MS/Art8/2018/D2/Spain/NE Atlantic: Bay of Biscay & Iberian Coast

Member State report / Art8 / 2018 / D2 / Spain / NE Atlantic: Bay of Biscay & Iberian Coast

Report type	Member State report to Commission
MSFD Article	Art. 8 Initial assessment (and Art. 17 updates)
Report due	2018-10-15
GES Descriptor	D2 Non-indigenous species
Member State	Spain
Region/subregion	NE Atlantic: Bay of Biscay & Iberian Coast
Reported by	Subdirección General para la protección del mar. D.G. Sostenibilidad de la Costa y del Mar. Minister
Report date	2020-02-03
Report access	msfd2018-ART8GES_MOD2020.xml

Demarcación marina noratlántica (ABI-ES-SD-NOR)

Simplified table

GES component	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2
Feature	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Newly-introduced non-indigenous species	Newly-introduced non-indigenous species	Established non-indigenous species
Element	Abludomelita aculeta	Acanthella acuta	Acartia (Acanthacartia) tonsa	Agardhiella subulata	Agarophyton vermiculophyllum	Aglaophenia kirchenpaueri	Aglaophenia picardi	Aglaothamnion cordatum	Aglaothamnion feldmanniae	Aglaothamnion tenuissimum	Aiolocolax puchellus	Alvania cimex	Alvania hispidula	Ampelisca cavicoxa	Ampelisca heterodactyla	Ampelisca lusitánica	Ampelisca pectenata	Ampelisca pseudosari	Ampelisca pseudospinimana	Amphibalanus amphitrite	Amphibalanus improvisus	Amphiroa rigida	Amphiroa vanbosseae	Anadara gibbosa	Anapagurus petiti	Anguillicoloides�crassus	Anotrichium furcellatum	Antithamnion amphigeneum	Antithamnion cruciatum	Antithamnion densum	Antithamnion diminuatum	Antithamnion hubbsii	Antithamnion nipponicum	Antithamnion villosum	Antithamnionella boergesenii	Antithamnionella elegans	Antithamnionella spirographidis	Antithamnionella ternifolia	Aphanocladia stichidiosa	Arca noae	Arichlidon reyssi	Armina maculata	Asclerocheilus ashworthi	Asparagopsis armata	Asparagopsis taxiformis	Aurelia coerulea	Bacteriastrum�hyalinum	Balanus trigonus	Biddulphia sinensis	Bivetiella cancellata	Blackfordia virginica	Boccardia proboscidea	Boccardia semibranchiata	Boccardiella ligerica	Bolinus brandaris	Bonamia�exitiosa	Bonamia�ostreae	Bonnemaisonia hamifera	Bostrycapulus odites	Botrylloides leachii	Botryllus schlosseri	Botryocladia wrightii	Branchiomma bairdi	Branchiomma luctuosum	Brania arminii	Bryopsis feldmanii	Cabestana cutacea	Callinectes sapidus	Callithamniella flexilis	Caprella mutica	Caprella scaura	Caulacanthus okamurae	Cavernularia pusilla	Centroceras clavulatum	Centrolabrus exoletus	Ceramium codii	Ceramium secundatum	Ceramium tenerrinum	Cerithiopsis jeffreysi	Cerithiopsis minima	Chaetopleura angulata	Chama gryphoides	Chondracanthus teedei	Chondrosia reniformis	Chrysymenia ventricosa	Ciona intestinalis	Clavularia crassa	Clytia�hummelincki	Coccinasterias tenuispina	Codium adherens	Codium fragile	Colpomenia peregrina	Colpomenia sinuosa	Corella eumyota	Coscinodiscus wailesii	Crepidula fornicata	Crepipatella dilatata	Crisia fistulosa	Crisia sigmoidea	Cyclope neritea	Cystoseira humilies myriophylloides	Cystoseira usneoides	Dasya baillouviana	Dasya sessilis	Dasybranchus gajolae	Dasysiphonia japonica	Desdemona ornata	Dexamine spiniventris	Diadema�setosum	Diadumene lineata	Dialychone longiseta	Didemnum vexillum	Dipolydora socialis	Dipolydora tentaculata	Ecteinascidia turbinata	Ectocarpus silicuosus hiemalis	Elminius modestus	Ensis leei	Eocuma dimorphum	Episcomitra cornicula	Ericthonius brasiliensis	Erinaceusyllis belizensis	Eriocheir sinensis	Eucheilota�menoni	Fibrocapsa japonica	Ficopomatus enigmaticus	Filellum serratum	Filicrisia franciscana	Fundulus heteroclitus heteroclitus	Gastroclonium clavatum	Gelidium serra	Genetyllis nana	Gibbula albida	Glycera celtica	Goniadella gracilis	Gracilipurpura rostrata	Grateloupia doryphora	Grateloupia filicina	Grateloupia subpectinata	Grateloupia turuturu	Gymnodinium catenatum	Gymnothamnion elegans	Halecicum liouvillei	