CMS CONVENTION ON MIGRATORY SPECIES Distribution: General UNEP/CMS/Inf.10.30 5 October 2011 Original: English TENTH MEETING OF THE CONFERENCE OF THE PARTIES Bergen, 20-25 November 2011 Agenda Item 19 ASSESSMENT OF BYCATCH IN GILL NET FISHERIES (Prepared by Sextant Technology Ltd. for CMS) Pursuant to the recommendation of the 16th Meeting of the Scientific Council, the CMS Secretariat commissioned Sextant Technology Ltd. to undertake an assessment of bycatch of CMS-listed species in gill net fisheries, as well as of available mitigation measures and their effectiveness. Their report is presented in this Information document in the original form in which it was delivered to the Secretariat. An executive summary is also provided as document UNEP/CMS/Conf.10.33. For reasons of economy, documents are printed in a limited number, and will not be distributed at the meeting. Delegates are kindly requested to bring their copy to the meeting and not to request additional copies. 2 Report to the Convention on Migratory Species Assessment of Bycatch in Gill Net Fisheries 30 September 2011 S. M.Waugh 1,2 D.P. Filippi 2 and R. Blyth 2, P.F. Filippi 2 1 Present add ress: Museum of New Zeala nd Te Papa Tonga rewa, PO Box 467, We llington, New Zeala nd. susa n.wa ugh@te papa.govt. nz 2Sexta nt Techno logy Ltd, 116 Wilton Road, We llington, New Zeala nd 1 2 Acknowledgements The report was funded by t he United Nat ions Environment Progra mme under cont ract. We a re grateful to Heid run Fris h a nd Ba rry Baker for t heir guida nce in t he prepa rat ion of t he report. Tha nks a lso to BirdLife Internat iona l for supply of data for t he a na lyses. The Minist ry of Fis heries in New Zea la nd supplied deta iled fis hery data. Tha nks to Cleo Sma ll a nd David Kirby for tec hnica l d iscussions in t he prepa rat ion of t he resea rc h. We a re grateful to Sea A round Us Proj ect for provision of fis hing effort data. Tha nks to Proj ect G lo ba l for provision of fis hing effort a nd bycatc h informat ion. Tha nks to Minist ry of Agricult ure a nd Livestoc k (T urkey), Swed is h Boa rd of Fis heries, Minist ry of Fis heries & Rod rigues (Ma urit ius), Minist ry of Agricult ure & Fis heries (Belgium), Inst it ut Fra nça is de Rec herc he pour l'Exploitat ion de la Mer, Fis heries Attac he Government of Ma lta, Va nuat u Fis heries Depa rt ment, Government of St Helena, Minist ry for Agricult ure, Forest ry a nd Food (Slovenia), Ba ha mas Depa rt ment of Fis heries for t heir replies to our request for informat ion. 3 I ti ." Summary Exec u ve ................................................................................................................................. 7" II Int rod ctio n ." ................................................................................................................................................ 9" u 1 11 n n i itio of g illnet f ishing ." Def ............................................................................................................ " 13 2 i int ti n w it h g illnet f isheries .......................................... " ." Spec es gro ups – modes of erac o 15 III t ." Me hod................................................................................................................................................... " 1 15 t t ." Da a search me hods ....................................................................................................................... " 2 16 illn t t i ti n ." G e me hod descr p o ............................................................................................................ " a)" A na lys is met hod ............................................................................................................................. 16" b) verla p a na lys is ............................................................................................................................. 16" " O c)" Spec ies inc luded in t he st udy ................................................................................................... 17" d)" Spec ies d ist ributio n ma ps .......................................................................................................... 17" e)" A reas of high s pec ies d ivers ity ................................................................................................. 19" f)" Overla p betwee n s pec ies a nd g illnet f isheries ..................................................................22" 3 22 ti n t t ." Ass ump o s of he s udy............................................................................................................... " nking a nd ote ntia l for g illnet f ishing to 4 i i t b illn t i in ." Spec es mpac ed y g e f sh g – ra p 2 i act o latio ns ............................................................................................................................... 7" mp p pu lt 31 IV ." Res u s .................................................................................................................................................... " 1 31 i i ti n ." F shery descr p o ............................................................................................................................ " a)" G lo ba l overv iew of t he g illnet f isheries ................................................................................ 31" b) 36 illnet f isheries in o t h s ia a nd o t h East s ia " G S u A S u A .......................................................... " c)" G illnet f isheries in Nort hwest Pac if ic ..................................................................................... 37" d)" G illnet f isheries in East As ia ....................................................................................................... 37" e)" G illnet f isheries in Nort hern Euro pe....................................................................................... 38" f)" G illnet f isheries in So ut h America ........................................................................................... 39" g)" G illnet f isheries in t he Med iterra nea n Sea ..........................................................................40" h)" G illnet f isheries in Africa .............................................................................................................41" 4 i) ill i i i i 2 G net f sher es n Ocean a ........................................................................................................4 " 2. Overlap ana lys is outputs.................................................................................................................4 5 " " d ll i i ) 5 a " Exposure n ex for a spec es...................................................................................................4 " " b) xposure index by spec ies group............................................................................................49" " E it igat ion methods and the ir applicat ion in g illnet f isheries..........................................66 3. " M " l Al i ) a " V sua erts .....................................................................................................................................66" b) Acoust ic Alerts: ...............................................................................................................................67 " " c)" Operat iona l measures:.................................................................................................................68" d) it igat ion conc lus ions ................................................................................................................70 " " M i i V." D scuss on .................................................................................................................................................71" 1." Spec ies ...................................................................................................................................................71" 2. A rea .........................................................................................................................................................71 " " it igat ion effects...............................................................................................................................72 3. " M " 4." Limitat ions of the study...................................................................................................................7 3" d i I V ." Recommen at ons:............................................................................................................................76" ibli 9 II V ." B ography.........................................................................................................................................7 " III A nnexes..................................................................................................................................................89 " V ." 1." Marine spec ies listed under the C MS part of the study.....................................................89" 2. Z stat ist ics.........................................................................................................................................93 " EE " 3. esults " R 4." Results by overlap index .............................................................................................................. 100 " by unÃwe ighted exposure............................................................................................ 10 3 " a)" UnÃwe ighted exposure of a ll spec ies ................................................................................. 10 3" b) nÃwe ighted exposure of sea birds ..................................................................................... 106" " U c)" UnÃwe ighted exposure of sea turt les ................................................................................. 108" d) nÃwe ighted exposure of sharks ......................................................................................... 109" " U e)" UnÃwe ighted exposure of pinnipeds and otters;........................................................... 110" 5. esults by EEZ and High Seas FAO areas.............................................................................. 111" " R 5 a)" High Seas FAO areas and EEZ sorted by t he ir cont ribut ion in t he unâwe ighted exposure for all spec ies .................................................................................................................... 111" b) gh Seas FAO areas and EEZ sorted by t he ir cont ribut ion in t he IUCN we ighted " Hi exposure for all spec ies .................................................................................................................... 115" c)" High Seas FAO areas EEZ sorted by t he ir cont ribut ion in t he exposures for all spec ies groups...................................................................................................................................... 119" 6. Survey .................................................................................................................................................. 139 " " 6 A study was cond ucted to assess the impacts of g illnet f is hing on s pec ies listed by the Conve nt ion of Mig rato ry Spec ies (C MS s pec ies) Conce rns a bo ut the impact of inc ide nta l . b d o r n g n f s n g s n r ss f o r ma rine ma mma ls, turt les, sea birds a nd t li t i ill et i h i h ee e x e e m a y a p s ha rks Suc h long lived a nd/o r to ppredato r po pulat ions have life histo ry t ra its that . ma ke the m inhe re nt ly v ulne ra ble to add it ive ad ult mo rta lity, w ith po pulat ion dec reases poss ible w ith add it iona l f is he ries mo rta lity . he rev iew of f is he ry info rmat ion conc luded that g illnet f is he ries a re too poo rly doc ume nted to e na ble a na lyses of f is he ry act iv ity o r c ha racte risat ion of the f is hing f leets us ing g illnet methods into d isc reet f is he ry units athe r the resea rc h used s umma ry . R g illnet data at a unive rsa l leve l T his a pproac h may lead biases in the a na lys is of impacts . of g illnet f is hing on nonta rget C MS s pec ies, s ha rks, turt les, ma rine ma mma ls a nd sea birds T . s n n o rmat ion a bo ut s pec ies a nd g illnet f is hing d ist ribut ion, the a na lys is exa mined the re lat ive ex pos ure of s pec ies to g illnet act iv ity T he info rmat ion was the n we ig hted by . a facto r to ta ke into acco unt the v ulne ra bility of po pulat ions to ext inct ion (I UC N we ig hted ex pos ure). Spec ies most ex posed to g illnet f is hing ca me f ro m a ll s pec ies g ro ups listed unde r the C MS U i g i f . A reas of hig h d ive rs ity (C MS s pec ies) we re west coast of So uth A me rica, west coast of Af rica f ro m the Ca pe of Good Ho pe to A lge ria, T he ed Sea / Pe rs ia n G ulf to A ra bia n R G ulf, New Zea la nd / Tas ma n Sea, a nd the Aegea n Sea . he twe nty Exc lus ive Econo mic Zones of 2 37 a reas, in w hic h the g reatest ex pos ure to f is hing ris k occ urs fo r C MS listed s pec ies (we ig hted by I UC N ra nk) we re: Mya nma r, V iet na m, Pe ru, I nd ia, uss ia (Pac if ic), C hile, So uth Af rica, C hina, Na mibia, G reece, R Ga la pagos, Ba ng lades h, Ja pa n (Ma in Is la nds), Weste rn I ndones ia, Easte rn I ndones ia, No rway, Ma urita nia, United Kingdo m, A lge ria, a nd Mo rocco T . he fo rty s pec ies most ex posed to ris k f ro m ra nk, by taxon g ro up we re: T ‚ net f is hing, w he n we ig hted by g ill I UC N ea birds – Af rica n Pe ng uin, Pe ruv ia n Div ing pet re l, Ja pa nese Murre let, Da rk rumped Pet re l, Waved A lbat ross, Socot ra Co rmo ra nt, Humbo ldt Pe ng uin, S 7 Ba lea ric A ‚ Shea rwate r , do in’s Au u Shea rwate r , G ll u , Sho rt 8ta iled o rpo ise o rt h etacea ns & Sire nia ns – Finless rrawaddy Do lphins D go ng P , I , u , N C Rig ht W ha le Bott le nose H um Sea ls Rive r Sea , O mu a nd , A o D lphin , p8bac ked W ha le ‚ ink8footed lbat ross . ac if ic P ‚ P O H um Heav is ide’s o D lphin , ra W ha le Sea t la nt ic Bl e u p8bac ked o D lphin , W ha le , B o D lphin , Fin W ha le , o rt he rn Rig ht W ha le N , Se i W ha le o rpo ise P , r e iste r u m , I ndo 8 ac if ic P Ba ird’s Bea ked . tte rs – Med ite rra nea n Mo nk Sea l , Ma rine tte r O , So t he rn u tte r O . T rt les u – Haws kbill T rt le u , e p’s K m Rid ley T u rt le , eat he rbac k L T u rt le , ogge rhead T rt le G ree n T rt le live Rid ley T rt le L u , u , O u . ‚ o ngf in Ma ko Sha rk o rbeag le Sha rk W ha le Sha rks – Bas king Sha rk , L , P , Sha rk , G reat W hite Sha rk . T he a in reco e ndat io n of t he resea rc h in re lat io n to it igat io n was t hat f is he ry 8 a nd m mm m s pec ies 8s pec if ic so l g t io ns need to be exa ined a nd prio rit ised T he st dy prov ides so e u m u m . ida nce as to w hic h a reas a nd w hic h s pec ies inte ract io n a re u f rt he r u o nito ring a nd m effect ive at red c los res u a nage e nt m m . o s ing le N m it igat io n ost like ly to be nef it f ro m m et hod was fo nd to m u c ing bycatc h of MS s pec ies ac ross taxo n g ro ps u u . C A be rea a nd seaso na l ay co e nea r to reso lv ing a ll s pec ies iss es b t a re nlike ly to be a feas ible m m u , u u o pt io n to i ple e nt g ive n t he hig h re lia nce of co nit ies o n f is h f ro g illnet f is hing m m , mmu m as a food so a nd pa rt ic u rce . Resea rc h to def ine s pec if ic po ints of inte ract io n betwee n MS s pec ies la r f is he ries is rge nt ly needed u u . T he re is a st ro ng need fo r i w it h a pa rt ic la r foc u m proved o bse rve r data , bette r reco rds of byca g ht s pec ies u s in t he a reas of hig h ove rla p of at 8ris k s pec ies a nd a hig h de ns ity u of f is hing effo rt T he . iss C next ste p is fo r f u rt he r f ine r8sca led , resea rc h to add ress bycatc h es in t hose a reas a nd fo r data to assess po p lat io n a nd be hav io ra l facto rs fo r t he u , u u s pec ies ide nt if ied as hig hest ris k in t his a na lys is is wa rra nted . 8 T he Co nve nt io n Mig rato ry on Spec ies was esta blis hed to co nse rve w hic h s pec ies t rave rse nat io na l bo unda ries Spec ies listed unde r t he Co nve nt io n (C MS s pec ies) inc lude . ma ny to ptpredato r s pec ies w hic h a re inhe re nt ly ‘ ra re’ in eco log ica l te rms (Co nve nt io n , on Mig rato ry 20 11) Spec ies . T hese s pec ies have ty pica lly lo ng lifes pa ns a nd low re prod uct ive o ut put T hese life thisto ry t ra its ma ke s uc h s pec ies pa rt ic ula rly se ns it ive to . f po pulat io n c ha nges as a res ult o add it ive mo rta lity (Stea rns 1992 Sibly a nd Ho ne 200 3) , , s uc h as t hat imposed by f is he ries bycatc h mpe rat ives ex ist w it hin inte rnat io na l f is he ries . I ma nage me nt f ra mewo rks to add ress no ntta rget effects of f is hing , inc lud ing minimiz ing waste a nd red uc ing catc h of no ntta rget s pec ies a nd a pply ing preca ut io na ry a pproac hes , to t he ma nage me nt f is hing act iv it ies w he n info rmat io n is unce rta in (FAO 199 5) G illnet f is hing a nd its muc h resea rc h f f pote nt ia l impacts o n no ntta rget s pec ies have bee n t he oc us o Me lv in (e g . . . et al . 1999 , G ilma n 2009 , o kke bo rg L 20 11) . I t is we ll doc ume nted t hat g illnet f is hing catc hes a w ide ra nge of no ntta rget s pec ies a nd co nce rn has bee n A mo ng ra ised t hese f is hing , o n t he C MS s pec ies mo rta lity T his . j urisd ict io ns , impacts is may of be t his bycatc h o n v ulne ra ble pa rt ic ula rly to v ulne ra ble w ild life po pulat io ns . ff po pulat io n e ects beca use t he ir nat ura l ra nges exte nd ove r wate rs of w it h c umulat ive effects f ro m ma ny d iffe re nt f is he ries act iv it ies of mult iple affect ing t he m a nd t he ir life thisto ries place g ive t he s pec ies po pulat io ns a n inhe re nt v ulne ra bility , to added ad ult mo rta lity Coo rd inated effo rts ac ross secto rs of t he resea rc h co mmunity , . f is hing o pe rato rs a nd reg ulat ing age nc ies a re needed to add ress t he inc ide nta l ca pt ure of C MS s pec ies in g illnet f is hing (Me lv in a nd Pa ris h 1999) Des pite ma ny yea rs of co nce rn ove r t he impacts of g illnet f is hing pro ble ms of . o n to ptpredato r s pec ies it re ma ins a n e nig mat ic f is he ry: litt le is know n of t he state of t he ta rget stoc ks , , f is hing f ff pract ices catc h bycatc h a nd d isca rd ing act iv it ies a nd is hing e ic ie ncy T his lac k , , , . of know ledge may be t he res ult of d ive rse d rive rs: g illnet f is he ries a re ofte n ‘ low va lue’ f is he ries (W ilso n et a l 20 10 Minist ry of , . Fis he ries 20 11) fo r w hic h deta iled mo nito ring reg imes a re uneco no mic to imple me nt; t hey a re ofte n c lassed as a s ing le f is he ry , w he n in rea lity t hey reg ro up a d ive rs ity of f is hing o pe rat io ns bot h in te rms of ta rget stoc ks a nd f is hing met hods; bot h a rt isa na l a nd ind ust ria l f is he ries a re desc ribed as o ne f is he ry catego ry yet c lea rly o pe rate o n a d iffe re nt bas is; g illnet f is hing in deve lo ping co unt ries a re a poo rly doc ume nted yet impo rta nt s ubs iste nce act iv ity , . 9 W hile t he inc ide nta l catc h of ma ny C MS s pec ies is doc ume nted, prio rit isat io n of effo rts is needed as to how to add ress t he pote nt ia l impacts of mo rta lity its on w ild life po pulat io n his is bot h in te rms of t he zo nes to ta rget fo r mit igat io n a nd in re lat io n to . T t he s pec ies pote nt ia lly impacted mit igate t he f is he ry o llow ing s uc h data gat he ring a nd a na lys is, effo rts to . F inte ract io ns ca n be ta rgeted, a nd t he f is he ries co nce rned ca n be mo nito red a nd f is he rme n me nto red to red uce pote nt ia l ris ks to s pec ies ppro priate . A mit igat io n tec hno log ies ca n be ta rgeted at t he a reas a nd f is he ries w hic h a re prod uce t he g reatest be nef it in te rms of ris k red uct io n . W it ho ut mo re like ly to deta iled info rmat io n o n s pec ies inte ract io ns w it h g illnet f is hing act iv ity, a nd data o n t he nat ure a nd exte nt of t he f is he ries, t he exte nt of mo rta lity of C MS s pec ies, a nd res ult ing ris k to po pulat io n v ia bility is pro ble mat ic to ex plo re in mea ningf ul ways . T he a pproac hes we a pplied to a na lys ing t he ris k posed by g illnet f is hing to C MS s pec ies co me f ro m a n Eco log ica l Ris k T hese a pproac hes have A ssess me nt bee n a pplied f ra mewo rk (e g (ER A) . . w ide ly to f is he ries 0 11 o bday et a l H . 2 ). ma nag ing iss ues of s usta ina bility a nd e nv iro nme nta l effects, in pa rt ic ula r in info rmat io n poo r e nv iro nme nts . We used a q ua litat ive assess me nt of t he ex pos ure of s pec ies to g illnet f is hing act iv ity by co mpa ring t he s pat ia l d ist ribut io ns a nd de ns ity of act iv ity (w he re ava ila ble ) fo r bot h t he he o utco mes prov ide a re lat ive ra nking of s pec ies in C MS s pec ies a nd g illnet f is he ries . T te rms of t he ir ex pos ure to f is hing effo rt, a nd t he co nt ribut io n of f is hing effo rt in eac h Exc lus ive Eco no mic Zo ne inte rnat io na lly, to t he ex pos ure index . We we re t hus a ble to ra nk s pec ies a nd a reas in te rms of t he like lihood of adve rse effects of g illnet f is hing . Beca use of t he limited info rmat io n a bo ut t he nat ure of t he f is hing o pe rat io ns fo und in o ur a nd rev iew, of be hav io ura l t he inte ract io ns of s pec ies w it h t hose f is he ries, o ur a na lys is sto ps s ho rt of exa mining s pec ies o r po pulat io n leve l impacts of mo rta lity f ro m t he f is he ries . Rat he r it ide nt if ies t he g ro ups of s pec ies, a nd t he a reas w hic h req uire most d ilige nt a nd deta iled exa minat io n fo r t he f ut ure, to add ress a ny ris k of mo rta lity no n C MS s pec ies po pulat io ns . T he need to mit igate adve rse effects of f is hing o n C MS s pec ies req uires f is he ry ºs pec if ic ta rget ing t he . C urre nt ly, t he o bsc urity of g illnet f is he ries, in te rms of t he info rmat io n a bo ut o pe rat io ns, reco mme ndat io ns leve l of be ing effo rt, catc h, deve lo ped to a nd bycatc h ta rget t hese occ urring prec ludes s pec if ic mit igat io n act iv it ies . F urt he r, deta iled resea rc h into t he pro ble ms t hat a ppea r to be of g reatest mo me nt is needed . 10 T he stated req uire me nt to f ra mewo rk fo r impe rat ives g lo ba lly s urro und ing meet t he f is he ries g illnet princ iples set o ut to needs f is hing. be in t he ecosyste m ma nage me nt ba la nced G illnet f is hing aga inst is a t he v ita l soc io Óeco no mic met hod of food gat he ring fo r a la rge po pulat io n g lo ba lly bot h in deve lo ping a nd ind ust ria lised nat io ns. , Fis h , inc lud ing aq uac ult ure prod ucts acco unted fo r 16% of prote in po pulat io ns g lo ba lly in 2008 (FAO 20 10). T his is a n inc reas ing food so urce , inta ke fo r w it h leve ls of t rade in f is h prod ucts s how ing a n ave rage a nnua l inc rease of 6% pe r yea r in t rade fo r t he last seve ra l yea rs (FAO 20 10). T he pro po rt io n of t he wo rld’s food inta ke t hat de rives f ro m g illnet f is hing is not c lea rl y re po rted , but of 142 millio n to nnes of f is h prod uct io n in 2008 (FAO 20 10) it was est imated t hat 20% of g lo ba l f is h prod uct io n is la nded f ro m g illnet f is hing a nnua lly (SA UP 20 11; ave rage rat io fo r 2004 – 2006). It acco unts fo r a hig h pro po rt io n of t he prote in de live red to ta ble , pa rt ic ula rly so me nat io ns re ly a lmost exc lus ive ly o n g illnet f is hing. in deve lo ping nat io ns w he re , " Fo r t he purposes of t his st udy g illnet f is hing inc ludes a ll f is he ries w hic h use pass ive net , met hods to ta rget f is h a nd inc ludes set net g illnet d rift net t ra mme l net f is hing. Set nets , , , , a re nets of a ny mes h s ize t hat a re de ployed by f loat ing t he net in t he wate r co lumn in , pe lag ic (nea r s urface) , midd le Óde pt hs o r e piÓbe nt hic wate r leve ls. G illnets a re made of a , f mate ria ls w it h rece nt inc rease in use of mo nof ila me nt prod ucts fo r nets d ue va riety o , , to its d ura bility a nd low cost. T he FAO (FAO 1990) def ines s ix maj o r g ro ups of g illnet f is he ries a nd eac h of w hic h has a FAO sta nda rd a bbrev iat io ns code (he re in brac kets): a) Set nets (G NS); b) e nc irc ling nets (G NC); c) co mbined g illnets – t ra mme l nets (GT N); d) d rift nets (G ND); e) t ra mme l nets (T NR); f) f ixed g illnets (G NF) (f ig ure 1). G illnets a re des ig ned to t ra p f is h by t he g ills. T hey ca n be of va ria ble d ime ns io n f ro m a , few mete rs to seve ra l kilo met res lo ng. put toget he r to fo rm a f leet. I n ind ust ria l f is he ries , bloc ks of g illnets (ta ns) a re La rge vesse ls ca n ca rry seve ra l f leets of kilo met res of net. 11 nets de ploy ing , a) b) c) d) e) f ure 1Gi llnet types as defi ned by the FAO (FAO 200 1). a) Set gi llnets, b) Enci rc li ng gi llnet, c) Combi ned gi llnet – tra mme l net, d) Drift net, e) T ra mme l nets, f) Fixed gi llnet Fig 12 Because of the need to work with data about f is hing effort for this st udy we have been , limited to researc hing reported (and therefore ‘ lega l’) gillnet f is hing only. T here are many separate problems associated with illega l gillnet f is hing and g host f is hing w hic h are not addressed here. T he work is only concerned with gillnet f is hing in the marine enviro nment. Gillnet bycatc h is a lso an issue for CMS species occupying est uarine environments suc h as the otters, manatees and some cetaceans but these issues are not addressed in this report. Gillnets are designed to be t ransparent and have the same density as water, them diff icult to detect in the water co lumn (Rowe 2007 ein 1980) and it is , L reason that many species become entang led. Interact ions between nonOtarget making for t his species and gillnets can be est imated only by t he proport ion of anima ls that are caug ht and drown in gillnets. It is not possible to est imate t he proport ion of species that become entang led and f ree the mse lves and/or break f ree wit h part of the f is hing gear attac hed to the m (T homas and Kaste lien 1990). Entang lement of cetaceans has occ urred in every region w here substant ia l gillnett ing operat ions and the presence of marine mamma ls overlap (Jefferson and Curry 1994). Here we inc lude sea cows as part of the group ‘cetaceans’ due to gross ly similar feeding be haviours to sma ll cetaceans. It is thoug ht that the ability for cetaceans to detect gillnets is primarily thro ug h acoust ic means (T homas and Kaste lein 1990). Cetaceans are able to detect gillnets by the so und the net makes as water passes throug h it and possibly by the acoust ic propert ies that f is h create w hen ent rapped in the net and Kaste lein 1990). Sma ller cetaceans (mainly do lphins and porpoises) entang led and may drown in the gillnet because they are not st rong enoug h (T homas become to break f ree and come to the surface to breathe w he reas larger cetaceans are more able to , th h t h t t th ft swim roug e ne s, bu is o en results in towing gear w hic h can cause inj ury and death (Cetacean Bycatc h Resource Center 20 11). Pinnipeds and other sma ll marine mamma ls (e.g. sea otters) interact with gillnets in a similar way to sma ll cetaceans, becoming entang led by their flippers/ limbs w hen they interact with the net. For sea ls, there have been reports that some become att racted to 13 gillnets through the use of acoustic pingers a nd associate gillnets with a n easy food source (referred to as the ‘d inner be ll effect’) causing a n increased risk of e nta ng leme nt as we ll as damage to the target catch (Beeso n a nd Ha na n 1996, Mate 1993). T he seabird species most susceptible to capt ure in gillnets are d iving species; e ncountering a nd becoming e nta ng led in the net whe n d iving to forage for food a nd d row ning before t he net is retrieved ( e lvin et a l. 1999 T rippe l et a l. 2003 re nc h 2011). M , ,F Seabird bycatch has bee n wide ly docume nted in coasta l highseas d rift a nd demersa l , , gillnet fisheries. Seabirds may be a lso be caught in gillnets set deeper tha n their max imum d iving depth as seabirds may e nco unter nets as they are set or hauled (Lokkeborg 2010). Seabirds might a lso be e nta ng led in lost gillnets or d iscarded piece of gillnets at this materia l is opportunistica lly co llected by seabirds for the co nstructio n of their nest. T his ca n a lso prese nt a risk for the chicks being caught in the nest by pieces of gillnet gathered by its pare nts d uring nestbuild ing (Mo ntevecchi 1991). Like marine mamma ls sea turt les become e nta ng led in gillnets a nd d row n if they ca nnot , break free from the gillnet a nd reach the surface for air. Serious inj ury ca n a lso be sustained to f lippers from lines a nd ropes which support the gillnet in the water co lumn (G illma n 2010). Sharks become e nta ng led in gillnets whe n they swim into the net a nd become caught , by fins/gills whe n trying free themse lves. Once wrapped in the gillnet, the shark the n suffocates. G illnets are a lso used to harvest sharks as a target spec ies. Shark damage to nets is unique as they leave behind s limy materia l a nd rough skin which they deposit o n the net. Aside from fish harvest, gillnets are a lso used to protect swimmers from shark attacks whic h results in shark morta lity. 14 All objectives of the work were addressed with a common methodology set out below. , The first approach used to evaluate the impact of gillnet fisheries o n CMS species was to get detailed information about gillnet fisheries species distribution bycatch and , , mitigation. T he informat io n was sought directly from the national departments in charge of the fisheries and thus for each j urisdictio n hav ing an Exc lusive Economic Zone (EEZ). Agencies were contacted by email and by fax covering the 262 EEZ and 18 high seas , FAO areas. Agencies we re inv ited to fill a form established for the purpose of this studies (see annex) or to indicate any relevant documents where the information requested could be found. The information solic ited was a technical desc ription about the gillnets used in EEZs and in the high seas area the number of vessels vessel size period of the year recent , , , , landed catc h estimation effort estimation spatial information mitigat ion and bycatc h , , , , summary data. Despite these efforts and nume ro us contact attempts less than 15 replies were received. , The information published found online were usually not detailed enough or too old , , for the requirements of t he research. In particular information to distinguish one fishery from another and to define fineºscaled information relevant to different target fisheries , , fleets or areas was lacking. , At the same time we rev iewed online and published literature. Most of t he documents , found were too old too general or could not be generalised to fishery specific to inform , the analysis of fishery characterisation. It was therefore not possible to establish a gillnet fishery classification and to produce accurate global maps of the fishing effort for eac h type of gillnet for the last 3 years (this met hod is detailed in the next chapter) 15 An alternative approach was ado pted which co ns isted of produc ing a mo re ge neral , v iew of t he g illnet f ishing activ ities at a g lobal scale. Fo r t his purpose, effo rt maps were based o n t he g illnet f isheries land catch estimatio n published o nline (SA UP 2011). Simultaneo usly to t he off ic ial req uests numero us local and g lobal No nàGovernme ntal , O rganisatio ns were co ntacted and info rmatio n was req uested rega rd ing animal bycatch and effective ness of mitigatio n. T hose req uests were f ruitf ul and de livered deta iled info rmat io n rega rd ing cetacean and sea bird bycatch and mo re ge neral info rmatio n fo r t he ot he r spec ies. An approach was ado pted to use t he ava ila ble info rmatio n based o n a s ing le g illnet , class reg ro uping all t he d iffere nt g illnet gea rs. T he se ns itiv ity of a spec ies to be caug ht in a g illnet has also bee n s implif ied based o nly o n be hav io ural info rmatio n. T his met hod is prese nted in t he next chapter. T he process of t he overlap analys is was staged in several phases: ‚ t he a rea of hig h spec ies d ivers ity was ex plo red based o n t he , d istributio ns of 123 ma rine spec ies listed under CMS. ‚ Seco ndly a reas of hig h de ns ity of g illnet f ishing fo r 262 EEZ and 18 hig h seas , FAO a reas were ide ntif ied. ‚ T hirdly t he ex posure of each CMS spec ies to g illnet f ishe ries at a g lobal scale , was calculated. T he results a re ranked a) by spec ies t he most ex posed and b) First by t he EEZ f ishery (all g illnet f ishing w it hin t he EEZ co mbined) hav ing t he most pote ntial impact in terms of bycatch. T hese ranks were t he n weig hted by t he t hreat ranking ide ntif ied by t he I nternat io nal Unio n fo r t he Co nservatio n of Nat ure (I UC N) fo r each spec ies in t he analys is to g ive a 16 weighted score by spec ies, ref lect ing t he like ly populat io n leve l of impact of fisheries ex pos ure ‚ F weighted ex pos ure). (I UC N ina lly, t he res ults were categorized in t hree leve ls of ex pos ure: highly ex posed, oderate ly ex posed, least ex posed. m he species inc luded in t he st udy T o nve nt io n o n C he T C MS M a re t he 12 3 ma rine species l isted der t he un igratory Species. spec ies were split in gro ups: cetacea ns 5 sea birds, sha rks, t urt les, ot her sea co nta ins respect ive ly & sire nia ns (hereafter cetacea ns), s (pinnipeds ma mma l d sea otters). an ch gro up Ea species, 59 spec ies, a nd 6 species each for t he re ma ining gro ups. T he categorisat io n of t he species is set o ut in t he a nnex of t his doc ume nt (Ta ble 18 Ta ble 19 Ta ble 20 Ta ble 2 1 a nd Ta ble 22). , , , or each spec ies F o ngit ude a 46 dist ribut io n ma p was esta blished wit h a reso lut io n 0. 1° x 0. 1° degrees t it ude derived fro m published dist ribut io n ma ps. Depe nding how we ll , know n was t he species t he dist ribut io n ma p co nta ins differe nt layers of a nima l de nsity. , l d an la Sing le lay er distribution map s ost of t he species (exc luding t he birds), t he ma ps co nsisted of a sing le layer dist ribut io n ra nge. T hose ma ps have bee n published by t he I UC N (I UC N 20 11) a nd have or F m bee n re edited for t he purpose of t he st udy. Dual lay er distribution map s e n species have t heir T t he species ra nges: a hose species were: S T h r , T urt le S a k H um d an pbac k a H W ma kn hortfin Ma k Tu o S ha rk, oggerhead L rt le. la yers of ce rta inty based o n ow n dist ribut io n, reas of ha le, w ksbill ps based o n two T he ma Tu s king a B rt le, G d an a ha rk, S ree n reas of G reat rt le, Tu certa in dist ribut io n. un W hite ha rk, S eat herbac k L ow ledge of kn Tu orbeag le P rt le, id ley R ps for t hose species were esta blished fro m t he 17 o nline publis hed ma ps of t he Fis he ries a nd Aq uac ult ure De pa rt me nt of t he 20 11) . W FAO (FAO e have affected a de ns ity of 1 fo r t he data fo r a reas of know n d ist ribut io n a nd 0 1 to t he a reas of unce rta in d ist ribut io n . . Bird distribution map s T he bird d ist ribut io n ma ps we re prov ided by Bird Life I nte rnat io na l (Bird Life I nte rnat io na l a nd Nat ure Se rve 20 11) . T he A rme nia n G ull is not recog nised as a d ist inct taxo n by Bird Life I nte rnat io na l t he refo re t he d ist ribut io n ma p f ro m publis hed so urces was used (De l Hoyo et a l 1996) A ll ma ps had a s ing le laye r s ha pef ile desc ribing t he ra nge of t he . . s pec ies Howeve r w he n t he s ize a nd t he locat io n of most of t he breed ing s ites was we llw . know n fo r s pec ies a A lbat rosses a nd d ist ribut io n ma ps a pproac h was (e g . . Pet re ls , t hose s hags , by add ing used fo r 32 listed by t he e nde mic Ag ree me nt s pec ies , pe ng uins) hots pots of d ist ribut io n a ro und s pec ies fo r w hic h we too k into t he on , we Co nse rvat io n improved of t he breed ing co lo nies T his . acco unt mo re t ha n 500 breed ing s ites (A nnex Ta ble 2 3) . Bird distribution with forag ing radius app roach To improve t he d ist ribut io n ma ps we ass umed t hat t he s pec ies we re c luste red a ro und , breed ing s ites d uring t he breed ing seaso n To imple me nt t his a pproac h it was ass umed , . t hat no nwbreede r birds occ upied t he f ull s pec ies ra nge , w hile t he breed ing ad ults in breed ing seaso n we re s pread a ro und t he ir breed ing co lo nies fo llow ing a n ex po ne nt ia l decay f unct io n w hic h exte nds up to t he ir max imum fo rag ing ra nge rad ius de noted r max . T he de ns ity of t he breede rs at a d ista nce r f ro m t he ir co lo ny fo llows a n ex po ne nt ia l decay def ined by: 経長追勅勅鳥勅追 岫堅岻 噺 欠 抜 結 r is t he d ista nce f ro m t he co lo ny a nd 欠噺 認 欠 嶋投"岫轍 轍迭岻抜認 認尿尼猫 """"""""岫'ł"な岻" def ined by t he eq uat io n be low: 牒迩任如 完轍 尿尼猫 勅 嶋投"岫轍 轍迭岻抜認 認尿尼猫 18 """"""""岫'ł"に岻 b rds at t he co lo ny . i ra nge, breede r de ns ty was ass umed to be ze ro . i 鶏頂墜鎮 s i t he numbe r of breed ng i eyo nd B t he max mum fo rag ng i i O uts de of t he i breed ng seaso n, we co ns de red t hat ad ults occ up ed t he f ull s pec es i i i i ra nge a lo ng w t h no n£breede rs he hot £s pots we re we g hted w t h t he rat o of t me . T i i i i i s pe nt o n t he breed ng s tes pe r yea r . i i Figu re 2 ¬ Exa mple of a n i mproved sea bi rd dist ri butio n fo r t he G rey Pet re l he squa re root of t he de nsity has . T bee n used i nstead of t he de nsity to hig hlig ht low de nsity a rea fo r t he pu rposes of t his ma p i llust ratio n o nly . exa m ned . i d st r but o n, t was poss ble to s how a reas of h g h s pec es d ve rs ty . i i i i i i i i i T he d st r but o n of i i i t he C MS s pec es i d st r but o n i i i no rma l zat o n was def ned as fo llow: i i i Fo r th s i purpose, t he c umulat ve ly i of eac h 19 was s pec es i was y B s umm ng i no rma l zed . i T he t he r i s pat a l i D sp 完栂墜追鎮鳥 経鎚椎 噺 な""""""""岫'ł"ぬ岻" e p ese nts t he s pat ia lly no a lized a ni a l de ns ity of t he s pec ies sp. r r rm m had t he sa e we ig ht, m unknow n o T he r a king t he m es ults r Eac h s pec ies inde pe nde nt f o po pulat io n s ize w hic h is r m poo ly know n fo a ny s pec ies, es pec ia lly cetacea ns. r r m s pat ia lly no a lized rm d ist ibut io ns r we e r su ed mm fo r a ll s pec ies. T he es ult r is eq uiva le nt to a de ns ity of s pec ies, he e ca lled t he s pec ies d ive s ity index a nd de noted r r SDI. Hig h va lues be m r nu of of SDI s pec ies 鯨経荊 噺 デ鎚椎勅頂沈勅鎚 経鎚椎 """"""""岫'ł"ね岻" e p ese nt r r p ese nt r a eas r a nd/o r of hig h s pec ies a eas r co nce nt ated (Fig u e 3). r r 20 w he e r d ive s ity, r o ne o r w hic h o e m r ind icate s pec ies a e r a hig h hig hly Figu re 3ÿ De nsity of species a no rmalised SDI. Hig h values re prese nt a reas of hig h species dive rsity. 