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Fig. 6 in Seasonal dynamics of small-scale fisheries in the Adriatic Sea

Fig. 6: Composition of trammel net landings. CRO_rocky = Croatia rocky bottoms; CRO_soft = Croatia soft bottoms; ITA_18 = Italy GSA18; MONT = Montenegro; SLOV = Slovenia.

Fig. 5 in Seasonal dynamics of small-scale fisheries in the Adriatic Sea

Fig. 5: Composition of gillnet landings. CROA = Croatia; ITA_17 = Italy GSA17; ITA_18 = Italy GSA18; MONT = Montenegro; SLOV = Slovenia.

Fig. 8 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 8: Live scleractinians from Tricase (all from st. MEMA12-36). (A) Juvenile Desmophyllum dianthus (14) growing on subfossil Madrepora; bar = 1 cm; (B) Co-occurring live Lophelia pertusa (10), Madrepora oculata (7) and D. dianthus (14); bar = 1 cm.; (C) Dead Madrepora frame colonized by D. dianthus (14) and Poecillastra compressa (22); bar = 1 cm; (D) Live L. pertusa; bar = 5 cm.

Fig. 2 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 2: (A) Paramuricea macrospina (1) growing on muddy bottom at st. A65; bar =10 cm; (B-D) Gorgonians (P. macrospina: 1 and Callogorgia verticillata: 3) and sponges (Pachastrella monilifera: 2) co-occurring at st. A65 and ALTRO31; bar = 10 cm; (E) Large colony of C. verticillata (3); note the unidentified nudibranch (4, red circle) at st. ALTRO31; bar = 10 cm; (F) The yellow coral Dendrophyllia cornigera (5) at st. ALTRO31; note the sponge P. monilifera (2) growing on subfossil branches of D. cornigera and the Euphasiacean Stylocheiron sp. (6); bar = 5 cm; (G) Madrepora oculata (7) fouling a lost fishline at st. A67; bar = 10 cm; (H) A gorgonian garden at st. ALTRO31 characterized by many individuals of C. verticillata (3) growing over a hardground; bar = 25 cm.

Fig. 3 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 3: Montenegrin margin. (A) Hardground at st. ALTRO31 colonized by gorgonians Callogorgia verticillata (3) and Paramuricea macrospina (1); note the pencil sea urchin Cidaris cidaris (8), one of the most common vagile organisms observable at such depths; bar = 25 cm; (B) A large colony of the anthipatharian Leiopathes glaberrima (11) settled by the scleractinian Lophelia pertusa (10) at st. A63; observe Rochinia rissoana (9) in the coral frame and the abundant zooplankton in the surrounding water (i.e. Stylocheiron sp.: 6); bar = 10 cm; (C) The fish Phycis phycis (12) hidden under a hardground at st. A63; bar = 10 cm; (D) Close-up of L. pertusa (10) growing on L. glaberrima (11) at st. A63 surrounded by abundant zooplankton (i.e. the euphasiacean Stylocheiron sp.: 6), bar = 10 cm; (E) A remarkable cnidarian assemblage at st. ALTRO35 ca. -505 m water depth, formed by a large (up to 2 m) colony of L. glaberrima (11), the scleractinians Madrepora oculata (7) and L. pertusa (10) and Desmophyllum dianthus (14); inset shows the byssate bivalve Delectopecten vitreus (13) and Annelida (Serpula vermicularis: 15) attached to L. glaberrima (11). C. verticillata (3) is visible below on the right. Scale bar = 10 cm; (F) The "Gorgonian garden" at st. A65 formed by a dense aggregation of C. verticillata colonies (3). The red circle shows the gorgonian P. macrospina (1). Scale bar = 10 cm.