Halichondria (Halichondria) semitubulosa	Haliclona (Haliclona) simulans	Haminoea japónica	Hemigrapsus penicillatus	Hemigrapsus takanoi	Herposiphonia secunda	Hexapleomera robusta	Hexaplex trunculus	Hincksia ovata	Holothuria (Holothuria) helleri	Hyale spinidactyla	Hydroclathrus clathratus	Hydroides dianthus	Hypnea musciformis	Jassa marmorata	Karenia mikimotoi	Lembos angularis	Lembos spiniventris	Leptocheirus longimanus	Liagora viscida	Lomentaria ercegovicii	Lomentaria hakodatensis	Lumbrinerides acuta	Magallana gigas	Mangiliella bertrandi	Marteilia�refringens	Megabalanus tulipiformis	Melanothamnus harveyi	Mercenaria mercenaria	Microcosmus squamiger	Microdeutopus similis	Microphthalmus similis	Mitrocomium cirratum	Molgula�manhattensis	Monocorophium acherusicum	Monocorophium sextonae	Monomyces pygmaea	Monophorus perversus	Monoplex corrugatus	Mya arenaria	Mycale (Mycale) massa	Myriocladia tormentosa	Namanereis littoralis	Oculina patagonica	Opisthodonta spinigera	Oriopsis eimeri	Pachymeniopsis lanceolata	Palaemon macrodactylus	Paleonotus chrysolepis	Parablennius incognitus	Parablennius pilicornis	Paracaprella pusilla	Paracartia grani	Paracerceis sculpta	Paradella dianae	Paralacydonia paradoxa	Paramuricea grayi	Paranaitis speciosa	Parapionosyllis brevicirra	Parexogone wolfi	Perkinsus olsenii	Perophora japonica	Petricolaria pholadiformis	Peyssonnelia coriácea	Peyssonnelia squamaria	Phorcus sauciatus	Photis longipes	Pikea califórnica	Pinna nobilis	Pista unibranchia	Polycera hedgpethi	Polycerella emertoni	Polycyathus muellerae	Polysiphonia morrowii	Polysiphonia polyspora	Polysiphonia scopulorum	Potamopyrgus antipodarum	Prionospio�pulchra	Pseudodactylogyrus�anguillae	Pseudodactylogyrus�bini	Pseudolithoderma extensum	Pseudopolydora�paucibranchiata	Pyropia koreana	Pyropia leucosticta	Pyropia suborbiculata	Pyropia tenera	Radicilungua thysanorhizans	Rapana venosa	Raphitoma echinata	Rhachotropis inermis	Rhithropanopeus harrisii	Rhodophysema elegans	Rissoa decorata	Ruditapes philippinarum	Sabella�spallanzanii	Sargassum flavifolium	Sargassum muticum	Sargassum vulgare	Scageliopsis patens	Scalarispongia scalaris	Schimmelmannia schousboei	Schizoporella errata	Scrupocaberea maderensis	Scytosiphon dotyi	Semicassis saburon	Sigambra parva	Solieria chordalis	Spermothamnion repens var. Flagelliferum	Spongoclonium caribaeum	Stauridiosarsia reesi	Steromphala adansonii	Steromphala adriatica	Stramonita haemastoma	Styela clava	Styela plicata	Syllides edentatus	Syllis westheidei	Syllis�pectinans	Synidotea laticauda	Tellina compressa	Tervia irregularis	Tonicia atrata	Tricellaria inopinata	Tricolia speciosa	Tritia corniculum	Tritia mutabilis	Turbonilla acuta	Turritella turbona	Ulva australis	Umbraulva dangeardii	Undaria pinnatifida	Urosalpinx cinerea	Xenostrobus securis	Zeuxo holdichi	Not applicable
Element code	102786	132455	345943	145677	1327786	117277	117282	144492	144494	144501	146359	141167	141195	179881	101899	101907	101445	101916	101917	421137	421139	145100	495067	504350	107220	458994	144505	494896	144509	144511	144512	214070	373793	144517	144518	144519	144521	163275	144786	138788	333033	138805	326666	144438	144439	292506	149119	106223	148969	341244	117313	327249	131113	131114	140389	563562	246871	144442	457048	250081	103862	1313615	421070	130881	131280	144451	141099	107379	371336	146768	236551	496188	128535	144531	126961	144541	144562	144567	139078	139079	848025	139119	145624	134112	145845	103732	125338	225740	123795	145078	145086	145856	145857	173223	156632	138963	234137	111698	111704	140487	145520	145537	144714	232221	129883	836896	130902	102134	213372	395099	882444	250126	131124	606816	103756	706498	106209	876640	181776	1060398	102401	195950	107451	221217	233761	130988	117691	470794	293599	145809	839160	130645	141779	130119	130145	1319814	145247	145248	370564	295880	109784	144592	117593	196765	132858	238369	107454	389288	214222	136527	140396	145438	124506	