01443nas a2200205 4500008004100000245035500041210010800396260011300504653001300617653001200630653001200642653001100654653001900665653002700684653002500711100002800736700002600764700005100790856039600841 1994 eng d00aΑΥΞΗΣΗ ΤΗΣ F6 ΚΑΙ F7 ΓΕΝΙΑΣ ΤΟΥ H. ASPERSA (ΝΑΥΠΑΚΤΟΥ) ΚΑΙ ΚΑΤΑΝΑΛΩΣΗ ΚΑΙ ΑΦΟΜΟΙΩΣΗ ΑΠΟΞΗΡΑΜΕΝΗΣ ΤΡΟΦΗΣ ΑΠΟ ΤΗΝ ΕΚΚΟΛΑΨΗ ΕΩΣ ΚΑΙ ΤΗΝ ΩΡΙΜΑΝΣΗ ΤΟΥ H. LUCORUM ΚΑΤΩ ΑΠΟ ΕΛΕΓΧΟΜΕΝΕΣ ΣΥΝΘΗΚΕΣ ΕΚΤΡΟΦΗΣ0 aΑΥΞΗΣΗ ΤΗΣ F6 ΚΑΙ F7 ΓΕΝΙΑΣ ΤΟΥ iH ASPERSAi ΝΑΥΠΑΚΤΟΥ ΚΑΙ ΚΑΤΑΝΑ aΒΟΛΟΣbΕΛΛΗΝΙΚΗ ΕΤΑΙΡΕΙΑ ΒΙΟΛΟΓΙΚΩΝ ΕΠΙΣΤΗΜΩΝc5 - 7 ΜΑΙΟΥ 199410abreeding10aculture10afarming10asnails10aεκτροφή10aκαλλιέργεια10aσαλιγκάρια1 aΚΥΦΩΝΙΔΗΣ, Ν.1 aΠΑΠΑΔΑΚΗ, Χ.1 aΛΑΖΑΡΙΔΟΥ-ΔΗΜΗΤΡΙΑΔΟΥ, Μ. uhttps://icgf.myspecies.info/content/%CE%B1%CF%85%CE%BE%CE%B7%CF%83%CE%B7-%CF%84%CE%B7%CF%83-f6-%CE%BA%CE%B1%CE%B9-f7-%CE%B3%CE%B5%CE%BD%CE%B9%CE%B1%CF%83-%CF%84%CE%BF%CF%85-h-aspersa-%CE%BD%CE%B1%CF%85%CF%80%CE%B1%CE%BA%CF%84%CE%BF%CF%85-%CE%BA%CE%B1%CE%B9-%CE%BA%CE%B1%CF%84%CE%B1%CE%BD%CE%B1%CE%BB%CF%89%CF%83%CE%B7-%CE%BA%CE%B1%CE%B9-%CE%B1%CF%86%CE%BF%CE%BC%CE%BF%CE%B9%CF%89%CF%83%CE%B701284nas a2200229 4500008004100000245009500041210006900136260001200205300001200217490000700229520056500236653001200801653001600813653001200829653001100841653001700852653001300869100002000882700001600902700002200918856011400940 1998 eng d00aBursaphelenchus hellenicus sp. n. (Nematoda, Aphelenchoididae) from Greek pine wood0 aiBursaphelenchus hellenicus isp n Nematoda Aphelenchoididae from c1998/// a623-6290 v443 aBursaphelenchus hellenicus sp. n. was found in the wood of a dying Pinus brutia tree in Thessaloniki, Greece, together with B. leoni, in 1996. The tree was affected by Blastophagus piniperda and blue stain of wood. B. hellenicus sp. n. is characterised by an a-value of 30 (22-38), styler length of 15 (13-17) ìm, distinct constriction of the lip region, spicules of males with blunt prominent rostrum, narrow high condylus and cucullus, females with slightly extended anterior vulval lip, medium long postuterine branch and conoid tail with rounded terminus.10aculture10aDescription10aGermany10aGreece10aPinus brutia10ataxonomy1 aSkarmoutsos, G.1 aBraasch, H.1 aMichalopoulou, H. uhttps://icgf.myspecies.info/content/bursaphelenchus-hellenicus-sp-n-nematoda-aphelenchoididae-greek-pine-wood02427nas a2200337 4500008004500000020001400045245015200059210006900211260000800280300001200288490000700300520132800307653001601635653002201651653001201673653002301685653002201708653002601730653000901756653002301765653003101788653001601819653001101835653001101846100001801857700001701875700002401892700002001916700002301936856013001959 2007 Engldsh a1355-557X00aPossible influence of reared gilthead sea bream (Sparus aurata L.) on wild stocks in the area of the Messolonghi lagoon (Ionian Sea, Greece)0 aPossible influence of reared gilthead sea bream iSparus auratai cMar a398-4080 v383 aMore than 25% of Greek fish farms and 20% of Greek hatcheries of gilthead sea bream (Sparus aurata) and sea bass (Dicentrarchus labrax) are located along the Western