Paweł Mateusz
Nowak
*a,
Michał
Kamiński
b,
Wojciech
Trybała
b,
Vittorio
Canale
*b and
Paweł
Zajdel
b
aJagiellonian University in Kraków, Faculty of Chemistry, Department of Analytical Chemistry, Laboratory of Forensic Chemistry, Gronostajowa St. 2, 30-387 Kraków, Poland. E-mail: pm.nowak@uj.edu.pl
bJagiellonian University Medical College, Faculty of Pharmacy, Department of Organic Chemistry, Medyczna St. 9, 30-688 Kraków, Poland. E-mail: vittorio.canale@uj.edu.pl
First published on 23rd December 2024
In analytical chemistry, the idea of assessing the “whiteness” of a method, which refers to the RGB model used in colour coding, has gained significant popularity in recent years. Whiteness represents the overall evaluation, which includes greenness (environmental impact) and functional features, represented by redness (analytical efficiency), and blueness (practicality). This work presents the first whiteness assessment model dedicated to chemical synthesis, called “RGBsynt”, inspired by the metrics used in analytics. The assessment may be applied to a set of 2–10 methods, described by parameters such as yield, product purity, E-factor, ChlorTox, time-efficiency and energy demand, which refer to the three primary colours. The model is implemented in an easy-to-use Excel spreadsheet where users input the values of the mentioned parameters, and then data analysis, evaluation and results visualization are carried out fully automatically. The RGBsynt model was employed to compare 17 solution-based procedures for O- and N-alkylation, nucleophilic aromatic substitution, and N-sulfonylation of amines with their corresponding 17 mechanochemical alternatives. The selection of synthesis processes was preceded by a thorough literature review to ensure representative examples and reliable comparison of methods. The evaluation results clearly indicate the superiority of mechanochemistry, both in reducing environmental impact (greenness), and in overall potential (whiteness). The RGBsynt model might be considered as a simple and useful tool for evaluating synthesis methods, allowing comparison of various reactions based on empirical data.
Various approaches have been proposed to reduce the amount of solvents in organic synthesis, among which mechanochemistry has been a focus of particular interest. In this approach chemical transformations occur upon direct absorption of mechanical energy supplied by grinding or milling substrates without or with a limited use of organic solvents.4,5 In such procedures, conventional laboratory glassware and heaters are replaced by vibratory or planetary ball mills that facilitate surface interactions between reactants.
The application of mechanochemistry results in a drastic reduction in the volume of solvents used in a reaction setup, and facilitates the purification step, mainly by avoiding traditional solvent-consuming column chromatography. This method is increasingly acknowledged for its efficiency and safety. It also offers control over reaction selectivity and allows access to products that cannot be achieved using solution-based methods.6 The contribution of mechanochemical methods to the preparation of active pharmaceutical ingredients (APIs) has resulted in the coining of the term “medicinal mechanochemistry”.7 Notably, this approach has expanded the medicinal chemistry toolbox for the generation of compound libraries.8,9
It is worth noting that a recent trend in analytical chemistry is the distinction between the greenness of a method and its “whiteness”, which represents the overall picture comprising both its greenness and functionality (usefulness). In analogy to the red–green–blue (RGB) model used in electronics for colour coding, green is one of the three primary attributes (colours), with the other two being red and blue.12 They refer to functional characteristics. Red indicates analytical parameters determined during method validation, e.g., accuracy, precision and sensitivity, while blue indicates practical features and cost effectiveness. As a result, determining that a certain method is whiter means that it is overall better suited to a given application and its average score for all considered criteria is better. This approach is known as white analytical chemistry.13 In our recent paper we also argue that “whiteness” is a more comprehensive and clear-cut term than “sustainability” – which is used in different contexts and does not embrace all functional aspects,11 and that “whiteness” as a general term can be applied beyond analytics.
Obviously, the most desirable scenario is to find a method that is both greener and more functional. However, this may be impossible and may require us finding a “golden mean” represented by whiteness. Therefore, we need to use appropriate metrics to assess whiteness in an objective way, allowing us to establish the right compromise between green, red, and blue criteria.
One of the three available versions of the RGB model can be used for this purpose. The versions published in 2019,12 and 2021,13 provide some flexibility and assume that the assessment of a given criterion is made by the user by awarding an appropriate number of points based on available data. The latest version from 2024, called “RGBfast”,14 was designed to automate the assessment process and eliminate the need to award points, thus reducing the possibility of manipulation. In RGBfast, six main criteria are assessed, covered by all 3 colours: trueness, precision, limit of detection, ChlorTox (see section 2.2.),15 energy demand and sample throughput. The reference point for the assessment of a given criterion is the average value of a given parameter obtained for the set of all compared methods (there must be at least 2 methods to apply this model).
