Planning for Biodiversity: Bringing Agriculture
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California's Freshwater Fishes: Status and Management
California’s freshwater fishes: status and management Rebecca M. Quiñones* and Peter B. Moyle Center for Watershed Sciences, University of California at Davis, One Shields Ave, Davis, 95616, USA * correspondence to [email protected] SUMMARY Fishes in Mediterranean climates are adapted to thrive in streams with dy- namic environmental conditions such as strong seasonality in flows. Howev- er, anthropogenic threats to species viability, in combination with climate change, can alter habitats beyond native species’ environmental tolerances and may result in extirpation. Although the effects of a Mediterranean cli- mate on aquatic habitats in California have resulted in a diverse fish fauna, freshwater fishes are significantly threatened by alien species invasions, the presence of dams, and water withdrawals associated with agricultural and urban use. A long history of habitat degradation and dependence of salmonid taxa on hatchery supplementation are also contributing to the decline of fish- es in the state. These threats are exacerbated by climate change, which is also reducing suitable habitats through increases in temperatures and chang- es to flow regimes. Approximately 80% of freshwater fishes are now facing extinction in the next 100 years, unless current trends are reversed by active conservation. Here, we review threats to California freshwater fishes and update a five-tiered approach to preserve aquatic biodiversity in California, with emphasis on fish species diversity. Central to the approach are man- agement actions that address conservation at different scales, from single taxon and species assemblages to Aquatic Diversity Management Areas, wa- tersheds, and bioregions. Keywords: alien fishes, climate change, conservation strategy, dams Citation: Quiñones RM, Moyle PB (2015) California’s freshwater fishes: status and man- agement. -
Phylogenetic Analysis of Anostracans (Branchiopoda: Anostraca) Inferred from Nuclear 18S Ribosomal DNA (18S Rdna) Sequences
MOLECULAR PHYLOGENETICS AND EVOLUTION Molecular Phylogenetics and Evolution 25 (2002) 535–544 www.academicpress.com Phylogenetic analysis of anostracans (Branchiopoda: Anostraca) inferred from nuclear 18S ribosomal DNA (18S rDNA) sequences Peter H.H. Weekers,a,* Gopal Murugan,a,1 Jacques R. Vanfleteren,a Denton Belk,b and Henri J. Dumonta a Department of Biology, Ghent University, Ledeganckstraat 35, B-9000 Ghent, Belgium b Biology Department, Our Lady of the Lake University of San Antonio, San Antonio, TX 78207, USA Received 20 February 2001; received in revised form 18 June 2002 Abstract The nuclear small subunit ribosomal DNA (18S rDNA) of 27 anostracans (Branchiopoda: Anostraca) belonging to 14 genera and eight out of nine traditionally recognized families has been sequenced and used for phylogenetic analysis. The 18S rDNA phylogeny shows that the anostracans are monophyletic. The taxa under examination form two clades of subordinal level and eight clades of family level. Two families the Polyartemiidae and Linderiellidae are suppressed and merged with the Chirocephalidae, of which together they form a subfamily. In contrast, the Parartemiinae are removed from the Branchipodidae, raised to family level (Parartemiidae) and cluster as a sister group to the Artemiidae in a clade defined here as the Artemiina (new suborder). A number of morphological traits support this new suborder. The Branchipodidae are separated into two families, the Branchipodidae and Ta- nymastigidae (new family). The relationship between Dendrocephalus and Thamnocephalus requires further study and needs the addition of Branchinella sequences to decide whether the Thamnocephalidae are monophyletic. Surprisingly, Polyartemiella hazeni and Polyartemia forcipata (‘‘Family’’ Polyartemiidae), with 17 and 19 thoracic segments and pairs of trunk limb as opposed to all other anostracans with only 11 pairs, do not cluster but are separated by Linderiella santarosae (‘‘Family’’ Linderiellidae), which has 11 pairs of trunk limbs. -
CATALINA CALIFORNIA QUAIL (Callipepla Californica Catalinensis) Paul W
II SPECIES ACCOUNTS Andy Birch PDF of Catalina California Quail account from: Shuford, W. D., and Gardali, T., editors. 2008. California Bird Species of Special Concern: A ranked assessment of species, subspecies, and distinct populations of birds of immediate conservation concern in California. Studies of Western Birds 1. Western Field Ornithologists, Camarillo, California, and California Department of Fish and Game, Sacramento. California Bird Species of Special Concern CATALINA CALIFORNIA QUAIL (Callipepla californica catalinensis) Paul W. Collins Criteria Scores Population Trend 0 Santa Range Trend 0 Barbara County Population Size 7.5 Range Size 10 Ventura Endemism 10 County Population Concentration 10 Threats 0 Los San Miguel Is. Santa Cruz Is. Angeles County Anacapa Is. Santa Rosa Is. Santa Barbara Is. Santa Catalina Is. San Nicolas Is. San Clemente Is. Current Year-round Range Historic Year-round Range County Boundaries Kilometers 20 10 0 20 Current and historic (ca. 1944) year-round range of the Catalina California Quail. Birds from Santa Catalina Island (perhaps brought by Native Americans) later introduced successfully to Santa Rosa (1935–1940) and Santa Cruz (late 1940s) islands, but unsuccessfully to San Nicolas Island (1962); quail from mainland populations of C. c. californica introduced unsuccessfully to Santa Cruz (prior to 1875) and San Clemente (late 19th century, 1913) islands. Catalina California Quail Studies of Western Birds 1:107–111, 2008 107 Studies of Western Birds No. 1 SPECIAL CONCERN PRIORITY HISTORIC RANGE AND ABUNDANCE Currently considered a Bird Species of Special IN CALIFORNIA Concern (year round), priority 3. This subspecies Grinnell and Miller (1944) described the Catalina was not included on prior special concern lists California Quail as a “common to abundant” (Remsen 1978, CDFG 1992). -
Volume 2, Chapter 10-2: Arthropods: Crustacea
Glime, J. M. 2017. Arthropods: Crustacea – Ostracoda and Amphipoda. Chapt. 10-2. In: Glime, J. M. Bryophyte Ecology. Volume 2. 10-2-1 Bryological Interaction. Ebook sponsored by Michigan Technological University and the International Association of Bryologists. Last updated 19 July 2020 and available at <http://digitalcommons.mtu.edu/bryophyte-ecology2/>. CHAPTER 10-2 ARTHROPODS: CRUSTACEA – OSTRACODA AND AMPHPODA TABLE OF CONTENTS CLASS OSTRACODA ..................................................................................................................................... 10-2-2 Adaptations ................................................................................................................................................ 10-2-3 Swimming to Crawling ....................................................................................................................... 10-2-3 Reproduction ....................................................................................................................................... 10-2-3 Habitats ...................................................................................................................................................... 10-2-3 Terrestrial ............................................................................................................................................ 10-2-3 Peat Bogs ............................................................................................................................................ 10-2-4 Aquatic ............................................................................................................................................... -
Aquatic Invertebrates and Waterbirds of Wetlands and Rivers of the Southern Carnarvon Basin, Western Australia
DOI: 10.18195/issn.0313-122x.61.2000.217-265 Records of the Western Australian Museum Supplement No. 61: 217-265 (2000). Aquatic invertebrates and waterbirds of wetlands and rivers of the southern Carnarvon Basin, Western Australia 3 3 S.A. Halsel, R.J. ShieF, A.W. Storey, D.H.D. Edward , I. Lansburyt, D.J. Cale and M.S. HarveyS 1 Department of Conservation and Land Management, Wildlife Research Centre, PO Box 51, Wanneroo, Western Australia 6946, Australia 2CRC for Freshwater Ecology, Murray-Darling Freshwater Research Centre, PO Box 921, Albury, New South Wales 2640, Australia 3 Department of Zoology, The University of Western Australia, Nedlands, Western Australia 6907, Australia 4 Hope Entomological Collections, Oxford University Museum, Parks Road, Oxford OXl 3PW, United Kingdom 5 Department of Terrestrial Invertebrates, Western Australian Museum, Francis Street, Perth, Western Australia 6000, Australia Abstract - Fifty-six sites, representing 53 wetlands, were surveyed in the southern Carnarvon Basin in 1994 and 1995 with the aim of documenting the waterbird and aquatic invertebrate fauna of the region. Most sites were surveyed in both winter and summer, although some contained water only one occasion. Altogether 57 waterbird species were recorded, with 29 292 waterbirds of 25 species on Lake MacLeod in October 1994. River pools were shown to be relatively important for waterbirds, while many freshwater claypans were little used. At least 492 species of aquatic invertebrate were collected. The invertebrate fauna was characterized by the low frequency with which taxa occurred: a third of the species were collected at a single site on only one occasion. -
Predator and Scavenger Aggregation to Discarded By-Catch from Dredge Fisheries: Importance of Damage Level
Journal of Sea Research 51 (2004) 69–76 www.elsevier.com/locate/seares Short Communication Predator and scavenger aggregation to discarded by-catch from dredge fisheries: importance of damage level S.R. Jenkinsa,b,*, C. Mullena, A.R. Branda a Port Erin Marine Laboratory (University of Liverpool), Port Erin, Isle of Man, British Isles, IM9 6JA, UK b Marine Biological Association, Citadel Hill, Plymouth, PL1 2PB, UK Received 23 October 2002; accepted 22 May 2003 Abstract Predator and scavenger aggregation to simulated discards from a scallop dredge fishery was investigated in the north Irish Sea using an in situ underwater video to determine differences in the response to varying levels of discard damage. The rate and magnitude of scavenger and predator aggregation was assessed using three different types of bait, undamaged, lightly damaged and highly damaged individuals of the great scallop Pecten maximus. In each treatment scallops were agitated for 40 minutes in seawater to simulate the dredging process, then subjected to the appropriate damage level before being tethered loosely in front of the video camera. The density of predators and scavengers at undamaged scallops was low and equivalent to recorded periods with no bait. Aggregation of a range of predators and scavengers occurred at damaged bait. During the 24 hour period following baiting there was a trend of increasing magnitude of predator abundance with increasing damage level. However, badly damaged scallops were eaten quickly and lightly damaged scallops attracted a higher overall magnitude of predator abundance over a longer 4 day period. Large scale temporal variability in predator aggregation to simulated discarded biota was examined by comparison of results with those of a previous study, at the same site, 4 years previously. -
Polymetallic Nodules Are Essential for Food-Web Integrity of a Prospective Deep-Seabed Mining Area in Pacific Abyssal Plains
www.nature.com/scientificreports OPEN Polymetallic nodules are essential for food‑web integrity of a prospective deep‑seabed mining area in Pacifc abyssal plains Tanja Stratmann1,2,3*, Karline Soetaert1, Daniel Kersken4,5 & Dick van Oevelen1 Polymetallic nodule felds provide hard substrate for sessile organisms on the abyssal seafoor between 3000 and 6000 m water depth. Deep‑seabed mining targets these mineral‑rich nodules and will likely modify the consumer‑resource (trophic) and substrate‑providing (non‑trophic) interactions within the abyssal food web. However, the importance of nodules and their associated sessile fauna in supporting food‑web integrity remains unclear. Here, we use seafoor imagery and published literature to develop highly‑resolved trophic and non‑trophic interaction webs for the Clarion‑Clipperton Fracture Zone (CCZ, central Pacifc Ocean) and the Peru Basin (PB, South‑East Pacifc Ocean) and to assess how nodule removal may modify these networks. The CCZ interaction web included 1028 compartments connected with 59,793 links and the PB interaction web consisted of 342 compartments and 8044 links. We show that knock‑down efects of nodule removal resulted in a 17.9% (CCZ) to 20.8% (PB) loss of all taxa and 22.8% (PB) to 30.6% (CCZ) loss of network links. Subsequent analysis identifed stalked glass sponges living attached to the nodules as key structural species that supported a high diversity of associated fauna. We conclude that polymetallic nodules are critical for food‑web integrity and that their absence will likely result in reduced local benthic biodiversity. Abyssal plains, the deep seafoor between 3000 and 6000 m water depth, have been relatively untouched by anthropogenic impacts due to their extreme depths and distance from continents 1. -
Ecologia D'ostracodes
Ecologia d’ostracodes simbionts (Entocytheridae) de carrancs invasors a Europa Tesi doctoral Alexandre Mestre Pérez Ecologia d’ostracodes simbionts (Entocytheridae) de carrancs invasors a Europa Ecology of symbiotic ostracods (Entocytheridae) inhabiting invasive crayfish in Europe Tesi doctoral 2014 Alexandre Mestre Pérez Departament de Microbiologia i Ecologia Universitat de València Programa de Doctorat en Biodiversitat i Biologia Evolutiva 2014 Ecologia d’ostracodes simbionts (Entocytheridae) de carrancs invasors a Europa Doctorand: Alexandre Mestre Pérez Directors: Francesc Mesquita Joanes Juan Salvador Monrós González La imatge de la portada està composada a partir de la foto d’un carranc de riu americà Pacifas- tacus leniusculus i una foto al microscopi electrònic (feta per Burkhard Scharf) d’una còpula d’ostracodes entocitèrids pertanyents a l’espècie Uncinocythere occidentalis, la qual s’ha tro- bat associada a poblacions exòtiques europees de P. leniusculus en aquest treball. Tesi presentada per Alexandre Mestre Pérez per optar al grau de Doctor en Biologia per la Universitat de València. Firmat: Alexandre Mestre Pérez Tesi dirigida pels doctors Francesc Mesquita Joanes Juan Salvador Monrós González Professors titulars d’Ecologia Universitat de València Firmat: Francesc Mesquita Joanes Firmat: Juan S. Monrós González Aquest treball ha estat finançat per un projecte del Ministeri de Ciència i In- novació (ECOINVADER, CGL2008-01296/BOS) i una beca predoctoral ("Cinc Segles") de la Universitat de València. A ma mare, a mon pare i al meu germà Agraïments Em considere molt afortunat i estic molt agraït d’haver gaudit, durant el llarg camí d’aprenentatge que representa la tesi, d’unes condicions excel lents per poder · desenvolupar aquest treball. -
International Symposium on Biological Control of Arthropods 424 Poster Presentations ______
POSTER PRESENTATIONS ______________________________________________________________ Poster Presentations 423 IMPROVEMENT OF RELEASE METHOD FOR APHIDOLETES APHIDIMYZA (DIPTERA: CECIDOMYIIDAE) BASED ON ECOLOGICAL AND BEHAVIORAL STUDIES Junichiro Abe and Junichi Yukawa Entomological Laboratory, Kyushu University, Japan ABSTRACT. In many countries, Aphidoletes aphidimyza (Rondani) has been used effectively as a biological control agent against aphids, particularly in greenhouses. In Japan, A. aphidimyza was reg- istered as a biological control agent in April 1999, and mass-produced cocoons have been imported from The Netherlands and United Kingdom since mass-rearing methods have not yet been estab- lished. In recent years, the effect of imported A. aphidimyza on aphid populations was evaluated in greenhouses at some Agricultural Experiment Stations in Japan. However, no striking effect has been reported yet from Japan. The failure of its use in Japan seems to be caused chiefly by the lack of detailed ecological or behavioral information of A. aphidimyza. Therefore, we investigated its ecological and behavioral attributes as follows: (1) the survival of pupae in relation to the depth of pupation sites; (2) the time of adult emergence in response to photoperiod during the pupal stage; (3) the importance of a hanging substrate for successful mating; and (4) the influence of adult size and nutrient status on adult longev- ity and fecundity. (1) A commercial natural enemy importer in Japan suggests that users divide cocoons into groups and put each group into a plastic container filled with vermiculite to a depth of 100 mm. However, we believe this is too deep for A. aphidimyza pupae, since under natural conditions mature larvae spin their cocoons in the top few millimeters to a maxmum depth of 30 mm. -
Section 5 References
Section 5 References 5.0 REFERENCES Akçakaya, H. R. and J. L. Atwood. 1997. A habitat-based metapopulation model of the California Gnatcatcher. Conservation Biology 11:422-434. Akçakaya, H.R. 1998. RAMAS GIS: Linking landscape data with population viability analysis (version 3.0). Applied Biomathematics, Setaauket, New York. Anderson, D.W. and J.W. Hickey. 1970. Eggshell changes in certain North American birds. Ed. K. H. Voous. Proc. (XVth) Inter. Ornith. Congress, pp 514-540. E.J. Brill, Leiden, Netherlands. Anderson, D.W., J.R. Jehl, Jr., R.W. Risebrough, L.A. Woods, Jr., L.R. Deweese, and W.G. Edgecomb. 1975. Brown pelicans: improved reproduction of the southern California coast. Science 190:806-808. Atwood, J.L. 1980. The United States distribution of the California black-tailed gnatcatcher. Western Birds 11: 65-78. Atwood, J.L. 1990. Status review of the California gnatcatcher (Polioptila californica). Unpublished Technical Report, Manomet Bird Observatory, Manomet, Massachusetts. Atwood, J.L. 1992. A maximum estimate of the California gnatcatcher’s population size in the United States. Western Birds. 23:1-9. Atwood, J.L. and J.S. Bolsinger. 1992. Elevational distribution of California gnatcatchers in the United States. Journal of Field Ornithology 63:159-168. Atwood, J.L., S.H. Tsai, C.H. Reynolds, M.R. Fugagli. 1998. Factors affecting estimates of California gnatcatcher territory size. Western Birds 29: 269-279. Baharav, D. 1975. Movement of the horned lizard Phrynosoma solare. Copeia 1975: 649-657. Barry, W.J. 1988. Management of sensitive plants in California state parks. Fremontia 16(2):16-20. Beauchamp, R.M. -
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Provided by the author(s) and University College Dublin Library in accordance with publisher policies. Please cite the published version when available. Title ESManage Programme: Irish Freshwater Resources and Assessment of Ecosystem Services Provision Authors(s) Feeley, Hugh B.; Bruen, Michael; Bullock, Craig; Christie, Mike; Kelly, Fiona; Kelly-Quinn, Mary Publication date 2017 Series Report no. 207 Publisher Environmental Protection Agency Link to online version http://www.epa.ie/researchandeducation/research/researchpublications/researchreports/research207.html Item record/more information http://hdl.handle.net/10197/8516 Downloaded 2021-10-01T00:38:27Z The UCD community has made this article openly available. Please share how this access benefits you. Your story matters! (@ucd_oa) © Some rights reserved. For more information, please see the item record link above. Report No. 207 ESManage Project: Irish Freshwater Resources and Assessment of Ecosystem Services Provision Authors: Hugh B. Feeley, Michael Bruen, Craig Bullock, Mike Christie, Fiona Kelly and Mary Kelly-Quinn www.epa.ie ENVIRONMENTAL PROTECTION AGENCY Monitoring, Analysing and Reporting The Environmental Protection Agency (EPA) is responsible for on the Environment protecting and improving the environment as a valuable asset for • Monitoring air quality and implementing the EU Clean Air the people of Ireland. We are committed to protecting people for Europe (CAFÉ) Directive. and the environment from the harmful effects of radiation and pollution. • Independent reporting to inform decision making by national and local government (e.g. periodic reporting on the State of The work of the EPA can be Ireland’s Environment and Indicator Reports). divided into three main areas: Regulating Ireland’s Greenhouse Gas Emissions Regulation: We implement effective regulation and • Preparing Ireland’s greenhouse gas inventories and projections. -
Egg Hatching and Life History of A
EGG HATCHING AND LIFE HISTORY OF A FAIRY SHRIMP BRANCHINECTA MACKINI DEXTER (CRUSTACEA: ANOSTRACA) IN A MOHAVE DOCKET PLAYA DRY LAKE)' DESERT (RABBIT 11-AFC-2 LARS CARPELAN LON R. BROWN AND H. DATE Universityof California, Riverside, California 92502 RECD. MAY 01 2012 Abstract. Observations on populations of Branchinecta mackini in temporaryponds, which last for as little as 3 days to as long as 4 months, on a desert playa showed that hatching of dehydratedcysts (eggs) follows initial entry of water into the basin if salinity remains low. Salinity ranges from an initial 0.5%o to as much as 34%o as the pond evaporates. Hatching is continuous at constant low salinity, but since salinity generally increases rapidly, initial hatch is usually of short duration. Additional periods of hatching follow further inflows of water or after melting of ice, that is, after reductions in salinity. The duration of hatching is in- versely proportional to rate of increase in salinity. When salinity of small-volume summer ponds increases at rates above 500 ppm (1,000 Vmhos) per day, there is virtual inhibitionof hatching. Laboratory studies showed that egg hatching was controlled by both salinity and oxygen operating in various combinations to inhibit or stimulate hatch. The hatching characteristics of desiccated eggs collected from the dried mud of the lake basin differedfrom non-dried eggs obtained from laboratory cultures after ejection from ovisacs of living females. The findingthat a salinity-oxygencomplex regulates hatching in a desert pond permitstenta- tive explanation of a differencebetween branchiopods of humid and arid regions. In both cases the branchiopods are characteristicof astatic waters, and stimulation of the egg to hatch must be by some factor that changes at the time of origin of the temporary pond.