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Daily Rules, Proposed Rules, and Notices of the Federal Government

DEPARTMENT OF COMMERCE

National Oceanic and Atmospheric Administration

50 CFR Part 223

[Docket No. 070910507-0037-02]

RIN 0648-AV94

Endangered and Threatened Wildlife and Plants: Final Rulemaking To Establish Take Prohibitions for the Threatened Southern Distinct Population Segment of North American Green Sturgeon

AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule and notice of availability of a final environmental assessment.
SUMMARY: This final ESA section 4(d) rule represents the regulations that we, the National Marine Fisheries Service (NMFS), believe necessary and advisable to conserve the threatened Southern Distinct Population Segment of North American green sturgeon (Acipenser medirostris;hereafter Southern DPS). We apply the prohibitions listed under ESA section 9 for the Southern DPS, and we highlight specific categories of activities that are likely to result in take of Southern DPS fish. We do not find it necessary and advisable to apply the take prohibitions to certain categories of activities that contribute to conserving the Southern DPS. We also provide a variety of methods by which take of the Southern DPS may be authorized. This document also announces the availability of a final draft environmental assessment (EA) that analyzes the environmental impacts of promulgating the 4(d) regulations for the Southern DPS.
DATES: The effective date of this final rule is July 2, 2010.
ADDRESSES: Reference materials regarding this final rule can be obtained via the Internet athttp://www.swr.nmfs.noaa.govor by submitting a request to the Assistant Regional Administrator, Protected Resources Division, Southwest Region, NMFS, 501 West Ocean Blvd., Suite 4200, Long Beach, CA 90802-4213.
FOR FURTHER INFORMATION CONTACT: Melissa Neuman, NMFS, Southwest Region (562) 980-4115, or Lisa Manning, NMFS, Office of Protected Resources (301) 713-1401.
SUPPLEMENTARY INFORMATION:

Background

We determined that the Southern DPS is at risk of extinction in the foreseeable future throughout all or a significant portion of its range and listed the species as threatened under the ESA on April 7, 2006 (71 FR 17757). At that time we summarized the process for considering the application of ESA section 9 prohibitions to the threatened Southern DPS. In the case of threatened species, ESA section 4(d) states that the Secretary shall decide whether, and to what extent, to extend the ESA section 9(a) prohibitions, including those regarding take of the species, and authorizes us to issue regulations we consider necessary and advisable for the conservation of the species. Such regulations may include any or all of the prohibitions that automatically apply to endangered species. Those prohibitions, in part, make it illegal for any person subject to the jurisdiction of the United States to take the listed species. The term “take” means to harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or attempt to engage in any such conduct. (16 U.S.C. 1532(19)). The term “harm” is defined as any act which actually kills or injures fish or wildlife. Such an act may include significant habitat modification or degradation which actually kills or injures fish or wildlife by significantly impairing essential behavioral patterns, including breeding, spawning, rearing, migrating, feeding, or sheltering. (50 CFR 222.102).

Whether take prohibitions or other protective regulations are necessary or advisable is in large part dependent onthe biological status of the species and potential impacts of various activities on the species. Green sturgeon have persisted for millions of years through cycles of naturally occurring perturbations that have likely presented short- and long-term challenges to the species' survival. We conclude that the threatened Southern DPS of North American green sturgeon is currently at risk of extinction primarily because of human-induced “takes” involving elimination of freshwater spawning habitat, degradation of freshwater and estuarine habitat quality, water diversions, fishing, and other causes. Therefore, we conclude that extending the take prohibitions to the Southern DPS is necessary and advisable.

When the final rule to list the Southern DPS was published on April 7, 2006, we solicited the public for information that would inform the ESA section 4(d) rulemaking. Specific information requested can be found in the final rule (71 FR 17757; April 7, 2006). No substantive additional comments, beyond those that had been received during prior solicitations for information, were received.

Public scoping workshops held on May 31 and June 1, 2006, helped advance our understanding of the threats that are likely to result in the take of Southern DPS fish. In cases where evidence of direct take due to a particular activity was lacking, activities that have caused take of species that use similar habitats (i.e.,migratory, spawning, and rearing), consume similar prey types, have similar morphologies and/or physiologies, and/or share other life history requirements (e.g.,white sturgeon (Acipenser transmontanus) and Chinook salmon (Oncorhynchus tshawytscha)) were identified and considered for their effects on Southern DPS fish. More detailed justification regarding the use of take information for surrogate species (i.e.,one that shares a similar life history or habitat requirements) to infer the take potential of an activity on the Southern DPS fish is provided in previousFederal Registernotices (70 FR 17386, April 6, 2005; 71 FR 17757, April 7, 2006).

On May 21, 2009, we proposed protective regulations under section 4(d) of the ESA to extend the prohibitions listed under ESA sections 9(a)(1)(A) through 9(a)(1)(G) for the threatened Southern DPS, but included certain exceptions and exemptions from the take prohibitions for activities that we have determined to be adequately protective of the Southern DPS (74 FR 23822).

Summary of Comments and Information Received in Response to the Proposed Rule and Draft Environmental Assessment

The public comment period for the proposed rule and draft Environmental Assessment (EA) was open from May 21, 2009, through July 6, 2009. During the comment period, NMFS received 7 written comments on the proposed rule and draft EA from various agencies, non-governmental organizations, and individuals. A summary of the comments and NMFS' responses to those comments are presented here.

Comments and Responses

Comment 1:One commenter requested clarification in the draft EA regarding the exception for emergency fish rescue activities under Alternative B. Specifically, the commenter was unclear what 4(d) programs were referred to in the sentence stating that “[p]roject-related activities * * * would not be considered an emergency fish rescue activity and would be subject to review under ESA section 7 or 10, or under another 4(d) program.”

Response:We corrected the sentence in the final EA to read “Project-related activities * * * would not be considered an emergency fish rescue activity and would be subject to review under ESA section 7 or 10.” We removed the phrase “or under another 4(d) program” because the ESA 4(d) Rule does not include a 4(d) program to cover such project-related activities.

Comment 2:One commenter stated that the draft EA needs to describe the specific categories of activities to which the take prohibitions would be applied under Alternative C.

Response:The final EA was revised to clarify that under Alternative C, the take prohibitions would apply to the same specific categories of activities and in the same areas as described under Alternative A. Those categories of activities are: Commercial, recreational, and tribal fisheries; collecting or handling Southern DPS fish for any purpose; habitat-altering activities affecting passage or spawning and rearing habitat in the Central Valley, California; operation of water diversion, dredging, and power plant activities resulting in entrainment or impingement of Southern DPS fish; application or discharge of pollutants adjacent to or within waterways occupied by Southern DPS fish; and introduction or release of non-native species adjacent to or within waterways occupied by Southern DPS fish.

