MINI REVIEW article

Front. Environ. Sci., 08 August 2014

Sec. Environmental Toxicology

Volume 2 - 2014 | https://doi.org/10.3389/fenvs.2014.00034

Are plant endogenous factors like ethylene modulators of the early oxidative stress induced by mercury?

  • 1. Laboratory of Plant Physiology, Department of Biology, Universidad Autonoma Madrid Madrid, Spain

  • 2. Plant Physiology, Department of Environmental Sciences, Universidad de Castilla-La Mancha Toledo, Spain

Abstract

The induction of oxidative stress is one of the quickest symptoms appearing in plants subjected to metal stress. A transcriptional analysis of the early responses of alfalfa (Medicago sativa) seedlings to mercury (Hg; 3 μM for 3, 6 and 24 h) showed that up-regulation of genes responding to ethylene were up-regulated, a phytohormone known to mediate in the cellular redox homeostasis. In this mini-review we have compared these quick responses with two other concurrent transcriptomic analysis in Barrel medic (Medicago truncatula) and barley (Hordeum vulgare) under Hg stress. Besides ethylene, ABA, and jasmonate related genes were up-regulated, all of them are endogenous factors known to intervene in oxidative stress responses. The information obtained may target future work to understand the cellular mechanisms triggered by Hg, enabling biotechnological approaches to diminish Hg-induced phytotoxicity.

Background

Mercury (Hg) is a natural component of the Earth crust that is released by mainly geothermal activity, but accumulates in land and water ecosystems, mainly as a consequence of different human activities, such as mining and industry (Nriagu, ; Järup, ). This represents a serious problem to the environment and risks for human health (Tchounwou et al., ) as occurs in the mining district of Almadén (Spain), which contains the largest deposits of Hg in the World, with soils heavily polluted which require in situ and economically feasible cleaning procedures (Millán et al., ). Different strategies to clean-up metal polluted soils have been developed; among them, phytoremediation is considered one of the most economic and environmental friendly procedures to restore soil fertility (Alkorta et al., ). This biotechnical approach relies on the innate capability of plants to uptake and to accumulate metals from the soil, but it requires plants able to tolerate Hg accumulation in their organs and to prevent the general oxidative damage induced by this metal (Cho and Park, ; Patra et al., 2004; Ortega-Villasante et al., 2005). The maintenance of the cellular redox homeostasis in cells, where antioxidant enzymes and metabolites ameliorate the accumulation of oxidant Reactive Oxygen Species (ROS), would modulate the final tolerance response to Hg (Rellán-Álvarez et al., ; Zhou et al., ; Sobrino-Plata et al., ). Cross-talk of oxidative stress signaling cascades and endogenous factors, like ethylene, jasmonate, auxin, or abscisic acid, is pivotal for plant acclimation to stress and development (Potters et al., ), where antioxidants modulate ROS production (Considine and Foyer, ). In particular, ethylene through the family of APETALA 2/Ethylene Response Element Binding Protein (AP2/EREBP) transcription factors is known to mediate in hormone and redox signaling processes in context of abiotic stresses (Dietz et al., ). Understanding the mechanisms controlling acclimation to hazardous environmental will help to optimize tolerance to Hg in plant cells, knowledge that has been elusive (Chen and Yang, ). However, recent research using improved transcriptomics is now paving the way to identify mechanisms involved in the early responses to Hg, putatively involved in the tolerance to this toxic metal, in particular with regards to redox homeostasis.

Early oxidative stress induced by metal toxcity

In spite of high concentration of Hg in polluted soils, only a modest amount is taken up by plants, a function of the predominant edaphic conditions (Xuexum and Linhai, ). Moreover, Hg translocation from roots to shoots occurs normally at low rates, and most toxic effects are found in roots (Boening, ). Mercury reduces dramatically the root growth, diminishes the nutrients uptake rates and enhances cell death, and induces an early oxidative burst (Cho and Park, ; Patra and Sharma, ; Patra et al., 2004; Ortega-Villasante et al., 2005). A strong lipid peroxidation and protein oxidation occurred after short-term exposure to Hg in maize (Rellán-Álvarez et al., ) and pea plants (Cho and Park, ), which represent chronic toxic effects with several alterations in cellular functions, such as cross-linking at the cell wall that may led to its stiffening and cell growth inhibition (Cargnelutti et al., ). Localization of Hg in plant tissues using X-ray synchrotron imaging showed that this metal enter the plant at the root tip, and accumulates in the vascular bundle, where vascular parenchyma cells showed corrugated morphology probably due to water balance alteration (Carrasco-Gil et al., 2013).

