
Figure 1
Study area and sampling stations
Table 1
Abundance and seasonal variations of ichthyoplankton species in different embryonic development stages in the Dardanelles between March 2012 and February 2013
| SPECIES | SEASON | |||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| SPRING | SUMMER | AUTUMN | WINTER | |||||||||
| EGG | PR | PL | EGG | PR | PL | EGG | PR | PL | EGG | PR | PL | |
| Arnoglossus laterna | 100 | 5 | 5 | 20 | 0 | 0 | 10 | 0 | 0 | 51 | 0 | 0 |
| Blennius ocellatus | 0 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Boops boops | 110 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 780 | 0 | 0 |
| Buglossidium luteum | 10 | 0 | 0 | 40 | 0 | 0 | 0 | 0 | 0 | 20 | 0 | 0 |
| Callionymus lyra | 20 | 0 | 30 | 0 | 0 | 10 | 0 | 0 | 0 | 20 | 0 | 0 |
| Centrolophus niger* | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1* |
| Coris julis | 1510 | 0 | 0 | 20 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 |
| Ctenolabrus rupestris | 0 | 0 | 0 | 30 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 10 |
| Dicenthrarchus labrax | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 10 |
| Diplodus annularis | 4200 | 0 | 10 | 30 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 |
| Diplodus sargus | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 0 |
| Engraulis encrasicholus | 30 | 30 | 20 | 80 | 40 | 294 | 0 | 0 | 10 | 0 | 0 | 0 |
| Eutrigla gurnardus* | 0 | 0 | 0 | 0 | 0 | 1* | 0 | 0 | 0 | 0 | 0 | 0 |
| Gaidropsarus mediterraneus | 130 | 0 | 0 | 0 | 0 | 0 | 110 | 0 | 0 | 820 | 0 | 0 |
| Gobius niger | 0 | 0 | 30 | 0 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 10 |
| Helicolenus dactylopterus | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 0 |
| Hippocampus hippocampus | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 |
| Liza saliens | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Merlangius merlangus | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1210 | 0 | 0 |
| Merluccius merluccius | 0 | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 0 | 220 | 0 | 0 |
| Microchirus variegatus | 40 | 0 | 0 | 20 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Micromesistius poutassou | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 120 | 0 | 0 |
| Mugil cephalus | 0 | 0 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Mullus barbatus barbatus | 5640 | 0 | 0 | 162 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Mullus surmuletus | 1020 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Naucrates ductor | 58 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 100 | 0 | 0 |
| Pegusa lascaris | 0 | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 0 | 10 | 0 | 0 |
| Pomatoschistus minutus | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 0 | 0 | 0 |
| Sarda sarda* | 0 | 0 | 0 | 2* | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Sardina pilchardus | 200 | 26 | 94 | 0 | 0 | 0 | 1782 | 0 | 0 | 3320 | 29 | 12 |
| Scomber japonicus | 40 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Scomber scombrus | 40 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 100 | 0 | 0 |
| Scorpaena porcus | 10 | 0 | 0 | 50 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 |
| Serranus cabrilla | 841 | 12 | 41 | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Serranus hepatus | 150 | 0 | 0 | 20 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Serranus scriba | 10 | 0 | 0 | 20 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Solea solea | 20 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Sparus aurata | 30 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Spicara maena* | 0 | 0 | 0 | 0 | 0 | 0 | 2* | 0 | 0 | 0 | 0 | 0 |
| Sprattus sprattus | 10 | 0 | 0 | 0 | 0 | 0 | 10 | 0 | 10 | 22741 | 255 | 90 |
| Symphodus ocellatus | 40 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Symphodus rostratus | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Symphodus tinca | 0 | 0 | 0 | 10 | 0 | 20 | 0 | 0 | 0 | 190 | 0 | 0 |
| Trachinus draco | 10 | 0 | 10 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Trachurus trachurus | 50 | 0 | 10 | 130 | 0 | 11 | 0 | 0 | 0 | 0 | 0 | 0 |
| Trigla lucerna | 30 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 180 | 0 | 0 |
| Lepidotrigla cavillone* | 1* | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Uronoscopus scaber | 60 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Total Abundance | 14438 | 73 | 270 | 650 | 40 | 384 | 1930 | 10 | 20 | 29902 | 284 | 131 |
The calculated densities were considered to represent the minimum ichthyoplankton density per 1000 m3 from horizontal tows.
