(DRAFT) - Taxonomy
                         Species BIRDS-BEAK, PALMATE-BRACTED
                                Species Id ESIS701041
                                   Date 13 MAR 96



TAXONOMY

NAME - BIRDS-BEAK, PALMATE-BRACTED OTHER COMMON NAMES - BIRDS-BEAK, PALMATE-BRACTED;BIRD'S-BEAK, PALMATE-BRACTED; BIRD'S-BEAK, FERRIS'; BIRD'S-BEAK and FLESHY ELEMENT CODE - CATEGORY - Angiosperm PHYLUM AND SUBPHYLUM - MAGNOLIOPHYTA, CLASS AND SUBCLASS - MAGNOLIOPSIDA, ORDER AND SUBORDER - SCROPHULARIALES, FAMILY AND SUBFAMILY - SCROPHULARIACEAE, GENUS AND SUBGENUS - CORDYLANTHUS, SPECIES AND SSP - PALMATUS, SCIENTIFIC NAME - CORDYLANTHUS PALMATUS AUTHORITY - TAXONOMY REFERENCES - COMMENTS ON TAXONOMY - Palmate-bracted birds-beak Cordylanthus palmatus (Ferris) Machr. KINGDOM: Plant GROUP: Angiosperm DIVISION: Magnoliophyta CLASS: Magnoliopsida ORDER: Scrophulariales FAMILY: Scrophulariaceae Cordylanthus palmatus is a low, much branched annual, 1 to 3 dm high, with yellow roots. The herbage is pale or grayish green, pilose or pubescent, with some of the hairs gland-tipped, the longest hairs less than 1 mm long. Salt crystals may be evident over much of the plant's surface. The leaves are 1-2 cm long, oblong-oblanceolate, mostly incised, the lower sometimes entire. The inflorescence consists of dense spikes 5 to 15 cm long. The bracts are ovate, with 2 to 3 pairs of ascending lobes radiating from the basal portion; the calyx is 12-15 mm long, oblong-lanceolate, entire or bidentate with teeth about 1 mm long. The purplish (or creamy with purplish veins) corolla is 12-16 mm long (01) (1.5-2 cm long in (02)), bilabiate, with a basal tube and an inflated pouch, its lower lip finely pubescent, the finely reflexed-pubescent galea with a wide glabrous thin margin. Two functional stamens, an upper pair lacking or reduced to rudimentary filaments; the capsule 6-7 mm long, with 14-18 brownish Taxonomy - 1 (DRAFT) - Taxonomy Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 seeds with conspicuously and deeply reticulate seed coat and prominently undulating crest. (01 and 02; some difference exists between descriptions by these two sources, although Dr. Larry Heckard, an authority on the genus, states these differences are not significant (03)). C. palmatus can be confused with Cordylanthus maritimus ssp. mollis, and these two sometimes grow together (03). The length of the pubescence is an important characteristic, as well as the palmate character of the floral bracts (01,02,03). The Scaramento Valley form of this taxon was originally named Adenostegia palmata by Ferris in 1918 (04), but the contents of this genus were soon placed in the conserved generic name Cordylanthus by Macbride in 1919 (05). The San Joaquin Valley form was described as C. carnulosus by Pennell in 1947 (06); this taxon was treated as a variety under C. palmatus by Munz in 1958 (07). Mason in his 1957 treatment of marsh plants (08) treated C. palmatus as an indistinguishable part of C. mollis. In a 1973 paper, Chuang and Heckard demonstrated that the chromosome number (n=21) was distinctive for C. palmatus within the genus, and that the differences between the two forms, C. palmatus and C. carnulosus were not sufficiently important to warrant intraspecific separation of the two forms (09,10). Other vernacular synonyms include: Ferris' birds-beak (11), and, for the San Joaquin Valley form, fleshy bird's-beak (09). The type specimen for C. palmatus was collected by R. Stinchfield (later R. S. Ferris) near College City and was reposited in the Dudley Herbarium, now maintained at the California Academy of Sciences, San Francisco. Isotypes are reposited at Philadelphia Herbarium, the Univeristy of California, and the US Herbarium (02). Type specimens of C. carnulosus are reposited at the California Academy of Sciences, the Jepson Herbarium, the University of California Herbarium, and Philadelphia Herbarium (02). Other specimens are kept at the Fresno State Herbarium (01). Drawings of the plant may be found in Abrams (09), and Chuang and Heckard (10). Color slides are available through the California Native Plant Society, Sacramento, CA. Taxonomy - 2
                                  (DRAFT) - Status
                         Species BIRDS-BEAK, PALMATE-BRACTED
                                Species Id ESIS701041
                                   Date 13 MAR 96



