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An endogenous microRNA (miRNA1166.1) can regulate photobio-H2 production in eukaryotic green alga Chlamydomonas reinhardtii

Biotechnology for Biofuels volume 11, Article number: 126 (2018) Cite this article

Abstract

Background

Hydrogen photoproduction from green microalgae is regarded as a promising alternative solution for energy problems. However, the simultaneous oxygen evolution from microalgae can prevent continuous hydrogen production due to the hypersensitivity of hydrogenases to oxygen. Sulfur deprivation can extend the duration of algal hydrogen production, but it is uneconomical to alternately culture algal cells in sulfur-sufficient and sulfur-deprived media.

Results

In this study, we developed a novel way to simulate sulfur-deprivation treatment while constantly maintaining microalgal cells in sulfur-sufficient culture medium by overexpressing an endogenous microRNA (miR1166.1). Based on our previous RNA-seq analysis in the model green alga Chlamydomonas reinhardtii, three endogenous miRNAs responsive to sulfur deprivation (cre-miR1166.1, cre-miR1150.3, and cre-miR1158) were selected. Heat-inducible expression vectors containing the selected miRNAs were constructed and transformed into C. reinhardtii. Comparison of H2 production following heat induction in the three transgenic strains and untransformed control group identified miR1166.1 as the best candidate for H2 production regulation. Moreover, enhanced photobio-H2 production was observed with repeated induction of miR1166.1 expression.

Conclusions

This study is the first to identify a physiological function of endogenous miR1166.1 and to show that a natural miRNA can regulate hydrogen photoproduction in the unicellular model organism C. reinhardtii.

Background

Hydrogen gas (H2) is a clean energy source, and hydrogen production from green algae is regarded as a promising alternative solution for energy problems, since green algae have iron hydrogenases with high enzyme activity and can rely on solar energy for growth [1,2,3,4,5,6,7,8]. However, hydrogen photoproduction in green algae lasts for just a few seconds to a few minutes due to the hypersensitivity of iron hydrogenases to simultaneously generate oxygen from photosynthesis. Moreover, algal cells only produce hydrogen with excess electrons from the photosynthetic chain to prevent overreduction [9,10,11,12]; thus, the critical problem restricting the application of hydrogen production by green algae is the unsustainability of hydrogen biosynthesis.

A conventional sustainable hydrogen production method depends on the reversible inactivation of oxygen evolution through two-stage algal cultivation [13,14,15]. The first stage is oxygenic photosynthesis to accumulate algal biomass, and the second stage is anaerobic hydrogen production in a sulfur-deprived medium. Under sulfur deprivation, algal cell respiration exhausts oxygen and causes anaerobiosis in the culture. Therefore, this two-stage method separates hydrogen production from oxygen evolution and carbon accumulation, and sulfur deprivation makes sustained hydrogen production possible [11]. However, the replacement of normal medium with sulfur-deprived medium requires the centrifugation of algal cells, which may affect cell activity and is difficult to apply in large-scale production.

Comparative studies of sulfur-deprived and sulfur-replete algae have been conducted at different molecular levels in Chlamydomonas reinhardtii [13,14,15,16,17,18,19,20]. A better understanding of the molecular mechanism of sulfur-deprived stress response may pave new ways for genetic regulation to improve algal photobio-H2 production. Previous results showed that sulfur-deprived cells had massive changes in cellular physiology and metabolism, along with the accumulation of proteins with fewer sulfur-containing amino acids [17]. Microarray analyses showed that photosynthetic genes, one exception being LHCBM9, are generally repressed by sulfur deprivation, suggesting a major remodeling of the photosystem II light-harvesting complex [16]. Sulfur deprivation also affects proteins related to photosynthetic machinery, protein biosynthetic apparatuses, molecular chaperones, and 20S proteasomal components [17]. Recently, we found that non-coding RNAs, including microRNAs (miRNAs), which function as important gene regulators, are also significantly influenced by sulfur deprivation [18, 19]. Further analysis suggested that miRNAs are potentially involved in photobio-H2 production in C. reinhardtii.

