, hobbie flahhbie o rii6enn flenbcfcwhob pe3yxibtateintranet.vef.hr/dolphins/radovi/odessa...

5
CnHcoK Hcnojib30BaHHbix hctohhhkob / References Kennedy S., Kuiken T., Jepson P.D., Deaville R., Forsyth M., Barrett T., van de Bildt M.W., Osterhaus A.D., Eybatov T., Duck C, Kydyrmanov A., Mitrofanov I., Wilson S., 2000. Mass die-off of Caspian seals caused by canine distem- per virus. Emerging Infectious Diseases 6: 637-639. Gauthier J.M., Dubeau H., Rassart E. 1998. Mercury-induced micronuclei in skin fibroblasts of beluga whales. Envi- ronmental Toxicology and Chemistry 17: 2487-2493. Graham J.A., Gardner D.E., Waters M.D., Coffin D.L. 1975. Effect of Trace metals on phagocytosis by alveolar macro- phages. Infection and Immunity 11: 1278-1283. Sengupta M., Bishayi B. 2002. Effect of lead and arsenic on murine macrophage response. Drug and Chemical Toxi- cology 25:459-472. Hughes M.F. 2002. Arsenic toxicity and potential mechanisms of action. Toxicology Letters 133: 1-16 Watson R.R., Moriguchi S., McRae B., Tobin L., Mayberry J.C., Lucas D. 1986. Effects of selenium in vitro on human T-lymphocyte functions and K562 tumor cell growth. Journal of Leukocyte Biology 39: 447-456. Soto-Pena G.A., Luna A.L., Acosta-Saavedra L., Conde-Moo P., Lopez-Carrillo L., Cebrian M.E., Bastida M., Calde- ron-Aranda E.S., Vega L. 2006. Assessment of lymphocyte subpopulations and cytokine secretion in children ex- posed to arsenic. FASEB J.: 05-4860fje. TajiOB A., ToMepHHH M.J\., ToMepHHq T., JIIOCHH X., LÜKpran LtypKOBHH C, ByKOBHH C, ToMepHHH X. HoBbie flaHHbie o r i i 6 e n n flenbcfcwHOB B pe3yxibTaTe CTpam-y- n^MMM ropTaHH B >Ka6epHbix cerax YHHBepcHTeT 3arpe6a, 3arpe6, XopBaTHfl Galov A., Gomercic M.D., Gomercic T., Lucie H., Skrtic D., Curkovic S., Vukovic S., Gomercic H. Newly documented consequence of dolphin depredation: larynx stran gulation with gillnet parts University of Zagreb, Zagreb, Croatia HeOßHOKpaTHO COOÖmaJIOCb O B3aHMO #eHCTBHH #eJIb(})HHOB c opy ^HHMM jioßa CB5I3H c TeM, HTO CTpaTerHH ^ejib({)HHa - yBe- jiHHHTb cKopocTb nHTaHHH npH CHH>KeHHH 3HeprHH, 3aTpa- HHBaeMOH Ha ßoöbißaHHe nHinH. (Fertl and Leatherwood 1997). HaHÖojiee nacTbiH B3aHM0,aeHCTBH5i c opyAHflMH JiOBa - 3anyTbiBaHHe b cerax. HMeercfl Heöojibuioe KOJiHHecTBO CBH ^eTejibCTB rHÖejiM >KMBOTHbix b pe3yjibTaTe nporjiaTbiBa- hhh opy^HH jiob. HMeioTCfl /jaHHbie 3arjiaTbiBaHHe pbiöojiOB- Hbix KpiOHKOB h ÖJieceH (Gorzelany 1998). CymecTByeT, ojx- HaKo, Mano AOKyMeHTHpoBaHHbix cBH^eTejibCTB 3arjraTbiBa- hhh pbiöojiOBHoro oöopy^OBaHHH, pe3yjibTaTOM KOToporo dajia cTpaHryjiHUHH ropTaHH. B HacroameH paöoTe Mbi pac- CMaTpHBaeM cnynaH crpaHryjiflUHH ropTaHH ac })ajiHH {Tursiops truncatus) H3 xopBaTCKOH nacTH A^pHaTHKH H3-3a nona^aHHa b >Ka6epHbie cera. Acf)ajiHHa HBjiaeTCH e^HHCT- BeHHblM BHßOM MOpCKHX MJieKOnHTaiOlJUHX, nOCTOHHHO >KH- ByiiJHX B XOpBaTCKOH MaCTH A /HDHaTHKH. HHCJieHHOCTb ac|)a- jihh b xopBaTCKOH HacTH A^pnaTHHecKoro Mopa - OT 220 jxo 250 (Gomercic et al. 2002). 3 t o yrpo>KaeMbiH bha, nojino- CTbK) 3aU4HLUaeMbIH 3aKOHOM XopBaTHH. XopBaTHH HMeeT /laBHHe TpaAHUMH MejiKOMacujTaÖHoro npHÖpe>KHoro pbiöo- jiOBCTBa, 3KcnjiyaTHpyiomero npn6pe>KHbie ÖHOJiorHHecKne pecypcbi. B MejiKOMacmnraÖHOM KOMMepnecKOM h HH/jHBH^y- ajibHOM pbiöojiOBCTBe ypoßeHb 3KcnjiyaTauHH pecypcoB He- H3BecTeH, t.k. yjioB b npH6pe>KHbie CeTH He (jWKCHpyCTCfl. 0/iHaKO no oueHKaM oömee kojihhcctbo pwoojiobob- jiK)6nTejieH npHMepHO 18.000, H3 hhx TOJibKo 8.500 HMeiOT jiHueH3HH (Dulcic et al. 2003). Pbiöa, 3anyTaBuia»CH b cerH, Interactions of dolphins with fishing gear have been regularly reported and they occur because of the ceta- cean strategy to increase the rate of feeding while de- creasing the energy expenditure associated with forag- ing (Fertl and Leatherwood 1997). The most frequent- ly reported form of cetacean interactions with fishing gear involves entanglement in fishing nets. Limited records exist related to depredation resulting in fishing gear ingestion. Ingestion of fishing hook and lure were documented by Gorzelany (1998). However, there are no documented cases of fishing gear ingestion result- ing in larynx strangulation. Here we present bottlenose dolphins {Tursiops truncatus) from the Croatian part of the Adriatic Sea that have been affected with larynx strangulation with gillnet parts. The bottlenose dolphin is the only resident marine mammal species in Croa- tian part of the Adriatic Sea with the total number of individuals estimated at between 220 to 250 (Gomer- cic et al. 2002). It is endangered and legally protected species in Croatia. Croatia has a long tradition of small-scale coastal fishing, which exploits near-shore biological resources. Small-scale commercial and pri- vate fisheries use gillnets throughout the year. The level of exploitation is unknown because the catches of the coastal fishing gears are not recorded. However, the total amount of small-scale, artisanal fishers is es- timated at around 18.000, of which only 8.500 are li- censed (Dulcic et al. 2003). Fish entangled in gillnets

