Correction: Çil, E.A. Seasonal Dynamics of Macroinvertebrate Communities in Offshore Mussel Aquaculture in the Southern Black Sea: Implications for Diversity. Life 2025, 15, 1471

Figure/Table Legend

There is no error in the legend. However, in the original publication [1], the uncorrected versions of Figure 3 and Table 2 were inadvertently used instead of their corrected versions.

Figure 3. Monthly physicochemical parameter data.

Figure 3. Monthly physicochemical parameter data.

Table 2. Taxa identified in the study. (SUM: Total number of individuals. % D: Dominant taxa by relative abundance).

	September-2023	October	November	December	January	February	March	April	May	June	July	August-2024	SUM	% D
	S1	S2	S3	S4	S5	S6	S7	S8	S9	S10	S11	S12
Cnidaria
Diadumene sp.	0	3	0	0	0	0	0	0	13	45	14	3	78	0.0782
Nemertea
Lineus sp.	0	3	0	0	0	0	0	0	0	0	0	0	3	0.0030
Nematoda
Nematoda (sp.)	0	15	0	0	0	0	0	0	68	0	0	42	125	0.1254
Platyhelminthes
Cryptocelis sinopae Gammoudi, Bulnes and Kurt, 2021	0	0	0	0	0	0	0	0	11	5	3	0	19	0.0191
Polychaeta
Nereis zonata Malmgren, 1867	6	2	57	16	47	0	20	13	53	41	12	100	367	0.3680
Perinereis cultrifera (Grube, 1840)	0	0	0	0	0	0	0	0	0	0	0	3	3	0.0030
Platynereis dumerilii (Audouin and Milne Edwards, 1833)	0	5	0	0	0	0	0	0	0	0	0	0	5	0.0050
Polyophthalmus pictus (Dujardin, 1839)	0	0	0	0	0	0	0	0	6	0	0	1	7	0.0070
Sigambra tentaculata (Treadwell, 1941)	0	0	0	0	0	0	0	0	0	2	0	15	17	0.0170
Crustacea
Balanus improvisus (Darwin, 1854)	7	0	16	2	1	0	0	1	0	0	2	0	29	0.0291
Hyale crassipes (Heller, 1866)	0	0	0	0	10	30	2	0	30	0	10	20	102	0.1023
Jassa marmorata Holmes, 1905	5.800	13.250	8.160	5.530	2.100	4.000	6.000	10.000	6.600	2.500	2.024	5.200	71.164	71.3645
Pachygrapsus marmoratus (Fabricius, 1787)	6	0	2	0	0	0	4	0	0	0	0	0	12	0.0120
Palaemon longirostris H. Milne Edwards, 1837	0	0	0	0	0	0	0	0	0	4	0	0	4	0.0040
Pectenogammarus olivii (H. Milne Edwards, 1830)	0	0	0	0	0	4	0	0	4	0	0	5	13	0.0130
Pilumnus hirtellus (Linnaeus, 1761)	0	0	9	0	0	4	2	0	0	7	0	0	22	0.0221
Pisidia longicornis (Linnaeus, 1767)	0	0	4	0	4	5	1	0	0	1	0	1	16	0.0160
Stenothoe monoculoides (Montagu, 1813)	1.900	5.000	5.290	1.040	500	2.000	2.000	2.000	4.520	1.000	1.006	1470	27.726	27.8041
Mollusca
Rapana venosa (Valenciennes, 1846)	0	0	2	0	0	0	1	0	0	0	0	0	3	0.0030
Striarca lactea (Linnaeus, 1758)	0	0	2	0	2	0	0	0	0	0	0	0	4	0.0040

Table 2. Taxa identified in the study. (SUM: Total number of individuals. % D: Dominant taxa by relative abundance).