21 Five important a reas of s pec ies d ivers ity a re a ppa re nt: outh A merica, es pec ially the western coast ‚ S ‚ T ‚ T he Western coast of Africa from the Ca pe of Good Hope to Algeria he Red ea/ Pers ian Gulf and A rabian Gulf S ew Zealand/Tas man Sea ‚ N ‚ Aegean ea S s s all hots pots a ppea r in the v ic inity of maj or seabird co lo nies, s uc h as those Numerou , m a reas show n in the mid ocean a reas of the southern Ind ian and Atlant ic Oceans, Hawa iian c ha in and south of ew Zealand. N An overla p index was noted uant ify ing the overla p betwee n a s pec ies 頚鎚椎 帳帳跳 q d ist ribut io n and the g illnet f isheries of an EEZ. he overla p index is def ined by the T fo llow ing e uat io n. q 填 頚鎚椎 帳帳跳 噺 謬完栂墜追鎮鳥 経鎚椎 抜 系帳帳跳 """"""""岫'ł"の岻" i i i Dsp is the s pat ially normalized de ns ity of the co ns idered s pec ies . 系帳帳跳 s the f sh ng effort de ns ity in the co ns idered EEZ or hig h seas a rea. i s/EEZ were sorted by order of importance and d iv ided h la ind a hs T e over p ex of e c pec e by the s um of the overla p index. Due to the lack of informat io n rega rd ing g illnet f ishing effort and the d iscrepancy of the units used to describe the effort by d iffere nt f ishery ad minist rat io ns, it was not poss ible to establish a g lo bal homoge nous effort de ns ity ma p for the g illnet f ishing. 22 Therefore t he estimation of t he gillnet catc h by EEZ and by hig h seas FAO areas by Sea A round Us Proj ect for t he years 2004 2005 and 2006 was used ore recent catc h , , . M estimation was not availa ble at t he time of t he study. Vectoria l maritime boundaries publis hed in t he Maritime Boundaries Geodata base availa ble from t he Flanders Marine I nstitute ( IZ Be lgium) were used to represent t he 262 EEZ in t he study ( IZ 2011) VL , VL . Figure 4 Maritime boundaries of the 262 EEZ and the 18 High Seas FAO areas. The catc h estimated by Sea A round Us Proj ect refers to 'reported land ings' as t he ot her catc h components are usua lly unknow n (e.g. unreported land ings, d iscards, and g host kills). The estimations were made from t he fo llow ing data sources: FAO Fis hstat, IC ES, GFC M, CCA MLR, RECO FI, C ECA F and adj usted among ot her t hings, to retain only marine finfis h species (e.g. fres hwater fis h, mo lluscs and crustacean) (SAUP 2011). The catc h estimation may be s lig ht ly greater t han t he officia l j urisd iction statistics, however, t hey constitute a homogenous set of data whic h ref lect t he importance of t he gillnet activity in eac hj urisd iction. 23 The estimation of catc h by Sea Around Us Proj ect applies to a w hole EEZ owever t he . H ex haustive rev iew of g illnet f is heries presented in t his report revealed t hat g illnets were used most ly w it hin 20 nautical miles (nm) from s hore. I nd ust rialized nations were more likely to extend g illnet f is heries across t he ir w hole EEZs and beyond, but coastal deployment of t he g illnet was still dominant . To ta ke into account t hese d ifferences in t he d ist ribution of t he effort, t he analys is was run w it h 3 d ifferent scenarios: oastal scenario: The effort was spread only w it hin 20 nm from t he coast. ‚ C 0: 0 scenario: The effort was spread equally between t he 20 nm coastal band and t he rema ining EEZ, w it h 50% of effort in eac h area. il consumption equivalent per capita: This is t he standard scenario used and ‚ O present in results. This intermed iate scenario was based on t he o il consumption equivalent per capita for eac h EEZ. The rev iew of g illnet f is heries hig hlig hted t hat ind ust rialized count ries were more likely to deploy ind ust rial f is hing activ ities across t he w hole EEZ, includ ing g illnet f is heries. Poorly ind ust rialized count ries have t he ir g illnets most ly deployed along t he coast w it hin 20 nm of t he coast. O il consumption equivalent per capita was c hosen to represent t he level of ind ust rialization of nations and as an index to spread g illnet effort in t he EEZs. If t he o il consumption equivalent per capita was less t han 1000 kg, t he g illnet effort was spread in t he coastal 20 nm st rip only. If t he o il consumption per capita is greater t han 1000 kg, t he effort is spread equally in t he 20 nm coastal st rip and t he rema ining area of t he EEZ. The o il consumption per capita per EEZ are presented in t he annexes (Ta ble 24, Figure ) 5. ‚ 5 5 The estimation of catc h for hig h seas areas were spread uniformly in t he entire hig h seas areas w hatever t he scenario. 24 Figure 5 Ò Oil consumption equiva le nt per capita sce nario. Light gree n areas represe nt t he EEZs having a n oil consumption equiva le nt per capita less t ha n 1000 kg. Dark gree n areas represe nt EEZs having a n oil consumption equiva le nt per capita greater t ha n 1000 kg. High seas zones are not represe nted. The hig hest g illnet effort de ns it ies were found in 6 ma ins areas: e ntra l As ia/I nd ia ‚ C est Africa ‚ W ‚ N ‚ W ‚ N ‚ Sout h As ia ort hern Euro pe est Sout h America ort h As ia (Ja pa n, C hina, Russ ia, Korea) 25 Figu re 6 Gillnet effo rt de nsity dist ri buted fo llowing t he oil co nsu mptio n equiva le nt per ca pita sce na rio ex pressed i n catc h de nsity [tonnes . km.2]1/ 2 26 T he a nalys is was run fo llow ing t he t hree effort d ist ribut io n sce na rios desc ribed a bove. To eva luate t he se ns it iv ity of t he o utco mes to t he d ist ribut io n of t he effo rt, fo r eac h s pec ies t he ex pos ure co mputed w it h t he coasta l sce nario and w it h t he ex pos ures co mputed w it h t he 50: 50 sce na rio was co mpa red. T he test of se ns it iv ity s howed t hat t he ra nk of t he s pec ies was bare ly affected by t he va riat io n of t he effo rt d ist ribut io n betwee n t he two sce narios, o ne w it h a ll t he effort w it hin t he coastal st rip, t he ot he r w it h it s pread 50: 50 betwee n coast a nd w ide r EEZ. T he o ut puts of t hese two extre me sce narios s howed ve ry litt le d iffe re nce in s pec ies ex pos ure (Fig ure 7), w it h t he s pec ies most affected by t his c ha nge was t he Sho rt Xta iled A lbat ross (PHA) w hic h was a bit mo re ex posed unde r t he 50: 50 sce nario. G ive n t his s lig ht move me nt in s pec ies ex pos ure ind ices, we proceeded to apply t he ‘o il eq uiva le nt’ sce nario to t he re maining as pects of t he analys is, co nf ide nt t hat t his c hange had litt le leve rage o n t he s pec ies list ings, but cons ide ring t hat it mo re realist ically re prese nted t he s pread of effo rt by EEZ t ha n eit he r of t he mo re s implist ic sce na rios. 27 0 .020 NPH ORB STB 0 .015 DUG STM SYW LSA SOC o ir a en sc 50 0 .010 50/ re , osu E xp 0 .005 0 .000 BMU CAC BAM BAO BOB BAE BAB BEB BAP 0 .000 TUAPOT PHG STI HGR SPD STV ST POP G ST E LAU CEH LIC PHV SDG LPV STR PEG EBJ SPH BAM STS EBG LGE LOF ST F BAO ST MMN BEB CEE POS PUM LML N LGA SBG LGB LHM EIM LPK CT MCAT GRG LAA CAC DCC DEL PUC HYA ST H DDE LGH RHT CHM LLE PHA SNA IPA OFL SNL IOX MMO TSNR UTCCC BAE BAP MNV BOB PCC OOR PYM PIR POB BMULGS PT G SNC LGO PCR LOP LAT CEC PHIGLM DIM PCW DNB PRK PHN LRL TORH HC THH DIP PXP DICSTP PCO BAB EBA CAM PCI PRO MA I MAH DIPOD X PHE PHF PTT POW DAM 0 .005 0 .0 10 0 .0 15 0 .020 Exposure, Coast al scenario Figu re 7 ¦ Co mpa riso n of t he ex posu re of a s pecies to gi llnet fis hi ng co mputed wit h t he coasta l scena rio a nd t he ex posu re co mputed wit h t he 50: 50 scena rio The s pec ies t hat were most ex posed to g illnet f is he ries we re coasta l s pec ies ove rla pping w it h t he reg io ns of hig h de nsity g illnet f is hing. Spec ies w it h s mall d ist ribut io ns in reg io n of hig h f is hing effo rt de ns ity (e.g. Te rns a nd G ulls) we re part ic ula rly ex posed. Howeve r some of t he m we re se ldo m o bse rved ca ug ht in g illnets. Conve rse ly s pec ies t hat we re less exposed we re so ut he rn pe lag ic s pec ies ove rla pping , litt le w it h g illnet f is he ries o r s pec ies w it h w ides pread ra nges ove rla pping moderate ly , h h w it g illnet f is e ries. Idea lly t he ex pos ure index s ho uld be we ig hted w it h a be hav io ura l index of ind iv id ua ls of t hat s pec ies to be ca ug ht in g illnets to est imate t he ris k of adve rse effects fo r t he w ho le , h po pulat io n. An est imat io n of t e t rue s usce pt ibility fo r eac h s pec ies to eac h g illnet f is he ry was not poss ible to do d ue to t he lac k of info rmat io n. 28 Howeve r o have a a pprox ima e es ima io n of he ex pos ure E f ro m he ove rla p O a sp sp , , t t t t t t d b d d s implif ie e havio ura l in ex Bsp was es ima e t t . 継鎚椎 帳帳跳 噺 稽鎚椎 抜 頚鎚椎 帳帳跳 """"""""岫'ł"は岻" T he s implif ied be hav ioura l index was def ined as fo llows: T he s pec ies was acco rded a be hav io ura l index of 1 if: .0 ‚ ‚ T he re was a leas o ne o bse rva io n of byca c h in a g illne f is he ry t t t t t . T he animal had a leas one be haviour prese n ing a ris k o be ca ug h by t t t t t g illne s t . Be havio urs w hic h may A ll t pu he anima l a ris k of be ing ca ug h we re: tt t t ‚ follow ing f is hing vesse ls , ‚ feed ing f ro m f is he ries offa l , ‚ d iving o ca c h prey t t , ‚ s ea ling ba i s f ro m f is hing lines t t , ‚ feed ing o n f is he ries a rge s pec ies (ad ul s ize) t t t . he o he r s pec ies a re acco rded a s implif ied be hav io ura l index of 1 t 0.0 T he nex s e p was o foc us o n hrea e ned s pec ies and ide n ify w hic h of he m we re he t t t t t t t t mos ex posed o he g illne f is he ries t t t t . Fo r his purpose he ex pos ure index Esp was we ig h ed w i h he hrea e ned s pec ies rank t , t t t t t t b se o u y he I n e rna iona l Unio n fo r he Co nse rva io n of Na ure (IUCN 2 11) T he IUCN t t t t t t t t 0 . coeff ic ien of he s pec ies was de no ed Tsp T he IUCN we ig h ed expos ure is no ed Wsp t t t t t . . 激鎚椎 帳帳跳 噺 劇鎚椎 抜 継鎚椎 帳帳跳 """"""""岫'ł"ば岻" T he coeff ic ie n T we re def ined as fo llows: t sp 29 Table 1 Weight Tsp functio n of IUCN ra nk IUCN Rank NT LC VU EN CR Not defined Tsp .4 .2 .6 .8 1.0 .5 30 The results of t he IUCN weig hted exposure ana lysis are out lined be low. The intermediate results, overlap and unFweig hted exposure, are presented in t he annexes of t his document (page 100 and page 103) In 2006, t he tota l from gillnet fis hing landed catc h was est imated about 16 million tonnes (SA UP 2011). This represented 20% of t he world tota l landed catc h. The catc h remained t he same during t he decade 1996 F 2006 however when examined in detail, great variat ions in t he cont ribut ion of t he gillnet fis heries varied in t ime and in space. The EEZs were sorted by order of importance of t heir gillnet catc h in 2006 (Table 2 data , source: SA UP 2011). The percentage of gillnet catc h of t he tota l fis h catc h for eac h j urisdict ion is noted. The regions present ing t he hig hest gillnet catc h in 2006 were : ‚ Nort heast & nort hwest Pacific: Russia Pacific nort hwest hig h seas FAO area. , ‚ Sout h Asia: India and Bang lades h, eastern Indian Ocean hig h seas FAO area ‚ Sout heast Asia: Viet nam, Myanmar, Philippines, Indonesia, Ma laysia, Thailand and Pacific western cent ra l hig h seas FAO area. ‚ East Asia: China, Japan. ‚ Nort hern Europe: Norway Ice land. , The c haracterist ics of gillnet fis heries are presented be low by region. Details about gillnet fis heries by j urisdict ion are presented when t hey make a significant cont ribut ion eit her in terms of gillnet effort on in bycatc h. A full descript ion of t he gillnet fis heries 31 are presented in the annex of this document based on the replies of our survey and public ly availa ble informat ion (Ta ble 38) Table 2 Gi llnet catch by EEZ i n 2006 (SAUP 2011). T he perce ntage of total fish catch f rom gi llnet catch and the gi llnet catch de nsity a re set out by EEZ sorted by gi llnet catch i n 2006 EEZ Russia Pacific Myanmar India Vietnam Pacific Western Central - High seas Areas Indian Ocean Eastern - High seas Areas Indonesia (Eastern) China Pacific Northwest - High seas Areas Indonesia (Western) Bangladesh Norway Japan Main Isl. Iceland Philippines Pacific Southeast - High seas Areas Morocco Malaysia Sarawak Indian Ocean Western - High seas Areas Malaysia East Japan Outer Isl. Thailand Russia Barrents Sea Korea South Korea North Peru Alaska Malaysia West Western Sahara (Morocco) Pacific Eastern Central - High seas Areas Mauritania United Kingdom Chile Mexico Malaysia Sabah Nigeria Svalbard Isl. (Norway) Madagascar Sierra Leone Canada Guinea Greenland Pakistan Brazil Iran Denmark Greece Cameroon Atlantic Eastern Central - High seas Areas Namibia Spain Taiwan Papua New Guinea Atlantic Western Central - High seas Areas Atlantic Southwest - High seas Areas Senegal South Africa Gillnet catch year 2006 [tonnes] 1597186 1462590 1446008 1443049 789796 711725 639530 634024 566316 464922 436808 355914 272443 244520 225021 181062 155914 152563 146348 136132 132840 127672 118336 117830 117423 113138 106897 103973 103422 103354 100007 96557 95415 92509 83896 83033 82922 79545 73260 71751 67199 62073 59522 58648 58463 54471 51617 51171 49839 49115 48679 47546 45652 44471 42820 39315 38101 32 Gillnet catch/ Total catch % 32 86 41 79 32 69 31 9 50 27 91 18 17 21 13 10 20 32 17 27 14 26 53 21 59 2 5 24 18 16 44 6 3 10 27 29 57 60 60 7 71 15 23 13 29 9 18 56 20 12 11 16 16 42 6 10 7 Gillnet catch Density [tonnes. km -2] 0.467 2.811 0.887 1.033 0.124 0.032 0.177 0.277 0.055 0.189 5.562 0.255 0.148 0.317 0.099 0.007 0.573 0.978 0.009 1.024 0.051 0.417 0.090 0.248 1.015 0.125 0.003 1.512 0.344 0.003 0.643 0.125 0.047 0.028 0.936 0.383 0.195 0.066 0.459 0.012 0.614 0.026 0.269 0.018 0.356 0.506 0.104 3.483 0.006 0.088 0.088 0.041 0.019 0.006 0.003 0.250 0.036 Cambodia Angola Pacific Southwest - High seas Areas Sweden Oman Guyana Somalia Yemen Saudi Arabia Persian Gulf Faeroe Isl.(Denmark) USA East Coast United Arab Emirates France Ecuador Australia Suriname Ireland Gabon Maldives Tunisia J. Fernandez, Felix and Ambrosio Isl. (Chile) Turkey Black Sea Turkey Mediterranean Sea Gambia Atlantic SouthEast - High seas Areas New Zealand Desventuradas Isl.(Chile) Algeria Poland Italy Ghana Venezuela Atlantic Northeast - High seas Areas Atlantic Northwest - High seas Areas Canary Isl.(Spain) Bahrain Croatia Andaman & Nicobar Isl. (India) Solomon Isl. Pacific Northeast - High seas Areas Fiji Tanzania Sudan Colombia Jan Mayen Isl. (Norway) Saudi Arabia Red Sea Germany Argentina Jamaica Kuwait Libya Sri Lanka Finland USA West Coast Egypt Haiti Netherlands Cote d'Ivoire USA Golf Of Mexico Portugal Latvia Galapagos Isl.(Ecuador) Dominican Rep. Russia Baltic Sea Kaliningrad Mauritius Cuba Congo Republic Uruguay Ukraine Kiribati 37400 36712 36354 32956 31791 31375 28805 28370 25789 25504 25412 25198 24526 23154 21886 19061 18776 18454 18353 17745 17658 16993 15979 15771 15361 15334 14906 14712 13889 12944 12915 12711 11117 11107 10801 10057 9723 9719 9646 9281 9063 8343 8264 7741 7641 7620 7566 7322 7100 6522 6456 6445 6444 6317 6139 5833 5599 5557 5352 4839 4798 4636 4587 4190 4178 4075 3973 3794 3609 3527 33 63 18 16 11 21 59 88 20 26 4 2 29 7 14 13 63 3 43 10 16 14 7 5 49 10 4 13 10 19 10 5 4 2 6 16 33 10 24 48 13 51 35 46 17 25 19 11 1 56 43 47 27 8 1 32 72 5 23 1 4 6 8 42 10 12 20 16 4 16 15 0.782 0.073 0.002 0.194 0.059 0.231 0.035 0.052 0.758 0.095 0.028 0.441 0.073 0.098 0.003 0.149 0.046 0.095 0.020 0.173 0.035 0.099 0.191 0.697 0.001 0.004 0.033 0.114 0.440 0.024 0.057 0.027 0.002 0.004 0.024 1.132 0.172 0.015 0.006 0.002 0.007 0.035 0.094 0.009 0.026 0.041 0.132 0.007 0.027 0.533 0.018 0.012 0.071 0.008 0.023 0.052 0.088 0.032 0.008 0.015 0.150 0.006 0.017 0.360 0.003 0.011 0.098 0.029 0.025 0.001 Qatar Russia Siberia Easter Isl.(Chile) Hong Kong Panama Singapore French Guyana Mozambique Mayotte (FR) Lebanon French Polynesia Brunei Cape Verde Estonia Malta Lithuania Congo Cyprus Israel Eritrea Navassa Isl. (Haiti) Albania Honduras Martinique Lord Howe Isl. (Australia) Montenegro Liberia Trinidad & Matin Isl (BR) Sao Tome & Principe Benin Micronesia Togo Trinidad & Tobago Channel Isl.(UK) Costa Rica Madeira Isl.(Portugal) Brit. Virgin Isl.(UK) Azores Isl.(Portugal) Guadeloupe (FR) Kenya Christmas Isl.(Australia) Syria Macau (China) El Salvador Cocos Isl.(Australia) St Lucia Puerto Rico (US) Dominica Russia Black Sea Equatorial Guinea Vanuatu Gaza Strip New Caledonia Marshall Isl. Seychelles Timor Leste Guinea-Bissau Wallis & Futuna (FR) Tuvalu Russia Baltic Sea St Petersburg Nicaragua Antigua & Barbuda Palau Comoros Isl. Haiwaii NorthWest Isl. Anguila (UK) Falkland Isl.(UK) St Paul & Amsterdam (FR) Belgium St Pierre & Miquelon (FR) 3014 2891 2864 2686 2680 2514 2256 2047 2022 1866 1863 1750 1738 1727 1670 1568 1533 1506 1387 1329 1267 1251 1251 1175 1133 1062 1045 1018 902 895 895 855 843 837 826 804 803 778 654 619 617 603 594 592 560 556 500 494 488 466 427 421 417 396 377 343 331 323 279 275 241 215 213 207 206 180 165 161 159 152 34 18 35 7 5 3 8 44 8 33 22 18 73 25 3 15 7 33 18 24 15 78 38 34 31 35 15 10 22 18 11 4 5 20 3 18 10 62 5 6 23 43 18 3 3 39 37 11 16 5 22 3 21 13 4 1 94 3 50 14 2 1 7 5 4 7 72 0 11 3 42 0.095 0.001 0.004 1.281 0.008 3.055 0.017 0.004 0.032 0.097 0.000 0.069 0.002 0.043 0.030 0.257 1.430 0.015 0.051 0.017 0.110 0.112 0.005 0.025 0.002 0.143 0.004 0.002 0.005 0.030 0.000 0.056 0.011 0.072 0.001 0.002 0.010 0.001 0.007 0.006 0.002 0.059 14.488 0.006 0.001 0.036 0.003 0.017 0.007 0.002 0.001 0.163 0.000 0.000 0.000 0.004 0.003 0.001 0.000 0.022 0.002 0.002 0.000 0.001 0.000 0.002 0.000 0.000 0.046 0.012 Mozambique Channel Isl. (FR) Haiwaii Main Isl. Grenada Ascencion Isl. Iraq Tonga St Vincent & The Grenadines Monaco American Samoa Norfolk Isl. (Australia) Windward Netherlands Antilles Arctic Sea - High seas Areas Cook Isl.(NZ) St Kitts & Nevis Indian Ocean Antarctic - High seas Areas Bahamas Brit. Indian Oce (UK) Guam (US) Montserrat (UK) Djibouti Barbados Bosnia Tromelin Isl.(FR) Crozet Isl.(FR) Leeward Netherland Antilles Palmyra Atoll & Kingman Reef (US) Cayman Isl.(UK) Reunion (FR) Jordan Johnston Atoll (US) Northern Marianas (US) Kerguelen Isl. (FR) Nauru Jarvis Isl.(US) Slovenia Bermuda (UK) Bulgaria Romania Tokelau (NZ) Guatemala Belize Georgia Prince Edward Isl. (SA) Clipperton Isl.(FR) Pitcairn (UK) Samoa Niue (NZ) St Helena (UK) Howland & Baker Isl.(US) Atlantic Antarctic - High seas Areas South Georgia & Sandwich Isl. (UK) Macquarie Isl.(Australia) Bouvet Isl.(Norway) Gibraltar (UK) Heard & McDonald Isl.(Australia) Turks & Caicos Isl. (UK) Wake Isl.(US) Pacific Antarctic - High seas Areas 149 145 128 122 107 103 91 86 75 69 69 69 69 67 64 58 56 54 50 50 46 45 42 41 40 37 35 24 22 21 16 16 15 14 14 13 12 10 8 7 5 4 4 4 3 3 1 1 1 1 0 0 0 0 0 0 0 0 35 2 3 12 12 26 15 59 11 6 33 93 88 15 15 4 1 5 2 100 19 17 8 1 5 28 4 100 1 14 3 0 0 1 2 2 8 5 17 31 1 0 5 3 0 100 1 33 2 0 0 0 0 0 0 0 0 0 0 0.000 0.000 0.005 0.000 0.179 0.000 0.003 0.302 0.000 0.000 0.006 0.000 0.000 0.007 0.000 0.000 0.000 0.000 0.007 0.007 0.000 3.214 0.000 0.000 0.001 0.000 0.000 0.000 0.232 0.000 0.000 0.000 0.000 0.000 0.075 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 EEZs in South Asia and South East Asia were c haracterized by a great variety of small scale/art isanal g illnet f is heries operat ing essent ially in coastal ins hore areas and , est uaries, target ing a w ide range of s pec ies. During the last decade, the smallÁscale f is heries beca me more and more mec hanized as many boats were equipped out board motors he coastal f is hing co mmunit ies of these reg ions have been severely impacted . T by the s una mi of ece mber 2004 T D . yanmar. Drift nets and g illnets are co mmonly used in Myanmar to f is h pelag ic s pec ies (f inf is h) and de mersal f is h s uc h as marine catf is h and j ewf is h and s hrimps (Proj ect G lo bal 2011). T he g illnet landed catc h was one the hig hest of the world in 2006 (1.46 million tonnes). T he g illnet catc h has almost t ripled in the last decade (0.48 million tonnes in 1996, 1.46 million tonnes in 2006, SAUP 2011). ‚ M angladesh. T he Banglades hi g illnet f is heries consisted most ly of art isanal g illnet d rift nets and set nets target ing de mersal f is h, I ndian salmon and s hrimps hese g illnets are operated between 8 m and 30 m depth in ins hore .T areas all year round excepted d uring the monsoon period (Hossa in 2004). d d i sd b di s( 8 s i 996 and T he g llnet lan e catc h ha ou le n 10 year 25 ,000 tonne n 1 437 000 tonnes in 2006) (SAUP 2011) and many of the targeted s pec ies have , been overÁexplo ited (Khan et al 200 3) Banglades h is one of the j urisdict ions . . w ith the hig hest density of g illnet catc h per km2. ‚ B ndia. I ndia f is heries relied heav ily on coastal art isanal g illnet f is heries (4 1% of the total catc h in 2006) (SAUP 2011). So me rev iews of f is hing cent res in I ndia indicated the use of motorized boats up to 15 m long deploy ing g illnets a bout 0. 5Á6 km long up to 70 km fro m the coast (Yous uf 2008). T he g illnet landed catc h has doubled in the last 10 years (0.68 million tonnes in 1996, 1.44 million tonnes in 2006) (SAUP 2011). ‚ I ietnam. he g illnet landed catc h in 2006 consisted of more than 86% of the T total landed catc h in 2006. It has increased by 4 5% d uring the years 1996 Á 2006 (SAUP 2011). T he g illnet f is hing density was a mong the hig hest in the world. T he number of g illnet boats and d rift net boats (non mec hanized and mec hanized) were est imated to be greater than 28000 in 2005 ( ung 2006) D . ‚ V 36 o a. Indo nesia is o ne the to p 5 j urisd ict io ns fo r g illnet catch w ith mo re ‚ Ind nesi tha n 1. 1 millio n to nnes fo r the yea r 2006 (Table 2). Indo nesia n f is he ries a re ext re me ly d ive rse. Fis he ries a re most ly s ma ll sca le invo lv ing nume ro us unpowe red a nd powe red s ma ll sized vesse l (334202 boats in 1998) ost of . M the unpowe red boats we re o pe rated in the v ic inity of coasta l v illages by 3 5 f is he rmen a nd a w ide va riety of gea r inc lud ing g illnets. T he f is hing secto r re presented 2 millio n f is he rmen in 1998 ( AO 20 11) ll r pr d F . G i net catch e esente ~30% of the tota l catch fo r both Weste rn a nd Easte rn Indo nesia. G illnet catch inc reased stead ily by abo ut 4% d uring the last 5 yea rs in both Easte rn a nd Weste rn Indo nesia (SAUP 20 11). ll d d rift nets a re abunda nt ly used in the No rthwest Pac if ic to catch Sockeye, G i nets a n Pink a nd C hum sa lmo n a nd sq uids 566 000 to nnes of f is h a nd sq uids we re ca ug ht w ith . g illnets a nd d rift net in 2006, re present ing ha lf of the tota l catch Since 1997, the tota l . catch a nd the g illnet catch has dec reased pro po rt io na lly by 50% (SAUP 20 11). acific Russia EEZ. G illnet act iv ity in the Pac if ic Russia EEZ is essent ia lly do minated by Russia n a nd Ja pa nese la rge sca le d rift net f is he ries ta rget ing Sockeye, Pink a nd C hum sa lmo ns a nd sq uids (Artukhin et al 20 10) Russia was . . o ne of the few j urisd ict io ns st ill a llow ing lo ng d rift net f is hing in its EEZ T hose . la rge sca le f is he ries co mpeted st ro ngly w ith a rt isa na l/s ma ll sca le f is he ries d ue to the de plet io n of the f is hing stock ‚ P . a. (so urce FAO 20 11) W ith 6 34000 to nnes of g illnet catch, C hina is o ne ‚ Chin of the most impo rta nt playe rs in g illnet f is he ries (SAUP 20 11) In 2004, the . r g l o C o d o 2 o o r d 9 9 37 7 ma ine f is hin f eet f hina c nsiste f m t ize vesse ls, s how ing litt le cha nge f ro m 1999 T he a reas in which the vesse ls o pe rated inc luded the . o l j ur d o o nat i na is ict i n f C hina a nd othe r a reas unde r agree ments between C hina a nd the East Asia n j urisd ict io ns (inc lud ing Ja pa n, Re public of Ko rea a nd V iet nam), as we ll as o n the hig h seas Tota l f leet powe r was 13 74 millio n kW . . . In 2004, the most co mmo n f is hing gea r used was the t raw l net. In te rms of 37 production, t rawlers accounted for 47.6% of catch, g illnets accounted for around 17%, set nets 15%, lines and hooks 6%, purse se ines 5. 3%, and ot her f ishing gears 9%. Compared w it h 1999, t he t rawl catch was s imilar, but t he proportion of g illnet, lines and hooks and purse se ines increased, while t he proportion of set nets and ot her f ishing gear decreased. T he catch in 2004 i t t i i i t ti i i ti bas cally reflec ed he ma n f shery resources n he na onal j ur sd c on of Z i t i t i i it i t C h na. O u s de he C h nese EE area, squ d, ha r a l, Jack mackerel and unas were t he ma in target stocks. I n 2004, t here were 4060 marine f ishery v illages, 82 more t han in 1999 and t here were 3 32 million t rad itional f ishermen in , . ’ i i i i i i i t t i C h na s mar ne f sher es. F shery v llages were ma nly concen ra ed n Shandon 946) uan on 896) Z hej ian 6 54) uj ian 522) iaonin 410) g ( ,G g g ( , g ( , F ( , L g ( 0) i i i t t t i t and Ha nan (29 . Fuj an prov nce had he g rea es number n erms of t rad itional f ishermen 900 000) followed y uan don 660 000) Shandon ( , b G g g ( , g 80 000) 380 000) 80 000) 80 000) Z i i i i and L aon ng (1 (5 , hej ang ( , Ha nan (2 . apan: T he FAO prof ilme was not ava ila ble for t his j urid iction at t he time of ‚ J writing. rway (source FAO 20 11) T he fleet was comprised of 9,9 31 vessels in 2003. ‚ No 3 6 i t t t i T h s was 25 per cen less han 1999 when here were 1 , 19 vessels. T he ma n spec ies targeted by t hese vessels were cod and herring. T he fleet is d iv ided into coastal and offshore administ rative cate ories i i g . Offshore f sher es are purse se iners, long liners and t rawlers. T he coastal fleet cons ists of relatively small vessels, most ly between e ig ht and 13 met res long. T he coastal fleet t t i it i t i i i i generally arge s demersal spec es w h a var e y of f sh ng gear, nclud ng i t i i i i t i i g llne s, handl nes, long l nes and Dan sh se nes. Cod were he ma n spec es t i t i bo h n erms of volume and value, followed by haddock, ang lerf sh and sa it he. T hese vessels were operated by 12 f ishermen and were on average 10. 5 g ross tonnage. land source celand ic isheries 20 11) illnets were ma inly used y small G b . ( I F ‚ Ice to intermed iate s ized oats s imilar in s ize to lon liners Each net is a out 50 b , g b . 0 ) t t t ti t t m long, bu a few (of en around 1 m ne s are ed oge her and a number of such units placed by each ship. T he nets are left to soak for one nig ht, 38 preferably not longer to maintain the quality of the catch. G illnets are used extensively during the late winter season when the cod is migrating to the spawning grounds. T hese fisheries begin in January, reach a peak in March and end in May. G illnets are used all around Iceland but by far the most important grounds are south Iceland and south west Iceland where the main spawning grounds are found (Figure 8). Cod is the primary target for gillnets as with so many other fishing gears, but large amounts of saithe are also fished, as well as lesser amounts of haddock, monkfish, ling. Besides cod gillnets, many specialized versions of bottom gillnets are also used, mainly differing in mesh size. For example, there are nets optimized for haddock (140½150 mm mesh size), lumpsuckers (180½270 mm), flatfish (165½200 mm) and Atlantic halibut (460 mm). Except for the lumpsucker nets, none of these are in large scale use. Common gillnets used in cod fisheries have a 140 to 204 mm mesh size the former being the minimum allowed in most grounds , . All of these nets are bottom gillnets. Driftnets have only been used in Herring fisheries (63 mm mesh size) and only prior to 1987 (G unnarsson et al. 1998, Kristjá nsson 198 3 ó r 2002 ó r 2003 ó r 2005) ,Þ ,Þ ,Þ Figure 8 Ò Location of effort with gillnets i n 2008 (sets), dark areas i ndicate hig hest effort (source Ice landic Fis heries 2011). mall scale fisheries in Peru are widespread and numerous (>100 ports, ‚ Peru. S >9500 vessels, >37000 fishermen) and operate industrial along the Peruvian 39 coastline (A lfaroþShigueto et al. 20 11). T he s mall scale fis heries have ra pid ly expanded in recent decades (i. e. 34% and 54% increase in t he number of fis hermen and vessels (A lfaroþShigueto et al 0 10) he ma in fis hing gear .2 . T cons ists of a variety of met hod includ ing g illnets, d riftnets, tra mmel nets and botto m setnets (A lfaroþShigueto et al. 20 11). T he s mall scale fis heries are primarily export oriented and all s pec ies are used ind iscriminately in fis hmeal prod uct ion, adversely affect ing marine biod ivers ity, conf lict ing also w it h art isanal s ubs istence fis heries occ urring w it hin 5 miles f ro m t he coast (Sue iro 00 5) he est imated g illnet landed catc h was 11 000 tonnes for 006 . T 3 2 , h i i i i 0 rank ng Peru a mong t e to p 2 most mportant g llnet contr butors g lo bally (SA UP 0 11) 2 2 . ile. G illnett ing is a co mmonly used art isanal and large scale fis hing met hod ‚ Ch in t he EEZ of Chile he g illnet fis heries cons ist of art isanal/ large scale d riftnet .T fis heries and art isanal coastal g illnets arge scale d riftnets target ma inly . L swordfis h. T he d riftnets mig ht range between 2.4 km and 4.3 km long, 60 m dee p des pite t he offic ial limitat ion of 47 km (We id ner and Serrano 1997) , 2. . I nd ustrial d riftnet fis heries o perate w it h boats between 18 m and 7 m long 3 . he number of vessels in t he ind ustrial f leet has red uced by one order of T mag nit ude between 1991 and 200 3 (IFO P 2006). A rt isanal d riftnets fis heries use s horter d riftnets up to 1.8 km long and 4 5 m dee p w it h a mes h s ize a bo ut 5 c m ident ical to ind ustrial d riftnet (We id ner and Serrano 1997) o perated by , 3 , f h d if 9 18 I s maller boats o þ m. n bot cases, r tnets are set between 9 m and 60 m de pt h. T he coastal art isanal g illnets are o perated by s maller boats w it h s maller mes h (20 c m) set at 1 to 2 miles f ro m t he s hore. T he art isanal g illnet ma inly targets are j ac k mac kerel, sard ines and anc hov ies. T he re ported landed catc h of t he SUBPESCA ind icated t hat t hese art isanal g illnet fis heries were t he ma in contributor of all Chilean g illnet fis heries (4 37,000 tonnes of fis h ca ug ht in 00 5 þ 006 co mpared to ~ 000 tonnes of fis h ca ug ht by d riftnets in 1995) 2 2 3 (SUBPESCA 2006). fi h i f h di dB i i i T e Me terranean an lac k Sea g llnet s er es cons st mostly o s mall scale art sanal fis heries o perat ing w it hin 1 miles of t he s hore 80% of t he Euro pean fis hing vessels are 2 . 40 <12m long (~33000 boats). The fis hing met hods are diverse traw ls, driftnets, gillnets, purse seines and long lines and many boats use multiple gear types (A nc ha 2008). G illnets are most ly used for ins hore fis heries but a lso in hig h seas area targeting hig h va lue species (e.g merlin, bluefin tuna, Black Sea turbot). The European Union banned pe lagic driftnet in 2002 however nonY European Union countries increasing ly use t he m in t he Mediterranean (OC EANA 2006). Illega l large sca le swordfis h driftnets fis heries are still operating a ll year long in severa l Mediterranean areas suc h as t he Alboran Sea. Genera l Fis heries Co mmission for t he Mediterranean adopted a binding reso lution w here driftnets of any lengt h were pro hibited for capturing large migratory species. However co mpliance wit h t hese agree ment is far to be co mplete and illega l fis h is still reported to occur according to OC EANA, (OC EANA 2009, EJF 2007, Secretary of Co mmerce of t he United State 2008). I n terms of gillnet fis heries in t he Mediterranean G reece has t he largest f leet wit h 21000 , boats and is a lso t he main European gillnet catc h contributor (Gerosa and Casa le 1999 ). France has 742 boats of an average lengt h of 7mY9m using gillnet driftnet encirc ling , , nets to target brea ms, so le hake, red mullets and crustacean in t he Mediterranean invo lving ~1000 fis hermen (IFREMER 2011). T urkey is a lso an important gillnet player wit h t he lack Sea turbot fis hery invo lving 185 B boats operating 19000 botto m gillnets fro m six ports in western T urkey (Oztürk 2001) Morocco Mediterranean fis heries was t he bulk of large sca le driftnet fis hing nations wit h a f leet invo lving 117 vesse ls using driftnets up to 14 km long (T ude la et a l. 2005). However t he Moroccan Government is phasing out of Morocco’s driftnet f leet under t he EUYMorocco Fis heries Partners hip Agree ment and initiatives wit h t he United State (Secretary of Co mmerce of t he United States 2008) orocco. I n its At lantic fis heries, Morocco wit h 259,000 tonnes of gillnet catc h in 2006 is one of t he 10 biggest contributors of gillnet catc h g lo ba lly. Morocco's gillnet fis heries are represented by an artisana l fis hery sector operating in coasta l areas and large sca le driftnet swordfis h fis hery operating in t he Mediterranean described previous ly. The artisana l fis hery consists of around 18000 s ma ll wooden boats (<6m long) wit h out board engines. The ‚ M 41 main fishing gear used are gillnets to catch sma ll species. Most of the catch supplies loca l markets (Franquesa et a l. 2001). auritania. (source FAO 2011) W ith 100000 tonnes of fish caught with gillnets in 2006, Mauritania is an important player in gillnet bycatch. ll l ll l l Mauritanian gi net fisheries are most y sma sca e/artisana fisheries supplying loca l markets. T he artisana l fishing sector consisted in 3000 dugout boats and 10000 fishermen. ‚ M uth Africa. Gillnets used in South Africa consist only of the shark gillnet fishery. T hey are used to protect the swimmers from shark attacks. T he overa ll length of shark nets is 27 km deployed in 38 loca lities hey are usua lly set .5 . T at 400 m from the coast in sha llow water, in 2 or 3 rows. T he dimension of the net ranged between 200 m and 300 m in length with wide stretched mesh (50cm) (Kwazulu®Nata l Sharks Board 2011). ‚ So w Zealand. (source: New Zea land Ministry of Fishery 2011). Gillnet fisheries in New Zea land were most ly represented by setnet fisheries (6278 tonnes in 2006) and inshore driftnet fisheries (44 tonnes in 2006) he number of vesse ls .T ll l 4 7 participating in gi netting in New Zea and was 5 in 2006 but decreased to 304 vesse ls in 2009. 