Fig. 6 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 6: Coral-sponge assemblages from the Bari Canyon. (A) Assemblage dominated by the white sponge Pachastrella monilifera (2) at st. A210; insets show an actiniarian belonging to the genus Peachia in the soft sediments (23); and the vagrant echinoid Echinus melo (24); bar = 25 cm; (B) The shrimp Plesionika martia (20) on Madrepora oculata (7) - Serpula vermicularis (15) bioconstruction at st. A210, undetermined fish belonging to the family Argentinidae (25); bar = 25 cm; (C) Madrepora-Pachastrella assemblage at st. A210; note the tiny seastar Peltaster placenta (27) hidden under the coral frame, and the encrusting yellow sponge Hexadella sp. (26); bar = 10 cm; (D) Canyon's flank at st. A210 showing the conspicuous presence of serpulids, mostly Bispira sp. (28) and the presence of the vagrant echinoid Cidaris cidaris (8); bar = 10 cm; (E) Benthos at st. A210 showing the encrusting sponge Hexadella sp. (26) and the cup-like sponge P. monilifera (2); also note the asteroid P. placenta (27); bar = 10 cm; (F) Scleractinian-sponge-serpulid cluster at st. A210, inset shows close-up of the sponges P. monilifera (2) and Poecillastra compressa (22); note the echinoid E. melo (24) and the scleractinian M. oculata (7); bar =10 cm; (G) The fish Phycis blennoides (29) and a fish related to family Argentinidae (25), foraging next to coral-sponge grounds at st. A210 (M. oculata 7; P. monilifera 2); bar = 10 cm; (H) Close-up of the orange cup-like sponge P. compressa (22) at st. A208, sheltering the decapod P. martia (20); note M. oculata (7) on the left side of the sponge; bar = 10 cm.

Fig. 5 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 5: Underwater photographs from the Bari Canyon. (A, B) Hardgrounds and boulders along the canyon's flank at st. A208 colonized by a cnidarian-sponge assemblage dominated by Madrepora oculata (7) and Pachastrella monilifera (2); note the occurrence of orange sponge (Poecillastra compressa: 22) and Cidaris cidaris (8) one of most common elements of the vagile bathyal benthos; bar = 25 cm; (C) Close-up of a cnidarian-sponge assemblage at st. A208 showing the coalescent growth of sponges and corals, and the subordinate presence of Serpula vermicularis (15); bar = 25 cm; (D) Intimately associated S. vermicularis (15) and M. oculata (7) established on a hardground crest at st. A210; bar =10 cm.

Fig. 1 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 1: Location of sites discussed in this study. Bathymetry from EMODnet (European Marine Observation and Data Network) Hydrography portal (resolution 500 m) (http://www. emodnet-hydrography.eu).

Fig. 7 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 7: Cnidarian habitats in the Bari Canyon: (A) Assemblage dominated by white massive sponges (Pachastrella monilifera: 2) and scleractinians (Madrepora oculata: 7) at st. A208; note Plesionika martia (20), one of the most recurrent decapods in such habitats; bar = 10 cm; (B) Hardground at st. A208, colonized by encrusting sponges (Hexadella sp.: 26) and serpulids (Parasabella sp.: 30); bar =10 cm; (C) Colony of the yellow coral Dendrophyllia cornigera (5) at st. A210, note the fish belonging to the family Myctophidae (31); bar = 10 cm; (D) Vermiliopsis sp. (32) and Serpula vermicularis (15) are the main constituents of the cnidarianserpulid assemblage at st. A208; Echinus melo (24) is probably grazing on a M. oculata (7) colony; bar = 10 cm; (E) M. oculata (7) - S. vermicularis (15) cluster at st. A210; bar =10 cm; (F) Canyon's flank at st. A210, inhabited by sponges (P. monilifera, 2; Hexadella sp., 26), cnidarians (M. oculata, 7) and serpulids (S. vermicularis, 15) plus vagile echinoids (Cidaris cidaris, 8); bar = 25 cm; (G, H) Scleractinian-sponge dominated habitats at st. A210, (M. oculata: 7, P. monilifera: 2, Hexadella sp.: 26), serving also as refuge for the decapods Munida tenuimana (18) and P. martia (20); the sea anemone Peachia sp. (23) inhabit surrounding soft substrata; bar = 10 cm.

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Fig. 3 in The nematode assemblage as a tool for the assessment of marine ecological quality status: a case-study in the Central Adriatic Sea

Fig. 3: Composition of colonizers-persisters (c-p) at each station and in each period. The c-p1 and c-p5 were excluded because they were not found in the study area.

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Fig. 2 in The nematode assemblage as a tool for the assessment of marine ecological quality status: a case-study in the Central Adriatic Sea

Fig. 2: a) Shannon Index; b) Pielou Index; c) Maturity Index; d) Index of Trophic Dominance calculated for the nematode assemblage at each station in the study area.