The knowledge about physiological responses of plants exposed to Hg has increased in the last few years as Hg, which has been compared frequently with the phytotoxicity caused by other toxic elements like Cd (Gallego et al., ). With regard to the induction of the oxidative burst, several authors observed alterations in antioxidant enzymes activities such as catalase (CAT), ascorbate peroxidase (APX), or superoxide dismutase (SOD) mainly in roots (Rellán-Álvarez et al., ; Zhou et al., ). Interestingly, Hg-specific responses were found in the activity of glutathione reductase (GR), key enzyme to maintain the redox balance of glutathione (GSH) that is strongly inhibited by Hg, while under Cd or As it is induced (Sobrino-Plata et al., , 2013); enzyme that has been suggested recently as a biomarker of Hg accumulation (Sobrino-Plata et al., 2013). A significant and early induction of ROS, such as superoxide anion (O2) and hydrogen peroxide (H2O2), has been observed in Brassica juncea plants exposed to Hg (Meng et al., ). Microscale experiments with alfalfa seedlings showed that the generation of ROS by Hg occurs within minutes (Ortega-Villasante et al., ), possibly associated with the induction of plasma membrane NADPH-oxidases responsible of the accumulation of H2O2 in the root apoplast (Montero-Palmero et al., ). This mechanism of ROS production may differ from that of triggered by Cd, possibly more related with mitochondrial electron transfer chain malfunction (Heyno et al., ). The Respiratory Burst Oxidase Homolog (Rboh)/NADPH-oxidases in plants has been reported as regulatory mechanisms of biotic and abiotic stress mediating in ROS production. Recently, the characterization of Arabidopsis RbohD, RbohF, and RbohC family members has been useful to understand better their role under stress conditions using atrbohD/atrbohF and atrbohC mutant plants, which demonstrated their relevance in the signaling network involved in stress cellular homeostasis (Torres and Dangl, ). In this sense, Arabidopsis atrbohD/atrbohF mutants and a 35S::AtrbohD overexpressor suggest the involvement of Rboh/NADPH-oxidases in the generation of H2O2 under Hg stress (Montero-Palmero et al., ).

ROS are considered as components of a signal cascade capable of triggering the induction of defense genes to cope with abiotic and biotic stresses. For example, Mittler et al. (2004) reviewed a list of more than 150 genes in Arabidopsis that participate in a complex network to regulate ROS levels after an oxidative burst. The identification of common components in the stress responses as key factors of cell homeostasis has been a major research effort recently (Kreps et al., ). Among others, the zinc-finger superfamily of transcription factors are one of the best functionally characterized group, which mediates in both biotic and abiotic stresses (Kodaira et al., ; Figueiredo et al., ). In this sense, the transcription factor Zat12 may canalize the oxidative burst signaling in Arabidopsis, as was observed when the tolerance was altered by interfering the expression of genes regulated by Zat12 (Davletova et al., ). This regulatory role was shared with WRKY transcription factors, which are thought to regulate the expression of several stress-related genes, such as those encoding several APXs (Davletova et al., ; Vanderauwera et al., ; Miao and Zentgraf, ; Chen et al., ).

Consistent with some physiological symptoms of Hg stress, changes in the transcription of genes needed for the regeneration of the photosynthetic apparatus and antioxidant enzymes were detected in Arabidopsis thaliana and tomato seedlings exposed to Hg (Cho and Park, ; Heidenreich et al., ). Similarly, there was an up-regulation of genes encoding peroxidases, NADH-dehydrogeneases and enzymes of the sulfur assimilatory pathway, as well as genes involved in secondary metabolism in Hg-treated pea plants (i.e., biosynthesis of salicylic acid (SA) and isoflavonoids; Sävenstrand and Strid, ). Additionally, heme oxygenases (HOs) may mediate in the Hg-related responses in Brassica napus (Shen et al., ), which are related with pathogenesis related proteins or small heat shock proteins (SHSPs) (Didierjean et al., ; Wollgiehn and Neumann, ).

