Next Article in Journal
KRM-II-81, a β3-Preferring GABAA Receptor Potentiator, Blocks Handling-Induced Seizures in Theiler’s Murine Encephalomyelitis Virus-Infected Mice
Previous Article in Journal
Antimicrobial Activity of N-Methyl 4-Piperidone-Derived Monoketone Curcuminoids Against Cariogenic Bacteria
Previous Article in Special Issue
Effects of Polydatin on Pentylenetetrazol-Induced Seizures in Zebrafish Larvae
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

AI-Driven Chemical Design: Transforming the Sustainability of the Pharmaceutical Industry

by
Antonio Ruiz-Gonzalez
Plantion Ltd., Benfleet SS7 1LS, UK
Future Pharmacol. 2025, 5(2), 24; https://doi.org/10.3390/futurepharmacol5020024
Submission received: 16 April 2025 / Revised: 19 May 2025 / Accepted: 27 May 2025 / Published: 29 May 2025
(This article belongs to the Special Issue Feature Papers in Future Pharmacology 2025)

Abstract

:
The pharmaceutical industry faces mounting pressure to reduce its environmental impact while maintaining innovation in drug development. Artificial intelligence (AI) has emerged as a transformative tool across healthcare and drug discovery, yet its potential to drive sustainability by improving molecular design remains underexplored. This review critically examines the applications of AI in molecular design that can support in advancing greener pharmaceutical practices across the entire drug life cycle—from design and synthesis to waste management and solvent optimisation. We explore how AI-driven models are being used to personalise dosing, reduce pharmaceutical waste, and design biodegradable drugs with enhanced environmental compatibility. Significant advances have also been made in the predictive modelling of pharmacokinetics, drug–polymer interactions, and polymer biodegradability. AI’s role in the synthesis of active pharmaceutical compounds, including catalysts, enzymes, solvents, and synthesis pathways, is also examined. We highlight recent breakthroughs in protein engineering, biocatalyst stability, and heterogeneous catalyst screening using generative and language models. This review also explores opportunities and limitations in the field. Despite progress, several limitations constrain impact. Many AI models are trained on small or inconsistent datasets or rely on computationally intensive inputs that limit scalability. Moreover, a lack of standardised performance metrics and life cycle assessments prevents the robust evaluation of AI’s true environmental benefits. In particular, the environmental impact of AI-driven molecules and synthesis pathways remains poorly quantified due to limited data on emissions, waste, and energy usage at the compound level. Finally, a summary of challenges and future directions in the field is provided.

1. Introduction

Worldwide markets for active pharmaceutical ingredients are currently growing at unprecedented levels, with the sector’s annual revenue having almost quadrupled over the past two decades [1]. This market was valued at USD 1.86 trillion in 2022 [1] and is expected to increase. This growth is driven by a combination of factors, including rising healthcare demands [2], increased life expectancy [3], and technological advancements in biomedical research [4].
However, healthcare industries produce a significant amount of CO2 emissions annually. It is estimated that, on average, the healthcare sector accounts for 5% of national CO2 emissions from OECD countries, China, and India [5]. The carbon footprint from pharmaceuticals can be as high as 20%, as observed in the UK’s National Health Service (NHS) [6]. Globally, the emission intensity from the pharmaceutical industry is about 55% higher than that of the automotive industry, and its CO₂ footprint is forecast to triple by 2050 if left unchecked [7] according to the World Economic Forum. These figures highlight a pressing need to rethink how drugs are discovered, manufactured, and administered.
Wynendaele et al. [8] proposed ten elements that define sustainability within drug discovery. These include (1) ecological–environmental impact (benign-by-design); (2) medical needs; (3) green chemistry; (4) artificial intelligence and big data; (5) the root cause of illness; (6) risk- and decision-taking models; (7) biomarkers and bioinformatics to support precision medicine; (8) cost-effectiveness; (9) the lean discovery process; (10) responsible research and innovation. These principles evidence that incorporating sustainability into drug discovery is a multifaceted and urgent challenge that interfaces with every step on the development journey, from energy use and material inputs to waste management, toxicity, and ecosystem disruption. The interest in sustainability in the drug discovery pipeline has greatly grown within the past few years, and there is a consensus around the need for more sustainable practices in pharmaceutical development. Moreover, recent policy changes show promise to reduce the environmental impact of the industry, especially in climate change, biodiversity loss, wildlife decline, and environmental pollution. This is a consequence of pharmaceutical life cycles being mostly driven by legislative measures [9]. Multiple policy frameworks have also been co-developed for pharmaceutical prescribing, with a focus on preventing pollution and reducing environmental impact [10]. However, public awareness of the impact of the pharmaceutical industry, especially on the presence of residues in drinking water, remains poor in multiple geographies [11,12].
The integration of artificial intelligence (AI) is emerging as a transformative tool for enabling sustainability across the drug development pipeline. AI models can accelerate the discovery of novel compounds, reduce experimental waste, optimise synthesis pathways, and predict properties such as toxicity, biodegradability, or pharmacokinetics [13]. This review summarises the latest advances in molecular design and clinical AI algorithms with a potential impact on the sustainability of the pharmaceutical industry. We cover every aspect of the drug development journey, from the discovery and exploration of appropriate solvents and catalysts to the resulting waste and strategies to mitigate environmental impact. The manuscript is organised as follows: Initially, advances in drug waste reduction are described, either through dosage optimisation or the design of biodegradable drugs. We describe approaches to optimise the materials required in the synthesis of drugs, focusing on biocatalysts (enzymes) and heterogeneous catalysts. We then review advances in synthesis optimisation, including the incorporation of AI in the design of new drugs, solvents, and optimised synthetic pathways. Finally, a summary of limitations, opportunities, and future perspectives of the field is provided.

2. Background Information on AI Models and Key Concepts

Artificial intelligence and machine learning have crucial roles in modern pharmaceutical research. Multiple models are used nowadays to estimate numerical outcomes (regression) or categorical labels (classification) based on patterns from a training set. Some of the most commonly used models include the following:
-
Deep Neural Networks (DNNs) are versatile architectures composed of multiple hidden layers, capable of learning complex, non-linear relationships in data. They are used for both regression (i.e., predicting solubility or melting point) and classification (i.e., toxic, non-toxic substances). DNNs are especially powerful when working with large, high-dimensional datasets such as molecular fingerprints [14].
-
Extreme Gradient Boosting (XGBoost) is mainly used with structured data and is widely applied in regression tasks (i.e., predicting pharmacokinetic parameters), as well as in classification problems (i.e., drug–target interaction) [15].
-
Support Vector Machines (SVMs) are supervised algorithms that can operate as classifiers or regressors. In drug discovery, they are often used in classification tasks (i.e., active vs. inactive compounds), but they are also applicable in regression settings (i.e., estimating binding affinity or partition coefficients). SVMs perform well in high-dimensional spaces and with small-to-medium-sized datasets [16].
-
Random Forests are ensemble models that build multiple decision trees and average their outputs for regression or vote for classification. They are robust to overfitting, handle missing values well, and are commonly used in tasks such as predicting biodegradability, toxicity, or release profiles in drug delivery systems [17].
Among the most transformative AI approaches are generative models, which learn data distributions and can propose novel compounds with desired properties. These include architectures like Generative Adversarial Networks (GANs), variational autoencoders (VAEs), and diffusion models. In pharmaceutical contexts, they are used to propose new molecular structures, reaction pathways, or polymer designs tailored for biodegradability or low environmental persistence. A subset of generative models, language models (LMs), has demonstrated particular success in molecular and protein design [18]. Initially developed for natural language processing, LMs such as GPT or BERT have been adapted to “learn” molecular syntax or protein sequences, enabling the design of synthetic enzymes and prediction of drug-like molecule behaviour. These models, especially when scaled to billions of parameters, show remarkable generalisation, allowing for zero-shot predictions and novel molecule generation without explicit prior examples.
To offer an objective and robust comparison between models, multiple metrics have been developed and are frequently reported. These include regression-based measures, such as Mean Absolute Error (MAE), Root Mean Squared Error (RMSE), Mean Relative Error (MRE), and Mean Absolute Percentage Error (MAPE), which quantify deviations between predicted and observed values. These metrics quantify the deviation between predicted and actual observed values:
-
Mean Absolute Error (MAE) measures the average magnitude of errors between predicted and true values. It is robust to outliers and provides a straightforward interpretation in the same units as the output variable. It is calculated as in (Equation (1)):
M A E = 1 n i = 1 n | y i y ^ i |
where y ^ i represent the predicted values, y i represents the actual values, and n is the number of samples.
-
Root Mean Squared Error (RMSE) is calculated as the square root of the average of the squared differences between the predicted and actual values. This value is more sensitive to outliers than MAE (Equation (2)):
R M S E = 1 n i = 1 n ( y i y ^ i ) 2
-
Mean Relative Error (MRE) expresses the absolute error as a proportion of the true value, averaged across all samples (Equation (3)):
M R E = 1 n i = 1 n | y i y ^ i | y i
-
Mean Absolute Percentage Error (MAPE) represents the average percentage difference between the predicted and actual values (Equation (4)):
M A P E = 100 n i = 1 n | y i y ^ i | y i
In addition to the above-mentioned absolute and relative error metrics, model performance can be evaluated using statistical and probabilistic measures such as R-squared (R2) for regression algorithms and Receiver Operating Characteristic (ROC) curves and the Area Under the Curve (AUC) for classification tasks. R2, a statistical measure of fit, evaluates how well model predictions explain variability in the data. It quantifies the proportion of variance in the dependent variable that is predictable from the independent variables (Equation (5)):
R 2 = 1 i = 1 n ( y i y ^ i ) 2 i = 1 n ( y i y ¯ ) 2
where y ¯ represents the mean of the observed data. For classification models, metrics such as Sensitivity, Specificity, Receiver Operating Characteristic (ROC) curves, and Area Under the ROC Curve (AUC) are used to assess discriminatory power:
-
ROC Curves (Receiver Operating Characteristic) are used for binary classification problems. They are graphical representations of the True Positive Rate (Sensitivity) against the False Positive Rate (1 − Specificity) at various threshold settings.
-
AUC (Area Under the ROC Curve) summarises the ROC curve into a single number ranging from 0 to 1. It represents the probability that a randomly chosen positive instance is ranked higher than a randomly chosen negative one. Values equal or below 0.5 indicate that the model has no ability to discriminate between categories.
Beyond model evaluation, life cycle assessment (LCA) provides a critical framework for assessing the full environmental impact of pharmaceuticals, from raw material extraction to disposal. It is a systematic methodology used to evaluate the environmental impacts associated with all stages of a product’s life, from the extraction of raw materials to its production, distribution, use, and end-of-life disposal or recycling [19].

3. Optimisation of Synthetic Routes

One of the future applications of AI in organic synthesis, and the development of pharmaceuticals, is the optimisation of chemical reactions, including designing new synthetic pathways and optimising existing reactions. Algorithms have been used, for example, to improve the yield and selectivity of reactions [20], which could reduce waste and energy expenditure. The yields obtained in the development of pharmaceuticals are generally low due to a number of factors:
  • Molecular Complexity: Many pharmaceutical compounds have intricate structures with multiple functional groups. While these complex structures have been associated with higher selectivity [21], it makes their synthesis challenging.
  • Multi-Step Synthesis: Drug molecules often require multiple synthetic steps, each with its own inefficiencies, side reactions, and purification losses [22,23].
  • Chirality and Selectivity: Over half of drugs require specific stereochemistry [24], meaning that reactions must favour the desired enantiomer or diastereomer, which can reduce the effective yield.
  • Purification Losses: Rigorous purification steps are needed to meet regulatory purity requirements, leading to additional material loss [25].
The use of catalysts can improve the yield of drug synthesis. It is estimated that around 90% of chemicals, including pharmaceuticals, derive from catalytic processes [26]. These include the use of biocatalysts, such as enzymes, or heterogeneous catalysts. Catalysts can boost the efficiency of synthetic processes and reduce environmental impact by minimising energy requirements. The synthetisation process of drugs contributes significantly to the CO2 production of pharmaceutical companies. This CO2 is generally a consequence of the reagents, solvents, and transport required. A life cycle study of a prostate cancer drug found its emissions per declared unit (blisters) to be equal to 34 kg CO2eq, with intermediate and active pharmaceutical ingredient synthesis being the largest contributors to this footprint (about 96%) [27]. However, the use of AI in the development and optimisation of new catalysts is still in the early stages.

