| Literature DB >> 28744261 |
Rafael M Gandra1,2,3, Pauraic Mc Carron3,4, Mariana F Fernandes1, Lívia S Ramos1, Thaís P Mello1, Ana Carolina Aor1, Marta H Branquinha1, Malachy McCann4, Michael Devereux3, André L S Santos1,2.
Abstract
Candida haemulonii, Candida haemulonii var. vulnera and Candida duobushaemulonii, which form the C. haemulonii complex, are emerging etiologic agents of fungal infections known to be resistant to the most commonly used antifungals. The well-established anti-Candida potential of metal complexes containing 1,10-phenanthroline (phen) ligands encouraged us to evaluate different copper(II), manganese(II), and silver(I) phen chelates for their ability to inhibit planktonic growth and biofilm of C. haemulonii species complex. Two novel coordination complexes, {[Cu(3,6,9-tdda)(phen)2].3H2O.EtOH}n and [Ag2(3,6,9-tdda)(phen)4].EtOH (3,6,9-tddaH2 = 3,6,9-trioxaundecanedioic acid), were synthesized in a similar fashion to the other, previously documented, sixteen copper(II), manganese(II), and silver(I) chelates employed herein. Three isolates of each C. haemulonii species complex were used and the effect of the metal chelates on viability was determined utilizing the CLSI standard protocol and on biofilm-growing cells using the XTT assay. Cytotoxicity of the chelates was evaluated by the MTT assay, employing lung epithelial cells. The majority of the metal chelates were capable of interfering with the viability of planktonic-growing cells of all the fungal isolates. The silver complexes were the most effective drugs (overall geometric mean of the minimum inhibitory concentration (GM-MIC) ranged from 0.26 to 2.16 μM), followed by the manganese (overall GM-MIC ranged from 0.87 to 10.71 μM) and copper (overall GM-MIC ranged from 3.37 to >72 μM) chelates. The manganese chelates (CC50 values ranged from 234.51 to >512 μM) were the least toxic to the mammalian cells, followed by the silver (CC50 values ranged from 2.07 to 13.63 μM) and copper (CC50 values ranged from 0.53 to 3.86 μM) compounds. When tested against mature biofilms, the chelates were less active, with MICs ranging from 2- to 33-fold higher levels when compared to the planktonic MIC counterparts. Importantly, manganese(II), copper(II), and silver(I) phen chelates are relatively cheap and easy to synthesize and they offer significant antifungal chemotherapeutic potential for the treatment of highly resistant pathogens.Entities:
Keywords: 1,10-phenanthroline; Candida haemulonii complex; anti-virulence; antifungal activity; biofilm; metal-based drugs
Year: 2017 PMID: 28744261 PMCID: PMC5504357 DOI: 10.3389/fmicb.2017.01257
Source DB: PubMed Journal: Front Microbiol ISSN: 1664-302X Impact factor: 5.640
Figure 1Structures of the copper(II) (1-7), manganese(II) (8-14), and silver(I) (15-18) chelates.
Effect of test compounds on planktonic growth of the clinical isolates belonging to the C. haemulonii complex.
