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Article

Effects of the Amino Acid Constituents of Microcystin Variants on Cytotoxicity to Primary Cultured Rat Hepatocytes

by
Kumiko Shimizu
1,*,
Tomoharu Sano
2,
Reiji Kubota
1,
Norihiro Kobayashi
1,
Maiko Tahara
1,
Tomoko Obama
1,
Naoki Sugimoto
3,
Tetsuji Nishimura
4 and
Yoshiaki Ikarashi
1
1
Division of Environmental Chemistry, National Institute of Health Sciences, 1-18-1 Kamiyoga, Setagaya-ku, Tokyo 158-8501, Japan
2
Center for Environmental Measurement and Analysis, National Institute for Environmental Studies, 16-2 Onogawa, Tsukuba-shi, Ibaraki 305-8506, Japan
3
Division of Food Additives, National Institute of Health Sciences, 1-18-1 Kamiyoga, Setagaya-ku, Tokyo 158-8501, Japan
4
Faculty of Pharmaceutical Sciences, Teikyo Heisei University, Nakano 4-21-2, Nakano-ku, Tokyo 164-8530, Japan
*
Author to whom correspondence should be addressed.
Toxins 2014, 6(1), 168-179; https://doi.org/10.3390/toxins6010168
Submission received: 13 November 2013 / Revised: 13 December 2013 / Accepted: 24 December 2013 / Published: 30 December 2013
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Abstract

:
Microcystins, which are cyclic heptapeptides produced by some cyanobacterial species from algal blooms, strongly inhibit serine/threonine protein phosphatase and are known as hepatotoxins. Microcystins have many structural variations, yet insufficient information is available on the differences in the cytotoxic potentials among the structural variants. In this study, the cytotoxicities of 16 microcystin variants at concentrations of 0.03–10 μg/mL to primary cultured rat hepatocytes were determined by measuring cellular ATP content, and subsequently determined by their 50% inhibitory concentration (IC50). Differences in the amino acid constituents were associated with differences in cytotoxic potential. [d-Asp3, Z-Dhb7] microcystin-LR exhibited the strongest cytotoxicity at IC50 of 0.053 μg/mL among the microcystin variants tested. Furthermore, [d-Asp3, Z-Dhb7] microcystin-HtyR was also highly cytotoxic. These results suggest that both d-Asp and Z-Dhb residues are important in determining the cytotoxic potential of microcystin variants.

1. Introduction

Algal blooms consist of the overgrowth of cyanobacteria in nutrient-rich standing water. When the occurring species produces toxins, these water blooms are hazardous to wildlife, livestock, humans and environmental water systems. Some cyanobacteria species, such as Microcystis, produce microcystins (MCs), which are potent hepatotoxins [1,2,3,4]. Moreover, because global warming causes an increase in the occurrence of blooms, there are concerns that MC variants may result in enhanced health hazards for people in countries under the subtropic and temperate region [5,6].
MCs are macrocyclic heptapeptides with the principal amino acids sequence, cyclo-(d-Ala1-l-X2-d-MeAsp3-l-Z4-Adda5-d-Glu6-MDha7), where d-MeAsp is d-erythro-β-methylaspartic acid, and Mdha is N-methyldehydroalanine. As an example, the sequence of MC-LR has X = leucine and Z = arginine [7,8,9]. There are many sequence variations depending on the identity of the l-amino acid at the X2 and Z4 positions as well as demethylation of d-MeAsp and/or Mdha, and these sequence variations are regarded as MC variants or congeners [10,11]. (2S,3S,8S,9S)-3-Amino-9-methoxy-2,6,8-trimethyl-10-phenyldeca-4,6-dienoic acid (Adda) is a common amino acid among the MC variants and is essential for the inhibition of protein phosphatases [12,13,14]. MCs are taken up by the specific bile acid transport system to hepatocytes [15,16]. Binding selectively to protein phosphatase 1 and 2A and inhibiting phosphatase activity, as a result, MCs cause severe damage to the liver [17,18]. MCs have also been reported to promote the development of liver tumors [17,19]. Moreover, they were reported that MCs have genotoxic potentials [20,21,22] and affects other organs such as heart, kidney and lung [21,23,24].
MC-LR is one of the first detected microcystins, and many studies on its toxic effects have since been conducted both in vitro [20,25,26] and in vivo [18,27,28,29,30]. The World Health Organization (WHO) adopted a provisional guideline value of 1 μg/L for a maximum concentration of MC-LR in drinking water [31]. A couple of reports evaluated the toxicity of each MC variant as a relative value to that of the toxicity of MC-LR [10,32]. Numerous MC variants have been identified from environmental water around the world [33,34,35,36]. Therefore it is important to evaluate the toxicity and environmental behavior of MCs and variants in environment water. However, there is not sufficient information of the cytotoxicity in various MC variants, although some studies for cytotoxicities of MC variants were reported [37,38,39].
In this study, we evaluated the cytotoxicity of 16 MC variants to primary cultured rat hepatocytes. Primary cultured rat hepatocytes were chosen in this study because there were reported that MC-LR induces severe toxicity to the rat liver in vivo [28,29] and causes cytotoxic effects in the hepatocyte [22,40,41]. Moreover, in the present study, we examined the correlation between the cytotoxicity and the amino acid constituents of the MC variants.

