Scalable ion focus polarization dialyzer for peritoneal dialysate regeneration | Journal of Nanobiotechnology


2-D scalable ion focus polarization dialyzer

To display scalability of ICP dialyzer in precept, a two-dimensional (2-D) micro-nanofluidic scaling machine was fabricated as proven in Fig.  2A. For particulars relating to its supplies used, fabrication course of and experimental setup, consult with the part of Experimental strategies and Supplementary Data (SI) Fig.  1A. To accommodate the Renal Panel’s requirement of a minimal of 100 µL undiluted pattern for measuring elements in a dialysate answer, we optimized effectivity by mitigating electrokinetic instability by way of micro-fin constructions close to the bifurcation level [35] and lowering electrical resistance utilizing double-patterned nanojunctions. Human used dialysate answer was repeatedly injected into each anodic and cathodic microchannels at a gentle circulation fee of 0.4 µL/min. Underneath these circumstances, ICP phenomenon was generated, resulting in the event of an ion depletion boundary forward of the nanojunction. This separation mechanism utilized for wastes elimination and purification, as depicted in Fig.  2B. Notably, a secure present measurement was sustained for 120 min, as demonstrated in SI Fig.  1B. Anionic fluorescent dye molecules (Alexa 488, Invitrogen, USA) and carboxylate micro-particles (1 μm diameter, Invitrogen, USA) had been unable to traverse the ion depletion boundary, redirecting them exterior this boundary, as indicated in SI Video 1.

As well as, Fig.  2C was integrated to underscore that the proposed ICP dialyzer employed a present density able to direct urea oxidation. It has been reported that, below excessive potentials exceeding 1.7 V versus the saturated calomel electrode (SCE), urea undergoes decomposition by way of a direct oxidation course of on the electrode floor, resulting in the formation of nitrogen and carbon dioxide fuel. This phenomenon is represented by the next equations [37,38,39]: Eq. (1) outlines the anodic response, Eq. (2) delineates the cathodic response, and Eq. (3) represents the general response.

$${rm{CO}}{left( {{rm{N}}{{rm{H}}_{rm{2}}}} proper)_{rm{2}}}{rm{ + 6O}}{{rm{H}}^{rm{ – }}} to {{rm{N}}_{rm{2}}}{rm{ + 5}}{{rm{H}}_{rm{2}}}{rm{O + C}}{{rm{O}}_{rm{2}}}{rm{ + 6}}{{rm{e}}^{rm{ – }}}$$

(1)

$${rm{6}}{{rm{H}}_{rm{2}}}{rm{O + 6}}{{rm{e}}^{rm{ – }}} to {rm{3}}{{rm{H}}_{rm{2}}}{rm{ + 6O}}{{rm{H}}^{rm{ – }}}$$

(2)

$${rm{CO}}{left( {{rm{N}}{{rm{H}}_{rm{2}}}} proper)_{rm{2}}}{rm{ + }}{{rm{H}}_{rm{2}}}{rm{O}} to {{rm{N}}_{rm{2}}}{rm{ + 3}}{{rm{H}}_{rm{2}}}{rm{ + C}}{{rm{O}}_{rm{2}}}$$

(3)

Right here, the electrochemical decomposition yields nitrogen and carbon dioxide gases, that are thought-about biologically inert with no antagonistic results on human well being. To offer experimental proof supporting urea direct oxidation utilized by the ICP phenomenon, the gas-to-liquid quantity ratio of N₂ and CO₂ generated from the anodic urea electrochemical decomposition response (1) was first calculated. When 0.29 g/mL of urea was added to contemporary dialysate, the gas-to-liquid ratio was decided to be roughly 14.8–17.6%. The detailed calculation course of was introduced in SI Fig.  2. Subsequently, experimental validation was carried out utilizing a tool as illustrated in SI Fig.  2A. From the effluent of the anodic aspect channel, steady fuel manufacturing was noticed as depicted in SI Fig.  2B. The gas-to-liquid quantity ratio was quantified as roughly 5–8%, primarily attributed to Faradaic losses. These fuel manufacturing outcomes offered oblique proof supporting urea direct oxidation utilized by the ICP phenomenon. Notice that when urea undergoes decomposition, nitrogen oxidants are fashioned, which can pose a danger to human well being below particular circumstances: both at potentials beneath 1.6 V versus SCE or below pure oxidation circumstances.

