A.18 Conservancy Fairy Shrimp (Branchinecta Conservatio)
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APPENDIX G-7 Listed, Proposed Species, and Critical Habitat Potentially Occurring or Known to Occur in the Project Region Listed, Proposed Species, and Critical Habitat Potentially Occurring or Known to Occur in the Project Region. Scientific Name/ Common Federal/State/ General Habitat Description Habitat Rationale Name CNPS/other Present/ Status Absent Invertebrates Adela oplerella --/--/G2G3, S2S3 Opler's longhorn moth is recorded from 18 sites A Suitable habitat for this species is not Opler’s longhorn moth extending along the west side of the San present within the project site. Francisco Bay from 5 miles southeast of Nicasio in Marin County south to the Gilroy area of Santa Clara County and from the Oakland area on the inner Coast Ranges. Habitat for Opler's longhorn moth consists of serpentine grassland (Federal Register 50CFR17). Andrena blennospermatis --/--/G2, S2 Known occurrences in Contra Costa, Lake, A Yellow carpet is absent from the Blennosperma vernal pool Sonoma, Solano, Yolo, Tehamea, Sacramento, project site. Upland habitat adjacent andrenid bee San Joaquin, El Dorado, and Placer Counties. to vernal pools in the area is Habitat consists of upland areas near vernal pools composed of substrate, such as containing yellow carpet (Blennosperma sp.). gravel, compacted soil, or heavily Forages exclusively on flowering yellow carpet. disturbed soil, which does not This species excavates nests in soil in adjacent provide suitable nesting habitat for upland areas (Thorp 2008). this species. Branchinecta conservatio FE/--/-- Conservancy fairy shrimp inhabit rather large, cool- A Suitable habitat for this species does conservancy fairy shrimp water vernal pools with moderately turbid water. It not occur on site. -
Fig. Ap. 2.1. Denton Tending His Fairy Shrimp Collection
Fig. Ap. 2.1. Denton tending his fairy shrimp collection. 176 Appendix 1 Hatching and Rearing Back in the bowels of this book we noted that However, salts may leach from soils to ultimately if one takes dry soil samples from a pool basin, make the water salty, a situation which commonly preferably at its deepest point, one can then "just turns off hatching. Tap water is usually unsatis- add water and stir". In a day or two nauplii ap- factory, either because it has high TDS, or because pear if their cysts are present. O.K., so they won't it contains chlorine or chloramine, disinfectants always appear, but you get the idea. which may inhibit hatching or kill emerging If your desire is to hatch and rear fairy nauplii. shrimps the hi-tech way, you should get some As you have read time and again in Chapter 5, guidance from Brendonck et al. (1990) and temperature is an important environmental cue for Maeda-Martinez et al. (1995c). If you merely coaxing larvae from their dormant state. You can want to see what an anostracan is like, buy some guess what temperatures might need to be ap- Artemia cysts at the local aquarium shop and fol- proximated given the sample's origin. Try incu- low directions on the container. Should you wish bation at about 3-5°C if it came from the moun- to find out what's in your favorite pool, or gather tains or high desert. If from California grass- together sufficient animals for a study of behavior lands, 10° is a good level at which to start. -
Vernal Pool Fairy Shrimp (Branchinecta Lynchi)
Invertebrates Vernal Pool Fairy Shrimp (Branchinecta lynchi) Vernal Pool Fairy Shrimp (Brachinecta lynchi) Status State: Meets the requirements as a “rare, threatened, or endangered species” under CEQA Federal: Threatened Critical Habitat: Designated 2006 (USFWS 2006) Population Trend Global: Declining due to habitat loss and fragmentation (Eriksen and Belk 1999) State: As above Within Inventory Area: Unknown Data Characterization The location database for the vernal pool fairy shrimp (Brachinecta lynchi) within the inventory area includes 6 records from 1993, 1997, and 1999. The majority of locations are vernal pools within non-native grassland. Other natural and artificial habitats have a high probability of being occupied by additional populations of the vernal pool fairy shrimp throughout the grassland habitats within the ECCC HCP/NCCP inventory area. Beyond the