Comment 3:One commenter felt that the proposed rule listed dredging as a threat to only juvenile green sturgeon and wanted NMFS to acknowledge that adult Southern DPS fish have the potential to be found in dredging areas outside the Central Valley, San Francisco Bay, Suisun Bay and San Pablo Bay.

Response:The final rule was revised to acknowledge that dredging is a potential threat to adult green sturgeon. Dredging occurs in the following areas where adults also occur: The Lower Sacramento River, Sacramento-San Joaquin Delta, Elkhorn Slough, Suisun Bay, San Pablo Bay, San Francisco Bay, Noyo Harbor, and Humboldt Bay in California; Coos Bay, Yaquina Bay, Tillamook Bay, and Nehalem Bay in Oregon; the Lower Columbia River Estuary, the Lower Columbia River, Willapa Bay, Grays Harbor, and Puget Sound in Washington; and coastal U.S. marine waters (74 FR 52300, October 9, 2009). Although adults occur in areas where dredging takes place, we don't have any direct evidence of the effect that dredging has on adult green sturgeon.

Comment 4:One commenter asked why the draft EA specifically excludes the Channel Islands from the list of areas known to be occupied by Southern DPS green sturgeon, noting that this exclusion was not mentioned in the proposed critical habitat designation for the species (73 FR 52084, September 8, 2008).

Response:At this time we do not have any data showing that Southern DPS green sturgeon occur in waters around the California Channel Islands and we specifically noted this in the description of occupied areas in the draft EA. However, the protections under the ESA 4(d) rule would apply to Southern DPS green sturgeon wherever they are found. Thus, if a Southern DPS green sturgeon occurred in the waters around the Channel Islands, the take prohibitions under the ESA 4(d) rule would apply to that fish. Because of similarity of appearance, any green sturgeon occurring in the marine environment (including estuaries in Washington, Oregon, and Humboldt Bay) would be considered the listed species as they cannot be identified as belonging to a particular DPS unless genetic samples are taken and analyzed. The final EA was revised to include a statement clarifying this.

Comment 5:Two commenters felt that the five alternative approaches need to be described in greater detail and that the geographic limitations and distinctions of the proposed rule and alternatives are not clearly laid out. Further clarification was requested.

Response:The final EA was revised to more clearly describe the geographic limitations and distinctions between the various alternatives considered.

Comment 6:One commenter recommended that NMFS consult with the Pacific Fishery Management Council (PFMC) as early in the process as possible concerning the effects of the ESA 4(d) Rule on fisheries managed under the PFMC.

Response:NMFS is currently working with the PFMC regarding the potential effects of the West Coast groundfish bottom trawl fishery on the listed Southern DPS of green sturgeon and its designated critical habitat.

Comment 7:One commenter stated that the San Francisco Bay is not used as habitat for green sturgeon and that regulating take and requiring consultation on activities that are not limiting the recovery of the Southern DPS diverts staff resources from other permitting actions that would have positive effects.

Response:The best available data for the San Francisco Bay indicate that green sturgeon are present in both Central and South San Francisco Bay, albeit in low numbers compared to other parts of the San Francisco Bay/Delta Region. The survey methods and sampling gear used in studies within San Francisco Bay were not designed to target green sturgeon, and thus the data may not be truly representative of the relative levels of green sturgeon use among the bays and the Delta. For example, given that all green sturgeon must pass through Central San Francisco Bay in their migrations to and from the ocean, it is expected that larger numbers of green sturgeon are using this area at certain times of the year. In addition, the catch data do not provide information about the distribution of juvenile green sturgeon throughout the bays and the Delta. Based on the best available information, juvenile green sturgeon are believed to distribute widely throughout the bays and Delta for feeding and rearing and be present in all months of the year. Detailed fishery-dependent data for the San Francisco Bay is provided in the final critical habitat designation (74 FR 52300, October 9, 2009).

Comment 8:One commenter strongly supports the 4(d) rule and provided the information that green sturgeon are vulnerable to selenium toxicity from feeding on the overbite clam. The commenter stated that selenium toxicity can cause reproductive failure and the threat of reduced recruitment through selenium toxicity puts additional stress on the Southern DPS population.

Response:NMFS appreciates the information provided regarding green sturgeon vulnerability to selenium toxicity. Recent studies have shown that green sturgeon are more sensitive to selenium than white sturgeon and continued monitoring of selenium levels in sediments and research on the sensitivity of green sturgeon to this and other contaminants would be supported (Kaufmanet al.,2008).

Comment 9:One commenter felt that including marine coastal waters as green sturgeon critical habitat is unjustified as there is no reliable data on the take of the Southern DPS in coastal waters.

Response:Comments pertaining to critical habitat were addressed in the final critical habitat designation for green sturgeon (74 FR 52300, October 9, 2009). Activities that occur in coastal marine waters that may cause take of green sturgeon include bottom trawling, disposal of dredged material, hydrokinetic projects and pollution from commercial shipping.

Comment 10:One commenter stated that sand mining operations in San Francisco and Suisun Bays are highly regulated and there is very little evidence that sand mining in the San Francisco Bay-Delta Estuary negatively impacts green sturgeon or their habitat. The commenter requested that additional exceptions be included for activities such as sand mining that pose a low risk of take.

Response:In 2006, NMFS completed formal consultation with the U.S. Corps of Engineers under section 7 of the ESA for sand mining activities in the San Francisco and Suisun Bay region. The resulting biological opinion concluded that sand mining activities were not likely to jeopardize threatened green sturgeon (NMFS, 2006). An Incidental Take Statement (that remains discretionary until a 4(d) rule has been promulgated) was included with the biological opinion that provides protection to the sand miners for the entrainment of one green sturgeon per year for each of the three sand mining companies operating in the region at the time the biological opinion was written.

Comment 11:One commenter stated that we do not have data to differentiate between Northern DPS and Southern DPS green sturgeon in fisheries bycatch, but we require a Fisheries Management and Evaluation Plan (FMEP) to include measures specifically to protect Southern DPS green sturgeon.

Response:Acknowledging the fact that we cannot tell the difference between NDPS and SDPS fish due to similarity of appearance, the FMEPs must address green sturgeon and do not require that the DPS be determined.

Comment 12:One commenter stated that the green sturgeon fishery was mismanaged and that more care should have been taken to prevent the fishery from becoming overfished.

