Vonalas Létesítmények És Egyéb Antropogén Zavarások Hatása a Vízi

Total Page:16

File Type:pdf, Size:1020Kb

Vonalas Létesítmények És Egyéb Antropogén Zavarások Hatása a Vízi Vonalas létesítmények és egyéb antropogén zavarások hatása a vízi ökoszisztémára, különös tekintettel az ott élő makroszkopikus vízi gerinctelenekre Doktori disszertáció Szerző: Gál Blanka Alexandra Környezettudományi Doktori Iskola Iskolavezető: Dr. Jánosi Imre Doktori program: Környezetbiológia Programvezető: Dr. Tóth Erika Témavezető: Dr. Farkas János egyetemi adjunktus Eötvös Loránd Tudományegyetem, Természettudományi Kar, Biológiai Intézet, Állatrendszertani és Ökológiai Tanszék ELTE TTK, Környezettudományi Doktori Iskola Budapest, 2019 Vonalas létesítmények és egyéb antropogén zavarások hatása a vízi ökoszisztémára, különös tekintettel az ott élő makroszkopikus vízi gerinctelenekre Tartalom 1. Bevezetés ..................................................................................................................... 4 2. Irodalmi áttekintés ........................................................................................................ 9 2.1. Urbanizáció jelentősége és hatása a vízi ökoszisztémára, különös tekintettel a makroszkopikus vízi gerinctelenek diverzitására, a diverzitási komponensek (alfa, béta, gamma diverzitás) és koncepció (taxonómiai, funkcionális, filogenetikai diverzitás) megjelenése az urbanizációval kapcsolatos tanulmányokban ...................... 9 2.2. Vonalas létesítmények hatása a vízi ökoszisztémára, különös tekintettel a makroszkopikus vízi gerinctelenek diverzitására ......................................................... 12 2.3. Eladó betolakodók: az ember szerepe az idegenhonos Decapoda fajok megtelepedésében és terjesztésében, az idegenhonos édesvízi rákfajok kockázatelemzése ......................................................................................................... 16 2.4. Felszínborítási adatok integrálása távérzékeléses vízminőség értékeléséhez ....... 19 3. Célkitűzések ............................................................................................................... 22 4. Anyag és módszer ...................................................................................................... 24 4.1. Urbanizáció hatásának vizsgálata meta- analízises módszerrel ............................ 24 4.1.1. Adatok szintetizálása ....................................................................................... 25 4.1.2. Publikációból adódó torzítások megbecsülése ................................................ 27 4.2. Az utakkal kapcsolatos átereszek hatásának vizsgálata ........................................ 28 4.2.1. Mintavételi terület ........................................................................................... 28 4.2.2. A környezeti változók értékelése .................................................................... 29 4.2.3. Makroszkopikus vízi gerinctelenek gyűjtése és identifikálása ....................... 29 4.2.4. Adatelemzés .................................................................................................... 29 4.3. Az idegenhonos édesvízi rákfajok kockázatelemzése Magyarországon terepi mintavétellel kiegészítve .............................................................................................. 31 4.3.1. Adatgyűjtés ..................................................................................................... 31 4.3.2. Az éghajlat összeegyeztetése a Magyarországon díszállatként tartott Decapoda fajok tekintetében ...................................................................................................... 31 4.3.3. Kockázatelemzés ............................................................................................. 32 4.3.4. Terepi mintavétel ............................................................................................ 32 4.3.5. Genetikai vizsgálat .......................................................................................... 33 4.4. Új index fejlesztése vízminőség értékeléséhez távérzékeléses adatokból lépésről- lépésre ........................................................................................................................... 33 4.4.1. Felszínborítási adatok ...................................................................................... 