Least Bell's Vireo Breeds in Restored Riparian at San Joaquin River

Least Bell’s Vireo Breeds in Restored Riparian at San Joaquin River National Wildlife Refuge

2005 Final Report

Submitted to: U.S. Fish and Wildlife Service San Luis National Wildlife Refuge Complex June 2006

Submitted by: Julian K. Wood, Christine A. Howell, Geoffrey R. Geupel [email protected], [email protected], [email protected]

PRBO Conservation Science 3820 Cypress Dr. Petaluma, CA 94954 (707) 781-2555 www.prbo.org

PRBO Contribution # 1511

Introduction

The historic nesting of Least Bell’s Vireos (Vireo bellii pusillus) on a restoration plot on the San Joaquin River National Wildlife Refuge (Refuge) represents a monumental success for CalFed, U.S. Fish and Wildlife Service (USFWS) and its partners in their efforts to restore riparian habitat to benefit wildlife. The Least Bell’s Vireo has not bred in the Central Valley for over 50 years and is rarely detected during the breeding season. The distance to the nearest known source population, along the Santa Clara River, is over 400 km. In order to establish a breeding population in the Valley, Franzreb (1990) proposed various reintroduction methods and considered natural dispersion highly unlikely. A single detection of a Least Bell’s Vireo anywhere in the Valley during the breeding season is a significant sighting but a nesting pair is unprecedented and was wholly unexpected.

On 10 June a male Least Bell’s Vireo was detected singing during a point count survey of the H8-9 restoration site. Soon after, a pair was found feeding two dependent young (Table 1.) indicating they nested in the immediate vicinity. On 28 June, the pair’s presumed second nest attempt was located in the same area in a three-year old arroyo willow (Salix lasiolepsis) cultivated by River Partners as part of the restoration of Hagemann’s Field (Figure 1). The nest was concealed by a dense stand of mugwort (Artemisia douglasiana) also cultivated by River Partners. The second nesting attempt was successful and produced four young bringing the total number of young fledged from the Refuge pair to at least six.

Background

The Least Bell's Vireo is one of four subspecies of Bell's Vireo recognized by the American Ornithologist's Union (AOU 1957). It is the western-most subspecies, breeding entirely within California and northern Baja California. Historically, the Least Bell's Vireo was a common to locally abundant species in lowland riparian habitat, ranging from coastal southern California through the Sacramento and San Joaquin valleys as far north as Red Bluff, Tehama County (Goldman 1908, Linton 1908, Grinnell and Miller 1944).

A decline in Least Bell’s Vireos was noticed by the early 1930’s (Grinnell and Miller 1944). The last confirmed breeding records for the Valley are from 1919 from Merced and Stanislaus Counties, (MVZ 1919 and WFVZ 1919). Although nesting likely continued after this date, records of Least Bell’s Vireo were uncommon by the 1960s. State sponsored surveys in the 1970s failed to detect a single Least Bell’s Vireo in northern California, leading to the conclusion that “no other California passerine has declined so dramatically in historic times” (Goldwasser et al. 1980). The loss of approximately 90% of riparian habitat and increased parasitism by Brown-headed Cowbird (Molothrus ater) resulted in its extirpation from the Valley and dramatic declines elsewhere in the state. By 1986, the population had declined to an estimated 300 pairs, with the majority occurring in San Diego County (Kus 2002). The Least Bell's Vireo was listed as a state endangered species in 1980 and as a federally endangered species in 1986. PRBO surveys throughout the Valley in the 1990s and 2000s failed to detect Bell’s Vireo during the breeding season.

Figure 1. Map of planting schematic used by River Partners with PRBO point count locations and Least Bell’s Vireo nest. Map by River Partners.

PRBO Point count location

LBVI nest

Riparian Restoration

The two successful broods of the Central Valley pair may be attributed to the quality of the riparian restoration at the Refuge. Three years ago, as part of a CalFed-funded restoration project initiated by USFWS, River Partners developed the San Joaquin River National Wildlife Refuge restoration design, the largest riparian restoration effort ever undertaken in California. Using recommendations from the California Partners in Flight Riparian Bird Conservation Plan (RHJV 2004) which included recommendations from PRBO, the planting design included native riparian vegetation such as mugwort, California wild rose (Rosa californica), arroyo willow, and Valley oak (Quercus lobata); plant species known to benefit riparian-associated birds. The restoration design also integrated the Riparian Plan recommendation to promote a dense, shrubby understory, an important component in the breeding habitat of Least Bell’s Vireo. Moreover, River Partners planted vegetation in a mosaic-design with shrub patches interspersed with trees under the assumption that plantings that are concentrated into clumps will more quickly create productive patches of habitat for nesting birds than plantings uniformly spaced over a large area (RHJV 2004).

