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24-Epibrassinolide modulates primary metabolites, antioxidants, and phytochelatins in Acutodesmus obliquus exposed to lead stress

  • Marta Talarek-Karwel
  • Andrzej BajguzEmail author
  • Alicja Piotrowska-Niczyporuk
Open Access
Article

Abstract

Aquatic organisms are exposed to many stressors, e.g., heavy metals. Brassinosteroids, a plant hormone group, can effectively stimulate plants to defend against the negative impact of a heavy metal. The present study was conducted with an aim to find out the influence of 24-epibrassinolide (EBL) on Acutodesmus obliquus treated with 0.01 and 500 μM of lead (Pb) ions during 7 days of cultivation. Pb has a toxic effect on algal cultures because it limits both the growth and development and induces oxidative stress. Simultaneously, 1 μM EBL was involved in protecting algal cells against the toxic effect of Pb. Despite the presence of Pb, EBL significantly increased the number of algal cells and their metabolite content (e.g., proteins, monosaccharides, chlorophylls, carotenes, and xanthophylls). Cultures treated concurrently with EBL and Pb were characterized by a reduction in their content of endogenous Pb, H2O2, and malondialdehyde. Also, EBL increased the activity of catalase, ascorbate peroxidase, superoxide dismutase, glutathione reductase, and the content of ascorbate and glutathione. EBL increased the phytochelatin synthase activity, thereby enhancing the production of phytochelatins accountable for both binding and detoxification of Pb. These results indicate the influence of EBL on the inhibitory effect of Pb in A. obliquus. These findings help to clarify the role of BRs in the algal adaptation to the prevailing stressful conditions.

Keywords

Brassinosteroids Detoxification Green alga Chlorophyta Heavy metal 

Introduction

Various environmental factors influence the life in ecosystems, and many factors affect the modification of morphological and physiological processes in plant organisms. Heavy metals contribute to a reduction of growth, decrease in the intensity of photosynthesis and content of pigments, carbohydrates, and proline, and increase in the content of malondialdehyde (MDA) or the emergence of oxidative stress in plants (Ahmad 2016). Increased content of toxic metals in the aquatic environment affects all organisms; however, the most endangered are algae, which are the main producers of aquatic ecosystems and are a valuable part of the food chain (Zhou et al. 2011; Rajamani et al. 2014). Recently, much attention has been devoted to research on substances showing the properties of plant growth regulators. One of the phytohormone groups is brassinosteroids (BRs), which are commonly found in angiosperms, gymnosperms, algae, pteridophyte, and bryophyte at very low concentrations (Bajguz and Tretyn 2003; Stirk et al. 2013, 2014; Kanwar et al. 2017; Bajguz 2019; Zullo and Bajguz 2019). BRs significantly affect the metabolism, growth of both algae and vascular plants, and have a major role in heavy metals stress alleviation (Bajguz and Hayat 2009; Rajewska et al. 2016). BRs increase the activity of antioxidant enzymes and the content of antioxidants, protecting plants against unfavorable environmental conditions. Also, BRs significantly reduce the accumulation of heavy metals, increasing the synthesis of phytochelatins (PC) (Bajguz 2002; Behnamnia et al. 2009; Sharma et al. 2011; Arora et al. 2012).

The green alga Acutodesmus obliquus is a good model for studying the direct action of exogenous growth substances, as the reception of the hormonal, environmental stimulus and the biochemical response is not dispersed and occurs within a single cell (Bajguz and Asami 2004). Furthermore, algae—thanks to the special structure of the cell wall, consisting of a fibrous structure and a high content of bound proteins with polysaccharides—can accumulate trace metals. Metal ions bond strongly with ligands to form the structure of the cell wall (Wang and Chen 2009; Javanbakht et al. 2013; Rajewska et al. 2016). Studies carried out on Chlorella vulgaris, Chlorella kesslerii, Scenedesmus quadricauda, Scenedesmus incrassatules, and A. obliquus proved that green algae effectively remove metals from aquatic ecosystems (Gin et al. 2002; Tripathi et al. 2006; Wilde et al. 2006; Bajguz 2010; Lourie et al. 2010; Bajguz 2011; Piotrowska-Niczyporuk et al. 2015, 2017).

One of a highly active representative of BRs is 24-epibrassinolide (EBL), which is the most often subjected to plants in experiments as a growth stimulator. EBL increases the cells number and the content of pigments (chlorophylls, carotenes, and xanthophylls), monosaccharide, and protein in C. vulgaris and A. obliquus (Bajguz and Czerpak 1998; Bajguz 2000b; Talarek-Karwel et al. 2018). Moreover, previous studies confirmed the toxic effect of Pb ions on the unicellular green alga. Heavy metal application caused the inhibition of growth and development of A. obliquus, as well as initiation of oxidative stress (Piotrowska-Niczyporuk et al. 2015). Therefore, the role of EBL in the adaptation of A. obliquus to Pb stress was the main aim of this study. We tested the hypotheses that (1) EBL mitigates Pb toxicity on the algal growth and the content of pigments, protein, and monosaccharides; (2) EBL can enhance the enzymatic and non-enzymatic antioxidants level; (3) EBL involves the synthesis of PC which represent one of the mechanisms of heavy metal detoxification in plants (reduction of the endogenous level of Pb).

Materials and methods

Algal cultivation

Acutodesmus obliquus (SAG 276-6) synchronous growth was established by the Prison and Lorenzen (1966) method. Algae were cultivated in 250-mL Erlenmeyer flasks with 100 mL of Bold Basal Medium (Andersen 2005; Andersen et al. 2005) at 25 ± 0.5 °C. Fluorescent lights (photon flux 50 μmol photons m−2 s−1 at the surface of the tubes) were used as illumination for 16 h. Algal cultures, initiated at 1.5 × 106 cells mL−1, were bubbled with air at 1 L min−1.

Previous research confirmed that the most stimulating impact of EBL (Sigma-Aldrich, USA) occurred at a concentration of 1 μM after the application of six different EBL concentrations from 0.0001 to 10 μM (with a multiplier of 10) on A. obliquus (Talarek-Karwel et al. 2018). Hence, 1 μM EBL was chosen in this experiment. The response of Pb action on A. obliquus cultures was presented in Piotrowska-Niczyporuk et al. (2015, 2017). Thus, Pb at the concentrations of 0.01 and 500 μM was used. Furthermore, this study shows the combined effect of EBL and Pb in A. obliquus cultures.