miRNAs are a class of endogenous non-coding small RNAs in eukaryotes. They are approximately 18–24 nucleotide (nt) in length and processed from RNAs into stem–loop precursor structures by the nuclease Dicer. miRNAs regulate target gene expression by promoting mRNA degradation and/or inhibiting protein translation. Since miRNAs are present in the unicellular green alga C. reinhardtii, the miRNA pathway represents an ancient gene regulation mechanism that evolved prior to the emergence of multicellularity [21, 22]. In multicellular organisms, miRNAs have been shown to be an important and widespread regulator. Animal miRNAs are involved in developmental timing, cell death, cell proliferation, and patterning of the nervous system [23, 24]. In fact, about one-third of human genes may be miRNA targets [25]. miRNAs are associated with the development of diseases including cancer [26, 27], and they regulate a range of developmental and physiological processes, such as hematopoiesis [28]. In plants, miRNAs also play dominant roles in post-transcriptional gene regulation and modulate organ development, phase transition, and stress responses [29]. In contrast, the functions of miRNAs in unicellular eukaryotic algae remain largely unknown [30]. In C. reinhardtii, some miRNAs (Cre-miR914 and Cre-miR910) were found related to multiple stresses (heat shock, UV-B, and salinity) [31], but functions of most miRNAs still haven’t been studied.

In this study, three endogenous miRNAs responsive to sulfur deprivation (cre-miR1166.1, cre-miR1150.3, and cre-miR1158) were selected from a previous RNA-seq database in the green alga C. reinhardtii. Heat-inducible miRNA overexpression transformants were constructed. By comparing H2 production following heat induction in the three transgenic strains and the WT group, miR1166.1 was identified as the best candidate for H2 production regulation. Moreover, the enhanced photobio-H2 production of miR1166.1-overexpressing algae could be repeatedly induced. To our knowledge, this is the first report of an endogenous miRNA affecting photobio-H2 production in C. reinhardtii.

Methods

Algal strains and culture conditions

The cell-wall-deficient C. reinhardtii strain CC-849 served as the receptor strain and negative control. Algal cells were cultured in TAP (Tris–acetate-phosphate) medium at 22 °C under continuous cool-white light. Sulfur-deprivation medium (TAP-S) was prepared by replacing the S-salts with their chloride counterparts. For 1 L of TAP-S medium, 40× Filner’s Beijernicks Solution (25 mL), 1 M potassium phosphate (1 mL), trace mineral solution (1 mL), and Tris base (2.42 g) were combined, and the pH was adjusted to 7.0 with glacial acetic acid. For sulfur-deprivation treatment, 400 mL cells at exponential phase were collected by centrifugation then washed twice with liquid TAP-S medium. Equal quantities of algal cells were resuspended in TAP and TAP-S media and grown for up to 72 h under continuous white light illumination (≈ 20 μmol photons m−2 s−1). The cells were collected for RNA isolation, and the sulfate concentration in the supernatant was detected using a Dionex ICS-1100 ion chromatograph [4, 15].

Sequencing of miRNA

Total RNA was extracted using Trizol reagent (Invitrogen) according to the manufacturer’s protocol, and RNA quality was examined on an Agilent 2100 Bioanalyzer. For library construction, small RNAs were purified by PAGE and ligated to adaptors. Sequencing of the two libraries was performed using Illumina Solexa sequencing. Raw reads were filtered and compared to the miRBase database (release 15.0). Further details can be found in our previous work [18].

Construction of miRNA overexpression vectors

The pH124 vector, which contains the ble gene for zeocin resistance, was used as the expression vector [32,33,34,35]. An artificial miRNA precursor was introduced into pH124 to permit inducibility by high heat shock treatment in C. reinhardtii. The artificial miRNA precursor was based on the backbone of the highly expressed cre-miR1162 precursor [36,37,38]. The constructed artificial miRNA precursor sequences were synthesized in vitro, and the NheI (GCTAGC) and PmaCI (CACGTG) digestion sites were used to insert the sequences into pH124. The construct containing the promoter, miRNA precursor, and ble gene integrated randomly into the alga nuclear genome.

Genomic DNA PCR analysis

PCR was performed to verify the transformation of the artificial miRNA precursor constructs into algal cells. PCR was performed using the primer pair 593-F (5′-TGACCTCCACTTTCAGCGACA-3′) and 593-R (5′-ACTTGAGAGCAGTATCTTCCATCCA-3′), which map to the region outside of the multiple cloning site in the pH124 vector. The PCR cycling conditions were as follows: pre-denaturation at 94 °C for 4 min; 30 amplification cycles of 94 °C for 30 s, 60 °C for 30 s, and 72 °C for 60 s; and a final extension for 10 min at 72 °C. All amplification products were verified by sequencing and alignment analysis.