Response:NMFS acknowledges that a lack of monitoring and directed management of the green sturgeon has likely contributed to its current threatened status. However, since the listing, academic institutions, the states, NMFS and the tribes have been conducting more comprehensive studies that focus on green sturgeon in an effort to better understand its biology, status and recovery needs. It is our hope that finalizing this 4(d) rule and enforcing the take prohibitions will further the conservation of the species and aid in its recovery.

Comment 13:One commenter provided the information that there is a new surge in the green sturgeon population in Yaquina Bay, and feels that listing green sturgeon as threatened in this area is inaccurate and unfounded.

Response:NMFS appreciates the information provided regarding observations of green sturgeon in Yaquina Bay and agrees that additional studies are needed to better understand the use of coastal estuaries (including Yaquina Bay) and coastal marine waters by both DPSs of green sturgeon. Southern DPS presence in Yaquina Bay was confirmed in 2006 by the detection of one tagged Southern DPS green sturgeon (pers. comm. with Dan Erickson, ODFW, September 3, 2008). The Southern DPS was listed based on several threats, including the concentration of spawning to one river. Each Southern DPS green sturgeon carries the listing with it wherever it goes as the listing is not limited by geographic area. We acknowledge the commenter's observations suggesting that the number of green sturgeon using Yaquina Bay has increased.While this news is promising:(1) We recognize that green sturgeon may experience sporadic recruitment success depending on many factors that are not well understood; and (2) this uncertainty coupled with a lack of population abundance estimates and a limited understanding of population structure has led us to adopt regulations necessary and advisable for the conservation of the Southern DPS. We will conduct periodic status reviews of both DPSs and as more information becomes available we will revise our regulations if necessary.

Comment 14:One commenter felt that the requirement that research or monitoring that involves action, permitting or funding by a Federal agency must still comply with therequirements of ESA section 7(a)(2) negates the exception from the take prohibitions for all researchers and stated that Federal employees who can fulfill all other requirements cannot use this exception. If non-Federal studies do not need to be analyzed in order to ensure that they would not jeopardize the species, then it seems counterintuitive that Federal studies with the same requirements would create jeopardy. The commenter also felt that the requirement that the activity must comply with required state reviews or permits negates the exception because as part of the application process, state permits require a copy of the authorization from NMFS when working with species listed under the ESA.

Response:Under the 4(d) Rule, we can exempt a non-Federal entity from the take prohibitions, but cannot exempt Federal agencies from the jeopardy standard under section 7 of the ESA. Compliance with section 7(a)(2) of the ESA would be required, but the consultation would be limited to an analysis of whether the activity may jeopardize the continued existence of the species or destroy or adversely modify critical habitat, and would not involve an assessment of take. Section 7 of the ESA does not apply to non-Federal entities. Although Federal employees are still subject to the section 7 jeopardy standard, under the exception they would not be required to obtain an ESA section 10(a)(1)(A) permit for their research/monitoring activities if conducted according to the exception criteria. The Federal biologists carrying out research activities would need to obtain state permits regardless of whether Federal take prohibitions are in place or not. The exception simplifies the NMFS review and approval process for research activities and relies on the state review and permits to minimize impacts related to the research activities. In the state application, applicants will need to identify that their activities meet the exception criteria and will need to indicate that they have submitted the information to NMFS or indicate that NMFS has confirmed that their activities meet the exception criteria.

Comment 15:One commenter felt that NMFS has not taken into account the extent of the existing regulatory programs and improvement to the health of the San Francisco Bay-Delta ecosystem that has taken place over the last 30 years and stated that certain activities are already regulated under other Federal, state and local programs that directly govern activities that NMFS stated could result in the take of green sturgeon. The commenter recommended that NMFS provide exceptions from the take prohibitions for navigation channel and harbor berths dredging, dredged material placement, mineral extraction and maintenance and installation of in-water and shoreline structures. The commenter also recommended that exceptions for the small business category of construction activities be considered.

Response:NMFS acknowledges that many of the activities that may cause take of green sturgeon are already regulated by existing Federal, state and local laws and regulations, and appreciates any efforts that have been made to protect and improve habitats where green sturgeon reside. However, these laws, regulations, and programs may not specifically address green sturgeon and may not be as protective of green sturgeon as the 4(d) Rule. For example, there is a 50-year dredging program in the San Francisco Bay region that currently has not implemented measures that would specifically protect green sturgeon. Construction activities conducted by small businesses may also not include measures that would be adequately protective of green sturgeon. However, any protections already afforded to green sturgeon through existing programs would be considered in NMFS' analyses under section 7 or section 10 of the ESA.

Comment 16:One commenter requested that a public hearing be held in coastal Oregon prior to publishing the final rule.

Response:A workshop to discuss the ESA 4(d) rule prohibitions and exceptions/exemptions with state fishery management agencies, NMFS, and representatives from the fishing industry was held in Newport, Oregon on March 15, 2010.

Comment 17:One commenter requested clarification on the Protection/Conservation Measures or Benefits under Table 1, as emergency rescue and habitat restoration indicates that there are no benefits provided to green sturgeon in these activities.

Response:The Note section under Table 1 was clarified to state that the “Protective/conservation measures or benefits” column refers to whether the activity, as it is currently conducted, includes protections or benefits to green sturgeon. Emergency rescue activities and habitat restoration activities that are not conducted according to the criteria under the exceptions do not provide benefits to green sturgeon and are therefore not covered under the exceptions. If these activities may cause take of green sturgeon, that take must be covered under section 7 or 10 of the ESA, or come under compliance with the exceptions criteria.

Comment 18:One commenter requested clarification in the draft EA regarding which states' recreational fishing regulations, prior to 2006, did not differentiate between white sturgeon and green sturgeon.

Response:The final EA was revised to clarify that, prior to 2006, state recreational fishing regulations in Washington, Oregon, and California did not differentiate between white sturgeon and green sturgeon.

Comment 19:One commenter suggested updating the 2005 reference for the Environmental Water Account because the program expired in 2007 and a revised program is currently in place with adjusted water amounts to augment instream flows.

Response:The final EA was updated to remove the outdated reference for the Environmental Water Account.