Data acquisition and analytical methods

Selected parameters were measured on the 1st, 3rd, 5th and 7th days of the cultivation. The algal cultures were collected by centrifugation (9000×g, 10 min; MPW-350R Med. Instruments, Poland) for biochemical analysis.

Number of cells

The cells number was counted under the Olympus CX-23 microscope using the Bürker counting chamber (Blaubrand, Germany) (Gunetti et al. 2012).

Determination of monosaccharide content

The content of monosaccharides was determined using Somogyi (1952) method. Algal pellets were homogenized in 2 mL of ethanol at 75 °C in bead mill (50 Hz, 5 min; TissueLyser LT, Qiagen, Germany) using two 5-mm zirconium balls and then centrifuged (9000×g, 10 min). After drying the supernatant, the residue was resuspended in 1 mL of water and desalted through a column of ion-exchange resin (Amberlite MB3). Samples were mixed with 50 μL of 0.1 M potassium ferricyanide and then 100 μL of reagent A [0.1 M NaOH, 0.1 N Na2CO3; 1:1 (v/v)] was added followed by water to 1000 μL. Then, the mixtures were heated (10 min, 95 °C) and cooled to 20 °C. The addition of reagent B (1 mL) [0.015 M o-phenanthroline, 0.1 M acetic acid; 1:1 (v/v)] and water (0.5 mL) was followed by mixing and heating the content of the tubes (10 min, 95 °C). The absorbance values were measured at 505 nm, after cooling to 20 °C.

Determination of pigment content

Algal pellets were homogenized in 1 mL of methanol (MeOH) in bead mill (50 Hz, 5 min) then centrifuged (9000×g, 10 min). Supernatants were filtered through 0.45 μm, PTFE, HPLC syringe cartridge filters fitted with glass fiber prefilters (A&A Biotechnology, Poland). An Agilent 1260 Infinity Series HPLC system with Eclipse XDB C8 column (150 mm × 4.6 mm, 5 μm), maintained at 25 °C, was used. The inlet method was set as follows: mobile phase A, MeOH/acetonitrile (ACN)/0.25 M aqueous pyridine (pH 5.0) solution (50/25/25, v/v/v) and B, MeOH/ACN/acetone (20/60/20, v/v/v). The gradient was linear from the specified initial percent solvent A (100% in the 1st min, 60% from the 22nd min, 5% from the 28th min, 5% from the 38th min, 100% in the 40th min). Flow rates were adjusted to keep back pressure below 180 bar (1 mL min−1) (Zapata et al. 2000). For the analytical data integration, ChemStation software was used.

Determination of lead content

Heavy metal level was determined by flame atomic absorption spectrometry using a Solaar M6 (Thermo Electron Corporation, UK) spectrometer with deuterium background correction system. Initially, algal cultures were centrifuged (9000g, 10 min) and the suspension was dried (105 °C, 6 h). Then, samples were mineralized in 200 μL of 65% nitric acid. Finally, the absorbance was measured in air-acetylene flame with 0.5 nm spectral bandpass at 217 nm (Piotrowska-Niczyporuk et al. 2015).

Determination of H2O2 and malondialdehyde contents

To determine H2O2 and MDA, algal pellets were homogenized in 1 mL of 5% (w/v) trichloroacetic acid in bead mill (50 Hz, 5 min). Then, the homogenates were centrifuged (9000g, 15 min, 3 °C). To measure H2O2 level, supernatant was mixed with reaction mixture (2.5 mM potassium phosphate buffer [pH 7.0] and 500 mM potassium iodide), and the absorbance was measured at 390 nm (Velikova et al. 2000). For determination of MDA, supernatant mixed with reaction mixture [0.5% (w/v) thiobarbituric acid (TBA) in 20% TCA] was incubated (95 °C, 20 min), then a reaction was terminated by placing vials on ice. Absorbance was measured at 532 nm. The nonspecific absorption at 600 nm was subtracted from the absorbance data. The amount of MDA-TBA complex was calculated using the extinction coefficient equal 155 mM−1 cm−1 (Cakmak and Horst 1991).

Determination of protein and antioxidant levels

For estimation of the content of protein and the activities of antioxidant enzymes, algal pellets were homogenized in 50 mM phosphate buffer (pH 7.0), 1 mM ethylenediaminetetraacetic acid (EDTA), 1 mM phenylmethanesulfonylfluoride, 0.5% (v/v) Triton X-100, and 2% (w/v) polyvinylpyrrolidone (PVP)-30 in bead mill (50 Hz, 5 min). For ascorbate peroxidase determination, 0.5 mM ascorbate was added to the extraction buffer. Then, the homogenate was centrifuged (9000×g, 15 min, 3 °C). The supernatant was further used for quantitative analysis of antioxidant enzymes and protein.

The protein content was estimated following the Bradford (1976) method using bovine serum albumin as a standard. Supernatant (100 μL) and 3 mL of the Bradford reagent [0.01% (w/v) Coomassie Brilliant Blue G-250, 4.7% (w/v) ethanol, 8.5% (w/v) H3PO4] were transferred to assay tube. Then, the absorbance at 595 nm was measured after 5 min and before 1 h to check the stability of the protein dye complex.

The activity of ascorbate peroxidase (APX) was measured according to Nakano and Asada (1981) method by monitoring the rate of absorbance at 290 nm using the extinction coefficient equal 2.8 mM−1 cm−1. The 3 mL reaction mixture contained 50 mM potassium phosphate buffer (pH 7.0), 0.5 mM ascorbate, 1 mM H2O2, and 100 μL enzyme extract (3 min, 25 °C). The enzyme activity was estimated as the amount of enzyme that oxidizes 1 μM of ascorbate consumed per milligram of soluble protein per minute.

The activity of sodium dismutase (SOD) was tested by registering the inhibition of photochemical reduction of nitroblue tetrazolium (NBT) at 560 nm. For total SOD assay, 3 mL reaction mixture contained 50 mM sodium carbonate (pH 10.2), 24 μM NBT, 0.1 mM EDTA, 1 mM hydroxylamine, 0.03% (v/v) Triton X-100, and 70 μL enzyme extract. The amount causing 50% inhibition of the photochemical reduction of NBT was assumed as one unit of SOD per milligram protein (Beauchamp and Fridovich 1971).

