Skip to main content
  • Research article
  • Open access
  • Published:

Time course study of oxidative and nitrosative stress and antioxidant enzymes in K2Cr2O7-induced nephrotoxicity

Abstract

Background

Potassium dichromate (K2Cr2O7)-induced nephrotoxicity is associated with oxidative and nitrosative stress. In this study we investigated the relation between the time course of the oxidative and nitrosative stress with kidney damage and alterations in the following antioxidant enzymes: Cu, Zn superoxide dismutase (Cu, Zn-SOD), Mn-SOD, glutathione peroxidase (GPx), glutathione reductase (GR), and catalase (CAT).

Methods

Nephrotoxicity was induced in rats by a single injection of K2Cr2O7. Groups of animals were sacrificed on days 1,2,3,4,6,8,10, and 12. Nephrotoxicity was evaluated by histological studies and by measuring creatinine clearance, serum creatinine, blood urea nitrogen (BUN), and urinary excretion of N-acetyl-β-D-glucosaminidase (NAG) and total protein. Oxidative and nitrosative stress were measured by immunohistochemical localization of protein carbonyls and 3-nitrotyrosine, respectively. Cu, Zn-SOD, Mn-SOD, and CAT were studied by immunohistochemical localization. The activity of total SOD, CAT, GPx, and GR was also measured as well as serum and kidney content of chromium and urinary excretion of NO2 -/NO3 -. Data were compared by two-way analysis of variance followed by a post hoc test.

Results

Serum and kidney chromium content increased reaching the highest value on day 1. Nephrotoxicity was made evident by the decrease in creatinine clearance (days 1–4) and by the increase in serum creatinine (days 1–4), BUN (days 1–6), urinary excretion of NAG (days 1–4), and total protein (day 1–6) and by the structural damage to the proximal tubules (days 1–6). Oxidative and nitrosative stress were clearly evident on days 1–8. Urinary excretion of NO2 -/NO3 - decreased on days 2–6. Mn-SOD and Cu, Zn-SOD, estimated by immunohistochemistry, and total SOD activity remained unchanged. Activity of GPx decreased on days 3–12 and those of GR and CAT on days 2–10. Similar findings were observed by immunohistochemistry of CAT.

Conclusion

These data show the association between oxidative and nitrosative stress with functional and structural renal damage induced by K2Cr2O7. Renal antioxidant enzymes were regulated differentially and were not closely associated with oxidative or nitrosative stress or with kidney damage. In addition, the decrease in the urinary excretion of NO2 -/NO3 - was associated with the renal nitrosative stress suggesting that nitric oxide was derived to the formation of reactive nitrogen species involved in protein nitration.

Peer Review reports

Background

K2Cr2O7 is a chemical compound that is widely used in metallurgy, chrome plating, chemical industry, textile manufacture, wood preservation, photography and photoengraving, refractory and stainless steel industry, and cooling systems [1]. Occupational exposure to chromium has been associated with welders, chrome-plating workers, and chromium pigment factories workers [2]. Chromium is known to cause allergic dermatitis [3], carcinogenicity [4], and ARF in humans [2, 5, 6] and in animals [711].

Acute renal failure (ARF) induced by potassium dichromate (K2Cr2O7) has been used as a model to study the pathophysiology of this disease [7, 9]. Experimental data show that chromate affects selectively the convoluted section of the proximal tubules [7, 1215] and induces acute necrosis of renal tubules [14, 15]. Clinical and experimental renal damage induced by K2Cr2O7 has been associated with oxidative stress [1520]. In fact, some antioxidants such as ascorbic acid, vitamin E, N-acetyl cysteine, and glutathione prevent the K2Cr2O7 induced renal damage [2125] whereas the inhibition of glutathione biosynthesis enhances it [22, 24]. Evidences suggest that reactive oxygen species (ROS) are involved in Cr(VI)-induced cell injury [16, 17, 19, 26]. Chromium reduction intermediates [Cr(V), Cr(IV), and Cr(III)], which could be generated under physiological conditions, may be toxic as they involve ROS production [2729]. In vitro chromate reduction via H2O2 has been shown to produce hydroxyl radicals via a Fenton-like reaction [27, 3033].

We recently showed that stannous chloride (SnCl2) pretreatment has a protective role in K2Cr2O7-induced nephrotoxicity [15, 34]. SnCl2 is a potent inductor of heme oxygenase-1 [15, 35] and the protective role of SnCl2 in this experimental model has been attributed, at least in part, to the heme oxygenase-1 preinduction [15, 34]. We also showed that renal activity of Cu, Zn-SOD, Mn-SOD, and GR remained unchanged at 24 and 48 h whereas GPx and CAT activities remained unchanged at 24 h but decreased at 48 h in K2Cr2O7-injected rats. In the present work we performed a time course study of functional and structural renal damage, oxidative and nitrosative stress, and the behavior of the antioxidant enzymes Cu, Zn superoxide dismutase (Cu, Zn-SOD), Mn superoxide dismutase (Mn-SOD), glutathione reductase (GR), glutathione peroxidase (GPx), and catalase (CAT) in K2Cr2O7-induced nephrotoxicity to know if the antioxidant enzymes respond in a coordinate way and if there is an association between (a) oxidative/nitrosative stress and renal damage, (b) oxidative/nitrosative stress and the antioxidant enzymes, and (c) antioxidant enzymes and renal damage.

