Increased CO2 Relevant to Future Ocean Acidification Alleviates the Sensitivity of a Red Macroalgae to Solar Ultraviolet Irradiance by Modulating the Synergy Between Photosystems II and I

While intertidal macroalgae are exposed to drastic changes in solar photosynthetically active radiation (PAR) and ultraviolet radiation (UVR) during a diel cycle, and to ocean acidification (OA) associated with increasing CO2 levels, little is known about their photosynthetic performance under the combined influences of these drivers. In this work, we examined the photoprotective strategies controlling electron flow through photosystems II (PSII) and photosystem I (PSI) in response to solar radiation with or without UVR and an elevated CO2 concentration in the intertidal, commercially important, red macroalgae Pyropia (previously Porphyra) yezoensis. By using chlorophyll fluorescence techniques, we found that high levels of PAR alone induced photoinhibition of the inter-photosystem electron transport carriers, as evidenced by the increase of chlorophyll fluorescence in both the J- and I-steps of Kautsky curves. In the presence of UVR, photoinduced inhibition was mainly identified in the O2-evolving complex (OEC) and PSII, as evidenced by a significant increase in the variable fluorescence at the K-step (Fk) of Kautsky curves relative to the amplitude of FJ−Fo (Wk) and a decrease of the maximum quantum yield of PSII (Fv/Fm). Such inhibition appeared to ameliorate the function of downstream electron acceptors, protecting PSI from over-reduction. In turn, the stable PSI activity increased the efficiency of cyclic electron transport (CET) around PSI, dissipating excess energy and supplying ATP for CO2 assimilation. When the algal thalli were grown under increased CO2 and OA conditions, the CET activity became further enhanced, which maintained the OEC stability and thus markedly alleviating the UVR-induced photoinhibition. In conclusion, the well-established coordination between PSII and PSI endows P. yezoensis with a highly efficient photochemical performance in response to UVR, especially under the scenario of future increased CO2 levels and OA.


INTRODUCTION
Living in the intertidal zone, macroalgae are often exposed to periodic harsh light fluctuations and air exposure associated with changes in tide levels. High levels of solar irradiance can significantly decrease photosynthesis and growth rates in macroalgae (Aline et al., 2006;Martin and Gattuso, 2009;Ji and Gao, 2020), while limited light would entail an insufficient energy supply and thus decrease photosynthesis and growth. Under limited light conditions, longer wavelengths within the range of ultraviolet radiation (UVR,, generally considered to be detrimental to aquatic ecosystems, can be used as light energy for photosynthesis . Moderate levels of UVA (315-400 nm) are beneficial for carbon fixation in several macroalgae Xu and Gao, 2010), and can also act as a signal to stimulate the activity of carbonic anhydrase and nitrate reductase (Viñegla et al., 2006), or prompt morphological development during germination of conchospores (Jiang et al., 2007). Furthermore, the effects of UVR also depend strongly on interactions with other environmental factors. For example, increased ocean temperatures result in stratification and shoaling of the upper mixed layer and thus expose organisms to increased levels of solar photosynthetically active radiation (PAR) and UVR (Häder and Barnes, 2019 and reference therein), and the global warming-induced melting of ice and snow would also aggravate the transmission of UVR and increase UVR exposure in polar regions (Williamson et al., 2019;Neale et al., 2021 and references therein). These interactive effects control the levels of exposure of macroalgae to UVR, and may modulate their photosynthetic performance, production of photoprotective compounds and/or repair mechanisms in response to UVR (see the review by Ji and Gao, 2020 and references therein).