Table 1. Timeline of significant events for Least Bell’s Vireo in 2005.

10 June Male and female discovered feeding 2 dependent young by Linette Lina and Julian Wood, PRBO biologists

11 June Eric Hopsen, Refuge Manager, visits Vireo site with Linette Lina

14 June Kenneth Griggs, Refuge Biologist, Julian Wood, Linette Lina, confirm sighting, John Trochet, Ornithologist, takes acoustic recording

15 June Special Use permit issued to PRBO to take photographs of pair and juveniles. Two rolls slide film taken by Po-Hon Liu, PRBO intern and delivered to USFWS.

25 June Federal permit obtained by PRBO to monitor Vireos

28 June Nest found on hatch day in arroyo willow with 2 eggs and 2 young

1 July Nest checked. 4 young observed (nestling age=4 days)

5 July Nest checked. 4 young observed (nestling age=7 days)

9 July Nest empty. 2 young fed by male. Female and other 2 young not seen but presumed fledged

13 July Male Vireo captured using playbacks and mist net and banded with USFWS band by Barbara Kus, USGS with assistance from Linette Lina, and Julian Wood

Presumably absent in the Central Valley for the past 50 years, Least Bell’s Vireo numbers have increased tenfold in southern California due to the tremendous efforts of a broad partnership of local, state and federal agencies involving habitat protection and restoration, and Brown-headed Cowbird control. In 1998, the population size was estimated at 2,000 pairs (L. Hays, USFWS, pers. comm.). Nesting Least Bell’s Vireos have re-colonized the Santa Clara River (Ventura County) to the north, where 67 pairs nested in 1998 (J. Greaves, pers. comm.), and the Mojave River (San Bernardino County) to the northeast (Kus and Beck 1998). Prior to 2005, the northernmost reported sighting of a mated pair was near Gilroy, Santa Clara County in 1997 although no nest was confirmed (M. Rogers, pers. comm.).

4 Site Fidelity

Data collected for color-banded birds indicate that site fidelity is high among adults, with many birds not only returning to the same territory, but placing nests in the same shrub used the previous year (Salata 1983, Kus unpubl. data). This high site fidelity, in concert with the recent population increases and large scale restoration efforts, provides hope for Least Bell’s Vireo re-colonization of the Refuge and in time perhaps its historic breeding range throughout the Central Valley. Re-establishment of San Joaquin and Sacramento Valley populations is part of the draft recovery plan to de-list the Least Bell’s Vireo (USFWS 1998). The recent documentation of Least Bell’s Vireos breeding at the Refuge underscores the role that habitat restoration can play in conserving biodiversity. Even highly disturbed ecosystems hold the potential for healthy habitat to recover and for many dependent species to return.

Habitat requirements

The Least Bell’s Vireo is a riparian obligate during the breeding season and is often associated with early successional riparian habitat that is structurally diverse (Kus 1998). The Least Bell’s Vireo will inhabit different riparian vegetation types (e.g., cottonwood- willow and oak woodland) and different vegetation age classes but are most often associated with a dense understory layer (0.6-3.0 m) (Goldwasser et al. 1980, Franzreb 1989). Least Bell’s Vireos respond favorably to restoration efforts, particularly when restoration sites are located adjacent to established riparian habitat. Restored riparian in the coastal lowlands of southern California has the habitat structure to support breeding Least Bell’s Vireos within 3-5 years following restoration (Kus 1998; Kus and Beck 1998). Least Bell’s Vireo habitat requirements are compatible with habitat at restored Refuge sites with its cottonwood-willow dominated riparian vegetation and densely planted shrub and understory layer (Table 2). This densely planted vegetation provides cover for nesting (Table 3 and Figure 4).

