Next Article in Journal
First Insights into the Repertoire of Secretory Lectins in Rotifers
Next Article in Special Issue
Marine Drug Discovery through Computer-Aided Approaches
Previous Article in Journal
Micrococcin P1 and P2 from Epibiotic Bacteria Associated with Isolates of Moorea producens from Kenya
Previous Article in Special Issue
Uncovering the Bioactive Potential of a Cyanobacterial Natural Products Library Aided by Untargeted Metabolomics
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Marine Drugs
Volume 20
Issue 2
10.3390/md20020129
marinedrugs-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Predicting Antifouling Activity and Acetylcholinesterase Inhibition of Marine-Derived Compounds Using a Computer-Aided Drug Design Approach

by
Susana P. Gaudêncio
1,2 and
Florbela Pereira
3,*
1
Associate Laboratory i4HB—Institute for Health and Bioeconomy, NOVA School of Science and Technology, NOVA University of Lisbon, 2819-516 Caparica, Portugal
2
UCIBIO—Applied Molecular Biosciences Unit, Department of Chemistry, Blue Biotechnology and Biomedicine Lab, NOVA School of Science and Technology, NOVA University of Lisbon, 2819-516 Caparica, Portugal
3
LAQV, Department of Chemistry, NOVA School of Science and Technology, NOVA University of Lisbon, 2829-516 Caparica, Portugal
*
Author to whom correspondence should be addressed.
Mar. Drugs 2022, 20(2), 129; https://doi.org/10.3390/md20020129
Submission received: 13 December 2021 / Revised: 28 January 2022 / Accepted: 6 February 2022 / Published: 8 February 2022
(This article belongs to the Special Issue Marine Drug Discovery through Computer-Aided Approaches)
Browse Figures
Versions Notes

Abstract

:
Biofouling is the undesirable growth of micro- and macro-organisms on artificial water-immersed surfaces, which results in high costs for the prevention and maintenance of this process (billion €/year) for aquaculture, shipping and other industries that rely on coastal and off-shore infrastructure. To date, there are still no sustainable, economical and environmentally safe solutions to overcome this challenging phenomenon. A computer-aided drug design (CADD) approach comprising ligand- and structure-based methods was explored for predicting the antifouling activities of marine natural products (MNPs). In the CADD ligand-based method, 141 organic molecules extracted from the ChEMBL database and literature with antifouling screening data were used to build the quantitative structure–activity relationship (QSAR) classification model. An overall predictive accuracy score of up to 71% was achieved with the best QSAR model for external and internal validation using test and training sets. A virtual screening campaign of 14,492 MNPs from Encinar’s website and 14 MNPs that are currently in the clinical pipeline was also carried out using the best QSAR model developed. In the CADD structure-based approach, the 125 MNPs that were selected by the QSAR approach were used in molecular docking experiments against the acetylcholinesterase enzyme. Overall, 16 MNPs were proposed as the most promising marine drug-like leads as antifouling agents, e.g., macrocyclic lactam, macrocyclic alkaloids, indole and pyridine derivatives.

Graphical Abstract

1. Introduction

Marine biofouling is the undesired accumulation of micro-organisms, e.g., bacteria, cyanobacteria, unicellular algae and protozoa, and macro-organisms, e.g., seaweeds, barnacles, mussels and shells, on artificial water-immersed surfaces in a dynamic process that starts immediately after water submersion and can be a fast or slow process taking only hours or months to develop, respectively [1]. Marine biofouling creates risks to various industries, such as aquaculture and shipping, as well as for non-marine industries, e.g., paper manufacturing, food processing, underwater construction, power plants and others [2,3]. Settlement on the vessel’s hull results in damage to the rudder and propulsion systems [2,4], leads to an increasing drag of up to 60%, as well as a fuel consumption increase by 40%, increasing carbon dioxide and sulfur dioxide emissions [5] and the spread of nonindigenous marine species into ecosystems worldwide, leading to environmental imbalances [6,7,8,9,10]. The most effective antifouling (AF) coatings contained biocides, such as tributyltin (TBT) and tributyltin oxide (TBTO), which were found to be harmful to non-target organisms and the environment [11] and thus were prohibited by the International Maritime Organization from Ship Surfaces in 2008, generating the demand for new generations of non-toxic or environment-friendly AF solutions [12,13,14].
Natural alternatives including primary or secondary metabolites isolated from marine organisms have been reported in several reviews to inhibit the settlement of different biofouling species [15,16,17,18,19,20,21,22,23,24]. The search for AF agents from marine sources began with bromo-derived metabolites, among the 2-furanone bromine derivatives extracted from red algae, which have been reported to prevent fouling [25], as well as bromopyrrole alkaloid derivatives with AF activity isolated from sponges (oroidin), inspiring the design of more than 50 synthetic analogues [26,27], and, more recently, antifouling bromotyrosine derivatives of the synoxazolidinone and the pulmonarin families [28]. Several studies reported MNPs with antifouling activity comprising the 2,5-diketopiperazine scaffold isolated from the marine sponge Geodia barretti [29], 6-benzyl and 6-isobutyl 2,5-diketopiperazine derivatives from marine-derived actinomycete Streptomyces praecox [30] and five diketopiperazines, cyclo-(L-Leu-L-Pro), cyclo-(L-Phe-L-Pro), cyclo-(L-Val-L-Pro), cyclo-(L-Trp-L-Pro) and cyclo-(L-Leu-L-Val), from deep-sea Streptomyces fungicidicus [31]. Comprising a meroterpenoid scaffold, napyradiomycin derivatives, isolated from marine-derived actinomycetes Streptomyces aculeolatus, were investigated by our group as antifouling inhibitors, having the advantage of inhibiting both micro- (antibiofilm activity) and macrofouling [32,33,34].
Computer-aided drug design (CADD) approaches have been used to guide decisions concerning the in vivo and in vitro testing of isolated NPs and extracts [35,36,37,38,39], to assist in the design of bioactive NP derivatives [40,41] and to virtually screen databases of known or proposed NPs [40,42,43,44]. To the best of our knowledge, the antifouling activity was quantitative structure–activity relationship (QSAR) modeled in only two previous works for the settlement of Mytilus galloprovincialis larvae [45,46]. Almeida et al. built two QSAR models using multilinear regression methods with, respectively, 19 and 16 nature-inspired (thio)xanthone [46] and chalcone [45] derivatives, including in vitro antifouling activity screening assays for the settlement of Mytilus galloprovincialis larvae.
Acetylcholinesterase (AChE) inhibitors are a class of drugs used for the treatment of Alzheimer’s disease, glaucoma and autoimmune disorders [47,48,49]. The enzymes AChE [28] and tyrosinase (Tyr) were associated with the adhesive processes in the settlement of different biofouling species [28,46,50]. Almeida et al. reported a molecular docking study conducted by modulation of Electrophorus electric (fish) AChE of the two most promising (thio)xanthone antifouling agents [46]. Recently, Arabshahi et al. [50] reported an extensive virtual Tetronarce californica (fish) AChE homology screening campaign for 10,000 small organic molecules from the Chembridge library. The authors also reported the experimental screening of the most promising AChE inhibitors proposed by the in silico model, against five microfouling marine bacteria and marine microalgae macrofouling tunicate Ciona savignyi, discovering a potent novel inhibitor of tunicate settlement [50].
Herein, we report comprehensive computational modeling for the prediction of antifouling activities from two MNP libraries, by employing structure- and ligand-based CADD methodologies. The two libraries comprised 14,492 MNP from Prof. Encinar (http://docking.umh.es/downloaddb, accessed on 25 October 2021) and 14 MNPs from the clinical pipeline of MNPs (eight drugs approved and six MNPs in Phase II and III clinical trials). All the MNPs from the virtual screening libraries that were predicted to belong to the active class, i.e., 125 MNPs, were selected to proceed to the CADD structure-based method, where 125 MNPs selected by QSAR approach were screened by molecular docking against the AChE enzyme. In this CADD approach, a virtual screening hit list comprising 19 MNPs was assented based on some established thresholds, such as the probability of being active in the best antifouling model and the prediction of affinity between the AChE of selected MNPs by molecular docking. A total of 16 MNPs have been proposed as the most promising marine drug-like leads as antifouling agents.

2. Results and Discussion

2.1. Chemical Space of the Antifouling Model

The whole data set (i.e., 141 small organic molecules) was randomly divided into a training set of 127 molecules (comprising 57 active and 70 inactive molecules) and a test set of 14 molecules (comprising six active and eight inactive molecules), which were used for the development and external validation of the QSAR classification models, respectively. The whole data set comprised seven structural classes or scaffold types, which are represented in Table 1 along with their antifouling activity classes and scaffold representative.
All seven structural clusters (I, acyclic derivative, II, O-heterocyclic derivative, III, N-heterocyclic derivative, IV, terpenoid derivative, V, diketopiperazine derivative, VI, chalcone derivative, and VII, miscellaneous) were well represented in the training set, each comprising more than 10 molecules per class. The active class was more represented in three structural clusters with a percentage higher than 50%, namely I—acyclic derivative (100%), III—N-heterocyclic derivative (74%) and V—diketopiperazine derivative (67%). In the test set, only five structural clusters were represented, II-V and VII. In Table 1, the most representative scaffolds of the structural cluster are highlighted—for instance, for cluster I, a polyacetylene derivative; II, a chromone and a xanthone derivative; III, a pyrrole and a piperidine derivative; IV, a sesquiterpene derivative; V, a diketopiperazine, VI, a chalcone derivative; and VII, various scaffolds such as peptides and nature-inspired sulfated compounds. All clusters for the training and test sets, except for cluster VII, had an average MW value of less than 500 Da.