3.1. Biocatalyst Design

Enzymes play a pivotal role in the synthesis of pharmaceuticals, especially in stereoselective reactions [28]. Enzymatic processes help improve reaction efficiency, reduce waste, and offer a greener alternative to traditional chemical synthesis [29]. Some examples of pharmaceuticals developed using enzymatic reactions include ibuprofen, where the use of an enzymatic catalyst has been shown to improve the sustainability of production [30]; L-DOPA, used as cardio stimulant [31]; and statins [32], among others. However, the number of drug synthesis pathways that can be improved through enzymatic catalysis is limited, and our ability to optimise reactions is limited to current methods to evolve enzymes. While some methods have been developed to develop new enzymes, including random mutagenesis [33] and recombination [34], their yields are suboptimal, leading to high resource and time requirements.
New AI models trained on protein sequences and conformation information can speed up the development of new enzymes by predicting their performance in silico. So far, multiple models, including adversarial networks, language models, variational autoencoders, and maximum entropy models, have been used in this field, each offering distinct advantages for modelling sequence–function relationships and exploring protein fitness landscapes [35]. In particular, language models are one of the most widespread algorithms used in the development of generative models for protein design. These models have been successful in the modification of proteins to obtain functional enzymes with desired properties, as well as the de novo design of proteins. Munsamy et al. [36] developed a conditional language model for the design of artificial enzymes. The ZymCTRL model developed by this team could generate active enzymes even when sequence identities were below 40% [37]. This concept was demonstrated by the design of carbonic anhydrases and lactate dehydrogenases. Moreover, Madani et al. [38] developed ProGen, that uses autoregressive LLMs to generate protein sequences with predictable functions. This model was trained on 280 million protein sequences and could produce curated protein sequences to generate lysosome analogues. Beyond language models, diffusion-based generative models have also been explored for protein engineering. These models, originally developed for high-fidelity image synthesis, have been adapted to operate in sequence or structure space, allowing for fine-grained control over protein design. Notably, diffusion models have been applied to the modification of cytochrome P450 enzymes, leading to engineered variants with enhanced biocatalytic activity toward flavonoid substrates [39].
AI in de novo protein design has also become of great interest within recent years, opening up a wealth of possibilities in the development of custom-made enzymes that can catalyse key reactions to produce molecules of interest for the pharmaceutical industry. The ability of these models to generate functional proteins has already been demonstrated. The recently published ESM3 generative model, for example, could generate a new green fluorescent protein, with a distance from existing proteins equivalent to simulating over 500 million years of evolution [40]. Moreover, Lauko et al. [41] designed de novo enzymes to mimic the serine hydrolase function, with catalytic efficiencies (kcat/km) up to 3.8 × 103 M−1 s−1 (Figure 1a). One of the limitations of these models is their high computational requirements. The ESM3 model was trained on 3.15 billion protein sequences, 236 million protein structures, and 539 million proteins with function annotations [40].
Another application of AI in enzyme design focuses on the enhancement of enzyme properties, particularly catalytic stability. Catalytic stability refers to the ability of an enzyme to retain its catalytic activity over extended periods and under a variety of physicochemical conditions. This trait is of paramount importance in industrial and pharmaceutical settings, where enzymes are often required to function in non-native environments such as elevated temperatures, extreme pH values, the presence of organic solvents, or inhibitory compounds without a significant loss of activity or structural integrity.
Stability is a particularly key parameter in the development of biocatalysts for large-scale chemical synthesis, where prolonged reaction times and harsh reaction conditions are common. Enhancing enzyme lifetime is key to reducing environmental CO2 emissions. Some cradle-to-gate evaluations of enzyme production estimates that each kg of enzyme produced for synthesis releases between 1 and 10 kg eCO2 [42]. These emissions can be even higher (between 16 and 25 kg eCO2) in the case of immobilised enzymes for pharmaceutical applications [43].
Traditional approaches to improving enzyme stability typically involve labour-intensive cycles of mutagenesis and screening, often limited by the size of sequence space that can be experimentally explored [44,45]. AI-based strategies now offer an efficient alternative by enabling the predictive modelling of stabilising mutations and guiding rational protein engineering. Deep learning models trained on datasets of thermostable and non-thermostable enzymes can identify sequence motifs or structural features correlated with enhanced stability. For example, bi-long short-term memory algorithms have been used to predict thermostability by mining hidden features that can be used to build a network classifier and distinguish between thermostable (active beyond 40 °C) and non-thermostable proteins [46]. Bayesian optimisation techniques have also been introduced to explore fitness landscapes for stability in a guided manner and determine the optimal catalytic temperature for enzymes which could be used to find favourable mutations [47]. Finally, large language models have also been incorporated in this field [48] by converting each mutant into a latent space representation. This algorithm allowed the design of a creatinase with a 10.2 °C increase in melting temperature and a 655-fold increase in half-life at 58 °C. These predictions can then be validated experimentally or integrated into directed evolution pipelines. Furthermore, structural AI tools, such as AlphaFold2, are being leveraged to assess the stability of designed sequences by modelling structural conformations and calculating their associated thermodynamic parameters. While some studies point out that AlphaFold excels at protein structure prediction, the ability to determine stability changes upon inducing mutations might be limited [49]. Nevertheless, collectively, these AI-driven approaches are streamlining the development of robust enzymes suitable for diverse applications, ranging from green chemistry to therapeutic enzyme formulations. A summary of the machine learning models trained to design enzymes is provided in Table 1.

3.2. Heterogeneous Catalyst Design

Heterogeneous catalysis, where the catalysts are used in solid form, represent around 80% of catalytic processes in industrial chemistry [51]. As such, they have been extensively used in the pharmaceutical industry, given their ability to support the synthesis of key active pharmaceutical ingredients. Some of the most used catalysts include platinum, used in the synthesis of certain antifungal medications, among others [52]; palladium, which can catalyse C-N Cross-Coupling Reactions [53]; and ruthenium, used in olefin metathesis [54].
The design of new catalysts has traditionally relied on trial and error, which has hindered the development of the field. While some in silico approaches have been proposed [55,56], computer modelling is still mainly applied to study the mechanism of catalysis after experimental results have been obtained, instead of virtual screening. Following this trend, Li. et al. [57] developed a general theory of metal–support interactions for metal catalyst supports, using a machine learning model trained on experimental results of nanoparticle adhesion to metal oxides. However, our understanding of metal catalysts and how they can be modified to enhance chemical reactions is still limited.
The research into AI models for heterogeneous catalyst discovery is complex, due to the involvement of multiple factors in the reaction pathways, including solvents, temperature, and substrates, among others. Moreover, these models often require molecular descriptors that require expensive computing (i.e., DFT, molecular mechanics). Moreover, there is a growing pool of chemical information, both for ligands tested on different catalysts and materials that can be used as substrates, that increases the demand for computing resources. Multiple public databases have been published, such as the CHGNet [58], M3GNet [59], or the Open Catalyst Project [60], among others. Consequently, it is estimated that the search for catalysts with desired functions is more computationally demanding compared to API discovery [61]. This has also led to most material screening approaches based on modelling-based approaches being limited, with potential artefacts that limit the discovery of catalysts [62].
One of the most prominent uses of AI in this area is the screening of the “chemical space” to identify the most optimal set of parameters and construct the chemical space for model training. An alternative which can reduce the need for complex quantum mechanical calculations is the use of machine learning potentials [63]. These are used as surrogate models to increase computational speed, enabling the exploration of large search spaces and the optimisation of catalyst structures [62].
Additionally, AI has been employed to leverage empirical data from the scientific literature to optimise catalyst synthesis conditions. For example, Lai et al. [64] combined Bayesian optimisation with LLMs to automate information extraction from published studies, subsequently identifying conditions that optimised ammonia synthesis using Co3Mo3 (Figure 1b). This approach then provided a set of conditions that could maximise ammonia synthesis using Co3Mo3. LLMs have also been used by Wang et al. [65] to provide insights into the design of new electrocatalytic materials by training them on published evidence. However, these approaches are limited by the heterogeneity and unstructured nature of the experimental literature, which often lacks consistent reporting standards. Addressing this, domain-specific languages have been developed to facilitate structured data extraction. As an example, the Chemical Markdown Language, developed by Park et al. [66], provides a simple syntax for experiment documentation. This enabled the training of machine learning models to design catalysts for ring-opening polymerisation and experimental validation (Figure 1c).
Despite these advances, significant challenges remain. The discovery of heterogeneous catalysts using AI is hindered by (1) the computational intensity required to generate accurate molecular descriptors and (2) the vastness and complexity of chemical space. A promising strategy to overcome these limitations is the integration of AI with high-throughput experimentation (HTE), which can accelerate the optimisation of catalytic reactions [67]. However, this integration introduces additional logistical and data management challenges, including experimental reproducibility, the standardisation of protocols, and seamless data flow between experimental and computational platforms.
Figure 1. (a) A schematic representation of the protein design process using an RFdiffusion model. The model uses information from a given active site to generate a protein structure and backbone. Image reprinted with permissions from [41] (Copyright © 2025, American Association for the Advancement of Science, CC-BY 4.0 licence). (b) A schematic representation of an AI-driven workflow for catalyst design and optimisation, using Bayesian optimisation to speed up the discovery of materials, and real-world validation. Image reprinted with permissions from [64] (Copyright © 2023, American Chemical Society). (c) The tree manifold projection and visualisation of the catalysts generated by a fine-tuned regression transformer model trained on historical experimental data. The colours represent the synthesisability score (1–8 scale). Image reprinted with permissions from [66] (Copyright © 2025 Springer Nature, Creative Commons Attribution 4.0 International Licence).
Figure 1. (a) A schematic representation of the protein design process using an RFdiffusion model. The model uses information from a given active site to generate a protein structure and backbone. Image reprinted with permissions from [41] (Copyright © 2025, American Association for the Advancement of Science, CC-BY 4.0 licence). (b) A schematic representation of an AI-driven workflow for catalyst design and optimisation, using Bayesian optimisation to speed up the discovery of materials, and real-world validation. Image reprinted with permissions from [64] (Copyright © 2023, American Chemical Society). (c) The tree manifold projection and visualisation of the catalysts generated by a fine-tuned regression transformer model trained on historical experimental data. The colours represent the synthesisability score (1–8 scale). Image reprinted with permissions from [66] (Copyright © 2025 Springer Nature, Creative Commons Attribution 4.0 International Licence).
Futurepharmacol 05 00024 g001
AI-enabled catalyst discovery holds considerable promise for the pharmaceutical industry, particularly in the pursuit of more sustainable and efficient drug synthesis. The ability to predict optimal catalysts and reaction conditions can reduce resource consumption, lower emissions, and shorten development timelines, key elements in the industry’s push toward net-zero targets. A summary of machine learning models trained to design heterogeneous catalysts is provided on Table 2.