Fig. 4 in New deep-water cnidarian sites in the southern Adriatic Sea

Fig. 4: Non-sessile fauna associated with cnidarian assemblages in the Montenegrin margin. (A) Large Madrepora oculata bush (up to 1 m) (7), at st. ALTRO36, hosting the crab Bathynectes maravigna (16), inset shows Helicolenus dactylopterus (17); (B) Munida tenuimana (18) taking shelter under hardground at st. ALTRO31; (C) Paromola cuvieri (19) carrying the sponge Pachastrella monilifera on its back (2) (possibly an antipredatory strategy: Capezzuto et al., 2012); (D) The shrimp Plesionika martia (20) and the fish Hoplostethus mediterraneus (21) from st. ALTRO31.

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Figure 4 in Feeding habits of Scorpaena notata (Scorpaenidae) from eastern Adriatic Sea

Figure 4. – Diet composition of Scorpaena notata throughout the year, based on the %IRI values of the major prey groups.

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Figure 1 in Feeding habits of Scorpaena notata (Scorpaenidae) from eastern Adriatic Sea

Figure 1. – Study area and sampling sites of Scorpaena notata in the eastern Adriatic Sea. A: Kvarner Archipelago; B: Near Dugi Island; C: Near Šolta Island; D: Near Hvar Island. All sampling sites supported biocoenosis on coastal terrigenous sediments.

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Figure 5 in Feeding habits of Scorpaena notata (Scorpaenidae) from eastern Adriatic Sea

Figure 5. – Dendrogram for hierarchical clustering of the prey composition of Scorpaena notata according to sampling sites, using group-average linking of Bray-Curtis similarities calculated on standardized and double root-transformed data of prey abundance. A: Kvarner Archipelago (n = 177); B: Near Dugi Island (n = 220); C: Near Šolta Island (n = 190); D: Near Hvar Island (n = 211).

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Figure 1 in First record of the weatherfish Misgurnus fossilis (Linnaeus, 1758) from the Adriatic Sea catchment area in Bosnia and Herzegovina

Figure 1. Distribution map of Misgurnus fossilis in Danube catchment area according literature records (blue spots) and new field record (red spot) in Adriatic Sea catchment area (shaded area) in Bosnia and Herzegovina (a); small pond at locality Srednja Voda (b); field work (c, d); specimen of Misgurnus fossilis (e)

Fig. 3 in Spatial Distribution of Suspended Solids During Short-Term High River Discharge in the Bay of Koper, Northern Adriatic Sea

Fig. 3: Rižana and Badaševica river hourly (QR and QB) and daily mean (Qr and Qb) discharge with related inflow concentrations of ISS (ISS and ISS) (a). Density profile (b) and wind direction and velocity applied (average wind velocity of 1.5 m s-1 221°) during the r b high-discharge event 21st June 2013 (c) (ARSO, 2014a).

Fig. 8 in Spatial Distribution of Suspended Solids During Short-Term High River Discharge in the Bay of Koper, Northern Adriatic Sea

Fig. 8: Salinity and ISS profiles after 24-hour simulation at comparison sites (P1- right, P2-center and P3-left); the event on 21st June 2013.

Fig. 4 in Spatial Distribution of Suspended Solids During Short-Term High River Discharge in the Bay of Koper, Northern Adriatic Sea

Fig. 4: ISS distribution in the surface layer on 8th June 2011: measurements (a) and model simulation – average velocities and ISS distribution (b). Spatial map of discrepancies between model and measurements (c) and ranging of cells with regard to discrepancies (d); ΔMIN and ΔMAX depict minimum and maximum discrepancy, respectively.

Fig. 7 in Spatial Distribution of Suspended Solids During Short-Term High River Discharge in the Bay of Koper, Northern Adriatic Sea

Fig. 7: ISS distribution in the surface layer on 21st June 2013: measurements (a) and model simulation – average velocities and ISS distribution (b). Spatial map of discrepancies between model and measurements (c) and ranging of cells with regard to discrepancies (d); ΔMIN and ΔMAX depict minimum and maximum discrepancy, respectively.