Implementation of the emulsification-diffusion method by solvent displacement for polystyrene nanoparticles prepared from recycled material.

From an integral perspective, nanotechnology can be used to care for the environment by improving current preparation methods and facilitating industrial scale-up. This article discusses the implementation of techniques for obtaining polystyrene nanoparticles (PSN), as an added value, using an emulsification and solvent displacement method (EDSD); the solvent displacement is a novel modification to the emulsion-diffusion methodology, where the diffusion is done directly on the emulsion, which allows concentrated dispersions that facilitate direct use to be obtained, eliminating the dilution with water and the recovery of water by additional processes. The solvent was recovered by reduced pressure, which is class 3, conforming to ICH, and making this method sustainable. The optimization of this process has not been reported elsewhere. This approach made it possible to obtain highly-concentrated nanoparticles while allowing the reuse of the solvent. A scaling proposal is presented that integrates the conditioning of the solid urban waste material called expanded polystyrene (EPS) foam that constitutes a serious environmental problem both nationally and globally. Hence, the article presents an alternative to the recycling of EPS, and a methodology in the context of green chemistry, because solvent is recovered to prepare other batches. The PSN obtained from this waste material had a minimum particle size of 225.8 nm, with a polydispersion index of 0.158. Process performance was 97.1%, and the solvent was recovered at a maximum rate of 85%. The morphology of the PSN was spherical and uniform, with a smooth surface. This journal is © The Royal Society of Chemistry.

Introduction

One of the most important challenges of nanotechnology consists of preparing nanoparticles by simple, non-polluting processes. In this regard, the use of preformed polymers is preferable to those that require polymerization reactions, due to the residues that may be generated.[1] Other objectives of preparing preformed polymer particles are: (i) obtaining dispersions with a high concentration of solids; (ii) using the minimum amount of solvents or, preferably, “green” solvents; (iii) devising more environmentally friendly processes (e.g., by reusing solvents or using waste polymers); and (iv) achieving technological feasibility such as easy implementation and susceptibility to industrial scale-up.[1-6] One recent proposal that has drawn attention consists of recycling polymers for industrial use by forming nanoparticles for later applications.[7,8] One polymer of interest is EPS, a waste material. In 2016, discarded plastics accounted for 12% of all solid waste worldwide. In Mexico, 10.9% of solid urban waste consisted of plastics, with EPS being one of the most common thermoplastics, after polyolefins and polyvinyl chloride. However, in Mexico in 2012, only around 9.63% of the total volume of urban waste generated was recycled (INECC, 2012).[9] EPS can be used to prepare polystyrene nanoparticles that could have various uses at a low cost, with scale-up potential, and environment-friendly processes. The task of scaling up nanoparticle production demands evaluating process design, optimizing preparation variables, and an adaptation process from small- to large-scale operating conditions.[10,11] Polystyrene nanoparticles obtained of EPS can be used for a huge variety of different purposes which can include: in the form of a coating on Kraft paper,[12] treatment of phenol contaminated industrial wastewater,[13] a paint binder,[14] wood plastic composites,[15] concrete impregnated,[16] DVD cases and office equipment,[17] materials for use in filtration applications,[18] among others.

Rajeev et al. reported the preparation of polystyrene particles from annealed expanded polystyrene by the nanoprecipitation or solvent displacement method using polar solvents. The final diameter was less than 500 nm.[19] Mangalara and Varughese obtained polystyrene nanoparticles using d-limonene as polystyrene solvent and PVAL as stabilizer by the emulsification-diffusion obtaining a maximum of 86% PE in the final dispersion. These authors stood out the sustainability of the method.[20]