Hydrogen detection

Equivalent culture volumes of CC-849 and the transgenic algal strains (400 mL) were cultured in 500 ml bottles sealed with rubber sheet septa until exponential phase. The cultures were pre-treated in the dark for 24 h then cultivated under continuous light to detect gas contents. Gas samples (1 mL sample volume) from the headspace of the cultures were drawn with a syringe and separated using a molecular sieve column (length 6 ft, 1/8 in. OD, 2 mm ID, MolSieve 5A packing, mesh size 60/80). A gas chromatograph with a thermal conductivity detector was used to detect the concentration of H2 (Agilent 7890A; Agilent Technologies Inc., USA). Argon was used as the carrier gas [4]. To test the sustained hydrogen production capacity (Fig. 6), we used triplicates for each strain, and cultured them with the same initial cell density under the same condition. Algal cells at exponential phase were treated in 40 °C water incubates for 1 h and then recovered to 22 °C. After 3, 5, 7, and 9 h of recovery, these cells were heated for the second time and recovered for 3, 5, and 7 h before the heat and recovery were repeated for the third time. H2 concentrations were measured respectively at the mentioned times.

Small RNA extraction

Small RNAs were isolated from both CC-849 and transgenic algae using the E.Z.N.A.® miRNA Kit (OMEGA) according to the manufacturer’s protocol. Polyadenylation was performed using the Poly (A) Tailing Kit (Takara) according to manufacturer’s instructions. The small RNAs were reverse transcribed using poly (T) adapter (Additional file 1: Table S1) according to the S-Poly(T) method [39].

Quantitative real-time PCR

Quantitative real-time PCR (qRT-PCR) was used to measure changes in miR1166.1 expression in CC-849 and transgenic algae. Quantitative real-time PCR was performed using SYBR Premix Ex TaqTM II (Takara, Japan) according to the manufacturer’s instructions on an Applied Biosystems 7300 Real-Time PCR System (Framingham, MA, USA). Quantitative real-time PCR was performed using a universal reverse primer and miR1166.1-specific and U4-specific forward primers [39]. The primer sequences are listed in Additional file 1: Table S1. The PCR cycling conditions were as follows: pre-denaturation at 95 °C for 30 s, followed by 40 two-step cycles of 95 °C for 10 s and 60 °C for 30 s. U4 snRNA was used as the reference gene for the quantitative real-time PCR detection of miR1166.1. The data were analyzed using the 2−ΔΔCt calculation method.

Results

Identification of miRNAs potentially involved in C. reinhardtii photobio-H2 production

We previously performed high-throughput RNA sequencing to identify differentially expressed miRNAs in C. reinhardtii after sulfur-deprivation stress. The analysis identified 310 miRNAs, including 85 miRNAs in miRBase (http://www.mirbase.org/) and 225 novel miRNAs [18]. Among the 310 miRNAs, 47 miRNAs (24 known and 23 novel ones) were responsive to sulfur deprivation, and most of them were up-regulated. We chose three miRNAs that were significantly up-regulated after sulfur deprivation, cre-miR1166.1, cre-miR1150.3, and cre-miR1158, which were up-regulated by 3.9, 2.8, and 3.0 fold, respectively (Fig. 1).

Fig. 1
figure1

Normalized expression levels of sulfur-deprivation-responsive miRNAs in sulfur-replete (+S) and sulfur-deprived (−S) samples. The numbers beside the boxes indicate the normalized expression levels from high-throughput sequencing. **Indicates fold change (log2) > 1 and p < 0.01. *Indicates fold change (log2) > 1 and 0.01 ≤ p < 0.05. Normalized expression = actual miRNA count/total count of clean reads * 1000000

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Construction of miRNA overexpression transgenic algae

The expression vector pH124 harbors the HSP70A-RBCS2 promoter upstream of the multiple cloning site [32] and is commonly used to drive exogenous gene expression upon heat induction in C. reinhardtii [4, 33,34,35]. The precursor of cre-miR1162, a highly expressed endogenous miRNA of C. reinhardtii, was used as the expression backbone [36], and the mature sequence of cre-miR1162 was replaced with that of cre-miR1166.1, cre-miR1150.3, and cre-miR1158 in our study (Fig. 2a). The three miRNA precursors were introduced into the heat-inducible expression vector pH124 (Fig. 2b), and the constructed vectors were transformed into the cell-wall-deficient C. reinhardtii strain CC-849. The transgenic algal strains, referred to as T-miR1166.1, T-miR1150.3, and T-miR1158, were screened with the antibiotic zeocin. Positive clones were confirmed by genomic DNA PCR, and the PCR products were sequenced and aligned (Additional file 2: Figure S1). The results showed that the mature miRNA sequences contained in the three vectors had been correctly integrated into the C. reinhardtii nuclear genome.

