Improving crop salt tolerance
全球气候变化对粮食生产的影响与适应考研英语作文范文
全球气候变化对粮食生产的影响与适应考研英语作文范文The Impact of Global Climate Change on Food Production and AdaptationIn recent years, global climate change has become a pressing issue that poses significant challenges to food production worldwide. The adverse effects of the changing climate, including rising temperatures, altered precipitation patterns, and increased frequency of extreme weather events, are already being witnessed in various regions around the globe. This essay aims to explore the impact of global climate change on food production and discuss potential strategies for adaptation.Firstly, rising temperatures have a direct impact on crop yields. High temperatures can lead to heat stress in plants,negatively affecting their growth and productivity. Crops such as wheat, maize, and rice are particularly vulnerable to temperature extremes. Studies have shown that a 1-degree Celsius increase in temperature during the growing season can result in a decline of 3-5% in wheat and rice yields. As global temperatures continue to rise, it is expected that crop productivity will be significantly reduced, leading to potential food shortages.Secondly, altered precipitation patterns due to climate change also pose challenges to food production. Some regions may experience increased rainfall, leading to waterlogging, soil erosion, and increased incidence of pests and diseases. On the other hand, other areas may face droughts and reduced water supplies, affecting crop growth and yield. For example, in regions heavily dependent on rainfall for agriculture, such as sub-Saharan Africa, decreased precipitation could lead to crop failures and increased food insecurity.Furthermore, global climate change is expected to increase the frequency and intensity of extreme weather events, such as hurricanes, typhoons, and floods. These events can cause significant damage to crops, livestock, and infrastructure, disrupting food production and distribution systems. In addition to physical damage, extreme weather events can also result in post-harvest losses and increased food waste due to transportation and storage difficulties. Consequently, the effects of these events can have long-lasting implications for food availability and accessibility.To adapt to the impact of global climate change on food production, various strategies can be employed. Firstly, there is a need for improved crop breeding and agronomic practices that enhance resilience and tolerance to higher temperatures and altered precipitation patterns. Research and development in drought-tolerant and heat-tolerant crop varieties can help mitigate the adverse effects of climate change on yields.Furthermore, investment in irrigation infrastructure and water management technologies is crucial to ensure water availability for agriculture, particularly in regions proneto droughts. Drip irrigation, rainwater harvesting systems, and improved water storage facilities can contribute to more efficient water use and reduce dependence on rainfall.Additionally, promoting sustainable and climate-smart agricultural practices can help enhance resilience and minimize greenhouse gas emissions. Practices such as conservation agriculture, agroforestry, and organic farming can improve soil health, reduce soil erosion, and enhance carbon sequestration. Moreover, adopting precision farming techniques that utilize data and technology to optimize crop management can improve resource efficiency and reduce environmental impacts.Lastly, strengthening global cooperation and implementing international policies to combat climate change are essential.Countries need to work together to reduce greenhouse gas emissions, promote renewable energy sources, and adapt to the consequences of climate change. International collaborations can provide support for developing countries in implementing adaptation strategies and ensure equitable access to resources and expertise.In conclusion, global climate change poses significant challenges to food production due to rising temperatures, altered precipitation patterns, and increased frequency of extreme weather events. These impacts have the potential to result in reduced crop yields, food shortages, and increased food insecurity. However, through the adoption of adaptation strategies such as improved crop varieties, water management techniques, sustainable agricultural practices, and global cooperation, it is possible to mitigate the effects of climate change and ensure food security for future generations.。
转基因的好处和坏处英语作文