Method of Aebi (1984) was used for determination of the activity of catalase (CAT) by monitoring the rate of absorbance of H2O2 at 240 nm for 0.5 min at 25 °C. The 3 mL reaction mixture contained 50 mM potassium phosphate buffer (pH 7.0), 15 mM H2O2, and 100 μL enzyme extract. One unit of CAT activity was defined as the amount of enzyme that decomposes 1 μM of H2O2 per milligram of soluble protein per minute.

The activity of glutathione reductase (GR) was determined following the procedure of Schaedle and Bassham (1977). The 3 mL reaction mixture contained 50 mM potassium phosphate buffer (pH 7.6), 1 mM oxidized glutathione, 0.5 mM EDTA, 0.1 mM reduced NADPH, and 100 μL enzyme extract. The reaction was started using 0.1 mM NADPH at 25 °C. The GR activity was defined from the rate of NADPH oxidation as measured by the decrease of absorbance at 340 nm (the extinction coefficient equal 6.2 mM−1 cm−1).

Determination of total ascorbate was tested by Kampfenkel et al. (1995) method. Algal pellets were homogenized in 2 mL 5% (w/v) TCA in bead mill (50 Hz, 5 min) and then centrifuged (9000×g, 10 min). The supernatant was transferred to a reaction mixture [10 mM DTT, 0.2 M phosphate buffer (pH 7.4), 0.5% N-ethylmaleimide, 10% TCA, 42% H3PO4, 4% 2,2′-bipyridyl and 3% FeCl3]. After shaking, a mixture was incubated (40 min, 42 °C) and the absorbance value was recorded at 525 nm.

Determination of glutathione and phytochelatin levels

For determination of GSH and different types of PC, HPLC analysis according to procedure of Le Faucheur et al. (2006) and Scheidegger et al. (2011) was used. The algal cultures were collected by centrifugation (9000×g, 10 min) and samples were homogenized with 0.1% trifluoroacetic acid (w/v) with 6.3 mM diethylenetriaminepentaacetic acid in bead mill (50 Hz, 5 min), after centrifugation supernatant and derivatized (30 min, 45 °C, dark) using monobromobimane (mBBr). HPLC analysis was performed using an Agilent Technologies 1260 Infinity series system consisting of the 1260 Infinity Agilent Quaternary pump G1311B, 1260 Infinity Fluorescence Detector G1321B, 1260 Infinity ALS G1329B Automated Sample Injector, 1290 Infinity Autosampler Thermostat G1330B, and a thermostatted column oven 1290 Infinity TCC G1316C. The system was controlled by Agilent OpenLab ChemStation software. Glutathione (GSH) and PC were separated with a Cosmosil Packed Column C18-MS-II (4.6 μm × 250 mm, 5 μm) and kept at 37 °C with a column oven. Samples (25 μL) were injected and run in a gradient: 0–15 min, 12–25% (v/v) MeOH; 15–29 min, 25–35% (v/v) MeOH; 29–50 min, 35–50% (v/v) MeOH. The column was then cleaned with 100% (v/v) MeOH and reequilibrated in 12% (v/v) MeOH. Excitation wavelength was 380 nm; emission wavelength was 470 nm. The retention time of GSH and PC was verified by their standards (AnaSpec, EGT Corporate, USA). To estimate the content of GSH and PC, a calibration curve (standards vs. resulting peak area) was prepared.

Determination of phytochelatin synthase activity

The activity of phytochelatin synthase (PCS) was determined by Finkemeier et al. (2003) method. Hence, 50 mL of algal culture was centrifuged (9000×g, 10 min) and extracted in 2 mL of buffer containing 20 mM HEPES-NaOH, pH 7.5, 10 mM β-mercaptoethanol, 100 μM CdSO4, 20% (w/v) glycerol, and 100 mg mL−1 PVP using bead mill (50 Hz, 5 min). After centrifugation (9000×g, 10 min), the sample contained 400 μL extract and 100 μL reaction buffer (25 mM GSH, 100 μM CdSO4, 10% (w/v) glycerol, 250 mM HEPES-NaOH, and pH 8.0) and protease inhibitor mix “Complete” (Sigma-Aldrich) was incubated (90 min, 35 °C). Reaction was stopped by addition of 125 μL 20% (w/v) TCA. After derivatization with mBBr, PCS activity was measured using HPLC method as described above for PC determination.

Statistics

All experiments were repeated five times (n = 5). The R language (R Core Team 2019) was used to perform the statistical analysis of the results, which were preliminarily described as mean ± standard deviation. The data were tested (α = 0.05) for normality [Shapiro-Wilk test – “stats” package (R Core Team 2019)] and homogeneity of variances [Levene’s test – “car” package (Fox and Weisberg 2011)]. One-way ANOVA (“stats” package) followed by the Scott-Knott’s post-hoc test [“laercio” package (da Silva 2010)] was applied to check the existence of statistically significant differences between means (p < 0.05). The data were visualized as plots with the help of “ggplot2” package.

Results

The number of cells and the content of protein and monosaccharides

Among the tested conditions, applying 1 μM EBL alone had the most stimulating effect on the number of A. obliquus cells, as well as on the protein and monosaccharides content (Fig. 1a, c, d). Exposure to 0.01 μM Pb did not cause changes in the number of cells and the content of the studied A. obliquus metabolites. The inhibition of growth and a reduction in the content of all the above parameters was detected in A. obliquus cultures exposed to 500 μM Pb. EBL alleviated the toxic effect of Pb. The biggest (80–90%) raise was reported on the 5th day of cultivation relative to the Pb alone, after the application of 1 μM EBL and the lower concentration of Pb (0.01 μM). In the presence of the highest Pb concentration (500 μM) mixed with EBL, a slight increase was observed for the number of cells (by 10–40%), protein level (9–54%), and monosaccharides level (10–40%) relative to the 500 μM Pb exposure. However, the level of these metabolites was lower than in the control condition. Moreover, the growth and level of studied A. obliquus metabolites increased together with the increase in the exposure time to EBL and/or Pb reaching the maximum on the 5th day of cultivation, except for 500 μM Pb and 500 μM Pb mixed with 1 μM EBL. A minor decrease in the parameters with respect to the 5th day was noted on the last day.
Fig. 1