Fig. 2
figure2

Construction of pre-miRNA vectors. The mature miRNA sequences of miR1166.1, miR1150.3, and miR1158 are shown in red, and the miRNA* sequences are shown in blue. a Stem–loop structures of the miR1162 precursor and the amiR1166.1, amiR1150.3, and amiR1158 precursors. The mature components (miRNA/miRNA* duplex) are shown in boxes. b Partial diagram of the pH124-miRNA expression vector. NheI and PmaCI sites were added to the left and right arms of the miR1162 precursor, respectively. 5′ HSP70A is a heat shock promoter, 5′ RBCS2 is a constitutive promoter, and ble is the zeocin resistance gene

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Selection of high H2 production transgenic algal strains

H2 production levels were compared between the three transgenic algae and the untransformed CC-849 control by gas chromatography to investigate the effect of the overexpressed miRNAs. Compared to CC-849, transformants T-miR1166.1 and T-miR1150.3 exhibited enhanced H2-producing capacity, while the capacity of T-miR1158 was similar to the control. The effect in T-miR1166.1 exceeded that in T-miR1150.3, and H2 production in T-miR1166.1 was twofold greater compared to CC-849 (Fig. 3). Consequently, we chose miR1166.1 for further analysis.

Fig. 3
figure3

Selection of high H2 production transgenic algae. The Y-axis (H2 concentration) indicates the H2 content in 1 mL gas sample detected by gas chromatography (GC), which was calculated from the H2 peak area. 0 untreated controls; HS1h heat shock treatment for 1 h; R1h, R3h, and R5h recovery at 22 °C for 1, 3, and 5 h after heat treatment, respectively. Since H2 detection of each sample takes 7–8 min, biological replicates were performed for each transgenic algal strain to avoid large treatment time differences. Biological replicates are shown in Fig. 6, Additional file 3: Figure S2, and Additional file 4: Figure S3

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Characteristics and secondary structure of miR1166.1

Cre-miR1166.1 is an endogenous miRNA in C. reinhardtii that is cataloged in miRBase (http://www.mirbase.org/) and was also recorded in our previous miRNA sequencing study. The natural miR1166.1 precursor is 372 nt in length, and the 21 nt mature miRNA is located in the 5′ end of the stem–loop structure (Fig. 4). In our miRNA sequencing data, the FPKM (expected number of fragments per kilobase of transcript sequence per million mapped reads) of miR1166.1 was up-regulated from 0.70 to 2.72 after sulfur deprivation (Fig. 1), which suggested a close relationship of this endogenous miRNA with sulfur-deprivation metabolism pathways in C. reinhardtii.

Fig. 4
figure4

Stem–loop structure of the natural cre-miR1166 precursor. A, U, C, and G indicate adenine, uracil, cytosine, and guanine, respectively. The precursor is 372 nt in length. The red and blue lines mark the position of mature miR1166.1 and mature miR1166.2 within the stem–loop structure, respectively

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Quantitative real-time PCR analysis of miR1166.1

To test the functionality of the constructed expression vector, the transcription levels of miR1166.1 were detected by qRT-PCR in both CC-849 and transgenic algae at four time points: before heat treatment, after 1 h heat treatment at 40 °C, and after 1 and 2 h of recovery following heat treatment. The primers used in the experiments are listed in Additional file 1: Table S1. miR1166.1 expression was significantly induced in the transgenic strain after heat treatment. miR1166.1 also increased in CC-849, but the levels in the transgenic algae were twice the levels in CC-849. The most significant difference was detected after 1 h of recovery, when the miR1166.1 transcription level in transgenic algae was about nine times greater than that in CC-849 (Fig. 5). These results indicate that mature miR1166.1 was significantly induced in the transgenic strain T-miR1166.1 upon heat induction.