转基因的好处和坏处英语作文The Pros and Cons of Genetic Engineering: A Balanced Perspective.Genetic engineering, often referred to as genetic modification or GM, has revolutionized the agricultural and medical landscapes, promising unprecedented benefits but also sparking concerns about its potential downsides. This technology allows scientists to alter the genetic makeup of organisms, conferring desired traits or characteristics. While the technology offers remarkable possibilities, it also raises ethical, environmental, and health-related questions.Advantages of Genetic Engineering.1. Improved Crop Resistance: Genetic engineering has enabled the development of crops that are resistant to herbicides, pests, and adverse environmental conditions. This has significantly reduced the need for chemicalpesticides and herbicides, thus minimizing environmental pollution and soil degradation.2. Enhanced Nutritional Value: GM crops can be engineered to have higher levels of vitamins, minerals, and other nutrients, making them more nutritious for human consumption.3. Increased Crop Yields: By inserting genes that confer drought tolerance, salt tolerance, or resistance to other abiotic stresses, genetic engineering has the potential to significantly increase crop yields, especially in marginal and stressed environments.4. Medical Breakthroughs: Genetic engineering has led to the development of innovative drugs and therapies, including gene therapies that aim to treat genetic diseases at their source. Additionally, biopharmaceuticals produced using GM microorganisms have revolutionized the treatment of various diseases.5. Environmental Restoration: GM microorganisms can beused to bioremediate polluted sites, breaking down harmful chemicals and toxins into harmless compounds. This has the potential to restore damaged ecosystems and protect the environment.Disadvantages of Genetic Engineering.1. Ecological Risks: The release of GM crops into the environment could lead to the transfer of genes to wild relatives or other species, potentially disrupting natural ecosystems and leading to the emergence of weedy or invasive varieties.2. Food Safety Concerns: There are concerns about the safety of GM foods for human consumption. Although numerous studies have found no significant risks, some studies have raised questions about potential allergenicity, toxicity, and nutritional changes in GM foods.3. Economic Implications: The widespread adoption of GM crops could have significant economic implications, potentially leading to the displacement of traditionalvarieties and affecting the livelihoods of farmers who rely on them.4. Ethical Dilemmas: Genetic engineering raises ethical questions about the manipulation of life and the potential impact on future generations. Some argue that it is unethical to modify the genetic material of organisms without fully understanding the long-term consequences.5. Social Acceptance: Despite the potential benefits of GM technology, there is widespread concern and resistance to its use, particularly among consumers who are concerned about the safety and ethics of GM foods. This social不接受ance can slow the adoption and dissemination of GM crops.Conclusion.Genetic engineering is a powerful technology thatoffers remarkable possibilities for improving agriculture, medicine, and environmental restoration. However, it also raises concerns about ecological risks, food safety, economic implications, ethical dilemmas, and socialacceptance. A balanced approach that considers both the benefits and risks is necessary to ensure that genetic engineering is used responsibly and sustainably. Ongoing research and monitoring are essential to address these concerns and ensure that the technology is used to benefit society while minimizing its potential downsides.。
土壤盐渍化的原因英文作文500字
土壤盐渍化的原因英文作文500字Soil salinization has become a severe global issue affecting agricultural productivity and ecosystem sustainability. Understanding its causes is crucial for developing effective mitigation and management strategies.In this essay, we will delve into the primary factors contributing to soil salinization.1. Natural Processes:a. Tectonic Activity: The uplift of certain geological formations, such as salt domes and ancient marine sediments, can bring salt-laden rocks close to the soil surface. Over time, weathering and erosion release these salts into the soil profile.b. Mineral Weathering: The weathering of certain minerals, such as pyrite and gypsum, can liberate soluble salts that accumulate in the soil. Pyrite oxidation, in particular, produces sulfuric acid, further exacerbatingsalinization.c. Atmospheric Deposition: Sea spray, volcanic eruptions, and dust storms can deposit salt particles into the soil. In coastal areas, salt deposition from ocean spray is a significant contributor to soil salinization.2. Human Activities:a. Irrigation: Over-irrigation is a major anthropogenic cause of soil salinization. When excess water is applied to soil, it dissolves and transports salts from deeper layers to the surface. As the water evaporates, these salts accumulate in the topsoil, increasing its salinity.b. Poor Drainage: Inadequate drainage systems allow water