The effect of lead and/or 24-epibrassinolide (EBL) on the number of cells (a) and the content of endogenous lead (b), protein (c), and monosaccharides (d) in Acutodesmus obliquus. Bars show the mean (n = 5) with standard deviation. Means with the same letters are not significantly different (p ≥ 0.05) according to Scott-Knott’s post-hoc test. Data were grouped by the day of cultivation and treatment for each pigment

The content of lead

As shown in Fig. 1 b, the intracellular Pb level in green alga was associated with the concentration of heavy metal, and this increased proportionally with increasing time of exposure. Algae exposed to 500 μM Pb on the last day exhibited the highest metal ion accumulation; however, the addition of EBL resulted in a decline in the metal accumulation by 15–44% in relation to Pb alone. On the other hand, the content of Pb was similar to the control during the whole period of cultivation under the influence of EBL and/or 0.01 μM Pb.

The content of photosynthetic pigments

The influence of 1 μM EBL on the level of chlorophyll a and b, carotenes (α-carotene and β-carotene), oxygen-poor xanthophylls (zeaxanthin, lutein, cryptoxanthin), and oxygen-rich xanthophylls (neoxanthin, violaxanthin, astaxanthin) was examined after treatment with 0.01 and 500 μM Pb (Table 1). In cultures treated with Pb, a remarkable loss in photosynthetic pigments content was reported. The highest inhibitory effect of Pb was observed at a concentration of 500 μM. In contrast, 0.01 μM Pb had a similar effect on the pigment content in A. obliquus cells compared with the control. The reduction of the studied photosynthetic pigments in algae treated with Pb was ameliorated by the addition of 1 μM EBL. The maximum increase of selected pigments was 72% for chlorophyll a, 52% for chlorophyll b, 24% for β-carotene, 61% for neoxanthin, 19% for astaxanthin, and 88% for zeaxanthin on the 5th day under 0.01 μM Pb and 1 μM EBL relative to 0.01 μM Pb alone. In turn, the greatest shares of EBL on the enhancement in the violaxanthin, lutein, and cryptoxanthin content was reported (84%, 68%, 117%, respectively) in alga treated with 500 μM Pb and 1 μM EBL on the 5th day with respect to the 500 μM Pb, except for α-carotene, where the maximum increase was noticed on the 7th day. Among all tested combinations, exposure to EBL alone caused the greatest increase in photosynthetic pigments content.
Table 1

The effect of lead and/or 24-epibrassinolide (EBL) on the content of pigments (fg cell−1) in Acutodesmus obliquus. Data represent the mean (n = 5) ± standard deviation. Means with the same letters are not significantly different (p ≥ 0.05) according to Scott-Knott’s post-hoc test. Data were grouped by the day of cultivation and treatment for each pigment