2.2. Establishment of QSAR Classification Model

Random Forests (RF) [51] were used to build models for antifouling prediction, exploring well-established PaDEL fingerprints (FPP and descriptors, e.g., five different types of FPs with different sizes (166 MACCS, MACCS keys; 307 Substructure; 881 PubChem fingerprints; 1024 CDK, circular fingerprints; 1024 CDK Ext, extended circular fingerprints with additional bits describing ring features) and 1376 1D&2D molecular descriptors (including electronic, topological and constitutional descriptors)) [52]. The performance of the models was successfully evaluated by internal validation (out-of-bag, OOB, estimation on the training set); see Table 2.
From the seven sets of FPs and descriptors used to build the QSAR classification model, the best set for each type, fragment FPs (Sub), circular FPs (ExtCDK) and molecular descriptors (1D&2D), were selected for further investigations; see Table 2. The 3D descriptors had a well-established relationship with biological activity and were expected to increase both the accuracy and robustness of the predictive models. After the exploration of models derived with molecular descriptors and FPs, we investigated the inclusion of 3D descriptors such as radial distribution function (RDF) descriptors (using a range of 128 and partial atomic charge as an atomic property) and the selection of descriptors using the RF descriptor importance parameter for the best three sets (Sub FPs, ExtCDK FPs and 1D&2D descriptors). Three sets of descriptors (Sub + RDF, ExtCDK + RDF and 1D&2D + RDF) as well as their selection were explored for modeling the antifouling activity using the RF algorithm in Table 3, where the results for the training set in OOB estimation are presented.
The 200 most important descriptors selected by the MeanDecreaseAccuracy parameter of the 1D&2D + RDF model were identified by the RF algorithm and enabled the training of a new RF model with better prediction accuracy in accordance with the Q and MCC values than the model trained with the whole set of descriptors (Table 3). A comparison of three machine learning (ML) techniques using the Weka software (support vector machines, SVM), R software (RF) and Keras software (deep learning multilayer perceptron networks, dMLP) for building the antifouling models with the 200 descriptors that were selected by the RF is shown in Table 4 for the test set.
The best models were accomplished with the RF and dMLP algorithms using the 200 1D&2D + RDF selected descriptors, which achieved, for both models, a Q and MCC of 0.714 and 0.417 for the external test set. Majority voting predictions (consensus) were obtained by the RF, SVM and dMLP models (the consensus model, CM), and did not improve the results, with a Q and MCC of 0.571 and 0.167 for the test set; thus, in the next step of the virtual screening, we used the best model obtained, RF, with the 200 selected descriptors; see Table 3 and Table 4).
The results obtained by the RF for the training and test sets that were in accordance with the seven structural clusters (I–VII), reported in Table 1, are shown in Table 5.
There were three structural clusters (I, II and IV, bold highlighted in Table 5) in which the predictions obtained were better than those obtained for the overall training set simultaneously considering the Q and MCC values. An improvement in the RF model prediction accuracies (Q = 0.821–1 and MCC = 0.64–1) was achieved for these three clusters of the training set, when compared with the prediction accuracy obtained for all the molecules of the training set (Q = 0.811 and MCC = 0.625). For the clusters II and V-VII, lower prediction accuracies were obtained, Q = 0.6–0.842 and MCC = 0.234–0.574. Interestingly, the best achieved predictions for structural clusters I and II were related to the best performance obtained for the active class prediction, with SE values of 1 and 0.889, respectively, compared to the SE value of 0.842 for all training sets. For example, for the test set, the average of the Prob_active (a_Prob_active) obtained by the active molecules predicted by the model as active, i.e., true positive (TP), was 0.59, which compares with the value of a_Prob_active of 0.54 obtained by the predicted molecules by the model as false positives (FP). The same relationship was obtained for molecules predicted as true negatives (FN) and false negatives (FN), with an a_Pro_active of 0.44 and 0.48, respectively. Additionally, it appears that, with a Prob_active higher than 0.59, there was no error in the prediction and all molecules predicted as active were active.

2.3. Analysis of Fingerprints and Descriptors Identified as Relevant for Modeling the Antifouling Activity

The selected 200 descriptors included 164 1D&2D (115 topological descriptors, 48 count type descriptors and one constitutional descriptor (Mannhold LogP, logarithm of the octanol–water partition coefficient)) and 36 RDF 3D descriptors (12 of type a (a positive and a negative charge), 12 of type b (two positive charges) and 12 of type c (two negative charges)). The 1D&2D descriptors comprised 72 autocorrelation topological descriptors, which were 50 Broto–Moreau, 12 Moran and 10 Geary autocorrelation descriptors, weighted by mass, charges, van der Waals volumes, Sanderson electronegativities, polarizabilities, first ionization potential or I-state. Other topological descriptors, such as 6 Barysz matrices, 24 Burden-modified eigenvalues, 1 Detour matrix, 2 MDEs, 2 path counts, 3 topological charges, 3 distance matrices, 1 walk count descriptor and 1 weighted path descriptor, were also presented. The count type descriptors included 28 electrotopological state atom types, 10 extended topochemical atoms and 10 information content descriptors. A comparison of the best twenty 1D&2D + RDF molecular descriptors selected by descriptor importance of RF was used to build the QSAR classification models, which are presented in Table 3 and Table 4, and these were analyzed and are presented in Figure 1.
Interestingly, no 3D RDF descriptor appeared in the list of the twenty most important descriptors and the first RDF descriptor appeared only in the 30th position (two positive charges). Moreover, there were only seven out the twenty most important descriptors that were more relevant in discriminating the active class, namely AATSC5m (5th), ATSC5m (7th), AATS8i (8th), maxssssC (9th), ATSC8p (16th), AATSC5c (17th) and minHCsats (19th). Of the nine Broto–Moreau autocorrelation descriptors existing in the list of the top 20, five of them were more relevant to discriminate the active class and, on the other hand, they also presented a lag higher than or equal to 5, which was related to a greater distance between the structural features of interest. In contrast, the four Broto–Moreau autocorrelation descriptors that were more relevant for the inactive class presented a lag lower than or equal to 5. The three most important descriptors in the top 20 list were three Burden-modified eigenvalue descriptors and all of them were most relevant in the inactive class discrimination. This eigenvalue was suggested as an index of molecular branching, the smallest values corresponding to chain graphs (SpMin3_Bhe) and the highest to the most branched graphs (SpMin5_Bhs and SpMin5_Bhm) [53]. A very interesting behavior was observed with the two electrotopological state atom types, maxssssC (maximum atom-type E-state: >C<) and SssCH2 (sum of atom-type E-state: -CH2-), which were more relevant for the active and inactive classes, respectively. The maxssssC descriptor encodes the maximum number of quaternary or asymmetric carbon atoms and could be seen as encoding structural complexity. On the other hand, the SssCH2 descriptor encoded the saturation of the molecule. Another very important descriptor to discriminate mainly the inactive class is the PaDEL weighted path descriptor, WTPT-5, which is the sum of all path weights starting from nitrogen atoms, revealing nitrogen-specific branching information. In agreement with the present work, the two QSAR studies reported by Almeida et al. highlighted the descriptors related to the branching, complexity and the influence of the molecule’s interatomic distance for the modeling of the antifouling activity [45,46].

2.4. Application of the In Silico Antifouling QSAR Model in Virtual Screening

A virtual screening campaign was carried out to search for new lead-like antifouling inhibitors. The best QSAR model, the RF model, was selected for the virtual screening procedure using 14,492 MNPs from Prof. Encinar’s website and 14 MNPs in the pharmaceutical pipeline (eight approved drugs and six MNPs in Phase II and III of clinical trials). The antifouling virtual screening of the MNP library in the pharmaceutical pipeline allowed us to assess the possibility of repurposing drugs of marine origin. Of these 14 MNPs from the pharmaceutical pipeline, only one MNP in Phase II of clinical trials presented activity against AChE, GTS-21 (DMXBA), a derivative of the NP, 2,4-dimethoxybenzylidene anabaseine dihydrochloride. There were 13,902 MNPs that were predicted to be active by the best QSAR model, of which 8349 MNPs were predicted to be active with a Prob_active greater than 0.59 (limit defined for the test set for which there are no prediction errors). From these MNPs, 5 (one approved drug and four MNPs in Phase II and III of clinical trials) and 8344 MNPs were from the pharmaceutical pipeline and from Encinar’s database, respectively. Interestingly, of the five MNPs from the MNP pharmaceutical pipeline predicted to be active with the highest Prob_active was DMXBA with a value of 0.658. A more demanding limit has been defined for the CADD structure-based approach: all the MNPs from the virtual screening libraries that were predicted as belonging to the active class with a Prob_active greater than or equal to 0.68 were selected for molecular docking experiments. In the CADD structure-based method, the 125 MNPs selected by the QSAR classification approach were screened by molecular docking against acetylcholinesterase enzyme (AChE).
The list of eleven lead-like AChE inhibitors against antifouling activity generated from the AChE homology virtual screening, which were experimentally screened in in vitro and micro- and macrofouling assays reported by Arabshahi et al. [50], was used in this study as a second virtual screening library (Supplementary Data, Table S5). Only one out of the eleven lead-like AChE inhibitors was predicted to have antifouling activity with a Prob_active higher than 0.59 (Table S5), the morpholine derivative (Figure 2), in which experimental antifouling activity IC50 = 16 μg/mL was reported (51.7 μM) [50]. However, none of the eleven compounds passed the established threshold, which was more demanding (Prob_active ≥ 0.68), to be selected for the molecular docking experiments.