87% of those vesse ls were less than 12 m long. T he top 5 targets species by tota l net length in order were: f latfish, rig, schoo l shark, grey mullet and tarakihi. T he number of fishing events by net length, mesh size and net height are presented in the Table 3. T he distribution of the gillnet catch for the period 2006 ®2010 is presented in Figure 9. ‚ Ne 42 Table 3 Ã The size of gi llnets used i n New Zealand by count of fis hi ng event (source New Zealand Mi nist ry of Fis hery 2011). Measure Total net length (m) Net height (m) Mesh Size (mm) Category <400 400 to <600 600 to <800 800 to <1000 1000 to <1200 Over 1200 Unknown <2 2 to <2.6 2.6 to <3 3 to <4 4 & over Unknown <120 120 to <125 125 to <130 130 to <175 175 & over Unknown 2006/2007 4,151 4,642 5,007 3,674 4,468 4,716 3 1,628 1,611 1,358 2,369 1,782 17,913 5,114 4,196 7,858 6,143 2,833 517 2007/2008 3,630 3,794 4,688 3,180 3,540 4,111 2008/2009 3,017 4,317 4,163 3,455 3,588 3,916 1,561 1,377 1,744 1,923 1,903 14,435 4,645 3,343 6,881 4,868 2,726 480 1,538 1,121 1,553 1,606 2,107 14,531 5,129 2,598 6,919 4,523 2,476 811 2009/2010 3,028 4,302 4,283 4,064 3,986 4,144 4 1,637 1,234 1,730 1,642 2,064 15,504 5,237 2,465 8,119 4,427 2,854 709 Table 4 Ã The number of gi llnet captures reported by fis hermenwithi n New Zealand EEZ for species listed by the Conventionon Migratory Species (source New Zealand Mi nist ry of Fis hery 2011). Species Name Common dolphin Dusky dolphin Green Turtle Humpback Whale Dolphins and Toothed Whales White Pointer Shark Southern Giant Petrel White -chinned Petrel 2008/2009 1 0 1 1 3 3 1 0 2009/2010 3 1 0 0 0 5 0 1 43 Figure 9 ì Total estimated catch for all gi llnetti ng events for t he period 2006 ì2010 i n t he New Zealand EEZ (source New Zealand Mi nistry of Fis hery 2011). The total number of captures for t he CMS species reported by fis hermen since t he introduction of t he nonfis h protected species catc h return are detailed in Table 4. 44 The analysis outputs were presented in tabular form and ma pped to s how relat ive ex posure levels wit hin eac h EEZ. For all s pecies summed, Figure 10 s hows t he areas w here most ex posure occurs (red colours). Figure 10 J EEZs and High Seas FAO areas s howi ng with the IUCN weighted exposures summed across species. A reas with colours furthest up the scale bar (red colours) had higher species exposures. The 30 EEZs having t he hig hest ex posure, for t he sum of all s pecies was ex plored (Table 5). 45 Table 5 p EEZ and high seas FAO areas prese nting t he highest ex posu re fo r all species (to p 30 ranked j u risdictio ns in desce nding o rde r of impo rtance). Sum of all species IUCN weighted exposures in the EEZ Rank 1 EEZ or high seas FAO area Myanmar 1.54 2 Vietnam 1.52 3 Peru 1.49 4 India 1.43 5 Russia Pacific 1.29 6 Chile 1.28 7 South Africa 1.27 8 China 1.27 9 Namibia 1.25 10 Greece 1.20 Galapagos Isl.(Ecuador) 1.16 Bangladesh 1.13 11 12 13 14 Japan Main Isl. 1.12 Indonesia (Western) 1.11 1.07 15 Indonesia (Eastern) 16 Norway 1.06 17 Mauritania 1.01 18 United Kingdom 0.99 19 Algeria 0.98 20 Morocco 0.95 21 Western Sahara (Morocco) 0.95 22 Pacific Western Central - High seas Areas 0.92 23 Iceland 0.91 24 Tunisia 0.87 Japan Outer Isl. 0.86 26 Turkey Mediterranean Sea 0.85 27 Pacific Northwest - High seas Areas 0.85 28 Philippines 0.84 29 Bahrain 0.83 30 Korea South 0.81 25 The most exposed species, using t he IUCN weig hted o utcomes were sorted into 3 categories; most exposed (pink), moderately exposed (green) and least exposed (blue). A ll five species gro ups in t he st udy were represented wit hin t he top 40 most exposed species to gillnet fis hing (Ta ble 6). 46 Table 6 ¹Species ranked by IUCN¹weighted exposure. All species. T hose marked wit h pink shading are t he most exposed 40 species, t hose shaded green were t he moderately exposed 40 species, and t hose shaded blue t he least exposed species Rank 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 Species code NPH ORB MMN SPD DUG EIM LPK PEG DCC LOF EBJ POT EBG SYW PTG PIR PHG CAC CHM SPH TUA LPV CEH BOB BAP BMU PUM SOC CTM IPA POS PHA PUC RHT LOP BEB CCC BAO LMN LAU IOX PYM DIM PCR POB PHN HYA Family cetacean cetacean marine mammals other seabirds cetacean turtle turtle seabirds turtle marine mammals other cetacean cetacean cetacean seabirds seabirds seabirds seabirds turtle turtle seabirds cetacean turtle cetacean cetacean cetacean cetacean seabirds cetacean shark shark cetacean seabirds seabirds shark marine mammals other cetacean shark cetacean shark seabirds shark cetacean seabirds seabirds cetacean seabirds cetacean species Neophocaena phocaenoides Orcaella brevirostris Monachus monachus Spheniscus demersus Dugong dugon Eretmochelys imbricata Lepidochelys kempii Pelecanoides garnotii Dermochelys coriacea Lontra felina Eubalaena japonica Sousa teuszii Eubalaena glacialis Synthliboramphus wumizusume Pterodroma phaeopygia Phoebastria_irrorata Phalacrocorax nigrogularis Caretta caretta Chelonia mydas Spheniscus humboldti Tursiops aduncus Lepidochelys olivacea Cephalorhynchus heavisidii Balaenoptera borealis Balaenoptera physalus Balaenoptera musculus Puffinus mauretanicus Sousa chinensis Cetorhinus maximus Isurus paucus Phocoena spinipinnis Phoebastria_albatrus Puffinus creatopus Rhincodon typus Lontra provocax Berardius bairdii Carcharodon carcharias Balaenoptera omurai Lamna nasus Larus audouinii Isurus oxyrinchus Physeter macrocephalus Thalassarche_melanophrys Pelecanus crispus Pontoporia blainvillei Phoebastria_nigripes Hyperoodon ampullatus 47 Common name Finless Porpoise Irrawaddy Dolphin Mediterranean Monk Seal African Penguin Dugong Sea Cow Dugong Hawksbill Turtle Kemp's Ridley Turtle Peruvian diving petrel Leatherback Turtle Marine Otter North Pacific Right Whale Atlantic Hump-backed Dolphin Northern Right Whale Japanese Murrelet Dark-rumped Petrel Waved Albatross Socotra Cormorant Loggerhead Turtle Green Turtle Humboldt Penguin Indian or Bottlenose Dolphin Ridley Turtle Heaviside's Dolphin Sei Whale Fin Whale Blue Whale Balearic shearwater Indo-Pacific Humpbacked Dolphin Basking shark Longfin Mako shark Burmeister Porpoise Short-tailed Albatross Pink-footed Shearwater Whale Shark Southern River Otter Baird's Beaked Whale Great White Shark Omura' Whale Porbeagle shark Audouin's Gull Shortfin Mako shark Sperm Whale Black-browed Albatross Dalmatian Pelican La Plata Dolphin Black-footed Albatross Northern Bottlenose Whale IUCN weighted exposure 2.466 2.421 2.204 2.201 2.164 2.073 2.009 1.972 1.965 1.852 1.842 1.795 1.779 1.762 1.743 1.642 1.592 1.572 1.484 1.466 1.433 1.386 1.383 1.369 1.366 1.324 1.269 1.267 1.234 1.140 1.131 1.131 1.116 1.113 1.102 1.097 1.094 1.094 1.090 1.085 1.075 1.019 1.004 0.972 0.971 0.941 0.915 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 SNL CEE OOR PHF THH LAT LGO DEL LGS SNC LLE STM PCW GLM MMO PRK CEC PRO DIC POW DIP DIX PHI PCO BAB POD HGR LIC PTT POP LGE DNB PHV LML BAM SBG LHM DAL LGA LGB THC PCI ORH GRG LAA PCC DDE LGH OFL PHE SNA SNR TUT MNV EBA MAI MAH cetacean cetacean cetacean seabirds seabirds seabirds cetacean cetacean cetacean cetacean seabirds seabirds seabirds cetacean cetacean seabirds cetacean seabirds seabirds seabirds seabirds seabirds seabirds seabirds cetacean cetacean marine mammals other seabirds seabirds cetacean seabirds seabirds marine mammals other seabirds cetacean seabirds seabirds cetacean cetacean cetacean seabirds seabirds cetacean cetacean seabirds seabirds cetacean cetacean marine mammals other seabirds cetacean cetacean cetacean cetacean cetacean seabirds seabirds Stenella longirostris Cephalorhynchus eutropia Orcinus orca Phoebetria fusca Thalassarche_chlororhynchos Larus atlanticus Lagenorhynchus obscurus Delphinapterus leucas Lagenorhynchus australis Stenella clymene Larus leucophthalmus Sterna maxima Procellaria westlandica Globicephala melas Monodon monoceros Procellaria parkinsoni Cephalorhynchus commersonii Procellaria aequinoctialis Thalassarche_chrysostoma Pterodroma cahow Diomedea epomophora Diomedea exulans Phoebastria_immutabilis Procellaria conspicillata Balaenoptera bonaerensis Phocoena dioptrica Halichoerus grypus Larus ichthyaetus Pterodroma atrata Phocoena phocoena Larus genei Thalassarche_bulleri Phoca vitulina Larus melanocephalus Balaena mysticetus Sterna bergii Larus hemprichii Phocoenoides dalli Lagenorhynchus acutus Lagenorhynchus albirostris Thalassarche_cauta Procellaria cinerea Orcaella heinsohni Grampus griseus Larus armenicus Pelecanus onocrotalus Delphinus delphis Lagenodelphis hosei Arctocephalus australis Phoebetria palpebrata Stenella attenuata Stenella coeruleoalba Tursiops truncatus Megaptera novaeangliae Eubalaena australis Macronectes giganteus Macronectes halli 48 Spinner Dolphin Chilean Dolphin Killer whale Sooty Albatross Yellow-nosed Albatross Olrog's Gull Dusky Dolphin White Whale Peale's Dolphin Clymene dolphin White-eyed Gull Royal Tern Westland Petrel Long-finned Pilot Whale Narwhal Black Petrel Commerson's Dolphin White-chinned Petrel Grey-headed Albatross Cahow Bermuda Petrel Royal Albatross Wandering Albatross Laysan Albatross Spectacled Petrel Antarctic Minke whale Spectacled Porpoise Grey Seal Great Black-headed Gull Henderson Petrel Common Porpoise Slender-billed Gull Buller's Albatross Common Seal Mediterranean Gull Bowhead Whale Great Crested Tern Sooty Gull Dall's Porpoise Atlantic White-sided Dolphin White-beaked Dolphin Shy Albatross Grey Petrel Australian Snubfin dolphin Risso's Dolphin Armenian Gull White Pelican Common Dolphin Fraser's Dolphin South American Seal Light-mantled Sooty Albatross Pantropical Spotted Dolphin Striped Dolphin Bottlenosed Dolphin Humpback Whale Southern Right Whale Southern Giant Petrel Northern Giant Petrel 0.906 0.852 0.849 0.830 0.829 0.816 0.764 0.764 0.754 0.752 0.748 0.720 0.718 0.678 0.675 0.658 0.636 0.621 0.592 0.591 0.584 0.575 0.571 0.564 0.549 0.530 0.522 0.518 0.511 0.504 0.485 0.471 0.470 0.462 0.448 0.429 0.428 0.428 0.419 0.417 0.408 0.405 0.402 0.399 0.390 0.384 0.373 0.372 0.369 0.364 0.361 0.355 0.351 0.341 0.235 0.195 0.191 105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 120 121 122 123 PXP STB STI LSA DAM STE BAE LRL CAM STV STR STS STG STN STF SDG CAT STH STP seabirds seabirds seabirds seabirds seabirds seabirds cetacean seabirds cetacean seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds Phalacrocorax pygmeus Sterna bernsteini Sterna lorata Larus saundersi Diomedea amsterdamensis Sterna balaenarum Balaenoptera edeni Larus relictus Caperea marginata Sterna sandvicensis Sterna repressa Sterna saundersi Sterna bengalensis Sterna nilotica Sterna albifrons Sterna dougallii Sterna caspia Sterna hirundo Sterna paradisaea Pygmy Cormorant Chinese Crested Tern Peruvian tern Saunder's Gull Amsterdam Albatross Damara Tern Bryde's whale Relict Gull Pygmy Right whale Sandwich Tern White-cheeked Tern Saunder's Tern Lesser Crested Tern Gull-billed Tern Little Tern Roseate Tern Caspian Tern Common Tern Arctic Tern 0.184 0.024 0.024 0.020 0.012 0.011 0.009 0.006 0.006 0.006 0.005 0.005 0.005 0.005 0.005 0.005 0.005 0.004 0.002 The res ults in t his sect ion a re prese nted wit h a table of s pecies leve l rat ings fo r s ix s pecies g roups (cetaceans, seabirds, pinnipeds & otters, t urt les and s ha rks). The res ults in t he first table s ums t he expos ure fo r CMS s pecies ac ross all fis hery a reas; second t he info rmat ion is prese nted in map fo rm, dis playing t he s pat ial dist ribut ion of s ummed s pecies in t he g roup and plotted by EEZ; t hirdly, t he cont ribut ion of expos ure f rom eac h EEZ is tabulated, and t hose wit h t he g reatest cont ribut ion included. Cetaceans & Sirenians This s pecies g roup was most affected in Sout heast As ia, Sout h As ia, East As ia, No rt heast Pacific, No rt hern Europe and Sout h A merica (Figure 11). G illnet expos ure affects s maller coastal dwe lling s pecies as we ll la rge w hales (Table 7). Cetaceans a re s pread eve nly betwee n t he hig hest, medium and lowest ris k g roupings in Table 7. The EEZs w here t he expos ure occurred a re set out in Table 8. 49 Figure 11 : EEZs and High Seas FAO areas s howi ng wit h t he IUCN weighted exposures summed across cetaceans. A reas wit h colours furt hest up t he scale bar (red colours) had higher cetaceanexposures. 50 Table 7 _ Cetaceans ranked by thei r IUCN_weig hted exposure. Those ma rked with pink s hading a re the most exposed 40 species, those s haded gree n were the moderate ly exposed 40 species, and those s haded blue the least exposed species Rank 1 2 5 11 12 13 21 23 24 25 26 28 31 36 38 42 45 47 48 49 50 54 55 56 57 61 62 64 72 73 77 82 85 86 87 90 91 94 95 98 99 100 101 102 111 113 Species code NPH ORB DUG EBJ POT EBG TUA CEH BOB BAP BMU SOC POS BEB BAO PYM POB HYA SNL CEE OOR LGO DEL LGS SNC GLM MMO CEC BAB POD POP BAM DAL LGA LGB ORH GRG DDE LGH SNA SNR TUT MNV EBA BAE CAM Family cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean species Neophocaena phocaenoides Orcaella brevirostris Dugong dugon Eubalaena japonica Sousa teuszii Eubalaena glacialis Tursiops aduncus Cephalorhynchus heavisidii Balaenoptera borealis Balaenoptera physalus Balaenoptera musculus Sousa chinensis Phocoena spinipinnis Berardius bairdii Balaenoptera omurai Physeter macrocephalus Pontoporia blainvillei Hyperoodon ampullatus Stenella longirostris Cephalorhynchus eutropia Orcinus orca Lagenorhynchus obscurus Delphinapterus leucas Lagenorhynchus australis Stenella clymene Globicephala melas Monodon monoceros Cephalorhynchus commersonii Balaenoptera bonaerensis Phocoena dioptrica Phocoena phocoena Balaena mysticetus Phocoenoides dalli Lagenorhynchus acutus Lagenorhynchus albirostris Orcaella heinsohni Grampus griseus Delphinus delphis Lagenodelphis hosei Stenella attenuate Stenella coeruleoalba Tursiops truncatus Megaptera novaeangliae Eubalaena australis Balaenoptera edeni Caperea marginata Common name Finless Porpoise Irrawaddy Dolphin Dugong Sea Cow Dugong North Pacific Right Whale Atlantic Hump-backed Dolphin Northern Right Whale Indian or Bottlenose Dolphin Heaviside's Dolphin Sei Whale Fin Whale Blue Whale Indo-Pacific Humpbacked Dolphin Burmeister Porpoise Baird's Beaked Whale Omura' Whale Sperm Whale La Plata Dolphin Northern Bottlenose Whale Spinner Dolphin Chilean Dolphin Killer whale Dusky Dolphin White Whale Peale's Dolphin Clymene dolphin Long-finned Pilot Whale Narwhal Commerson's Dolphin Antarctic Minke whale Spectacled Porpoise Common Porpoise Bowhead Whale Dall's Porpoise Atlantic White-sided Dolphin White-beaked Dolphin Australian Snubfin dolphin Risso's Dolphin Common Dolphin Fraser's Dolphin Pantropical Spotted Dolphin Striped Dolphin Bottlenosed Dolphin Humpback Whale Southern Right Whale Bryde's whale Pygmy Right whale 51 IUCN weighted exposure 2.466 2.421 2.164 1.842 1.795 1.779 1.433 1.383 1.369 1.366 1.324 1.267 1.131 1.097 1.094 1.019 0.971 0.915 0.906 0.852 0.849 0.764 0.764 0.754 0.752 0.678 0.675 0.636 0.549 0.530 0.504 0.448 0.428 0.419 0.417 0.402 0.399 0.373 0.372 0.361 0.355 0.351 0.341 0.235 0.009 0.006 Table 8 EEZ and high seas FAO areas prese nting t he highest ex posure fo r all t he cetacean & sire nians listed in desce nding o rde r of impo rtance. EEZ or high seas FAO area Vietnam Myanmar India China Indonesia (Western) Russia Pacific Indonesia (Eastern) Japan Main Isl. Norway Bangladesh Chile Philippines Pacific Northwest - High Seas Areas Indian Ocean Eastern - High Seas Areas Iceland Malaysia Sarawak Korea South Malaysia East Malaysia Sabah Thailand Malaysia West Japan Outer Isl. Korea North Canada United Kingdom Angola Pacific Western Central - High Seas Areas South Africa Brazil Mauritania Cambodia Taiwan Peru Western Sahara (Morocco) Namibia Alaska Madagascar Argentina Australia Pacific Southeast - High Seas Areas Morocco Nigeria Pakistan Guinea Papua New Guinea Sierra Leone Mexico USA East Coast Greenland Indian Ocean Western - High Seas Areas Senegal Svalbard Isl. (Norway) Atlantic Southwest - High Seas Areas Cameroon Pacific Eastern Central - High Seas Areas Ireland Pacific Southwest - High Seas Areas Iran Russia Barrents Sea Faeroe Isl.(Denmark) France Sum of all cetacean and sirenian IUCN weighted exposures in the EEZ 1.000 0.953 0.903 0.801 0.751 0.743 0.733 0.655 0.642 0.635 0.571 0.570 0.549 0.536 0.521 0.518 0.516 0.507 0.502 0.502 0.497 0.486 0.468 0.419 0.416 0.405 0.403 0.394 0.388 0.386 0.384 0.383 0.378 0.374 0.373 0.373 0.354 0.348 0.340 0.333 0.328 0.324 0.322 0.317 0.317 0.317 0.309 0.309 0.308 0.306 0.297 0.296 0.291 0.289 0.288 0.283 0.278 0.276 0.273 0.265 0.265 52 Seabirds Seabirds are most affected by gillnet f ishing in Sout h A merica Sout h Af rica & Namibia , , New Zea land and nort heast Pacif ic (Figure 12). They are a lso hig hly exposed in most of t he sout hern and cent ra l hig h seas areas. The mode of interact ions wit h gillnets was apparent for t his s pecies group wit h many of t he d iving seabirds more exposed to gillnet f ishing t han s urface feeders (Table 9). Seabirds were represented in t he hig hest, med ium and least exposed groups. The expos ure in EEZs most cont ribut ing for seabirds is set out in Table 10. Figure 12 Õ EEZs and High Seas FAO areas s howi ng wit h t he IUCN weighted exposures summed across seabi rds. A reas wit h colours furt hest up t he scale bar (red colours) had higher seabi rd exposures. 53 Table 9 ú Seabird I UCNúweighted exposu re Rank 4 8 14 15 16 17 20 27 32 33 40 43 44 46 51 52 53 58 59 60 63 65 66 67 68 69 70 71 75 76 78 79 81 83 84 88 89 92 93 97 103 104 105 106 107 108 109 110 112 114 115 116 Species code PEG SYW PTG PIR PHG SPH PUM PHA PUC LAU DIM PCR PHN PHF THH LAT LLE STM PCW PRK PRO DIC POW DIP DIX PHI PCO LIC PTT LGE DNB LML SBG LHM THC PCI LAA PCC PHE MAI MAH PXP STB STI LSA DAM STE LRL STV STR STS STG Family seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds species Pelecanoides garnotii Synthliboramphus wumizusume Pterodroma phaeopygia Phoebastria_irrorata Phalacrocorax nigrogularis Spheniscus humboldti Puffinus mauretanicus Phoebastria_albatrus Puffinus creatopus Larus audouinii Thalassarche_melanophrys Pelecanus crispus Phoebastria_nigripes Phoebetria fusca Thalassarche_chlororhynchos Larus atlanticus Larus leucophthalmus Sterna maxima Procellaria westlandica Procellaria parkinsoni Procellaria aequinoctialis Thalassarche_chrysostoma Pterodroma cahow Diomedea epomophora Diomedea exulans Phoebastria_immutabilis Procellaria conspicillata Larus ichthyaetus Pterodroma atrata Larus genei Thalassarche_bulleri Larus melanocephalus Sterna bergii Larus hemprichii Thalassarche_cauta Procellaria cinerea Larus armenicus Pelecanus onocrotalus Phoebetria palpebrata Macronectes giganteus Macronectes halli Phalacrocorax pygmeus Sterna bernsteini Sterna lorata Larus saundersi Diomedea amsterdamensis Sterna balaenarum Larus relictus Sterna sandvicensis Sterna repressa Sterna saundersi Sterna bengalensis Common name Peruvian diving petrel Japanese Murrelet Dark-rumped Petrel Waved Albatross Socotra Cormorant Humboldt Penguin Balearic shearwater Short-tailed Albatross Pink-footed Shearwater Audouin's Gull Black-browed Albatross Dalmatian Pelican Black-footed Albatross Sooty Albatross Yellow-nosed Albatross Olrog's Gull White-eyed Gull Royal Tern Westland Petrel Black Petrel White-chinned Petrel Grey-headed Albatross Cahow Bermuda Petrel Royal Albatross Wandering Albatross Laysan Albatross Spectacled Petrel Great Black-headed Gull Henderson Petrel Slender-billed Gull Buller's Albatross Mediterranean Gull Great Crested Tern Sooty Gull Shy Albatross Grey Petrel Armenian Gull White Pelican Light-mantled Sooty Albatross Southern Giant Petrel Northern Giant Petrel Pygmy Cormorant Chinese Crested Tern Peruvian tern Saunder's Gull Amsterdam Albatross Damara Tern Relict Gull Sandwich Tern White-cheeked Tern Saunder's Tern Lesser Crested Tern 54 IUCN weighted exposure 1.972 1.762 1.743 1.642 1.592 1.466 1.269 1.131 1.116 1.085 1.004 0.972 0.941 0.830 0.829 0.816 0.748 0.720 0.718 0.658 0.621 0.592 0.591 0.584 0.575 0.571 0.564 0.518 0.511 0.485 0.471 0.462 0.429 0.428 0.408 0.405 0.390 0.384 0.364 0.195 0.191 0.184 0.024 0.024 0.020 0.012 0.011 0.006 0.006 0.005 0.005 0.005 117 118 119 120 121 122 123 STN STF SDG CAT STH STP PEG seabirds seabirds seabirds seabirds seabirds seabirds seabirds Sterna nilotica Sterna albifrons Sterna dougallii Sterna caspia Sterna hirundo Sterna paradisaea Pelecanoides garnotii Gull-billed Tern Little Tern Roseate Tern Caspian Tern Common Tern Arctic Tern Peruvian diving petrel 55 0.005 0.005 0.005 0.005 0.004 0.002 1.972 Table 10 EEZ and high seas FAO areas presenti ng t he highest ex posure for all t he seabi rds i n descendi ng order of importance EEZ or high seas FAO area Peru Chile South Africa Pacific Southeast - High Seas Areas Namibia Indian Ocean Eastern - High Seas Areas New Zealand Galapagos Isl.(Ecuador) Atlantic Southwest - High Seas Areas Japan Main Isl. Pacific Southwest - High Seas Areas Russia Pacific Pacific Eastern Central - High Seas Areas Argentina Morocco Japan Outer Isl. Indian Ocean Western - High Seas Areas Iran Atlantic SouthEast - High Seas Areas Yemen Australia India Angola Brazil Greece Turkey Mediterranean Sea J. Fernandez, Felix and Ambrosio Isl. (Chile) Pacific Northwest - High Seas Areas Mexico Egypt Alaska Mauritania Spain United Arab Emirates Ecuador Somalia Uruguay China Pacific Western Central - High Seas Areas Pakistan Western Sahara (Morocco) Bahrain Oman Korea South Saudi Arabia Persian Gulf Italy Tunisia Saudi Arabia Red Sea Algeria France Senegal Croatia Sudan Kuwait Qatar Pacific Northeast - High Seas Areas Canada Falkland Isl.(UK) Lebanon Gambia Mozambique Sum of all seabird IUCN weighted exposures in the EEZ 0.576 0.566 0.436 0.384 0.366 0.321 0.314 0.279 0.275 0.264 0.257 0.242 0.226 0.222 0.222 0.221 0.201 0.188 0.185 0.180 0.176 0.175 0.172 0.172 0.161 0.160 0.159 0.156 0.155 0.152 0.149 0.146 0.142 0.142 0.141 0.141 0.140 0.135 0.134 0.131 0.129 0.125 0.125 0.123 0.123 0.120 0.117 0.112 0.108 0.106 0.099 0.097 0.092 0.091 0.089 0.088 0.086 0.085 0.083 0.081 0.080 56 Seals and otters IUCN?weighted exp osure Seals and otters are most exposed to gillnet fishing in Sout h America ast of , E o rt h Af rica and o rt hern uro pe (Figure 13) he most exposed Mediterranean Sea , N N E .T spec ies included Mediterranean Mo nk Seal, fo llowed by t he two otter spec ies, all in t he most exposed g roup of spec ies (Ta ble 11). T he EEZs co nt ributing most to t he expos ure are set out in Ta ble 12. Figure 13 t EEZs and High Seas FAO areas s howi ng wit h t he IUCN weighted exposures summed across i p nni peds and otters. A reas wit h colours furt hest up t he scale bar (red colours) had higher pi nni ped and otter exposures. 57 Table 11 Seals and otters ranked by thei r IUCNweighted exposure. Those marked with pi nk s hadi ng are the most exposed 40 species those s haded g reen were the moderately exposed 40 species, and those s haded blue the least exposed specie , Rank 3 10 35 74 80 96 Species code MMN LOF LOP HGR PHV OFL Family marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other species Monachus monachus Lontra feline Lontra provocax Halichoerus grypus Phoca vitulina Arctocephalus australis Common name Mediterranean Monk Seal Marine Otter Southern River Otter Grey Seal Common Seal South American Seal IUCN weighted exposure 2.204 1.852 1.102 0.522 0.470 0.369 Table 12 EEZ and high seas FAO areas presenti ng the highest exposure fo r all the seals and otters i n descendi ng o rder of i mpo rtance. Sum of all seal and otter IUCN weighted exposures in the EEZ 0.242 0.152 0.149 0.122 0.114 0.107 0.106 0.099 0.063 0.062 0.052 0.043 0.037 0.035 0.034 0.033 0.032 0.031 0.028 0.028 0.028 0.026 0.025 0.023 0.023 0.022 0.022 0.022 0.021 0.021 0.018 EEZ or high seas FAO area Chile Peru Greece Algeria Argentina Tunisia Turkey Mediterranean Sea Croatia Norway Montenegro Iceland United Kingdom Sweden Russia Barrents Sea Denmark Madeira Isl.(Portugal) Canada Faeroe Isl.(Denmark) Bosnia Poland Ireland Russia Pacific Finland France Albania Germany Netherlands Latvia USA East Coast Russia Baltic Sea Kaliningrad Cyprus 58 Turtle IUCNËweighted exposure Turtles we re most affected by gillnet f ishing in so ut h Asia, so ut heast Asia, east Asia, no rt hwest Af rica, weste rn Europe, Mexico a nd Ja pa n (Fig ure 14). T his species g ro up may be highly affected by gillnet f ishing wit h all t urtle species represented wit hin t he top 40 species most exposed to gillnet f ishing (Ta ble 13) T he EEZs cont ribut ing t he g reatest components of t he risk to t urtles a re set o ut in Ta ble 14. Figure 14 EEZs and Hig h Seas FAO a reas s howi ng with t he IUCN weig hted exposures su mmed ac ross turtles. A reas wit h co lours furthest u p the scale ba r (red co lours) had hig her turt le exposures. " 59 Table 13 ( Turt les ra nked by their IUCN(weig hted ex posure. Those ma rked wit h pi nk s hadi ng a re t he most exposed 40 species, those s haded green we re t he mode rately exposed 40 species, a nd t hose s haded blue t he least exposed species Rank 6 7 9 18 19 22 Species code EIM LPK DCC CAC CHM LPV Family turtle turtle turtle turtle turtle turtle species Eretmochelys imbricata Lepidochelys kempii Dermochelys coriacea Caretta caretta Chelonia mydas Lepidochelys olivacea Common name Hawksbill Turtle Kemp's Ridley Turtle Leatherback Turtle Loggerhead Turtle Green Turtle Ridley Turtle 60 IUCN weighted exposure 2.073 2.009 1.965 1.572 1.484 1.386 Table 14 O EEZ and hig h seas FAO areas prese nting t he hig hest ex posure fo r a ll t he turt les in desce nding o rde r of impo rta nce. EEZ or high seas FAO area India Vietnam Myanmar China Indonesia (Eastern) Mauritania Pacific Western Central - High seas Areas Bangladesh Indonesia (Western) Morocco Western Sahara (Morocco) Mexico Philippines United Kingdom Malaysia Sarawak Senegal Malaysia East Thailand Japan Main Isl. Japan Outer Isl. Korea South Malaysia West Spain Pacific Northwest - High seas Areas Korea North Malaysia Sabah Madagascar Indian Ocean Eastern - High seas Areas Nigeria USA East Coast France Sierra Leone Guinea Pakistan Taiwan Venezuela Atlantic Eastern Central - High Seas Areas Namibia Brazil Angola Cameroon South Africa Denmark Papua New Guinea Cambodia Canary Isl.(Spain) Tunisia Atlantic Western Central - High Seas Areas Peru Guyana Sum of all turtle IUCN weighted exposures in the EEZ 0.422 0.420 0.415 0.347 0.340 0.323 0.319 0.316 0.313 0.295 0.277 0.269 0.264 0.254 0.243 0.241 0.235 0.230 0.224 0.224 0.219 0.218 0.217 0.212 0.211 0.209 0.208 0.208 0.200 0.200 0.196 0.196 0.195 0.193 0.191 0.187 0.185 0.184 0.182 0.178 0.178 0.178 0.170 0.170 0.168 0.167 0.166 0.166 0.165 0.162 61 Shark I UCNpweig hted exp osure Sha rks were most ex posed to g illnet f is hing in East Asia, Ja pan, Sout hEast As ia, Sout h As ia, Morocco but a lso widely spread in many EEZs a nd hig h seas areas (Figure 15) his .T h h h h h h ff t t f t f f t species group may be ig ly a ec ed by gillne is ing w i ive o e six s ark species represented wit hin t he top 40 spec ies most ex posed to gillnet f is hing (Ta ble 15). T he EEZs cont ribut ing most to t he expos ure of s ha rks to g illnet f is hing are set out in Table 16. Figure 15 « EEZs and High Seas FAO a reas showing wit h t he IUC N weighted ex posures summed across sha rks. A reas wit h colours furt hest u p t he sca le ba r (red co lours) had hig he r sha rk ex posures. 62 Table 15 Ò Sha rk ra nked by thei r IUC NÒweig hted exposure. T hose marked with pi nk shadi ng are t he most exposed 40 species, those shaded g reen were t he mode rately exposed 40 species, a nd t hose shaded blue t he least exposed species Ra nk 29 30 34 37 39 41 Species code CTM IPA RHT CCC LMN IOX Family shark shark shark shark shark shark species Cetorhinus maximus Isurus paucus Rhincodon typus Carcharodon carcharias Lamna nasus Isurus oxyrinchus Common name Basking shark Longfin Mako shark Whale Shark Great White Shark Porbeagle shark Shortfin Mako shark 63 IUCN weighted exposure 1.234 1.140 1.113 1.094 1.090 1.075 Table 16 ú EEZ and hig h seas of i mpo rta nce. FAO EEZ or high seas FAO area China Japan Main Isl. Vietnam India Pacific Western Central - High Seas Areas Myanmar Morocco Indian Ocean Eastern - High Seas Areas Pacific Northwest - High Seas Areas Russia Pacific Pacific Southeast - High Seas Areas Mauritania Indonesia (Eastern) Western Sahara (Morocco) Chile Korea South Peru South Africa Bangladesh Indonesia (Western) Guinea Japan Outer Isl. USA East Coast Taiwan Korea North Spain United Kingdom Mexico Greece Philippines Namibia Indian Ocean Western - High Seas Areas Norway Senegal Brazil Pacific Eastern Central - High Seas Areas Madagascar France Italy Tunisia Malaysia Sarawak Australia Iceland Atlantic Eastern Central - High Seas Areas Atlantic Southwest - High Seas Areas Malaysia East Thailand Canada Canary Isl.(Spain) Atlantic Western Central - High Seas Areas Malaysia West Algeria Gambia Turkey Mediterranean Sea Croatia Malaysia Sabah Sierra Leone Ecuador Angola Libya Nigeria a reas e e nti ng t he hig hest ex posu re fo r all t he s ha rks i n desce ndi ng o rde r pr s Sum of all shark IUCN weighted exposures in the EEZ 0.241 0.213 0.202 0.199 0.198 0.192 0.192 0.190 0.183 0.171 0.164 0.158 0.156 0.156 0.153 0.153 0.152 0.149 0.146 0.145 0.144 0.144 0.144 0.141 0.141 0.140 0.138 0.136 0.135 0.135 0.133 0.133 0.132 0.130 0.129 0.128 0.127 0.118 0.117 0.117 0.112 0.111 0.110 0.110 0.110 0.109 0.106 0.105 0.104 0.102 0.101 0.100 0.100 0.100 0.098 0.096 0.096 0.095 0.094 0.092 0.092 64 S p ecies level analy sis conclusion: T he d d res ults of t he st u y s how t hat a ll taxo n g ro ups a re affecte eac h g ro up b y g illnet f is hing w it h b d d t e ing re prese nte w it hin t he to p 40 s pec ies most hig hly ex pose o g illnet d d f is hing of t he C MS s pec ies inc lu e d d d in t he st u y T urt les a n s ha rks a re hig hly affecte . d d d w it h 5/6 s ha rk s pec ies re prese nte w it hin t he to p 40, a n a ll t urt le s pec ies ra nke w it hin t he to p 2 5 T hese two g ro ups of C MS s pec ies a re . f is hing . 65 b d b like ly to e most impacte y g illnet T he mit igat io n tec hniq ues a im of d l inc i e nta ca pt ure c irc umsta nces t hat ld s ho u no nWta rget of l d ea to t he b e no nWta rget b ll o r s u sta nt ia y 200 3). (Bac hce s pec ies d eat h of l e iminate to s pec ies re d uce Unde rsta nd ing ll in g i nets is t he t he esse nt ia l t o d t l b d d e e rmining how f ut ure mo rta it ies ca n e preve nte (Rowe 2007), a n as s uc h, c ha nges to pract ices a nd imple me nt ing mit igat io n is esse nt ia l. Ma ny mit igat io n met hods to red uce bycatc h have bee n pro posed a lt ho ug h ve ry few of t hese have Exte ns ive ll g i net b l d ee n a pp ie rev iews f is hing ll (Fre nc h 20 11) o r a re o pe rat io na y l fo r s ing e mit igat io n tec hniq ues of ge ne ra ll y have b d d ee n co n ucte bl uns uita e s pec ies Wg ro ups Me lv in (e.g. & (Dawso n 199 1). or Pa rris h l re at io n to in 1999, ll Bu 2006, ll l l l b Rowe 2007. G i ma n et a . 2009, G i ma n et a . 20 10, ACA P 20 11, Lo kke o rg 20 11). T hese rev iews d an o rig ina l resea rc h pa pe rs l re at ing to mit igat io n resea rc h a re d s umma rise b l d ll l d d. e ow. Mit igat io n met ho s w hic h a re s pec if ic to g i net f is he ries o n y a re isc usse T his met hod invo lves a le rt ing no nWta rget s pec ies to g illnets w it h v is ua l c ues in o rde r to d t d l e e r no nWta rget s pec ies, w it h t he a im of ec reas ing e nta ng e me nt l d l inc u e c ha ng ing net co o ur, net ll i uminat io n, us ing l l rates. V is ua a e rts l bl ) t a rge r (mo re v is i e w ine s izes fo r b l d d l nets, inc reas ing t he num e r of f i a me nts use in t he nets a n v is ua ma rke rs (i.e.: co rks) l d l l b d b w hic h a re p ace a o ng t he net. V is ua c ues have ee n effect ive at re uc ing ycatc h fo r sea b d ir s ll (Bu 2007), l l. (G i ma n et a 20 10). re d uce d d an nets. t he pinnipe d s l (Ba r ow d an 200 3) Ca me ro n d an t urt les O ne iss ue w it h t his met hod is t hat ta rget catc h rates a re ofte n a lso l l l as a res u t of v is ua a e rts. Me lv in et a l. 20 cetacea ns, 50 d th t (1999) fo un a mes hes of t he l Rhinoce ros a uk et net b d d ec rease w he n t he ycatc h of co mmo n murres we re ma d e b l ycatc h was a so mo re re d uce bl , v is i e d b d co mpa re l ut o n y in t he w it h uppe r l l nets. T he catc h of t he ta rget soc keye sa mo n howeve r was a so re d uppe r l mo nof i a me nt 50 uce mes hes of d b y mo re t ha n ha lf w he n t he uppe r 50 mes hes we re made mo re v is ible. Wa ng et a l. (20 10) invest igated t he use of v is ua l a le rts to red uce t he bycatc h of t urt les in ll d lh l d l ll d ll g i nets. Sha rk s ha pe si o uettes we re p ace a o ng t he g i net a n i uminat io n of nets 66 b ch ca l l h d as p t nt a l d t h l e mi ig ts we re use o e i e e rre nts fo r g ree n sea t urt les. W ie y LED a nd s ha rk s ha ped s ilho uettes ta rget s pec ies catc h rate. re d c d u e sea b catc h y , t urt le Bot h ty pes of t hey a lso c hn illuminat io n te iq ues s ubsta nt ia lly re d c d u e re d c d u e b catc h w h l ie y ha c c catc h at s. r e v ing no effe t o n ta rget s pe ies Ping ers Pinge rs we re f irst deve lo ped to dete r ma rine ma mma ls f ro m g illnets. Pinge rs a re s ma ll c wa n n d c hat h h¢f d s hat w h n unde rwate r aco ust i r i g ev i es t e mit ig req ue ncy pulse ig na ls t e , attac hed a lo ng a A lt ho ug h net , d t c h n h e e r no n¢ta rget s pe ies f ro m a pproac i g t e ha ve pinge rs c effe t ive ness a ppea rs to b cc ssf ee n s u e ul in re d c u ing b catc h y b h c c c e ve ry f is e ry a nd s pe ies s pe if i leve ls (Rowe 2007). net fo r so me (Zo llet 2009). b c d c n b catc h c d h ee n effe t ive at re u i g of o mmo n o lp ins (Eva ns et a l. 1977) y d h o lp ins (Bo rd ino et a l. 2002) , , Jo hnsto n 2002) h 2002) a nd s o rt bac d um p ke a rbo ur po rpo ises H d h o lp ins H Pinge rs ha , ve ca na ra nc is , F (C ulik et a l. 200 1 ea rin et a l. 2000 , G , (Pedde mo rs b a d c d h e ke o mmo n o lp ins s pec ies pinniped 2000) s pec ies (Jo hnsto n (Ba rlow a nd Ca me ro n 200 3). Ca rretta et a l. (2008) o bse rved t he co mplete e liminat io n of bea ked w ha le b catc h w h n p n e i ge rs we re y d c d t h d ft h int ro u e o t e Ca lifo rnia ri g illnet f is e ry. I nfo rmat io n o n t he use of pinge rs at dete rring sea bird bycatc h is ve ry limited. Me lv in et a l. (1999) d t e e rre nts fo und we re t hat c o mmo n d inco rpo rate murre w it h b catc h y was mo nof ila me nt re d nets. c d u e In b y t he w he n 50% sa me st udy aco ust ic h w o eve r , pinge rs had no effect at dete rring Rhinoce ros a uklets f ro m e nta ng le me nt. Ba rlow a nd Ca me ro n (200 3) o bs d e rve a re d c d u e b catc h y rate of sea ls a nd s ea lio ns w he n aco ust ic dete rre nts we re used yet in ot he r st ud ies pinnipeds have assoc iated t he , , so und of pinge rs w it h food (Bo rd ino et a l. 2002) , t hus inc reas ing acc ide nta l h c e nta ng le me nt of t ese s pe ies. Pro ble ms assoc iated w it h aco ust ic dete rre nts c asta l a c c o reas fo r ing so me s pe ies Rowe 2007). a bit uat io n H may a lso d inc lu e ha b tat c c i ex lus io n es pe ia lly f ro m , b¢ pt into s u o ima l fo rag ing b e an iss ue putt ing into ha b tat i (C ulik et a l. 200 1 , h q uest io n t e lo ng te rm c c st l c h effe t ive ness of pinge rs (Cox et a l. 200 3). Pinge rs a re a lso o o mpa riso n to ot e r y (in 67 i i i m t gat o n met hods), t hey need i i se rv c ng, reg ula r t hey a nd ca n f i t n e r e re i w th net i i i o pe rat o ns s uc h as sett ng a nd ha ul ng . fl Passi ve Re ectors T his i met hod (ma inly nvo lves cetacea ns) if i y ng mod a re mo re f i pro pe rt es o t he aco ust ic ik l e ly to detect t he t he g illnet so t hat a nima ls prese nce o f i g llnets . od M if i i cat o ns f ib f f ib i i i i i i i nc lude c he m ca lly e nha nc ng net res, nc reas ng t he de ns ty o net res, a nd add ng f ex t ra b ased loat or on t he i g llnets i c ha ns (Goodso n . T ria ls et t he a lo ng i ass umpt o n t hat (Read 2000) i do lph ns o b ead i do lph ns i us ng a nd . o r cetacea ns, F i po rpo ses ha rbo ur a nd 2007) f re lecto rs i pass ve 994) 1 al .. (Rowe net have i ec ho locate red uced i po rpo ses t his n t he f b ycatc h o (T rippe l et al .. meas ure i s f i i i v c n ty o b tt o le nose 200 3) . A n b bi b b i i i se rved red uct o n n sea rd ycatc h occ urred w he n a r um s ulphate was added to t he f ny lo n o as t hey 200 3) f bi i i ib t i i ibi it g llnets, yet t h s was att r u ed to t he nc reased v s l y o t he nets to sea rds had b ee n dyed b lue to mas f th k th i i i i e co lo ur o e c he m ca l add t o n (T r ppe l et a l . . Iss ues i i w th th s i nc lude met hod net ha nd ling pro b le ms, t he hig h cost f o i c he m ca lly f f i i i if i e nha nc ng nets a nd t he leve l o va r at o n o r cetacea ns to detect t he mod ed net (Rowe 2007) . l Time/ A rea c osures T ime/a rea c los ures have t he i pote nt a l to b e f s uccess ul f or a ll i s pec es g ro ups if f i hi f i i i i i if i mple me nted a ppro pr ate ly T h s met hod nvo lves c los ng a n a rea to s ng o r a s pec c . t ime i pe r od w he n i co ns de red to leve ls b e too f o i i nc de nta l e nta ng le me nt hig h (Rowe 2007) f th f k now ledge o e te mpo ra l patte rns o . i or th s F f or i pote nt a l met hod to b i ycatc h s pec es a re ff b i i e e ect ve, a n ex te ns ve fi h b th b i i o pote nt a l ycatc h s pec es a nd ta rget s i i i s pec es s req u red . i i i i i urray et a l (2000) noted t hat t he s pat a l a nd te mpo ra l va r at o n n occ ure nce n so me M . f i s pec es ro m yea r to yea r may a rea f b i o r s u ta le c los ure fi h i g llnet s e ry i . A ma k e it iff i i i i d c ult to dete rm ne t he a ppro pr ate t me a nd n exa mple o f f n t he G ul o f t hi s was f i a ne o r t he M hig hlig hted f mo nt h o 68 f th b i k y t he c los ure o e s n N b ove m e r, 994 1 i n a n atte mpt to a rbo ur po rpoise bycatc h. Hig hest bycatc h rates we re obse rved in Se pte mbe r; we ll befo re t he c los ure dates and t his, co upled wit h t he small a rea w hic h t he meas ure 1999) howeve r s howed t hat cove red , proved t he c los ure ineffective. Me lvin et al. ( , , red uce h ope ning fis he ries only ing peak salmon abundance s uppo rting t he time/a rea mitigation tec hniq ue. d ur red uced seabird bycatc h, Subsurface net setting T his met hod involves anging t he pt h at w hic h t he net is set to red uce bycatc h. It is pa rtic ula rly applicable fo r seabirds as most seabird bycatc h is obse rved at de pt hs of less t han 20m be low t he s urface (Zyde lis et al. 2009) and by setting t he net be low t he maximum d iving de pt h, it g reatly red uces bycatc h of d iving seabirds (Lokke bo rg 20 11). A red uction in seabird bycatc h was obse rved in t he Japanese gillnet fis he ry w he n nets ch de we re set 2 m be low t he s urface, howeve r fis hing effic ie ncy was also 9 5% 199 3 c ited by e lvin et al 1999) , (Hayase & Yats u M . . red uced by u p to Net modifications Fis hing eq uipme nt mod ifications have bee n effective at red uc ing bycatc h in seabirds 11) 3) F ( re nc h 20 , pinnipeds, cetaceans (No rt hridge and Sande rson 200 and t urtles R ) ( ome ro 2008 . It is ofte n d iffic ult, howeve r, to alte r fis hing eq uipme nt att ributes wit ho ut red uc ing fis hing effective ness (Bull 2007). Eq uipme nt size, anges inc lude mod ifying t he ch d iamete r of monofilame nt twine and mes h ing net pane l he ig ht and red uc ing t he numbe r and le ngt h of tie downs used. 3) No rt hridge and Sande rson (200 obse rved significantly red uced bycatc h leve ls in seal and ha rbo ur po rpoise bycatc h w he n t hinne r twine d iamete r was used, possibly beca use red uc t he t hinne r twine meant it was easie r fo r t hese spec ies to break f ree. Nets t hat we re smalle r in profile (half pane l he ig ht) had less t urtle bycatc h and re leasing t urtles was 9) 1 ) E easie r in smalle r nets ( c ke rt et al. 2008 and Gea rha rt et al. 200 . Cambie (20 0 s uggested t hat setting eq uipme nt in s hallowe r wate r and adj usting t he we ig hting de sign of t he nets, wo uld allow e ntangled t urtles to 69 re ac h t he s urface to breat he. Time of day fishing restrictions The time of day t hat fis hing nets are set can potentially impact bycatc h rates elvin et . M al (1999) s howed t hat by avoiding fis hing at dawn, bycatc h rates of bot h t he auklet and t he common murre were reduced significantly w hile target catc h rates were only reduced by around 5%. Ot her operational measures t hat may potentially reduce bycatc h include: ‚ reduced net soak time, ‚ provisional equipment carried on board to release incidental bycatc h, ‚ regular patrolling of nets to release incidental bycatc h, ‚ avoiding congregations of bycatc h species w here possible, ‚ attac hing suspender lines to t he gillnet w hic h hold t he net below t he float line. This review demonstrates t hat t here is no one universal solution to t he problem of gillnet bycatc h. Many mitigation tec hniques are species{ and area{specific and w hile one measure may work for one species or species group, it may be ineffective or detrimental to anot her. Additionally, some tec hniques t hat are very effective at reducing bycatc h are also linked to reductions in fis hing efficiency. Bycatc h reduction t hroug h mitigation has been demonstrated to some degree in all species groups, yet t he effectiveness t hese met hods wit hin eac h species group in not universal. T ime/area closures have t he potential to be useful at reducing bycatc h across multiple species groups yet t he effectiveness of t his met hod is closely linked to spatial and temporal patterns of t he non{target species (Lokkeborg 20 11). For many species, more in{dept h biological information is needed to apply t his met hod effectively. 