Recent evidences suggest that metal homeostasis depend on a complex crosstalk between different signaling processes, where ROS signals are integrated with phytohormones signaling. Therefore, ROS are considered as important clues for development and ontogeny of plant cells (Mittler et al., ). It is possible that hormone and ROS signaling are playing their role at the same level in the stress response (Fujita et al., ), but they could also be involved in different steps of signaling cascade. Thus, phytohormones could alter ROS production or, in the contrary, ROS could be promoting the hormone cascade activation (Bartoli et al., ). Therefore, more complete studies of massive transcriptional analysis are required to understand the complex levels of responses normally studied using a heuristic incomplete approach, which has been recently undertaken as discussed below.

Characterization of the massive transcriptional pattern under Hg stress

Recent bioinformatics and technological advances based on “omics” research have revitalized the integration at the transcriptional level of many physiological processes in plants (Mochida and Shinozaki, ). In this sense, DNA microarrays technology is a powerful tool used widely in the last decades after genome sequencing projects, that are enabling a more complete understanding of the global transcriptional changes under different environmental conditions and effectors, endogenous signals, interaction with pathogens, and so on (Amaratunga et al., ). With regard to metal homeostasis, a substantial effort has been done to characterize the primary cellular mechanisms involved in the heavy metal stress perception and defense mechanisms using different RNA-DNA microarray technologies. Arabidopsis DNA chips have been used to identify global transcriptional pattern in response to metals such as Zn (Becher et al., ), As (Abercrombie et al., ) or Cd (Herbette et al., ; Weber et al., ); where in most cases the transcriptional response of Arabidopsis thaliana has been compared with that of the metalliferous Arabidopsis halleri. Transcriptional activity of the metal Zn/Cd accumulator Noccaea (Thlaspi) caerulescens has also been compared with Arabidopsis in response to Cd (Van De Mortel et al., ). Apart from Arabidopsis, sensitive and tolerant cultivars of rice (Oryza sativa) have been used to assess their transcriptional response to As (Norton et al., ; Chakrabarty et al., ; Huang et al., ; Yu et al., ), Cu (Sudo et al., ) using different DNA microarray platforms. In addition, the transcriptional responses of Cd were compared with those of essential trace micronutrients like Cu in Arabidopsis (Zhao et al., ) or in rice roots (Lin et al., ).

With respect to Hg, three very recent concurrent studies were completed to characterize the massive transcriptional profile in seedlings of Medicago sativa (Montero-Palmero et al., ), Medicago truncatula (Zhou et al., ), and Hordeum vulgare (Lopes et al., ). The main purpose of these transcriptional studies was to obtain a comprehensive understanding of the metabolic pathways involved in the Hg-stress response, which would shed light in the tolerance mechanisms involved. Genes encoding enzymes of the plant secondary metabolism, and other known to participate in biotic and abiotic stresses genes were differently expressed in the three transcriptomic studies performed with different plant species. For example, there was a clear up-regulation of genes encoding enzymes of the lignin biosynthesis pathway, such as those producing lignin precursors like coumarins, caffeoyl, and other monolignols (Table 1). It is known that lignin polymerization promotes cell wall stiffening (Passardi et al., ); lignin cross-linking reactions that may be responsible of the observed rapid root growth inhibition under Hg stress (Ortega-Villasante et al., ; Montero-Palmero et al., ). In addition, these phenolic metabolites are known antioxidants under metal stress conditions (Van De Mortel et al., ), which would counteract the rapid ROS induction by Hg Moreover observed in our experiments (Ortega-Villasante et al., ; Montero-Palmero et al., ). Other strongly regulated genes, common to all three plant species, fall in several stress-related categories such as glutathione-S-transferases, heat shock proteins or pathogenesis related proteins (Table 1). It is thought that toxic metabolites, protein instability and other alterations in the cellular components may compromise cell survival in plants subjected to different types of environmental stresses (Mittler et al., ), indicating that a general unspecific response is also triggered by Hg. Interestingly, several phytohormone signaling pathways seemed to operate under Hg stress: ethylene, ABA and auxin related genes are among those significantly up-regulated after a short-term treatment (Table 1), which may be key players in metal perception and homeostasis.

