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Code · REGISTER · 2006-02-27 · Import Administration, International Trade Administration, Department of Commerce · Notices

Notices. Notice; request for comments

7,749 words·~35 min read·/register/2006/02/27/06-1874

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BILLING CODE 3410-11-M DEPARTMENT OF COMMERCE International Trade Administration [A-588-867] Notice of Preliminary Negative Determination of Critical Circumstances: Metal Calendar Slides From Japan. AGENCY: Import Administration, International Trade Administration, Department of Commerce. SUMMARY: The Department of Commerce (Department) has preliminarily determined that critical circumstances do not exist with respect to imports of metal calendar slides
(MCS)from Japan. EFFECTIVE DATE: February 27, 2006. FOR FURTHER INFORMATION CONTACT: Scott Lindsay, Dara Iserson, or Kimberley Hunt, AD/CVD Operations, Office 6, Import Administration, International Trade Administration, U.S. Department of Commerce, 14th Street and Constitution Avenue, NW., Washington, DC 20230; telephone:
(202)482-0780,
(202)482-4052, or
(202)482-1272, respectively. SUPPLEMENTARY INFORMATION: Period of Investigation The POI is April 1, 2004 through March 31, 2005. This period corresponds to the four most recent fiscal quarters prior to the month of filing of the *Petition for Imposition of Antidumping Duties on Metal Calendar Slides from Japan* , (June 29, 2005) ( *Petition* ) involving imports from a market economy, and is in accordance with the Department's regulations. *See* 19 CFR 351.204(b)(1). Scope of Investigation For the purpose of this investigation, the products covered are MCS. The products covered in this investigation are “V” and/or “U” shaped MCS manufactured from cold-rolled steel sheets, whether or not left in black form, tin plated or finished as tin free steel (TFS), typically with a thickness from 0.19 mm to 0.23 mm, typically in lengths from 152 mm to 915 mm, typically in widths from 12 mm to 29 mm when the slide is lying flat and before the angle is pressed into the slide (although they are not typically shipped in this “flat” form), that are typically either primed to protect the outside of the slide against oxidization or coated with a colored enamel or lacquer for decorative purposes, whether or not stacked, and excluding paper and plastic slides. MCS are typically provided with either a plastic attached hanger or eyelet to hang and bind calendars, posters, maps or charts, or the hanger can be stamped from the metal body of the slide itself. These MCS are believed to be classified under Harmonized Tariff Schedule of the United States (HTSUS) subheading 7326.90.1000 (Other articles of iron and steel: Forged or stamped; but not further worked: Other: Of tinplate). This HTSUS number is provided for convenience and U.S. Customs and Border Protection purposes. The written description of the scope of this investigation is dispositive. Case History This investigation was initiated on July 19, 2005. *See Notice of Initiation of Antidumping Duty Investigation: Metal Calendar Slides from Japan* , 70 FR 43122 (July 26, 2005) (Initiation Notice). The preliminary determination was published on February 1, 2006. *See Notice of Preliminary Determination of Sales at Less Than Fair Value: Metal Calendar Slides from Japan* , 71 FR 5244 (February 1, 2006). Although critical circumstances were not alleged in *Petition* , Stuebing Automatic Machine Co. (Petitioner) has maintained since the inception of this investigation that there is a reasonable basis to believe or suspect that critical circumstances exist with regard to imports of MCS from Japan. *See Petition* at 35. In *Petition* , Petitioner requested that the Department monitor imports of MCS pursuant to section 351.206(g) of the Department's regulations. *Id* . In the initiation, the Department stated that it would monitor imports of MCS from Japan and would request that the U.S. Customs and Border Protection
(CBP)compile information on an expedited basis regarding entries of the subject merchandise. *See Initiation Notice* . Respondent, Nishiyama Kinzoku Co., Ltd. (Nishiyama), in its response to the Department's December 7, 2005, supplemental questionnaire, submitted the volume and value of its monthly shipments to the United States for calendar years 2003 through 2005. *See* Nishyama's Supplemental Questionnaire Response (December 27, 2005) at Exhibit 25. On January 10, 2006, the Department placed CBP IM 115 data covering the period of January 1, 2003 through October 31, 2005 on the record of this investigation. *See Memorandum from Dara Iserson, Case Analyst, through Thomas Gulgunn, Program Manager, to the File: Antidumping Duty Investigation of Metal Calendar Slides from Japan: The Placing of U.S. Bureau of Customs and Border Protection IM-115 Data on the Record* , (January 10, 2006) ( *IM 115 Memo* ). On January 19, 2006, petitioner alleged that critical circumstances exist with respect to imports of MCS from Japan. *See* Petitioners' Comments on Calculation Issues (January 19, 2006) at 17. Comments of the Parties Petitioner states that the record clearly demonstrates that shipments and imports surged during the post-Petition period ( *i.e.* , June-December 2005) when compared to the pre-Petition period ( *i.e.* , January-June 2005). *See* Petitioner's Comments on Calculation Issues (January 19, 2006) at 17. Petitioner claims that the *IM 115 Memo* demonstrates that imports were more than 25 percent greater in the post-Petition period in comparison to the pre-Petition period based on CBP's IM115 data. *Id* . Additionally, petitioner states that Nishiyama's shipment data shows an increase of more than 25 percent based on pieces and value. *Id* . (citing Nishiyama's Supplemental Questionnaire Response (December 27, 2005) at Exhibit 25). Petitioner states that these increases clearly meet the Department's standards for determining that imports were massive within a relatively short period. Analysis Section 733(e)(1) of the Tariff Act of 1930, as amended (“the Act”), provides that the Department will preliminarily determine that critical circumstances exist if there is a reasonable basis to believe or suspect that: (A)(i) there is a history of dumping and material injury by reason of dumped imports in the United States or elsewhere of the subject merchandise; or