Subsequent, every stream was individually extracted, and quantifiable focus profiles of key indicators – urea, creatinine, Na+, Cl, and phosphorus (P) – essential for affected person well being evaluation, had been established, as proven in Fig.  2D. The focus modifications of every key indicator had been nondimensionalized as follows.

$${C_N} = {matrix{ focus,of,every,indicator hfill cr ,at,the,outlet,({C_{indicator_outlet}}) hfill cr} over matrix{ focus,of,every,indicator hfill cr ,at,the,inlet,({C_{indicator_inlet}}) hfill cr} }$$

First, the positively charged species (Na+ and creatinine) had been faraway from the purified stream relying on their electrophoretic mobility [36]. A considerable proportion of Na+ ions transited the nanojunction by way of cationic flux, yielding a ultimate assortment of 90% desalted stream (normalized focus of 0.1). Whereas creatinine (sub nanometer molecule and one of many main toxins of physique wastes from a used dialysate) is impartial at pH 7.4, it acquires a optimistic cost below pH 7.4. Given the marginally acidic nature of the dialysate, we confirmed that creatinine follows a cationic-like transport mechanism throughout the ICP phenomenon growth. Creatinine focus decreased each exterior (yellow channel) and inside (blue channel) the ion depletion boundary on the anodic aspect, however elevated on the cathodic aspect (brown channel). Roughly 50% of creatinine crossed the nanojunction, with round 33% passing by way of the stream exterior the ion depletion boundary. Finally, round 17% of creatinine remained inside the ion depletion boundary, resulting in a big discount within the purified stream focus (normalized focus of 0.34). Second, the negatively charged chloride ions (Cl) underwent electrochemical reactions on the anodic electrode to take care of electro-neutrality because of the ICP phenomenon, inflicting a redistribution of focus profiles close to the nanojunction. Third, urea, an uncharged molecule and a serious toxin in physique wastes alongside creatinine, underwent full elimination by way of electrochemical reactions in anodic aspect streams, together with the purified stream (normalized concentrations of 0.01). Final, the weakly charged phosphorus (P) was considerably faraway from each anodic and cathodic channels (normalized concentrations of 0.17). To know the distinct elimination mechanism of P in comparison with different elements, we monitored the motion of the ion depletion boundary throughout a 3-hour machine operation, as introduced in SI Fig. 1C. The principal constituent of those precipitates was recognized as phosphorus as demonstrated in SI Fig. 1D. Thus, we deduced that P didn’t traverse the ion depletion boundary or the nanojunction; reasonably, it underwent decomposition on account of an electrical subject, subsequently being expelled by way of the anionic wastes channel.

As depicted in Fig.  2E, we tried to search out candidates for transportable peritoneal dialyzer utilizing micro-nanofluidic units fabricated based mostly on three completely different mass switch physics. First, we fabricated a easy microfluidic machine that was ruled solely to electrochemical reactions and electrophoresis (known as “EPH” in Fig. 2E). On this setup, two electrodes had been positioned inside a single microchannel: one in proximity to the inlet reservoir and the opposite adjoining to the outlet reservoir, with no interconnecting junctions. The microchannel was loaded with used dialysate, and a mix of optimistic voltage and strain was utilized to the inlet reservoir. Underneath these circumstances, full elimination of urea was achieved, whereas creatinine elimination reached roughly 5%, Na+ elimination roughly 14%, Cl elimination roughly 31%, and P elimination roughly 52%. The decisive issue for the whole elimination of urea may be attributed to an electrochemical response.

Second, to imitate the ED cell construction, three completely different microchannels and nanojunctions had been constructed throughout them (known as “ED” in Fig.  2E). One microchannel was designated for anodic processes positioned on the higher aspect, one other for the managed circulation of a pattern alongside the center path, and a 3rd for cathodic processes located on the decrease aspect. Inside this association, it was noticed that the ion depletion efficiently manifested inside the middle-bifurcated channel. This was because of the institution of a strong electrical subject throughout the nanojunction between the higher anodic channel and the decrease cathodic channel. Notably, urea skilled no alteration because of the absence of electrodes within the center channel, whereas creatinine and Na+ ions had been eliminated by way of electrical transport pushed by the ICP phenomenon.