to stagnate in the soil, promoting the accumulation of salts. Poor soil permeability, high water tables, and excessive watering can lead to waterlogging and subsequent salinization.c. Deforestation: The removal of vegetation cover,particularly in arid and semi-arid regions, can disrupt the natural water cycle and increase soil evaporation rates. This leads to the concentration of salts in the topsoil, as water evaporates and leaves behind dissolved solids.d. Fertilization: The excessive application of certain fertilizers, especially those containing high levels of soluble salts, can contribute to soil salinization. Synthetic fertilizers, such as ammonium sulfate and potassium chloride, can release significant amounts ofsalts when applied in excessive quantities.3. Climate Change:a. Rising Sea Levels: In coastal areas, rising sea levels can lead to the intrusion of saltwater into freshwater aquifers and soil profiles. This saltwater intrusion increases the salinity of the soil, affecting plant growth and ecosystem health.b. Changes in Precipitation Patterns: Climate change can alter precipitation patterns, leading to more frequentand intense droughts or floods. These extreme events can exacerbate soil salinization through reduced water availability or increased salt deposition.c. Temperature Rise: Higher temperatures can increase the rate of evaporation, which in turn can concentratesalts in the topsoil. This is especially concerning in arid and semi-arid regions where water scarcity is already a challenge.Understanding the causes of soil salinization is essential for developing tailored management strategies. To mitigate the impact of natural processes, proper irrigation practices, adequate drainage systems, and sustainable land-use planning are crucial. Human activities can be regulated through responsible water use, efficient fertilizer application, and the promotion of sustainable agricultural practices. Climate change adaptation measures, such as improved drought tolerance in crops and the development of salt-tolerant plant varieties, are becoming increasingly important. By addressing the root causes of soil salinization, we can work towards preserving theproductivity of agricultural lands and safeguarding the health of ecosystems around the world.。
Plant tolerance to drought and salinity stress regulating
REVIEWPlant tolerance to drought and salinity:stress regulating transcription factors and their functional significance in the cellular transcriptional networkDortje Golldack •Ines Lu¨king •Oksoon Yang Received:18February 2011/Revised:25March 2011/Accepted:25March 2011/Published online:8April 2011ÓSpringer-Verlag 2011Abstract Understanding the responses of plants to the major environmental stressors drought and salt is an important topic for the biotechnological application of functional mechanisms of stress adaptation.Here,we review recent discoveries on regulatory systems that link sensing and signaling of these environmental cues focusing on the integrative function of transcription activators.Key components that control and modulate stress adaptive pathways include transcription factors (TFs)ranging from bZIP,AP2/ERF,and MYB proteins to general TFs.Recent studies indicate that molecular dynamics as specific homodimerizations and heterodimerizations as well as modular flexibility and posttranslational modifications determine the functional specificity of TFs in environ-mental adaptation.Function of central regulators as NAC,WRKY,and zinc finger proteins may be modulated by mechanisms as small RNA (miRNA)-mediated posttran-scriptional silencing and reactive oxygen species signaling.In addition to the key function of hub factors of stress tolerance within hierarchical regulatory networks,epige-netic processes as DNA methylation and posttranslational modifications of histones highly influence the efficiency of stress-induced gene prehensive elucidation of dynamic coordination of drought and salt responsive TFs in interacting pathways and their specific integration in the cellular network of stress adaptation will provide newopportunities for the engineering of plant tolerance to these environmental stressors.Keywords Drought ÁEpigenetics ÁTranscription factor ÁRNAi ÁSalt tolerance ÁArabidopsisIntroductionA major challenge for current agricultural biotechnology is to satisfy an ever increasing demand in food production facing a constantly increasing world population that will reach more than 9billion in 2050(Godfray et al.2010;Tester and Langridge 2010).This growing demand for food is paralleled by dramatic losses of arable land due to increasing severity of soil destruction by abiotic environ-mental conditions.Thus,drought and salinity are the two major environmental factors that adversely affect plant growth and development and have a crucial impact on agricultural productivity and yields.Drought due to