33 4.4.2. A koncepcionális modell és megvalósítása ..................................................... 34 4.4.3. In situ vízminőség adatbázis ........................................................................... 36 2 Vonalas létesítmények és egyéb antropogén zavarások hatása a vízi ökoszisztémára, különös tekintettel az ott élő makroszkopikus vízi gerinctelenekre 4.4.4. Fizikai- kémiai vizsgálatok ............................................................................. 37 4.4.5. Biológiai értékelés .......................................................................................... 37 4.4.6. A BWQ és RWQ közötti kapcsolat ................................................................. 37 4.4.7. CWQ vs RWQ ................................................................................................. 38 4.4.8. RWQ érték validálása ..................................................................................... 39 5. Eredmények ............................................................................................................... 40 5.1. Urbanizáció hatásával foglalkozó tanulmányok vizsgálata és a meta- analízises módszer eredménye ...................................................................................................... 40 5.1.1. Diverzitás mérések módszertana ..................................................................... 40 5.1.2. Az urbanizáció hatása a makrogerinctelenek diverzitására............................. 42 5.1.3. Publikációból adódó torzítások megbecsülése ................................................ 43 5.2. Az utakkal kapcsolatos átereszek hatásának vizsgálata ........................................ 44 5.2.1. Környezeti változók ........................................................................................ 44 5.2.2. Őshonos makrogerinctelen fajok taxonszáma és abundanciája ...................... 45 5.2.3. A védett és idegenhonos makrogerinctelen fajok abundanciája és taxonszáma ................................................................................................................................... 49 5.2.4. A makrogerinctelen közösségek kompozíciója ............................................... 50 5.3. Az idegenhonos édesvízi rákfajok magyarországi kockázatelemzésének és a terepi mintavételek eredménye ............................................................................................... 52 5.4. Új index fejlesztése vízminőség értékeléséhez távérzékeléses adatokból lépésről- lépésre ........................................................................................................................... 56 6. Diszkusszió ................................................................................................................ 61 6.1. Az urbanizáció hatása a makrogerinctelenekre- a témával kapcsolatos hiányok és a jövőbeli kutatási irányok............................................................................................ 61 6.2. Az utakkal kapcsolatos átereszek hatása makrogerinctelenek diverzitására ......... 65 6.3. Az idegenhonos édesvízi rákfajok kockázatelemzése Magyarországon, bizonyíték a Cherax quadricarinatus (von Martens, 1868) jelenlétéről hazánkban ...................... 68 6.4. Felszínborítási adatok integrálása távérzékeléses vízminőség értékeléséhez: előrelépés a folyami hálózatok heterogenitásának elemzésében .................................. 70 6.5. Eredmények megvitatása, levont következtetések ................................................ 73 7. Összefoglalás ............................................................................................................. 77 8. Summary .................................................................................................................... 80 9. Köszönetnyilvánítás ................................................................................................... 83 10. Felhasznált irodalom .................................................................................................. 84 11. Függelék .................................................................................................................... 