Upload: others

Post on 11-Oct-2020

1 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: , HoBbie flaHHbie o rii6enn flenbcfcwHOB pe3yxibTaTeintranet.vef.hr/dolphins/radovi/Odessa 2008/Galov Ukraina 2008 sazetak.pdfMass die-off of Caspian seals caused by canine distem

CnHcoK Hcnojib30BaHHbix hctohhhkob / References

Kennedy S., Kuiken T., Jepson P.D., Deaville R., Forsyth M., Barrett T., van de Bildt M.W., Osterhaus A.D., Eybatov T., Duck C , Kydyrmanov A., Mitrofanov I., Wilson S., 2000. Mass die-off of Caspian seals caused by canine distem­per virus. Emerging Infectious Diseases 6: 637-639.

Gauthier J.M., Dubeau H., Rassart E. 1998. Mercury-induced micronuclei in skin fibroblasts of beluga whales. Envi­ronmental Toxicology and Chemistry 17: 2487-2493.

Graham J.A., Gardner D.E., Waters M.D., Coffin D.L. 1975. Effect of Trace metals on phagocytosis by alveolar macro­phages. Infection and Immunity 11: 1278-1283.

Sengupta M., Bishayi B. 2002. Effect of lead and arsenic on murine macrophage response. Drug and Chemical Toxi­cology 25:459-472.

Hughes M.F. 2002. Arsenic toxicity and potential mechanisms o f action. Toxicology Letters 133: 1-16 Watson R.R., Moriguchi S., McRae B., Tobin L., Mayberry J.C., Lucas D. 1986. Effects of selenium in vitro on human

T-lymphocyte functions and K562 tumor cell growth. Journal of Leukocyte Biology 39: 447-456. Soto-Pena G.A., Luna A.L., Acosta-Saavedra L., Conde-Moo P., Lopez-Carrillo L., Cebrian M.E., Bastida M., Calde-

ron-Aranda E.S., Vega L. 2006. Assessment of lymphocyte subpopulations and cytokine secretion in children ex­posed to arsenic. FASEB J.: 05-4860fje.

TajiOB A. , ToMepHHH M.J\., ToMepHHq T., JIIOCHH X . , LÜKpran LtypKOBHH C , ByKOBHH C , ToMepHHH X .

