Overexpression of Ferredoxin, PETF, Enhances Tolerance to Heat Stress in Chlamydomonas reinhardtii

1. Introduction

Excessive greenhouse gas emissions from human activities raise the global temperature, and high ambient temperatures lead to biochemical and physiological changes in plants, thereby affecting plant growth and development. High temperatures cause protein denaturation and aggregation, inhibiting protein function and compromising membrane integrity. Reactive oxygen species (ROS) are subsequently generated when high-energy state electrons are released from heat-disrupted membrane-associated processes such as photosynthesis [1,2]. ROS are highly reactive and toxic, and they can cause oxidative damage to cells [3,4]. To counter the threat of oxidative damage under various environmental stresses, plants have developed ROS-scavenging mechanisms to eliminate ROS [5,6]. By combining antioxidant enzymes with antioxidants, plant cells can detoxify hydrogen peroxide and superoxide [7,8]. Several pieces of evidence indicate that antioxidant enzymes and antioxidants are associated with the plant heat tolerance [7,9–12].

Ferredoxins (FDXs) in chloroplasts are electron transfer proteins that deliver reducing equivalents from photosystem I (PSI) in photosynthetic organisms [13]. Electrons from reduced FDXs are accepted by FDX-NADPH-oxidoreductase (FNR) to generate NADPH, which is required for carbon assimilation in the Calvin cycle [14,15]. FDXs can also donate electrons to nitrite reductase (NiR), sulfite reductase (SiR) and fatty acid desaturases (FADs) for nitrogen and sulfur assimilation as well as fatty acid desaturation [16,17]. In addition, FDXs are key regulators of FDX-thioredoxin reductase (FTR) in thioredoxin systems [14]. Moreover, FDXs are components in the water-water cycle, a ROS-scavenging pathway, and generate ascorbate and peroxiredoxin to protect the photosynthetic apparatus [18–20].

FDX transcripts have been observed to decrease under drought, cold, or salt stress conditions in Arabidopsis [21]. The amount of FDX is also decreased in tobacco under various stresses [22]. Decreasing FDX by antisense RNA in transgenic plants causes leaf yellowing under high light stress, and the ROS level is increased in FDXs-limiting plants [23,24]. These results suggest that the expression of FDXs is down regulated by abiotic stress, resulting in increased the ROS level and subsequent oxidative damage to cells. In addition, ectopic expression of a cyanobacterial flavodoxin, which is a functional analog of FDXs found in cyanobacteria and some algae, decreases the ROS level in transgenic tobacco and enhances plant tolerance to heat, high light, chilling, drought, UV radiation, and iron starvation [22,25,26]. However, ectopic expression of a cyanobacterial FDX in tobacco chloroplasts does not improve the tolerance of transgenic plants to oxidative and chilling stresses [27]. Although the level of foreign cyanobacterial FDX has been shown to decrease in the manner of an endogenous FDX in transgenic tobacco under stress [27], whether FDX functions under adverse environment stresses remains uncertain.

The single-celled green alga Chlamydomonas reinhardtii is an excellent photosynthetic model organism for examining physiological responses of cells under abiotic stresses [28]. Recent studies on hydrogen production by FDXs and hydrogenase in Chlamydomonas have proposed methods for potentially generating clean energy [29–31]. Previous studies have shown that Chlamydomonas contains six FDXs, PETF, and FDX2—FDX6 [32,33]. Although the expression levels of PETF, and FDX2–FDX6 vary under hypoxia, iron- and copper-deficient conditions [34], PETF is a major photosynthetic ferredoxin in chloroplasts and performs a function in electron transfers between PSI and FNR [34,35]. In this study, we generated transgenic Chlamydomonas overexpressing PETF to clarify whether increasing FDX gene expression levels enhance the tolerance of algae to heat stress.

2. Results

2.1. Generation and Characterizations of Transgenic Lines Overexpressing

PETF Using an electroporation transformation system, three transgenic Chlamydomonas lines, P1-5, P1-7 and P1-10, carrying a recombinant Chlamydomonas FDX gene, PETF, under the control of constitutive β2-tubulin promoter (P_T), were generated (Figure 1A). The P_T::PETF transgene was detected in all three PETF-transgenic lines by using genomic DNA PCR (Figure 1B). Furthermore, the levels of total PETF mRNA in all three transgenic lines were 1.7- to 2.7-fold higher than that of the non-transgenic line (CC125), as shown using quantitative RT-PCR (Figure 1C). Cellular protein extracts were probed with an antiserum of PFLP, a photosynthetic type FDX isolated from sweet pepper [36], however, no signal was detected, possibly because of its low affinity to the Chlamydomonas FDXs.