Spatial Context for ESA 4(d) Rule Application

As described in aFederal Registernotice (68 FR 4433) published on January 23, 2003, we determined that based on genetic and behavioral information, North American green sturgeon is comprised of at least two DPSs that qualify as species under the ESA: (1) A northern DPS consisting of populations originating from coastal watersheds northward of and including the Eel River (“Northern DPS”); and (2) a southern DPS consisting of populations originating from coastal watersheds south of the Eel River (“Southern DPS”) and the Central Valley of California. These geographic boundaries were largely defined by genetic evidence indicating that, among samples from rivers where green sturgeon are known to spawn (i.e., the Rogue, Klamath, and Sacramento rivers), the Rogue and Klamath River fish were more similar to one another than to the Sacramento River fish (Israelet al.,2004). Although the Southern DPS boundaries are defined by the species' genetic structure and its likely strong homing capabilities and spawning site fidelity, the spatial extent of the ESA listing and take prohibitions for the Southern DPS is not confined to areas south of the Eel River. Detailed information on occurrences of the Southern DPS green sturgeon is provided in the proposed 4(d) rule (74 FR 23822, May 21, 2009).

Sections 10(a)(1)(A) and 10(a)(1)(B) provide exceptions to the section 9 take prohibitions. NMFS can authorize research and enhancement through section 10(a)(1)(A) permits andincidental take through section 10(a)(1)B) permits. While this rule applies the section 9 take prohibitions to any activity that takes the Southern DPS, we wanted to determine which activities would most likely impede efforts necessary to conserve and recover the Southern DPS. To do this, we considered the following questions: (1) For which activities do we have evidence of take of Southern DPS fish; (2) for those activities where evidence of Southern DPS take does not exist, is there evidence of take of surrogate species that share similar biological requirements with Southern DPS fish; (3) are protective/conservation measures underway to reduce or minimize take imposed by some activities; and (4) are there additional protective/conservation measures that, if taken, would reduce take to low enough levels such that particular activities could proceed without appreciably reducing the likelihood of survival and recovery of the Southern DPS?

Commercial and Recreational Fisheries Activities

Take of Southern DPS fish occurs during commercial and recreational fishing activities throughout the range of North American green sturgeon. However, quantifying fishery-related take reliably and assessing its effects is challenging because: (1) Northern and Southern DPS fish are morphologically indistinguishable from one another and when green sturgeon have been taken, they have rarely been identified to the DPS level; (2) until recently some fisheries did not report green sturgeon take; and (3) in cases where data on take of green sturgeon is available, methods for estimating the total annual take by a fishery are still being developed. The two DPSs co-inhabit some coastal areas and bays in Northern California, Oregon, and Washington, and the proportion of Southern DPS fish contributing to overall populations in these areas may be high (e.g.,80 percent in the Columbia River; J. Israel, UC Davis, 2008, unpublished data). Thus, while we know that fisheries-related take is occurring, we are uncertain how this take is apportioned between the two DPSs, different locales, and different types of fisheries.

Green sturgeon are taken as bycatch in white sturgeon fisheries, salmon gillnet fisheries, coastal groundfish trawl fisheries, and coastal California halibut set net fisheries (Adamset al.,2006; R. Rasmussen, NMFS, 2006, unpublished data; J. Ferdinandet al.,NMFS, 2006, unpublished data). These fisheries have taken large numbers of green sturgeon historically and have been cited as factors in the decline of the species (70 FR 17386, April 6, 2005; 71 FR 17757, April 7, 2006). For example, from 1985 to 1993, the harvest of green sturgeon in commercial fisheries in the Columbia River and in Washington ranged from 3,000 to over 7,500 fish per year. Sport fishing harvest during the same period ranged from less than 100 to over 500 fish, with the majority harvested from the Columbia River. Since 1993, commercial and sport harvest of green sturgeon has declined in the Columbia River and Washington fisheries to about 150 fish harvested in 2003 (Adamset al.2006).

State recreational and commercial fishing regulations have been revised in response to evidence of recent sturgeon declines and to the listing of the Southern DPS. In California, the California Fish and Game Commission approved revised regulations, effective March 1, 2007, to prohibit retention of green sturgeon, alter the slot (size) limit (142 cm) and bag limit (one individual daily; 3 individuals annually) for white sturgeon, and require implementation of a sturgeon report card system. Recently, the California Fish and Game Commission approved revised regulations, effective March 1, 2010, that prohibit all sturgeon fishing in the upper Sacramento River where southern DPS green sturgeon spawn. The Washington Fish and Wildlife Commission adopted a permanent rule to prohibit retention of green sturgeon in recreational fisheries statewide effective May 1, 2007. In addition, the Washington Department of Fish and Wildlife and Oregon Department of Fish and Wildlife voted to prohibit the retention of green sturgeon in Columbia River recreational fisheries from Bonneville Dam to the mouth of the river, effective January 1, 2007. For commercial fisheries, the retention of green sturgeon has been prohibited in the Columbia River by emergency rule since July 2006 and statewide in Washington by permanent rule since January 26, 2007. The Oregon Fish and Wildlife Commission voted to prohibit the retention of green sturgeon in commercial nearshore fisheries, effective January 1, 2010, and is prohibiting the retention of green sturgeon in recreational fisheries statewide, effective April 1, 2010. The State of California has prohibited commercial fishing for sturgeon since 1917. While these emergency and permanent rules offer Southern DPS fish protection, it is unclear whether the state closures will remain in effect over the long-term and ultimately what overall effect the closures will have on the Southern DPS.

Commercial groundfish trawl fisheries occurring in coastal waters along the West Coast of North America take green sturgeon. Fish are primarily caught as bycatch off the coast of California. Over a 6-year period, from 2001-2007, 450 green sturgeon were reported as by-catch in trawls off the California coast. Almost all green sturgeon caught in this fishery are released alive (J. Majewski, NMFS, 2006, unpublished data), but the long-term fate of these individuals remains unknown. A program for monitoring green sturgeon take was established with the NMFS Observer Program in January 2007 to determine the amount of take, the DPS of the green sturgeon that are caught (through genetic analysis), and in the future to address the long-term fate of these individuals through tagging. Additional measures that may be implemented to protect green sturgeon and the Southern DPS include zero retention of green sturgeon in all fisheries, minimizing incidental catch, monitoring of incidental catch, increased enforcement, fisheries closures in areas important to the species, and outreach and education on proper catch and release methods and green sturgeon conservation issues.