| 0.5 | 0.25 | 0.125 | 0.25 | 0.25 | 0.25 | 0.5 | 0.315 | 0.125 | 0.25 | 0.125 | 0.157 | 0.23 (0.18 μM) | |
| 1 | 1 | 1 | 1 | 1 | 1 | 0.5 | 0.79 | 1 | 1 | 1 | 1 | 0.93 (5.16 μM) | |
| 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 4 | 2 | 2.52 | 2.16 (10.27 μM) | |
| >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 (>23 μM) | |
| >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 (>28 μM) | |
| 1 | 0.5 | 1 | 0.79 | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 | 0.5 | 1 | 0.63 | 0.63 (3.93 μM) | |
| [Cu(ph)(phen)(H2O)2] ( | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 (>72 μM) |
| [Cu(ph)(phen)2].3H2O.2EtOH ( | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 | >32 (>43.52 μM) |
| [Cu(isoph)(phen)2].6H2O.EtOH ( | 8 | 8 | 16 | 10.08 | 4 | 8 | 8 | 6.35 | 4 | 8 | 4 | 5.04 | 6.86 (9.21 μM) |
| [{Cu(phen)2}2(terph)](terph).13.5H2O.2EtOH ( | >32 | >32 | >32 | >32 | 32 | 32 | 32 | 32 | >32 | >32 | >32 | >32 | >32 (>21.92 μM) |
| [Cu2(oda)(phen)4](ClO4)2.2.76H2O.EtOH ( | 8 | 8 | 16 | 10.08 | 8 | 16 | 8 | 10.08 | 8 | 8 | 8 | 8 | 9.33 (7.09 μM) |
| [Cu(phendione)3](ClO4)2.4H2O ( | 16 | 16 | 16 | 16 | 4 | 8 | 8 | 6.35 | 8 | 16 | 4 | 8 | 9.33 (9.65 μM) |
| {[Cu(3,6,9-tdda)(phen)2].3H2O.EtOH} | 4 | 4 | 2 | 3.17 | 2 | 2 | 4 | 2.52 | 2 | 2 | 2 | 2 | 2.52 (3.37 μM) |
| [Mn(ph)(phen)(H2O)2] ( | 8 | 4 | 4 | 5.04 | 4 | 4 | 4 | 4 | 8 | 4 | 4 | 5.04 | 4.67 (10.71 μM) |
| [Mn(ph)(phen)2(H2O)].4H2O ( | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 (2.98 μM) |
| [Mn2(isoph)2(phen)3].4H2O ( | 8 | 8 | 4 | 6.35 | 4 | 4 | 4 | 4 | 8 | 8 | 4 | 6.35 | 5.44 (5.15 μM) |
| {[Mn(phen)2(H2O)2]}2(isoph)2(phen).12H2O ( | 4 | 2 | 2 | 2.52 | 4 | 2 | 2 | 2.52 | 2 | 4 | 2 | 2.52 | 2.52 (1.54 μM) |
| [Mn(tereph)(phen)2].5H2O ( | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 | 4 (5.96 μM) |
| [Mn2(oda)(phen)4(H2O)2][Mn2(oda)(phen)4(oda)2]4H2O ( | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 4 | 2 | 2.52 | 2.16 (0.87 μM) |
| {[Mn(3,6,9-tdda)(phen)2].3H2O.EtOH} | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 2 | 4 | 4 | 2 | 3.17 | 2.33 (3.15 μM) |
| [Ag(phendione)2]ClO4( | 1 | 1 | 1 | 1 | 2 | 1 | 1 | 1.26 | 2 | 2 | 2 | 2 | 1.36 (2.16 μM) |
| [Ag2(3,6,9-tdda)(phen)4].EtOH ( | 1 | 1 | 1 | 1 | 1 | 0.5 | 1 | 0.79 | 2 | 1 | 1 | 1.26 | 1 (0.83 μM) |
| [Ag(phen)2]ClO4 ( | 1 | 1 | 1 | 1 | 1 | 0.5 | 0.5 | 0.63 | 2 | 1 | 2 | 1.59 | 1 (1.76 μM) |
| [Ag2(phen)3(udda)].3H2O ( | 0.125 | 0.25 | 0.125 | 0.16 | 0.5 | 0.125 | 0.25 | 0.25 | 0.5 | 0.25 | 1 | 0.5 | 0.27 (0.26 μM) |
All the MIC values are shown as mg/L. GM-MIC—Geometric mean of the compound MIC values (mg/L) for each species of Candida haemulonii complex. The last column presents the overall MIC geometric mean values for each of the test compounds across all nine strains of the C. haemulonii complex. The MIC values (μM) between copper(II), manganese(II) and silver(I) chelates were statistically significant (P = 0.038, one-way ANOVA).
Statistical analysis using one-way ANOVA evidenced that the MIC values of this compound among the three species were significant (compound .