Fig. 5
figure5

Quantitative real-time PCR analysis of miR1166.1. Expression levels of miR1166.1 in CC-849 and the transgenic strain before and after heat shock and after 1 and 2 h of recovery. 0 untreated controls; HS1h heat shock treatment for 1 h; RT1h and RT2h recovery at 22 °C for 1 and 2 h after heat treatment, respectively

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Enhanced H2 production of transgenic algae

To investigate the effect of heat-induced miR1166.1 expression on algal H2 production, we designed an experiment involving repeated heat treatment. Algae at exponential phase were treated with 40 °C heat shock, and the H2 production levels were detected immediately. The algae were allowed to recover at 22 °C for several hours followed by H2 detection. The heat treatment and detections were repeated three times. The raw data for H2 production are listed in Additional file 1: Table S2. Each heat shock treatment induced an increase in H2 production in both the transgenic and CC-849 algae. However, the transgenic algae maintained a higher H2 yield (1.21- to 1.68-fold greater) than CC-849 from the first time point to the end of the experiment (Fig. 6). These results indicate that the overexpression of miR1166.1 can modulate H2 production in C. reinhardtii.

Fig. 6
figure6

H2 production of CC-849 and transgenic algae after heat induction. 0 control; HS heat shock; R recovery at 22 °C. Gas samples from the headspace of the CC-849 and transgenic algae cultures were measured before and after 1 h heat treatment. The cultures were recovered at 22 °C, and after 3, 5, 7, and 9 h of recovery, H2 concentrations were measured. The heat treatment and recovery were implemented three times

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Discussion

miRNA functions have been studied extensively in animals and plants, but much has yet to be uncovered about the physiological functions of endogenous miRNAs in the unicellular model organism C. reinhardtii. Firstly, there are few studies providing foundational information about non-coding RNAs in this green alga. Additionally, phenotypic assessment of genetic mutants to functionally characterize miRNAs, a powerful approach in plants, is uncommon in microalgae because their phenotypes are difficult to observe. In plants, miRNA regulation affects plant development and morphology, and plant phenotypes can be very informative about miRNA functions and expression levels [29, 37]. In C. reinhardtii, a few miRNAs have been confirmed to cleave mRNAs or repress mRNA translation, but no significant phenotypes attributable to miRNA alteration have been reported. The present findings link the phenotype of enhanced hydrogen production with a natural miRNA in the unicellular microalga C. reinhardtii, thereby identifying a physiological function of this miRNA.

Sulfur deprivation induces sustained hydrogen production in C. reinhardtii [13], and we found that miR1166.1 was significantly up-regulated after sulfur deprivation. We therefore hypothesized that miR1166.1 might be a hydrogen biosynthesis regulating factor. The hydrogen yield data from the heat-inducible miR1166.1 transgenic algal strain confirmed that miR1166.1 enhanced hydrogen biosynthesis and that the high transcription level of miR1166.1 led to the increase in hydrogen yield. This is the first evidence that a natural miRNA in green algae regulates hydrogen photoproduction.

miRNAs in C. reinhardtii were considered to play a limited role in responses to nutrient deprivation, including sulfur or phosphate deprivation [40]. In general, the miRNA overexpression transgenic strains usually don’t have lethal phenotype or significantly growth phenotypes according to our experience. In this study, our result shows that endogenous miRNA1166.1 significantly affects H2 production in C. reinhardtii. We propose that, compared to a signal miRNA like miRNA1166.1, multiple miRNA regulation may have more significant effect. What’s more, the miRNA target prediction in C. reinhardtii should be different from that in higher plants and animals, with the rather complicated identification of miRNA target genes, thus the results obtained from predicted targets may not be able to represent the function of miRNAs accurately. More studies on C. reinhardtii miRNA functions are still necessary.

We established an efficient heat-inducible system based on the regulatory function of a natural miRNA to control sustained hydrogen production in green algae. The miRNA transcription level (Fig. 5) and hydrogen yield (Fig. 6) showed that the baseline expression of miR1166.1 in the transgenic algal strain was slightly higher than in CC-849. This is probably because the HSP70-RBCS2 promoter can be induced by light as well as heat [4, 32]. However, heat treatment had a stronger effect and could be applied repeatedly to achieve sustained hydrogen production.

We performed qPCR and sequencing to investigate the transcription levels of the miRNA. The result showed that the artificial miRNA precursor had been successfully cleaved to yield the endogenous mature miR1166.1 sequence. Previous studies have demonstrated that the miR1162 backbone is a powerful tool for expressing artificial miRNA sequences [4, 36]. This study further shows that the miR1162 backbone is also applicable for the transgenic expression of natural miRNA sequences.

