Influence of Cadmium(II) Ions and Brewery Sludge on Metallothionein Level in Earthworms (Eisenia fetida) – Bio- transforming of Toxic Wastes

Abstract

Metallothioneins belong to a group of intracellular, high molecular and cysteine-rich proteins whose content in an organism increase with increasing concentration of a heavy metal. The aim of this work was to apply the electrochemical analysis for the analysis of metallothioneins in earthworms exposed to cadmium ions and brewery sludge. Here we utilized adsorptive transfer technique coupled with differential pulse voltammetry Brdicka reaction to determine metallothionein in different biological samples. By means this very sensitive technique it was possible to analyze metallothionein in concentrations below 1 μmol.l⁻¹ with the standard deviation of 4-5%. We found out that the average MT level in the non-treated earthworms oscillated between 19 and 48 μmol.l⁻¹. When we analysed samples of earthworms treated by cadmium, we observed that the MT content increased with the exposition length and increase dose of cadmium ions. Finally, we attempted to study and compare the toxicity of the raw sludge and its leach by using of earthworms. The raw brewery sludge caused the death of the earthworms quickly. Earthworms held in the presence of leach from brewery sludge increased their weight of 147 % of their original weight because they ingested the nutrients from the sludge. The metallothionein level changes markedly with increasing time of exposition and applied dose of toxic compound. It clearly follows from the obtained results that the MT synthesis is insufficient in the first hours of the exposition and increases after more than 24 h.

1. Introduction

According to the principles of environment protection in the Czech Republic, the markedly increase of sewage-farm sludge's production from various sources can be expected. Their processing and disposing is one from the most important troubles connected with waste water purification. The sludge coming from plants of industrial purpose often contains dangerous compounds like heavy metals, organic residues and pathogenic organisms. During the waste water disposing the adsorption of heavy metals to activated and biological sludge occurs. From 20 to 90 % of total content of heavy metals in the sludge can be removed by waste-water disposing according to its technological parameters, age of the sludge and its pH value. Cadmium and lead can be removed effectively from the waste water by procedures based on physically-chemical processes. High concentration of toxic heavy metals in sludge can influence negatively their utilizing for fertilization and composting. In addition, the utilizing of the sludge can be markedly improved by biological disposing through using of various microorganisms, fungi and animals [1-7].

The ecotoxicological markers such as various peptides and proteins could be very useful tool for rapid and easy assessment of the sludge toxicity [8,9]. Metallothioneins (MTs) is thought to be a marker of environment polluting by heavy metals [10]. MTs belongs to group of intracellular and cysteine-rich proteins with molecular weight from 6 to 10 kDa [10-12], which are able to bind heavy metal ions thanks to its high cysteine content. MTs consist of two binding domains (α, β) that are assembled from cysteine clusters. The heavy metals detoxification and maintaining of their homeostasis in an organism can be considered as the main physiological function of MTs [13-19]. The aim of this work was to investigate the effect of cadmium ions and brewery sludge on MT levels in earthworms (Eisenia fetida).

2. Material and Methods

2.1 Chemicals and pH measurements

Rabbit liver MT (MW 7143 g.mol⁻¹), containing 5.9 % Cd and 0.5 % Zn, was purchased from Sigma Aldrich (St. Louis, USA). Co(NH₃)₆Cl₃ and other chemicals used were purchased from Sigma Aldrich unless noted otherwise. The stock standard solutions of MT (10 μg.ml⁻¹) was prepared by ACS water (Sigma-Aldrich, USA) and stored in the dark at −20 °C. Working standard solutions were prepared daily by dilution of the stock solutions with ACS water. The pH value was measured using WTW inoLab Level 3 with terminal Level 3 (Weilheim, Germany), controlled by the personal computer program (MultiLab Pilot; Weilheim, Germany). The pH-electrode (SenTix-H, pH 0–14/3M KCl) was regularly calibrated by set of WTW buffers (Weilheim, Germany).