This article aims at presenting a new whiteness assessment model, called “RGBsynt”, which is used to address chemical synthesis methods (hence “synt”). Its structure has been adapted from the RGBfast model, which was originally developed for analysts. Our motivation for developing a new version of the RGB model aimed at chemical synthesis was the significant analogy of analytical and synthetic procedures, differing mainly in the red functional criteria, which allows the model, upon some modification, to be easily implemented in a totally new research domain. To illustrate and validate RGBsynt, we compared various mechanochemical and solution-based methods leading to analogous products.
To facilitate the use of RGBsynt, we designed a special Excel spreadsheet containing coded formulas, designated fields for data entry, and functions for visualization of the results. The table containing the place for user input, including the six aforementioned parameters, is shown in Fig. 1. The Excel spreadsheet containing an empty template and completed sheets for all studied methods is attached as a supplement to this article.†
The basis of this approach is to refer hazards related to the substance of interest to the hazards identified for the standard substance – chloroform, and to consider the precisely known mass of the substance used in the method. The results are expressed as the equivalent mass of chloroform, indicating the degree of estimated chemical risk. This calculation is performed using the following simple equation:
![]() | (1) |
The ChlorTox values characterizing different substances can be combined to express the total chemical risk predicted for the entire method (Total ChlorTox). The ChlorTox value has a purely theoretical meaning; it is not directly reflected in reality, but it indicates the general scale of potential risk. For example, a method with a Total ChlorTox value of 10 g indicates a risk equivalent to a method using 10 g of pure chloroform as the sole hazardous chemical reagent. To facilitate rapid evaluation of the method using the ChlorTox Scale, a simple model for quantifying general chemical hazard, called the Weighted Hazards Number (WHN), was developed. This model involves gathering relevant information on the hazards posed by given chemical reagents from publicly available safety data sheets, presented in the commonly used Globally Harmonized System of Classification and Labelling of Chemicals (GHS) format. The GHS covers hazards associated with storage and transport, direct health hazards (e.g., poisoning, chemical burns, irritation, carcinogenicity), and environmental hazards (e.g., impact on model species of microorganisms, plants, and animals). In addition, the hazard categories are further classified by degree, ranging from 1 to 4, with category 1 indicating the highest hazard level (the greatest potential danger), and category 4 representing the lowest. This information is always presented in Section 2 (Hazards identification) of these safety data sheets.
In the WHN approach, the overall hazard of the substance of interest (CHsub) and chloroform (CHCHCl3) is expressed by its WHN value. The WHN is calculated as the sum of the hazards identified in Section 2 of the relevant safety data sheet (in its GHS format), with weights reflecting the degree of potential danger (hazard category): 1 for category 1, 0.75 for category 2, 0.5 for category 3 and 0.25 for category 4:
![]() | (2) |
Noticeably, hazard data provided by different reagent manufacturers may vary quite considerably. There are two ways to ensure the consistency of the assessment. The first is to choose one preferred data supplier. Another approach, which seems more rigorous and objective, is to take into account data published for a given substance by different suppliers, and then calculate the average WHN value. Safety data sheets for a given substance can be easily searched using freely available tools, e.g., the search engine on chemicalsafety.com.18 In addition, comprehensive data for nearly 700 different reagents, including ready-to-use averaged WHN values, have been collected and published in a specially designed database – ChlorTox Base.19
The Excel file containing ChlorTox Base has been integrated (as one of the sheets) into RGBsynt, allowing users to quickly access information on commonly used reagents. If a reagent is not included in the database, it is recommended that one independently calculates its WHN value (eqn (2)). It is then recommended to average the values obtained from the data sheets of different manufacturers. If this is not possible, e.g. when a given reagent has not yet been characterized, it is recommended that the value of WHN = 5.83, corresponding to chloroform, is used. Since chloroform is a highly toxic reference reagent, using this value helps prevent underestimation of chemical risk. RGBsynt users may also adopt an alternative method of determining relative chemical hazard (CHsub/CHCl3), different from WHN, as long as it is reasonable and well described.
![]() | (3) |
It should be emphasized that this approach does not require estimating the operating time of each individual device, because, first, it would significantly complicate the evaluation process, and second, some instruments require being placed in stand-by mode, which could introduce some inconsistency. The adopted formula (eqn (3)) seems to us to be a good compromise between simplicity and reliability of the assessment.