4. Synthesis Optimisation

4.1. Speeding Up the Discovery of Drugs

One of the most immediate benefits of AI in the pharmaceutical industry is the faster development of drugs. The development of models to predict protein structures, such as AlphaFold 3 [68], has enabled the accurate modelling of proteins and interactions (Figure 2a,b). This has allowed for the development of models that can accurately predict drug interactions with targets and generate drugs with specific properties in terms of synthesisability or target properties (Figure 2c). Current projections estimate that, if the success rates observed between Phase I and II clinical trials from AI-discovered molecules hold, the end-to-end probabilities for a molecule to succeed across all phases would almost double, from 5–10% to 9–18% [69].
The faster development of pharmaceuticals due to accurate AI models could potentially reduce the number of laboratory tests and failed clinical trials. Current estimates may indicate a carbon consumption of 27.5 million tonnes of CO2 spanning all clinical trials [70], just under a third of the emissions of Bangladesh. AI models could also be used in the repurposing of drugs [71], which could avoid further environmental costs due to pharmaceutical production (Figure 2d). One of the limitations of current AI models in drug discovery is the lack of synthesisability considerations when designing new small molecules. Challenges in the synthesis of algorithmically developed molecules have been described since 1995 [72]. This parameter refers to how easily a given molecule can be synthesised and could lead to target drugs being difficult or impossible to synthesise. In turn, drugs with low synthesisability can be translated into costly processes, which increases their carbon footprint. To circumnavigate these challenges, multiple approaches have been developed. Parrot et al. [73] introduced a Retro Score for molecular generator algorithms, which compute synthetic accessibility scores of molecules through a retrosynthesis analysis. This score correlated well with the assessments performed by chemists and could be implemented as a constraint in complex molecular generation algorithms. Alternatively, Swanson et al. [74] assembled a database containing 132,000 molecular building blocks and 13 well-validated chemical synthesis pathways which could be used to explore a chemical space of nearly 30 billion easy-to-synthesise molecules. The team employed the resulting algorithm to design and experimentally validate 58 molecules with antibacterial activity. Models are expected to improve in accuracy as the size of the available molecule libraries increases. However, accurate measurements of CO2 derived from the training and use of these model are still required to determine the benefits of AI in the field.
Figure 2. (a) Predicted structures and interaction of designed proteins with three different ligands. Image reprinted with permissions from [68] (Copyright © 2023 American Association for the Advancement of Science, Creative Commons Attribution 4.0 International Licence). (b) Example of protein designed using Alpha Fold 3. Image reprinted with permissions from [68] (Copyright © 2023 American Association for the Advancement of Science, Creative Commons Attribution 4.0 International Licence). (c) Schematic representation of training of generative models for de novo drug design of molecules. Process includes using databases and iterating over model weight adjustments and accessibility scores to design novel drugs to meet specifications. Image reprinted with permissions from [73] (Copyright © 2023 Springer Nature, Creative Commons Attribution 4.0 International Licence). (d) Schematic representation of TxGNN processing of queries to calculate predictions for drug–disease relationships. Approach takes into account interconnectedness between both factors. Predictions from model align with off-label prescriptions from clinicians in large healthcare systems. Image reprinted with permissions from [71] (Copyright © 2024 Springer Nature, American Association for the Advancement of Science, Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International Licence).
Figure 2. (a) Predicted structures and interaction of designed proteins with three different ligands. Image reprinted with permissions from [68] (Copyright © 2023 American Association for the Advancement of Science, Creative Commons Attribution 4.0 International Licence). (b) Example of protein designed using Alpha Fold 3. Image reprinted with permissions from [68] (Copyright © 2023 American Association for the Advancement of Science, Creative Commons Attribution 4.0 International Licence). (c) Schematic representation of training of generative models for de novo drug design of molecules. Process includes using databases and iterating over model weight adjustments and accessibility scores to design novel drugs to meet specifications. Image reprinted with permissions from [73] (Copyright © 2023 Springer Nature, Creative Commons Attribution 4.0 International Licence). (d) Schematic representation of TxGNN processing of queries to calculate predictions for drug–disease relationships. Approach takes into account interconnectedness between both factors. Predictions from model align with off-label prescriptions from clinicians in large healthcare systems. Image reprinted with permissions from [71] (Copyright © 2024 Springer Nature, American Association for the Advancement of Science, Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International Licence).
Futurepharmacol 05 00024 g002

4.2. Solvent Usage

Solvents represent a major contributor to pharmaceutical synthesis. It is estimated that only around 35% of solvent waste generated by the US pharmaceutical industry is recycled, and about 45% of the energy from the incineration of the remaining 65% is recovered [75]. Solvents are used across the whole pharmaceutical synthesis process, from reactions to the extraction of compounds, and they represent the majority of mass utilisation (between 80 and 90%) [76]. An average of six different solvents is used in any given process, with dichloromethane being the most common compound. Dichloromethane is a largely unregulated ozone-depleting compound, with emissions that have increased over the years. This increase could significantly delay the recovery of the ozone layer [77]. Moreover, it has shown negative environmental and toxicological properties [78]. As such, there is a need for greener solutions to reduce the impact of solvent use in the pharmaceutical industry. AI algorithms have been employed to allow a selection of alternative solvents based on their physical–chemical properties [79]. Some advanced models can also predict reactivity rates in asymmetric catalysis [80]. However, in most cases, AI models do not include environmental considerations to support the selection of solvents.
The incorporation of deep eutectic solvents (DESs) represents a promising approach in this field. DESs are a family of green solvents made by mixing two or more components that interact through hydrogen bonding, resulting in a eutectic mixture with a melting point lower than that of its individual constituents [81]. They are considered an alternative to ionic liquids and conventional organic solvents due to their low toxicity, biodegradability, and ease of preparation [82]. Traditional industrial solvents amount to 80–90% of the total mass used during a reaction in the pharmaceutical industry, and 80–85% of the waste produced [83]. This leads to high exposure rates, either through the volatiles produced or through their presence in the environment [84]. Moreover, solvent production and disposal plays a major role in the CO2 emissions of the pharmaceutical industry. While the process material intensity for API manufacturing can vary, recent estimates indicate that approximately 40–50% of the industry’s carbon footprint can be attributed to solvent use. This is a consequence of their extensive use (accounting for 50–60% of materials required per kg of API produced) and the energy-intensive processes required for their production and waste management [75].
DESs are emerging as greener alternatives to conventional organic solvents due to their lower environmental impact and sustainability benefits. They can be made from natural sources including polyalcohols, sugars, or organic acids, including amino acids [85]. These solvents have the advantage of displaying low toxicity and having high biodegradability [85], and can potentially be synthesised through sustainable routes. However, the sustainability of these substances needs to be assessed on a case-by-case basis. In the case of citric acid, production is carried out through fermentation, leading to high water consumption (about 153 L kg−1) and releasing CO2 in the process [86].
While the development of DESs is still in an early stage, multiple applications have been described in the pharmaceutical industry, from helping in the delivery of drugs to supporting their synthesis and helping with the dissolution of reagents [87]. DESs have also been used in the extraction of bioactive compounds from plants [88], the green synthesis of pharmaceutical ingredients [89], and the solubilisation and crystallisation of pharmaceutical ingredients [90] (Figure 3a).
Despite the growing interest in DESs, their adoption in the pharmaceutical industry is limited by several challenges; the range of available DES formulations remains narrow, and their physicochemical properties need further characterisation. Additionally, regulatory approvals and industry-wide standardisation are necessary for their widespread implementation. To overcome these barriers, new methodologies for identifying and designing DES-compatible compounds must be developed. AI-driven solvent design, coupled with experimental validation, could significantly expand the repertoire of available DESs, ensuring they meet the stringent requirements of pharmaceutical applications.
New AI models have been developed to support the discovery of deep eutectic solvents with desired properties for the pharmaceutical industry. However, the limited amount of experimentally validated data represents a challenge in the development of AI algorithms for predicting DES formation. Abbas et al. [94] developed a machine learning approach to predict the formation of DESs which would allow for the discovery of new molecular candidates. This algorithm was based on modelled data on the hydrogen bond formation of compounds using molecular simulations. The library employed only included examples of 186 simulated systems and 34 experimentally verified cases as a validation dataset. Despite the limitations of the dataset, the model achieved a good performance, achieving an average ROC-AUC score of 0.8 in the validation set using the hydrogen bond lifetimes. However, this model required complex simulation data to calculate the hydrogen bonding lifetime, which could limit its scalability. Alternative approaches explored the prediction of melting temperatures for the screening of DES components. Lavrinenko et al. [95] trained a Support Vector Regression model using information from 1648 mixtures’ melting temperatures for 237 experimentally validated DESs. While the final algorithm showed good performance in the prediction of eutectic temperatures (R2 = 0.74, RMSE = 22.5), its accuracy in eutectic composition was relatively low (R2 = 0.34, RMSE = 0.11). The authors attributed these results to the limitations of the methodology, considering only the molar ratio of the lowest temperature predicted as the eutectic point. Diffusion models have also been employed which use the quantum mechanical properties of compounds (HOMO, LUMO, Free Energy, and heat capacity). These models could be used to generate new structures while achieving a good performance on prediction tasks (R2 = 0.93). However, the datasets used for training were small (402 DES compositions).
Besides the design of new DES compounds, AI has been employed to select compositions with optimal characteristics through the prediction of their physical–chemical properties (Figure 3c). Among those, density is a key parameter in the extraction and purification of chemicals, especially liquid–liquid extractions. Common methods for extraction, such as counter-current extraction columns, rely on the use of solvents with different densities for phase flow control [96]. As such, multiple models have been focused on predicting DES densities [97], as well as other relevant properties, such as heat capacity [92], among others. A summary of the machine learning models trained to optimise DES design is provided in Table 3.

4.3. Synthetic Pathway Optimisation

AI can aid in the design of efficient reaction pathways for the pharmaceutical industry. A reduction in the number of synthetic steps can contribute, for example, to reducing the amounts of solvents used during a chemical synthesis process. This has led to some companies to reducing their usage from 94 kgsolvent/kgAPI to 75 kgsolvent/kgAPI within just five years, with a consequent reduction in environmental impact [76]. AI has been used in organic chemistry for over 50 years. One of the first manuscripts in the field dates back to 1969, when Corey and Wipke developed a computer-aided synthesis planning program [103]. Since then, multiple models have been developed to simplify reaction pathways. However, the field’s evolution has progressed slowly, given the time required to evaluate results experimentally.
One of the key applications of AI in this field involves the simplification of reactions and purification processes. This approach has enabled the one-pot synthesis of trans β-lactams, which typically requires multiple steps [104]. The algorithm created reaction rules using the training set of reactions without the need for human inputs. It proposed over 2000 possible reactions, from which researchers selected a one-pot preparation route. Similarly, Takabatake et al. [105] developed a synthetic route for the common intermediate methyl 2-formylbenzofuran-7-carboxylate. However, so far, the range of reactions that can be optimised using this approach is limited due to the lack of reaction data.
To circumnavigate the challenges of the poor availability of large chemical datasets and improve the interpretability of variables across chemical spaces, multiple frameworks have been developed. King-Smith et al. [106] proposed a high-throughput experimentation method to analyse the impact of variables among different reactions. This method was able to find the most important variables for a given reaction, as well as the impact of the reagents. Thus, from reducing solvent use and synthetic complexity to enabling one-pot reactions and data-driven optimisation, AI has already demonstrated the capacity to transform traditional workflows. However, challenges remain, particularly concerning data availability and experimental validation. Addressing these limitations through collaborative efforts, such as combining high-throughput experimentation, Open Access datasets, and robust modelling frameworks, will be essential for unlocking the full potential of AI in green chemistry. As these tools continue to mature, they are poised to play a central role in creating more sustainable, efficient, and innovative pharmaceutical manufacturing processes.

5. Artificial Intelligence in Drug Waste Reduction

Waste generated from the pharmaceutical industry has a significant footprint in the environment. Some drugs, for example, can act as hormone disruptors for certain species, inducing the feminisation of male fish [107] or collapsing populations [108]. In particular, household pharmaceutical waste is becoming a global challenge given its deleterious effects and persistence in the environment. In recent years, the demand has also increased. It is estimated that the global consumption of antibiotics increased by 65% between 2000 and 2015 [109], and about three quarters of households hold, on average, 138 g of unwanted or unused drugs, of which 60% will be wasted [110]. The main sources of pharmaceuticals in the environment are human waste, including excretion through faeces and urine, and incorrect disposal [111]. As such, new strategies to minimise the release of drug components into the environment, as well as to accelerate their biodegradability, are needed.

5.1. Reduction in Drug Waste Through Dosage Optimisation

A potentially viable route to minimise pharmaceutical waste is the personalisation of patient dosage [112]. Zhu et al. [113] developed a machine learning algorithm to optimise dosage through non-invasive clinical parameters, such as demographics, age, weight, and co-medication status. The algorithm was trained using data from 1141 therapeutic drug-monitoring measurements from 347 patients, demonstrating good precision when determining the dose-adjusted concentration (Mean Absolute Error = 8.7 μg mL−1 g−1 day). However, the potential savings in environmental footprints from this approach have not yet been quantified in real-world settings. Instead, the prescription of pharmaceuticals only when they are required seems to represent a more effective approach to reducing the footprint of pharmaceuticals. AI has extensively been used in this field, incorporating patient data (i.e., age, gender, weight) as well as information from electronic records [114].
The prediction of absorption, distribution, metabolism, and excretion (ADME) represents a key tool for determining drug dosing [115]. AI-driven approaches have also demonstrated significant potential in predicting ADME properties, reducing the reliance on extensive in vitro and in vivo experiments. For instance, Satheeskumar et al. [116] tested multiple machine learning algorithms to predict clearance, volume distribution, half-life, and bioavailability, using a dataset of 10,000 compounds, with high accuracy. Alternative models have been developed recently, incorporating further molecular considerations, such as docking, and physicochemical molecular features [117]. However, there are multiple ethical considerations when using AI in prescriptions [118]. These include privacy, data protection, and the need for informed consent.
Despite the limitations, dosage prediction for particularly high-environmental-footprint compounds such as anaesthetics could lead to the greatest impact. Emissions derived from inhaled anaesthetics account for at least 3% of the total healthcare footprint [6]. While the figures of how much these gases contribute to climate change can vary greatly due to inconsistencies in the methodology used for assessment, it is estimated that they amount to 0.01–0.1% of total global greenhouse gas emissions [119], with annual emissions of 5 × 106 tonnes CO2e/y [120]. This is a consequence of the high greenhouse effect of common anaesthetic gases, such as nitrous oxide, and their long lifetimes [119]. Current models in this field have been used to predict the effects of anaesthesia in patients or to control their continuous administration [121,122]. Some of these models employ additional electroencephalogram monitoring data to predict the depth of anaesthesia [123]. However, they are focused on monitoring patient consciousness to administer gas anaesthetics, which produce high amounts of waste due to their intensive usage and uncontrolled escape into the surrounding environment, paired with the poor efficiency of scavenging systems [124]. Some studies have explored alternative methods to optimise anaesthetic administration, with the potential to reduce environmental impact. In particular, increasing the use of intravenous anaesthetic can reduce the overall consumption of volatile agents without compromising patient safety. Schamberg et al. [125] developed a reinforcement learning algorithm to improve the administration of propofol anaesthetics, leading to low performance errors (1.1% ± 0.5). This model was trained using simulated data. However, these advancements highlight the potential for reducing the environmental footprint of drug compound usage, especially anaesthesia, through predictive modelling. Moreover, the amount of experimentally validated data is low, which hinders the training of accurate models. A summary of the machine learning algorithms used in drug dosage optimisation is provided in Table 4.