2.2 Biological samples

Earthworms (Eisenia fetida; average weight 0.25 g) were kept at laboratory temperature in lid cultivation flasks which contained five litters of artificial soil (OECD 207) and 175 ml of distilled water or Cd(NO₃)₂ solution. The earthworms were exposed to cadmium(II) ions (0, 5, 10, 20, 30, 40 and 50 μmol.l⁻¹) for seven days. The samples were collected daily. In the case of experiments with brewery sludge, flasks were filled with five litters of brewery sludge and/or its leach obtained from Cerna Hora Brewery (Cerna Hora, Czech Republic), whereas the earthworms were treated for fourteen days. After 14 days, earthworms were sampled and killed by deep-freezing. In the both experimental models, flasks were stored in digester with continuous lighting of 450 lux. The collected earthworms were weighed and subsequently grinded in the presence of 1 ml of phosphate buffer (50 mM, pH 7) by Ika A11 basic grinder (IKA Werke GmbH and Co., Staufen, KG, Germany).

2.3 Preparation of biological samples for electrochemical analysis

The grinded samples of earthworms (approximately 0.5 g) were homogenized in liquid nitrogen, diluted with 1 ml of phosphate buffer (50 mM, pH 7), and vortexed for 15 min on Vortex-2 Genie (Scientific industries, USA). After that, the homogenised samples were heat treated and solvent precipitated (Petrlova et al, 2006). Briefly, the samples were kept at 99 °C in a thermomixer (Eppendorf 5430, USA) for 15 min with occasional stirring, and then cooled to 4 oC. The denatured homogenates were centrifuged at 4 °C, 15 000 g for 30 min. (Eppendorf 5402, USA). Heat treatment and solvent precipitation effectively denature and remove high molecular weight proteins out from samples.

2.4 Electrochemical measurements

Electrochemical measurements were performed with AUTOLAB Analyser (EcoChemie, Netherlands) connected to VA-Stand 663 (Metrohm, Switzerland), using a standard cell with three electrodes. The working electrode was a hanging mercury drop electrode (HMDE) with a drop area of 0.4 mm². The reference electrode was an Ag/AgCl/3M KCl electrode and the auxiliary electrode was a graphite electrode. For smoothing and baseline correction the software GPES 4.4 supplied by EcoChemie was employed. The Brdicka supporting electrolyte containing 1 mmol.l⁻¹ Co(NH₃)₆Cl₃ and 1 M ammonia buffer (NH₃(aq) + NH₄Cl, pH = 9.6) was used and changed after five measurements; surface-active agent was not added. The samples of the MT were reduced before each measurement by 1 mM tris(2-carboxyethyl)phosphine addition according to [20,21]. Adsorptive transfer stripping technique coupled with differential pulse voltammetry Brdicka reaction parameters were as follows: an initial potential of −0.6 V, an end potential −1.6 V, a modulation time 0.057 s, a time interval 0.2 s, a step potential of 1.05 mV.s⁻¹, a modulation amplitude of 250 mV, temperature of supporting electrolyte of 5 °C, E_ads = 0 V. The temperature of supporting electrolyte was maintained by the flow electrochemical cell coupled with thermostat JULABO F12/ED (Labortechnik GmbH, Germany). Other details have been published by Petrlova et al. [21] and Adam et al. [22].

2.5 Statistical analysis

Data were processed using MICROSOFT EXCEL® (USA). Results are expressed as mean ± S.D. unless noted otherwise. Statistical significance of the differences between MT in control and treated earthworms was determined. Differences with p < 0.05 were considered significant.

3. Results and Discussion

Heavy metals ions are very threaten for living organisms. For example, cadmium and lead are classified as very dangerous and toxic. These heavy metals are often cumulated in biosphere and can entry the human food chain [23,24]; moreover they are often present in various kinds of wastes.