2. Results

We evaluated the cytotoxicities of 16 MC variants. Their structures are shown in Figure 1. Figure 2 shows the dose response curves of primary cultured rat hepatocytes after exposure to five MC-LR variants, namely [Dha7] MC-LR, [d-Asp3] MC-LR, [d-Asp3, Dha7] MC-LR, [d-Asp3, E-Dhb7] MC-LR and [d-Asp3, Z-Dhb7] MC-LR. These five MC-LR variants exhibited higher cytotoxic activities than MC-LR. The IC50 values of the MC variants are listed in Table 1. Based on the IC50 values, the cytotoxic potentials of the MC-LR variants were determined. The cytotoxic potentials of the MC-LR variants are ranked as follows: [d-Asp3, Z-Dhb7] MC-LR > [d-Asp3, E-Dhb7] MC-LR > [d-Asp3, Dha7] MC-LR = [d-Asp3] MC-LR = [Dha7] MC-LR > MC-LR (Table 1).
Toxins 06 00168 g001 1024
Figure 1. Structures of the MC variants. MC variants are cyclic peptides consisting of seven amino acids. The sequence position numbers of the amino acids number are denoted by a superscript.
Figure 1. Structures of the MC variants. MC variants are cyclic peptides consisting of seven amino acids. The sequence position numbers of the amino acids number are denoted by a superscript.
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[Dha7] MC-LR and [d-Asp3] MC-LR are demethylated at the R3 and R2 positions, respectively, compared to MC-LR, and their cytotoxic activities were found to be higher than that of MC-LR. [d-Asp3, Z-Dhb7] MC-LR and [d-Asp3, E-Dhb7] MC-LR, which contain substituted methyl groups at the R4 and R5 positions, respectively, were also highly cytotoxic (Figure 2).
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Figure 2. Cytotoxicities of the MC-LR variants in primary cultured rat hepatocytes after 72-h exposure, determined by the cell viability assay. Primary cultured rat hepatocytes were exposed to purified MC-LR, [Dha7] MC-LR, [d-Asp3] MC-LR, [d-Asp3, Dha7] MC-LR, [d-Asp3, E-Dhb7] MC-LR, [d-Asp3, Z-Dhb7] MC-LR. After 72 h of exposures, cytotoxicities were determined by the cell viability assay and the values are shown as % viability. Results are presented as the mean ± SD of three independent experiments. * Significantly different from the control: p < 0.05. (Compounds No.1: MC-LR (◊); No.2: [Dha7] MC-LR (▲); No.3: [d-Asp3] MC-LR (○); No.4: [d-Asp3, Dha7] MC-LR (■); No.5: [d-Asp3, E-Dhb7] MC-LR (∆); No.6: [d-Asp3, Z-Dhb7] MC-LR (□)).