Target gene prediction of miR1166.1 was performed to investigate the molecular mechanism of this miRNA, but the verification of miRNA target genes is difficult and considerable. Unlike the typically extensive complementarity of miRNAs to their targets in land plants, complementarity to the miRNA seed region is sufficient to induce target gene repression in C. reinhardtii [38]. This difference leads to a broader range of miRNA target genes and a higher probability of inaccurate prediction, consequently making miRNA target identification in C. reinhardtii more complicated. The investigation of the target genes of endogenous miR1166.1 is currently ongoing in our laboratory.

Conclusions

miRNAs in the unicellular model organism C. reinhardtii were initially reported in 2007, and there have been a few studies about the functional mechanisms of miRNAs in this species. However, the present study is the first to identify the physiological function of a natural miRNA in C. reinhardtii. Moreover, natural miR1166.1 regulates hydrogen photoproduction, which is considered a promising strategy for solving energy problems. We previously found that an artificial miRNA targeting OEE2 could enhance hydrogen production; here, we demonstrated that a natural miRNA could also be a hydrogen photoproduction regulator. The findings may provide a novel approach for improving hydrogen production without medium replacement.

References

  1. 1.

    Happe T, Hemschemeier A, Winkler M, Kaminski A. Hydrogenases in green algae: do they save the algae’s life and solve our energy problems. Trends Plant Sci. 2002;7:246–50.

  2. 2.

    Happe T, Naber JD. Isolation, characterization and N-terminal amino acid sequence of hydrogenase from the green alga Chlamydomonas reinhardtii. Eur J Biochem. 1993;214:475–81.

  3. 3.

    Ghirardi ML, Zhang L, Lee JW, Flynn T, Seibert M, Greenbaum E, et al. Microalgae: a green source of renewable H2. Trends Biotechnol. 2000;18:506–11.

  4. 4.

    Li H, Zhang L, Shu LF, Zhuang XS, Liu YM, Chen J, et al. Sustainable photosynthetic H2-production mediated by artificial miRNA silencing of OEE2 gene in green alga Chlamydomonas reinhardtii. Int J Hydrog Energy. 2015;40:5609–16.

  5. 5.

    Saifuddin NM, Priatharsini P. Developments in bio-hydrogen production from algae: a review. Res J Appl Sci Eng Technol. 2016;12:968–82.

  6. 6.

    Florin L, Tsokoglou A, Happe T. A novel type of iron hydrogenase in the green alga Scenedesmus obliquus is linked to the photosynthetic electron transport chain. J Biol Chem. 2001;276:6125–32.

  7. 7.

    Yang S, Guarnieri MT, Smolinski S, Ghirardi M, Pienkos PT. De novo transcriptomic analysis of hydrogen production in the green alga Chlamydomonas moewusii through RNA-Seq. Biotechnol Biofuels. 2013;6(1):118.

  8. 8.

    Eilenberg H, Weiner I, Ben-Zvi O, Pundak C, Marmari A, Liran O, et al. The dual effect of a ferredoxin-hydrogenase fusion protein in vivo: successful divergence of the photosynthetic electron flux towards hydrogen production and elevated oxygen tolerance. Biotechnol Biofuels. 2016;9(1):182.

  9. 9.

    Peltier G, Tolleter D, Billon E, Cournac L. Auxiliary electron transport pathways in chloroplasts of microalgae. Photosynth Res. 2010;106:19–31.

  10. 10.

    Yacoby I, Pochekailov S, Toporik H, Ghirardi ML, King PW, Zhang S. Photosynthetic electron partitioning between [FeFe]− hydrogenase and ferredoxin:NADPþ-oxidoreductase (FNR) enzymes in vitro. PNAS. 2011;108:9396–401.

  11. 11.

    Rumpel S, Siebel JF, Farès C, Duan J, Reijerse E, Happe T, et al. Enhancing hydrogen production of microalgae by redirecting electrons from photosystem I to hydrogenase. Energy Environ Sci. 2014;7:3296–301.

  12. 12.

    Melis A, Happe T. Hydrogen production. green algae as a source of energy. Plant Physiol. 2001;127:740–8.

  13. 13.

    Melis A, Zhang L, Forestier M, Ghirardi ML, Seibert M. Sustained photobiological hydrogen gas production upon reversible inactivation of oxygen evolution in the green alga Chlamydomonas reinhardtii. Plant Physiol. 2000;122:127–36.

  14. 14.