Methods

Reagents

Formaldehyde, anhydrous absolute ethanol, xylol, methanol, chloroform, and K2Cr2O7 were from J.T. Baker (México, D.F.), p-nitrophenyl-N-acetyl-β-D-glucosaminide, acrylamide, NADPH, N, N'-methylene-bis-acrylamide, xanthine, xanthine oxidase, nitroblue tetrazolium (NBT), β-nicotinamide adenine dinucleotide phosphate, reduced form (β-NADPH), aprotinin, leupeptin, pepstatin, and 2,4-dinitrophenylhydrazine (DNPH) were from Sigma Chemical Co. (St. Louis, MO, USA). Commercial kits to measure creatinine and blood urea nitrogen were from Spinreact (Girona, Spain). Rabbit anti-rat polyclonal antibodies against Mn-SOD (Cat. # SOD 111) and Cu, Zn-SOD (Cat. # SOD 101) were from Stressgen Biotechnologies Co. (Victoria, BC, Canada). Rabbit anti-human CAT polyclonal antibodies (Cat. # 219010) were from Calbiochem (San Diego, CA, USA). Goat anti-dinitrophenol (DNP) polyclonal antibodies (Cat. # J06) were from Biomeda Corporation (Foster City, CA, USA). Rabbit anti-3-nitrotyrosine (3-NT) polyclonal antibodies (Cat. #06-284) were from Upstate (Lake Placid, NY, USA). Anti-rabbit immunoglobulin horseradish peroxidase antibodies (Cat. # NA-934) were from Amersham (Buckinghamshire, UK). Donkey anti-goat horseradish peroxidase antibodies (Cat. # SC2020) were from Santa Cruz Biotechnology, Inc. (Santa Cruz, CA, USA). Enhanced chemiluminiscence (ECL) kit for Western blot was purchased from Amersham Life Sciences (Buckinghamshire, England). All other chemicals were reagent grade and commercially available.

Experimental design

Seven-week-old male Wistar rats with an initial body weight of 200–210 g were used. Experimental work was approved by CONACYT (#25441) and DGAPA (IN210201) and followed the guidelines of Norma Oficial Mexicana (NOM-ECOL-087-1995). Two groups of rats were studied: 1) CT, control injected subcutaneously with 0.5 ml isotonic saline solution (n = 40); and 2) K2Cr2O7, treated with a single subcutaneous injection of 15 mg/Kg K2Cr2O7 [7] in a volume of 0.5 ml (n = 43). The study was performed in two stages: rats from days 1,2,3,4, and 6 were studied in the first one (n = 5/per group) and rats from days 8, 10, and 12 were studied in the second one (n = 5 for control group and n = 6 for K2Cr2O7 group). Rats were sacrificed on days 1,2,3,4,6,8,10, and 12. There was no mortality. Rats had free access to water and CT group was pair-fed to match the food intake of K2Cr2O7 group. Animals were maintained in metabolic cages to collect 24-h urine to measure N-acetyl-β-D-glucosaminidase (NAG), total protein, creatinine, and NO2 -/NO3 -.

Animals were sacrificed by decapitation and trunk blood was collected at room temperature to obtain serum to measure chromium content and the markers of renal function, creatinine and blood urea nitrogen (BUN). Glomerular filtration rate was estimated by creatinine clearance. The kidneys were obtained to perform histological analysis, chromium determination, the activity of antioxidant enzymes, Western blot of CAT, Cu, Zn-SOD, and Mn-SOD, and the immunohistochemical localization of 3-NT, protein carbonyls, CAT, Cu, Zn-SOD, and Mn-SOD.

Chromium concentration

Chromium content in serum and in total kidney was measured by graphite-furnace atomic-absorption spectrometry on a Perkin Elmer 3110 device with furnace.

Markers of nephrotoxicity

Creatinine and BUN were measured using commercial kits according to the instructions of manufacturers and were expressed as mg/dL. Creatinine clearance was calculated with the serum and urine data according to the standard formula. Urinary NAG excretion was determined at 405 nm using p-nitrophenyl-N-acetyl-β-D-glucosaminide as substrate and the data were expressed as U/24 h [7, 15]. One unit of NAG was defined as the amount of enzyme that releases 1 μmol of p-nitrophenol in the assay conditions. Total protein in urine was measured by a turbidimetric method with 12.5% trichloroacetic acid at 420 nm [7, 15] and the data were expressed as mg/24 h.

Histological studies

Thin slices of kidney tissue with cortex and medulla were fixed by immersion in buffered formalin (pH 7.4), dehydrated and embedded in paraffin. Sections (4 μm) were stained with hematoxylin and eosin (H&E) [15]. A quantitative histological damage was determined by using a Leica Qwin Image Analyzer (Cambridge, UK). The histological profile of twenty proximal tubules randomly selected per rat (5 rats per group) was recorded (n = 100 tubuli/group at each time point). The number of tubules with histopathological alterations like swelling, cytoplasmic vacuolization, desquamation or necrosis was registered and the data were expressed as percentage of damaged tubules. The percentage of damaged tubules of K2Cr2O7 and control groups was compared.

