish may relocate to avoid certain areas of sound energy. Additional studies have documented effects of pile driving on fish, although several are based on studies in support of large, multiyear bridge construction projects (e.g., Scholik and Yan 2001, 2002; Popper and Hastings 2009). Sound pulses at received levels of 160 dB may cause subtle changes in fish behavior. SPLs of 180 dB may cause noticeable changes in behavior (Pearson et al., 1992; Skalski et al., 1992). SPLs of sufficient strength have been known to cause injury to fish and fish mortality.

The most likely impact to fish from pile driving and drilling activities at the Project area would be temporary behavioral avoidance of the area. The duration of fish avoidance of this area after pile driving stops is unknown, but a rapid return to normal recruitment, distribution and behavior is anticipated. In general, impacts to marine mammal prey species are expected to be minor and temporary due to the short timeframe for the Project.

The area likely impacted by the Project is relatively small compared to the available habitat in Sitka Sound (e.g., most of the impacted area is limited to inside Symonds Bay, and some scenarios include a ZOI that extends several km into Sitka Sound (see the FAA's application)). Avoidance by potential prey (i.e., fish) of the immediate area due to the temporary loss of this foraging habitat is also possible. The duration of fish avoidance of this area after pile driving stops is unknown, but a rapid return to normal recruitment, distribution and behavior is anticipated. Any behavioral avoidance by fish of the disturbed area would still leave significantly large areas of fish and marine mammal foraging habitat in the nearby vicinity in Sitka Sound.

The duration of the construction activities is relatively short. The construction window is for a maximum of 70 days and each day, construction activities would only occur for a few hours during the day. Impacts to habitat and prey are expected to be minimal based on the short duration of activities.

In summary, given the short daily duration of sound associated with individual pile driving and drilling events and the relatively small areas being affected, pile driving and drilling activities associated with the proposed action are not likely to have a permanent, adverse effect on any fish habitat, or populations of fish species. Thus, any impacts to marine mammal habitat are not expected to cause significant or long-term consequences for individual marine mammals or their populations.

This section provides an estimate of the number of incidental takes proposed for authorization through this IHA, which will inform both NMFS' consideration of whether the number of takes is “small” and the negligible impact determination.

Harassment is the only type of take expected to result from these activities. Except with respect to certain activities not pertinent here, section 3(18) of the MMPA defines “harassment” as: Any act of pursuit, torment, or annoyance which (i) has the potential to injure a marine mammal or marine mammal stock in the wild (Level A harassment); or (ii) has the potential to disturb a marine mammal or marine mammal stock in the wild by causing disruption of behavioral patterns, including, but not limited to, migration, breathing, nursing, breeding, feeding, or sheltering (Level B harassment).

Authorized takes would be by Level A and Level B harassment, in the form of disruption of behavioral patterns for individual marine mammals resulting from exposure to vibratory and impact pile driving and removal and DTH drilling, and potential PTS for animals that may transit through the Level A zones undetected. Based on the nature of the activity and the anticipated effectiveness of the mitigation measures (i.e., soft start, ramp-up, etc.—discussed in detail below in Proposed Mitigation section), Level A harassment is not anticipated; however, a small number of takes by Level A harassment are proposed to be authorized for all species as a precaution if animals go undetected before a shutdown is in place.

As described previously, no mortality is anticipated or proposed to be authorized for this activity. Below we describe how the take is estimated.

Described in the most basic way, we estimate take by considering: (1) Acoustic thresholds above which NMFS believes the best available science indicates marine mammals will be behaviorally harassed or incur some degree of permanent hearing impairment; (2) the area or volume of water that will be ensonified above these levels in a day; (3) the density or occurrence of marine mammals within these ensonified areas; and, (4) and the number of days of activities. Below, we describe these components in more detail and present the proposed take estimate.

The estimation of marine mammal takes typically uses the following calculation since site-specific density is unavailable:

Level B exposure estimate = N (number of animals) in the area * Number of days of noise generating activities.

Using the best available science, NMFS has developed acoustic thresholds that identify the received level of underwater sound above which exposed marine mammals would be reasonably expected to be behaviorally harassed (equated to Level B harassment) or to incur PTS of some degree (equated to Level A harassment).

Level B Harassment for non-explosive sources—Though significantly driven by received level, the onset of behavioral disturbance from anthropogenic noise exposure is also informed to varying degrees by other factors related to the source (e.g., frequency, predictability, duty cycle), the environment (e.g., bathymetry), and the receiving animals (hearing, motivation, experience, demography, behavioral context) and can be difficult to predict (Southall et al., 2007, Ellison et al., 2011). Based on what the available science indicates and the practical need to use a threshold based on a factor that is both predictable and measurable for most activities, NMFS uses a generalized acoustic threshold based on received level to estimate the onset of behavioral harassment. NMFS predicts that marine mammals are likely to be behaviorally harassed in a manner we consider Level B harassment when exposed to underwater anthropogenic noise above received levels of 120 dB re 1 μPa (rms) for continuous (e.g., vibratory pile-driving, drilling) and above 160 dB re 1 μPa (rms) for non-explosive impulsive (e.g., seismic airguns) or intermittent (e.g., scientific sonar) sources.

The FAA's proposed activities include the use of continuous (vibratory pile driving and DTH drilling) and impulsive (impact pile driving) sources, and therefore the 120 and 160 dB re 1 μPa (rms) are applicable.

Level A harassment for non-explosive sources—NMFS' Technical Guidance for Assessing the Effects of Anthropogenic Sound on Marine Mammal Hearing (NMFS 2016) identifies dual criteria to assess auditory injury (Level A harassment) to five different marine mammal groups (based on hearing sensitivity) as a result of exposure to noise from two different types of sources (impulsive or non-impulsive). The FAA's proposed activity includes the use of impulsive (impact pile driving) and non-impulsive (vibratory pile driving and DTH drilling) sources.

These thresholds were developed by compiling and synthesizing the best available science and soliciting input multiple times from both the public and peer reviewers to inform the final product, and are provided in the table below. The references, analysis, and methodology used in the development of the thresholds are described in NMFS 2016 Technical Guidance, which may be accessed at: http://www.nmfs.noaa.gov/pr/acoustics/guidelines.htm.

Here, we describe operational and environmental parameters of the activity that will feed into identifying the area ensonified above the acoustic thresholds.

Pile driving and removal and DTH drilling generates underwater noise that can potentially result in disturbance to marine mammals in the Project area. Transmission loss (TL) is the decrease in acoustic intensity as an acoustic pressure wave propagates out from a source. TL parameters vary with frequency, temperature, sea conditions, current, source and receiver depth, water depth, water chemistry, and bottom composition and topography. The general formula for underwater TL is:

This formula neglects loss due to scattering and absorption, which is assumed to be zero here. The degree to which underwater sound propagates away from a sound source is dependent on a variety of factors, most notably the water bathymetry and presence or absence of reflective or absorptive conditions including in-water structures and sediments. Spherical spreading occurs in a perfectly unobstructed (free-field) environment not limited by depth or water surface, resulting in a 6 dB reduction in sound level for each doubling of distance from the source (20 * log[range]). Cylindrical spreading occurs in an environment in which sound propagation is bounded by the water surface and sea bottom, resulting in a reduction of 3 dB in sound level for each doubling of distance from the source (10 * log[range]). A practical spreading value of 15 is often used under conditions, such as at the Biorka Island dock, where water increases with depth as the receiver moves away from the shoreline, resulting in an expected propagation environment that would lie between spherical and cylindrical spreading loss conditions. Practical spreading loss (4.5 dB reduction in sound level for each doubling of distance) is assumed here.

Underwater Sound—The intensity of pile driving and removal sounds is greatly influenced by factors such as the type of piles, hammers, and the physical environment in which the activity takes place. A number of studies, primarily on the west coast, have measured sound produced during underwater pile driving projects. These data are largely for impact driving of steel pipe piles and concrete piles as well as vibratory driving of steel pipe piles.

JASCO Applied Sciences (JASCO) conducted acoustic modeling of pile installation and removal activities planned for the Project, which is included as Appendix A of the FAA's application. To assess potential underwater noise exposure of marine mammals during construction activities, Quijano and Austin (2017) determined source levels for six different construction scenarios (see Table 3). The source levels are frequency-dependent and suitable for modeling underwater acoustic propagation using JASCO's Marine Operations Noise Model (MONM). The modeling predicted the extent of ensonification and the acoustic footprint from construction activities, taking into account the effects of pile driving equipment, bathymetry, sound speed profile, and seabed geoacoustic parameters. Auditory weighting was applied to the modeled sound fields to estimate received levels relative to hearing sensitivities of five marine mammal hearing groups following NMFS 2016 guidance.

The results are based on currently adopted sound level thresholds for auditory injury (Level A) expressed as peak pressure level (PK) and 24-hr sound exposure level (SEL), and behavioral disturbance (Level B) expressed as sound pressure level (SPL). Using these guidelines, Quijano and Austin (2017) calculated the maximum extent (distance and ensonified areas) of the Level A and Level B exposure zones for each marine mammal functional hearing group. This was calculated for both impact and vibratory pile driving of 18- and 30-in piles for each of the following six Project scenarios.

The model required as input, source sound levels in 1/3-octave bands between 10 Hz and 25 kHz. Source levels for sheet pile and H pile installation were obtained from literature, but the available measurements did not cover the full frequency spectrum of interest; data for vibratory installation of sheet and H piles were available to maximum frequencies of 4 kHz and 10 kHz, respectively. Modeling of the six construction scenarios at the Project site on Biorka Island followed three steps:

1. Piles driven into the sediment by impact, vibratory, or downhole drilling were characterized as sound-radiating sources. Source levels in 1/3-octave-bands were obtained by modeling or by adjusting source levels found in the literature. The exact method to obtain the 1/3-octave-band levels depends on the pile geometry and pile driving equipment, and it is described on a case-by-case basis (see Appendix A);

2. Underwater sound propagation was applied to predict how sound propagates from the pile into the water column as a function of range, depth, and azimuthal direction. Propagation depends on several conditions including the frequency content of the sound, the bathymetry, the sound speed in the water column, and sediment geoacoustics; and

3. The propagated sound field was used to compute received levels over a grid of simulated receivers, from which distances to criteria thresholds and maps of ensonified areas were generated.

Modeled results are presented as tables of distances at which SPLs or SELs fell below thresholds defined by criteria. For marine mammal injury, the Level A thresholds considered here follow the NMFS guidelines (NMFS 2016). A detailed description of the modeling process is provided in Appendix A of the FAA's IHA application.