109 3 Vonalas létesítmények és egyéb antropogén zavarások hatása a vízi ökoszisztémára, különös tekintettel az ott élő makroszkopikus vízi gerinctelenekre 1. Bevezetés Egy görög filozófus, Hérakleitosz körülbelül 2500 évvel ezelőtt az emberi élet változásával kapcsolatosan azt mondta, hogy „Nem léphetsz kétszer ugyanabba a folyóba”. Az ökológusok számára ez a kifejezés szó szerint igaz, hiszen a folyton változó biotikus és abiotikus környezet az, mely a lotikus rendszerek térbeli és időbeli változását biztosítják. Ennek a variabilitásnak egyértelmű forrásai a természetes zavarások, melyet az áramló víz mennyiségének a megnövekedése okoz és a megnövekedett áramlással járó aljzat mozgása kísér. Azonban az elhúzódó ideig tartó lecsökkent áramlási sebesség (pl. aszályok esetén) és az antropogén tényezők szintén zavarást idézhetnek elő (Resh et al., 1988). Az emberek által előidézett zavarások, melyek legtöbbször a tájhasználatban történt változásokban nyilvánulnak meg, az egész világon veszélyeztetik a folyók ökológiai integritását (Vörösmarty et al., 2010). Zavarásnak nevezünk minden olyan eseményt, mely megváltoztatja a populáció, a közösség, vagy az ökoszisztéma struktúráját,
Recommended publications
  • The Species Flocks in the Ancient Lakes of Sulawesi, Indonesia
    12 Aquatic biodiversity hotspots in Wallacea: the species fl ocks in the ancient lakes of Sulawesi, Indonesia T h o m a s v o n R i n t e l e n , K r i s t i n a v o n R i n t e l e n , M a t t h i a s G l a u b r e c h t , C h r i s t o p h D . S c h u b a r t a n d F a b i a n H e r d e r 12.1 Introduction Some of the world’s most spectacular species radiations or species fl ocks are found in so-called ‘ancient lakes’. Th ese are long-lived lakes that have existed for 100 000 years (Gorthner et al. 1994 , but see also Albrecht and Wilke 2008 ) or more (e.g. Lake Tanganyika and Lake Baikal). Ancient lakes are justifi ably regarded as hotspots of diversifi cation (e.g. Martens 1997 , Rossiter and Kawanabe 2000 ), even if not all ancient lake species fl ocks match the diversity of the super-fl ock of East African cichlids (e.g. Kornfi eld and Smith 2000 , Kocher 2004 ). Studies on the evo- lution of ancient lake organisms have continuously resulted in important insights into general patterns of speciation and radiation (e.g. Streelman and Danley 2003 ) ever since the seminal review of Brooks ( 1950 ). During the last decade, smaller ancient lakes (c. <1 000 km 2 ), which are generally less well investigated, have attracted increasing attention.
    [Show full text]
  • Dytiscid Water Beetles (Coleoptera: Dytiscidae) of the Yukon
    Dytiscid water beetles of the Yukon FRONTISPIECE. Neoscutopterus horni (Crotch), a large, black species of dytiscid beetle that is common in sphagnum bog pools throughout the Yukon Territory. 491 Dytiscid Water Beetles (Coleoptera: Dytiscidae) of the Yukon DAVID J. LARSON Department of Biology, Memorial University of Newfoundland St. John’s, Newfoundland, Canada A1B 3X9 Abstract. One hundred and thirteen species of Dytiscidae (Coleoptera) are recorded from the Yukon Territory. The Yukon distribution, total geographical range and habitat of each of these species is described and multi-species patterns are summarized in tabular form. Several different range patterns are recognized with most species being Holarctic or transcontinental Nearctic boreal (73%) in lentic habitats. Other major range patterns are Arctic (20 species) and Cordilleran (12 species), while a few species are considered to have Grassland (7), Deciduous forest (2) or Southern (5) distributions. Sixteen species have a Beringian and glaciated western Nearctic distribution, i.e. the only Nearctic Wisconsinan refugial area encompassed by their present range is the Alaskan/Central Yukon refugium; 5 of these species are closely confined to this area while 11 have wide ranges that extend in the arctic and/or boreal zones east to Hudson Bay. Résumé. Les dytiques (Coleoptera: Dytiscidae) du Yukon. Cent treize espèces de dytiques (Coleoptera: Dytiscidae) sont connues au Yukon. Leur répartition au Yukon, leur répartition globale et leur habitat sont décrits et un tableau résume les regroupements d’espèces. La répartition permet de reconnaître plusieurs éléments: la majorité des espèces sont holarctiques ou transcontinentales-néarctiques-boréales (73%) dans des habitats lénitiques. Vingt espèces sont arctiques, 12 sont cordillériennes, alors qu’un petit nombre sont de la prairie herbeuse (7), ou de la forêt décidue (2), ou sont australes (5).
