Lipid Content and Fatty Acid Composition of Aquatic Insects
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
List of Animal Species with Ranks October 2017
Washington Natural Heritage Program List of Animal Species with Ranks October 2017 The following list of animals known from Washington is complete for resident and transient vertebrates and several groups of invertebrates, including odonates, branchipods, tiger beetles, butterflies, gastropods, freshwater bivalves and bumble bees. Some species from other groups are included, especially where there are conservation concerns. Among these are the Palouse giant earthworm, a few moths and some of our mayflies and grasshoppers. Currently 857 vertebrate and 1,100 invertebrate taxa are included. Conservation status, in the form of range-wide, national and state ranks are assigned to each taxon. Information on species range and distribution, number of individuals, population trends and threats is collected into a ranking form, analyzed, and used to assign ranks. Ranks are updated periodically, as new information is collected. We welcome new information for any species on our list. Common Name Scientific Name Class Global Rank State Rank State Status Federal Status Northwestern Salamander Ambystoma gracile Amphibia G5 S5 Long-toed Salamander Ambystoma macrodactylum Amphibia G5 S5 Tiger Salamander Ambystoma tigrinum Amphibia G5 S3 Ensatina Ensatina eschscholtzii Amphibia G5 S5 Dunn's Salamander Plethodon dunni Amphibia G4 S3 C Larch Mountain Salamander Plethodon larselli Amphibia G3 S3 S Van Dyke's Salamander Plethodon vandykei Amphibia G3 S3 C Western Red-backed Salamander Plethodon vehiculum Amphibia G5 S5 Rough-skinned Newt Taricha granulosa -
Martina Hortvíková
MASARYKOVA UNIVERZITA PŘÍRODOVĚDECKÁ FAKULTA ÚSTAV BOTANIKY A ZOOLOGIE PREDAČNĚ-DISTURBAČNÍ EFEKT BLEŠIVCE POTOČNÍHO NA POČETNOST LAREV DVOUKŘÍDLÝCH V PRAMENNÉM BIOTOPU Diplomová práce Martina Hortvíková Vedoucí práce: Mgr. Vít Syrovátka, Ph.D. Brno 2016 Bibliografický záznam Autor: Bc. Martina Hortvíková Přírodovědecká fakulta, Masarykova univerzita Ústav botaniky a zoologie Název práce: Predačně-disturbační efekt blešivce potočního na početnost larev dvoukřídlých v pramenném biotopu Studijní program: Chemie Studijní obor: Učitelství chemie pro střední školy Učitelství biologie pro střední školy Vedoucí práce: Mgr. Vít Syrovátka, Ph.D. Akademický rok: 2015/2016 Počet stran: 61+6 Klíčová slova: Blešivec potoční, Gammarus fossarum, predace, prameništní slatiniště, prameniště, minerotrofní gradient, pH, Chironomidae, Ceratopogonidae, Atrichopogon, Oligochaeta, obsah střeva Bibliographic Entry Author Bc. Martina Hortvíková Faculty of Science, Masaryk University Department of Botany and Zoology Title of Thesis: Predator-disturbance effect of Gammarus fossarum on the abundance of Diptera larvae at a spring biotope Degree programme: Chemistry Upper Secondary School Teacher Training in Field of Study: Chemistry Upper Secondary School Teacher Training in Biology Supervisor: Mgr. Vít Syrovátka, Ph.D. Academic Year: 2015/2016 Number of Pages: 61+6 Keywords: Gammarus fossarum, predation, spring fens, minerotrophic gradient, pH, Chironomidae, Ceratopogonidae, Atrichopogon, Oligochaeta, gut content Abstrakt Prameniště jsou vodní biotopy s relativně -
Influences of Diet on the Life Histories of Aquatic Insectsi,2 Toplankton Toxicants, N
PERSPECTIVES 335 Res. Board Influences of Diet on the Life Histories of Aquatic Insectsi,2 toplankton toxicants, N. H. ANDERSON AND KENNETH W. CUMMINS Fish. Res. Department of Entomology and Department of Fisheries and Wildlife, Oregon State University, Corvallis, OR 97331, USA iver into a !33. ,RAM. 1975. ANDERSON, N. H., AND K. W. CUMMINS. 