STATUS

Coded Status E: Federal Endangered COMMENTS ON STATUS - U.S. STATUSES AND LAWS: The Palmate-bracted birds-beak (Cordylanthus palmatus) has been designated an Endangered species pursuant to the Endangered Species Act of 1973 (50 CFR 17.12; P.L. 93-205, 87 Stat. 884; 16 U.S.C. 1531-1540), as amended. The species has this status wherever found including the State of California. Removal and reduction to possession of any Federally listed plant from an area under Federal jurisdiction is unlawful (50 CFR 17.61 and 17.71). This species is protected by the Lacey Act (P.L. 97-79, as amended; 16 U.S.C. 3371 et seq.) which makes it unlawful to possess any wild plant (including roots, seeds, and other parts) within U.S. territorial or special maritime jurisdiction (as defined in 18 U.S.C. 7); or to import, export, transport, sell, receive, acquire, or purchase in interstate or foreign commerce any wild plant (including roots, seeds, and other parts) taken, possessed, transported, or sold in violation of any State law or regulation. It is also unlawful to import, export, transport, sell, receive, acquire, or purchase any wild plant (including roots, seeds, and other parts) taken or possessed in violation of any U.S. law, treaty, or regulation or in violation of Indian tribal law. RESPONSIBLE FEDERAL AGENCIES: USFWS -Responsible for the management/recovery, listing, and law enforcement/protection of this species. All Federal agencies have responsibility to ensure that any action authorized, funded, or carried out by that agency is not likely to jeopardize the continued existence of the species or result in the destruction or adverse modification of Critical Habitat (50 CFR 402), and to utilize their authorities to carry out programs for the conservation of the species. STATE STATUSES AND LAWS: STATE: California DESIGNATED STATUS: Endangered ADMINISTRATIVE AGENCY: Calif. Department of Fish and Game STATE STATUTE: Calif. Endangered Species Act; Fish and Game Code Chapter 1.5, Article 1, Sect. 2050 INTERNATIONAL STATUSES, TREATIES, AND AGREEMENTS: Status - 1 (DRAFT) - Status Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 None. ECONOMIC STATUSES: None. 85/07/15:50 FR 28870/ - Proposed rule, List as Endangered 85/10/24:50 FR 43260/ - Notice of public hearing/comment period 86/07/01:51 FR 23765/23769 - Final rule, Listed as Endangered Status - 2
     

