(DRAFT) - Taxonomy
                           Species BIRD'S-BEAK, SALT MARSH
                                Species Id ESIS701013
                                   Date 13 MAR 96



TAXONOMY

NAME - BIRD'S-BEAK, SALT MARSH OTHER COMMON NAMES - BIRD'S-BEAK, SALT MARSH;BIRDS BEAK and SALT MARSH 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 - MARITIMUS, SSP. SCIENTIFIC NAME - CORDYLANTHUS MARITIMUS SSP. AUTHORITY - TAXONOMY REFERENCES - COMMENTS ON TAXONOMY - Salt Marsh Bird's-beak Cordylanthus maritimus Nutt. ex Benth. ssp. maritimus KINGDOM: Plant GROUP: Angiosperm DIVISION: Magnoliophyta CLASS: Magnoliopsida ORDER: Scrophulariales FAMILY: Scrophulariaceae Chuang and Heckard's (01) description of Cordylanthus maritimus ssp. maritimus follows: "Plants 15-30 cm tall, diffusely and usually much branched, the lateral branches laxly spreading-ascending or decumbent, usually exceeding the central spike; herbage pale to grayish green, occasionally purplish, villous or short-pilose to puberulent or glabrescent, sparsely glandular. Leaves lanceolate to narrowly lanceolate, 5-20 mm long, 2-5 mm broad, the apex acute to acuminate. Inflorescence of loose to dense spikes. Floral bracts oblong or occasionally lanceolate, usually with a pair of short teeth near apex. Corolla 1.5-2.0 (-2.3) cm long, cream-white with pale yellow galea and lower tube, the apex of lower lip tinged with purplish red or pale brownish red that often continues as Taxonomy - 1 (DRAFT) - Taxonomy Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 dots along 3 main veins of pouch. Seeds ca. 2 mm long, 15-20 in each capsule. Habitat and distribution: Salt marshes along the coast from northern Baja California to Carpinteria, Santa Barbara Co., California; flowering May to October." Cordylanthus maritimus ssp. maritimus has been previously known as: Cordylanthus maritimus Nutt. ex Benth. in DC. Prodr. 10:598 1846 (01); Adenostegia maritima (Nutt. ex Benth.) Greene, Prittonia 2:181 (01); Chloropyron maritimum (Nutt. ex Benth.) Heller, Muhlenbergia 3:133 (01) 1907 (12). Some literature (08,10) cite this subspecies as Cordylanthus maritimus subsp. maritimus or C. m. maritimus. Except for Jepsen, who treated Cordylanthus maritimus as one species with two varieties (var. canescens and var. parryi, with var. canescens encompassing the salt marsh bird's-beak), all others (Ferris, Pennell, Mason and Munz) have separated it into two species (Cordylanthus maritimus and C. canescens) (01). Chuang and Heckard (01) pointed out that the morphological criteria used to separate the species are not absolute. Since there is much variation and overlap between groups, they treated them as one species (maritimus) with three subspecies (maritimus, palustris, and canescens) based on geographical distribution and morphological characteristics. They describe Cordylanthus maritimus as consisting of "a complex of three geographically and, to a lesser extent, morphologically separable entities with ssp. palustris at one extreme and ssp. canescens at the other, bridged by a more variable third entity, ssp. maritimus, which approaches but does not completely resemble the others in its morphological variation" (01). Old collections (from San Bernardino Co.-San Bernardino Valley, Parish collection from 1880-1889; San Diego Co.-Oak Grove, Hall 206 in 1895) were assigned to subspecies maritimus by Chuang and Heckard (01), but were judged by them to be intermediate toward subspecies canescens. No collections from either of these locations have been made in this century and the plants are presumed extinct (08). Variations in morphological characteristics of Cordylanthus maritimus ssp. maritimus have been observed. Fox noted clinal differences in flower color, phenological development, branching patterns, population densities and seed production (04). Differences in flower color were described by Dow (08) with those at Pt. Mugu, Ventura Co. Game Preserve, Ormond Beach (Ventura Co.) and Carpenteria (Santa Barbara Co.) having conspicuous purple tri-lobed floral bracts while those farther south were pale cream with faint purple lines. Phenological development is generally thought to occur earlier in the southern populations. Growth form is usually of two types: 1) large and profusely branched, and 2) erect, compact and scarcely branched (08). Plants in the northern part of the range (Santa Barbara Co.) are generally more dense and larger than in the south (San Diego Co.) (08). The holotype for Cordylanthus maritimus ssp. maritimus is at Kew Royal Botanic Gardens, England (01). Other representative specimens Taxonomy - 2 (DRAFT) - Taxonomy Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 can be found at: Herbarium of Pomona College, Rancho Santa Ana Botanic Garden, Claremont, CA (01); Herbarium Dept. of Botany, U.C. Berkeley, Berkeley CA (01); and Dudley Herbarium of Stanford U., San Francisco CA (01). Illustrations showing differences in morphological characteristics of the three subspecies of Cordylanthus maritimus can be found in Chuang and Heckard (01). Taxonomy - 3
                                  (DRAFT) - Status
                           Species BIRD'S-BEAK, SALT MARSH
                                Species Id ESIS701013
                                   Date 13 MAR 96