5.2. Design of Biodegradable Drug Delivery Systems

While the optimisation of drug dosage can lead to a reduced waste and minimise environmental impact, most common drugs have very low biodegradability [126]. In particular, hydrophobic drugs with low water solubility have been shown to bioaccumulate, triggering concern [127]. Recent studies estimate that over 25% of rivers globally might contain active pharmaceutical ingredients at levels higher than those considered safe for aquatic life [128]. As such, the development of biodegradable drugs shows promise in mitigating the pharmaceutical environmental footprint. These are normally developed using biodegradable nanoparticles, encapsulating the drug of interest inside a polymeric matrix [129]. Traditionally, synthetic polymers such as poly (ethylene glycol) [130,131], poly (lactic acid) [132,133] or poly (lactic-co-glycolic acid) [134] have been used alone, or in combination with other matrix elements. Natural polymers such as cellulose [135] or starch [136] have also been employed. However, their use is limited due to their general variability in purity and, in some cases, the need for chemical treatments.
Biodegradable drug delivery systems have been designed using AI to allow for the precise optimisation of drug formulations, enhancing their biodegradability while maintaining therapeutic efficacy. AI-driven computational models can predict the interactions between different polymers and active pharmaceutical ingredients [137]. This interaction allows the study of drug release behaviours [138], including those of stimuli-responsive hydrogels, which ultimately enables the selection of optimal biodegradable carriers. These models could potentially be paired with recent AI algorithms to predict the biodegradability of polymers and allow for the in silico selection of the most optimal materials for drug design with a Mean Absolute Percentage Error (MAPE) between 7.6 and 16.99% [139].
Recent advancements in modelling and AI have also enabled the discovery of new biodegradable polymers by predicting the molecular structures that exhibit desirable properties, such as high drug-loading capacities and tuneable degradation rates [140]. AI can also integrate multi-objective optimisation strategies, balancing biodegradability, drug stability, and manufacturing feasibility to create next-generation eco-friendly pharmaceuticals. However, the application of AI in the drug design space, specifically to reduce the environmental impact of treatments, has been limited so far. A summary of the machine learning algorithms developed to predict drug–polymer interactions and polymer biodegradability is provided in Table 5.

6. Current Status of Molecular Design for Sustainability and Future Perspectives

The integration of sustainability into molecular design is gaining momentum across the pharmaceutical industry, driven by regulatory pressure, environmental concerns, and the need for more efficient R&D pipelines to reduce production costs. Traditionally, the discovery and optimisation of active pharmaceutical ingredients prioritised efficacy and safety, with less emphasis on the environmental impact of synthetic routes, degradation products, or raw material sourcing. However, a paradigm shift is underway. There is an increasing number of reported manuscripts focusing on how specific aspects of drug life cycles can be optimised to reduce their environmental impact. The need for this shift has been highlighted by key pharmaceutical stakeholders, including the WHO [143].
Currently, sustainable molecular design leverages advances in cheminformatics, high-throughput screening, and retrosynthetic analysis to identify and optimise molecules with improved biodegradability, lower toxicity, and reduced reliance on rare or hazardous reagents (Figure 4). Frameworks such as the ACS Green Chemistry Institute’s Pharmaceutical Roundtable (GCIPR) [144] have accelerated best practice sharing, and metrics like Process Mass Intensity (PMI) are increasingly being adopted to quantify sustainability performance [145].
AI is beginning to reshape this landscape. Machine learning models trained on large-scale chemical and biological datasets are enabling the generation of novel compound libraries optimised for pharmacological activity, synthetic tractability, and environmental compatibility. Predictive models for aqueous persistence, bioaccumulation, and toxicity are being integrated into molecular design workflows, offering a proactive approach to reducing the environmental footprint of future pharmaceuticals. However, in some cases, there are limitations regarding the size of the available datasets, which limits the accuracy of models.
Besides the need for data to enable the training of accurate models, there is a lack of life cycle assessments, especially regarding the environmental impact and standardisation of methodologies used to study drug compounds. This could reveal further challenges and unique opportunities for improvement [19]. The fusion of AI with system-level sustainability assessments and life cycle analysis holds transformative potential. Generative AI models will be able to design compounds that meet complex multi-objective criteria, including efficacy, safety, manufacturability, and sustainability [13]. Moreover, the emergence of generative models and reinforcement learning could open new frontiers in green-by-design molecules, tailored for minimal environmental impact throughout their life cycle.
To fully realise this potential, cross-sector collaboration will be essential. Interdisciplinary partnerships between computational chemists, environmental scientists, process engineers, and regulators will help ensure that AI-driven molecular design not only accelerates innovation but also aligns with broader sustainability goals. As the field evolves, the pharmaceutical industry stands at the cusp of a more responsible and resource-efficient future, where AI is not just a tool for drug discovery but a cornerstone of sustainable innovation. Moreover, Open Source initiatives making molecular information available to researchers across all fields will be key to allowing the development and training of more accurate AI models. Some examples of Open Source initiatives include the Open Reaction Database [146] or PubChem [147]. These initiatives, alongside trained online AI platforms, are playing increasingly central roles in accelerating innovation. They provide researchers with powerful tools for virtual screening, property prediction, protein structure modelling, and synthesis planning, often without the need for specialised local infrastructure. Notable examples include AlphaFold [148] for protein structure prediction, SwissADME [149] for pharmacokinetic profiling, DeepChem [150] for molecular property prediction, and ProGen [151] for designing novel protein sequences with desired functions. These platforms can lower the barrier to entry for sustainable molecular design and support the rapid prototyping of drug candidates.

7. Conclusions

AI is playing an increasingly pivotal role in enhancing the sustainability of the pharmaceutical industry. From optimising drug dosage and enabling the design of biodegradable compounds to streamlining synthesis pathways and discovering green solvents and catalysts, AI offers transformative potential across the pharmaceutical value chain. However, several systemic limitations hinder the full realisation of AI’s environmental impact. In some areas, such as in the design of deep eutectic solvents, progress is constrained by the lack of large, high-quality databases. This leads to the need to calculate quantum parameters to increase the accuracy of models. In contrast, other domains, such as enzyme engineering and catalyst discovery, involve computationally intensive models, often involving billions of parameters that require vast and complex datasets. This leads to high energy costs for training, which have not yet been fully and accurately quantified. In fact, across most applications, there is a general scarcity of robust environmental data, limiting our ability to quantify sustainability benefits.
A critical gap remains in the integration of life cycle assessments into AI-driven pharmaceutical development. The general lack of drug-specific life cycle assessments makes it challenging to evaluate the true environmental implications of AI interventions. Moreover, inconsistencies in the size, quality, and structure of training datasets, as well as the lack of standardised metrics for evaluating model performance, further complicate cross-study comparisons and model reproducibility.
Despite these limitations, the breadth of potential impact remains wide. AI can enable the multi-objective optimisation of drug candidates, balancing pharmacological efficacy with factors such as biodegradability, synthesisability, and environmental persistence. The ability to incorporate sustainability considerations into early-stage design and development offers a unique opportunity for the pharmaceutical sector to align innovation with broader climate and environmental goals.
Going forward, addressing these challenges will require coordinated efforts: expanding Open Access datasets, standardising performance metrics, incorporating sustainability endpoints into training objectives, and fostering collaboration between AI researchers, chemists, and environmental scientists. More importantly, with the right frameworks, AI can become not just a tool for faster and more effective drug discovery, but a catalyst for a more sustainable pharmaceutical future.

Funding

This research received no external funding.

Conflicts of Interest

Author Antonio Ruiz-Gonzalez works for Plantion Ltd. The company had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results. The author declares that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