As a consequence of anthropogenic CO 2 emissions, the atmospheric CO 2 concentration has been predicted to increase to above 1,000 μatm by the end of this century (e.g., IPCC, 2014). In addition to possible direct effects of higher aqueous CO 2 , this will also result in an increase in proton concentration in the seawater (a drop in pH from 8.1 to 7.8), known as ocean acidification (OA). A number of previous studies have shown that OA hindered calcification processes (Gao et al., 1993;Semesi et al., 2009;Gao and Zheng, 2010;Büdenbender et al., 2011) and thus exposed calcified algae to more UVR exposure. In contrast, the elevated availability of dissolved inorganic carbon (DIC) in seawater has been reported to stimulate both photosynthesis and growth in a number of non-calcified macroalgae such as in Pyropia sp. (Gao et al., 1991;Zhang et al., 2020), Palmaria sp. (Beer and Koch, 1996), Gloiopeltis sp., Gigartina sp. (Zou and Gao, 2005), Gracilaria sp. (Andría et al., 1999(Andría et al., , 2001, Hypnea sp. (Suárez-Álvarez et al., 2012), and Ellisolandia sp. (Korbee et al., 2014). In addition, the increased DIC would also down-regulate the CO 2 -concentrating mechanisms (CCMs), which utilize HCO 3 − to compensate for the limitation of CO 2 in seawater and maintain high intracellular CO 2 levels for photosynthesis and growth of the macroalgae (e.g., a green algae Ulva prolifera in Xu and Gao, 2012, and a red algae Pyropia yezoensis in Li et al., 2016). Since down-regulation of CCMs is known to save operational energy cost (Raven et al., 2014 and references therein), the energy savings can either stimulate algal growth under low light and increase the risk of photoinhibition under high light (especially with the presence of UVR; see the review by Gao et al., 2019 and references therein).
Pyropia (previously known as Porphyra; Rhodophyta), an economically important marine crop worth ~US$1.3 billion per year (Blouin et al., 2011), has been widely cultivated in both China and other Asian countries. Previously, we showed that UVR inhibited both carbon assimilation and growth of P. yezoensis, while elevated CO 2 exhibited a positive effect and participated in the alleviation of the UVR-induced inhibition . In that work, increases of non-photochemical quenching (NPQ) and UV-absorbing compounds (UVACs) were suggested to dissipate and/or absorb the excess energy originating from UVR, while little attention was paid to the transfer of such absorbed energy. In red algae, phycobilisomes (PBS) form the light-harvesting antennae on the outer surface of thylakoid membranes, in the proximity of photosystem II (PSII), the specific mechanisms for this are unclear but may involve state transitions or mobility of PBS, redistributing the energy between the two photosystems and thus altering photosynthetic electron transport and supply of energy for CO 2 fixation and reduction (Su et al., 2010 and references therein). Moreover, regulation of photosynthetic electron transport, e.g., via alternative electron transport chains, including cyclic electron transport (CET) around photosystem I PSI, photorespiration and the water-water cycle along with reactive oxygen species (ROS)-scavenging systems, has also been supposed to protect photosynthetic systems from photoinhibition/photodamage (Eberhard et al., 2008 andreferences therein, Miyake, 2010). In P. yezoensis, CET has been verified to play a vital role in photoprotection when thalli suffered from dehydration (Gao and Wang, 2012), severe salt stress (Lu et al., 2016;Yu et al., 2018), and irradiance stress (Niu et al., 2016). The active CET not only participates in NPQ, but also alleviates the over-reduction of plastoquinone and, thus, balance the redox state of the photosynthetic electron transport chain (Miyake, 2010).
In the present study, effects of OA and UVR on the photosynthetic performance of P. yezoensis were investigated by growing these algae under incident solar radiation with or without UVR at ambient and elevated CO 2 concentrations projected for future OA by the end of 2100. While high CO 2 and the concomitant OA may have separate effects on algal physiology in nature (Hurd et al., 2020), technically, it is hard to distinguish the specific effects of pH or CO 2 . Moreover, pH and CO 2 covary oppositely even in algal blooms or with progressive OA, thus we did not attempt to disentangle the interactions between these two variables. Our aims are 1) characterized the electron transport flux from PSII to PSIl, 2) examined an alternative electron sink, i.e., CET; and 3) evaluated the coordination between PSII and PSI, under the influences of UVR and OA.