2.5. Molecular Docking against AChE Enzyme

The 125 MNPs from Encinar’s database selected by the QSAR classification approach were screened by molecular docking against AChE enzyme (PDB ID: 6TT0) [54]. The antifouling agents, synoxazolidinone A, synoxazolidinone C and donepezil, known as AChE inhibitors [28], were used as positive controls and the phenolic derivative that was predicted to not have antifouling activity in virtual screening was used as a negative control in the molecular docking experiments. A list of virtual screening hits comprising 19 MNPs was approved based on molecular docking experiments, in which a threshold of ΔGB ≤ −7 kcal/mol was established for predicting the affinity between AChE and selected MNPs. To prioritize the best marine drug-like leads as antifouling AChE inhibitors from the list of 19 selected MNPs by the antifouling QSAR model and molecular docking of AChE enzyme, the absorption, distribution, metabolism, excretion and toxicity (ADMET) properties were predicted via in silico methods using the pKCSM software (http://biosig.unimelb.edu.au/pkcsm/, accessed on 25 October 2021) [55]. Sixteen MNPs, a macrocyclic lactam (CAS 156310-18-8), seven macrocyclic alkaloids (CAS 126622-63-7, 126622-64-8, 156310-18-8, 155944-26-6, 157536-35-1, 105305-54-2 and 105418-77-7), seven indole derivatives (CAS 142677-10-9, 134029-43-9, 134029-44-0, 134029-45-1, 142677-09-6, 223596-72-3, 134779-34-3) and a pyridine derivative (CAS 59697-14-2) were proposed as marine drug-like leads as antifouling AChE inhibitors. Three MNPs were excluded due to their predicted toxicity to fish, namely against flathead minnows. The Autodock Vina software (http://vina.scripps.edu/, accessed on 25 October 2021) [56] was used to perform the flexible virtual screening of the 125 MNPs to find the most favorable binding interactions, and the calculated free binding energies by the set of search space coordinates are reported in Table 6 for the 16 MNPs selected, and the positive (synoxazolidinone A and C; donepezil, an AChE inhibitor used for Alzheimer disease therapy) and the negative (phenolic derivative derivative) controls.
The prediction of the ADMET properties of the sixteen selected MNPs by the antifouling QSAR model and molecular docking of AChE enzyme is presented in Table S1, in the Supplementary Materials. In Figure 3, the interaction profile of the best-docked pose for the two most probable lead-like antifouling AChE inhibitors, a lactam derivative—cylindramide—and a macrocyclic alkaloid—haliclamine B—is represented.
New scoring functions based on more precise physics-based descriptors to better represent the protein–ligand recognition process have been developed. DockThor, a web service for molecular docking simulation (https://dockthor.lncc.br/v2/, accessed on 6 January 2022), was used to perform molecular docking of the two best macrocycle hits (cylindramine and haliclamine B), the best non-macrocycle hit (indole derivative, CAS 142677-10-9) and the positive and negative controls against the AChE enzyme (PDB ID: 6TT0). In DockThor, a set of new empirical scoring functions to estimate protein–ligand binding affinity were developed by explicitly accounting for physics-based interaction terms based on the MMFF94S force field combined with ML [57]. The DockThor scores obtained for the two best macrocycle hits (cylindramine and haliclamine B), the best non-macrocycle hit (indole derivative, CAS 142677-10-9) and the positive (synoxazolidinone A and C; donepezil) and negative (phenolic derivative) controls were −8.508 kcal/mol (−11.3 kcal/mol using Autodock Vina), −7.008 kcal/mol (−8.2 kcal/mol using Autodock Vina), −8.634 kcal/mol (−7.5 kcal/mol using Autodock Vina), −7.749 kcal/mol (−6.5 kcal/mol using Autodock Vina), −7.56 kcal/mol (−6.7 kcal/mol using Autodock Vina) and −6.416 kcal/mol (−5.1 kcal/mol using Autodock Vina), respectively. The interaction profiles of the best-docked poses predicted by DockThor for the two best macrocycle hits, the best non-macrocycle hit and the positive and negative controls are presented in Figure 4.
The peripheral anionic site (PAS) of AChE is composed of five residues (TYR-70, ASP-72, TYR-121, TRP-279 and TYR-334) and is involved in the allosteric modulation of catalysis at the active center [46]. This site is the target of various anti-cholinesterase inhibitors. In this work, other residues (e.g., ARG-88, ASN-65, PRO-64, GLY-32, THR-62, TRP-58 and ASN-59) forming the hydrophobic interactions in the PAS pocket are highlighted in Figure 3 and Figure 4. The binding of donepezil to the PAS of AChE is in accordance with its proposed peculiar inhibitory mechanism, which involves a reversible double-binding site interaction with the catalytic anionic site and PAS of the enzyme [54]. Unlike our approach and in other reported studies [46,54], Arabshahi et al. [50] performed a virtual screening by molecular docking of AChE at the catalytic anionic site and not at the PAS. Although none of the 11 reported compounds [50] passed the QSAR model threshold to be subjected to molecular docking, we still performed the molecular docking and the docking scores are presented in Table S5 (Supplementary Data). It was verified that none of these compounds exceeded the established threshold in the molecular docking experiments, ΔGB ≤ −7 kcal/mol.

3. Materials and Methods

3.1. Data Sets/Selection of Training and Test Sets

The antifouling data set comprising 142 molecules, 63 and 79 organic molecules, was extracted from the ChEMBL (https://www.ebi.ac.uk/chembl/, accessed on 21 July 2021) [58] and by searching in the literature indexed in the Web of Science Core Collection until June 2021, respectively. The ChEMBL data set was obtained by searching for marine organisms with antifouling activity, such as barnacles (e.g., Balanus amphitrite), mussels (e.g., Mytilus galloprovincialis), bushy bryozoan (e.g., Bugula neritina) and marine algae (e.g., Ulva conglobata). The antifouling activity was classified using two activity classes: (A, active)—inhibition % > 52% and EC50, IC50 ≤ 25 μg/mL; (B, inactive)—inhibition % ≤ 52% and EC50, IC50 > 25 μg/mL. After collecting these data sets, the duplicates were removed based on the IUPAC international chemical identifier (InChI) codes; however, the chirality was considered, and racemic compounds (or cases where no stereochemistry was indicated) were considered as one of the possible stereoisomers. Thereafter, the final data set comprised 141 organic molecules and was divided into a training set comprising 127 molecules (class A, 57 molecules and class B, 70 molecules) and a test set comprising 14 molecules (class A, 6 molecules and class B, 8 molecules). The partitioning of the data set into training and testing sets was performed randomly according to the composition of the antifouling classes (active and inactive). The composition of the 10 structural categories shown in Table 1 was not considered. The built QSAR models were developed and externally validated using the training and test sets, respectively.
The virtual data set comprised 14,492 MNPs from Prof. Encinar’s website (http://docking.umh.es/downloaddb, accessed on 25 October 2021) saved in the MDL SDF data format and 14 MNPs from the pharmaceutical pipeline set (eight approved drugs and six MNPs in Phase II and III of clinical trials). Three duplicates with the training and test sets were removed and the final virtual data set comprised 14,503 molecules.
A second virtual library comprising eleven lead-like AChE inhibitors against antifouling activity reported by Arabshahi et al. [50] was also used.
SMILES strings of the data sets, and the corresponding experimental and predicted activities, are available as Supplementary Data, Tables S2, S3 and S5.