  1. Stacciarini, J.H.S. The Global Pharmaceutical Sector: Numbers and dynamics. Caminhos Geogr. 2024, 25. [Google Scholar] [CrossRef]
  2. Rachet-Jacquet, L.; Rocks, S.; Charlesworth, A. Long-term projections of health care funding, bed capacity and workforce needs in England. Health Policy 2023, 132, 104815. [Google Scholar] [CrossRef] [PubMed]
  3. Stegemann, S.; van Riet-Nales, D.; de Boer, A. Demographics in the 2020s—Longevity as a challenge for pharmaceutical drug development, prescribing, dispensing, patient care and quality of life. Pharmacology 2020, 86, 1899–1903. [Google Scholar] [CrossRef] [PubMed]
  4. Benam, K.H.; Gilchrist, S.; Kleensang, A.; Satz, A.B.; Willett, C.; Zhang, Q. Exploring new technologies in biomedical research. Drug Discov. Today 2019, 24, 1242–1247. [Google Scholar] [CrossRef]
  5. Pichler, P.-P.; Jaccard, I.S.; Weisz, U.; Weisz, H. International comparison of health care carbon footprints. Environ. Res. Lett. 2019, 14, 064004. [Google Scholar] [CrossRef]
  6. Tennison, I.; Roschnik, S.; Ashby, B.; Boyd, R.; Hamilton, I.; Oreszczyn, T.; Owen, A.; Romanello, M.; Ruyssevelt, P.; Sherman, J.D.; et al. Health care’s response to climate change: A carbon footprint assessment of the NHS in England. Lancet Planet. Health 2021, 5, e84–e92. [Google Scholar] [CrossRef]
  7. Iyer, J.K. 6 Ways the Pharmaceutical Industry can Reduce Its Climate Impact. 2022. Available online: https://www.weforum.org/stories/2022/11/pharmaceutical-industry-reduce-climate-impact/ (accessed on 14 April 2025).
  8. Wynendaele, E.; Furman, C.; Wielgomas, B.; Larsson, P.; Hak, E.; Block, T.; Van Calenbergh, S.; Willand, N.; Markuszewski, M.; Odell, L.R.; et al. Sustainability in drug discovery. Med. Drug Discov. 2021, 12, 100107. [Google Scholar] [CrossRef]
  9. De Spiegeleer, B.; Wynendaele, E. Sustainability of drug discovery, development and use as embedded in European pharmaceutical policies. Curr. Opin. Green Sustain. Chem. 2025, 53, 101028. [Google Scholar] [CrossRef]
  10. Niemi, L.; Arakawa, N.; Glendell, M.; Gagkas, Z.; Gibb, S.; Anderson, C.; Pfleger, S. Co-developing frameworks towards environmentally directed pharmaceutical prescribing in Scotland—A mixed methods study. Sci. Total Environ. 2024, 955, 176929. [Google Scholar] [CrossRef]
  11. Mohd Nasir, F.A.; Praveena, S.M.; Aris, A.Z. Public awareness level and occurrence of pharmaceutical residues in drinking water with potential health risk: A study from Kajang (Malaysia). Ecotoxicol. Environ. Saf. 2019, 185, 109681. [Google Scholar] [CrossRef]
  12. Domingo-Echaburu, S.; Abajo, Z.; Sánchez-Pérez, A.; Elizondo-Alzola, U.; de la Casa-Resino, I.; Lertxundi, U.; Orive, G. Knowledge and attitude about drug pollution in pharmacy students: A questionnaire-based cross sectional study. Curr. Pharm. Teach. Learn. 2023, 15, 461–467. [Google Scholar] [CrossRef] [PubMed]
  13. Sahrawat, T.R. Role of Artificial Intelligence and Machine Learning in Sustainable Drug Discovery. Braz. Arch. Biol. Technol. 2024, 67, e24240538. [Google Scholar] [CrossRef]
  14. Askr, H.; Elgeldawi, E.; Ella, H.A.; Elshaier, Y.A.M.M.; Gomaa, M.M. Deep learning in drug discovery: An integrative review and future challenges. Artif. Intell. Rev. 2023, 56, 5975–6037. [Google Scholar] [CrossRef]
  15. Wiens, M.; Verone-Boyle, A.; Henscheid, N.; Podichetty, J.T.; Burton, J. A Tutorial and Use Case Example of the eXtreme Gradient Boosting (XGBoost) Artificial Intelligence Algorithm for Drug Development Applications. Clin. Transl. Sci. 2025, 18, e70172. [Google Scholar] [CrossRef]
  16. Heikamp, K.; Bajorath, J. Support vector machines for drug discovery. Expert Opin. Drug Discov. 2014, 9, 93–104. [Google Scholar] [CrossRef]
  17. Ahn, S.; Lee, S.E.; Kim, M.-H. Random-forest model for drug–target interaction prediction via Kullback–Leibler divergence. J. Cheminform. 2022, 14, 67. [Google Scholar] [CrossRef]
  18. Ruffolo, J.A.; Madani, A. Designing proteins with language models. Nat. Biotechnol. 2024, 42, 200–202. [Google Scholar] [CrossRef]
  19. Chen, Z.; Lian, J.Z.; Zhu, H.; Zhang, J.; Zhang, Y.; Xiang, X.; Huang, D.; Tjokro, K.; Barbarossa, V.; Cucurachi, S.; et al. Application of Life Cycle Assessment in the pharmaceutical industry: A critical review. J. Clean. Prod. 2024, 459, 142550. [Google Scholar] [CrossRef]
  20. Struble, H.G.J.; Coley, C.W.; Green, Y.W.H.; Jensen, K.F. Using Machine Learning to Predict Suitable Conditions for Organic Reactions. ACS Cent. Sci. 2018, 4, 1465–1476. [Google Scholar]
  21. Méndez-Lucio, O.; Medina-Franco, J.L. The many roles of molecular complexity in drug discovery. Drug Discov. Today 2017, 22, 120–126. [Google Scholar] [CrossRef]
  22. Bloemendal, V.R.L.J.; Janssen, M.A.C.H.; van Hest, J.C.M.; Rutjes, F.P.J.T. Continuous one-flow multi-step synthesis of active pharmaceutical ingredients. React. Chem. Eng. 2020, 5, 1186–1197. [Google Scholar] [CrossRef]
  23. Roy, J. Pharmaceutical impurities—A mini-review. AAPS PharmSciTech 2002, 3, 6. [Google Scholar] [CrossRef] [PubMed]
  24. Senkuttuvan, N.; Komarasamy, B.; Krishnamoorthy, R.; Sarkar, S.; Dhanasekarand, S.; Anaikutti, P. The significance of chirality in contemporary drug discovery-a mini review. RSC Adv. 2024, 14, 33429–33448. [Google Scholar] [CrossRef]
  25. Portoghese, P.S. Revision of Purity Criteria for Tested Compounds. J. Med. Chem. 2009, 52, 1. [Google Scholar] [CrossRef]
  26. Alcántara, A.R. Special Issue Entitled “10th Anniversary of Catalysts: Recent Advances in the Use of Catalysts for Pharmaceuticals”. Catalysts 2024, 14, 161. [Google Scholar] [CrossRef]
  27. Verlinden, A.; Boone, L.; De Soete, W.; Dewulf, J. Environmental impacts of drug products: The effect of the selection of production sites in the supply chain. Sustain. Prod. Consum. 2024, 52, 1–11. [Google Scholar] [CrossRef]
  28. Reetz, M.T.; Qu, G.; Sun, Z. Engineered enzymes for the synthesis of pharmaceuticals and other high-value products. Nat. Synth. 2024, 3, 19–32. [Google Scholar] [CrossRef]
  29. Alcántara, A.R. Biocatalysis and Pharmaceuticals: A Smart Tool for Sustainable Development. Catalysts 2019, 9, 792. [Google Scholar] [CrossRef]
  30. Grimaldi, F.; Tran, N.N.; Sarafraz, M.M.; Lettieri, P.; Gonzalez, O.M.M.; Hessel, V. Life Cycle Assessment of an Enzymatic Ibuprofen Production Process with Automatic Recycling and Purification. ACS Sustain. Chem. Eng. 2021, 9, 13135–13150. [Google Scholar] [CrossRef]
  31. Kumagai, H.; Katayama, T.; Koyanagi, T.; Suzuki, H. Research overview of L-DOPA production using a bacterial enzyme, tyrosine phenol-lyase. Proc. Jpn. Acad. Ser. B 2023, 99, 75–101. [Google Scholar] [CrossRef]
  32. García-Bofill, M.; Sutton, P.W.; Guillén, M.; Álvaro, G. Enzymatic synthesis of a statin precursor by immobilised alcohol dehydrogenase with NADPH oxidase as cofactor regeneration system. Appl. Catal. A Gen. 2021, 609, 117909. [Google Scholar] [CrossRef]
  33. Zhao, S.; Tan, M.-Z.; Wang, R.-X.; Ye, F.-T.; Chen, Y.-P.; Luo, X.-M.; Feng, J.-X. Combination of genetic engineering and random mutagenesis for improving production of raw-starch-degrading enzymes in Penicillium oxalicum. Microb. Cell Factories 2022, 21, 272. [Google Scholar] [CrossRef] [PubMed]
  34. Moore, J.C.; Jin, H.-M.; Kuchner, O.; Arnold, F.H. Strategies for the in vitro evolution of protein function: Enzyme evolution by random recombination of improved sequences. J. Mol. Biol. 1997, 272, 336–347. [Google Scholar] [CrossRef]
  35. Xie, W.J.; Warshel, A. Harnessing generative AI to decode enzyme catalysis and evolution for enhanced engineering. Natl. Sci. Rev. 2023, 10, nwad331. [Google Scholar] [CrossRef]
  36. Munsamy, G.; Lindner, S.; Lorenz, P.; Ferruz, N. ZymCTRL: A conditional language model for the controllable generation of artificial enzymes. In Proceedings of the NeurIPS Machine Learning in Structural Biology Workshop, New Orleans, LA, USA, 3 December 2022. [Google Scholar]
  37. Munsamy, G.; Illanes-Vicioso, R.; Funcillo, S.; Nakou, I.T.; Lindner, S.; Ayres, G.; Sheehan, L.S.; Moss, S.; Eckhard, U.; Ferruz, N. Conditional language models enable the efficient design of proficient enzymes. bioRxiv 2024. [Google Scholar] [CrossRef]
  38. Madani, A.; Krause, B.; Greene, E.R.; Subramanian, S.; Mohr, B.P.; Holton, J.M.; Olmos, J.L., Jr.; Xiong, C.; Sun, Z.Z.; Socher, R.; et al. Large language models generate functional protein sequences across diverse families. Nat. Biotechnol. 2023, 41, 1099–1106. [Google Scholar] [CrossRef]
  39. Wang, Q.; Liu, X.; Zhang, H.; Chu, H.; Shi, C.; Zhang, L.; Bai, J.; Liu, P.; Li, J.; Zhu, X.; et al. Cytochrome P450 Enzyme Design by Constraining the Catalytic Pocket in a Diffusion Model. Research 2024, 7, 0413. [Google Scholar] [CrossRef]
  40. Hayes, T.; Rao, R.; Akin, H.; Sofroniew, N.J.; Oktay, D.; Lin, V.O.R.I.P.; Verkuil, R.; Tran, V.Q.; Deaton, J.; Wiggert, M.; et al. Simulating 500 million years of evolution with a language model. Science 2025, 387, 850–858. [Google Scholar] [CrossRef]
  41. Lauko, A.; Pellock, S.J.; Sumida, K.H.; Anishchenko, I.; Juergens, D.; Ahern, W.; Jeung, J.; Shida, A.F.; Hunt, A.; Kalvet, I.; et al. Computational design of serine hydrolases. Science 2025, 388, eadu2454. [Google Scholar] [CrossRef]
  42. Nielsen, P.H.; Oxenbøll, K.M.; Wenzel, H. Cradle-to-gate environmental assessment of enzyme products produced industrially in denmark by novozymes A/S. Int. J. Life Cycle Assess. 2007, 12, 432–438. [Google Scholar] [CrossRef]
  43. Kim, S.; Jiménez-González, C.; Dale, B.E. Enzymes for pharmaceutical applications—A cradle-to-gate life cycle assessment. Int. J. Life Cycle Assess. 2009, 14, 392–400. [Google Scholar] [CrossRef]
  44. Vanella, R.; Küng, C.; Schoepfer, A.A.; Doffini, V.; Nash, J.R.M.A. Understanding activity-stability tradeoffs in biocatalysts by enzyme proximity sequencing. Nat. Commun. 2024, 15, 1807. [Google Scholar] [CrossRef] [PubMed]
  45. Wilkinson, H.C.; Dalby, P.A. Fine-tuning the activity and stability of an evolved enzyme active-site through noncanonical amino-acids. FEBS J. 2021, 288, 1935–1955. [Google Scholar] [CrossRef] [PubMed]
  46. Xiang, X.; Gao, J.; Ding, Y. DeepPPThermo: A Deep Learning Framework for Predicting Protein Thermostability Combining Protein-Level and Amino Acid-Level Features. J. Comput. Biol. 2023, 31, 147–160. [Google Scholar] [CrossRef]
  47. Nielsen, G.L.S.R.; Engqvist, M.K.M. Machine Learning Applied to Predicting Microorganism Growth Temperatures and Enzyme Catalytic Optima. ACS Synth. Biol. 2019, 8, 1411–1420. [Google Scholar]
  48. Bian, J.; Tan, P.; Nie, T.; Hong, L.; Yang, G.-Y. Optimizing enzyme thermostability by combining multiple mutations using protein language model. mLife 2024, 3, 492–504. [Google Scholar] [CrossRef]
  49. Pak, M.A.; Markhieva, K.A.; Maksimova, E.S.; Kondrashov, F.A.; Ivankov, D.N. Using AlphaFold to predict the impact of single mutations on protein stability and function. PLoS ONE 2023, 18, e0282689. [Google Scholar] [CrossRef]