1979. Influences of diet on the life histories of aquatic le effect of insects. J. Fish. Res. Board Can. 36: 335-342. growth of Benthic species are partitioned into functional feeding groups based on food-acquiring mechanisms. Effects of food quality on voltinism, growth rate, and size at maturity are demon- I larvae of strated for representatives of gougers and shredders, collectors, and scrapers. Food quality for iscidae). J. predators is uniformly high, but food quantity (prey density) obviously influences their life histories. A food switch from herbivory to predation, or some ingestion of animal tissues, in large dams stream flow the later stages is a feature of the life cycle of many aquatic insects. Temperature interacts with and C. H. both food quality and quantity in effects on growth as well as having a direct effect on control of metabolism. Thus further elaboration of the role of food in life history phenomena will d seasonal require controlled field or laboratory studies to partition the effects of temperature and food. .ructure of Key words: aquatic insects, feeding strategies, functional groups, life histories i. W. Esch II, ERDA ANDERSON, N. H., AND K. W. CUMMINS. 1979. Influences of diet on the life histories of aquatic G. -
(12) United States Patent (10) Patent No.: US 7,781,648 B2
USOO7781648B2 (12) UnitedO States Patent (10) Patent No.: US 7,781,648 B2 Wang et al. (45) Date of Patent: * Aug. 24, 2010 (54) RESISTANCE TO SOYBEAN APHID IN 5,569,834 A 10/1996 Hinchee et al. ............. 800/312 EARLY MATURING SOYBEAN GERMPLASM 5,574,210 A 1 1/1996 Saghai-Maroof et al. .... 800/265 5,584.807 A 12/1996 McCabe ...................... 604f71 (75) Inventors: Dechun Wang, Okemos, MI (US); A R 2. C t - - - - - - - - - - - - - ty R wk 4 Tl2S Cal. 8ED"S.R. MI 5,763,241. A 6/1998 Fischhoff et al. ............ 800,279 s s 5,824,877. A 10/1998 Hinchee et al. ............. 800,294 (US) 5,846,795 A 12/1998 Ahlquist et al. ............. 435/468 O O 5,861,543 A 1/1999 Lambert et al. ............. 800,279 (73) Assignee: Board of Trustees of Michigan State 5,866,785 A 2/1999 Donson et al. .............. 800,298 University, East Lansing, MI (US) 5.965,794. A 10/1999 Turpen ....................... 800,288 5,977.438 A 1 1/1999 Turpen et al. ............... 800,288 (*) Notice: Subject to any disclaimer, the term of this 5,981,839 A 1 1/1999 Knaufetal. ................ 800,287 patent is extended or adjusted under 35 5,981,840. A 1 1/1999 Zhao et al. .................. 800,294 U.S.C. 154(b) by 426 days. 6,051,757 A 4/2000 Barton et al. ............... 800,294 6,096,944 A 8/2000 Vierling et al. .............. 800,265 This patent is Subject to a terminal dis- 6,143,550 A 11, 2000 Lambert et al. -
Bibliographia Trichopterorum
Entry numbers checked/adjusted: 23/10/12 Bibliographia Trichopterorum Volume 4 1991-2000 (Preliminary) ©Andrew P.Nimmo 106-29 Ave NW, EDMONTON, Alberta, Canada T6J 4H6 e-mail: [email protected] [As at 25/3/14] 2 LITERATURE CITATIONS [*indicates that I have a copy of the paper in question] 0001 Anon. 1993. Studies on the structure and function of river ecosystems of the Far East, 2. Rep. on work supported by Japan Soc. Promot. Sci. 1992. 82 pp. TN. 0002 * . 1994. Gunter Brückerman. 19.12.1960 12.2.1994. Braueria 21:7. [Photo only]. 0003 . 1994. New kind of fly discovered in Man.[itoba]. Eco Briefs, Edmonton Journal. Sept. 4. 0004 . 1997. Caddis biodiversity. Weta 20:40-41. ZRan 134-03000625 & 00002404. 0005 . 1997. Rote Liste gefahrdeter Tiere und Pflanzen des Burgenlandes. BFB-Ber. 87: 1-33. ZRan 135-02001470. 0006 1998. Floods have their benefits. Current Sci., Weekly Reader Corp. 84(1):12. 0007 . 1999. Short reports. Taxa new to Finland, new provincial records and deletions from the fauna of Finland. Ent. Fenn. 10:1-5. ZRan 136-02000496. 0008 . 2000. Entomology report. Sandnats 22(3):10-12, 20. ZRan 137-09000211. 0009 . 2000. Short reports. Ent. Fenn. 11:1-4. ZRan 136-03000823. 0010 * . 2000. Nattsländor - Trichoptera. pp 285-296. In: Rödlistade arter i Sverige 2000. The 2000 Red List of Swedish species. ed. U.Gärdenfors. ArtDatabanken, SLU, Uppsala. ISBN 91 88506 23 1 0011 Aagaard, K., J.O.Solem, T.Nost, & O.Hanssen. 1997. The macrobenthos of the pristine stre- am, Skiftesaa, Haeylandet, Norway. Hydrobiologia 348:81-94. -
Microsoft Outlook