3.2. Calculation of Descriptors

The molecular structures of molecules in all data sets were standardized by normalizing tautomeric and mesomeric groups and by removing small disconnected fragments using the JChem Standardizer tool, version 5.7.13.0 (ChemAxon Ltd., Budapest, Hungary). The optimization of the three-dimensional molecular structures was carried out with CORINA version 2.4 (Molecular Networks GmbH, Erlangen, Germany). PaDEL-Descriptor (Pharmaceutical Data Exploration Laboratory, Singapore) version 2.21 (http://www.yapcwsoft.com/dd/padeldescriptor/, accessed on 21 July 2021) [52] was used to calculate empirical molecular fingerprints (FPs) and 1D&2D molecular descriptors. FPs of various types were calculated and exploited to build QSAR models, namely 166 MACCS (MACCS keys), 307 Substructure (presence and count of SMARTS patterns for Laggner functional group classification—Sub), 881 PubChem fingerprints (ftp://ftp.ncbi.nlm.nih.gov/pubchem/specifications/pubchem_fingerprints.txt, accessed on 21 July 2021), 1024 CDK (circular fingerprints) and 1024 CDK extended (Ext circular fingerprints with additional bits describing ring features). The 1D&2D molecular descriptors comprised descriptors of various types, including electronic, topological and constitutional descriptors, in a total of 1376 descriptors. Radial distribution function (RDF) pair descriptors [59] and 3D RDF descriptors were calculated by sampling the function of Equation (1) at 128 equally distributed values of r between 0 and 12.8 Å:
R D F ( r ) = ∑ i = 1 N − 1 ∑ j = 1 + 1 N p i p j e − B   ( r − r i j ) 2
where N is the number of atoms in the molecule, pi is the charge of atom i, B is a fuzziness parameter (it was 100 in this study), and rij is the 3D distance between atoms i and j. The RDF descriptors were separated into three sets of 128 descriptors per pair of atoms with (a) one positive and one negative charge, (b) two positive charges and (c) two negative charges. The partial atomic charges—natural bond orbital (NBO) partial atomic charges—were estimated using an ML tool developed by Aires-de-Sousa and co-workers (http://joao.airesdesousa.com/charges, accessed on 21 July 2021) [60].

3.3. Selection of Descriptors and Optimization of QSAR Models

In the quest for QSAR models with the minimum possible number of descriptors, descriptor selection was performed based on the importance of descriptors assessed by the RF (computeAttributeImportance) algorithm [51] implemented in the R program [61]. Selection of descriptors was accomplished using this procedure, with the importance of descriptors assessed by RF within an OOB methodology using the 12, 25, 50, 100, 150, 200 and 250 most important descriptors and RF algorithm as an ML technique employing the following statistical metrics: true positives (TP), true negatives (TN), false positives (FP), false negatives (FN), sensitivity (SE, prediction accuracy for active antifouling molecules), specificity (SP, prediction accuracy for inactive antifouling molecules), overall predictive accuracy (Q) and Matthews correlation coefficient (MCC).

3.4. Class Balancer

In general, class imbalance is more demanding for ML algorithms and this imbalance introduces a bias due to their preference for the majority class [62]. Our antifouling activity training set was unbalanced, and the imbalance ratio was 1:1.22 for the A: active and B: inactive classes, respectively. To solve this problem, the classes were balanced using the RF sampsize parameter with R version 3.6.1. [61]. This parameter was set to be of the same size as the minority class (active class). With this parameter, some molecules belonging to the minority class were used more than once.

3.5. Machine Learning (ML) Methods

3.5.1. Random Forest (RF)

The RF model [51,63] was built from a set of unpruned classification trees, which were created using bootstrap samples from the training set. For each individual tree, the best split at each node was defined using a randomly selected subset of descriptors. Each of the individual classification trees was created using different training and validation sets. The final prediction of the model resulted from the majority vote of classification trees in the forest. Model performance was evaluated internally with the prediction error for molecules left out in the bootstrap procedure (OOB estimation). The method quantifies the importance of a descriptor by the increase in misclassification that occurs when descriptor values are randomly permuted, correlated with the mean decrease in the precision parameter. RFs also assigned a probability to every prediction based on the number of votes obtained by the predicted class. RFs were grown with the R program [61], version 3.6.1, using the random forest library [64]. As a result of the nature of the two-class imbalance, this problem was alleviated by defining the class weight ranges of 1–57 and 1–57 for classes A and B, respectively, using the sampsize parameter.

3.5.2. Support Vector Machines (SVMs)

SVMs [65] map the training data into a hyperspace through a nonlinear mapping (a boundary or hyperplane) and then separate the classes of objects in this space. The examples of the training set—the support vectors—allowed us to position the boundary. To transform data into a hyperspace where classes become linearly separable, kernel functions were used. In this study, SVMs were implemented with Scikit-learn [66] using the LIBSVM package [67]. The type of SVM was set to C-SVM-classification and the radial basis function was used for the kernel function. Hyperparameter tuning was performed using ten-fold cross-validation with the GridSearchCV tool. C and γ values varied in the range of 1 × 10−2 to 1 × 1013 and 1 × 10−9 to 1 × 1013, respectively. In total, 10,000 experiments were performed. The C and γ values were finally set to 1 × 107 and 1 × 10−8, respectively, and the other parameters were used with default values. To alleviate the imbalanced two-class problem, the class_weight parameter was set to be “balanced”, in which the smaller class was replicated until it had as many molecules as in the larger one class.

3.5.3. Deep Learning Multilayer Perceptron Networks (dMLP)

The feed-forward neural networks were implement using the open-source software library Keras [68] version 2.2.5 based on the Tensorflow numerical backend engine [69]. These popular software tools, written in Python, make it easy to develop and apply deep neural networks; however, the main challenge in applying dMLP is the design of an adequate network architecture. After several experiments, the final optimal hyperparameter settings were selected for our study based on 10-fold cross-validation experiments with the training set and are listed in Table 7.

3.6. Molecular Docking

The virtual screening using the best QSAR model, the RF classification model using the 200 most important 1D&2D + RDF molecular descriptors, allowed the prioritization of a list of the 125 MNP virtual screening hits. OpenBabel software (version 2.3.1, freely available under an open-source license from http://openbabel.org, accessed on 21 July 2021) [70] was used to convert mol2 files into PDBQT files. PDBQT files were used for coupling to the AChE enzyme with Autodock Vina (version 1.1, Center for Computational Structural Biology, Scripps Research Institute, CA, USA) [56]. The macromolecule coupling target was the AChE enzyme from Tetronarce californica (PDB ID: 6TT0) [54]. Water molecules, carbohydrate molecules and ligands (1R, 3S-cis- and 1S, 3R-cis-donepezil derived enantiomers) were removed from 6TT0 [54] prior to docking using AutoDockTools (http://mgltools.scripps.edu/, accessed on 21 July 2021). During enzyme preparation, GTT0, explicit hydrogen atoms and Gasteiger charges for each atom were added. Autodock Vina performed a flexible molecular docking in which the target’s conformation was considered a rigid unit while the ligands were flexible and adaptable to the target. Autodock Vina looked for the lowest binding affinity conformations and returned ten different conformations for each ligand. The search space coordinates of the AChE enzyme were maximized to allow the entire macromolecule to be considered for docking. The search space coordinates were center X: 25.179 Y: 72.212 Z: 281.175; dimensions X: 20,000 Y: 20,000 Z: 20,000. AchE enzyme ligand tethering was performed by regulating the parameters of the genetic algorithm (GA), using 10 runs of the GA criteria. DockThor, a web service for molecular docking simulation (https://dockthor.lncc.br/v2/, accessed on 6 January 2022), was used to perform molecular docking of the two best macrocycle hits (cylindramine and haliclamine B), the best non-macrocycle hit (indole derivative, CAS 142677-10-9) and the positive and negative controls against AChE enzyme (PDB ID: 6TT0) [57]. The search space coordinates were center X: 25.179 Y: 72.212 Z: 281.175; dimensions X: 20,000 Y: 20,000 Z: 20,000. AChE enzyme ligand tethering was performed by regulating the parameters of the GA, using 12,750 and 500,000 runs, population size and number of evaluations of the GA criteria, respectively.
The docking binding poses were visualized with PyMOL Molecular Graphics System, Version 2.0 (Schrödinger, LLC). Docking scores of 125 virtual hits against the AChE enzyme are shown in Table S4, Supplementary Data.

4. Conclusions

A CADD approach relying on ligand- and structure-based methodologies was successfully used to predict new inhibitory MNPs against antifouling AChE. Two MNPs, cylindramide (CAS 147362-39-8) and haliclamine B (CAS 126622-63-7), were proposed as the most promising marine drug-like leads as antifouling AChE inhibitors. To the best of our knowledge, the CADD ligand-based study using a QSAR classification model, developed here in this study, is the largest study ever performed with regard both to the number of molecules involved and to the number of structural families involved in the modeling of the antifouling activity, and the best model achieved an overall predictive accuracy score of up to 71% for both test and training sets. In future works, the proposed sixteen marine drug-like leads against antifouling AChE enzyme may be validated experimentally. These results enabled us to build virtual libraries of marine-derived drug-like leads, which may be virtually screened using the best antifouling QSAR model and molecular docking against the AChE enzyme. In addition, for MNPs that are experimentally confirmed to have antifouling activity, the AChE inhibitory mechanism will be studied to determine the type of action, e.g., reversible interaction with both the catalytic anionic site and the PAS, sterically blocking ligands from entering and leaving the active site gorge and allosteric alteration of the catalytic triad conformation.