(ii)the person by whom, or for whose account, the merchandise was imported knew or should have known that the exporter was selling the subject merchandise at less than its fair value and that there was likely to be material injury by reason of such sales; and,
(B)there have been massive imports of the subject merchandise over a relatively short period. Section 351.206(h)(1) of the Department's regulations provides that, in determining whether imports of the subject merchandise have been “massive,” the Department normally will examine:
(i)The volume and value of the imports;
(ii)seasonal trends; and
(iii)the share of domestic consumption accounted for by the imports. In addition, section 351.206(h)(2) of the Department's regulations provides that an increase in imports of 15 percent during the “relatively short period” of time may be considered “massive.” Section 351.206(i) of the Department's regulations defines “relatively short period'' as normally being the period beginning on the date the proceeding begins ( *i.e.* , the date the petition is filed) and ending at least three months later. The Department's regulations also provide, however, that if the Department finds that importers, exporters, or producers had reason to believe, at some time prior to the beginning of the proceeding, that a proceeding was likely, the Department may consider a period of not less than three months from that earlier time. In determining whether the relevant statutory criteria have been satisfied, we considered:
(i)Exporter-specific shipment data submitted in Nishiyama's December 27, 2005, response;
(ii)the CBP IM 115 data the Department placed on the record on January 10, 2006, and
(iii)the ITC preliminary injury determination. To determine whether there is a history of injurious dumping of the merchandise under investigation, in accordance with section 733(e)(1)(A)(i) of the Act, the Department normally considers evidence of an existing antidumping duty order on the subject merchandise in the United States or elsewhere to be sufficient. *See Preliminary Determination of Critical Circumstances: Steel Concrete Reinforcing Bars From Ukraine and Moldova* , 65 FR 70696 (November 27, 2000). With regard to imports of MCS from Japan, the petitioners make no specific mention of a history of dumping for Japan. We are not aware of any antidumping duty order in the United States or in any other country on MCS from Japan. For this reason, the Department does not find a history of injurious dumping of the subject merchandise from Japan pursuant to section 733(e)(1)(A)(i) of the Act. To determine whether the person by whom, or for whose account, the merchandise was imported knew or should have known that the exporter was selling the subject merchandise at less than its fair value and that there was likely to be material injury by reason of such sales in accordance with Section 733(e)(1)(A)(ii) of the Act, the Department normally considers margins of 25 percent or more for EP sales, or 15 percent or more for CEP transactions, sufficient to impute knowledge of dumping. *See e.g., Preliminary Determination of Sales at Less Than Fair Value: Certain Cut-to-Length Carbon Steel Plate from the People's Republic of China* , 62 FR 31972, 31978 (October 19, 2001). For Nishiyama, we determine that there is not a sufficient basis to find that the importer should have known that the exporter was selling the subject merchandise at less than its fair value and that there was likely to be material injury by reason of such sales pursuant to section 733(e)(1)(A)(ii) of the Act because the calculated preliminary margin for Nishiyama's EP sales, 7.68 percent, was less than 25 percent. *See Notice of Preliminary Determination of Sales at Less Than Fair Value: Metal Calendar Slides from Japan* , 71 FR 5244 (February 1, 2006). Nishayama did not have any CEP sales during this period. Because the knowledge criterion has not been met, we will not address the second criterion of whether imports were massive in the comparison period when compared to the base period. Regarding the companies subject to the “all others” rate, it is the Department's normal practice to conduct its critical circumstances analysis for these companies based on the experience of investigated companies. *See Notice of Final Determination of Sales at Less Than Fair Value: Certain Steel Concrete Reinforcing Bars From Turkey* , 62 FR 9737, 9741 (March 4, 1997). However, the Department does not automatically extend an affirmative critical circumstances determination to companies covered by the “all others” rate. *See Notice of Final Determination of Sales at Less Than Fair Value: Stainless Steel Sheet and Strip in Coils from Japan* , 64 FR 30574 and accompanying Issues and Decision Memorandum, at Comment 14 (June 8, 1999) ( *Stainless Steel from Japan* ). Instead, the Department considers the traditional critical circumstances criteria with respect to the companies covered by the “all others” rate. Consistent with *Stainless Steel from Japan* , the Department has, in this case, applied the traditional critical circumstances criteria to the “all others” category for the antidumping investigation of MCS from Japan. The dumping margin for the “all others” category in the instant case, 7.68 percent, does not exceed the 25 percent threshold necessary to impute knowledge of dumping. Therefore, we find that there is no reasonable basis to determine that importer knew or should have known that the exporter was selling the subject merchandise at less than its fair value and that there was likely to be material injury by reason of such sales. Conclusion Given the analysis discussed above, we preliminarily determine critical circumstances do not exist for imports of MCS