Ascorbate is one of the major antioxidant metabolites in plant tissues. To determine whether the ratios of reduced ascorbate were effected by ectopic expression of P_T::PETF, the late-log phase cell cultures of transgenic lines were collected and subjected to measurement of ascorbate. The result showed that the ratios of reduced ascorbate in the P1-5, P1-7, and P1-10 lines were higher than that of CC125 (Figure 1D).

Chloroplasts are known to be the main targets of ROS-related damage under environmental stresses [37]. To determine whether ectopic expression of P_T::PETF affects growth rate and chlorophyll content, the doubling time and chlorophyll content of the transgenic lines were measured. Under normal growth conditions, the doubling time was 11.5 h for CC125 C. reinhardtii and 12.0–12.3 h for transgenic lines (Figure 2A). The contents of chlorophyll a, chlorophyll b, and total chlorophyll were not significantly different between non-transgenic and transgenic C. reinhardtii under normal conditions (Figure 2B and

Table 1. Chlorophyll contents of transgenic Chlamydomonas overexpressing PETF.

	Chlorophyll contents (μg/3 × 106 cells)
	25 °C			42 °C
	Chl a	Chl b	Total	Chl a	Chl b	Total
CC125	10.6 ± 0.6 a	4.5 ± 0.1 a	15.1 ± 0.6 a	7.1 ± 0.8 a	2.7 ± 0.2 a	9.8 ± 1.0 a
P1-5	11.3 ± 0.9 a	4.1 ± 0.3 a	15.4 ± 1.1 a	10.5 ± 0.8 c	4.4 ± 0.3 c	14.9 ± 1.1 c
P1-7	11.3 ± 0.7 a	4.6 ± 0.3 a	15.9 ± 1.0 a	9.4 ± 0.1 b	3.9 ± 0.1 b	13.3 ± 0.2 b
P1-10	11.3 ± 0.6 a	4.5 ± 0.1 a	15.8 ± 0.8 a	11.1 ± 0.6 c	4.9 ± 0.1 d	15.9 ± 0.6 c

Chlorophyll contents in cell cultures were measured immediately after control (25 °C) or heat treatment (42 °C) for 40 min. Values are the mean ± standard deviation for five repeats, and letters indicate the significant differences of each column based on Duncan’s multiple range test (p < 0.05).

). These results suggested that overexpression of PETF did not significantly change growth behaviors.

2.2. Overexpression of PETF in Chlamydomonas Enhances Stress Tolerance to Heat

Hema et al. reported that a growth temperature of 42 °C markedly inhibited the growth of C. reinhardtii cells [28]. To determine whether PETF provided protection under heat stress, we compared the survival rates of the P_T::PETF transgenic lines with those of non-transformant lines under heat-stress. Cells were subjected to heat treatment at 42 °C for 40 min and recovered for 2 days. The cell viability of the non-transgenic line, CC125, dropped from 97.1% to 50% (Figure 3A). In addition, the color of the culture changed from greenish to yellowish, and the chlorophyll contents decreased immediately after heat treatment (Figure 3B and Table 1). By contrast, the survival rate of the P_T::PETF transgenic lines was maintained at 85% (Figure 3C). The chlorophyll contents indicated that there are no significant difference for P_T:PETF transgenic lines grown under normal and heat-stress conditions (Table 1). These results showed that over-expression of the PETF gene apparently increased the survival rates of C. reinhardtii under heat stress.