70 The results of t his st udy s how t hat g illnet bycatc h is a ubiquitous pro blem w it h all taxon , g roups in t his st udy (s harks cetaceans sea birds t urt les pinnipeds otters) be ing , , , , , represented w it hin t he top 40 hig hest ranked spec ies for likely adverse effects of g illnet f is hing. The s hark and t urt le g roups were bot h hig hly ranked w it h all t urt le spec ies ranked w it hin t he top 25 spec ies most exposed spec ies, and 5 out of t he 6 s hark spec ies ranked w it hin t he top 40. W it hin t he CMS listed spec ies, t hese are t he two spec ies g roups w hic h are most likely affected by adverse effects of g illnet f is hing. The impact t hat g illnet f is hing is hav ing on spec ies populat ions was not eluc idated from t his analys is; all populat ions could to some deg ree be affected by g illnet f is hing but t he , , hig hest ranking spec ies are likely to be affected more st rong ly. The results from t his analys is hig hlig ht f ive important areas w here t here was a hig h overlap between spec ies and g illnet f is hing and t hat require furt her examinat ion. These areas were: ‚ Sout h A merica (bot h At lant ic and Pac if ic coast lines) ‚ West coast of Africa (from Cape of Good Hope to A lgeria) ‚ The Red Sea/Pers ian Gulf to A ra bian Gulf ew Zealand/Tasman Sea ‚ N ‚ The Aegean Sea If spec if ic populat ions are affected by bycatc h mortality from g illnets t hese areas are t he , ones in w hic h adverse effects are most likely to be o bserved. These are also t he areas w here more monitoring and deta iled f is hing stat ist ics are required to assess impacts at a populat ion level in more deta iled analys is. 71 Table 17 ¾ Top 10% of EEZs most like ly to be affecting each species group. Species Group Top 10% EEZ most affected Cetaceans China, Russ ia Pac ific, India, Myanmar Seabirds and Vietnam . Chile, Pe ru, So ut h Af rica and Mo rocco Sharks Russ ia Pac ific, Myanmar, Mo rrocco, India, Vietnam, Ja pan (Ma in Is l ) and . China T urt les ang lades h, Indo nes ia B aste rn), (E China, Myanmar, Vietnam and India . Sea ls and Otte rs Chile and r ay No w C urre nt ly, t he re is no s ing le so lut io n t hat can be a pplied g lo ba lly to so lve g illnet bycatc h issues fo r t he C MS s pec ies T he st udy of how gear tec hno logy a lo ne, o r in co mbinat io n . i h h t t r m a r an b o e e su es c e used as an effect ive so lut io n is st ill in its infancy (G ilman et w a l 20 10) So lut io ns to g illnet bycatc h pro ble ms are extre me ly co mplex and need to be . . add ressed o n a case by case bas is T he re are many facto rs t hat co ntribute to t he efficacy . of a part icular measure inc luding t he g illnet fis he ry ty pe, catc h pe r unit effo rt, t he area fis hed, and t he s ize and be hav io ur of t he no ntarget s pec ies (G ilman et a l 20 10, Wa llace . et a l. 20 10). So me tec hniq ues t hat are ve ry effect ive at red uc ing bycatc h are a lso linked to red uct io ns in fis hing effic ie ncy . he leve l of effect ive ness fo r so me mit igat io n met hods varies bot h betwee n and w it hin s pec ies g ro ups. T his was o bse rved by Me lv in et a l. (1999) w ho fo und t hat Co mmo n Murre bycatc h was red uced by 50% w he n aco ust ic pinge rs we re inco rpo rated w it h mo nofilame nt nets In t he same st udy howeve r, pinge rs had no effect at dete rring . Rhinoce ros A uklets f ro m e ntang le me nt . T mo ngst t he most effect ive mit igat io n so lut io ns rev iewed in t his st udy we re t ime/area c losures. T his met hod has proved to be ve ry effect ive in a numbe r of diffe re nt areas, and A 72 ca n pote nt ia lly f be s uccess ul at met hod pro ble m w it h t his o pe rat io na lly a nd s pec ies v ia ble ta rget howeve r is t hat to exte ns ive , red uc ing bycatc h ac ross mult iple s pec ies g ro ups ne . O s pec ies te mpo ra l a nd req uired is be imple me nted a ppro priate ly a nd , (Murray et of know ledge s pat ia l 000) 2 . al . G pote nt ia l at he ring t his be bycatc h ty pe of info rmat io n ca n be ve ry t ime co ns uming to s uff ic ie nt ly ta ke into acco unt t he leve ls of seaso na l va riat io n needed to def ine t he s ize of t he a rea a rea w ill be c losed , a nd t he t ime pe riod t hat t he . It is a lso c rit ica l t hat t he soc ioeco no mic s it uat io n is assessed w he n ta king into acco unt 0 10) I n ma ny deve lo ping co unt ries g illnet f is hing v ia ble mit igat io n meas ures ( ilma n , G 2 . is ma in too l fo r food t he fo r s ubs iste nce gat he ring co mmunit ies ma king t ime/a rea mit igat io n meas ures c los ures s imply not a po lit ica lly v ia ble ma nage me nt o pt io n . ea r G tec hno logy used a pproac hes in co nj unct io n w it h ot he r s pec if ic to ind iv id ua l f is he ries a nd no nDta rget s pec ies is like ly to be t he most v ia ble way fo rwa rd in ma ny a reas he effect ive use of aco ust ic dete rre nts (cetacea ns pinnipeds) , , . T pass ive ref lecto rs (cetacea ns sea birds pinnipeds) a nd t he a lte rat io n of f is hing met hods , , (a ll s pec ies f urt he r g ro ups) have deve lo pme nt req uire me nt fo r a ll s how n a nd eve ry pro mise imple me ntat io n s pec ies g ro up at be ing of effect ive mit igat io n rev iewed in t his mit igat io n too ls . meas ures st udy . is oweve r , H an t he T he urge nt lac k of info rmat io n o n bot h mit igat io n meas ures a nd ind iv id ua l s pec ies be hav io urs has made it d iff ic ult to reco mme nd t he s pec ies/ s pec ies g ro up e . W most effect ive ty pes of mit igat io n meas ures fo r eac h reco mme nd t he f urt he r mo re deta iled a na lys is of s pec if ic , f is he ry/ s pec ies g ro up co uplings to deve lo p t hese so lut io ns f urt he r . a llace et a l ( 0 10) ac know ledges t hat w he n exa mining t he impacts of f is hing bycatc h W . 2 o n t urt le po pulat io ns , ff f f bycatc h mit igat io n e o rts s ho uld oc us o n a reas o hig h bycatc h / hig h effo rt a reas reas t hat have low o bse rved effo rt but pote nt ia lly hig h impacts o n , . A t he po pulat io n mea ns t he re is less co nf ide nce in bycatc h rates a nd o bse rve r effo rts , s ho uld be inc reased to q ua nt ify t hese iss ues . T his st udy most prov ides a g lo ba l a na lys is of t he g illnet impo rta nt reg io ns fo r f urt he r invest igat io n . bycatc h pro ble m a nd o ut lines t he ac k of L info rmat io n has like ly t hat s ma ll but impo rta nt effects a re c urre nt ly unde rDre prese nted 73 mea nt it is ine sca le effects . F (to co uld ) km 0 .1 info r at io n m has li be m ex plo red ited by t he a na lyt ica l a pplicat io ns t he add ress g illnet bycatc h pro ble of t he ode l m used a nd a na lys is , he re but ea nt m poo r q ua lity t hat we ca nnot s at a loca l leve l m . It is i po rta nt to note t hat t he ove rla p betwee n s pec ies d ist ribut io ns a nd g illnet f is hing m effo rt is lin ed k not to hig h req uire be hav io ura l info r info r at io n t hat m is rates of bycatc h o rta lity m . T leve l of his wo uld a na lys is odes of inte ract io ns w it h g illnets; at io n fo r eac h s pec ies o n m m no nnex iste nt o r d iff ic ult to o bta in fo r a ny s pec ies to a s uff ic ie nt m leve l fo r t his st udy o r exa ple a ny of t he coasta l s pec ies have hig h ra n s d ue to , m . F m k , hig h ex pos ure dete r m to g illnet act iv ity (co nocc urre nce in t he sa a reas) e m it re a ins m to be ined w het he r ex pos ure eq uates to inte ract io ns betwee n t he s pec ies a nd g illnets a nd t he o rta lity occ urs in pro po rt io n to t he leve l of ex pos ure n atte pt to acco unt m . A m in t he a na lys is was do ne by inco rpo rat ing t he be hav io ur of eac h s pec ies into t he a na lys is to o ut line a ny pote nt ia l inte ract io ns t hat a s pec ies ay have w it h g illnets ve n ta ing m . E k be hav io ur into co ns ide rat io n it is st ill ay be li e ly t hat t he ag nit ude of t he pro ble , m k m m be ing unde rnre prese nted fo r so T he a na lys is has bee n do ne ide nt if ied as hav ing a fo r t he low ex pos ure ot he r s pec ies had bee n ta Ove rnest i e s pec ies m . C MS s pec ies o nly . in o ur st ud ies co uld So e m be a reas of he re hig h ex pos ure if e n into acco unt k . at io n of t he ex pos ure ay occ ur w he n t he re is no te po ra l ove rla p betwee n m m m t he f is hing seaso n a nd s pec ies d ist ribut io ns in t he a rea d ue to T bee n Zs w hic h have EE ay m be a co ns ide ra ble unde rest i at io n of m t he hig hly co nce nt rated his . T d ist ribut io n into do n't ta e k acco unt loca l ig rat io n . ex pos ure g illnet f is hing a nd s pec ies a re a ps m m ay m hots pots in a reas w he re bot h be so w he n t he s pec ies s uc h as feed ing zo nes , ig rat io n co rrido rs re prod uct io n s ites his ay affect pa rt ic ula rly t urt les a nd sea birds , m . T m w hic h breed o n t he coast line a nd so co uld g illnet act iv it ies be pote nt ia lly hig hly ex posed to ins ho re . Mis re prese ntat io n of t he ex pos ure re prese ntat io n of t he ay occ ur d ue to bot h unifo r m m ot h d ist ribut io ns s pec ies d ist ribut io n a nd t he g illnet catc h d ist ribut io n ay not ove rla p . B m in rea lity at s T he re was wate rs of a ll te po ra l a nd s pat ia l sca les m m . a hig he r leve l of re po rt ing a nd o bse rvat io n of bycatc h inc ide nce in t he o re ind ust ria lised nat io ns It is poss ible t hat bycatc h o rta lity of s pec ies t hat m . m 74 a re d ist ributed f req ue nt ly . o uts ide ind ust ria lised a reas is occ urring , but not be ing re po rted as G ilma n (20 10) o ut lines t hat t he re a re fo ur catego ries of info rmat io n t hat a re needed to catego rise t he ris k t hat coasta l nets a re pos ing to sea t urt les . T hese catego ries ca n be a pplied broad ly to cove r a ll s pec ies g ro ups in t his st udy . T hese a re: wledge o n t he Kno ‚ mag nit ude of t he pro ble m in te rms of bot h no n¤ta rget s pec ies a nd t he f is he ry f t e f f aracterisati is ery ; gea r ty pes used c ha racte rist ics o eac h gea r , Ch on o h h ‚ ty pe a nd f is hing o pe rat io ns a nd catc h c ha racte rist ics . f ramew a ageme t M n n ‚ o rk; w hic h inc ludes mo nito ring a nd mit igat io n prog ra mmes f ci ec mic c siderati w hat a re t he implicat io ns o how mit igat io n So o ono on on – ‚ meas ures w ill effect soc ia l a nd eco no mic s it uat io ns ? T he st udy impacts prese nted on he re no n¤ta rget re prese nts a s pec ies . I t nove l e le me nt uses t he in unde rsta nd ing g illnet f is hing ext re me ly poo r info rmat io n a bo ut t he f is he ries to ex plo re ff w hic h a reas a nd s pec ies t hat may be to have adve rse ly a ected by mo rta lity s pec ies in g illnets or . T he po pulat io ns info rmat io n we re not req uire me nts met . to eve rt he less , N exa mine ta rget ing info rmat io n gat he ring ca n be prio rit ised as a res ult of t he st udy . 75 f is he ries of impacts mit igat io n on a nd T he st udy fo und: ‚ T he info rmat io n a bo ut ava ila ble f is he ries g illnet ext re me ly is poo rly doc ume nted, ha mpe ring deta iled a na lys is of t he pro ble m of inc ide nta l catc h in t hese w ide ly used f is hing met hods . ‚ ycatc h B linked w it h g illnet f is he ries is reco rded, s pa rse ly c reat ing poss ible biases in a ny a na lyses . ‚ ist ribut io n fo r D ma ny po pulat io n data s pec ies, cetacea ns, s uc h as is know n, poo rly as a re a nges may be desc ribed, but a reas of inte nse use a re not . R desc ribed fo r ma ny g ro ups of a nima ls listed o n C MS a ppe nd ices . ‚ ffo rt E was co nce nt rated so ut h in east As ia, no rt he rn E uro pe, Pac if ic, west Af rica n Coast a nd t he west coast of So ut h A me rica ‚ no rt h west . A reas of hig h s pec ies d ive rs ity fo r C MS s pec ies we re t he west coast of So ut h A me rica, west coast of Af rica f ro m t he Ca pe of Good Ho pe to A lge ria, t he Sea / Pe rs ia n G ulf Aegea n Sea ‚ T he twe nty to A ra bia n G ulf, New Zea la nd / Tas ma n Sea, a nd ed R t he . xc lus ive E co no mic E Zo nes 2 37 of a reas a na lysed, in w hic h t he g reatest ex pos ure to f is hing ris k occ urs fo r C MS listed s pec ies (we ig hted by I UC N ra nk) we re: Mya nma r, V iet na m, Pe ru, I nd ia, Af rica, C hina, Na mibia, G reece, Ga la pagos, Weste rn I ndo nes ia, aste rn I ndo nes ia, E A lge ria, a nd Mo rocco ‚ R uss ia (Pac if ic), C hile, So ut h a ng lades h, Ja pa n (Ma in Is la nds), B No rway, Ma urita nia, United Kingdo m, . T he fo rty s pec ies most ex posed to ris k f ro m g illnet f is hing, w he n we ig hted by I UC N ra nk, by taxo n g ro up we re: ‚ eabirds S Murre let, Humbo ldt – Af rica n a rkørumped D Pe ng uin, Pe ng uin, Pet re l, a lea ric B Waved . iv ing øpet re l, D A lbat ross, Shea rwate r, A udo uin’s G ull, Sho rt øta iled A lbat ross 76 Pe ruv ia n Socot ra Pinkøfooted Ja pa nese Co rmo ra nt, Shea rwate r, ‚ ns & Sir ni ns – Finless Porpoise, Irrawaddy Dolphins, Dugong, Nort h Pacif ic Rig ht W hale, At lant ic Hump$backed Dolphin, Nort hern Rig ht W hale, Bott lenose Dolphin, Heaviside’s Dolphin, Fin W hale, Sei W hale, Indo $Pacif ic Hump$backed Dolphin, Blue W hale, Burmeister Porpoise, Baird’s Beaked W hale, Omura W hale tac a Ce e a e ‚ S ls nd S O Sout hern River Otter. ‚ S Tur l s – Hawskbill Turt le, Kemp’s Rid ley Turt le , Leat herback Turt le, Loggerhead Turt le, Green Turt le, Olive Rid ley Turt le. ‚ Sh rks – Basking Shark, Longf in Mako Shark, Porbeagle Shark, W hale Shark, Great W hite Shark. a a a e e a e tt e rs – Med iterranean Monk Seal, Marine Otter, t e a Bycatc h t hroug h entanglement was known to occur for sea t urt les, cetaceans, pinnipeds, sirenians and s harks. Diving sea birds were documented entangled w hen d iving for food, but some species may become entangled d uring hauling or sett ing of nets . Among most likely to be affected, CMS listed s harks and t urt les have hig h ‚ rankings compared to ot her taxa: All six t urt le species are listed among t he top 23 ranked species ident if ied in t he analysis, and all 6 s hark species are in t he top 41 ranked species. ‚ ‚ Mit igat ion met hods ident if ied included visual alerts, acoust ic alerts, seasonal or area closures or c hanges to net conf igurat ions. ‚ However, mit igat ion met hods were found to eit her red uce f is hing eff iciency considera bly, or had litt le documented of bycatc h red uct ion effect. ‚ Seasonal or area closure t herefore appears to be t he most effect ive way of avoid ing bycatc h of non$target species in gillnet f is heries. ‚ Target ing closures to cover periods of most intensive interact ion between affected non$target species is necessary, and f urt her researc h is needed to examine t he interact ions in areas ident if ied in t his st udy, specif ically to examine be havioural data and seasonal occurrence of affected species and f is heries . 77 ‚ Next steps: There are strong requirements for improved observer data, better records of bycaught species with a particular focus in the areas of high overlap of at^risk species and strong fishing effort. Further, finer^scaled research to address bycatch issues in the areas, and for the species identified as highest risk in this analysis is warranted. 78 Absal, R.(2007) Two dugongs found trapped in gillnet. Published: 16 :47 December 17,2007;Gulf News AlfaroShigueto, J., Dutton, P., Van Bressem, M. and Mangel, J. (2007). Interactions between leatherback turtles and Peruvian artisanal fisheries .Chelonian Conservation and Biology 6 : 129134 . AlfaroShigueto, J., Mangel, J.C ., Pajuelo, M., Dutton, P., Seminoff , J. & Godley, B.J . (2010) Where small scale can have a large impact: structure and characterization of smallscale fisheries in Peru. Fisheries Research , 106 ,8–17. AlfaroShigueto,J., Mangel,J.C., Bernedo, F., Dutton, P. H.,Seminoff ,J. A .and Godley, B.J.(2011),Smallscale fisheries of Peru: a major sink for marine turtles in the Pacific.Journal of Applied Ecology.doi: 10.1111/j.13652664 .2011.02040.x Amir, O. A . (2002). The incidental catch of dolphins in gillnet fisheries in Zanzibar, Tanzania. Western Indian Ocean Journal of Marine Science 1(2): 155 162. Ancha, L. (2008), Regional bycatch of longlived species (sea birds , marine mammals and sea turtles) in the Mediterranean and Black Seas . http://hdl.handle.net/ 1016 1/478 Arata, J. A ., Sievert, P. R., Naughton, M. B. (2009). Status Assessment of Laysan and BlackFooted Albatrosses , North Pacific Ocean, 1923–2005 . Artukhin, Yu. B., Vyatkin,P.S ., Lobkov E. G., Biryukov, A . M., Kupriyanov, S. V., Kurnosov, D. S., Report under the Small Grant for Marine/Seabirds Conservation BirdLife Asia on Kitllitz’s Murrelet Conservation in Kamchatka, PetropavlovskKamchatsky,2010 Ayala,L.(2008).Catch and bycatch of Albatross and Petrel in longline and gillnet fisheries in northern Peru. Rufford Small Grants for Nature Conservation. Badrudeen, M., Nammalwar, P., and Dorairai, K. (2004). Status of Sea Cow (Dungong Dungon) along SE coast of India. Journal of Bombay Natural History Society 100(3): 381 387. Barlow, J., Baird, R.W ., Heyning, J.E., Wynne, K., Manville, A .M., Lowry, L.F., Hanan, D., Sease, J., Burkanov, V.N. (1994). A review of cetacean and pinniped mortality in coastal fisheries along the West Coast of the ISA and Canada and the East Coast of the Russian Federation. Report for the International Whaling Committee (Special edition 15) Report:SC/090/G28. Barlow, J., Cameron, G.A (2003). Field experiments show that acoustic pingers reduce marine mammal bycatch in the California drift gill net fishery. Marine Mammal Science 19:265 283 . Barraff , L. S., Loughlin, T. R. (2000). Trends and Potential Interactions Between Pinnipeds and Fisheries of New England and the U.S .West Coast. Marine Fisheries Review 62(4). Beeson, M.J ., Hanan, D.A . (1996). An evaluation of pinnipedfishery interactions in California. Report to the Pacific States Marine Fisheries Commission: 46 p. Belden, D. L., Orphanides , C. D., Rossman, M. R., and Palka, D. L. (2006). Estimates of Cetacean and Seal Bycatch in the 2004 Northeast Sink Gillnet and MidAtlantic Coastal Gillnet Fisheries . Northeast Fisheries Science Center Reference Document 0613 . Benjamins , S., Kulka, D. W., Lawson, J. (2010). Recent incidental catch of sharks in gillnet fisheries of Newfoundland and Labrador,Canada. Endangered Species Research 11: 133 146 . BirdLife International and NatureServe (2011) Bird species distribution maps of the world. BirdLife International,Cambridge, UK and NatureServe, Arlington, USA . Bisack , K. D. (2003). Estimates of marine mammal bycatch in the Northeast ( New England) multispecies sink gillnet fishery in 1996 . Northeast Fisheries Science Center Reference Document 0318:21. 79 Bjorge,A.,Godoy, H.,and Skern½Mauritzen, M.(2011) . Estimated bycatch of harbour porpoise (Phocoena phocoena) in two coastal gillnet fisheries in Norway. International Whaling Committee. Report: SC63/SM18 ) ,and Bjørge, A.,ØIen, N., Hartvedt , S., Bøthun, G., Bekkby,T. (2002) . Dispersal and Bycatch Mortality in Gray ( Harbour ( Phoca vitulina) seals tagged in the Norwegian Coast . Marine Mammal Science 18(4):963 ½ 976. Halichoerus grypus Bordino, P., Kraus, S., Albareda, D., Fazio, A., Palmerio, A., Mendez , M., Botta, S.(2002) . Reducing incidental mortality of Franciscana dolphin (Pontoporia blainvillei) with acoustic warning devices attached to fishing nets. Marine Mammal Science 18(4): 833 ½ 842. Buencuerpo,V., Rios,S., Moron, J.(1998) . Pelagic sharks associated with the swordfish fishery in the eastern North Atlantic Ocean and Straight of Gibralter. Fish Bulletin 96(4): 667 ½ 685 . Bull, L. (2006) . A review of methodologies aimed at avoiding and/or migrating incidental catch of protected seabirds, Draft Report . ACAP½ Second meeting of advisory committee. Brazil, 5 ½ 8 June. Cambie, G., Camin, J.A ., Franquesa R, Mingozzi T. (2010) . Fishing activity and impacts along the main nesting area of loggerhead sea turtle (Caretta caretta) in Italy : overwhelming discrepancy with the official data.Scientia Marina 74(2): 275½285 . ) in trammel nets off the western coast of Sardinia (Italy): statistical models Cambie, G. (2010) . Incidental capture of ( caretta tic Conservation : Marine and Freshwater Ecosystems Published online in Wiley of capture abundance and immediate survCaretta ival.Aqua Online Library (wileyonlinelibrary.com) . DOI: 10.1002/aqc.1155 . Carretta, J., Price, T., Peterson, D., and Read, R. (2004) . Title Estimates of marine mammal, sea turtle, and seabird mortality in the California drift gillnet fishery US National Marine Fisheries Service Marine Fisheries Review 66(2): 21½ 30. Carretta, J. V., Barlow , J. (2008) . Acoustic pingers eliminate beaked whale bycatch in a gill net fishery. Marine Mammal Science 24(4):956 ½ 961. Chan, E. H., Liew H. C., & Mazlan, A. G. (1988) . The Incidental Capture of Sea Turtles in Fishing Gear in Terengganu, Malaysia. Biological Conservation 43 : 1½ 7 Cheng I.J ., Chen, T. (1997) . The incidental capture of five species of sea turtles by coastal setnet fisheries in the eastern waters of Taiwan. Biological Conservation 82 : 235 ½ 239 . Chivers,S.J., Robertson, K. M.,and Henshaw , M. D. (1997) .Composition of the incidental kill of cetaceans in two California gillnet fisheries : 1990½1995 . Report for the International Whaling Committee (Special edition 15) 47:909½9 15 . Cetacean Bycatch Resource Center (2011) .<www .cetaceanbycatch .org>.Consulted February½August 2011 . Cliff, G., Dudley, S.F.J ., Davis, B. (1989) . Sharks caught in the protective gill nets off Natal, South Africa; The great white shark (Carcharodon carcharias) .South African Journal of Marine Science 8(1): 131½ 144. Commission of the European communities (2006) , Report of the Scientific, technical and economic committee for fisheries 2006. Deep½sea Gillnet Fisheries. Brussels. Convention on Migratory Species (2011) . http ://www .cms.int/about/intro.htm.Accessed 20 Sept 2011. Costas,G., Fariña, C., Sampedro, P., Landa, J., Morlán, R., Azevedo, M., Duarte, R.,Cardador, F. (2007) Standardization of Catch per unit effort for Anglerfish caught by Iberian artisanal gillnet fleet in IC ES Division VIIIc . International Council for the Exploration of the Sea,Copenhagen. Cox, T. M., Read, A. J., Swanner,D., Urian, K., Waples, D. (2003) . Behavioral responses of bottlenose dolphins, (Tursiops ) , to gillnets and acoustic alarms. Biological Conservation 115: 203–212. truncates Crowder L.B., Myers, R.A .(2001) . A Comprehensive Study of the Ecological Impacts of the Worldwide Pelagic Longline Industry. First Annual Report To The Pew Charitable Trusts. Culik , B.M., Koschinski, S., Tregenza, N., Ellis, G.M. (2001) . Reactions of harbor porpoises ( Phocoena phocoena) and herring (Clupean harengus) to acoustic alarms. Ecology Progress Series 211: 255–260. 80 D'Argrosa a a or a o a a Phocoena sinus g s r s r g or or raoa a g o a D'Argrosa r o a a a a o's ar sa a g s r s Dr g a s a o a o o o o s r a o o og Da so a a o or s o s or g s ar a a D oo o A a arga a s a oo o rso or o oa o A s o s ar o a D ar o s r s aa sa s r o Agr r Agro as sr aa sa A a s r s a s s o go os r ar A g s D o A ar o a aro A a Ag ar A o r s o a o ogg r a s a r s s r rra a o r a r g o g s o r a o ar D A oA a a os o og a o s r a o o ra s a a Pontoporia blainvillei or o o a ro a ra o r a o a a s ar a a ag Do Dossa A s r o o g a s ar s r s A s ra A rogr a a A s ra s o r a a a or a a or s a os D ar o s r s r a s a ar oo o a g a s s r s so r s r s D ar o s r s sr o s r sa so as a a a D a a Do ar a a o s a a a s s r s aa a ra sa as a or r a ao s or or raoa a g o a r ra a oa A s r ogg r a r ra o s o a s sa r o og a o r a r A ar ar rg a a r g a ra sa r a s ra r g s r r a a o ao s r ro a s o ao ga Dr g rra a ro a s o ao o o A r as r a r ors a r ors ro gs o ara r s o s s o a o o o s Delphinus delphis o s a a a o s a s D a s ra s o o o r o o og o ar a a s r a D go a or a a oas a a rs a o s s a o g s o o (gadus morhua) s or o os a sa s r s D o aas a o a a s Ar sa a s g ar a or r g or s o o o r s Ass ss o o r s r a a s o ar as a a A r D ag a o a r s s a a rs a ors or s a r ra o s og s r s s r a ra a s r a ra a s r s o ss o o D o a ass a o o s g g ar a gor s A s r s oo a Agr r rga a o a a r s o oo a Agr r rga a o o aos o oo a Agr r rga a o o o o or s o s s r s oo a Agr r rga sa o o aos o A ar oo oo a Agr r rga a o s r a A a r a s s oo a Agr r rga sa o o aos o oo a Agr ra rga a o o aos s r o r ro s r a A a r Ags o r ro s FAO Fisheries and Aquaculture Department o o a a s 81 , C ., Vid the Inte n f ti l , O ., W illi m , C . G ( 1995) . M l Wh n lin dy , C .E., Vid , C ., Lenne tC t n e v ti extincti n . C , J ., Elli tt , H y el Edici n ,B cel n e Queved , I. i Beneditt f Ri , ne d tment ep tment St nd He pet ic l Ecke t , S . t f Envi nment Ev n , W .E.; b t ct ) h tc h C l Ju tice F und tive e p f Fi he ie ke 1993 1994 . Rep t ivin : m ll p ti pul n l Science 7(3) : 283295 . ld . V lume 3 . H f the W lin tzin t . Lynx . uk y i nnu l Fi he ie . ti tic 2006 , tu tle in the St nd c ch n e v nd M n uine n h b k f ce ti n k fi he ie nci c n f the f b t . nd P n e ) in the n ( th ct . In : P Bh b in h k n, nd mm b t , 13th ct EE Fi he ie Re u ce Su vey Sy tem , the n Mind n , 46 pp . l Vi w n , Cent P l t , G .X .) : 55 B n l de h 2005–2006 . in fi he ie n e he d f l ement 3(2) : 185 192 . ey , G . & Yu te , L. l Ye f byc tch ine Science 67(4) : 77 685 . nd y N in the C mmittee Speci l 15 . in , B u ed Indu t y M l . (20 10) . S u ce , f M nd Live t ck , M t hy m ll cet f l Wh n m . (20 10) . Gillnet fi he y l e he d tu tle inte nd Ecke t , K.L. (2008) . Reducin nn , C . mmunic ti n New lette ti n (2007) , Ille in the Gulf cti n f G be , Tuni i . f me h Filippi , ., W in the we te n u h , S ., nd ment e Nic l . S . nd cent l lphin f M nd twine type le fi he ie e , B. (2006) . Byc mp ehen ive fi he ie ize m ll c f y l in the Medite ne n , Envi In Reed , J .C .; S te , J .E. (edit n d mm n the Bi nfe ence le the b ck tch ce d ift u f illnet ) 1977 . ) t ( ine M mm illnet n nment l , 12 15 electivity vi u ecembe l Ju tice F und ti n , L nd n , UK. In Reed , J .C .; S te , J .E. (edit nd l c u tic 1977 , S n ie ,C in icel d f c l timuli . P lif ni ) ceedin . ndic c t l w te . PPE) . (I f tu tle byc tch in the e 8 : 26 . iftnettin l f c ptive c n e nd C f the Sec n C illnet fi he ie n l ine M mm . M B uil y l f the n Fi he y St ti tic ti nd n Re e wb ey , F.T .; Gu evich , V .S . 1977 . the devel pment k h p ti Bi d f the k . IC ES J u n l in (ed .M , Sp i , M., t , J ., Be Felix , F., Mun z , M., H W ce de c ipti l t d B F ife , J .R. (2003) . Effect In titute f du in l 20 : 25 30 d . Byc mp illnet fi he ie u u t 20 11. . (200 1) . Bi f Cet l c , Mini t y the Inte n l J u n ., Ge ( 1977) . C u n Fi he y (2007) . fi he y in T inid illnet e icultu e & f y line l n , R. M. zil . J de M ll Echwikhi , K., J ib , I. F., ( R m te , B f Fi he ie Rep lphin in in h ., Pubill , E., , n d iftin th , L. L. ( 199 1) . Incident l Phillipine tch in Mexic byc 1996 . H ndb (20 11) , Mini t y , S .J . (2009) . f d ’ n ulted Feb u , L., de H n the n . P. M., p , M.S ., ep f Hect t l J . (ed ) y i M l nfe ence 2009 , P lm C l , O . (2000) . V quit tch nd S ., ., C de J nei ) in ( y 14(4) : 1110 1119 . l v .my/277 > . C f. we te n Medite f V quit . f Fi he ie tment ep <http ://www .d i n Bi n , S . M. ( 199 1) . Incident l c w lity t C mmittee Speci l 16 . Humpb ck Wh le in ti 20 10 . WC PFC p pe . Revi ed p ti l Fi hin n l f S uthe n Hemi phe e Humpb ck Wh le , H b i k indic t P cific . WC PFCSC620 10 EB IP0 1. We te n in Ge t,T f m e nd Cent l Ecu ni d : 37 bi d inte P cific du in 2005 . IWC p il 2006 . cti with l n Fi he ie n C mmi line i n, P hnpei . F d nd icultu e O 222 . Revi i n 1. F F d nd F F d d n nd ni ti n ( 1990) . icultu e O niz ti efiniti niz ti n ( 1995) . C O niz ti n f the United N ti n icultu file niz ti n de n nd cl ific ti n f the United N ti n f C nduct f f fi hin ie c te e . FO Fi he ie Technic l P pe , R me . Re p n ible Fi he ie . F d nd icultu e O ni ti n f the , R me . icultu e n nd unt y p nd icultu e O United N ti O d . In : l O niz (20 10) . F O ye b k 2008 . Fi he y nd qu cultu e St ti tic . d F nd icultu e , R me . ti n f the United N ti n (20 11) . Fi he y c unt y p [ nline] . R me . Upd file © 200420 11. Fi he y ted 1 M y 2009 . Vi ited 3 u nd qu cultu e u t 20 11. Forney . K. A ., Benson . S . R., Cameron , G . A .(200 1) . Central California Gillnet Effort and Bycatch of Sensitive Species , 1990i 1998 . Proceedings — Seabird Bycatch : Trends , Roadblocks , and Solutions Franquesa , R., Idrissi , M. , Alarcón , J . (200 1) . Feasibility assessment for a database on socioeconomic indicators for Mediterranean fisheries . Studies and reviews . General Fisheries Commission for the Mediterranean , Rome , FAO , 7 1:1i55 . Frazier , J . G ., and Montero , J . L. B. ( 1990) . Incidental Capture of Marine Turtles by the Swordfish Fishery at San Antonio , Chile . Marine Turtle Newsletter 49 : 8 i 13 . French , G ., Taylor , P. (20 11) . The Incidental Catch of Seabirds in Gillnet Fisheries : A Global Review . Unpublished Report , Birdlife International , Royal Society for the Protection of Birds . Gaos , A . R., Maldonado , D., and Peckham , S . H. (2008) . Loggerhead Bycatch and Reduction off the Pacific Coast of Baja California Sur , Mexico . Project Global Workshop Proceedings i Tackling Fisheries Bycatch ; managing and reducing sea turtle bycatch in gillnets , Loreto , Baja California Sur , Mexico . Gass , J . (2006) . Bycatch Mortality Of Leatherback Turtles In Trinidad’s Artisanal Gillnet Fishery . Nicholas School of the Environment and Earth Sciences Durham , North Carolina , Duke University . Gearhart , J ., Eckert , S . and Inniss , A . (2009) . Reducing leatherback ( fisheries of Trinidad , West Indies . ) sea turtle bycatch in the surface gillnet Dermochelys coriacea Proceedings of the Technical Workshop on Mitigating Sea Turtle Bycatch in Coastal Net Fisheries . Gearin , P. J ., Gosho , M.E., Leake , J .L., Cooke , L., De Long , R.L., and Hughes , R.L. (2000) . Experimental testing of acoustic alarms (pingers) to reduce bycatch of harbour porpoise , ( Research and Management 2( 1) : 1i9 . ) , in the state of Washington . The Journal of Cetacean Phocoena phocoena Gerosa , G ., Casale , P.( 1999) . Interaction of Marine Turtles with Fisheries in the Mediterranean . UNEPi MA Pi RAC/S PA ,Tunis . Gilman , E., Gearhart , J ., Price , B., Eckert , S ., Milliken , H., Wang , J ., Swimmer , Y ., Abe , O ., Peckham , S . H., Shiode , D., Hall , M., Mangel , J ., AlfaroiShigueto , J ., Dalzell , P., Shizaki , A . (20 10) . " Mitigating sea turtle bycatch in coastal Chaloupka , M., passive net fisheries ." Fish and Fisheries 11( 1) : 57 i 88 . Gomercic , M., Galov , A ., Gomercic , T ., Škrti Bottlenose dolphin ( 25(2) : 392 i 40 1. 5 , D., urkovi 4 5 , S ., Luci 5 , H., Vukovi 5 , S ., Arbanasi 5 , H., Gomer i ) depredation resulting in larynx strangulation with gillinet parts . Marine Tursiops truncatus 75 , H. (2009) . Mammal Science Gunnarsson , K., Jónsson , G ., & Pálsson , O . K. ( 1998) . Sjávarnytjar við Ísland (p . 280 p) . Reykjav ík : Mál og menning . Hamman , M., Limpus , C ., Hughes , G ., Mortimer , J ., and Pilcher , N. (2006) . Assessment of the conservation status of the leatherback turtle in the Indian Ocean and South East Asia IOS EA Species Assessment : Volume I. Indian Ocean – Southi East Asian Leatherback Turtle Assessment IOS EA I. M. T . M. Secretariat . Bangkok , Thailand . Harrington , J . M., Myers , R.A ., (2005) Wasted Resources : Bycatch and discards in U. S . Fisheries . Prepared by MRAG Americas , Inc . Hayase , S . and Yatsu , A . ( 1993) . Preliminary report of a squid subsurface driftnet experiment in the North Pacific during 199 1. North Pacific Commission Bulletin 53(557i576) . Hobday , A .J ., Smith , A . Stobutzki . I, Bulman , C . Daley , R. Dambacher J ., Deng , R, J . Dowdney , Fuller , M. D. Furlani , Griffiths , S ., Johnson , D., Kenyon , R., Knuckey , I., Ling S ., Pitcher , R., Sainsbury , K., Sporcic , M., Smith , T ., Turnbull C ., Walker , T ., Wayte , S ., Webb , H., Williams , A ., Wise , B., Zhou , S . (20 11) . Ecological risk assessment for the effects of fishing Fisheries Research 108 : 372i384 Hossain , Md .M.M. (2004) . On sustainable management of the Bay of Bengal Large Marine Ecosystem ( BO BLME) . National Report of Bengladesh , p .12 1. House of Commons Environment Food and Rural Affairs Committee (2004) . Caught in the net : bycatch of dolphins and porpoises off the UK coast . Third Report of Session 2003–04 . Icelandic Fisheries (20 11) , Information centre of the Icelandic Ministry of http ://www .fisheries .is/fisheries/fishingigear/gillnets/> . Consulted FebruaryiAugust 20 11. 