Immunohistochemical localization of 3-NT, protein carbonyls, Cu, Zn-SOD, Mn-SOD, and CAT

For immunohistochemistry, 4 μm sections were deparaffined with xylol and rehydrated with ethanol. Endogenous peroxidase was quenched/inhibited with 4.5% H2O2 in methanol by incubation for 1.5 h at room temperature. The sections used for DNP immunohistochemistry were incubated with 0.2% DNPH in 2 N HCl for 60 min at room temperature in absence of light and then were extensively washed with phosphate buffer saline. Nonspecific adsorption was minimized by leaving the sections in 3% bovine serum albumin in phosphate buffer saline for 30 min. Sections were incubated overnight with a 1:700 dilution of anti-3-NT antibodies [15], or a 1:500 dilution of anti-DNP antibodies, or a 1:250 dilution of anti Cu, Zn-SOD antibodies, or a 1:500 dilution of anti Mn-SOD antibodies, or a 1:500 dilution of anti CAT antibodies. The sections were incubated with a 1:500 dilution of a peroxidase conjugated anti-rabbit immunoglobulin antibodies (for 3-NT, Cu, Zn-SOD, Mn-SOD, and CAT) or with a 1:500 dilution of a peroxidase conjugated anti-goat Ig (for DNP) for 1 h, and finally incubated with H2O2-diaminobenzidine for 1 min. Sections were counterstained with hematoxylin and observed under light microscopy. All the sections were incubated under the same conditions with the same concentration of antibodies, and in the same running, so the immunostaining was comparable among the different experimental groups. The stained area was quantified using a SigmaScan Pro (version 4.01.003) (Jandel Scientific, San Rafael, CA). The data are expressed as percent respect to day 0.

Urinary excretion of NO2 -/NO3 -

Nitric oxide (NO) is a labile substance with a short half-life and it decomposes rapidly to NO2 - and NO3 - in biological solutions [36], and these stable breakdown products have been measured as an index of NO production [37]. NO2 - and NO3 - were measured in the 24-hour urine samples at all time points. Urine samples were first incubated with E. coli nitrate reductase to convert the NO3 - to NO2 -, as described previously [38, 39]. To prepare this enzyme, E. coli was grown for 18 hours under anaerobic conditions in nitrate rich medium, washed, resuspended in phosphate buffer and frozen at -70°C until use. The samples were incubated with the enzyme in phosphate ammonium formate buffer (pH 7.3) for one hour at 37°C. After incubation, total NO2 - in the samples (representing both NO2 - and reduced NO3 -) was measured using the Griess reagent. Known concentrations of NaNO2 and NaNO3 were used as standards in each assay. Data were expressed as nmol/min.

Activity of antioxidant enzymes

Kidney was homogenized in a Polytron (Model PT 2000, Brinkmann, Westbury, NY, USA) for 10 seconds in cold 50 mM potassium phosphate, 0.1% Triton X-100, pH = 7.0. The homogenate was centrifuged at 19,000 × g and 4°C for 30 min and the supernatant was separated to measure total protein and the activities of CAT, GPx, GR, and total SOD.

Total SOD activity in renal cortex homogenates was assayed spectrophotometrically at 560 nm by a previously reported method using NBT as the indicator reagent [34]. The amount of protein that inhibited NBT reduction to 50% of maximum was defined as one unit of SOD activity. Results were expressed as U/mg protein. CAT activity in renal cortex, was assayed by a method based on the disappearance of 30 mM H2O2 at 240 nm [34] and the data were expressed as k/mg protein. GPx activity in renal cortex was measured at 340 nm using GR and NADPH in a coupled reaction [34]. One unit of GPx was defined as the amount of enzyme that oxidize 1 μmol of NADPH/min. Data were expressed as U/mg protein. GR activity in renal cortex was assayed using oxidized glutathione as substrate and measuring the disappearance of NADPH at 340 nm [34]. One unit of GR was defined as the amount of enzyme that oxidize 1 μmol of NADPH/min. Data were expressed as U/mg protein.

Western blot

Renal cortex (100 mg) was homogenized in 300 μl of phosphate buffer 50 mM, pH 7.4 containing the following cocktail of protease inhibitors: leupeptin 5 μg/ml, pepstatin 7 μg/ml, aprotinin 5 μg/ml, and EDTA 1 mM. The homogenates were centrifuged at 1,000 × g and 4°C for 10 min. Thirty μg of protein were fractionated by reducing 12.5% sodium dodecyl sulfate polyacrylamide gel electrophoresis and electroblotted to a nitrocellulose membrane (Hybond™ ECL™, Amersham, Buckinghamshire, England). Immunodetection was performed using specific primary antibodies against CAT (1:500 dilution), Mn-SOD (1,5000 dilution), or Cu, Zn-SOD (1:5,000 dilution). Membranes were then probed with the appropriate secondary antibody-peroxidase conjugate (1:5,000 dilution). The hybrids were visualized using ECL detection system and quantified by densitometry (Sigma ScanPro, version 4.0, San Rafael, CA, USA). Data were expressed as % of the control.

Statistics

The data are expressed as the mean ± SEM and were analyzed by two-way analysis of variance followed by Bonferroni t-test using the software Prism 2.01 (GraphPad, San Diego, CA, USA). A P value less than 0.05 was considered statistically significant.

Results and discussion

ROS have been involved in the pathophysiology of ARF induced by K2Cr2O7 and some antioxidants are able to ameliorate renal damage induced by this compound [15, 16, 18, 23, 25]. In addition, it has been previously shown that renal heme oxygenase-1 preinduction by SnCl2 ameliorates ARF and prevents oxidative and nitrosative stress induced 24 h after K2Cr2O7 injection [15, 34]. In the present work we performed a time-course analysis of the nephrotoxicity, oxidative and nitrosative stress, and changes in antioxidant enzymes induced by K2Cr2O7. Body weight of control and K2Cr2O7-treated rats was similar at all time points (see additional file 1). Urinary volume was increased in K2Cr2O7-treated animals on days 3 (1.9-fold) and 4 (1.6-fold) and returned to control values thereafter (see additional file 1). Polyuria observed in our rats is consistent with previous data [2]. We measured the chromium content in serum and kidney and it was found that it increased on days 1–6 and 1–12, respectively (Fig. 1). In both cases the peak value was reached on day 1 and then the chromium concentration decreased gradually, but in kidney remained still significantly high on day 12 and in serum reached values not different from control rats since day 6. Our data are consistent with previous pharmacokinetic studies which have shown that chromium is rapidly distributed [40] and that the half life of chromium is longer in kidney than in blood serum [41].