Table 1

Functional categoriesM. sativaM. truncatulaH. vulgare
No DEG%DEGNo DEG%DEGNo DEG%DEG
StressGlutathione/ascorbate cycle60.6630.1220.14
Sulfate transporters10.1120.0810.07
S-assimilation (APS-APR)30.3320.0840.27
Glutathione S-transferases192.09120.46251.71
Small heat shock proteins90.9960.2340.27
Heat shock proteins141.54110.4350.34
Heat shock factors40.4430.1240.27
Pathogenesis related proteins343.7480.31221.50
Fungal elicitor proteins10.1120.0820.14
Chitinases40.4420.0890.61
Subtotal DEGs9510.44511.98785.32
PhytohormonesEthylene metabolism40.4430.1230.20
Ethylene responsive factors101.1090.3530.20
ABA responsive genes20.2220.0870.48
Jasmonate metabolism101.1070.2740.27
Jasmonate responsive genes10.07
Auxin metabolism30.33
Auxin responsive genes80.88130.50110.75
Subtotal DEGs374.07341.32291.98
Second. Met.Lignins232.53150.58100.68
Phenylpropanoids192.0940.15110.75
Anthocyanins60.6610.0430.20
Chalcones222.42240.9310.07
Other flavonoids151.65100.3950.34
Subtotal DEGs859.34542.09302.05
Total DEGs number91025821466

Number of DEGs and percentages obtained from the total DEGs number in different functional categories.

Differential expressed genes (DEGs) from the microarray of Medicago sativa root-seedlings exposed to 3 μM Hg during 3, 6, or 24 h (FDR < 0.01), compared to the transcriptomics analyses made in Medicago truncatula seedlings treated with 10 μM HgCl2 during 6, 12, 24, and 48 h (FDR < 0.001; Fold Change over 1) and in Hordeum vulgare root-seedlings exposed to approximately 300 μM Hgin sand semi-hydroponics for 15 days (P < 0.05), and classified into the main functional MapMan categories.

Involvement of ethylene in the oxidative burst induced by Hg

Plant cells exposed to toxic metals experience drastic metabolic changes, ranging from primary signaling events, biochemical and metabolic responses to transcriptional activation, as outlined in Figure 1A. An important feature of the early responses to toxic metals is the induction of ROS accumulation and oxidative stress (Baier et al., ), which occur minutes after the exposure of root epidermal cells to Cd and Hg (Hernández et al., ). Metal perception by plant cells is normally accomplished by a stress signaling network that would involve the activation of a Ca-signaling cascade (DalCorso et al., ), accumulation of ROS and reactive nitrogen species (RNS; i.e., nitric oxide or NO), or with the accumulation of certain stress-related phytohormones like salicylic, jasmonate and oxylipins (Rodríguez-Serrano et al., ; Tamás et al., ). Downstream signaling events include changes in the activity of several antioxidant enzymes, such as APX, GR, or SOD, along with modified concentration of antioxidant metabolites, such as ascorbate and GSH (Jozefczak et al., ), activation of Ca-dependent calmodulins, and mitogen-activated protein kinases (MAPKs; Jonak et al., ; Ye et al., ). Ethylene accumulated in Brassica juncea leaves when exposed to Ni and Zn, phytohormone that promoted the activation of APX and GR enzymatic activities and augmented the pool of reduced GSH, conceivably required to enhance the antioxidant defensive barriers against metal stress (Khan and Khan, ). On the other hand, ethylene mediates in the assimilation process and the nutrition balance of sulfur, a fundamental macronutrient for plant acclimation to stress via GSH metabolism (Iqbal et al., ). The defenses to metal stress also comprise transcriptional changes, necessarily orchestrated by certain families of transcription factors, in particular some responding to ethylene, ABA, jasmonate, or auxin (i.e., ERF/AP2, WRKY, MYB, and ARF, respectively), that would recognize different cis-DNA regulatory motifs to control the transcription of genes involved in metal detoxification and tolerance (Thapa et al., ; Figure 1B). Expression of different metal transporters (for example the HMA1-4 and CDF families), enzymes of sulfur metabolism and GSH biosynthesis, and SHSPs are among the cellular defenses activated upon the commented transcriptional activation (Gallego et al., ; Figure 1).