Day of cultivation

Treatment

Chlorophyll a

Chlorophyll b

α-carotene

β-carotene

Neoxanthin

Violaxanthin

Astaxanthin

Lutein

Zeaxanthin

Cryptoxanthin

1st

0

67.59 ± 2.96H

20.36 ± 1.57K

3.54 ± 0.10I

5.58 ± 0.51H

8.52 ± 0.65I

3.39 ± 0.21H

1.54 ± 0.08H

1.66 ± 0.15J

11.21 ± 0.82H

5.23 ± 0.34K

0.01 μM Pb

67.15 ± 2.06H

19.66 ± 0.45K

3.48 ± 0.11I

5.63 ± 0.20H

8.57 ± 0.24I

3.19 ± 0.10I

1.50 ± 0.05H

1.58 ± 0.06J

11.41 ± 0.45H

5.04 ± 0.14K

500 μM Pb

58.58 ± 1.42I

14.13 ± 0.53M

3.02 ± 0.12J

5.66 ± 0.20H

5.27 ± 0.18L

2.07 ± 0.04K

1.08 ± 0.04J

1.21 ± 0.04K

8.25 ± 0.29J

4.42 ± 0.23L

1 μM EBL

109.10 ± 2.98D

31.56 ± 1.78F

4.02 ± 0.13G

6.74 ± 0.17E

12.01 ± 0.34F

4.66 ± 0.19E

2.03 ± 0.10G

2.54 ± 0.15G

18.17 ± 0.74E

8.11 ± 0.51G

0.01 μM Pb + 1 μM EBL

80.35 ± 2.45F

27.27 ± 0.67G

3.58 ± 0.05I

5.62 ± 0.11H

9.45 ± 0.24H

3.64 ± 0.15H

1.59 ± 0.04H

1.69 ± 0.09J

12.46 ± 0.50G

5.88 ± 0.41J

500 μM Pb + 1 μM EBL

65.53 ± 1.59H

17.90 ± 0.45L

3.53 ± 0.13I

5.63 ± 0.16H

8.07 ± 0.63J

3.02 ± 0.11I

0.52 ± 0.05L

1.63 ± 0.11J

11.13 ± 0.47H

5.46 ± 0.43K

3rd

0

70.19 ± 3.83G

22.32 ± 1.57J

4.15 ± 0.14G

6.10 ± 0.34G

9.13 ± 0.58I

4.03 ± 0.22G

2.16 ± 0.08G

2.49 ± 0.26G

12.16 ± 0.94G

6.19 ± 0.41J

0.01 μM Pb

70.46 ± 3.18G

21.34 ± 0.34J

3.87 ± 0.22H

6.15 ± 0.25G

9.49 ± 0.24H

3.86 ± 0.16G

2.05 ± 0.06G

2.28 ± 0.09H

11.65 ± 0.62H

5.88 ± 0.18J

500 μM Pb

66.77 ± 3.42H

17.34 ± 0.56L

3.81 ± 0.23H

6.15 ± 0.31G

6.23 ± 0.39K

2.57 ± 0.12J

1.55 ± 0.08H

1.88 ± 0.14I

10.01 ± 0.37I

5.06 ± 0.27K

1 μM EBL

122.38 ± 4.54C

37.56 ± 1.44D

5.04 ± 0.16D

7.94 ± 0.29C

15.32 ± 0.79C

6.54 ± 0.27C

3.33 ± 0.09C

4.43 ± 0.29D

23.03 ± 1.30C

11.07 ± 0.47D

0.01 μM Pb + 1 μM EBL

93.73 ± 2.32E

30.31 ± 1.26F

4.51 ± 0.04F

6.94 ± 0.18E

12.76 ± 0.37E

4.51 ± 0.18E

2.38 ± 0.14F

3.35 ± 0.11F

18.93 ± 0.67E

7.74 ± 0.65G

500 μM Pb + 1 μM EBL

66.35 ± 2.48H

21.17 ± 0.67J

4.37 ± 0.10F

6.94 ± 0.26E

8.85 ± 0.23I

3.66 ± 0.27H

0.75 ± 0.10K

2.33 ± 0.18H

13.39 ± 0.69G

8.69 ± 0.33F

5th

0

73.33 ± 2.69G

24.95 ± 0.83H

4.94 ± 0.50D

6.94 ± 0.33E

9.94 ± 0.84H

4.84 ± 0.17E

2.94 ± 0.28D

3.32 ± 0.36F

12.89 ± 1.12G

7.03 ± 0.51H

0.01 μM Pb

73.13 ± 2.61G

25.91 ± 1.10H

4.77 ± 0.19E

6.63 ± 0.20F

10.55 ± 0.53G

4.66 ± 0.18E

2.71 ± 0.18E

3.36 ± 0.16F

12.33 ± 0.52G

6.74 ± 0.32I

500 μM Pb

65.53 ± 1.91H

18.70 ± 0.56K

4.43 ± 0.23F

7.21 ± 0.11D

7.60 ± 0.37J

2.59 ± 0.12J

1.90 ± 0.06G

1.96 ± 0.09I

10.85 ± 0.33H

5.19 ± 0.18K

1 μM EBL

140.28 ± 3.20A

48.53 ± 1.76A

6.64 ± 0.17A

9.66 ± 0.39A

20.04 ± 0.87A

9.01 ± 0.43A

5.18 ± 0.34A

7.16 ± 0.46A

29.60 ± 1.28A

15.34 ± 0.88A

0.01 μM Pb + 1 μM EBL

125.68 ± 3.11C

39.43 ± 0.78C

5.43 ± 0.15C

8.25 ± 0.16B

16.96 ± 0.32B

6.35 ± 0.24C

3.23 ± 0.08C

5.06 ± 0.20C

23.13 ± 0.61C

12.20 ± 0.65C

500 μM Pb + 1 μM EBL

68.73 ± 4.01H

22.31 ± 0.38J

5.23 ± 0.09C

8.43 ± 0.08B

10.84 ± 0.44G

4.76 ± 0.24E

1.58 ± 0.09H

3.29 ± 0.18F

17.51 ± 0.63E

11.27 ± 0.59D

7th

0

71.18 ± 3.05G

23.33 ± 1.11I

4.58 ± 0.26F

6.45 ± 0.17F

9.40 ± 0.51H

4.41 ± 0.23F

2.43 ± 0.12F

2.81 ± 0.31G

12.38 ± 1.82G

6.53 ± 0.44I

0.01 μM Pb

70.25 ± 4.49G

23.49 ± 0.74I

4.53 ± 0.20F

6.08 ± 0.43G

10.16 ± 0.33G

4.02 ± 0.22G

2.40 ± 0.10F

2.59 ± 0.10G

11.72 ± 0.65H

6.01 ± 0.25J

500 μM Pb

59.24 ± 2.16I

17.52 ± 1.40L

3.68 ± 0.15I

6.81 ± 0.41E

7.51 ± 0.20J

3.21 ± 0.11I

1.41 ± 0.04H

1.89 ± 0.04I

9.80 ± 0.26I

4.59 ± 0.18L

1 μM EBL

129.90 ± 3.97B

41.38 ± 1.08B

5.91 ± 0.21B

8.57 ± 0.24B

17.09 ± 0.76B

7.61 ± 0.24B

3.95 ± 0.27B

5.42 ± 0.26B

25.83 ± 1.72B

12.97 ± 0.68B

0.01 μM Pb + 1 μM EBL

108.43 ± 3.08D

35.12 ± 0.90E

4.82 ± 0.13E

7.22 ± 0.10D

13.96 ± 0.76D

5.19 ± 0.45D

2.64 ± 0.07E

3.88 ± 0.21E

21.59 ± 0.50D

10.48 ± 0.66E

500 μM Pb + 1 μM EBL

61.93 ± 2.03I

19.28 ± 0.44K

4.74 ± 0.10E

7.34 ± 0.26D

9.76 ± 0.18H

4.25 ± 0.34F

1.18 ± 0.05I

2.73 ± 0.28G

15.50 ± 0.60F

9.02 ± 0.61F

The content of H2O2 and malondialdehyde

Pb at the concentrations of 0.01 and 500 μM produced an increase in oxidative stress in A. obliquus cells (Fig. 2a, b), due to the noticeably high H2O2 and accelerated lipid peroxidation process (expressed as a level of MDA) related with the rise in the metal concentration. The application of 1 μM EBL limited the H2O2 level and MDA content after the application of Pb. The biggest reduction in H2O2 (by 60%) and MDA (by 61%) contents by EBL were recorded under 0.01 μM Pb on the 5th day, relative to the 0.01 μM Pb alone. EBL minimized the level of these compounds at 500 μM Pb to a lesser extent. The content of H2O2 and MDA was smaller (by 20%) than in the A. obliquus treated only with 500 μM Pb, but higher than in control by 29% and 37%, respectively.
Fig. 2

The effect of lead and/or 24-epibrassinolide (EBL) on the content of H2O2 (a), malondialdehyde (MDA, b), the activity of ascorbate peroxidase (APX, c), ascorbate content (d), the activity of superoxide dismutase (SOD, e) and catalase (CAT, f) in Acutodesmus obliquus. Bars show the mean (n = 5) with standard deviation. Means with the same letters are not significantly different (p ≥ 0.05) according to Scott-Knott’s post-hoc test. Data were grouped by the day of cultivation and treatment for each pigment