Figure 1
figure 1

Chromium concentration in (A) serum and (B) kidney in control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P < 0.001 vs. control group. n = 3–6.

Markers of nephrotoxicity are shown in Figs. 2 and 3. Creatinine clearance decreased on days 1–4 (Fig. 2A), and serum creatinine and BUN increased on days 1–4 and 1–6, respectively (Figs. 2B and 2C). Urinary excretion of NAG and total protein increased on days 1–4 and 1–6, respectively (Figs. 3A and 3B). The major damage was observed on days 2–4 (Figs. 2 and 3). On day 8, all these markers returned to control values indicating that K2Cr2O7-induced ARF is reversible which is consistent with previous observations [10]. These functional findings are in a close agreement with the histological data. Significant structural abnormalities were seen in the kidney cortex since the first day after K2Cr2O7 administration. Specifically, 50% of the epithelium from the proximal convoluted tubules showed cellular swelling, necrosis and partial or complete detachment from the basal membrane. On day 2, when the peak of the tubular damage was observed, 70% of the proximal convoluted tubules was affected (Figs. 4B and 5). On days 3 and 4 proximal convoluted tubules showing the above mentioned abnormalities decreased to 40 and 25%, respectively (Fig. 5). On day 4, many tubules also showed numerous cellular debris in their lumen and epithelium regeneration was also seen but it was more evident on days 6 and 8 (data not shown). On days 10 and 12 the kidney histology was almost normal (Fig. 4C), only few tubules were revisted by active regenerative epithelium (small cuboidal cells with big nucleus and occasional mitotic figures). The high levels of serum and kidney chromium correlated with the structural and functional renal alterations on days 1–6. Interestingly, the renal damage disappeared in spite of the kidney still having high levels of chromium on days 8–12. This may be explained by the fact that chromium (VI), which is readily taken up into tissues, is reduced inside the cell to the final stable product chromium (III) [19]. The biological effects of chromium (VI) are generally attributed to cellular uptake, because chromium (VI), in contrast to chromium (III), is easily taken up by cells through the sulfate anion transport system [42, 43]. However, once inside, chromium (VI) is reduced through reactive intermediates such as chromium (V) and chromium (IV) to the more stable chromium (III) by cellular reductants including glutathione, vitamins C and B2, and flavoenzymes [42]. Thus, the formation of chromium (III) or other intermediate oxidation states, in particular chromium (V), is believed to play a role in the biological effect of chromium (VI) compounds. In vitro studies have shown that this reduction process causes the generation of active oxygen species [44] which are involved in renal damage [15, 34]. Interestingly, it has been shown that a low dose of K2Cr2O7 (10 mg/Kg) is unable to induce nephrotoxicity suggesting a threshold of this compound to induce renal damage [10]. In addition, it is know that chromium is located in vacuoles inside the proximal tubular cells which may delay the excretion of this metal [13]. In fact it has been shown that chromium remains for a long time in several tissues including kidney [13, 40, 41] which is consistent with our data.

Figure 2
figure 2

(A) Creatinine clearance, (B) serum creatinine, and (C) blood urea nitrogen control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P at least <0.05 vs. control group. n = 4–6.

Figure 3
figure 3

Urinary excretion of (A) NAG and (B) total protein in control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P at least <0.05 vs. control group. n = 4–18.

Figure 4
figure 4

Representative images of histology (first row) and immunohistochemical detection of 3-NT (second row) and DNP (third row) during the evolution of the kidney damage produced by K2Cr2O7. The study was performed in control rats (day 0) and on days 2 and 12 after a single injection of K2Cr2O7 (15 mg/Kg). (A) Normal kidney histology from control rat (H/E). (B) On day 2, there is extensive tubular damage manifested by swollen and necrotic epithelial cells (H/E). (C) total kidney regeneration has been produced on day 12 post K2Cr2O7 administration (H/E). (D) Normal kidney from control animals shows scarce 3-NT immunoreactivity. (E) On day 2, there is strong 3-NT immunostaining in the epithelium from the convoluted tubules. (F) Slight 3-NT immunostaining is observed in the tubular epithelium on day 12. (G) Normal kidney from control rat shows scarce DNP immunostaining in the tubular epithelium. (H) In contrast, on day 2 there is clear DNP immunostaining in the cytoplasm and nucleus of the tubular epithelial cells and mesangium. (I) Slight DNP immunostaining is observed on day 12. 400 X.

Figure 5
figure 5

Quantitative histological analysis in control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P < 0.05 vs. control group. n = 20 tubules/rat and 5 rats/group.

The histological abnormalities correlated with renal functional alterations (days 1–6) and with the immunohistochemical detection of 3-NT and protein carbonyls. DNPH reacts with free carbonyls forming DNP-derived proteins which can be detected using antibodies against DNP. Carbonyl derivatives are formed by ROS mediated oxidation of side-chains of some amino acid residues and are important detectable markers of oxidative damage to proteins [45]. Kidneys from control non-treated animals did not show or only had slight immunostaining to 3-NT or protein carbonyls (Figs. 4D and 4G), while kidneys from K2Cr2O7-treated animals on day 2 showed strong 3-NT immunostaining in necrotic and swollen tubular epithelial cells, as well as some mesangial cells (Fig. 4E). This increase was significative (P < 0.0001 vs. day 0) (Table 1). In fact, it was observed from day 1 to day 8 (data not shown). Protein carbonyls immunostaining was also clear in the cytoplasm and nuclei from tubular epithelium and mesangial glomerular cells at the same time points (Fig. 4H and data not shown) (P < 0.001 vs. day 0) (Table 1). Then, on days 10 to 12, a striking decrease of 3-NT and DNP immunostaining was seen, being similar to the control non-treated rats (Figs. 4F and 4I). In previous works, we also have found in K2Cr2O7-treated rats an intense 3-NT immunostaining [15] and an increase in protein carbonyl content [15, 34]. Our data confirm that ROS are involved in K2Cr2O7-induced nephrotoxicity [16, 17, 19, 26, 44] which has additionally been supported by the protective effect of several antioxidants in this experimental model [2125].