82 Fisheries and Agriculture . Gillnets . Instituto de Fomento de Pesquero (2003) . Plan de Acción Nacional de Chile para mitigar efectos de la pesca de palangre sobre Aves Marinas ( PA N A M) , IFO P and Universidad Austral de Chile . FIP 2003 2 1: Informe Final : 132 p . » » Instituto de Fomento de Pesquero (2006) , <http ://www .ifop .cl> . Accessed : August 20 11. IFREMER, 20 10 . Synthese des flottillles de pêche 2008 : flotte de Mer du Nord» Manche»Atlantique , flotte de Mediterranée . Réalisation du projet "Systeme d' Informations halieutiques de l' Ifremer , 256 p . Iniguez , M. A ., Hevia , M., Gasparrou , C ., Tomsin , A . L., Secchi , E. R. (2003) . Preliminary estimate of incidental mortality of Commerson's dolphins ( ) in an artisanal setnet fishery in La Angelina Beach and Ria Gallegos , Santa Cephalorhynchus commersonii 4. Cruz , Argentina . Latin American Journal of Aquatic Mammals 2(2) : 87 »9 Ishihara , T . (2007) . Japan coastal bycatch investigations . North Pacific Loggerhead Sea Turtle Expert Workshop December 1 20 , 9– 2007 Honolulu , Hawaii , USA . IUC N 20 11. IUC N Red List of Threatened Species . Version 20 11.1. <www .iucnredlist .org> . Consulted May June 20 11 . » Jefferson , T . A ., Curry , T .A ., Black , N.A . ( 1989) ." Harbour Porpoise mortality in Monterey Bay , Halibut Gillnet Fishery . Report International Whaling Committee , Special Issue 15 445 448 . » Jefferson , T .A . and Curry , B.E. ( 1 4) . A 99 global review of porpoise Conservation 67(2) : 167 183 . » ( ) mortality Cetacea: Phocoenidae Johnston , D. W . (2002) . The effect of acoustic harassment devices on harbour porpoises ( Fundy , Canada . Biological Conservation 108 : 113 118 . » in gillnets . Biological ) in the Phocoena phocoena Bay of Julian , F., and Beeson , M. ( 1998) . Estimates of marine mammal , turtle , and seabird mortality for two California gillnet fisheries : 1990 » 1 5 99 Fishery Bulletin 6(27 1 284) . 9 » Karamanlidis , A ., Androukaki , E., Paravas , V ., Adamantopoulou , S ., Paximadis , G ., Pires , R., Tounta , E., Mediterranean monk seal ( Khan , M.A .A ., Sad Management and Chatzispyrou ,A ., Johnson , W . M., Kotomatas , S ., ) . Endangered Species Research 5 : 205 2 13 . » Monachus monachus N.U., Chowdhury , Z .A ., (2003) : Status of the demersal fishery resources of Future Papadopoulos , A ., Dendrinos , P. (2008) . Assessing accidental entanglement as a threat to the Direction of Coastal Bangladesh . In : Assessment , Fisheries in Asian Countries . Eds : Silvestre G , Garces L, Stobutzki I, Ahmed M, Valmonte Santos RA , Luna C , Lachica Aliño L, Munro P, Christensen V , Pauly D, World Fish Center Conference Proceeding 67 63 » » » 82 . Kiszka , J ., Muir , C ., Amir , O .A ., Cox , T .M., Boujea , J ., Poonian ,C ., Razafindraoto , Y ., Wambiji , N., & and N. Bristol (2008) . Marine mammal bycatch in the southwest Indian Ocean : review and need for a comprehensive status assessment , Indian Ocean Tuna Commission . W PEB 06 . Kiszka , K., Muir , C ., Poonian , C , Cox , T .M., Amir , O .,Bourjea , J ., Razafindrakoto , Y ., Mammal Bycatch in the Southwest Indian Ocean : Review and Wambitji , N., & Bristol , N. (200 ) . Marine 9 Need for a Comprehensive Status Assessment . Western Indian Ocean Journal Marine Science 7(2) : 11 136 . 9 » Kristjánsson , L. ( 1 83) . Íslenskir sjávarhættir 3 (p . 4 8 p) . Reykjav ík , Iceland : Bókaútgafa Menningarsjóðs . ( In Icelandic) 9 » 9 Kroese , M., Sauer , W . H., Penny , A .J ( 1 6) . An overview of shark catches and bycatches in South African Fisheries . Collective 99 Volume of Scientific Papers ICCAT 43(3) . Kwazulu Natal Sharks Board (20 11) . <http ://www .shark .co .za> Accessed May August 20 11 » » Lee Lum , L. (2006) . Assessment of incidental sea turtle catch in the artisanal gillnet fishery in Trinidad and Tobago , West Indies . Applied Herpetology 3 : 357 » 368 . Lien , J ., Fawcett , L ( 1 86) . Distribution of basking sharks , 9 Newfoundland . Canadian field»naturalist 100(2) : 246 » 252 . (Cetorhinus maximus) Lo ´pez , B. D. (2006) . Interactions between Mediterranean bottlenose dolphins ( Journal of Marine Science 63 : 946 » 95 1. 83 , incidentally caught in inshore fishing gear in ) and gillnets off Sardinia , Italy . Tursiops truncatus Løkkeborg , S . (20 11) . Review and assessment of mitigation measures to reduce incidental catch of seabirds in longline , trawl and gillnet fisheries FAO Fisheries and Aquaculture Circular . No . 1040 Mangel , J .C ., AlfaroShigueto , J ., Van Waerebeek , K., Caceres , C ., Bearhop , S ., Witt , M. J ., Godley , B.J . (20 10) . Small cetacean captures in Peruvian artisanal fisheries : High despite protective legislation . Biological Conservation 143 ( 1) : 136 143 . Mate , B. ( 1993) . Experiments with an acoustic harassment system to limit seal movements . Journal of the Acoustical Society of America 94(3) : 1828 . Melvin , E. F., Parrish , J .K., Conquest , L.L. ( 1999) . Novel tools to reduce seabird bycatch in coastal gillnet fisheries . Conservation Biology 13(6) : 1386 1397 . Melvin , E. F., Parrish , J . K. ( 1999) . Proceedings of the Symposium ; Seabird Bycatch : Trends , Roadblocks , and Solutions ,. Annual Meeting of the Pacific Seabird Group , Blaine , Washington ,. Ministry of Fisheries 20 11. http ://fs .fish .govt .nz/ Page .aspx?pk=6 1&tk=2 12 . Accessed 29 September 20 11. Montevecchi , W .A . ( 199 1) . Incidence and types of plastic in gannets' nests in the Nortwest Atlantic . Can . J . Zool ., 69 :295297 . Moore , J . E., Wallace , B.P., Lewison , R.L., Zˇydelis , R., Cox , T .M., Crowder , L.B. (2009) . A review of marine mammal , sea turtle and seabird bycatch in USA fisheries and the role of policy in shaping management . Marine Policy 33 : 435 45 1. Muir , C ., Ngasaru , A ., and Mwakanema , L. (2004) . Towards a W estern Indian Ocean Dugong Conservation Strategy . The status of Dugongs in the Western Indian Ocean region and priority conservation actions . W orld W ildlife Fund . Dar es Salaam , Tanzania . Muir , C . E., Sallema , A ., Omari , A ., De Luca , D., & Davenport , T .R.B. (2003) . The dugong ( assessment of status , distribution and threat . Wildlife Conservation 22 . ) in Tanzania : A national Dugong dugon Murray , K. T ., Read , A .J ., Solow , A , R. (2006) . 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 and Management 2(2) : 135 14 1. Murray , K. T . (2009) . Characteristics and magnitude of sea turtle bycatch in US midAtlantic gillnet gear . Endangered Species Research 8 : 2 11 224 . Murray , K.T .; Read , A .J .; Solow , A .R. (2000) . The use of time/area closures to reduce bycatches of harbour porpoises : lessons from the Gulf of Maine sing gillnet fishery . Journal of Cetacean Research and Management 2 : 135 14 1. Nammalwar , P., Dorairaj , K. (2004) . Status of seacow Dugong dugon ( Müller) along the southeast coast of India . Journal of Bombay Natural History Society 10 1(3) : 38 1387 . New Zealand Ministry of Fishery (20 11) Official Information Request 117 1, Gillnetting within New Zealand . New Zealand Government 12/09/20 11 Northridge , S . and Kingston , A . (2009) . Common Dolphin Bycatch in UK Fisheries . SC6 1S M37 , Sea Mammal Research Unit , University of St Andrews . Northridge , S . P. ( 199 1) . Driftnet fisheries and their impacts on nontarget species : a worldwide review . Fisheries Technical Paper Food and Agriculture Organization of the United Nations . Rome : 115 . Northridge , S ., Sanderson , D. (2003) . Analysis and mitigation of cetacean bycatch in UK fisheries . Final Report to DEFRA Project . MF0726 , S MRU. United Kingdom : 18 p . Oceana (2006) . The use of drifnets by the Moroccan fleet . Online report . www .oceana .org . November 2006 Oceana MarViva Mediterranean Sea Project 2008 (2008) . Adrift ! Swordfish and driftnets in the Mediterranean Sea . Online report . www .oceana .org . August 2009 Orphanides , C . D. (20 10) . Northeast Fisheries Science Center Reference Document 10 10iii , 145 20 10 . Northeast Fisheries Science Center Reference Document 10 10iii , 145 20 10 . Ozturk , B., Ozturk , A . A . and Dede , A . ( 1999) . Cetacean bycatch in the western coast of the Tirkish Black Sea in 1993 1997 . X III. Annual Conference of the European Cetacean Society . Valencia , Spain . 84 Ozturk , B , Ozturk , A A , Dede , A 200 1) Dolphin bycatch in the swordfish driftnet fishery in the Aegean Sea app Comm int er . . . . ( . . R . . .M ) edit M .(36 . Peckham , S , , Nichols , T , W allace , J 2008) aldonadoh Diaz , D , Koch , V , ancini , A , Gaos , A , Tinker , igh mortality of . H. M . . M . . M. . .( . H loggerhead turtles due to bycatch , human consumption and strandings at Baja California Sur , exico , 200 to 2007 ndangered M 3 . E 17 1 h 18 Speices esearch Vol R .5 3. Peddemors , V 2000) Pingers : A dolphin conservation tool for the next millennium? 10th Southern African . ( . Symposium SA SS 2000) and , Sea and People in the New illennium h Abstracts p 1 ( M . L M . . . arine Science M Perez , J A A , Wahrlich , 2004) A bycatch assessment of the gillnet monkfish ophius gastrophysus fishery off southern Brazil . . . R.( . L . Fisheries esearch 72 : 8 1 h 9 R 5. Phan ong Dung 200 Status of leatherback turtles in Vietnam , p 1 4h 17 1 H . 6. . 6 Assessment h February 200 6 In Asian eatherbackhTsunami ndian Ocean &S E L I Þ 2002) Sjósókn og sjávarfang h Saga sjávarútvegs a Íslandi h 1 bindi h Árabáta og skútuöld p 24 p) Akureyri , celand : . .( . . ( . 3 . I ólar Bókaútgafan n celandic) H . (I I Þór , J Þ 200 ) Sjósókn og sjávarfang h Saga sjávarútvegs a Íslandi h 2 bindi h Uppgangsár og barningaskeið p 29 p) Akureyri , . .( 3 . . ( . 6 . ólar celand : Bókaútgafan n celandic) H .(I I I Þór , J Þ 200 ) Sjósókn og sjávarfang h Saga sjávarútvegs a Íslandi h bindi h Nýsköpunaröldin p 28 p) Akureyri , celand : . . ( 5 . 3. ( . 6 . I ólar Bókaútgafan n celandic) H . (I I Þór , J Price , B 2008) Sea turtle bycatch monitoring of the 2007 Fall Gillnet Fisheries in southeastern Pamlico Sound , North Carolina .( . . North Carolina Department of nvironment and Natural esources Completion eport : 1 28 : 2 E R . R 5 5. Proh Delphinus 200 ) Assesment of seabird bycatch in ( 6 . Conservation Programme ima , Peru . L . Project Global August 20 11 . ( 20 11) , Global Bycatch Assessment of Peruvian Artisanal Fisheries . Final eport to the R British Petroleum ongh ived Species , http ://bycatch nicholas duke edu Accessed Februaryh L L . . . . ead , A J 2000) Potential mitigation measures for reducing the bycatches of small cetaceans in ASCO BA NS waters eport to R . .( . . R ASCO BA NS : 0 p 3 . eport of the Scientific , technical and economic committee for fisheries 200 ) Deephsea Gillnet Fisheries Commission of the R ( 6 . . uropean communities , Brussels E . , Perrin , W F , eeves , , eynolds , J ontgomery , S , agen , T J 200 ) arine ammal esearch : Conservation beyond R . E. . . R R.R. M . R . .( 5 . M M R crisis Baltimore , USA , The Johns opkins University Press . H . 2007) , ogan , ackey egafauna bycatch in drift nets for albacore tuna R E. M M. ( . M ( Thunnus esearch 8 : h 14 R 6 6 . ) in the N Atlantic Fisheries E . alalunga 2008) Gillnet Bycatch in the Southern Part of “ Bah ía De Ulloa ,” Baja California Sur TAC K NG F S omero , J S S R . . L. ( . . LI I HERIE BYCATC : anaging and reduciing sea turtlle bycatch in gillnets , oreto , Baja California Sur , exico H M L M . 2004) The Net oss , A , saac , S ffect? A review of cetacean bycatch in pelagic trawls and other fisheries in the northheas t R . I . ( . E Atlantic W DCS eport for Greenpeace . R C and 1999) ultispecies Sink Gillnet Fishery and the ossman , errick , arbor Porpoise Bycatch in the Northeast idh R M. . M R. L. ( . H M M Atlantic Coastal Gillnet Fishery in 1998 and during Januaryh ay 1999 Northeast Fisheries Science Center eference Document M . R C NT O F CO U S D PA T 99h 17 . . E R ME MMER E. . 2007) A review of methodologies for mitigating incidental catch of protected marine mammals DOC owe , S J esearch & R . . ( . . R Development Series 28 . 3. Sea Around Us Project 20 11 http ://www seaaroundus org Accessed 1 August 20 11 . . . . 5 . 85 Secchi , E , Kinas , P G ncidental catches of Franciscana in coastal gillnet fisheries in the Francis cana uelbert , . R. . .& M M. (2004) . I anagement Area atin American Journal of Aquatic ammal 3 1 1· eriod 1999· M III: p 2000 .L M ( ) : 6 68 . Secretary of Commerce of the United State e ort of the Secretary of Commerce to the Congress of the United Sates (2008) R p arine Fisheries Service concerning U S actions taken on foreign large·scale high seas driftnet fishing Com iled by the National . . . p M Pursuant to Section E of the agnuson·Stevens Fishery Conservation and anagement Act , as Amended by Public aw 1 · 206( ) M M L 04 97 , The Sustainable Fisheries Act of 199 2 6 Sextant Technology Survey (20 arch·June 11 erformed in p M 20 Sextant Technology Survey (20 arch·June 11 M 20 Sextant Technology Survey Sextant Technology survey 11a , Fisheries Attache Government of alta , alta fficial re ly to Sextant Technology survey ) M M . O p 11b , Government of St Helena , St Helena fficial re ly to Sextant Technology survey erformed in ) .O p p 11c , nstitut francais de recherche our l'ex loitation de la mer F E E , France fficial re ly to (20 ) I p p ( I R M R) .O p arch·June 11 erformed in p M 20 Sextant Technology Survey 11d , inistry of Agriculture Fisheries , Belgium fficial re ly to Sextant Technology survey ) M & . O p Sextant Technology Survey 11e , inistry of Agriculture and ivestock , Turkey fficial re ly to Sextant Technology survey ) M L . O p (20 arch·June 11 erformed in p M 20 (20 arch·June 11 erformed in p M 20 Sextant Technology Survey survey p erformed in 11f , inistry for Agriculture , Forestry and Food , Slovenia fficial re ly to Sextant Technology (20 ) M . O p arch·June 11 M 20 Sextant Technology Survey (20 arch·June 11 erformed in p M 20 Sextant Technology Survey arch·June 11 M 20 (20 Sextant Technology Survey 11g , inistry of Fisheries odrigues , auritius fficial re ly to Sextant Technology survey ) M & R M . O p 11h , Swedish Board of Fisheries , Sweden fficial re ly to Sextant Technology survey erformed in ) .O p p (20 arch·June 11 erformed in p M 20 11c , Vanuatu ) Fisheries De artment , Vanuatu fficial re ly to Sextant p . O p Technology survey Shigueto , J A , angel , J C , Seminoff , J A , Dutton , P H Demogra hy of loggerhead turtles in the . . M . . . . . . (2008) . p ( Caretta caretta) southeastern Pacific cean fisheries·based observations and i m lications for management Endangered S ecies esearch 5 1 9 O : p . p R : 2 · 135 . Sibly , and Hone , J , Hone , J and Clutton· 3 Po ulation growth rate and its determinants an overview n Sibly , R. M. . 200 . p : . I R.M. . Brock , T H ildlife Po ulation Growth ates Cambridge University Press P 11· 3 . . 200 . W p R . . p. 40 . Silvani , S anish driftnet fishing and incidental catches in the western , Gazo , , Aguilar , A 1999 editerranean Biological L. M. . ( ). p M . Conservation 9 1 0( ) . Simeone , A , Bernal , 1999 ncidental mortality of Humboldt Penguins eza , J . M. & M .( ). I ( Spheniscus arine rnithology 7 157– 1 1 . M O 2 : 6 . Chile humboldti) in gill nets , central Smith , B D and Beasley , arked declines in o ulations of rrawaddy dol hins 1· 3 ryx Conservation News 37 . I. (200 ) . M p p I p .O : (4) : 40 406 . Stearns , S C 199 The Evolution of ife Histories xford University Press , xford . . 2. L .O O . Subsecretar ía de Pesca , S UBPESCA Government of Chile nforme Sectorial de Pesca y Acuicultura (2006) . I 2006 . Soczek , in New England Commercial Fisheries De artment of Environmental An Analysis of Seabird Bycatch , M. (2006) . 2006 . p Studies , Antioch University asters f Science . M O . Southeast Asian Fisheries Develo ment Center egional Framework for Fishery Statistics of Southeast Asia Southeast p (2008) . R . Asian Fisheries Develo ment Center , Bangkok , Thailand 33 p . pp . Southeast Asian Fisheries Develo ment Center 11 , onogra h htt //ma seafdec org/ onogra h/> Consulted February· p (20 ) M p . < p: p. . M p . 11 August 20 . 86 Southeast Asian Fisheries Development Center (20 11) , Stats , Catch of Marine Fishery by Type of Fishing Gear and by Species . <http ://fishstat .seafdec .org > . Consulted FebruaryÿAugust 20 11. q Environment and S uires , D., Grafton , Streftaris , R.Q ., Omar , I.H. (2003) . Technical efficiency in the Malaysian Economics , Cambridge University Press , vol . 8(03) , pages 48 1ÿ504 , July . Alam , M.F., Development N., and Nixon , S . (2004) . ( FIS H 5) Accidental bycatch : birds , mammals and turtles ; Indicator gill net artisanal fishery , Fact Sheet – Demonstration indicator . Y ., Giotom , M., Mengstu , T ., Abraha , H. and Indian Ocean Turtle Newsletter 9 . Teclemariam , Thomas , 9 Mahmud , S . (200 ) . An update on marine turtles in Eritrea , Red Sea . J . A ., and Kastelein , R.A . ( 1989) . Sensory abilities of cetaceans : laboratory and field evidence Proceedings of the NATO Research Workshop and Symposium of the Fifth International Theriological Congress on Sensory Ability of Cetaceans Advanced Rome , Italy z Tregen a , N. J . C ., Berrow , S .D., Hammond , P.S . and Leaper , R. ( 1997) . Harbour porpoise ( .) bycatch in set Phocoena phocoena L I ES Journal of Marine Science 54(5) : 896 ÿ 904 . gill nets in the Celtic Sea . C Andhra B., Shanker K., Choudhury , B. C . (2003) . Important nesting habitats of olive ridley turtles ( ) along the Lepidochelys olivacea Pradesh coast of eastern India . Oryx 37(4) . Trippel , E. A ., Wang , J .Y ., Strong , Tripathy , M. B., Carter , L.S ., and Conway , J .D. ( 1996) . Incidental mortality of harbour porpoise ( Phocoena wer Bay of Fundy . Canadian Journal of Fisheries and Aquatic Sciences 53 : 1294ÿ 1300 . ) by the gillÿnet fishery in the lo phocoena Trippel , ) bycatch E. A ., Strong , M.B., Terhune , J .M., and Conway , J .D. ( 1999) . Mitigation of harbour porpoise ( Phocoena phocoena wer Bay of Fundy . Canadian Journal of Fisheries and Aquatic Sciences 56( 113– 123) . in the gillnet fishery in the lo Trippel , E.A ., Holy , N.L., Palka , L D. ., Shepherd , T .D., Melvin , G .D., Terhune , 9 4 43 . J .M. (2003) . Nylon barium sulphate gillnet reduces porpoise and seabird mortality . Marine Mammal Science 1 ( 1) : 2 0ÿ2 Tudela , S ., Kai Kai , A ., Francesc , M., Mohamed , E.A ., and Guglielmi , P. (2005) . Driftnet fishing and biodiversity conservation : the case study of the largeÿscale Moroccan driftnet fleet operating in the Alboran Sea (S 65 – 78 Vlaams Instituut voor de Zee (20 11) . Maritime Boundaries http ://www .vliz .be/vmdcdata/marbound . Consulted on 20 11ÿ05ÿ 16 W Mediterranean) . Geodatabase , version v Biological Conservation 6 .1. Available online 12 1: at Van Waerebeek , K., and Reyes , J . C ( 1994) . Postÿban small cetacean takes off Peru : a review . Reports of the International Whaling Commission (Special Edition 15) : 503 ÿ 520 . Van Waerebeek , K., AlaroÿShigueto , J ., Onton , K., Santulan , L., Van Bressem , Mÿ F., and Vega , D. (2002) . Fisheries waters of Peru in 1999 ÿ 200 1. International Whaling Commission Report . SC/S4/S M10 Montes , D., related mortality of small cetaceans in neritic Van Waerebeek , K., Van Bressem , M.F., Félix , F., Alfaro , J ., Garc ía ÿGodos , and C . A ., L., Ontón , K., Montes , D. and Bello , R. ( 1997) . Mortality of dolphins and porpoises in coastal fisheries off Peru and southern Ecuador in 1994 . Biological Conservation 8 1: 43 ÿ 49 . Van Waerebeek , K. R., Julio Conservation 5 1 ( Issue 1) . 988) . C. (1 Catch of small cetaceans at Pucusana Port , central Vidal , O . Van Waerebeek , K. Findley , L.T . ( 1994) . Cetaceans and Gillnet Fisheries in Mexico , Caribbean : A preliminary Report . Report International W haling Committee Special Edition 15 . Vinther , M., and Larsen , during 987 Biological 1 Central America and the 4 Updated estimates of harbour porpoise ( Phocoena phocoena) bycatch in the Research and Management 6( 1) : 19 ÿ 24 . F. (200 ) . J Peru , Danish Wider North Sea bottomÿset gillnet fishery . ournal of Cetacean Wallace , B. P., Lewison , R., Mc Donald , S .L., Mc Donald , R.K., Kot , C .Y ., Kelez , S ., Bjorkland , R.K., Finkbeiner , E.M., Helmbrecht , S ., & Crowder , L. (20 10) . Global patterns of marine turtle bycatch . Conservation Letters 3(3) : 13 1ÿ 142 . Wang , J ., wimmer , Y . (2009) . Developing visual deterrents to reduce sea turtle bycatch : testing shark Proceedings of the Technical Workshop on Mitigating Sea Turtle Bycatch in Coastal Net Fisheries . Fisler , S . and S net illumination . 87 shapes and Watts , S . (200 1) . The end of the line? Global threats to sharks . W ILDA ID. Waugh , S., Filippi , D., Kirby D, Walker N.. in press .Ecological Risk Assessment for longline fishing effects on seabirds in the Western and Central Pacific . Marine policy Weidner , D., Serrano J . ( 1997) . World swordfish fisheries , An analysis of swordfish fisheries , market trend and trade patterns PastU PresentU Future . Volume IV . Part A . Section 1. Segment B. Chile . NOAA Tech . Memo NMFSU F/S POU27 : 843 p. Western and Central Pacific Fisheries Commission (20 10) . Annual report to the commission 20 10 . Scientific committee sixth regular session , Tonga . Whale and Dolphin Conservation Society (20 11) .<www .wdcs .org .uk> . Ecology of Comerson's Dolphin . W DCS . Online document consulted 1st August 20 11. Wilson , D. T ., Curtotti , R., Begg , G .A . (20 10) . Fishery status reports 2009 : status of fish stocks and fisheries managed by the Australian Government , Australian Bureau of Agricultural and Resource Economics U Bureau of Rural Sciences , Canberra . Woodley, T . H., and Lavigne , D.M ( 199 1) . Incidental capture of pinipeds in commercial fishing gear International Marine Mammal Association Technical Report 91U0 1. WW F, Morocco to eliminate destructive driftnet fishing . http ://mediterranean .panda .org . Consulted FebruaryUAugust 20 11. Yeo , B.H., Squires , D., Ibrahim , K., Gjertsen , H., Syed Mohd Kamil , S.K., Zulkifi , R., Groves , T ., Hong , M.C ., Tan , C .H. (2007) Fisher Profiles and Perceptions of Sea TurtleU Fishery Interactions : Case Study of East Coast Peninsular Malaysia . The World Fish Center Discussion Serial No . 6 . Yousuf , K. S . S. M. ,Anoop , A . K., Anoop , B., Afsal , V . V ., Vivekanandan , E. Kumarran , R. P., Rajagopalan , M., Krishnakumar , P. J MBA 2 K., Jayasankar , P. (2008) Observations on incidental catch of cetaceans in three landing centres along the Indian coast. Biodiversity Records . pp . 1U6 . Zerbini , A. N., Kotas , J .E. ( 1998) . A note on cetacean bycatch in pelagic driftnetting off Southern Brazil . Report International Whaling Committee 48 Zollet , E. A . (2009) . Bycatch of protected species and other species of concern in US east coast commercial fisheries . Endangered Species Research 9 : 49 U 59 Zydelis , R., Wallace , B., Gilman, E. and Werner , T . (2009) . Conservation of marine megafauna requires avoiding and minimizing fisheries bycatch . Conservation Biology 23 : 608U6 16 . 88 Ta ble 18 u T he 46 s pecies of t he C MS pa rt of t he cetacea n a nd si re nia n g rou p . CMS list I II I/II II I II I/II II II II II II II II II I I I II II II II II II II II I II II I/II II II II II II II I/II I/II II II II II II II II II Species code BAM BAB BOB BAE BMU BAO BAP BEB CAM CEC CEE CEH DEL DDE DUG EBA EBG EBJ GLM GRG HYA LGH LGA LGB LGS LGO MNV MMO NPH ORB ORH OOR POD POP POS DAL PYM POB SOC POT SNA SNC SNR SNL TUA TUT Group Species Cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean Balaena mysticetus Balaenoptera bonaerensis Balaenoptera borealis Balaenoptera edeni Balaenoptera musculus Balaenoptera omurai Balaenoptera physalus Berardius bairdii Caperea marginata Cephalorhynchus commersonii Cephalorhynchus eutropia Cephalorhynchus heavisidii Delphinapterus leucas Delphinus delphis Dugong dugon Eubalaena australis Eubalaena glacialis Eubalaena japonica Globicephala melas Grampus griseus Hyperoodon ampullatus Lagenodelphis hosei Lagenorhynchus acutus Lagenorhynchus albirostris Lagenorhynchus australis Lagenorhynchus obscurus Megaptera novaeangliae Monodon monoceros Neophocaena phocaenoides Orcaella brevirostris Orcaella heinsohni Orcinus orca Phocoena dioptrica Phocoena phocoena Phocoena spinipinnis Phocoenoides dalli Physeter macrocephalus Pontoporia blainvillei Sousa chinensis Sousa teuszii Stenella attenuate Stenella clymene Stenella coeruleoalba Stenella longirostris Tursiops aduncus Tursiops truncates Alternative species name Common name Bowhead Whale Antarctic Minke whale Sei Whale Bryde's whale Blue Whale Omura' Whale Fin Whale Baird's Beaked Whale Pygmy Right whale Commerson's Dolphin Chilean Dolphin Heaviside's Dolphin White Whale Common Dolphin Dugong Sea Cow Dugong Southern Right Whale Northern Right Whale North Pacific Right Whale Long-finned Pilot Whale Risso's Dolphin Northern Bottlenose Whale Fraser's Dolphin Atlantic White-sided Dolphin White-beaked Dolphin Peale's Dolphin Dusky Dolphin Humpback Whale Narwhal Finless Porpoise Irrawaddy Dolphin Australian Snubfin dolphin Killer whale Spectacled Porpoise Common Porpoise Burmeister Porpoise Dall's Porpoise Sperm Whale La Plata Dolphin Indo-Pacific Humpbacked Dolphin Atlantic Hump-backed Dolphin Pantropical Spotted Dolphin Clymene dolphin Striped Dolphin Spinner Dolphin Indian or Bottlenose Dolphin Bottlenosed Dolphin 89 Ta ble 19 T he 59 s pecies of t he C MS i n t he sea bi rd g rou p . CMS list I II II II I I/II II II II I/II II I I II II I I/II I/II II II I II II II II II II II II II II I I I I I II I II II II II I II II II I II II II II II II I II II Species code DAM DIP DIX LAA LAT LAU LGE LHM LIC LLE LML LRL LSA MAI MAH PEG PCR PCC PHG PXP PHA PHI PIR PHN PHF PHE PRO PCI PCO PRK PCW PTT POW PTG PUC PUM SPD SPH STF STE STG SBG STB CAT SDG STH STI STM STN STP STR STV STS SYW DNB THC Group Species Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds Seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds Diomedea amsterdamensis Diomedea epomophora Diomedea exulans Larus armenicus Larus atlanticus Larus audouinii Larus genei Larus hemprichii Larus ichthyaetus Larus leucophthalmus Larus melanocephalus Larus relictus Larus saundersi Macronectes giganteus Macronectes halli Pelecanoides garnotii Pelecanus crispus Pelecanus onocrotalus Phalacrocorax nigrogularis Phalacrocorax pygmeus Phoebastria_albatrus Phoebastria_immutabilis Phoebastria_irrorata Phoebastria_nigripes Phoebetria fusca Phoebetria palpebrata Procellaria aequinoctialis Procellaria cinerea Procellaria conspicillata Procellaria parkinsoni Procellaria westlandica Pterodroma atrata Pterodroma cahow Pterodroma phaeopygia Puffinus creatopus Puffinus mauretanicus Spheniscus demersus Spheniscus humboldti Sterna albifrons Sterna balaenarum Sterna bengalensis Sterna bergii Sterna bernsteini Sterna caspia Sterna dougallii Sterna hirundo Sterna lorata Sterna maxima Sterna nilotica Sterna paradisaea Sterna repressa Sterna sandvicensis Sterna saundersi Synthliboramphus wumizusume Thalassarche_bulleri Thalassarche_cauta Alternative species name Larus michahellis Diomedea albatrus Diomedea immutabilis Diomedea irrorata Diomedea nigripes Diomedea bulleri Diomedea cauta 90 Common name Amsterdam Albatross Royal Albatross Wandering Albatross Armenian Gull Olrog's Gull Audouin's Gull Slender-billed Gull Sooty Gull Great Black-headed Gull White-eyed Gull Mediterranean Gull Relict Gull Saunder's Gull Southern Giant Petrel Northern Giant Petrel Peruvian diving petrel Dalmatian Pelican White Pelican Socotra Cormorant Pygmy Cormorant Short-tailed Albatross Laysan Albatross Waved Albatross Black-footed Albatross Sooty Albatross Light-mantled Sooty Albatross White-chinned Petrel Grey Petrel Spectacled Petrel Black Petrel Westland Petrel Henderson Petrel Cahow Bermuda Petrel Dark-rumped Petrel Pink-footed Shearwater Balearic shearwater African Penguin Humboldt Penguin Little Tern Damara Tern Lesser Crested Tern Great Crested Tern Chinese Crested Tern Caspian Tern Roseate Tern Common Tern Peruvian tern Royal Tern Gull-billed Tern Arctic Tern White-cheeked Tern Sandwich Tern Saunder's Tern Japanese Murrelet Buller's Albatross Shy Albatross II II II THH DIC DIM seabirds seabirds seabirds Thalassarche_chlororhynchos Thalassarche_chrysostoma Thalassarche_melanophrys Diomedea chlororhynchos Diomedea chrysostoma Diomedea melanophris Yellow-nosed Albatross Grey-headed Albatross Black-browed Albatross Ta ble 20 ® T he 6 s pecies of t he C MS i n t he s ha rk g roup CMS list I/II I/II II II II II Species code CCC CTM IOX IPA LMN RHT Group Species Shark Shark Shark Shark Shark Shark Carcharodon carcharias Cetorhinus maximus Isurus oxyrinchus Isurus paucus Lamna nasus Rhincodon typus Alternative species name Common name Great White Shark Basking shark Shortfin Mako shark Longfin Mako shark Porbeagle shark Whale Shark Ta ble 2 1 ® T he 6 s pecies of t he C MS i n t he tu rt le g rou p CMS list I/II I/II I/II I/II I/II I/II Species code CAC CHM DCC EIM LPK LPV Group Species Alternative species name Turtle Turtle Turtle Turtle Turtle Turtle Caretta caretta Chelonia mydas Dermochelys coriacea Eretmochelys imbricata Lepidochelys kempii Lepidochelys olivacea Common name Loggerhead Turtle Green Turtle Leatherback Turtle Hawksbill Turtle Kemp's Ridley Turtle Ridley Turtle Ta ble 22 ® T he 6 s pecies of t he C MS i n t he ot he r sea ma mma ls g rou p CMS list II I I I/II II II Species code HGR LOF LOP MMN OFL PHV Group Species Marine mammals other Marine mammals other Marine mammals other Marine mammals other Marine mammals other Marine mammals other Halichoerus grypus Lontra feline Lontra provocax Monachus monachus Arctocephalus australis Phoca vitulina Alternative species name Common name Grey Seal Marine Otter Southern River Otter Mediterranean Monk Seal South American Seal Common Seal 91 Ta ble 2 3 Ë T hi rty two sea bi rd s pecies fo r w hic h a fo ragi ng Ëradius a pproac h was a pplied Species code Species Common name World population DAM DIP DIX LAT LAU MAI MAH PHG PHA PHI PIR PHN PHF PHE PRO PCI PCO PRK PCW PTT POW PTG PUC SPD SPH STB STI DNB THC THH DIC DIM Diomedea amsterdamensis Diomedea epomophora Diomedea exulans Larus atlanticus Larus audouinii Macronectes giganteus Macronectes halli Phalacrocorax nigrogularis Phoebastria albatrus Phoebastria immutabilis Phoebastria irrorata Phoebastria nigripes Phoebetria fusca Phoebetria palpebrata Procellaria aequinoctialis Procellaria cinerea Procellaria conspicillata Procellaria parkinsoni Procellaria westlandica Pterodroma atrata Pterodroma cahow Pterodroma phaeopygia Puffinus creatopus Spheniscus demersus Spheniscus humboldti Sterna bernsteini Sterna lorata Thalassarche bulleri Thalassarche cauta Thalassarche chlororhynchos Thalassarche chrysostoma Thalassarche melanophrys Amsterdam Albatross Royal Albatross Wandering Albatross Olrog's Gull Audouin's Gull Southern Giant Petrel Northern Giant Petrel Socotra Cormorant Short-tailed Albatross Laysan Albatross Waved Albatross Black-footed Albatross Sooty Albatross Light-mantled Sooty Albatross White-chinned Petrel Grey Petrel Spectacled Petrel Black Petrel Westland Petrel Henderson Petrel Cahow Bermuda Petrel Dark-rumped Petrel Pink-footed Shearwater African Penguin Humboldt Penguin Chinese Crested Tern Peruvian tern Buller's Albatross Shy Albatross Yellow-nosed Albatross Grey-headed Albatross Black-browed Albatross 26 7900 8050 3500 19200 50170 11800 110000 470 591356 9620 61307 13890 22611 1241000 111684 10000 3333 4000 74999.5 71 14999.5 24000 28500 15000 25 1750 30460 12585 69100 95748 601686 92 Pop type (0 whole; 1 breeding pairs) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 1 0 1 1 1 1 1 1 1 1 1 1 Foragi ng radius (km) 1200 1000 1800 7 160 189 550 0 1500 1000 165 250 350 1516 1868 600 600 522 400 195 200 200 200 400 170 100 100 413 200 1800 800 1100 Start of the Breeding season month 2 10 1 7 2 6 8 1 10 9 3 10 7 9 10 2 9 10 2 1 10 4 11 11 5 1 10 12 7 8 9 9 Endt of the Breeding season month 2 10 1 11 7 6 5 1 6 7 12 6 5 5 5 12 3 6 12 1 6 9 5 11 5 1 1 9 7 4 5 5 Table 24 ä Ene rgy use (kg of oi l equiva le nt pe r ca pita) by EEZ Ene rgy use refe rs to use of pri ma ry e ne rgy . befo re t ra nsfo rmatio n to ot he r e nd äuse fue ls hic h is equa l to i ndige nous productio n plus i mpo rts a nd stoc k ,w c ha nges, mi nus ex po rts a nd fue ls su pplied to s hi ps a nd ai rc raft e ngaged i n i nte rnatio na l t ra ns po rt. Esti matio n f ro m t he Wo rld Ba nk: ave rage va lue fo r pe rio2002ä200 a nd United Natio n Statistics Divisio n yea r 2004 2005 , o r 2006. Listed i n a lpha betica l o rde r by EEZ na me. Country Albania Algeria Sovereign Albania Algeria ISO ALB DZA Energy use (kg of oil eq per capita) average 2000-2005 615 901 American Samoa Angola Antigua and Barbuda Argentina Australia United States Angola Antigua and Barbuda Argentina Australia ASM AGO 7827 536 ATG ARG AUS 1695 1652 5647 Macquarie Island Australia Australia Australia AUS AUS 5647 5647 Bahamas Exclusive Economic Zone Bahraini Exclusive Economic Zone Bangladeshi Exclusive Economic Zone Bahamas Bahrain Bangladesh Bahamas Bahrain Bangladesh BHS BHR BGD 2144 9407 142 Barbados Exclusive Economic Zone Belgian Exclusive Economic Zone Barbados Belgium Barbados Belgium BRB BEL 1451 5594 Bermudian Exclusive Economic Zone Bosnian and Herzegovinian Exclusive Economic Zone Bouvet Island Exclusive Economic Zone Brazilian Exclusive Economic Zone Trindade Exclusive Economic Zone Bermuda Bosnia and Herzegovina Bouvet Island Brazil Trindade United Kingdom Bosnia and Herzegovina Norway Brazil Brazil BMU 2717 BIH BVT BRA BRA 1167 5772 1091 1091 Belizean Exclusive Economic Zone British Indian Ocean Territory Exclusive Economic Zone Solomon Islands Exclusive Economic Zone British Virgin Islands Exclusive Economic Zone Belize British Indian Ocean Territory Belize BLZ 1021 United Kingdom IOT 3729 EEZ name Albanian Exclusive Economic Zone Algerian Exclusive Economic Zone American Samoa Exclusive Economic Zone Angolan Exclusive Economic Zone Antigua and Barbuda Exclusive Economic Zone Argentinean Exclusive Economic Zone Australian Exclusive Economic Zone Macquarie Island Exclusive Economic Zone Lord Howe Isl Australia Solomon Islands SLB 123 United Kingdom Brunei Darussalam Bulgaria Myanmar Eritrea Cambodia Cameroon Canada VGB 1464 Brunei Darussalam Bulgarian Exclusive Economic Zone Myanmar Exclusive Economic Zone Eritrean Exclusive Economic Zone Cambodian Exclusive Economic Zone Cameroonian Exclusive Economic Zone Canadian Exclusive Economic Zone Solomon Islands British Virgin Islands Brunei Darussalam Bulgaria Myanmar Eritrea Cambodia Cameroon Canada BRN BGR MMR ERI KHM CMR CAN 7472 2500 270 194 323 392 8012 Cape Verdean Exclusive Economic Zone Cape Verde Cape Verde CPV 209 Cayman Islands Exclusive Economic Zone Sri Lankan Exclusive Economic Zone Cayman Islands Sri Lanka United Kingdom Sri Lanka CYM LKA 3387 438 Chilean Exclusive Economic Zone Chile Chile CHL 1475 93 Source World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank World Bank 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) Chile CHL 1475 Chile CHL 1475 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) Chile China Taiwan CHL CHN TWN 1475 906 906 2006 (United Nation Statistics Division) World Bank World Bank Christmas Island Cocos Islands Colombia Australia Australia Colombia CXR CCK COL 5647 5647 676 Comoro Islands France Democratic Republic of the Congo République du Congo COM MYT 60 1108 COD 330 World Bank Congolese Exclusive Economic Zone Comoro Islands Mayotte Democratic Republic of the Congo République du Congo COG 292 Cook Islands Exclusive Economic Zone Costa Rican Exclusive Economic Zone Croatian Exclusive Economic Zone Cuban Exclusive Economic Zone Cypriote Exclusive Economic Zone Beninese Exclusive Economic Zone Bornholm Exclusive Economic Zone Danish Exclusive Economic Zone Cook Islands Costa Rica Croatia Cuba Cyprus Benin Denmark Denmark New Zealand Costa Rica Croatia Cuba Cyprus Benin Denmark Denmark COK CRI HRV CUB CYP BEN DNK DNK 1033 770 1822 956 2653 335 3602 3602 Dominican Exclusive Economic Zone Dominican Republic Exclusive Economic Zone Ecuadorean Exclusive Economic Zone Dominica Dominican Republic Ecuador DMA 578 DOM ECU 818 716 World Bank World Bank Galapagos Exclusive Economic Zone El Salvador Exclusive Economic Zone Equatorial Guinean Exclusive Economic Zone Estonian Exclusive Economic Zone Dominica Dominican Republic Ecuador Galapagos Islands El Salvador Equatorial Guinea Estonia World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) Ecuador El Salvador ECU SLV 716 696 Equatorial Guinea Estonia GNQ EST 1008 3790 Faeroe Islands Exclusive Economic Zone Faeroe Islands Denmark FRO 4671 Falkland Islands Exclusive Economic Zone Falkland Islands South Georgia and the South Sandwich Islands United Kingdom FLK 4725 World Bank World Bank 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) United Kingdom SGS 3729 Fiji Finland France Glorioso Islands Juan de Nova Island Bassas da India Ile Europa Ile Tromelin Fiji Finland France France FJI FIN FRA ATF 665 6420 4294 1062 France France France France ATF ATF ATF ATF 1062 1062 1062 1062 French Guiana Exclusive Economic Zone French Polynesian Exclusive Economic Zone French Guiana France GUF 1413 French Polynesia France PYF 1108 Djiboutian Exclusive Economic Zone Djibouti Djibouti DJI 174 Easter Island Exclusive Economic Zone Desventuradas Isl.