3.1. Headspace Analysis
Determination of VOC emissions from different materials is crucial for human safety and the development of the least harmful products. However, this aspect of polymeric materials is not very often investigated and described in the literature. In the case of polymeric materials, emissions during materials’ processing are more commonly analyzed [
29]. On the other hand, emissions during processing are often related to the changes in the chemical structure of the material, which can result in emissions during the further stages: postproduction treatment, packing, transport, and use of various products. Therefore, to fully evaluate the benefits and drawbacks of the product, it is essential to determine its impact on the environment and human health during use, when the humans’ contact with the product is the most intensive [
30]. Such an approach is more and more pronounced these days. In the presented case of POM and EVA materials, which are intended to be used in 3D printing, this is especially important, because of the growing popularity and accessibility of 3D printers, not only for industrial but also for hobby and household applications [
31]. Generally, recently conducted studies of Noguchi and Yamasaki [
32] indicate that both POM and EVA are characterized by relatively low VOC emission rates in comparison to polyolefins or, especially, poly(vinyl chloride). However, these authors conducted their analysis at 50 °C and did not investigate emitted VOCs in qualitative terms, as is done in the present work. Our results are summarized in
Figure 2 and
Table 4, where emission is shown quantitatively and qualitatively.
It can be seen that the volume of emission strongly depends on the content of EVA. Such an effect is associated with higher emissions related to neat EVA when compared to POM [
32]. The highest emissions were observed for 5.0 wt.% content of EVA. However, for all contents, emissions are relatively at similar levels. Moreover, values of the TVOCs parameter obtained after two times of sample conditioning are presented in
Figure 2. Before the analysis, samples present in chambers were purged with gas to stabilize the analysis conditions. It can be seen that the conditioning of samples for a longer time significantly decreases the emission level, which indicates that the majority of VOCs are emitted during the first 30 min of analysis. Such an effect can be exciting and essential for the potential applications of analyzed materials because proper postproduction treatment of the product may significantly reduce its environmental impact. Considering the more and more pronounced issues of the environmental aspects of different processes and products, the influence of sample conditioning on the VOC emission should be investigated in further studies.
Table 4 presents the main VOCs detected during analysis of the prepared materials. They are grouped according to their chemical structure. Regarding POM, literature reports related to the VOCs emitted by this material are mainly focused on the most abundant compound—formaldehyde [
29,
33,
34]. However, this compound was not detected here because of the application-defined type of sample-treating instrument and the kind of sorption material. The application of Tenax TA as a sorption material gives a possibility to collect the analytes from the VOCs group, from C
5 even up to C
30.
In consequence, there is a very low possibility that any formaldehyde potentially emitted from the studied samples will be adsorbed and collected by applied type of sorption medium. Besides, the application of the GC-FID system and defined type of GC column gives a possibility to perform the analysis of a broad spectrum of VOCs, excluding formaldehyde. The TD-GC system is not a suitable configuration for the formaldehyde analysis. Generally, in the analytical laboratory practice for formaldehyde emission studies, the containers filled with silica gel, cellulose, or glass fiber filters coated with appropriate reagent, namely 2,4-DNPH (2,4-dinitrophenylhydrazine), are applied. Then, the derivatization product (2,4-dinitrophenylhydrazine derivative of formaldehyde) is analyzed with the use of high-performance liquid chromatography (HPLC) combined with a UV-Vis detector [
35].
It can be seen that significant traces of hydrocarbons, alcohols, phenols, aldehydes, and ketones, as well as carboxylic acids and esters, were emitted from the samples. Such a combination of organic compounds is typical for the headspace analysis of polymeric materials [
30]. For EVA materials, a similar composition of VOCs was already reported for SAFC Biosciences EVA BIOEAZE bags [
36]. The presence of hydrocarbons is related to the polymeric nature of materials. These compounds are often detected, as confirmed by other works [
32,
37]. The presence of other compounds mentioned above is often associated with the processing of the material and even minimal changes in chemical structure during thermal and mechanical treatment, e.g., extrusion. Although polymeric materials are usually processed at temperatures noticeably below their onset of degradation, they are still subjected to oxidation. In the case of POM, even at 160 °C, slight decomposition may occur, resulting in the generation of aldehydes, ketones, or alcohols [
38]. For EVA, the most commonly reported compounds are those containing hydroxyl and carbonyl functional groups, such as alcohols, lactones, esters, and ketones [
39]. Barlow et al. [
37] detected a significant amount of hydrocarbons, of which over 80% were characterized as heavy hydrocarbons. Among other groups, they noted the presence of acetaldehyde, benzaldehyde, acetone, and formic and acetic acids. These results correspond with the data presented in
Table 4. Except for these compounds, related to the use of POM and EVA, other chemicals were detected, whose presence was ascribed to the storage and processing of various polymeric materials in the same laboratory hall. The presence of low amounts of toluene, styrene, and trichloromethane was noted and was not mentioned here.