In this section we provide the information about the presence, density, or group dynamics of marine mammals that will inform the take calculations.

At-sea densities for marine mammal species have not been determined for marine mammals in Sitka Sound; therefore, all estimates here are determined by using observational data from biologists, peer-reviewed literature, and information obtained from personal communication with researchers and state and Federal biologists, and from local charter boat operators.

Harbor seals are expected to be in the Project area in low numbers (see Description of Marine Mammals in the Area of the Specified Activity Section). We estimate that up to five harbor seals per day may be present in the Project area on all days of construction. Therefore, we propose to authorize 350 takes by Level B harassment. Because the Level A ZOI for harbor seals is nearly 1 km, the FAA requests up to two harbor seal takes by Level A harassment if the animals enter the ZOI undetected and marine mammal observers (MMO)s are not able to request a shutdown prior to the seals being exposed to potential Level A harassment.

Steller sea lion abundance in the Project area is dependent on prey availability. Prey species are uncommon during the Project window; therefore, sea lion abundance is expected to be low. The FAA estimates that five sea lions may be in the Project area every day (70 days) of construction, therefore, we estimate that 350 sea lions may be taken by Level B harassment. We estimate that these takes would be split equally between the eDPS and wDPS (175 each). The Level A zone is less than 10 m; however, to be conservative, the FAA is requesting a small group of Steller sea lions to be taken by Level A harassment. This would equate to six total animals if split equally by DPS (3 each).

Humpback whales are found in Sitka Bay seasonally. During mid-summer, tour boats generally see four to five whales per day, in the middle of Sitka Sound. Therefore, a count of 5 humpback whales per day (70 days) was used to estimate takes per day on every day of construction for a total of 350 takes by Level B harassment. All takes would be from the Central North Pacific stock under the MMPA. For ESA purposes, 93.9 percent would be from the Hawaii DPS (328 animals) and 6.1 percent would be from the Mexico stock (22 animals) based on Wade et al., 2016. The maximum distance at which a humpback whale may be exposed to noise levels that exceed Level A thresholds is 1.4 km during Scenario 6. Even though the ensonified area extends outside of the entrance to Symonds Bay, a MMO stationed near the mouth of the bay at Hanus Point would be able to see a humpback whale outside Symonds Bay before it enters the Level A zone and could shut down the noise producing activity to avoid Level A take. In the unlikely event a whale would go undetected and enter the Level A zone, the FAA has requested three takes by Level A harassment for humpback whales. We estimate that all three humpback whales would be from the Hawaii DPS.

Generally, transient killer whales follow the movements of Steller sea lions and harbor seals on which they prey. Given the low numbers of Steller sea lions in Sitka Sound during summer, it is consistent that transient killer whales would also be rare or infrequent in the Project area (e.g., killer whales were only observed on five or six days by the whale watching industry). Small groups of 5 to 6 transient killer whales per day could be observed throughout the summer months; therefore, we estimate that a group of 6 animals could enter the Project area on 6 occasions during the construction window, for a total of 36 takes by Level B harassment. No Level A takes of killer whales is proposed to be authorized for this species. The maximum linear distance to the Level A threshold for killer whales is less than 250 m from the source and a MMO would be able to observe animals at this distance and shutdown activities in time to avoid Level A take.

Harbor porpoise are expected to occur in the Project area in low numbers during the construction window. Sightings during this time period are infrequent; this species is not observed every day. The mean group size of harbor porpoise in Southeast Alaska was estimated to be between 2 to 3 individuals (Dahlheim et al., 2009); therefore, we conservatively estimate that a group of three harbor porpoise may be present every other day of construction for a total of 105 takes by Level B harassment. The distances to Level A thresholds for harbor porpoise (HFC) are largest during impulse driving under Scenarios 5 and 6 (see Table 3), and extend beyond the entrance to Symonds Bay. The duration of Scenarios 5 and 6 is expected to be 21 days (see Table 3); therefore, we expect that a small group of three harbor porpoise may enter the Level A zone on half of the days of Scenarios 5 and 6 (10.5 days) for a total of 32 takes by Level A harassment.

Here we describe how the information provided above is brought together to produce a quantitative take estimate.

All estimates are conservative and include the following assumptions:

• All pilings installed at each site would have an underwater noise disturbance equal to the piling that causes the greatest noise disturbance (i.e., the piling farthest from shore) installed with the method that has the ZOI. The largest underwater disturbance (Level B) ZOI would be produced by DTH drilling; therefore take estimates were calculated using the vibratory pile-driving ZOIs. The ZOIs for each threshold are not spherical and are truncated by land masses on either side of the Project area, which would dissipate sound pressure waves.

• Exposures were based on an estimated total of 70 work days. Each activity ranges in amount of days needed to be completed (Table 3).

• All marine mammal individuals potentially available are assumed to be present within the relevant area, and thus incidentally taken;

• An individual can only be taken once during a 24-hour period; and,

• Exposures to sound levels at or above the relevant thresholds equate to take, as defined by the MMPA.

Estimates of potential instances of take may be overestimates of the number of individuals taken. In the context of stationary activities such as pile driving and in areas where resident animals may be present, this number represents the number of total take that may accrue to a smaller number of individuals, with some number of animals being exposed more than once per individual. While pile driving and removal can occur any day throughout the in-water work window, and the analysis is conducted on a per day basis, only a fraction of that time (typically a matter of hours on any given day) is actually spent pile driving/removal. The potential effectiveness of mitigation measures in reducing the number of takes is typically not quantified in the take estimation process. For these reasons, these take estimates may be conservative.

In order to issue an IHA under section 101(a)(5)(D) of the MMPA, NMFS must set forth the permissible methods of taking pursuant to such activity, and other means of effecting the least practicable impact on such species or stock and its habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance, and on the availability of such species or stock for taking for certain subsistence uses (latter not applicable for this action). NMFS regulations require applicants for incidental take authorizations to include information about the availability and feasibility (economic and technological) of equipment, methods, and manner of conducting such activity or other means of effecting the least practicable adverse impact upon the affected species or stocks and their habitat (50 CFR 216.104(a)(11)).

In evaluating how mitigation may or may not be appropriate to ensure the least practicable adverse impact on species or stocks and their habitat, as well as subsistence uses where applicable, we carefully balance two primary factors:

(1) The manner in which, and the degree to which, the successful implementation of the measure(s) is expected to reduce impacts to marine mammals, marine mammal species or stocks, and their habitat—which considers the nature of the potential adverse impact being mitigated (likelihood, scope, range), as well as the likelihood that the measure will be effective if implemented; and the likelihood of effective implementation, and;

(2) The practicability of the measures for applicant implementation, which may consider such things as cost, impact on operations, and, in the case of a military readiness activity, personnel safety, practicality of implementation, and impact on the effectiveness of the military readiness activity.

The ZOIs were used to develop mitigation measures for pile driving and removal activities at the Project area. The ZOIs effectively represent the mitigation zone that would be established around each pile to prevent Level A harassment to marine mammals, while providing estimates of the areas within which Level B harassment might occur. In addition to the specific measures described later in this section, the FAA would conduct briefings between construction supervisors and crews, marine mammal monitoring team, and staff prior to the start of all pile driving activity, and when new personnel join the work, in order to explain responsibilities, communication procedures, marine mammal monitoring protocol, and operational procedures.

The following measures would apply to the FAA's mitigation through shutdown and disturbance zones:

Shutdown Zone—For all pile driving activities, the FAA will establish a shutdown zone intended to contain the area in which SPLs equal or exceed the auditory injury criteria for cetaceans and pinnipeds. The purpose of a shutdown zone is to define an area within which shutdown of activity would occur upon sighting of a marine mammal (or in anticipation of an animal entering the defined area), thus preventing injury of marine mammals (as described previously under Potential Effects of the Specified Activity on Marine Mammals, serious injury or death are unlikely outcomes even in the absence of mitigation measures). Modeled radial distances for shutdown zones are shown in Table 9. However, a minimum shutdown zone of 10 m will be established during all pile driving activities, regardless of the estimated zone; and

Disturbance Zone—Disturbance zones are the areas in which SPLs equal or exceed 160 and 120 dB rms (for impulse and continuous sound, respectively). Disturbance zones provide utility for monitoring conducted for mitigation purposes (i.e., shutdown zone monitoring) by establishing monitoring protocols for areas adjacent to the shutdown zones. Monitoring of disturbance zones enables observers to be aware of and communicate the presence of marine mammals in the Project area but outside the shutdown zone and thus prepare for potential shutdowns of activity. However, the primary purpose of disturbance zone monitoring is for documenting instances of Level B harassment; disturbance zone monitoring is discussed in greater detail later (see Proposed Monitoring and Reporting). Nominal radial distances for disturbance zones are shown in Table 9.

Given the size of the disturbance zone for vibratory pile driving and DTH drilling, it is impossible to guarantee that all animals would be observed or to make comprehensive observations of fine-scale behavioral reactions to sound, and only a portion of the zone (e.g., what may be reasonably observed by visual observers stationed between Symonds Bay and Sitka Sound) would be observed. In order to document observed instances of harassment, monitors record all marine mammal observations, regardless of location. The observer's location, as well as the location of the pile being driven, is known from a GPS. The location of the animal is estimated as a distance from the observer, which is then compared to the location from the pile. It may then be estimated whether the animal was exposed to sound levels constituting incidental harassment on the basis of predicted distances to relevant thresholds in post-processing of observational and acoustic data, and a precise accounting of observed incidences of harassment created. This information may then be used to extrapolate observed takes to reach an approximate understanding of actual total takes.

Monitoring Protocols—Monitoring would be conducted before, during, and after pile driving and vibratory removal activities. In addition, observers shall record all instances of marine mammal occurrence, regardless of distance from activity, and shall document any behavioral reactions in concert with distance from piles being driven. Observations made outside the shutdown zone will not result in shutdown; that pile segment would be completed without cessation, unless the animal approaches or enters the shutdown zone, at which point all pile driving activities would be halted. Monitoring will take place from 15 minutes prior to initiation through 30 minutes post-completion of pile driving and removal activities. Pile driving activities include the time to install or remove a single pile or series of piles, as long as the time elapsed between uses of the pile driving equipment is no more than 30 minutes. Please see Section 11 of the FAA's application (www.nmfs.noaa.gov/pr/permits/incidental/construction.htm), for the FAA's proposed monitoring protocols.