Figure 2. Cytotoxicities of the MC-LR variants in primary cultured rat hepatocytes after 72-h exposure, determined by the cell viability assay. Primary cultured rat hepatocytes were exposed to purified MC-LR, [Dha7] MC-LR, [d-Asp3] MC-LR, [d-Asp3, Dha7] MC-LR, [d-Asp3, E-Dhb7] MC-LR, [d-Asp3, Z-Dhb7] MC-LR. After 72 h of exposures, cytotoxicities were determined by the cell viability assay and the values are shown as % viability. Results are presented as the mean ± SD of three independent experiments. * Significantly different from the control: p < 0.05. (Compounds No.1: MC-LR (◊); No.2: [Dha7] MC-LR (▲); No.3: [d-Asp3] MC-LR (○); No.4: [d-Asp3, Dha7] MC-LR (■); No.5: [d-Asp3, E-Dhb7] MC-LR (∆); No.6: [d-Asp3, Z-Dhb7] MC-LR (□)).
Toxins 06 00168 g002
[Dha7] MC-YR and three MC-HtyR variants showed higher cytotoxic activities than those of MC-YR and -LR (Figure 3). The IC50 values are ranked as follows: MC-YR > [Dha7] MC-YR > [d-Asp3] MC-HtyR > [d-Asp3, E-Dhb7] MC-HtyR > [d-Asp3, Z-Dhb7] MC-HtyR (Table 1). [Dha7] MC-YR, which is a demethylated variant (at the R3 position) of MC-YR, caused an increase in cytotoxic activity relative to MC-YR (Figure 1 and Figure 3).
[d-Asp3, Z-Dhb7] MC-HtyR, which has a methyl group at the R4 position, exhibited significantly high cytotoxic activity, compared to [d-Asp3, E-Dhb7] MC-HtyR, which has a methyl group at the R5 position (Figure 1 and Figure 3).
MC-RR was less cytotoxic than both MC-LR and -YR (Table 1). Four MC-RR variants exhibited higher cytotoxic activities than MC-RR (Figure 4). [Dha7] MC-RR, which lacks a methyl group at the R3 position of MC-RR, induced a slightly high cytotoxic activity relative to [d-Asp3] MC-RR, which lacks a methyl group at the R2 position of MC-RR (Figure 4).
Toxins 06 00168 g003 1024
Figure 3. Cytotoxicities of the MC-YR variants in primary cultured rat hepatocytes after 72-h exposure, determined by the cell viability assay. Primary cultured rat hepatocytes were exposed to MC-LR, MC-YR, [Dha7] MC-YR, [d-Asp3] MC-HtyR, [d-Asp3, E-Dhb7] MC-HtyR, [d-Asp3, Z-Dhb7] MC-YR. After 72 h of exposures, cytotoxicities were determined by the cell viability assay and the values were shown as % viability. Results are presented as the mean ± SD of three independent experiments. * Significantly different from the control: p < 0.05. (Compounds No.1: MC-LR (◊); No.7: MC-YR (♦); No.8: [Dha7] MC-YR (▲); No.9: [d-Asp3] MC-HtyR (○); No.10: [d-Asp3, E-Dhb7] MC-HtyR (∆); No.11: [D-Asp3, Z-Dhb7] MC-HtyR (□)).
Figure 3. Cytotoxicities of the MC-YR variants in primary cultured rat hepatocytes after 72-h exposure, determined by the cell viability assay. Primary cultured rat hepatocytes were exposed to MC-LR, MC-YR, [Dha7] MC-YR, [d-Asp3] MC-HtyR, [d-Asp3, E-Dhb7] MC-HtyR, [d-Asp3, Z-Dhb7] MC-YR. After 72 h of exposures, cytotoxicities were determined by the cell viability assay and the values were shown as % viability. Results are presented as the mean ± SD of three independent experiments. * Significantly different from the control: p < 0.05. (Compounds No.1: MC-LR (◊); No.7: MC-YR (♦); No.8: [Dha7] MC-YR (▲); No.9: [d-Asp3] MC-HtyR (○); No.10: [d-Asp3, E-Dhb7] MC-HtyR (∆); No.11: [D-Asp3, Z-Dhb7] MC-HtyR (□)).