![]() | (4) |
Adopting this formula allows for a simple interpretation of the score. When the criterion is rated as being close to ideal and the result value is extremely low in comparison with the average result, the score is close to 100; when the result and average result show the same value, the score is 50; when the result is worse (higher) than the average result, the score is <50 (note that score = 0 is unattainable in practice, as it would require the method to perform infinitely poorly).
The saturation of a given primary colour and the overall whiteness are calculated as the geometric average of the corresponding score values (eqn (5)–(8)). The outcomes are presented by the model in the tables/pictograms shown in Fig. 2, as well as in the bar chart shown in Fig. 3. The G1/B1 and G3/B3 criteria (which are assigned to two colours simultaneously), have the same importance for the final result (whiteness) as all other criteria. Concurrently, G2 and B2 are twice as important from the point of view of greenness and blueness considered individually (eqn (6) and (7)). Thanks to this, the share of each parameter in the model is equal, and the tables/pictograms (Fig. 2) reflect well the model's structure:
![]() | (5) |
![]() | (6) |
![]() | ||
Fig. 3 The results of the evaluation of individual colours (red, green, blue, and white, respectively) for 4 examples of methods shown in a bar chart (created automatically in the Excel spreadsheet). |
where G1/B1 is E-factor, G2 is ChlorTox, and G3/B3 is estimated energy demand;
![]() | (7) |
![]() | (8) |
Of note, the use of the geometric average guarantees consistency and balances the method's potential without introducing significant bias. For example, while the arithmetic mean of the sets (1,4,10) and (5,5,5) is the same, i.e. 5, the geometric mean for the first set is approximately 3.4, while for the second it remains 5. A better result was obtained for the second set, where the values show less variation. In the first set, the value “1” may constitute a significant bottleneck of the method, excluding its use. The adopted model therefore rewards the search for the reasonable compromise between individual criteria and primary colours.
Another issue is the use of appropriate terminology. In a recently published article about UG-theory,11 we devoted significant attention to the theoretical analysis of the “greenness” concept, pointing out three different interpretations of the “state of being green”: purist, pragmatic, and formal. Now it is only worth mentioning that there is no universal correct interpretation, with each of them having its own advantages and disadvantages. The RGBsynt model clearly indicates which method appears more/less green or white, or which method appears to be the best of all (the greenest or whitest), but does not assume any specific interpretation of the “state of being green or white”. In other words, the RGBsynt model does not explicitly state that “some method appears generally green or white” as this would require certain assumptions that were deliberately avoided to provide the user with a freedom of choice in how they want to see greenness and whiteness as a state.
![]() | ||
Fig. 4 Graphic representation of RGBsynt model source data: from the selection of synthetic protocols to the assessment of synthesis methods using the RGBsynt model. |
The limited number of available mechanochemical methods for medicinal chemistry purposes restricted our data source to our in-house reported protocols (Fig. 5).9,22,23 To assess the representativeness of our routinely used solution-based protocols (alternatives to mechanochemical methods), we gathered data from 80 solution-based procedures reported in the literature and patents (Fig. 4, Stage 2A). To ensure unbiased comparison, we selected only in-batch methods that provided the same derivatives or, in the absence of reports, their structurally related analogues. Then, solution-based protocols for each selected reaction were systematically compiled (Tables 1–4 in the ESI†), using conventional parameters employed by synthetic chemists, such as type of reagents and solvents, reaction conditions (time, temperature), work-up and purification procedures, as well as yields, purity and scale. Assuming the isolated yield as a reliable parameter to assess the quality of a synthesis protocol, we then calculated the average value for each type of in-batch chemical transformations from the literature review and compared it to isolated yields obtained accordingly to in-house solution-based procedures (Fig. 4, Stage 2B).24–26 The results confirmed that our routinely used in-solution protocols are representative and consistent with those reported by other research groups (Tables 1–4 in the ESI†).