    [Show full text]
  • Keanekaragaman Udang Air Tawar (Decapoda: Caridea) Di Sungai Batusuya, Sulawesi Tengah, Indonesia
    SCRIPTA BIOLOGICA | VOLUME 5 | NUMBER 2 | JUNE 2018 | 65–71 | HTTPS://DOI.ORG/10.20884/1.SB.2018.5.1.821 KEANEKARAGAMAN UDANG AIR TAWAR (DECAPODA: CARIDEA) DI SUNGAI BATUSUYA, SULAWESI TENGAH, INDONESIA DIKY DWIYANTO, FAHRI, ANNAWATY Jurusan Biologi, Fakultas Matematika dan Ilmu Pengetahuan Alam, Universitas Tadulako, Palu, Sulawesi Tengah, Indonesia ABSTRACT Sulawesi is one of the four Greater Sunda Islands characterized by rivers and lakes habitats of freshwater shrimps and prawns with a high degree of endemism. The freshwater shrimp and prawns diversity in the Batusuya river of Donggala is less studied compared to the ancient lakes in the Central Sulawesi area. This study aimed to determine the diversity of freshwater shrimp and prawns of the Batusuya river. The sample was collected in November 2016 using tray net. The study site divided into three sampling stations based on the type of habitat. Nine species of freshwater shrimps and prawns were found, i.e., Macrobrachium australe, M. esculentum, M. horstii, M. lar, M. placidulum, Caridina brevicarpalis, C. gracilipes, C. weberi, and Atyopsis spinipes. Six species were found in all localities including Macrobrachium australe, M. esculentum, M. horstii, M. lar, C. brevicarpalis, and C. gracilipes, while M. placidulum, C. weberi, and A. spinipeswere not found in all stations. The highest diversity index (H') was found in the station III indicated freshwater shrimps and prawns favored the environmental conditions of this station. The highest measure of species richness (R) was found in the station I and presumably related to the life cycle of freshwater shrimps and prawns which is amphidromous. The occurrence of nine species of freshwater shrimps and prawns along the Batusuya river indicated the environmental condition of the stream was suitable for most freshwater shrimps and prawns, and the Macrobrachium australe was found as the most abundant species.
    [Show full text]
  • The Water Beetles of Miller Blue Hole, Sandusky County, Ohio (Insecta: Coleoptera)1-2
    THE WATER BEETLES OF MILLER BLUE HOLE, SANDUSKY COUNTY, OHIO (INSECTA: COLEOPTERA)1-2 BRIAN E. MELIN AND ROBERT C. GRAVES Department of Biology, Bowling Green State University, Bowling Green, Ohio 43408 ABSTRACT Thirty-one species of aquatic beetles, representing the families Dytiscidae, Hydro- philidae, Haliplidae, and Gyrinidae, were collected in the Miller Blue Hole, a large spring, between October 21, 1967, and January 27, 1969. The numbers of each species collected are tabulated by monthly intervals. Some of the species present in this unusual habitat are rare; Tropisternus columbianus is apparently recorded from Ohio for the first time. INTRODUCTION The Ohio "blue holes" are the outlets of an extensive underground drainage system occurring in limestone bedrock. They may best be thought of as gigantic springs reaching the surface as deep, conical pools or ponds which are drained by streams flowing into Lake Erie. There are several "blue holes" located in San- dusky and Erie counties, the best known being the Castalia Blue Hole, which has been "developed" as a commercial tourist attraction, with the result that its original natural environment has been destroyed. Closely adjacent to this one is the biggest of the "blue holes," the large spring-fed lake in the center of the town of Castalia. The Miller Blue Hole, six miles to the west of this town, is nearly two acres in size, and has been preserved by the state since 1932 in a relatively natural condi- tion. It is located in a 13-acre wooded tract surrounded by agricultural lands. Earlier works dealing with Miller Blue Hole have only briefly mentioned water beetles.