  50. Repecka, D.; Jauniskis, V.; Karpus, L.; Rembeza, E.; Rokaitis, I.; Zrimec, J.; Poviloniene, S.; Laurynenas, A.; Viknander, S.; Abuajwa, W.; et al. Expanding functional protein sequence spaces using generative adversarial networks. Nat. Mach. Intell. 2021, 3, 324–333. [Google Scholar] [CrossRef]
  51. Li, H. AI unveils metal-support interaction principle to optimize catalyst design. Chem Catal. 2025, 5, 101231. [Google Scholar] [CrossRef]
  52. Marguí, E.; Queralt, I.; Hidalgo, M. Determination of platinum group metal catalyst residues in active pharmaceutical ingredients by means of total reflection X-ray spectrometry. Spectrochim. Acta Part B At. Spectrosc. 2013, 86, 50–54. [Google Scholar] [CrossRef]
  53. Ruiz-Castillo, P.; Buchwald, S.L. Applications of Palladium-Catalyzed C–N Cross-Coupling Reactions. Chem. Rev. 2016, 116, 12564–12649. [Google Scholar] [CrossRef] [PubMed]
  54. Ogba, O.M.; Warner, N.C.; O’leary, D.J.; Grubbs, R.H. Recent advances in ruthenium-based olefin metathesis. Chem. Soc. Rev. 2018, 47, 4510–4544. [Google Scholar] [CrossRef] [PubMed]
  55. Motagamwala, A.H.; Dumesic, J.A. Microkinetic Modeling: A Tool for Rational Catalyst Design. Chem. Rev. 2021, 121, 1049–1076. [Google Scholar] [CrossRef]
  56. Ahn, S.; Hong, M.; Sundararajan, M.; Ess, D.H.; Baik, M.-H. Design and Optimization of Catalysts Based on Mechanistic Insights Derived from Quantum Chemical Reaction Modeling. Chem. Rev. 2019, 119, 6509–6560. [Google Scholar] [CrossRef]
  57. Wang, T.; Hu, J.; Ouyang, R.; Wang, Y.; Huang, Y.; Hu, S.; Li, W.-X. Nature of metal-support interaction for metal catalysts on oxide supports. Science 2024, 386, 915–920. [Google Scholar] [CrossRef]
  58. Deng, B.; Zhong, P.; Jun, K.; Riebesell, J.; Han, K.; Bartel, C.J.; Ceder, G. CHGNet as a pretrained universal neural network potential for charge-informed atomistic modelling. Nat. Mach. Intell. 2023, 5, 1031–1041. [Google Scholar] [CrossRef]
  59. Merchant, A.; Batzner, S.; Schoenholz, S.S.; Aykol, M.; Cheon, G.; Cubuk, E.D. Scaling deep learning for materials discovery. Nature 2023, 624, 80–85. [Google Scholar] [CrossRef]
  60. Chanussot, L.; Das, A.; Goyal, S.; Lavril, T.; Shuaibi, M.; Riviere, M.; Tran, K.; Heras-Domingo, J.; Ho, C.; Hu, W.; et al. Open Catalyst 2020 (OC20) Dataset and Community Challenges. ACS Catal. 2021, 11, 6059–6072. [Google Scholar] [CrossRef]
  61. Mace, S.; Xu, Y.; Nguyen, B.N. Automated Transition Metal Catalysts Discovery and Optimisation with AI and Machine Learning. ChemCatChem 2024, 16, e202301475. [Google Scholar] [CrossRef]
  62. Broderick, K.; Lopato, E.; Wander, B.; Bernhard, S.; Kitchin, J.; Ulissi, Z. Identifying limitations in screening high-throughput photocatalytic bimetallic nanoparticles with machine-learned hydrogen adsorptions. Appl. Catal. B Environ. 2023, 320, 121959. [Google Scholar] [CrossRef]
  63. Choung, S.; Park, W.; Moon, J.; Han, J.W. Rise of machine learning potentials in heterogeneous catalysis: Developments, applications, and prospects. Chem. Eng. J. 2024, 494, 152757. [Google Scholar] [CrossRef]
  64. Lai, N.S.; Tew, Y.S.; Zhong, X.; Yin, J.; Li, J.; Yan, B.; Wang, X. Artificial Intelligence (AI) Workflow for Catalyst Design and Optimization. Ind. Eng. Chem. Res. 2023, 62, 17835–17848. [Google Scholar] [CrossRef]
  65. Wang, L.; Chen, X.; Du, Y.; Zhou, Y.; Gao, Y.; Cui, W. CataLM: Empowering catalyst design through large language models. Int. J. Mach. Learn. Cybern. 2025. [Google Scholar] [CrossRef]
  66. Park, N.H.; Manica, M.; Born, J.; Hedrick, J.L.; Erdmann, T.; Zubarev, D.Y.; Arrechea, N.A.-M.P.L. Artificial intelligence driven design of catalysts and materials for ring opening polymerization using a domain-specific language. Nat. Commun. 2023, 14, 3686. [Google Scholar] [CrossRef]
  67. Benavides-Hernández, J.; Dumeignil, F. From Characterization to Discovery: Artificial Intelligence, Machine Learning and High-Throughput Experiments for Heterogeneous Catalyst Design. ACS Catal. 2024, 14, 11749–11779. [Google Scholar] [CrossRef]
  68. Abramson, J.; Adler, J.; Dunger, J.; Evans, R.; Green, T.; Pritzel, A.; Ronneberger, O.; Willmore, L.; Ballard, A.J.; Bambrick, J.; et al. Accurate structure prediction of biomolecular interactions with AlphaFold 3. Nature 2024, 630, 493–500. [Google Scholar] [CrossRef]
  69. Jayatunga, M.K.P.; Ayers, M.; Bruens, L.; Jayanth, D.; Meier, C. How successful are AI-discovered drugs in clinical trials? A first analysis and emerging lessons. Drug Discov. Today 2024, 29, 104009. [Google Scholar] [CrossRef]
  70. Adsheada, F.; Salmanb, R.A.-S.; Aumonierc, S.; Collinsc, M.; Hoodd, K.; McNamarae, C.; Moorea, K.; Smithf, R.; Sydesg, M.R.; Williamson, P.R. A strategy to reduce the carbon footprint of clinical trials. Lancet 2021, 398, 281–282. [Google Scholar] [CrossRef]
  71. Huang, K.; Chandak, P.; Wang, Q.; Havaldar, S.; Vaid, A.; Leskovec, J.; Nadkarni, G.N.; Glicksberg, B.S.; Zitnik, N.G.M. A foundation model for clinician-centered drug repurposing. Nat. Med. 2024, 30, 3601–3613. [Google Scholar] [CrossRef]
  72. Gillet, V.J.; Myatt, G.; Zsoldos, Z.; Johnson, A.P. SPROUT, HIPPO and CAESA: Tools for de novo structure generation and estimation of synthetic accessibility. Perspect. Drug Discov. Des. 1995, 3, 34–50. [Google Scholar] [CrossRef]
  73. Parrot, M.; Tajmouati, H.; da Silva, V.B.R.; Atwood, B.R.; Fourcade, R.; Gaston-Mathé, Y.; Huu, N.D.; Perron, Q. Integrating synthetic accessibility with AI-based generative drug design. J. Cheminform. 2023, 15, 83. [Google Scholar] [CrossRef] [PubMed]
  74. Swanson, K.; Liu, G.; Catacutan, D.B.; Arnold, A.; Zou, J.; Stokes, J.M. Generative AI for designing and validating easily synthesizable and structurally novel antibiotics. Nat. Mach. Intell. 2024, 6, 338–353. [Google Scholar] [CrossRef]
  75. Available online: https://www.mckinsey.com/industries/life-sciences/our-insights/decarbonizing-api-manufacturing-unpacking-the-cost-and-regulatory-requirements (accessed on 20 February 2025).
  76. Constable, D.J.C.; Jimenez-Gonzalez, C.; Henderson, R.K. Perspective on Solvent Use in the Pharmaceutical Industry. Org. Process Res. Dev. 2007, 11, 133–137. [Google Scholar] [CrossRef]
  77. An, M.; Western, L.M.; Say, D.; Chen, L.; Claxton, T.; Ganesan, A.L.; Hossaini, R.; Krummel, P.B.; Manning, A.J.; Mühle, J.; et al. Rapid increase in dichloromethane emissions from China inferred through atmospheric observations. Nat. Commun. 2021, 12, 7279. [Google Scholar] [CrossRef]
  78. Tsai, W.T. Fate of Chloromethanes in the Atmospheric Environment: Implications for Human Health, Ozone Formation and Depletion, and Global Warming Impacts. Toxics 2017, 5, 23. [Google Scholar] [CrossRef]
  79. Sels, H.; De Smet, H.; Geuens, J. SUSSOL—Using Artificial Intelligence for Greener Solvent Selection and Substitution. Molecules 2020, 25, 3037. [Google Scholar] [CrossRef]
  80. Amar, Y.; Schweidtmann, A.M.; Deutsch, P.; Cao, L.; Lapkin, A. Machine learning and molecular descriptors enable rational solvent selection in asymmetric catalysis. Chem. Sci. 2019, 10, 6697–6706. [Google Scholar] [CrossRef]
  81. Dai, Y.; van Spronsen, J.; Witkamp, G.-J.; Verpoorte, R.; Choi, Y.H. Natural deep eutectic solvents as new potential media for green technology. Anal. Chim. Acta 2013, 766, 61–68. [Google Scholar] [CrossRef]
  82. Joarder, S.; Bansal, D.; Meena, H.; Kaushik, N.; Tomar, J.; Kumari, K.; Bahadur, I.; Choi, E.H.; Kaushik, N.K.; Singh, P. Bioinspired green deep eutectic solvents: Preparation, catalytic activity, and biocompatibility. J. Mol. Liq. 2023, 376, 121355. [Google Scholar] [CrossRef]
  83. Available online: https://www.chemistryworld.com/features/solvents-and-sustainability/3008751.article (accessed on 20 February 2025).
  84. Prabhune, A.; Dey, R. Green and sustainable solvents of the future: Deep eutectic solvents. J. Mol. Liq. 2023, 379, 121676. [Google Scholar] [CrossRef]
  85. Usmani, Z.; Sharma, M.; Tripathi, M.; Lukk, T.; Karpichev, Y.; Gathergood, N.; Singh, B.N.; Thakur, V.K.; Tabatabaei, M.; Gupta, V.K. Biobased natural deep eutectic system as versatile solvents: Structure, interaction and advanced applications. Sci. Total Environ. 2023, 881, 163002. [Google Scholar] [CrossRef] [PubMed]
  86. Zaib, Q.; Eckelman, M.J.; Yang, Y.; Kyung, D. Are deep eutectic solvents really green? A life-cycle perspective. Green Chem. 2022, 24, 7924–7930. [Google Scholar] [CrossRef]
  87. Hayyan, M. Versatile applications of deep eutectic solvents in drug discovery and drug delivery systems: Perspectives and opportunities. Asian J. Pharm. Sci. 2023, 18, 100780. [Google Scholar] [CrossRef] [PubMed]
  88. Socas-Rodríguez, B.; Torres-Cornejo, M.V.; Álvarez-Rivera, G.; Mendiola, J.A. Deep Eutectic Solvents for the Extraction of Bioactive Compounds from Natural Sources and Agricultural By-Products. Appl. Sci. 2021, 11, 4897. [Google Scholar] [CrossRef]
  89. Domingues, L.; Duarte, A.R.C.; Jesus, A.R. How Can Deep Eutectic Systems Promote Greener Processes in Medicinal Chemistry and Drug Discovery? Pharmaceuticals 2024, 17, 221. [Google Scholar] [CrossRef]
  90. Shah, P.A.; Chavda, V.; Hirpara, D.; Sharma, V.S.; Shrivastav, P.S.; Kumar, S. Exploring the potential of deep eutectic solvents in pharmaceuticals: Challenges and opportunities. J. Mol. Liq. 2023, 390, 123171. [Google Scholar] [CrossRef]
  91. Li, J.; Wang, J.; Wu, M.; Lifang, H.C.; Qi, C.Z. Deep Deterpenation of Citrus Essential Oils Intensified by In Situ Formation of a Deep Eutectic Solvent in Associative Extraction. Ind. Eng. Chem. Res. 2020, 59, 9223–9232. [Google Scholar] [CrossRef]
  92. Halder, A.K.; Haghbakhsh, R.; Ferreira, E.S.C.; Duarte, A.R.C.; Cordeiro, M.N.D.S. Machine learning-driven prediction of deep eutectic solvents’ heat capacity for sustainable process design. J. Mol. Liq. 2025, 418, 126707. [Google Scholar] [CrossRef]
  93. Cysewski, P.; Jeliński, T.; Przybyłek, M.; Mai, A.; Kułak, J. Experimental and Machine-Learning-Assisted Design of Pharmaceutically Acceptable Deep Eutectic Solvents for the Solubility Improvement of Non-Selective COX Inhibitors Ibuprofen and Ketoprofen. Molecules 2024, 29, 2296. [Google Scholar] [CrossRef]
  94. Abbas, U.L.; Zhang, Y.; Tapia, J.; Md, S.; Chen, J.; Shi, J.; Shao, Q. Machine-Learning-Assisted Design of Deep Eutectic Solvents Based on Uncovered Hydrogen Bond Patterns. Engineering 2024, 39, 74–83. [Google Scholar] [CrossRef]
  95. Lavrinenko, A.K.; Chernyshov, I.Y.; Pidko, E.A. Machine Learning Approach for the Prediction of Eutectic Temperatures for Metal-Free Deep Eutectic Solvents. ACS Sustain. Chem. Eng. 2023, 11, 15492–15502. [Google Scholar] [CrossRef]
  96. Chen, M.; Xie, T.; Xu, C. Continuous counter-current centrifugal extraction column with high throughput using a spiral inner cylinder. Chem. Eng. Process. Process Intensif. 2018, 125, 1–7. [Google Scholar] [CrossRef]
  97. Patel, D.; Suthar, K.J.; Balsora, H.K.; Patel, D.; Panda, S.R.; Bhavsar, N. Estimation of density and viscosity of deep eutectic solvents: Experimental and machine learning approach. Asia-Pac. J. Chem. Eng. 2024, 19, e3151. [Google Scholar] [CrossRef]