Hellenic coast. The part of sea bream production is about 60% of the total production of these species. During the last decade, a spectacular increase in both the number of farms and their production, accompanied by a substantial price decrease and modification of their structure and functioning, has been recorded. These changes resulted in the maintenance in cages of large individuals (more than 500 g) of gilthead sea bream which are potential spawners. The study, based on both the maturity stage and the decrease in individual mean weights during the reproductive period of the species, confirmed reproduction in cages. In parallel, during the last 5 years a remarkable increase (about 80%) in sea bream landings from the fish trap fisheries of the Messolonghi-Etoliko lagoon, which is a typical nursery for the species, was recorded. The increase was accompanied by a decrease both in price and mean size of the O-group individuals. The possible influence of the rearing activities in the area, the density-dependent mechanisms and the negative impacts of this unintentional enhancement of the traditional lagoon fisheries of the area are discussed.10aaquaculture10acarrying capacity10aculture10adensity dependence10aecological impact10aEnvironmental impacts10afish10agilthead sea bream10aMessolonghi-Etoliko lagoon10apopulations10asalmon10atrends1 aDimitriou, E.1 aKatselis, G.1 aMoutopoulos, D., K.1 aAkovitiotis, C.1 aKoutsikopoulos, C. uhttps://icgf.myspecies.info/content/possible-influence-reared-gilthead-sea-bream-sparus-aurata-l-wild-stocks-area-messolonghi03845nas a2200565 4500008004500000020001400045245016600059210006900225260000800294300001200302490000800314520226000322653001302582653002302595653001002618653002202628653002002650653002602670653001202696653002302708653002502731653001102756653002002767653001102787653001802798653002302816653002402839653001802863653002202881653001302903653001102916653002302927653003102950100001402981700002202995700001403017700001403031700001503045700002203060700001403082700001903096700001503115700002003130700002103150700001603171700001703187700001903204700001403223856004203237 2009 Engldsh a0044-848600aAssessing the suitability of a range of benthic indices in the evaluation of environmental impact of fin and shellfish aquaculture located in sites across Europe0 aAssessing the suitability of a range of benthic indices in the e cAug a231-2400 v2933 aThe European Union-funded ECASA project (Ecosystem Approach for Sustainable Aquaculture) studied the impacts from aquaculture on ecosystems from northern Norway to Greece. The objectives of this investigation were to identify quantitative indicators of the effects of aquaculture on marine communities. and to assess their applicability over a range of ecosystems and aquaculture production systems. The study included 6 Mediterranean and 4 Atlantic sites, 7 of which produced finfish (seabream, seabass, tuna, salmon and cod), and 2 bivalve molluscs (oysters, mussels, and clams); one site produced both fish and