Experimental Treatments and Measurements of UV Irradiance and pH
Thalli of P. yezoensis (Ueda) M.S.Hwang & H.G.Choi were collected from rafts offshore of Gaogong Island (34°43′31′ N, 119°31′57′ E), Lianyungang, Jiangsu Province, China, on December 12, 2017, and transported to the laboratory in a cooled Styrofoam box within 2 h. Following rinsing, thalli of ~0.05 g fresh weight were grown outdoors for 9 days in 1 L open-ended quartz tubes filled with natural seawater, which were partly immersed in a flow-through water bath to maintain the seawater temperature at 8 ± 1°C. The seawater in each tube was continuously aerated (300 ml per min) with air containing 400 ± 20 or 1,000 ± 50 μatm CO 2 , and was renewed every day. The low-CO 2 air was directly obtained with an air pump while the high-CO 2 level was obtained from a CO 2 enricher (HP 1000 G-D, Ruihua Instruments, Wuhan, China), which controls the CO 2 concentration with less than 5% variation. Different radiation treatments were achieved by covering the quartz tubes with Ultraphan film 395 (UV Opak, Digefra, Munich, Germany), Folex 320 film (Montagefolie, Folex, Dreieich, Germany), or Ultraphan film 295 (Digefra), respectively, so that the thalli were exposed to irradiances above 395 nm (PAR alone), above 320 nm (PA, PAR + UVA) and above 295 nm (PAB, PAR + UV-A + B), respectively. Considering the low density of algal blades in the tubes, the self-shading in our present study can be considered minimal. Measurements of photochemical activities (see below) were carried out around 14:00 on the 10th day of treatments. A total of 18 tubes containing different individual thalli were used for measurements, and three independent thalli were used as replicates for each parameter. According to published papers (Mercado et al., 1999;Zou, 2005;Chen et al., 2016Chen et al., , 2017, and also based on our previous experience (Zou et al., 2003;Gao, 2008, 2010), 10 days culture is enough for full acclimation of the photosynthetic and other biochemical traits in Pyropia spp. and other tested marine macroalgae.
The pH NBS was measured at the end of each day by a pH meter (pH 700, Eutech Instruments, Singapore) equipped with an Orion ® 8102BN Ross combination electrode (Thermo Electron Co., United States), which was calibrated with NBS standard buffers every day during the experiment (Thermo Fisher Scientific Inc., United States). Total alkalinity (TA) was measured with a TA analyzer (AS-ALK1, Apollo SciTech, United States) by Gran acidimetric titrations. The values of other carbonate chemistry parameters (total inorganic carbon concentration, TIC, bicarbonate and carbonate ions) were calculated by the Excel program CO2SYS (Pierrot et al., 2006) according to the measured values of TA and pH NBS .
Before the final measurements, the in situ diurnal variations (daytime) of pH and CO 2 were measured. These results showed that the total alkalinity (TA) was around ~2,400 μm throughout the day, pH ranged from ~8.2 to 8.4 and the dissolved CO 2 ranged from about 10 to 13 μm. The maximal and daily average PAR values during the experimental period were 812.6 ± 57.4 and 186.1 ± 35.1 μmol photons m −2 s −1 , respectively, while the corresponding values for UVA were 8.1 ± 0.7 and 1.9 ± 0.3 W m −2 , and that for UVB 0.3 ± 0.03 and 0.1 ± 0.01 W m −2 . PAR, UVA and UVB levels were 635 μmol photons m −2 s −1 and 6.5 and 0.2 W m −2 , respectively, when the following parameters were measured at 14:00 on the 10th day. During the experiment, the enhanced CO 2 level (from 400 to 1000 μatm in the air phase) resulted a pH drop from 8.24 ± 0.03 to 7.92 ± 0.03 (n = 27). While TA remained unaltered, the TIC increased from 2,131 ± 20 to 2,310 ± 20 μm and that of CO 2 from 12 ± 1 to 28 ± 3 μm (n = 27) under the high-CO 2 treatment.