original description (Eng et al. 1990), a scanning electron micrograph of the cyst (resting egg) (Hill and Shepard 1997), and some generalized natural history data (Helm 1997), no peer-reviewed technical literature has been published concerning the vernal pool fairy shrimp. Eriksen and Belk (1999) presented a brief discussion of the vernal pool fairy shrimp and provided a distribution map. Range The vernal pool fairy shrimp is found from Jackson County near Medford, Oregon, throughout the Central Valley, and west to the central Coast Ranges. Isolated southern populations occur on the Santa Rosa Plateau and near Rancho California in Riverside County (Eng et al.1990, Eriksen -
Freshwater Crustaceans As an Aboriginal Food Resource in the Northern Great Basin
UC Merced Journal of California and Great Basin Anthropology Title Freshwater Crustaceans as an Aboriginal Food Resource in the Northern Great Basin Permalink https://escholarship.org/uc/item/3w8765rq Journal Journal of California and Great Basin Anthropology, 20(1) ISSN 0191-3557 Authors Henrikson, Lael S Yohe, Robert M, II Newman, Margaret E et al. Publication Date 1998-07-01 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Joumal of Califomia and Great Basin Anthropology Vol. 20, No. 1, pp. 72-87 (1998). Freshwater Crustaceans as an Aboriginal Food Resource in the Northern Great Basin LAEL SUZANN HENRIKSON, Bureau of Land Management, Shoshone District, 400 W. F Street, Shoshone, ID 83352. ROBERT M. YOHE II, Archaeological Survey of Idaho, Idaho State Historical Society, 210 Main Street, Boise, ID 83702. MARGARET E. NEWMAN, Dept. of Archaeology, University of Calgary, Alberta, Canada T2N 1N4. MARK DRUSS, Idaho Power Company, 1409 West Main Street, P.O. Box 70. Boise, ID 83707. Phyllopods of the genera Triops, Lepidums, and Branchinecta are common inhabitants of many ephemeral lakes in the American West. Tadpole shrimp (Triops spp. and Lepidums spp.) are known to have been a food source in Mexico, and fairy shrimp fBranchinecta spp.) were eaten by the aborigi nal occupants of the Great Basin. Where found, these crustaceans generally occur in numbers large enough to supply abundant calories and nutrients to humans. Several ephemeral lakes studied in the Mojave Desert arul northern Great Basin currently sustain large seasonal populations of these crusta ceans and also are surrounded by numerous small prehistoric camp sites that typically contain small artifactual assemblages consisting largely of milling implements. -
Appendix a California Tiger Salamander and California Fairy Shrimp Aquatic Sampling Survey Report
Appendix A California Tiger Salamander and California Fairy Shrimp Aquatic Sampling Survey Report California Tiger Salamander and California Fairy Shrimp Aquatic Sampling Survey Report Prepared for: Shaw Environmental, Inc. Prepared By: Denise Duffy & Associates, Inc. Contact: Josh Harwayne Senior Project Manager (831) 373-4341 September 2007 SUMMARY The Army is required to conduct wetland monitoring surveys in any areas where environmental cleanup activities could possibly impact protected wetland species on the Former Fort Ord U.S. Army base (Fort Ord), in Monterey County, California (Figure 1). This study provides faunal baseline data for Ranges where soil remediation is likely to be performed in the near future, and could possibly have biological impacts on protected wetland species or habitat. The monitoring study is consistent with the “Wetland Monitoring and Restoration Plan for Munitions and Contaminated Soil Remedial Activities at Former Fort Ord” (ACOE, 2006). Faunal baseline aquatic sampling studies were conducted by Denise Duffy and Associates, Inc. (DD&A) to determine the presence/absence of the federally Threatened California tiger salamander (Ambystoma californiense, CTS) and invertebrates, including the California fairy shrimp (Linderiella occidentalis), a federal species of special concern, at several locations within Fort Ord. Four study sites (Pools 8, 10, 21, and 30) and three control sites (Pools 5, 56, and 101 East) were identified for surveys (Figure 2). Due to the lack of sufficient ponding at three of the study pools during 2007, aquatic sampling occurred only at one of the study sites (Pool 10) and the three control sites. All four water bodies were sampled twice between January and March 2007 for invertebrates. -
Federal Register/Vol. 81, No. 217/Wednesday, November 9
Federal Register / Vol. 81, No. 217 / Wednesday, November 9, 2016 / Notices 78843 Permit No. TE–046262 California for the purpose of enhancing Department of the Interior, Bureau of the species’ survival. Land Management (BLM), the San Juan Applicant: Blake Claypool, San Diego, California Permit No. TE–048739 Islands National Monument Advisory Committee (MAC) will meet as The applicant requests a new permit Applicant: Daniel A. Cordova of U.S. indicated below: to take (survey by pursuit) the Quino Bureau of Reclamation, Sacramento, checkerspot butterfly (Euphydryas California DATES: The MAC will hold a public editha quino); and take (harass by meeting Monday, November 28th, 2016. survey, capture, handle, release, collect The applicant requests a permit The meeting will run from 8:30 a.m. to vouchers, and collect branchiopod amendment to take (harass by survey, 4:30 p.m. The meeting will be held at cysts) the Conservancy fairy shrimp capture, handle, release, collect San Juan Island Grange Hall in Friday (Branchinecta conservatio), longhorn vouchers, and collect branchiopod Harbor on San Juan Island. Public fairy shrimp (Branchinecta cysts) the Conservancy fairy shrimp comment periods will be available in (Branchinecta conservatio), longhorn longiantenna), San Diego fairy shrimp the afternoon from noon until 12:30 and fairy shrimp (Branchinecta (Branchinecta sandiegonensis), 3:00 p.m. until 3:30 p.m. Riverside fairy shrimp (Streptocephalus longiantenna), and vernal pool tadpole woottoni), and vernal pool tadpole shrimp (Lepidurus packardi); in FOR FURTHER INFORMATION CONTACT: shrimp (Lepidurus packardi) in conjunction with survey activities Marcia deChadene`des, San Juan Islands conjunction with survey activities throughout the range of the species in National Monument Manager, P.O. -
Persistence of Branchinecta Paludosa (Anostraca) in Southern Wyoming, with Notes on Zoogeography
This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. JOURNAL OF CRUSTACEAN BIOLOGY, 13(1): 184-189, 1993 PERSISTENCE OF BRANCHINECTA PALUDOSA (ANOSTRACA) IN SOUTHERN WYOMING, WITH NOTES ON ZOOGEOGRAPHY James F. Saunders III, Denton Belk, and Richard Dufford ABSTRACT The fairy shrimp Branchinectapaludosa is a persistentresident of aestival ponds at high elevation in the Medicine Bow Mountains of southernWyoming. These populationsare far removed from the Arctic tundrahabitat that typifiesthe distributionof the species, and appear to representthe southern margin of the range in North America. All of the records for the northernUnited States and southernCanada appear to lie along the CentralFlyway that is a major migrationroute for waterfowland shorebirdsthat nest in the Arctic. Passive dispersal probablyprovides for frequentcolonization of marginalhabitats and gene flow to established populations. The fairy shrimp Branchinectapaludosa have been deposited in the University of (Muller)is widely distributedin the circum- Colorado Museum (UCM 2192, 2193, polar tundra of the Holarctic region (Vek- 2194). The Snowy Range is an axial rem- hoff, 1990). In Europe, it occurs chiefly at nant which rises about 300 m above the latitudes above 60?N, but there are isolated surrounding Medicine Bow Mountains recordsfrom the High Tatra Mountains on (Houston and others, 1978). The ponds are the borderbetween Czechoslovakiaand Po- mainly in the upperTelephone Creek drain- land at about 49?N (Brtek, 1976). Records age at elevations of 3,200-3,350 m. Most for Russia are typically along the Arctic of the ponds are underlainby the Nash Fork margin, but include the southern tip of the formation (Houston and others, 1978), and Kamchatka Peninsula at 52?N (Linder, the characteristicmetadolomite is present 1932). -
Final Designation of Critical Habitat for Four Vernal Pool Crustaceans and Eleven Vernal Pool Plants in California and Southern Oregon; Final Rule
Wednesday, August 6, 2003 Part II Department of the Interior Fish and Wildlife Service 50 CFR Part 17 Endangered and Threatened Wildlife and Plants; Final Designation of Critical Habitat for Four Vernal Pool Crustaceans and Eleven Vernal Pool Plants in California and Southern Oregon; Final Rule VerDate jul<14>2003 21:54 Aug 05, 2003 Jkt 200001 PO 00000 Frm 00001 Fmt 4717 Sfmt 4717 E:\FR\FM\06AUR2.SGM 06AUR2 46684 Federal Register / Vol. 68, No. 151 / Wednesday, August 6, 2003 / Rules and Regulations DEPARTMENT OF THE INTERIOR SUPPLEMENTARY INFORMATION: court orders and court-approved settlement agreements, compliance with Preamble Fish and Wildlife Service which now consumes nearly the entire Designation of Critical Habitat Provides listing program budget. This leaves the 50 CFR Part 17 Little Additional Protection to Species Service with little ability to prioritize its activities to direct scarce listing RIN 1018–AI26 In 30 years of implementing the ESA, resources to the listing program actions the Service has found that the with the most biologically urgent Endangered and Threatened Wildlife designation of statutory critical habitat and Plants; Final Designation of species conservation needs. provides little additional protection to The consequence of the critical Critical Habitat for Four Vernal Pool most listed species, while consuming Crustaceans and Eleven Vernal Pool habitat litigation activity is that limited significant amounts of conservation listing funds are used to defend active Plants in California and Southern resources. The Service’s present system Oregon lawsuits and to comply with the for designating critical habitat is driven growing number of adverse court orders. -
Longhorn Fairy Shrimp (Branchinecta Longiantenna)
Invertebrates Longhorn Fairy Shrimp (Branchinecta longiantenna) Longhorn Fairy Shrimp (Branchinecta longiantenna) Status State: Meets the requirements as a “rare, threatened, or endangered species” under CEQA Federal: Endangered Critical Habitat: Designated 2006 (USFWS 2006) Population Trend Global: Declining due to habitat loss and fragmentation (Eriksen and Belk 1999) State: As above Within Inventory Area: Unknown Data Characterization The location database for the longhorn fairy shrimp (Branchinecta longiantenna) within the inventory area includes 2 records from 1982 and 1990 near the Los Vaqueros Reservoir (Eng et. al. 1990, California Natural Diversity Database 2001). These 2 locations are shallow, sandstone-rock-outcrop vernal pools within non-native grassland. Other natural and artificial habitats have a high probability of being occupied by additional populations of the longhorn fairy shrimp throughout the grassland habitats within the ECCC HCP/NCCP inventory area. In addition to the original description (Eng et. al. 1990), Eriksen and Belk (1999) presented a brief discussion of the longhorn fairy shrimp and provided a distribution map. Hill and Shepard (1997) produced a scanning electron micrograph of the cyst (resting egg), and Helm (1997) provided some generalized natural history data. No other peer-reviewed technical literature has been published concerning the longhorn fairy shrimp. Range Only 8 populations of the longhorn fairy shrimp are known (U.S. Fish and Wildlife Service 1996). Longhorn fairy shrimp occurrences are rare and highly disjunct with specific pool characteristics largely unknown (USFWS 2003). The Altamont pass subunits of the species occur within clear depression pools in sandstone outcrops (Eriksen and Belk 1999; EBRPD 2001; CNDDB 2002). Other populations in the middle and southern range of the species occur in loam and shallow alkaline soil, respectively (USFWS 2003). -
Longhorn Fairy Shrimp Research EA
Longhorn Fairy Shrimp Habitat Research in Contra Costa and Alameda Counties Environmental Assessment U.S. Department of the Interior Bureau of Reclamation March 2017 Mission Statements The Department of the Interior protects and manages the Nation's natural resources and cultural heritage; provides scientific and other information about those resources; and honors its trust responsibilities or special commitments to American Indians, Alaska Natives, and affiliated island communities The mission of the Bureau of Reclamation is to manage, develop, and protect water and related resources in an environmentally and economically sound manner in the interest of the American public. List of Abbreviations and Acronyms BPRP Brushy Peak Regional Preserve CCWD Contra Costa Water District CFR Code of Federal Regulations CVP Central Valley Project CVPCP Central Valley Project Conservation Program EBRPD East Bay Regional Park District Geographic Information System GPS Global Positioning System LARPD Livermore Area Recreation and Park District LFS Longhorn Fairy Shrimp NHPA National Historic Properties Act USFWS U.S. Fish and Wildlife Service VCRP Vasco Caves Regional Preserve Contents Page Section 1 Introduction ................................................................................... 1 1.1 Background ........................................................................................... 1 1.2 Need for the Proposal............................................................................ 1 Section 2 Alternatives Including the Proposed -
Factors Affecting the Distribution and Co-Occurrence of Two Southern Californian Anostracans (Branchiopoda), Branchinecta Sandiegonensis and Streptocephalus Woo1toni
JOURNAL O f' CRUSTAC EA N BIOL OGY . 16(4) : 669 - 677, 1996 FACTORS AFFECTING THE DISTRIBUTION AND CO-OCCURRENCE OF TWO SOUTHERN CALIFORNIAN ANOSTRACANS (BRANCHIOPODA), BRANCHINECTA SANDIEGONENSIS AND STREPTOCEPHALUS WOO1TONI Stacie A. Hathaway and Marie A. Simovicn ABSTRACT We address the role of temp erature and maturation rate in limiting the distribution and co-o c currence of 2 ephemeral pool branchiopods, Branchinecta sandiegon ensis and Streptocephalus wool/ani (Anostraca), in southern California. Branchinecta sandiegon ensis occurs in pools of variable depth (fro m < S em to > 30 em) and duration, while Streptocephalus wool/ani is found only in deeper pool s (>30 ern) of longer duration. These 2 species co-occur in a few pools, but their adults are never observed simultaneously. To bett er understand these patt erns, field collected cysts of both species wer e hatched at an array of constant and 12-h fluctuating tem peratures. Maturation rates were compared in aquaria at room temperature (-20- 22°C) and by field observation. Both species hatched best at cooler temperatures ( lOOC and fluctuating S IYC), but S. WOOl/an i was more eurythermal. Both were inhibited at higher temperatures unless these temperatures were included in a fluctuating regime. After hatching, B. sandiegon ensis did not mature at soc. In laboratory and field observations, B. sandiegonensis matured quickly ( 1 2 week s) at moderate temperatures and died before S. WOOl/ani rea ched maturity. These results indi cate that temperature play s a role in re stri cting the distribution of the se species to the coast, where temperatures are favorable. -
Genetic Population Structure of the Fairy Shrimp Branchinecta Coloradensis (Anostraca) in the Rocky Mountains of Colorado
Color profile: Disabled Composite Default screen 2049 Genetic population structure of the fairy shrimp Branchinecta coloradensis (Anostraca) in the Rocky Mountains of Colorado Andrew J. Bohonak Abstract: Dispersal rates for freshwater invertebrates are often inferred from population genetic data. Although genetic approaches can indicate the amount of isolation in natural populations, departures from an equilibrium between drift and gene flow often lead to biased gene flow estimates. I investigated the genetic population structure of the pond- dwelling fairy shrimp Branchinecta coloradensis in the Rocky Mountains of Colorado, U.S.A., using allozymes. Glaciation in this area and the availability of direct dispersal estimates from previous work permit inferences regarding the relative impacts of history and contemporary gene flow on population structure. Hierarchical F statistics were used θ θ to quantify differentiation within and between valleys ( SV and VT, respectively). Between valleys separated by 5– θ 10 km, a high degree of differentiation ( VT = 0.77) corresponds to biologically reasonable gene flow estimates of 0.07 individuals per generation, although it is possible that this value represents founder effects and nonequilibrium ≤ θ conditions. On a local scale ( 110 m), populations are genetically similar ( SV = 0.13) and gene flow is estimated to be 1.7 individuals exchanged between ponds each generation. This is very close to an ecological estimate of dispersal for B. coloradensis via salamanders. Gene flow estimates from previous studies on other Anostraca are also similar on comparable geographic scales. Thus, population structure in B. coloradensis appears to be at or near equilibrium on a local scale, and possibly on a regional scale as well.