| Literature DB >> 35049862 |
Kyriakos C Prousis1, Stefanos Kikionis2, Efstathia Ioannou2, Silvia Morgana3, Marco Faimali3, Veronica Piazza3, Theodora Calogeropoulou1, Vassilios Roussis2.
Abstract
Marine biofouling is an epibiotic biological process that affects almost any kind of submerged surface, causing globally significant economic problems mainly for the shipping industry and aquaculture companies, and its prevention so far has been associated with adverse environmental effects for non-target organisms. Previously, we have identified bromosphaerol (1), a brominated diterpene isolated from the red alga Sphaerococcus coronopifolius, as a promising agent with significant antifouling activity, exerting strong anti-settlement activity against larvae of Amphibalanus (Balanus) amphitrite and very low toxicity. The significant antifouling activity and low toxicity of bromosphaerol (1) motivated us to explore its chemistry, aiming to optimize its antifouling potential through the preparation of a number of analogs. Following different synthetic routes, we successfully synthesized 15 structural analogs (2-16) of bromosphaerol (1), decorated with different functional groups. The anti-settlement activity (EC50) and the degree of toxicity (LC50) of the bromosphaerol derivatives were evaluated using cyprids and nauplii of the cirriped crustacean A. amphitrite as a model organism. Derivatives 2, 4, and 6-16 showed diverse levels of antifouling activity. Among them, compounds 9 and 13 can be considered as well-performing antifoulants, exerting their activity through a non-toxic mechanism.Entities:
Keywords: Amphibalanus amphitrite; Sphaerococcus coronopifolius; antifouling activity; bromosphaerol; synthetic analogs
Mesh:
Substances:
Year: 2021 PMID: 35049862 PMCID: PMC8781426 DOI: 10.3390/md20010007
Source DB: PubMed Journal: Mar Drugs ISSN: 1660-3397 Impact factor: 5.118
Figure 1Bromosphaerol (1) and its synthetic derivatives 2–16.
Figure 2Synthesis of bromosphaerol derivatives 2–8.
Figure 3Synthesis of bromosphaerol derivatives 9 and 10.
Figure 4Synthesis of bromosphaerol derivatives 11–16.
EC50, LC50(cypris), and LC50(nauplii) values (in mg/L, with 95% confidence limits in parentheses) for cypris larvae settlement inhibition, cypris larvae mortality, and naupliar mortality of Amphibalanus amphitrite after exposure for 72, 72, and 48 h, respectively, to bromosphaerol derivatives 2, 4, and 6–16, as well as therapeutic ratios for bromosphaerol derivatives 2, 4, and 6–16 calculated against both LC50(nauplii) values from naupliar toxicity test (TRN) and LC50(cypris) values from cyprids toxicity assay (TRC).
| Compounds | EC50 (72 h) | LC50(cypris) (72 h) | LC50(nauplii) (48 h) | TRN
| TRC
|
|---|---|---|---|---|---|
|
| 0.23 (0.17–0.30) | >100 | 3.63 (3.05–4.33) | 15.78 | 434.78 |
|
| 10.44 † | 25.2 † | 2.75 (2.47–3.07) | 0.26 | 2.39 |
|
| 7.19 (4.57–11.3) | >50 | 1.27 † | 0.17 | 6.95 |
|
| 7.53 (5.82–9.73) | 10.2 † | 7.57 (6.10–9.38) | 1.00 | 1.32 |
|
| 8.75 (6.75–11.34) | >50 | 11.53 (9.53–13.95) | 1.31 | >5.71 |
|
| >50 | >50 | >50 | n.d. ‡ | n.d. ‡ |
|
| <0.5 | >50 | 1.19 † | 2.38 | >100 |
|
| 3.87 † | >50 | 2.31 † | 0.59 | 12.90 |
|
| >50 | >50 | 21.64 (16.57–28.28) | n.d. ‡ | n.d. ‡ |
|
| >50 | >50 | 1.21 † | n.d. ‡ | n.d. ‡ |
|
| <0.5 | >50 | 1.26 † | 2.52 | >100 |
|
| >50 | >50 | >50 | n.d. ‡ | n.d. ‡ |
|
| <0.5 | 12.5 † | 1.81 † | 3.62 | 25.00 |
|
| <0.5 | 2.7 † | 1.36 † | 2.72 | 5.40 |
† Confidence limits could not be defined. ‡ TR values were not calculated for derivatives with high EC50 values (not considered promising as antifoulants).