	September-2023	October	November	December	January	February	March	April	May	June	July	August-2024	SUM	% D
	S1	S2	S3	S4	S5	S6	S7	S8	S9	S10	S11	S12
Cnidaria
Diadumene sp.	0	3	0	0	0	0	0	0	13	45	14	3	78	0.0782
Nemertea
Lineus sp.	0	3	0	0	0	0	0	0	0	0	0	0	3	0.0030
Nematoda
Nematoda (sp.)	0	15	0	0	0	0	0	0	68	0	0	42	125	0.1254
Platyhelminthes
Cryptocelis sinopae Gammoudi, Bulnes and Kurt, 2021	0	0	0	0	0	0	0	0	11	5	3	0	19	0.0191
Polychaeta
Nereis zonata Malmgren, 1867	6	2	57	16	47	0	20	13	53	41	12	100	367	0.3680
Perinereis cultrifera (Grube, 1840)	0	0	0	0	0	0	0	0	0	0	0	3	3	0.0030
Platynereis dumerilii (Audouin and Milne Edwards, 1833)	0	5	0	0	0	0	0	0	0	0	0	0	5	0.0050
Polyophthalmus pictus (Dujardin, 1839)	0	0	0	0	0	0	0	0	6	0	0	1	7	0.0070
Sigambra tentaculata (Treadwell, 1941)	0	0	0	0	0	0	0	0	0	2	0	15	17	0.0170
Crustacea
Balanus improvisus (Darwin, 1854)	7	0	16	2	1	0	0	1	0	0	2	0	29	0.0291
Hyale crassipes (Heller, 1866)	0	0	0	0	10	30	2	0	30	0	10	20	102	0.1023
Jassa marmorata Holmes, 1905	5.800	13.250	8.160	5.530	2.100	4.000	6.000	10.000	6.600	2.500	2.024	5.200	71.164	71.3645
Pachygrapsus marmoratus (Fabricius, 1787)	6	0	2	0	0	0	4	0	0	0	0	0	12	0.0120
Palaemon longirostris H. Milne Edwards, 1837	0	0	0	0	0	0	0	0	0	4	0	0	4	0.0040
Pectenogammarus olivii (H. Milne Edwards, 1830)	0	0	0	0	0	4	0	0	4	0	0	5	13	0.0130
Pilumnus hirtellus (Linnaeus, 1761)	0	0	9	0	0	4	2	0	0	7	0	0	22	0.0221
Pisidia longicornis (Linnaeus, 1767)	0	0	4	0	4	5	1	0	0	1	0	1	16	0.0160
Stenothoe monoculoides (Montagu, 1813)	1.900	5.000	5.290	1.040	500	2.000	2.000	2.000	4.520	1.000	1.006	1470	27.726	27.8041
Mollusca
Rapana venosa (Valenciennes, 1846)	0	0	2	0	0	0	1	0	0	0	0	0	3	0.0030
Striarca lactea (Linnaeus, 1758)	0	0	2	0	2	0	0	0	0	0	0	0	4	0.0040

Error in Figure 3

In Figure 3, the term “Dissolved Oxygen (g/kg)” was incorrectly used; in the corrected version it has been replaced with “Dissolved Oxygen (mg/L)”. The same correction (g/kg → mg/L) has also been made in the main text on Section 3.1 paragraph 5.

Error in Table 2

In Table 2, the order of the taxa had been modified according to the first reviewer’s recommendation; however, the incorrect (uncorrected) version of the table was mistakenly uploaded. It has now been replaced with the corrected version. Only the taxonomic order has been changed—the content and data remain the same.

Missing Citation

Only the reference list was corrected. Some citation errors and misspellings remained unedited prior to the reviewer suggestions, and these have now been carefully revised. No new citations were added.

Text Correction

The corrections made were on Section 3.1 paragraph 5 and Section 3.3 paragraph 5, 7, 8 and 9, where the expression “Dissolved Oxygen (g/kg)” was replaced with “mg/L” and the “Figure 5” should be “Figure 6” which was incorrectly numbered. The original “Figure 6” should be corrected as “Figure 7” and original “Figure 7” corrected as “Figure 6” because the figures need to appear after the first citation.