Figure 1

; (2) Zhou et al., , ; (3) Sobrino-Plata et al., ; Sobrino-Plata et al., ,; (4) Lopes et al., ; (5) Zhou et al., ; (6) Montero-Palmero et al., . (B) Cellular responses in plants treated with metals (divalent toxic metal cation; HM2+). Metal cations can interact with cell wall components and then enter the cytoplasm via ion Ca2+ channels or active transporters (HMA). Once inside the cell, ROS production (H2O2 or O2) is induced possibly by NADPH-oxidases, in addition with electron transfer reactions in the chloroplast and mitochondria. Metals may be chelated with phytochelatins (PC) before are transferred to the vacuole. Antioxidant enzymes, such as catalase (CAT), superoxide dismutase (SOD), and ascorbate peroxidases (APX), are activated to maintain the cellular redox homeostasis. At the transcriptional level, the expression of certain stress genes (i.e., heat shock proteins, pathogen related proteins, or cell wall stiffening) is up-regulated, including stress-related transcription factors, antioxidantant proteins, microRNAs, and sulfur metabolism related genes. ROS/phytohormones crosstalk in response to metal stress would modulate the overall transcriptional profile, promoting the expression of the corresponding transcription factors.

Stress related phytohormones like SA or jamonate (derived from oxylipins) are known effectors that modulate responses to toxic metals (Xiang and Oliver, ; Zhou et al., ). In fact, several hormone responsive genes and genes involved in hormones synthesis are up-regulated, indicating that phytohormones play an important role in the Hg-induced response (Table 1). SA, brassinosteroids, cyotokinins, gibberellins, or IAA have been described stimulating the antioxidant response in terrestrial and aquatic plants exposed to Cd, Cu, or Pb (Hayat et al., 2007; Noriega et al., ; Piotrowska-Niczyporuk et al., 2012). On the contrary, jasmonate is known to trigger ROS production under metal stress (Maksymiec and Krupa, ), and accumulated in leaves of Arabidopsis and Phaseolous coccineus under Cu and Cd stress (Maksymiec et al., ). Interestingly, jasmonate-induced ROS is mediated by the oxidative status of GSH, as has been shown in GR defective mutants (Mhamdi et al., ). Subsequently, the transcriptional activity due to jasmonate has been recently associated with the oxidative burst led by changes in the redox potential of GSH in plant cells (Han et al., ). In addition, jasmonate entwines with ethylene in a complex signaling cascade that results in ROS production (Mittler, ). The stress response induced by ethylene may be associated with the jasmonate pathway, mediated by the COI1-jasmonate receptor as was shown in the root meristematic activity (Adams and Turner, ). This draws a rather complex picture where redox unbalance in the cell is required in turn for cysteine and GSH synthesis, possibly as part of a positive feedback mechanism where jasmonate or ethylene may intervene (Queval et al., ).

Ethylene plays also a complex role along with ROS in the defense responses to biotic and abiotic stresses (Mittler et al., ). Insensitive plants to ethylene, such as Arabidopsis ein2-5, were unable to promote the oxidative burst after a pathogen elicited response (De Jong et al., 2002), highlighting the contribution of this phytohormone in the oxidative burst that precedes plant immune responses (Mersmann et al., 2010). This hormone could also interfere in the ROS signaling in Arabidopsis exposed to Cu and Cd (Arteca and Arteca, ) and Al (Sun et al., ). Moreover, the Hg-induced release of H2O2 by roots was attenuated when the ethylene perception was blocked in alfalfa and Arabidopsis seedlings, implying that ethylene is required by the activation of NADPH-oxidases to generate ROS under metal stress (Montero-Palmero et al., ).