    [Show full text]
  • De Grave & Fransen. Carideorum Catalogus
    De Grave & Fransen. Carideorum catalogus (Crustacea: Decapoda). Zool. Med. Leiden 85 (2011) 407 Fig. 48. Synalpheus hemphilli Coutière, 1909. Photo by Arthur Anker. Synalpheus iphinoe De Man, 1909a = Synalpheus Iphinoë De Man, 1909a: 116. [8°23'.5S 119°4'.6E, Sapeh-strait, 70 m; Madura-bay and other localities in the southern part of Molo-strait, 54-90 m; Banda-anchorage, 9-36 m; Rumah-ku- da-bay, Roma-island, 36 m] Synalpheus iocasta De Man, 1909a = Synalpheus Iocasta De Man, 1909a: 119. [Makassar and surroundings, up to 32 m; 0°58'.5N 122°42'.5E, west of Kwadang-bay-entrance, 72 m; Anchorage north of Salomakiëe (Damar) is- land, 45 m; 1°42'.5S 130°47'.5E, 32 m; 4°20'S 122°58'E, between islands of Wowoni and Buton, northern entrance of Buton-strait, 75-94 m; Banda-anchorage, 9-36 m; Anchorage off Pulu Jedan, east coast of Aru-islands (Pearl-banks), 13 m; 5°28'.2S 134°53'.9E, 57 m; 8°25'.2S 127°18'.4E, an- chorage between Nusa Besi and the N.E. point of Timor, 27-54 m; 8°39'.1 127°4'.4E, anchorage south coast of Timor, 34 m; Mid-channel in Solor-strait off Kampong Menanga, 113 m; 8°30'S 119°7'.5E, 73 m] Synalpheus irie MacDonald, Hultgren & Duffy, 2009: 25; Figs 11-16; Plate 3C-D. [fore-reef (near M1 chan- nel marker), 18°28.083'N 77°23.289'W, from canals of Auletta cf. sycinularia] Synalpheus jedanensis De Man, 1909a: 117. [Anchorage off Pulu Jedan, east coast of Aru-islands (Pearl- banks), 13 m] Synalpheus kensleyi (Ríos & Duffy, 2007) = Zuzalpheus kensleyi Ríos & Duffy, 2007: 41; Figs 18-22; Plate 3.
    [Show full text]
  • Bulletin of the United States Fish Commission Seattlenwf
    WATER BEETLES IN RELATION TO PONDFISH CULTURE, WITH LIFE HISTORIES OF THOSE FOUND. IN FISHPONDS AT FAIRPORT, IOWA. By CHARLES BRANCH WILSON, Ph. D. State Normal School, Department ofScience, WesVield, Mass. Contribution from the U. S. Fisheries Biological Station, Fairport, Iowa• .:I­ CONTENTS. Page. Page. Introduction . 232 Enemies of adults . 247 Importance of water beetles . 232 Turtles . 247 Ignorance of Americanspecies . 232 Birds '" .......•. 247 Lakes versus fishponds...........•.... 233 Toads and frogs ". 248 Methods..•.......................... 233 Electric lights . 248 Ecology .. 235 Beetlesas fish eaters . 249 Modifications of structure and vestiture. 235 Fish as beetle eaters .. 252 Locomotion .. 235 Evidence from fish bait.......•....... 252 Migration from one pond to another . 237 Evidence from fish stomachs•.......... 253 Distribution according to size . 238 General summary and suggestions . 260 . Structural adaptations :. 238 Beetledistributionin Fairportfishponds . 263 For locomotion . 238 Source of material.. 264 Forrespiration . 239 Influence of environment . 264 For flotation . 241 Restriction ofBpecies . 266 For sex functions '" ." . 242 Relative importance of species . 267 For sight . 242 Systematicdescription of Fairportspecies . 267 Enemies of larvse " . 242 Key for identification of larvre . 268 The larva . 242 Key foridentification of pupse . 269 Time of pupation . 243 Peltodytes __ . 271 Dragonfly nymphs . 243 P. edentulus . 271 Mites . 244 Haliplus . 273 Hydra . 244 H. ruficollis . 274 Ants . 244 Coptotomus . 275 Turtles . 244 C. interrogatus . 275 Frogs . 244 Cybister . 277 Snails . 245 C. fimbriolatus. : , 277 Parasites . 245 Dytiscus '" . 282 Enemies of pupre . 245 D. verticalis ; . 282 Water . 245 Hydroporus ,. 285 Imperfect pupation . 246 H. niger ,. 285 Parasites . 246 Laccophilus . 286 The black horsefly . 246 L. maculosus .. 286 Ants . 247 L. proximus.........•............ 290 231 232 BULLETIN OF THE BUREAU OF FISHERIES.