    Geier SC, Huyer S, Praebst K, Husmann M, Walter C, Buchholz R. Outdoor cultivation of Chlamydomonas reinhardtii for photobiological hydrogen production. J Appl Phycol. 2011;24:319–27.

  15. 15.

    Wirth R, Lakatos G, Maróti G, Bagi Z, Minárovics J, Nagy K, et al. Exploitation of algal-bacterial associations in a two-stage biohydrogen and biogas generation process. Biotechnol Biofuels. 2015;8:59.

  16. 16.

    Nguyen AV, Thomas-Hall SR, Malnoë A, Timmins M, Mussgnug JH, Rupprecht J, et al. Transcriptome for photobiological hydrogen production induced by sulfur deprivation in the green alga Chlamydomonas reinhardtii. Eukaryot Cell. 2008;7:1965–79.

  17. 17.

    Chen M, Zhao L, Sun YL, Cui SX, Zhang LF, Yang B, et al. Proteomic analysis of hydrogen photoproduction in sulfur-deprived Chlamydomonas cells. J Proteome Res. 2010;9:3854–66. https://doi.org/10.1021/pr100076c.

  18. 18.

    Shu LF, Hu ZL. Characterization and differential expression of microRNAs elicited by sulfur deprivation in Chlamydomonas reinhardtii. BMC Genom. 2012;13:108.

  19. 19.

    Li H, Wang YT, Chen MR, Xiao P, Hu CX, Zeng ZY, et al. Genome-wide long non-coding RNA screening, identification and characterization in a model microorganism Chlamydomonas reinhardtii. Sci Rep. 2016;6:34109.

  20. 20.

    González-Ballester D, Casero D, Cokus S, Pellegrini M, Merchant SS, Grossman AR. RNA-seq analysis of sulfur-deprived Chlamydomonas cells reveals aspects of acclimation critical for cell survival. Plant Cell. 2010;22:2058–84.

  21. 21.

    Zhao T, Li G, Mi S, Li S, Hannon GJ, Wang XJ, et al. A complex system of small RNAs in the unicellular green alga Chlamydomonas reinhardtii. Genes Dev. 2007;21:1190–203.

  22. 22.

    Molnár A, Schwach F, Studholme DJ, Thuenemann EC, Baulcombe DC. miRNAs control gene expression in the single-cell alga Chlamydomonas reinhardtii. Nature. 2007;447:1126–9.

  23. 23.

    Ambros V. The functions of animal microRNAs. Nature. 2004;431:350–5.

  24. 24.

    Wienholds E, Kloosterman WP, Miska E, Alvarez-Saavedra E, Berezikov E, de Bruijn E, et al. MicroRNA expression in zebrafish embryonic development. Science. 2005;309:310–1.

  25. 25.

    Lewis BP, Burge CB, Bartel DP. Conserved seed pairing, often flanked by adenosines, indicates that thousands of human genes are microRNA targets. Cell. 2005;120:15–20.

  26. 26.

    Calin GA, Croce CM. MicroRNA signatures in human cancers. Nat Rev Cancer. 2006;6:857–66.

  27. 27.

    Wang J, Chen S, Sen S. MicroRNA as biomarkers and diagnostics. J Cell Physiol. 2016;231:25–30.

  28. 28.

    Hong SH, Kim KS, Oh IH. Concise review: exploring miRNAs–toward a better understanding of hematopoiesis. Stem Cells. 2015;33:1–7.

  29. 29.

    Li C, Zhang B. MicroRNAs in control of plant development. J Cell Physiol. 2016;231:303–13. https://doi.org/10.1002/jcp.25125.

  30. 30.

    Shu LF, Hu ZL. Small silencing RNAs in Chlamydomonas reinhardtii. Minerva Biotecnologica. 2010;22:29–37.

  31. 31.

    Gao X, Zhang F, Hu J, Cai W, Shan G, Dai D, et al. MicroRNAs modulate adaption to multiple abiotic stresses in Chlamydomonas reinhardtii. Sci Rep. 2016;6:38228.

  32. 32.

    Schroda M, Blöcker D, Beck CF. The HSP70A promoter as a tool for the improved expression of transgenes in Chlamydomonas. Plant J. 2000;21:121–31.

  33. 33.

    Wang CG, Hu ZL, Lei AP, Jin BH. Biosynthesis of poly-3-hydroxybutyrate (PHB) in the transgenic green alga Chlamydomonas Reinhardtii. J Phycol. 2010;46:396–402.