102322	145861	131000	145634	102433	233024	102016	102024	102037	145764	145827	232230	130228	836033	137820	395091	106226	1027787	141919	236666	102050	130176	117756	103788	225814	148603	135200	141720	476518	140430	168647	144926	334078	135210	421053	130941	496180	181372	129934	126771	126773	211364	104264	261827	261839	130545	125388	157522	157522	943463	625984	103758	156961	145276	145288	689178	102384	145229	140780	131521	140835	140839	135165	232563	144658	144664	147123	558845	119498	119499	144990	131168	626054	626059	699639	626074	144780	140416	139366	102233	107414	145774	141349	231750	130969	145556	494791	145565	144692	165376	145234	111527	760316	145868	509237	130702	145681	550745	526670	565164	1039842	1039844	140417	103929	103936	131407	131461	131450	257397	141584	111751	386327	111254	141702	876831	876840	141052	141874	660661	840293	145721	140429	140485	416601	Not applicable
Element code source	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Undefined	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Undefined	Link to other vocabulary or code lists that may be relevant
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	Other
Criterion																																																																																																																																																																																																																																																																																							D2C1	D2C2
Parameter																																																																																																																																																																																																																																																																																							Presence	Abundance
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend																																																																																																																																																																																																																																																																																							Improving	Unknown
Parameter achieved																																																																																																																																																																																																																																																																																							Yes	Not assessed
Description parameter
Related indicator
Criteria status																																																																																																																																																																																																																																																																																							Good	Not assessed
Description criteria																																																																																																																																																																																																																																																																																							Taking into account criterion D2C1, the result is âESTA EN BEAâ. Environmental objectives related to Descriptor 2 have been reached in relation to the baseline assessment, however: monitoring should be strengthened with standardised sampling protocols and review of the list of non-native and non-native speakers.	This criterion could not be assessed due to a lack of data on the abundance and distribution of species, having analysed only the presence. The scale used in future marine strategies cycles for the assessment of this criterion shall be the same as used for the assessment of groups of species or major habitat types under Descriptors 1 and 6, which at the same time will contribute assessment of criterion D2C3 (adverse effects of non-indigenous species). Criterion D2C2 is it shall be expressed by species assessed.