Tribal Fisheries

Green sturgeon are taken as bycatch in tribal salmon and sturgeon fisheries conducted by the Quinault Tribe in coastal Washington waters. Tribal harvest of green sturgeon occurs in Grays Harbor and at the mouth of tributaries, primarily the Chehalis and Humptulips rivers. The number of green sturgeon taken annually from 1985 to 2003 ranged from less than 10 to almost 200 fish (Adamset al.,2006). In 2006, the Quinault Tribe implemented zero retention of green sturgeon for the Grays Harbor fishery (J. Schumacker, Quinault Indian Tribe, 2006, personal communication). A large proportion of green sturgeon caught in Grays Harbor may be Southern DPS fish, based on hydroacoustic tracking information (Lindley and Moser, 2006) and a genetic study indicating that approximately 50 percent of green sturgeon sampled in Grays Harbor belong to the Southern DPS (J. Israel and B. May, UC Davis, 2006, unpublished data).

Green sturgeon are also taken, though rarely, in tribal commercial and subsistence salmon fisheries occurring in freshwater and coastal marine waters of Washington, including the Strait of Juan de Fuca, Georgia and Rosario straits, and Puget Sound (W. Beattie, NW Indian Fisheries Commission, 2008, personal communication). The Yurokand Hoopa Tribes harvest green sturgeon in the Klamath River in California, but most of the fish are believed to be Northern DPS green sturgeon (J. Israel, UC Davis, 2006, unpublished data). Overall, the take of green sturgeon in tribal fisheries has been low compared to non-tribal fisheries. Measures that may be implemented to conserve the Southern DPS include a commitment by the Quinault Tribe, and perhaps other Tribes within the occupied range of the Southern DPS, to minimize take and monitor incidental catch of green sturgeon over the long-term.

Poaching

Poaching is a potential threat to the Southern DPS. In recent years, several arrests have been made for illegal harvest of white sturgeon for their meat and roe from the Sacramento River (CDFG, 2003 and 2006), the Sacramento-San Joaquin Delta (CDFG, 2004), and the lower Columbia River (Cohen, 1997). In the lower Columbia River, an estimated 2,000 sturgeon were killed over a 5-year period by poachers to produce caviar (Cohen, 1997). Poaching may be less significant than incidental take associated with white sturgeon sportfishing (Williamson, 2003). However, the tendency for green sturgeon to form aggregations for long periods of time may make them easy targets for poachers (Ericksonet al.,2002). Increased public outreach and awareness, increased enforcement, and heavier sentences and fines for poachers may help to protect green sturgeon from the threats of poaching.

Research and Monitoring Activities

Scientific research and monitoring of the Southern DPS contributes valuable information for the management, conservation, and future status reviews of the species. However, collection or handling associated with scientific research and monitoring constitutes take and may result in stress, injuries, or mortality of Southern DPS fish. In recent years, much research and monitoring effort has been placed on: (1) Tracking the movements and habitat use of Southern DPS fish by using a variety of non-lethal tagging techniques; and (2) identifying the DPS of origin using non-lethal genetic sampling techniques. These two research and monitoring activities provide information crucial to the development of an effective recovery strategy for the species. The best available information indicates that these procedures, when done according to accepted protocols, result in minimal short-term stress to the fish and do not result in lethal take. Important scientific information (e.g.,genetic, pathologic, taxonomic, meristic) is also gathered from already dead individuals, thereby providing valuable data without putting the species at further risk.

Emergency Rescue and Salvage Activities

Emergency fish rescue activities, including aiding sick, injured, or stranded fish, disposing of dead fish, or salvaging dead fish for use in scientific studies, are forms of take. Rescue activities would benefit the Southern DPS in the event of emergency situations that result from natural disasters, man-made habitat alterations, national defense activities, security emergencies, etc. Allowing take of the Southern DPS for emergency rescue and salvage activities is likely to enhance survival and recovery of the listed species. However, it is important that measures be taken to investigate emergency events during or after they have occurred in order to determine whether a non-ESA-compliant action(s) necessitated the rescue or salvage.

Habitat-Altering Activities

Dams and water diversion structures have caused the elimination, obstruction, or delay of passage for green sturgeon and other sturgeon species and may reduce body condition and reproductive success. For example, dams and water diversion structures have been observed to obstruct or disrupt the upstream spawning migrations of shortnose sturgeon in the lower Cape Fear River, NC (Moser and Ross, 1995). White sturgeon have also been found stranded behind the Fremont Weir in the Yolo Bypass, CA (Harrell and Sommer, 2006). Disruptions in migration may cause fish to stop their upstream migration or may delay access to spawning habitats (Moser and Ross, 1995). The inability to reach spawning habitats may cause fish to spawn in habitats of lower quality, resulting in decreased recruitment (Cooke and Leach, 2004). Several dams and water diversion structures exist along the spawning migration route of the Southern DPS and would be expected to have detrimental effects similar to those observed in surrogate species. Fish passage studies at the Red Bluff Diversion Dam (RBDD) in the Sacramento River show that the RBDD blocks the upstream migration of the Southern DPS when the gates are lowered between May 15 and September 15 (Heubleinet al.,2006; Brown, 2007). Mitigation measures have been implemented, including the raising of RBDD gates from September 15 to June 15 each year to allow fish passage and the protection and restoration of spawning and rearing habitat along the Sacramento River, bays, and the Sacramento-San Joaquin Delta. However, when the gates are raised, green sturgeon may become disoriented or suffer injuries due to the high velocity of water passing under the gates (M. Tucker, NMFS, 2007, personal communication). Between May 18 and June 10, 2007, carcasses of 10 adult Southern DPS fish (168-226 cm total length) were found at (n=2) or downstream (n=8) of RBDD (E. Campbell, USFWS, 2007, unpublished data). Locations of the retrieved carcasses and necropsy results suggest that the fish suffered mortality due to injuries inflicted by the gates at RBDD. Installation of adequate fish passage facilities, modification of existing passage facilities, or other provisions to specifically aid sturgeon passage at dams and diversions, and application of other mitigation measures, such as salvage operations, would contribute to the protection of the Southern DPS.

The elimination, obstruction, or delay of downstream passage is a concern for larval and juvenile stages of the Southern DPS, as are habitat-altering activities that destroy, modify, or curtail spawning or rearing habitats for egg, larval, or juvenile stages. Specific concerns include, but are not limited to: Increased sediment input or runoff into streams; filling in or isolation of stream channels, side channels, and intermittent waters; direct removal or alteration of physical structures; and obstruction of downstream migration.