Supplementary Materials

The following data are available online at https://www.mdpi.com/article/10.3390/md20020129/s1, Tables S1–S5 (XLSX). The following files are available free of charge. SMILES strings of the data set (training and test sets), the corresponding experimental and predicted activities are available as Supplementary Materials, Tables S2 and S3, respectively. Moreover, SMILES strings of the 14,492 MNPs from Encinar’s website and MNPs clinical pipeline sets, for the virtual screening data set, the corresponding predicted activities are available as Supplementary Materials, Table S4. Predictions of ADMET properties with in silico methods, using the pKCSM software for a list of 16 selected MNPs by QSAR antifouling model and molecular docking of AChE enzyme are available as Supplementary Materials, Table S1. The list of eleven lead-like AChE inhibitors by Arabshahi et al. [50], the corresponding experimental, predicted activities and docking scores against the AChE enzyme are available as Supplementary Materials, Table S5.

Author Contributions

Conceptualization: F.P. and S.P.G.; Methodology: F.P.; Software: F.P.; Validation: F.P. (in silico modeling), S.P.G. (pharmaceutical pipeline data); Formal Analysis: F.P. (in silico modeling); Investigation: F.P. (in silico modeling) and S.P.G. (pharmaceutical pipeline data and MNP meroterpenoid library); Resources: F.P. (in silico modeling) and S.P.G. (pharmaceutical pipeline data and MNP meroterpenoid library); Writing—Original Draft Preparation: F.P. and S.P.G.; Writing—Review and Editing: F.P. and S.P.G.; Funding Acquisition: F.P. and S.P.G. All authors have read and agreed to the published version of the manuscript.

Funding

Financial support from Fundação para a Ciência e Tecnologia (FCT) Portugal, under grant UIDB/50006/2020 (provided to the Associate Laboratory for Green Chemistry LAQV), is greatly appreciated. F.P. thanks Fundacão para a Ciência e a Tecnologia, MCTES, for the Norma transitória DL 57/2016 Program Contract. This work is financed by national funds from FCT—Fundação para a Ciência e a Tecnologia, I.P., in the scope of the project UIDP/04378/2020 of the Research Unit on Applied Molecular Biosciences—UCIBIO and the project LA/P/0140/2020 of the Associate Laboratory Institute for Health and Bioeconomy—i4HB.

Data Availability Statement

Data are contained within the article or Supplementary Material.