from Japan. We will make a final determination concerning critical circumstances for MCS from Japan when we make our final dumping determination in this investigation, on April 10, 2006 (unless extended). International Trade Commission Notification In accordance with section 733(f) of the Act, we will notify the International Trade Commission of our determination. This determination is issued and published pursuant to sections 733(f) and 777(i)(1) of the Act. Dated: February 21, 2006. David M. Spooner, Assistant Secretary for Import Administration. [FR Doc. E6-2732 Filed 2-24-06; 8:45 am] BILLING CODE 3510-DS-S DEPARTMENT OF COMMERCE International Trade Administration [A-570-879] Notice of Extension of Time Limit for the Antidumping Administrative Review of Polyvinyl Alcohol From the People's Republic of China AGENCY: Import Administration, International Trade Administration, Department of Commerce. EFFECTIVE DATE: February 27, 2006. FOR FURTHER INFORMATION CONTACT: Lilit Astvatsatrian, AD/CVD Operations, Office 8, Import Administration, International Trade Administration, U.S. Department of Commerce, 14th Street and Constitution Avenue, NW., Washington, DC 20230; telephone:
(202)482-6412. Background On November 7, 2005, the Department of Commerce (“the Department”) published the preliminary results of the administrative review of the antidumping duty order on polyvinyl alcohol (“PVA”) from the People's Republic of China (“PRC”), covering the period August 11, 2003, through September 30, 2004. *See Polyvinyl Alcohol from the People's Republic of China: Preliminary Results of Antidumping Duty Administrative Review* , 70 FR 67434 (November 7, 2005) (“ *Preliminary Results* ”). In the *Preliminary Results* we stated that we would make our final determination for the antidumping duty review no later than 120 days after the date of publication of the preliminary results ( *i.e.* , March 7, 2006). Extension of Time Limit of Preliminary Results Section 751(a)(3)(A) of the Tariff Act of 1930, as amended (“the Act”), requires the Department to issue the final results in an administrative review within 120 days of publication date of the preliminary results. However, if it is not practicable to complete the review within this time period, the Department may extend the time limit for the final results to 180 days. Completion of the final results within the 120-day period is not practicable because this review involves certain complex issues, including the revision of an allocation methodology of co-products, application of by-products and self-produced inputs, and valuation of certain factors. Therefore, in accordance with section 751(a)(3)(A) of the Act, the Department is extending the time period for issuing the final results of review by 30 days until April 6, 2006. Dated: February 21, 2006. Stephen J. Claeys, Deputy Assistant Secretary for Import Administration. [FR Doc. E6-2731 Filed 2-24-06; 8:45 am] BILLING CODE 3510-DS-S DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration I.D. [081905B] Notice of Decision to Expand Scope of the Environmental Impact Statement Analyzing the Makah Tribe's Proposed Gray Whale Hunting and Reopening of Comment Period AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce. ACTION: Notice; request for comments. SUMMARY: NMFS announces our decision to expand the scope of the Makah Whale Hunt Environmental Impact Statement
(EIS)to include analysis of the proposed action on the affected environment under both the Marine Mammal Protection Act
(MMPA)and the Whaling Convention Act (WCA). Our previous notices of intent to prepare an EIS for the Makah Whale Hunt under the MMPA were published on August 25, 2005 and October 4, 2005. We are reopening the comment period for 30 days. DATES: Written or electronic comments from all interested parties are encouraged and must be received no later than 5 p.m. Pacific Standard Time March 29, 2006. ADDRESSES: All comments concerning the preparation of the EIS and NEPA process should be addressed to: Kassandra Brown, NMFS Northwest Region, Building 1, 7600 Sand Point Way NE., Seattle, WA 98115. Comments may also be submitted via fax (206)526-6426 Attn: Makah Whale Hunt EIS, or by electronic mail to *MakahEIS.nwr@noaa.gov* with a subject line containing the document identifier:“Makah Whale Hunt EIS.” FOR FURTHER INFORMATION CONTACT: Kassandra Brown, NMFS Northwest Region,
(206)526-4348. SUPPLEMENTARY INFORMATION: Background On August 25, 2005 (70 FR 49911) and October 4, 2005 (70 FR 57860), NMFS announced our intent to prepare an EIS pursuant to the National Environmental Policy Act
(NEPA)(42 U.S.C. *et seq.* ) and conduct public scoping meetings related to the Makah Indian Tribe's request that NMFS allow for limited treaty right hunting of eastern North Pacific gray whales by waiving the MMPA's (16 U.S.C. 1361 *et seq.* ) moratorium on take of marine mammals under section 101(a)(3)(A) (16 U.S.C. 1371(a)(3)(A)), and issuing regulations and any necessary permit(s). We opened a 60-day public comment period from August 25, 2005 to October 24, 2005, and held public scoping meetings at four locations in October 2005, including Neah Bay, Port Angeles, and Seattle, WA, and the Washington, DC area (Silver Spring, MD). We sought public input on the scope of the required NEPA analysis at that time, in addition to seeking comment for a range of reasonable alternatives and impacts to resources. Due in part to our examination of public comments related to the International Whaling Commission