    [Show full text]
  • Risk Assessment of Pet-Traded Decapod Crustaceans in Hungary with Evidence of Cherax Quadricarinatus (Von Martens, 1868) in the Wild
    NORTH-WESTERN JOURNAL OF ZOOLOGY 15 (1): 42-47 ©NWJZ, Oradea, Romania, 2019 Article No.: e171303 http://biozoojournals.ro/nwjz/index.html Risk assessment of pet-traded decapod crustaceans in Hungary with evidence of Cherax quadricarinatus (von Martens, 1868) in the wild András WEIPERTH1*, Blanka GÁL1,2, Pavlína KUŘÍKOVÁ3, Iva LANGROVÁ3, Antonín KOUBA4 and Jiří PATOKA3 1. Centre for Ecological Research, Hungarian Academy of Sciences, Danube Research Institute, Karolin út 29, H-1113 Budapest, Hungary. 2. Doctoral School of Environmental Sciences, Eötvös Loránd University, Pázmány Péter sétány 1/C, H-1117 Budapest, Hungary. 3. Czech University of Life Sciences Prague, Faculty of Agrobiology, Food and Natural Resources, Department of Zoology and Fisheries, Kamýcká 129, CZ-16500 Prague-Suchdol, Czech Republic. 4. University of South Bohemia in České Budějovice, Faculty of Fisheries and Protection of Waters, South Bohemian Research Center of Aquaculture and Biodiversity of Hydrocenoses, Zátiší 728/II, CZ-38925 Vodňany, Czech Republic. *Corresponding author, A. Weiperth, E-mail: [email protected] Received: 16. April 2017 / Accepted: 14. September 2017 / Available online: 23. September 2017 / Printed: June 2019 Abstract. The pet trade is one of the most important sources of introduction of freshwater non-native decapod crustaceans. Precise and timely identification of potentially hazardous species is necessary for the effective prevention of new introductions. Here, we present a list of species of ornamental freshwater decapod crustaceans pet-traded in Hungary and their risk assessment, including the probability of establishment based on climate matching. The list contains 13 shrimps, eight crayfish, two crabs, and one hermit crab. Three crayfish, Cherax destructor, Procambarus clarkii, P.
    [Show full text]
  • Functional Diversity of Non‐Lethal
    Ecology, 97(12), 2016, pp. 3517–3529 © 2016 by the Ecological Society of America Functional diversity of non- lethal effects, chemical camouflage, and variation in fish avoidance in colonizing beetles 1 WILLIAM J. RESETARITS JR. AND MATTHEW R. PINTAR Department of Biology, The University of Mississippi, Oxford, Mississippi 38677 USA Abstract. Predators play an extremely important role in natural communities. In freshwater systems, fish can dominate sorting both at the colonization and post- colonization stage. Specifically, for many colonizing species, fish can have non- lethal, direct effects that exceed the lethal direct effects of predation. Functionally diverse fish species with a range of predatory capabilities have previously been observed to elicit functionally equivalent responses on oviposition in tree frogs. We tested this hypothesis of functional equivalence of non- lethal effects for four predatory fish species, using naturally colonizing populations of aquatic beetles. Among taxa other than mosquitoes, and with the exception of the chemically camouflaged pirate perch, Aphredoderus sayanus, we provide the first evidence of variation in colonization or oviposition responses to different fish species. Focusing on total abundance,Fundulus chrysotus, a gape- limited, surface- feeding fish, elicited unique responses among colonizing Hydrophilidae, with the exception of the smallest and most abundant taxa, Paracymus, while Dytiscidae responded similarly to all avoided fish. Neither family responded toA. sayanus. Analysis of species richness and multivariate characterization of the beetle assemblages for the four fish species and controls revealed additional variation among the three avoided species and confirmed that chemical camouflage inA. sayanus results in assemblages essentially identical to fishless controls. The origin of this variation in beetle responses to different fish is unknown, but may involve variation in cue sensitivity, different behavioral algorithms, or differential responses to species-specific fish cues.