  98. Luu, R.K.; Wysokowski, M.; Buehler, M.J. Generative discovery of de novo chemical designs using diffusion modeling and transformer deep neural networks with application to deep eutectic solvents. Appl. Phys. Lett. 2023, 122, 234103. [Google Scholar] [CrossRef]
  99. Jin, H.; Jin, Z.; Kim, Y.-G.; Fan, C.; Ghanbari, A. A promising artificial intelligence-based tool to simulate the efficient and sustainable hydrogen sulfide elimination using deep eutectic solvents. Sep. Purif. Technol. 2023, 324, 124472. [Google Scholar] [CrossRef]
  100. Odegova, V.; Lavrinenko, A.; Rakhmanov, T.; Sysuev, G.; Dmitrenko, A.; Vinogradov, V. DESignSolvents: An open platform for the search and prediction of the physicochemical properties of deep eutectic solvents. Green Chem. 2024, 26, 3958–3967. [Google Scholar] [CrossRef]
  101. Ayres, L.B.; Gomez, F.J.V.; Silva, M.F.; Garcia, J.R.L.C.D. Predicting the formation of NADES using a transformer-based model. Sci. Rep. 2024, 14, 2715. [Google Scholar] [CrossRef]
  102. Abdollahzadeh, M.; Khosravi, M.; Masjidi, B.H.K.; Behbahan, A.S.; Bagherzadeh, A.; Shahdost, A.S.F.T. Estimating the density of deep eutectic solvents applying supervised machine learning techniques. Sci. Rep. 2022, 12, 4954. [Google Scholar] [CrossRef]
  103. Corey, E.J.; Wipke, W.T. Computer-Assisted Design of Complex Organic Syntheses. Science 1969, 166, 178–192. [Google Scholar] [CrossRef]
  104. Sarkar, R.; De Joarder, D.; Mukhopadhyay, C. Recent advances in the syntheses and reactions of biologically promising β-lactam derivatives. Tetrahedron 2025, 177, 134565. [Google Scholar] [CrossRef]
  105. Takabatake, T.; Fujiwara, K.; Okamoto, S.; Kishimoto, R.; Kagawa, N.; Toyota, M. Discovery of orthogonal synthesis using artificial intelligence: Pd(OAc)2-catalyzed one-pot synthesis of benzofuran and bicyclo[3.3.1]nonane scaffolds. Tetrahedron Lett. 2020, 61, 152275. [Google Scholar] [CrossRef]
  106. King-Smith, E.; Berritt, S.; Bernier, L.; Hou, X.; Klug-McLeod, J.L.; Mustakis, J.; Sach, N.W.; Tucker, J.W.; Yang, Q.; Lee, R.M.H.A.A. Probing the chemical ‘reactome’ with high-throughput experimentation data. Nat. Chem. 2024, 16, 633–643. [Google Scholar] [CrossRef] [PubMed]
  107. Sanchez, W.; Sremski, W.; Piccini, B.; Palluel, O.; Maillot-Maréchal, E.; Betoulle, S.; Jaffal, A.; Aït-Aïssa, S.; Brion, F.; Thybaud, E.; et al. Adverse effects in wild fish living downstream from pharmaceutical manufacture discharges. Environ. Int. 2011, 37, 1342–1348. [Google Scholar] [CrossRef] [PubMed]
  108. Kidd, K.A.; Blanchfield, P.J.; Mills, K.H.; Flick, R.W. Collapse of a fish population after exposure to a synthetic estrogen. Proc. Natl. Acad. Sci. USA 2007, 104, 8897–8901. [Google Scholar] [CrossRef]
  109. The State of the World’s Antibiotics 2021, a Global Analysis of Antimicrobial Resistance and Its Drivers, the Center for Disease Dynamics, Economics & Policy. 2021. Available online: https://onehealthtrust.org/wp-content/uploads/2021/02/SOWA_01.02.2021_Low-Res.pdf (accessed on 10 October 2021).
  110. Chung, S.-S.; Brooks, B.W. Identifying household pharmaceutical waste characteristics and population behaviors in one of the most densely populated global cities. Resour. Conserv. Recycl. 2019, 140, 267–277. [Google Scholar] [CrossRef]
  111. Vieno, N.; Hallgren, P.; Wallberg, P.; Pyhälä, M.; Zandaryaa, S. Baltic Marine Environment Protection Commission. In Pharmaceuticals in the Aquatic Environment of the Baltic Sea Region: A Status Report; CCB Report: Pharmaceutical Pollution in the Baltic Sea Region; UNESCO Publishing: Uppsala, Sweden, 2017; Volume 1. [Google Scholar]
  112. Daughton, C.G.; Ruhoy, I.S. Lower-dose prescribing: Minimizing “side effects” of pharmaceuticals on society and the environment. Sci. Total Environ. 2013, 443, 324–337. [Google Scholar] [CrossRef]
  113. Zhu, X.; Huang, W.; Lu, H.; Wang, Z.; Ni, X.; Hu, J.; Deng, S.; Tan, Y.; Li, L.; Zhang, M.; et al. A machine learning approach to personalized dose adjustment of lamotrigine using noninvasive clinical parameters. Sci. Rep. 2021, 11, 5568. [Google Scholar] [CrossRef]
  114. Iancu, A.; Leb, I.; Prokosch, H.-U.; Rödle, W. Machine learning in medication prescription: A systematic review. Int. J. Med. Inform. 2023, 180, 105241. [Google Scholar] [CrossRef]
  115. Lai, Y.; Chu, X.; Di, L.; Gao, W.; Guo, Y.; Liu, X.; Lu, C.; Mao, J.; Shen, H.; Tang, H.; et al. Recent advances in the translation of drug metabolism and pharmacokinetics science for drug discovery and development. Acta Pharm. Sin. B 2022, 12, 2751–2777. [Google Scholar] [CrossRef]
  116. Satheeskumar, R. Enhancing drug discovery with AI: Predictive modeling of pharmacokinetics using Graph Neural Networks and ensemble learning. Intell. Pharm. 2024, 3, 127–140. [Google Scholar] [CrossRef]
  117. Swanson, K.; Walther, P.; Leitz, J.; Mukherjee, S.; Wu, J.C.; Shivnaraine, R.V.; Zou, J. ADMET-AI: A machine learning ADMET platform for evaluation of large-scale chemical libraries. Bioinformatics 2024, 40, btae416. [Google Scholar] [CrossRef] [PubMed]
  118. Farhud, D.D.; Zokaei, S. Ethical Issues of Artificial Intelligence in Medicine and Healthcare. Iran J. Public Health 2021, 50, i–v. [Google Scholar] [CrossRef] [PubMed]
  119. Sulbaek Andersen, M.P.; Nielsen, O.J.; Sherman, J.D. Assessing the potential climate impact of anaesthetic gases. Lancet Planet. Health 2023, 7, e622–e629. [Google Scholar] [CrossRef]
  120. White, S.M.; Shelton, C.L. Abandoning inhalational anaesthesia. Sci. Rep. 2020, 75, 451–454. [Google Scholar] [CrossRef]
  121. Miyaguchi, N.; Takeuchi, K.; Kashima, H.; Morita, M. Predicting anesthetic infusion events using machine learning. Sci. Rep. 2021, 11, 23648. [Google Scholar] [CrossRef]
  122. Hu, Y.-J.; Ku, T.-H.; Jan, R.-H.; Wang, K.; Tseng, Y.-C. Decision tree-based learning to predict patient controlled analgesia consumption and readjustment. BMC Med. Inform. Decis. Mak. 2012, 12, 131. [Google Scholar] [CrossRef]
  123. Ortolani, O.; Conti, A.; Di Filippo, A.; Adembri, C.; Moraldi, E.; Evangelisti, A.; Maggini, M.; Roberts, S.J. EEG signal processing in anaesthesia. Use of a neural network technique for monitoring depth of anaesthesia. Br. J. Anaesth. 2002, 88, 644–648. [Google Scholar] [CrossRef]
  124. Anderson, W.A.; Rao, A. Anesthetic Gases: Environmental Impacts and Mitigation Strategies for Fluranes and Nitrous Oxide. Environments 2024, 11, 275. [Google Scholar] [CrossRef]
  125. Schamberg, G.; Badgeley, M.; Meschede-Krasa, B.; Kwon, O.; Brown, E.N. Continuous action deep reinforcement learning for propofol dosing during general anesthesia. Artif. Intell. Med. 2022, 123, 102227. [Google Scholar] [CrossRef] [PubMed]
  126. Nyirenda, J.; Mwanza, A.; Lengwe, C. Assessing the biodegradability of common pharmaceutical products (PPs) on the Zambian market. Heliyon 2020, 6, e05286. [Google Scholar] [CrossRef]
  127. Barra Caracciolo, A.; Topp, E.; Grenni, P. Pharmaceuticals in the environment: Biodegradation and effects on natural microbial communities. A review. J. Pharm. Biomed. Anal. 2015, 106, 25–36. [Google Scholar] [CrossRef] [PubMed]
  128. Wilkinson, J.L.; Boxall, A.B.A.; Kolpin, D.W.; Leung, K.M.Y.; Lai, R.W.S.; Galbán-Malagón, C.; Adell, A.D.; Mondon, J.; Metian, M.; Marchant, R.A.; et al. Pharmaceutical pollution of the world’s rivers. Proc. Natl. Acad. Sci. USA 2022, 119, e2113947119. [Google Scholar] [CrossRef] [PubMed]
  129. Anwar, M.; Muhammad, F.; Akhtar, B. Biodegradable nanoparticles as drug delivery devices. J. Drug Deliv. Sci. Technol. 2021, 64, 102638. [Google Scholar] [CrossRef]
  130. Sun, S.; Cui, Y.; Yuan, B.; Dou, M.; Wang, G.; Xu, H.; Wang, J.; Yin, W.; Wu, D.; Peng, C. Drug delivery systems based on polyethylene glycol hydrogels for enhanced bone regeneration. Front. Bioeng. Biotechnol. 2023, 11, 1117647. [Google Scholar] [CrossRef]
  131. Sanchez Armengol, E.; Alexander, U.; Laffleur, F. PEGylated drug delivery systems in the pharmaceutical field: Past, present and future perspective. Drug Dev. Ind. Pharm. 2022, 48, 129–139. [Google Scholar] [CrossRef]
  132. Vlachopoulos, A.; Karlioti, G.; Balla, E.; Daniilidis, V.; Kalamas, T.; Stefanidou, M.; Bikiaris, N.D.; Christodoulou, E.; Koumentakou, I.; Karavas, E.; et al. Poly(Lactic Acid)-Based Microparticles for Drug Delivery Applications: An Overview of Recent Advances. Pharmaceutics 2022, 14, 359. [Google Scholar] [CrossRef]
  133. Tyler, B.; Gullotti, D.; Mangraviti, A.; Utsuki, T.; Brem, H. Polylactic acid (PLA) controlled delivery carriers for biomedical applications. Adv. Drug Deliv. Rev. 2016, 107, 163–175. [Google Scholar] [CrossRef]
  134. Hines, D.J.; Kaplan, D.L. Poly(lactic-co-glycolic) acid-controlled-release systems: Experimental and modeling insights. Crit. Rev. Ther. Drug Carr. Syst. 2013, 30, 257–276. [Google Scholar] [CrossRef]
  135. El Allaoui, B.; Benzeid, H.; Zari, N.; el kacem Qaiss, A.; Bouhfid, R. Functional cellulose-based beads for drug delivery: Preparation, functionalization, and applications. J. Drug Deliv. Sci. Technol. 2023, 88, 104899. [Google Scholar] [CrossRef]
  136. Sivamaruthi, B.S.; Nallasamy, P.K.; Suganthy, N.; Kesika, P.; Chaiyasut, C. Pharmaceutical and biomedical applications of starch-based drug delivery system: A review. J. Drug Deliv. Sci. Technol. 2022, 77, 103890. [Google Scholar] [CrossRef]
  137. Boztepe, C.; Künkül, A.; Yüceer, M. Application of artificial intelligence in modeling of the doxorubicin release behavior of pH and temperature responsive poly(NIPAAm-co-AAc)-PEG IPN hydrogel. J. Drug Deliv. Sci. Technol. 2020, 57, 101603. [Google Scholar] [CrossRef]
  138. Aghajanpour, S.; Amiriara, H.; Esfandyari-Manesh, M.; Ebrahimnejad, P.; Jeelani, H.; Henschel, A.; Singh, H.; Dinarvand, R.; Hassan, S. Utilizing machine learning for predicting drug release from polymeric drug delivery systems. Comput. Biol. Med. 2025, 188, 109756. [Google Scholar] [CrossRef] [PubMed]
  139. Cardoso, R.; da Costa, C.A.; de Figueiredo, R.M.; Zehetmeyer, G.; Schmith, J. A method to predict the percentage of biodegradation in polymeric materials. Comput. Electr. Eng. 2024, 118, 109473. [Google Scholar] [CrossRef]
  140. Chen, T.; Pang, Z.; He, S.; Li, Y.; Shrestha, S.; Little, J.M.; Yang, H.; Chung, T.-C.; Sun, J.; Whitley, H.C.; et al. Machine intelligence-accelerated discovery of all-natural plastic substitutes. Nat. Nanotechnol. 2024, 19, 782–791. [Google Scholar] [CrossRef]
  141. Alshahrani, S.M.; Alotaibi, H.F.; Alqarni, M. Modeling and validation of drug release kinetics using hybrid method for prediction of drug efficiency and novel formulations. Front. Chem. 2024, 12, 1395359. [Google Scholar] [CrossRef]
  142. AL-Rajabi, M.M.; Alzyod, S.; Patel, A.; Teow, Y.H. A hybrid machine learning framework for predicting drug-release profiles, kinetics, and mechanisms of temperature-responsive hydrogels. Polym. Bull. 2025, 82, 2911–2932. [Google Scholar] [CrossRef]