![]() | ||
Fig. 5 Selected reactions for verifying the greenness and whiteness of the mechanochemical and solvent-based methods using the RGBsynt model. Experimental conditions for the presented mechanochemical O-alkylation (O1–3), N-alkylation (N1–3), nucleophile aromatic substitutions (SNAr1–3), and sulfonylation (S1–3) reactions were taken from our previously reported data.9,22,23 Newly developed synthetic procedures for obtaining selected drugs – propranolol and brexipiprazole as well as intermediates of vortioxetine and sulfasalazine – are presented in detail in the ESI.† Solvent-based chemical transformations are in accordance with in-house protocols,23–26 and the literature data.27–31 |
In parallel, to expand the set of evaluated methods for RGBsynt assessment (Fig. 4, Stage 3A), we adapted the reported O- and N-alkylation mechanochemical procedures for the synthesis of propranolol (a first-in-class β-blocker) and brexpiprazole (a third-generation antipsychotic; see structures in Fig. 5). Additionally, we optimized SNAr and sulfonylation reactions in the ball mill for key intermediates of the antidepressant vortioxetine and the anti-inflammatory agent sulfasalazine, respectively (Fig. 5). To meet the objective criteria, we selected in-solution methods for synthesis of the abovementioned drugs and drug intermediates from the literature review (Tables 5–9 in the ESI†). Due to the limitation in finding detailed and reliable experimental procedures reporting on amounts of reagents and solvents used, reaction condition work-up/purification step protocols and yields, patents were excluded from the analysis. The selection was based on the following criteria: (i) laboratory scale (up to 20 g), (ii) the use of the least toxic reagents and solvents; (iii) cost-effective and commercially available substrates (excluding explosives and highly flammable reagents), (iv) the shortest reaction time and lowest reaction temperature and (v) smooth work-up procedures (e.g., extraction and/or crystallization) for purification, excluding column chromatography methods where possible. This enabled the identification of high-quality in-batch methods suitable for the comparison with the newly developed mechanochemical procedures (Fig. 4, Stage 3B).27–31
Finally, the 17 known and newly developed mechanochemical reactions were compared with the 17 solution-based alternatives in terms of their greenness and whiteness, using the RGBsynt model (Fig. 4, Stage 4). The experimental details referring to all the reactions disclosed herein are shown in the ESI.†
HPLC analyses were performed by using an Arc Waters System (Waters Corporation, Milford, MA, USA) equipped with a UV/Vis PDA spectrophotometric detector. Spectra were analysed in the 200–800 nm range with 1.2 nm resolution. Chromatographic separations were carried out using a Chromolith SpeedROD RP 18 column with dimensions of 4.6 × 50 mm and particle size of 1.7 μm. The column was maintained at 40 °C, and eluted under gradient conditions from 95% to 0% with eluent A over 3 min, at a flow rate of 3 mL min−1. Eluent A was water/formic acid (0.1%, v/v); eluent B was acetonitrile/formic acid (0.1%, v/v).
Mass spectra were recorded using a UPLC-MS/MS system comprising a Waters Acquity Premier instrument coupled to a Waters Xevo TQ-S Cronos mass spectrometer (electrospray ionization mode, ESI). The Analyses were carried out using an Acquity UPLC BEH (bridged ethylene hybrid) C18 column (2.1 × 100 mm, and 1.7 μm particle size), equipped with an Acquity UPLC BEH C18 VanGuard pre-column (2.1 × 5 mm, and 1.7 μm particle size). The column was maintained at 40 °C, and eluted under gradient conditions from 95% to 0% with eluent A over 10 min, at a flow rate of 0.3 mL min−1. Eluent A was water/formic acid (0.1%, v/v); eluent B was acetonitrile/formic acid (0.1%, v/v). Chromatograms were recorded using a Waters eλ PDA detector. Spectra were analyzed in the 200–500 nm range with 1.2 nm resolution and sampling rate of 20 points per second. MS detection settings of the Waters Xevo TQ-S Cronos mass spectrometer were as follows: source temperature 150 °C, desolvation temperature 350 °C, desolvation gas flow rate 600 L h−1, cone gas flow 100 L h−1, capillary potential 3.00 kV, cone potential 30 V. Nitrogen was used as both the nebulizing and drying gas. The data were obtained in scan mode ranging from 50 to 1000 m/z in 0.5 s time intervals. Data acquisition software was MassLynx V 4.2 (Waters). 1H-NMR spectra were respectively recorded using a JEOL JNM-ECZR500 RS1 instrument (ECZR version) at 500 MHz (JOEL Ltd, Tokyo, Japan), and reported in ppm using deuterated solvent for calibration (CDCl3 or DMSO-d6). The other experimental details are shown in the ESI.†
The assessment results shown in Fig. 6 and 7 clearly indicate that the mechanochemical approach is both greener and whiter, i.e. better overall. Among the criteria divided into three attributes, the differences observed for the red parameters were relatively the smallest. In particular, product purity was usually similar in both reaction cases, although yield values were almost always higher for mechanochemical reactions. The largest differences were recorded for the remaining green and blue criteria.