bivalves. Cultivation methods included finfish cages, long-lines and trestles. Similar sampling methodologies were employed at the 10 study sites, obtaining sediment, hydrodynamic, and benthic faunal data. The horizontal impact from organic enrichment extended 50 m from the farms, with contradictory responses in several indicators (individual abundance, biomass) and a more consistent response of the Infaunal Trophic Index (ITI) and AZTI's Marine Biotic Index (AMBI). By means of Partial Redundancy Analysis, it was demonstrated that the environmental variables explained 53.2% of the variability in the macrofaunal variables (individual abundance, species richness. diversity, AMBI and ITI), whilst the explained variance was partialled out within three groups of variables: (i) 'hydrography' (depth, distance to farm, average current speed), which explained 11.5% of the variance; (ii)'sediment'(Eh and percentages of silt and total organic matter), which explained 5.4%: and (iii) 'cages' (years of production and annual production), which explained 15.2%. The shared variance explained by interactions among these groups was 21.1%. These results, together with multiple regression analysis, provide an accurate assessment of the degree of impact from aquaculture. In conclusion, the use of several benthic indicators, in assessing farm impacts, together with the investigation of dynamics of the studied location, water depth, years of farm activity, and total annual production, must be included when interpreting the response of benthic communities to organic enrichment from aquaculture. (C) 2009 Elsevier B.V. All rights reserved.10aAtlantic10aBenthic indicators10acages10aCARRYING-CAPACITY10aCOASTAL SYSTEMS10aCOMMUNITY COMPOSITION10aculture10aEcological quality10aEnvironmental impact10aEurope10aFISH FARM WASTE10afishes10aHydrodynamics10aMarine aquaculture10amarine biotic index10aMediterranean10aMEDITERRANEAN SEA10aMolluscs10amussel10aORGANIC ENRICHMENT10aPOSIDONIA-OCEANICA MEADOWS1 aBorja, A.1 aRodriguez, J., G.1 aBlack, K.1 aBodoy, A.1 aEmblow, C.1 aFernandes, T., F.1 aForte, J.1 aKarakassis, I.1 aMuxika, I.1 aNickell, T., D.1 aPApageorgiou, N.1 aPranovi, F.1 aSevastou, K.1 aTomassetti, P.1 aAngel, D. uhttps://icgf.myspecies.info/node/381202375nas a2200361 4500008004500000020001400045245007300059210006800132260000800200300001200208490000700220520148500227653001701712653001701729653001201746653001401758653001201772653000901784653001101793653001201804653001601816653001001832653001501842653001001857653001601867653001301883653001301896653001301909100001301922700001801935700001801953856004201971 2007 Engldsh a0960-311500aThe political culture of poaching: a case study from northern Greece0 apolitical culture of poaching a case study from northern Greece cFeb a399-4180 v163 aPoaching has deep social and cultural roots and its meanings are multi-layered. This article explores the meanings attached to the practice of illegal hunting and fishing around Lake Kerkini in northern Greece. Here poaching must