Acknowledgments

We thank ChemAxon Ltd. for access to JChem and Marvin.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Magin, C.M.; Cooper, S.P.; Brennan, A.B. Non-toxic antifouling strategies. Mater. Today 2010, 13, 36–44. [Google Scholar] [CrossRef]
  2. Schultz, M.P.; Bendick, J.A.; Holm, E.R.; Hertel, W.M. Economic impact of biofouling on a naval surface ship. Biofouling 2011, 27, 87–98. [Google Scholar] [CrossRef] [PubMed]
  3. Schultz, M.P. Effects of coating roughness and biofouling on ship resistance and powering. Biofouling 2007, 23, 331–341. [Google Scholar] [CrossRef]
  4. Schultz, M.P.; Walker, J.M.; Steppe, C.N.; Flack, K.A. Impact of diatomaceous biofilms on the frictional drag of fouling-release coatings. Biofouling 2015, 31, 759–773. [Google Scholar] [CrossRef] [PubMed]
  5. Bhushan, B. Biomimetics: Lessons from nature—An overview. Philos. Trans. Royal Soc. A 2009, 367, 1445–1486. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  6. Ware, C.; Berge, J.; Sundet, J.H.; Kirkpatrick, J.B.; Coutts, A.D.M.; Jelmert, A.; Olsen, S.M.; Floerl, O.; Wisz, M.S.; Alsos, I.G. Climate change, non-indigenous species and shipping: Assessing the risk of species introduction to a high-Arctic archipelago. Divers. Distrib. 2014, 20, 10–19. [Google Scholar] [CrossRef] [Green Version]
  7. Ashton, G.V.; Davidson, I.C.; Geller, J.; Ruiz, G.M. Disentangling the biogeography of ship biofouling: Barnacles in the Northeast Pacific. Glob. Ecol. Biogeogr. 2016, 25, 739–750. [Google Scholar] [CrossRef]
  8. Pettengill, J.B.; Wendt, D.E.; Schug, M.D.; Hadfield, M.G. Biofouling likely serves as a major mode of dispersal for the polychaete tubeworm Hydroides elegans as inferred from microsatellite loci. Biofouling 2007, 23, 161–169. [Google Scholar] [CrossRef] [Green Version]
  9. Piola, R.F.; Johnston, E.L. The potential for translocation of marine species via small-scale disruptions to antifouling surfaces. Biofouling 2008, 24, 145–155. [Google Scholar] [CrossRef]
  10. Yamaguchi, T.; Prabowo, R.E.; Ohshiro, Y.; Shimono, T.; Jones, D.; Kawai, H.; Otani, M.; Oshino, A.; Inagawa, S.; Akaya, T.; et al. The introduction to Japan of the Titan barnacle, Megabalanus coccopoma (Darwin, 1854) (Cirripedia: Balanomorpha) and the role of shipping in its translocation. Biofouling 2009, 25, 325–333. [Google Scholar] [CrossRef] [PubMed]
  11. Sonak, S.; Pangam, P.; Giriyan, A.; Hawaldar, K. Implications of the ban on organotins for protection of global coastal and marine ecology. J. Environ. Manag. 2009, 90, S96–S108. [Google Scholar] [CrossRef]
  12. Callow, J.A.; Callow, M.E. Trends in the development of environmentally friendly fouling-resistant marine coatings. Nat. Commun. 2011, 2, 244. [Google Scholar] [CrossRef] [PubMed]
  13. Kirschner, C.M.; Brennan, A.B. Bio-Inspired Antifouling Strategies. Annu. Rev. Mater. Res. 2012, 42, 211–229. [Google Scholar] [CrossRef]
  14. Chambers, L.D.; Stokes, K.R.; Walsh, F.C.; Wood, R.J.K. Modern approaches to marine antifouling coatings. Surf. Coat. Technol. 2006, 201, 3642–3652. [Google Scholar] [CrossRef] [Green Version]
  15. Othmani, A.; Bunet, R.; Bonnefont, J.L.; Briand, J.F.; Culioli, G. Settlement inhibition of marine biofilm bacteria and barnacle larvae by compounds isolated from the Mediterranean brown alga Taonia atomaria. J. Appl. Phycol. 2016, 28, 1975–1986. [Google Scholar] [CrossRef]
  16. Satheesh, S.; Ba-akdah, M.A.; Al-Sofyani, A.A. Natural antifouling compound production by microbes associated with marine macroorganisms—A review. Electron. J. Biotechnol. 2016, 21, 26–35. [Google Scholar] [CrossRef] [Green Version]
  17. Almeida, J.R.; Vasconcelos, V. Natural antifouling compounds: Effectiveness in preventing invertebrate settlement and adhesion. Biotechnol. Adv. 2015, 33, 343–357. [Google Scholar] [CrossRef] [PubMed]
  18. Qian, P.-Y.; Li, Z.; Xu, Y.; Li, Y.; Fusetani, N. Mini-review: Marine natural products and their synthetic analogs as antifouling compounds: 2009-2014. Biofouling 2015, 31, 101–122. [Google Scholar] [CrossRef] [PubMed]
  19. Qian, P.-Y.; Xu, Y.; Fusetani, N. Natural products as antifouling compounds: Recent progress and future perspectives. Biofouling 2010, 26, 223–234. [Google Scholar] [CrossRef]
  20. Dobretsov, S.; Dahms, H.U.; Qian, P.Y. Inhibition of biofouling by marine microorganisms and their metabolites. Biofouling 2006, 22, 43–54. [Google Scholar] [CrossRef]
  21. Wang, K.-L.; Wu, Z.-H.; Wang, Y.; Wang, C.-Y.; Xu, Y. Mini-Review: Antifouling Natural Products from Marine Microorganisms and Their Synthetic Analogs. Mar. Drugs 2017, 15, 266. [Google Scholar] [CrossRef] [Green Version]
  22. Qi, S.-H.; Ma, X. Antifouling Compounds from Marine Invertebrates. Mar. Drugs 2017, 15, 263. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  23. Dahms, H.U.; Dobretsov, S. Antifouling Compounds from Marine Macroalgae. Mar. Drugs 2017, 15, 265. [Google Scholar] [CrossRef] [PubMed]
  24. Moodie, L.W.K.; Sepcic, K.; Turk, T.; Frangez, R.; Svenson, J. Natural cholinesterase inhibitors from marine organisms. Nat. Prod. Rep. 2019, 36, 1053–1092. [Google Scholar] [CrossRef]
  25. Dworjanyn, S.A.; de Nys, R.; Steinberg, P.D. Chemically mediated antifouling in the red alga Delisea pulchra. Mar. Ecol. Prog. Ser. 2006, 318, 153–163. [Google Scholar] [CrossRef] [Green Version]
  26. Richards, J.J.; Ballard, T.E.; Huigens, R.W., III; Melander, C. Synthesis and screening of an oroidin library against Pseudomonas aeruginosa biofilms. Chembiochem 2008, 9, 1267–1279. [Google Scholar] [CrossRef]
  27. Melander, C.; Moeller, P.D.R.; Ballard, T.E.; Richards, J.J.; Huigens, R.W., III; Cavanagh, J. Evaluation of dihydrooroidin as an antifouling additive in marine paint. Int. Biodeterior. Biodegradation 2009, 63, 529–532. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  28. Trepos, R.; Cervin, G.; Hellio, C.; Pavia, H.; Stensen, W.; Stensvag, K.; Svendsen, J.-S.; Haug, T.; Svenson, J. Antifouling Compounds from the Sub-Arctic Ascidian Synoicum pulmonaria: Synoxazolidinones A and C, Pulmonarins A and B, and Synthetic Analogues. J. Nat. Prod. 2014, 77, 2105–2113. [Google Scholar] [CrossRef] [PubMed]
  29. Sjogren, M.; Goransson, U.; Johnson, A.L.; Dahlstrom, M.; Andersson, R.; Bergman, J.; Jonsson, P.R.; Bohlin, L. Antifouling activity of brominated cyclopeptides from the marine sponge Geodia barretti. J. Nat. Prod. 2004, 67, 368–372. [Google Scholar] [CrossRef] [PubMed]
  30. Cho, J.Y.; Kang, J.Y.; Hong, Y.K.; Baek, H.H.; Shin, H.W.; Kim, M.S. Isolation and Structural Determination of the Antifouling Diketopiperazines from Marine-Derived Streptomyces praecox 291-11. Biosci. Biotechnol. Biochem. 2012, 76, 1116–1121. [Google Scholar] [CrossRef] [Green Version]
  31. Li, X.; Dobretsov, S.; Xu, Y.; Xiao, X.; Hung, O.S.; Qian, P.-Y. Antifouling diketopiperazines produced by a deep-sea bacterium, Streptomyces fungicidicus. Biofouling 2006, 22, 201–208. [Google Scholar] [CrossRef] [PubMed]
  32. Prieto-Davo, A.; Dias, T.; Gomes, S.E.; Rodrigues, S.; Parera-Valadezl, Y.; Borralho, P.M.; Pereira, F.; Rodrigues, C.M.P.; Santos-Sanches, I.; Gaudencio, S.P. The Madeira Archipelago As a Significant Source of Marine-Derived Actinomycete Diversity with Anticancer and Antimicrobial Potential. Front. Microbiol. 2016, 7, 1594. [Google Scholar] [CrossRef] [PubMed]
  33. Bauermeister, A.; Pereira, F.; Grilo, I.R.; Godinho, C.C.; Paulino, M.; Almeida, V.; Gobbo-Neto, L.; Prieto-Davo, A.; Sobral, R.G.; Lopes, N.P.; et al. Intra-clade metabolomic profiling of MAR4 Streptomyces from the Macaronesia Atlantic region reveals a source of anti-biofilm metabolites. Environ. Microbiol. 2019, 21, 1099–1112. [Google Scholar] [CrossRef] [PubMed]
  34. Pereira, F.; Almeida, J.R.; Paulino, M.; Grilo, I.R.; Macedo, H.; Cunha, I.; Sobral, R.G.; Vasconcelos, V.; Gaudencio, S.P. Antifouling Napyradiomycins from Marine -Derived Actinomycetes Streptomyces aculeolatus. Mar. Drugs 2020, 18, 63. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  35. Cruz, S.; Gomes, S.E.; Borralho, P.M.; Rodrigues, C.M.P.; Gaudencio, S.P.; Pereira, F. In Silico HCT116 Human Colon Cancer Cell-Based Models En Route to the Discovery of Lead-Like Anticancer Drugs. Biomolecules 2018, 8, 56. [Google Scholar] [CrossRef] [Green Version]
  36. Dias, T.; Gaudencio, S.P.; Pereira, F. A Computer-Driven Approach to Discover Natural Product Leads for Methicillin-Resistant Staphylococcus aureus Infection Therapy. Mar. Drugs 2019, 17, 16. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  37. Wang, M.; Carver, J.J.; Phelan, V.V.; Sanchez, L.M.; Garg, N.; Peng, Y.; Don Duy, N.; Watrous, J.; Kapono, C.A.; Luzzatto-Knaan, T.; et al. Sharing and community curation of mass spectrometry data with Global Natural Products Social Molecular Networking. Nat. Biotechnol. 2016, 34, 828–837. [Google Scholar] [CrossRef] [Green Version]
  38. Lang, G.; Mayhudin, N.A.; Mitova, M.I.; Sun, L.; van der Sar, S.; Blunt, J.W.; Cole, A.L.J.; Ellis, G.; Laatsch, H.; Munro, M.H.G. Evolving trends in the dereplication of natural product extracts: New methodology for rapid, small-scale investigation of natural product extracts. J. Nat. Prod. 2008, 71, 1595–1599. [Google Scholar] [CrossRef]
  39. Camp, D.; Davis, R.A.; Campitelli, M.; Ebdon, J.; Quinn, R.J. Drug-like Properties: Guiding Principles for the Design of Natural Product Libraries. J. Nat. Prod. 2012, 75, 72–81. [Google Scholar] [CrossRef]
  40. Gaudencio, S.P.; Pereira, F. A Computer-Aided Drug Design Approach to Predict Marine Drug-Like Leads for SARS-CoV-2 Main Protease Inhibition. Mar. Drugs 2020, 18, 633. [Google Scholar] [CrossRef]