(IWC)and WCA (16 U.S.C. 916 *et seq.* ) quota granting and issuance processes, we are expanding the scope of this EIS to include analysis of the WCA quota issuance. The MMPA waiver determination and the WCA quota issuance are best treated as connected actions (50 CFR 1508.25(a)(1)) for NEPA review because the Makah's proposed action of hunting whales cannot occur without NMFS' approvals under both statutory regimes. Request for Comments NMFS solicits written comments from the public. We request that the comments be as specific as possible with regard to our expansion of the scope of the EIS to include the WCA quota issuance. All comments and materials received, including names and addresses, will become part of the administrative record and may be released to the public. The environmental review of this project will be conducted in accordance with the requirements of the NEPA of 1969 as amended, Council on the Environmental Quality Regulations (40 CFR parts 1500 - 15080), other applicable Federal laws and regulations, and applicable policies and procedures. This notice is being furnished in accordance with 40 CFR 1501.7 of NEPA to obtain suggestions and information from other agencies and the public on the scope of issues and alternatives to be addressed in the EIS. Dated: February 17, 2006. D. Robert Lohn, Regional Administrator, Northwest Region, National Marine Fisheries Service. [FR Doc. E6-2735 Filed 2-24-06; 8:45 am] BILLING CODE 3510-22-S DEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration [I.D. 011806H] Taking of Marine Mammals Incidental to Specified Activities; On-ice Seismic Operations in the Beaufort Sea AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce. ACTION: Notice of receipt of application and proposed incidental take authorization; request for comments. SUMMARY: NMFS has received an application from ASRC Energy Services, Lynx Enterprises, Inc. (AES Lynx) for an Incidental Harassment Authorization
(IHA)to take marine mammals, by harassment, incidental to conducting on-ice vibroseis seismic operations in the Harrison Bay portion of the western U.S. Beaufort Sea in late winter/early spring (March through May 20, 2006). Pursuant to the Marine Mammal Protection Act (MMPA), NMFS is requesting comments on its proposal to issue an authorization to AES Lynx to incidentally take, by harassment, small numbers of two species of pinnipeds for a limited period of time this year. DATES: Comments and information must be received no later than March 29, 2006. ADDRESSES: Comments on the application should be addressed to Steve Leathery, Chief, Permits, Conservation and Education Division, Office of Protected Resources, National Marine Fisheries Service, 1315 East-West Highway, Silver Spring, MD 20910-3225, or by telephoning one of the contacts listed here. The mailbox address for providing email comments is *PR1.011806H@noaa.gov* . Please include in the subject line of the e-mail comment the following document identifier: 011806H. Comments sent via e-mail, including all attachments, must not exceed a 10-megabyte file size. A copy of the application containing a list of the references used in this document may be obtained by writing to this address or by telephoning the first contact person listed here and is also available at: *http://www.nmfs.noaa.gov/pr/permits/incidental.htm* FOR FURTHER INFORMATION CONTACT: Shane Guan, Office of Protected Resources, NMFS,
(301)713-2289, ext 137 or Brad Smith, Alaska Region, NMFS,
(907)271-5006. SUPPLEMENTARY INFORMATION: Background Sections 101(a)(5)(A) and
(D)of the MMPA (16 U.S.C. 1361 *et seq.* ) direct the Secretary of Commerce to allow, upon request, the incidental, but not intentional, taking 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. Permission 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, and that 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.” Section 101(a)(5)(D) of the MMPA established an expedited process by which citizens of the United States can apply for an authorization to incidentally take small numbers of marine mammals by harassment. Except for certain categories of 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]. Section 101(a)(5)(D) establishes a 45-day time limit for NMFS review of an application followed by a 30-day public notice and comment period on any proposed authorizations for the incidental harassment of marine mammals. Within 45 days of the close of the comment period, NMFS must either issue or deny issuance of the authorization. Summary of Request On October 24, 2005, NMFS received an application from AES Lynx for the taking, by harassment, of two species of marine mammals incidental to conducting an on-ice seismic survey program. The seismic operations will be conducted in the Harrison Bay portion of the western U.S. Beaufort Sea. The proposed survey would be conducted from March through about May 20, 2006. The operation would consist of laying seismic cables with geophones on the frozen sea ice, employing the vibroseis method of energy (sound source) production, and recording the seismic signals. Water depths in the majority of the planned survey area are less than 3 m (10 ft). The purpose of the project is to gather information about the subsurface of the earth by measuring acoustic waves, which are generated on or near the surface. The acoustic waves reflect at boundaries in the earth that are characterized by acoustic impedance contrasts. Description of the Activity The seismic surveys use the “reflection” method of data acquisition. Seismic exploration uses a controlled energy source to generate acoustic waves that travel through the earth, including sea ice and water, as well as sub-sea geologic formations, and then uses ground sensors to record the reflected energy transmitted back to the surface. When acoustic energy is generated, compression and shear waves form and travel in and on the earth. The compression and shear waves are affected by the geological formations of the earth as they travel in it and may be reflected, refracted, diffracted or transmitted when they reach a boundary represented by an acoustic impedance contrast. Vibroseis seismic operations use large trucks with vibrators that systematically put variable frequency energy into the earth. Sea ice thickness of at least 1.2 m (4 ft) is required to support the various equipment and vehicles used to transport seismic equipment offshore for exploration activities. These ice conditions generally exist from 1 January until 31 May in the Beaufort Sea. Several vehicles are normally associated with a typical vibroseis operation. One or two vehicles with