STATUS

Coded Status E: Federal Endangered Non-consumptive recreational COMMENTS ON STATUS - U.S. STATUSES AND LAWS: The salt marsh bird's-beak has been designated an Endangered species pursuant to the Endangered Species Act (ESA) of 1973 (50 CFR 17.12; P.L. 93-205, 87 Stat. 884; 16 U.S.C. 1531-1540), as amended. This listing includes populations in California and Mexico (Baja California), however, the species is protected wherever found. Critical Habitat has not been designated. 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 subspecies 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 - Has primary responsibility for the management/recovery, listing, and law enforcement/protection of this plant. DOD - Is responsible for cooperation in the management/recovery and protection of the salt marsh bird's-beak where it occurs on DOD lands. STATE STATUSES AND LAWS: STATE: California DESIGNATED STATUS: Endangered ADMINISTRATIVE AGENCY: California Department of Fish and Game STATE STATUTE: California Endangered Species Act; Fish and Game Code, Chapter 1.5, Article 1, Section 2050. Also, California Plant Protection Act of 1977, as amended, Chapter 10. Status - 1 (DRAFT) - Status Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 INTERNATIONAL STATUSES, TREATIES, AND AGREEMENTS: None. ECONOMIC STATUSES: The salt marsh bird's-beak is valued as a rare plant by botanists and plant enthusiasts. 75/07/01:40 FR 27823/27924 - Acceptance of Smithsonian Report 76/06/16:41 FR 24523/ - Proposed rule, list as Endangered 78/09/28:43 FR 44810/44812 - Final rule, listed as Endangered 83/12/08:48 FR 55100/55102 - Five-year review 85/07/22:50 FR 29900/29901 - Notice of 5-year review completion Status - 2
     

HABITAT ASSOCIATIONS

HABITAT - TERRESTRIAL COASTAL LAND USE - Transportation, communications, and Util Mixed Urban or Built-up Land Bays and Estuaries Nonforested Wetland Sandy Areas other than Beaches Transitional Areas Mixed Barren Land NATIONAL WETLAND INVENTORY CODES NWI NWICLS NWIMOD NWISPEC Palustrine FL3 Palustrine EM1 Palustrine EM Estuarine, intertidal FL Estuarine, intertidal EM6 Estuarine, intertidal EM5 Estuarine, intertidal EM3 Estuarine, intertidal EM2 Estuarine, intertidal EM1 Estuarine, subtidal UB2 COMMENTS ON HABITAT ASSOCIATIONS - Cordylanthus maritimus ssp. maritimus is found exclusively in coastal salt marshes from Santa Barbara Co. south. Many of these marshes are small in size and are adjacent to urbanized areas. The species typically occurs between mean high water and extreme high water (08), which falls in a zone commonly dominated by Salicornia (01). In addition to the importance of that specific area, associated habitats which help maintain the conditions normally found there are also critical to C. m. ssp. maritimus survival (08). These associated habitats include the lower marsh and the estuary mouth which maintain tidal influence, upstream areas and the watershed which could effect inflow of fresh water, and adjacent upland areas which have been suggested as possible habitat for pollinators (08). Although there has been some work on elevation preferences and associated vegetation density, little is known about the specific habitat needs of the salt marsh bird's-beak or why it is both spatially and temporally patchy. The following information on habitat preferences is generally based on observations from a specific marsh and may not be true for the subspecies throughout its range. C. m. ssp. maritimus is found in low lying areas, berms, roadsides (09) and in freshwater seeps (08) at Pt. Mugu, and in depressions caused by vehicular traffic at Ormond Beach (09). The species may be found infrequently behind barrier dunes, on dunes, mounds and old oyster-shell dredge spoil (08). Soils have been reported as typically not well drained (09), but also as well-drained, well-aerated and generally dry during summer (08). Data collected at Mugu show a soil pH range from 7.9-9.6, water salinity from 15-132 ppt, electrical conductivity from 3.4-34.0 mmhos/cm (15 mmhos = 34 ppt) and no clear habitat preferences in values for calcium, manganese, sodium and potassium, although potassium largely dominated all plots (09). Soils on which C. m. Habitat Associations - 1 maritimus occurs at Mugu range from silty clays to sandy loams, with sandy loams predominating (09). Water levels and salinity appear to be important factors for C. m. ssp. maritimus survival. Germination occurs in spring when soil salinities are low and soil moisture is high (09). Although tidal influence has been suggested as an important factor, this species is found in areas not influenced by tides (09). Unseasonal high water has resulted in early death (09). C. m. ssp. maritimus is assumed to be absent from the lower marsh because it has no aerenchyma in its roots and therefore is intolerant of constant flooding by tides (Purer as cited in 08). It usually occurs along a narrow elevational band within each marsh (Fox pers. obs. as cited in 08). At Tijuana Estuary the colonies studied were found to inhabit an elevational gradient of only 0.9 ft (from 6.3' to 7.2' above mean lower low water) (03). Mean elevation at Mugu is 0.52 m above mean sea level (0.03-1.18 m MSL) (09). Newman, Ferguson and Dow observed that C. m. ssp. maritimus is associated with sparse to moderate vegetation cover (08). At Mugu, removal of perennial vegetation appeared to promote an increase in C. m. ssp. maritimus (Vanderweir pers. comm. as cited in 08). Dunn (03) also observed higher seedling densities in open areas but suggested that continued survival may be lower. Soil moisture, water salinity and competition with surrounding perennial vegetation appear to be the most critical factors in determining its distribution at Mugu (09). On State lands colonies are known from State park land at Tijuana River Estuary and California Dept. of Fish and Game land at Upper Newport Bay (08). Habitat Associations - 2
                                (DRAFT) - Food Habits
                           Species BIRD'S-BEAK, SALT MARSH
                                Species Id ESIS701013
                                   Date 13 MAR 96



FOOD HABITS

TROPHIC LEVEL - AUTOTROPH Food Habits - 1
                         (DRAFT) - Environment Associations
                           Species BIRD'S-BEAK, SALT MARSH
                                Species Id ESIS701013
                                   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 Aquatic Features: Springs [flowing] G Coastal Wetlands: Mangrove swamps G G G G G G Environment Associations - 1
                               (DRAFT) - Life History
                           Species BIRD'S-BEAK, SALT MARSH
                                Species Id ESIS701013
                                   Date 13 MAR 96