HABITAT ASSOCIATIONS

HABITAT - TERRESTRIAL TERRESTRIAL INLAND AQUATIC LAND USE - Transportation, communications, and Util Herbaceous Rangeland Shrub and Brush Rangeland Nonforested Wetland Dry Salt Flats NATIONAL WETLAND INVENTORY CODES NWI NWICLS NWIMOD NWISPEC Palustrine FL6 Palustrine FL5 Palustrine FL COMMENTS ON HABITAT ASSOCIATIONS - Cordylanthus palmatus grows in saline-alkaline soils of lowland flats and plains (03), often in overflow lands which flood intermittently during the winter rainy season (01). The plant community where C. palmatus grows is alkaline scrub, allenrolfea scrub, and vally bottmland scrub. The characteristic aspect of vegetation is very sparse in this uninviting habitat. Soil series, appearance and texture. The soils at two sites have been reported as Pescadero clays and Solano fine sandy loams (19,20). In some reports, a white, powdery residue has been observed on the soil surface during the dry period (15); this is reported as being sodium bicarbonate (03). Although Solano fine sandy loams appear considerably less fine-textured than Pescadero clays, both have a dense clay subsoil which retard both infiltration, percolation, and groundwater movement (14). Both soil types are characterized as saline or saline-alkaline (20); however, since C. palmatus appears to occupy only the most extreme sites, this characterization is consistent with Heckard's description of habitat (10). Soil chemistry: The soil series at one Mendota site was reported by Heckard as being black-alkali, meaning they are saline-alkaline; they had a pH of 8-9 (10). In this same report (10), Heckard suggests that C. palmatus may grow on saline-alkaline soils rather than on strictly saline soils. Nonsaline alkali soils also occur in general areas where C. palmatus has been collected; these areas may also contain saline-alkali soils. Dr. Heckard believes that this species, while occurring in soils with high levels of dissolved salts, may require the inundation and flushing associated with periodic stream overflow during the winter months to reduce salinity and thereby stimulate germination (Heckard pers comm). The plant apparently can tolerate higher concentrations of dissolved solids at later periods in its life cycle. Microhabitat: Various microhabitats have been reported for C. palmatus; however, an understanding of the hydrology of the various sites may help to create a more unified picture of its requirements (see hydrology section). Heckard (03) has observed the plant growing in the lowest part of roadsides; Taylor (16) reported it growing on the dirt thrown up on a roadside as result of grading operations. Habitat Associations - 1 The plant may be seen at the edges of shallow drainages at the Livermore site, as well as at the edges of scalds on higher ground (23). In all cases, the plant grows in largely barren areas, with few plant associates, and in areas of the most extreme salinity and alkalinity. As will be discussed in the life history section, the areas where C. palmatus occurs are probably saturated for periods of time during the winter season; this may be a requirement for germination (03). Hydrology: The hydrologic requirements of C. palmatus are imperfectly known, at least to the extent required to alter land use nearby with some assurance that habitat for this species could be preserved (21). However, the following may be speculated about the requirements of this species, with respect to water and dissolved solids: Both surface and subsurface movement are important to the habitat characteristics. As ponded water evaporates dissolved solids are collected, contributing to the salinity and alkalinity of the soils. If infiltration exceeds evaporation, dissolved solids may collect in basins (such as low points along roadsides). Where infiltration is very slow and water is ponded, evaporation may take place directly from ponded areas, and water may move up into hummocks through capillary action, allowing saline or alkaline deposits to collect in higher zones. The more clayey soils may experience a greater effect due to capillary action than the sandy soils, thus forming the very clayey, alkaline "scalds" seen so often in the San Joaquin Valley (14,23). The interaction between available water, soil texture, and microtopography may therefore determine the microhabitat occupied by C. palmatus--high ground or low ground--at a given site. Because of the extreme environment occupied by this species, soil saturation may play a critical part in the life cycle of C. palmatus. Germination is the most vulnerable stage in the life cycle of a plant, and the bird's-beak may rely on the flooded winter period as a time when the dissolved solids present in the soil solution are most dilute, enabling germination and survival (03). Although speculative at this time, it suggests that a natural regime of flooding or at least saturation during winter is essential for this plant. Natural community: C. palmatus grows in alkali sink scrub (01). Competition: That C. palmatus is found at the outermost border of vegetation in soils so alkaline or saline suggests that this species is unusually tolerant of extreme soil conditions (pers obs). It may, however, be a poor competitor under more favorable conditions for growth. In the greenhouse, the species grows under non-saline conditions without competition quite well, but it may not be competitive in the field under non-saline conditions (03). Tolerance of disturbance: Since one recently-mapped locality was noted as occurring on disturbed soil at the shoulder of a dirt road (16), lack of soil disturbance appears less important than other factors. Habitat Associations - 2
                                (DRAFT) - Food Habits
                         Species BIRDS-BEAK, PALMATE-BRACTED
                                Species Id ESIS701041
                                   Date 13 MAR 96



FOOD HABITS

TROPHIC LEVEL - AUTOTROPH Food Habits - 1
                         (DRAFT) - Environment Associations
                         Species BIRDS-BEAK, PALMATE-BRACTED
                                Species Id ESIS701041
                                   Date 13 MAR 96



ENVIRONMENTAL ASSOCIATIONS

G = General A = Adult LIM = Limiting RA = Resting Adult J = Juvenile FA = Feeding Adult RJ = Resting Juvenile BA = Breeding Adult FJ = Feeding Juvenile P = Pupae L = Larvae E = Egg RL = Resting Larvae FL = Feeding Larvae
LIFESTAGE ENVIRONMENTAL ASSOCIATIONS G G Terrestrial Features: Depressions G G G G G G G G G G Environment Associations - 1
                               (DRAFT) - Life History
                         Species BIRDS-BEAK, PALMATE-BRACTED
                                Species Id ESIS701041
                                   Date 13 MAR 96



LIFE HISTORY

HABIT: The palmate-bracted birds-beak (Cordylanthus palmatus) is an herb (01,02,03). LIFE CYCLE: Cordylanthus palmatus is unusual among annual plants of the Central Valley in growing, reproducing and setting seed so late in the summer. This is made possible, it is theorized, because it is a hemiparasite on perennial plants, whose moisture and nutrient reserves can be drawn upon late in the summer (10,22). TYPE OF REPRODUCTION: The palmate-bracted birds-beak reproduces sexually (03). Chromosomes are 21 while other members of the genus contain 12, 13, 14, 15 and 16 chromosomes (Heckard 1985). REPRODUCTIVE PHENOLOGY: Germination dates are uncertain, but is estimated to occur after the rains begin. Leafing dates are unknown, budding occurs most likely in May to June, anthesis in May/June to September/October, and fruiting occurs in August to October. Seed/fruit dispersal dates are unknown (03,19). Heckard (03) reports that little is known of the winter habitat for C. palmatus; it is difficult to find in its early stages, and on those occasions when it has been searched for in winter, the ground it occupies is sticky, wet, and difficult to traverse. SEX OR SPORE STATUS: The palmate-bracted birds-beak is monoecious (02,03). POLLINATION, SPORE AND SEED DISSEMINATION: Heckard (03) suspects this species is bee pollinated, as the insect must be able to pry the lips of the flower open. Other members of the genus are bee-pollinated. This species will not self-pollinate in the greenhouse. Its seed dissemination agent is most likely water. C. palmatus has the most elaborate reticulations on the seed-coat of any member of the genus, and it has waxy formations on the seed-coat as well. These two features would tend to form a water-resistant envelope of air pockets which would serve to float the seed (03). SEED BIOLOGY: Cordylanthus palmatus, like many highly specialized species of intermittently flooded plant species in the California Central Valley, almost undoubtedly has considerable capacity for extended periods of dormancy, since the irregular weather conditions typical of the region may result in unfavorable conditions for germination for more than one year. In the greenhouse, the present year's seed germinated without any pre-treatment and was known to germinate up to four years later (03). In germination trials, Chuang and Heckard (22) found C. palmatus germinated most readily at 80 degrees F. in comparison with other Life History - 1 (DRAFT) - Life History Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 Western North American congeners: it had 12 percent germination while the others had a maximum of 4 percent. It germinated better at 50 degrees F; they obtained 94 percent germination at that temperature. They found no difference in germination between light and dark regimes. Germination typically took place in 10-14 days, with an epigeous radicle emerging first, followed by hypocotyl and cotyledon (22). No information has been reported on the annual average or variation in seed production. POPULATION BIOLOGY: Those populations which have been observed over a period of several years or more have shown downward trends in numbers, even in the absence of apparent outside influences. ECOLOGICAL/EDAPHIC FACTORS: Cordylanthus palmatus grows in saline-alkaline soils of lowland flats and plains (03), often in overflow lands which flood intermittently during the winter rainy season (01). Soil: The soils at two sites have been reported as Pescadero clays and Solano fine sandy loams (19,20). Both soils are alfisols formed over quaternary alluvium. Solano soils are typic natrixeralfs, fine loamy mixed-thermic soils. Pescadero soils are aquic natrixeralfs, fine textured montmorillonitic, thermic soils (24). Both have massive clay subsoils, and percolation and infiltration are slow. In some reports, a white, powdery residue has been observed on the soil surface during the dry period (15); this is reported as being sodium bicarbonate (03). Both soil types are characterized as saline or saline-alkaline (20), but C. palmatus appears to occupy only the most extreme microsites. Soil chemistry: The soil series at one Mendota site was reported by Heckard (03) as being black-alkali, or saline-alkaline; they had a pH of 8-9 (10). Dr. Heckard believes that this species, while occurring in soils with high levels of dissolved salts, may require inundation and flushing associated with periodic stream overflow during the winter months to reduce salinity and thereby stimulate germination (03). The plant apparently can tolerate higher concentrations of dissolved solids at later periods in its life cycle. Microhabitat: Various microhabitats have been reported for C. palmatus; however, an understanding of the hydrology of the various sites may help to create a more unified picture of its requirements (see hydrology section). Heckard (03) has observed the plant growing in the lowest part of roadsides; Taylor (16) reported it growing on the dirt thrown up on a roadside as result of grading. The plant is at the edges of shallow drainages at the Livermore site, as well as at the edges of scalds on higher ground (23). The available water, dissolved solids, soil texture, and microtopography and patterns of water movement and salt accumulation probably determine the microhabitat occupied by C. palmatus--high ground or low ground--at a given site. Life History - 2 (DRAFT) - Life History Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 Soil saturation may play a critical part in the life cycle of C. palmatus. Germination is the most vulnerable stage in the life cycle of a plant, and the bird's-beak may rely on the flooded winter period as a time when the dissolved solids present in the soil solution are most dilute, enabling germination and survival (03). Although speculative at this time, it suggests that a natural regime of flooding or at least saturation during winter is essential for this plant. TROPHIC STATUS: C. palmatus is a hemiparasitic plant. Heckard and Chuang (22) investigated the parasitic relations of this and other members of Cordylanthus in the greenhouse. They found members of the genus to not be host-specific, although there were variations in plant growth between different hosts. Heckard (03) reports the haustorial connections extremely difficult to see. Taylor (16) speculated that Suaeda fruticosa and Atriplex cordulata may be the hosts; Heckard also speculates that Distichlis may be a host (03). CHARACTERISTIC DOMINANCE: The areas where C. palmatus are found are dominated typically by Frankenia grandifolia, Suaeda fruticosa, Distichlis spicata var. stricta, Cressa truxillensis var. vallicola, Allenrolfea occidentalis and Hemizonia pungens (02,15,19). C. palmatus is by no means a dominant or co-dominant in the community (it is a component) (02,03, 14,15,19). The characteristic aspect of vegetation is very sparse in this uninviting habitat. Other species reported as growing in close association with C. palmatus are as follows (asterisks indicate the species is non-native): Bassia hyssopifolia*, Atriplex argentea var. expansa, Spergularia bocconii*, Lasthenia platycarpha, Medicago polymorpha*, Heleochloa schoenoides, Plantago bigelovii, Polypogon monspeliensis*, Eryngium aristulatum, Hordeum geniculatum*, and Salicornia subterminalis (02,14,15,19). COMMUNITY ECOLOGY: The plant community where palmate-bracted birds-beak is found has been described as an alkaline scrub. SPECIES INTERRELATIONSHIPS: C. palmatus is hemiparasitic; the host species are not well known, but likely hosts are Distichlis spicata var. stricta, Suaeda fruticosa and Atriplex fruticosa, as well as possibly Allenrolfea occidentalis, Salicornia subterminalis (03,16). OTHER LIFE HISTORY DESCRIPTORS: None. Life History - 3
                           (DRAFT) - Management Practices
                         Species BIRDS-BEAK, PALMATE-BRACTED
                                Species Id ESIS701041
                                   Date 13 MAR 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Adverse Harassment/Vandalism/Indiscriminate Killing Existing Harassment/Vandalism/Indiscriminate Killing Adverse Off Road Vehicles Existing Off Road Vehicles Adverse Inherent Reproductive Characteristics Existing Inherent Reproductive Characteristics Adverse Low Gene Pool Existing Low Gene Pool Adverse Recreational development Existing Recreational development Adverse Salinity alteration Existing Salinity alteration Adverse Draining wetlands, marshes, ponds, lakes Existing Draining wetlands, marshes, ponds, lakes Adverse Strip mining Existing Strip mining Adverse Water Level Stabilization Existing Water Level Stabilization Adverse Flooding Existing Flooding Adverse Groundwater drawdown Existing Groundwater drawdown Adverse Existing COMMENTS ON MANAGEMENT PRACTICES - Land conversion to agricultural and urban uses. Although the seasonally ponded "black-alkali" (nonsaline alkaline or saline-alkaline) soils are marginal for agriculture, salt-tolerant strains of crops have been developed, making the conversion to agriculture economically feasible. As a result, even these poor soils have been increasingly farmed in the Central Valley of California. Of the 11 extant and historic sites, the College City type locality, the greater portion of the Woodland site, possible all or part of the Kerman, Madera and Stockton sites may have been lost to agriculture. The suitability of these soils for urban use is likewise marginal; however, urban encroachment into C. palmatus habitat seems to make development irresistible to land owners. The Livermore site, which was discovered during the course of environmental surveys for a proposed housing project, continues to be in jeopardy from urbanization, both from development and as a result of recreation pressure from adjacent suburban residents. In addition, in January, 1983, about 90 ac of the Livermore site was bulldozed and a portion of the associated wetlands were filled (12, 13); this was probably done intentionally in an attempt to eliminate the birds-beak and pave the way for development (14). The Woodland site was extirpated by a sewage pond, and a portion of the Davis property lies on City of Davis lands (01). Management Practices - 1 (DRAFT) - Management Practices Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 Aside from direct loss of habitat from agricultural or urban uses, indirect effects to the population caused by changes in soil or water flow regime on adjacent lands may threaten the species as well. Runoff made more rapid or more sluggish may be detrimental to the population (12); changes in the water table, whether higher or lower, could affect the salt concentrations in the soil, creating too saline an environment or rendering the site habitable for more competitive species (14); off-site pollution flowing onto existing populations may cause deleterious effects; and changes in the levels of naturally-occurring dissolved solids may adversely affect the life cycle of this species (13). Grazing: Historically, cattle grazing affected many of the areas once supporting this species. In some areas the plant species composition was undoubtedly altered significantly by grazing animals. Since palmate-bracted birds-beak is a hemiparasite, it might be subject to effects indirectly. Existing grazing levels do not appear to threaten those areas still supporting C. palmatus (14). Waterfowl management: The marginally productive overflow areas of the Central Valley were, before coming under pressure for agricultural conversion, to a large degree managed for waterfowl use by private duck clubs and government refuges. Although not documented as clearly as loss to agricultural conversion, seasonal fall flooding would almost certainly degrade habitat for this species (03). Evidence for this is that the recently-discovered remnant populations at the Colusa NWR and the Mendota WMA are found in areas which do not receive the seasonal flooding required for waterfowl, but instead are found in sites nearby which are not flooded. Doug Stone (15) indicates that the levee adjacent to the Colusa NWR site represents a threat to the population, as inadvertent flooding could destroy the site. Off-road vehicle use: Half of the ten individuals reintroduced to the Mendota WMA in 1973 by Dr. Larry Heckard were destroyed by off-road vehicles (02). The newly-mapped colony at the Mendota WMA is located on the shoulder of a dirt road and is clearly vulnerable to off-road pressures (16). The discoverer of the newly-mapped population at the Colusa NWR, Doug Stone, noted in his field notes (15) that the site is accessible by road and by foot; it appears that ORV use may also represent a threat at that site. The Livermore site is also threatened by off-road vehicles; on several occasions, Dr. Larry Stromberg has observed dirt bikes, presumably ridden by nearby residents, in the C. palmatus site (14). Here, the danger is most acute, since the prospect of continuing, increasing, and heavy ORV use is not merely a possibility but a certainty. Inadequate legal protection: Although C. palmatus is listed as endangered by both the USFWS and the California Department of Fish and Game, agricultural conversion is not precluded by the legal protection afforded under either the Endangered Species Act or the California Native Plant Protection Act. Penalties for intentional vandalism, although covered under the Endangered Species Act, are not sufficient to represent a deterrent in some cases. Considerable protection may Management Practices - 2 (DRAFT) - Management Practices Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 be afforded under the regulations of the U.S. Army Corps of Engineers, which have jurisdiction over wetlands, including the seasonal wetlands inhabited by Cordylanthus palmatus). The Corps has asserted its jurisdiction over portions of the Livermore site; however, its criteria for defining wetland sites, which includes consideration of soil, water and vegetation characteristics, may not include the actual habitat occupied by C. palmatus (14). Inherent reproduction and population characteristics: Dr. Larry Heckard has reported observing an otherwise undisturbed population decline to zero on a barren alkali plain east of Mendota (02,03). Genetic depletion and reduced reproductive potential may further threaten the species (17,18). UNAPPROVED PLAN: Management Practices - 3
                                   (DRAFT) - References
                           Species BIRDS-BEAK, PALMATE-BRACTED
                                  Species Id ESIS701041
                                      Date 13 MAR 96



     

References

***** REFERENCES FOR ALL NARRATIVES EXCEPT N-OCCURRENCE ***** 01 Munz, P.A. and David Keck. 1973. A California flora and supplement. Univ. of Calif. Press, Berkeley, CA. 1905 pp. 02 Heckard, L.R. 1977. Rare plant status report, Cordylanthus palmatus. Calif. Native Plant Society, Sacramento, CA. 3 pp. 03 Heckard, Larry R. 1987. Pers. comm. Research botanist, Jepson Herbarium, Sacramento, CA. 04 Ferris, R.S. 1918. Taxonomy and distribution of Adenostegia. Bull. Torrey Bot. Club. 45:399-423. 05 Macbride, J.F. 1919. Reclassified or new spermatophytes, chiefly North American. Contr. Gray Herbarium. 59:28-39. 06 Pennell, F.W. 1947. Some hitherto undescribed Scrophulariaceae of the Pacific States. Proc. Acad. Nat. Sci. Philadelphia 99:155-199. (see p 199). 07 Munz, P.A. 1958. California miscellany IV. Aliso 4:87-100. 08 Mason, H.W. 1957. Flora of the marshes of California. Univ. of Calif. Press, Berkeley. 878 pp. 09 Abrams, Leroy. 1951. Illustrated flora of the Pacific States. Vol III. Stanford Univ. Press. 866 pp. (see pp 850-851). 10 Chuang, T.I. and L.R. Heckard. 1973. Taxonomy of Cordylanthus subgenus Hemistegia (Scrophulariaceae). Brittonia 25:135-158. 11 Smith J.P., Jr., and R.P. York. 1984. Inventory of rare and endangered vascular plants of California (third edition). Calif. Native Plant Society, Sacramento. 174 pp. 12 Farless, Jack. 1983. Letter dated 12 December, 1983 from Jack Farless, Acting Chief, Construction and Oper. Div., U.S. Army Corps of Engineers, to Gerald Peeler, Assist. City Manager, City of Livermore, CA. 13 Farless, Jack. 1985. Letter dated September 16, 1985, from Jack Farless, Chief, Construction Oper. Div., U.S. Army Corps of Enginers, to William Shake, USFWS, Portland, OR. 14 Stromberg, Larry. 1987. Pers. comm. Consulting plant ecologist, Albany, CA. 15 Stone, Doug. 1987. Biologist, Biosystems Analysis, Santa Cruz. Field notes on file at Calif. Nat. Diversity Data Base, Sacramento, CA. 3 pp. 16 Taylor, Dean. 1987. Letter dated January 28, 1987 to Calif. Nat. Diversity Data Base, Sacramento, CA. 17 U.S. Fish and wildlife Service. 1985. Proposed rule, Cordylanthus palmatus (Palmate-Bracted Birds-Beak). Fed. Reg. 50 (136) 28870-28873. 18 U.S. Fish and Wildlife Service. 1986. Final rule, Cordylanthus palmatus, (Palmate-Bracted Birds-Beak). Fed. Reg. 51(126): 23765-23769. 19 California Native Plant Society. (various dates). California native plant field survey forms. On file at: Calif. Dept. of Fish and Game Nat. Diversity Data Base, Sacramento, CA. 20 U.S. Soil Conservation Society. 