  143. WHO Calls for Transformative Action Towards a Greener Future in Pharmaceutical Manufacturing and Distribution. 23 December 2024. Available online: https://www.who.int/news/item/23-12-2024-who-calls-for-transformative-action-towards-a-greener-future-in-pharmaceutical-manufacturing-and-distribution (accessed on 16 May 2025).
  144. Available online: https://acsgcipr.org/ (accessed on 16 May 2025).
  145. Benison, C.H.; Payne, P.R. Manufacturing mass intensity: 15 Years of Process Mass Intensity and development of the metric into plant cleaning and beyond. Curr. Res. Green Sustain. Chem. 2022, 5, 100229. [Google Scholar] [CrossRef]
  146. Available online: https://open-reaction-database.org/browse (accessed on 16 May 2025).
  147. Available online: https://pubchem.ncbi.nlm.nih.gov/ (accessed on 16 May 2025).
  148. Available online: https://alphafold.ebi.ac.uk/ (accessed on 16 May 2025).
  149. Available online: http://www.swissadme.ch/ (accessed on 16 May 2025).
  150. Available online: https://deepchem.io/ (accessed on 16 May 2025).
  151. Available online: https://github.com/salesforce/progen (accessed on 16 May 2025).
Figure 3. (a) A schematic representation of drug extraction and purification using deep eutectic solvents as sustainable alternatives. This process involves the use of hydrogen bond acceptors (HBAs) and hydrogen bond donors (HBDs). Image reprinted with permissions from [91] (Copyright © 2020 ACS Publications). (b) A schematic representation of the workflow employed for training an AI model to predict heat capacity for deep eutectic solvents. This process involves collecting data and obtaining quantum-chemical COSMO-RS-based descriptors. Image reprinted with permissions from [92] (Copyright © 2025 Elsevier, Creative Commons CC-BY licence). (c) The prediction of drug–solvent interactions using AI could accelerate the adoption of sustainable solvents by enabling the selection of compounds with optimal solubility properties. Image reprinted with permissions from [93] (Creative Commons CC BY 4.0 licence).
Figure 3. (a) A schematic representation of drug extraction and purification using deep eutectic solvents as sustainable alternatives. This process involves the use of hydrogen bond acceptors (HBAs) and hydrogen bond donors (HBDs). Image reprinted with permissions from [91] (Copyright © 2020 ACS Publications). (b) A schematic representation of the workflow employed for training an AI model to predict heat capacity for deep eutectic solvents. This process involves collecting data and obtaining quantum-chemical COSMO-RS-based descriptors. Image reprinted with permissions from [92] (Copyright © 2025 Elsevier, Creative Commons CC-BY licence). (c) The prediction of drug–solvent interactions using AI could accelerate the adoption of sustainable solvents by enabling the selection of compounds with optimal solubility properties. Image reprinted with permissions from [93] (Creative Commons CC BY 4.0 licence).
Futurepharmacol 05 00024 g003
Figure 4. A schematic representation of different stages where AI-guided molecular design can improve drug sustainability. Pre-drug-synthesis, AI could be used for the design of efficient, highly selective catalysts, including enzymes and metal-based catalysis, as well as solvents, some of the most energy-intensive chemicals used by pharmaceutical companies. AI models have also been developed to improve drug synthetic pathways, even enabling the one-pot synthesis of compounds, and tailor drug dosage to reduce waste. Ultimately, AI holds the potential to design biodegradable chemicals, such as solvents and active pharmaceutical ingredients, and reduce the associated CO2 emissions.
Figure 4. A schematic representation of different stages where AI-guided molecular design can improve drug sustainability. Pre-drug-synthesis, AI could be used for the design of efficient, highly selective catalysts, including enzymes and metal-based catalysis, as well as solvents, some of the most energy-intensive chemicals used by pharmaceutical companies. AI models have also been developed to improve drug synthetic pathways, even enabling the one-pot synthesis of compounds, and tailor drug dosage to reduce waste. Ultimately, AI holds the potential to design biodegradable chemicals, such as solvents and active pharmaceutical ingredients, and reduce the associated CO2 emissions.
Futurepharmacol 05 00024 g004
Table 1. A comparison of the AI models used in the design of enzymes and the prediction of protein stability.
Table 1. A comparison of the AI models used in the design of enzymes and the prediction of protein stability.
DatasetModel Prediction AlgorithmPerformanceRefs.
280 million protein sequences from >19,000 familiesProtein function1.2-billion-parameter neural networkAUC = 0.85
(experimentally validated)
[38]
BRENDA DATASET (37,624,812 sequences)Protein activity (model made available as Open Source)Language model-[36,37]
3.15 billion protein sequences, 236 million protein structures, and 539 million proteins with function
annotations
Protein activityLanguage modelSS3 > 80%
pTM > 0.8
pLDDT > 0.8
RMSD < 1.5 Å
(experimentally validated)
[40]
Protein–small molecule complexes in PDBEnzyme structureDeep Neural NetworkRMSD < 1.5 Å
(experimentally validated)
[41]
2950 thermophilic protein sequencesEnzyme thermostabilityDeep Neural Network and bi-long short-term memoryACC (%) = 94.34
PR (%) = 93.97
REC (%) = 94.81
REC (%) = 94.36
MCC (%) = 88.73
AUROC (%) = 98.68
[46]
Dataset from 21,498 microorganismsEnzyme optimal temperature (model made available as Open Source)Random Forest regressor R2 = 0.94
RMSE = 4.46
[47]
Optimal growth temperatures for 96 million host bacterial strainsEnzyme thermostabilityLanguage modelExperimentally validated[48]
16,706 unique sequencesCatalytic activityGenerative Adversarial NetworkExperimentally validated[50]
Table 2. Comparison of AI models used in design of heterogeneous catalysts.
Table 2. Comparison of AI models used in design of heterogeneous catalysts.
DatasetModel PredictionAlgorithmPerformanceRef.
603 articlesCatalyst synthesis optimisationLarge language model and Bayesian optimisationExperimentally validated[64]
22,000 articles from Web of ScienceCatalyst synthesis optimisationLanguage modelAverage predicted faraday efficiency = 64.15%[65]
549 monomer–catalyst pairs for catalyst modelMonomer conversion, dispersity, and average molecular weightRegression transformerPearson correlation = 0.59
(Experimentally validated)
[66]
Table 3. Machine learning models developed to optimise design of DESs.
Table 3. Machine learning models developed to optimise design of DESs.
DatasetModel PredictionAlgorithmPerformanceRef.
186 (simulated systems) + 34 (experimentally verified)DES formationSupport Vector MachineAverage ROC-AUC score = 0.8
(experimentally validated)
[94]
237 experimentally validated DESsMelting temperatureSupport Vector RegressionR2 = 0.74, RMSE = 22.5[95]
530 DESsHeat capacityNeural Network Multilayer PerceptronAARD = 4%[92]
402 different DES compositions Diffusion model with self-/cross-attentionR2 = 0.93
(experimentally validated)
[98]
435 recordsHydrogen sulphide (H2S) elimination capacityCascade neural networkMAE = 0.02
MSE = 0.0031
AARE = 3.03
R2 = 0.99943
(experimentally validated)
[99]
-Melting temperature, density, viscosity (model made available as Open Source)CatBoostR2 = 0.6–0.91
AARD = 3.14–19.05%
(experimentally validated)
[100]
-SolubilityNon-linear Support Vector RegressionExperimentally validated[93]
1000 labelled mixtures of DESs and NADESsDES formationTransformer-based neural network modelF1-Score = 0.82
(experimentally validated)
[101]
1239 recordsDES densityLeast-squares Support Vector RegressionR2 = 0.99798
MAPE = 0.26%
[102]
Table 4. Comparison of AI models used in prediction of pharmacokinetics and dosing of drugs.
Table 4. Comparison of AI models used in prediction of pharmacokinetics and dosing of drugs.
DatasetModel Prediction AlgorithmPerformanceRef.
1141 therapeutic drug-monitoring measurements from 347 patientsDose-adjusted concentrations of lamotrigineExtra-trees regression algorithmMAE  =  8.7 μg mL−1 g−1 day
Mean Relative Error (%) =   3%
(experimentally validated)
[113]
1099 patients, each described with 280 attributesPostoperative analgesic requirementsDecision treesPrediction accuracies of total analgesic consumption of 80.9%
(experimentally validated)
[122]
10,000 bioactive compounds from ChEMBL databaseClearance, volume distribution, half-life, bioavailabilityStacking ensemble modelR2 = 0.92
MAE = 0.062
[116]
Simulated pharmacokinetic and pharmacodynamic dataAnaesthetic dosingReinforcement learning algorithmMedian episode median
performance error of 1.1% ± 0.5
(experimentally validated with retrospective data)
[125]
210 case dataIncrease in flow rate of remifentanilLong short-term memorySpecificity = 0.73
Sensitivity = 0.66
ROC-AUC = 0.75
[121]
13 processed EEG
parameters from 200 patients
Anaesthesia scoresReinforcement learning algorithmR2 = 0.94
(experimentally validated)
[123]
Table 5. Comparison of AI models used in prediction of biodegradable drug delivery systems.
Table 5. Comparison of AI models used in prediction of biodegradable drug delivery systems.
DatasetModel PredictionAlgorithmPerformanceRef.
540 experimental data pointsRelease kineticsSupport Vector MachineR2 = 0.998
RMSE = 0.3701
MSE = 0.137
MAPE = 0.944
(experimentally validated)
[137]
76 biodegradation curvesBiodegradation kinetics (%)Long short-term memory neural networkMAPE = 7.6–16.99%
MAE = 0.018–0.027
MSE = 0.0004–0.001
RMSE = 6.71–11.33
(experimentally validated with validation dataset)
[139]
Data from 133 experimentsPolymer properties (Young’s modulus, flammability)Artificial neural networkMRE = 21%
(experimentally validated with molecular dynamic simulations)
[140]
15,000 data samples Drug release kineticsDecision Tree RegressionR2 = 0.94652
RMSE = 6.04 × 10−5
MAE = 4.83 × 10−5
[141]
500 datapointsDrug release kineticsRandom ForestR2 = 0.99
MAPE = 0.002
(experimentally validated)
[142]
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Ruiz-Gonzalez, A. AI-Driven Chemical Design: Transforming the Sustainability of the Pharmaceutical Industry. Future Pharmacol. 2025, 5, 24. https://doi.org/10.3390/futurepharmacol5020024

AMA Style

Ruiz-Gonzalez A. AI-Driven Chemical Design: Transforming the Sustainability of the Pharmaceutical Industry. Future Pharmacology. 2025; 5(2):24. https://doi.org/10.3390/futurepharmacol5020024

Chicago/Turabian Style

Ruiz-Gonzalez, Antonio. 2025. "AI-Driven Chemical Design: Transforming the Sustainability of the Pharmaceutical Industry" Future Pharmacology 5, no. 2: 24. https://doi.org/10.3390/futurepharmacol5020024

APA Style

Ruiz-Gonzalez, A. (2025). AI-Driven Chemical Design: Transforming the Sustainability of the Pharmaceutical Industry. Future Pharmacology, 5(2), 24. https://doi.org/10.3390/futurepharmacol5020024

Article Metrics

Back to TopTop