The literature contains several reports on preparation methods that incorporate preformed polymers into emulsified systems, developed as a first step towards increasing the exposed surface area and permitting processes of polymeric aggregation in non-solvent microphases. A second step involves forming nanoparticles by controlled aggregation and “diffusion-stranding” stabilization of the polymer.[2,21-23] The best-known processes are emulsification–evaporation,[1,24-28] salting-out,[5,22,29-31] solvent displacement (or nanoprecipitation)[4,21,32-34] and emulsification-diffusion.[24,27,35-38] Modalities of these processes include dialysis,[21] emulsification with solvent displacement,[1,3,39] and spray-drying.[21,40-42] In this regard, Campardelli et al. evaluated adding a continuous supercritical fluid processing step to improve the emulsification-diffusion method by eliminating the organic solvent from the nanosuspension obtained.[43] Naranjos et al. evaporated the solvent using reduced pressure.[24] Kwon et al. removed the nanoparticles by dialysis to separate the added water from the nanoparticles,[37] while Quintanar et al. used distillation, or cross-flow, filtration to eliminate the organic solvent, according to its boiling point,[5] and recovering the solvent by a distillation process.[20] Staff et al. prepared nanoparticles of polystyrene by the emulsion–solvent evaporation process, using chloroform, toluene and other solvents.[44]

The emulsification-diffusion method by solvent displacement is a modality of the emulsification-diffusion method that consists in carrying out the diffusion phase via direct extraction of the solvent under moderate temperature and reduced pressure. This process was developed to obtain concentrated pseudolatexes,[1,3,39] but has been proposed, as well, for applications in biotechnology and nanomedicine.[1] It has important advantages over other methods; for example, using acceptable organic solvents, allowing the preparation of nanospheres and nanocapsules with high yield and excellent reproducibility, and facilitating particle size control, among others.[45] The emulsion-diffusion method consists of two steps. First, an emulsion is formed from a mixture of a partially-miscible solvent in water (previously saturated with water) that contains the polymer, with an aqueous phase (previously saturated with the solvent) containing the stabilizer. Once the emulsion is obtained, the second step consists in diffusing the solvent from the internal phase (globules) by diluting the emulsion, using considerable amounts of water. This change in composition causes the polymer to enter a “non-solvent” phase that produces polymer aggregates called “protonanoparticles” of colloidal size from which nanoparticles will form, provided the stabilizer impedes coalescence.[3,5,21,36,46] This method has been adapted successfully and has produced important results, such as developing micro and nanospheres in which drugs can be either trapped in a matrix or dispersed into an oil core covered by a polymeric membrane that can be dissolved, chemically adsorbed, or bonded to the surface of the particles.[2,47]

The aims of this project are to develop and optimize the emulsion-diffusion method for preparing polystyrene nanoparticles as a recycling procedure, presenting a modification to the emulsion-diffusion method where one of the main advantages is that the diffusion is done directly on the emulsion (EDSD), which allows us to obtain concentrated dispersions that facilitate its direct use, evaluating the parameters for industrial scale-up. The use of nanoparticles preformed from waste material can have potential technological applications for the industry. This can minimize the useful life of large volumes of polymer waste, while decreasing production in synthesizing new materials with a favourable impact on the environment.

Experimental protocol

Materials

EPS waste from packaging materials used with household appliances was collected in signposted containers at the Faculty in a pilot waste recovery program. Ethyl acetate (EtAc) was supplied by Fermont, Mexico. The stabilizer, polyvinyl alcohol (PVA, Mowiol® 4-88 Mw ∼ 31 000), was purchased from Sigma-Aldrich, USA. Purified water was of Milli-Q quality (Millipore, USA-Bedford, MD). All other reagents were of at least analytical grade and were used without further purification.

Methods

EPS densification

The EPS was first washed in a commercial detergent solution (1%) and then rinsed with sufficient water to remove all foreign matter. This cleaning process also decreased the presence of electrostatic charges. Subsequently, the material was exposed to heat treatment at 130 °C for 15 minutes in an oven (Thelco model 16, GCA/Precision Scientific) to effectuate the transformation from a foamy to a plastic state that reduced the volume and increased the original density, thus facilitating handling and final disposal.[48]