survey crews move ahead of the operation and mark the energy input points. Crews with wheeled vehicles often require trail clearance with bulldozers for adequate access to and within the site. Crews with tracked vehicles are typically limited by heavy snow cover and may require trail clearance beforehand. With the vibroseis technique, activity on the surveyed seismic line begins with the placement of sensors. All sensors are connected to the recording vehicle by multi-pair cable sections. The vibrators move to the beginning of the line and begin recording data. The vibrators begin vibrating in synchrony via a simultaneous radio signal to all vehicles. In a typical survey, each vibrator will vibrate four times at each location. The entire formation of vibrators subsequently moves forward to the next energy input point (e.g. 67 m, or 220 ft, in most applications) and repeats the process. In a typical 16- to 18-hour day, surveys will complete 6-16 km (4 to 10 linear miles) in 2-dimensional seismic operations and 24 to 64 km (15 to 40 linear miles) in a 3-dimensional seismic operation. Description of Habitat and Marine Mammals Affected by the Activity A detailed description of the Beaufort Sea ecosystem can be found in several documents (Corps of Engineers, 1999; NMFS, 1999; Minerals Management Service (MMS), 1992, 1996, 2001). A more detailed description of the seismic survey activities and affected marine mammals can be found in the AES Lynx application (see ADDRESSES ). Four marine mammal species are known to occur within the proposed study area: ringed seal ( *Phoca hispida* ), bearded seal ( *Erignathus barbatus* ), spotted seal ( *Phoca larghs* ), and polar bear ( *Ursus maritimus* ). The applicant will seek a take Authorization from the U.S. Fish and Wildlife Service (USFWS) for the incidental taking of polar bears because USFWS has management authority for this species. Spotted seals are not known winter users of the project area, therefore, no incidental take is expected for this species. Ringed seals are widely distributed throughout the Arctic basin, Hudson Bay and Strait, and the Bering and Baltic seas. There is no reliable worldwide population assessment for ringed seals, however, it is estimated to be in the millions (Reeves *et al.* , 1992). Ringed seals inhabiting northern Alaska belong to the subspecies *P. h. hispida* , and they are year-round residents in the Beaufort Sea. The Alaska stock of ringed seals in the Bering-Chukchi-Beaufort area is estimated at 1 to 1.5 (Frost, 1985) or 3.3 to 3.6 million seals (Frost *et al.* , 1988). Although there are no recent population estimates in the Beaufort Sea, Bengston *et al.*
(2000)estimated ringed seal abundance from Barrow south to Shismaref in a portion of the Chukchi Sea to be 245,048 animals from aerial surveys flown in 1999. The NMFS 2003 Stock Assessment Report (Angliss and Lodge, 2004) states that there are at least that many ringed seals in the Beaufort Sea. Frost *et al.*
(1999)reported that observed densities within the area of industrial activity along the Beaufort Sea coast were generally similar between 1985-87 and 1996-98, suggesting that the regional population has been relatively stable during this 13-year period of industrial activity. During winter and spring, ringed seals inhabit landfast ice and offshore pack ice. Seal densities are highest on stable landfast ice but significant numbers of ringed seals also occur in pack ice (Wiig *et al.* , 1999). Seals congregate at holes and along cracks or deformations in the ice (Frost *et al.* , 1999). Breathing holes are established in landfast ice as the ice forms in autumn and are maintained by seals throughout winter. Adult ringed seals maintain an average of 3.4 holes per seal (Hammill and Smith, 1989). Some holes may be abandoned as winter advances, probably in order for seals to conserve energy by maintaining fewer holes (Brueggeman and Grialou, 2001). As snow accumulates, ringed seals excavate lairs in snowdrifts surrounding their breathing holes, which they use for resting and for the birth and nursing of their single pups in late March to May (McLaren, 1958; Smith and Stirling, 1975; Kelly and Quakenbush, 1990). Pups have been observed to enter the water, dive to over 10 m (33 ft), and return to the lair as early as 10 days after birth (Brendan Kelly, pers comm to CPA, June 2002), suggesting pups can survive the cold water temperatures at a very early age. Mating occurs in late April and May. From mid-May through July, ringed seals haul out in the open air at holes and along cracks to bask in the sun and molt. Most on-ice seismic activity occurs from late January through May. The seasonal distribution of ringed seals in the Beaufort Sea is affected by a number of factors but a consistent pattern of seal use has been documented since aerial survey monitoring began over 20 years ago. Seal densities have historically been substantially lower in the western than the eastern part of the Beaufort Sea (Burns and Kelly, 1982; Kelly, 1988). Frost *et al.*
(1999)reported consistently lower ringed seal densities in the western versus eastern sectors they surveyed in the Beaufort Sea during 1996, 1997, and 1998. The relatively low densities appear to be related to shallow water depths in much of the area occurring between the shore and the barrier islands. This area of historically low ringed seal density is the focus of much of the recent on-ice seismic surveys. The bearded seal has a circumpolar distribution in the Arctic, and it is found in the Bering, Chukchi, and Beaufort seas (Jefferson *et al.* , 1993). There are no reliable population estimates for bearded seals in the Beaufort Sea or in the activity area (Angliss and Lodge, 2004), but numbers are considerably higher in the Bering and Chukchi seas, particularly during winter and early spring. Early estimates of bearded seals in the Bering and Chukchi seas range from 250,000 to 300,000 (Popov, 1976; Burns, 1981). Based on the available data there is no evidence of a decline in the bearded seal population. Bearded seals are generally associated with pack ice and only rarely use shorefast ice (Jefferson *et al.