Blood and breath profiles of volatile organic compounds in patients with end-stage renal disease

Patients (7 males and 7 females) were recruited from the Dialyse Trainingszentrum Innsbruck and the Department of Nephrology and Hypertension of Innsbruck Medical University. Their baseline characteristics are presented in Table 1. All test subjects were dialyzed three times a week during 4-hours-sessions using high-flux Helixone Fresenius FX-100 dialyzers (Fresenius Medical Care, Germany) and a Fresenius type 5008, or Gambro type AK 200 S device. Patients suffered from a variety of underlying conditions including coronary heart disease, peripheral vascular disease, asthma, cancer, liver diseases and urinary tract infections. Four patients were diabetic. The recruitment was carried out with the following exclusions: inability to provide breath samples, immaturity and legal incompetence. No special dietary regimes were applied both before and during HD treatment. All subjects gave written consent to participate. The collection of samples was approved by the Ethics Commission of Innsbruck Medical University.

Contaminants emitted by the extracorporeal circuit materials and thus being introduced into the organism during the HD treatment were identified on the basis of analyses of air within freshly unpacked bloodlines and Helixone membranes as well as head-space above fragments of the aforementioned materials placed in sealed vials. In the latter case vials were stored for 1-2 hours to let potential pollutants accumulate.

Patients were dialyzed via an upper extremity native fistula and provided two blood samples taken from the arterial inflow line into 2.7 mL blood monovettes (Sarstedt, Germany) using a protocol described in our recent article [25]. The first blood sample was taken shortly (<10 min) after the onset of dialysis procedure and the second one a few minutes before its end. In parallel, one blank sample containing 2.7 mL of distilled water was collected using the same materials as in the case of blood sampling. This was done to identify possible contaminants stemming from sources other than blood. Blank samples were analyzed in the same way as blood samples and the resulting concentration levels were subtracted from the respective blood sample values.

End-exhaled breath samples were collected into 3-liter Tedlar bags (SKC Inc., USA) in a CO₂ controlled manner using breath sampler developed at Innsbruck Medical University, Austria [25‐27]. The evolution of breath constituents during dialysis was monitored by taking breath samples every 40-60 minutes throughout the dialysis session. The first sampling instant was at the onset of hemodialysis, the last one just before removing the extracorporeal circuit. Effectively, 5-7 breath samples were collected per patient. Additionally, two separate room air samples were taken (one at the onset of dialysis and one at the end of the treatment) for determining the background levels of VOCs under study.

Blood sample preparation, breath and blood calibration and the chromatographic analysis itself were performed in analogy with the procedures outlined in our recent article [25]. However, breath sample preparation relied on solid phase microextraction (SPME) and followed procedure described in King et al. [28].

We stress the fact that the identification of compounds was performed in two steps. First, the peak spectrum was checked against the NIST mass spectral library. Next, the NIST identification was confirmed by comparing the retention times of peaks of interest with retention times obtained for standard mixtures prepared from pure compounds. Peak integration was based on extracted ion chromatograms. The applied quantifier ions are presented in Table 2.

Limits of detection/quantification (LOD/LOQ) as well as relative standard deviations (RSDs) for the measurements were calculated as described in [25]. The obtained validation parameters are shown in Table 2 and were recognized as satisfactory for the goals of this study. With a few exceptions (pyrrole, pyrimidine and 2-pentyl-furan), most of the reported compounds could be quantified in both blood and breath. Blood acetone levels generally exceeded the dynamic range of the MS detector.

The Helixone membrane was found to emit predominantly n-alkanes (C3-C7), methylated alkanes (2-methyl-propane, 2-methyl-butane, 2-methyl-pentane and 2,4-dimethyl-heptane) and alkenes (propene, 2-methyl-1-propene, 2-pentene, 1-hexene and 2,4-dimethyl-1-heptene). Apart from hydrocarbons it also emitted considerable amounts of acetone and hexamethyl disiloxane.

More than 60 volatile contaminants were found to be released by the bloodlines and 43 of them could reliably be identified. Among these, hydrocarbons were the predominant chemical class with eighteen representatives. This number includes n-alkanes (C4-C7), methylated alkanes (2-methyl-propane, 2-methyl-pentane, 3-methyl-pentane, 4-methyl-heptane, 4-methyl-octane), cyclic HCs (methyl cyclopentane and cyclohexane) and alkenes (2-methyl-1-propene, 1-pentene, 2-heptene, 3-heptene, 3-ethyl-3-hexene, 3-methylene-heptane, 4-octene and 2,4-dimethyl-1-heptene). Furthermore, there were nine aldehydes (2-propenal, propanal, 2-methyl-2-propenal, pentanal, hexanal, heptanal, benzaldehyde, 2-ethyl-hexanal and nonanal), seven ketones (acetone, 3-buten-2-one, 2-hexanone, cyclohexanone, 2-cyclohexen-1-one, 3-methyl-2-hexanone and 3-heptanone), three furans (furan, 2,3-dihydroxy-furan and tetrahydrofuran), three terpenes (α-pinene, β-pinene and 3-carene) and two aromatics (toluene and p-xylene). The only alcohol present was 2-ethyl-hexanol. Two species namely tetrahydrofuran and 2-ethyl-hexanol exhibited especially high abundances. Pollutants affecting the levels of species reported within this study have been marked in Table 3.