Lastly, the circumstances of ICP was employed inside a micro-nanofluidic machine. As talked about earlier, the whole elimination of urea and the elimination of different substances had been achieved by way of electrical transportation utilized by the ICP phenomenon (known as “ICP” in Fig.  2E). The appliance of a decrease potential hindered the elimination effectivity of all elements.

Based mostly on the insights gleaned from these analyses, we concluded that the purification of dialysate can solely be achieved when the ICP phenomenon was induced by way of the presence of an electrode inside the stream of dialysate (known as “ICP”). We named these micro-nanofluidic units as a 2-D scalable ICP dialyzer. As well as, by enhancing the throughput capability from 0.1 µL/min (inset Fig. 1C) to 0.4 µL/min (Fig.  2B), we had been capable of conduct exact analyses by minimizing errors brought on by extended experiments for making certain minimal pattern quantity requirement of the Renal Panel measurement.

Fig. 2
figure 2

(A) A microscopic picture of 2-D scalable ICP dialyzer. Polymeric materials, PDMS was used for constructing microchannels and nanoporous membrane, Nafion was used for patterning nanojunctions, and the microchannel width was expanded utilizing a micro-fin construction which suppressed an electroosmotic instability (EOI). (B) A microscopic picture of dialysate purification because of the ICP phenomenon. Anionic wastes had been rerouted exterior the ion depletion boundary and cationic wastes had been eliminated by way of the nanojunction by cationic flux in order that purified dialysate was extracted from stream contained in the ion depletion boundary. (C) A measurement results of present densities versus time when 70 V was utilized for ICP era. The present densities used for separation of the purified and anionic wastes streams exceeded the identified present densities for urea direct oxidation [38]. (D) Nondimensionalized focus profiles of main dialysis indicators inside (blue) and out of doors (brown) the ion depletion boundary of the anodic aspect streams, and the cathodic aspect stream (purple). Concentrations of all indicators within the used dialysate decreased to beneath 30% within the purified channel (blue bar). (E) Graph exhibiting the outcomes of a management experiment to confirm the dialysate purification mechanism. Dialysate purification was profitable just for ICP situation

Improvement of 3-D ion focus polarization dialyzer

Whereas the feasibility of ICP dialyzer was demonstrated inside a micro-nanofluidic hybrid configuration, the throughput of the machine proved insufficient for sensible dialysate recycling, both for human or animal testing functions. On this chapter, we now have engineered a macro-scale ICP dialyzer with a throughput capability of milliliters per minute, as illustrated in Fig. 3A. This machine includes: (a) a cathodic aspect macro-channel, that includes an inlet for introducing contemporary dialysate and an outlet for the elimination of cationic wastes; (b) a nanoporous membrane sheet, serving to take away positively charged species; (c) a nanoporous resin-coated micro-mesh construction, supposed to mitigate electroosmotic instability (EOI) and increase cationic flux; and (d) an anodic aspect macro-channel, incorporating an inlet for used dialysate and shops for every purified and anionic wastes stream.

The elemental idea revolved round establishing a microfluidic area inside a macro-fluidic equipment [40]. The enlargement of the ICP layer was crucial for efficient dialysate filtration on this high-throughput configuration. Nonetheless, if the channel dimensions exceeded O(100) µm, analogous to different micro-nanofluidic units, the machine’s purification efficacy waned [35, 41]. ICP formation within the micro-nanofluidic regime was demarcated by three principal traits: (1) floor conduction (SC), (2) electroosmotic circulation (EOF), and (3) electroosmotic instability (EOI), all of which exerted a pivotal affect on ion conveyance throughout the nanojunction [42]. Relying on the channel’s attribute size, SC, EOF, and EOI held sway over ion transportation in very slim channels (< 5 μm), reasonably slim channels ( < ~ O(100) µm), and wider channels ( > ~ O(100) µm), respectively. Consequently, this macroscale machine was anticipated to exhibit EOI traits. Nevertheless, it’s necessary to notice that EOI-dominated techniques inherently undergo from avoidable instability [43,44,45] and heightened power consumption on account of decreased overlimiting conductance [46]. To transition the system from an EOI-dominant state to EOF or SC, micro-fin constructions had been beforehand employed in a two-dimensional micro-nanofluidic setup [35]. These fins successfully curbed EOI and allowed for the mixing and elevation of throughput as much as ranges comparable to traditional ICP units. Nonetheless, channel enlargement solely in a single aircraft was inadequate to realize greater than laboratory-scale throughput.