short-age of water is critical for crop production in large agro-nomic areas worldwide and it is usually coped with extensive irrigations.Although earth is rich in water,most water resources are highly salinized whereas high quality fresh water that is suitable for irrigation is extremely lim-ited.Accordingly,not only drought but also soil salinity becomes increasingly an agricultural problem due to extensive spreading of agricultural practices as irrigation (Flowers 2004)and it urgently requires the breeding of crops with increased water use efficiency and salt tolerance.Exposure of plants to excess salt causes ion imbalance and ion toxicity-induced imbalances in metabolism.Another component of salinity is hyperosmotic stress that results in water deficit in a comparable way to drought-induced water deficit.Plants basically counteract theCommunicated by R.Reski.D.Golldack (&)ÁI.Lu¨king ÁO.Yang Department of Biochemistry and Physiology of Plants,Faculty of Biology,Bielefeld University,33615Bielefeld,Germanye-mail:dortje.golldack@uni-bielefeld.dePlant Cell Rep (2011)30:1383–1391DOI 10.1007/s00299-011-1068-0negative effects of salinity and drought by activation of biochemical responses that include(1)the synthesis and accumulation of osmolytes,(2)maintaining the intracel-lular ion homeostasis,and(3)scavenging of reactive oxygen species(ROS)generated as a secondary effect of drought(Flowers2004;Ashraf and Akram2009).Plant engineering strategies for cellular and metabolic reprogramming to increase the efficiency of plant adaptive processes may either focus on(1)conferring stress toler-ance by directly re-programming ion transport processes and primary metabolism or(2)by modulating signaling and regulatory pathways of the adaptive mechanisms.The second approach seems to be more perspective because it is likely that signaling and regulatory factors orchestrate as key signaling components the transcriptional and transla-tional control of group(1)adaptive mechanisms(Die´dhiou et al.2008;Popova et al.2008).Accordingly,molecular re-programming to enhance stress tolerance of plants would probably require the genetic engineering of a single or a few master regulators of adaptation instead of modulating numerous metabolic and cellular adaptive mechanisms.However,although several plant stress signaling com-ponents have been dissected in detail the knowledge on integration of regulatory mechanisms in stress signaling cascades and on key regulators is still limited,although knowledge on the regulating key factors of stress adap-tation is highly necessary for biotechnological engineering of stress tolerance.In this review,we focus on recent advances in transcription factor(TF)-based engineering of increased drought and salt adaptation.Putative integra-tions and links of TFs in stress adaptive signaling net-works coordinating the endogenous programs of environmental adaptation will be highlighted.Accord-ingly,for this review TFs out of the wider range of all stress inducible TFs were selected so that we do not comprehensively cover all stress-related factors.Major criterion for this selection was a putative potential of the TFs in controlling sub-regulons of stress-adaptive cellular mechanisms within the hierarchical transcriptional net-work that will be discussed in the review.Arabidopsis and related model species:learningfrom species with different natural stress tolerance Traditional breeding attempts for sustainable agricultural use of dry and salinized soils have been clearly facilitated and stimulated by the wealth of knowledge of genomics and transcriptomics data available from the model species Arabidopsis(Arabidopsis thaliana)and rice(Oryza sativa). Linear general frameworks of plant drought and salt adaptation have been established that were mainly based on systematic and comprehensive mutant analyses.Thus,it is now accepted that changes in membrane integrity and modulation of lipid synthesis are key factors in the primary sensing of drought and salt(Kader and Lindberg2010).Secondary,osmotic stress-induced sig-naling involves changes in plasma membrane H?-ATPase and Ca2?-ATPase activities that trigger concerted changes of Ca2?influx,cytoplasmic pH,and apoplastic production of ROS(Beffagna et al.2005).In addition,osmotic stress-induced Ca2?fluxes are linked to abscisic acid(ABA),and calcium-responsive protein kinases act as key regulators in drought and salinity-induced signaling cascades(Die´dhiou et al.2008).As convergent down-stream elements of transcriptional activation,many genes that are responsive to drought and to salinity belong to the ABA-responsive element(ABRE)and dehydration-responsive element/C-repeat element(DRE/CRT)regulons(Yamaguchi-Shino-zaki and Shinozaki2005).Despite this knowledge derived from the model plants Arabidopsis and rice,the applicability of these data for biotechnological engineering of