The following additional measures apply to visual monitoring:

(1) Monitoring will be conducted by qualified observers, who will be placed at the best vantage point(s) practicable to monitor for marine mammals and implement shutdown/delay procedures when applicable by calling for the shutdown to the hammer operator. A minimum of two observers will be required for all pile driving/removal activities. Marine Mammal Observer (MMO) requirements for construction actions are as follows:

(a) Independent observers (i.e., not construction personnel) are required;

(b) At least one observer must have prior experience working as an observer;

(c) Other observers (that do not have prior experience) may substitute education (undergraduate degree in biological science or related field) or training for experience;

(d) Where a team of three or more observers are required, one observer should be designated as lead observer or monitoring coordinator. The lead observer must have prior experience working as an observer; and

(e) NMFS will require submission and approval of observer resumes.

(2) Qualified MMOs are trained biologists, and need the following additional minimum qualifications:

(a) Visual acuity in both eyes (correction is permissible) sufficient for discernment of moving targets at the water's surface with ability to estimate target size and distance; use of binoculars may be necessary to correctly identify the target;

(b) Ability to conduct field observations and collect data according to assigned protocols;

(c) Experience or training in the field identification of marine mammals, including the identification of behaviors;

(d) Sufficient training, orientation, or experience with the construction operation to provide for personal safety during observations;

(e) Writing skills sufficient to prepare a report of observations including but not limited to the number and species of marine mammals observed; dates and times when in-water construction activities were conducted; dates and times when in-water construction activities were suspended to avoid potential incidental injury from construction sound of marine mammals observed within a defined shutdown zone; and marine mammal behavior; and

(f) Ability to communicate orally, by radio or in person, with project personnel to provide real-time information on marine mammals observed in the area as necessary.

(3) Prior to the start of pile driving activity, the shutdown zone will be monitored for 15 minutes to ensure that it is clear of marine mammals. Pile driving will only commence once observers have declared the shutdown zone clear of marine mammals; animals will be allowed to remain in the shutdown zone (i.e., must leave of their own volition) and their behavior will be monitored and documented. The shutdown zone may only be declared clear, and pile driving started, when the entire shutdown zone is visible (i.e., when not obscured by dark, rain, fog, etc.). In addition, if such conditions should arise during impact pile driving that is already underway, the activity would be halted.

(4) If a marine mammal approaches or enters the shutdown zone during the course of pile driving operations, activity will be halted and delayed until either the animal has voluntarily left and been visually confirmed beyond the shutdown zone or 15 minutes have passed without re-detection of small cetaceans and pinnipeds, and 30 minutes for humpback whales. Monitoring will be conducted throughout the time required to drive a pile.

(5) Using delay and shut-down procedures, if a species for which authorization has not been granted or if a species for which authorization has been granted but the authorized takes are met, approaches or is observed within the Level B harassment zone, activities will shut down immediately and not restart until the animals have been confirmed to have left the area.

The use of a soft start procedure is believed to provide additional protection to marine mammals by warning or providing a chance to leave the area prior to the hammer operating at full capacity, and typically involves a requirement to initiate sound from the hammer at reduced energy followed by a waiting period. This procedure is repeated two additional times. It is difficult to specify the reduction in energy for any given hammer because of variation across drivers and, for impact hammers, the actual number of strikes at reduced energy will vary because operating the hammer at less than full power results in “bouncing” of the hammer as it strikes the pile, resulting in multiple “strikes.” For impact driving, we require an initial set of three strikes from the impact hammer at reduced energy, followed by a 30-second waiting period, then 2 subsequent 3 strike sets. Soft start will be required at the beginning of each day's impact pile driving work and at any time following a cessation of impact pile driving of 30 minutes or longer.

The FAA will only conduct construction activities during daytime hours. Construction will also be restricted to the months of May through September to avoid overlap with times when marine mammals have higher densities in the Project area.

We have carefully evaluated the FAA's proposed mitigation measures and considered their effectiveness in past implementation to preliminarily determine whether they are likely to effect the least practicable impact on the affected marine mammal species and stocks and their habitat.

Any mitigation measure(s) we prescribe should be able to accomplish, have a reasonable likelihood of accomplishing (based on current science), or contribute to the accomplishment of one or more of the general goals listed below:

(1) Avoidance or minimization of injury or death of marine mammals wherever possible (goals 2, 3, and 4 may contribute to this goal);

(2) A reduction in the number (total number or number at biologically important time or location) of individual marine mammals exposed to stimuli expected to result in incidental take (this goal may contribute to 1, above, or to reducing takes by behavioral harassment only);

(3) A reduction in the number (total number or number at biologically important time or location) of times any individual marine mammal would be exposed to stimuli expected to result in incidental take (this goal may contribute to 1, above, or to reducing takes by behavioral harassment only);

(4) A reduction in the intensity of exposure to stimuli expected to result in incidental take (this goal may contribute to 1, above, or to reducing the severity of behavioral harassment only);

(5) Avoidance or minimization of adverse effects to marine mammal habitat, paying particular attention to the prey base, blockage or limitation of passage to or from biologically important areas, permanent destruction of habitat, or temporary disturbance of habitat during a biologically important time; and

(6) For monitoring directly related to mitigation, an increase in the probability of detecting marine mammals, thus allowing for more effective implementation of the mitigation.

Based on our evaluation of the FAA's proposed measures, as well as any other potential measures considered by NMFS, NMFS has preliminarily determined that the proposed mitigation measures provide the means of effecting the least practicable impact on marine mammal species or stocks and their habitat, paying particular attention to rookeries, mating grounds, and areas of similar significance.

In order to issue an IHA for an activity, section 101(a)(5)(D) of the MMPA states that NMFS must set forth requirements pertaining to the monitoring and reporting of such taking. The MMPA implementing regulations at 50 CFR 216.104 (a)(13) indicate that requests for authorizations must include the suggested means of accomplishing the necessary monitoring and reporting that will result in increased knowledge of the species and of the level of taking or impacts on populations of marine mammals that are expected to be present in the proposed action area. Effective reporting is critical to both compliance and ensuring that the most value is obtained from the required monitoring.

Monitoring and reporting requirements prescribed by NMFS should contribute to improved understanding of one or more of the following:

• Occurrence of marine mammal species in action area (e.g., presence, abundance, distribution, density);

• Nature, scope, or context of likely marine mammal exposure to potential stressors/impacts (individual or cumulative, acute or chronic), through better understanding of: (1) Action or environment (e.g., source characterization, propagation, ambient noise); (2) affected species (e.g., life history, dive patterns); (3) co-occurrence of marine mammal species with the action; or (4) biological or behavioral context of exposure (e.g., age, calving or feeding areas);

• Individual marine mammal responses (behavioral or physiological) to acoustic stressors (acute, chronic, or cumulative), other stressors, or cumulative impacts from multiple stressors;

• How anticipated responses to stressors impact either: (1) Long-term fitness and survival of individual marine mammals; or (2) population, species, or stock;

• Effects on marine mammal habitat (e.g., marine mammal prey species, acoustic habitat, or other important physical components of marine mammal habitat); and

• Mitigation and monitoring effectiveness.

The FAA will collect sighting data and behavioral responses to construction for marine mammal species observed in the region of activity during the period of activity. All MMOs will be trained in marine mammal identification and behaviors and are required to have no other construction-related tasks while conducting monitoring. A minimum of two MMOs will be required for all pile driving/removal activities. The FAA will monitor the shutdown zone and disturbance zone before, during, and after pile driving, with observers located at the best practicable vantage points. Based on our requirements, the FAA would implement the following procedures for pile driving and removal:

• MMOs would be located at the best vantage point(s) in order to properly see the entire shutdown zone and as much of the disturbance zone as possible;

• During all observation periods, observers will use binoculars and the naked eye to search continuously for marine mammals;

• If the shutdown zones are obscured by fog or poor lighting conditions, pile driving at that location will not be initiated until that zone is visible. Should such conditions arise while impact driving is underway, the activity would be halted; and

• The shutdown and disturbance zones around the pile will be monitored for the presence of marine mammals before, during, and after any pile driving or removal activity.

We require that observers use approved data forms. Among other pieces of information, the FAA will record detailed information about any implementation of shutdowns, including the distance of animals to the pile and description of specific actions that ensued and resulting behavior of the animal, if any. In addition, the FAA will attempt to distinguish between the number of individual animals taken and the number of incidences of take. We require that, at a minimum, the following information be collected on the sighting forms:

• Date and time that monitored activity begins or ends;

• Construction activities occurring during each observation period;

• Weather parameters (e.g., percent cover, visibility);

• Water conditions (e.g., sea state, tide state);

• Species, numbers, and, if possible, sex and age class of marine mammals;

• Description of any observable marine mammal behavior patterns, including bearing and direction of travel, and if possible, the correlation to SPLs;

• Distance from pile driving or removal activities to marine mammals and distance from the marine mammals to the observation point;

• Description of implementation of mitigation measures (e.g., shutdown or delay);

• Locations of all marine mammal observations; and

• Other human activity in the area.

A draft report would be submitted to NMFS within 90 days of the completion of marine mammal monitoring, or 60 days prior to the requested date of issuance of any future IHA for projects at the same location, whichever comes first. The report will include marine mammal observations pre-activity, during-activity, and post-activity during pile driving and removal days, and will also provide descriptions of any behavioral responses to construction activities by marine mammals and a complete description of all mitigation shutdowns and the results of those actions and an extrapolated total take estimate based on the number of marine mammals observed during the course of construction. A final report must be submitted within 30 days following resolution of comments on the draft report.

NMFS has defined negligible impact as an impact resulting from the specified activity that cannot be reasonably expected to, and is not reasonably likely to, adversely affect the species or stock through effects on annual rates of recruitment or survival (50 CFR 216.103). A negligible impact finding is based on the lack of likely adverse effects on annual rates of recruitment or survival (i.e., population-level effects). An estimate of the number of takes alone is not enough information on which to base an impact determination. In addition to considering estimates of the number of marine mammals that might be “taken” through harassment, NMFS considers other factors, such as the likely nature of any responses (e.g., intensity, duration), the context of any responses (e.g., critical reproductive time or location, migration), as well as effects on habitat, and the likely effectiveness of the mitigation. We also assess the number, intensity, and context of estimated takes by evaluating this information relative to population status. Consistent with the 1989 preamble for NMFS's implementing regulations (54 FR 40338; September 29, 1989), the impacts from other past and ongoing anthropogenic activities are incorporated into this analysis via their impacts on the environmental baseline (e.g., as reflected in the regulatory status of the species, population size and growth rate where known, ongoing sources of human-caused mortality, or ambient noise levels).

Pile driving and removal activities associated with the dock replacement Project, as outlined previously, have the potential to disturb or displace marine mammals. Specifically, the specified activities may result in take, in the form of Level A and Level B harassment (PTS and behavioral disturbance), from underwater sounds generated from pile driving and removal. Potential takes could occur if individuals of these species are present in the ensonified zone when pile driving and removal occurs. Most of the Level A takes are precautionary as marine mammals are not expected to enter and stay in the Level A ensonified area for the duration needed to incur PTS. However, if all authorized takes be Level A harassment were to occur, they would be of small numbers compared to the stock sizes and would not adversely affect the stock through effects on annual rates of recruitment or survival. Additionally, the FAA's mitigation measures, including a shutdown of construction activities if animals enter the Level A zone, further reduces the chance for PTS in marine mammals. Therefore, the effects to marine mammals are expected to be negligible.

No TTS, serious injury, or mortality is anticipated given the nature of the activities and measures designed to minimize the possibility of injury to marine mammals. The potential for these outcomes is minimized through the construction method and the implementation of the planned mitigation measures. Specifically, vibratory and impact hammers and drilling will be the primary methods of installation. Impact pile driving produces short, sharp pulses with higher peak levels and much sharper rise time to reach those peaks. If impact driving is necessary, implementation of soft start and shutdown zones significantly reduces any possibility of injury. Given sufficient “notice” through use of soft start (for impact driving), marine mammals are expected to move away from a sound source that is annoying prior to it becoming potentially injurious, however, as noted previously a small number of potential takes by PTS are proposed for authorization and have been analyzed. The FAA will use a minimum of two MMOs stationed strategically to increase detectability of marine mammals, enabling a high rate of success in implementation of shutdowns to avoid injury.

The FAA's proposed activities are localized and of relatively short duration (a maximum of 70 days for pile driving and removal). The entire Project area is limited to Symonds Bay and into Sitka Sound for some scenarios. These localized and short-term noise exposures may cause short-term behavioral modifications in harbor seals, Steller sea lions, harbor porpoises, killer whales, and humpback whales. Moreover, the proposed mitigation and monitoring measures are expected to reduce the likelihood of injury. Additionally, no important feeding and/or reproductive areas for marine mammals are known to be within the ensonified area during the construction window.

Effects on individuals that are taken by Level B harassment, on the basis of reports in the literature as well as monitoring from other similar activities, will likely be limited to reactions such as increased swimming speeds, increased surfacing time, or decreased foraging (if such activity were occurring) (e.g., Thorson and Reyff 2006; Lerma 2014). Significant behavioral modifications that could potentially lead to effects on growth, survival, or reproduction are not expected to occur given the short duration and small scale of the project activities. Most likely, individuals will simply move away from the sound source and be temporarily displaced from the areas of pile driving and drilling, although even this reaction has been observed primarily only in association with impact pile driving. Thus, even repeated Level B harassment of some small subset of the overall stock is unlikely to result in any significant realized decrease in fitness for the affected individuals, and thus would not result in any adverse impact to the stock as a whole. Non-auditory physiological effects and masking are not expected to occur from the FAA's Project activities.

The Project also is not expected to have significant adverse effects on affected marine mammals' habitat. The Project activities would not modify existing marine mammal habitat for a significant amount of time. The activities may cause some fish to leave the area of disturbance, thus temporarily impacting marine mammals' foraging opportunities in a limited portion of the foraging range. However, because of the short duration of the activities and the relatively small area of the habitat that may be affected, and the decreased potential of prey species to be in the Project area during the construction work window, the impacts to marine mammal habitat are not expected to cause significant or long-term negative consequences.

In summary and as described above, the following factors primarily support our preliminary determination that the impacts resulting from this activity are not expected to adversely affect the species or stock through effects on annual rates of recruitment or survival:

• No mortality or serious injury is anticipated or authorized;

• Level B harassment may consist of, at worst, temporary modifications in behavior (e.g. temporary avoidance of habitat or changes in behavior);

• The lack of important feeding, pupping, or other areas in the action area during the construction window;

• Mitigation is expected to minimize the likelihood and severity of the level of harassment; and

• The small percentage of the stock that may be affected by Project activities (<15 percent for all stocks).

Based on the analysis contained herein of the likely effects of the specified activity on marine mammals and their habitat, and taking into consideration the implementation of the proposed monitoring and mitigation measures, NMFS preliminarily finds that the total marine mammal take from the FAA's construction activities will have a negligible impact on the affected marine mammal species or stocks.

As noted above, only small numbers of incidental take may be authorized under Section 101(a)(5)(D) of the MMPA for specified activities other than military readiness activities. The MMPA does not define small numbers and so, in practice, where estimated numbers are available, NMFS compares the number of individuals taken to the most appropriate estimation of abundance of the relevant species or stock in our determination of whether an authorization is limited to small numbers of marine mammals. Additionally, other qualitative factors may be considered in the analysis, such as the temporal or spatial scale of the activities.

Table 10 details the number of instances that animals could be exposed to received noise levels that could cause Level A and Level B harassment for the proposed work at the Project site relative to the total stock abundance. The numbers of animals authorized to be taken for all species would be considered small relative to the relevant stocks or populations even if each estimated instance of take occurred to a new individual—an extremely unlikely scenario. The total percent of the population (if each instance was a separate individual) for which take is requested is less than 15 percent for all stocks (Table 10). For pinnipeds, especially harbor seals occurring in the vicinity of the Project area, there will almost certainly be some overlap in individuals present day-to-day, and the number of individuals taken is expected to be notably lower.

Based on the analysis contained herein of the proposed activity (including the proposed mitigation and monitoring measures) and the anticipated take of marine mammals, NMFS preliminarily finds that small numbers of marine mammals will be taken relative to the population size of the affected species or stocks.

In order to issue an IHA, NMFS must find that the specified activity will not have an “unmitigable adverse impact” on the subsistence uses of the affected marine mammal species or stocks by Alaskan Natives. NMFS has defined “unmitigable adverse impact” in 50 CFR 216.103 as: an impact resulting from the specified activity: (1) That is likely to reduce the availability of the species to a level insufficient for a harvest to meet subsistence needs by: (i) Causing the marine mammals to abandon or avoid hunting areas; (ii) Directly displacing subsistence users; or (iii) Placing physical barriers between the marine mammals and the subsistence hunters; and (2) That cannot be sufficiently mitigated by other measures to increase the availability of marine mammals to allow subsistence needs to be met.

Harbor seals and Steller sea lions are subsistence harvested in Alaska. During 2012, the estimated subsistence take of harbor seals in southeast Alaska was 595 seals with 49 of these taken near Sitka (Wolfe et al., 2013). This is the lowest number of seals taken since 1992 (Wolfe et al., 2013) and is attributed to the decline in subsistence hunting pressure over the years as well as a decrease in efficiency per hunter (Wolf et al., 2013).

The peak hunting season in southeast Alaska occurs during the month of November and again over the March to April time frame (Wolfe et al., 2013). This corresponds to times when seals are aggregated in shoal areas as they prey on forage species such as herring, making them easier to find and hunt.

The proposed Project is in an area where subsistence hunting for harbor seals or sea lions could occur (Wolfe et al., 2013), but the location is not preferred for hunting. There is little to no hunting documented in the vicinity and there are no harvest quotas for non-listed marine mammals. For these reasons and the fact that Project activities would occur outside of the primary subsistence hunting seasons, there would be no impact on subsistence activities or on the availability of marine mammals for subsistence use.

To satisfy requirements under Section 106 of the National Historic Preservation Act, R&M Consultants, Inc. reached out to the Sitka Tribe of Alaska, Central Council of the Tlingit and Haida, and Sealaska regarding cultural resources in 2016. No issues or concerns with the Project were raised during this effort.

Based on the description of the specified activity, the measures described to minimize adverse effects on the availability of marine mammals for subsistence purposes, and the proposed mitigation and monitoring measures, NMFS has preliminarily determined that there will not be an unmitigable adverse impact on subsistence uses from the FAA's proposed activities.

Section 7(a)(2) of the Endangered Species Act of 1973 (ESA: 16 U.S.C. 1531 et seq.) requires that each Federal agency insure that any action it authorizes, funds, or carries out is not likely to jeopardize the continued existence of any endangered or threatened species or result in the destruction or adverse modification of designated critical habitat. To ensure ESA compliance for the issuance of IHAs, NMFS consults internally, in this case with the Alaska regional Protected Resources Division Office, whenever we propose to authorize take for endangered or threatened species.

NMFS is proposing to authorize take of two DPSs (i.e., wDPS of Steller sea lions and Mexico DPS of humpback whales), which are listed under the ESA. The Permit and Conservation Division has requested initiation of Section 7 consultation with the Alaska Region for the issuance of this IHA. NMFS will conclude the ESA consultation prior to reaching a determination regarding the proposed issuance of the authorization.

As a result of these preliminary determinations, NMFS proposes to issue an IHA to the FAA for conducting their Biorka Island Dock Replacement Project, provided the previously mentioned mitigation, monitoring, and reporting requirements are incorporated. This section contains a draft of the IHA itself. The wording contained in this section is proposed for inclusion in the IHA (if issued).

1. This IHA is valid for 1 year from May 1, 2018 through April 30, 2019.

2. This IHA is valid only for pile driving and removal activities associated with the Biorka Island Dock Replacement Project in Symonds Bay, Alaska from May 1 to September 30, 2018.

3. General Conditions

(a) A copy of this IHA must be in the possession of the FAA, its designees, and work crew personnel operating under the authority of this IHA.

(b) The species authorized for taking are summarized in Table 11.

(c) The taking, by Level A and Level B harassment, is limited to the species listed in condition 3(b). See Table 1 for numbers of take authorized.

(d) The taking by injury (Level A harassment), serious injury, or death of the species listed in condition 3(b) of the Authorization or any taking of any other species of marine mammal is prohibited and may result in the modification, suspension, or revocation of this IHA, unless authorization of take by Level A harassment is listed in condition 3(b) of this Authorization.

(e) The FAA shall conduct briefings between construction supervisors and crews, marine mammal monitoring team, and staff prior to the start of all pile driving and removal activities, and when new personnel join the work.

4. Mitigation Measures

The holder of this Authorization is required to implement the following mitigation measures.

(a) For all pile driving and removal, the FAA shall implement a minimum shutdown zone of 10 m radius around the pile. Additionally, the FAA shall implement shutdown zones for each construction scenario as presented in Table 12. If a marine mammal comes within or approaches the applicable shutdown zone, such operations shall cease.

(b) For in-water heavy machinery work other than pile driving (e.g., standard barges, tug boats, barge-mounted excavators, or clamshell equipment used to place or remove material), if a marine mammal comes within 10 meters, operations shall cease and vessels shall reduce speed to the minimum level required to maintain steerage and safe working conditions.

(c) The FAA shall establish monitoring locations as described below. Please also refer to the FAA's application (see www.nmfs.noaa.gov/pr/permits/incidental/construction.htm).

i. For all pile driving and removal activities, a minimum of two observers shall be deployed, with one positioned to achieve optimal monitoring of the shutdown zones and the second positioned to achieve optimal monitoring of surrounding waters of Biorka dock and portions of Symonds Bay and Sitka Sound. If practicable, the second observer should be deployed to an elevated position with clear sight lines to the Project area.

ii. These observers shall record all observations of marine mammals, regardless of distance from the pile being driven, as well as behavior and potential behavioral reactions of the animals.

iii. All observers shall be equipped for communication of marine mammal observations amongst themselves and to other relevant personnel (e.g., those necessary to effect activity delay or shutdown).

(d) Monitoring shall take place from 15 minutes prior to initiation of pile driving and removal activity through 30 minutes post-completion of pile driving and removal activity. In the event of a delay or shutdown of activity resulting from marine mammals in the shutdown zone, animals shall be allowed to remain in the shutdown zone (i.e., must leave of their own volition) and their behavior shall be monitored and documented. Monitoring shall occur throughout the time required to drive a pile. The shutdown zone must be determined to be clear during periods of good visibility (i.e., the entire shutdown zone and surrounding waters must be visible to the naked eye).

(e) If a marine mammal approaches or enters the shutdown zone, all pile driving and removal activities at that location shall be halted. If pile driving is halted or delayed due to the presence of a marine mammal, the activity may not commence or resume until either the animal has voluntarily left and been visually confirmed beyond the shutdown zone or fifteen minutes have passed without re-detection of small cetaceans and pinnipeds and 30 minutes for humpback whales.

(f) Using delay and shut-down procedures, if a species for which authorization has not been granted or if a species for which authorization has been granted but the authorized takes are met, approaches or is observed within the Level B harassment zone (Table 2), activities will shut down immediately and not restart until the animals have been confirmed to have left the area.

(g) Monitoring shall be conducted by qualified observers. Trained observers shall be placed from the best vantage point(s) practicable to monitor for marine mammals and implement shutdown or delay procedures when applicable through communication with the equipment operator. Observer training must be provided prior to project start and in accordance with the monitoring measures in the application, and shall include instruction on species identification (sufficient to distinguish the species listed in 3(b)), description and categorization of observed behaviors and interpretation of behaviors that may be construed as being reactions to the specified activity, proper completion of data forms, and other basic components of biological monitoring, including tracking of observed animals or groups of animals such that repeat sound exposures may be attributed to individuals (to the extent possible).

(h) The FAA shall use soft start techniques recommended by NMFS for impact pile driving. Soft start requires contractors to provide an initial set of strikes at reduced energy, followed by a thirty-second waiting period, then two subsequent reduced energy strike sets. Soft start shall be implemented at the start of each day's impact pile driving and at any time following cessation of impact pile driving for a period of thirty minutes or longer.

(i) Pile driving shall only be conducted during daylight hours.

5. Monitoring

The holder of this Authorization is required to conduct marine mammal monitoring during pile driving and removal activities. Marine mammal monitoring and reporting shall be conducted in accordance with the monitoring measures in the application.

(a) The FAA shall collect sighting data and behavioral responses to pile driving and removal and drilling activities for marine mammal species observed in the region of activity during the period of activity. All observers shall be trained in marine mammal identification and behaviors, and shall have no other construction-related tasks while conducting monitoring.

(b) For all marine mammal monitoring, the information shall be recorded as described in the monitoring measures section of the application.

6. Reporting

The holder of this Authorization is required to:

(a) Submit a draft report on all monitoring conducted under the IHA within 90 days of the completion of marine mammal monitoring, or 60 days prior to the issuance of any subsequent IHA for projects at the Project area, whichever comes first. A final report shall be prepared and submitted within thirty days following resolution of comments on the draft report from NMFS. This report must contain the informational elements described in the application, at minimum (see www.nmfs.noaa.gov/pr/permits/incidental/construction.htm), and shall also include:

i. Detailed information about any implementation of shutdowns, including the distance of animals to the pile and description of specific actions that ensued and resulting behavior of the animal, if any.

ii. Description of attempts to distinguish between the number of individual animals taken and the number of incidents of take, such as ability to track groups or individuals.

iii. An estimated total take estimate extrapolated from the number of marine mammals observed during the course of construction activities, if necessary.

(b) Reporting injured or dead marine mammals:

i. In the unanticipated event that the specified activity clearly causes the take of a marine mammal in a manner prohibited by this IHA, such as a serious injury or mortality, the FAA shall immediately cease the specified activities and report the incident to the Office of Protected Resources, NMFS, and the Alaska Regional Stranding Coordinator. The report must include the following information:

A. Time and date of the incident;

B. Description of the incident;

C. Environmental conditions (e.g., wind speed and direction, Beaufort sea state, cloud cover, and visibility);

D. Description of all marine mammal observations in the 24 hours preceding the incident;

E. Species identification or description of the animal(s) involved;

F. Fate of the animal(s); and

G. Photographs or video footage of the animal(s).

Activities shall not resume until NMFS is able to review the circumstances of the prohibited take. NMFS will work with the FAA to determine what measures are necessary to minimize the likelihood of further prohibited take and ensure MMPA compliance. The FAA may not resume their activities until notified by NMFS.

ii. In the event that the FAA discovers an injured or dead marine mammal, and the lead observer determines that the cause of the injury or death is unknown and the death is relatively recent (e.g., in less than a moderate state of decomposition), the FAA shall immediately report the incident to the Office of Protected Resources, NMFS, and the Alaska Regional Stranding Coordinator.

The report must include the same information identified in 6(b)(i) of this IHA. Activities may continue while NMFS reviews the circumstances of the incident. NMFS will work with the FAA to determine whether additional mitigation measures or modifications to the activities are appropriate.

iii. In the event that the FAA discovers an injured or dead marine mammal, and the lead observer determines that the injury or death is not associated with or related to the activities authorized in the IHA (e.g., previously wounded animal, carcass with moderate to advanced decomposition, scavenger damage), the FAA shall report the incident to the Office of Protected Resources, NMFS, and the Alaska Regional Stranding Coordinator, NMFS, within 24 hours of the discovery. The FAA shall provide photographs or video footage or other documentation of the stranded animal sighting to NMFS.

7. This Authorization may be modified, suspended or withdrawn if the holder fails to abide by the conditions prescribed herein, or if NMFS determines the authorized taking is having more than a negligible impact on the species or stock of affected marine mammals.

We request comment on our analyses, the draft authorization, and any other aspect of this Notice of Proposed IHAs for the FAA's dock replacement construction activities. Please include with your comments any supporting data or literature citations to help inform our final decision on the FAA's request for MMPA authorization.

This meeting is being held under the provisions of the Federal Advisory Committee Act (FACA) of 1972 (5 U.S.C., Appendix, as amended), the Government in the Sunshine Act of 1976 (5 U.S.C. 552b, as amended), and 41 CFR 102-3.140 and 102-3.150.

In accordance with Public Law 110-181 sec. 598; the 2008 National Defense Authorization Act authorized the Secretary of Defense to establish the Vietnam War Commemoration Office. The Office promotes events, exhibits, partnerships, and other activities to meet the objectives specified in Law: 1. To thank and honor veterans of the Vietnam War, including personnel who were held as prisoners of war (POW), or listed as missing in action (MIA), for their service and sacrifice on behalf of the United States and to thank and honor the families of these veterans. 2. To highlight the service of the Armed Forces during the Vietnam War and the contributions of Federal agencies and governmental and non-governmental organizations that served with, or in support of, the Armed Forces. 3. To pay tribute to the contributions made on the home front by the people of the United States during the Vietnam War. 4. To highlight the advances in technology, science, and medicine related to military research conducted during the Vietnam War. 5. To recognize the contributions and sacrifices made by the allies of the United States during the Vietnam War.

Purpose of the Meeting: The Vietnam War Commemoration Advisory Committee is providing recommendations on the Vietnam War Commemoration Office's Strategic Plan.

Agenda: The meeting will begin at 10:00 a.m. and end at 12:00 p.m. on September 28, 2017. Members will share their individual comments on the Strategic Plan and will then build a consensus on their recommendations.

Meeting Accessibility: The walk to the meeting room will take approximately 10 minutes. Ramp access is available for the physically challenged. Visitors in wheelchairs must be accompanied by someone who will assist them.

Written Statements: The public is invited to submit written statements to the Designated Federal Officer by Friday, September 22, 2017 using the contact information in the FOR FURTHER INFORMATION CONTACT section.

I. General Information A. Does this action apply to me?

This action may be of particular interest to entities that manufacture (defined under TSCA to include import), process, distribute in commerce, use or dispose of methylene chloride or other chemicals in furniture restoration, especially entities identified under North American Industrial Classification System (NAICS) code 811420. Since other entities may also be interested, the Agency has not attempted to describe all the specific entities and corresponding NAICS codes for entities that may be interested in or affected by this action.

The docket for this action, identified by docket identification (ID) number EPA-HQ-OPPT-2017-0139 is available at http://www.regulations.gov or at the Office of Pollution Prevention and Toxics Docket (OPPT Docket), Environmental Protection Agency Docket Center (EPA/DC), West William Jefferson Clinton Bldg., Rm. 3334, 1301 Constitution Ave. NW., Washington, DC. The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The telephone number for the Public Reading Room is (202) 566-1744, and the telephone number for the OPPT Docket is (202) 566-0280. Please review the visitor instructions and additional information about the docket available at http://www.epa.gov/dockets.