2.3. Accumulation of Reactive Oxygen Species (ROS) Is Reduced in Transgenic Lines Overexpressing PETF

High temperature is a type of oxidative stress that induces ROS to cause oxidative damage in plant cells [2], and FDX participates in ROS scavenging by reducing ascorbate [18]. The P_T::PETF transgenic lines showed an approximately 2-fold increase in survival rates after heat treatment at 42 °C for 40 min (Figure 3C). A cell permeable fluorogenic dye, 2′,7′-dichorofluorescein diacetate (DCFDA), was used to detect ROS by confocal microscopy. The chlorophyll autofluorescence signal was used as an indicator for detecting chloroplasts. As shown in Figure 4A, no ROS signal was detected in either the non-transgenic or transgenic lines under normal growth conditions. However, after heat treatment, the level of the ROS fluorescent signal increased and chlorophyll image declined in the non-transgenic cells, whereas a low level of the ROS signal was observed, and the chlorophyll fluorescence signals remained stable in the P1-10 cells (Figure 4B). These results indicated that the increase of PETF in a cell could reduce ROS accumulation and prevent chlorophyll degradation under heat treatment. Furthermore, the content of H₂O₂, a major species of ROS, was measured after heat treatment. Although the amount of H₂O₂ increased in both CC125 and transformants after heat treatment, H₂O₂ concentration was significantly lower in the transgenic lines than in the heat-treated non-transgenic cells (Figure 4C). These results showed that ROS, including the major species H₂O₂, were significantly reduced in the PETF-transgenic lines, regardless of heat treatment.

2.4. Expression of PETF Correlates Positively to Thermotolerance Ability in Transgenic Lines

To demonstrate whether an increase in thermotolerance ability in transgenic lines is correlated to the PETF expression level, the mRNA quantity of PETF was measured using quantitative RT-PCR. After heat treatment, PETF mRNA in the non-transgenic lines was reduced by approximately 32% compared with normal growth conditions (Figure 5A). However, PETF mRNA in three transgenic lines remained at a high level after heat treatment. As shown in Figure 5B, the relative levels of PETF mRNA in P1-5, P1-7 and P1-10 were 177%, 123% and 245%, respectively, compared with those of the non-transgenic line (Figure 4D). The P1-10 line accumulated the highest level of PETF mRNA (Figure 4D) and exhibited the highest survival rate under heat treatment (Figure 3C) among the three transgenic lines. These results indicated that the levels of PETF transcripts were positively correlated with the thermotolerance ability in the transgenic Chlamydomonas lines.

3. Discussion

Reduction of ROS level is a major biotechnology strategy used to protect plants from various abiotic stresses [38–40]. In the study reported herein, ROS produced by C. reinhardtii cause oxidative damage, which results in cell death under heat treatment at 42 °C for 40 min. Three Chlamydomonas transgenic lines overexpressing PETF were generated, and ROS levels in these transgenic lines were significantly reduced even after heat treatment. These transgenic algae presented highly thermotolerant phenotypes that are correlated to the transgene PETF expression levels. These findings indicate that overexpression of the PETF gene decreases ROS levels and contributes to the tolerance of heat stress. However, plant responses to heat stress are highly complex, and have effects on protein denaturation, membrane destabilization, metabolic equilibration, and redox homeostasis [9,41]. Integration of different protective mechanisms contributes to plant tolerance under heat stress, and the complex protective networks can be facilitated by overexpression of PETF.

The Chlamydomonas genome contains six ferrdoxin (FDX) genes and the expression of each FDX gene is responsive to different environmental stress and nutrient conditions [34]. For example, transcription of FDX2 was upregulated by H₂O₂, although the FDX2 protein was rapidly damaged after H₂O₂ treatment. On the other hand, the expression of the FDX5 transcript was responsive to O₂, copper, and nickel supplementation [34]. The most abundant FDX transcript found in Chlamydomonas grown in TAP medium under normal growth condition is PETF, and its expression remains constitutive in most tested conditions, including under H₂O₂ treatment [34]. In this study, it was demonstrated that PETF mRNA decreased slightly after heat treatment, and Terauchi et al. (2009) showed that PETF protein is not significantly degraded under oxidative stresses [34]. Therefore, it was proposed that high-level PETF mRNA can be maintained and translated to functional PETF, which contributes to transgenic algae resistant to heat stress. Moreover, it is known that monodehydroascorbate (MDA) is a major sink of photosynthetic electrons and can be reduced to ascorbate by FDX in cells [28,37]. Our results showed that the ratios of reduced ascorbate in the P1-5, P1-7, and P1-10 lines were higher than that of CC125 (Figure 1D), suggesting that the PETF-transgenic lines contained more functional PETF and reduced more ascorbate than the non-transgenic line did.