Joey Steil From: Leslie Jordan <[email protected]> Sent: Tuesday, September 25, 2018 1:13 PM To: Angela Ruberto Subject: Potential Environmental Beneficial Users of Surface Water in Your GSA Attachments: Paso Basin - County of San Luis Obispo Groundwater Sustainabilit_detail.xls; Field_Descriptions.xlsx; Freshwater_Species_Data_Sources.xls; FW_Paper_PLOSONE.pdf; FW_Paper_PLOSONE_S1.pdf; FW_Paper_PLOSONE_S2.pdf; FW_Paper_PLOSONE_S3.pdf; FW_Paper_PLOSONE_S4.pdf CALIFORNIA WATER | GROUNDWATER To: GSAs We write to provide a starting point for addressing environmental beneficial users of surface water, as required under the Sustainable Groundwater Management Act (SGMA). SGMA seeks to achieve sustainability, which is defined as the absence of several undesirable results, including “depletions of interconnected surface water that have significant and unreasonable adverse impacts on beneficial users of surface water” (Water Code §10721). The Nature Conservancy (TNC) is a science-based, nonprofit organization with a mission to conserve the lands and waters on which all life depends. Like humans, plants and animals often rely on groundwater for survival, which is why TNC helped develop, and is now helping to implement, SGMA. Earlier this year, we launched the Groundwater Resource Hub, which is an online resource intended to help make it easier and cheaper to address environmental requirements under SGMA. As a first step in addressing when depletions might have an adverse impact, The Nature Conservancy recommends identifying the beneficial users of surface water, which include environmental users. This is a critical step, as it is impossible to define “significant and unreasonable adverse impacts” without knowing what is being impacted. To make this easy, we are providing this letter and the accompanying documents as the best available science on the freshwater species within the boundary of your groundwater sustainability agency (GSA). -
WDNR July, 2001 ACUTE TOXICITY CRITERIA
DERIVATION OF ACUTE AND CHRONIC TOXICITY CRITERIA FOR NICKEL PREPARED BY: JIM SCHMIDT - WDNR July, 2001 ACUTE TOXICITY CRITERIA EPA SPECIES MEAN ACUTE VALUES (values from 3/86 EPA AWQC document, EPA 440/5-86-004 and 3/95 GLWQI Criteria Document for the Protection of Aquatic Life in Ambient Water) NOTE: Normalized hardness and nickel values are listed for a species when information was available over a sufficient hardness range (EPA: maximum hardness > 3 X lowest hardness and > 100 PPM above lowest hardness). Normalized value equals individual result / geometric mean result (rounded to 3 dec. places). Worm, Nais sp. HARDNESS VALUE METHOD NORMALIZED NORMALIZED REFERENCE (PPM) (ug/L) HARDNESS VALUE 50 14100 S M Rehwoldt, et al. 1973 50 14100 GEO MEAN (1 result) Snail, Amnicola sp. HARDNESS VALUE METHOD NORMALIZED NORMALIZED REFERENCE (PPM) (ug/L) HARDNESS VALUE 50 11400 S M Rehwoldt, et al. 1973 50 14300 S M Rehwoldt, et al. 1973 50 12767.9 GEO MEAN (2 results) Snail, Physa gyrina HARDNESS VALUE METHOD NORMALIZED NORMALIZED REFERENCE (PPM) (ug/L) HARDNESS VALUE 26 239 FT U Nebeker, et al. 1986 26 239 GEO MEAN (1 result) Cladoceran, Daphnia magna HARDNESS VALUE METHOD NORMALIZED NORMALIZED REFERENCE (PPM) (ug/L) HARDNESS VALUE 45.3 510 S U 0.570 0.312 Biesinger and Christensen, 1972 51.1 915 S M 0.643 0.561 Call, et al. 1983 51 1800 S M 0.641 1.103 Chapman, et al. Manuscript 100 2360 S M 1.257 1.446 Chapman, et al. Manuscript 104 1920 S M 1.308 1.176 Chapman, et al. -
Combining Taxonomy and Function in the Study of Stream Macroinvertebrates
J. Limnol., 2016; 75(s1): 235-241 ORIGINAL ARTICLE DOI: 10.4081/jlimnol.2016.1373 Combining taxonomy and function in the study of stream macroinvertebrates Kenneth W. CUMMINS* Department of Entomology, Michigan State University, Michigan and Humboldt State University, 1 Harpst Street , Arcata, CA 95521, USA *Corresponding author: [email protected] ABSTRACT Over the last fifty years, research on freshwater macroinvertebrates has been driven largely by the state of the taxonomy of these animals. In the great majority of studies conducted during the 2000s macroinvertebrates have been operationally defined by investigators as invertebrates retained by a 250 µ mesh in field sampling devices. Significant advances have been and continue to be made in devel- oping ever more refined keys to macroinvertebrate groups. The analysis by function is a viable alternative when advances in macroin- vertebrate ecological research is restricted by the level of detail in identifications. Focus on function, namely adaptations of macroinvertebrates to habitats and the