Table 1 Quantitative analysis of 3-NT, DNP, catalase, Cu, Zn-SOD, and Mn-SOD immunostaining.

On the other hand, it was found that urinary excretion of NO2 -/NO3 - decreased significantly in K2Cr2O7-treated rats on days 2–6 (Fig. 6). Urinary excretion of NO2 -/NO3 - is considered as an index of NO production [37] and therefore these data may suggest that NO production is decreased in K2Cr2O7-treated rats. However, the strong nitrosative stress observed in our rats by 3-NT immunostaining, may suggest that the decrease in urinary NO2 -/NO3 - excretion could be secondary to the NO consumption by its reaction with superoxide anion to generate peroxynitrite and other reactive nitrogen species involved in protein tyrosine nitration [46]. This is supported by the association between the time course alterations in 3-NT immunostaining (days 1–8) and the decrease in urinary NO2 -/NO3 - excretion (days 2–6).

Figure 6
figure 6

Urinary excretion of NO2 -/NO3 - in control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P < 0.05 vs. Control group. n = 4–10.

Further we investigated the time response of the renal antioxidant enzymes in K2Cr2O7-treated rats. In control rats, strong CAT immunostaining was seen in the epithelial cells from proximal and distal convoluted tubules (Fig. 7A). From day 2 to day 10 after K2Cr2O7 administration, CAT immunostaining showed striking decrease, particularly in the epithelium from tubules with evident cellular damage (Fig. 7B and data not shown). Then, at day 12, when almost normal kidney histology was seen, strong CAT immunostaining was observed in a similar pattern than in the kidney from control animals (Fig. 7C). CAT activity (Fig. 8A) and content (Fig. 8B) decreased on days 2–10 and 3–10, respectively. In control animals the epithelial cells from the proximal and convoluted tubules showed strong immunoreactivity to Cu, Zn-SOD and Mn-SOD (Figs. 7D and 7G). This pattern of immunostaining did not show evident changes during the time course study (days 1–12) (Figs. 7E, 7F, 7H, 7I, and data not shown); even the damaged swollen epithelial tubular cells exhibited strong immunostaining to both SOD enzymes. These data are in agreement with kidney total SOD activity (Fig. 9) and with the protein content of Mn-SOD and Cu, Zn-SOD measured by Western blot which remained unchanged at all time points in K2Cr2O7-treated rats (data not shown). Finally, the activity of GPx and GR decreased on days 3–12 and on days 2–10, respectively (Fig. 10). It is very clear from the above data that there was a differential response of the antioxidant enzymes to K2Cr2O7 injection. Interestingly, no enzyme (SOD, CAT, GPx, and GR) was altered on day 1 when the kidney damage was very severe. Surprisingly, SOD activity and content remained essentially unchanged at all time points. This may be a consequence of the fact that both SOD enzymes were immunolocalized even in the damaged epithelial tubular cells. In contrast, the other enzymes decreased to reach their lowest values on day 6 returning then to basal values by day 12 with the exception of GPx which remained low. On days 2–6, there was some degree correlation between CAT, GPx, and GR and the markers of nephrotoxicity. However, from day 8 these enzymes remained low in spite of renal function and structure returned to control. Furthermore, the time course study suggests that the decrease in GPx, GR, and CAT activities may be secondary to the oxidative and nitrosative stress which are evident since day 1. In fact, it has been demonstrated that peroxynitrite impairs GPx activity [47] and superoxide anion inactivates GPx [48] and CAT [49]. Interestingly, GR and CAT remained low until day 10 and GPx remained low until day 12 in absence of oxidative and nitrosative stress. The reason why these enzymes remained low at the end of the study is not clear, however we may speculate that factors other than oxidative/nitrosative stress are involved in the diminution in these enzymes and/or proximal tubules have not reached yet the full capacity to synthesize these enzymes. Therefore, additional studies are required to explain why some antioxidant enzymes remained low on days 10–12 in absence of oxidative/nitrosative stress.

Figure 7
figure 7

Representative immunohistochemical detection of CAT (first row), Cu, Zn-SOD (second row), and Mn-SOD (third row) during acute renal failure induced by K2Cr2O7. The study was performed in control rats (day 0) and on days 2 and 12 after a single injection of K2Cr2O7 (15 mg/Kg). (A) Normal kidney from control rats shows intense CAT immunoreactivity in the proximal and distal convoluted tubules. (B) In contrast, kidney cortex on day 2 shows evident decrease of CAT immunostaining. (C) Strong CAT immunoreactivity in the tubular epithelium is observed on day 12. (D) Normal kidney from control animals also showed strong Cu, Zn-SOD immunostaining in the cortex convoluted tubules. This strong Cu, Zn-SOD immunoreactivity is also observed on day 2 (E) and on day 12 (F). A similar pattern of Mn-SOD immunostaining is observed in normal kidney from control rat (G), and after 2 (H) and 12 (I) days of K2Cr2O7 injection. A-C and G-I 100X, D-F 400X.