In this study, three transgenic lines of Chlamydomonas expressing the PETF gene were obtained. The growth curve and chlorophyll content of transgenic lines did not have significant differences compared to that of non-transgenic lines under normal growth conditions. However, after heat treatment, the survival rates of PETF-overexpressing lines increased significantly compared to that of non-transgenic line. In addition, chloroplasts in transgenic cells remained intact and exhibited little chlorophyll content decrease after heat treatment. Interestingly, chlorophyll b (Chl b) was more protected than chlorophyll a (Chl a) in transgenic lines. This report indicated that maintenance of chlorophylls by PETF would protect Chlamydomonas against heat stress. However, the mechanism of PETF-mediated chlorophylls protection needs further investigation. Plant membrane systems including thylakoid membrane are known as direct targets of ROS under heat stress [1]. Biosynthesis and degradation of chlorophyll determine the amount of chlorophyll present, and both processes are known to require FDX-dependent enzymes in plants [42–46]. Chlorophylls and their binding proteins form complexes when they are inserted into thylakoid membranes. When chlorophyll–protein complexes are dissociated, chlorophyll molecules enter the degradation pathway [47]. Therefore, there is a strong correlation between thylakoid membrane stability and chlorophyll degradation under heat conditions. Moreover, several reports showed that degree of lipid saturation in membranes increases in plants under high temperature and thus reduces membrane stability [48,49]. Saturated fatty acid containing membrane glycerolipids are converted to unsaturated fatty acid by desaturases in plastids and endoplasmic reticulum (ER) [50,51], and the plastid desaturases required FDX to provide electrons for fatty acid desaturation [42]. It is possible that overexpression of PETF facilitates electron donation to desaturase for desaturation of fatty acids, and hence maintains membrane stability and chlorophyll content under heat stresses.

Chl b is synthesized from and can be reconverted to Chl a. The levels of Chl b are determined by the activity of three enzyme reactions; conversion of Chl a to Chl b by chlorophyllide a oxygenase (CAO), conversion of Chl b to 7-hydroxymethyl Chl a (HMChl a) by Chl b reductase (CBR), and conversion of HMChl a to Chl a by 7-hydroxymethyl-chlorophyll reductase (HCAR) [52]. The CAO has been suggested to accept electrons from FDX to convert Chl a to Chl b, and both CBR and HCAR are FDX-dependent enzymes [42]. Overexpression of PETF in transgenic lines showed no alteration in levels of Chl a and Chl b, compared to the wild type, and it suggested that PETF contributes equally to both sides of conversion under normal growth condition. Chl b degradation is primarily performed via conversion of Chl a by CBR and HCAR and followed by two FDX-dependent enzymes, Pheide a oxygenase (PAO) and RCC reductase (RCCR) [42]. It is proposed that PETF favors electron donation to PAO and RCCR, and accelerates Chl a degradation; therefore Chl b was protected more than Chl a in transgenic lines under heat stresses.

Mitochondria and chloroplasts have been clearly recognized as main sources of ROS in plant cells [53]. In chloroplasts, increased levels of ROS are produced under adverse environmental conditions, such as drought, salt, high temperature and high-light, causing stress through the photosynthetic electron-transport chain (PETC) due to unsmooth electron flow [53–55]. In this study, the major ferredoxin PETF was overexpressed in expectations of reducing overproduction of high-energy electrons from PETC in Chlamydomonas cells under heat stress and then decreasing ROS production to prevent cell damage. Consequently, transgenic algae overexpressing PETF showed thermotolerance. Indeed, overexpression of chloroplast FNR, which is involved in the last step of PETC, increased tolerance to oxidative stress in tobacco [56]. In addition, ectopic expression of a prokaryotic flavodoxin, an electron carrier flavoprotein not found in plants, targeted to chloroplast in transgenic tobacco plants is shown to increase tolerance against various abiotic stress [22]. Similar hypotheses were tested in mitochondria of the mammalian cell line Cos-7 cells and results showed that ectopic expressed heterologous FNR and flavodoxin can protect Cos-7 cells against oxidative stress [57]. On the other hand, ferredoxin can transfer electrons to generate ascorbate, which is employed by ascorbate peroxidase (APX) to scavenge H₂O₂[18,20,58,59]. Although electrons from ferredoxin can provide an alternative sink to generate O₂⁻ from O₂ in the Mehler reaction, the reducing power of ferredoxin also acts for ascorbate reduction [60]. Results aforementioned indicated that transgenic Chlamydomonas lines overexpressing PETF generated more reduced ascorbate than non-transgenic algae did, and it can donate electrons in ascorbate-mediated ROS scavenging to detoxify ROS generated under heat stress in chloroplast.