Table 2. Lest Bell’s Vireo nest and nest substrate description. Concealment recorded as % of nest concealed by vegetation at one meter distance from nest

Substrate Substrate Nest height Substrate Primary concealment Secondary concealment dbh (cm) height (cm) (cm) Salix lasiolepsis Artemisia douglasiana Salix lasiolepsis 4 450 84

Table 3. Least Bell’s Vireo nest concealment recorded as % of nest concealed by vegetation at one meter distance from nest (from above, below and from each cardinal direction)

% of nest concealed Above Below North South East West 40 0 0 30 0 90

5 Figure 2. Least Bell’s Vireo nest in Arroyo Willow (Salix lasiolepsis) with four 7-day old nestlings.

Photo by Linette Lina/PRBO

Identification

The Least Bell’s Vireo is one of four subspecies of Bell’s Vireo and is characterized by dull grayish plumage. Sub-specific differences in plumage are most evident in fresh plumage when other races show yellow and olive-gray wash (Pyle 1997). In worn plumage these individuals of other races may resemble the grayer pusillus (P. Unitt pers. comm.). The individuals at the Refuge were in worn plumage consistent with pusillus. However, sub specific identification of these birds cannot be confirmed based on plumage alone. The most convincing argument is the pair’s location within the former breeding range of pusillus. The distance from the nearest arizonae source population and the physical barriers between makes the possibility of arizonae extremely remote. The nearest known source population of pusillus, although still far, is much closer (Ventura County). There is also the possibility that these birds came from an undocumented location closer to the San Joaquin Valley such as the Coast Range, especially as there are several confirmed sightings from the south bay area (M. Rogers pers. Comm.). Interestingly, one of the last probable occurrences of breeding Bell’s Vireos in the San Joaquin Valley is from Corral Hollow, Stanislaus County, (only 26 km northwest of the Refuge) where a dependent juvenile was collected in 1932 (MVZ 1932). The likelihood of the Refuge Bell’s Vireos being of the pusillus race is very high considering the combination of light gray plumage, nest location within former pusillus breeding range and the extreme distance and physical barriers between source populations of other subspecies (P. Unitt and B. Kus pers. comm.).

Acoustic documentation

On 14 June 2005, a recording of the Least Bell’s Vireo was made by ornithologist John Trochet. Due to wind, other birdsongs in the area, and the quality of the recording equipment used the sound quality was relatively low. A copy of the original tape was made and delivered to USFWS (Jim Nickles, public affairs/media relations) by PRBO biologist Andrea Pfeffer in July 2005.

6 Photographic documentation

Photographs of the Least Bell’s Vireo were taken in order to document its presence at the Refuge and to provide material to educate the public (Figure 3). USFWS requested PRBO intern and former professional wildlife photographer for Nikon, Po-Hon Liu, to photograph the vireos. On June 15, Po-Hon Liu and PRBO biologist Julian Wood visited the Least Bell’s Vireo site and shot two rolls of slide film using a 600 mm lens. The slide film was delivered to USFWS for printing. Figure 3 shows the male Least Bell’s Vireo in a cultivated arroyo willow (Salix lasiolepsis) at Hagemman’s Field 8.

Figure 3. Least Bell’s Vireo foraging in cultivated arroyo willow (Salix lasiolepsis).

Photo by Po-Hon Liu/PRBO

On 1 July and 5 July, additional photos of the nest were taken in digital format by Linette Lina (Figure 2). All photos taken will be given to USFWS on CD.

Target mist netting

On 13 July 2005, the male Least Bell’s Vireo was captured and banded with a blue anodized USFWS band by Barbara Kus, Research Ecologist with USGS, who possesses a permit for banding Least Bell’s Vireo (Figure 4). Dr. Kus is an expert on Least Bell’s Vireo having worked with them for over 19 years and published numerous peer-reviewed articles on the species. PRBO did not have the permit necessary to capture and band Least Bell’s Vireo. We used two standard 12 m long soft polyester mesh nets one stacked on top of the other. We used song and call playback to lure the male into the net. During banding two body feathers fell from the bird and were saved by Dr. Kus for potential future genetic analysis. Dr. Kus anticipates that genetic analysis will be conducted in fall 2006 as she is still setting up her genetics lab.

7 Figure 4. Photo of PRBO and USGS biologists banding Least Bell’s Vireo male on 13 July 2005. Left to right: Linette Lina- PRBO, Barbara Kus- USGS, Julian Wood- PRBO.

Photo by Po-Hon Liu/PRBO

Nest monitoring precautions

PRBO biologists took precautions in monitoring the activities of the Least Bell’s Vireo by following the guidelines outlined in Martin and Geupel (1993) to minimize potential human impacts on nest success. Examples include:

1) Only one PRBO biologist to visit active nest during a nest check. Visitors or photographers not permitted to approach active nest.

2) In general, use a nest stick to check nests. This prevents human scent from being left on or near a nest.

3) Never use flagging or other visible markers less than 10 m from a nest.

4) Check nests with nestlings near fledging date done at a distance using binoculars to avoid force fledging.

5) Never make a dead-end path to the nest which could draw predators to the nest.