LIFE HISTORY

HABIT: The salt marsh bird's-beak is an herb (05). LIFE CYCLE: Annual (05). TYPE OF REPRODUCTION: Cordylanthus maritimus ssp. maritimus reproduces by sexual means (05). REPRODUCTIVE PHENOLOGY: Germination dates are March (Ferguson pers. comm. as cited in 08) through April (11). Budding occurs in May (11). Anthesis occurs from May through June (01). Fruiting occurs from June through July (11). Seed is dispersed beginning in mid-Sept. at Mugu (09) and in July at Tijuana Estuary (11). Timing of germination, flowering, and senescene probably depends on yearly weather patterns. In general plants in the southern part of the range will precede those farther north in each stage. Most of the dates noted above are specific to those areas studied and may reflect only one season of observation (01,08,09,11). SEX OR SPORE STATUS: Monoclinous (05). POLLINATION, SPORE AND SEED DISSEMINATION: Three possible pollinators were observed at Mugu: leaf cutter bees (Anthidium), sweat bees (Lasioglossum) and Sonoran bumble bee (Bombus sonoras) (09). Modification of upland areas adjacent to salt marshes could destroy habitat that may support C. m. ssp. maritimus pollinators (08). It is proposed that seed is dispersed by water and animals (08). SEED BIOLOGY: Chuang and Heckard (01) report 15-20 seeds ca. 2 mm long in each capsule. Seed production per plant is not known, but may be decreased from predation by leaf roller moth larvae and deleterious impacts from lepidopteran larvae and locusts (08). Seed production can be eliminated if plants are infected with a pathogenic fungus in late spring and early summer (Newman pers. comm. as cited in 08). Germination can occur as soon as seeds are shed from the capsule, but rate and percent germination are enhanced after two years of dry, dark storage (09). Rate and percent germination are also enhanced by stratification at 7 degrees C for 35 days or seed coat scarification (09). Fresh seed germinates better under illumination, but after storage needs less light (09). Germination is inhibited by temperatures greater than 27 degrees C (09) and salinity above 12 ppt (Newman as cited in 08). Dunn (13) observed soil salinities from 9-16 ppt during gemination at Tijuana Estuary, but noted that salinities above 8 ppt begin to inhibit germination. Life History - 1 (DRAFT) - Life History Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 POPULATION BIOLOGY: Little is known about the population biology of this species. At Mugu it is found in dense monotypic stands (09), but at Tijuana Estuary salt marsh bird's-beak is found mostly in small patches interspersed with other vegetation. C. m. ssp. maritimus is both temporally and spatially patchy with some patches failing to germinate each season (03). Ferguson (pers. comm. as cited in 03) attributed colony failure at Tijuana Estuary to flooding, but Dunn (03) suggests a lack of rain, which is needed to lower soil salinity for germination. ECOLOGICAL/EDAPHIC FACTORS: Populations of C. m. ssp. maritimus from Seal Beach south occur on Xerorthants with Xeralfs and Xerolls (07). Those to the north are on Xeralfs with Xerolls, Xerorthants, and Xererts (07). At Mugu, C. m. ssp. maritimus is found on silty clays to sandy loams, with sandy loams predominating (09). Occasionally it occurs behind barrier dunes, reported as being both typically well drained (08) and not well drained (09). At Mugu Lagoon, it occupies low lying areas, berms, roadsides and depressions from vehicular traffic (09). Fox observed that it occurs only within a narrow elevational band in each marsh (08). Germination was shown to be more likely in patches where perennial vegetation had been removed (09). Greater germination in open areas was also observed by Dunn (03), but he suggests that survival may not be high in those areas. TROPHIC STATUS: As with other species of Cordylanthus, C. m. ssp. maritimus is phototrophic and hemi-parasitic (02). Evidence suggests that this is what allows Cordylanthus to stay green and flower after other annuals have fruited and died (06). The roots of C. m. ssp. maritimus produce haustoria, enlarged structures with vascular connections to the hosts roots (02). Chuang and Heckard (02) found that other species of Cordylanthus were facultative rather than obligative parasites and could grow without a host under favorable greenhouse conditions. This was also found to be true for C. m. ssp. maritimus (01). C. m. ssp. maritimus is found in association with Salicornia virginica, Jaumea carnosa, Frankenia grandifolia, Limonium californica