Preparation of PSN

The dispersions were prepared by the EDSD with emulsion at a recommended ratio of 1 : 2 EtAc/water.[1] For this purpose, the EtAc and water were mutually saturated in a separating funnel under manual agitation for 1 minute before use to ensure the thermodynamic equilibrium of both liquids. The densified EPS was dissolved from 1 to 10% (w/v) in the saturated EtAc (organic phase) using magnetic agitation until dissolution was complete. The organic phase was emulsified in a saturated aqueous solution containing from 1 to 5% (w/v) of PVA (aqueous phase) under agitation at 733.04, 1152.92 and 1623.16 s−1 from 1 to 10 min in a rotor–stator device (Ultra-Turrax® T18 Basic, IKA-Werke, Staufen, Germany). Finally, the emulsion was subjected to distillation under reduced pressure to remove the solvent by evaporation (Laborota 4000 Heidolph Instruments, Schwabach, Germany) at 40 °C and 9.3 kPa with stirring at 6.28 s−1, until complete evaporation was achieved. As much as 85% of the EtAc was recovered and reused to prepare other batches.

Process performance calculation of PSN

The process performance of the method was determined using eqn (1). The PSN suspension was filtered through medium-pore filter paper (previously weighed, PP). After filtration, purified water was added to remove any nanoparticles that might have been trapped in the filter paper. The filter paper (PF) was dried at room temperature for 48 hours to a constant weight.PP: initial weight of the filter paper without residue. PF: weight of the dry filter paper with residue.

Experimental design

The influence of certain quantitative factors (see Table 1) was evaluated using a 4-factor fractional response surface factorial design; however, for the purposes of this study, only a few results were reported for such quantitative factors as the polymer and stabilizer with respect to particle size, the polydispersion index, and process performance.[8] The experimental design was based on a concentration range of the polymer of 1.0 to 10.0%, and 1.0 to 5.0% for the stabilizer. The software used was Design Expert®, version 10, StatEase Minneapolis, U.S.A. The experimental batches that resulted from these factors are summarized in Table 2.

Initial quantitative factors in the nanoparticle preparation by the EDSD method

Factor	Range analysed
Polymer	1.0–10.0%
Stabilizer	1.0–5.0%
Stirrer speed	7000, 11 000 and 15 500 rpm
Agitation time	1–10 minutes

Experimental batches of the I-optimal design of polymer and stabilizing factors

Batch no.	Polymera (w/v%)	Stabilizerb (w/v%)	Batch no.	Polymera (w/v%)	Stabilizerb (w/v%)
1	5.77	4.70	14	10.00	1.00
2	5.86	5.00	15	1.00	5.00
3	5.95	1.00	16	8.65	1.00
4	8.65	1.00	17	1.00	1.00
5	1.00	1.00	18	1.00	3.64
6	1.00	4.56	19	1.00	5.00
7	5.32	3.56	20	1.00	3.64
8	10.00	3.50	21	5.77	4.70
9	10.00	5.00	22	1.00	1.00
10	10.00	5.00	23	10.00	3.50
11	1.00	1.52	24	10.00	1.00
12	5.32	3.56	25	5.65	1.00
13	10.00	2.95	—	—	—

Organic phase.

Aqueous phase.

The information corresponding to the analysis by the 3-D response surface methodology proceeds from the results obtained from the characterization of the 25 experimental runs proposed by the I-optimal design. The variables analyzed to study the relation between the response and independent variables and so determine the optimal preparation conditions were particle size, the polydispersion index, and process performance. It is important to mention, however, that these results were determined by the mathematical model that best fitted the data obtained from the I-optimal design. Likewise, the equation from the model used in the diagnostic graphs was analysed using the quadratic polynomial model, after validation through a suitability verification analysis, according to the assumptions of normality, constant variance, and independence, to ensure the accuracy of the representation of the real system.[49] According to Hernández this procedure generates results with a strong correlation between the model's predictions and real results, and so allows analyses of the values of the factors that optimized those of the variables.[8]

Characterization of the PSN

Particle size analysis

The average particle size and polydispersity index were determined using the dynamic light-scattering (DLS) technique on a Nano ZS Zetasizer (ZEN3600, Malvern Instruments Ltd., Enigma Business Park, Grovewood Road, UK) at 25 °C with a detection angle of 173°. All samples were diluted with an excess of purified water and analyzed in triplicate.