Element status	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description element										The outcome of the element assessment D2C2 is Good when the species is established before 2012 but has not invasive potential. The outcome is Not good when the element assessed D2C1 is newly introduced and has invasive potential.
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved	GES achieved
Description overall status	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.	As regards the number of non-native species, a reduction of non-native species identified in the area of about 50Â % is detected in relation to the initial evaluation. Good environmental status in the area as a whole does not seem to be seriously threatened by the presence of non-native species.	As regards the number of non-native species, a reduction of non-native species identified in the area of about 50Â % is detected in relation to the initial evaluation. Good environmental status in the area as a whole does not seem to be seriously threatened by the presence of non-native species.	And, finally, the group of crustaceans. All groups reduce the number of species with a validated status. In view of the fact that the species register depends on their identification by experts, this order of abundance for taxa could be modified in the future to the extent that more identifications are validated by the taxonomy, in this sense ascites are an increasing group.
Assessments period	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018
Related pressures	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species			Input or spread of non-indigenous species
Related targets	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8	A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8			A.N.10 A.N.9 B.N.14 B.N.15 C.N.15 C.N.17 C.N.18 C.N.2 C.N.5 C.N.6 C.N.7 C.N.8

Demarcación marina sudatlántica (ABI-ES-SD-SUD)

Simplified table

GES component	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2	D2
Feature	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Established non-indigenous species	Newly-introduced non-indigenous species	Newly-introduced non-indigenous species	Established non-indigenous species
Element	Acartia (Acanthacartia) tonsa	Aetea anguina	Aetea ligulata	Aetea longicollis	Aetea sica	Aetea truncata	Aglaothamnion feldmanniae	Amphibalanus amphitrite	Amphibalanus improvisus	Anguillicoloides�crassus	Anotrichium furcellatum	Antithamnion densum	Antithamnion diminuatum	Antithamnionella spirographidis	Argyrosomus regius	Asparagopsis armata	Asparagopsis taxiformis	Beania mirabilis	Biddulphia sinensis	Bonamia�ostreae	Bonnemaisonia hamifera	Botrylloides leachii	Botryllus schlosseri	Bugula neritina	Bugulina avicularia	Bugulina fulva	Bugulina simplex	Bugulina stolonifera	Callinectes sapidus	Caprella scaura	Caulacanthus okamurae	Caulerpa racemosa	Cephalopholis nigri	Ceramium atrorubescens	Ceramium cingulatum	Chaetopleura angulata	Chorizopora brongniartii	Codium fragile	Colpomenia peregrina	Colpomenia sinuosa	Corbicula fluminea	Cordylophora caspia	Corynophlaea cystophorae	Crambe crambe	Cyclope neritea	Cystodytes dellachiajei	Diadumene lineata	Dicentrarchus labrax	Diplosoma listerianum	Dipteroshiphonia dendritica	Ecteinascidia turbinata	Electra pilosa	Elminius modestus	Eriocheir sinensis	Escharina vulgaris	Fenestrulina malusii	Ficopomatus enigmaticus	Filellum serratum	Fundulus heteroclitus	Gibbula albida	Gracilaria vermiculophylla	Grateloupia doryphora	Grateloupia imbricata	Grateloupia subpectinata	Grateloupia turuturu	Gymnodinium catenatum	Gymnophycus hapsiphorus	Haminoea callidegenita	Hemigrapsus penicillatus	Heterosiphonia japonica	Jellyella tuberculata	Karenia mikimotoi	Laurencia caduciramulosa	Lomentaria hakodatensis	Magallana gigas	Marteilia�refringens	Megabalanus tulipiformis	Membranipora tuberculata	Microporella ciliata	Monodactylus sebae	Mytilopsis leucophaeata	Neosiphonia harveyi	Oculina patagonica	Pachymeniopsis lanceolata	Palaemon macrodactylus	Paracaprella pusilla	Paracerceis sculpta	Paradella dianae	Perophora japonica	Petricolaria pholadiformis	Phaeocystis pouchetii	Phorcus�sauciatus	Polycera hedgpethi	Polycerella�emertoni	Pomacanthus maculosus	Potamopyrgus antipodarum	Predaea huismanii	Prognathodes marcellae	Puellina innominata	Reptadeonella violacea	Rhithropanopeus harrisii	Rhopalophthalmus mediterraneus	Ruditapes philippinarum	Sargassum muticum	Schizoporella errata	Schizoporella unicornis	Scinaia acuta	Scruparia ambigua	Scytosiphon dotyi	Sparus�aurata	Sphaerospora testicularis	Steromphala adansonii	Styela plicata	Stypopodium schimperi	Synidotea laticauda	Terebra corrugata	Tonicia atrata	Tricellaria inopinata	Ulva australis	Undaria pinnatifida	Watersipora cucullata	Womersleyella setacea	Xenostrobus securis	Not applicable