Cytotoxicity and selectivity index values of the test compounds.
| 4.30 | 4.30 | 5.42 | 4.30 | 4.67 | |
| 2.02 | 1.01 | 1.01 | 0.80 | 0.94 | |
| 123.68 | >3.87 | >3.87 | >3.87 | >3.87 | |
| 133.76 | >4.18 | >4.18 | >4.18 | >4.18 | |
| 16.98 | 21.39 | 33.96 | 26.95 | 27.43 | |
| [Cu(ph)(phen)(H2O)2] ( | 0.53 | <0.02 | <0.02 | <0.02 | <0.02 |
| [Cu(ph)(phen)2].3H2O.2EtOH ( | 1.93 | <0.06 | <0.06 | <0.06 | <0.06 |
| [Cu(isoph)(phen)2].6H2O.EtOH ( | 0.89 | 0.09 | 0.14 | 0.18 | 0.14 |
| [{Cu(phen)2}2(terph)](terph).13.5H2O.2EtOH ( | 3.86 | <0.12 | 0.12 | <0.12 | ND |
| [Cu2(oda)(phen)4](ClO4)2.2.76H2O.EtOH ( | 0.98 | 0.10 | 0.10 | 0.12 | 0.11 |
| [Cu(phendione)3](ClO4)2.4H2O ( | 0.68 | 0.04 | 0.11 | 0.09 | 0.08 |
| {[Cu(3,6,9-tdda)(phen)2].3H2O.EtOH} | 1.06 | 0.33 | 0.42 | 0.53 | 0.43 |
| [Mn(ph)(phen)(H2O)2] ( | 234.51 | 46.53 | 58.63 | 46.53 | 50.56 |
| [Mn(ph)(phen)2(H2O)].4H2O ( | 259.34 | 129.67 | 129.67 | 129.67 | 129.67 |
| [Mn2(isoph)2(phen)3].4H2O ( | 255.87 | 40.30 | 63.97 | 40.30 | 48.19 |
| {[Mn(phen)2(H2O)2]}2(isoph)2(phen).12H2O ( | 251.76 | 99.91 | 99.91 | 99.91 | 99.91 |
| [Mn(tereph)(phen)2].5H2O ( | 251.94 | 62.99 | 62.99 | 62.99 | 62.99 |
| [Mn2(oda)(phen)4(H2O)2][Mn2(oda)(phen)4(oda)2]4H2O ( | >512 | >256 | >256 | >203.19 | >236.40 |
| {[Mn(3,6,9-tdda)(phen)2].3H2O.EtOH} | 261.67 | 130.84 | 130.84 | 82.42 | 114.70 |
| [Ag(phendione)2]ClO4( | 3.76 | 3.76 | 2.98 | 1.88 | 2.87 |
| [Ag2(3,6,9-tdda)(phen)4].EtOH ( | 2.21 | 2.21 | 2.78 | 1.75 | 2.25 |
| [Ag(phen)2]ClO4 ( | 2.07 | 2.07 | 3.29 | 1.30 | 2.22 |
| [Ag2(phen)3(udda)].3H2O ( | 13.63 | 86.55 | 54.52 | 27.26 | 56.11 |
Selectivity indexes (SI) were calculated using the formula CC.
Inhibitory effects of test compounds on biofilm-growing cells of the clinical isolates of the Candida haemulonii complex.