The level of antioxidants

Under 0.01 μM Pb exposure, a slight increase in the activity of antioxidants in algal cultures, especially on the 5th day of the experiment, was observed (Figs. 2c–f and Fig. 5a). In turn, the activity of the antioxidant system was limited after the application of 500 μM Pb. EBL greatly stimulated the level of antioxidants. In the case of 1 μM EBL, we detected a greater than twofold increase in ascorbate content and CAT and APX activities, as well as a doubling in SOD activity. However, hormone alone had a smaller impact on GR activity and GSH content. EBL mixed with 0.01 μM Pb was found to have a remarkable stimulating effect on the antioxidant system. On the 5th day, the activity of SOD, APX, CAT, and GR, and the content of ascorbate and GSH increased by 70, 80, 75, 80, 89, and 72%, respectively, compared with the heavy metal alone. The application of 500 μM Pb caused a major reduction of the antioxidants level; however, co-application of EBL did not lead to any improvement. Treatment of the A. obliquus cultures with 500 μM Pb and EBL was associated with reduced GSH content. However, the stimulation of the GSH content by 20–35% in algal cultures in relation to the control was noticed during the whole study under the highest Pb concentration.

The content of phytochelatin

Treatment of A. obliquus cells with Pb and/or EBL affects PC2, PC3, PC4, and PC5 synthesis (Fig. 3a–d). The highest PC2-5 level was detected under 1 μM EBL exposure, and the lowest after application of 0.01 μM Pb, but 500 μM Pb caused the inhibition of PC2-5 synthesis. The level of PC2 and PC3 in algal cells increased until the third day, and then the content of both peptides reduced gradually. On the 3rd day of cultivation, the highest content of PC2 and PC3 (fourfold rise) was recorded in cultures grown in the presence of 1 μM EBL and Pb. In the case of longer oligomers of PC, the highest content of PC4 and PC5 (an almost fourfold increase compared with the control group) was noted in cells exposed to 1 μM EBL and Pb on the last day. Under heavy metal exposure, a significant impact on PC synthesis was also observed. After the application of 0.01 μM Pb, the content of PC2 tripled on the 5th day and PC4 on the 7th day. Moreover, under the above conditions, the content of PC3 and PC5 doubled on the 3th and 7th days, respectively. The weakest effect on the PC2-5 content was noted in the whole period of the experiment when the highest concentration of Pb (500 μM) was used. During 7 days of cultivation, PC2 had the highest share among PC (74–89%) (Fig. 4). The percentage shares of PC3, PC4, and PC5 were 7–17%, 3–9%, and 1–9%, respectively.
Fig. 3

The effect of lead and/or 24-epibrassinolide (EBL) on the content of phytochelatins (PC2, a; PC3, b; PC4, c; PC5, d) and the activity of phytochelatins synthase (PCS, e) in Acutodesmus. Bars show the mean (n = 5) with standard deviation. Means with the same letters are not significantly different (p ≥ 0.05) according to Scott-Knott’s post-hoc test. Data were grouped by the day of cultivation and treatment for each pigment

Fig. 4

Percentage share of phytochelatins in Acutodesmus obliquus treated with lead and 24-epibrassinolide (EBL)

The activity of phytochelatin synthase

The effect of 1 μM EBL and 0.01 μM or 500 μM Pb on the activity of PCS in A. obliquus cultures was examined (Fig. 3e). The stimulating effect of BR on the enzyme activity was observed from the 1st to 7th days and peaked on the 5th day in Pb-treated cultures. Algae treated with Pb alone showed a weaker PCS activity increase than in cultures treated with EBL and Pb. The highest, almost sixfold increase in the activity of PCS in A. obliquus cells, relative to the control, was exerted at a concentration of 1 μM EBL and Pb. Application of 0.01 μM and 500 μM Pb produced a fourfold and doubling in the PCS activity, respectively, relative to untreated algae. The present study shows that both EBL and Pb had a large influence on the enzyme activity during PC synthesis.

Discussion

The obtained results suggest that the biosorption of Pb by A. obliquus is associated with a variety of biochemical changes that contribute to heavy metal tolerance. Pb caused an inhibition of algal growth (Fig. 1a) and decrease in the content of pigments (Table 1), protein (Fig. 1c), and monosaccharides (Fig. 1d). In addition, a stimulating effect of Pb in the formation of H2O2, together with increased lipid peroxidation, was observed (Fig. 2a, b), thereby demonstrating the influence of metal on the initiation of oxidative stress. Pb at low concentration (0.01 μM) increased the level of antioxidants (Figs. 2 and 5). Dao and Beardall (2016) confirmed that Scenedesmus sp. was very sensitive to 0.03–0.87 nM Pb with a continuous decline in growth rate. On the other hand, a lethal effect of Pb on C. vulgaris was observed at 1 mM Pb (Bajguz 2000a). Cao et al. (2015) demonstrated that 2.4–4.8 μM Pb accelerated the growth of Cladophora, while Pb up to 48 μM inhibited their growth. Moreover, photosynthesis was limited under heavy metal stress. The outcomes of the correlation analysis showed that the Pb content in Cladophora was significantly correlated with growth and peroxidase (POD), MDA, and metallothionein levels.
Fig. 5

The effect of lead and/or 24-epibrassinolide (EBL) on the activity of glutathione reductase (GR, a) and the content of glutathione (GSH, b) in Acutodesmus obliquus. Bars show the mean (n = 5) with standard deviation. Means with the same letters are not significantly different (p ≥ 0.05) according to Scott-Knott’s post-hoc test. Data were grouped by the day of cultivation and treatment for each pigment