Altogether 60 compounds were quantified in blood and breath of patients undergoing HD. Their detection and quantification incidences as well as the observed concentrations are given in Tables 3 and 4. In blood hydrocarbons comprised 32% of all quantified species, ketones 20%, heterocyclic compounds 14%, terpenes 11%, aromatics 7%, volatile sulphur compounds 7% and aldehydes 5%. In breath the predominant chemical classes were hydrocarbons (40%) and ketones (21%). Other well represented classes were heterocyclic compounds (10%), terpenes (8%), volatile sulphur compounds (6%), aromatics (6%) and aldehydes (6%).

Four volatile sulphur compounds (DMS, AMS, MPS and thiophene) were quantified in blood and breath. Interestingly, their concentrations were decreasing during the HD treatment in both investigated fluids (see Tables 3 and 4 for Wilcoxon tests and Figure 1 for representative MPS and DMS profiles). For example, blood levels of DMS after the HD session were on average three-fold lower than at the onset of the treatment. Analogously, breath concentrations dropped approximately by a factor of 1.5. The reason for this response of sulphur species remains unclear. They were not found to be released by the dialyzer materials and their room air levels were relatively low. Thus, exogenous contamination can be excluded as a potential reason for elevated VSC concentrations before HD. It rather seems that volatile sulphur species were effectively removed from blood during the haemodialysis session. Conversely, Goerl et al. [29] reported stable levels of DMS in breath of patients undergoing dialysis. The reason for this discrepancy remains speculative. Perhaps, some differences in HD treatment affect DMS washout.

22 aliphatic hydrocarbons were detected in the blood or breath of HD patients. A great majority of them (17) were pollutants originating from the dialyzer materials. Breath levels of four species (n-butane, n-pentane, 2-methyl-1-pentene, and 1-hexene) were significantly higher than room air ones and exhibited a statistically significant decrease during the treatment (see Figure 2 for exemplary profiles). This observation is in good agreement with the results reported by Lee et al. [24] evidencing the influx of hydrocarbon pollutants into blood from the extracorporeal circuit. Whereas Lee et al. [24] reported HC levels that were elevated only for a rather short period of time (20 minutes), the increased HC concentrations observed within this study were still present at the end of hemodialysis. The composition and intensity of the contaminant influx are clearly manufacturing process dependent and may differ significantly between different vendors. Strikingly, the aforementioned concentration drops were not observed in blood samples. This discrepancy can be explained by the poor blood solubility of aliphatic hydrocarbons [30] as well as the fact that the arterial blood sampling point was located at the beginning of the extracorporeal circulation before the membrane. Consequently, the samples correspond to blood degassed during pulmonary gas exchange. Thus, it seems that this excess of hydrocarbons is quickly and effectively removed by the lungs and the exposure of tissues to these pollutants is probably limited. Amongst the hydrocarbons not being treatment-related pollutants there were four smoking-induced species (1,3-Butadiene, (E/Z)-1,3-Pentadiene and 1-heptene) and isoprene. Both blood and breath levels of isoprene increased significantly after the hemodialysis (see Figure 3 and Figure 4). In exhaled air this rise amounted to about 36%, whereas in blood an average difference of 52% was observed. This characteristic breath isoprene behavior in response to dialysis has already been reported by numerous investigators [18‐29], however, this is the first time that it is confirmed by parallel blood measurements. The advanced explanations for this phenomenon include hemodynamic stress, fluctuations of respiratory variables, or activation of metabolic pathways leading to mevalonic acid synthesis [19, 21‐23], nevertheless, none of them seems to be adequate [18]. Isoprene has received a growing interest in the field of breath gas analysis due to the fact that it may serve as a sensitive, non-invasive indicator of several diseases in human organism [31]. Strikingly, despite this interest the source of isoprene and its function in humans are still a matter of debate [32, 33]. In this context, the elucidation of isoprene evolution during hemodialysis could be valuable for understanding its function in human organism.