utilization of food resources, has facilitated ecological evaluation of freshwater ecosystems (Functional feeding groups; FFG). As the great stream ecologist Noel Hynes observed, aquatic insects around the world exhibit similar morphologies and behaviors, even though they are in very different taxonomic groups. This is the basis for the FFG analysis that was initially developed in the early 1970s. FFG analysis applies taxonomy only to the level of detail that allows assignment to one of six FFG categories: scrapers adapted to feed on periphyton, detrital shredders adapted to feedonly on coarse (CPOM) riparian-derived plant litter that has been colonized by microbes, herbivore shredders that feed on live, rooted aquatic vascular plants, filtering collectors adapted to remove fine particle detritus (FPOM) from the water column, gathering collectors adapted to feed on FPOM where it is de- posited on surfaces or in crevices in the sediments, and predators that capture live prey. -
The Effect of Pond Dyes on Mosquitoes and Other Freshwater Invertebrates
The effect of pond dyes on mosquitoes and other freshwater invertebrates A thesis submitted for the degree of Doctor of Philosophy School of Biological Sciences Natali Ortiz Perea January 2018 Declaration I confirm that this is my own work and the use of all material from other sources has been properly and fully acknowledged. Natali Ortiz Perea ii ABSTRACT Freshwater habitats are important because they represent two percent of Earth’s water resources, are highly diverse in aquatic organisms and are the most productive and threatened ecosystem worldwide. Pollution, urbanization and climatic changes are responsible for drastic changes in these ecosystems. The creation of new ponds offers an opportunity to increase biodiversity, landscape connectivity and provide new habitat for organisms. However, new ponds might be a good habitat for mosquitoes to lay eggs. Mosquitoes have worldwide distribution and are responsible for most of the vector-borne diseases, affecting thousands of people and causing millions of deaths. British mosquitoes currently do not carry human diseases, but they are a biting nuisance. Their distribution, abundance, species composition and potential for mosquito disease transmission are intimately linked to the physical environment. Culex pipiens is commonly found in UK gardens and is a potential vector of viruses including the West Nile Virus. However, any environmental factors that significantly change the distribution and population of Cx. pipiens could impact future risks of disease transmission. Pond dyes are a cosmetic product for garden ponds and lakes; they inhibit algal growth and improve the overall appearance of the water body reflecting surrounding planting. The dyes block red light from entering the water, interrupting the process of photosynthesis and therefore inhibiting the growth of certain aquatic plants such as algae. -
Lineage Sorting by Parameres in Limnephilinae Subfamily (Trichoptera): with Description of a New Tribe, New Genera and New Species
Opusc. Zool. Budapest, 2019, 50(Supplementum 1): 03–98 Lineage sorting by parameres in Limnephilinae subfamily (Trichoptera): with description of a new tribe, new genera and new species 1 2 3 4 5 6 J. OLÁH , T. ANDERSEN , S. BESHKOV , A. BILALLI , G. COPPA , H. IBRAHIMI , K.A. 7 8 9 10 11 12 JOHANSON , T. KOVÁCS , W. MEY , M. MUSLIU J. OLÁH JR & A. RUIZ-GARCIA 1János Oláh, Residence postal address: Tarján u. 28, H-4032 Debrecen, Hungary, [email protected] 2Trond Andersen, Department of Natural History, University Museum of Bergen, University of Bergen, P.O. Box 7800, N-5020 Bergen, Norway, [email protected] 3Stoyan Beshkov, National Museum of Natural History, 1 Tsar Osvoboditel Blvd. 1000 Sofia, Bulgaria, [email protected] 4Astrit Bilalli, University of Peja "Haxhi Zeka", Faculty of Agribusiness, “UÇK” street, 30000 Pejë, Republic of Kosovo, [email protected] 5Gennaro Coppa, 1, rue du Courlis, F-08350 Villers-sur-Bar, France, [email protected] 6Halil Ibrahimi, University of Prishtina, Faculty of Mathematics and Natural Sciences, Department of Biology, Mother Teresa p.n., 10000 Prishtina, Kosovo, [email protected] 7Kjell Arne Johanson, Swedish Museum of Natural History, Department of Zoology, Box 50007, SE-10405 Stockholm, Sweden, [email protected] 8Tibor Kovács, Mátra Museum of Hungarian Natural History Museum, Kossuth Lajos u. 40, H-3200 Gyöngyös, Hungary, [email protected] 9Wolfram Mey, Museum für Naturkunde, Humboldt-Universität, Invalidenstr. 43, D-10115 Berlin, Germany, [email protected] 10Milaim Musliu, University of Peja "Haxhi Zeka", Faculty of Agribusiness, “UÇK” street, 30000 Pejë, Republic of Kosovo, [email protected] 11János Oláh jr., Residence postal address: Tarján u. -