Increased input or runoff of fine sediments into streams may result from a number of activities including, but not limited to, mining, logging, farming, grazing, and bridge and road construction. Increased erosion and sediment input or runoff into streams caused by land use and other human activities have been found to reduce the survival and successful development of eggs and embryos of salmon and other fish species (Scrivener and Brownlee, 1989; Owenet al.,2005). The effects on green sturgeon eggs and embryos are likely to be similar. Green sturgeon eggs are large and dense and likely sink into rock crevices or attach to hard surfaces (Denget al.,2002; Kynardet al.,2005). Once hatched, green sturgeon embryos remain near the bottom and use rocks as cover (Kynardet al.,2005). Excess fine sediments can compromise successful development by burying already-deposited eggs, reducing interstitial dissolved oxygen available for eggs (Scrivener and Brownlee, 1989), or filling areas used by embryos for cover. Thus, Southern DPS eggs or embryosmay be taken due to habitat-altering activities that increase input of fine sediments or runoff into spawning or rearing habitat. The effect that increased input of fine sediments or runoff has at the individual, population and species levels will depend on the temporal and spatial extent of habitat change. The only way to determine this is to analyze particular activities on a case-by-case basis.

The filling in or isolation of stream channels, side channels, and intermittent waters may destroy or block access to rearing habitats, or impede or delay downstream migration by trapping larvae and juveniles that have entered these areas. Activities that fill in or isolate waters include, but are not limited to, the installation of tide gates, culverts, and debris- or sediment-trapping road crossing structures. These activities and their effects are a concern for listed salmon and steelhead and may also affect larval and juvenile Southern DPS fish. However, we currently lack the information needed to quantitatively assess these effects. Although relatively large numbers of juveniles have been collected in shallow areas of the Santa Clara shoal in the Sacramento-San Joaquin Delta (Radtke, 1966), the use of stream channels, side channels, and intermittent waters as rearing habitat by green sturgeon larvae and juveniles has not been documented. Information regarding the use of these habitats by early life stages of green sturgeon is needed.

Direct removal or alteration of physical structures essential to the integrity and function of the Southern DPS's spawning or rearing habitat, including rocks, soil, gravel, and vegetation, may adversely affect the growth and survival of larvae and juveniles. Green sturgeon likely use specific substrate types at different life stages, but observations of early life stages of green sturgeon in the field are lacking. Studies suggest that spawning most likely occurs over cobble substrates that provide crevices and cover for eggs (Kynardet al.,2005; Nguyen and Crocker, 2006). However, in a laboratory study of substrate use by post-hatch larval green sturgeon, growth and survival was greatest in flat slate-rock substrates that provided cover and sufficient foraging opportunities (Nguyen and Crocker, 2006). Survival was low in cobble substrates, because larvae became trapped in crevices and died; whereas in sand substrates, the cause of lower survival and growth was attributed to the ingestion of sand particles similar in size to food particles (Nguyen and Crocker, 2006). Juveniles likely use deep pool habitats with rock structure during the winter (Kynardet al.,2005). Removal or alteration of these physical structures (i.e.cobble for spawning and egg development; flat rock for larval rearing; deep pool habitats with rock structure for juvenile rearing) may reduce spawning or rearing success rates. Additional studies regarding the use of spawning habitats by Southern DPS early life stages and the effects of removing or altering physical components of Southern DPS spawning habitat on recruitment success are encouraged.

The construction and maintenance of dams and water diversion structures may impede or delay downstream migration and alter habitats important to larval and juvenile stages of the Southern DPS. Dams and water diversions may block downstream migration of larvae and juveniles, unless fish transport or bypass facilities exist. Passage across dams and water diversion structures may also disorient or injure larvae and juveniles and make them more vulnerable to predation, as has been observed for juvenile salmonids at RBDD (Bigelow and Johnson, 1996; Gaines and Martin, 2002). The actual construction of dams and water diversion structures may cause increased erosion and sedimentation and disrupt or alter physical structures in spawning or rearing habitats, with effects as described in the previous paragraphs.

While existing laws require mining, timber harvest, and other resource use plans to address erosion and other adverse impacts on stream habitats, these laws may not be adequate to protect the Southern DPS. Additional measures that would help reduce potential adverse impacts on Southern DPS fish are: (1) Protection of riparian habitat by limiting activities that cause erosion, sediment input or runoff into streams, or roadway and other linear development near or across streams; (2) construction of fish protection and passage facilities; and (3) limiting the temporal and/or spatial scopes of habitat alteration activities that occur in and near spawning and rearing locations.

Habitat Restoration

The primary purpose of habitat restoration is to restore natural aquatic or riparian habitat conditions or processes over the long-term. Specifically, we define habitat restoration as the process of reestablishing a self-sustaining habitat that closely resembles natural conditions in terms of structure and function for the Southern DPS. A variety of habitat-altering activities such as barrier removal or modification to restore natural water flows, river and estuarine bed restoration, natural bank protection, restoration of native vegetation, removal of non-native species, and removal of contaminated sediments has been used to reestablish natural river and estuarine functions over the long-term. Although take of green sturgeon could potentially occur during the course of completing restoration activities, we do not have evidence that these types of activities have taken the Southern DPS or a surrogate species. It is likely that these activities are important to the conservation and recovery of the Southern DPS.

Entrainment and Impingement Risks

The operation of water diversions, power generating projects, and dredging activities pose entrainment and impingement threats to all life stages of the Southern DPS. We define entrainment to mean the incidental trapping of any life stage of fish within waterways or structures that carry water being diverted for anthropogenic use. We define impingement to mean the entrapment of any life stage of fish on the outer part of any structure (e.g.,intake structures, screening devices) that separates water traveling a natural course of passage from water that is being diverted for anthropogenic use. Unscreened water diversions number in the hundreds to thousands in the Sacramento River and the Sacramento-San Joaquin Delta (Herren and Kawasaki, 2001). Factors that determine the entrainment risk of fish at diversions include the location and size of fish. A study of fish entrainment at an unscreened diversion in the Sacramento River documented entrainment of fish ranging in size from 9 to 59 mm fork length (FL) in July 2000 and 2001 (Nobrigaet al.,2004). Green sturgeon were not among the species documented in the study, but Southern DPS larvae and small juveniles within the size range of 9-59 mm FL occur in the Sacramento River at that time of year and are believed to also be at risk of entrainment at unscreened diversions. Entrainment of juvenile green sturgeon has been documented at the state and Federal fish facilities in the south Sacramento-San Joaquin Delta, where fish are salvaged before they enter the pumps (Adamset al.,2006). Programs to install fish screens at water diversions are being implemented and many major diversions have already been screened. Installation of fish screens, construction of bypass and other fish protection facilities (Bigelow and Johnson, 1996; Gaines and Martin, 2002), adjustmentsin the timing of operations, and continuation of fish salvage operations, where applicable, would help minimize and mitigate entrainment of Southern DPS fish at water diversions.