Figure 8
figure 8

(A) Activity and (B) content of CAT in kidney from control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P at least <0.05 vs. control group. n = 4–6.

Figure 9
figure 9

Total superoxide dismutase activity in kidney from control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. n = 3–6.

Figure 10
figure 10

Activity of (A) glutathione peroxidase and (B) glutathione reductase in kidney from control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P at least <0.05 vs. control group. n = 5–6.

Conclusion

The data show an association between oxidative/nitrosative stress and functional and structural renal damage induced by K2Cr2O7 in rats at different time points, but not between this damage and antioxidant enzymes.

Abbreviations

ARF:

Acute renal failure

BUN:

Blood urea nitrogen

CAT:

Catalase

Cu Zn-SOD:

Copper and zinc superoxide dismutase

DNP:

Dinitrophenol

DNPH 2:

4-dinitrophenylhydrazine

ECL:

Enhanced chemiluminiscence

GPx:

Glutathione peroxidase

GR:

Glutathione reductase

H2O2 :

Hydrogen peroxide

K2Cr2O7 :

Potassium dichromate

Mn-SOD:

Manganese superoxide dismutase

NADPH:

Nicotinamide adenine dinucleotide phosphate

NAG:

N-acetyl-β-D-glucosaminidase

NBT:

Nitroblue tetrazolium

NO:

Nitric oxide

NO2 - :

Nitrate

NO3 - :

Nitrite

3-NT:

3-Nitrotyrosine

ROS:

Reactive oxygen species

SEM:

Standard error of the mean

References

  1. Barceloux DG: Chromium. J Toxicol Clin Toxicol . 1999, 37: 173-194. 10.1081/CLT-100102418.

    Article  CAS  PubMed  Google Scholar 

  2. Verschoor MA, Braget PC, Herber RFM, Zielhuis RL, Zwennis WC: Renal function of chrome-plating workers and welders. Int Arch Occup Environ Health. 1988, 60: 67-70. 10.1007/BF00409381.

    Article  CAS  PubMed  Google Scholar 

  3. Ingber A, Gammelgaard B, David M: Detergents and bleaches are sources of chromium contact dermatitis in Israel. Contact Dermatitis. 1998, 38: 101-104.

    Article  CAS  PubMed  Google Scholar 

  4. Norseth T: The carcinogenicity of chromium and its salts. Br J Ind Med. 1986, 43: 649-651.

    CAS  PubMed  PubMed Central  Google Scholar 

  5. Sharma BK, Singhal PC, Chugh KS: Intravascular haemolysis and renal failure following potassium dichromate poisoing. Postgrad Med J. 1978, 54: 414-415.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  6. Picaud JC, Cochat P, Parchoux B, Berthier JC, Gilly J, Chareyre S, Larbre F: Acute renal failure in a child after chewing of match heads. Nephron. 1991, 57: 225-226.

    Article  CAS  PubMed  Google Scholar 

  7. Pedraza-Chaverri J, Moreno-Muñiz SI, Cruz C, Hernandez-Pando R, Larriva-Sahd J, Tapia E: Urinary Angiotensin I-converting enzyme activity is increased in experimental acute renal failure. Clin Invest Med. 1995, 18: 424-434.

    CAS  PubMed  Google Scholar 

  8. Michael UF, Logan JL, Meeks LA: The beneficial effects of thyroxine on nephrotoxic acute renal failure in the rat. J Am Soc Nephrol. 1991, 1: 1236-1240.

    CAS  PubMed  Google Scholar 

  9. Seiken G, Grillo FG, Schaudies RP, Johnson JP: Modulation of renal EGF in dichromate-induced acute renal failure treated with thyroid hormone. Kidney Int. 1994, 45: 1622-1627.

    Article  CAS  PubMed  Google Scholar 

  10. Gumbleton M, Nicholls PJ: Dose-response and time-response biochemical and histological study of potassium dichromate-induced nephrotoxicity in the rat. Food Chem Toxicol. 1988, 26: 37-44. 10.1016/0278-6915(88)90039-7.

    Article  CAS  PubMed  Google Scholar 

  11. Ngaha EO: Renal effects of potassium dichromate in the rat: comparison of urinary enzyme excretion with corresponding tissue patterns. Gen Pharmacol. 1981, 12: 497-500.

    Article  CAS  PubMed  Google Scholar 

  12. Evan AP, Dail WG: The effects of sodium chromate on the proximal tubules of the rat kidney. Fine structural damage and lysozymuria. Lab Invest. 1974, 30: 704-715.

    CAS  PubMed  Google Scholar 

  13. Berry JP, Hourdry J, Galle P, Lagrue G: Chromium concentration by proximal renal tubule cells: an ultrastructural, microanalytical and cytochemical study. J Histochem Cytochem. 1978, 26: 651-657.

    Article  CAS  PubMed  Google Scholar 

  14. Franchini I, Mutti A, Cavatorta A, Corradi A, Cosi A, Olivetti G, Borghetti A: Nephrotoxicity of chromium. Remarks on an experimental and epidemiological investigation. Contrib Nephrol. 1978, 10: 98-110.

    Article  CAS  PubMed  Google Scholar 

  15. Barrera D, Maldonado PD, Medina-Campos ON, Hernández-Pando R, Ibarra-Rubio ME, Pedraza-Chaverri J: HO-1 induction attenuates renal damage and oxidative stress induced by K2Cr2O7. Free Radic Biol Med. 2003, 34: 1390-1398. 10.1016/S0891-5849(03)00068-6.

