DOI: 10.1007/s10535-013-0374-5 BIOLOGIA PLANTARUM 58 (1): 9-17, 2014 REVIEW Brassinosteroids and their role in response of plants to abiotic stresses Q. FARIDUDDIN1*, M. YUSUF1,2, I. AHMAD2, and A. AHMAD1 Plant Physiology and Biochemistry Section, Department of Botany1, and Department of Agricultural Microbiology2, Faculty of Agricultural Sciences, Aligarh Muslim University, Aligarh-202002, Uttar Pradesh, India Abstract Brassinosteroids (BRs) are polyhydroxylated steroidal plant hormones that play pivotal role in the regulation of various plant growth and development processes. BR biosynthetic or signaling mutants clearly indicate that these plant steroids are essential for regulating a variety of physiological processes including cellular expansion and proliferation, vascular differentiation, male fertility, timing senescence, and leaf development. Moreover, BRs regulate the expression of hundreds of genes, affect the activity of numerous metabolic pathways, and help to control overall developmental programs leading to morphogenesis. On the other hand, the potential application of BRs in agriculture to improve growth and yield under various stress conditions including drought, salinity, extreme temperatures, and heavy metal (Cd, Cu, Al, and Ni) toxicity, is of immense significance as these stresses severely hamper the normal metabolism of plants. Keeping in mind the multifaceted role of BRs, an attempt has been made to cover the various aspects mediated by BRs particularly under stress conditions and a possible mechanism of action of BRs has also been suggested. Additional key words: antioxidant system, drought, heavy metals, high temperature, low temperature, oxidative stress, photosynthesis. Introduction Plants constantly regulate their developmental and physiological processes in response to various internal and external stimuli. Studies have indicated that biological processes are integrated by multiple hormonal signals, and stresses induce the activities of different hormonal signaling pathways in plants (Teale et al. 2008). Out of the recognized categories of plant hormones, much attention has been focused on auxins, cytokinins, gibberellins, abscisic acid, and ethylene. Furthermore, brassinosteroids (BRs) are a group of steroidal hormones that play pivotal roles in wide range of developmental phenomena including cell division and cell elongation in stems and roots, photo-morphogenesis, reproductive development, leaf senescence, and also in stress responses (Choudhary et al. 2012). The identification of plant endogenous steroidal hormones is the result of nearly 30 years of efforts to identify novel growth-promoting substances present in pollen grains of different plant species (Steffens 1991). Mitchell et al. (1970) showed that the growth stimulating activity was found in the organic solvent extract of pollen from Brassica napus and the unidentified active compound was named as brassin. The specific growth promoting effects of the brassin have been reflected in many bioassays including the bean second-internode bioassay (Mandava 1988). Based on their ability to cause marked changes in growth and differentiation at low concentrations, Mitchell et al. (1970) proposed that brassins constituted a new family of plant hormones known as brassinosteroids (BRs). Further work demonstrated that brassinosteroids not only induce stem elongation, they also increase total biomass and yield. Although brassinosteroids were known to be endogenous regulators that induce dramatic growth ⎯⎯⎯⎯ Submitted 10 October 2012, last revision 24 June 2013, accepted 29 July 2013. Abbreviations: 28norCS - 28-norcasterone; 6deoxoCS - 6-deoxocasterone; 6-deoxoTY - 6-deoxotyphasterol; BL - brassinolide; BRI1 - brassinosteroids insensitive I; BRs - brassinosteroids; CAT - catalase; CS - castasterone; EBL - 24-epibrassinolide; HBL 28-homobrassinolide; LRR - leucine rich repeat; MT-sHSP - mitochondrial small heat shock protein; NPR1 - non-expressor of pathogenesis related genes 1; P5C - pyrroline-5-carboxylase; POX - peroxidase; PR-1 - pathogenesis related 1; PS II - photosystem II; ROS - reactive oxygen species; S/T kinase - serine/threonine kinase; SOD - superoxide dismutase; TE - teasterone; TY - typhasterol. Acknowledgements: M. Yusuf gratefully acknowledges the financial assistance rendered by the University Grant Commission, New Delhi, India in a form of the Dr. D.S. Kothari Postdoctoral