Evidence exists for the impingement of green sturgeon in the operation of coastal power plants using cooling water intake systems, and there is a possibility that green sturgeon are also entrained at power plants. Two juvenile green sturgeon were impinged and died on cooling water intake screens at the now retired Contra Costa Plant Units 1-5 in 1978-1979 and at the Moss Landing Power Plant in 2006 (C. Raifsnider and J. Steinbeck, Tenera Environmental, 2006, personal communication). Current conservation efforts include the installation of screens to reduce entrainment, studies of fish impingement and entrainment at power plants, and laws that require the minimization of fish impingement and entrainment. Other actions that can be taken to reduce impingement and entrainment include altering the time of day when water intake pumps are operated, altering the velocity of water intake, and the use of alternative cooling systems that do not require water intake.

Dredging operations in freshwater rivers, bays, and estuaries where Southern DPS fish occur may pose entrainment risk. Although entrainment of green sturgeon in dredging operations has not been documented, the effects could be significant. Approximately 2,000 juvenile white sturgeon were entrained during operation of a large suction dredge in the lower Columbia River (Buell, 1992). Juvenile green sturgeon would be expected to face similar entrainment risks from dredging operations because they are also bottom-oriented and occur in habitats similar to white sturgeon. Dredging may also be a potential threat to adult green sturgeon because they occur in areas where dredging operations take place. Dredging stirs up the sediments causing the release of contaminants that would have adverse impacts on growth, reproductive development, and reproductive success of green sturgeon. Long-term management strategies for San Francisco Bay dredging operations have established regional environmental work windows, or periods of time when certain fish species are not likely to be present in a location. Currently, it is believed that Southern DPS juveniles reside in San Francisco, Suisun, and San Pablo bays year-round so environmental work windows will likely not be effective in reducing the risks of dredging operations to the Southern DPS in these locations (Ganssle, 1966; Miller, 1972; CDFG, 2002; Jahn, 2006; BDAT, 2009). However, the use of specific types of dredging equipment with modified designs would reduce the entrainment risk to Southern DPS fish from dredging operations.

Pesticides and Discharge of Pollutants

The application of pesticides adjacent to or within waterways that contain any life stage of the Southern DPS may adversely affect their growth and reproductive success. Several pesticides have been detected in the Sacramento River Basin at levels that are likely to be harmful to aquatic life (Domagalskiet al.,2000). The accumulation of industrial chemicals and pesticides such as polychlorinated biphenyls (PCBs), dichloro-diphenyl-trichloroethanes (DDTs), and chlordanes in white sturgeon gonad, liver, and muscle tissues affects growth and reproductive development and results in lower reproductive success (Faireyet al.,1997; Fosteret al.,2001a; Fosteret al.,2001b; Kruse and Scarnecchia, 2002; Feistet al.,2005; Greenfieldet al.,2005). Green sturgeon are believed to experience similar risks from contaminants, although their exposure may be reduced because a greater proportion of their subadult and adult lives are spent in marine waters (70 FR 17386, April 6, 2005). Pesticides may also indirectly affect green sturgeon through effects on their prey species. For example, green sturgeon are believed to enter Willapa Bay to feed on burrowing ghost shrimp (Neotrypaea californiensis), which have declined in abundance due to the deliberate application of carbaryl (Moser and Lindley, 2006).

The discharge or dumping of toxic chemicals or other pollutants into waters and areas where Southern DPS fish occur would be expected to reduce their growth and reproductive success. Pollutants including mercury, selenium, and arsenic have been detected in white sturgeon gonad, liver, and muscle tissues and are believed to affect growth, reproductive development, and reproductive success (Faireyet al.,1997; Daviset al.,2002; Kruse and Scarnecchia, 2002; Greenfieldet al.,2005; Webbet al.,2006). Again, the effects on green sturgeon are likely to be similar.

Under the Federal Clean Water Act, acceptable levels for contaminants in waterways have been established by the States and the U.S. Environmental Protection Agency (EPA). Entities must also obtain National Pollutant Discharge Elimination System (NPDES) permits to discharge contaminants. However, NPDES permits are not required for irrigated agriculture and agricultural stormwater runoff. Furthermore, the national standards for use of pesticides and toxic substances may not be conservative enough to adequately protect the Southern DPS as was found for listed salmonids in recent draft and final jeopardy biological opinions issued by NMFS to the EPA (NMFS 1998, NMFS 2000, NMFS 2008). Thus, programs to aid agricultural producers in meeting NMFS-imposed water quality standards may be required to minimize adverse impacts on the Southern DPS.

Non-Native Species Introductions

Non-native species are a continuing problem in freshwater rivers and coastal bays and estuaries and may affect the Southern DPS through trophic interactions. Introduced species, such as striped bass in the Sacramento River and the Sacramento-San Joaquin Delta, may prey on green sturgeon juveniles. Non-native species may also replace prey species of green sturgeon and result in greater bioaccumulation of contaminants. For example,Potamocorbula amurensis,a non-native bivalve, has become widespread in the San Francisco Bay and the Sacramento-San Joaquin Delta and has replaced other common prey items for white sturgeon.P. amurensisis an efficient bioaccumulator of selenium, a reproductive toxin that causes deformities in embryos and reduced hatchability of eggs, and has been linked with increased selenium levels in white sturgeon (Linvilleet al.,2002).P. amurensishas also been identified in the gut contents of at least one green sturgeon (CDFG, 2002). Non-native species may also alter the Southern DPS' habitat or compete with the Southern DPS for space or food. Although existing laws prohibit the release of non-native species into the environment, accidental and intentional introduction of non-native species remains a problem. Eradication programs for non-native species, increased public education and outreach, and increased fines or penalties for the release of non-native species would help to alleviate this problem.

4(d) Protective Regulations for the Southern DPS

We apply the prohibitions listed under ESA sections 9(a)(1)(A) through 9(a)(1)(G) for the Southern DPS, including all the ESA section 9(a)(1)(B) and 9(a)(1)(C) prohibitions (the “take prohibitions”) except for specific activities described below (see Exceptions, Criteria for Exceptions, andReporting Requirements). ESA section 9(a)(1)(A) states that it is unlawful to import or export endangered species into or from the United States; ESA section 9(a)(1)(B) states that it is illegal to take endangered species within the United States or the territorial sea of the United States; ESA section 9(a)(1)(C) states that it is illegal to take endangered species upon the high seas; ESA section 9(a)(1)(D) states that it is illegal to possess, sell, deliver, carry, transport, or ship, by any means whatsoever, endangered species taken in violation of 9(a)(1)(B) and 9(a)(1)(C); ESA section 9(a)(1)(E) states that it is illegal to deliver, receive, carry, transport, or ship in interstate or foreign commerce by any means whatsoever and in the course of a commercial activity, endangered species; ESA section 9(a)(1)(F) states that it is illegal to sell or offer for sale in interstate or foreign commerce, endangered species; and ESA section 9(a)(1)(G) states that it is illegal to violate any regulation pertaining to endangered species or to any threatened species of fish or wildlife listed pursuant to section 4 of the ESA and promulgated by the Secretary pursuant to authority provided by the ESA.