HoBbie flaHHbie o r i i 6 e n n flenbcfcwHOB B pe3yx ibTaTe C T p a m - y -

n^MMM r o p T a H H B >Ka6epHbix c e r a x YHHBepcHTeT 3arpe6a, 3arpe6, XopBaTHfl

Galov A., Gomercic M.D., Gomercic T., Lucie H., Skrtic D., Curkovic S., Vukovic S., Gomercic H. Newly documented consequence of dolphin depredation: larynx stran gulation with gillnet parts

University of Zagreb, Zagreb, Croatia

HeOßHOKpaTHO COOÖmaJIOCb O B3aHMO#eHCTBHH #eJIb(})HHOB c opy HHMM jioßa CB5I3H c TeM, HTO CTpaTerHH ^ejib({)HHa - yBe-jiHHHTb cKopocTb nHTaHHH npH CHH>KeHHH 3HeprHH, 3aTpa-HHBaeMOH Ha ßoöbißaHHe nHinH. (Fertl a n d Leatherwood 1997). HaHÖojiee nacTbiH B3aHM0,aeHCTBH5i c opyAHflMH JiOBa - 3anyTbiBaHHe b cerax. HMeercfl Heöojibuioe KOJiHHecTBO CBH eTejibCTB rHÖejiM >KMBOTHbix b pe3yjibTaTe nporjiaTbiBa-hhh opy^HH jiob. HMeioTCfl /jaHHbie 3arjiaTbiBaHHe pbiöojiOB-Hbix KpiOHKOB h ÖJieceH (Gorzelany 1998). CymecTByeT, ojx-HaKo, Mano AOKyMeHTHpoBaHHbix cBH^eTejibCTB 3arjraTbiBa-hhh pbiöojiOBHoro oöopy^OBaHHH, pe3yjibTaTOM KOToporo dajia cTpaHryjiHUHH ropTaHH. B HacroameH p a ö o T e Mbi pac-CMaTpHBaeM cnynaH crpaHryjiflUHH ropTaHH ac})ajiHH {Tursiops truncatus) H3 xopBaTCKOH nacTH A^pHaTHKH H3-3a nona^aHHa b >Ka6epHbie cera. Acf)ajiHHa HBjiaeTCH e^HHCT-BeHHblM BHßOM MOpCKHX MJieKOnHTaiOlJUHX, nOCTOHHHO >KH-ByiiJHX B XOpBaTCKOH MaCTH A/HDHaTHKH. HHCJieHHOCTb ac|)a-jihh b xopBaTCKOH HacTH A^pnaTHHecKoro Mopa - OT 220 jxo 250 (Gomercic et al. 2002). 3 t o yrpo>KaeMbiH bha, n o j i n o -CTbK) 3aU4HLUaeMbIH 3aKOHOM XopBaTHH. XopBaTHH HMeeT /laBHHe TpaAHUMH MejiKOMacujTaÖHoro npHÖpe>KHoro pbiöo-jiOBCTBa, 3Kcnj iyaTHpyiomero npn6pe>KHbie ÖHOJiorHHecKne pecypcbi. B MejiKOMacmnraÖHOM KOMMepnecKOM h HH/jHBH^y-ajibHOM pbiöojiOBCTBe ypoßeHb 3KcnjiyaTauHH pecypcoB He-H3BecTeH, t.k. yjioB b npH6pe>KHbie CeTH He (jWKCHpyCTCfl. 0/iHaKO no oueHKaM oömee kojihhcctbo pwoojiobob-jiK)6nTejieH npHMepHO 18.000, H3 hhx TOJibKo 8.500 HMeiOT jiHueH3HH (Dulcic et al. 2003). Pbiöa, 3anyTaBuia»CH b cerH,

Interactions of dolphins with fishing gear have been regularly reported and they occur because of the ceta­cean strategy to increase the rate of feeding while de­creasing the energy expenditure associated with forag­ing (Fertl and Leatherwood 1997). The most frequent­ly reported form of cetacean interactions with fishing gear involves entanglement in fishing nets. Limited records exist related to depredation resulting in fishing gear ingestion. Ingestion of fishing hook and lure were documented by Gorzelany (1998). However, there are no documented cases of fishing gear ingestion result­ing in larynx strangulation. Here we present bottlenose dolphins {Tursiops truncatus) from the Croatian part of the Adriatic Sea that have been affected with larynx strangulation with gillnet parts. The bottlenose dolphin is the only resident marine mammal species in Croa­tian part of the Adriatic Sea with the total number of individuals estimated at between 220 to 250 (Gomer­cic et al. 2002). It is endangered and legally protected species in Croatia. Croatia has a long tradition of small-scale coastal fishing, which exploits near-shore biological resources. Small-scale commercial and pri­vate fisheries use gillnets throughout the year. The level of exploitation is unknown because the catches of the coastal fishing gears are not recorded. However, the total amount of small-scale, artisanal fishers is es­timated at around 18.000, of which only 8.500 are li­censed (Dulcic et al. 2003). Fish entangled in gillnets