Chlorophyll Fluorescence Measurements and Analyses
A dual-wavelength pulse-amplitude-modulated (PAM) fluorescence monitoring system (Dual-PAM-100, Walz, Effeltrich, Germany) was employed to simultaneously measure the performance of PSII and PSI. To avoid the effect of phycobiliproteins on chlorophyll fluorescence, blue light (440 nm) was used as excitation light in the following measurements. Rapid fluorescence induction kinetics (Kautsky curves) showed a typical polyphasic rise pattern between O (the minimum fluorescence) and P (the maximum fluorescence) during the first second of illumination (Neubauer and Schreiber, 1987). The typical Kaustsky curve plotted against a logarithmic time scale represented different processes of photosynthetic electron transport (Supplementary Figure S1). According to Strasser and Strasser (1995) and Guisse et al. (1995), the fluorescence characterized of several different phases, where the time-specific steps were labeled as O, K (at ~300 μs), J (at ~2 ms), I (at ~30 ms) and P. Fluorescence intensities at different phases were noted as F o , F k , F J , F I and F m . The standardized fluorescence intensity from the O-to P-phase was calculated as V t = (F t −F o )/ (F m −F o ). To assess the donor side activity of PSII, the normalized variable fluorescence at the K-step relative to the amplitude The acceptor side activity of PSII, i.e., the probability that a trapped exciton moves an electron into the electron transport chain beyond Q A − ( y ET O 2 ) and the quantum yield of electron transport (φ Eo ) was calculated as y ET O 2 = 1−V J and φ Eo = (1−F o /F m ) × (1−V J ), respectively. The redox state of inter-photosystem electron carriers and the acceptor side activity of PSI, i.e., the probability that an electron moves from reduced Q A beyond PSI ( y RE O 1 ), and the quantum yield for reduction of the end electron acceptors on the PSI acceptor side (φ Ro ), were calculated as y RE O 1 = 1−V I and φ Ro = (1-F o /F m ) × (1−V I ), respectively. All these parameters were derived from JIP-tests Strasser et al., 2004). According to the theory of energy fluxes in biomembranes (Strasser, 1981), the density of the PSII reaction center per excited cross section (RC/CSo), the absorbed flux (ABS), the trapping flux (TRo), the electron transport flux (ETo), and the dissipated energy flux (DIo) by active reaction centers were calculated as.

P700 Measurements and Analyses
As suggested by Klughammer and Schreiber (1994), the P700 + signal measured with the dual-wavelength (830/875 nm) unit of the instrument was taken as a measure of the redox state of P700. After 10 s exposure to far-red light, a saturation flash was applied to determine the maximum P700 + signal (P m ). The steady-state P700 + signal (P) was monitored under actinic light generated by the instrument at similar PAR levels as the natural sunlight (~800 μmol photons m −2 s −1 ). The 0.8 s saturating flash of ~10, 000 μmol photons m −2 s −1 was applied to induce the maximum P700 + value (P m ′). The effective quantum yield of PSI (YI) was calculated as (P m ′−P)/P m . In Pyropia spp., several published papers have demonstrated that the CET around PSI could account for up to 97.7% of total electron flow when algal blades suffered from severe desiccation (Gao and Wang, 2012). This was thus supposed to be one of the most important alternative electron transport pathway during exposure to stresses (Gao et al., 2013;Yu et al., 2018). Accordingly, our present study paid more attention on the physiological role of CET during the exposure to UVR and high-CO 2 induced OA. CET around PSI was evaluated by the measurement of the re-reduction kinetics of P700 + . After ~10 s exposure to far-red light, the applied saturation flash drives P700 + to combine with electrons, and the initial linear slope of the re-reduction of P700 + indicated the activity of CET.
All measured and calculated parameters are summarised in Table 1.

Statistical Analyses
In the present study, UVR-induced inhibition for a particular parameter was calculated as (P PAR − P PAR + UVR )/P PAR × 100%, where P PAR and P PAR + UVR represent the values of the physiological parameter for the thalli grown under PAR alone or PAR + UVR, respectively. UVB-induced inhibition was derived from the difference in the values between the PAB (PAR + UVA + B) and PA (PAR + UVA) treatments.
Statistical analyses were performed using SPSS 19.0 (SPSS Inc., Chicago, IL, United States). The homogeneity of variance was examined using Levene's test before all statistical analyses. One-way ANOVA and t-test were used to establish differences among treatments. A two-way ANOVA was used to identify the effects of CO 2 concentration, light, UV, and their interactions. Differences were considered to be statistically significant at p < 0.05.