* , 1993). Bearded seals occasionally have been observed maintaining breathing holes in annual ice and even hauling out from holes used by ringed seals (Mansfield, 1967; Stirling and Smith, 1977). However, since bearded seals are normally found in broken ice that is unstable for on-ice seismic operation, bearded seals will be rarely encountered during seismic operations. Additional information on these species is also available at: *http://www.nmfs.noaa.gov/pr/readingrm/MMSARS/sar2003akfinal.pdf* with updated information available at: *http://www.nmfs.noaa.gov/pr/readingrm/MMSARS/2005alaskasummarySARs.pdf* Potential Effects on Marine Mammals Incidental take may result from short-term disturbances by noise and physical activity associated with on-ice seismic operations. These operations have the potential to disturb and temporarily displace some seals. Pup mortality could occur if any of these animals were nursing and displacement were protracted. However, it is unlikely that a nursing female would abandon her pup given the normal levels of disturbance from the proposed activities, potential predators, and the typical movement patterns of ringed seal pups among different holes. Seals also use as many as four lairs spaced as far as 3,437 m (11,276 ft) apart. In addition, seals have multiple breathing holes. Pups may use more holes than adults, but the holes are generally closer together than those used by adults. This indicates that adult seals and pups can move away from seismic activities, particularly since the seismic equipment does not remain in any specific area for a prolonged time. Given those considerations, combined with the small proportion of the population potentially disturbed by the proposed activity, impacts are expected to be negligible for the ringed and bearded seal populations. Not taking into account water depth (i.e., the activity area is marginal seal habitat, with a majority of the water in the area less than 3 m (10 ft) deep), the estimated number of ringed seals potentially within the vibroseis activity area is expected to be very low. Frost and Lowry
(1999)reported an observed density of 0.61 ringed seals per km 2 on the fast ice from aerial surveys conducted in spring 1997 of an area (Sector B2) overlapping the activity area, which is in the range of densities (0.28-0.66) reported for the Northstar development from 1997 to 2001 (Moulton *et al.* , 2001). This value (0.61) was adjusted to account for seals hauled out but not sighted by observers (x 1.22, based on Frost *et al.* (1988)) and seals not hauled out during the surveys (x 2.33, based on Kelly and Quakenbush (1990)) to obtain the 1.73 seal per km 2 . This estimate covered an area from the coast to about 2-20 miles beyond the activity area; and it assumed that habitat conditions were uniform and, therefore, it was not adjusted for water depth. Since most of the activity area is within water less than 3 m (10 ft) deep, which Moulton *et al.*
(2001)reported for Northstar supported about five times fewer seals (0.12-0.13 seals/km 2 ) than was reported by Frost and Lowry (i.e., 0.61), the actually seal density is expected to be much lower in the proposed project area. In the winter, bearded seals are restricted to cracks, broken ice, and other openings in the ice. On-ice seismic operations avoid those areas for safety reasons. Therefore, any exposure of bearded seals to on-ice seismic operations would be limited to distant and transient exposure. Bearded seals exposed to a distant on-ice seismic operation might dive into the water. An indication of their low numbers is provided by the results of aerial surveys conducted east of the activity area near the Northstar and Liberty project sites. Three to 18 bearded seals were observed in these areas compared to 1,911 to 2,251 ringed seals in the spring (May/June) of 1999 through 2001 (Moulton *et al.* , 2001; Moulton and Elliott, 2000; and Moulton *et al.* , 2000). Similarly only small numbers of bearded seals would be expected to occur in the activity area, where habitat is even less favorable because of the shallow water area. Consequently, no significant effects on individual bearded seals or their population are expected, and the number of individuals that might be temporarily disturbed would be very low. In addition, the area affected by seismic operations represents only a small fraction of the Beaufort Sea pinniped habitat, any impacts would be localized and temporary. Sea-ice surface rehabilitation is often immediate, occurring during the first episode of snow and wind that follows passage of the equipment over the ice. Potential Effects on Subsistence Residents of the village of Nuiqsut are the primary subsistence users in the activity area. The subsistence harvest during winter and spring is primarily ringed seals, but during the open-water period both ringed and bearded seals are taken. Nuiqsut hunters may hunt year round; however, most of the harvest has been in open water instead of the more difficult hunting of seals at holes and lairs (McLaren, 1958; Nelson, 1969). Subsistence patterns may be reflected through the harvest data collected in 1992, when Nuiqsut hunters harvested 22 of 24 ringed seals and all 16 bearded seals during the open water season from July to October (Fuller and George, 1997). Harvest data for 1994 and 1995 show 17 of 23 ringed seals were taken from June to August, while there was no record of bearded seals being harvested during these years (Brower and Opie, 1997). Only a small number of ringed seals was harvested during the winter to early spring period, which corresponds to the time of the proposed on-ice seismic operations. Based on harvest patterns and other factors, on-ice seismic operations in the activity area are not expected to have an unmitigable adverse impact on subsistence uses of ringed and bearded seals because:
(1)Operations would end before the spring ice breakup, after which subsistence hunters harvest most of their seals.