  41. Wang, L.; Le, X.; Li, L.; Ju, Y.C.; Lin, Z.X.; Gu, Q.; Xu, J. Discovering New Agents Active against Methicillin-Resistant Staphylococcus aureus with Ligand-Based Approaches. J. Chem. Inf. Model. 2014, 54, 3186–3197. [Google Scholar] [CrossRef] [PubMed]
  42. Pereira, F.; Aires-de-Sousa, J. Computational Methodologies in the Exploration of Marine Natural Product Leads. Mar. Drugs 2018, 16, 236. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  43. Pereira, F. Have marine natural product drug discovery efforts been productive and how can we improve their efficiency? Expert Opin. Drug Discov. 2019, 14, 717–722. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  44. Llanos, M.A.; Gantner, M.E.; Rodriguez, S.; Alberca, L.N.; Bellera, C.L.; Talevi, A.; Gavernet, L. Strengths and Weaknesses of Docking Simulations in the SARS-CoV-2 Era: The Main Protease (Mpro) Case Study. J. Chem. Inf. Model. 2021, 61, 3758–3770. [Google Scholar] [CrossRef]
  45. Almeida, J.R.; Moreira, J.; Pereira, D.; Pereira, S.; Antunes, J.; Palmeira, A.; Vasconcelos, V.; Pinto, M.; Correia-da-Silva, M.; Cidade, H. Potential of synthetic chalcone derivatives to prevent marine biofouling. Sci. Total Environ. 2018, 643, 98–106. [Google Scholar] [CrossRef] [PubMed]
  46. Almeida, J.R.; Palmeira, A.; Campos, A.; Cunha, I.; Freitas, M.; Felpeto, A.B.; Turkina, M.V.; Vasconcelos, V.; Pinto, M.; Correia-da-Silva, M.; et al. Structure-Antifouling Activity Relationship and Molecular Targets of Bio-Inspired(thio)xanthones. Biomolecules 2020, 10, 1126. [Google Scholar] [CrossRef] [PubMed]
  47. Tadesse, M.; Svenson, J.; Sepicic, K.; Trembleau, L.; Engqvist, M.; Andersen, J.H.; Jaspars, M.; Stensvag, K.; Haug, T. Isolation and Synthesis of Pulmonarins A and B, Acetylcholinesterase Inhibitors from the Colonial Ascidian Synoicum pulmonaria. J. Nat. Prod. 2014, 77, 364–369. [Google Scholar] [CrossRef] [Green Version]
  48. Kaur, J.; Zhang, M.Q. Molecular modelling and QSAR of reversible acetylcholinesterase inhibitors. Curr. Med. Chem. 2000, 7, 273–294. [Google Scholar] [CrossRef] [Green Version]
  49. Munoz-Torrero, D. Acetylcholinesterase Inhibitors as Disease-Modifying Therapies for Alzheimer’s Disease. Curr. Med. Chem. 2008, 15, 2433–2455. [Google Scholar] [CrossRef]
  50. Arabshahi, H.J.; Trobec, T.; Foulon, V.; Hellio, C.; Frangez, R.; Sepcic, K.; Cahill, P.; Svenson, J. Using Virtual AChE Homology Screening to Identify Small Molecules With the Ability to Inhibit Marine Biofouling. Front. Mar. Sci. 2021, 8, 762287. [Google Scholar] [CrossRef]
  51. Breiman, L. Random forests. Mach. Learn. 2001, 45, 5–32. [Google Scholar] [CrossRef] [Green Version]
  52. Yap, C.W. PaDEL-Descriptor: An Open Source Software to Calculate Molecular Descriptors and Fingerprints. J. Comput. Chem. 2011, 32, 1466–1474. [Google Scholar] [CrossRef]
  53. Todeschini, R.; Consonni, V. Molecular Descriptors for Chemoinformatics; WILEY-VCH: Weinheim, Germany, 2009; Volumes 1–2. [Google Scholar]
  54. Catto, M.; Pisani, L.; de la Mora, E.; Belviso, B.D.; Mangiatordi, G.F.; Pinto, A.; De Palma, A.; Denora, N.; Caliandro, R.; Colletier, J.-P.; et al. Chiral Separation, X-ray Structure, and Biological Evaluation of a Potent and Reversible Dual Binding Site AChE Inhibitor. ACS Med. Chem. Lett. 2020, 11, 869–876. [Google Scholar] [CrossRef]
  55. Pires, D.E.V.; Blundell, T.L.; Ascher, D.B. pkCSM: Predicting Small-Molecule Pharmacokinetic and Toxicity Properties Using Graph-Based Signatures. J. Med. Chem. 2015, 58, 4066–4072. [Google Scholar] [CrossRef] [PubMed]
  56. Trott, O.; Olson, A.J. Software News and Update AutoDock Vina: Improving the Speed and Accuracy of Docking with a New Scoring Function, Efficient Optimization, and Multithreading. J. Comput. Chem. 2010, 31, 455–461. [Google Scholar] [CrossRef] [Green Version]
  57. Guedes, I.A.; Barreto, A.M.S.; Marinho, D.; Krempser, E.; Kuenemann, M.A.; Sperandio, O.; Dardenne, L.E.; Miteva, M.A. New machine learning and physics-based scoring functions for drug discovery. Sci. Rep. 2021, 11, 1–19. [Google Scholar] [CrossRef]
  58. Mendez, D.; Gaulton, A.; Bento, A.P.; Chambers, J.; De Veij, M.; Felix, E.; Magarinos, M.P.; Mosquera, J.F.; Mutowo, P.; Nowotka, M.; et al. ChEMBL: Towards direct deposition of bioassay data. Nucleic Acids Res. 2019, 47, D930–D940. [Google Scholar] [CrossRef]
  59. Selzer, P.; Ertl, P. Identification and classification of GPCR ligands using self-organizing neural networks. QSAR Comb. Sci. 2005, 24, 270–276. [Google Scholar] [CrossRef]
  60. Zhang, Q.; Zheng, F.; Fartaria, R.; Latino, D.A.R.S.; Qu, X.; Campos, T.; Zhao, T.; Aires-de-Sousa, J. A QSPR approach for the fast estimation of DFT/NBO partial atomic charges. Chemom. Intell. Lab. Syst. 2014, 134, 158–163. [Google Scholar] [CrossRef]
  61. R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing: Vienna, Austria. 2014. Available online: http://www.R-project.org (accessed on 21 July 2021).
  62. Jain, S.; Kotsampasakou, E.; Ecker, G.F. Comparing the performance of meta-classifiers-a case study on selected imbalanced data sets relevant for prediction of liver toxicity. J. Comput.-Aided Mol. Des. 2018, 32, 583–590. [Google Scholar] [CrossRef] [Green Version]
  63. Svetnik, V.; Liaw, A.; Tong, C.; Culberson, J.C.; Sheridan, R.P.; Feuston, B.P. Random forest: A classification and regression tool for compound classification and QSAR modeling. J. Chem. Inform. Comput. Sci. 2003, 43, 1947–1958. [Google Scholar] [CrossRef] [PubMed]
  64. Liaw, A.; Wiener, M. Classification and Regression by randomForest. R News 2002, 2, 18–22. [Google Scholar]
  65. Cortes, C.; Vapnik, V. Support-Vector Networks. Mach. Learn. 1995, 20, 273–297. [Google Scholar] [CrossRef]
  66. Pedregosa, F.; Varoquaux, G.; Gramfort, A.; Michel, V.; Thirion, B.; Grisel, O.; Blondel, M.; Prettenhofer, P.; Weiss, R.; Dubourg, V.; et al. Scikit-learn: Machine Learning in Python. J. Mach. Learn. Res. 2011, 12, 2825–2830. [Google Scholar]
  67. Chang, C.-C.; Lin, C.-J. LIBSVM: A Library for Support Vector Machines. ACM Trans. Intell. Syst. Technol. 2011, 2. [Google Scholar] [CrossRef]
  68. Chollet, F.K. GitHub, Seattle, WA, USA. 2015. Available online: https://github.com/fchollet/keras (accessed on 21 July 2021).
  69. Abadi, M.; Agarwal, A.; Barham, P.; Brevdo, E.; Chen, Z.; Citro, C.; Corrado, G.S.; Davis, A.; Dean, J.; Devin, M.; et al. TensorFlow: Large-Scale Machine Learning on Heterogeneous Distributed Systems. arXiv 2016, arXiv:1603.04467. [Google Scholar]
  70. O’Boyle, N.M.; Banck, M.; James, C.A.; Morley, C.; Vandermeersch, T.; Hutchison, G.R. Open Babel: An open chemical toolbox. J. Cheminform. 2011, 3, 33. [Google Scholar] [CrossRef] [Green Version]
Marinedrugs 20 00129 g001 550
Figure 1. The twenty most important 1D&2D +RDF descriptors selected in RF classification models, where the first three descriptors in terms of importance are three Burden-modified eigenvalue descriptors weighted by relative I-state, mass and Sanderson electronegativities, respectively; there are several Broto–Moreau autocorrelations 4th–5th, 7th–8th, 14th, 16th–18th, 20th weighted by I-state, mass, mass, first ionization potential, mass, polarizabilities, charge, Sanderson electronegativities and I-state; two Moran autocorrelation descriptors, 6th and 15th weighted by charge and mass, respectively; four electrotopological state atom type descriptors, 9th (>C<), 11th (weak hydrogen bond acceptors), 13th (-CH2-), 19th (H bonded to B, Si, P, Ge, As, Se, Sn or P); one PaDEL weighted path descriptor, 10th (sum of path lengths starting from nitrogens); and one topological charge descriptor, 12th (mean topological charge index of order 1).
Figure 1. The twenty most important 1D&2D +RDF descriptors selected in RF classification models, where the first three descriptors in terms of importance are three Burden-modified eigenvalue descriptors weighted by relative I-state, mass and Sanderson electronegativities, respectively; there are several Broto–Moreau autocorrelations 4th–5th, 7th–8th, 14th, 16th–18th, 20th weighted by I-state, mass, mass, first ionization potential, mass, polarizabilities, charge, Sanderson electronegativities and I-state; two Moran autocorrelation descriptors, 6th and 15th weighted by charge and mass, respectively; four electrotopological state atom type descriptors, 9th (>C<), 11th (weak hydrogen bond acceptors), 13th (-CH2-), 19th (H bonded to B, Si, P, Ge, As, Se, Sn or P); one PaDEL weighted path descriptor, 10th (sum of path lengths starting from nitrogens); and one topological charge descriptor, 12th (mean topological charge index of order 1).
Marinedrugs 20 00129 g001
Marinedrugs 20 00129 g002 550
Figure 2. Chemical structure of the morpholine derivative.
Figure 2. Chemical structure of the morpholine derivative.
Marinedrugs 20 00129 g002
Marinedrugs 20 00129 g003 550
Figure 3. Interaction profiles of the best-docked poses for the two hits (a) cylindramide and (b) haliclamine B.
Figure 3. Interaction profiles of the best-docked poses for the two hits (a) cylindramide and (b) haliclamine B.
Marinedrugs 20 00129 g003
Marinedrugs 20 00129 g004 550
Figure 4. Interaction profiles of the best-docked poses for the two macrocyclic hits (cylindramide and haliclamine B), the best non-macrocycle hit (indole derivative) and the positive (synoxazolidinone A and C; donepezil) and negative (phenolic derivative) controls.