and Cressa truxillensis, but Distichlis spicata is the only species at Mugu Lagoon with which it is always present (01). Chuang and Heckard (02) suggest Distichlis spicata as host for other Cordylanthus species. However, at Tijuana Estuary C. m. ssp. maritimus occurs without Distichlis spicata (03) and in experiments was found to form haustoria with a species not found in salt marshes (01). It is therefore thought to be non-host specific (01). CHARACTERISTIC DOMINANCE: The salt marsh bird's-beak is a component of its vegetative community (05,08). COMMUNITY ECOLOGY: C. m. ssp. maritimus occurs in higher marsh areas above Spartina foliosa, and typically in the zone dominated by Salicornia (08). Life History - 2 (DRAFT) - Life History Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 Other plants found in association with it are Monanthochloe littoralis, Distichlis spicata, Frankenia grandifolia and Limonium californica (03, Newman 1981 as cited in 08). A sparse canopy, or areas with open patches may be beneficial for its growth, as vegetation removal at Mugu Lagoon resulted in C. m. ssp. maritimus growth where there had been none previously (09). SPECIES INTERRELATIONSHIPS: See Trophic Status above. OTHER LIFE HISTORY DESCRIPTORS: None. Life History - 3
                           (DRAFT) - Management Practices
                           Species BIRD'S-BEAK, SALT MARSH
                                Species Id ESIS701013
                                   Date 13 MAR 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Beneficial Controlling/Restricting Off-Road Vehicles Beneficial Restricting/regulating human disturbance of populations Beneficial Maintaining/Controlling Water Flow Beneficial Beneficial Developing/maintaining/protecting wetlands Beneficial Controlling water levels Beneficial Land Acquisition Beneficial Controlling pollution [thermal, chemical, physical] Beneficial Maintaining Sperm/Seed Banks Beneficial Transplanting Wild Eggs/Wild Seeds Beneficial Disease Control Measures Beneficial Controlling/Removing Invertebrates Adverse Off Road Vehicles Existing Off Road Vehicles Adverse Gas/Oil Development Existing Gas/Oil Development Adverse Rural Residential/Industrial Areas Existing Rural Residential/Industrial Areas Adverse Highway/Railroads Existing Highway/Railroads Adverse Soil compaction by heavy equipment in mine areas Existing Soil compaction by heavy equipment in mine areas Adverse Siltation Existing Siltation 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 Irrigating Existing Irrigating Adverse Reservoirs Existing Reservoirs Adverse Dredging Existing Dredging Adverse Developing/maintaining stream bank vegetation Existing Developing/maintaining stream bank vegetation Adverse Shoreline modification/development Existing Shoreline modification/development Adverse Applying herbicides Existing Applying herbicides Adverse Exotic/Feral/Introducted Species Management Practices - 1 (DRAFT) - Management Practices Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 RESULT MANAGEMENT PRACTICE Existing Exotic/Feral/Introducted Species Adverse Erosion Existing Erosion Adverse Vegetation Composition Changes Existing Vegetation Composition Changes COMMENTS ON MANAGEMENT PRACTICES - The main reason for the endangered status of Cordylanthus maritimus ssp. maritimus is loss of its southern California coastal salt marsh habitat. In addition to this, remaining marshes have been altered to various extents. Salt marsh habitat has recently been used for marina and industrial development, beach recreational facilities, and housing (08). Changes to hydrologic processes (e.g., closure to tidal flushing and other adverse changes to water level fluctuations) have been shown to affect both the composition of salt marsh vegetation and the processes occurring within the marsh (08). Because of this, any alteration of tidal circulation or changes in the estuary mouth such as: shoreline, bank and channel modification (with associated heavy equipment); wetland filling; or freshwater influence (i.e., reservoirs, water diversion, surface drainage, erosion, groundwater drawdown, flooding, siltation, and resultant changes in salinity levels) could adversely affect this species. Other factors with adverse effects include oil development within the estuaries and the introduction of exotic species. The introduction of Melaleuca quinquenervia (paperbark tree) to a portion of the Tijuana Estuary caused the loss of the salt marsh bird's-beak and its host plant in that area (14). In addition, changes in upland habitat could not only affect the hydrology of the marsh and directly destroy plants and seed, but also could destroy habitat that may support C. m. ssp. maritimus pollinators (08). In areas where salt marsh habitat is being preserved, C. m. ssp. maritimus still may receive adverse impacts which are typical for high marsh areas such as trampling by humans, vehicular traffic, herbicide application along railroad rights-of-ways (08), and refuse dumping (03). It has been suggested that the lack of any C. m. ssp. maritimus populations in Los Angeles Co. may contribute to inbreeding (08). Since little is known of this species biology, factors which are currently unknown could easily be a major influence on its present and future status. APPROVED PLAN: U.S. Fish and Wildlife Service. 1984. Salt Marsh Bird's-beak Recovery Plan (Cordylanthus maritimus subsp. maritimus). U.S. Fish and Wildlife Service, Portland, OR. 92 pp. The primary objective for reclassifying the salt marsh bird's-beak is the protection and management of secure and sufficient habitat. In order to reclassify to threatened status, at least 8 marshes (each containing 15 acres of habitat) supporting Management Practices - 2 (DRAFT) - Management Practices Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 self-maintaining populations must be conserved for 8 years. For delisting, at least 12 (total) marshes (each containing 20 acres of habitat) supporting self-maintaining populations must be conserved for 10 years. Existing populations and colonies of the salt marsh bird's-beak need potection on U.S. Fish and Wildlife Service lands through development and implementation of marsh management plans. These plans will protect high marsh habitat by excluding unauthorized vehicles, imposing visitor restrictions, and avoiding conversions of high marsh to low marsh. Fresh and salt water influences will be maintained by preventing destructive flooding of marshes, alleviating deleterious effects of sewage effluent, preventing channelization of water passing though the marshes, preventing salt water intrusions into the aquifers of the marshes, and protecting all shallow water impoundment systems in the marshes. Marsh management programs need to be developed to protect colonies and habitat on military lands, on State lands, and on other lands (owned by cities, counties, and private concerns). Colonies in marshes of Baja California, Mexico, also need to be protected. For instituting emergency actions, a plan for storing seed from each population needs to be implemented; exotic insect or disease infestations need to be treated; and colonies which suffer seed or plant losses need to be reestablished. Criteria for downlisting or delisting need to be revised; these criteria consist of genetic exchange and host requirements. Dynamics of seed production and loss, seed germination/dormancy, and dispersal mechanisms need to be investigated. The boundaries for managing each marsh need to be determined, and effects of salt and fresh water upon colonies need to be investigated. Pollination and herbivory need to be examined. Autecological studies of associated species need to be conducted to determine effects on survival. Identification and treatment of exotic insect infestations or other diseases are recommended if appropriate. The salt marsh bird's-beak needs to be reestablished by sowing seed in suitable marshes within its historical range, including Mexico. Acreages, boundaries, and ownership of each marsh need to be determined. Habitat of all colonies and marshes, including those in Mexico, need to be biennially monitored to detect changes in distribution and abundance of the salt marsh bird's-beak. Ecological changes in marshes also need to be monitored in those marshes where the species is not extant. Laws, regulations, and policy need to be enforced. Law enforcement efforts and Section 7 consultations need to be evaluated and new regulations or revisions should be promulgated as appropriate. Public education and awareness programs for preserving the species and its marsh ecosystems need to be developed and implemented. The current recovery activities consist of a study (last phase of a two year contract) to assess the success of transplanting (from seed) the species into other suitable habitats. Management Practices - 3
                                   (DRAFT) - References
                             Species BIRD'S-BEAK, SALT MARSH
                                  Species Id ESIS701013
                                      Date 13 MAR 96



     

References

***** REFERENCES FOR ALL NARRATIVES EXCEPT N-OCCURRENCE ***** 01 Chaung, T.I. and L.R. Heckard. 1973. Taxonomy of Cordylanthus subgenus Hemistegia (Scrophulariaceae). Brittonia 25:135-158. 02 Chuang, T.I. and L.R. Heckard. 1971. Observations on root-parasitism in Cordylanthus (Scrophulariaceae). Am. J. Bot. 58(3):218-228. 03 Dunn, P. 1981. Field observations of Cordylanthus maritimus ssp. maritimus at Tijuana Estuary, California. Draft Report. U.S. Dept. of the Navy, San Diego, CA. 17 pp. 04 U.S. Fish and Wildlife Service, Area Manager. July, 1981. [Letter to Commander Hartman, North Island Naval Air Station, San Diego, CA]. On file at: U.S. Fish and Wildlife Service, Sacramento, CA. 05 Munz, P.A. 1974. A flora of southern California. Univ. of Calif. Press, Berkeley. 06 Piehl, M.A. 1962. The root parasitism of Cordylanthus and some of its ecological implications. Am. J. Bot. 53:622. 07 Soil Conservation Service. Soil Taxonomy: A basic ystem of soil classification for making and Interpreting soil surveys. USDA-SCS Agriculture Handbook No. 436. 08 U.S. Fish and Wildlife Service. 1984. Salt Marsh Bird's-Beak Recovery plan, Draft. U.S. Fish and Wildlife Service, Portland, OR. 91 pp. 09 Vanderwier, J.M. 1983. A study of Cordylanthus maritimus ssp. maritimus at Mugu Lagoon, Ventura County, CA. Unpublished report. Available at: Nat. Res. Mgmt. Off., Code 6230-2, Pacific Missile Test Center, Point Mugu, CA 93042. 10 Vanderwier, J.M. 1984. Observations of haustoria and host preference in Cordylanthus maritimus subsp. maritimus (Srophulariaceae) at Mugu Lagoon. Madrono 31(3):185-186. 11 Zedler, J.B. 1984. Salt marsh restoration: A guidebook for southern California. California Sea Grant Report No. T-CSGCP-009, La Jolla, CA. 12 Pennell, F.W. 1951. IN: Illustrated flora of the Pacific states 3. L.R. Abrams. Stanford University Press. 13 Dunn, P. 1981. Unpublished data. U.S. Dept. of the Navy, San Diego, CA. 14 Zedler, J.B. 1986. Personal communication. Biology Department, San Diego State University, San Diego, CA 92182. ***** REFERENCES FOR N-OCCURRENCE NARRATIVE ONLY ***** 01 California Dept. of Fish and Game. July, 1985. Ca. Natural Diversity Data Base: printout on reported locations of Cordylanthus maritimus ssp. maritimus. Endangered Plant Prog., Calif. Dept. of Fish & Game, 1416 Ninth St., Sacramento, CA 95814. 02 Jorgensen, Paul. 1985. Personnal communication. Tijuana River Natl. Estuarine Sanctuary, Calif. Dept. of Parks and Rec., 3990 Old Town Ave., Suite 300-C, San Diego, CA 92110. 03 Newman, Judith. 1985. Personal data. References - 1 (DRAFT) - References Species BIRD'S-BEAK, SALT MARSH Species Id ESIS701013 Date 13 MAR 96 04 U.S. Fish and Wildlife Service. 1984. Salt Marsh Bird's-Beak Recovery Plan, Draft. U.S. Fish & Wildlife Service, Portland, OR. 91 pp. 05 Vanderwier, J.M. 1985. Personal communication. Botanist, Natural Resources Mgmt. Office, Code 6230-2, Pacific Missile Test Center, Point Mugu, CA 93042. 06 Zembel, D. 1985. Personal communication. U.S. Fish and Wildlife Service, Laguna Niguel, CA. 07 Chaung, T.I. and L.R. Heckard. 1973. Taxonomy of Cordylanthus subgenus Hemistegia (Scrophulariaceae). Brittonia 25:135-158. References - 2