Ethylene is also a phytohormone that determines root architecture and controls defense responses of plants to stress (Swarup et al., ). The rapid root growth inhibition observed under Hg (Ortega-Villasante et al., ) was counteracted when ethylene perception was blocked in alfalfa and Arabidopsis, implying a direct relationship between this phytohormone and the root architecture (Montero-Palmero et al., ). It is feasible that this role occurs under other metal stress conditions, as it was shown that ethylene synthesis antagonists alleviated the Al-induced arrest of root elongation (Tian et al., ). This control is exerted in combination of other hormones like auxins, salicylic acid, jasmonate, ABA, or strigolactones, contributing to a general mechanism of tolerance and resistance to a wide range of biotic and abiotic stresses (Bari and Jones, ). For instance, a downstream regulation of auxin-related genes (such as YUCCA, PIN, or ARF), and cell cycle related-genes (CDKs and cyclins), are also interconnected with a H2O2 signaling cascade under Cd stress in rice plants (Zhao et al., ) and barley roots (Liptakova et al., ). Interestingly, there are clear evidences that auxins accumulation in roots depends partially on ethylene metabolism, which may affect ultimately the architecture of roots by promoting the appearance of secondary roots emergence (Ruzicka et al., ; Swarup et al., ). Uptake of mineral nutrients and exudation of malate could be also modulated by ethylene and auxin, possibly via a transcriptional regulation, which could be related with root architecture under metal stress (Tian et al., ). Similarly, jasmonate mediates in ASA1 expression, a protein involved in auxin synthesis and distribution-related, which also modulates root development (Wasternack and Hause, ). All these endogenous factors would interact with oxidative stress promoted signaling, composing a complex transduction network that regulates cell division, expansion, and ultimately root architecture (Considine and Foyer, ), which would be altered in plants exposed to toxic metals.

Future perspectives and challenges

Current evidences support the concept that phytohormones are playing a significant role in the perception and response to toxic metals, possibly by interacting with a ROS-dependent signaling pathway. Being said that, the current understanding of the crosstalk between phytohormones and ROS networks is still obscure and very limited. Thus, future work should be directed to describe in detail the genetic network that regulates the perception of the stress induced by metals, and how different phytohormones and signaling components interact using the available collection of mutants with inhibited or blocked receptors, together with current massive transcriptomic profile analyses, and bioinformatic tools to obtain an integrated picture. This will allow the development of biotechnical strategies to enhance tolerance of plants to metal toxicity.

Conflict of interest statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Statements

Acknowledgments

This work was funded by the Ministry of Economy and Competitiveness (Project PROBIOMET AGL2010-15151), Junta Comunidades Castilla-La Mancha (FITOALMA2, POII10-007-6458), and Comunidad de Madrid (EIADES consortium S2009/AMB-1478).

Conflict of interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

Summary

Keywords

ethylene, homeostasis, hormones, mercury, oxidative stress, transcription

Citation

Montero-Palmero MB, Ortega-Villasante C, Escobar C and Hernández LE (2014) Are plant endogenous factors like ethylene modulators of the early oxidative stress induced by mercury?. Front. Environ. Sci. 2:34. doi: 10.3389/fenvs.2014.00034

Received

26 May 2014

Accepted

16 July 2014

Published

08 August 2014

Volume

2 - 2014

Edited by

Naser A. Anjum, University of Aveiro, Portugal

Reviewed by

Naser A. Anjum, University of Aveiro, Portugal; Nafees A. Khan, Aligarh Muslim University, India

Copyright

*Correspondence: Luis E. Hernández, Laboratory of Plant Physiology BS13, Department of Biology, Universidad Autonoma Madrid, Edif. Biológicas, C/Darwin 2, Campus Universitario Cantoblanco, 28049 Madrid, Spain e-mail:

This article was submitted to Environmental Toxicology, a section of the journal Frontiers in Environmental Science.

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