(2)Operations would temporarily displace relatively few seals, since most of the habitat in the activity area is marginal to poor and supports relatively low densities of seals during winter. Displaced seals would likely move a short distance and remain in the area for potential harvest by native hunters (Frost and Lowry, 1988; Kelly *et al.* , 1988).
(3)The area where seismic operations would be conducted is small compared to the large Beaufort Sea subsistence hunting area associated with the extremely wide distribution of ringed seals. In order to ensure the least practicable adverse impact on the species and the subsistence use of ringed seals, all activities will be conducted as far as practicable from any observed ringed seal structure. Finally, the applicant will consult with subsistence hunters of Nuiqsut and provide the community, the North Slope Borough, and the Inupiat Community of the North Slope with information about its planned activities (timing and extent) before initiating any on-ice seismic activities. Mitigation and Monitoring The following mitigation measures are proposed for the subject surveys. All activities will be conducted as far as practicable from any observed ringed or bearded seal lair and no energy source will be placed over a ringed or bearded seal lair. Only vibrator-type energy-source equipment shown to have similar or lesser effects than proposed will be used. AES Lynx will provide training for the seismic crews so they can recognize potential areas of ringed seal lairs and adjust the seismic operations accordingly. Ringed seal pupping occurs in ice lairs from late March to mid-to-late April (Smith and Hammill, 1981). Prior to commencing on-ice seismic surveys in mid-March, experienced Inupiat subsistence hunters would be hired to screen for lairs along the planned on-ice seismic transmission routes in areas where water depths exceed 3 m (10 ft) to identify and determine the status of potential seal structures along the planned on-ice transit routes. The seal structure survey will be conducted before selection of precise transit routes to ensure that seals, particularly pups, are not injured by equipment. The locations of all seal structures will be recorded by Global Positioning System (GPS), staked, and flagged with surveyor's tape. Surveys will be conducted 150 m (492 ft) to each side of the transit routes. Actual width of route may vary depending on wind speed and direction, which strongly influence the efficiency and effectiveness of dogs at locating seal structures. Few, if any, seals inhabit ice-covered waters shallower than 3 m (10 ft) due to water freezing to the bottom or poor prey availability caused by the limited amount of ice-free water. AES Lynx will also continue to work with NMFS, other Federal agencies, the State of Alaska, Native communities of Barrow and Nuiqsut, and the Inupiat Community of the Arctic Slope
(ICAS)to assess measures to further minimize any impact from seismic activity. A Plan of Cooperation will be developed between AES Lynx and Nuiqsut to ensure that seismic activities do not interfere with subsistence harvest of ringed or bearded seals. The level of impacts, while anticipated to be negligible, will be assessed by conducting a second seal structure survey shortly after the end of the seismic surveys. A single on-ice survey will be conducted by biologists on snow machines using a GPS to relocate and determine the status of seal structures located during the initial survey. The status (active vs. inactive) of each structure will be determined to assess the level of incidental take by seismic operations. The number of active seal structures abandoned between the initial survey and the final survey will be the basis for enumerating possible harassment takes. If dogs are not available for the initial survey, takings will be estimated by using observed densities of seals on ice reported by Moulton *et al.*
(2001)for the Northstar development, which is approximately 24 nm (46 km) from the eastern edge of the proposed activity area. In the event that seismic surveys can be completed in that portion of the activity area with water depths greater than or equal to 3 m (10 ft) before mid-March, no field surveys would be conducted of seal structures. Under this scenario, seismic surveys would be completed before pups are born and disturbance would be negligible. Therefore, take estimates would be determined for only that portion of the activity area exposed to seismic surveys after mid-March, which would be in water depths of 3 m (10 ft) or less. Take for this area would be estimated by using the observed density (13/100 km 2 ) reported by Moulton *et al.*
(2001)for water depths between 0 to 3 m (0 to 10 ft) in the Northstar project area, which is the only source of a density estimate stratified by water depth for the Beaufort Sea. This would be an overestimation requiring a substantial downward adjustment to better reflect the likely take of seals using lairs, since few if any of the structures in these water depths would be used for birthing, and the Moulton et al.