In adverse environmental conditions, plants activate different defense strategies against heavy metals, e.g., by regulation of antioxidants system and the synthesis of PCs. BRs can regulate many aspects of growth and responses to stresses (Krishna 2003; Bajguz and Hayat 2009; Rajewska et al. 2016). BRs have an anti-stress effect on C. vulgaris exposed to heavy metals (Bajguz 2000a, 2002, 2010, 2011). The present study revealed the considerable impact of 1 μM EBL in the decrease in the level of Pb in response to metal treatments in A. obliquus culture. The largest effect of EBL in decreasing accumulate of Pb was observed after the application of 0.01 μM Pb (Fig. 1b). Previous studies described a notable decline in the copper (Cu), cadmium (Cd), and Pb accumulation in C. vulgaris cultures treated with exogenous BR (Bajguz 2000a, 2002, 2010, 2011). In the case of higher plants, such as tomato, barley, spring wheat, mustard, and radish, application of EBL also significantly reduced the metal absorption by more than 50% lower relative to the control condition in sugar beet roots (Khripach et al. 2000; Kroutil et al. 2010; Bajguz 2011; Kanwar et al. 2012). Growth inhibition was associated with the concentration of heavy metal in algal cell and the number of metal ions bound to the cell surface and intracellular metal ions, as well as to the chemical character of the metal (Tripathi et al. 2006; Polonini et al. 2015). In our experiment, Pb toxicity resulted in a decrease of A. obliquus growth, which was restored by the application of EBL (Fig. 1a). Similarly, Bajguz (2010) showed that the application of BL improved the growth of C. vulgaris cultures treated with heavy metals. Other studies have confirmed that growth suppression of mustard (Brassica juncea) treated with nickel (Ni) (Alam et al. 2007; Ali et al. 2008b; Kanwar et al. 2012), aluminum (Al) in mungbean (Vigna radiata) (Ali et al. 2008a), as well as Cd in chickpea (Cicer arietinum) (Hasan et al. 2008) and radish (Raphanus sativus) (Anuradha and Rao 2007), was restored by exogenous BR. The favorable role of BRs in the regulation of plant growth in the presence of metal has been reported by many researchers. It suggests that the relationship between phytohormones and metal might be used as a defense mechanism against heavy metal toxicity.

Proteins are crucial markers of irreversible and reversible changes in plant metabolism (Singh et al. 2006). Pb excess in A. obliquus caused the inability of cells to accumulate proteins. However, this study indicates that the addition of EBL might be useful to induce the biosynthesis of protein (Fig. 1c). The co-application of EBL and Pb led to a greater amount of protein (almost double increase) than the action of Pb alone. Bajguz (2011) also indicated that the inhibitory effect of Cu, Pb, and Cd on the protein content in C. vulgaris cells was suppressed by EBL. In the case of higher plants, Choudhary et al. (2012) found that the application of 1 μM EBL to chromium (Cr) stressed radish seedlings increased the content of protein in comparison to plant treated with Cr alone. Solanum lycopersicum treated with EBL showed a greater protein content than the control despite the presence Ni stress (Nazir et al. 2019). Zhou et al. (2018) showed that the content of protein significantly increased after the application of EBL in grape (Vitis vinifera) under Cu stress. Hence, the declining content of protein in algal cells and higher plants treated with Pb can be restored by applying EBL, which increases the chances of plant survival in ecosystems polluted with heavy metals.

Couée et al. (2006) presented the theory that soluble sugars can play a double role with regard to reactive oxygen species (ROS) by engaging or relating to ROS-producing metabolic pathways. On the other hand, soluble sugars could also boost NADPH-producing metabolic pathways, for example the oxidative pentose-phosphate pathway, which can cooperate with ROS scavenging. Our research confirmed the stimulating impact of EBL on the monosaccharide content in A. obliquus treated with Pb (Fig. 1d). We also noted a rise in the content of this parameter (by 10–80%) when treated with EBL plus Pb mix, relative to Pb alone. Bajguz (2011) reported that heavy metals (Cu, Cd, and Pb) biosorption is negatively correlated with monosaccharides contents in C. vulgaris cultures treated with BL. In the case of two wheat Triticum aestivum cultivars (LOK-1 and 502), the application of EBL enhanced the sugar content. Moreover, the maximum rise in the content of sugar was detected in the plants treated with the combination of Al and salt stress and sprayed with EBL in LOK-1 (Yusuf et al. 2017).

The Pb-induced cellular damage in microalgal cells could be monitored by the decrease in the chlorophylls content. The high concentration of heavy metal might limit biosynthesis of pigment and enzymes that are involved in this process (Bajguz 2011; Piotrowska-Niczyporuk et al. 2015). The decrease in pigment content in algae under metal stress might also be caused by peroxidation of chloroplast membranes through the intensification of ROS production (Bajguz 2011). Our results demonstrate that the reduction of chlorophylls content in A. obliquus treated with Pb was prevented by EBL (Table 1). The combination of EBL and Pb showed a significant increase in the content of chlorophylls in the algal cells when compared with Pb treatment alone. According to Bajguz (2011), an increase of the chlorophyll content was noted in the C. vulgaris cultures exposed to EBL mixed with Cu, Pb or Cd. Wu et al. (2019) confirmed that antimony (Sb) exposure (50 μM) led to a marked decrease in the content of chlorophylls in Arabidopsis thaliana leaves but exogenous 0.01 μM EBL application strongly alleviated this adverse effect. Similar stimulating effects of EBL were reported by Guo et al. (2018), who showed that EBL increases the content of chlorophylls a and b in Cd stressed tomato plants. Additionally, Yusuf et al. (2016) also presented that SPAD chlorophyll has been significantly enhanced in the presence of EBL under Cu stress or stress-free conditions, whereas Cu alone lowered the chlorophyll content in the mustard plant. On the other hand, under iron deficiency in Eucalyptus urophylla plants, 100 nM EBL effectively increased chlorophylls a and b, and total chlorophylls contents and chlorophyll fluorescence (Lima et al. 2018).

The carotenes and xanthophylls can free radical quenching and might protect the photosynthetic apparatus against oxidative stress, for example, by heavy metals (Janik et al. 2010; Lavoie et al. 2016). Hence, the increased accumulation of carotenes observed in A. obliquus exposed to Pb can explain the oxidative stress enhancement. Furthermore, these experiments confirmed the contribution of EBL to the increased resistance to carotenes degradation in algal treated with Pb (Table 1). A substantial rise in the content of xanthophylls (by 19–117%) was detected, after application of EBL with Pb. Similarly, an increase of 20% in total carotenoids content was also observed by Lin et al. (2018) in C. vulgaris cultures treated with 1 μM EBL. Other studies show that EBL increased the pigment levels, i.e., chlorophyll a (83%), chlorophyll b (68%), and carotenoids (61%) in Cr-stressed radish seedlings (Choudhary et al. 2012).