Table 4 also presents areas under the peaks related to the included compounds; however, in this case, these should not be directly used to determine the specific amounts of particular emissions quantitatively. Nevertheless, changes in signals’ intensity still can suggest an increase or decrease of specific emissions. With the addition of EVA, a significant increase in the intensity was noted for peaks ascribed to the presence of vinyl compounds, acetic and formic acids, acetone, and butylated hydroxytoluene (BHT). Except for the last one, the presence of other compounds is associated with the chemical structure of EVA and was previously noted by Barlow et al. [
37]. BHT is commonly applied as an antioxidant for polymers, e.g., for polyolefins, and was also detected by headspace analysis of PP and PE in another work [
40].
Regarding hydrocarbons, the intensity of signals was quite similar; however, in total, the area under peaks related to presented hydrocarbons slightly decreased with EVA content. For alcohols, phenols, and aldehydes, the decrease or absence of signals associated with a particular compound was followed by the increase or appearance of other ones. In the case of phenols, signals for BHT were weakened with the increase of the EVA content, but they were substituted by 6-
tert-butyl-2,4-xylenol, the compound used as polymerization inhibitor [
41]. The primary ketone detected for neat POM was acetophenone. When POM was partially substituted by EVA, acetophenone was still present, but its amount was noticeably lowered, and it was replaced with other ketones. Therefore, the total area under peaks ascribed to the presence of ketones was higher when EVA was added. Generally, these differences are associated with the different composition of the material and hence also the different products of thermo-oxidative decomposition, which may partly occur during thermomechanical processing with extruders or injection molding machines.
Values of vapor pressure, which can be considered as the quantitative measure of a material’s volatility, are presented for all compounds. In general, there is no actual value of vapor pressure that determines if the compound is considered to be a VOC [
42]. Although it is not a strict definition or standard, the United States Environmental Protection Agency exempts solvents in consumer products with a maximum vapor pressure of 13.3 Pa at 20 °C. These compounds show little or no volatility, which would not result in significant VOC emissions [
43]. According to these criteria, part of the compounds listed in
Table 4 should not be considered as VOCs. Nevertheless, for the full assessment of the harmful effects of chemicals, except the volatility, the exposure limits should also be considered. A combination of these factors would provide a broader view of the threat posed by particular materials.
Therefore, except for the vapor pressure,
Table 4 presents codes according to NFPA 704 (Standard System for the Identification of the Hazards of Materials for Emergency Response), which is commonly used for classification of chemicals by the risk they pose towards human health and safety [
44]. The NFPA 704 system is commonly known as the “safety square” or “fire diamond” and is applied to quickly and easily identify the risks and select the proper procedure for handling chemicals. It was developed by the National Fire Protection Association from the United States. It assesses chemicals’ flammability, health risk, and instability (noted as F, H and I in
Table 4) on a scale from 0 (minimal hazard) to 4 (severe hazard), also providing information about special hazards related to the material.
It can be seen that a couple compounds are listed whose health hazard (blue) indicator is at level 3, meaning that short exposure could cause serious temporary or moderate residual injury. Among these compounds, limonene, acetic acid, and formic acid should be considered as a significant threat, especially considering their values of vapor pressure. On the other hand, they are also characterized by the flammability rating (red) of 2, meaning that they must be moderately heated or exposed to relatively high ambient temperature before ignition can occur. Such compounds are characterized by the flash point values between 37.8 and 93.3 °C.
3.9. Suitability for 3D Printing
The extruded 3D-printing filament with a diameter beyond the tolerance range of 2.85 ± 0.05 mm due to the limitation of the twin-screw extruder and original filament collection system was printed on modified 3D printers, allowing the use of a wide range of diameters with reduced print quality. ISO 527-2-1A specimens were printed with each material ten times. The results of the performed tests are presented in
Table 10 and
Figure 7.
From the beginning of the printing process, the 3D printer operator was waiting for any sign of print detachment from the printing bed. If the problem occurred, the process was stopped and considered as unsuccessful. Each research material was used in at least one attempt to complete an unsuccessful print in order to check for adhesion to the printing table, where despite the peeling problem it was allowed to finish the printing process.
The main problem with printing with this material was insufficient adhesion to the printing table despite using glue adhesive. Most of the printed specimens started to warp at the beginning of the printing process, like POM without any addition, which is shown in
Figure 7 in comparison to the completed 3D-printed specimen.
Specimens with 7.5% addition of elastic EVA exhibited low filament column strength. This problem caused bending and buckling of the filament before plasticization of the material in the printing nozzle.
The addition of EVA improved material adhesion to printing bed and resulted in higher prints before warping, in addition to allowing some printings to finish without any deformation. Such an effect can be related to the lower shrinkage and higher flexibility of the EVA phase in comparison to the POM material. Incorporation of 5.0 and 7.5 wt.% EVA resulted in a similar success rate. As a result, these concentrations of modifier may be considered as practically equally suitable for use, depending on the desired properties of the final print (such as those related to the mechanical performance). Nevertheless, further works should examine the impact of the temperature of the printing table and the type of glue used to provide adhesion between print and table.
Figure 8 shows unsuccessful attempts to print ISO-527 specimens with the addition of 2.5 and 5.0 wt.% of EVA in comparison to one of the successful prints.