4. Experimental Section

4.1. Cultivation of Chlamydomonas reinhardtii

Chlamydomonas reinhardtii Wild-type strain CC125 and PETF-transgenic lines were grown in TAP medium [61] under a continuous light (125 μE m⁻² s⁻¹) at 25 °C. Cell density was counted using a standard hemocytometer. The doubling time and growth curve were determined by methods described by Stern et al. [62].

4.2. Construction of Plasmids

To construct a plasmid for constitute expressing the PETF gene, a promoter region of β2-tubulin gene was amplified by polymerase chain reaction (PCR) with primers B2T-F: 5′-CGGGTACCGAATTVGATATCAAGCTTC-3′ (KpnI site underlined) and B2T-R: 5′-GGGCCCGTTTGCGGGTTGTG-3′ (ApaI site underlined) from pHYG3 [63]. The amplified DNA fragment was digested with KpnI and ApaI, and then ligated into pHYG3 to generate pHyG3-B2T. The PETF cDNA fragment was amplified by reverse transcription polymerase chain reaction (RT-PCR) with cPETF-F: 5′-GGGCCGGGCCCATGGCCATGGCTATGCGCTC-3′ (ApaI site underlined) and cPETF-R: 5′-ACCATACATATGTTAGTACAGGGCCTCCTCCTG-3′ (NdeI site underlined). The PCR product was digested with ApaI and NdeI, and ligated into pHYG3-B2T to generate pHYG3-PETF.

4.3. Gene Transformation of Chlamydomonas reinhardtii

Electroporation protocol of the method as described [64] was performed for cell transformation. Late log phase algal cell culture was quickly collected and washed with 10% Tween-20. Then, the cell pellet was resuspended with TAP broth containing 40 mM of sucrose. Before electroporation, cells were mixed with ScaI-digested linear form DNA of plasmid pHYG3-PETF. The mixture was transferred into a 4-mm gap electroporation cuvette at 10 °C. The electric pulse conditions were 2000 V/cm, 25 μF, and 500 Ω. After electroporation, cells were transferred to TAP broth medium and incubated at 25 °C for 72 h. The putative transgenic lines were screened on TAP plate with 20 μg/mL of hygromycin. All of the putative PETF-transgenic cell lines were confirmed by genomic PCR with primers 2201F (5′-CCACTTCTACACAGGCCACT-3′) and 3071R (5′-GGGCGACACGGAAATGTTG-3′).

4.4. Heat Treatment and Cell Survival Determination

For heat stress treatment, a single colony was incubated in TAP broth. The cell cultures with concentration of 3 × 10⁶ cell/mL were subjected to treatment at 42 °C under continuous light (125 μE m⁻² s⁻¹) for 40 min, and then recovered for an additional 72 h under continuous light at 25 °C. The cell survival rate was determined by trypan blue staining analysis [65]. The cell suspension was mixed with an equal volume of 0.4% (w/v) trypan blue solution. The numbers of unstained living cells (Nu) and total cells (Nt) were counted using a hemocytometer, and the survival rate was determined to be Nu/Nt × 100%.

4.5. Quantitative RT-PCR

Total RNA was isolated by using a plant total RNA kit (Viogene, Taipei, Taiwan). The cDNA was synthesized using Transcriptor First Strand cDNA Synthesis Kit (Roche, Penzberg, Germany) from 1 μg of total RNA. To measure the total PETF transcripts in PETF-transgenic and non-transgenic lines, quantitative PCR was performed by 7500 Fast Real-Time PCR Systems (Applied Biosystem, Foster City, CA, USA). Primers Re-PETF-F (5′-TGAGTGCCCCGCTGACACCT-3′) and Re-PETF-R (5′-GCACCAGCGCGGCAAGAGTA-3′) were designed for amplifying PETF transcripts. The Cblp gene encodes for G-protein beta subunit-like polypeptide is constitutively expressed in C. reinhardtii [47]. Primers Re-Cblp-F (5′-ACCTGGAGAGCAAGAGCATCGT-3′) and Re-Cblp-R (5′-TGCTGGTGATGTTGAACTCGG-3′) were designed according to its sequence (Genbank: X53574.1) for amplifying Cblp transcripts as an internal control.