RESULTS
Under the ambient CO 2 conditions (low-CO 2 ), the presence of UVR significantly inhibited the O 2 -evolving complex (OEC) of PSII activities as evidenced by an increase of the variable fluorescence at the K-step of the Kautsky curve relative to the amplitude of F J −F O (W k ; t-test, p < 0.05; Figure 1) and a decrease of the maximum quantum yield of PSII (F v /F m ; t-test, p < 0.05; Figure 2). Furthermore, UVB-induced inhibition of the OEC, with an amplitude of up to ~24%, was significantly higher than that induced by UVA (~16%; t-test, p < 0.05). In contrast, the PSII acceptor side activity (y ET O 2 ; Figure 3A), quantum yield of electron transport (φ Eo ; Figure 3B), PSI donor side activity (y RE O 1 ; Figure 3C), and quantum yield for reduction of PSI acceptor side (φ Ro ; Figure 3D) were significantly increased by UVR, as shown here by the negative inhibition values (t-test, p < 0.05 for these four parameters). However, under the low-CO 2 conditions, the effective quantum yield of PSI showed no significant change (t-test, p = 0.487; Figure 4) between PAR and PAR + UVR treatments, indicating that PSI activity was less affected by UVR. However, an increase in the re-reduction rate of P700 + showed that UVR significantly stimulated the activity of CET around PSI, especially in the presence of UVB, normalized variable fluorescence at the K-step relative to the amplitude of with increasing amplitude by up to ~17% (~7% for UVA and ~ 10% for UVB, respectively; t-test, p < 0.05 for both UVA and UVB treatments; Figure 5). Due to the fact that CET relates to electron transport rate in both PSII and PSI [as it could be calcultated by the difference between ETRI and ETRII (Yamori et al., 2011;Gao and Wang, 2012)], the asynchronous variation between PSI activity and CET was mainly attributed to the decrease of PSII photochemical efficiency. The active CET thus compensates for the loss of linear electron transport rate, maintaining a high efficiency of generating ATP. Analyses of the specific energy fluxes of PSII showed that UVR significantly inhibited the density of PSII reaction centers (RC/CSo), the absorbed photon flux (ABS), the trapping photon flux (TRo) and the electron transport flux (ETo; t-test, p < 0.05 for these four parameters), while there was an up-regulation of the dissipated energy flux (DIo; t-test, p < 0.05; Figure 6).
In the future-simulated high-CO 2 conditions, leading also to ocean acidification (OA), PAR alone did not induce any significant changes in W k and F v /F m (t-test, p = 0.378 and 0.523, respectively; Figures 1, 2), indicating that both OEC and PSII were unaffected. The enhancements of y ET O 2 (Figure 3A), φ Eo (Figure 3B), y RE O 1 (Figure 3C), and φ Ro (Figure 3D) suggested that more electrons were transferred through the intersystem electron carriers under OA (t-test, p < 0.05 for these four parameters). Regarding the downstream electron transport chain, YI (Figure 4) and re-reduction rate of P700 + (Figure 5) increased by up to ~11% and ~ 23%, respectively, implying an up-regulation in PSI and CET (t-test, p < 0.05 for these two parameters). Changes of the specific energy fluxes of PSII indicated the efficiency of active PSII reaction centers were enhanced by OA (t-test, p < 0.05; Figure 6).