  34. 34.

    Mu FY, Li H, Hu ZL. Expression of tandem repeat Cecropin B in Chlamydomonas reinhardtii and its antibacterial effect. Prog Biochem Biophys. 2012;39:344–51.

  35. 35.

    Wang CG, Hu ZL, Zhao CN, Mao XM. Isolation of the β-carotene ketolase gene promoter from Haematococcus pluvialis and expression of ble in transgenic Chlamydomonas. J Appl Phycol. 2012;24:1303–10.

  36. 36.

    Zhao T, Wang W, Bai X, Qi Y. Gene silencing by artificial microRNAs in Chlamydomonas. Plant J. 2009;58:157–64.

  37. 37.

    Yan J, Gu Y, Jia X, Kang W, Pan S, Tang X, et al. Effective small RNA destruction by the expression of a short tandem target mimic in Arabidopsis. Plant Cell. 2012;24:415–27.

  38. 38.

    Yamasaki T, Voshall A, Kim EJ, Moriyama E, Cerutti H, Ohama T. Complementarity to an miRNA seed region is sufficient to induce moderate repression of a target transcript in the unicellular green alga Chlamydomonas reinhardtii. Plant J. 2013;76:1045–56. https://doi.org/10.1111/tpj.12354.

  39. 39.

    Niu Y, Zhang L, Qiu H, Wu Y, Wang Z, Zai Y, et al. An improved method for detecting circulating microRNAs with S-Poly(T) Plus real-time PCR. Sci Rep. 2015;5:15100.

  40. 40.

    Voshall A, Kim EJ, Ma X, Yamasaki T, Moriyama EN, Cerutti H. miRNAs in the alga Chlamydomonas reinhardtii are not phylogenetically conserved and play a limited role in responses to nutrient deprivation. Sci Rep. 2017;7:5462.

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Authors’ contributions

ZH designed and guided the study. HL participated in study design and manuscript writing. YW participated in manuscript writing and performed the statistical analysis. XZ performed vector construction and positive transformant identification. MC participated in primer design and performed quantitative real-time PCR. XC carried out the gas detection. All authors read and approved the final manuscript.

Competing interests

The authors declare that they have no competing interests.

Availability of data and materials

All data generated or analyzed during this study are included in this published article and its Additional files.

Ethics approval and consent to participate

Not applicable.

Funding

This work was supported by the National Natural Science Foundation of China (31470431), Guangdong Natural Science Foundation (2014A030308017 and 2016A030313052), Project of DEGP (2015KTSCX125), Shenzhen Grant Plan for Science & Technology (Shenzhen basic research projects, Subject layout project), Demonstration Project for Marine Economic Development in Shenzhen (2017 documents No.283, Department of the Science and Technology, China’s State Oceanic Administration) and Shenzhen special funds for Bio-industry development (NYSW20140327010012).

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Author notes

  1. Yuting Wang and Xiaoshan Zhuang contributed equally to this work

Affiliations

  1. Guangdong Technology Research Center for Marine Algal Bioengineering, Guangdong Key Laboratory of Plant Epigenetic, College of Life Sciences and Oceanography, Shenzhen University, Shenzhen, 518060, People’s Republic of China
    • Yuting Wang
    • , Xiaoshan Zhuang
    • , Meirong Chen
    • , Zhiyong Zeng
    • , Xiaoqi Cai
    • , Hui Li
    •  & Zhangli Hu
  2. Shenzhen Key Laboratory of Marine Bioresource & Eco-environmental Science, Longhua Innovation Institute for Biotechnology, College of Life Sciences and Oceanography, Shenzhen University, Shenzhen, 518060, People’s Republic of China
    • Xiaoshan Zhuang
    • , Meirong Chen
    • , Zhiyong Zeng
    • , Xiaoqi Cai
    • , Hui Li
    •  & Zhangli Hu
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  1. Yuting Wang
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Wang, Y., Zhuang, X., Chen, M. et al. An endogenous microRNA (miRNA1166.1) can regulate photobio-H2 production in eukaryotic green alga Chlamydomonas reinhardtii. Biotechnol Biofuels 11, 126 (2018). https://doi.org/10.1186/s13068-018-1126-8

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Keywords

  • Biohydrogen
  • Green alga
  • Chlamydomonas reinhardtii
  • microRNA
  • Gene regulation

Biotechnology for Biofuels

ISSN: 1754-6834

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