To beat this limitation, we prolonged the fins within the z-direction (i.e., three-dimensionally), leading to micro-meshes as depicted in Fig. 3B. This mesh was meticulously devised to generate an electrical subject perpendicular to the dialysate circulation path, thereby enabling cationic wastes transport alongside the electrical subject’s orientation. Moreover, an optimized micro-mesh grid measurement was decided by way of experimentation with three variants: (1) no micro-mesh, (2) 200 μm, and (3) 400 μm micro-meshes, as detailed in SI Fig. 3A. Optimum purification effectivity was realized with a micro-mesh possessing a 400 μm grid measurement, as this configuration exhibited essentially the most pronounced distinction in conductance between purified and anionic wastes streams. To increase the cation transport area inside the macroscale machine, we utilized a nanoporous resin coating to the micro-mesh construction. Microscopic photos of the micro-meshes earlier than and after the nanoporous resin coating had been offered in SI Fig. 3B, confirming profitable coating inside the open areas. The conductance outcomes, displayed in SI Fig. 3C demonstrated the influence of the nanoporous resin coating on the micro-mesh construction. When the nanoporous resin was coated on the micro-meshes, the conductance of anionic wastes and cationic wastes streams elevated, indicating enhanced cationic flux.

Subsequently, we discovered the optimum present and circulation fee circumstances that yielded the best dialysate purification effectivity for the preliminary model of the 3-D scaling-up machine, as depicted in Fig. 3B. The precise picture of the Fig. 3B was introduced in SI Fig. 3D. Because of the traits of the dialyzer, fluid-cell interplay happens, making it necessary to make use of biocompatible supplies [47]. Due to this fact, a 3-D ICP dialyzer was fabricated utilizing biocompatible materials appropriate for medical purposes. Supplies used, fabrication and experimental particulars had been written within the part of Experimental strategies, respectively. First, as proven in SI Fig. 4A, the conductance of the purified, anionic wastes, and cationic wastes streams was measured in accordance with modifications in present and circulation fee. In an effort to comprehensively analyze the rise in conductance because of the enhance of anionic wastes within the anionic wastes stream and the lower in conductance because of the lower of each anionic and cationic wastes within the purified stream, purification effectivity was outlined as follows and plotted in Fig. 3C.

$$eqalign{& Purification,effectivity cr & = left( {1 – {matrix{ conductance,of hfill cr purified,stream hfill cr} over matrix{ conductance,of hfill cr ,anodic,wastes,stream hfill cr} }} proper) occasions 100(% ) cr} $$

Underneath the I = 0.01 A utility, the purification effectivity decreased exponentially because the circulation fee elevated, and below the I = 0.02 A and I = 0.04 A utility, the best purification effectivity was obtained at Q = 0.2 mL/min and was comparatively decrease below the I = 0.04 A utility.

Second, as proven in Fig. 3D, we confirmed the pH modifications because the utilized present elevated below the situation of Q = 0.2 mL/min, which confirmed maximal purification effectivity. Right here, we used Pt and Ag as anode and cathode electrodes materials, respectively, based mostly on the leads to SI Fig. 4B. Because the utilized present elevated, the lower in pH of the anionic wastes and purified streams elevated, and above I = 0.04 A, they converged and maintained the same pH worth. In the meantime, the pH of the cationic wastes stream elevated with the rise in utilized present, and converged above I = 0.04 A. Based mostly on the outcomes of Fig. 3 C and D, the optimum working circumstances of the three-dimensional (3-D) ICP dialyzer had been established as I = 0.02 A, Q = 0.2 mL/min, the place the pH of the purified stream was comparatively excessive and the purification effectivity was the utmost. This electrical and mechanical situation ensured a harmonious steadiness between excessive circulation fee and secure purification effectivity.