Toxins 06 00168 g003
Toxins 06 00168 g004 1024
Figure 4. Cytotoxicities of the MC-RR variants in primary cultured rat hepatocytes after 72-h exposure, determined by the cell viability assay. Primary cultured rat hepatocytes were exposed to MC-LR, MC-RR, [d-Asp3] MC-RR, [Dha7] MC-RR, [d-Asp3, Dha7] MC-RR, [d-Asp3, E-Dhb7] MC-RR. After 72 h of exposures, cytotoxicities were determined by the cell viability assay and the values were shown as % viability. Results are presented as the mean ± SD of three independent experiments. * Significantly different from the control: p < 0.05. (Compounds No.1: MC-LR (◊); No.12: MC-RR (●); No.13: [d-Asp3] MC-RR (○); No.14: [Dha7] MC-RR (▲); No. 15: [d-Asp3, Dha7] MC-RR (■); No.16, [d-Asp3, E-Dhb7] MC-RR (∆)).
Figure 4. Cytotoxicities of the MC-RR variants in primary cultured rat hepatocytes after 72-h exposure, determined by the cell viability assay. Primary cultured rat hepatocytes were exposed to MC-LR, MC-RR, [d-Asp3] MC-RR, [Dha7] MC-RR, [d-Asp3, Dha7] MC-RR, [d-Asp3, E-Dhb7] MC-RR. After 72 h of exposures, cytotoxicities were determined by the cell viability assay and the values were shown as % viability. Results are presented as the mean ± SD of three independent experiments. * Significantly different from the control: p < 0.05. (Compounds No.1: MC-LR (◊); No.12: MC-RR (●); No.13: [d-Asp3] MC-RR (○); No.14: [Dha7] MC-RR (▲); No. 15: [d-Asp3, Dha7] MC-RR (■); No.16, [d-Asp3, E-Dhb7] MC-RR (∆)).
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Table
Table 1. Comparison of the IC50 of MC variants. Each IC50 value was estimated from the 50% viability concentration shown in Figure 2, Figure 3 and Figure 4. Data are arranged in the order of increasing cytotoxic activity.
Table 1. Comparison of the IC50 of MC variants. Each IC50 value was estimated from the 50% viability concentration shown in Figure 2, Figure 3 and Figure 4. Data are arranged in the order of increasing cytotoxic activity.
No.MC variants nameIC50 (μg/mL)
6[d-Asp3, Z-Dhb7] MC-LR0.053
11[d-Asp3, Z-Dhb7] MC-HtyR0.120
5[d-Asp3, E-Dhb7] MC-LR0.133
4[d-Asp3, Dha7] MC-LR0.217
3[d-Asp3] MC-LR0.217
2[Dha7] MC-LR0.217
10[d-Asp3, E-Dhb7] MC-HtyR0.327
9[d-Asp3] MC-HtyR0.347
8[dha7] MC-YR0.418
1MC-LR0.800
7MC-YR1.48
15[d-Asp3, Dha7] MC-RR4.11
16[d-Asp3, E-Dhb7] MC-RR4.95
14[Dha7] MC-RR5.33
13[d-Asp3] MC-RR>10
12MC-RR>10