Page 2: , HoBbie flaHHbie o rii6enn flenbcfcwHOB pe3yxibTaTeintranet.vef.hr/dolphins/radovi/Odessa 2008/Galov Ukraina 2008 sazetak.pdfMass die-off of Caspian seals caused by canine distem

Galov et al. Newly documented consequence of dolphin depredation: larynx strangulation with gillnet parts

npeziCTaBJiaeT COÖOH ßoöbiny B TeneHne B c e r o roixa, H HBJIX-

eTCH, B03MO>KHO, e HHCTBCHHblM HCTOHHHKOM nHTaHHfl flJIfl

>KHBOTHbIX C OrpaHHHeHHOH B03MO>KHOCTbK) OXOTHTbCfl. PaC-

nojio>KeHHe ropTaHH y 3y6aTbix KHTOB ;je.riaeT e e V5Ï3BHMOH

j\m nona^aHH« nocTopoHHHx npe^MeTOB BO BpeMH rjioTa-

HHSL Mx ropTaHb yzuiHHeHa H HMeeT TpyÔHaryio obopMy, H

/ibixaTejibHoe OTBepcTHe, KOTopoe O O M H H O Ha3biBaK)T «Ha^-

ropTaHHbiM KJiKDBOM» HJiH «rycHHbiM KJiK)BOM» (Gorzelany 1998), nepece icaeT nHmeßapHTejibHbiH TpaKT, nepexo/j f l B

HOCOByio noj iocTb, rj\e OHO ocTaeTca B BepTHKajibHOM n o j i o -

>KeHHH BO BpeMH moTaHHfl. BbijiH H3yneHbi 120 n o r n ô u i n x

a(J)ajiHH, ocTaHKH KOTopbix 6biJiH HaH^eHbi B nepHOA c 1990 r. n o cero^HHiiiHHH #eHb. B o 3 p a c T onpe^e j ia j i ca n o TOJ\W\-

HblM pOCTOBbIM CJIOflM (FPC) 3 y 6 0 B n o MeTOßHKe, OnHCaHHOH

CiiyTeHOM (Slooten 1991). y 12 ao)ajiHH H3 120 H3yneHHbix (10%) ropTaHb ôbijia c^aBJieHa >Ka6epHbiMH CCTHMH. y ÔOJIbllJHHCTBa nOCTpa^aBllIHX OÔpbIBOK pblÔOJTOBHOH ceTH

CBeilIHBaJICH H30 pTa, MTO 6bIJ10 nepBbiM npH3HaK0M CTpaH-

ryjiHUHH ropTaHH. )Ka6epHafl, ceTb Bbi3BaBuiaa CTpaHryjia-

U H K ) , ôbijia c^ejiaHa H3 njieTeHbix iiiHypoB, O Ô B H B U I H X C A B O -

Kpyr ^opcojiaTepajibHOH CTCHKH Ha^ropTaHHoro mirOBa.

ynymeHne B pe3yjibTaTe oaaBjiHBaHHfl ropTaHH, O H C B H ^ H O ,

npoHcxo/ iHT, KOTjxà ^ejib(J)HHbi nHTaiOTca pbiöoH, 3anyTaB-lueHCH B acaöepHbix ceTHx H cjiynaHHO OTpbiBaiOT nacTb ceTH.

OTopßaHHbiH obpanvieHT acaöepHOH ceTH MoaceT j inuib n a c -

T H H H O nepexo^HTb B nniueBOß BO BpeMH niOTaHHfl, OH Haxo-

ÄHTCH B rjiOTKe H poTOBOH nojiocTH H cBeuiHBaeTca H30 pTa.