3.1 Changes in metallothionein level in earthworms exposed to cadmium ions

Papers devoted to MT induction in earthworms under various stresses have been published [4,25-27]. In addition the distribution of the MT isoforms has been studied by various specific techniques [26,28,29]. The given methods are appropriate for MT determination, but they are heavy for instrumentation. Electrochemical methods are also very appropriate for MTs determination, as shown in [21,30]. Thus we utilized adsorptive transfer technique coupled with differential pulse voltammetry Brdicka reaction to determine MT according to [21]. Use this very sensitive technique it was possible to analyze MT in concentrations below 1 μmol.l⁻¹ with the standard deviation of 4-5%. The calibration curve measured in the presence of Brdicka supporting electrolyte at 5°C was linear (y = 4.87x + 6.55; R² = 0.9946). Based on our previous experimental data the dilution of a homogenized sample of interest can markedly affect the electrochemical analysis. The earthworms' homogenates were diluted prior the analysis (10 ×, 100 × and 1000 ×). It was observed that the dilution of the sample of 1000 × with phosphate buffer (pH 7.0) was very advantageous for electrochemical analyses due to the lowest experimental deviations and the most reproducible results obtained. Thanks to this methodology, the voltammograms of the samples with very well defined catalytic signals of MT (Cat1, Cat2 and Cat3) were obtained. For our purposes the change of the signal Cat3 was determined. We found out that the average MT level in the non-treated earthworms oscillated between 19 and 48 μmol.l⁻¹. This variability could be associated with different metabolic activity of certain earthworms. The typical voltammograms of earthworms both exposed to cadmium ions and controls are shown in Figure 1. The curves obtained by analyzing control samples are very similar during the whole experiment, but the differences in voltammograms of earthworms exposed to seven different cadmium concentrations are well detectable [31]. The average MT level in samples of treated earthworms increased with the applied dose of cadmium(II) ions (see

Table 1. The average metallothionein level in earthworms treated by cadmium ions

Applied concentration of Cd(NO3)2(μmol.l−1)	Mean concentration of MTa,b(μmol.l−1)	Standard deviationa,b	Concentration of MTa,b Maximum Minimum (μmol.l−1)
0	31.6	10.3	48.5	19.8
5	38.0	15.0	56.1	17.9
10	39.1	13.3	52.6	13.1
20	45.4	15.5	68.2	17.8
30	48.3	16.3	64.7	20.5
40	53.3	25.1	95.6	21.9
50	53.5	26.2	99.9	21.2

^a… number of analyzed samples; n = 5

^b… sample volume (5 μl)

). The MT levels at the earthworms exposed to cadmium(II) ions varied from 17.9 to 99.9 μmol.l⁻¹. If these results have been subtracted from the control ones, the interesting experimental data were obtained. In the first day of the experiment the MT level determined in the exposed earthworms the same or even slightly lower in comparison with controls (Figure 2, column 1). This phenomenon can be associated with immediate toxicity of cadmium(II) ions, whereas the synthesis of stress proteins including MT starts. It is likely that the synthesis of MT is insufficient in the first day of the experiment. After the following 24 hours of the treatment the synthesis of MT increases markedly at all doses (Figure 2, column 2). In the conclusion, the MT level increased with increasing time of treatment at all experimental variants, which was confirmed by plotted lines (dashed line, Figure 2) with correlation coefficients (R²) from 0.79 to 0.87. Moreover, during the treatment the moderate differences in earthworm's weights with increasing concentration of cadmium ions were observed. At the highest cadmium dose (50 μmol.l⁻¹) the weight of earthworms decreased of about 10 %.

3.2 Influence of the brewery sludge and/or its leach on earthworms

Earthworms are a potentially suitable tool for biodegradation technologies of the industrial waste including sludge from waste waters. Here we were concerned with the influence of the brewery sludge on the earthworms. To compare the toxicity of the raw sludge and its leach the earthworms were used. Primarily, we determined MT concentration in the presence of brewery sludge (inset in Fig. 2). It clearly follows from the results obtained that we were able to determine MT in the presence of such complex matrix. During 14 days long experiment except the controls only earthworms kept in the leach of the sludge survived. The raw brewery sludge caused the death of the earthworms quickly. The weight of earthworms kept in the presence of leach from brewery sludge increased about 150 % of their original weight because they ingested the nutrients from the sludge. The MTs content at the earthworms kept in the presence of brewery sludge leach was 11.1 ± 0.5 μmol.l⁻¹, whereas the content of MT in control samples was 1.2 ± 0.4 μmol.l⁻¹. The obtained result indicates the markedly stress of the earthworms caused by the sludge components (both organic and inorganic).

4. Conclusion

Biotechnologies employing invertebrates are topic. Here, we report on the investigation of the ability of earthworms (Eisenia fetida) to withstand toxic environment. We observed interesting behaviour of the earthworms treated with brewery sludge leach, at which the earthworms had higher weight compared with the control ones. This phenomenon can be connected with the overproduction of MT at the treated worms.