    Article  CAS  PubMed  Google Scholar 

  16. Sengupta T, Chattopadhyay D, Ghosh N, Maulik G, Chatterjee GC: Impact of chromium on lipoperoxidative processes and subsequent operation of the glutathione cycle in rat renal system. Indian J Biochem Biophys. 1992, 29: 287-290.

    CAS  PubMed  Google Scholar 

  17. Stohs SJ, Bagchi D: Oxidative mechanisms in the toxicity of metal ions. Free Radic Biol Med. 1995, 18: 321-336. 10.1016/0891-5849(94)00159-H.

    Article  CAS  PubMed  Google Scholar 

  18. Huang YL, Chen CY, Sheu JY, Chuang IC, Pan JH, Lin TH: Lipid peroxidation in workers exposed to hexavalent chromium. J Toxicol Environ Health A. 1999, 56: 235-247. 10.1080/009841099158088.

    Article  CAS  PubMed  Google Scholar 

  19. Liu KJ, Shi X: In vivo reduction of chromium (VI) and its related free radical generation. Mol Cell Biochem. 2001, 222: 41-47. 10.1023/A:1017994720562.

    Article  CAS  PubMed  Google Scholar 

  20. Bagchi D, Hassoun EA, Bagchi M, Stohs SJ: Chromium-induced excretion of urinary lipid metabolites, DNA damage, nitric oxide production, and generation of reactive oxygen species in Sprague-Dawley rats. Comp Biochem Physiol C Pharmacol Toxicol Endocrinol. 1995, 110: 177-187. 10.1016/0742-8413(94)00093-P.

    Article  CAS  PubMed  Google Scholar 

  21. Hojo Y, Satomi Y: In vitro nephrotoxicity induced in mice by chromium (VI): involvement of glutathione and chromium (V). Biol Trace Elem Res. 1991, 31: 21-31.

    Article  CAS  PubMed  Google Scholar 

  22. Standeven AM, Wetterhahn KE: Possible role of glutathione in chromium(VI) metabolism and toxicity in rats. Pharmacol Toxicol. 1991, 68: 469-476.

    Article  CAS  PubMed  Google Scholar 

  23. Na KJ, Jeong SY, Lim CH: The role of glutathione in the acute nephrotoxicity of sodium dichromate. Arch Toxicol. 1992, 66: 646-651.

    Article  CAS  PubMed  Google Scholar 

  24. Sugiyama M: Role of physiological antioxidants in chromium(VI)-induced cellular injury. Free Radic Biol Med. 1992, 12: 397-407. 10.1016/0891-5849(92)90089-Y.

    Article  CAS  PubMed  Google Scholar 

  25. Appenroth D, Winnefeld K: Vitamin E and C in the prevention of metal nephrotoxicity in developing rats. Exp Toxicol Pathol. 1998, 50: 391-396.

    Article  CAS  PubMed  Google Scholar 

  26. Bagchi D, Stohs SJ, Downs BW, Bagchi M, Preuss HG: Cytotoxicity and oxidative mechanisms of different forms of chromium. Toxicology. 2002, 180: 5-22. 10.1016/S0300-483X(02)00378-5.

    Article  CAS  PubMed  Google Scholar 

  27. O'Brien P, Kortenkamp A: Chemical models important in understanding the way in which chromate can damage DNA. Environ Health Perspect. 1994, 102 (Suppl 3): 3-10.

    Article  PubMed  PubMed Central  Google Scholar 

  28. Shi X, Dalal NS: Generation of hydroxyl radical by chromate in biologically relevant systems: role of Cr(VI) complex versus tetraperochromate(V). Environ Health Perspect. 1994, 102 (Suppl 3): 231-236.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  29. Stohs SJ: The role of free radicals in toxicity and disease. J Basic Clin Physiol Pharmacol. 1995, 6: 205-228.

    Article  CAS  PubMed  Google Scholar 

  30. Shi XL, Dalal NS: Evidence for a Fenton type mechanism for the generation of OH radicals in the reduction of Cr(VI) in cellular media. Arch Biochem Biophys. 1990, 281: 90-95. 10.1016/0003-9861(90)90417-W.

    Article  CAS  PubMed  Google Scholar 

  31. Aiyar J, Berkovits HJ, Floyd RA, Wetterhahn KE: Reaction of chromium (VI) with glutathione or with hydrogen peroxide: identification of reactive intermediates and their role in chromium (VI)-induced DNA damage. Environ Health Perspect. 1991, 92: 53-62.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  32. Tsou TC, Chen CL, Liu TY, Yang JL: Induction of 8-hydroxydeoxyguanosine in DNA by chromium (III) plus hydrogen peroxide and its prevention by scavengers. Carcinogenesis. 1996, 17: 103-108.

    Article  CAS  PubMed  Google Scholar 

  33. Liu KJ, Shi X, Dalal NS: Synthesis of Cr(VI)-GSH, its identification and its free hydroxyl radical generation: a model compound for Cr(VI) carcinogenicity. Biochem Biophys Res Commun. 1997, 235: 54-58. 10.1006/bbrc.1997.6277.

    Article  CAS  PubMed  Google Scholar 

  34. Barrera D, Maldonado PD, Medina-Campos ON, Hernández-Pando R, Ibarra-Rubio ME, Pedraza-Chaverri J: Protective effect of SnCl2 on K2Cr2O7-induced nephrotoxicity in rats: the indispensability of HO-1 preinduction and lack of association with some antioxidant enzymes. Life Sci. 2003, 73: 3027-3041. 10.1016/j.lfs.2003.06.002.