Dissolved Oxygen (DO): Dissolved oxygen levels peaked in February at 10.35 mg/L and reached their lowest level in July at 5.30 mg/L. This pattern corresponds to the reduced solubility of oxygen at higher temperatures and increased biological oxygen demand during the warmer months.

A pronounced increase in both taxon richness and individual abundance was observed during summer and early autumn (June–September). This seasonal peak coincides with periods of higher temperatures and reduced hydrodynamic impact, indicating enhanced macrofaunal productivity. The consistent dominance of J. marmorata during these months reflects the taxon’s rapid colonization ability and competitive advantage on artificial structures. In contrast, the lower and more stable abundances recorded in winter and spring are consistent with suppressed benthic activity under low temperatures and elevated oxygen conditions (Figure 6).

Figure 6 has been moved to after its first mention.

While the dominant amphipods J. marmorata and S. monoculoides largely shaped the overall temporal trends, several low-abundance taxa such as Balanus improvisus, C. sinopae, H. crassipes, and N. zonata contributed to short-term peaks in richness during specific sampling periods (e.g., S4, S9) (Table 2). Although these episodic fluctuations had minimal influence on total abundance, they underscore the ecological variability of the community and the occurrence of sporadic settlement events (Figure 7).

The RDA biplot illustrated the relationships between taxa and environmental variables (pH, dissolved oxygen, temperature, and salinity) (Figure 6). These findings are of considerable importance for understanding the influence of environmental variables on taxon distribution and habitat preferences.

The results of RDA indicated that pH and temperature were the most influential physicochemical factors shaping taxa distribution. pH showed a strong relationship to sensitive taxa such as H. crassipes, D. leucolena, and C. sinopae, suggesting that even small fluctuations in alkalinity may regulate their settlement and persistence. In contrast, the dominant amphipods J. marmorata and S. monoculoides were primarily aligned with temperature along the first axis, reflecting their seasonal proliferation during warmer months. The opportunistic polychaete N. zonata was more closely associated with oxygen, showing higher abundances during winter. Rare or episodic taxa (Rapana venosa, Platynereis dumerilii, Striarca lactea) exhibited no strong correlation with environmental gradients, instead reflecting sporadic recruitment events. Overall, the results demonstrate a clear seasonal structuring of the community, with pH influencing sensitive taxa, temperature driving dominant taxa, and oxygen regulating opportunistic taxa (Figure 6). This pattern indicates that community structure beneath mussel aquaculture is strongly influenced by seasonal hydrographic variations.

References

Author revised some of the references, they are listed as follows:

4.

Aral, O. Growth of the Mediterranean mussel (Mytilus galloprovincialis lam., 1819) on ropers in the Black Sea, Turkey. Turk. J. Vet. Anim. Sci. 1999, 23, 183–190.

5.

Ivanov, V.N.; Bulatov, K.V. Population genetic investigations of Black Sea Mytilus galloprovincialis Lam. Hydrores 1990, 7, 106–111.

6.

Aydemir-Çil, E.; Birinci-Özdemir, Z.; Özdemir, S. First find of the starfish, Asterias rubens Linnaeus, 1758, off the Anatolian coast of the Black Sea (Sinop). Mar. Biol. J. 2023, 8, 97–101. https://doi.org/10.21072/mbj.2023.08.3.07.

26.

Acarlı, S.; Vural, P.; Yıldız, H. An and suitability for human consumption of Mediterranean mussels (Mytilus galloprovincialis Lamarck, 1819) from the Yalova coast of the Marmara Sea. Memba Kastamonu Üniv. Su Ürünleri Fak. Derg. 2023, 9, 12–24.

27.