(Chile) J. Fernandez Felix and Ambrosio Isl. (Chile) Chinese Exclusive Economic Zone Taiwanese Exclusive Economic Zone Christmas Island Exclusive Economic Zone Cocos Islands Exclusive Economic Zone Colombian Exclusive Economic Zone Comoran Exclusive Economic Zone Mayotte Exclusive Economic Zone Democratic Republic of the Congo Exclusive Economic Zone South Georgian Exclusive Economic Zone Fijian Exclusive Economic Zone Finnish Exclusive Economic Zone French Exclusive Economic Zone Glorioso Exclusive Economic Zone Juan de Nova Exclusive Economic Zone Bassas da India Exclusive Economic Zone Ile Europa Exclusive Economic Zone Ile Tromelin Exclusive Economic Zone Easter Island Desventuradas Island J. Fernandez Felix and Ambrosio Isl. (Chile) China Taiwan 94 World Bank World Bank World Bank 2006 (United Nation Statistics Division) Reunion Island World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) Gabonese Exclusive Economic Zone Georgian Exclusive Economic Zone Gabon Georgia Gabon Georgia GAB GEO 1240 630 Gambian Exclusive Economic Zone Gambia Palestinian territories Germany Ghana United Kingdom GMB 75 Gaza strip German Exclusive Economic Zone Ghanaian Exclusive Economic Zone Gibraltarian Exclusive Economic Zone Gambia Palestinian territories Germany Ghana Gibraltar PSE DEU GHA GIB 265 4135 397 4429 Line Group Exclusive Economic Zone Line Group Kiribati KIR 92 Phoenix Group Exclusive Economic Zone Phoenix Group Kiribati KIR 92 Kiribati Exclusive Economic Zone Greek Exclusive Economic Zone Kiribati Greece Kiribati Greece KIR GRC 92 2568 Greenlandic Exclusive Economic Zone Greenland Denmark GRL 3360 Grenadian Exclusive Economic Zone Grenada GRD 925 Guadeloupe Exclusive Economic Zone Guam EEZ Guatemalan Exclusive Economic Zone Grenada Guadeloupe and Martinique Guam Guatemala France United States Guatemala GLP GUM GTM 1503 7827 612 Guinea Bissau Exclusive Economic Zone Guinea Bissau Guinea Bissau GNB 67 Guyanese Exclusive Economic Zone Haitian Exclusive Economic Zone Heard and McDonald Islands Exclusive Economic Zone Honduran Exclusive Economic Zone Guyana Haiti Heard and McDonald Islands Honduras Guyana Haiti GUY HTI 626 247 Australia Honduras HMD HND 5647 540 Honk Kong Icelandic Exclusive Economic Zone Indian Exclusive Economic Zone Andaman and Nicobar Islands Exclusive Economic Zone Indonesian Exclusive Economic Zone (eastern) Indonesian Exclusive Economic Zone (western) Iranian Exclusive Economic Zone Iraqi Exclusive Economic Zone Irish Exclusive Economic Zone Israeli Exclusive Economic Zone Italian Exclusive Economic Zone Ivory Coast Exclusive Economic Zone Jamaican Exclusive Economic Zone Japanese Exclusive Economic Zone Japan Outer Isl. Johnston Atoll Exclusive Economic Zone Jordanian Exclusive Economic Zone Kenyan Exclusive Economic Zone North Korean Exclusive Economic Zone South Korean Exclusive Economic Zone Kuwaiti Exclusive Economic Zone Lebanese Exclusive Economic Zone China Iceland India Andaman and Nicobar China Iceland India CHN ISL IND 1746 11333 455 India CHN 906 World Bank Indonesia Indonesia IDN 790 World Bank Indonesia Iran Iraq Ireland Israel Italy Ivory Coast Jamaica Japan Japan Johnston Atoll Jordan Kenya North Korea South Korea Kuwait Lebanon Indonesia Iran Iraq Ireland Israel Italy Ivory Coast Jamaica Japan Japan United States Jordan Kenya North Korea South Korea Kuwait Lebanon IDN IRN IRQ IRL ISR ITA CIV JAM JPN JPN USA JOR KEN PRK KOR KWT LBN 790 1972 1102 3452 2911 3014 387 1431 4033 4033 7827 1021 449 865 4074 9142 1326 Latvian Exclusive Economic Zone Latvia Latvia LVA 1453 Liberian Exclusive Economic Zone Libyan Exclusive Economic Zone Liberia Libya Liberia Libya LBR LBY 61 3063 95 World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank World Bank 2004 (United Nation Statistics Division) 2004 (United Nation Statistics Division) 2004 (United Nation Statistics Division) World Bank 2004 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank Lithuanian Exclusive Economic Zone Lithuania Lithuania LTU 2517 Macao China China CHN 1594 Madagascan Exclusive Economic Zone Malaysian Exclusive Economic Zone (west) Malaysian Exclusive Economic Zone (east) Malaysia Sabah Madagascar Madagascar MDG 45 Malaysia Malaysia MYS 2098 World Bank Malaysia Malaysia Malaysia Malaysia MYS MYS 2098 2098 Maldives Exclusive Economic Zone Malaysia Sarawak Maltese Exclusive Economic Zone Maldives Malaysia Malta Maldives Malaysia Malta MDV MYS MLT 965 2098 1995 Martinique Martinique France MTQ 1577 Mauritanian Exclusive Economic Zone Mauritania Mauritania MRT 165 Mauritian Exclusive Economic Zone Mexican Exclusive Economic Zone Hawai borthwest islands Monégasque Exclusive Economic Zone Mauritius Mexico United States Monaco Mauritius Mexico United States Monaco MUS MEX USA MCO 835 1511 7827 4294 Montserrat Exclusive Economic Zone Moroccan Exclusive Economic Zone Mozambican Exclusive Economic Zone Omani Exclusive Economic Zone Namibian Exclusive Economic Zone Montserrat Morocco Mozambique Oman Namibia United Kingdom Morocco Mozambique Oman Namibia MSR MAR MOZ OMN NAM 2235 372 400 3499 616 Nauruan Exclusive Economic Zone Dutch Exclusive Economic Zone Nauru Netherlands Southern SaintMartin Netherlands Antilles Nauru Netherlands NRU NLD 3457 4705 Netherlands ANT 1204 Netherlands ANT 1204 New Caledonia France NCL 3631 Vanuatu Exclusive Economic Zone New Zealand Exclusive Economic Zone Nicaraguan Exclusive Economic Zone Nigerian Exclusive Economic Zone Vanuatu New Zealand Nicaragua Nigeria Vanuatu New Zealand Nicaragua Nigeria VUT NZL NIC NGA 139 4086 542 730 Niue Exclusive Economic Zone Norfolk Island Exclusive Economic Zone Norwegian Exclusive Economic Zone Jan Mayen Exclusive Economic Zone New Zealand Australia Norway Norway NIU NFK NOR SJM 605 5647 5772 5772 Northern Mariana Islands Economic Zone Micronesian Exclusive Economic Zone Niue Norfolk Island Norway Jan Mayen Northern Mariana Islands and Guam Micronesia World Bank World Bank 2006 (United Nation Statistics Division) World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2004 (United Nation Statistics Division) World Bank World Bank France 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank United States Micronesia MNP FSM 7827 605 Marshall Islands Exclusive Economic Zone Marshall Islands Marshall Islands MHL 584 Palau Exclusive Economic Zone Pakistani Exclusive Economic Zone Panamanian Exclusive Economic Zone Papua New Guinean Exclusive Economic Zone Peruvian Exclusive Economic Zone Philippines Exclusive Economic Zone Pitcairn Exclusive Economic Zone Polish Exclusive Economic Zone Palau Pakistan Panama Papua New Guinea Peru Philippines Pitcairn Poland Palau Pakistan Panama Papua New Guinea Peru Philippines United Kingdom Poland PLW PAK PAN 3168 460 842 PNG PER PHL PCN POL 257 464 493 3729 2445 Sint-Maarten Exclusive Economic Zone Netherlands Antilles Exclusive Economic Zone New Caledonian Exclusive Economic Zone 96 World Bank 2006 (United Nation Statistics Division) 2004 (United Nation Statistics Division) World Bank Niue 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank Portuguese Exclusive Economic Zone Madeiran Exclusive Economic Zone Azores Exclusive Economic Zone Portugal Madeira Azores Portugal Portugal Portugal PRT PRT PRT 2385 2385 2385 Guinean Exclusive Economic Zone Guinea Guinea GIN 47 East Timor Exclusive Economic Zone Oecussi Ambeno Exclusive Economic Zone East Timor East Timor TLS 56 Oecussi Ambeno Puerto Rico and Virgin Islands of the United States Qatar East Timor TLS 56 United States Qatar PRI QAT 165 19354 Puerto Rican Exclusive Economic Zone Qatari Exclusive Economic Zone World Bank World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) World Bank World Bank World Bank World Bank World Bank Réunion Exclusive Economic Zone Romanian Exclusive Economic Zone Russia (Barents Sea) Russia (Black Sea) Russia (Baltic Sea Kalinigrad) Russia (Pacific) Russian Exclusive Economic Zone (Siberia) Russia (Baltic Sea St Petersburg) St. Helena Exclusive Economic Zone Saint Kitts and Nevis Exclusive Economic Zone Réunion Romania Russia Russia Russia Russia France Romania Russia Russia Russia Russia REU ROU RUS RUS RUS RUS 1062 1799 4293 4293 4293 4293 Russia Russia Saint Helena Saint Kitts and Nevis Russia Russia United Kingdom Saint Kitts and Nevis RUS RUS SHN 4293 4293 3729 KNA 1080 Anguilla Exclusive Economic Zone Anguilla United Kingdom AIA 1242 Saint Lucia Exclusive Economic Zone Saint-Pierre and Miquelon Exclusive Economic Zone Saint Vincent and the Grenadines Exclusive Economic Zone Sao Tome and Principe Exclusive Economic Zone Saudi Arabian Exclusive Economic Zone (Red Sea) Saudi Arabian Exclusive Economic Zone (persian Gulf) Senegalese Exclusive Economic Zone Saint Lucia Saint Pierre and Miquelon Saint Vincent and the Grenadines Sao Tome and Principe Saint Lucia LCA 749 France Saint Vincent and the Grenadines Sao Tome and Principe SPM 4294 VCT 595 STP 236 Saudi Arabia Saudi Arabia SAU 5249 World Bank Saudi Arabia Senegal Saudi Arabia Senegal SAU SEN 5249 237 Seychellois Exclusive Economic Zone Seychelles Seychelles SYC 2877 Sierra Leonian Exclusive Economic Zone Singaporean Exclusive Economic Zone Vietnamese Exclusive Economic Zone Slovenian Exclusive Economic Zone Sierra Leone Singapore Vietnam Slovenia Sierra Leone Singapore Vietnam Slovenia SLE SGP VNM SVN 44 4548 513 3402 Somali Exclusive Economic Zone South African Exclusive Economic Zone Prince Edward Islands Exclusive Economic Zone Canary Islands Exclusive Economic Zone Spanish Exclusive Economic Zone Western Saharan Exclusive Economic Zone Sudanese Exclusive Economic Zone Somalia South Africa Prince Edward Islands Canary Islands Spain Somalia South Africa SOM ZAF 21 2621 World Bank World Bank 2006 (United Nation Statistics Division) 2004 (United Nation Statistics Division) World Bank World Bank World Bank 2006 (United Nation Statistics Division) World Bank South Africa Spain Spain ZAF ESP ESP 2621 3059 3059 World Bank World Bank World Bank Western Sahara Sudan Morocco Sudan ESH SDN 372 390 Surinamese Exclusive Economic Zone Svalbard Isl. (Norway) Suriname Svalbard Isl. Suriname Norway SUR GGY 1416 5772 Swedish Exclusive Economic Zone Syrian Exclusive Economic Zone Thailand Exclusive Economic Zone Sweden Syria Thailand Sweden Syria Thailand SWE SYR THA 2953 979 1235 97 World Bank World Bank World Bank 2004 (United Nation Statistics Division) 2006 (United Nation Statistics Division) 2004 (United Nation Statistics Division) World Bank 2004 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank World Bank 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) World Bank World Bank Togolese Exclusive Economic Zone Tokelau Exclusive Economic Zone Togo Tokelau Togo New Zealand TGO TKL 392 605 Tongan Exclusive Economic Zone Trinidad and Tobago Exclusive Economic Zone United Arab Emirates Exclusive Economic Zone Tunisian Exclusive Economic Zone Turkish Exclusive Economic Zone (Mediterranean Sea) Turkey Black Sea Turks and Caicos Exclusive Economic Zone Tuvaluan Exclusive Economic Zone Ukrainian Exclusive Economic Zone Egyptian Exclusive Economic Zone United Kingdom Exclusive Economic Zone Jersey Exclusive Economic Zone Guernsey Exclusive Economic Zone Tanzanian Exclusive Economic Zone Alaskan Exclusive Economic Zone Hawaiian Exclusive Economic Zone (main island) Navassa Isl (Haiti) Palmyra Atoll Exclusive Economic Zone Jarvis Island Exclusive Economic Zone Howland and Baker Island Exclusive Economic Zone United States Exclusive Economic Zone (West Coast) USA East Coast USA Golf Of Mexico Ascension Exclusive Economic Zone Tristan Da Cunha Exclusive Economic Zone Uruguayan Exclusive Economic Zone Venezuelan Exclusive Economic Zone Wake Island Exclusive Economic Zone Wallis and Futuna Exclusive Economic Zone Tonga Trinidad and Tobago United Arab Emirates Tunisia Tonga Trinidad and Tobago United Arab Emirates Tunisia TON 555 TTO 8019 World Bank ARE TUN 10724 799 World Bank World Bank Turkey Turkey Turks and Caicos Islands Tuvalu Ukraine Egypt United Kingdom Jersey Guernsey Tanzania Alaska Turkey Turkey TUR TUR 1118 1118 World Bank World Bank United Kingdom Tuvalu Ukraine Egypt United Kingdom United Kingdom United Kingdom Tanzania United States TCA TUV UKR EGY GBR GBR GBR TZA USA 3729 -1 2938 686 3729 3729 3729 410 7827 World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank World Bank Hawaii Haiti Palmyra Atoll Jarvis Island Howland Island and Baker Island United States Haiti United States United States USA HTI USA USA 7827 247 7827 7827 World Bank World Bank World Bank World Bank United States USA 7827 World Bank United States United States United States Ascension United States United States United States United Kingdom USA USA USA ASC 7827 7827 7827 3729 World Bank World Bank World Bank World Bank Tristan da Cunha Uruguay Venezuela Wake Island United Kingdom Uruguay Venezuela United States TAA URY VEN WAK 3729 892 2304 7827 Wallis and Futuna France WLF 537 Samoa Yemen SerbiaMontenegro Amsterdam Island and Saint Paul Island Crozet Islands Kerguelen Islands Samoa Yemen SerbiaMontenegro WSM YEM 303 273 SCG 1562 World Bank World Bank World Bank World Bank 2006 (United Nation Statistics Division) 2006 (United Nation Statistics Division) World Bank 2006 (United Nation Statistics Division) France France ATF ATF 4294 4294 World Bank World Bank France ATF 4294 World Bank Clipperton Island France Disputed China/Taiwan/Viet nam Disputed China/Philippines/ Vietnam/Taiwan/M alaysia Disputed Russia/Japan Joint Regime Colombia/Jamaic CPT 4294 World Bank XXX 906 World Bank XXX 905 World Bank XXX 4293 World Bank XXX 1431 World Bank Samoan Exclusive Economic Zone Yemeni Exclusive Economic Zone Serbia-Montenegrian Exclusive Economic Zone Amsterdam Island & St. Paul Island Exclusive Economic Zone Crozet Islands Exclusive Economic Zone Kerguelen Islands Exclusive Economic Zone Clipperton Island Exclusive Economic Zone Paracel Islands Exclusive Economic Zone Paracel Islands Spratly Islands Exclusive Economic Zone Spratly Islands Russia-Japan conflict zone Southern Kuriles Colombia Jamaica Colombia - Jamaica (Joint Regime) 98 World Bank Niue 2006 (United Nation Statistics Division) Japan - South Korea Conflict Zone Nigeria - Sao Tome and Principe Joint Regime Japan/ South Korea Disputed China/Taiwan Japan - South Korea Conflict Zone Joint Development Area Australia - East Timor Australia - East Timor Protected Zone established under the Torres Strait Treaty Area en controversia (disputed - Peruvian point of view) Antarctic 200NM zone beyond the coastline Australia - Papua New Guinea Disputed Chile/Peru Nigeria - Sao Tome and Principe Joint Joint Japan - Korea Conflict Zone Saint-Martin Exclusive Economic Zone Azerbaijanis Exclusive Economic Zone Kazakh Exclusive Economic Zone Turkmen Exclusive Economic Zone Antarctica Northern SaintMartin Azerbaijan Kazakhstan Turkmenistan a Joint Regime Nigeria - Sao Tome and Principe Joint Regime Japan/ South Korea Disputed China/Taiwan Disputed Japan/South Korea Joint Regime Australia/East Timor Joint Regime Australia - Papua New Guinea Disputed Chile/Peru XXX 730 World Bank XXX 4074 World Bank XXX 906 World Bank XXX 4074 World Bank XXX 5647 World Bank XXX 5647 XXX 1475 World Bank 2006 (United Nation Statistics Division) Antarctica ATA 0 World Bank France Azerbaijan Kazakhstan Turkmenistan MAF AZE KAZ TKM 1503 1466 3100 3314 Guadeloupe World Bank World Bank World Bank 99 Table 25 Species ranked by overla p. A ll species Rank 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 Species code NPH STB ORB DUG STM LSA SOC STI POT SYW TUA STV CEH SPD STE LAU PHG HGR STR LIC STS STG STN POP PEG SPH LGE STF PHV LOF LML LPV EBJ SDG CAT POS BAM EBG MMN BEB BAO SBG LHM DAL CEE PUM Family cetacean seabirds cetacean cetacean seabirds seabirds cetacean seabirds cetacean seabirds cetacean seabirds cetacean seabirds seabirds seabirds seabirds marine mammals other seabirds seabirds seabirds seabirds seabirds cetacean seabirds seabirds seabirds seabirds marine mammals other marine mammals other seabirds turtle cetacean seabirds seabirds cetacean cetacean cetacean marine mammals other cetacean cetacean seabirds seabirds cetacean cetacean seabirds Species Neophocaena phocaenoides Sterna bernsteini Orcaella brevirostris Dugong dugon Sterna maxima Larus saundersi Sousa chinensis Sterna lorata Sousa teuszii Synthliboramphus wumizusume Tursiops aduncus Sterna sandvicensis Cephalorhynchus heavisidii Spheniscus demersus Sterna balaenarum Larus audouinii Phalacrocorax nigrogularis Halichoerus grypus Sterna repressa Larus ichthyaetus Sterna saundersi Sterna bengalensis Sterna nilotica Phocoena phocoena Pelecanoides garnotii Spheniscus humboldti Larus genei Sterna albifrons Phoca vitulina Lontra felina Larus melanocephalus Lepidochelys olivacea Eubalaena japonica Sterna dougallii Sterna caspia Phocoena spinipinnis Balaena mysticetus Eubalaena glacialis Monachus monachus Berardius bairdii Balaenoptera omurai Sterna bergii Larus hemprichii Phocoenoides dalli Cephalorhynchus eutropia Puffinus mauretanicus 100 Common name Finless Porpoise Chinese Crested Tern Irrawaddy Dolphin Dugong Sea Cow Dugong Royal Tern Saunder's Gull Indo-Pacific Humpbacked Dolphin Peruvian tern Atlantic Hump-backed Dolphin Japanese Murrelet Indian or Bottlenose Dolphin Sandwich Tern Heaviside's Dolphin African Penguin Damara Tern Audouin's Gull Socotra Cormorant Grey Seal White-cheeked Tern Great Black-headed Gull Saunder's Tern Lesser Crested Tern Gull-billed Tern Common Porpoise Peruvian diving petrel Humboldt Penguin Slender-billed Gull Little Tern Common Seal Marine Otter Mediterranean Gull Ridley Turtle North Pacific Right Whale Roseate Tern Caspian Tern Burmeister Porpoise Bowhead Whale Northern Right Whale Mediterranean Monk Seal Baird's Beaked Whale Omura' Whale Great Crested Tern Sooty Gull Dall's Porpoise Chilean Dolphin Balearic shearwater Overlap index 1.729834 1.717597 1.698112 1.518014 1.515499 1.388563 1.332731 1.271844 1.259429 1.235895 1.206462 1.205789 1.164302 1.158219 1.150589 1.141359 1.116908 1.099358 1.090445 1.089308 1.089156 1.078656 1.061086 1.060545 1.037612 1.028118 1.02097 1.008609 0.988178 0.974533 0.973279 0.972248 0.968866 0.959458 0.956267 0.952267 0.942369 0.935856 0.92759 0.923174 0.920814 0.90351 0.900748 0.899804 0.897024 0.890444 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 LGA LGB EIM CTM LPK GRG CAC DCC LAA STH PCC DEL IPA PHA LLE DDE LGH PUC CHM RHT OFL HYA CCC LMN SNL SNA IOX SNR TUT BAE PTG BOB BAP MNV PYM OOR MMO BMU PIR PCR POB LGO LGS SNC PHI LOP LAT GLM CEC DIM DAM PCW DNB PHN EBA CAM BAB cetacean cetacean turtle shark turtle cetacean turtle turtle seabirds seabirds seabirds cetacean shark seabirds seabirds cetacean cetacean seabirds turtle shark marine mammals other cetacean shark shark cetacean cetacean shark cetacean cetacean cetacean seabirds cetacean cetacean cetacean cetacean cetacean cetacean cetacean seabirds seabirds cetacean cetacean cetacean cetacean seabirds marine mammals other seabirds cetacean cetacean seabirds seabirds seabirds seabirds seabirds cetacean cetacean cetacean Lagenorhynchus acutus Lagenorhynchus albirostris Eretmochelys imbricata Cetorhinus maximus Lepidochelys kempii Grampus griseus Caretta caretta Dermochelys coriacea Larus armenicus Sterna hirundo Pelecanus onocrotalus Delphinapterus leucas Isurus paucus Phoebastria_albatrus Larus leucophthalmus Delphinus delphis Lagenodelphis hosei Puffinus creatopus Chelonia mydas Rhincodon typus Arctocephalus australis Hyperoodon ampullatus Carcharodon carcharias Lamna nasus Stenella longirostris Stenella attenuata Isurus oxyrinchus Stenella coeruleoalba Tursiops truncatus Balaenoptera edeni Pterodroma phaeopygia Balaenoptera borealis Balaenoptera physalus Megaptera novaeangliae Physeter macrocephalus Orcinus orca Monodon monoceros Balaenoptera musculus Phoebastria_irrorata Pelecanus crispus Pontoporia blainvillei Lagenorhynchus obscurus Lagenorhynchus australis Stenella clymene Phoebastria_immutabilis Lontra provocax Larus atlanticus Globicephala melas Cephalorhynchus commersonii Thalassarche_melanophrys Diomedea amsterdamensis Procellaria westlandica Thalassarche_bulleri Phoebastria_nigripes Eubalaena australis Caperea marginata Balaenoptera bonaerensis 101 Atlantic White-sided Dolphin White-beaked Dolphin Hawksbill Turtle Basking shark Kemp's Ridley Turtle Risso's Dolphin Loggerhead Turtle Leatherback Turtle Armenian Gull Common Tern White Pelican White Whale Longfin Mako shark Short-tailed Albatross White-eyed Gull Common Dolphin Fraser's Dolphin Pink-footed Shearwater Green Turtle Whale Shark South American Seal Northern Bottlenose Whale Great White Shark Porbeagle shark Spinner Dolphin Pantropical Spotted Dolphin Shortfin Mako shark Striped Dolphin Bottlenosed Dolphin Bryde's whale Dark-rumped Petrel Sei Whale Fin Whale Humpback Whale Sperm Whale Killer whale Narwhal Blue Whale Waved Albatross Dalmatian Pelican La Plata Dolphin Dusky Dolphin Peale's Dolphin Clymene dolphin Laysan Albatross Southern River Otter Olrog's Gull Long-finned Pilot Whale Commerson's Dolphin Black-browed Albatross Amsterdam Albatross Westland Petrel Buller's Albatross Black-footed Albatross Southern Right Whale Pygmy Right whale Antarctic Minke whale 0.882536 0.877474 0.872379 0.865391 0.845511 0.839958 0.826912 0.826912 0.820656 0.811912 0.807091 0.803405 0.799951 0.793051 0.786896 0.785438 0.783364 0.782582 0.781022 0.780718 0.776876 0.770532 0.767739 0.764928 0.762594 0.759866 0.754187 0.746145 0.739723 0.737189 0.733426 0.720079 0.718872 0.716756 0.715051 0.714425 0.709832 0.696779 0.690936 0.682034 0.681307 0.64286 0.634419 0.63313 0.600686 0.579696 0.572399 0.570857 0.535107 0.528156 0.525587 0.503979 0.495736 0.495035 0.494585 0.491002 0.462312 104 105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 120 121 122 123 PRK POD PHF THH PRO LRL THC PCI STP ORH DIC MAI DIP DIX MAH PCO PXP PHE POW PTT seabirds cetacean seabirds seabirds seabirds seabirds seabirds seabirds seabirds cetacean seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds Procellaria parkinsoni Phocoena dioptrica Phoebetria fusca Thalassarche_chlororhynchos Procellaria aequinoctialis Larus relictus Thalassarche_cauta Procellaria cinerea Sterna paradisaea Orcaella heinsohni Thalassarche_chrysostoma Macronectes giganteus Diomedea epomophora Diomedea exulans Macronectes halli Procellaria conspicillata Phalacrocorax pygmeus Phoebetria palpebrata Pterodroma cahow Pterodroma atrata 102 Black Petrel Spectacled Porpoise Sooty Albatross Yellow-nosed Albatross White-chinned Petrel Relict Gull Shy Albatross Grey Petrel Arctic Tern Australian Snubfin dolphin Grey-headed Albatross Southern Giant Petrel Royal Albatross Wandering Albatross Northern Giant Petrel Spectacled Petrel Pygmy Cormorant Light-mantled Sooty Albatross Cahow Bermuda Petrel Henderson Petrel 0.46143 0.445766 0.436894 0.436009 0.435673 0.430667 0.428971 0.426469 0.426419 0.423199 0.415607 0.410614 0.41002 0.403693 0.403004 0.395583 0.388056 0.382575 0.311002 0.268927 Figure 16 _ EEZs and High Seas FAO a reas s howing wit h t he u n_weighted exposures summed ac ross all s pecies. A reas wit h co lours furt hest up t he scale ba r (red co lours) had higher s pecies exposures. Ta ble 26 _ All s pecies ranked by t hei r u n_weighted exposure index Rank 1 2 3 4 5 6 7 8 9 10 11 12 13 14 Species code NPH ORB DUG STM SOC POT SYW TUA CEH SPD LAU PHG HGR LIC Family cetacean cetacean cetacean seabirds cetacean cetacean seabirds cetacean cetacean seabirds seabirds seabirds marine mammals other seabirds Species Neophocaena phocaenoides Orcaella brevirostris Dugong dugon Sterna maxima Sousa chinensis Sousa teuszii Synthliboramphus wumizusume Tursiops aduncus Cephalorhynchus heavisidii Spheniscus demersus Larus audouinii Phalacrocorax nigrogularis Halichoerus grypus Larus ichthyaetus 103 Common name Finless Porpoise Irrawaddy Dolphin Dugong Sea Cow Dugong Royal Tern Indo-Pacific Humpbacked Dolphin Atlantic Hump-backed Dolphin Japanese Murrelet Indian or Bottlenose Dolphin Heaviside's Dolphin African Penguin Audouin's Gull Socotra Cormorant Grey Seal Great Black-headed Gull Un-weighted exposure index 2.090 2.052 1.834 1.831 1.610 1.522 1.493 1.458 1.407 1.399 1.379 1.349 1.328 1.316 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 70 71 POP PEG SPH LGE PHV LOF LML LPV EBJ POS BAM EBG MMN BEB BAO SBG LHM DAL CEE PUM LGA LGB EIM CTM LPK GRG CAC DCC LAA PCC DEL IPA PHA LLE DDE LGH PUC CHM RHT OFL HYA CCC LMN SNL SNA IOX SNR TUT PTG BOB BAP MNV PYM OOR MMO BMU PIR cetacean seabirds seabirds seabirds marine mammals other marine mammals other seabirds turtle cetacean cetacean cetacean cetacean marine mammals other cetacean cetacean seabirds seabirds cetacean cetacean seabirds cetacean cetacean turtle shark turtle cetacean turtle turtle seabirds seabirds cetacean shark seabirds seabirds cetacean cetacean seabirds turtle shark marine mammals other cetacean shark shark cetacean cetacean shark cetacean cetacean seabirds cetacean cetacean cetacean cetacean cetacean cetacean cetacean seabirds Phocoena phocoena Pelecanoides garnotii Spheniscus humboldti Larus genei Phoca vitulina Lontra felina Larus melanocephalus Lepidochelys olivacea Eubalaena japonica Phocoena spinipinnis Balaena mysticetus Eubalaena glacialis Monachus monachus Berardius bairdii Balaenoptera omurai Sterna bergii Larus hemprichii Phocoenoides dalli Cephalorhynchus eutropia Puffinus mauretanicus Lagenorhynchus acutus Lagenorhynchus albirostris Eretmochelys imbricata Cetorhinus maximus Lepidochelys kempii Grampus griseus Caretta caretta Dermochelys coriacea Larus armenicus Pelecanus onocrotalus Delphinapterus leucas Isurus paucus Phoebastria_albatrus Larus leucophthalmus Delphinus delphis Lagenodelphis hosei Puffinus creatopus Chelonia mydas Rhincodon typus Arctocephalus australis Hyperoodon ampullatus Carcharodon carcharias Lamna nasus Stenella longirostris Stenella attenuata Isurus oxyrinchus Stenella coeruleoalba Tursiops truncatus Pterodroma phaeopygia Balaenoptera borealis Balaenoptera physalus Megaptera novaeangliae Physeter macrocephalus Orcinus orca Monodon monoceros Balaenoptera musculus Phoebastria_irrorata 104 Common Porpoise Peruvian diving petrel Humboldt Penguin Slender-billed Gull Common Seal Marine Otter Mediterranean Gull Ridley Turtle North Pacific Right Whale Burmeister Porpoise Bowhead Whale Northern Right Whale Mediterranean Monk Seal Baird's Beaked Whale Omura' Whale Great Crested Tern Sooty Gull Dall's Porpoise Chilean Dolphin Balearic shearwater Atlantic White-sided Dolphin White-beaked Dolphin Hawksbill Turtle Basking shark Kemp's Ridley Turtle Risso's Dolphin Loggerhead Turtle Leatherback Turtle Armenian Gull White Pelican White Whale Longfin Mako shark Short-tailed Albatross White-eyed Gull Common Dolphin Fraser's Dolphin Pink-footed Shearwater Green Turtle Whale Shark South American Seal Northern Bottlenose Whale Great White Shark Porbeagle shark Spinner Dolphin Pantropical Spotted Dolphin Shortfin Mako shark Striped Dolphin Bottlenosed Dolphin Dark-rumped Petrel Sei Whale Fin Whale Humpback Whale Sperm Whale Killer whale Narwhal Blue Whale Waved Albatross 1.281 1.254 1.242 1.233 1.194 1.177 1.176 1.175 1.171 1.150 1.138 1.131 1.121 1.115 1.112 1.092 1.088 1.087 1.084 1.076 1.066 1.060 1.054 1.045 1.021 1.015 0.999 0.999 0.991 0.975 0.971 0.966 0.958 0.951 0.949 0.946 0.945 0.944 0.943 0.939 0.931 0.928 0.924 0.921 0.918 0.911 0.901 0.894 0.886 0.870 0.868 0.866 0.864 0.863 0.858 0.842 0.835 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 120 121 122 123 PCR POB LGO LGS SNC PHI LOP LAT GLM CEC DIM PCW DNB PHN EBA BAB PRK POD PHF THH PRO THC PCI ORH DIC MAI DIP DIX MAH PCO PXP PHE POW PTT STB LSA STI STV STE STR STS STG STN STF SDG CAT STH BAE DAM CAM LRL STP seabirds cetacean cetacean cetacean cetacean seabirds marine mammals other seabirds cetacean cetacean seabirds seabirds seabirds seabirds cetacean cetacean seabirds cetacean seabirds seabirds seabirds seabirds seabirds cetacean seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds cetacean seabirds cetacean seabirds seabirds Pelecanus crispus Pontoporia blainvillei Lagenorhynchus obscurus Lagenorhynchus australis Stenella clymene Phoebastria_immutabilis Lontra provocax Larus atlanticus Globicephala melas Cephalorhynchus commersonii Thalassarche_melanophrys Procellaria westlandica Thalassarche_bulleri Phoebastria_nigripes Eubalaena australis Balaenoptera bonaerensis Procellaria parkinsoni Phocoena dioptrica Phoebetria fusca Thalassarche_chlororhynchos Procellaria aequinoctialis Thalassarche_cauta Procellaria cinerea Orcaella heinsohni Thalassarche_chrysostoma Macronectes giganteus Diomedea epomophora Diomedea exulans Macronectes halli Procellaria conspicillata Phalacrocorax pygmeus Phoebetria palpebrata Pterodroma cahow Pterodroma atrata Sterna bernsteini Larus saundersi Sterna lorata Sterna sandvicensis Sterna balaenarum Sterna repressa Sterna saundersi Sterna bengalensis Sterna nilotica Sterna albifrons Sterna dougallii Sterna caspia Sterna hirundo Balaenoptera edeni Diomedea amsterdamensis Caperea marginata Larus relictus Sterna paradisaea 105 Dalmatian Pelican La Plata Dolphin Dusky Dolphin Peale's Dolphin Clymene dolphin Laysan Albatross Southern River Otter Olrog's Gull Long-finned Pilot Whale Commerson's Dolphin Black-browed Albatross Westland Petrel Buller's Albatross Black-footed Albatross Southern Right Whale Antarctic Minke whale Black Petrel Spectacled Porpoise Sooty Albatross Yellow-nosed Albatross White-chinned Petrel Shy Albatross Grey Petrel Australian Snubfin dolphin Grey-headed Albatross Southern Giant Petrel Royal Albatross Wandering Albatross Northern Giant Petrel Spectacled Petrel Pygmy Cormorant Light-mantled Sooty Albatross Cahow Bermuda Petrel Henderson Petrel Chinese Crested Tern Saunder's Gull Peruvian tern Sandwich Tern Damara Tern White-cheeked Tern Saunder's Tern Lesser Crested Tern Gull-billed Tern Little Tern Roseate Tern Caspian Tern Common Tern Bryde's whale Amsterdam Albatross Pygmy Right whale Relict Gull Arctic Tern 0.824 0.823 0.777 0.766 0.765 0.726 0.700 0.692 0.690 0.646 0.638 0.609 0.599 0.598 0.598 0.559 0.557 0.539 0.528 0.527 0.526 0.518 0.515 0.511 0.502 0.496 0.495 0.488 0.487 0.478 0.469 0.462 0.376 0.325 0.021 0.017 0.015 0.015 0.014 0.013 0.013 0.013 0.013 0.012 0.012 0.012 0.010 0.009 0.006 0.006 0.005 0.005 Figure 17 ¯ EEZs and High Seas FAO areas s howi ng with the un¯weighted exposures summed across seabi rds. A reas with colours furthest up the scale bar (red colours) had higher seabi rd exposures. Table 27 ¯ Seabi rds ranked by thei r un¯weighted exposure i ndex Rank 4 7 10 11 12 14 16 17 18 21 30 31 34 43 44 47 48 Species code STM SYW SPD LAU PHG LIC PEG SPH LGE LML SBG LHM PUM LAA PCC PHA LLE Family seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds Species Sterna maxima Synthliboramphus wumizusume Spheniscus demersus Larus audouinii Phalacrocorax nigrogularis Larus ichthyaetus Pelecanoides garnotii Spheniscus humboldti Larus genei Larus melanocephalus Sterna bergii Larus hemprichii Puffinus mauretanicus Larus armenicus Pelecanus onocrotalus Phoebastria_albatrus Larus leucophthalmus Common name Royal Tern Japanese Murrelet African Penguin Audouin's Gull Socotra Cormorant Great Black-headed Gull Peruvian diving petrel Humboldt Penguin Slender-billed Gull Mediterranean Gull Great Crested Tern Sooty Gull Balearic shearwater Armenian Gull White Pelican Short-tailed Albatross White-eyed Gull 106 Un-weighted exposure index 1.831 1.493 1.399 1.379 1.349 1.316 1.254 1.242 1.233 1.176 1.092 1.088 1.076 0.991 0.975 0.958 0.951 51 63 71 72 77 79 82 83 84 85 88 90 91 92 93 94 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 118 120 122 123 PUC PTG PIR PCR PHI LAT DIM PCW DNB PHN PRK PHF THH PRO THC PCI DIC MAI DIP DIX MAH PCO PXP PHE POW PTT STB LSA STI STV STE STR STS STG STN STF SDG CAT STH DAM LRL STP seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds Puffinus creatopus Pterodroma phaeopygia Phoebastria_irrorata Pelecanus crispus Phoebastria_immutabilis Larus atlanticus Thalassarche melanophrys Procellaria westlandica Thalassarche bulleri Phoebastria nigripes Procellaria parkinsoni Phoebetria fusca Thalassarche chlororhynchos Procellaria aequinoctialis Thalassarche cauta Procellaria cinerea Thalassarche chrysostoma Macronectes giganteus Diomedea epomophora Diomedea exulans Macronectes halli Procellaria conspicillata Phalacrocorax pygmeus Phoebetria palpebrata Pterodroma cahow Pterodroma atrata Sterna bernsteini Larus saundersi Sterna lorata Sterna sandvicensis Sterna balaenarum Sterna repressa Sterna saundersi Sterna bengalensis Sterna nilotica Sterna albifrons Sterna dougallii Sterna caspia Sterna hirundo Diomedea amsterdamensis Larus relictus Sterna paradisaea Pink-footed Shearwater Dark-rumped Petrel Waved Albatross Dalmatian Pelican Laysan Albatross Olrog's Gull Black-browed Albatross Westland Petrel Buller's Albatross Black-footed Albatross Black Petrel Sooty Albatross Yellow-nosed Albatross White-chinned Petrel Shy Albatross Grey Petrel Grey-headed Albatross Southern Giant Petrel Royal Albatross Wandering Albatross Northern Giant Petrel Spectacled Petrel Pygmy Cormorant Light-mantled Sooty Albatross Cahow Bermuda Petrel Henderson Petrel Chinese Crested Tern Saunder's Gull Peruvian tern Sandwich Tern Damara Tern White-cheeked Tern Saunder's Tern Lesser Crested Tern Gull-billed Tern Little Tern Roseate Tern Caspian Tern Common Tern Amsterdam Albatross Relict Gull Arctic Tern 107 0.945 0.886 0.835 0.824 0.726 0.692 0.638 0.609 0.599 0.598 0.557 0.528 0.527 0.526 0.518 0.515 0.502 0.496 0.495 0.488 0.487 0.478 0.469 0.462 0.376 0.325 0.021 0.017 0.015 0.015 0.014 0.013 0.013 0.013 0.013 0.012 0.012 0.012 0.010 0.006 0.005 0.005 Figure 18 Þ EEZs and High Seas FAO areas s howi ng with the unÞweighted exposures summed across turtles. A reas with co lours furthest up the sca le bar (red co lours) had higher turtle exposures. Table 28 Þ Turtles ranked by thei r unÞweighted exposure i ndex Rank 22 37 39 41 42 52 Species code LPV EIM LPK CAC DCC CHM Family turtle turtle turtle turtle turtle turtle Species Lepidochelys olivacea Eretmochelys imbricata Lepidochelys kempii Caretta caretta Dermochelys coriacea Chelonia mydas Common name Ridley Turtle Hawksbill Turtle Kemp's Ridley Turtle Loggerhead Turtle Leatherback Turtle Green Turtle 108 Un-weighted exposure index 1.175 1.054 1.021 0.999 0.999 0.944 Figure 19 EEZs and High Seas FAO areas s howi ng with the un weighted exposures summed across s harks. A reas with colours furthest up the scale bar (red colours) had higher s hark exposures. Table 29 Sharks ranked by thei r un weighted exposure i ndex Rank 38 46 53 56 57 60 Species code CTM IPA RHT CCC LMN IOX Family shark shark shark shark shark shark Species Cetorhinus maximus Isurus paucus Rhincodon typus Carcharodon carcharias Lamna nasus Isurus oxyrinchus Common name Basking shark Longfin Mako shark Whale Shark Great White Shark Porbeagle shark Shortfin Mako shark 109 Un-weighted exposure index 1.045 0.966 0.943 0.928 0.924 0.911 Figure 20 5 EEZs and High Seas FAO areas s howi ng with the un5weighted exposures summed across pi nni peds and otters. A reas with colours furthest up the scale bar (red colours) had higher pi nni ped and otter exposures. Table 30 5 Seal, sea lions and otters ranked by thei r un5weighted exposure i ndex Rank 13 19 20 27 54 Species code HGR PHV LOF MMN OFL Family marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other Species Halichoerus grypus Phoca vitulina Lontra felina Monachus monachus Arctocephalus australis Common name Grey Seal Common Seal Marine Otter Mediterranean Monk Seal South American Seal 110 Un-weighted exposure index 1.328 1.194 1.177 1.121 0.939 Table 31 _ EEZs and high seas FAO areas sorted presenti ng t he highest u n_weighted ex posu re for all s pecies Rank 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 EEZ or High Seas FAO area Myanmar Vietnam India Russia Pacific China Peru Chile Norway Bangladesh Morocco Indonesia (Western) Namibia Japan Main Isl. Indonesia (Eastern) Western Sahara (Morocco) Mauritania Iceland South Africa Angola Nigeria Sierra Leone Guinea United Kingdom Philippines Pacific Northwest - High seas Areas Bahrain Japan Outer Isl. Senegal Greece Cameroon Pacific Western Central - High seas Areas Malaysia West Malaysia East Thailand Korea South Pakistan Iran Yemen Malaysia Sarawak Russia Barrents Sea United Arab Emirates Indian Ocean Eastern - High seas Areas Korea North Saudi Arabia Persian Gulf Malaysia Sabah Spain Svalbard Isl. (Norway) Alaska Galapagos Isl.