Fig. 3
figure 3

(A) Schematic diagram of 3-D scalable ICP dialyzer. The machine consisted of a cathodic aspect macro-channel with inlet for contemporary dialysate and outlet for cationic wastes flowing, a nanoporous membrane sheet for eradicating positively charged species, micro-meshes for lowering EOI and enhancing cationic flux an anodic aspect macro-channel with inlet for used dialysate and shops for purified and anionic wastes flowing. (B) Schematic diagram and graph of micro-mesh construction design optimization. Coated nanoporous resin on the micro-meshes floor ensured that the cationic wastes had been transported in the direction of the nanoporous membrane sheet alongside the path of the electrical subject in order that purified dialysate handed by way of the micro-meshes perpendicular to the electrical subject. The micro-mesh grid measurement of 400 μm was chosen because the distinction in conductance between purified and anionic wastes streams was the best, and conductance of cationic wastes was the best. (C) Graph exhibiting modifications in purification effectivity in accordance with modifications in present and circulation fee. Most purification effectivity was noticed when making use of I = 0.02 A and Q = 0.2 mL/min. (D) Graph exhibiting modifications in pH because the utilized present elevated below the situation of Q = 0.2 mL/min. Because the utilized present worth elevated, the pH of anionic wastes and purified streams decreased, and that of cationic wastes elevated

3-D scalable ion focus polarization dialyzer

The beforehand fabricated 3-D ICP dialyzer, which had a circulation fee of Q = 0.2 mL/min, was additional scaled as much as obtain a Q = 1 mL/min, as proven in Fig. 4A, and an precise picture of the machine was proven in SI Fig. 3E. The fabrication course of and meeting components of the machine had been the identical, solely the components measurement was expanded within the y-axis path. As illustrated in Fig. 4B, the design parameters of the machine had been scaled proportionally in relation to the throughput enhance (0.2, 0.4, and 1 mL/min), together with the entire quantity inside the machine (Vwhole), the amount excluding the mesh body (Vwhole−mesh), and the nanoporous membrane’s contact space (Acontacted membrane) with the fluid. Based mostly on acceptable proportional constants, a tool with a most throughput of 1.0 mL/min was realized. Additional evaluation concerned the ability consumption of scaled units, as proven in Fig. 4C. Though greater throughput correlated with decrease energy consumption, the variations had been modest (inside 10%), and the temporal developments remained constant. Accumulation of fuel byproducts across the anodic electrode heightened electrical resistance, with the 1 mL/min machine demonstrating the bottom energy consumption because of the ample outlet area for fuel dispersal. Over time, the presence of trapped gases close to the electrode led to growing energy consumption, finally reaching a saturation level. Regardless of parallel design and manufacturing of units, discrepancies in dialysis efficiency would possibly come up.

Determine 4D confirmed the conductance of streams from units with various throughput capacities following the infusion of contemporary dialysate. Within the case of purified stream, the conductance exhibited a constant lower of round 10% in comparison with the launched contemporary dialysate, plateauing at roughly 10 mS/cm whatever the circulation fee (0.2, 0.4, 1 mL/min). Conversely, the conductivity of the anionic wastes stream decreased with growing remedy capability. This pattern was attributed to lowered electrode-fluid contact space per unit capability, leading to decreased electrochemical response and wastes elimination effectivity [48]. For cationic wastes stream, the conductance remained secure at roughly 15 mS/cm, regardless of throughput capability. This consistency was ascribed to the nanoporous membrane’s capability to take care of a uniform ion transport fee per unit space from the anodic to the cathodic channel.

Subsequent evaluation concerned the efficiency of ICP dialysis utilizing human peritoneal dialysate, as depicted in Fig. 4E. Elimination ratios for urea, creatinine, Na+, Cl, and P had been measured from purified stream. Whereas urea’s elimination ratio exhibited heightened variability with growing throughput capability, it maintained a median of over 50%. In distinction, the typical elimination ratio for anionic wastes stream was 99% (SI Fig. 5A), indicating localized decomposition of urea close to the electrode. Elimination ratio of Na+ remained constant at round 40%, whereas creatinine, characterised as a weak natural cation, confirmed a elimination ratio beneath 25%, which elevated with greater throughput capacities. Cl exhibited common elimination ratios of 20% for the 0.2 mL/min machine and 25% for the 0.4 and 1 mL/min units. P elimination ratios demonstrated an growing pattern with greater throughput capacities. Focus modifications within the cationic wastes channel had been introduced in SI Fig. 5B, highlighting elevated concentrations of Na+ and creatinine on account of their cationic nature upon passing by way of the nanoporous membrane sheet.

