1 Introduction
The commonly used electro discharge machining (EDM) is a technique to postprocess metallic and/or electrically conductive components for achieving desired shapes or textures with a defined material removal [
1,
2]. EDM techniques are based on an erosive character of electrical discharges between two electrodes in a dielectric fluid. Thereby, a conversion from electrical into thermal energy leads to the material removal. Nowadays, the two predominant techniques are die-sink EDM and wire EDM [
1,
3], which are important for sectors within the mold and construction industry for implementing features with high aspect ratios or bigger cavities and slots. Mostly, different types of die or hot work steels, which have in general a martensitic microstructure, are processed with both techniques. The main differences are the used dielectrics on the one hand, and the tool electrode material as well as geometry on the other hand. In wire EDM a brass or copper wire is used as an electrode, whereas in die-sink EDM mostly graphite electrodes are common. These processes are performed in deionized water (wire) and synthetic hydrocarbon oil (die-sink), respectively [
4,
5]. In this study, the focus lies on die-sink EDM and its waste streams operating with a graphite tool electrode and a martensitic hot work steel as the workpiece electrode, which is quite often H11 alloy.
In contrast, the sector of additive manufacturing (AM) gains more attention and a greater influence in several industries due to some major advantages [
6,
7]. However, AM powders are expensive due to their tight specifications regarding particle size distribution (PSD), circular/spherical shapes, chemical composition, allowable number of defects as well as flowability and bulk mechanics [
8‐
10]. Particle sizes in the range from 15 to 60 µm with a median particle size x
50,3 of around 30 µm are used in selective laser melting (SLM) [
9,
11] and sizes from 60 to 100 µm, max. 125 µm, with a x
50,3 of 70 to 80 µm for the electron beam melting (EBM) [
12,
13] process. Apart from that, the process of Binder Jetting (BJT) [
14,
15] and direct energy deposition (DED) [
16,
17] should also be taken into account, where various metal-based powders of different and/or bimodal PSD are used. Moreover, a low number of defects, good flowability characteristics as well as high circularities and sphericities of the powders are required for the formation of a homogenous powder layer to achieve good qualities of printed parts [
18,
19]. A checking on crystallographic information of appearing structures, lattices and phase fractions is another quality assurance tool for characterizing generated powders. Metallographic investigations of metallic samples, compact parts or powders, respectively, are important regarding their microstructure since this is influencing the manufacturing process itself and the final parts properties.
The main reason for the high costs of AM powders is the production. Nowadays, there is only the opportunity to manufacture powders via the cost and energy intensive process of powder atomization of metal melts [
20,
21]. In Germany the costs for raw materials in AM industry amount to approx. 50% of the total manufacturing costs, according to the Federal Statistical Office [
22]. Therefore, it is indispensable to focus on alternative ways of supplying metal powders. Current works related to this topic are mostly different recycling strategies for used powders to increase the resource efficiency. Most commonly, used powders with an undefined number of processed cycles in the AM chamber get manufactured again with or without creating mixtures in different ratios with virgin powder. For SLM it is reported, that a powder reuse comes along with changes in physical (particle fusion and agglomerates) and chemical (contaminations) properties caused by heat conduction and spatters in the powder bed degrading the powder layer [
23]. Lu et al. compared virgin and recycled 316L powder in SLM over several cycles and found an increase of coarser particles (particle spatter, fusion) with higher circularities and hardness in general [
24]. Moreover, the microstructure remains unaffected, whereas a slight change in the crystal structure and a significant increase of the oxygen content was observable. Rayan et al. investigated a maraging steel powder in SLM over several cycles leading to coarser particles and a degradation of the particle shape, but no changes in the bulk density [
25]. Besides that, tensile properties and fatigue behavior of printed parts are slightly affected with simultaneously more internal defects due to lack of fusion, gas entrapments and carbon inclusions.
Looking on powder recycling conducted for EBM devices, Popov et al. reported for recycled Ti-6Al-4V powders a formation of various defects leading to deteriorations of mechanical properties and the fatigue behavior, but unaffecting the developed microstructure [
26]. In contrast to that, Tang et al. found for the same material after a reuse of 21 cycles in EBM a better flowability of the powders as well as no significant influences on mechanical properties in manufactured components [
27]. For H11 powder no detailed studies of powder recycling could be found. Another study by Richter et al. investigated the mechanical recycling of Ti-6Al-4V parts for providing secondary powders. Therefore, molten and sintered support structures were comminuted in a hammer mill and mixtures of these obtained powders with virgin powder were processed via EBM [
28]. This stays in contrast to the recycling of unmolten powders mentioned above. In general, some powder mixtures can meet the mechanical properties and fatigue behavior of reference specimen only affected by an iron contamination of the milling tools due to mechanical alloying.
Another approach to achieve the matter of reducing raw material costs and energy consumption is the secondary usage of waste streams from EDM. Thereby, a certain amount of erosion sludge accumulates and is collected in filter cartridges or can be found at the bottom of the working basin. Considering the enclosed particle sizes as well as shapes, it could be stated, that some requirements can be fulfilled quite easily [
29,
30]. Besides that, the EDM mechanism can be a useful tool for a customized synthesis of powder particles [
31]. Thus, any aspects of a recycling of these EDM wastes are not under investigation. Currently, generated waste sludges and filter cartridges are collected and getting directly disposed for metallurgical processes or smelting. In this paper, a holistic characterization of enclosed eroded particle systems from sludge in filter cartridges and sludge from the basin bottom is performed to give detailed information about eroded particles and their applicability in AM-processes. Characterizations of the particle size, particle morphologies, chemical composition and bulk powder properties for different size classes as well as structural information about occurring crystal lattices and possible transitions are discussed. Analyses of the particle microstructure as well as the developed microstructure and inner structure after remelting is presented to derive information for further application fields. All results are presented to highlight an opportunity of recycled eroded particles as a secondary raw material for applicable processes in AM.
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