Determination of zeta potential

The electrical charge of the nanoparticles in dispersion was determined by electrophoretic mobility using Doppler Laser Electrophoresis equipment and a Nano ZS Zetasizer (ZEN3600, Malvern Instruments Limited, UK). Measurements were made in triplicate at 25 °C after diluting the samples in water.

Differential thermal analysis

The thermal stability of the undensified and densified EPS, and of the lyophilized PSN, was analyzed by differential scanning calorimetry (DSC) in a Q10 TA Instruments, DSC Discovery (New Castle, DE, USA), with a heating ramp of 10 °C min−1, from 0 to 200 °C in a nitrogen atmosphere at a flow of 50 mL min−1. The PSN were previously lyophilized in a Labconco freeze-dryer (77520-00 Labconco, Millrock Technology, Inc. Kinsgston, NY, USA).

Scanning electron microscopy

The morphology of the PSN was registered by scanning electron microscopy (SEM) in a microscope (model LV-SEM, JSM 5600 LV, JEOL, Tokyo, Japan) with a resolution of 5 nm at 7 kV, and a voltage chamber pressure of 12–20 Pa. The samples were prepared by covering the surface with a gold film (∼20 nm) in a sputter coater cathode evaporator (JFC-1100, JEOL, Tokyo, Japan) under exposure to the environment until removal of the excess water.

Results and discussion

Densification of EPS waste

This study was designed to evaluate the use of waste material with potential technological applications, such as preparing PSN to introduce them in useful materials giving them functionality or improvement of properties, such as construction materials, as in gypsum-boards mentioned in section 3.5. In this regard, Fig. 1 shows the material in its original volume (Fig. 1a), and after heat treatment (Fig. 1b). The thermal treatment sufficed to reduce the volume/weight ratio and facilitate the final disposition for easy handling with a low generation of electrostatic charge. Thermal densification was achieved by changing the foamy state to a compact solid state (rigid texture). This approach is consistent with the study by Kan and Demirboğa, who described a rigid texture with a morphology distinct from that of the original foams after EPS thermal treatment.[48] This result justifies proposing the thermal treatment method to reduce the volume of EPS at the industrial level to approximately 90%, thus facilitating its handling, storage, and disposal.

Fig. 1

Waste EPS cut into pieces (a) and densified by heat treatment (b).

Preparation of the PSN

Another objective was to prepare preformed PSN from recycled material, while evaluating the maximum quantities of EPS that can be transformed into nanoparticles by EDSD in a modification of the emulsification-diffusion method[1] (Fig. 2). In addition, we proposed determining optimal fabrication conditions. It is important to emphasize that one of the main advantages of this method is that it induces diffusion from the emulsion by evaporation instead of water dilution. This allowed us to obtain dispersions with high solid content, as we report in detail in the following section. Introducing a water-soluble organic solvent to the continuous phase has favourable effects on the formation of the nanoparticles. He et al. observed the evolution of the internal structures of polystyrene microspheres went from porous to hollow, after introducing ethanol which allowed control of the internal structures of the microspheres as well as decreased the particle size of them, attributing this effect to the decrease in surface tension caused by solvent.[50]

Fig. 2

Emulsification-displacement process of the solvent at laboratory scale.[36]