HacTHHHO nporjioneHHbiH abparMeHT >Ka6epHOH ceTH Bbi3bi-

BaeT MbiiiieMHbie ^ B H ^ K C H H » , Be /rymne K peryprHTauHH. B

pe3yjibTaTe 3THX MbimeHHbix ABHHCCHHH nporjioneHHbiH

4>parMeHT ceTH nepexo/jHT H3 nnmeBO^a B moTKy . ECJIH

nporjioneHHbiH obparMeHT HanpaBJiaeTCfl B nacTb n n m e B o r o

KaHana, n p o T H B o n o n o K H y i o T O H , OTKyaa CBeuiHBaeTCfl obpar-

MeHT ceTH, OH oÔBHBaeTca BOKpyr Ha,aropTaHHoro miioBa H

B03HHKaeT cTpaHryjifliiHH. Bee >KHBOTHbie, nocTpa^aBuine OT

CTpaHryjifliiHH rjiOTaHHH, 6buiH c r a p i n e 7 jieT, H ôojibuiHHCT-

BO H3 H H X ôbijio CTapuie 17 JieT, TaK HTO nHTaHHe pbi6on H3

ceTen 6biJio ycBoeHO H M H OT ^ p y r n x npe^CTaBHTejien jx^nwo-ro BH^a. M3yHeHHbie Tpynbi / m y r n x KHToo6pa3Hbix He HMCJIH

npH3HaK0B CTpaHryji5iUHH ropTaHH. CTpaHryjiauHfl CCTHMH

Morjia 0Ka3bmaTb BJIHAHHC Ha ÄHHaMHKy HHCJICHHOCTH aoba-

JIHH B A^pnaTHKe, T.K . 10% H3yneHHbix TpynoB 6yTbiJiKOHO-COB HMejiH npH3HaKH CTpaHryjiHUHH. npeAJraraiOT pa3JiHH-

Hbie Mepbl /UTA CHH>KeHHH B3aHMO^eHCTBHH AeJIb(J)HHOB c >Ka-

6epHbiMH ceT^MH, HanpHMep, orpaHHHeHHe p w ô o j i o B H o r o

ce30Ha H panoHOB JiOBa (Murray et al . 2000), opraHH3aiJH5i oxpaHfleMbix aKBaTopHH, B KOTopbix He pa3peuiaeTC5i CTaBHTb

ceTH (Dawson a n d Slooten, 1993) H McanqbHRauHfl opyzjHH

JiOBa (Dawson, 1991). 3aKOHO£aTenbHbie Mepbi, KOTopbie

oöecneHHjiH 6w oTcyTCTBHe npocTpaHCTBeHHO-BpeMeHHoro

nepeKpbiBaHHH. KpoMe nHTaHHH ßejib<})HHOB H JiOBa pwôbi c

n o M o m b i o ^caöepHbix ceTen B BOCTOHHOH nacTH A/npnaTHKH

He 6y#yT paöoTarb , T.K. nocTpa^aBUinx .zjejib^HHOB Haxo^H-

JIH n o BceMy 6epery AapnaTHKH B JHOÖOH ce30H. KpoMe T O -

ro, 3anpemeHHe JiOBa B onpe,aejieHHbix aKBaTopnax opraHH-

3auHH oxpaHfleMbix aKBaTopHH MoryT OKa3aTb OTpnuaTejib-

Hoe B03ßeHCTBHe Ha pbiôojioBHbie c o o ö i u e c T B a (Mooney et al. 2007). B öy^ymeM HCOÖXOAHMO oöpaTHTb o c o ö o e BHHMa-HHe Ha naTOJiorHHecKHe H3MeHeHH» ropTaHH B pe3y^bTaTe