1966. Soil Survey, Alameda Area, CA. US Department of Agriculture. See map 10 for Alameda County site. References - 1 (DRAFT) - References Species BIRDS-BEAK, PALMATE-BRACTED Species Id ESIS701041 Date 13 MAR 96 21 Zander, M. 1984. Memo dated October 1, 1984 to Vicki Reynolds, Robin Cox, Lin Grayson, Kathy Zavitz, Paul Kelly, Monty Knudsen. 4 pp. 22 Chuang, T.I. and L.R. Heckard. 1971. Observations on root-parasitism in Cordylanthus (Scrophulariaceae). Amer. J. Bot. 58(3):218-228. 23 Leitner, Barbara. 1987. Pers. observ. Oakland, CA 94618. 24 Rogers, John. 1987. Pers. comm. USDA, Soil Cons. Soc., Davis, CA. ***** REFERENCES FOR N-OCCURRENCE NARRATIVE ONLY ***** 01 California Native Plant Society. (various dates). California native plant field survey forms. On file: Calif. Dept. of Fish and Game Natural Diversity Data Base, Sacramento. 02 U.S. Fish and Wildlife Service. 1985. Proposed rule, Cordylanthus palmatus (Palmate-bracted birds-beak). Fed. Reg. 50(136) 28870-28873. 03 U.S. Fish and Wildife Service. 1986. Final rule, Cordylanthus palmatus (Palmate-bracted birds-beak). Fed. Reg. 51(126):23765- 23769. 04 Heckard, L.R. 1977. Rare plant status report, Cordylanthus palmatus. Calif. Native Plant Society, Sacramento. 3 pp. 05 Cox, Robin. 1984. Element preservation plan, Cordylanthus palmatus. The Nature Conservancy, San Francisco, CA. 3 pp + attachments. 06 Stromberg, Larry. 1987. Pers. comm. Consulting plant ecologist, Albany, CA. 07 Farless, Jack. 1983. Letter dated 12 December, 1983, from Jack Farless, Acting Chief, Construction and Operations Division, U.S. Army Corps of Engineers, to Gerald Peeler, Assistant City Manager, Livermore, CA. 08 Farless, Jack. 1985. Letter dated September 15, 1985, from Jack Farless, U.S. Army Corps pf Engineers Construction Division, San Francisco, to William Shake, USFWS, Portland, OR. 09 Zander, Michael. 1982. Garaventa, Barnet Range, Anden Mitigation Planning, Phase I. ESA/Madrone, Novato, CA. Cited in Farless 1985 memo. 10 Taylor, Dean. 1987. Letter dated January 28, 1987 to California Natural Diversity Data Base, Sacramento, CA. 11 Harlow, David. 1987. Memorandum dated September 9, 1987 to Refuge Manager, Sacramento National Wildife Refuge Comples, Willows, CA. 12 Heckard, Larry R. 1987. Pers. comm. Research botanist, Jepson Herbarium, Univ. of Calif., Berkeley. 13 Steele, Dale T. 1985. Letter from Dale Steele (no address) dated November 15, 1985 to Regional Director, USFWS, Portland, OR. References - 2