In the Federal Register of January 19, 2017 (82 FR 7464) (FRL-9958-57), EPA proposed to prohibit manufacture (including import), processing, and distribution in commerce of methylene chloride in consumer paint and coating removal and in most types of commercial paint and coating removal, excluding commercial furniture refinishing. In that notice, the Agency announced its intention to hold a public meeting to learn more about methylene chloride use in furniture refinishing. This workshop will help EPA and all stakeholders better understand challenges in commercial furniture refinishing. The workshop aims to facilitate an exchange of information on existing use and work practices, the needs, and preferences and expertise of craftspeople, and the availability and effectiveness of paint and coating removal approaches. Federal and state governments, industry professionals, furniture restoration experts, non-profit organizations, and academic experts, among others, will discuss the role of methylene chloride in furniture restoration. The workshop will include presentations by subject matter experts, with sessions focused on current use practices, the availability of safer alternatives in furniture refinishing, and worker protection measures. The workshop will include opportunities for public comment.

To attend the meeting in person or to receive remote access, you must register no later than September 10, 2017, by visiting: https://www.eventbrite.com/e/us-epa-public-meeting-on-methylene-chloride-in-furniture-refinishing-tickets-36895406153. While on-site registration will be available, seating will be on a first-come, first-served basis, with priority given to early registrants, until room capacity is reached. For registrants not able to attend in person, the meeting will also provide remote access capabilities; registered participants will be provided information on how to connect to the meeting prior to its start.

You may submit written information for consideration during or after this meeting. Information should be submitted to docket ID number EPA-HQ-OPPT-2017-139 available at through https://www.regulations.gov. Follow the online instructions for submitting information or comments. Once submitted, this information cannot be edited or withdrawn. EPA may publish any information received to its public docket. Do not submit electronically any information you consider to be Confidential Business Information or other information whose disclosure is restricted by statute. Multimedia submissions (audio, video, etc.) must be accompanied by a written statement or information. Information must be received on or before November 12, 2017.

While not required by law, the Equal Employment Opportunity Commission (EEOC) has determined that reissuance of an agency's EEO policy statement each fiscal year is a symbol of the agency leadership's commitment to EEO and Diversity principles. The FCA conducted its annual review of Policy Statement FCA-PS-62 on Equal Employment Opportunity (EEO) and Diversity. The policy has no changes other than a citation clarification.

The text of the updated Policy Statement is set forth below in its entirety. All FCA Board policy statements may be viewed on FCA's Web site. From www.fca.gov, select “Laws & Regulations,” then select “FCA Handbook,” then select “FCA Board Policy Statements.”

Effective Date: August 24, 2017.

Effect on Previous Action: Replaces FCA-PS-62 [NV16-14] dated August 12, 2016 (81 FR 53482, 8/12/16).

Source of Authority: Title VII of the Civil Rights Act of 1964, as amended (42 U.S.C. 2000e et seq.); Age Discrimination in Employment Act (29 U.S.C. 621 et seq.); Section 501 of the Rehabilitation Act of 1973, as amended (29 U.S.C. 791); Equal Pay Act of 1974 (29 U.S.C. 206(d)); Civil Service Reform Act of 1978 (5 U.S.C. 3112); Notification and Federal Employee Antidiscrimination and Retaliation Act of 2002 (No FEAR Act) (5 U.S.C. 2301); Genetic Information Nondiscrimination Act of 2008 (42 U.S.C. 2000ff et seq.); section 5.9 of the Farm Credit Act of 1971, as amended (12 U.S.C. 2243); Executive Order 11478 (Equal Employment Opportunity in the Federal Government), as amended by Executive Orders 13087 and 13152 to include prohibitions on discrimination based on sexual orientation and status as a parent; Executive Order 13166 (Improving Access to Services for Persons with Limited English Proficiency); 29 CFR part 1614; Equal Employment Opportunity Commission Management Directives.

The Farm Credit Administration Board hereby adopts the following policy statement:

The Farm Credit Administration (FCA or Agency) Board reaffirms its commitment to Equal Employment Opportunity (EEO) and Diversity (EEOD) and its belief that all FCA employees should be treated with dignity and respect. The Board also provides guidance to Agency management and staff for deciding and taking action in these critical areas.

Unquestionably, the employees who comprise the FCA are its most important resource. The Board fully recognizes that the Agency draws its strength from the dedication, experience, and diversity of its employees. The Board is firmly committed to taking whatever steps are needed to protect the rights of its staff and to carrying out programs that foster the development of each employee's potential. We believe an investment in efforts that strongly promote EEOD will prevent the conflict and the high costs of correction for taking no, or inadequate, action in these areas.

The Farm Credit Administration (FCA) Board adopts the following policy statement:

It is the policy of the FCA to prohibit discrimination in Agency policies, program practices, and operations. Employees, applicants for employment, and members of the public who seek to take part in FCA programs, activities, and services will be treated fairly. The FCA Board Chairman and Chief Executive Officer (CEO) is ultimately responsible for ensuring that FCA meets all EEOD requirements and initiatives in accordance with laws and regulations, to maintain a workplace that is free from discrimination and that values all employees. FCA, under the appropriate laws and regulations, will:

• Ensure equal employment opportunity based on merit and qualification, without discrimination because of race, color, religion, sex (including sexual orientation), age (40 or older), national origin, disability, status as a parent, genetic information, or filing of a complaint, participation in discrimination or harassment complaint proceedings, or other opposition to discrimination;

• Provide for the prompt and fair consideration of complaints of discrimination;

• Make reasonable accommodations for qualified applicants for employment and employees with physical or mental disabilities under law;

• Make reasonable accommodations based on applicants' and employees' religious beliefs or practices, consistent with Title VII;

• Provide an environment free from harassment to all employees;

• Create and maintain an organizational culture that recognizes, values, and supports employee and public diversity and inclusion;

• Develop objectives within the Agency's operation and strategic planning process to meet the goals of EEOD and this policy;

• Implement affirmative programs to carry out this policy within the Agency; and

• To the extent practicable, seek to encourage the Farm Credit System to continue its efforts to promote and increase diversity.

The FCA intends to be a model employer. That is, as far as possible, FCA will build and maintain a workforce that reflects the rich diversity of individual differences evident throughout this Nation. The Board views individual differences as complementary and believes these differences enrich our organization. When individual differences are respected, recognized, and valued, diversity becomes a powerful force that can contribute to achieving superior results. Therefore, we will create, maintain, and continuously improve on an organizational culture that fully recognizes, values, and supports employee diversity. The Board is committed to promoting and supporting an inclusive environment that provides to all employees, individually and collectively, the chance to work to their full potential in the pursuit of the Agency's mission. We will provide everyone the opportunity to develop to his or her fullest potential. When a barrier to someone achieving this goal exists, we will strive to remove this barrier.

The Board reaffirms its commitment to ensuring FCA conducts all of its employment practices in a nondiscriminatory manner. The Board expects full cooperation and support from everyone associated with recruitment, selection, development, and promotion to ensure such actions are free of discrimination. All employees will be evaluated on their EEOD achievements as part of their overall job performance. Though staff commitment is important, the role of supervisors is paramount to success. Agency supervisors must be coaches and are responsible for helping all employees develop their talents and give their best efforts in contributing to the mission of the FCA.

It is the policy of the FCA to provide a work environment free from unlawful discrimination in any form, and to protect all employees from any form of harassment, either physical or verbal. The FCA will not tolerate harassment in the workplace for any reason. The FCA also will not tolerate retaliation against any employee for reporting harassment or for aiding in any inquiry about reporting harassment. FCA begins prompt, thorough, and impartial investigations within 10 days of receiving notice of harassment allegations.

A disabled veteran is defined as someone who is entitled to compensation under the laws administered by the Veterans Administration or someone who was discharged or released from active duty because of a service-connected disability.

The FCA is committed to increasing the representation of disabled veterans within its organization. Our Nation owes a debt to those veterans who served their country, especially those who were disabled because of service. To honor these disabled veterans, the FCA shall place emphasis on making vacancies known to and providing opportunities for employing disabled veterans.

I. Background

FRBNY, in cooperation with the U.S. Office of Financial Research (OFR), is considering publishing three rates based on overnight repurchase agreement (repo) transactions on U.S. Treasury securities (Treasury repo). The publication of these rates, targeted to commence by mid-2018, is intended to improve transparency into the repo market by increasing the amount and quality of information available about the market for overnight Treasury repo activity. The three overnight Treasury repo rates would be based on transaction-level data from various segments of the repo market.

The U.S. Treasury securities market is the deepest and most liquid government securities market in the world. It plays a critical and unique role in the global economy, serving as a means of financing the U.S. federal government, a significant investment instrument and hedging vehicle for global investors, a risk-free benchmark for other financial instruments, and an important market for the Federal Reserve's implementation of monetary policy.

Treasury repos are critically important for the U.S. financial system and for the implementation of monetary policy. A repo transaction is the sale of a security, or a portfolio of securities, combined with an agreement to repurchase the security or portfolio on a specified future date at a prearranged price.1 A repo also has the economic characteristics of a collateralized loan. The initial seller of the security (the “securities provider”) may view itself as a borrower of cash and the initial buyer of the security (the “cash provider”) may view itself as a lender in a secured transaction. The discount on the repurchase is equivalent to an interest rate. In the event the securities provider is unable to repurchase the securities (i.e., repay the loan) at maturity, the cash provider is entitled to liquidate the securities to obtain repayment.

The market for Treasury repos includes a “tri-party” segment (a submarket of which is executed through the GCF Repo® service offered by the Fixed Income Clearing Corporation (FICC)) and a bilateral segment. All tri-party repos—and some bilateral repos—are made against a pool of “general” collateral rather than specific securities. In a general collateral (GC) repo, the cash provider stipulates a population of acceptable collateral (e.g., all Treasury securities), but does not stipulate the specific securities that the securities provider must pledge.

In a tri-party repo, a clearing bank is used to facilitate the clearing and settlement of the transaction by managing the securities and ensuring that the securities adhere to the cash provider's eligibility requirements (as noted above, all repo transactions currently conducted over tri-party repo platforms are GC repos). Tri-party repos settle on the books of the clearing bank, where cash and securities are transferred between the cash provider's and securities provider's respective accounts. Among the most prominent cash providers in this segment are money market mutual funds and cash collateral reinvestment accounts managed for securities lenders, while the primary securities providers are securities dealers. Bank of New York Mellon (BNYM) and JPMorgan Chase (JPMC) currently serve as the two clearing banks in the tri-party repo market. JPMC announced in July 2016 that it plans to exit government securities settlement for broker-dealers by the end of 2018. After 2018, BNYM may become the sole clearing bank in the tri-party repo market for Treasury securities.