4) Wait 10-15 minutes before approaching a nest after a cowbird or nest predator has been sighted in the area.

5) Use long extendable mirrors to check contents without approaching nest.

6) Take all possible care in minimizing disturbance to vegetation concealing the nest.

8 Brown-headed Cowbird Impacts

Brown-headed Cowbirds are a major threat to Least Bell’s Vireos throughout their range (Kus 1999), as well as to other vireo species and subspecies. Brown-headed Cowbirds are obligate brood parasites that rely on unsuspecting host species to raise the Cowbird young. Unsuspecting host parents will abandon parasitized nests or raise them at the expense of the host young (host young may be ejected or die from lack of food). Least Bell’s Vireos are frequent Cowbird hosts in Southern California and they experience high reproductive failure of their own offspring in the presence of Cowbird young (Kus 1999).

Brown-headed Cowbirds are common at the Refuge and parasitize host species’ nests, especially those with open-cup nests located in the understory. Through our nest- monitoring efforts, we have detected eight open-cup nesting species that have been parasitized by Brown-headed Cowbirds at the Refuge (Lazuli Bunting (Passerina amoena), California Towhee (Pipilo crissalis), Common Yellowthroat (Geothlypis trichas), Blue Grosbeak (Passerina caerulea), Spotted Towhee (Pipilo maculatus), Song Sparrow (Melospiza melodia), American Goldfinch (Carduelis tristis), and Black-headed Grosbeak (Pheucticus melanocephalus). Of the over 600 nests found on the Refuge from 2000 to 2005, a total of 542 were open cup nests susceptible to Brown-headed Cowbird parasitism. Of these nests, 118 (22%) were parasitized. Of the parasitized nests only 20 (17%) successfully fledged one or more host young and 33 nests (28%) successfully fledged Brown-headed Cowbird young.

Any future monitoring of Least Bell’s Vireo on the Refuge should include an assessment of the potential threat to nest success by Brown-headed Cowbirds especially in restored riparian habitat.

Recommendations for Least Bell’s Vireo monitoring

We recommend gathering data and information necessary to manage for the recovery of the federally Endangered Least Bell’s Vireo in the vicinity of the Refuge. We outline the following actions to properly monitor and manage for a successful Least Bell’s Vireo population at the Refuge.

• Develop a map of potentially suitable Least Bell’s Vireo Habitat.

Identify areas within the Refuge and vicinity that currently provide potential suitable habitat for the Least Bell’s Vireo. Review existing aerial photography and conduct on- the-ground surveys to identify areas that have the proper floristic and structural components noted in this report or in published research on the species (e.g. Kus 1999, USFWS 1998). Produce a map (GIS layer) indicating areas that provide potentially suitable Least Bell’s Vireo habitat within the region and concentrate monitoring efforts in those areas.

• Monitor for the presence and abundance of Least Bell’s Vireos

Conduct point count surveys to detect the presence and measure abundance of Least Bell’s Vireos in areas identified in the habitat suitability map as well as historic PRBO

9 point count locations throughout the Refuge. In addition, the area search method, a nationally standardized time-constrained survey method, should be used to locate Least Bell’s Vireos. This method allows the researcher to survey an area more thoroughly than other methods there and is ideal for smaller habitat fragments. The area search and point count methods are repeatable and can be used to collect information on other species such as Brown-headed Cowbirds without compromising the search for Least Bell’s Vireos.

• Monitor the reproductive success of breeding Least Bell’s Vireo.

Search for the nests of all Least Bell’s Vireos detected at any of the survey locations. Once found, nests should be carefully monitored to determine nest outcome (successful or unsuccessful, number of young fledged, Brown-headed Cowbird status, etc.). Nest monitoring should follow behavioral approaches described in Martin and Geupel (1993) that minimize disturbance to adults and nests.

• Monitor potential Brown-headed Cowbird impacts on the Least Bell’s Vireo and other riparian bird species.

Brown-headed Cowbirds can cause high reproductive failure in Least Bell’s Vireo populations (Kus 1999). Therefore it is extremely important to determine the magnitude and extent of potential Cowbird impacts on Least Bell’s Vireo in the vicinity of the Refuge. Because of the limited number of potential Least Bell’s Vireo nests we recommend using songbirds with similar nesting characteristics as a proxy for vireo nests (e.g., similar nest configuration, construction, and placement relative). Likely candidates for proxy species include Song Sparrow (Melospiza melodia), Spotted Towhee (Pipilo maculatus) and American Goldfinch (Carduelis tristis) and other low open cup-nesting species. The parasitism rates of proxy species can be used to infer the potential parasitism rates of the Least Bell’s Vireo population. With this knowledge, different Brown-headed Cowbird management scenarios can be assessed including removing Cowbird eggs from Least Bell’s Vireo nests, implementing a Cowbird removal program, or managing livestock feedlot placement in the landscape.