Turan, H.; Sönmez, G.; Çelik, M.Y.; Yalçın, M.; Kaya, Y. Effects of different salting process on the storage quality of Mediterranean mussel (Mytilus galloprovincialis L. 1819). J. Muscle Foods 2007, 18, 380–390. https://doi.org/10.1111/j.1745-4573.2007.00093.x.

28.

Mititelu, M.; Neacșu, S.M.; Oprea, E.; Dumitrescu, D.E.; Nedelescu, M.; Drăgănescu, D.; Nicolescu, T.O.; Roșca, A.C.; Ghica, M. Black Sea mussels qualitative and quantitative chemical analysis: Nutritional benefits and possible risks through consumption. Nutrients 2022, 14, 964. https://doi.org/10.3390/nu14050964.

29.

Çınar, M.E.; Açık, Ş.; Kurt, G.; Erdoğan Dereli, D. Diversity of Annelida from the coasts of Türkiye. Turk. J. Zool. 2024, 48, 413–445. https://doi.org/10.55730/1300-0179.3193.

31.

Fauchald, K. The Polychaete Worms. Definitions and Keys to the Orders, Families and Genera. In Natural History Museum of Los Angeles County Science Series; Natural History Museum of Los Angeles County: Los Angeles, CA, USA, 1977; Volume 28, pp. 1–188.

32.

Hutchings, P.; Murray, A. Taxonomy of Polychaetes from the Hawkesbury River and the Southern Estuaries of New South Wales, Australia (Vol. 3); Australian Museum: Sydney, Australia, 1984; Volume 3, pp. 1–118. https://doi.org/10.3853/j.0812-7387.3.1984.101.

44.

Anistratenko, V.V.; Anistratenko, O.Y. Fauna Ukraine: In 40 vol. Vol. 29: Mollusca. Fasc. 1. B. 1: Class Polyplacophora or Chitons, Class Gastropoda—Cyclobranchia, Scutibranchia and Pectinibranchia (part). Kiev Veles. 2001, 1–240.

50.

Brander, K.; Cochrane, K.; Barange, M.; Soto, D. Climate change implications for fisheries and aquaculture. Clim. Change Impacts Fish. Aquac. A Glob. Anal. 2017, 1, 45–62. https://doi.org/10.1002/9781119154051.ch3.

53.

Aslan, H.; İşmen, P. Peracarid crusteceans species from upper infralittoral rocky shores of Gokceada Island (Aegean Sea). Çanakkale Onsekiz Mart Univ. J. Mar. Sci. Fish. 2019, 2, 109–119.

55.

Filgueira, R.; Grant, J.; Petersen, J.K. Identifying the optimal depth for mussel suspended culture in shallow and turbid environments. J. Sea Res. 2018, 132, 15–23. https://doi.org/10.1016/j.seares.2017.11.006.

56.

Roman, M.R.; Altieri, A.H.; Breitburg, D.; Ferrer, E.M.; Gallo, N.D.; Ito, S.I.; Limburg, K.; Rose, K.; Yasuhara, M.; Levin, L.A. Reviews and syntheses: Biological indicators of low-oxygen stress in marine water-breathing animals. Biogeosciences 2024, 21, 4975–5004. https://doi.org/10.5194/egusphere-2024-616.

61.

Govorin, I.A. The predatory marine gastropod Rapana venosa (Valenciennes, 1846) in Northwestern Black Sea: Morphometric variations, imposex appearance and biphallia phenomenon. In Molluscs; IntechOpen: London, UK, 2019; pp. 31–45. https://doi.org/10.5772/intechopen.81209.

64.

Karayücel, S.; Çelik, M.Y.; Karayücel, İ.; Erik, G. Growth and production of raft cultivated Mediterranean mussel (Mytilus galloprovincialis Lamarck, 1819) in Sinop, Black Sea. Turk. J. Fish. Aquat. Sci. 2010, 10. https://doi.org/10.4194/trjfas.2010.0102.

The authors state that the scientific conclusions are unaffected. This correction was approved by the Academic Editor. The original publication has also been updated.