The tri-party Treasury repo market is important because it provides market liquidity and price transparency for U.S. government securities and thereby fosters stable financing costs for the U.S. government. It also serves as a critical source of funding for many systemically important broker-dealers that make markets in U.S. government securities. The tri-party repo market interconnects with other payment, clearing, and settlement services that are central to U.S. financial markets.

Currently, information available to the public about rates of return in the market for tri-party Treasury repos is limited. Pursuant to the Board's supervisory authority, however, the FRBNY collects trade-by-trade data on tri-party Treasury repo transactions on a daily basis from the two clearing banks. This data set includes: the interest rate of the transaction; the parties to the transaction; information on the collateral that may be pledged in the transaction; the type of transaction; the date the transaction is initiated; the date the transaction becomes effective; the date the transaction matures; whether the transaction is open-ended (i.e., has no specific maturity date); the value of funds borrowed in the transaction; whether the transaction includes an option (e.g., the ability to extend or terminate early); and, if the transaction includes an option, the minimum notice period required to exercise such an option.

GCF Repo, introduced by FICC in 1998, permits FICC's netting members to trade cash and securities among themselves based on negotiated rates and terms. GCF Repo trades are completed on an anonymous basis through interdealer brokers and settle on the two clearing banks' tri-party repo platforms. FICC acts as a central counterparty in GCF Repo, serving as the legal counterparty to each side of the repo transaction for settlement purposes. GCF Repo is designed as a general collateral repo service, where FICC defines the set of permissible collateral classes.

Securities dealers currently rely on GCF Repo transactions for a variety of functions, including raising funds and seeking securities to fulfill tri-party repo obligations. FRBNY has entered into an agreement with DTCC Solutions LLC (DTCC Solutions), an affiliate of the Depository Trust & Clearing Corporation (DTCC), to obtain data regarding GCF Repo transactions.2 This data set includes: the interest rate of the transaction; information on the collateral that may be pledged in the transaction; the date the transaction is initiated; the date the transaction becomes effective; the date the transaction matures; the value of funds borrowed in the transaction; and an indicator differentiating between repos and reverse repos in relation to the central counterparty.

Unlike the tri-party repo market, in the bilateral repo market, counterparties instruct their custodians to exchange cash and securities without the use of a third party to manage collateral and facilitate centralized settlement. In order to effect settlement, the parties identify specific securities for their custodians to transfer. As a result, the bilateral repo market can be used to temporarily acquire specific securities (referred to as specific-issue collateral). Depending on the individual market for each security, repos for specific-issue collateral can take place at much lower rates than GC trades, as cash providers may be willing to accept a lesser return on their cash, or even at times accept a negative return, in order to secure a particular security. Such securities are commonly referred to as “specials.” However, because all bilateral transactions must identify the securities being delivered in order to settle, it is not possible to determine from settlement data whether, in any particular trade, a cash provider intended to invest cash against general collateral (at the general collateral market rate) or to acquire specific securities (at a possibly lower rate for “specials”).

Bilateral repo transactions fall into two segments: Bilateral repo cleared through FICC's Delivery-versus-Payment (DVP) service and non-cleared bilateral repo. Repos cleared through FICC's DVP service are similar to GCF Repo in that they both allow for clearing in interdealer repo markets and both novate transactions to FICC. GCF repos, however, are exclusively blind brokered, while DVP repos can be blind brokered or directly negotiated. Non-cleared bilateral repo transactions are conducted entirely outside the services offered by FICC and do not settle on the clearing banks' tri-party repo platforms, and detailed information about that segment is not currently available.

FRBNY has entered into an agreement with DTCC Solutions to obtain data regarding FICC-cleared Treasury bilateral repo transactions. This data set includes: the interest rate of the transaction; information on the specific collateral that is pledged in the transaction; the date the transaction is initiated; the value of funds borrowed in the transaction; and an indicator differentiating between repos and reverse repos in relation to the central counterparty.

In order to provide the public with more information regarding the interest rates associated with repo transactions, the FRBNY proposes to publish interest rate statistics for overnight Treasury repos. As described below, the FRBNY proposes to publish three different rates.

This rate would measure the rate of return available on overnight repo transactions against Treasury securities in the tri-party repo market, excluding GCF Repo and transactions in which the Federal Reserve is a counterparty.3 As currently envisioned, the FRBNY would calculate the rate based on the transaction-level tri-party data collected from BNYM under the Board of Governors' supervisory authority as described above. This rate would focus on the dealer-to-customer activity in tri-party repo and would capture a narrower set of transactions relative to the other two proposed rates.

This rate would provide a broader measure of rates on overnight Treasury GC repo transactions. As currently envisioned, the FRBNY would calculate the rate based on the same transaction-level tri-party data collected from BNYM as in the TGCR plus GCF Repo data obtained from DTCC Solutions as described above. This rate would therefore reflect both dealer-to-customer and interdealer repos. By including data from different tri-party platforms, this rate would represent a broader, more diverse transaction set than the first rate, resulting in greater resiliency to market evolution. However, idiosyncratic pricing behavior over month- and quarter-ends in the GCF Repo transaction base could result in divergence from other money market rates depending on relative volume in the GCF Repo market.

This rate would be the broadest measure of rates on overnight Treasury financing transactions by also including bilateral Treasury repo transactions cleared through FICC's DVP service, filtered to remove some (but not all) transactions considered “specials.” 4 As currently envisioned, the FRBNY would calculate the rate based on the tri-party data from BNYM, GCF Repo data from DTCC Solutions, and FICC-cleared bilateral repo data from DTCC Solutions. This rate would capture the broadest set of transactions, resulting in the rate most resilient to market evolution, but would not be a pure GC repo rate.

The FRBNY proposes to use a volume-weighted median as the central tendency measure for each of the three Treasury repo rates described above. While the volume-weighted mean, median, and trimmed mean would be similar to each other based on historical data, the median is more resistant to erroneous data, and would be consistent with the methodology used for the Effective Federal Funds Rate (EFFR) and Overnight Bank Funding Rate (OBFR).5 Further, in instances when the three statistical measures differ considerably from each other, the median has generally been more representative of where the bulk of trading has taken place. FRBNY also proposes to publish summary statistics to accompany the daily publication of the rate, which would consist of the 1st, 25th, 75th and 99th volume-weighted percentile rates, as well as volumes.

The target publication time for the three rates and their summary statistics would be each morning at 8:30 ET. The repo rates would only be revised on a same-day basis, and only if the updated data would result in a shift in the volume-weighted median by more than one basis point. Such revisions, which should be a rare occurrence, would be effected that same day at or around 2:30 ET and would result in a republication of updated summary statistics. In the event the previously noted data sources were unavailable, the rates would be calculated based upon back-up repo market survey data collected each morning from FRBNY's primary dealer counterparties. FRBNY may decide to revise the summary statistics or publish additional summary statistics on a lagged basis.

For each rate, FRBNY would exclude trades between affiliated entities when relevant and the data to make such exclusions are available. To the extent possible, “open” trades for which pricing resets daily (making such transactions economically similar to overnight transactions) would be included in the calculation of the rates. The inclusion of these open transactions is intended to ensure that the proposed rates incorporate all relevant transactions, and will mitigate risks around potential changes in market practice. Each of the rates could be modified in the future in response to market evolution or to incorporate additional market segments if data become available.

To assist the Board in considering the production of the proposed rates, the Board seeks public comment on the following questions:

1. Would the proposed rates be useful to market participants, researchers, or others? For what purpose(s)?

2. Are one or more of the proposed rates more likely to be useful than the other(s)? For what purpose(s)?

3. Are there changes to one or more of the rates that would make them more useful? For what purpose(s)?

4. Are there particular sources of data or data sets that should be incorporated in the calculation of the rates that would make the rates more useful to the public?

5. Are there changes that should be made to the proposed manner of calculating and publishing the three rates?

6. Is the proposed time of publication early enough to facilitate the use of the rates for various purposes?

7. Is the use of the volume-weighted median appropriate? Is there a different measure of the central tendency of the distribution of individual transacted rates that would be better suited? For what purpose(s)?

8. Are the proposed summary statistics useful to the market? For what purposes? Would other summary statistics be more useful to accompany the daily publication, instead of or in addition to those proposed?

In accordance with the Paperwork Reduction Act of 1995 (44 U.S.C. 3506; 5 CFR part 1320, Appendix A.1), the Board reviewed the proposal under the authority delegated to the Board by the Office of Management and Budget. For purposes of calculating burden under the Paperwork Reduction Act, a “collection of information” involves 10 or more respondents. As noted above, the data to be used to produce the proposed rates will be obtained solely from (1) BNYM with respect to tri-party GC repo data and (2) DTCC Solutions with respect to GCF repo data and DVP bilateral repo data. Therefore, no collection of information pursuant to the Paperwork Reduction Act is contemplated by the proposed rate production at this time.

The Regulatory Flexibility Act (5 U.S.C. 601 et seq.) (“RFA”) generally requires an agency to perform an initial and a final regulatory flexibility analysis on the impact a rule is expected to have on small entities. The RFA imposes these requirements in situations where an agency is required by law to publish a general notice of proposed rulemaking for any proposed rule. The production of the rates does not create any obligations or rights for any private parties, including any small entities, and so the publication of a general notice of proposed rulemaking is not required. Accordingly, the RFA does not apply and an initial and final regulatory flexibility analysis is not required.

The Deepwater Horizon oil spill led to passage of the Resources and Ecosystems Sustainability, Tourist Opportunities, and Revived Economies of the Gulf Coast States Act of 2012 (RESTORE Act) (33 U.S.C. 1321(t) and note), which dedicates 80 percent of all Clean Water Act administrative and civil penalties related to the oil spill to the Gulf Coast Restoration Trust Fund (Trust Fund). The RESTORE Act also created the Council, an independent Federal entity comprised of the five Gulf Coast states and six Federal agencies. Among other responsibilities, the Council administers a portion of the Trust Fund known as the Council-Selected Restoration Component in order to “undertake projects and programs, using the best available science, that would restore and protect the natural resources, ecosystems, fisheries, marine and wildlife habitats, beaches, coastal wetlands, and economy of the Gulf Coast.” Additional information on the Council can be found here: https://www.restorethegulf.gov.