    [Show full text]
  • A Checklist of the Aquatic Invertebrates of the Delaware River Basin, 1990-2000
    A Checklist of the Aquatic Invertebrates of the Delaware River Basin, 1990-2000 By Michael D. Bilger, Karen Riva-Murray, and Gretchen L. Wall Data Series 116 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior Gale A. Norton, Secretary U.S. Geological Survey Charles G. Groat, Director U.S. Geological Survey, Reston, Virginia: 2005 For sale by U.S. Geological Survey, Information Services Box 25286, Denver Federal Center Denver, CO 80225 For more information about the USGS and its products: Telephone: 1-888-ASK-USGS World Wide Web: http://www.usgs.gov/ Any use of trade, product, or firm names in this publication is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this report is in the public domain, permission must be secured from the individual copyright owners to repro- duce any copyrighted materials contained within this report. Suggested citation: Bilger, M.D., Riva-Murray, Karen, and Wall, G.L., 2005, A checklist of the aquatic invertebrates of the Delaware River Basin, 1990-2000: U.S. Geological Survey Data Series 116, 29 p. iii FOREWORD The U.S. Geological Survey (USGS) is committed to providing the Nation with accurate and timely sci- entific information that helps enhance and protect the overall quality of life and that facilitates effec- tive management of water, biological, energy, and mineral resources (http://www.usgs.gov/). Informa- tion on the quality of the Nation’s water resources is critical to assuring the long-term availability of water that is safe for drinking and recreation and suitable for industry, irrigation, and habitat for fish and wildlife.
    [Show full text]
  • Habitat Preferences and Distribution of The
    HJB21_proof ■ 17 May 2016 ■ 1/6 HAYATI Journal of Biosciences xxx (2016) 1e6 55 HOSTED BY Contents lists available at ScienceDirect 56 57 HAYATI Journal of Biosciences 58 59 journal homepage: http://www.journals.elsevier.com/ 60 hayati-journal-of-biosciences 61 62 63 Original research 64 65 1 Habitat Preferences and Distribution of the Freshwater Shrimps of the 66 2 67 3 Genus Caridina (Crustacea: Decapoda: Atyidae) in Lake Lindu, 68 4 69 Q8 Sulawesi, Indonesia 5 70 6 1* 2 3 3 3 71 7 Q7 Annawaty, Daisy Wowor, Achmad Farajallah, Dede Setiadi, Bambang Suryobroto 72 8 Q1 1 Department of Biology, Faculty of Mathematics and Sciences Tadulako University, Palu, Indonesia. 73 9 2 Division of Zoology, Research Center for Biology, Indonesian Institute of Sciences (LIPI), Cibinong, Indonesia. 74 3 10 Department of Biology, Bogor Agricultural University, Bogor, Indonesia. 75 11 76 12 77 article info abstract 13 78 14 79 Article history: 15 Q2 The objectives of this study were to reveal ecological preferences and distribution of all species of 80 Received 3 November 2015 Caridina found in Lake Lindu and their catchment area. Specimens from 39 sampling sites were caught 16 81 Received in revised form using tray net and hand net. There are three species of Caridina found in the lake system, i.e. Caridina 17 13 April 2016 82 linduensis (Roux 1904); Caridina kaili (Annawaty & Wowor 2015) and Caridina dali (Annawaty & Wowor 18 Accepted 25 April 2016 2015). There is no overlapping distribution among the species. C. kaili is a true riverine species and it is 83 19 Available online xxx never encountered sympatric with C.