* Refers to species that were sampled only by vertical tows and the density unit of these species reflects number of individuals. PR refers to prelarvae and PL refers to postlarvae.
* Refers to species that were sampled only by vertical tows and the density unit of these species reflects number of individuals. PR refers to prelarvae and PL refers to postlarvae.
* Refers to species that were sampled only by vertical tows and the density unit of these species reflects number of individuals. PR refers to prelarvae and PL refers to postlarvae.
* Refers to species that were sampled only by vertical tows and the density unit of these species reflects number of individuals. PR refers to prelarvae and PL refers to postlarvae.
* Refers to species that were sampled only by vertical tows and the density unit of these species reflects number of individuals. PR refers to prelarvae and PL refers to postlarvae.

Figure 2
(A) fish egg density, (B) larval fish density, (C) Shannon-Wiener Index H for fish eggs, (D) Shannon-Wiener Index H for larval fish assemblages between March 2012 and February 2013. Egg and larval fish abundance are standardized by volume of water filtered (number of eggs or larvae per 1000 m3).
Table 2
Temporal variation in the abundance, species richness and values of some biodiversity indices for fish eggs and larvae
| Numeric data | Stage | March | April | May | June | July | April | September | October | November | December | January 13 | February 13 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Individuals | Egg | 4234 | 97 | 1108 | 1912 | 60 | 47 | 39 | 13 | 284 | 35 | 368 | 233 |
| Larvae | 57 | 19 | 17 | 44 | 14 | 69 | 27 | 5 | 2 | 2 | 9 | 6 | |
| Species richness | Egg | 13 | 16 | 15 | 23 | 10 | 16 | 8 | 3 | 4 | 5 | 7 | 9 |
| Larvae | 4 | 5 | 4 | 11 | 3 | 7 | 6 | 3 | 2 | 2 | 1 | 2 | |
| Abundance (ind. 1000 m−3) | Egg | 26420 | 740 | 3440 | 10380 | 250 | 160 | 220 | 70 | 1700 | 200 | 2100 | 1290 |
| Larvae | 360 | 130 | 80 | 210 | 70 | 240 | 90 | 20 | 0 | 10 | 30 | 20 | |
| Dominance (D) | Egg | 0.6526 | 0.1553 | 0.3718 | 0.2222 | 0.2294 | 0.1019 | 0.3149 | 0.7278 | 0.8736 | 0.569 | 0.4672 | 0.6483 |
| Larvae | 0.7248 | 0.4404 | 0.3841 | 0.1477 | 0.7449 | 0.7845 | 0.6159 | 0.44 | 0.5 | 0.5 | 1 | 0.7222 | |
| Shannon-Wiener Index (H) | Egg | 0.8537 | 2.198 | 1.439 | 1.81 | 1.816 | 2.498 | 1.453 | 0.536 | 0.2897 | 0.9221 | 1.01 | 0.7782 |
| Larvae | 0.5441 | 1.129 | 1.115 | 2.107 | 0.5091 | 0.5521 | 0.8765 | 0.9503 | 0.6931 | 0.6931 | 0 | 0.4506 | |
| Pielou’s evenness component (J’) | Egg | 0.3328 | 0.7926 | 0.5314 | 0.5772 | 0.7885 | 0.9011 | 0.6989 | 0.4879 | 0.209 | 0.5729 | 0.5189 | 0.3542 |
| Larvae | 0.3925 | 0.7012 | 0.8044 | 0.8787 | 0.4634 | 0.2837 | 0.4892 | 0.865 | 1 | 1 | 0 | 0.65 |