be considered in the context of a disordered ecosystem, where the dominance of locally maligned fish and bird species results from economic and environmental policy designed to benefit distant farmers. We conclude that poaching cannot be understood only as an individual action, but as one where collective and personal identities are defended in the face of seemingly irrevocable economic and social decline. The discussion shows that poachers identify different kinds of poaching. Some of the most apparent forms of poaching, done by local inhabitants, may be less damaging than other commercially oriented forms, including by outsiders. Poaching is motivated through a complex mix of factors. Our data lead us to discuss two manifestations of poaching (a) poaching as a form of collective resistance; and (b) poaching as a violation of culturally valued types of human-nature interaction. Some people who admit undertaking what they perceive as least detrimental forms of poaching are antagonistic towards what they construe to be truly harmful forms. Such people appear willing to act and to support actions against types of poaching they agree to be threatening. This is a message with potential importance for environmental management strategy.10abiodiversity10aconservation10aculture10afisheries10afishing10agame10aGreece10ahunting10alivelihoods10alocal10amanagement10amodel10aMOTIVATIONS10apoaching10awetlands10awildlife1 aBell, S.1 aHampshire, K.1 aTopalidou, S. uhttps://icgf.myspecies.info/node/345401014nas a2200277 4500008004100000245007300041210006900114260011200183653001900295653003300314653002500347653001600372653001200388653001100400653001800411653001500429653001700444653001900461653002700480653002300507653003700530100003400567700001400601700002200615856009900637 2006 eng d00aEXPERIMENTAL REARING OF SEA URCHIN IN GREECE: AN INNOVATIVE APPROACH0 aEXPERIMENTAL REARING OF SEA URCHIN IN GREECE AN INNOVATIVE APPRO aΘεσσαλονίκηbΕλληνικό Κέντρο Θαλασσίων Ερευνώνc4-8 ΙΟΥΝΙΟΥ10alividus10aParacentrotus lividus10aParacentrotus10aaquaculture10aculture10alarval10ametamorphosis10asea urchin10aαχινός10aεκτροφή10aμεταμόρφωση10aπρονυμφών10aυδατοκαλλιέργεια1 aPancucci-Papadopoulou, M., A.1 aKolios, P1 aTheodoropoulos, D uhttps://icgf.myspecies.info/content/experimental-rearing-sea-urchin-greece-innovative-approach01712nas a2200325 4500008004100000245023500041210012700276260009200403653001000495653001600505653001200521653001300533653001200546653000900558653001600567653001400583653002000597653001100617653002100628653001700649653002100666653002300687653002700710653002400737653001900761653003700780653001300817100001900830856053700849 2000 eng d00aΕκτίμηση ένος Εντατικού Συστήματος Καλλιέργειας Βενθικών Κωπηπόδων και το Αποτέλεσμα Χρήσης Φυτοπλαγκτού στη Διατροφή τους0 aΕκτίμηση ένος Εντατικού Συστήματος Καλλιέργειας Βενθικών Κωπηπόδ aΧίοςbΕθνικό Κέντρο Θαλασσίων Ερευνώνc23-26 Μαΐου10aalgae10aaquaculture10abenthic10aCopepoda10aculture10adiet10afatty acids10aintensive10aKωπήποδα10alipids10aβενθικός10aβένθος10aδιατροφή10aεντατικός10aκαλλιέργεια10aλιπαρό