cTpaHryjiHUHH, H HX B03^eHCTBHe Ha o ô m e e COCTOHHHC 3AO-

poBbfl nocTpa^aBuiHx >KHBOTHbix. U,ejiecoo6pa3HO TaK>Ke

ö y n e T oueHHTb AajTbHewuiee B03^eHCTBHe CTpaHryjiHUHH Ha

üHHaMHKy HHCJieHHOCTH a(J)ajiHH B A/npnaTHHecKOM Mope H

present a source of concentrated prey all year round and are probably the only feeding source for animals with reduced hunting ability. The position of larynx in toothed whales makes it vulnerable to foreign bodies during deglutition. Their larynx is elongated into a tubular extension, the laryngeal spout, also commonly referred to as the "epiglottal beak" or "goose beak" (Gorzelany 1998) that transverses the digestive tract into the nasal cavity, where it remains in the erect po­sition during deglutition. 120 bottlenose dolphins found dead throughout Croatian part of the Adriatic Sea were examined from 1990 till today. Age was es­timated using annual growth layer groups (GLGs) from extracted teeth and based on modified methods described in Slooten (1991). Twelve bottlenose dol­phins out of 120 examined (10%) had larynx strangu­lated with a gillnet part. In the majority of affected animals a fishing net part was hanging from the mouth and was the first indication of larynx strangulation. The gillnet part causing larynx strangulation was in form of a weaved cord encircling the dorsolateral wall of the laryngeal spout. Larynx strangulations most probably occur when dolphins feed on entangled fish from gillnets and accidentally tear off a part of the fishing net. The torn gillnet part might only partly pass into the esophagus during the swallowing of the prey and the rest of it hangs through the pharynx and the oral cavity out of the mouth. Partially swallowed gill­net part causes muscular actions of the pharynx ad­vancing regurgitation. This muscular action brings the swallowed part of gillnet out of the esophagus and into the pharynx. If the swallowed part is directed into the opposite food channel of the food channel where the hanging part lies, it will encircle the laryngeal spout and larynx strangulation occurs. All animals affected by larynx strangulation were older than 7 years and the majority were older than 17 years, indicating that the animals acquired the feeding behavior of taking fish from gillnets from other conspecifics. The examined carcasses of other cetacean species did not show signs of larynx strangulation. Gillnet strangulations could impact the population dynamics of bottlenose dolphin population in the Adriatic Sea as much as 10% of ex­amined bottlenose dolphin carcasses were affected. There are different measures proposed to reduce dol­phin interactions with gillnets, e.g. reducing fishing seasons or regions (Murray et al. 2000), establishing marine protected areas free of gillnet fishing (Dawson and Slooten, 1993) and gear modifications (Dawson, 1991). The legislative regulation that would ensure avoiding spatio-temporal overlap of dolphin foraging and human gillnet fishing activities along the Eastern Adriatic Sea would not be feasible since the affected animals were found throughout the Croatian coast of the Adriatic Sea during all seasons. Additionally, both fishing ground closures and creation of MPAs can have deleterious social and economic effects on fish­ing-based communities (Mooney et al. 2007). Future investigations should focus on investigating pathologi­cal changes of larynxes affected by strangulation and their influence on the overall health of the individuals affected, since larynx strangulation seems to be a chronic condition. We also propose assessing further

190 Marine Mammals of the Holarctic. 2008

Page 3: , HoBbie flaHHbie o rii6enn flenbcfcwHOB pe3yxibTaTeintranet.vef.hr/dolphins/radovi/Odessa 2008/Galov Ukraina 2008 sazetak.pdfMass die-off of Caspian seals caused by canine distem

TanoB \A flp. Hoebie daHHbie o euôenu denbcpUHoe e pe3ynbmame cmpaHaynmi,uu aopmaHU e xaôepHbix cemnx

paccMOTperb Taicne KOHCTPVKLIHH ceTeH, KOTopwe ycrpaHflT

>KecTKOCTb >Ka6epHbix ceTeH. impact of larynx strangulations on the population dy­namics of bottlenose dolphin in the Adriatic Sea and considering net alterations that would improve stiff­ness properties of the gillnets.

CnHcoK Hcnojib30BaHHbix HCTOHHHKOB / R e f e r e n c e s

Dawson S. 1991. Modifying gillnets to reduce entanglement of cetaceans. Marine Mammal Science, 7: 274-282. Dawson S., Slooten E. 1993. Conservation of Hector's dolphin: the case and process which led to establishment of the

Banks Peninsula Marine Mammal Sanctuary. Aquatic Conservation: Marine and Freshwater Ecosystems, 3: 207-221. Dulcic J., Soldo A., Jardas I. 2003. Small-scale fisheries in Croatia. Adriatic Sea Small-Scale Fisheries, Report of the

AdriaMed Technical Consultation on Adriatic Sea Small-Scale Fisheries, Split, Croatia, 14th-15th October 2003. (http://www.faoadriamed.org)

Fertl D., Leatherwood S. 1997. Cetacean interactions with trawls: a preliminary review. Journal of Northwest Atlantic Fishery Science, 22: 219-248.

Gomercic H., Huber C , Mihelic D., Lucie H., Gomercic T., Curas M. 2002. Estimation of the bottlenose dolphin (Tur-siops truncatus) population in the Croatian part of the Adriatic Sea. 9th International Congress on the Zoogeography and Ecology of Greece and Adjacent Regions, Abstracts, p. 43. The Hellenic Zoological Society. Thessaloniki, 2002

Gorzelany J.F. 1998. Unusual deaths of two free-ranging Atlantic bottlenose dolphins (Tursiops truncatus) related to ingestion of recreational fishing gear. Marine Mammal Science, 14: 614-617.

Mooney T.A., Au W.W.L., Nachtigall P.E., Trippel E.A. 2007. Acoustic and stiffness properties of gillnets as they re­late to small cetacean bycatch. ICES Journal of Marine Science, 64: 1324-1332.

Murray K.T., Read A., Solow A. 2000. The use of time/area closures to reduce bycatches of harbour porpoises: lessons from the Gulf of Maine sink gillnet fishery. Journal of Cetacean Research Management, 2: 135-141.