Fellowship [F.4-2/2006(BSR) 13-608/2012/BSR]. * Corresponding author; fax: (+91) 571 2702016, e-mail: [email protected] 9 Q. FARIDUDDIN et al. effects in the bean second-internode bioassay, they were not immediately accepted as plant hormones, as their role in normal plant growth and development remained elusive for many years. Young growing tissues contain a higher content of BRs than mature tissues. Pollen and immature seeds are the richest sources of BR with a range of 1 - 100 μg kg-1(fresh mass), whereas shoots and leaves usually possess lower amounts of 0.01 - 0.1 μg kg-1(f.m.). Clouse and Sasse (1998) and Sasse (2003) disclosed that BRs are required for normal growth and development including shoot and root growth (Nemhauser et al. 2004), vascular differentiation (Caño-Delgado et al. 2004), fertility and seed germination (Taiz and Zeiger 2004). Such responses may be involved in cell elongation (Catterou et al. 2001), vascular differentiation (Ashraf et al. 2010), xylem formation in epicotyls (Zurek et al. 1994), and also in the regulation of expression of several genes involved in xylem development. However, a great diversity exists in effects of BRs on pigments and photosynthesis. Their influence on chlorophyll content depends to some extent on the mode of application of BRs and the relationship between exogenously applied BRs and the basal chlorophyll content in various crop species (Gomes 2011). In addition to this, BRs have the ability to confer resistance to plants against various biotic and abiotic stresses, such as salinity (Hayat et al. 2010), water stress (Fariduddin et al. 2009a), temperature extremes (Fariduddin et al. 2011, Gomes 2011), and heavy metals (Bajguz and Hayat 2009, Fariduddin et al. 2009b, Yusuf et al. 2011, 2012). In the following sections, the relationship between BRs with oxidative stress, antioxidant system, and further details of the role of BRs in relation to various abiotic stresses are discussed. Apart from this, we tried to suggest a possible mode of action of BRs established till date. Relationship of brassinosteroids with oxidative stress and antioxidant system Like all aerobic organisms, plants have also welldeveloped metabolic pathways to utilize its energetic potential in the presence of oxygen (Navrot et al. 2007). One potentially damaging effect of this fact is the deleterious production of reactive oxygen species (ROS) during normal respiration, photosynthesis, and nitrogen fixation (Mittler et al. 2011). Inhibition of the antioxidant systems leads to oxidative stress causing degradative changes of lipids, proteins, and nucleic acids (Prasad 2004) and to disruption of the redox homeostasis (Gille and Sigler 1995). Moreover, when plants are subjected to stresses, a variety of ROS are generated, such as superoxide radical, hydroxyl radical, and hydrogen peroxide. ROS can undergo a series of oxidation/reduction reactions known as the Halliwell-Asada pathway (Gratao et al. 2006). To defend themselves, plants contain antioxidant enzymes, such as superoxide dismutase (SOD), catalase (CAT), guaicol peroxidase (POX), ascorbate peroxidase (APX), monodehydroascorbate reductase (MDHAR), glutathione reductase (GR), and glutathione peroxidase (GPX) (Ruley et al. 2004, Simonovicova et al. 2004), and non-enzymatic antioxidants, namely ascorbate, gluthathione, α-tocopherol, and carotenoids (Vardhini and Rao 2003, Ozdemir et al. 2004, Sharma and Dubey 2005). However, little is known about the role of BRs in the plant response to oxidative stress. It was shown that application of BRs modifies antioxidant enzymes as well as non-enzymatic antioxidants. When maize seedlings treated with brassinolide (BL) are subjected to water stress, the activities of SOD, CAT, APX, as well as ascorbic acid and carotenoid content increase (Li et al. 1998). On the other hand, BRs enhance the activity of CAT and reduce the activities of POX and ascorbic acid oxidase under osmotic stress in sorghum (Vardhini and Rao 2003) and also regulate secondary metabolism in tomato which may enhance tolerance to phenanthrene 10 (Ahammed et al. 2013). Rice seedlings exposed to salinity stress and treated with BRs show a significant increase in the activities of CAT, SOD, and GR and a slight increase in the APX activity (Nunez et al. 2003). Epibrassinolide (EBL) treatment, at least in part, improves the tolerance of saltsensitive rice seedlings to short-term salt stress. The differences in activities of antioxidant enzymes in saltsensitive rice cultivar suggest that the increased salt stress tolerance in sensitive seedlings induced by EBL could be due to an increased APX activity (Ozdemir et al. 2004). Treatment of Chlorella vulgaris with brassinolide increases activities of CAT, GR, and APX and a content of ascorbic acid, carotenoids and glutathione (Bajguz and Hayat 2009). A treatment of tomato leaf discs exposed to high temperature by EBL leads to high activities of CAT, POX, and SOD (Mazorra 2002). It has been shown that the Arabidopsis mutant det-2, which is blocked in the biosynthetic pathway of BRs, has significantly thicker leaves, thicker cuticle and cell walls in epidermis and mesophyll, increased stomatal density, and more compact leaves due to smaller intercellular spaces than the wild-type when grown under normal conditions (Choe 2006). However, an addition of BL to the growth medium results in leaves that are more similar in morphology to those of the wild type. It has also been demonstrated that ATPA-2 and ATP-24, genes encoding peroxidases, are constitutively up-regulated in the det-2 Arabidopsis mutant (Goda et al. 2002). Furthermore, oxidative stress-related genes encoding MDHAR and thioredoxin, cold and drought stress response genes COR-47 and COR-78, and heat stress-related genes hsp83, hsp70, hsf3, hsc70-3, and hsc70-G7 have been identified by a microarray analysis of either BR-deficient or BR-treated plants (Mussig et al. 2002). The enhanced oxidative stress resistance in det-2 plants correlates with a constitutive increase in the SOD activity and increased BRASSINOSTEROIDS UNDER ABIOTIC STRESSES transcription of the CAT gene. Therefore, a possible explanation for the fact that the det-2 mutant exhibits an enhanced oxidative stress resistance is that the long-term BR deficiency in the det-2 mutant results in a constant physiological stress that, in turn, activates the constitutive expression of some defense genes and, consequently, the activities of related antioxidant enzymes. It may be suggested that endogenous BRs in wild-type plants somehow act to repress the transcription or post- transcription activities of the defense genes to ensure the normal growth and development of plants. However, it is still unclear whether BRs directly or indirectly modulate the responses of plants to oxidative stress (Cao et al. 2005). Moreover, BRs induce stress tolerance by triggering the accumulation of apoplast H2O2 which subsequently up regulates the antioxidant system (Jiang et al. 2012). Water stress Water stress is characterized by a reduction of water content and leaf water potential, closure of stomata, and decreased growth. Severe water stress may result in the arrest of photosynthesis, disturbance of metabolism and finally the death of plant (Jaleel et al. 2008). However, application of EBL or HBL prior to water stress results in increased root nodulation, zeatin content, and nitrogenase activity in unstressed Phaseolus vulgaris plants and also ameliorates stress-induced decline in the same parameters. Moreover, EBL was relatively more effective than HBL (Upreti and Murti, 2004). Arabidopsis thaliana and Brassica napus seedlings grown in nutrient solution containing 1 µM EBL and then transplanted to sand were subjected to a drought stress by withholding water for 96 h (Arabidopsis thaliana) or 60 h (Brassica napus). In this case, an EBL treatment enhances seedling tolerance to drought stresses in both species (Kagale et al. 2007). The ability of EBL to confer tolerance of plants to a variety of stresses was confirmed by the analysis of expression of drought stress marker genes (Kagale et al. 2007). In addition, Li et al. (2012) reported that EBL induces changes in antioxidative enzyme activities and content of antioxidant and so improve plant growth under drought stress. Leaf wilting, reduction in growth, and complete drying of some seedlings are frequently observed in untreated, but are considerably reduced in EBL-treated seedlings. In leaves of soybean drought stressed plants, a BRs treatment increases the maximum quantum yield of photosystem II (PS II), the activity of ribulose-1,5-bisphosphate carboxylase/oxygenase, the water potential, the content of soluble sugars and proline, and the activities of POX and SOD in comparison with a drought stress alone. BRs also decrease the malondialdehyde content and electrical conductivity of leaves under drought stress, and increase biomass accumulation and a seed yield in both control and drought stressed soybean plants (Zhang et al. 2008). Moreover, Fariduddin et al. (2009a) reported elevated activities of CAT, POX, SOD, and an elevated proline content in mustard plants treated with HBL and/or exposed to drought stress. This study shows that BR can be used to minimize the loss of yield in mustard caused by water deficits. However, further investigation is necessary for an explanation of the mechanism by which BRs confer tolerance to water stress. Salinity Salinity is a major abiotic stress affecting growth, development and productivity of plants. It causes an osmotic stress, ionic toxicity, and also disturbs the uptake and translocation of mineral nutrients (Turkan and Demiral 2009). Proline accumulates in plants exposed to salinity and serves as osmolyte (Ashraf and Foolad 2007) and a stress signal influencing adaptive responses (Lin and Kao 2007). Under salinity and drought, a proline accumulation is dependent on the activity of Δ1-pyrroline-5-carboxylate synthetase (P5CS), a rate limiting enzyme in the proline biosynthesis, and the activity of proline dehydrogenase (PDH) which catalyzes proline degradation. Özdemir et al. (2004) reported that a treatment of seeds of salt-sensitive rice cv. IR-28 with EBL improves seedling growth, alleviates lipid damage, and decrease proline accumulation compared to the seedlings treated with NaCl alone. However, except for APX, EBL does not increase the activities of POX, CAT, and GR under salinity. Moreover, Kagale et al. (2007) demonstrated that EBL has an ability to ameliorate NaCl-induced inhibition in seed germination of Arabidopsis thaliana and Brassica napus. The application of BRs increases the accumulation of proline and enhances activities of antioxidant enzymes in salt stressed Cicer arietinum (Ali et al. 2007) and Vigna radiata (Hayat et al. 2010). In addition, an EBL application counteracts the salt stress-induced deterioration of growth in eggplant (Ding et al. 2012) and grain yield inhibition in wheat (Ali et al. 2008b). Divi et al. (2010) reported that the redox-sensitive protein NPR1 (non-expressor of pathogenesis-related genes1) is likely a critical component of an EBL-mediated increase in salt tolerance, but it is not required for the EBL-mediated induction of PR-1 (pathogenesis-related 1) gene expression. 11 Q. FARIDUDDIN et al. High-temperature stress High temperature stress is a serious threat to crop production worldwide (Hopkins 1995). High temperature severely damages the mesophyll cells and increases the permeability of plasma membrane, e.g., in grapes (Zhang et al. 2005), and also reduces water availability (Simoes Aranjao et al. 2003), thus affecting leaf water potential and photosynthesis that are considered as the most important temperature sensitive processes (Bery and Björkman 1980). However, tomato plants treated with EBL were found more tolerant to high temperature than untreated plants (Singh and Shono 2005) and this could be due to a higher accumulation of mitochondrial small heat shock proteins (MT-sHSP) in EBR treated tomato under temperature stress, and also improved photosynthetic efficiency. In tomato cv. Amalia treated with EBL and a polyhydroxylated spirostanic analog MH-5, a SOD activity increased at both 25 and 40 °C (Mazorra et al. 2002), and MH-5 was more prominent in its effect. Moreover, Ogweno et al. (2008) showed that application of EBL to tomato plants before exposure to high temperature protects Rubisco and other enzymes involved in the Calvin cycle and RuBP regeneration under a heat stress. Furthermore, Arabidopsis thaliana seedlings were exposed to 43 °C in the presence or absence of EBL for 1, 2, 3, or 4 h and then recovered at 22 °C for 7 d. Seedlings exposed to the 2-, 3-, or 4-h heat stress exhibit increasing bleaching, whereas EBL-treated seedlings show bleaching only after 4 h of the heat stress (Kagale et al. 2007). Low-temperature stress Low temperature (chilling and frost stress) is a major limiting factor for the productivity of plant indigenous to tropical and subtropical climates (Saltveit 2001). Chilling stress has a direct impact on the photosynthetic apparatus, essentially by disrupting the thylakoid electron transport, the carbon reduction cycle, and the stomatal control of CO2 supply, together with an increased accumulation of sugars, peroxidation of lipids, and disturbance of water balance (Allen and Ort 2001). A treatment with EBL partially recovers the growth of mung bean subjected to a chilling stress and 17 proteins (involved in methionine assimilation, ATP synthesis, cell wall construction, etc.) down-regulated by chilling are up-regulated (Huang et al. 2006). EBL injected into cotyledons or primary leaves of rape seedlings diminishes a cold-induced increase in membrane permeability (Janeckzo et al. 2007). Furthermore, the seedlings exposed to 2 °C and treated with EBL have a significantly higher pigment content in leaves as compared to a control, but at 20 °C, there is no difference in the pigment content between leaves injected with EBL or water. Brassica napus and Arabidopsis thaliana grown on a nutrient solution containing EBL were exposed to a cold stress by transferring seedlings to a growth chamber set at 2 °C for 3 d. The transcription analysis indicates that cold-related genes accumulate to higher levels in the plants treated with EBL (Kagale et al. 2007). Furthermore, a study conducted by Xia et al. (2009) indicates the involvement of EBL in enhancing activation of Rubisco and expression of photosynthetic genes in cucumber seedlings subjected to a chilling stress. Heavy metal stress Brassinosteroids have ability to regulate the uptake of ions into plant cells and can be used to reduce the accumulation of heavy metals and radioactive elements in plants. Moreover, BRs also minimizes the toxic effects and symptoms generated by excess of heavy metals (Bajguz and Hayat 2009) Cadmium is extremely toxic to plants even in traces. It retards the biosynthesis of chlorophyll, alters water balance, decreases activities of various enzymes, favors stomatal closure, induces oxidative stress, and slows down the rate of photosynthesis. Cd inhibits both the “light” and “dark” reactions of photosynthesis, but the Calvin cycle is most sensitive. The inhibition of photochemical processes by Cd may mainly result from the limitation in the use of ATP and NADPH in the Calvin cycle (Vassilev and Yordanov 1997). Seedlings of winter rape were cultured in vitro on media containing EBL and Cd (Janeckzo et al. 2005). After 14 d of growth, the kinetics of chlorophyll a fluorescence and the content 12 of photosynthetic pigments and Cd in cotyledons were measured. Cd was strongly accumulated but its content in cotyledons was 14.7 % lower in the presence of EBL. Neither Cd nor EBR influenced the content of Chl a, Chl b, and carotenoids. The number of active reaction centres of photosystem II decreased by about 21.0 % and the electron transport by about 17.1 %. Simultaneously, under the influence of Cd, the activity of O2 evolving centers diminished by about 19.5 % and energy dissipation increased by about 14.6 % (Janeczko et al. 2005). The change in growth and photosynthesis of plants subjected to a Cd stress and the role of HBL was also verified by Hayat et al. (2007) in Brassica juncea. They observed that plants fed with Cd alone exhibited a decline in growth, the activity of carbonic anhydrase, the content of chlorophyll, net photosynthetic rate, nitrate content, the activity of nitrate reductase, and sugar content. These effects are overcome if stressed plants are sprayed with HBL. The activities of CAT, POX, and SOD and the BRASSINOSTEROIDS UNDER ABIOTIC STRESSES content of proline increases in Cd-treated plants and especially in mustard plants also supplemented with HBL (Bajguz and Hayat 2009). The effects of EBL and HBL on seed germination and seedling growth of radish under Cd stress were studied by Anuradha and Rao (2007a). Both the BRs (EBL or HBL) cause a considerable increase in seedling growth under the stress and restore their growth to the level of unstressed control seedlings. Beside this, BR enhanced proline accumulation and CAT, APX, GPX, and SOD activities, whereas reduced POX and ascorbic acid oxidase activities. Moreover, lipid peroxidation induced by Cd was reduced with the supplementation of BRs (Anuradha and Rao 2007). Hasan et al. (2008) revealed that the negative effects of Cd were overcome by foliar application of HBL through increased accumulation of proline and activities of CAT, POX, and SOD). Among the pollutants of agricultural soils, copper has become increasingly hazardous due to its involvement in fertilizers, fungicides, and pesticides. The high content of Cu may be phytotoxic and may cause an inhibition of plant growth or even death. When Brassica juncea seeds are treated with EBL before germination and then submitted to a Cu stress, there is an improvement in shoot emergence and plant biomass production, but reduced Cu uptake and accumulation (Sharma and Bhardwaj 2007). In addition, Fariduddin et al. (2009a) reported that the activities of SOD, CAT, and POX, and proline content increase in response to a Cu stress and more after a HBL treatment. Therefore, it may be suggested that the elevated activity of the antioxidant system by HBL may be at least in part responsible for conferring resistance against Cu stress in Brassica juncea reflected in the improvement of plant growth and photosynthesis in the presence of Cu. The aluminum toxicity is the major growth-limiting factor for crop cultivation on acidic soils. Seedlings of mung bean were subjected to an Al stress and sprayed with EBL or HBL (Ali et al. 2008a). The activities of SOD, CAT, and POX, and proline content increased in response to the Al stress and more in the HBL or EBL treated plants. The increase in the Al resistance conferred by BRs was reflected in the improvement of plant growth, photosynthesis, and related processes in the presence of Al. It was also noticed that EBL is more effective than HBL. Other study verified that BLs promote growth of mung bean seedlings under an Al stress (Abdullahi 2003). EBL significantly increases the fresh masses of shoots and roots, and chlorophyll content in mung bean under an Al stress (Ali et al. 2008a). Although nickel is an essential element, its high concentration is toxic and inhibits photosynthesis, respiration, the activities of enzymes, and protein content. The plants of Brassica juncea supplied with 50 or 100 µM Ni were subsequently sprayed with HBL (Alam et al. 2007). The plants treated with Ni alone exhibited reduced growth, net photosynthetic rate, the content of chlorophyll, and the activities of nitrate reductase and carbonic anhydrase, whereas the activities of POX and CAT and proline content increased. Spraying with HBL partially neutralizes the toxic effect of Ni on most of the parameters. Also, seeds of Brassica juncea soaked in solutions with different concentrations of HBL were subjected to a Ni stress (Sharma et al. 2008). The growth of seedlings was inhibited by Ni and this reduction was restored by the HBL treatment. The protein content and activities of CAT, GR, APX, SOD, and GPX were also increased by the HBL treatment. Seed germination and seedling growth is significantly reduced by the Ni treatment but the HBL treatment enhanced germination percentage as well as shoot and root lengths in Ni stressed as well as unstressed seedlings (Yusuf et al. 2011), and EBL also increases the nitrogen metabolism of Vigna radiata plants under different concentrations of Ni (Yusuf et al. 2012). Possible mode of brassinosteroids action The mechanism of action of BRs has been an attractive target for many researchers but it is still far from final solution. Considering the high variability of the physiological effects of BRs, it is believed that more than one molecular mechanism of their action exists. Two main aspects of the primary mechanism have to be considered: 1) the effects of BRs on the biosynthesis of different enzymes via their effects on gene expressions and 2) the effects of BRs on membrane properties. It is well documented that steroids function as signaling molecules both in animals and plants, and BRs in plants are perceived by a cell surface receptor kinase, brassinosteroid-insensitive 1 (BRI1). EBL and HBL, the most active BRs in bioassays, bind to the extracellular domain of the BRI1 receptor. BRI1 is the plasma membrane localized leucine-rich repeat (LRR) receptor of a serine/threonine (S/T) kinase (Friedrichsen et al. 2000). The LRR receptor kinases constitute the largest receptor class predicted in the Arabidopsis genome, with over 230 family members. This family has a conserved domain structure composed of a N-terminal extracellular domain with multiple tandem (adjacent) LRR motifs, a single trans-membrane domain, and a cytoplasmic kinase domain with specificity towards serine and threonine residues. In case of BRI1, the number of LRRs is 25. BRI1 has also a unique feature that is required for BR binding, a stretch of amino acids called an island domain that interrupts the LRRs between LRRs 21 and 22 (Kinoshita et al. 2005). This domain plus the flanking LRR22 compose the minimum binding site for BRs. BL binding to BRI1 triggers the interaction between BRI1 and BRI1 associated receptor kinase 1 (BAK1). BRI1 is phosphorylated at multiple sites along with its intracellular domain, some of them have been 13 Q. FARIDUDDIN et al. shown to regulate receptor activity (Choudhary et al. 2012). The BR signal is then transmitted to the cytoplasm by an unknown mechanism where it inhibits brassinosteroid-insensitive 2 (BIN2) which is a negative regulator of the BR biosynthetic pathway. BIN2 is a protein kinase that interacts with and phosphorylates two nearly identical transcription factors, BRI 1-EMS supressor 1 (BES1) and brassinazole resistant 1 (BZR1), negatively regulating their activities. BRI 1 supressor 1 (BSU1) dephosphorylates BES1 and BZR1 to counteract the effect of BIN2. BRs regulate the expression of hundreds of genes. A significant portion of the unregulated genes is predicted to play a role in growth processes. The BES1 binding activity and expression of its target genes are enhanced synergistically by BES1interacting MYC-like1 (BIM1). B1M1 is another transcription factor that dimerizes with BES1 and increases its activity. Genes that are down-regulated by BRs include several BR biosynthetic genes. BZR1 binds to specific elements in their promoters to repress their activity. The gene repression by BZR1 represents a negative feedback loop for the regulation of growth by BR (Fig. 1) (Wang et al. 2006, Kim and Wang 2010). Fig. 1. BR binding to BRI-1 leads to decrease in an active BIN2 level; inactivated BIN2 favors the BR induced genes by transcription factor BES1 which binds E-box elements to activate the expression of BR induced genes leading to physiological or morphological changes. Alternatively, binding active BZR1 to CGTG(T/C)G sequences (mostly occurring at the promoter of BR biosynthetic genes) represses the BR biosynthetic pathway (dotted). Abbreviations: BR - brassinosteroids, LRRRK - leucine rich repeat receptor like kinase, BRI1 - BR receptor insensitive 1, BAK1 - BRI1-associated receptor kinase 1, BIN2 - brassinosteroid insensitive 2, BES1 - bril1 EMS-suppressor 1, BZR1 - brassinazole resistant 1, BSU1 - BRI1 suppressor 1, BIM2 - BES1-interacting-Myc-like 2. Adapted from Yuzuf (2011). Concluding remarks and future perspectives The end of the 20th and particularly the beginning of the 21st centuries brought unquestionable evidence that BRs have the ability to improve yield quantity and quality of various crop species, and also to protect plants against various kinds of stresses. However, although several 14 attempts to resolve the actual relationship between these phytohormones and functioning various parts of the photosynthetic apparatus have been made, our knowledge on the mode of BR actions in the regulation of photosynthetic processes is still far from being complete. BRASSINOSTEROIDS UNDER ABIOTIC STRESSES So far, it seems that the main site of BR impacts on photosynthesis is probably the photosynthetic carbon reduction cycle and that BRs can perhaps somehow affect the activation state of Rubisco. We can also speculate about the possible effect of BRs on the activity of carbonic anhydrase. The challenges that we are expected to face in order to elucidate the relationship between BRs and photosynthesis are: 1) the detailed examination of participation of these phytohormones in the development of photosynthetically active chloroplasts; 2) the analysis of the role of BRs in photosynthetic electron transfer; 3) the determination of BR influences on all enzymes participating in photosynthetic CO2 fixation (not only in plants with the C3 pathway but also with the C4 and CAM pathways) to clarify whether this part of photosynthesis really serves as the main target for the action of BRs; 4) more comprehensive BR structure analyses which provide reasons why some photosynthetic characteristics seem to be affected only by a specific BR type; 5) to answer a question why the effect of BRs on photosynthesis is more pronounced in plants subjected to unfavourable environmental factors; 6) more frequent utilization of modern methods of molecular and cell biology including various “omics” technologies to enhance our knowledge on BR roles in the regulation of photosynthesis at the cellular level. 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