Particle size, the polydispersion index, and process performance

The effect of PVA concentration on the particle size of different EPS concentrations is shown in Fig. 3a. Lower stabilizer concentrations (≥0.25%) were sufficient to obtain nanometric dispersions. A pronounced decrease in particle size was observed from 0.5 to 1.0% PVA. The smallest size obtained for all EPS concentrations was near 300 nm; higher PVA concentrations did not contribute significantly to a size reduction. Similar results were reported by Rao & Geckeler, in PSN 300 nm in size using solvent removal under reduced pressure to purify the dispersions.[21] Quintanar et al. obtained polymeric nanoparticles approximately 300 nm in size using direct displacement of the solvent by distillation, thus omitting any homogenization step.[1] In contrast to the results reported by Mangalara and Varughese obtaining smaller particle sizes and a narrow polydispersity with increasing PVA concentration (10 wt%).[20] Other authors have reported polymer nanoparticle sizes of 100–500 nm using the emulsion-diffusion approach, depending on the technique used to carry out the diffusion process; for example, solvent evaporation, adding water, or salting out, among others.[23,26,36,37,51,52] Quintanar et al. prepared polymeric nanocapsules with a mean size of 303–510 nm, depending on the organic phase, emulsifier, and drug systems used. To diffuse the solvent, water was added during the diffusion process.[5] Naranjos et al. used emulsion-diffusion with added water to diffuse the solvent and obtain some nanopolymers with particle size values in the range of 182–400 nm. They observed that the increase in the concentration of the emulsifier decreased the size of the nanoparticles by reducing the interfacial tension through the interaction of the emulsifier in the system interface that impeded the coalescence of the globules during emulsification and fostered a decrease in the size of the NP by increasing their concentration.[3] Hong et al. used the emulsion diffusion method and added water to diffuse the solvent and form polymeric nanoparticles below 100 nm in size.[53] Staff et al. observed a large polydispersion of the polystyrene particles formed by the emulsion–solvent evaporation process, requiring more control in the critical variables of process to prepare nanoparticles with a low polydispersion index.[44]

Fig. 3

Effect of polymer and stabilizer concentrations on average particle size (a), the polydispersion index (b), and process performance (c) by the EDSD method.

The manufacturing batches produced were characterized by a concentration of up to 10%, though particle size increased significantly as the amount of EPS increased, mainly at low stabilizer concentrations. This behaviour is related to the mechanism of the formation of the nanoparticles, since during the diffusion stage a higher polymer concentration contributes to forming a more saturated aggregation layer. Known as “diffusion–stranding”, this procedure generates the formation of nanoparticles,[38,54] considering that the stabilizer concentration is involved in the complex interfacial phenomena formed by the emulsion-diffusion technique,[55] but without taking into account the nucleation and growth of the nanoparticles.[38] Thus, even though the stabilizer may function adequately, the probability of particle aggregates passing from a more concentrated region is very high, which would explain the particle size increments with the increase in EPS. Concordant results were observed for the polydispersion index (Fig. 3b), as the distribution curve becomes wider at higher EPS concentrations. These differences were significant at low PVA concentrations (0.25%) but not at high ones, suggesting that the stabilizer function is appropriate for these concentrations (1.0%). PVA can stabilize globules in the emulsion and impede aggregation during diffusion in the solid–liquid interface.[54] This behaviour was also observed by Mora et al. where, regardless of the polymer, particle size increased at higher concentrations.[36]

Process performance in relation to the stabilizer content for different EPS concentrations is depicted in Fig. 3c. Low stabilizer concentrations (0.25%) make it possible to obtain dispersions with low yield. Differences among EPS concentrations are marked. PVA concentrations of 0.5% allowed yields above 70%, a level considered adequate. Quintanar et al. prepared nanoparticles of poly(d,l-lactic acid) with a yield >95%. In their study, diffusion was performed by adding water.[51] High production yields of particles (>70%) have been reported using emulsion-diffusion during the preparation of nanocapsules; however, it is essential to note that water must be added during diffusion.[43,54,56-59] Concentrations above 1.0% did not significantly increase the yield at any EPS concentration.

The response surface graph is shown in Fig. 4, illustrating the effect of polymer and stabilizer concentrations on process performance. The EPS concentration has the greatest influence on the process performance of the PSN, possibly due to the diffusion of the solvent, which allows the transport of polystyrene molecules into the “non-solvent” phase, and from the globules into the aqueous phase, leading to the formation of supersaturated areas of polymer, where the presence of the stabilizer prevents coalescence. With respect to the PVA concentration, this factor has a greater influence on process performance at higher concentrations. This mechanism allows the particles to form polymer aggregates in drops by interfacial phenomena, which are stabilized by the PVA, thus avoiding fusion and the formation of agglomerates, while remaining at the interfaces. PVA presents an adequate protection effect during the step of forming the PSN,[5,60] which requires a few milliseconds during the diffusion stage of the solvent from the emulsion drops to the aqueous phase of the system.[61]

Fig. 4

3-D response surface graph of the effect of polymer and stabilizer concentrations on process performance by the EDSD method.