    Article  CAS  PubMed  Google Scholar 

  35. Toda N, Takahashi T, Mizobuchi Z, Fujii H, Nakahira K, Takahashi S, Yamashita M, Morita K, Hirakawa M: Tin chloride pretreatment prevents renal injury in rats with ischemic acute renal failure. Crit Care Med. 2002, 30: 1512-1522. 10.1097/00003246-200207000-00020.

    Article  CAS  PubMed  Google Scholar 

  36. Marletta MA, Yoon PS, Iyengar R, Leaf CD, Wishnok JS: Macrophage oxidation of L-arginine to nitrite and nitrate: nitric oxide is an intermediate. Biochemistry. 1988, 27: 8706-8711. 10.1021/bi00424a003.

    Article  CAS  PubMed  Google Scholar 

  37. Moncada S, Palmer RM, Higgs EA: Nitric oxide: physiology, pathophysiology, and pharmacology. Pharmacol Rev. 1991, 43: 109-142.

    CAS  PubMed  Google Scholar 

  38. Bartholomew B: A rapid method for the assay of nitrate in urine using the nitrate reductase enzyme of Escherichia coli. Food Chem Toxicol. 1984, 22: 541-543. 10.1016/0278-6915(84)90224-2.

    Article  CAS  PubMed  Google Scholar 

  39. Granger DL, Hibbs JB, Perfect JR, Durack DT: Metabolic fate of L-arginine in relation to microbiostatic capability of murine macrophages. J Clin Invest. 1990, 85: 264-273.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  40. O'Flaherty EJ: A physiologically based model of chromium kinetics in the rat. Toxicol Appl Pharmacol. 1996, 138: 54-64. 10.1006/taap.1996.0097.

    Article  PubMed  Google Scholar 

  41. Weber H: Long-term study of the distribution of soluble chromate-51 in the rat after a single intratracheal administration. J Toxicol Environ Health. 1983, 11: 749-764.

    Article  CAS  PubMed  Google Scholar 

  42. De Flora S, Wetterhahn KE: Mechanism of chromium (VI) metabolism and genotoxicity. Life Chem Rep. 1989, 7: 169-244.

    CAS  Google Scholar 

  43. Dartsch PC, Hildenbrand S, Kimmel R, Schmahl FW: Investigations on the nephrotoxicity and hepatotoxicity of trivalent and hexavalent chromium compounds. Int Arch Occup Environ Health. 1998, 71 (Suppl): S40-S45.

    PubMed  Google Scholar 

  44. Sugiyama M: Role of cellular antioxidants in metal-induced damage. Cell Biol Toxicol. 1994, 10: 1-22. 10.1007/BF00757183.

    Article  CAS  PubMed  Google Scholar 

  45. Smith MA, Sayre LM, Anderson VE, Harris PL, Beal MF, Kowall N, Perry G: Cytochemical demonstration of oxidative damage in Alzheimer disease by immunochemical enhancement of the carbonyl reaction with 2,4-dinitrophenylhydrazine. J Histochem Cytochem. 1998, 46: 731-735.

    Article  CAS  PubMed  Google Scholar 

  46. Radi R: Nitric oxide, oxidants, and protein tyrosine nitration. Proc Natl Acad Sci U S A. 2004, 101: 4003-4008. 10.1073/pnas.0307446101.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  47. Padmaja S, Squadrito GL, Pryor WA: Inactivation of glutathione peroxidase by peroxynitrite. Arch Biochem Biophys. 1998, 349: 1-6. 10.1006/abbi.1997.0407.

    Article  CAS  PubMed  Google Scholar 

  48. Blum J, Fridovich I: Inactivation of glutathione peroxidase by superoxide radical. Arch Biochem Biophys. 1985, 240: 500-508. 10.1016/0003-9861(85)90056-6.

    Article  CAS  PubMed  Google Scholar 

  49. Rister M, Baehner RL: The alteration of superoxide dismutase, catalase, glutathione peroxidase, and NAD(P)H cytochrome c reductase in guinea pig polymorphonuclear leukocytes and alveolar macrophages during hyperoxia. J Clin Invest. 1976, 58: 1174-1184.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

Pre-publication history

Download references

Acknowledgements

This work was supported by CONACYT (#25441) given to MEIR and DGAPA (IN210201) given to JPCH.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to José Pedraza-Chaverrí.

Additional information

Competing interests

The author(s) declare that they have no competing interests.

Authors' contributions

JPCH conceived and coordinated the study and wrote and edited the manuscript. DB performed histological, immunohistochemical and statistical analyses. Coordinated the study and wrote the manuscript. ONMC performed Western blot analysis. RCC performed animal studies and collected samples. RHP performed the histological and immunohistochemical analyses. NAMR performed animal studies and collected samples. PDM measured antioxidant enzyme activity. MIS performed animal studies and collected samples. ET measured urinary excretion of NO2 -/NO3 -. LS and MEC measured chromium concentration. MEIR coordinated the study and edited the manuscript.

Electronic supplementary material

12882_2004_45_MOESM1_ESM.doc

Additional File 1: (A) Body weight, and (B) urinary volume in control () and K2Cr2O7 ()-treated rats. Data are mean ± SEM. *P at least <0.01 vs. control group. n = 5–18. (DOC 36 KB)

Authors’ original submitted files for images

Rights and permissions

Reprints and permissions

About this article

Cite this article

Pedraza-Chaverrí, J., Barrera, D., Medina-Campos, O.N. et al. Time course study of oxidative and nitrosative stress and antioxidant enzymes in K2Cr2O7-induced nephrotoxicity. BMC Nephrol 6, 4 (2005). https://doi.org/10.1186/1471-2369-6-4

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/1471-2369-6-4

Keywords