(Ecuador) Turkey Mediterranean Sea Somalia Denmark Algeria Sum of all species un-weighted exposure index 1.530 1.497 1.478 1.325 1.240 1.218 1.190 1.173 1.157 1.146 1.106 1.103 1.102 1.072 1.063 1.051 1.006 0.992 0.950 0.917 0.890 0.883 0.875 0.834 0.825 0.823 0.823 0.805 0.804 0.797 0.795 0.793 0.787 0.778 0.771 0.765 0.758 0.747 0.743 0.742 0.742 0.740 0.738 0.737 0.736 0.734 0.728 0.713 0.697 0.688 0.678 0.671 0.666 111 54 55 56 57 58 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 120 121 122 123 Tunisia Ghana Gambia Brazil Oman J. Fernandez, Felix and Ambrosio Isl. (Chile) Argentina Greenland Turkey Black Sea Madagascar Cambodia Canada New Zealand France Taiwan Sweden Ireland Cote d'Ivoire Faeroe Isl.(Denmark) Gabon Italy Pacific Southeast - High seas Areas Sudan Mexico Saudi Arabia Red Sea Croatia Australia Papua New Guinea Qatar USA East Coast Egypt Uruguay Indian Ocean Western - High seas Areas Lebanon Pacific Eastern Central - High seas Areas Atlantic Southwest - High seas Areas Congo Republic Pacific Southwest - High seas Areas Kuwait Tanzania Poland Netherlands Germany Ecuador Atlantic Eastern Central - High seas Areas Atlantic Western Central - High seas Areas Libya Syria Israel Finland Guyana Portugal Congo Pacific Northeast - High seas Areas Solomon Isl. Atlantic Northeast - High seas Areas Canary Isl.(Spain) USA West Coast Venezuela Mozambique Liberia Andaman & Nicobar Isl. (India) Sri Lanka Latvia Suriname Hong Kong Montenegro Eritrea Russia Baltic Sea Kaliningrad Atlantic Northwest - High seas Areas 0.656 0.655 0.650 0.647 0.625 0.624 0.623 0.620 0.620 0.614 0.610 0.609 0.608 0.603 0.602 0.577 0.573 0.572 0.567 0.564 0.563 0.561 0.542 0.533 0.531 0.527 0.525 0.523 0.511 0.510 0.507 0.502 0.502 0.487 0.484 0.449 0.448 0.441 0.441 0.434 0.433 0.428 0.419 0.406 0.402 0.400 0.395 0.392 0.381 0.378 0.378 0.359 0.355 0.352 0.352 0.352 0.348 0.347 0.342 0.340 0.339 0.339 0.337 0.335 0.328 0.324 0.323 0.321 0.318 0.318 112 124 125 126 127 128 129 130 131 132 133 134 135 136 137 138 139 140 141 142 143 144 145 146 147 148 149 150 151 152 153 154 155 156 157 158 159 160 161 162 163 164 165 166 167 168 169 170 171 172 173 174 175 176 177 178 179 180 181 182 183 184 185 186 187 188 189 190 191 192 193 Togo Benin Jan Mayen Isl. (Norway) Atlantic SouthEast - High seas Areas Maldives Cyprus Colombia USA Golf Of Mexico Malta Falkland Isl.(UK) Estonia Ukraine Brunei Channel Isl.(UK) Jamaica Fiji Guinea-Bissau Desventuradas Isl.(Chile) Albania Cuba Haiti Singapore Lithuania Haiwaii NorthWest Isl. Dominican Rep. Kenya Gaza Strip Russia Siberia Mayotte (FR) Panama Cape Verde Sao Tome & Principe French Polynesia Equatorial Guinea Kiribati French Guyana Macau (China) Mauritius Madeira Isl.(Portugal) Trinidad & Tobago Belgium Azores Isl.(Portugal) Iraq Martinique Timor Leste Honduras Christmas Isl.(Australia) St Pierre & Miquelon (FR) Bermuda (UK) Vanuatu Costa Rica Micronesia Jordan Bosnia Brit. Virgin Isl.(UK) Russia Black Sea Djibouti Cocos Isl.(Australia) Guadeloupe (FR) Comoros Isl. Trindade & Matin Isl (BR) New Caledonia St Lucia Lord Howe Isl. (Australia) El Salvador Dominica Puerto Rico (US) Seychelles Palau Georgia 0.317 0.316 0.314 0.312 0.302 0.298 0.291 0.291 0.282 0.279 0.272 0.270 0.267 0.262 0.261 0.256 0.247 0.245 0.244 0.243 0.243 0.243 0.239 0.230 0.230 0.225 0.223 0.223 0.218 0.214 0.213 0.206 0.205 0.204 0.201 0.197 0.194 0.192 0.190 0.180 0.179 0.178 0.169 0.164 0.164 0.163 0.161 0.159 0.158 0.156 0.155 0.155 0.155 0.152 0.150 0.150 0.150 0.148 0.144 0.143 0.140 0.140 0.137 0.136 0.135 0.133 0.131 0.126 0.121 0.119 113 194 195 196 197 198 199 200 201 202 203 204 205 206 207 208 209 210 211 212 213 214 215 216 217 218 219 220 221 222 223 224 225 226 227 228 229 230 231 232 233 234 235 236 237 238 239 240 241 242 243 244 245 246 247 248 249 250 251 252 253 254 255 St Paul & Amsterdam (FR) Monaco Marshall Isl. Norfolk Isl. (Australia) Tuvalu Easter Isl.(Chile) Nicaragua Antigua & Barbuda Grenada Prince Edward Isl. (SA) Anguila (UK) Wallis & Futuna (FR) Haiwaii Main Isl. Kerguelen Isl. (FR) St Vincent & The Grenadines Romania Bulgaria Pitcairn (UK) Crozet Isl.(FR) Mozambique Channel Isl. (FR) Leeward Netherland Antilles Bahamas St Kitts & Nevis Indian Ocean Antarctic - High seas Areas Windward Netherlands Antilles Tonga Montserrat (UK) Cook Isl.(New Zealand) Brit. Indian Oce (UK) Slovenia Cayman Isl.(UK) Guam (US) Ascencion Isl. Arctic Sea - High seas Areas American Samoa Nauru Tromelin Isl.(FR) Barbados Palmyra Atoll & Kingman Reef (US) Belize South Georgia & Sandwich Isl. (UK) Northern Marianas (US) Guatemala Clipperton Isl.(FR) Reunion (FR) Samoa Johnston Atoll (US) Tokelau (NZ) Jarvis Isl.(US) Howland & Baker Isl.(US) St Helena (UK) Atlantic Antarctic - High seas Areas Macquarie Isl.(Australia) Bouvet Isl.(Norway) Gibraltar (UK) Heard & McDonald Isl.(Australia) Niue (NZ) Russia Baltic Sea St Petersburg Turks & Caicos Isl (UK) Navassa Isl. (Haiti) Wake Isl.(US) Pacific Antarctic - High seas Areas 0.118 0.116 0.115 0.115 0.111 0.110 0.109 0.105 0.105 0.105 0.104 0.100 0.099 0.095 0.093 0.091 0.089 0.089 0.084 0.083 0.083 0.081 0.081 0.080 0.079 0.077 0.075 0.073 0.070 0.070 0.069 0.068 0.068 0.067 0.065 0.063 0.063 0.061 0.060 0.059 0.057 0.057 0.056 0.056 0.055 0.052 0.046 0.044 0.041 0.028 0.026 0.021 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 114 Table 32 EEZs and high seas FAO areas sorted presenti ng t he highest IUCN weighted ex posure for all s pecies Rank 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 EEZ or High Seas FAO area Myanmar Vietnam Peru India Russia Pacific Chile South Africa China Namibia Greece Galapagos Isl.(Ecuador) Bangladesh Japan Main Isl. Indonesia (Western) Indonesia (Eastern) Norway Mauritania United Kingdom Algeria Morocco Western Sahara (Morocco) Pacific Western Central - High seas Areas Iceland Tunisia Japan Outer Isl. Turkey Mediterranean Sea Pacific Northwest - High seas Areas Philippines Bahrain Korea South Malaysia East Malaysia West Angola Thailand Croatia Korea North Malaysia Sarawak Denmark Indian Ocean Eastern - High seas Areas Malaysia Sabah Nigeria Guinea Sierra Leone Saudi Arabia Persian Gulf Senegal Spain Mexico United Arab Emirates Pacific Southeast - High seas Areas Alaska France Iran Brazil Ireland USA East Coast Cameroon Pakistan Yemen Sum of all species IUCN weighted exposure index 1.539 1.518 1.488 1.432 1.294 1.280 1.271 1.268 1.246 1.195 1.164 1.132 1.121 1.115 1.075 1.057 1.011 0.987 0.976 0.949 0.947 0.917 0.908 0.873 0.860 0.851 0.848 0.836 0.826 0.808 0.805 0.802 0.795 0.794 0.792 0.777 0.767 0.762 0.753 0.742 0.741 0.735 0.727 0.725 0.721 0.710 0.687 0.687 0.684 0.681 0.672 0.669 0.668 0.667 0.667 0.663 0.639 0.636 115 59 60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 120 121 122 123 124 125 126 127 128 J. Fernandez, Felix and Ambrosio Isl. (Chile) Madagascar Argentina Cambodia Taiwan New Zealand Canada Ecuador Somalia Pacific Eastern Central - High seas Areas Oman Papua New Guinea Gambia Indian Ocean Western - High seas Areas Ghana Atlantic Southwest - High seas Areas Canary Isl.(Spain) Qatar Montenegro Venezuela Uruguay Gabon Russia Barrents Sea Italy Netherlands Germany Atlantic Western Central - High seas Areas Svalbard Isl. (Norway) Faeroe Isl.(Denmark) Atlantic Eastern Central - High seas Areas Cote d'Ivoire Australia Sweden Pacific Southwest - High seas Areas Portugal Guyana Kuwait Mozambique USA Golf Of Mexico Greenland Sudan Egypt Saudi Arabia Red Sea Colombia Suriname Pacific Northeast - High seas Areas Tanzania Solomon Isl. Libya Atlantic Northwest - High seas Areas Andaman & Nicobar Isl. (India) USA West Coast Atlantic SouthEast - High seas Areas Congo Republic Sri Lanka Malta Hong Kong Atlantic Northeast - High seas Areas Cape Verde Fiji Jamaica Madeira Isl.(Portugal) Maldives Haiwaii NorthWest Isl. Channel Isl.(UK) Congo Falkland Isl.(UK) Haiti Panama Cuba 0.628 0.626 0.623 0.618 0.612 0.587 0.578 0.572 0.553 0.544 0.540 0.536 0.533 0.524 0.524 0.505 0.502 0.499 0.496 0.489 0.486 0.485 0.485 0.485 0.471 0.467 0.465 0.461 0.459 0.457 0.456 0.451 0.449 0.446 0.435 0.430 0.425 0.423 0.420 0.407 0.398 0.379 0.378 0.376 0.373 0.372 0.370 0.369 0.367 0.365 0.364 0.363 0.363 0.355 0.335 0.333 0.327 0.322 0.308 0.305 0.299 0.295 0.295 0.292 0.291 0.281 0.281 0.276 0.275 0.274 116 129 130 131 132 133 134 135 136 137 138 139 140 141 142 143 144 145 146 147 148 149 150 151 152 153 154 155 156 157 158 159 160 161 162 163 164 165 166 167 168 169 170 171 172 173 174 175 176 177 178 179 180 181 182 183 184 185 186 187 188 189 190 191 192 193 194 195 196 197 198 Liberia Brunei Poland French Polynesia Dominican Rep. Azores Isl.(Portugal) Turkey Black Sea Togo Benin Trinidad & Tobago Lebanon Singapore Kiribati Desventuradas Isl.(Chile) Eritrea Finland Jan Mayen Isl. (Norway) Albania Bosnia Mayotte (FR) French Guyana Sao Tome & Principe Israel Bermuda (UK) Cyprus Latvia Costa Rica Guinea-Bissau Belgium Macau (China) Mauritius Russia Baltic Sea Kaliningrad Syria Kenya Honduras Martinique El Salvador Equatorial Guinea Gaza Strip Micronesia Brit. Virgin Isl.(UK) Estonia Vanuatu Trindade & Matin Isl (BR) Timor Leste Ukraine Christmas Isl.(Australia) Guadeloupe (FR) St Pierre & Miquelon (FR) Iraq New Caledonia St Lucia Grenada Dominica Puerto Rico (US) Cocos Isl.(Australia) Russia Siberia Comoros Isl. Lithuania Lord Howe Isl. (Australia) Seychelles Nicaragua St Paul & Amsterdam (FR) Norfolk Isl. (Australia) Tuvalu Palau Marshall Isl. Antigua & Barbuda Leeward Netherland Antilles Pitcairn (UK) 0.272 0.270 0.268 0.262 0.262 0.259 0.252 0.251 0.250 0.249 0.247 0.245 0.241 0.237 0.237 0.237 0.229 0.228 0.227 0.224 0.224 0.217 0.215 0.212 0.209 0.207 0.206 0.197 0.196 0.196 0.196 0.195 0.190 0.190 0.190 0.186 0.184 0.183 0.179 0.174 0.171 0.168 0.167 0.166 0.165 0.164 0.164 0.164 0.162 0.162 0.157 0.156 0.152 0.151 0.149 0.148 0.147 0.146 0.146 0.143 0.138 0.136 0.134 0.134 0.132 0.132 0.131 0.121 0.120 0.119 117 199 200 201 202 203 204 205 206 207 208 209 210 211 212 213 214 215 216 217 218 219 220 221 222 223 224 225 226 227 228 229 230 231 232 233 234 235 236 237 238 239 240 241 242 243 244 245 246 247 248 249 250 251 252 253 254 255 St Vincent & The Grenadines Wallis & Futuna (FR) Anguila (UK) Prince Edward Isl. (SA) Easter Isl.(Chile) Djibouti Bahamas Haiwaii Main Isl. Monaco Mozambique Channel Isl. (FR) St Kitts & Nevis Tonga Windward Netherlands Antilles Russia Black Sea Crozet Isl.(FR) Montserrat (UK) Jordan Cook Isl.(New Zealand) Kerguelen Isl. (FR) Guam (US) Cayman Isl.(UK) Ascencion Isl. Indian Ocean Antarctic - High seas Areas Belize American Samoa Brit. Indian Oce (UK) Nauru Guatemala Clipperton Isl.(FR) Palmyra Atoll & Kingman Reef (US) Tromelin Isl.(FR) Barbados Slovenia Northern Marianas (US) Samoa Reunion (FR) South Georgia & Sandwich Isl. (UK) Georgia Tokelau (NZ) Romania Johnston Atoll (US) Bulgaria Jarvis Isl.(US) Arctic Sea - High seas Areas Howland & Baker Isl.(US) St Helena (UK) Atlantic Antarctic - High seas Areas Macquarie Isl.(Australia) Bouvet Isl.(Norway) Gibraltar (UK) Heard & McDonald Isl.(Australia) Niue (NZ) Russia Baltic Sea St Petersburg Turks & Caicos Isl (UK) Navassa Isl. (Haiti) Wake Isl.(US) Pacific Antarctic - High seas Areas 0.119 0.119 0.118 0.114 0.114 0.111 0.100 0.099 0.095 0.093 0.092 0.091 0.090 0.089 0.088 0.086 0.083 0.081 0.081 0.079 0.078 0.077 0.077 0.076 0.075 0.075 0.074 0.074 0.074 0.071 0.070 0.070 0.063 0.063 0.062 0.057 0.053 0.053 0.052 0.052 0.051 0.049 0.047 0.045 0.033 0.031 0.021 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 0.000 118 Table 33 ª High Seas FAO areas EEZ sorted by t hei r cont ri bution i n t he different exposures for all cetacean sorted by IUCN weighted exposure EEZ, High Seas FAO area Vietnam Myanmar India China Indonesia (Western) Russia Pacific Indonesia (Eastern) Japan Main Isl. Norway Bangladesh Chile Philippines Pacific Northwest - High seas Areas Indian Ocean Eastern - High seas Areas Iceland Malaysia Sarawak Korea South Malaysia East Thailand Malaysia Sabah Malaysia West Japan Outer Isl. Korea North Canada United Kingdom Angola Pacific Western Central - High seas Areas South Africa Brazil Mauritania Cambodia Taiwan Peru Western Sahara (Morocco) Alaska Namibia Madagascar Argentina Australia Pacific Southeast - High seas Areas Morocco Nigeria Pakistan Papua New Guinea Sierra Leone Guinea USA East Coast Mexico Greenland Indian Ocean Western - High seas Areas Senegal Svalbard Isl. (Norway) Atlantic Southwest - High seas Areas Cameroon Pacific Eastern Central - High seas Areas Ireland Overall rank 937 127 462 187 477 857 472 517 732 57 167 782 1257 1232 457 612 547 597 1002 602 592 522 542 147 1067 17 1272 952 87 627 137 192 777 972 1082 672 587 27 32 1262 657 717 762 772 927 427 1117 637 402 1237 917 987 1217 142 1247 492 Family cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean 119 Overlap index 0.935 0.892 0.859 0.766 0.703 0.783 0.707 0.663 0.664 0.614 0.58 0.548 0.589 0.588 0.515 0.496 0.486 0.48 0.474 0.47 0.466 0.466 0.415 0.438 0.433 0.399 0.422 0.432 0.396 0.417 0.359 0.373 0.397 0.402 0.366 0.412 0.372 0.339 0.367 0.39 0.358 0.333 0.327 0.318 0.327 0.327 0.327 0.332 0.344 0.351 0.32 0.359 0.319 0.298 0.32 0.292 Unweighted exposure index 1.064 1.013 0.974 0.875 0.8 0.928 0.802 0.76 0.787 0.694 0.642 0.622 0.662 0.626 0.61 0.562 0.561 0.544 0.538 0.535 0.529 0.527 0.491 0.515 0.513 0.454 0.462 0.47 0.45 0.471 0.408 0.423 0.448 0.453 0.434 0.446 0.418 0.383 0.405 0.409 0.403 0.374 0.367 0.358 0.367 0.367 0.371 0.371 0.407 0.369 0.361 0.425 0.344 0.335 0.356 0.346 IUCN weighted exposure index 1 0.953 0.903 0.801 0.751 0.743 0.733 0.655 0.642 0.635 0.571 0.57 0.549 0.536 0.521 0.518 0.516 0.507 0.502 0.502 0.497 0.486 0.468 0.419 0.416 0.405 0.403 0.394 0.388 0.386 0.384 0.383 0.378 0.374 0.373 0.373 0.354 0.348 0.34 0.333 0.328 0.324 0.322 0.317 0.317 0.317 0.309 0.309 0.308 0.306 0.297 0.296 0.291 0.289 0.288 0.283 Pacific Southwest - High seas Areas Iran Russia Barrents Sea Faeroe Isl.(Denmark) France Somalia Spain United Arab Emirates Denmark Atlantic Eastern Central - High seas Areas Oman Yemen Gambia Atlantic Western Central - High seas Areas New Zealand Ghana Saudi Arabia Persian Gulf Atlantic Northeast - High seas Areas Gabon Atlantic Northwest - High seas Areas Uruguay Solomon Isl. Tanzania Sri Lanka Cote d'Ivoire Guyana Brunei Pacific Northeast - High seas Areas Hong Kong Atlantic SouthEast - High seas Areas Andaman & Nicobar Isl. (India) Bahrain USA West Coast Suriname Sweden Canary Isl.(Spain) Netherlands Portugal Venezuela Germany Kuwait Singapore Mozambique Egypt Ecuador Maldives Colombia J. Fernandez, Felix and Ambrosio Isl. (Chile) Congo Republic Saudi Arabia Red Sea Jamaica Jan Mayen Isl. (Norway) Sudan Qatar USA Golf Of Mexico Falkland Isl.(UK) Mayotte (FR) Galapagos Isl.(Ecuador) Desventuradas Isl.(Chile) Haiti Fiji Cuba Liberia Dominican Rep. Italy Greece Congo Togo Tunisia Benin 1267 482 842 302 327 947 967 1027 262 1197 667 1157 367 1222 707 382 912 1202 357 1207 1132 107 1077 162 507 432 117 1252 452 1212 467 52 1112 982 992 962 682 797 1137 377 552 932 662 1062 277 607 207 182 222 907 512 737 977 827 1122 307 217 282 177 437 317 247 567 272 502 397 227 1007 1032 257 cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean 120 0.314 0.279 0.322 0.275 0.27 0.265 0.242 0.253 0.293 0.265 0.255 0.25 0.255 0.247 0.254 0.233 0.21 0.244 0.226 0.225 0.213 0.202 0.203 0.197 0.205 0.225 0.172 0.173 0.175 0.205 0.177 0.165 0.181 0.191 0.163 0.179 0.186 0.146 0.177 0.18 0.145 0.141 0.162 0.148 0.167 0.161 0.163 0.154 0.146 0.132 0.155 0.154 0.126 0.123 0.147 0.118 0.129 0.149 0.128 0.142 0.129 0.139 0.121 0.134 0.12 0.137 0.115 0.113 0.117 0.112 0.327 0.317 0.381 0.326 0.32 0.297 0.287 0.29 0.347 0.294 0.286 0.281 0.287 0.274 0.268 0.262 0.248 0.288 0.254 0.257 0.237 0.227 0.229 0.222 0.23 0.249 0.196 0.196 0.198 0.217 0.198 0.196 0.205 0.212 0.193 0.199 0.221 0.173 0.196 0.213 0.172 0.16 0.177 0.176 0.184 0.176 0.18 0.15 0.163 0.157 0.172 0.182 0.15 0.146 0.163 0.13 0.145 0.163 0.14 0.157 0.141 0.154 0.136 0.149 0.142 0.162 0.129 0.127 0.138 0.126 0.278 0.276 0.273 0.265 0.265 0.26 0.259 0.259 0.256 0.247 0.245 0.243 0.236 0.231 0.227 0.226 0.222 0.22 0.218 0.209 0.207 0.204 0.2 0.199 0.199 0.198 0.183 0.182 0.182 0.179 0.175 0.175 0.172 0.168 0.162 0.16 0.158 0.156 0.155 0.153 0.153 0.151 0.15 0.15 0.143 0.142 0.142 0.139 0.139 0.138 0.136 0.136 0.131 0.13 0.129 0.128 0.127 0.125 0.125 0.124 0.122 0.122 0.118 0.118 0.112 0.112 0.11 0.11 0.109 0.109 Macau (China) French Guyana Cape Verde Channel Isl.(UK) Sao Tome & Principe Panama Algeria Mauritius Christmas Isl.(Australia) Kenya Timor Leste Equatorial Guinea French Polynesia Kiribati Guinea-Bissau Cocos Isl.(Australia) Honduras Eritrea Trinidad & Tobago Martinique Vanuatu New Caledonia Comoros Isl. Lord Howe Isl. (Australia) Croatia St Pierre & Miquelon (FR) Brit. Virgin Isl.(UK) Trindade & Matin Isl (BR) Turkey Mediterranean Sea Libya Azores Isl.(Portugal) Costa Rica Guadeloupe (FR) Poland Micronesia Russia Siberia St Lucia Norfolk Isl. (Australia) Dominica Puerto Rico (US) Seychelles Palau Madeira Isl.(Portugal) Belgium Finland Easter Isl.(Chile) Iraq Latvia El Salvador Nicaragua Russia Baltic Sea Kaliningrad Malta Antigua & Barbuda Anguila (UK) Djibouti St Paul & Amsterdam (FR) Marshall Isl. Tuvalu Wallis & Futuna (FR) Haiwaii NorthWest Isl. Mozambique Channel Isl. (FR) Estonia Grenada St Vincent & The Grenadines Montenegro Indian Ocean Antarctic - High seas Areas Bahamas Haiwaii Main Isl. Albania St Kitts & Nevis 582 342 152 1072 902 767 7 632 197 537 817 292 347 392 812 202 447 132 1022 622 702 697 212 42 242 892 112 92 1037 572 807 237 412 792 747 862 887 727 267 822 922 757 802 67 322 172 487 562 287 712 852 617 22 882 352 1167 752 1052 1147 642 332 297 407 897 1162 1227 47 1087 2 877 cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean 121 0.104 0.119 0.114 0.118 0.109 0.119 0.105 0.112 0.099 0.101 0.096 0.093 0.095 0.093 0.089 0.084 0.098 0.081 0.096 0.095 0.087 0.09 0.082 0.099 0.091 0.081 0.088 0.08 0.098 0.086 0.07 0.085 0.084 0.057 0.076 0.08 0.08 0.081 0.078 0.076 0.069 0.066 0.072 0.077 0.051 0.065 0.055 0.045 0.066 0.063 0.043 0.062 0.061 0.061 0.053 0.05 0.055 0.054 0.05 0.055 0.053 0.037 0.053 0.052 0.052 0.039 0.047 0.049 0.047 0.047 0.118 0.132 0.127 0.139 0.122 0.131 0.124 0.123 0.112 0.113 0.108 0.104 0.099 0.101 0.099 0.093 0.108 0.095 0.106 0.106 0.097 0.099 0.092 0.102 0.108 0.096 0.097 0.088 0.116 0.102 0.08 0.094 0.093 0.068 0.084 0.094 0.088 0.083 0.086 0.084 0.076 0.073 0.079 0.092 0.06 0.068 0.065 0.053 0.073 0.07 0.051 0.073 0.068 0.067 0.06 0.054 0.059 0.059 0.055 0.06 0.059 0.043 0.059 0.057 0.061 0.042 0.052 0.053 0.056 0.052 0.108 0.105 0.105 0.104 0.104 0.103 0.102 0.101 0.099 0.099 0.095 0.088 0.086 0.086 0.086 0.086 0.085 0.085 0.084 0.084 0.083 0.083 0.081 0.08 0.08 0.08 0.077 0.077 0.076 0.075 0.075 0.074 0.073 0.073 0.073 0.071 0.07 0.068 0.068 0.067 0.066 0.066 0.066 0.065 0.065 0.062 0.057 0.057 0.056 0.055 0.055 0.054 0.054 0.053 0.052 0.052 0.051 0.051 0.048 0.047 0.047 0.047 0.047 0.045 0.045 0.043 0.043 0.042 0.041 0.041 Lebanon Lithuania Windward Netherlands Antilles Montserrat (UK) Ascencion Isl. Israel Leeward Netherland Antilles Tonga Brit. Indian Oce (UK) Kerguelen Isl. (FR) Cayman Isl.(UK) Cook Isl.(New Zealand) Cyprus Guam (US) Tromelin Isl.(FR) Gaza Strip Barbados American Samoa Syria Prince Edward Isl. (SA) Belize Reunion (FR) Jordan Crozet Isl.(FR) Bermuda (UK) Palmyra Atoll & Kingman Reef (US) Northern Marianas (US) Guatemala Nauru Samoa Turkey Black Sea Monaco Clipperton Isl.(FR) Johnston Atoll (US) Bosnia Tokelau (NZ) Jarvis Isl.(US) South Georgia & Sandwich Isl. (UK) Ukraine Pitcairn (UK) St Helena (UK) Atlantic Antarctic - High seas Areas Howland & Baker Isl.(US) Slovenia Arctic Sea - High seas Areas Russia Black Sea Romania Bulgaria Georgia Macquarie Isl.(Australia) Bouvet Isl.(Norway) Gibraltar (UK) Heard & McDonald Isl.(Australia) Niue (NZ) Russia Baltic Sea St Petersburg Turks & Caicos Isl (UK) Navassa Isl. (Haiti) Wake Isl.(US) Pacific Antarctic - High seas Areas 557 577 687 652 1127 497 692 1017 102 1177 157 232 252 417 337 372 62 12 997 957 97 832 532 1172 72 1097 742 422 677 1152 1042 647 1182 527 77 1012 1102 312 1057 787 872 1192 1107 942 1187 847 837 122 362 37 82 387 442 722 867 1047 1092 1142 1242 cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean cetacean 122 0.05 0.032 0.046 0.044 0.04 0.045 0.042 0.039 0.039 0.033 0.04 0.037 0.04 0.035 0.036 0.038 0.036 0.033 0.037 0.028 0.034 0.033 0.027 0.027 0.029 0.03 0.029 0.03 0.028 0.026 0.049 0.025 0.028 0.023 0.022 0.02 0.02 0.015 0.036 0.016 0.014 0.011 0.013 0.014 0.012 0.019 0.012 0.011 0.01 0 0 0 0 0 0 0 0 0 0 0.059 0.038 0.051 0.049 0.043 0.053 0.047 0.042 0.042 0.036 0.045 0.04 0.048 0.038 0.04 0.045 0.04 0.036 0.043 0.03 0.038 0.036 0.032 0.028 0.032 0.033 0.031 0.034 0.03 0.029 0.059 0.029 0.031 0.025 0.026 0.022 0.022 0.016 0.042 0.017 0.015 0.012 0.014 0.017 0.015 0.022 0.014 0.013 0.011 0 0 0 0 0 0 0 0 0 0 0.041 0.041 0.041 0.039 0.038 0.037 0.037 0.036 0.036 0.036 0.035 0.035 0.033 0.033 0.033 0.032 0.031 0.031 0.03 0.03 0.03 0.03 0.029 0.029 0.028 0.028 0.027 0.026 0.026 0.025 0.024 0.024 0.024 0.021 0.019 0.019 0.019 0.016 0.016 0.016 0.013 0.013 0.012 0.012 0.01 0.009 0.005 0.005 0.004 0 0 0 0 0 0 0 0 0 0 Table 34 × High Seas FAO areas EEZ sorted by t hei r cont ri bution i n t he different exposures for all seabi rds sorted by IUCN weighted exposure EEZ, High Seas FAO area Peru Chile South Africa Pacific Southeast - High seas Areas Namibia Indian Ocean Eastern - High seas Areas New Zealand Galapagos Isl.(Ecuador) Atlantic Southwest - High seas Areas Japan Main Isl. Pacific Southwest - High seas Areas Russia Pacific Pacific Eastern Central - High seas Areas Argentina Morocco Japan Outer Isl. Indian Ocean Western - High seas Areas Iran Atlantic SouthEast - High seas Areas Yemen Australia India Angola Brazil Greece Turkey Mediterranean Sea J. Fernandez, Felix and Ambrosio Isl. (Chile) Pacific Northwest - High seas Areas Mexico Egypt Alaska Mauritania Spain United Arab Emirates Ecuador Somalia Uruguay China Pacific Western Central - High seas Areas Pakistan Western Sahara (Morocco) Bahrain Oman Saudi Arabia Persian Gulf Korea South Italy Tunisia Saudi Arabia Red Sea Algeria France Senegal Croatia Sudan Kuwait Qatar Pacific Northeast - High seas Areas Canada Falkland Isl.(UK) Lebanon Overall rank 776 166 951 1261 671 1231 706 281 1216 516 1266 856 1246 26 656 521 1236 481 1211 1156 31 461 16 86 396 1036 181 1256 636 1061 1081 626 966 1026 276 946 1131 186 1271 761 971 51 666 911 546 501 1031 906 6 326 916 241 976 551 826 1251 146 306 556 Family seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds 123 Overlap index 0.459 0.491 0.513 0.3 0.412 0.382 0.311 0.133 0.215 0.288 0.257 0.3 0.152 0.186 0.5 0.243 0.262 0.48 0.15 0.403 0.277 0.763 0.332 0.116 0.246 0.292 0.131 0.117 0.126 0.369 0.116 0.501 0.255 0.333 0.131 0.431 0.109 0.533 0.157 0.548 0.385 0.204 0.351 0.281 0.216 0.187 0.265 0.291 0.242 0.174 0.364 0.149 0.295 0.214 0.19 0.065 0.064 0.076 0.147 Unweighted exposure index 0.421 0.511 0.382 0.336 0.315 0.35 0.33 0.158 0.245 0.225 0.269 0.211 0.181 0.211 0.379 0.205 0.204 0.297 0.166 0.282 0.201 0.338 0.2 0.137 0.23 0.256 0.155 0.139 0.117 0.266 0.135 0.303 0.203 0.209 0.081 0.226 0.129 0.147 0.144 0.26 0.264 0.146 0.207 0.17 0.105 0.183 0.173 0.223 0.16 0.149 0.202 0.155 0.186 0.124 0.125 0.077 0.067 0.082 0.146 IUCN weighted exposure index 0.576 0.566 0.436 0.384 0.366 0.321 0.314 0.279 0.275 0.264 0.257 0.242 0.226 0.222 0.222 0.221 0.201 0.188 0.185 0.18 0.176 0.175 0.172 0.172 0.161 0.16 0.159 0.156 0.155 0.152 0.149 0.146 0.142 0.142 0.141 0.141 0.14 0.135 0.134 0.131 0.129 0.125 0.125 0.123 0.123 0.12 0.117 0.112 0.108 0.106 0.099 0.097 0.092 0.091 0.089 0.088 0.086 0.085 0.083 Gambia Mozambique Turkey Black Sea United Kingdom Libya USA West Coast Syria Israel Bangladesh Norway Guinea Colombia Denmark Taiwan Desventuradas Isl.(Chile) Haiwaii NorthWest Isl. Cyprus Albania Eritrea Ukraine Montenegro French Polynesia Myanmar Portugal Ireland Prince Edward Isl. (SA) St Paul & Amsterdam (FR) Panama Netherlands Crozet Isl.(FR) Nigeria Kerguelen Isl. (FR) Germany Atlantic Western Central - High seas Areas Atlantic Northwest - High seas Areas Indian Ocean Antarctic - High seas Areas Gaza Strip Iraq Philippines Malta Sierra Leone Costa Rica Ghana Faeroe Isl.(Denmark) El Salvador Cameroon Vietnam Russia Black Sea Kiribati Bermuda (UK) South Georgia & Sandwich Isl. (UK) Gabon Channel Isl.(UK) Djibouti Congo Republic Hong Kong Tanzania Cote d'Ivoire Indonesia (Eastern) Monaco Haiwaii Main Isl. Indonesia (Western) Congo Madagascar Nicaragua Lord Howe Isl. (Australia) Bosnia Belgium Russia Siberia USA East Coast 366 661 1041 1066 571 1111 996 496 56 731 426 206 261 191 176 641 251 1 131 1056 1161 346 126 796 491 956 1166 766 681 1171 716 1176 376 1221 1206 1226 371 486 781 616 926 236 381 301 286 141 936 846 391 71 311 356 1071 351 221 451 1076 506 471 646 1086 476 226 586 711 41 76 66 861 1116 seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds 124 0.289 0.134 0.145 0.133 0.166 0.065 0.114 0.141 0.358 0.101 0.331 0.045 0.126 0.18 0.046 0.039 0.092 0.085 0.184 0.151 0.064 0.034 0.337 0.079 0.105 0.043 0.051 0.031 0.088 0.041 0.334 0.041 0.1 0.022 0.021 0.038 0.076 0.073 0.265 0.039 0.29 0.025 0.261 0.031 0.016 0.242 0.517 0.078 0.032 0.014 0.025 0.178 0.027 0.089 0.151 0.096 0.165 0.212 0.345 0.026 0.016 0.278 0.122 0.21 0.012 0.036 0.031 0.034 0.061 0.03 0.165 0.086 0.158 0.078 0.107 0.059 0.117 0.132 0.175 0.055 0.163 0.042 0.065 0.072 0.055 0.047 0.092 0.084 0.11 0.104 0.069 0.04 0.127 0.064 0.052 0.048 0.043 0.028 0.053 0.045 0.111 0.045 0.046 0.026 0.025 0.04 0.064 0.049 0.06 0.046 0.089 0.022 0.087 0.027 0.019 0.078 0.071 0.056 0.03 0.017 0.028 0.067 0.03 0.051 0.064 0.03 0.06 0.058 0.057 0.028 0.018 0.052 0.051 0.043 0.012 0.029 0.033 0.022 0.033 0.012 0.081 0.08 0.079 0.079 0.076 0.073 0.072 0.071 0.068 0.064 0.063 0.063 0.06 0.06 0.057 0.057 0.056 0.056 0.054 0.054 0.051 0.049 0.049 0.049 0.048 0.046 0.045 0.045 0.044 0.043 0.043 0.043 0.041 0.041 0.038 0.038 0.037 0.036 0.036 0.035 0.035 0.034 0.034 0.031 0.031 0.031 0.029 0.029 0.029 0.027 0.026 0.026 0.026 0.025 0.025 0.024 0.023 0.023 0.022 0.021 0.021 0.02 0.02 0.02 0.02 0.019 0.019 0.018 0.018 0.018 Clipperton Isl.(FR) Jordan Benin Togo Honduras Macau (China) Malaysia Sarawak Kenya Norfolk Isl. (Australia) Guinea-Bissau Malaysia East Thailand Pitcairn (UK) Sri Lanka Malaysia West Bulgaria Marshall Isl. Atlantic Northeast - High seas Areas Liberia Malaysia Sabah Guatemala Romania Trindade & Matin Isl (BR) Georgia Papua New Guinea Slovenia Cambodia Cook Isl.(New Zealand) Atlantic Antarctic - High seas Areas Poland Maldives Northern Marianas (US) Johnston Atoll (US) Guam (US) Solomon Isl. Equatorial Guinea Fiji Tonga Brunei American Samoa Mauritius New Caledonia Micronesia Singapore Christmas Isl.(Australia) Vanuatu Easter Isl.(Chile) Tuvalu Mozambique Channel Isl. (FR) Timor Leste Wallis & Futuna (FR) Palau Seychelles Nauru Samoa Tokelau (NZ) Jarvis Isl.(US) Reunion (FR) Howland & Baker Isl.(US) Korea North Sweden Finland Andaman & Nicobar Isl. (India) Canary Isl.(Spain) Comoros Isl. Mayotte (FR) Cuba Dominican Rep. Estonia Haiti 1181 531 256 1006 446 581 611 536 726 811 596 1001 786 161 591 121 751 1201 566 601 421 836 91 361 771 941 136 231 1191 791 606 741 526 416 106 291 316 1016 116 11 631 696 746 931 196 701 171 1051 331 816 1146 756 921 676 1151 1011 1101 831 1106 541 991 321 466 961 211 216 246 271 296 436 seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds 125 0.01 0.036 0.127 0.127 0.02 0.076 0.251 0.122 0.02 0.09 0.195 0.24 0.008 0.14 0.178 0.033 0.017 0.01 0.127 0.154 0.01 0.032 0.006 0.021 0.148 0.019 0.117 0.01 0.01 0.056 0.091 0.008 0.006 0.008 0.077 0.059 0.022 0.008 0.064 0.006 0.036 0.029 0.015 0.053 0.012 0.023 0.002 0.007 0.013 0.041 0.006 0.016 0.03 0.005 0.003 0.003 0.002 0.009 0.002 0.057 0.067 0.033 0.036 0.045 0.014 0.022 0.015 0.016 0.026 0.017 0.012 0.036 0.045 0.046 0.011 0.02 0.04 0.041 0.019 0.04 0.04 0.038 0.01 0.037 0.037 0.025 0.017 0.012 0.034 0.033 0.008 0.02 0.008 0.018 0.028 0.016 0.028 0.012 0.01 0.024 0.024 0.008 0.007 0.008 0.02 0.019 0.019 0.009 0.013 0.007 0.012 0.01 0.011 0.011 0.009 0.009 0.002 0.008 0.004 0.008 0.007 0.007 0.005 0.005 0.004 0.003 0.003 0.001 0.002 0.001 0.001 0 0 0 0 0 0 0 0 0 0.018 0.018 0.018 0.018 0.017 0.017 0.016 0.016 0.016 0.015 0.015 0.015 0.015 0.014 0.014 0.014 0.014 0.014 0.013 0.013 0.012 0.012 0.012 0.011 0.011 0.011 0.011 0.01 0.01 0.009 0.009 0.008 0.008 0.008 0.008 0.007 0.007 0.006 0.005 0.005 0.005 0.004 0.004 0.004 0.004 0.003 0.003 0.003 0.003 0.003 0.003 0.003 0.002 0.002 0.001 0.001 0.001 0.001 0.001 0 0 0 0 0 0 0 0 0 0 0 Iceland Jamaica Latvia Lithuania Azores Isl.(Portugal) Russia Barrents Sea Russia Baltic Sea Kaliningrad USA Golf Of Mexico Antigua & Barbuda Macquarie Isl.(Australia) Bahamas Barbados Bouvet Isl.(Norway) Belize Brit. Indian Oce (UK) Brit. Virgin Isl.(UK) Cape Verde Cayman Isl.(UK) Cocos Isl.(Australia) Dominica Tromelin Isl.(FR) French Guyana Gibraltar (UK) Greenland Grenada Guadeloupe (FR) Guyana Heard & McDonald Isl.(Australia) Martinique Montserrat (UK) Windward Netherlands Antilles Leeward Netherland Antilles Niue (NZ) Jan Mayen Isl. (Norway) Madeira Isl.(Portugal) Puerto Rico (US) Russia Baltic Sea St Petersburg St Helena (UK) St Kitts & Nevis Anguila (UK) St Lucia St Pierre & Miquelon (FR) St Vincent & The Grenadines Sao Tome & Principe Suriname Svalbard Isl. (Norway) Trinidad & Tobago Turks & Caicos Isl (UK) Navassa Isl. (Haiti) Palmyra Atoll & Kingman Reef (US) Ascencion Isl. Venezuela Wake Isl.(US) Arctic Sea - High seas Areas Atlantic Eastern Central - High seas Areas Pacific Antarctic - High seas Areas 456 511 561 576 806 841 851 1121 21 36 46 61 81 96 101 111 151 156 201 266 336 341 386 401 406 411 431 441 621 651 686 691 721 736 801 821 866 871 876 881 886 891 896 901 981 986 1021 1046 1091 1096 1126 1136 1141 1186 1196 1241 seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds seabirds 126 0.012 0.013 0.02 0.014 0.013 0.019 0.026 0.014 0.004 0 0.003 0.002 0 0.003 0.002 0 0 0.003 0 0.006 0.009 0.007 0 0.01 0 0 0 0 0.007 0 0.003 0.003 0 0.003 0.009 0.004 0 0 0.003 0 0.007 0 0 0.01 0 0.01 0 0 0 0 0 0.007 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Table 35 Hig h Seas FAO a reas EEZ so rted by t hei r co nt ri butio n i n t he different exposu res for all s harks sorted by I UC N weig hted ex posu re EEZ, High Seas FAO area China Japan Main Isl. Vietnam India Pacific Western Central - High seas Areas Morocco Myanmar Indian Ocean Eastern - High seas Areas Pacific Northwest - High seas Areas Russia Pacific Pacific Southeast - High seas Areas Mauritania Indonesia (Eastern) Western Sahara (Morocco) Korea South Chile Peru South Africa Bangladesh Indonesia (Western) Guinea Japan Outer Isl. USA East Coast Taiwan Korea North Spain United Kingdom Mexico Philippines Greece Namibia Indian Ocean Western - High seas Areas Norway Senegal Brazil Pacific Eastern Central - High seas Areas Madagascar France Italy Tunisia Malaysia Sarawak Australia Iceland Atlantic Eastern Central - High seas Areas Atlantic Southwest - High seas Areas Malaysia East Thailand Canada Canary Isl.(Spain) Atlantic Western Central - High seas Areas Malaysia West Algeria Gambia Turkey Mediterranean Sea Croatia Malaysia Sabah Sierra Leone Ecuador Angola Overall rank 188 518 938 463 1273 658 128 1233 1258 858 1263 628 473 973 548 168 778 953 58 478 428 523 1118 193 543 968 1068 638 783 398 673 1238 733 918 88 1248 588 328 503 1033 613 33 458 1198 1218 598 1003 148 963 1223 593 8 368 1038 243 603 928 278 18 Family shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark 127 Overlap index 0.175 0.154 0.147 0.144 0.144 0.139 0.139 0.138 0.133 0.124 0.119 0.115 0.113 0.113 0.111 0.111 0.11 0.108 0.106 0.105 0.104 0.104 0.104 0.102 0.102 0.101 0.1 0.098 0.098 0.098 0.097 0.096 0.096 0.094 0.094 0.093 0.092 0.086 0.085 0.085 0.081 0.08 0.08 0.08 0.079 0.079 0.077 0.076 0.075 0.074 0.073 0.073 0.073 0.072 0.071 0.07 0.07 0.069 0.068 Unweighted exposure index 0.207 0.183 0.174 0.171 0.17 0.165 0.165 0.164 0.157 0.147 0.141 0.136 0.134 0.134 0.131 0.131 0.131 0.128 0.126 0.124 0.124 0.124 0.123 0.121 0.121 0.12 0.119 0.116 0.116 0.116 0.114 0.114 0.113 0.112 0.111 0.11 0.109 0.101 0.101 0.101 0.096 0.095 0.095 0.095 0.094 0.093 0.091 0.09 0.089 0.088 0.086 0.086 0.086 0.086 0.084 0.083 0.083 0.081 0.081 IUCN weighted exposure index 0.241 0.213 0.202 0.199 0.198 0.192 0.192 0.19 0.183 0.171 0.164 0.158 0.156 0.156 0.153 0.153 0.152 0.149 0.146 0.145 0.144 0.144 0.144 0.141 0.141 0.14 0.138 0.136 0.135 0.135 0.133 0.133 0.132 0.13 0.129 0.128 0.127 0.118 0.117 0.117 0.112 0.111 0.11 0.11 0.11 0.109 0.106 0.105 0.104 0.102 0.101 0.1 0.1 0.1 0.098 0.096 0.096 0.095 0.094 Nigeria Libya Pakistan Pacific Southwest - High seas Areas Egypt Galapagos Isl.(Ecuador) Ireland Atlantic Northeast - High seas Areas Ghana New Zealand Cameroon Portugal Atlantic Northwest - High seas Areas Papua New Guinea Atlantic SouthEast - High seas Areas USA West Coast Russia Barrents Sea Cambodia Faeroe Isl.(Denmark) Guyana Denmark Oman USA Golf Of Mexico Somalia Iran Yemen J. Fernandez, Felix and Ambrosio Isl. (Chile) Alaska Argentina Gabon Maldives Malta Colombia Suriname Cuba Tanzania Venezuela Lebanon Uruguay Netherlands Cote d'Ivoire United Arab Emirates Sri Lanka Montenegro Solomon Isl. Andaman & Nicobar Isl. (India) Sweden Israel Jamaica Azores Isl.(Portugal) Albania Congo Republic Greenland Cyprus Haiti Hong Kong Gaza Strip Mauritius Madeira Isl.(Portugal) Channel Isl.(UK) Panama Dominican Rep. Cape Verde Kiribati Syria Pacific Northeast - High seas Areas Mozambique Desventuradas Isl.(Chile) Germany French Polynesia 718 573 763 1268 1063 283 493 1203 383 708 143 798 1208 773 1213 1113 843 138 303 433 263 668 1123 948 483 1158 183 1083 28 358 608 618 208 983 248 1078 1138 558 1133 683 508 1028 163 1163 108 468 993 498 513 808 3 223 403 253 438 453 373 633 803 1073 768 273 153 393 998 1253 663 178 378 348 shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark 128 0.067 0.067 0.065 0.064 0.064 0.063 0.063 0.062 0.061 0.06 0.06 0.059 0.059 0.057 0.057 0.057 0.057 0.056 0.056 0.054 0.054 0.054 0.054 0.053 0.053 0.052 0.051 0.051 0.051 0.05 0.049 0.048 0.048 0.047 0.047 0.045 0.044 0.043 0.043 0.042 0.041 0.041 0.04 0.041 0.04 0.04 0.04 0.039 0.038 0.038 0.037 0.037 0.036 0.035 0.035 0.035 0.034 0.034 0.033 0.033 0.033 0.033 0.033 0.033 0.032 0.032 0.032 0.032 0.032 0.031 0.079 0.079 0.077 0.076 0.076 0.075 0.075 0.073 0.072 0.071 0.071 0.07 0.07 0.068 0.068 0.067 0.067 0.067 0.066 0.064 0.064 0.064 0.064 0.063 0.062 0.062 0.061 0.061 0.06 0.059 0.058 0.057 0.057 0.056 0.055 0.053 0.052 0.051 0.051 0.049 0.049 0.049 0.048 0.048 0.048 0.047 0.047 0.047 0.045 0.045 0.044 0.044 0.042 0.042 0.042 0.041 0.041 0.04 0.04 0.04 0.039 0.039 0.039 0.039 0.038 0.038 0.038 0.038 0.037 0.037 0.092 0.092 0.089 0.089 0.088 0.087 0.087 0.085 0.084 0.083 0.083 0.081 0.081 0.079 0.079 0.079 0.078 0.078 0.077 0.075 0.075 0.075 0.074 0.073 0.073 0.072 0.071 0.07 0.07 0.069 0.068 0.066 0.066 0.065 0.064 0.062 0.06 0.06 0.059 0.057 0.057 0.057 0.056 0.056 0.055 0.055 0.055 0.054 0.053 0.052 0.051 0.051 0.049 0.049 0.048 0.048 0.047 0.046 0.046 0.046 0.046 0.046 0.045 0.045 0.045 0.045 0.045 0.044 0.044 0.043 Fiji Svalbard Isl. (Norway) Mayotte (FR) Congo Sudan Liberia French Guyana Saudi Arabia Red Sea Brunei Brit. Virgin Isl.(UK) Saudi Arabia Persian Gulf Honduras Martinique Trinidad & Tobago Micronesia Kenya Trindade & Matin Isl (BR) Guinea-Bissau Togo Falkland Isl.(UK) Sao Tome & Principe Benin Guadeloupe (FR) Costa Rica Singapore Lord Howe Isl. (Australia) Belgium Macau (China) Haiwaii Main Isl. Christmas Isl.(Australia) Haiwaii NorthWest Isl. New Caledonia St Lucia Cocos Isl.(Australia) Bahrain Easter Isl.(Chile) Equatorial Guinea Dominica Poland Puerto Rico (US) El Salvador Marshall Isl. Vanuatu Comoros Isl. Antigua & Barbuda Anguila (UK) Seychelles Timor Leste Eritrea Kuwait Bosnia St Pierre & Miquelon (FR) Finland Monaco Norfolk Isl. (Australia) Bahamas Tuvalu Jan Mayen Isl. (Norway) Nicaragua Palau Latvia Qatar Russia Baltic Sea Kaliningrad Grenada Mozambique Channel Isl. (FR) St Vincent & The Grenadines Bermuda (UK) Brit. Indian Oce (UK) Estonia Wallis & Futuna (FR) 318 988 218 228 978 568 343 908 118 113 913 448 623 1023 748 538 93 813 1008 308 903 258 413 238 933 43 68 583 1088 198 643 698 888 203 53 173 293 268 793 823 288 753 703 213 23 883 923 818 133 553 78 893 323 648 728 48 1053 738 713 758 563 828 853 408 333 898 73 103 298 1148 shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark 129 0.03 0.03 0.03 0.029 0.029 0.029 0.028 0.028 0.026 0.026 0.025 0.024 0.024 0.024 0.023 0.023 0.023 0.023 0.023 0.023 0.023 0.023 0.022 0.022 0.022 0.021 0.021 0.021 0.02 0.02 0.02 0.02 0.02 0.019 0.019 0.019 0.019 0.019 0.019 0.019 0.018 0.018 0.018 0.018 0.018 0.018 0.018 0.017 0.017 0.017 0.017 0.017 0.017 0.017 0.016 0.016 0.016 0.016 0.016 0.015 0.015 0.015 0.014 0.013 0.013 0.013 0.013 0.012 0.012 0.012 0.036 0.035 0.035 0.035 0.034 0.034 0.034 0.034 0.031 0.03 0.029 0.029 0.028 0.028 0.028 0.027 0.027 0.027 0.027 0.027 0.027 0.027 0.026 0.026 0.026 0.025 0.024 0.024 0.024 0.024 0.024 0.024 0.023 0.023 0.023 0.023 0.023 0.023 0.022 0.022 0.022 0.022 0.022 0.022 0.021 0.021 0.021 0.021 0.02 0.02 0.02 0.02 0.02 0.02 0.02 0.019 0.019 0.019 0.019 0.018 0.018 0.017 0.017 0.016 0.015 0.015 0.015 0.015 0.014 0.014 0.041 0.041 0.041 0.04 0.04 0.04 0.039 0.039 0.036 0.035 0.034 0.033 0.033 0.033 0.032 0.032 0.032 0.031 0.031 0.031 0.031 0.031 0.03 0.03 0.03 0.029 0.028 0.028 0.028 0.028 0.028 0.027 0.027 0.027 0.027 0.027 0.027 0.026 0.026 0.026 0.025 0.025 0.025 0.025 0.025 0.025 0.024 0.024 0.024 0.024 0.023 0.023 0.023 0.023 0.023 0.023 0.022 0.022 0.022 0.021 0.02 0.02 0.02 0.018 0.018 0.018 0.017 0.017 0.017 0.016 St Kitts & Nevis Windward Netherlands Antilles Nauru Cook Isl.