Slooten E. 1991. Age, growth, and reproduction in Hector's dolphins. Canadian Journal of Zoology, 69: 1689-1700.

TaBpHJio M.B., TpeTbflKOB B.K).

Ha6j iK ) f leHne n o r m p H b i x k u t o b (Balaena mysticetus) b B o c t o h h o -

Cn6npcKOM M o p e b ce30H 2 0 0 7 r. c a H O M a n b H O h m 3 k o m jneAOBiiTOCTbio

ApKTHMeCKHH H AHTapKTHHeCKHH HayHHO-HCCJie#OBaTeJTbCKHH H H C T H T V T , CaHKT-HeTepÔypr, POCCHA

Gavrilo M.V., Tretiakov V.Yu.

Observation of Bowhead Whales (Balaena mysticetus) in the East-Siberian Sea during 2007 season with record-low ice cover Arctic and Antarctic Research Institute, Saint-Petersburg, Russia

CBQJXQHÌÌH O 3 a n a ^ H O M n p e ^ e n e pacnpocTpaHeHHH nojiapHbix KHTOB 6epHHr0B0-HyK0TCK0-60CJ)0pT0BCK0r0 cTa^a KpanHe CKyAHbi H, nopof ì , npoTHBopeHHBbi (Braham et al. 1984, Belikov et al. 1998, TOMHJIMH 2001). B poccHHCKHe BO/IM Boc-TOHHOH ApKTHKH JieTOM coBepuiaiOT HaryjibHbie MHrpauHH

KHTbl, 3HMVK)mHe B EepHHTOBOM MOpe. MaKCHMaJIbHOC HHCJIO

BCTpen OTMeneHO B KO Hue jieTa B paftoHe 6aHKH Tepajib^ M y o . BpaHrejiH, a TaioKe B ripH6pe>KHbix Bo^ax HyKOTCKoro n o n y -

ocTpoBa.

JieTOM 2007 r. B XORQ 3Kcne/iHUHH AAHHH «ApKTHKa-2007»

Ha HHC «Aica/jeMHK Oe^opoB» BO BpeM5ï HenpepbiBHbix BH3y-ajibHbix rHApojiorHHecKHx HaôJiioaeHHH c xo^OBoro MOCTHKa

OAHHM H3 aBTOpOB (B.TpeTbHKOBblM) ÔbIJIH 3a(J)HKCHpOBaHbI H

3acH5iTbi Ha BH^eoKaiviepy nojinpHbie KHTW . Berpena npoH3om-jia 30 aBrycTa B pafioHe K ceBepy OT M . Bepe>KHbix, HOBOCH-

ÓHpcKHe ocTpoBa. KHTbi HaÔJHOAajiHCb B TeneHHe 2 nacoB, 3a

3TO BpeMH cyziHO npouiJio oKOJio 40 KM; KOop/iHHaTbi pawoHa BCTpen: OT 76°36' cm. / 141°2T B .A . JXO 76°34,5'C.IH. /

Data on the westernmost distribution of the Bowhead Whales of Bering-Chukchi- Beaufort stock are scarce and sometimes contradictory (Braham et al. 1984, Belikov et al. 1998, Tomilin 2001). Waters of the Russian Eastern Arctic are visited in summer by whales wintering in the Bering Sea. Most records are known from the Herald Bank and Wrangel Island as well as from inshore waters of the Chukotka Penin­sula during late summer/autumn.

Bowhead Whales were sighted and video recorded by one of the authors (Victor Tretiakov) during con­tinuous visual hydrological observations from the pilot bridge of RV Akademik Fedorov in the course of the AARI Arctic-2008 Expedition. Observation was made on August 30th, noth off Cape Berezh-nykh, New-Siberian Islands. Whale were observing during two hours during which the vessel sailed ca. 40 km. Whales were recorded within the coordinates

Page 4: , HoBbie flaHHbie o rii6enn flenbcfcwHOB pe3yxibTaTeintranet.vef.hr/dolphins/radovi/Odessa 2008/Galov Ukraina 2008 sazetak.pdfMass die-off of Caspian seals caused by canine distem

COBeT n o MOpCKHM MJieKOnHTaiOIUHM (rOCCHfl) HHCTHTyT oKeaHOJiorHH HM. n . FI. LÜHpuiOBa PAH (POCCHJI)

«HepHOMOpCKHH COBeT n o MOpCKHM MJieKOIIHTaiOmHM» QzjeccKHH ueHTp lOrHHPO (YicpaHHa)

rocy^apcTBeHHWH neAarorHnecKHH yHHBepcHTeT HM. K. J\. YuiHHCKoro (YKpaHHa) O^eccKHH HauHOHajibHMH yHHBepcHTeT HMeHH H. H. MenHHKOBa (YKpaHHa)