οξύ10aλιπίδιο10aυδατοκαλλιέργεια10aφύκη1 aΚολής, Α uhttps://icgf.myspecies.info/content/%CE%B5%CE%BA%CF%84%CE%AF%CE%BC%CE%B7%CF%83%CE%B7-%CE%AD%CE%BD%CE%BF%CF%82-%CE%B5%CE%BD%CF%84%CE%B1%CF%84%CE%B9%CE%BA%CE%BF%CF%8D-%CF%83%CF%85%CF%83%CF%84%CE%AE%CE%BC%CE%B1%CF%84%CE%BF%CF%82-%CE%BA%CE%B1%CE%BB%CE%BB%CE%B9%CE%AD%CF%81%CE%B3%CE%B5%CE%B9%CE%B1%CF%82-%CE%B2%CE%B5%CE%BD%CE%B8%CE%B9%CE%BA%CF%8E%CE%BD-%CE%BA%CF%89%CF%80%CE%B7%CF%80%CF%8C%CE%B4%CF%89%CE%BD-%CE%BA%CE%B1%CE%B9-%CF%84%CE%BF-%CE%B1%CF%80%CE%BF%CF%84%CE%AD%CE%BB%CE%B5%CF%83%CE%BC%CE%B1-%CF%87%CF%81%CE%AE%CF%83%CE%B7%CF%8201424nas a2200277 4500008004100000245019800041210010200239260007100341653001600412653001500428653002600443653001200469653000900481653001500490653001500505653001200520653001300532653001300545653003700558653002700595653002100622653002100643653003700664100002500701856042000726 1986 eng d00aΔιατροφική Αξία των Rotiferes Br. plicatilis Προβλήματα στην Παραγωγή. Προτεινόμενες Λύσεις για τη Βελτίωση της.0 aΔιατροφική Αξία των Rotiferes iBr plicatilisi Προβλήματα στην Πα aΞενοδοχείο Χανδρής, Αθήνα.c23-25 Μαΐου10aaquaculture10aBrachionus10aBrachionus plicatilis10aculture10afish10aplicatilis10aproduction10arotifer10aRotifera10arotifers10aΙχθυοκαλλιέργεια10aκαλλιέργεια10aπαραγωγή10aτροχόζωα10aυδατοκαλλιέργεια1 aΠετσάλης, Γ uhttps://icgf.myspecies.info/content/%CE%B4%CE%B9%CE%B1%CF%84%CF%81%CE%BF%CF%86%CE%B9%CE%BA%CE%AE-%CE%B1%CE%BE%CE%AF%CE%B1-%CF%84%CF%89%CE%BD-rotiferes-br-plicatilis-%CF%80%CF%81%CE%BF%CE%B2%CE%BB%CE%AE%CE%BC%CE%B1%CF%84%CE%B1-%CF%83%CF%84%CE%B7%CE%BD-%CF%80%CE%B1%CF%81%CE%B1%CE%B3%CF%89%CE%B3%CE%AE-%CF%80%CF%81%CE%BF%CF%84%CE%B5%CE%B9%CE%BD%CF%8C%CE%BC%CE%B5%CE%BD%CE%B5%CF%82-%CE%BB%CF%8D%CF%83%CE%B5%CE%B9%CF%8201619nas a2200349 4500008004100000245022800041210010400269260007100373653001600444653000800460653001200468653001800480653002500498653001300523653002100536653001100557653001200568653002500580653002700605653001700632653001700649653001700666653001900683653001900702653003600721653003700757100002100794700002100815700002700836700002300863856038300886 1986 eng d00aΗ Καλλιέργεια Λαυρακιού (Dicentrarchus labrax) σε Κλωβούς στον Όρμο "Γαλήνη" του Νομού Θεσπρωτίας; Συγκριτικά Αποτελέσματα 1984-19860 aΗ Καλλιέργεια Λαυρακιού iDicentrarchus labraxi σε Κλωβούς στον Ό aΞενοδοχείο Χανδρής, Αθήνα.c23-25 Μαΐου10aaquaculture10abay10aculture10adicentrarchus10aDicentrarchus labrax10aeuropean10aeuropean seabass10alabrax10aseabass10aΘεσπρωτίας10aκαλλιέργεια10aκλωβοί10aκλωβός10aκόλπος10aλαβράκι10aλαυράκι10aΝομός Θεσπρωτίας10aυδατοκαλλιέργεια1 aΔρούκα, Ε1 aΚουφός, Σ1 aΦιλιόγλου, Μ1 aΘεοχάρη, Β uhttps://icgf.myspecies.info/content/%CE%B7-%CE%BA%CE%B1%CE%BB%CE%BB%CE%B9%CE%AD%CF%81%CE%B3%CE%B5%CE%B9%CE%B1-%CE%BB%CE%B1%CF%85%CF%81%CE%B1%CE%BA%CE%B9%CE%BF%CF%8D-dicentrarchus-labrax-%CF%83%CE%B5-%CE%BA%CE%BB%CF%89%CE%B2%CE%BF%CF%8D%CF%82-%CF%83%CF%84%CE%BF%CE%BD-%CF%8C%CF%81%CE%BC%CE%BF-%CE%B3%CE%B1%CE%BB%CE%AE%CE%BD%CE%B7-%CF%84%CE%BF%CF%85-%CE%BD%CE%BF%CE%BC%CE%BF%CF%8D