increased drought and salt tolerance is clearly prehensive comparisons of the salt inducible transcriptomes of the salt-sensitive spe-cies Arabidopsis and rice and,for example,transcriptional data of the closely related salt-tolerant model species Lobularia maritima(Brassicaceae)and Festuca rubra ssp. litoralis(Poaceae)show extensive differences in salt responsive expressional regulations(Popova et al.2008; Die´dhiou et al.2009b;Fig.1).In contrast to salt excluding and avoiding halophyte models as Thellungiella halophila with a very limited number of salt responsive transcripts, the salt-accumulating and-detoxifying halophytes L. maritima and F.rubra ssp.litoralis allowed identification of a wide range of transcripts with different salt responsive regulation in the salt-sensitive and salt-tolerant species (Volkov et al.2003;Taji et al.2004;Popova et al.2008; Die´dhiou et al.2009b).In addition,transgenic modulation of regulatory and signaling elements in Arabidopsis and rice according to the pattern in the halophytes L.maritima and F.rubra ssp.litoralis successfully activated stress adaptation in the sensitive model species(Die´dhiou et al. 2008;Yang et al.2009).Accordingly,understanding of stress-induced signaling complexity in stress-sensitive model species has to be complemented by comparisons with naturally tolerant species for a systematic identifica-tion of key regulators of stress tolerance with the potential of biotechnological application.bZIP TFs and their role in conferring stress tolerance to plantsResearch on salt and drought regulatory TFs has mainly focused on single factors and linear pathways.Emergingfindings increasingly suggest,however,integration of the TFs in dynamic network hubs as well as interaction and competition of pathways manifesting complexity of molecular links in stress adaptation.The emerging view of the salt-and drought-signaling network unequivocally supports a key and integrative function of members of the bZIP TFs in these regulatory networks(Fig.2)and the potential of these factors to confer enhanced stress tolerance has been demonstrated repeatedly.A key regulator of salt stress adaptation,the group F bZIP TF bZIP24,was identified by differential screening of salt-inducible transcripts in A.thaliana and a halophytic Arabidopsis-relative model species(Yang et al. 2009).Expressional regulation of bZIP24was different with induced transcription in the salt-sensitive and tran-scriptional repression in the halotolerant species,and RNAi-mediated repression of the factor conferred increased salt tolerance to Arabidopsis.The improved tolerance was mediated by stimulated transcription of a wide range of stress-inducible genes that are e.g.involved in cytoplasmic ion homeostasis,osmotic adjustment,as well as in plant growth and development demonstrating a central function of bZIP24in salt tolerance by regulatingmultiple mechanisms that are essential for stress adaptation (Yang et al.2009).Next to bZIP24and its function in salt adaptation,group A bZIP factors AREB1,AREB2,and ABF3have a key regulatory role in ABA signaling under drought stress.Thus,A.thaliana areb1areb2abf3triple knock out mutants had increased tolerance to ABA and reduced drought tolerance(Yoshida et al.2010).In addi-tion,in other species as rice and tomato transgenic modi-fication of group A bZIP TFs modified the tolerance of plants to water deficit and to salt stress(Amir Hossain et al. 2009;Hsieh et al.2010)strongly suggesting trans-species potential of these factors for increasing stress tolerance.From animal systems dynamic coordinations of numer-ous bZIP controlled signal transduction pathways by molecular re-organization and by posttranslational mech-anisms are well-known(Jindra et al.2004;Miller2009). Thus,specific homodimerizations and heterodimerizations within the class of bZIP TFs as well as modularflexibility of the interacting proteins and posttranslational modifica-tions might determine the functional specificity of bZIP factors in cellular transcription networks(Miller2009). Excitingly,evidences for involvement of homologous mechanisms in signaling hubs in plant systems are just now 20304050At Lm Os Fremerging.As an example,the three factors AREB1,AREB2,and ABF3can form homodimers and heterodi-mers as well as interact with a SnRK2protein kinase suggesting ABA-dependent phosphorylation of the proteins (Yoshida et al.2010).As another example for the function of bZIP factors in salt adaptation in A.thaliana ,salt stress induced proteolytic processing and translocation of the group B factor AtbZIP17to the nucleus followed by transcriptional up-regulation of salt-responsive transcripts (Liu et al.2007).The group F factor AtbZIP24shows salt-inducible subcellular re-targeting to the nucleus and for-mation of homodimers suggesting that molecular dynamics of bZIP factors could mediate new signaling connections within