| 512 | 2 | 2 | 12.70 | 4 | 32 | 8 | 10.08 | 1 | 1 | 1 | 1 | 5.04 (27.96 μM) | |
| >512 | 8 | 16 | 11.31 | 16 | 16 | 32 | 20.16 | 4 | 32 | 16 | 12.70 | 14.67 (76 μM) | |
| >512 | 8 | 32 | 16 | 128 | 64 | 8 | 40.32 | 16 | 16 | 128 | 32 | 29.34 (172 μM) | |
| [Cu(isoph)(phen)2].6H2O.EtOH ( | 32 | 16 | 16 | 20.16 | 16 | 8 | 16 | 12.70 | 32 | 8 | 8 | 12.70 | 14.81 (19.95 μM) |
| [Cu2(oda)(phen)4](ClO4)2.2.76H2O.EtOH ( | 32 | 16 | 16 | 20.16 | 32 | 8 | 16 | 16 | 32 | 8 | 16 | 16 | 17.28 (13.19 μM) |
| [Cu(phendione)3](ClO4)2.4H2O ( | 256 | 32 | 16 | 50.80 | 32 | 32 | 32 | 32 | 16 | 16 | 8 | 12.70 | 27.43 (28.42 μM) |
| {[Cu(3.6.9-tdda)(phen)2].3H2O.EtOH} | 32 | 4 | 4 | 8 | 4 | 4 | 2 | 3.17 | 16 | 4 | 8 | 8 | 5.88 (7.9 μM) |
| [Mn(ph)(phen)(H2O)2] ( | >512 | 4 | 16 | 8 | 32 | 16 | 8 | 16 | 16 | 8 | 8 | 10.08 | 11.31 (25.98 μM) |
| [Mn(ph)(phen)2(H2O)].4H2O ( | 512 | 2 | 16 | 25.40 | 16 | 4 | 4 | 6.35 | 16 | 4 | 2 | 5.04 | 9.33 (13.93 μM) |
| [Mn2(isoph)2(phen)3].4H2O ( | >512 | 8 | 32 | 16 | 32 | 8 | 8 | 12.70 | 16 | 16 | 16 | 16 | 14.67 (13.96 μM) |
| {[Mn(phen)2(H2O)2]}2(isoph)2(phen).12H2O ( | >512 | 8 | 32 | 16 | 16 | 4 | 8 | 8 | 8 | 8 | 4 | 6.35 | 8.72 (5.3 μM) |
| [Mn(tereph)(phen)2].5H2O ( | >512 | 16 | 16 | 16 | 2 | 4 | 16 | 5.04 | 32 | 8 | 16 | 16 | 10.37 (15.48 μM) |
| [Mn2(oda)(phen)4(H2O)2][Mn2(oda)(phen)4(oda)2]4H2O ( | >512 | 32 | 16 | 22.63 | 16 | 4 | 8 | 8 | 4 | 4 | 8 | 5.04 | 8.72 (3.5 μM) |
| {[Mn(3.6.9-tdda)(phen)2].3H2O.EtOH}n ( | 512 | 4 | 4 | 20.16 | 16 | 4 | 8 | 8 | 16 | 4 | 16 | 10.08 | 11.76 (4.7 μM) |
| [Ag(phendione)2]ClO4( | >512 | 8 | 16 | 11.31 | 32 | 32 | 32 | 32 | 8 | 32 | 4 | 10.08 | 16 (25.48 μM) |
| [Ag2(3.6.9-tdda)(phen)4].EtOH ( | 32 | 16 | 8 | 16 | 4 | 1 | 4 | 2.52 | 4 | 8 | 8 | 6.35 | 6.35 (5.2 μM) |
| [Ag(phen)2]ClO4 ( | 32 | 32 | 8 | 20.16 | 8 | 0.5 | 8 | 8 | 16 | 8 | 8 | 10.08 | 12.34 (21.73 μM) |
| [Ag2(phen)3(udda)].3H2O ( | 32 | 8 | 16 | 16 | 8 | 0.5 | 16 | 11.31 | 16 | 8 | 8 | 10.08 | 12.34 (12.04 μM) |
All biofilm MIC (bMIC) values are shown in mg/L. The values of bMIC were statistically different between Candida haemulonii strains and the other two species (P = 0.04. t-test). No significant differences were detected when comparing C. haemulonii var. vulnera and C. duobushaemulonii. The values of bMIC were statistically different between the strains (P ≤ 0.0001. one-way ANOVA).
These values do not include the results obtained with the LIP Ch4 strain that could not be established (>512).