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Fig. 7 Results of assessing various types of synthesis reactions in terms of the saturation of the corresponding colours of the RGB model. |
The E-factor and ChlorTox values were significantly lower (i.e., better) for the mechanochemical methods in each case. This improvement is primarily due to the elimination of column chromatography purification steps, which are typically required for solution-based reactions. Large volumes of reagents such as n-hexane, ethyl acetate, dichloromethane and methanol – used as components of the mobile phase – resulted in an unfavourable comparison of the E-factor value indicating increase in the waste production. Moreover, their high harmfulness reflected in WHN values (hazards presented in safety data sheets) contributed to the significant differences in the ChlorTox values. However, mechanochemical methods were not completely “pure”. The extraction stage still involves the use of harmful solvents such as dichloromethane and ethyl acetate, albeit in much smaller amounts than in the case of the solution-based reaction. To illustrate how these two approaches compare to each other with respect to chemical risk, the ChlorTox values obtained for O-alkylation in-solution suggest a risk corresponding to approximately 276 grams of chloroform, whereas the respective mechanochemical reactions for obtaining the same product correspond to only 35 grams.
An important reason for the worse assessment of the whiteness of the traditional solution-based approach is also the time of the entire synthesis procedure, which due to the need for chromatographic purification, was several times longer. The energy demand estimation for this type of reaction also results in it having a worse performance since it also depends on the procedure time (eqn (3)). However, it is worth mentioning that the number of instruments powered by electricity and their overall power used in both methods were similar. An interesting example of an electrical device is the magnetic stirrer used in solution mixing, which displays higher overall energy consumption than the vibrational ball-mill used in the mechanochemical approach due to the prolonged heating and operation time required for solution-based procedures.
An interesting aspect is also the mutual comparison of O-alkylation, N-alkylation, nucleophilic aromatic substitution and sulfonylation (Fig. 6 and 7), even though this was not the main goal of this study. It turns out that for both solution-based and mechanochemical reactions, the sulfonylation reaction was rated the highest in terms of greenness and whiteness. On the other hand, the aromatic substitution reaction scored the worst in the case of the solution-based approach, while N-alkylation had the lowest green and white score among reactions performed by mechanochemistry.
To ensure unbiased comparisons, a comprehensive database was created, gathering data from the literature survey on in-batch procedures (i.e., O- and N-alkylation, SNAr, and sulfonylation reactions), followed by newly developed synthesis procedures for selected drugs (propranolol, brexpiprazole) and key drug intermediates for vortioxetine and sulfasalazine. This allowed us to establish that our already disclosed solution-based methods are representative and suitable for analysis. In parallel, the mechanochemical procedures already reported by our group were supplemented with new protocols adapted specifically for this study. In total, 34 methods were assessed, half of which were solution-based reactions and half that were their mechanochemical counterparts.
RGBsynt is the first whiteness metric applied to synthesis methods, taking into account their specificity and considering the most important parameters determining individual attributes represented by red, green and blue primary colours. The greenness assessment using the E-factor is enriched with the ChlorTox Scale – a chemical risk indicator that considers the hazards of each reagent independently enabling a quantitative comparison of methods. In addition, a simplified approach for estimating energy demand is used, which does not require direct electricity measurements for each device. By taking into account only the most important criteria, the model remains transparent, intuitive and user-friendly.
The assessment results demonstrate the superiority of mechanochemistry as an overall better synthetic strategy than traditional solution-based methods, as indicated by the higher whiteness and greenness scores. In particular, mechanochemistry offers several advantages such as improvement of yields, limitation of the use of organic solvents, and simplification of workup procedures while avoiding the need for chromatographic purification, which usually involves huge amounts of mobile phase components. This also ensures shorter duration times for the synthesis process and reduces the energy consumption. Importantly, our conclusions are consistent with the recent report by Sharma et al. on the greenness of mechanochemistry, which was analyzed with the DOZN 2.0 tool.20 However, the obtained results cannot be easily extrapolated to other types of reactions.
In addition, although the calculated green metrics (E-factor and ChlorTox) may seem very favourable, the mechanochemical approach may not be considered an ideally green approach. In our case, the purification stage by extraction following a mechanochemical reaction still involves the use of harmful solvents (ethyl acetate and dichloromethane), albeit in much smaller quantities than those used in solution-based reactions.
Finally, we postulate that a novel RGBsynt model can be successfully used to compare other synthesis methods, where the attached Excel template† can be used for that purpose. We strongly believe that whiteness, as a measure of “how greenness is reconciled with functionality”, might serve as a valuable parameter for identifying the overall best organic synthesis methods within the assessed group.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4gc05097e |
This journal is © The Royal Society of Chemistry 2025 |