    [Show full text]
  • Methods for Collecting Macroinvertebrate Samples For
    Page Intentionally Left Blank Methods for Collecting Macroinvertebrate Samples As Required For TMDL Alternative Studies and/or Watershed-based Plans Effective Date: September 30, 2015 Page 2 of 122 Document Revision History Date of Revision Page(s) Revised Revision Explanation September 2015 All Methods for Collecting Macroinvertebrate Samples As Required For TMDL Alternative Studies and/or Watershed- based Plans; original document; extracted in part from “Methods for Conducting Resource Extraction Individual Permit Intensive Surveys in Non-OSRW Streams of the Eastern Kentucky Coalfields, June 2014, Revision 2” Suggested Citation: Kentucky Division of Water (KDOW). 2015. Methods for Collecting Macroinvertebrate Samples As Required For TMDL Alternative Studies and/or Watershed-based Plans. Department for Environmental Protection. Division of Water, Frankfort, Kentucky. Methods for Collecting Macroinvertebrate Samples As Required For TMDL Alternative Studies and/or Watershed-based Plans Effective Date: September 30, 2015 Page 3 of 122 Table of Contents 1. Scope and Applicability .................................................................................................. 6 2. Definitions....................................................................................................................... 6 3. Personnel Qualifications ................................................................................................. 7 4. Equipment and Supplies ................................................................................................
    [Show full text]
  • Habitat Preferences and Distribution of the Freshwater Shrimps of the Genus Caridina (Crustacea: Decapoda: Atyidae) in Lake Lindu, Sulawesi, Indonesia
    HAYATI Journal of Biosciences 23 (2016) 45e50 HOSTED BY Contents lists available at ScienceDirect HAYATI Journal of Biosciences journal homepage: http://www.journals.elsevier.com/ hayati-journal-of-biosciences Original research article Habitat Preferences and Distribution of the Freshwater Shrimps of the Genus Caridina (Crustacea: Decapoda: Atyidae) in Lake Lindu, Sulawesi, Indonesia * Annawaty Annawaty,1 Daisy Wowor,2 Achmad Farajallah,3 Dede Setiadi,3 Bambang Suryobroto3 1 Department of Biology, Faculty of Mathematics and Sciences Tadulako University, Palu, Indonesia. 2 Division of Zoology, Research Center for Biology, Indonesian Institute of Sciences (LIPI), Cibinong, Indonesia. 3 Department of Biology, Bogor Agricultural University, Bogor, Indonesia. article info abstract Article history: The objectives of this study were to reveal ecological preferences and distribution of all species of Caridina Received 3 November 2015 found in Lake Lindu and their catchment area. Specimens from 39 sampling sites were caught using tray Received in revised form net and hand net. There are three species of Caridina found in the lake system, i.e. Caridina linduensis, 13 April 2016 Caridina kaili and Caridina dali. There is no overlapping distribution among the species. Caridina kaili is a Accepted 25 April 2016 true riverine species and it is never encountered sympatric with C. dali nor C. linduensis. This species is Available online 17 May 2016 abundant in streams and ditches with moderate flow running water and gravelecobble substrate. It is mainly spread within streams west to the lake. Both C. dali and C. linduensis can be found in the lake and KEYWORDS: Caridina, streams with very slow current to almost stagnant water, muddy sand substrate and associated with roots distribution, of water plants and leaf litter.
    [Show full text]