Stability of the PSN

The values obtained upon measuring the zeta potential for all formulations – shown in Table 3 – represented a condition of stability. Values are higher than −30.00 mV,[61,62] where particle aggregation is less likely to occur due to the electrical repulsion provided by the PVA.[62] The charge is sufficiently high for the colloidal system to remain discrete, dispersed and in suspension.

Zeta potential values of the I-optimal design experimental formulations

Batch no.	Zeta potential (mV)	Batch no.	Zeta potential (mV)
1	−31.80	14	−34.17
2	−28.70	15	−30.33
3	−30.20	16	−28.37
4	−33.77	17	−33.37
5	−31.50	18	−32.00
6	−31.90	19	−33.87
7	−32.33	20	−32.10
8	−31.53	21	−26.40
9	−32.23	22	−26.87
10	−32.20	23	−26.57
11	−19.23	24	−28.90
12	−32.47	25	−26.97
13	−35.40	—	—

Differential scanning calorimetry

Thermal analysis showed that the thermal densification process at 130 °C does not affect EPS. It further revealed that the curves obtained by DSC were similar for densified EPS, virgin EPS, and the reference polystyrene (PS) (Fig. 5). Likewise, a change in the baseline at approximately 100 °C was observed, indicating the glass transition of the densified polystyrene, likely due to the evaporation of the gases contained in the cellular structure of this material, which presented a negative slope at lower temperatures. Similar results were reported by Samper et al. who observed glass transition temperatures around 105 °C for EPS, without observing degradation of the material up to 136 °C.[60] Those authors also reported an important fact regarding the glass transition temperature of unprocessed polystyrene particles, which is lower than that for EPS, thus allowing a higher state of thermal resistance of EPS than of unprocessed polystyrene particles. The physical transitions of EPS have also been studied by Mehta et al. with results for the density temperature between approximately 110 and 120 °C. In comparison, the melting temperature was observed at 160 °C. The vaporization temperature was reported to be 275 °C, while total volatilization occurred between 460 and 500 °C. This allowed us to observe temperature ranges of EPS handling that did not affect the environment when the material decomposed due to the effect of temperature. This also facilitated proper handling.[63] With respect to the undensified EPS, our analysis demonstrated a glass transition of the polymer from 100 to 110 °C, similar to that of densified polystyrene. This finding could be due to the effect just mentioned. Therefore, the DSC analysis confirmed that the densification process was adequate, since it verified that there was no degradation of the polymer.

Fig. 5

Results of differential scanning calorimetry analysis for the characterization of virgin EPS and densified EPS vs. reference PS.

Scanning electron microscopy

SEM depicted a spherical, uniform, smooth surface morphology of the PSN (Fig. 6). This shows that the EDSD method is suitable for forming nanoparticles of uniform morphology using low amounts of stabilizer. The sample shown corresponded to the optimized formulation of the I-optimal design, which agreed in size with the measurements made in DLS; that is 230.6 nm. Magnification at 7500× was sufficient to observe a well-defined morphology in the samples.

Fig. 6

Micrographs of nanoparticles obtained by the EDSD method at 5000 and 7000×.