(New Zealand) Ascencion Isl. Montserrat (UK) Palmyra Atoll & Kingman Reef (US) Djibouti Lithuania Leeward Netherland Antilles Tromelin Isl.(FR) Guam (US) Cayman Isl.(UK) Northern Marianas (US) Reunion (FR) Slovenia Johnston Atoll (US) St Paul & Amsterdam (FR) Barbados Tonga Belize Clipperton Isl.(FR) American Samoa Guatemala Tokelau (NZ) Jarvis Isl.(US) Iraq Samoa Jordan Pitcairn (UK) St Helena (UK) Howland & Baker Isl.(US) Crozet Isl.(FR) Kerguelen Isl. (FR) Prince Edward Isl. (SA) Indian Ocean Antarctic - High seas Areas South Georgia & Sandwich Isl. (UK) Turkey Black Sea Atlantic Antarctic - High seas Areas Macquarie Isl.(Australia) Bouvet Isl.(Norway) Bulgaria Georgia Gibraltar (UK) Heard & McDonald Isl.(Australia) Niue (NZ) Romania Russia Black Sea Russia Siberia Russia Baltic Sea St Petersburg Turks & Caicos Isl (UK) Ukraine Navassa Isl. (Haiti) Wake Isl.(US) Arctic Sea - High seas Areas Pacific Antarctic - High seas Areas 878 688 678 233 1128 653 1098 353 578 693 338 418 158 743 833 943 528 1168 63 1018 98 1183 13 423 1013 1103 488 1153 533 788 873 1108 1173 1178 958 1228 313 1043 1193 38 83 123 363 388 443 723 838 848 863 868 1048 1058 1093 1143 1188 1243 shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark shark 130 0.012 0.011 0.011 0.011 0.011 0.011 0.011 0.011 0.011 0.01 0.01 0.01 0.01 0.01 0.009 0.009 0.009 0.009 0.009 0.009 0.008 0.008 0.008 0.008 0.007 0.007 0.007 0.006 0.006 0.005 0.004 0.004 0.003 0.003 0.003 0.003 0.002 0.002 0.001 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.014 0.014 0.013 0.013 0.013 0.013 0.013 0.013 0.013 0.012 0.012 0.012 0.012 0.011 0.011 0.011 0.011 0.011 0.01 0.01 0.01 0.009 0.009 0.009 0.008 0.008 0.008 0.007 0.007 0.006 0.005 0.005 0.004 0.004 0.003 0.003 0.003 0.002 0.001 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.016 0.016 0.015 0.015 0.015 0.015 0.015 0.015 0.015 0.014 0.014 0.014 0.014 0.013 0.013 0.013 0.013 0.012 0.012 0.012 0.012 0.011 0.011 0.011 0.009 0.009 0.009 0.008 0.008 0.007 0.006 0.006 0.004 0.004 0.004 0.004 0.003 0.002 0.001 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Table 36 5 Hig h Seas FAO a reas EEZ so rted by t hei r co nt ri bution i n t he different ex posures for all pi nni peds and otters so rted by IUC N weig hted ex posu re EEZ, High Seas FAO area Chile Peru Greece Algeria Argentina Tunisia Turkey Mediterranean Sea Croatia Norway Montenegro Iceland United Kingdom Sweden Russia Barrents Sea Denmark Madeira Isl.(Portugal) Canada Faeroe Isl.(Denmark) Bosnia Poland Ireland Russia Pacific Finland France Albania Germany Netherlands Latvia USA East Coast Russia Baltic Sea Kaliningrad Cyprus Estonia Alaska Greenland Lithuania Svalbard Isl. (Norway) Japan Main Isl. Channel Isl.(UK) Ecuador Uruguay Belgium USA West Coast St Pierre & Miquelon (FR) Mexico Falkland Isl.(UK) Brazil Atlantic Southwest - High seas Areas American Samoa Angola Antigua & Barbuda Australia Macquarie Isl.(Australia) Lord Howe Isl. (Australia) Bahamas Bahrain Bangladesh Barbados Bermuda (UK) Bouvet Isl.(Norway) Trindade & Matin Isl (BR) Overall rank 169 779 399 9 29 1034 1039 244 734 1164 459 1069 994 844 264 804 149 304 79 794 494 859 324 329 4 379 684 564 1119 854 254 299 1084 404 579 989 519 1074 279 1134 69 1114 894 639 309 89 1219 14 19 24 34 39 44 49 54 59 64 74 84 94 Family marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other 131 Overlap index 0.172 0.124 0.065 0.053 0.085 0.047 0.046 0.043 0.136 0.027 0.114 0.095 0.081 0.075 0.074 0.014 0.069 0.067 0.012 0.061 0.06 0.058 0.054 0.051 0.01 0.048 0.048 0.048 0.046 0.045 0.008 0.039 0.038 0.035 0.034 0.032 0.031 0.03 0.025 0.024 0.02 0.019 0.019 0.018 0.017 0.015 0.013 0 0 0 0 0 0 0 0 0 0 0 0 0 Un-weighted exposure index 0.203 0.147 0.077 0.063 0.101 0.055 0.055 0.051 0.162 0.032 0.135 0.112 0.096 0.089 0.088 0.017 0.081 0.079 0.015 0.072 0.072 0.068 0.064 0.06 0.012 0.057 0.057 0.056 0.054 0.054 0.01 0.046 0.045 0.041 0.04 0.038 0.037 0.035 0.03 0.028 0.024 0.023 0.022 0.021 0.02 0.018 0.015 0 0 0 0 0 0 0 0 0 0 0 0 0 IUCN weighted exposure index 0.242 0.152 0.149 0.122 0.114 0.107 0.106 0.099 0.063 0.062 0.052 0.043 0.037 0.035 0.034 0.033 0.032 0.031 0.028 0.028 0.028 0.026 0.025 0.023 0.023 0.022 0.022 0.022 0.021 0.021 0.018 0.018 0.017 0.016 0.016 0.015 0.014 0.014 0.012 0.011 0.009 0.009 0.009 0.008 0.008 0.007 0.006 0 0 0 0 0 0 0 0 0 0 0 0 0 Belize Brit. Indian Oce (UK) Solomon Isl. Brit. Virgin Isl.(UK) Brunei Bulgaria Myanmar Eritrea Cambodia Cameroon Cape Verde Cayman Isl.(UK) Sri Lanka Easter Isl.(Chile) Desventuradas Isl.(Chile) J. Fernandez, Felix and Ambrosio Isl. (Chile) China Taiwan Christmas Isl.(Australia) Cocos Isl.(Australia) Colombia Comoros Isl. Mayotte (FR) Congo Republic Congo Cook Isl.(New Zealand) Costa Rica Cuba Benin Dominica Dominican Rep. Galapagos Isl.(Ecuador) El Salvador Equatorial Guinea South Georgia & Sandwich Isl. (UK) Fiji Mozambique Channel Isl. (FR) Tromelin Isl.(FR) French Guyana French Polynesia Djibouti Gabon Georgia Gambia Gaza Strip Ghana Gibraltar (UK) Kiribati Grenada Guadeloupe (FR) Guam (US) Guatemala Guinea Guyana Haiti Heard & McDonald Isl.(Australia) Honduras Hong Kong India Andaman & Nicobar Isl. (India) Indonesia (Eastern) Indonesia (Western) Iran Iraq Israel Italy Cote d'Ivoire Jamaica Japan Outer Isl. Johnston Atoll (US) 99 104 109 114 119 124 129 134 139 144 154 159 164 174 179 184 189 194 199 204 209 214 219 224 229 234 239 249 259 269 274 284 289 294 314 319 334 339 344 349 354 359 364 369 374 384 389 394 409 414 419 424 429 434 439 444 449 454 464 469 474 479 484 489 499 504 509 514 524 529 marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other 132 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Jordan Kenya Korea North Korea South Kuwait Lebanon Liberia Libya Macau (China) Madagascar Malaysia West Malaysia East Malaysia Sabah Maldives Malaysia Sarawak Malta Martinique Mauritania Mauritius Haiwaii NorthWest Isl. Monaco Montserrat (UK) Morocco Mozambique Oman Namibia Nauru Windward Netherlands Antilles Leeward Netherland Antilles New Caledonia Vanuatu New Zealand Nicaragua Nigeria Niue (NZ) Norfolk Isl. (Australia) Jan Mayen Isl. (Norway) Northern Marianas (US) Micronesia Marshall Isl. Palau Pakistan Panama Papua New Guinea Philippines Pitcairn (UK) Portugal Azores Isl.(Portugal) Guinea-Bissau Timor Leste Puerto Rico (US) Qatar Reunion (FR) Romania Russia Black Sea Russia Siberia Russia Baltic Sea St Petersburg St Helena (UK) St Kitts & Nevis Anguila (UK) St Lucia St Vincent & The Grenadines Sao Tome & Principe Saudi Arabia Red Sea Saudi Arabia Persian Gulf Senegal Seychelles Sierra Leone Singapore Vietnam 534 539 544 549 554 559 569 574 584 589 594 599 604 609 614 619 624 629 634 644 649 654 659 664 669 674 679 689 694 699 704 709 714 719 724 729 739 744 749 754 759 764 769 774 784 789 799 809 814 819 824 829 834 839 849 864 869 874 879 884 889 899 904 909 914 919 924 929 934 939 marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other 133 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Slovenia Somalia South Africa Prince Edward Isl. (SA) Canary Isl.(Spain) Spain Western Sahara (Morocco) Sudan Suriname Syria Thailand Togo Tokelau (NZ) Tonga Trinidad & Tobago United Arab Emirates Turkey Black Sea Turks & Caicos Isl (UK) Tuvalu Ukraine Egypt Tanzania Haiwaii Main Isl. Navassa Isl. (Haiti) Palmyra Atoll & Kingman Reef (US) Jarvis Isl.(US) Howland & Baker Isl.(US) USA Golf Of Mexico Ascencion Isl. Venezuela Wake Isl.(US) Wallis & Futuna (FR) Samoa Yemen St Paul & Amsterdam (FR) Crozet Isl.(FR) Kerguelen Isl. (FR) Clipperton Isl.(FR) Arctic Sea - High seas Areas Atlantic Antarctic - High seas Areas Atlantic Eastern Central - High seas Areas Atlantic Northeast - High seas Areas Atlantic Northwest - High seas Areas Atlantic SouthEast - High seas Areas Atlantic Western Central - High seas Areas Indian Ocean Antarctic - High seas Areas Indian Ocean Eastern - High seas Areas Indian Ocean Western - High seas Areas Pacific Antarctic - High seas Areas Pacific Eastern Central - High seas Areas Pacific Northeast - High seas Areas Pacific Northwest - High seas Areas Pacific Southeast - High seas Areas Pacific Southwest - High seas Areas Pacific Western Central - High seas Areas 944 949 954 959 964 969 974 979 984 999 1004 1009 1014 1019 1024 1029 1044 1049 1054 1059 1064 1079 1089 1094 1099 1104 1109 1124 1129 1139 1144 1149 1154 1159 1169 1174 1179 1184 1189 1194 1199 1204 1209 1214 1224 1229 1234 1239 1244 1249 1254 1259 1264 1269 1274 marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other marine mammals other 134 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Table 37 c Hig h Seas FAO a reas EEZ so rted by t hei r co nt ri butio n i n t he different exposu res for all tu rt les so rted by I UC N weig hted ex posu re EEZ, High Seas FAO area India Vietnam Myanmar China Indonesia (Eastern) Mauritania Pacific Western Central - High seas Areas Bangladesh Indonesia (Western) Morocco Western Sahara (Morocco) Mexico Philippines United Kingdom Malaysia Sarawak Senegal Malaysia East Thailand Japan Main Isl. Japan Outer Isl. Korea South Malaysia West Spain Pacific Northwest - High seas Areas Korea North Malaysia Sabah Madagascar Indian Ocean Eastern - High seas Areas Nigeria USA East Coast France Sierra Leone Guinea Pakistan Taiwan Venezuela Atlantic Eastern Central - High seas Areas Namibia Brazil Cameroon Angola South Africa Papua New Guinea Denmark Cambodia Canary Isl.(Spain) Atlantic Western Central - High seas Areas Tunisia Peru Guyana Oman Yemen Somalia Iran Indian Ocean Western - High seas Areas Norway Ireland Italy Pacific Eastern Central - High seas Areas Overall rank 465 940 130 190 475 630 1275 60 480 660 975 640 785 1070 615 920 600 1005 520 525 550 595 970 1260 545 605 590 1235 720 1120 330 930 430 765 195 1140 1200 675 90 145 20 955 775 265 140 965 1225 1035 780 435 670 1160 950 485 1240 735 495 505 1250 Family turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle 135 Overlap index 0.221 0.219 0.217 0.182 0.178 0.158 0.163 0.165 0.164 0.137 0.129 0.134 0.138 0.118 0.127 0.12 0.123 0.12 0.116 0.117 0.114 0.114 0.101 0.112 0.111 0.109 0.109 0.109 0.104 0.093 0.091 0.102 0.102 0.101 0.1 0.092 0.093 0.096 0.095 0.093 0.093 0.093 0.089 0.079 0.088 0.078 0.083 0.078 0.087 0.085 0.084 0.083 0.083 0.083 0.08 0.071 0.071 0.072 0.077 Unweighted exposure index 0.262 0.26 0.257 0.216 0.21 0.187 0.193 0.196 0.194 0.162 0.153 0.159 0.164 0.14 0.15 0.143 0.146 0.143 0.138 0.138 0.135 0.135 0.12 0.132 0.132 0.129 0.129 0.13 0.124 0.11 0.108 0.121 0.121 0.12 0.118 0.109 0.11 0.114 0.112 0.111 0.11 0.11 0.105 0.093 0.104 0.092 0.099 0.092 0.103 0.101 0.099 0.098 0.098 0.098 0.095 0.084 0.084 0.085 0.091 IUCN weighted exposure index 0.422 0.42 0.415 0.347 0.34 0.323 0.319 0.316 0.313 0.295 0.277 0.269 0.264 0.254 0.243 0.241 0.235 0.23 0.224 0.224 0.219 0.218 0.217 0.212 0.211 0.209 0.208 0.208 0.2 0.2 0.196 0.196 0.195 0.193 0.191 0.187 0.185 0.184 0.182 0.178 0.178 0.178 0.17 0.17 0.168 0.167 0.166 0.166 0.165 0.162 0.159 0.158 0.158 0.157 0.154 0.153 0.152 0.151 0.147 Canada Russia Pacific Colombia Suriname Gambia Ghana USA Golf Of Mexico Gabon Australia Pacific Southeast - High seas Areas Atlantic Southwest - High seas Areas Portugal United Arab Emirates Saudi Arabia Persian Gulf Cote d'Ivoire Pacific Southwest - High seas Areas Andaman & Nicobar Isl. (India) Tanzania Alaska Netherlands Sudan Germany Saudi Arabia Red Sea Libya Solomon Isl. Algeria Fiji New Zealand Egypt Jamaica Chile Sri Lanka Cape Verde Greece Haiti Cuba Ecuador Malta Trinidad & Tobago Dominican Rep. Atlantic Northeast - High seas Areas Bahrain Sweden Congo Republic Maldives Faeroe Isl.(Denmark) Galapagos Isl.(Ecuador) Atlantic SouthEast - High seas Areas Hong Kong Azores Isl.(Portugal) Channel Isl.(UK) Kuwait Kiribati French Guyana Mozambique Atlantic Northwest - High seas Areas Panama Brunei Turkey Mediterranean Sea Madeira Isl.(Portugal) Congo Croatia Mayotte (FR) Qatar Liberia USA West Coast Martinique Eritrea Togo Uruguay 150 860 210 985 370 385 1125 360 35 1265 1220 800 1030 915 510 1270 470 1080 1085 685 980 380 910 575 110 10 320 710 1065 515 170 165 155 400 440 250 280 620 1025 275 1205 55 995 225 610 305 285 1215 455 810 1075 555 395 345 665 1210 770 120 1040 805 230 245 220 830 570 1115 625 135 1010 1135 turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle 136 0.074 0.072 0.073 0.074 0.073 0.073 0.065 0.072 0.071 0.071 0.068 0.06 0.068 0.066 0.064 0.063 0.062 0.062 0.065 0.054 0.06 0.053 0.059 0.054 0.057 0.054 0.056 0.057 0.057 0.056 0.056 0.057 0.052 0.053 0.055 0.052 0.053 0.047 0.049 0.052 0.047 0.052 0.044 0.05 0.05 0.045 0.049 0.047 0.047 0.041 0.04 0.046 0.043 0.044 0.044 0.04 0.041 0.041 0.039 0.036 0.04 0.038 0.039 0.039 0.038 0.04 0.037 0.036 0.035 0.033 0.088 0.085 0.086 0.087 0.087 0.087 0.077 0.086 0.084 0.084 0.08 0.071 0.081 0.078 0.076 0.074 0.074 0.073 0.076 0.064 0.071 0.063 0.07 0.064 0.067 0.063 0.067 0.067 0.068 0.066 0.066 0.067 0.061 0.063 0.065 0.062 0.063 0.055 0.058 0.061 0.056 0.061 0.052 0.059 0.059 0.053 0.058 0.056 0.056 0.049 0.048 0.054 0.051 0.052 0.052 0.048 0.049 0.049 0.046 0.042 0.047 0.045 0.046 0.046 0.045 0.047 0.044 0.042 0.042 0.039 0.146 0.145 0.145 0.141 0.14 0.14 0.139 0.138 0.136 0.135 0.131 0.13 0.129 0.124 0.123 0.123 0.119 0.118 0.117 0.116 0.115 0.114 0.112 0.112 0.112 0.111 0.111 0.11 0.109 0.109 0.108 0.108 0.108 0.106 0.104 0.101 0.101 0.099 0.099 0.099 0.098 0.098 0.096 0.096 0.096 0.093 0.093 0.092 0.09 0.088 0.088 0.086 0.085 0.084 0.084 0.082 0.079 0.078 0.077 0.076 0.076 0.076 0.075 0.074 0.073 0.072 0.07 0.069 0.068 0.068 Sao Tome & Principe Benin Honduras Singapore Brit. Virgin Isl.(UK) Mauritius Iceland French Polynesia Guadeloupe (FR) Micronesia Kenya St Lucia Grenada Costa Rica Dominica Puerto Rico (US) Trindade & Matin Isl (BR) Equatorial Guinea Pacific Northeast - High seas Areas New Caledonia Christmas Isl.(Australia) Macau (China) Guinea-Bissau Timor Leste Vanuatu El Salvador Lord Howe Isl. (Australia) St Vincent & The Grenadines Tuvalu Belgium J. Fernandez, Felix and Ambrosio Isl. (Chile) Lebanon Comoros Isl. Seychelles Antigua & Barbuda Leeward Netherland Antilles Anguila (UK) Marshall Isl. Palau Nicaragua Norfolk Isl. (Australia) Wallis & Futuna (FR) Montenegro Israel Bahamas Albania Cyprus Desventuradas Isl.(Chile) Cocos Isl.(Australia) Gaza Strip Argentina Syria St Kitts & Nevis Mozambique Channel Isl. (FR) Poland Windward Netherlands Antilles Iraq Tonga Montserrat (UK) Djibouti Easter Isl.(Chile) Finland Bermuda (UK) Cayman Isl.(UK) Belize Guam (US) Ascencion Isl. American Samoa Nauru Barbados 905 260 450 935 115 635 460 350 415 750 540 890 410 240 270 825 95 295 1255 700 200 585 815 820 705 290 45 900 1055 70 185 560 215 925 25 695 885 755 760 715 730 1150 1165 500 50 5 255 180 205 375 30 1000 880 335 795 690 490 1020 655 355 175 325 75 160 100 420 1130 15 680 65 turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle 137 0.035 0.035 0.033 0.034 0.034 0.033 0.03 0.032 0.032 0.031 0.031 0.031 0.028 0.03 0.03 0.029 0.029 0.029 0.03 0.028 0.028 0.028 0.028 0.027 0.026 0.027 0.026 0.025 0.024 0.022 0.024 0.024 0.024 0.024 0.024 0.022 0.023 0.023 0.023 0.023 0.022 0.022 0.021 0.021 0.02 0.02 0.019 0.019 0.02 0.018 0.018 0.017 0.018 0.018 0.017 0.018 0.018 0.017 0.017 0.017 0.016 0.014 0.014 0.015 0.013 0.014 0.014 0.014 0.013 0.014 0.042 0.042 0.039 0.04 0.04 0.04 0.036 0.038 0.038 0.037 0.037 0.036 0.034 0.035 0.035 0.035 0.034 0.034 0.036 0.033 0.034 0.033 0.033 0.032 0.031 0.031 0.031 0.03 0.029 0.027 0.029 0.028 0.029 0.028 0.028 0.027 0.028 0.027 0.027 0.027 0.026 0.026 0.025 0.025 0.024 0.023 0.023 0.023 0.024 0.022 0.021 0.021 0.021 0.021 0.02 0.021 0.021 0.02 0.02 0.02 0.019 0.017 0.016 0.018 0.016 0.017 0.016 0.016 0.016 0.016 0.067 0.067 0.065 0.065 0.064 0.064 0.063 0.062 0.062 0.061 0.06 0.059 0.057 0.057 0.057 0.056 0.056 0.056 0.055 0.054 0.054 0.053 0.053 0.052 0.052 0.051 0.051 0.051 0.048 0.048 0.048 0.047 0.046 0.046 0.045 0.045 0.045 0.044 0.044 0.044 0.043 0.043 0.043 0.043 0.041 0.039 0.038 0.038 0.038 0.036 0.036 0.035 0.035 0.034 0.034 0.034 0.034 0.033 0.032 0.032 0.031 0.03 0.029 0.029 0.029 0.028 0.027 0.027 0.026 0.026 Cook Isl.(New Zealand) Tromelin Isl.(FR) Greenland Brit. Indian Oce (UK) Haiwaii NorthWest Isl. Haiwaii Main Isl. St Pierre & Miquelon (FR) Jordan Palmyra Atoll & Kingman Reef (US) Latvia Samoa Guatemala Northern Marianas (US) Estonia Tokelau (NZ) Reunion (FR) Monaco Russia Baltic Sea Kaliningrad Bosnia Johnston Atoll (US) Jarvis Isl.(US) Clipperton Isl.(FR) Slovenia Lithuania Howland & Baker Isl.(US) Pitcairn (UK) St Helena (UK) St Paul & Amsterdam (FR) Falkland Isl.(UK) Crozet Isl.(FR) Prince Edward Isl. (SA) Indian Ocean Antarctic - High seas Areas Macquarie Isl.(Australia) Bouvet Isl.(Norway) Bulgaria South Georgia & Sandwich Isl. (UK) Georgia Gibraltar (UK) Heard & McDonald Isl.(Australia) Niue (NZ) Jan Mayen Isl. (Norway) Romania Russia Barrents Sea Russia Black Sea Russia Siberia Russia Baltic Sea St Petersburg Svalbard Isl. (Norway) Turkey Black Sea Turks & Caicos Isl (UK) Ukraine Navassa Isl. (Haiti) Wake Isl.(US) Kerguelen Isl. (FR) Arctic Sea - High seas Areas Atlantic Antarctic - High seas Areas Pacific Antarctic - High seas Areas 235 340 405 105 645 1090 895 535 1100 565 1155 425 745 300 1015 835 650 855 80 530 1105 1185 945 580 1110 790 875 1170 310 1175 960 1230 40 85 125 315 365 390 445 725 740 840 845 850 865 870 990 1045 1050 1060 1095 1145 1180 1190 1195 1245 turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle turtle 138 0.013 0.014 0.012 0.013 0.013 0.013 0.011 0.012 0.012 0.011 0.011 0.011 0.01 0.009 0.01 0.01 0.009 0.009 0.009 0.008 0.008 0.007 0.006 0.006 0.006 0.006 0.006 0.005 0.003 0.003 0.002 0.001 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.016 0.016 0.014 0.015 0.016 0.015 0.014 0.014 0.014 0.013 0.013 0.013 0.012 0.011 0.011 0.012 0.011 0.01 0.011 0.01 0.009 0.008 0.008 0.007 0.007 0.007 0.007 0.006 0.004 0.003 0.003 0.002 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0.026 0.026 0.025 0.024 0.024 0.024 0.023 0.023 0.023 0.023 0.022 0.022 0.02 0.019 0.019 0.019 0.018 0.018 0.018 0.016 0.015 0.013 0.013 0.013 0.012 0.011 0.011 0.011 0.006 0.005 0.005 0.003 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Table 38 Gi llnet survey fo rm add ressed to eac hj u risdictio n DATA REQUESTED Fishery Fi hery name s Fishing season (starting month ,ending month) Fishery target species for up to five main target species Target 1 Target 2 Target 3 Target 4 Target 5 Vessels Number of vessels in the fishery Vessel length (m)* Vessel type (artisinal/industrial) Number of crew Effort Effort (km/h/yr)* number of sets/yr (note that catch data are not requested) Distance from the coast fished (km)* (or please join an effort map if available) Spatial descriptors of fishing effort Does the fishery occur exclusively within the EEZ, straddling this boundary or in high seas exclusively? Fishing gear Gear type (name) Net length (m)* Setting depth (m)* Mesh size (cm)* Net height (m)* Soak time (min)* Fishery gear setting details Depth of water fished (m)* Depth from the bottom fished (categories : pelagic, epipelagic , middleÓdepths , epibenthic , benthic) Mitigation Are mitigation strategies used to avoid nonÓtarget species captures (see species list for species of interest in the study)? a) turtles – what and how are they deployed b) sharks Ó what and how are they deployed c) marine mammals Ó what and how are they deployed d) seabirds Ó what and how are they deployed * specify the unit if different 139 Ta ble 39 à Gillnet fis he ries s urvey res ults. Bette r printed in A 3 Fish adis am y Co y Na ocefr ishFni er me de MALAYSIA MYS MY1 MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS MYS nt x er MY1 MY1 MY1 MY1 MY1 MY1 MY1 MY1 MY1 MY2 MY MY22 Pelagic Fishery m g 9 adis min nt Av Fish in ocefr ishFni g aS c m g le am (m B e P oa g oa oxa b b B ) tS iz tH SSF tG tG RT RT 0 Gi Gi ( GN oB et t Ves N min Av g oa ishF sse um er nli ob y ht erf e 40 eot/ S et t ) m b Demersal Fishery 9 SSF 0 40 b Prawn Fishery 9 SSF 0 40 b MY4 Other Fisheries 9 SSF 0 40 b MY4 b aTr ( GT mm ) R lNe et b b b b b TURKEY TR1 Turkey Gillnet Fishery SSF 9 15201 b TUR TR1 TUR TR1 TUR TR1 TUR TR1 REFERENCES : (Sextant Turkey Survey 2011) ISL ICELAND IS1 Bottom Gillnet Fishery ISL IS1 ISL IS1 ISL IS1 ISL IS1 ISL IS1 REFERENCES : (Icelandic Fisheries 2011) SWEDEN SWE SE1 SWE SWE SE1 SE1 SWE SE2 SWE SE2 SWE SWE SWE SWE SE3 SE SE33 SE4 om s y tLik ke Co yp T m e/Fish aGe men r t y er (p 0 o a:e Zn g lic se Cod Fishery Baltic Sea b 9.14 299 mostly small scale fishing. b Mostly Artisanal Fishery Herring Fishery Baltic Sea SSF 8.7 127 b Mostly Artisanal Fishery Demersal Skagerrak/Kattegatt SSF 9.06 66 b Mostly Artisanal Fishery Gadus morhua Pollachius virens SWE SE4 SWE SE4 REFERENCES : (Sextant Sweden Survey 2011) 8.62 32 ha Co D abi mo p het ttM mn aR in Fish g n e x 20 10 5 0 20 2 100 0 am min abi mo ttMa mn Fish ( m Mshe m s ) iz e min am ( m eLt ) en g ht ( m et ) enl g ht Av n gM ( m xMhse m s ( m she m ) iz e 65 101 38 70 140 140 180 460 165 4 20 150 270 46 0 200 ) Siz e xn M Av gN ( ni e m) Ltne g ht h in am g hei ( m eHt ) hei g N t xn ( tm e ) t Av min gN ( m eHt ) hei g t p Dhe S t ( m etin ) g am Av p dhe xS De g S p h t ( m eint t enti ) g g Fish Fishh i ho nE g a ( d Soes urs ) aS in rt g aS t eos n n 90 70 150 100 0 150 200 b 50 60 35 50 80 10 10 200 200 130 00 100 35 35 150 10 50 50 200 1200 50 2000 90 Clupea harengus. SSF 01 2 2 Bottom Gillnet is widely used by small-intermediate boats to catch the Atlantic Cod in the S/SW of iceland. Gadus morhua Melanogrammus aeglefinus Cyclopterus lumpus. Hippoglossus hippoglossus other Flatfishes Gadus morhua other Flatfishes Pelagic Skagerrak/Kattegatt 125 20 30 14 45 264 0 6700 ha Co 2 2 5 2 5 2 2 SSF/LSF SSF ) Gillnet/Driftnet widely used for pelagic fishing and mostly in coastal waters Rastrelliger spp. Scomberomorus spp. Ilisha elongata Anodontostoma chacunda Megalaspis cordyla Selar crumenopthalmus Chirocentrus spp. Thunnus tonggol Euthynnus affinis Marine Catfish and Jewfish also uses set gillnet. Fishing operations in coastal waters Croakers Sea Catfish The prawn drift and gill nets are actually trammel nets. Fishing operations in coastal waters prawns Sharks and Rays Himantura spp./ Gymnura spp. / Myliobatis spp./ Aetobatus spp./Carcharhinus spp./Sphyrna spp. Sarda Sarda Pomatomus saltatrix Sparus auratus Dicentrarchus labrax SSF len g ht g vAf ( cm ish 2 REFERENCES : (Squires et al. 2003) (Project Global 2011) (SEAFDEC Stats 2011) (DoF Malaysia 2006) (SEAFDEC Framework 2008) TUR g in oC les ta m rt bin mm ed el 0 0 0 0 04 1 1 1 MY3 MY3 nE nt ( G circ ( G Fixe e N inl N dG ( GtN ) C g Gi ) F in le nl t )D et Drif nl nl Main Targets ISO Fish Mostly Artisanal Fishery Scomber scombrus. Clupea harengus. 140 5 2 100 150 5 30 0 200 5 2 100 60 150 37 200 364 0 5 30 30 0 0 200 200 200 50 500 10 1 5 1 1 1 1 1 1 1 1 200 60 90 60 me Ti k aS Avo MAURITIUS MUS MU1 Mauritius Gillnet Fishery SSF 7 6 b Artisanal and Costal Fishery. MUS MU1 MUS MU1 MUS MU1 MUS MU1 MUS MU1 REFERENCES : (Sextant Mauritius Survey 2011) BELGIUM BEL BE1 BEL BEL BE1 BE1 BEL BE2 FRA FRA FRA FRA FRANCE FR1 FR1 FR1 FR1 FR2 Sole and Cod Fishery, zone IVC 13.5 6 b Sole and Cod Fishery, zone VIID 13.5 2 b MALTA MT1 France Atlantic Set Nets France Mediterranean Set Nets Set Gillnet Fishery MLT MT2 MLT MLT MLT MLT MT MT22 MT2 MT2 Combined Gillnet/Trammel Fishery MT3 50 SSF 10.5 1200 150 10 5 2 100 35 2 2 2 35 Sparus aurata Solea solea Merluccius merluccius Mullus surmuletus Mullus barbatus Palinurus elephas 2 2 2 2 2 3 Auxis thazard Seriola dumerili Oblada melanura Boops boops Auxis Rochei Rochei adus morhua SGolea solea b 30 SSF 8 742 b SSF SSF 5.89 6.4 34 b b b 23 b trammel Net SSF 6.39 603 b Scorpaena spp. Sepia officinalis Mullus surmuletus Shark Gillnet and Shark Hook Sectors 44 b Coastal Reef Fishery REFERENCES : (Sextant Vanuatu Survey 2011) b 150 10 200 60 140 90 10 0 60 75 35 35 45 25 20 40 1 10 70 1500 10 30 60 400 409 300 70 0 4 5 2 0 160 00 20 20 50 18 2 2 2 2 25 20 2 2 2 25 100 5 0 100 5 Reef Associated Fisheries by coastal communities..Drifnet is banned. 141 75 125 160 0 37 37 2 3 3 9 1 1 10 11 11 2.5 2 10 200 1 1 10 400 1 1 11 45 150 12 0 100 1 12 10 22 40 153 6.6 20 100 1 12 11 22 45 150 1.6 20 100 1 12 11 183 5 4 72 130 00 200 409 100 200 409 152.4 2 2 2 2 5 2.5 1.5 Demersal Fishing. West Coast Tasmania, Set Depth can not exceed 130m Callorhinchus milii Mustelus antarcticus Pristiophorus cirratus Pristiophorus nudipinnis Galeorhinus galeus SSF 200 60 100 250 175 00 150 20 140 90 b b AUS AU1 AUS AU1 AUS AU1 AUS AU1 AUS AU1 REFERENCES : (Wilson et al. 2010) VANUATU VUT VU1 5 2 100 35 Sepia officinalis Mullus surmuletus Boops boops Scorpaena spp. Fishery MLT MT MLT MT33 MLT MT3 REFERENCES : (Sextant Malta Survey 2011) AUSTRALIA AUS AU1 10 2 20 0 Solea solea Lophius sp. Maja Squinado MT1 MT1 MT1 MT1 MT1 MLT 70 40 30 50 40 Gadus morhua Solea solea FRA FR FRA FR22 FRA FR2 FRA FR2 FRA FR2 FRA FR2 REFERENCES : (Sextant France Survey 2011) MLT MLT MLT MLT MLT MLT 4 4 4 5 4 Lethrinus nebulosus Lethrinus mahsena Siganus sutor Mugil cephalus Valamugil seheli BEL BE BEL BE22 REFERENCES : (Sextant Belgium Survey 2011) FRA 110 227 80 146 165 470 4200 St HELENA SHN SH1 no gill-net fishery is carried out within the EEZ’s of St Helena REFERENCES : (Sextant St Helena Survey 2011) BANGLADESH BGD BD1 BGD BGD BD1 BD1 BGD BD2 BGD BGD BD2 BD2 BGD BD3 Mechanised Gillnetters Fishery SSF 18,992 b Main Target is the pelagic Tenualosa ilisha Tenualosa ilisha promfret,jewfish,catfish,ray,sharks Non-Mechanised Gillnetters Fishery SSF 6,377 b Main Target is the pelagic Tenualosa ilisha Tenualosa ilisha promfret,Bambay Duck,jewfish,ray,sharks Trammel Net Fishery SSF 1,103 b Please note that driftnet are used for Hilsha shad, large Mesh drift net for the indian salmon, bottom gillnet for shrimps, croakers, ribon fish, bombay duck and Mullet gillnet for grey mullet. REFERENCES : (Hossain 2004) (DoF Bangladesh 2007) THAILAND THA TH1 THA TH1 THA TH2 THA TH2 THA TH3 THA TH3 THA TH4 THA THA THA THA THA THA TH4 TH4 TH4 TH4 TH4 TH4 THA TH5 THA THA THA THA THA THA TH5 TH5 TH5 TH5 TH5 TH5 Indian Ocean Driftnet Fishery 22 Indian Ocean Encircling Gillnet Fishery 22 LSF 10.5 LSF 12 SSF 9.5 22 36 200 0 36 200 Main Targets are jewfish and shrimps promfret,shrimp,jewfish,catfish,ray,sharks b 5 Pelagic fish mostly b Main Target Indo-Pacific mackerel 60 Indo Pacific Mackerel,Scad,dorad wolf-hering,croaker,Fourfingers threadfin,spanish mackerel,sardine,pomfret,mullet 40 Scomberomorus guttatus Indian Ocean Trammel Net Fishery 5 0 55 20 100 45 90 b 40 260 5 20 3 40 3 3 3 40 40 40 prawns, drums & croakers, indo-pacific mackerel, anchovies, swimming crabs, red snapper, indian mackerel Indian Ocean Other Gillnet Fishery 22 SSF 5 b b b 7.5 Gulf of Thaillan Other Gillnet Fishery 22 surface gillnet b 11 b 11 11 11 b b b b SSF 5 b 7.5 surface gillnet b 11 b b b b 5 5 THA TH6 TH6 Gulf of Thailland Driftnet Fishery 22 LSF THA TH7 22 LSF 12 THA THA TH7 TH7 Gulf of Thailland Encircling Gillnet Fishery THA TH8 Indo-Pacific mackerel, swimming crab, Sillago Whitings, mullet, sardine Fourfingers threadfin, mullet, sardine 22 SSF THA TH8 REFERENCES : (SEAFDEC Stats 2011) (SEAFDEC Framework 2008) (SEAFDEC Monograph 2011) 9.5 seabass,mangrove crabs,red snapper,spinny lobster,threadfin,snapper,emperor,red frog crab,seabass swimming crabs giant queenfish whiting b Main Target Indo-Pacific mackerel 120 95 30 100 90 25 60 120 95 30 100 Longtail Tuna, Eastern Little Tuna, Narrow-barred king mackerel, Trash Fish, IndoPacific mackerel, indian mackerel 40 45 Pelagic fish mostly b 5 100 90 25 85 Indo-Pacific mackerel, swimming crab, mangrove crabs, Sillago Whitings, Threadfin, mullet, sardine, indian mackerel Fourfingers threadfin, mullet, sardine 40 85 Scomberomorus guttatus Jacks, Cavalla, Trevallies, Trash Fish Gulf of Thailland Trammel Net Fishery 40 seabass,mangrove crabs,red snapper,spinny lobster,threadfin,snapper,emperor,red frog crab,seabass swimming crabs giant queenfish whiting b 11 11 11 10.5 THA 5 0 b 0 55 20 142 40 40 40 40 5 20 90 40 prawns, Narrow-barred king mackerel, crabs 3 3 3 3 260 VIETNAM VNM VN1 VNM VNM Driftnet Fisheries SSF VN1 VN1 VNM 15 40 b Mostly pelagic targets some largng e scn at le fishi iNang he Da province. SSF/LSF VNM VN2 VN2 Drift Bottom Gillnet Fisheries SSF 40 VNM VNM VN3 VN3 Bag Gillnet Fisheries SSF 13 40 VNM VN4 Trammel Net Fisheries SSF 10 40 b b PHL PHL PHL PHL PHL PHL PHL PHL PH1 PH1 PH1 PH1 PH1 PH1 PH2 PH2 PHL Surface Gillnet Fisheries 15 SSF 8 3 b PHL PH3 PH3 Bottom Gillnet Fisheries 15 SSF PHL PHL PHL PH4 PH4 PH4 Trammel Net Fisheries 15 SSF 8.5 3 PHL PH5 Encircling Gillnet Fisheries 15 SSF 9 3 b BRN BN1 BRN 10 3 20 3 44 75 800 480 30 40 42 45 14.5 30 25 90 Black Fin Mullet, Big-Eye/Yellowstripe/Round Scad, FLying Fish, Fresh water Herring,Skipjack, Tuna, Blue Marlin, Spanish/Indian/Stripped/Short-bodied/Frigate Mackerel,Leather Jacket, Squid, Milkfis Manta Ray 650 30 150 b b 30 crabs, nimipterids, lizard fish, slipmouths, hairtail, snapper, white shrimp, prawn b halfbeak fish, Spotted halfbeak, garfish b 38.1 43.5 28 76.2 60.9 40 51 76 35 270 270 460 1.5 40 35 35 35 35 45 40 90 90 90 600 600 100 100 100 800 800 300 300 300 14 12 6 6 6 16 5.5 SSF 7.5 5 b Demersal and small pelagic fishes BRN BN2 BN2 Trammel Net Fisheries 5.5 SSF 6 2 b Mostly Shrimps BRN BRN BN3 BN3 Crab Gillnet Fisheries 5.5 SSF BRN BN4 Trammel Net Fisheries 5.5 SSF 7 pony fish, hard-tail scads, croakers, etc Schrimps and Crabs b Crabs BRN BN4 REFERENCES : (SEAFDEC Stats 2011) (SEAFDEC Framework 2008) (SEAFDEC Monograph 2011) Gillnet Fisheries CMR CM1 CMR CM1 CMR CM1 CMR CM1 CMR CM1 REFERENCES : (Project Global 2011) 3.2 24 Mackerel,Milkfish,Round Scad, Herring, Scad, Sting Ray, Shark, Sardine Bottom Gillnet Fisheries CAMEROON CMR CM1 400 12 pelagic fishing REFERENCES : (SEAFDEC Stats 2011) (SEAFDEC Framework 2008) (SEAFDEC Monograph 2011) BRUNEI BN1 48 Operated mostly in shallow waters Long torn,big-eye Scad anchovy Sardine/Mackerel Garfish Flying Fish SSF BRN 50 105 6 Bag Gillnet Tiggertoothed Croaker,Lobster Shrimps Cuttlefish 15 PH5 30 70 0 Crabs, Blue swimming crab, Tigertooth croake Driftnet Fisheries PHL Sardine, Flying Fish Tuna and Mackerel 20 grouper, croaker, bream, swimming crab b VNM VN4 VNM VN4 VNM VN4 REFERENCES : (SEAFDEC Stats 2011) (SEAFDEC Framework 2008) (SEAFDEC Monograph 2011) PHILIPPINES PHL PH1 2 7.66 SSF 2 b b 9 9 7.5 7.5 7.5 b b b b b b b pelagic fish pomfret,bonito,scomberoides Scomberomorus commerson 0 120 10 70 Ethmalosa fimbriata Sardinella maderensis Pseudotolithus senegalensis Pseudotolithus typus Galoides/Pentanemus/Polydactylus 0 0 2 2 2 25 25 50 50 0 0 0 0 50 80 70 150 70-80% pelagic feishing, 20-30% Demersal SOUTH 143 AFRICA ZAF ZA1 Shark Gillnet Fisheries 0.4 SSF 15 b b Fishery to protect swimmers from shark attack ZAF ZA1 REFERENCES : (KwazuluNatal Sharks Board 2011) DENMARK DNK DK1 DNK DNK DNK DK1 DK1 DK2 Kattegat Gillnet Fisheries Baltic Gillnet NK DK2 Fisheries REFERENCES : (Project Global 2011) Sharks SSF SSF 10.9 10.9 96.1 b 96.1 b D SLOVENIA SVN SI1 Gillnet Fisheries SSF 41 41 416 b b b b N GIN GIN GIN GUINEA GN1 N1 N1 GN1 G Gillnet Fisheries b N JPN 1 b b b b b MOZAMBIQUE MOZ MZ1 M Z Z1 Gillnet Fisheries Z MZ1 REFERENCES : (Faife 2003) (FAO 6 10 14 775.77 1018.43 600 710.56 600 Bonga shads Bonga Shads,Otholtis Leptocharias smithii,Rhinobatos cemiculus, Sphyrna lewini,Rhinobatos rhinobatos b b b skipjack tuna,yellowfin tuna,bigeye tuna,Pacific bluefin tuna,Albacore SSF MO 6 b b b b Grouper, sea bream, sharks Sardines b Profile) PER PERU PE P P ER PER PER PER PER PER E1 PE1 PE1 PE1 PE1 PE Shark and Ryas Driftnet Fisheries Salaverry and San Jose Gillnet Fisheries SSF SSF b SPAIN ES1 ESP ES1 Anglerfish Gillnet Fisheries SSF 1 1 1 1 335 335 2750 40 0 1 0 0 200 350 740 55 0 Paralonchurus peruanus Genypterus maculatus Mustelus whitneyi 2 2 2 30 5 0 10 16 221 b REFERENCES : (Ayala 2008) (Mangel ) et al . 2009 ESP Sphyrna zygaena Myliobatis spp. Prionace glauca Isurus oxyrinchus Alopias vulpinus b Operates in ICES Div. VIIIc 280 Lophius piscatorius Lophius budegassa 144 2 2 100 5 0 20 300 1000 1013 1 1 15 160 18 18 6.9 11.8 2 1.1 3 b REFERENCES : (WCPFC 2010) MO 214 110 50 52 38 62 80 b SSF SSF 110 b b Gillnet Fisheries Cod b G JAPAN JP1 JP 90 130 23400 European Pilchard, Comomon Sole, European Flounder REFERENCES : (Diop et al. 2009) JP Sole Cod b REFERENCES : (Sextant Slovenia Survey 2011) GI b 510 200 900 REFERENCES : (Costas et al 007) . 2 EU EU deep sea gillnet fisheries SSF b Hake Gillnet Fisheries b ishing in f ICES sub area IVa, 43 Merluccius merluccius 2 Lophius spp. 2 Centrophorus squamosus 2 Chaceon affinis 3 45 3 0 107 0 1000 5 120 1500 2500 12 100 600 1 1 16 250 7000 22500 3.64 100 800 84 220 6500 9000 6.4 800 1600 84 3.64 600 1200 VII, VIII, Ixa onk ish Tangle net M f Fisheries ishing in f ICES sub area IIa, 9 2 IVa,b, VI, VII, VIII Deepwater Shark Gillnet Fisheries ishing in f ICES sub area VI, VII, 2 1 45 24 00 VIII, IX, X, XII Crab Tangle Net f ishing in f ICES sub area IVa, isheries 1 0 3 0 7 2 4 220 Vb, VI,VII, VIII, XII REFERENCES : (STECF CAMBODIA KHM KH1 KH M KH1 KHM KH2 KH M 2 006) Shrimp Trammel Fisheries b Mackerel Gillnet Fisheries 38 No ishing f allowed between 1 b 100 Shrimp. Catfish, sivler and black pomfrets 1 5 january and 1 march 3 KHM KH2 KH3 KH M KH 3 KH M KH 3 KHM KH4 KH M KH 4 Mackerel Scomberomorus Gillnet Fisheries b b 2 SSF L Boats less 0HP o f Boats 9 SF greater than 0HP Crab Gillnet Fisheries mostly 2 9 18 2 Fishing 10000 Scomberomorus, scads and shack. 9 b 1000 Scomberomorus, scads and shack. 40 0 100 Portunus spp., Scylla serrata operates in the shallow or inshore water KHM KH5 KH M KH 5 Clupea Gillnet Fisheries b 2 Fishing mostly 35 150 200 1 1 Clupea operates in the shallow or inshore water REFERENCES : (SEAFDEC Stats 011) (SEAFDEC Framework 2 008) (SEAFDEC onograph 011) 2 2 M CHL CHILE CL1 CH L C 1 L CHL CL2 CH L CH L CH L C L2 C L2 C L2 CHL CL3 Industrial Swordfish Driftnet Fisheries LSF b Boats are greater than 18m in 560 510 560 2470 60 8 length, typically 1mg6 m 2 2 Artisanal Swordfish Driftnet Fisheries SSF 15 b Boats are 3.2 SSF b Xiphias gladius 1 3 00 0 800 less than 18m in length Artisanal Coastal Gillnet Fisheries 510 . Boats are Xiphias gladius Merluccius australis Merluccius gayi 5 00 3 80 5 0 0 2 5 8 0 800 1000 5 00 200 less than 18m in length 1 1100 . jack mackerel,Sardines,Anchovies REFERENCES : (SEAFDEC Stats 2011) (SEAFDEC Framework 2008) (SEAFDEC Monograph 2011) 14 5 9 60 30 MOROCCO MAR MA1 MAR MA1 Artisanal Gillnet Fisheries SSF 6 b catch are sold directly for fresh Target small fish species consumption MAR MA2 Deep-sea Gillnet Fisheries LSF 173 177 b This Fishery is being 6500 14000 6800 25 30 27.5 12 Swordfish phased out. REFERENCES : (Tudela et al. 2005) (Franquesa et al. 2001) (WW F 2011) ARGENTINA ARG AR1 ARG AR1 Set Gillnet Fisheries SSF 13.5 b b Each fisherman with a permit 120 140 30 50 1.8 2.5 12 100 160 2000 6860 8.5 16 12 300 400 2000 7400 8 30 12 140 400 4.5 27 130 140 60 270 40 70 Patagonian blenny, silverside, parona leatherjack, southern king crab is allowed to operate up to 12 nets, each with 30 to 50m length and 1.8 to 2.5m height. REFERENCES : (Project Global 2011) BRA BRAZIL BR1 BRA BR1 BRA BR2 BRA BR2 BRA BR3 BRA BR3 BRA BR3 Port of Ubatuba Driftnet Fisheries 80 LSF 13 12 b hammerhead sharks and bony fishes Ports of Itajaí, Navegantes, Porto Belo and Laguna Drifnet Fisheries LSF 18.75 Bottom Set Gillnet Fisheries LSF 20 40 b hammerhead sharks and bony fishes ports of Itajaí, Navegantes, Porto Belo and Laguna b 19 croaker, weakfish, and lobster Micropogonias furnieri >150 2 45 20 40 1850 25928 3.06 REFERENCES : (Project Global 2011) ERI ERITREA ER1 Artisanal pelagic gillnet fisheries SSF b Sardines and Anchovies ERI ER2 Artisanal Shark Gillnet fisheries SSF b Coastal Shark REFERENCES : (Project Global 2011) COSTA RICA CRI CR1 Artisanal gillnet fisheries SSF 8 b REFERENCES : (Project Global 2011) IND INDIA IN1 IND IN1 Kakinada Gillnet Fisheries IND IN1 Chenai Gillnet Fisheries IND IN1 Mangalore Gillnet Fisheries India gillnet fisheries b 4 10 9 25 20 70 12.5 79 12.5 75 b b b b b b seerfish, perches 60 seerfish, sharks, carangids, tuna seerfish, sharks, carangids REFERENCES : (Yousuf et al. 2008) 14 6 25 75 1000 1500 1000 6000 500 1500 6 8 12 20 100 5 30 200 7 25 70 8