Whereas Fig. 4E confirmed the instant measurement of collected answer upon powering on, Fig. 4F introduced measurements taken from 10 to 60 min thereafter utilizing the 3-D ICP dialyzer with Q = 1 mL/min. Noticeably, the elimination ratio of all indicators exhibited constant upkeep over time, barring creatinine, and urea elimination ratio was dropped beneath 20%. On this research, we used electrode supplies with the identical size and floor space whatever the machine measurement. Urea was decomposed on the electrodes, and whereas bubble formation on the electrode floor was not distinguished within the 0.2 mL/min machine, it observably elevated within the 1 mL/min machine. The bubbles collected across the electrodes lowered the efficient electrode floor space required for urea decomposition and hindered electrical paths for creatinine transportation by way of the nanoporous membrane. As indicated in SI Fig. 5A, the urea elimination ratio remained near 99% even within the 1 mL/min machine for the anionic wastes stream, collected close to the electrode, suggesting that the difficulty lies not with electrode efficiency however with machine optimization. Based mostly on these experimental evidences, we inferred that urea decomposition could possibly be stably achieved by (1) putting in a bubble elimination membrane across the electrode, (2) designing the hole between the electrode and purified channel extra carefully, or (3) growing the electrode floor space.

ICP Dialyzer-assisted peritoneal Dialysis

Lastly, to match the in vivo toxicity discount efficiency of typical PD and ICP dialyzer-assisted PD, we employed a bilateral nephrectomy rat mannequin. The peritoneal cavity of the rat was too small to repeatedly drain the injected dialysate, so, we carried out quasi-continuous PD to confirm the development in in vivo toxicity discount when the ICP dialyzer-assisted typical PD, as depicted in Fig. 5A. Put up-surgery, all rats had been allowed a 24-hour recuperation interval, adopted by 2 h of respective PD classes, throughout which concentrations of uremic and different pivotal elements had been monitored. Just for group 3 (rat with bilateral nephrectomy), after injection of contemporary dialysate (0 h), 12 mL of the used dialysate was extracted and infused into the ICP dialyzer for dialysate regeneration. 4 mL of the regenerated purified dialysate was discharged and re-injected into the rat’s peritoneal cavity at 30-minute intervals.

Subsequent, modifications in serum concentrations of all main indicators had been monitored and plotted, as proven in Fig. 5B for group 1, Fig. 5C for group 2, and Fig. 5D for group 3. Serum concentrations had been normalized as follows.

$${C_{N_{serum}}}left( t proper) = {{{C_{serum}}left( t proper)} over {{C_{serum}}left( { – 24 h} proper)}}$$

Inside the preliminary 24-hour interval, rats with surgically eliminated kidneys (teams 2 and three) exhibited a noticeable escalation in toxin concentrations, in distinction to the negligible change noticed in regular rats (group 1). In teams 2 and three, the concentrations of urea and creatinine elevated sharply throughout the first 24 h after surgical procedure. Following the initiation of typical PD, the speed of enhance in urea and creatinine concentrations decreased in each teams 2 and three, whereas there have been no vital modifications in any of the indications in group 1. To evaluate the speed of change in urea and creatinine concentrations in teams 2 and three, the focus derivatives over time had been plotted in Fig. 5E. When PD was assisted by the ICP dialyzer, a definite discount in in vivo toxin concentrations inside the first hour was noticed, whereas no such discount was achieved with out the help. These outcomes prompt that the ICP dialyzer might regenerate dialysate, efficiently aiding PD whereas utilizing a smaller dialysate quantity.

Nevertheless, by the second hour, a rise in in vivo toxin concentrations was noticed in each teams 2 and three. To determine the trigger, we examined the elimination ratios over time as proven in Fig. 5F. The outcomes confirmed that the typical elimination ratios of urea and creatinine decreased progressively to 31.8%, 13.7%, and a pair of.6% for the primary, second, and third infusion occasions, respectively. For the reason that used dialysate discharged from the rat’s peritoneal cavity was intermixed with varied seen suspended substances, it collected contained in the ICP dialyzer, inflicting non-uniformity in circulation fee, electrode reactions, and electrical subject formation. This interplay lowered the efficient floor space of the nanoporous membrane, resulting in a lower in purification effectivity over time. This impact was notably pronounced for urea and creatinine, that are comparatively bigger in measurement in comparison with electrolyte ions.

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