O r y «Me^cBcziOMCTBeHHaH HXTHOJiorHHecicaa KOMHCCHA» (POCCHH) OßeccKHH 4>HJiHaji HHCTHTyTa ÓHOJiorHH IOHCHMX Mopefi HauHOHajibHOH aKa^eMHH HayK YKpaHHw

YKpaHHCKoe OTOejieHHe MoiqjyHapoflHOH aKajjeMHH HayK 3KOJiorHH, Be3onacHOCTH HejiOBeica H flpHpoflbi

M O P C K M E

M J l E K O n M T A f O l H H E

r O J I A P K T M K M

CBOPHMK HAYMHblX TPYflOB n o MaTepHanaM riflTOH MeacayHapoflHOH KOH^epemjHH

Odecca, YKpaima 14-18 OKmnopn 2008 2.

Marine Mammal Council (Russia) P. P. Shirshov Institute of Oceanology, RAS (Russia)

«The Black Sea Marine Mammal Council» Odessa Center of the Southern Research Institute for Fishery and Oceanography (Ukraine)

Ushinskiy State Pedagogical University (Ukraine) Mechnikov Odessa National University (Ukraine)

Interdepartmental Ichthyological Commission (Russia) Odessa branch of the Research Institute for Southern Seas of National Academy of Sciences of Ukraine

Ukrainian Branch of International Academy of Sciences of Ecology, Security of People and Nature

M A R I N E M A M M A L S

O F T H E H O L A R C T I C

COLLECTION OF SCIENTIFIC PAPERS After the Fifth International Conference

Odessa, Ukraine October 14-18, 2008

Page 5: , HoBbie flaHHbie o rii6enn flenbcfcwHOB pe3yxibTaTeintranet.vef.hr/dolphins/radovi/Odessa 2008/Galov Ukraina 2008 sazetak.pdfMass die-off of Caspian seals caused by canine distem

y/JK 599.5:599.745:599.742.2:599.742.4 BBK 28.07-28.08-28.6

M80

C o c T a B H T e j i f e : A. H. BojiTyHOB riepeBO^ TeKCTOB c p y c c K o r o H a H r j i H H C K o r o : n. A. AJICHHHKOB

npoBczjeHHe KoH^epemjHH H H3#aHHe H a c r o a m e r o côopHHKa ocymecTBjieHO npn (JwHaHcoBOH no/wep^Ke:

• POCCHHCKOH AKa^eMHH HayK • O O O «YTPHIIICKHH Aejib<J)HHapHH», POCCHH • Alaska SeaLife Center, USA • North Pacific Wildlife Consulting, LLC, USA • US Fish and Wildlife Service, USA • Marine Mammal Commission, USA • National Marine Mammal Laboratory, USA • North Pacific Research Board, USA • Shell Exploration & Production Company, Alaska, USA • BceMHpHoro 4>oima #HKOH npHpo^bi (WWF)

• MeacflyHapo/iHoro 4>otma 3amHTbi )KHBOTHWX (IFAW)

• Kapa#arcKoro npHpo^Horo 3anoBeßHHKa (KypopTHoe, Oeo^ociw) • KoKTeöejibCKoro aejibcJMHapHa (Koicreöejib) • KIT JlaöopaTopHH Bpaivia (CHM(^eponojib) • OômecTBa 3amHTbi apxeojiorHHecKHx H HCTopHHecKHx naMHTHHKOB TepaKJieHCKoro

nojiyocxpoBa, e r o 4>jiopbi, (JmyHbi H npHÖpeacHbix BOA «Oa3HC» (CeBacTonojib) • O O O JleneOHO-^HarHOCTHHecKoro u e m p a «Ha3apeT» (EßnaTOpiw) • mi EnojiorHHecKaa CTaHUHH (CeBacTonojib) • O O O OfleccKHH ^ejib(J)HHapHH «HeMO»

OprKOMHTeT KoH^epeHUHH :

• C. T. ByiuyeB - conpeAce^aTejib

• K). A. MHxajieB - conpczjcezjaTejib

• A. B. Ü6JIOKOB - 3aM. npe^ce^aTejiH • B . M. BejibKOBHH - 3aM. npeflccaaTejia • B. H. BypnaHOB - 3aM. npe^ce^aiejw • JX. M. Tjia30B • H. B. CMejiOBa • JI. M. MyxaMeTOB • J\. BeHITCOH • A. H. BojiTyHOB • J\. KaJIKHHC • B. n. CaBycHH

ISBN 978-966-190-025-6 © P O O «CoBeT no MOPCKHM MJieKonHTaiomHM», 2008