A diversity of ROS is generated as an answer of plants to metal stress. Exposure to Pb accelerated the ROS production, including H2O2, hence unbalancing the cellular redox status in A. obliquus. ROS react with cellular components (lipids, nucleic acids, proteins, and pigments) to cause lipid peroxidation, enzyme inactivation, and membrane damage (Ahmad 2016; Maia et al. 2018). MDA level is used as an index of lipid peroxidation because it is an indicator of free radical formation in the tissues exposed to adverse environmental conditions (Cuypers et al. 2016). The present study showed that the application of EBL decreased the level of MDA and H2O2 content by about 20–60% in Pb-stressed A. obliquus cells, relative to cultures treated with heavy metal alone (Fig. 2a, b). It was shown that microalgae exposed to EBL exhibited higher membrane stability index and reduced peroxidation of membrane lipid, and also a decrease in ROS content. Similarly, the application of EBL reduces the level of MDA and H2O2 in Ni-stressed Solanum nigrum seedlings (Soares et al. 2016). In the presence of EBL, the level of oxidative radicals was reduced in Solanum lycopersicum growing under Ni stress (Nazir et al. 2019). According to Wu et al. (2019), foliar application of 0.01 μM EBL induced a slight decline in the content of MDA (by 15%) in A. thaliana under 50-μM Sb stress relative to the control. However, in relation to seedlings treated by Sb alone, the level of H2O2 increased (by 27%) after application of Sb and EBL. Moreover, EBL mitigated the negative effects oxidative stress in cowpea plants (Vigna unguiculata) exposed to Cd toxicity by reducing the content of MDA, with decreases in lipid peroxidation and escape of electrolytes (Santos et al. 2018).

BRs can regulate the stress response by modifying the level of antioxidants (Bajguz and Hayat 2009). Our experiments found that EBL significantly enhanced the activity of antioxidants in A. obliquus exposed to metal (Figs. 2c–f and 5a, b). Bajguz (2010) previously reported that BL activated both enzymatic and non-enzymatic antioxidants in C. vulgaris treated with Cu, Pb, and Cd. Ali et al. (2008a) noted that the foliar spray of either with EBL or 28-homobrassinolide meaningfully intensified the content of antioxidant enzymes in Al-stressed mungbean plants. Moreover, EBL enhanced the activity of SOD, CAT, GR, and POD in mustard plants grown under both Ni stress and stress-free conditions (Ali et al. 2008b). Similarly, exogenous 0.01 μM EBL application provoked an increase in the activity of enzymatic antioxidants and proline content in A. thaliana compared to seedlings treated with Sb alone (Wu et al. 2019). Also, the optimal performance in the alleviation of Cu toxicity was noted after application of 0.2 μM EBL. The balance of the ascorbate-GSH cycle in grape cuttings was also regulated by increasing the activities of monodehydroascorbate and dehydroascorbate reductase, as well as GR, APX, and the contents of the antioxidant ascorbate and dehydroascorbic acid. However, the contents of GSH and oxidized glutathione decreased (Zhou et al. 2018). Furthermore, Kapoor et al. (2016) reported that EBL alleviated the harmful impact of Cd in radish seedlings (Raphanus sativus) by enhancing the level of antioxidants, such as ascorbic acid, GSH, and tocopherols. In the case of soybean seedlings (Glycine max) (Ribeiro et al. 2019) and cowpea (Vigna unguiculata) (Lima and Lobato 2017) under water deficit conditions and Eucalyptus urophylla exposed to salt stress (Oliveira et al. 2019), EBL caused increases in SOD, CAT, APX, and POX activities, indicating that BR has a significant impact on the antioxidant system in plants subjected to abiotic stresses. Additionally, EBL reduced the superoxide and H2O2 levels as well as membrane damages (MDA and electrolyte leakage) in soybean under water deficit (Pereira et al. 2019).

The chelation of the metal ions by PC is one of the mechanisms of heavy metal detoxification in plants. PC are cysteine-rich polypeptides derived from GSH. The enzymatically catalyzed PC synthesis reaction requires the presence of PCS (Bajguz 2002; Cobbett and Goldsbrough 2002; Grill et al. 2007; Pal and Rai 2010; Rajewska et al. 2016). The improved PCS activity in algae treated with EBL and Pb was concurrent with the highly raised level of PC4, suggesting that the polymerization of PC2 into PC3-5 was a direct consequence of a higher PCS activity noted under the highest concentration of Pb (Figs. 3a and 4). The results reported by Scarano and Morelli (2002) indicate that Pb and Cd are capable of inducing the PC synthesis and form stable complexes with PC3-6 in a marine microalga Phaeodactylum tricornutum. Moreover, Scenedesmus vacuolatus exposure to 80–800 pM Pb resulted in more than twofold GSH increase; the synthesis of PC2 was noted (Le Faucheur et al. 2006). Present results suggest that EBL is involved in the synthesis of PC in response to Pb stress (Figs. 3a and 4). In general, EBL has a meaningful impact on the detoxification of metal by boosting PC synthesis.

Conclusion

In the study, EBL was applied to mitigate Pb stress in the green alga A. obliquus for the first time. After applying 1 μM EBL to the alga treated with 0.01 and 500 μM Pb, EBL effectively mitigated the toxic effect of Pb on protein and sugar as well as chlorophylls and carotenoids content. Pb limited the algal growth and metabolism which was then restored by the application of EBL. Thus, EBL enhanced the antioxidants, GSH, and PC levels as well as reduced the endogenous level of Pb. These facts confirm that EBL accelerates the metal detoxification and has an anti-stress activity in A. obliquus occurring in Pb-polluted water.

Notes

Authors’ contributions

Concept of the study: AB; collection and assembly of data: MT-K; drafting of the article: MT-K; analysis and interpretation of the data: MT-K, AP-N; statistical analysis: AB; critical revision and important intellectual content: AB; final approval of the article: all authors

Funding information

This project has been financed from the funds of the National Science Centre allocated based on the decision number DEC-2012/05/B/NZ8/00958. This work was funded by the Ministry of Science and Higher Education as part of subsidies for maintaining research potential awarded to the Faculty of Biology and Chemistry of the University of Bialystok.

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Authors and Affiliations

  1. 1.University of BialystokBialystokPoland

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