These prohibitions are necessary and advisable for the conservation of the Southern DPS because human “take” via activities including, but not limited to, detrimental habitat alteration, modification, and curtailment; fisheries catch and bycatch; application of pesticides, toxic chemicals, or other pollutants adjacent to or within waterways; entrainment or impingement of eggs or fish during water diversion operations, dredging, or power generation; unnecessary collection or handling; and introduction of non-native species that disrupt trophic pathways, has contributed to the decline of the Southern DPS and is likely to impede its conservation and recovery. Evaluation of activities that may occur throughout the area affected by the prohibitions for Southern DPS fish, eggs or larvae is shown in Table 1.

Exceptions, Criteria for Exceptions, and Reporting Requirements

We establish exceptions to the ESA section 9(a)(1)(B) and 9(a)(1)(C) prohibitions (the “take prohibitions”) for specific activities. These exceptions encompass specific activities that may be excluded from the take prohibitions for the Southern DPS through the relatively informal coordination process described below. In determining that it is necessary and advisable to not impose take prohibitions on certain activities, we are mindful that new information may require a reevaluation of that conclusion at any time. For any of the exceptions to the take prohibitions described below, we would evaluate on a regular basis the effectiveness of the activities in conserving and protecting the Southern DPS. If the activities are not effective in conserving and protecting the Southern DPS, we would identify ways in which the activities need to be altered or strengthened. For habitat-related exceptions to the take prohibitions, changes may be required if the activities are not achieving desired habitat functionality or the habitat is not supporting population productivity levels needed to conserve the Southern DPS. If the agency or entity carrying out the activity does not make changes to respond adequately to the new information, we would publish notification in theFederal Registerannouncing the intention to impose take prohibitions on those activities. Such an announcement would provide for a comment period of not less than 30 days, after which we would make a final determination whether to extend the ESA section 9(a)(1)(B) and (C) take prohibitions to the activities. If the activities do not meet the exception criteria any take must be covered under an ESA section 7 incidental take statement (i.e.for activities with a Federal nexus) or ESA section 10(a)(1)(B) incidental take permit. The take of the Southern DPS will not be prohibited during the course of the following activities:

(1) Federal, state, or private-sponsored research or monitoring activities if they adhere to all of the following: (a) The activity must comply with required state reviews or permits; (b) the research or monitoring activity must be directed at the Southern DPS and not be incidental to research or monitoring of another species; (c) take of live mature adults in the lower Feather River from the confluence with the Sacramento River to the Oroville Dam (rkm 116), the lower Yuba River from the confluence with the Feather River to the Daguerre Dam (rkm 19), or Suisun, San Pablo, and San Francisco Bays or the Sacramento-San Joaquin Delta from the Golden Gate Bridge up into the Sacramento River to Keswick Dam (rkm 483) may only occur from July 1 through March 1 so as to substantially increase the likelihood that uninterrupted upstream spawning migrations of adults will occur; (d) take must be non-lethal; (e) take involving the removal of any life stage of the Southern DPS from the wild must not exceed 60 minutes; (f) take must not involve artificial spawning or enhancement activities; (g) a description of the study objectives and justification, a summary of the study design and methodology, estimates of the total non-lethal take of Southern DPS fish anticipated, estimates of incidental take of other ESA listed species anticipated and proof that those takes have been authorized by NMFS or the USFWS, identification of funding sources, and a point of contact must be reported to the NMFS Southwest Regional Office (seeADDRESSES:above) at least 60 days prior to the start of the study, or, for ongoing studies, by August 31, 2010; (h) reports that include the total number of Southern DPS and any other ESA listed species taken, information that supports that take was non-lethal, and a summary of the project results must be submitted to NMFS on a schedule to be determined by NMFS staff; (i) research or monitoring that involves action, permitting, or funding by a Federal agency must still comply with the requirements of ESA section 7(a)(2) in order to ensure that the action will not jeopardize the continued existence of the threatened Southern DPS. NMFS will respond in a letter either confirming the activities meet the exception criteria or stating that the activities do not meet the exception criteria and are subject to the take prohibitions. The letter would acknowledge receipt of the project information and provide the schedule for submission of research/progress reports and technical assistance to clarify when the ESA section 9 prohibitions apply.

(2) Emergency fish rescue and salvage activities that include aiding sick, injured, or stranded fish, disposing of dead fish, or salvaging dead fish for use in scientific studies, if they adhere to all of the following: (a) The activity must comply with required state or other Federal reviews or permits; (b) activities may only be conducted by an employee or designee of NMFS or the U.S. Fish and Wildlife Service (USFWS), any Federal land management agency, or California Department of Fish and Game (CDFG), Oregon Department of Fish and Wildlife (ODFW), Washington Department of Fish and Wildlife (WDFW), or Alaska Department of Fish and Game (ADFG); (c) the emergency rescue must benefit the Southern DPS; (d) a report must be submitted to the NMFS Southwest Regional Office (see ADDRESSES:above) that includes, at a minimum, the number and status of fish handled, the location of rescue and/or salvage operations and the potential cause(s) of the emergency situation within 10 business days after carrying out the rescue.

(3) Habitat restoration activities, including barrier removal ormodification to restore water flows, riverine or estuarine bed restoration, natural bank stabilization, restoration of native vegetation, removal of non-native species, or removal of contaminated sediments, that reestablish self-sustaining habitats for the Southern DPS, if they adhere to all of the following: (a) Compliance with required state and Federal reviews and permits; (b) a detailed description of the restoration activity sent to the NMFS Southwest Regional Office (see ADDRESSES:above) at least 60 days prior to the start of the restoration project, or, for ongoing studies, by August 31, 2010, which includes: the geographic area affected; when activities will occur; how they will be conducted; and the severity of direct, indirect, and cumulative impacts of activities on the Southern DPS; identification of funding sources; demonstration that all state and Federal regulatory requirements have been met; a description of methods used to ensure that the likelihood of survival or recovery of the listed species i