(2001)estimate includes all seals. Reporting An annual report must be submitted to NMFS within 90 days of completing the year's activities. Endangered Species Act
(ESA)NMFS has determined that no species listed as threatened or endangered under the ESA will be affected by issuing an incidental harassment authorization under section 101(a)(5)(D) of the MMPA to AES Lynx for this on-ice seismic survey. National Environmental Policy Act
(NEPA)The information provided in Environmental Assessments
(EAs)prepared in 1993 and 1998 for winter seismic activities led NOAA to conclude that implementation of either the preferred alternative or other alternatives identified in the EA would not have a significant impact on the human environment. Therefore, an Environmental Impact Statement was not prepared. The proposed action discussed in this document is not substantially different from the 1993 and 1998 actions, and a reference search has indicated that no significant new scientific information or analyses have been developed in the past several years that would warrant new NEPA documentation. Preliminary Conclusions The anticipated impact of winter seismic activities on the species or stock of ringed and bearded seals is expected to be negligible for the following reasons:
(1)The activity area supports a small proportion (<1 percent) of the ringed and bearded seal populations in the Beaufort Sea.
(2)Most of the winter-run seismic lines will be on ice over shallow water where ringed seals are absent or present in very low abundance. Most of the activity area is near shore and/or in water less than 3 m (10 ft) deep, which is generally considered poor seal habitat. Moulton *et al.*
(2001)reported that only 6 percent of 660 ringed seals observed on ice in the Northstar project area were in water between 0 to 3 m (0 to 10 ft) deep.
(3)For reasons of safety and because of normal operational constraints, seismic operators will avoid moderate and large pressure ridges, where seal and pupping lairs are likely to be most numerous.
(4)The sounds from energy produced by vibrators used during on-ice seismic programs typically are at frequencies well below those used by ringed seals to communicate (1000 Hz). Thus, ringed seal hearing is not likely to be very good at those frequencies and seismic sounds are not likely to have strong masking effects on ringed seal calls. This effect is further moderated by the quiet intervals between seismic energy transmissions.
(5)There has been no major displacement of seals away from on-ice seismic operations (Frost and Lowry, 1988). Further confirmation of this lack of major response to industrial activity is illustrated by the fact that there has been no major displacement of seals near the Northstar Project. Studies at Northstar have shown a continued presence of ringed seals throughout winter and creation of new seal structures (Williams *et al.* , 2001).
(6)Although seals may abandon structures near seismic activity, studies have not demonstrated a cause and effect relationship between abandonment and seismic activity or biologically significant impact on ringed seals. Studies by Williams *et al.* (2001), Kelley *et al.* (1986, 1988) and Kelly and Quakenbush
(1990)have shown that abandonment of holes and lairs and establishment or re-occupancy of new ones is an ongoing natural occurrence, with or without human presence. Link *et al.*
(1999)compared ringed seal densities between areas with and without vibroseis activity and found densities were highly variable within each area and inconsistent between areas (densities were lower for 5 days, equal for 1 day, and higher for 1 day in vibroseis area), suggesting other factors beyond the seismic activity likely influenced seal use patterns. Consequently, a wide variety of natural factors influence patterns of seal use including time of day, weather, season, ice deformation, ice thickness, accumulation of snow, food availability and predators as well as ring seal behavior and population dynamics. In winter, bearded seals are restricted to cracks, broken ice, and other openings in the ice. On-ice seismic operations avoid those areas for safety reasons. Therefore, any exposure of bearded seals to on-ice seismic operations would be limited to distant and transient exposure. Bearded seals exposed to a distant on-ice seismic operation might dive into the water. Consequently, no significant effects on individual bearded seals or their population are expected, and the number of individuals that might be temporarily disturbed would be very low. As a result, AES Lynx believes the effects of on-ice seismic are expected to be limited to short-term and localized behavioral changes involving relatively small numbers of seals. NMFS has preliminarily determined, based on information in the application and supporting documents, that these changes in behavior will have no more than a negligible impact on the affected species or stocks of ringed and bearded seals. Also, the potential effects of the proposed on-ice seismic operations during 2006 are unlikely to result in more than small numbers of seals being affected and will not have an unmitigable adverse impact on subsistence uses of these two species. Proposed Authorization NMFS proposes to issue an IHA to AES Lynx for conducting seismic surveys in the Harrison Bay area of the western U.S. Beaufort Sea, provided the previously mentioned mitigation, monitoring, and reporting requirements are incorporated. NMFS has preliminarily determined that the proposed activity would result in the harassment of small numbers of marine mammals; would have no more than a negligible impact on the affected marine mammal stocks; and would not have an unmitigable adverse impact on the availability of species or stocks for subsistence uses. Information Solicited NMFS requests interested persons to submit comments and information concerning this request (see ADDRESSES ). Dated: February 21, 2006. James H. Lecky, Director, Office of Protected Resources, National Marine Fisheries Service. [FR Doc. E6-2740 Filed 2-24-06; 8:45 am] BILLING CODE 3510-22-S COMMODITY FUTURES TRADING COMMISSION Sunshine Act Meetings Time and Date: 2:30 p.m., Wednesday, March 8, 2006. Place: 1155 21st St. NW., Washington, DC, 9th Floor Conference Room. Status: Closed. Matters to be Considered: Registered Futures Association Review. FOR MORE INFORMATION CONTACT: Jean A. Webb, 202-418-5100. Jean A. Webb, Secretary of the Commission. [FR Doc. 06-1874 Filed 2-23-06; 2:54 pm]
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  • 50 CFR 1508.25(a)(1)
  • 40 CFR 1501.7
  • 50 CFR 216.103
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