A total of number of eleven ketones were quantified in blood and breath samples. For 6 of them significant differences between breath and room air levels were found (Wilcoxon signed-rank test) both before and after HD. Species from this family were also found to be affected by background emission from the dialyzer fabrics. This especially applies to cyclohexanone, 2-cyclohexen-1-one, 3-heptanone, 3-buten-2-one and 2-hexanone. Due to the shortage of the literature values for arterial blood levels of ketones in humans it is difficult to evaluate the blood concentrations obtained within this study. In our recent paper [25] we established venous blood levels of 62 VOCs including ketones in healthy volunteers. While VOCs levels in arterial blood are significantly lower than in venous blood due to pulmonary gas exchange [34], a comparison of results obtained within this study with the ones reported in our recent paper can provide some valuable information. In general despite degassing the arterial blood levels observed within this study were much higher than the ones observed in venous blood of healthy volunteers. For example, pre-dialysis blood levels of 2-pentanone were approx. three times higher (mean: 94 vs 35 nmol/L), 2-heptanone four times higher (mean: 10.5 vs 2.7 nmol/L) and 4-heptanone sixty five times higher (mean: 54 vs 0.83 nmol/L) than in healthy individuals (see Figure 4). The same holds true for the average breath levels (e.g. 2.78 vs 0.62 ppb for 2-pentanone, 0.6 vs 0.03 ppb for 4-heptanone). Interestingly, elevated levels of ketones in ESRD patients were present already before the HD treatment. Since ketones were reported to be particularly abundant in human urine [30, 35, 36], this fluid seem to be an important sink of these species in human organism. Consequently, any impairment of kidney function may significantly affect the excretion of ketones and hence lead to their retention within the uremic syndrome. Two heptanone isomers (2- and 4-heptanone) exhibited high levels in blood and breath despite the fact that they were neither found room in air nor extracorporeal circuit contaminants. Moreover, their blood levels increased significantly during the hemodialysis. Such an excess of 4-heptanone in hemodialysis patients has already been reported in the literature and attributed to the metabolism of di(2-ethylhexyl) phthalate (DEHP) [37]- a plasticizer used in polyvinyl chloride products. In humans DEHP is rapidly metabolized to 2-ethylhexanol, which is then oxidized to 2-ethylhexanoic acid and finally to 2-heptanone and 4-heptanone [37, 38]. Indeed, the bloodlines used within this study were found to emit significant amounts of 2-ethylhexanol and its oxidation product 2-ethyl-hexanal. Consequently, it is plausible that the high concentrations of 2- and 4-heptanone in HD patients originated from this source. At least one of aforementioned ketones can be considered as a uremic toxin: cyclohexanone emitted from extracorporeal circuits was reported to impair cardiovascular function [39].

Only three aldehydes (2-propenal, propanal and 2-metyl-2-propenal) were found in blood samples. 2-propenal and propanal showed incidence rates of 50% and 2-metyl-2-propenal was detected only once. In breath all three species were omnipresent, however, their levels were lower (propanal), or comparable (2-propenal and 2-metyl-2-propenal) to the ones in room air. The high room air levels and the observed emission by bloodlines render the aforementioned species pollutants rather than endogenous compounds. 2-propenal was also reported to accumulate in blood of renal failure patients as the result of spermine degradation by polyamine oxidase being released from damaged kidney [40]. Since this compound was also found to be a uremic toxin damaging the functions of cells and proteins [40] its additional exogenous influx may accelerate the progression of uremia. Interestingly, while the dialyzer bloodlines also emitted several heavier aldehydes (pentanal, hexanal, heptanal, benzaldehyde, 2-ethyl-hexanal and nonanal), the latter were not detected in blood. Perhaps, the analysis of species from this chemical class requires a special sample treatment (e.g., derivatisation) [41], or they are rapidly metabolized by human tissues [42, 43]. Moreover, room air concentrations of these aldehydes were generally much higher than in breath (data not shown), suggesting an additional influx of these analytes from the surrounding atmosphere.

Amongst terpenes α-pinene and 3-carene were contaminants from fabrics showing relatively high occurrences and levels in HD patients as compared to healthy volunteers [25]. p-cymene and DL-limonene also displayed very high abundances in blood, usually 20-30 times higher than in healthy individuals. However, it is not clear if they result from renal impairment, or stems from relatively high room air levels of these compounds.

Amongst aromatics there were two dialyzer pollutants (toluene and p-xylene), benzene and o-xylene. The levels of toluene tended to decrease over the course of dialysis both in blood and breath, whereas p-xylene showed stable concentrations. Benzene decreased in both fluids after haemodialysis, perhaps due to a treatment-related washout that would be consistent with the findings reported by Goerl et al. [29] (see Figure 3 and Figure 4). Since only 3 patients were smokers the elevated levels of benzene seem to stem from an environmental exposure. If so, this finding would evidence the retention of benzene within the uremic syndrome.

Amongst heterocyclic species only furan exhibited a difference between pre- and post-dialysis levels. Nevertheless, this effect can be ascribed to the excretion of this compound in lungs in response to its emission by bloodlines. Several heterocyclic compounds, although not detected in blood of healthy individuals [25], were quite abundant in blood of HD patients. Pyrimidine (found in 65% of all samples) showed concentration levels around 45 nmol/L, pyridine (found in 70% of all samples) around 28.6 (before HD) and 22.6 nmol/L (after HD) and 2-pentyl-furan (found in 35% of all samples) exhibited mean concentration values of 13 nmol/L. The elevated pyrimidine levels are consistent with previous studies reporting an accumulation of pyrimidine compounds in blood of patients with CKD [44].