A two-way ANOVA analysis showed that both CO 2 concentration, UVR, and their interaction, significantly affected OEC, PSII, the intersystem electron transport and CET activities, but not always PSI ( Table 2). Under the high CO 2 condition, UVR-induced inhibition of both OEC and PSII photochemical efficiency significantly decreased, with UVA-and UVB-induced inhibition of OEC decreased from ~15% to ~9%, and from ~24% to ~11%, respectively (t-test, p < 0.05 for both UVA and UVB treatment); that of PSII by UVA and UVB ranged from ~16% to ~5%, and from ~15% to ~10%, respectively (t-test, p < 0.05 for both UVA and UVB treatment; Figures 1, 2). Although the extent of UVR-induced inhibition on y ET O 2 , φ Eo , y RE O 1 , and φ Ro exhibited significant differences between low-and high-CO 2 conditions (Figure 3), the absolute values of these parameters were less affected (t-test, p = 0.647, 0.548, 0.398 and 0.712 respectively). The significant difference in P700 + re-reduction between low-and high-CO 2 indicated that there was a synergistic effect between increased CO 2 /OA and UVR, the high-CO 2 further enhanced CET activity by up to ~4% and ~ 5% under the influences of UVA and UVB, respectively (t-test, p < 0.05 for both UVA and UVB treatment; Table 2, Figure 5). In PSII, UVR-induced inhibition on the density of PSII reaction centers (RC/CSo), the absorbed photon flux (ABS), the trapping photon flux (TRo), and the electron transport flux (ETo) was alleviated by the high-CO 2 treatment (t-test, p < 0.05 for both UVA and UVB treatment; Figure 6). Meanwhile, UVR-induced up-regulation of dissipated energy flux (DIo) was further enhanced under the high-CO 2 /OA condition (ttest, p < 0.05 for both UVA and UVB treatment; Figure 6).

DISCUSSION
Our results suggest that in the red algae P. yezoensis (Ueda) M. S. Hwang and H. G. Choi, future elevated CO 2 and ocean acidification (OA) can alleviate both UVB-and UVA-induced inhibition on PSII by modulating the synergy between PSII FIGURE 1 | Values (a.u., left pair of bars) and UVR-induced inhibition (%, right two pairs of bars) on the O 2 -evolving complex (OEC) activity (the normalized variable fluorescence at the K-step relative to the amplitude of F J −F o , W k ) of Pyropia yezoensis growing for 9 days at low (~400 μatm, open bars) and high (~1000 μatm, closed bars) CO 2 conditions. Data are means ± SD (n = 3). The symbol "*" indicates a significant (p < 0.05, t-tests) difference between the treatments in each pair.
FIGURE 2 | Values (a.u., left pair of bars) and UVR-induced inhibition (%, right two pairs of bars) of PSII photochemical efficiency (F v /F m ) of P. yezoensis growing for 9 days at low (~400 μatm, open bars) and high (~1000 μatm, closed bars) CO 2 conditions. Data are means ± SD (n = 3). The symbols "*" indicates a significant (p < 0.05, t-tests) difference between the treatments in each pair. and PSI. Such synergy was found to relate mainly to the up-regulation of the intersystem electron transport efficiencies and CET around PSI (see Figure 7). In contrast with highlight-induced over-reduction of inter-photosystem electron transfer carriers (Figure 7A), UVR (especially UVB)-induced photoinhibition, characterized by the inhibition of OEC and PSII (Figure 7B), significantly decreased its quantum yield (Figure 2), which should be responsible for the reduced rates of carbon assimilation and growth ( Figure 7B; Zhang et al., 2020). When grown and acclimated in the high-CO 2 condition (Figure 7C), the well-established coordination between PSII and PSI, as well as the enhanced CET around PSI sustain the efficient electron transport, consequently increasing the resilience of P. yezoensis to PAR and/or UVR.
Previous studies have shown that the presence of UVR would reduce primary productivity in cyanobacteria and of phytoplankton assemblages by about 20% due to the concomitant photoinhibition (Helbling et al., 2003;Neale and Thomas, 2017;Williamson et al., 2019). In our previous study , UVR-induced growth inhibition of P. yezoensis was ~31%, with only about 5% being attributable to UVB, implying that UVR-induced loss of carbon fixation was mainly driven by the negative effects of UVA. However, here, we show that both UVA and UVB significantly inhibited the OEC and PSII, and the presence of UVB markedly exacerbated photoinhibition by 24% for OEC and 15% for PSII (Figures 1, 2). Macroalgae have evolved several adaptive mechanisms to cope with photoinhibition, by increasing NPQ and UVACs Zheng and Gao, 2009;Zhang et al., 2020), enhancing the xanthophyll cycle (Häder et al., 2002;Aigner et al., 2017;Xie et al., 2020) as well as antioxidant systems (Sureda et al., 2008;Li et al., 2010). In the present work, the responses of photosynthetic electron transport to UVR (UVA and UVB) and the related modulations between the photosystems are , panel (C)] and the quantum yield for reduction of PSI acceptor side [φ Ro , panel (D)] of P. yezoensis growing for 9 days at low (~400 μatm, open bars) and high (~1000 μatm, closed bars) CO 2 conditions. Data are means ± SD (n = 3). The symbols "*" indicates a significant (p < 0.05, t-tests) difference between the treatments in each pair.