3. Discussion

We evaluated the cytotoxicities of MC variants isolated from some cyanobacteria to primary cultured rat hepatocytes. Accumulation of toxicity information for MC variants is absolutely essential to conduct the risk assessment or management of them. Therefore, toxic properties of 16 MV variants indicated in this study would be helpful basic information for the risk assessment or management of many MC variants in environmental water.
In this study, IC50 of MC-LR to primary rat hepatocytes was 0.8 μg/mL, however earlier study was reported that IC50 of MC-LR to the same cells was 48 ng/mL [42]. The MTT assay used in the earlier study and the assay which measure the cellular ATP contents (ATP assay) show occasional different IC50 with certain differences of cell lines, exposure chemicals, number of cells etc. [43,44]. Therefore, the difference of IC50 might be attributed to these assay methods to evaluate the cell viability. Moreover, in this study, we used the freeze-thawed cells and seeded 2.5-fold of cell number compared to the cell number in the earlier study. These differences might have caused the reduction of the cytotoxicity. We think that it is important to evaluate the result taking the difference of the experimental methods into consideration in the risk assessment or management.
Lack of a methyl group at either the R3 or R2 position of Dha7 or d-Asp3, resulted in enhanced cytotoxic activities of MC-LR, -YR, and -RR. In particular, for MC-RR, the lack of a methyl group at the R3 position might be responsible for the slight enhancement of cytotoxic activity, compared to demethylation at the R2 position (Figure 4).
It has been reported that [Asp3, Dhb7] MC-RR exhibits higher cytotoxicity than MC-RR [45,46]. In this study, d-Asp3 and E-Dhb7 or d-Asp3 and Z-Dhb7 on MC-LR and -HtyR also induced higher cytotoxic activities than d-Asp3 or Dha7 on MC-LR and -HtyR. These results suggest that substitution of the methyl group at the R4 or R5 positions is associated with cytotoxic potential, rather than the lack of a methyl group at the R3 or R2 positions. In fact, [d-Asp3, Z-Dhb7] MC-LR exhibited the strongest cytotoxic activity among the 16 variants, and [d-Asp3, Z-Dhb7] MC-HtyR also exhibited high cytotoxicity. A comparison of the IC50 values among [d-Asp3, Z-Dhb7] and [d-Asp3, E-Dhb7] on MC-LR and -HtyR suggests that the presence of a methyl group at the R4 position caused stronger effects on cytotoxic activity than the presence of a methyl group at the R5 position (Table 1). Although the d-Asp3 residue may be essential for the enhancement of cytotoxicity, the R4 methyl group of the Z-Dhb7 residue may also play a key role in the cytotoxic activities of MCs such as the Adda moiety.
Distinct properties of MC variants in terms of uptake, cytotoxicity, protein phosphatase 1 and 2A inhibition, were reported in other organisms cells, brain and neuron cells of mice or Caco-2 cells from human [37,38,39,47]. It is thought that MC variants with the same hydrophobic properties show the same permeabilities to the cell membrane. Vesterkvist et al. suggested that the hydrophobic MC has pronounced cytotoxic potentials in Caco-2 cells [38]. Since [d-Asp3, Z-Dhb7]-MC-LR and -HtyR are geometric isomers of [d-Asp3, E-Dhb7]-MC-LR and -HtyR, respectively, they have same hydrophobic property. However, the Z geometric isomers had more potent cytotoxic activities than the E geometric isomers in primary cultured rat hepatocytes in our study. Therefore, at R4 and R5 position of 7th amino acid (Mdha, Dha or Dhb), the conformational property would be an important factor for cytotoxicity to rat hepatocytes. Differences in the response of the proteins on cell surface or inside the cell, which are caused by differences of the conformational property, might determine the toxic potentials. While the protein phosphatase inhibition activities of MCs were reported in various studies, it was reported that the activity with MC variants did not correlate with their toxic potential [38,46]. There is little information of cellular uptake of MC variants in each organ. More information on membrane permeability, cellular uptake in various organs or species, interaction with target proteins etc. is needed to fully understand different toxic potentials of MC variants.

4. Experimental Section

4.1. MC Variants

The 16 MC variants were separated and purified by high performance liquid chromatography. The details of the separation procedure have been described in a previous report [48]. MC-LR, [d-Asp3, Dha7] MC-LR, [Dha7] MC-LR, MC-YR, [Dha7] MC-YR, MC-RR, [Dha7] MC-RR and [d-Asp3, Dha7] MC-RR were obtained from cultured Microcystis aeruginosa (NIES-90). [d-Asp3] MC-LR, [d-Asp3] MC-HtyR and [d-Asp3] MC-RR were obtained from Planktothrix agardhii (NIES-595 and NIES-1263). [d-Asp3, Z-Dhb7] MC-LR and [d-Asp3, Z-Dhb7] MC-HtyR were isolated from bloom of Planktothrix agardhii [49]. [d-Asp3, E-Dhb7] MC-LR, [d-Asp3, E-Dhb7] MC-HtyR and [d-Asp3, E-Dhb7] MC-RR were obtained from cultured Planktothrix rubescens (NIES-610 and NIES-928). The accurate concentrations of isolated MC variant solutions were determined based on the absorbance at 238 nm using the molar extinction coefficient (42000). The structures of these MC variants are shown in Figure 1.