Exhibit D to Cummins Declaration
Case 1:09-cv-01053-OWW-DLB Document 445-4 Filed 08/06/10 Page 1 of 11 Case 1:09-cv-01053-OWW-DLB Document 445-4 Filed 08/06/10 Page 2 of 11 CUMMINS REPRINT LIST March, 2009 1961 1. Lauff, G. W., K. W. Cummins, C. H. Eriksen, and M. Parker. 1961. A method for sorting bottom fauna samples by elutriation. Limnol. Oceanogr. 6:462466. 1962 2. Cummins, K. W. 1962. An evaluation of some techniques for the collection and analysis of benthic samples with special emphasis on lotic waters. Amer. Midl. Nat. 67:477-504. 1964 3. Cummins, K.W. 1964. Factors limiting the microdistribution of the caddisflies Psycnopsyche lepida ( Hagan) and Psycnpsyche guttifer ( Walker) in a Michigan stream (Trichoptera: Limnephilidae). Ecol. Monogr. 34:271-295. 4. Lauff, G.H. and K.W. Cummins. 1964. A model stream for studies in lotic ecology. Ecology 45: 188-191. 5. Mecom, J.O. and K.W. Cummins. 1964. A preliminary study of the trophic relationships of the larvae of Brachycentrus americanus ( Banks) (Trichoptera: Brachycentridae). Trans. Am. Microsc. Soc. 83.233-245. 6. Cummins, K.W. 1964. A review of stream ecology with special emphasis on organism- substrate relationships. in: Organisms-Substrate Relationships In Streams, Pymatuning Lab special publication no. 4, Cummins, K.W., C.A. Tryon, and R.T. Hartman, eds. pp. 2-51. 1966 7. Cummins, K.W., W.P. Coffman, and P.A. Roff. 1966. Trophic relationships in a small woodland stream. Verh. Int. Verein. Limol. 16:627-638. 1969 8. Cummins, K.W., R.R. -
Standard Methods for the Examination of Water and Wastewater
Standard Methods for the Examination of Water and Wastewater Part 8000 TOXICITY 8010 INTRODUCTION*#(1) 8010 A. General Discussion 1. Uses of Toxicity Tests Toxicity tests are desirable in water quality evaluations because chemical and physical tests alone are not sufficient to assess potential effects on aquatic biota.1-3 For example, the effects of chemical interactions and the influence of complex matrices on toxicity cannot be determined from chemical tests alone. Different species of aquatic organisms are not equally susceptible to the same toxic substances nor are organisms equally susceptible throughout the life cycle. Even previous exposure to toxicants can alter susceptibility. In addition, organisms of the same species can respond differently to the same level of a toxicant from time to time, even when all other variables are held constant. Toxicity tests are useful for a variety of purposes that include determining: (a) suitability of environmental conditions for aquatic life, (b) favorable and unfavorable environmental factors, such as DO, pH, temperature, salinity, or turbidity, (c) effect of environmental factors on waste toxicity, (d) toxicity of wastes to a test species, (e) relative sensitivity of aquatic organisms to an effluent or toxicant, (f) amount and type of waste treatment needed to meet water pollution control requirements, (g) effectiveness of waste treatment methods, (h) permissible effluent discharge rates, and (i) compliance with water quality standards, effluent requirements, and discharge permits. In such regulatory assessments, use toxicity test data in conjunction with receiving-water and site-specific discharge data on volumes, dilution rates, and exposure times and concentrations. 2. Test Procedures There is a need to use correct terminology (see Section 8010B, Terminology), and environmentally relevant test procedures to meet regulatory, legal, and research objectives.3-8 The procedures given below allow measurement of biological responses to known and unknown concentrations of materials in both fresh and saline waters.