FIGURE 4 | Values (a.u., left pair of bars) and UVR-induced inhibition (%, right two pairs of bars) of the effective quantum yield of PSII (YI) of P. yezoensis growing for 9 days at low (~400 μatm, open bars) and high (~1000 μatm, closed bars) CO 2 conditions. Data are means ± SD (n = 3). The symbols "*" indicates a significant (p < 0.05, t-tests) difference between the treatments in each pair. speculated to be responsible for the observed asymmetric responses between photoinhibition and growth.
Under the influence of UVR, the deactivation of OEC would lower the efficiency of water splitting, and thus the excess excitation energy would also result in an accumulation of ROS, as well as P680 + (Turcsányi and Vass, 2000;Tyystjärvi, 2008). These oxidized components can damage the D1 protein and lead to PSII photoinhibition (Zsiros et al., 2006). Our present study suggested that UVR inhibited the catalytic manganese cluster of the water-oxidizing complex, which has also been shown in other photosynthetic organisms (Vass et al., 1996;Turcsányi and Vass, 2000). Such damages are correlated with decreased O 2 evolution in the tested species of Pyropia (Supplementary Table S1, Figueroa et al., 1997;Aguilera et al., 1999Aguilera et al., , 2008. Nevertheless, such photoinhibition could lower electron transport from PSII to PSI and thus protect the intersystem electron carriers and PSI from over-reduction and alleviating PSI from photoinhibition (Figures 4, 5, 7C; as suggested also by Larosa et al., 2018).
In view of the impacts of increased CO 2 and OA, a number of previous studies have shown that high CO 2 /OA treatments did benefit O 2 evolution and carbon assimilation in Pyropia spp. (Supplementary Table S2, Gao et al., 1991;Mercado et al., FIGURE 5 | Values (a.u., left pair of bars) and UVR-induced inhibition (%, right two pairs of bars) of CET activity (the P700 + re-reduction rate) of P. yezoensis growing for 9 days at low (~400 μatm, open bars) and high (~1000 μatm, closed bars) CO 2 conditions. Data are means ± SD (n = 3). The symbols "*" indicates a significant (p < 0.05, t-tests) difference between the treatments in each pair. LC and HC stand for low (~400 μatm) and high (~1000 μatm) CO 2 conditions, respectively. P, PA, and PAB stand for PAR only, PAR + UVA, and PAR + UVA + UVB, respectively. A B C FIGURE 7 | Schematic representation of the coordination in P. yezoensis photosynthetic electron transport when exposed to PAR-only (A), or to PAR + UVR under low-CO 2 (B) or high-CO 2 (C) concentrations. The green area indicates a normal state, the dark blue areas indicated a more severe inhibition, the light blue indicates a moderate inhibition, the orange area indicates an up-regulation, and the gray areas represent the unmeasured sites. Black arrows indicate linear electron transport flow, the colored arrows CET around PSI and the orange/red arrows indicate the up-regulation of CET.
1999; Chen et al., 2016Chen et al., , 2017Zhang et al., 2020). Our results showed here that both OEC and PSII of P. yezoensis were less affected under PAR-only conditions, with PSI and CET being significantly up-regulated (Figures 4, 5). In contrast to the donor side photoinhibition induced by UVR, high-light induced photoinhibition is usually related to the over-reduction of intersystem electron carriers (Vass et al., 2005;Tyystjärvi, 2008). In the present work, the enhancement of CET would work as an alternative electron flow sink, together with the oxidized PSI, promoting the intersystem electron carriers to become oxidized, as reflected in negative inhibition (i.e., enhancement; Figure 3). Moreover, the up-regulated CET could also regulate the energy balance by consuming NADPH and generating ATP; NADP + can also accept more electrons transferred from PSII and then oxidize the intersystem electron carriers (as suggested by Bukhov and Carpentier, 2004;Rumeau et al., 2007;Gao and Wang, 2012;Yu et al., 2018), thus contributing to the supply of energy for carboxylation.