Figure 4. Interaction profiles of the best-docked poses for the two macrocyclic hits (cylindramide and haliclamine B), the best non-macrocycle hit (indole derivative) and the positive (synoxazolidinone A and C; donepezil) and negative (phenolic derivative) controls.
Marinedrugs 20 00129 g004
Table
Table 1. Structural clusters and antifouling activity class counts within the seven structural clusters.
Table 1. Structural clusters and antifouling activity class counts within the seven structural clusters.
Clusters 1# 2 (Active Class)Average MW (Da) 3Average ALogP 4
TrTeTrTeTrTe
I—acyclic derivative
Marinedrugs 20 00129 i001		11 (11)0 (0)361.6502.860
II—O-heterocyclic derivative
Marinedrugs 20 00129 i002		28 (9)3 (1)328.09334.643.183.22
III—N-heterocyclic derivative
Marinedrugs 20 00129 i003		19 (14)1 (0)363.92493.042.503.65
IV—terpenoid derivative
Marinedrugs 20 00129 i004		22 (5)6 (3)264.64341.763.004.49
V—diketopiperazine derivative
Marinedrugs 20 00129 i005		15 (10)3 (2)392.54415.153.063.10
VI—chalcone derivative
Marinedrugs 20 00129 i006		16 (3)0 (0) 352.3704.560
VII—miscellaneous16 (5)1 (0)1164.53975.69−0.88−1.57
1 Cluster code and chemical structure of the cluster scaffold. 2 Number of molecules in the training (Tr) and the test (Te) sets. 3 Molecular weight (MW) within the cluster for the training and test sets. 4 Octanol–water partition coefficient prediction within the cluster for the training and test sets.
Table
Table 2. Evaluation of the predictive performance of FPs and 1D&2D molecular descriptors for modeling the antifouling activity using the RF algorithm for the training set with an OOB estimation. The best models are highlighted in bold.
Table 2. Evaluation of the predictive performance of FPs and 1D&2D molecular descriptors for modeling the antifouling activity using the RF algorithm for the training set with an OOB estimation. The best models are highlighted in bold.
Descriptors (#)TP 1TN 2FN 3FP 4SE 5SP 6Q 7MCC 8
MACCS (166) 9415116190.7190.7290.7240.446
Sub (307) 9415316170.7190.7570.7400.476
PubChem (881) 9434814220.7540.6860.7170.438
CDK (1024) 9424715230.7370.6710.7010.406
ExtCDK (1024) 9414916210.7190.7000.7090.417
1D&2D (1376)405317170.7020.7570.7320.459
1 True positive. 2 True negative. 3 False negative. 4 False positive. 5 Sensitivity, the ratio of true positive to the sum of true positive and false positive. 6 Specificity, the ratio of true negative to the sum of true negative and false negative. 7 Overall predictive accuracy, the ratio of the sum of true positive and true negative to the sum of true positive, true negative, false positive and false negative. 8 Matthews correlation coefficient. 9 Fingerprints, FPs.
Table
Table 3. Evaluation of the predictive performance of RDF descriptors and descriptor selection for modeling the antifouling activity using the RF algorithm for the training set with an OOB estimation. The best models are highlighted in bold.
Table 3. Evaluation of the predictive performance of RDF descriptors and descriptor selection for modeling the antifouling activity using the RF algorithm for the training set with an OOB estimation. The best models are highlighted in bold.
Model#SE 1SP 2Q 3MCC 4
Sub + RDF6910.6670.7140.6930.380
Selection 5500.6670.7140.6930.380
Selection 51000.6840.7570.7240.442
Selection 51500.7020.7860.7480.489
Selection 52000.6840.7570.7240.442
ExtCDK + RDF14080.6670.7430.7090.410
Selection 5120.7540.7290.7400.481
Selection 5250.7370.7860.7640.523
Selection 5500.7020.7710.7400.474
Selection 51000.6840.7710.7320.457
1D&2D + RDF17600.7190.7140.7170.432
Selection 5500.8070.8000.8030.605
Selection 51000.8250.7860.8030.607
Selection 51500.8070.8000.8030.605
Selection 52000.8420.7860.8110.625
Selection 52500.7720.8000.7870.571
1 Sensitivity, the ratio of true positive to the sum of true positive and false positive. 2 Specificity, the ratio of true negative to the sum of true negative and false negative. 3 Overall predictive accuracy, the ratio of the sum of true positive and true negative to the sum of true positive, true negative, false positive and false negative. 4 Matthews correlation coefficient. 5 The descriptor selection was evaluated based on the importance assigned by the RF model with the R program.
Table
Table 4. Exploration of different ML algorithms using the 200 selected descriptors.
Table 4. Exploration of different ML algorithms using the 200 selected descriptors.
ModelSE 1SP 2Q 3MCC 4
RF0.6670.7500.7140.417
SVM0.8300.5000.6430.344
dMLP0.6700.7500.7140.417
1 Sensitivity, the ratio of true positive to the sum of true positive and false positive. 2 Specificity, the ratio of true negative to the sum of true negative and false negative. 3 Overall predictive accuracy, the ratio of the sum of true positive and true negative to the sum of true positive, true negative, false positive and false negative. 4 Matthews correlation coefficient.
Table
Table 5. The predictions of the best RF model by the seven structural clusters for the training and test sets. The best models are highlighted in bold.
Table 5. The predictions of the best RF model by the seven structural clusters for the training and test sets. The best models are highlighted in bold.
Cluster#SE 1SP 2Q 3MCC 4
Training set
I111.000-1.0001.000
II280.8890.7890.8210.640
III191.0000.4000.8420.574
IV220.8000.9410.9090.741
V150.9000.0000.600-
VI160.0001.0000.813-
VII160.4000.8120.6880.234
All0.8420.7860.8110.625
Test set
II31.0001.0001.0001.000
III1-1.0001.0001.000
IV60.3331.0000.6670.447
V31.0000.0000.667-
VII1-0.0000.000-
All0.6670.7500.7130.417
1 Sensitivity, the ratio of true positive to the sum of true positive and false positive. 2 Specificity, the ratio of true negative to the sum of true negative and false negative. 3 Overall predictive accuracy, the ratio of the sum of true positive and true negative to the sum of true positive, true negative, false positive and false negative. 4 Matthews correlation coefficient.
Table
Table 6. Structures and calculated free binding energies (∆GB, in kcal/mol) of the sixteen selected MNPs, the positive (synoxazolidinone A and C; donepezil) and negative (phenolic derivative) controls.
Table 6. Structures and calculated free binding energies (∆GB, in kcal/mol) of the sixteen selected MNPs, the positive (synoxazolidinone A and C; donepezil) and negative (phenolic derivative) controls.
CASChemical StructureName/Structural
Category		Natural SourceProb_A∆GB (kcal/mol) 1
147362-39-8 Marinedrugs 20 00129 i007cylindramide/lactammarine sponge 20.684−11.3
126622-63-7 Marinedrugs 20 00129 i008haliclamine B/macrocyclic
alkaloid		marine sponge 30.682−8.2
126622-64-8 Marinedrugs 20 00129 i009haliclamine A/macrocyclic
alkaloid		marine sponge 30.682−7.8
156310-18-8 Marinedrugs 20 00129 i010ingamine B/macrocyclic
alkaloid		marine sponge 40.682−7.8
155944-26-6 Marinedrugs 20 00129 i011madangamines A/macrocyclic alkaloidmarine sponge 40.694−7.7
105305-54-2 Marinedrugs 20 00129 i012serain 3/
macrocyclic
alkaloid		marine sponge 50.686−7.5
142677-10-9 Marinedrugs 20 00129 i013chondriamide B/indolered alga 60.682−7.5
134029-43-9 Marinedrugs 20 00129 i014nortopsentin A/indolemarine sponge 70.702−7.3
134029-44-0 Marinedrugs 20 00129 i015nortopsentin B/indolemarine sponge 70.698−7.3
134029-45-1 Marinedrugs 20 00129 i016nortopsentin C/indolemarine sponge 70.700−7.3
105418-77-7 Marinedrugs 20 00129 i017serain 1/
macrocyclic
alkaloid		marine sponge 50.686−7.2
142677-09-6 Marinedrugs 20 00129 i018chondriamide A/indolered alga 60.682−7.2
223596-72-3 Marinedrugs 20 00129 i019isobromodeoxytopsent/
indole		marine sponge 80.680−7.2
134779-34-3 Marinedrugs 20 00129 i020nortopsentin D/indolemarine sponge 70.688−7.1
157536-35-1 Marinedrugs 20 00129 i021keramaphidin B/macrocyclic alkaloidmarine sponge 90.684−7.1
59697-14-2 Marinedrugs 20 00129 i022nemertelline/
pyridine		marine worm 100.680−7.0
positive control Marinedrugs 20 00129 i023synoxazolidinone A--−6.5
positive control Marinedrugs 20 00129 i024synoxazolidinone C--−6.7
positive control Marinedrugs 20 00129 i025donepezil--−6.5
negative control Marinedrugs 20 00129 i026phenolic--−5.1
1 AChE enzyme: center X: 25.435 Y: 69.621 Z: 278.986; 2 Halichondria cylindrata; 3 Haliclona sp.; 4 Xestospongia ingens; 5 Reniera sarai; 6 Chondria sp.; 7 Spongosorites ruetzleri and Haliclona sp.; 8 Spongosorites sp.; 9 Amphimedon sp.; 10 Amphiporus angulatus.
Table
Table 7. Hyperparameter settings of the best dMLP model.
Table 7. Hyperparameter settings of the best dMLP model.
HyperparameterSetting
InitializerGlorot uniform
Number of hidden layers2
Number of neurons in the 1st and 2nd layers200
Number of neurons in the 3rd2
Activation 1st–2nd layersRelu
Activation 3rd layerSigmoid
Batch size36
OptimizerAdadelta
LossBinary crossentropy
Epochs100
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Gaudêncio, S.P.; Pereira, F. Predicting Antifouling Activity and Acetylcholinesterase Inhibition of Marine-Derived Compounds Using a Computer-Aided Drug Design Approach. Mar. Drugs 2022, 20, 129. https://doi.org/10.3390/md20020129

AMA Style

Gaudêncio SP, Pereira F. Predicting Antifouling Activity and Acetylcholinesterase Inhibition of Marine-Derived Compounds Using a Computer-Aided Drug Design Approach. Marine Drugs. 2022; 20(2):129. https://doi.org/10.3390/md20020129

Chicago/Turabian Style

Gaudêncio, Susana P., and Florbela Pereira. 2022. "Predicting Antifouling Activity and Acetylcholinesterase Inhibition of Marine-Derived Compounds Using a Computer-Aided Drug Design Approach" Marine Drugs 20, no. 2: 129. https://doi.org/10.3390/md20020129

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop