NADP-malate dehydrogenase from unicellular green alga Chlamydomonas reinhardtii. A first step toward redox regulation?

The determinants of the thioredoxin (TRX)-dependent redox regulation of the chloroplastic NADP-malate dehydrogenase (NADP-MDH) from the eukaryotic green alga Chlamydomonas reinhardtii have been investigated using site-directed mutagenesis. The results indicate that a single C-terminal disulfide is responsible for this regulation. The redox midpoint potential of this disulfide is less negative than that of the higher plant enzyme. The regulation is of an all-or-nothing type, lacking the fine-tuning provided by the second N-terminal disulfide found only in NADP-MDH from higher plants. The decreased stability of specific cysteine/alanine mutants is consistent with the presence of a structural disulfide formed by two cysteine residues that are not involved in regulation of activity. Measurements of the ability of C. reinhardtii thioredoxin f (TRX f) to activate wild-type and site-directed mutants of sorghum (Sorghum vulgare) NADP-MDH suggest that the algal TRX f has a redox midpoint potential that is less negative than most those of higher plant TRXs f. These results are discussed from an evolutionary point of view.     

Thioredoxin and Redox Control within the New Concept of Oxidative Signaling

During the last decade, plant thioredoxins (TRX) h-type have been shown to be implicated in several new roles like the protection against the oxidative stress by their ability to reduce some antioxidant proteins as peroxiredoxins (PRX) or methionine-sulphoxide-reductases (MSR). However, the concept of the oxidative stress is changing and this fact raises the question of the TRX roles in this new context. In the January issue of Plant Physiology, we have presented two TRXsh from Pisum sativum differently involved in the control of the redox status. PsTRXh1 is an h-type TRX that acts by reducing classical antioxidant proteins. PsTRXh2 seems to be also involved in redox control, however it could act contrary to its counterpart h1. Both proteins may play antagonistic roles in pea in order to lead a better control of the redox status.Key Words: abiotic stress, oxidative signalling, thioredoxins, Pisum sativum, ROSHigh concentration of reactive oxygen species (ROS) in plant cells involve the activation of different antioxidant systems which reestablish the redox status leading to better physiological conditions. On the other hand, it has been well established that at certain levels, the ROS act as second messengers in signal transduction cascades in several processes in plant cells.¹ At the light of these events, it has been proposed the reevaluation of the concept of oxidative stress towards “oxidative signalling.”² This concept involves all the cellular mechanisms that let the plant cells sense and act in response to modified environmental conditions. Several cellular systems are involved in such role, and in these last years, plant TRXs have been shown to be involved in several number of metabolic pathways linked to the regulation of the redox imbalance,³ mainly for the case of the h-type cluster of the TRXs.^4–6In our last work,⁷ we have described two pea TRXs of the h-type cluster, PsTRXh1 and PsTRXh2 that are differentially, and even antagonistically, involved in the redoxregulation control, probably through their interaction with different target proteins. We proposed that PsTRXh1 might be involved in the control of the ROS levels in pea tissues due to its ability to interact with several antioxidant proteins in vivo. It is now very well known that some members of the TRX family reduce PRX,^8–10 an antioxidant enzyme involves in the direct deactivation of some oxidant agents or the MSR,^11,14,15 in charge of the recovery of the oxidized methionine, both in a very specific manner. Due to the increase of PsTRXh1 both at gene expression and protein levels in plant heterotrophic tissues in response to the H₂O₂ treatment, and because it is also capable of conferring resistance towards hydrogen peroxide when produced in a yeast trx1Δ trx2Δ strain,¹⁶ one function of this TRX member could be the reduction in vivo of some PRX and/or MSRA counterparts in Pea tissues in the context of the oxidative signalling.Interestingly, PsTRXh2 gene and its corresponding protein showed very different behaviours to that presented by its homologous h1, reinforcing the idea that some TRX isoforms in plants are capable of functional specificity in vivo. PsTRXh2 is expressed in all tissues assays, mainly in roots, but at an extremely low level compared with that of PsTRXh1. Its divergent functional behaviour was confirmed both in Pea plantlets and yeast. In fact, contrary to PsTRXh1, PsTRXh2 provides hypersensitivity in the yeast trx1Δ trx2Δ mutant. We explained the different behaviour by suggesting that PsTRXh2 might interact with some target(s) involved either directly or indirectly in hydrogen peroxide detoxification, either by compromising the target function in resistance to the ROS or by reinforcing the target function in producing sensitivity to H₂O₂. Most probably, PsTRXh1 and PsTRXh2 interact with very different partners, and the characterization of such targets may help in the deciphering of PsTRX isoforms. As short-term future experiments, using the TRX-specific two-hybrid system that was published recently,⁸ comparative efficiencies of PsTRX isoforms could be performed to reduce some putative target involved in H₂O₂ detoxification, including PsTRXh3 and PsTRXh4.¹⁷ Unravelling Pea TRX interactome should help in deciphering the function of each isoform.However, we have also considered the possibility that PsTRXh2 could interact with the same target that PsTRXh1, but producing an opposite effect. In the yeast context, the protein targeted by the heterologous plant TRXs responsible of this complementation is a type-II PRX.⁵ We think that PsTRXh2 could interact with this yeast PRX blocking it and producing the hypersensitivity. In fact, we have found a similar effect in other protein targeted in vitro by TRXs. In the (Fig. 1), we present the in vitro ability of PsTRXh1 and PsTRXh2 to reduce and activate the pea chloroplastic fructose-1,6-bisphosphatase (FBPase). In the presence of PsTRXh1, FBPase presents TRX-dependent activity but lower than that found when chloroplastic f and m1 isoforms are used.¹² On the opposite, PsTRXh2 presents no only FBPase activation capability but its presence induces the FBPase inhibition, as the enzymatic activity was lower than that exhibited by this enzyme without TRX.Open in a separate windowFigure 1TRX-dependent chloroplastic FBPase activity two-step procedure.¹³ , PsTRXf; ▴, PsTRXm1; •, PsTRXh1; , PsTRXh2. The negative control (no TRX) is represented by a symbol-less line. Numbers in each line represent maximum enzymatic velocity as OD₃₄₀/min.Considering all data, we think that the behaviour showed by both pea h-type TRXs is due to their interactions with several protein-targets, as the PRXs: when the ROS levels increase drastically, cells develop high redox imbalances or even undergo oxidative stress. In this situation, all antioxidant mechanisms must be activated, including the increase of PsTRXh1 expression and protein quantities, giving rise to a more efficient cell detoxification. Under nonimbalance conditions of the redox status, PsTRXh2 could act by interacting (activating or inhibiting) with some protein targets. However, the physiological target for PsTRXh2 are not yet described nor supposed. Our results suggest that its role in the redox control is by producing sensitivity to oxidant agents, maybe by allowing physiological ROS levels in cells.     

Thioredoxin h2 contributes to the redox regulation of mitochondrial photorespiratory metabolism

Thioredoxins (TRXs) are important proteins involved in redox regulation of metabolism. In plants, it has been shown that the mitochondrial metabolism is regulated by the mitochondrial TRX system. However, the functional significance of TRX h2, which is found at both cytosol and mitochondria, remains unclear. Arabidopsis plants lacking TRX h2 showed delayed seed germination and reduced respiration alongside impaired stomatal and mesophyll conductance, without impacting photosynthesis under ambient O₂ conditions. However, an increase in the stoichiometry of photorespiratory CO₂ release was found during O₂-dependent gas exchange measurements in trxh2 mutants. Metabolite profiling of trxh2 leaves revealed alterations in key metabolites of photorespiration and in several metabolites involved in respiration and amino acid metabolism. Decreased abundance of serine hydroxymethyltransferase and glycine decarboxylase (GDC) H and L subunits as well as reduced NADH/NAD⁺ ratios were also observed in trxh2 mutants. We further demonstrated that the redox status of GDC-L is altered in trxh2 mutants in vivo and that recombinant TRX h2 can deactivate GDC-L in vitro, indicating that this protein is redox regulated by the TRX system. Collectively, our results demonstrate that TRX h2 plays an important role in the redox regulation of mitochondrial photorespiratory metabolism.     

Secretory type of recombinant thioredoxin h induces ER stress in endosperm cells of transgenic rice

Thioredoxin h (TRX h) functions as a reducing protein and is present in all organisms. As a new approach for inducing the endoplasmic reticulum (ER) stress, TRX h (OsTRX23) was expressed as a secretory protein using the endosperm-specific glutelin GluB-1 promoter and a signal peptide. In transgenic rice seeds, the majority of the recombinant TRX h accumulated in the ER but some was also localized to the protein body IIs (PB-IIs). The rice grain quality was dependent on the TRX h accumulation level. Increased TRX h expression resulted in aberrant phenotypes, such as chalky and shriveled features, lower seed weight and lower seed protein content. Furthermore, the accumulation of some seed storage proteins (SSPs) was significantly suppressed and the morphology of the protein bodies (PB-Is and PB-IIs) changed according to the level of TRX h. SSPs, such as 13 kDa prolamin and GluA, were specifically modified via the reducing action of TRX h. These changes led to the activation of the ER stress response, which was accompanied by the expression of several chaperone proteins. Specifically, the ER stress markers BiP4 and BiP5 were significantly up-regulated by an increase in the level of TRX h. These results suggest that changes in the conformation of certain SSPs via the action of recombinant TRX h lead to an induced ER stress response in transgenic rice seeds.     

Crosstalk between chloroplast thioredoxin systems in regulation of photosynthesis

Thioredoxins (TRXs) mediate light‐dependent activation of primary photosynthetic reactions in plant chloroplasts by reducing disulphide bridges in redox‐regulated enzymes. Of the two plastid TRX systems, the ferredoxin‐TRX system consists of ferredoxin‐thioredoxin reductase (FTR) and multiple TRXs, while the NADPH‐dependent thioredoxin reductase (NTRC) contains a complete TRX system in a single polypeptide. Using Arabidopsis plants overexpressing or lacking a functional NTRC, we have investigated the redundancy and interaction between the NTRC and Fd‐TRX systems in regulation of photosynthesis in vivo. Overexpression of NTRC raised the CO₂ fixation rate and lowered non‐photochemical quenching and acceptor side limitation of PSI in low light conditions by enhancing the activation of chloroplast ATP synthase and TRX‐regulated enzymes in Calvin–Benson cycle (CBC). Overexpression of NTRC with an inactivated NTR or TRX domain partly recovered the phenotype of knockout plants, suggesting crosstalk between the plastid TRX systems. NTRC interacted in planta with fructose‐1,6‐bisphosphatase, phosphoribulokinase and CF₁γ subunit of the ATP synthase and with several chloroplast TRXs. These findings indicate that NTRC‐mediated regulation of the CBC and ATP synthesis occurs both directly and through interaction with the ferredoxin‐TRX system and is crucial when availability of light is limiting photosynthesis.     

Crystal structure of chloroplastic thioredoxin z defines a type-specific target recognition

Thioredoxins (TRXs) are ubiquitous disulfide oxidoreductases structured according to a highly conserved fold. TRXs are involved in a myriad of different processes through a common chemical mechanism. Plant TRXs evolved into seven types with diverse subcellular localization and distinct protein target selectivity. Five TRX types coexist in the chloroplast, with yet scarcely described specificities. We solved the crystal structure of a chloroplastic z-type TRX, revealing a conserved TRX fold with an original electrostatic surface potential surrounding the redox site. This recognition surface is distinct from all other known TRX types from plant and non-plant sources and is exclusively conserved in plant z-type TRXs. We show that this electronegative surface endows thioredoxin z (TRXz) with a capacity to activate the photosynthetic Calvin–Benson cycle enzyme phosphoribulokinase. The distinct electronegative surface of TRXz thereby extends the repertoire of TRX–target recognitions.     

The Glutaredoxin Family in Oxygenic Photosynthetic Organisms

Glutaredoxins (GRXs) are small redox proteins of the thioredoxin (TRX) superfamily. Compared to TRXs, much less information on the GRX family is available, especially in photosynthetic organisms since GRXs have been mainly studied in E. coli, yeast and mammal cells. The analysis of the TRX family in oxygenic photosynthetic organisms revealed an unsuspected multiplicity of TRXs but it is not known if the same situation holds for GRXs. Despite the availability of genome sequences from different oxygenic photosynthetic organisms, the number of GRXs and the different groups present in these organisms are still undescribed. This paper presents a comparative analysis of the GRX families present in Arabidopsis, Chlamydomonas and Synechocystis which were found to contain 30, 6 and 3 GRX genes, respectively. The putative subcellular localization of each GRX and its relative expression level, based on EST data, have been investigated. This analysis reveals the presence of three major classes of GRXs, the CPYC type, the CGFS type and a previously undescribed type, called the CC type that appears specific to higher plants. These data are discussed in view of recent results suggesting a complex cross-regulation between the TRX and GRX systems.     

Thioredoxins m are major players in the multifaceted light-adaptive response in Arabidopsis thaliana

Thioredoxins (TRXs) are well-known redox signalling players, which carry out post-translational modifications in target proteins. Chloroplast TRXs are divided into different types and have central roles in light energy uptake and the regulation of primary metabolism. The isoforms TRX m1, m2, and m4 from Arabidopsis thaliana are considered functionally related. Knowing their key position in the hub of plant metabolism, we hypothesized that the impairment of the TRX m signalling would not only have harmful consequences on chloroplast metabolism but also at different levels of plant development. To uncover the physiological and developmental processes that depend on TRX m signalling, we carried out a comprehensive study of Arabidopsis single, double, and triple mutants defective in the TRX m1, m2, and m4 proteins. As light and redox signalling are closely linked, we investigated the response to high light (HL) of the plants that are gradually compromised in TRX m signalling. We provide experimental evidence relating the lack of TRX m and the appearance of novel phenotypic features concerning mesophyll structure, stomata biogenesis, and stomatal conductance. We also report new data indicating that the isoforms of TRX m fine-tune the response to HL, including the accumulation of the protective pigment anthocyanin. These results reveal novel signalling functions for the TRX m and underline their importance for plant growth and fulfilment of the acclimation/response to HL conditions.     

Redox regulation of chloroplast metabolism

Regulation of enzyme activity based on thiol-disulfide exchange is a regulatory mechanism in which the protein disulfide reductase activity of thioredoxins (TRXs) plays a central role. Plant chloroplasts are equipped with a complex set of up to 20 TRXs and TRX-like proteins, the activity of which is supported by reducing power provided by photosynthetically reduced ferredoxin (FDX) with the participation of a FDX-dependent TRX reductase (FTR). Therefore, the FDX–FTR–TRXs pathway allows the regulation of redox-sensitive chloroplast enzymes in response to light. In addition, chloroplasts contain an NADPH-dependent redox system, termed NTRC, which allows the use of NADPH in the redox network of these organelles. Genetic approaches using mutants of Arabidopsis (Arabidopsis thaliana) in combination with biochemical and physiological studies have shown that both redox systems, NTRC and FDX-FTR-TRXs, participate in fine-tuning chloroplast performance in response to changes in light intensity. Moreover, these studies revealed the participation of 2-Cys peroxiredoxin (2-Cys PRX), a thiol-dependent peroxidase, in the control of the reducing activity of chloroplast TRXs as well as in the rapid oxidation of stromal enzymes upon darkness. In this review, we provide an update on recent findings regarding the redox regulatory network of plant chloroplasts, focusing on the functional relationship of 2-Cys PRXs with NTRC and the FDX–FTR–TRXs redox systems for fine-tuning chloroplast performance in response to changes in light intensity and darkness. Finally, we consider redox regulation as an additional layer of control of the signaling function of the chloroplast.

Thiol-dependent redox regulatory and antioxidant systems act concertedly to modulate chloroplast metabolism and signaling function.

Advances

• Plant chloroplasts harbor a complex redox network composed of the FDX–FTR–TRXs pathway, linking redox regulation to light, and NTRC, an NADPH-dependent system required for the activity of TRXs. Both systems adjust chloroplast performance to environmental cues.
• A relevant function of NTRC is redox control of 2-Cys PRXs, which maintains the reductive activity of chloroplast TRXs in the light. The NTRC–2-Cys PRXs redox system helps fine-tune the redox state of chloroplast enzymes thereby adjusting photosynthetic performance to changes in light.
• 2-Cys PRXs participate in the rapid oxidative inactivation of chloroplast enzymes in the dark, mediating the transfer of reducing equivalents from reduced enzymes, via TRXs, to hydrogen peroxide.
• Involvement of redox regulation in chloroplast retrograde signaling modulates early stages of plant development and response to environmental stress.

     

Immunocytochemical localization of Pisum sativum TRXs f and m in non-photosynthetic tissues

Plants are the organisms containing the most complex multigenic family for thioredoxins (TRX). Several types of TRXs are targeted to chloroplasts, which have been classified into four subgroups: m, f, x, and y. Among them, TRXs f and m were the first plastidial TRXs characterized, and their function as redox modulators of enzymes involved in carbon assimilation in the chloroplast has been well-established. Both TRXs, f and m, were named according to their ability to reduce plastidial fructose-1,6-bisphosphatase (FBPase) and malate dehydrogenase (MDH), respectively. Evidence is presented here based on the immunocytochemistry of the localization of f and m-type TRXs from Pisum sativum in non-photosynthetic tissues. Both TRXs showed a different spatial pattern. Whilst PsTRXm was localized to vascular tissues of all the organs analysed (leaves, stems, and roots), PsTRXf was localized to more specific cells next to xylem vessels and vascular cambium. Heterologous complementation analysis of the yeast mutant EMY63, deficient in both yeast TRXs, by the pea plastidial TRXs suggests that PsTRXm, but not PsTRXf, is involved in the mechanism of reactive oxygen species (ROS) detoxification. In agreement with this function, the PsTRXm gene was induced in roots of pea plants in response to hydrogen peroxide.     

The Thioredoxin-Thioredoxin Reductase System Can Function in Vivo as an Alternative System to Reduce Oxidized Glutathione in Saccharomyces cerevisiae

Cellular mechanisms that maintain redox homeostasis are crucial, providing buffering against oxidative stress. Glutathione, the most abundant low molecular weight thiol, is considered the major cellular redox buffer in most cells. To better understand how cells maintain glutathione redox homeostasis, cells of Saccharomyces cerevisiae were treated with extracellular oxidized glutathione (GSSG), and the effect on intracellular reduced glutathione (GSH) and GSSG were monitored over time. Intriguingly cells lacking GLR1 encoding the GSSG reductase in S. cerevisiae accumulated increased levels of GSH via a mechanism independent of the GSH biosynthetic pathway. Furthermore, residual NADPH-dependent GSSG reductase activity was found in lysate derived from glr1 cell. The cytosolic thioredoxin-thioredoxin reductase system and not the glutaredoxins (Grx1p, Grx2p, Grx6p, and Grx7p) contributes to the reduction of GSSG. Overexpression of the thioredoxins TRX1 or TRX2 in glr1 cells reduced GSSG accumulation, increased GSH levels, and reduced cellular glutathione E_h′. Conversely, deletion of TRX1 or TRX2 in the glr1 strain led to increased accumulation of GSSG, reduced GSH levels, and increased cellular E_h′. Furthermore, it was found that purified thioredoxins can reduce GSSG to GSH in the presence of thioredoxin reductase and NADPH in a reconstituted in vitro system. Collectively, these data indicate that the thioredoxin-thioredoxin reductase system can function as an alternative system to reduce GSSG in S. cerevisiae in vivo.     

Heavy metal resistant strains are widespread along Streptomyces phylogeny

The genus Streptomyces comprises a group of bacteria species with high economic importance. Several of these species are employed at industrial scale for the production of useful compounds. Other characteristic found in different strains within this genus is their capability to tolerate high level of substances toxic for humans, heavy metals among them. Although several studies have been conducted in different species of the genus in order to disentangle the mechanisms associated to heavy metal resistance, little is known about how they have evolved along Streptomyces phylogeny. In this study we built the largest Streptomyces phylogeny generated up to date comprising six genes, 113 species of Streptomyces and 27 outgroups. The parsimony-based phylogenetic analysis indicated that (i) Streptomyces is monophyletic and (ii) it appears as sister clade of a group formed by Kitasatospora and Streptacidiphilus species, both genera also monophyletic. Streptomyces strains resistant to heavy metals are not confined to a single lineage but widespread along Streptomyces phylogeny. Our result in combination with genomic, physiological and biochemical data suggest that the resistance to heavy metals originated several times and by different mechanisms in Streptomyces history.     

Enhanced Toxic Metal Accumulation in Engineered Bacterial Cells Expressing Arabidopsis thaliana Phytochelatin Synthase

Phytochelatins (PCs) are metal-binding cysteine-rich peptides, enzymatically synthesized in plants and yeasts from glutathione in response to heavy metal stress by PC synthase (EC 2.3.2.15). In an attempt to increase the ability of bacterial cells to accumulate heavy metals, the Arabidopsis thaliana gene encoding PC synthase (AtPCS) was expressed in Escherichia coli. A marked accumulation of PCs was observed in vivo together with a decrease in the glutathione cellular content. When bacterial cells expressing AtPCS were placed in the presence of heavy metals such as cadmium or the metalloid arsenic, cellular metal contents were increased 20- and 50-fold, respectively. We discuss the possibility of using genes of the PC biosynthetic pathway to design bacterial strains or higher plants with increased abilities to accumulate toxic metals, and also arsenic, for use in bioremediation and/or phytoremediation processes.     

Violets of the section Melanium, their colonization by arbuscular mycorrhizal fungi and their occurrence on heavy metal heaps

Violets of the sections Melanium were examined for their colonization by arbuscular mycorrhizal fungi (AMF). Heartsease (Viola tricolor) from several heavy metal soils was AMF-positive at many sites but not at extreme biomes. The zinc violets Viola lutea ssp. westfalica (blue zinc violet) and ssp. calaminaria (yellow zinc violet) were always AMF-positive on heavy metal soils as their natural habitats. As shown for the blue form, zinc violets germinate independently of AMF and can be grown in non-polluted garden soils. Thus the zinc violets are obligatorily neither mycotrophs nor metalophytes. The alpine V. lutea, likely ancestor of the zinc violets, was at best poorly colonized by AMF. As determined by atomic absorption spectrometry, the contents of Zn and Pb were lower in AMF colonized plants than in the heavy metal soils from where the samples had been taken. AMF might prevent the uptake of toxic levels of heavy metals into the plant organs. Dithizone staining indicated a differential deposition of heavy metals in tissues of heartsease. Leaf hairs were particularly rich in heavy metals, indicating that part of the excess of heavy metals is sequestered into these cells.     

Detoxification of Multiple Heavy Metals by a Half-Molecule ABC Transporter,HMT-1, and Coelomocytes of Caenorhabditis elegans

Background

Developing methods for protecting organisms in metal-polluted environments is contingent upon our understanding of cellular detoxification mechanisms. In this regard, half-molecule ATP-binding cassette (ABC) transporters of the HMT-1 subfamily are required for cadmium (Cd) detoxification. HMTs have conserved structural architecture that distinguishes them from other ABC transporters and allows the identification of homologs in genomes of different species including humans. We recently discovered that HMT-1 from the simple, unicellular organism, Schizosaccharomyces pombe, SpHMT1, acts independently of phytochelatin synthase (PCS) and detoxifies Cd, but not other heavy metals. Whether HMTs from multicellular organisms confer tolerance only to Cd or also to other heavy metals is not known.

Methodology/Principal Findings

Using molecular genetics approaches and functional in vivo assays we showed that HMT-1 from a multicellular organism, Caenorhabditis elegans, functions distinctly from its S. pombe counterpart in that in addition to Cd it confers tolerance to arsenic (As) and copper (Cu) while acting independently of pcs-1. Further investigation of hmt-1 and pcs-1 revealed that these genes are expressed in different cell types, supporting the notion that hmt-1 and pcs-1 operate in distinct detoxification pathways. Interestingly, pcs-1 and hmt-1 are co-expressed in highly endocytic C. elegans cells with unknown function, the coelomocytes. By analyzing heavy metal and oxidative stress sensitivities of the coelomocyte-deficient C. elegans strain we discovered that coelomocytes are essential mainly for detoxification of heavy metals, but not of oxidative stress, a by-product of heavy metal toxicity.

Conclusions/Significance

We established that HMT-1 from the multicellular organism confers tolerance to multiple heavy metals and is expressed in liver-like cells, the coelomocytes, as well as head neurons and intestinal cells, which are cell types that are affected by heavy metal poisoning in humans. We also showed that coelomocytes are involved in detoxification of heavy metals. Therefore, the HMT-1-dependent detoxification pathway and coelomocytes of C. elegans emerge as novel models for studies of heavy metal-promoted diseases.     

Noninvasive Evaluation of Heavy Metal Uptake and Storage in Micoralgae Using a Fluorescence Resonance Energy Transfer-Based Heavy Metal Biosensor

We have developed a fluorescence resonance energy transfer (FRET)-based heavy metal biosensor for the quantification of bioavailable free heavy metals in the cytoplasm of the microalga Chlamydomonas reinhardtii. The biosensor is composed of an end-to-end fusion of cyan fluorescent protein (CFP), chicken metallothionein II (MT-II), and yellow fluorescent protein (YFP). In vitro measurements of YFP/CFP fluorescence emission ratios indicated that the addition of metals to the purified biosensor enhanced FRET between CFP and YFP, consistent with heavy metal-induced folding of MT-II. A maximum YFP/CFP FRET ratio of 2.8 was observed in the presence of saturating concentrations of heavy metals. The sensitivity of the biosensor was greatest for Hg²⁺ followed by Cd²⁺ ≈ Pb²⁺ > Zn²⁺ > Cu²⁺. The heavy metal biosensor was unresponsive to metals that do not bind to MT-II (Na⁺ and Mg²⁺). When expressed in C. reinhardtii, we observed a differential metal-dependent response to saturating external concentrations (1.6 mm) of heavy metals (Pb²⁺ > Cd²⁺) that was unlike that observed for the isolated biosensor (in vitro). Significantly, analysis of metal uptake kinetics indicated that equilibration of the cytoplasm with externally applied heavy metals occurred within seconds. Our results also indicated that algae have substantial buffering capacity for free heavy metals in their cytosol, even at high external metal concentrations.Many proteins utilize metals to stabilize their structures or as cofactors to catalyze redox and other chemical reactions. Metals such as zinc, copper, iron, magnesium, cobalt, and manganese are required by most living organisms for their normal cellular functions. Essential metals are often present at low concentrations in the environment, however, and must be imported into cells, often at the expense of energy (Hanikenne et al., 2005; Merchant et al., 2006). In contrast to essential metals, toxic metals such as cadmium, lead, and mercury can disrupt cellular functions by competing with essential metals for their metal-binding sites and/or by altering the redox state of cells. Exposure of organisms to high concentrations of toxic metals can impair their cellular functions, growth, and reproduction. To prevent metal-induced cellular anomalies, organisms have evolved a variety of strategies to reduce the toxicity of heavy metals. One such strategy involves the selective binding of toxic metals in the cytoplasm by metal-binding proteins and other small molecules. As discussed below, both enzymatically and ribosomally synthesized Cys-rich peptides, including phytochelatins and metallothioneins (MTs), are utilized by a variety of organisms to sequester toxic heavy metals, including cadmium, mercury, lead, silver, and gold. The peptides may also serve as storage reserves for essential metals such as copper and zinc (Cobbett and Goldsbrough, 2002).Phytochelatins are enzymatically synthesized polypeptides containing repeating units of (γ-Glu-Cys)_n-Gly, where n = 2 to 11 (Rauser, 1990), whereas MTs are genetically encoded, ribosomally synthesized polypeptides (Cobbett and Goldsbrough, 2002). MTs have molecular mass values ranging from 6 to 7 kD and contain approximately 20 conserved Cys residues (Cobbett and Goldsbrough, 2002; Romero-Isart and Vasák, 2002). Metals are characteristically bound to MT via the thiolate sulfur ligands of Cys residues (Kägi, 1991). It is estimated that the metal-saturated MT contains about 10% thiolate sulfur and bound metals by mass (Romero-Isart and Vasák, 2002). Structural analyses of metal-free and metal-complexed MTs demonstrated that MTs undergo a structural transition from a metal-free random-coil structure to a metal-bound compact dumbbell-shaped structure having metal saturated α- and β-domains (Pearce et al., 2000; Romero-Isart and Vasak, 2002; Hong and Maret, 2003). The N-terminal β-domain binds three metal ion equivalents, and the C-terminal α-domain binds four metal ion equivalents (Romero-Isart and Vasák, 2002; Vasák, 2005). Furthermore, several decades of work on MTs have provided a great deal of information regarding their metal-binding affinity, specificity, and domain selectivity for select metals (Cobbett and Goldsbrough, 2002; Romero-Isart and Vasák, 2002; Vasák, 2005).Fluorescence resonance energy transfer (FRET) involves the nonradioactive transfer of energy between the excited state of a luminescent or fluorescent donor molecule and a nearby acceptor molecule that has overlapping excited state transitions. Proteins that are modified to have efficient energy donor and acceptor domains and that undergo structural changes upon binding a specific ligand are good candidates for FRET-based sensors. For ligand-specific FRET-based biosensors, the distance and/or the orientation between the energy donor and acceptor molecules is changed upon ligand binding in a concentration-dependent manner (Selvin, 1995; Weiss, 2000; Hong and Maret, 2003; Looger et al., 2005). Relevant to this discussion, a FRET-based biosensor with GFP variants fused to MT was previously shown to be an effective means to monitor metal release during nitric oxide-induced signaling in endothelial cells (Pearce et al., 2000).Unicellular algae such as Chlamydomonas species are often found in areas that might be contaminated by toxic heavy metals (Merchant et al., 2006). Chlamydomonas species have also been shown to sequester toxic metals (e.g. cadmium and mercury) and have potential use for bioremediation of these metals (Cai et al., 1999; Adhiya et al., 2002; Siripornadulsil et al., 2002; He et al., 2011; Priyadarshani et al., 2011). To determine the kinetics and selectivity of exogenous heavy metal uptake as well as free heavy metal concentration in the cytoplasm of Chlamydomonas species, we developed an MT, FRET-based metal-binding sensor and expressed this in the cytoplasm of the unicellular green alga Chlamydomonas reinhardtii. We demonstrate that heavy metal uptake is rapid in C. reinhardtii and that cytoplasmic free heavy metal concentrations are substantially lower than exogenous free heavy metal concentrations, implying that heavy metals are rapidly sequestered by various biological molecules in the cell.     

A new model for predicting time course toxicity of heavy metals based on Biotic Ligand Model (BLM)

A new model for predicting time course toxicity of heavy metals was developed by extending the effective ratio of biotic ligand binding with toxic heavy metals to the total biotic ligand for 50% of test organisms (f₅₀) derived by the Biotic Ligand Model (BLM). BLM has been well-known as a useful model for prediction of heavy metal toxicity. BLM can consider the effect of exposure conditions such as pH and Ca²⁺ on heavy metal toxicity. In addition to the exposure conditions, heavy metal toxicity is strongly dependent on exposure time. In this study, BLM is extended to predict time dependency of heavy metal toxicity by connecting with the concept of primary reaction. The model developed in this study also generates the estimation of the 50% effect concentration (EC₅₀) for toxicologically unknown organisms and heavy metals. Two toxicological and kinetic constants, f_50,0 and k, were derived from the initial value of f₅₀ (f_50,0) and a time constant (k) independent of time. The model developed in this study enables us to acquire information on the toxicity of heavy metals such as Cu, Cd and Co easily.     

Assessment of the bioaccumulation pattern of Pb,Cd, Cr and Hg in edible fishes of East kolkata Wetlands,India

Waste water fed pisciculture is nowadays a common feature in aquaculture belts across the globe. East Kolkata Wetlands (EKW) a nature’s wonder where waste water fed natural aquaculture beltis is active for more than 70 years now and is efficiently operating as a natural waste management system. The peri urban wetland is also a site of international importance and is listed in Ramsar. Field and lab-based investigations were carried out using three commonly edible carp variety of fishes such as Rohu (Labeorohita), Catla (Catlacatla) and Nile Tilapia (Oreochromisniloticus) collected from ponds (bheries) of the wetland located on the eastern fringes of Kolkata, India. The lab-based analysis revealed the presence of toxic metals such as Cr, Pb, Cd and Hg in the samples with the seasonal order of accumulation being monsoon > post-monsoon > winter > pre-monsoon in the successive years of 2016, 2017 and 2018. Bio-accumulation of toxic heavy metals in fishes follows the order Tilapia > Rohu > Catla where as the bioaccumulation pattern of toxic metals shows the trend Pb > Cd > Cr > Hg across all the seasons and years. The ambient media was also investigated to understand in detail the bioaccumulation pattern at different trophic levels of the ecosystem. Water and sediments were analyzed to evaluate the contamination of toxic heavy metals from point and non-point sources. Current study shows the observed bioaccumulation pattern of the toxic heavy metals in one of the fragile ecosystems that raises an important question of environmental safety in the food we intake on daily basis.     

The psbO mutant of Chlamydomonas reinhardtii is capable of assembling stable, photochemically active reaction center of photosystem II

The functional status of photosystem II (PSII) complex in the dark-grown PsbO-deficient mutant of green alga Chlamydomonas reinhardtii was studied. It was found that ΔpsbO mutant cells of C. reinhardtii grown under heterotrophic conditions (dark + acetate) were capable of assembling stable, photochemically-competent reaction centers of PSII (as confirmed by immunological analysis of D1 protein level, pigments content and photoinduced changes of PSII chlorophyll fluorescence yield), while O₂-evolution activity was not revealed. The ratio F _v/F _m for the dark-grown ΔpsbO mutant C. reinhardtii was 0.37 and that for the dark-grown wild type cells was 0.56. Analysis of chlorophyll fluorescence induction curve indicated that the absence of oxygen-evolving activity could be due to some defects in the organization of the PSII catalytic manganese cluster. Decrease of the rate of the electron donation from water-oxidizing complex to the PSII reaction center as well as the appearance of an additional transient fluorescence peak during the dark relaxation of F _v testify to the damages to the PSII donor side. The data obtained suggest that the dark-grown PsbO-deficient cells of C. reinhardtii are able to form stable, photochemically active PSII reaction center, unable to oxidize water due to probable defects in the assembly of the manganese cluster.