Possible scale-up of PSN production

Considering the high production yields obtained, and the high concentrations achieved from PSN, it is possible to predict successful industrial-scale production that will give commercial value to the production of PSN, highlighting production based on recycling EPS waste and solvent recovery. PSN can be used in several applications with no risk for the environment; for example, in the construction industry. An application in gypsum-boards produced satisfactory results obtained by measuring the percentage of moisture absorption, which was lower than in gypsum-boards with no PSN incorporated.[8]

Based on the emulsification-diffusion method – which has been widely-researched – and total compression in the formation of nanoparticles, which is essential for easy scale-up.[53,54,58,64-68] All authors have predicted the factors and conditions that determine the optimization of the method. In this sense, Quintanar et al. mentioned as a key factor the relation between rapid solvent displacement and nanoparticle formation during diffusion.[35] This facilitates scale-up because, as the present study proposes, the solvent can be recovered for future use and the process fosters polymer aggregation, resulting in high nanoparticle yields when compared to the evaporation or filtration techniques commonly used as a subsequent emulsion step to form nanoparticles.[69] Mendoza et al. described the evaporation stage as a limitation in scale-up to produce large batches of nanoparticles because it must be efficient to obtain residual solvent.[3] In contrast to using solvent displacement in this method, the approach proposed is easy, versatile, and useful. In addition, the displacement of the solvent from the internal to the external phase is fast and, ultimately, leads to polymer aggregation.[35]

Fig. 7 presents a proposal for both the laboratory scale and industrial scale-up for producing PSN, and indicates the critical variables involved. The main components at the industrial scale are a mill and heating tunnel for the densification process. The fabrication of nanoparticles comprises various phases: the saturation system, mixing with a propeller stirrer, solvent evaporation under reduced pressure, and storage in a tank. Laboratory studies show that the critical variables – the bulk size of EPS, stirring times, volumetric mixtures ratios, concentrations, stirring times and rates, and temperatures – must all be controlled to prepare small nanoparticles with a low polydispersity index. Thus, the operating equipment required does not have to be highly-sophisticated to enable efficient scale-up.[3,35,54] Solvent evaporation under reduced pressure permits solvent recovery. As mentioned above, removing the organic solvent is the main aim in the solvent displacement step in this novel method, which has been used to resolve the formation of nanoparticles by rapid diffusion and allow the formation of supersaturated regions near the interface. In addition, environmental problems are avoided, so we can disregard this obstacle to the implementation of an efficient system for extracting the solvent and quickly achieving scale-up.[3]

Fig. 7

Schematic description of scaling-up to prepare polystyrene nanoparticles from urban waste using the EDSD method.

Other authors have identified drawbacks of scale-up; for example, that the emulsification-diffusion method requires diffusing a large amount of water to dissolve the organic phase during diffusion and, as a consequence, the need to dispose of large volumes of water.[54,64] In this case, the nanoprecipitation method must be controlled throughout the process, since the preparation of the emulsion requires large amounts of both phases, causing certain difficulties.[34] The high-pressure homogenization method demands a substantial increase in the circulation time of continuous 10 kg batches; thus requiring a change of batch size or a more discontinuous system.[70] Emulsification–reverse salting out methods, meanwhile, have potential problems of incompatibility between the salts and the drugs during the manufacture of nanocapsules, and due to the presence of electrolytes, which makes an additional stage of purification necessary.[53]

Conclusions

EPS foams can be treated by recycling to help reduce the problem of urban waste. The EDSD method allowed us to obtain satisfactory results when producing high-concentration polystyrene nanoparticles that meet the optimized formulation of the I-optimal design, with a 97.1% of process yield. This method not include the diffusion step with large amount water, and allowing the recovery of the solvent by up to 85%. The polystyrene nanoparticles obtained from this waste material presented a minimum particle size of 225.8 nm, and a polydispersion index of 0.158, with process values of 10% polystyrene and 4.8% stabilizer. The morphology of the polystyrene nanoparticles was spherical and uniform, with a smooth surface. The use of recycled material to produce polystyrene nanoparticles can aid in the treatment of solid urban waste, generate a value-added product with broad potential in the field of construction, and contribute to mitigating environmental pollution. In addition, solvent recovery for use in new batches can also benefit the environment, and it is a solvent class 3 considered not human health hazard conform to ICH. The experience in the handling of this technique allowed us to demonstrate the feasibility of industrial scale-up, due to such advantages as high reproducibility and versatility.

Conflicts of interest

There are no conflicts to declare by any of the authors.