The interactive effects of UVR and CO 2 enrichment have been previously reported to be species-specific and UV-intensitydependent (Gordillo et al., 2015;Ji and Gao, 2020 and references therein). A moderate UVR exposure amplified the positive effects of CO 2 and OA on the red coralline algae Corallina officinalis under low PAR (Yildiz et al., 2013), while the synergistic effect of incident solar UVR and OA resulted in a decrease in both photosynthesis and calcification of the coralline algae Corallina sessilis (Gao and Zheng, 2010). In P. yezoensis, our results suggested that the increased CO 2 and associated OA alleviated UVR-induced inhibition of the photosynthetic processes. Under the high-CO 2 conditions, the up-regulation of CET would generate a higher trans-thylakoid proton gradient (ΔpH), which increase NPQ and could produce ATP for carbon assimilation. Moreover, the higher ΔpH-induced acidification of the lumen could also drive a Ca 2+ /H + antiport to sequester Ca 2+ into the lumen (Krieger and Weis, 1993;Ettinger et al., 1999), and thus aid in maintaining OEC stability, as reflected by our data showing alleviation of UVR-induced OEC inhibition by high CO 2 treatments (Figure 1). Accordingly, OEC inhibition-induced photooxidative damage was significantly decreased, as evidenced by the increase of PSII photochemical efficiency (Figure 2), as well as the enhancement of the efficiency of the active PSII reaction center (Figure 6). Similar response was also observed in a tropical tree species (Huang et al., 2016) and marine angiosperm (Tan et al., 2020).
As mentioned above, the elevated DIC/CO 2 in seawater can down-regulate the CCMs, which is also true for P. yezoensis (Li et al., 2016). However, little attention has been paid to the effects of high PAR/UVR as well as its combined effects with high CO 2 -induced OA. According to several published papers, high PAR/UVR affects the CCMs in different ways, and the effect is species-specific and light intensity dependent. For example, UVR enhanced the activity of extracellular carbonic anhydrase in Skeletonema costatum and thus enhanced its CCM (Wu and Gao, 2009), while a short-term exposure to UVR did not affect the inorganic carbon acquisition in Dunaliella tertiolecta (Beardall et al., 2002). Considering the fact that inorganic carbon acquisition is the prerequisite for carbon assimilation, which is the main photosynthetic electron sink, investigations of CCMs under high PAR/UVR and high CO 2 are expected in future studies.
Under natural conditions in sea-farming areas, macroalgae experience low pH and high CO 2 during the early morning period due to respiratory CO 2 release at night. Our results imply that the red algae P. yezoensis can take advantage of the concomitant changes in the pCO 2 and pH to cope with increasing UV exposure following sunrise. In addition, progressive OA associated with CO 2 rise could positively enhance the alga's photosynthesis and growth even under the influences of UVR, owing to the modulated synergy between PSII and PSI. 2 | Two-way ANOVA for the effects of CO 2 (~400 and ~ 1,000 μatm) and irradiance quality photosynthetically active radiation (PAR, PAR + UVA and PAR + UVA + UVB) on the OEC activity (W k ), photosystem II (PSII) photochemical efficiency (F v /F m ), intersystem electron transport efficiencies ( ET2O ψ , φ Eo, RE1O ψ , φ Ro ), photosystem I (PSI) activity (YI) and CET activity (P700 + re-reduction).

DATA AVAILABILITY STATEMENT
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.

AUTHOR CONTRIBUTIONS
DZ: conceptualization, data collection and curation, data analysis, visualization, writing -original draft, and review and editing. JX: data collection and curation and review and editing. SB and JB: data analysis, formal analysis, and writing -review and editing. CZ: formal analysis and writing -review and editing. KG: conceptualization, funding acquisition, project administration, writing -original draft, and review and editing. All authors contributed to the article and approved the submitted version.

FUNDING
This study was supported by the National Natural Science Foundation (41720104005, 41721005, and 41890803).