On December 9, 2015, the Council approved the FPL, which includes projects and programs approved for funding under the Council-Selected Restoration Component, along with other activities the Council identified as priorities for potential future funding. Activities approved for funding in the FPL are included in “Category 1;” the priorities for potential future funding are in “Category 2.” In the FPL the Council approved approximately $156.6 million in Category 1 restoration and planning activities, and prioritized twelve Category 2 activities for possible funding in the future, subject to environmental compliance and further Council and public review. The Council included planning activities for Robinson Preserve in Category 1 and implementation activities for Robinson Preserve in Category 2.

The Council reserved approximately $26.6 million for implementing priority activities in the future. These reserved funds may be used to support some, all or none of the activities included in Category 2 of the FPL and/or to support other activities not currently under consideration by the Council. As appropriate, the Council intends to review each activity in Category 2 in order to determine whether to: (1) Move the activity to Category 1 and approve it for funding, (2) remove it from Category 2 and any further consideration, or (3) continue to include it in Category 2. A Council decision to amend the FPL to move an activity from Category 2 into Category 1 must be approved by a Council vote after consideration of public and Tribal comments.

Prior to approving an activity for funding in FPL Category 1, the Council must comply with NEPA and other applicable Federal environmental laws. At the time of approval of the FPL, the Council had not addressed NEPA and other laws applicable to implementation of Robinson Preserve. The Council did, however, recognize the potential ecological value of Robinson Preserve, based on the review conducted during the FPL process. For this reason, the Council approved $470,910 in planning funds for Robinson Preserve, a portion of which would be used to complete any needed environmental compliance activities. As noted above, the Council placed the implementation portion of Robinson Preserve into FPL Category 2, pending the outcome of this environmental compliance work and further Council review. The estimated cost of implementation of Robinson Preserve was $1,319,636.

To comply with NEPA for Robinson Preserve, the Council is proposing to adopt the 2015 PEIS developed by NOAA's Restoration Center. This PEIS addresses a range of restoration types including those in the Robinson Preserve implementation funding proposal. NOAA has determined that the specific implementation activities for which funding is being sought are fully covered by this PEIS, and therefore no further NEPA review would be needed.

On May 22, 2017, the U.S. Army Corps of Engineers issued a Clean Water Act (CWA) Section 404 permit for the Robinson Preserve project. NOAA has confirmed that this permit addresses its Magnuson-Stevens Act recommendations pertaining to Essential Fish Habitat. The permit also contains conditions pertaining to compliance with the Endangered Species Act and the National Historic Preservation Act. In addition, the Florida State Historic Preservation Officer and U.S. Fish and Wildlife Service have reviewed the overall Robinson Preserve project. These reviews were conducted as part of their respective reviews of a smaller Robinson Preserve restoration project which is sponsored by the Environmental Protection Agency (EPA) and is being funded separately under the Council-Selected Restoration Component.

The Council has reviewed the aforementioned environmental compliance documentation. Based on this review, the Council is proposing to adopt the PEIS to support the approval of implementation funds for Robinson Preserve, provided that the project is implemented in accordance with the terms and conditions of the CWA Section 404 permit. This permit and the associated documentation can be found here: https://www.restorethegulf.gov/funded-priorities-list. (See: Robinson Preserve Wetlands Restoration—Implementation.)

If approved by the Council, the funds to implement Robinson Preserve would be used to create habitat and natural flow regimes through hydrologic connections, as well as complete exotic and invasive vegetation removal, native planting, monitoring, community outreach, restoration practitioner education, and an inventory of potential Tampa Bay watershed hydrologic restoration projects.

The Initial FPL describes Robinson Preserve as a project to restore 140-acres of upland and wetland habitat (85 acres of upland habitat and 55 acres of created wetland and sub-tidal habitats). The actual acreage to be restored under this proposed FPL amendment would be 118.2 acres (57.6 acres of coastal upland habitat and 60.6 acres of wetland, open water sub-tidal, and open freshwater habitats). This acreage adjustment is the result of refinements in project design (in response to public input) and subtraction of acreage being restored through the complementary EPA restoration effort referenced above. The project design was reduced by 7 acres to balance public access interests, input from nearby residents and habitat suitability. The remainder of the acreage adjustment for this Robinson Preserve funding request is 14.8 acres, which is the amount of adjoining acreage that will be restored by the EPA.

While the acreage footprint of NOAA's Robinson Preserve project has decreased, the complexity and per unit cost of the project have increased. To maintain the long-term viability of the restoration design and protect existing habitats, the scope of the hydrologic restoration expanded to include more complex connections. The expanded scope also provides added benefits outside of the restoration footprint by integrating and hydrologically interconnecting the entire 632-acre preserve. NOAA has indicated that these changes, make up more than one third of the restoration implementation budget, increasing the wetland and sub-tidal creation cost per acre for the project. The total of $1,790,546 will be needed to implement this project.

Additional information on Robinson Preserve, including metrics of success, response to science reviews and more is available in an activity-specific appendix to the FPL, which can be found at https://www.restorethegulf.gov. Please see the table on page 25 of the FPL and click on: Robinson Preserve Wetlands Restoration (Implementation).

Under the Paperwork Reduction Act of 1995 (PRA) (44 U.S.C. 3501-3520), Federal agencies must obtain approval from the Office of Management and Budget (OMB) for each collection of information they conduct or sponsor. In addition, the PRA also requires Federal agencies to provide a 60-day notice in the Federal Register concerning each proposed collection of information, including each new proposed collection, each proposed extension of existing collection of information, and each reinstatement of previously approved information collection before submitting the collection to OMB for approval. To comply with this requirement, we are publishing this notice of a proposed data collection as described below.

Comments are invited on: (a) Whether the proposed collection of information is necessary for the proper performance of the functions of the agency, including whether the information shall have practical utility; (b) the accuracy of the agency's estimate of the burden of the proposed collection of information; (c) ways to enhance the quality, utility, and clarity of the information to be collected; (d) ways to minimize the burden of the collection of information on respondents, including through the use of automated collection techniques or other forms of information technology; and (e) estimates of capital or start-up costs and costs of operation, maintenance, and purchase of services to provide information. Burden means the total time, effort, or financial resources expended by persons to generate, maintain, retain, disclose or provide information to or for a Federal agency. This includes the time needed to review instructions; to develop, acquire, install and utilize technology and systems for the purpose of collecting, validating and verifying information, processing and maintaining information, and disclosing and providing information; to train personnel and to be able to respond to a collection of information, to search data sources, to complete and review the collection of information; and to transmit or otherwise disclose the information.

Assessment of Chemical Exposures (ACE) Investigations (OMB Control Number 0923-0051; expiration 3/31/2018)—Revision—Agency for Toxic Substances and Disease Registry (ATSDR).

The Agency for Toxic Substances and Disease Registry (ATSDR) is requesting to revise “Assessment of Chemical Exposures (ACE) Investigations” information collection project and seek a three-year OMB approval to assist state and local health departments after toxic substance spills or chemical incidents. The OMB Control number for this information collection expires 3/31/2018. We are renaming the form previously titled the Rapid Response Registry Form as the ACE Short Form. This revision better describes that we use the ACE Short Form in time-limited investigations where longer surveys are not possible. We do not use the form to establish registries. In addition, we are removing two insurance questions from the ACE Short Form, as we do not ask in the longer surveys and have never been asked as part of an ACE Investigation. There are no changes to the requested burden hours.

ATSDR has successfully completed three investigations to date. With the uses of this valuable mechanism, ATSDR would like to continue this impactful information collection. See below a brief summary of information collections approved under this tool:

• During 2015, in U.S. Virgin Islands there was a methyl bromide exposure at a condominium resort. Under this ACE investigation, awareness among pest control companies that methyl bromide currently prohibited in the homes and other residential settings. Additionally, awareness for clinicians about the toxicologic syndrome caused by exposure to methyl bromide and the importance of notifying first responders immediately when they have encountered contaminated patients.

• During 2016, ACE team conducted a rash investigation in Flint, Michigan. Persons exposed to Flint municipal water and had current or worsening rashes surveyed and referred too free dermatologist screening if desired. Findings revealed that when the city was using water from the Flint River, there were large swings in chorine, pH, and hardness, which could be one possible explanation for the eczema-related rashes.

• During 2016, ACE team also conducted a follow-up investigation for people whom been exposed to the Flint municipal water and sought care from the free dermatologists. Data analysis for this project is in process and results are pending. However, the follow-up interviews resulted in improving the exam and referral processes that were still on going at the time.

The ACE investigations focus on performing rapid epidemiological assessments to assist state, regional, local, or tribal health departments (the requesting agencies) to respond to or prepare for acute chemical releases.

The main objectives for performing these rapid assessments are to:

1. Characterize exposure and acute health effects of respondents exposed to toxic substances from discrete, chemical releases and determine their health statuses;

2. Identify needs (i.e., medical and basic) of those exposed during the releases to aid in planning interventions in the community;

3. Assess the impact of the incidents on health services use and share lessons learned for use in hospital, local, and state planning for chemical incidents; and

4. Identify cohorts may be followed and assessed for persistent health effects resulting from acute releases.

Because each chemical incident is different, it is not possible to predict in advance exactly what type of and how many respondents will be consented and interviewed too effectively evaluate the incident. Respondents typically include, but are not limited to emergency responders such as police, fire, hazardous material technicians, emergency medical services, and personnel at hospitals where patients from the incident were treated. Incidents may occur at businesses or in the community setting; therefore, respondents may also include business owners, managers, workers, customers, community residents, pet owners, and those passing through the affected area.

The multidisciplinary ACE team consisting of staff from ATSDR, the Centers for Disease Control and Prevention (CDC), and the requesting agencies that will be collecting data. ATSDR has developed a quickly tailored series of draft survey forms used in the field to collect data that will meet the goals of the investigation. ATSDR collections will be administered based on time permitted and urgency. For example, it is preferable to administer the general survey to as many respondents as possible. However, if there are time constraints, the shorter household survey or the ACE Short Form may be administered instead. The individual surveys collect information about exposure, acute health effects, health services use, medical history, needs resulting from the incident, communication during the release, health impact on children and pets, and demographic data. Hospital personnel are asked about the surge, response and communication, decontamination, and lessons learned.

Depending on the situation, data collected by face-to-face interviews, telephone interviews, written surveys, mailed surveys, or on-line surveys can be consider collected. Medical and veterinary charts may also be consider for review. In rare situations, an investigation might involve collection of clinical specimens.

ATSDR anticipates up to four ACE investigations per year. The number of participants has ranged from 30-715, averaging about 300 per year. Therefore, the total annualized estimated burden will be 591 hours per year. Participation in ACE investigations is voluntary and there are no anticipated costs to respondents other than their time.