4.6. Determination of Ascorbate Content

The amounts of reduced ascorbate (Ar) and total ascorbate pool (At) were measured as described with modification [66]. The total 3 × 10⁶ algal cells were collected and homogenized with a steel ball after freezing in liquid nitrogen. One milliliter of 6% trichloroacetic acid (TCA) was added to resuspend the algal extracts, which were centrifuged, and the supernatant was used for determining the ascorbate content. For determining the amount of At, 100 μL of supernatant was mixed with 50 μL of 100 mM dithiothreitol and 50 μL of a 75 mM phosphate buffer (pH 7.0). The mixture was incubated at room temperature for 30 min. For determining the amount of Ar, 100 μL of supernatant was added with 50 μL of deionized water and 50 μL of a 75 mM phosphate buffer for 30 min. The mixtures were then reacted with a reaction buffer (250 μL of 10% TCA, 200 μL of 43% H₃PO₄, 200 μL of 4% α-α′-bipyridyl and 100 μL of 3% FeCl₃) at 37 °C for 1 h. The ascorbate concentrations were determined by the absorbance at 525 nm according to the standard curve made by 0.15–10 mM of ascorbate (Sigma, St. Louis, MO, USA) standards in 6% TCA. The ratio of reduced ascorbate in total ascorbate pools was calculated at (Ar/At) × 100%.

4.7. Reactive Oxygen Species (ROS) Detection and H₂O₂ Measurement

Two methods were used to quantify ROS formation. The first is semi-quantification using ROS staining [67], and the second is H₂O₂ quantification. For ROS staining, cells were stained with 10 μM of 2′,7′-dichlorodihydrofluorescein diacetate (H₂DCFDA) for 20 min and then subjected to a confocal laser-scanning microscopy (LSM 510 META, Zeiss, Jena, Germany). Signals of H₂DCFDA and autofluorescence of chlorophyll were visualized with excitation at 488 nm and emissions at 500–530 nm and 650–710 nm, respectively.

For H₂O₂ measurement, cells were treated with reagents of an Amplex Red Hydrogen Peroxide/Peroxidase Assay Kit (Molecular Probes/ Invitrogen, Carlsbad, CA, USA). In brief, a total of 3 × 10⁶ algal cells in log phase were collected by centrifugation, and the pellet was frozen in liquid nitrogen and ground using a steel ball. The cell debris was dissolved in a 100 μL of a 1× reaction buffer in the assay kit. The mixture was centrifuged and the supernatant was then used to measure the cellular H₂O₂ concentrations after incubation with horseradish peroxidase at 25 °C for 30 min. The H₂O₂ concentrations were determined by the standard curve developed using 0.2–1.0 μM of H₂O₂ standards. Data were collected with five repeats and statistically analyzed using Duncan’s multiple range test.

4.8. Determination of Chlorophyll Content

Chlamydomonas cells in log phase (total 3 × 10⁶ cells) were collected and resuspended in 1 mL of 80% acetone. After centrifugation, the chlorophyll content of the supernatant was measured according to optical absorbance at 663 nm and 645 nm by using a U-2001 spectrophotometer (Hitachi, Tokyo, Japan). The chlorophyll content was determined by the following Equations (1)–(3) [68]:

$$\text{Chlorophyll\hspace{0.17em}}a\hspace{0.17em}(\mu \text{g}/\text{mL})=(22.9\times {\text{A}}_{645})-(4.68\times {\text{A}}_{663})$$

(1)

$$\text{chlorophyll\hspace{0.17em}}b\hspace{0.17em}(\mu \text{g}/\text{mL})=(12.7\times {\text{A}}_{663})-(2.698\times {\text{A}}_{645})$$

(2)

$$\text{total\hspace{0.17em}chlorophyll\hspace{0.17em}}(\mu \text{g}/\text{mL})=\text{chlorophyll\hspace{0.17em}}a+\text{chlorophyll\hspace{0.17em}}b=(20.2\times {\text{A}}_{645})+(8.02\times {\text{A}}_{663})$$

(3)

5. Conclusions

In this study, we generated transgenic Chlamydomonas overexpressing PETF to show that increasing FDX gene expression levels enhance the tolerance of algae to heat stress. Based on the expression levels of PETF transcripts, ascorbate content, H₂O₂ content, chlorophyll content, and survival rates, we concluded that PETF can enhance tolerance to heat stress in Chlamydomonas. These findings imply that the enhancement of crop tolerant to heat stress can be achieved by the regulation of ferredoxin.