Element code	345943	111062	111064	111065	111066	111067	144494	421137	421139	458994	144505	144511	144512	144521	127007	144438	144439	111072	148969	246871	144442	250081	103862	111158	833990	834010	834016	834018	107379	236551	496188	144472	279151	371747	144539	848025	111304	145086	145856	145857	181580	117428	144948	133445	140487	250429	395099	126975	103579	144809	103756	111355	106209	107451	111520	111418	130988	117691	159306	141779	236157	145247	372191	370564	295880	109784	144591	181196	107454	232226	396730	233024	375452	232230	836033	395091	106226	183266	111421	278304	156887	233888	135210	496180	181372	211364	261827	261839	103758	156961	115106	689178	140835	140839	220005	147123	145645	126838	111330	111061	107414	120199	231750	494791	111527	111538	495386	111539	145868	151523	120481	1039842	103936	145391	257397	225102	386327	111254	660661	145721	111590	146371	140485	Not applicable
Element code source	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Species (D1) http://www.marinespecies.org/	Link to other vocabulary or code lists that may be relevant
Element 2
Element 2 code
Element 2 code source
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	Other
Criterion																																																																																																																													D2C1	D2C2
Parameter																																																																																																																													Presence	Abundance
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Threshold value source
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend																																																																																																																													Unknown	Unknown
Parameter achieved																																																																																																																													Unknown	Not assessed
Description parameter
Related indicator
Criteria status																																																																																																																													Unknown	Not assessed
Description criteria																																																																																																																													Could not be assessed due to the lack of updating of the database, not incorporation of new species and failure to verify the status of the detected. Good environmental State in the area as a whole does not seem to be seriously threatened by the presence of non-native species. It is recommended to follow up and put in place the measures of control to control and avoid negative impacts.	This criterion has not been assessed in this cycle. The scale used in future cycles of marine strategies for evaluation shall be the same as used for the assessment of groups. species or large habitat types under Descriptors 1 and 6 than at the same time contribute to the evaluation of criterion D2C3 (adverse effects of non-indigenous species). The criterion D2C2 shall be expressed per species assessed.
Element status	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed	Not assessed
Description element							The outcome of the element assessment D2C2 is Good when the species is established before 2012 but has not invasive potential. The outcome is Not good when the element assessed D2C1 is newly introduced and has invasive potential																																																																														T
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Description overall status	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.	In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.			In 2012, in summary it was concluded that neither the good environmental status of the whole area of the district, neither the survival of the different types of habitats included, appeared to be in serious danger. presence of invasive species. However, if significant negative impacts could be given at local level, and the high number of non-native species detected, and in particular the tens of them with invasive potential, advised to put in place as soon as possible to monitor the and in particular to carry out specific impact studies in order to be able to assess with knowledge of the potential risks. The same conclusion is maintained in 2018.
Assessments period	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018	2018
Related pressures	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Input or spread of non-indigenous species	Newly-introduced non-indigenous species	Newly-introduced non-indigenous species	Input or spread of non-indigenous species
Related targets	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8	A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8			A.S.10 A.S.9 B.S.14 B.S.15 C.S.15 C.S.17 C.S.18 C.S.2 C.S.5 C.S.6 C.S.7 C.S.8