• Conduct public outreach activities related to the Least Bell’s Vireo and the importance of riparian habitats for wildlife.

Education and community outreach are critical components of riparian restoration efforts. We recommend outreach efforts at 1) the community, 2) private landowners, 3) agencies and stakeholders with riparian conservation interests and 4) local and national media.

In addition, we recommend planning a “State of the San Joaquin River” conference to share information and communicate research findings among groups working on the San Joaquin River with interests relating to riparian habitats, riparian restoration, and endangered species recovery.

10 Literature Cited

American Ornithologists' Union. 1957. Check-list of North American birds. 5th edition. Port City Press, Inc. Baltimore, Md.

Franzreb, K. 1989. Ecology and conservation of the endangered Least Bell's Vireo. U.S. Fish and Wildlife Service, Biological Report 89(1). 17 pp.

Franzreb, K. 1990. An analysis of options for reintroducing a migratory, native passerine, the endangered Least Bell’s Vireo Vireo bellii pusillus in the Central Valley, California. Biological Conservation 53:105-123.

Goldman, E.A. 1908. Summer Birds of the Tulare Lake Region. Condor 10:200-204.

Goldwasser, S., D. Gaines, and S.R. Wilbur. 1980. The Least Bell’s Vireo in California: a de facto endangered race. American Birds 34:742-745.

Grinnell, J., and A. Miller. 1944. The distribution of the birds of California. Pacific Coast Avifauna No. 26.

MVZ (Museum of Vertebrate Zoology). 1919. Bell’s Vireo (Vireo bellii) nest and eggs collected by Joseph Grinnell 2 miles southwest of Lagrange, Stanislaus County. Catalogue #1786.

MVZ (Museum of Vertebrate Zoology). 1932. Bell’s Vireo (Vireo bellii) dependent juvenile collected near head of Corral Hollow, San Joaquin County by Gordon L. Bolander. Catalogue #60897.

Martin, T. E. & G. R. Geupel. 1993. Nest monitoring plots: Methods for locating nests and monitoring success. J. Field. Ornith. 64: 507-519.

RHJV (Riparian Habitat Joint Venture). 2004. Version 2.0. The Riparian Bird Conservation Plan: a strategy for reversing the decline of riparian associated birds in California. California Partners in Flight. http://www.prbo.org/calpif/pdfs/riparian.v-2.pdf

Kus, B. E. 1998. Use of restored riparian habitat by the endangered Least Bell’s Vireo. Restoration Ecology 6:75-82.

Kus, B. E. 1999. Impacts of brown-headed cowbird parasitism on productivity of the endangered Least Bell's Vireo. Studies in Avian biology 18:160-166.

Kus, B. E. 2002. Least Bell's Vireo (Vireo bellii pusillus). In The Riparian Bird Conservation Plan: a strategy for reversing the decline of riparian-associated birds in California. California Partners in Flight. http://www.prbo.org/calpif/htmldocs/riparian_v-2.html.

Kus, B. E. and P. Beck. 1998. Distribution and abundance of the Least Bell's Vireo (Vireo bellii pusillus) and the southwestern willow flycatcher (Empidonax traillii extimus) at selected southern California sites in 1997. Prepared for California Department of Fish and Game, Wildlife Management Division, Sacramento, CA.

Linton, C. B. 1908. Notes from Buena Vista Lake, May 20 to June 16, 1907. Condor 10:196-198.

PRBO. 2002. Songbird Monitoring on the San Joaquin River National Wildlife Refuge: Progress Report for the 2001 field Season. Unpubl. Rept., U. S. Fish and Wildlife Service, Los Banos, CA.

Salata, L. 1983. Status of the Least Bell's Vireo on Camp Pendleton, California: report on research done in 1983. Unpubl. Rept., U. S. Fish and Wildlife Service, Laguna Niguel, CA.

USFWS (U.S. Fish and Wildlife Service). 1998. Draft Recovery Plan for the Least Bell’s Vireo. Fish and Wildlife Service, Portland, OR. 139 pp.

WFVZ (Western Foundation of Vertebrate Zoology). 1919. 4 eggs collected by John G. Tyler near Delhi, Merced County. Catalogue #33085.