4.2. Cells

Primary cultured rat hepatocytes, which maintain both phase I and II metabolic activity as well as uptake transporter activity, were isolated from Sprague Dawley. The cells were purchased from Biopredic International (Rennes, France) and were stored at −135 °C until further use. Thawing medium, seeding medium, and long-term culture medium were purchased from Biopredic International (Rennes, France). The primary cultured rat hepatocytes were thawed in a water bath at 37 °C. The cells were poured into 30 mL of pre-warmed thawing medium. The cell suspension was centrifuged at 900 rpm (160 × g) for 1 min. The supernatant was removed and the cell pellets were re-suspended in 2 mL of the seeding medium. The cells were seeded in 96-well white plates at 0.3 × 106 cells/mL in 0.1 mL/well of the seeding medium and incubated at 37 °C in 5% CO2. The following day, the cells were exposed to sixteen MC variants with the long-term culture medium.

4.3. Cytotoxicity Assay

MC variants were dissolved in a mixture of DMSO:water = 9:1 (v/v) to make 1.0 mg/mL stock solutions taking the solubility of MC variants to DMSO into consideration. Stock solutions were diluted to 3–1000 μg/mL with DMSO, and subsequently diluted to final concentrations of 0.03–10 μg/mL in the medium. 1% DMSO solution was diluted 100-fold with the medium, and the resulting solution was used as a negative control. Cells were seeded in 96-well white plates and pre-cultured at 37 °C in 5% CO2 overnight. Cells were then exposed to various concentrations of MC variants in the long-term culture medium for 72 h. Cytotoxicity was evaluated using the Cell Titer-Glo Luminescent Cell Viability Assay Kit (Promega Corporation, Madison, WI, USA), based on cellular ATP content. After 10 min of incubation with an equal volume of the Cell Titer-Glo reagent at room temperature, luminescence was measured for 1 s/well. The luminescence intensity of each well treated with an MC variant was determined, relative to the control, and those concentrations of the MC variants that showed 50% cell viability (IC50) were calculated. MC-LR was used as a positive reference substance for every assay.

4.4. Statistical Analysis

All experiments values were expressed as the mean ± standard deviations (SD) of three independent experiments. The results were analyzed statistically with the Student’s t-test. The test was conducted to verify the difference between each group exposed to MC variants and the control. Differences with p < 0.05 were considered statistical significant.

5. Conclusions

We have determined the cytotoxic potentials of 16 types of MC variants primary culture rat hepatocytes. MC variants containing d-Asp3 and Dha7 and/or Dhb7 residues were found to exhibit stronger cytotoxic activities than their corresponding normal MC variants. The Z-Dhb7 residue of the MC variants is important for their cytotoxic potential. Toxic properties of 16 MC variants indicated in this study would help accumulation of toxicity basic information on various MCs, and eventually contribute to the risk assessment and/or management of environmental water.

Acknowledgments

This work was supported by a research grant from the Ministry of the Environment of Japan and the Ministry of Health, Labour and Welfare in Japan.

Conflicts of Interest

The authors declare that there are no conflict of interest.

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MDPI and ACS Style

Shimizu, K.; Sano, T.; Kubota, R.; Kobayashi, N.; Tahara, M.; Obama, T.; Sugimoto, N.; Nishimura, T.; Ikarashi, Y. Effects of the Amino Acid Constituents of Microcystin Variants on Cytotoxicity to Primary Cultured Rat Hepatocytes. Toxins 2014, 6, 168-179. https://doi.org/10.3390/toxins6010168

AMA Style

Shimizu K, Sano T, Kubota R, Kobayashi N, Tahara M, Obama T, Sugimoto N, Nishimura T, Ikarashi Y. Effects of the Amino Acid Constituents of Microcystin Variants on Cytotoxicity to Primary Cultured Rat Hepatocytes. Toxins. 2014; 6(1):168-179. https://doi.org/10.3390/toxins6010168

Chicago/Turabian Style

Shimizu, Kumiko, Tomoharu Sano, Reiji Kubota, Norihiro Kobayashi, Maiko Tahara, Tomoko Obama, Naoki Sugimoto, Tetsuji Nishimura, and Yoshiaki Ikarashi. 2014. "Effects of the Amino Acid Constituents of Microcystin Variants on Cytotoxicity to Primary Cultured Rat Hepatocytes" Toxins 6, no. 1: 168-179. https://doi.org/10.3390/toxins6010168

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