the complex cellular signaling network (Yang et al.2009).In contrast to the homodimerization of bZIP24,specific heterodimerization was shown for the salt-responsive group S AtbZIP1with group C bZIP TFs (Weltmeier et al.2009).In conclusion,it might be hypothesized that specific homodimerizations and hetero-dimerizations as well as posttranslational modifications (e.g.phosphorylations)might determine the functional specificity of bZIP factors in the cellular transcription networks of drought and salt adaptation.Interestingly,transgenic over-expression of rice SnRK2-type SAPK4in rice regulated ion and ROS homeostasis under salt stresssupporting the hypothesis of key functions of SnRK kina-ses in the intracellular signaling cascades of osmotic adaptation thus further supporting key modulatory function of posttranslational phosphorylations in diverse plant sys-tems that might,e.g.target bZIP factors (Die´dhiou et al.2008;Fig.2).Recently,it was recognized that general TFs might also have an important role in stress-responsive transcription.Thus,the TBP-associated factor AtTAF10has a specific and key function in plant salt and osmotic stress adaptation by regulating accumulation of Na ?and proline (Gao et al.2006).This functional overlap to bZIP24(Yang et al.2009)strongly suggests linked regulation and cofunctions of bZIP proteins and TAFs within the complex drought and salt signaling network—a hypothesis that awaits further clarification (Fig.2).The role of WRKY TFs and Cys2/His2zinc finger proteins in the regulation of adaptation to osmotic stressOur understanding of plant stress-inducible signaling has been greatly facilitated by research on TFs that regulate and control subsets of stress-responsive geneexpression.Fig.2Model of signaling pathways and regulatorytranscription factors involved in plant adaptation to drought and saltThus,WRKY proteins regulate diverse plant processes ranging from development to various biotic and abiotic stresses as well as hormone-mediated pathways(Rama-moorthy et al.2008).Involvement of WRKY factors in plant salt adaptation were shown for WRKY25and WRKY33that increased salt tolerance and ABA sensitivity independent of the SOS-pathway when over-expressed in A.thaliana(Jiang and Deyholos2009).In A.thaliana, wrky63knock out mutants showed decreased sensitivity to ABA and drought(Ren et al.2010).In these plants,the stomatal closure and the expression of the AREB1/ABF2 TF were affected indicating involvement of WRKY fac-tors in the ABA-dependent pathway of drought and salt adaptation(Ren et al.2010).Potential of WRKY-type TFs to confer increased salt tolerance by transgenic expression is further supported by the different salt-induced regula-tion of a WRKY protein in salt-sensitive rice and a hal-ophytic rice-relative model species(Die´dhiou et al.2009a, b).Interestingly,A.thaliana WRKY25and WRKY33are not only responsive to osmotic stresses but they are also regulated by oxidative stress(Miller et al.2008).In addition,down-stream regulated target genes of WRKY33 include transcripts with function in ROS detoxification as peroxidases and glutathione-S-transferases(Jiang and Deyholos2009)suggesting function of WRKY factors as key regulators in both osmotic and oxidative stress adaptation.Alternatively,it is tempting to hypothesize involvement of WRKY factors in the osmotic stress sig-naling via control of the intracellular stress-induced ROS levels(Fig.2).Interestingly,Zat proteins(TFIIIA-type Cys2/His2zinc finger proteins)have been suggested to control and regulate WRKY functions(Miller et al.2008).Thus,in soybean overexpression of GmWRKY54conferred increased salt and drought tolerance and regulation of the GmWRKY54 by Zat10/STZ was hypothesized(Zhou et al.2008).In addition,in rice stomatal closure is regulated by the Cys2/ His2zincfinger protein DST(drought and salt tolerance) via ABA-independent targeting of genes that are involved in ROS homeostasis(Huang et al.2009).Thesefindings further support involvement of zincfinger proteins and probably WRKY TFs in osmotic adaptation via ROS sig-naling(Fig.2).Interestingly,although both drought and salt stress might result in intracellular accumulation of toxic amounts of ROS,hydrogen peroxide(H2O2)and nitric oxide(NO)also function as signaling molecules in ABA-mediated stomatal responses(Miller et al.2010; Wilkinson and Davies2010).Mutation of a cellulose synthase-like protein induced accumulation of ROS, changed sensitivity to salt stress and to water deficit,and regulation of plant osmotic stress tolerance via control of intracellular stress-induced ROS levels has been suggested (Zhu et al.2010a).Stress adaptation and multi-transcriptional regulation: AP2/ERF,MYB,and bHLH TFsNext to TFs with possible upstream position in the hier-archical network of stress adaptation as the bZIP factors described above,integrative stress-adaptive functional roles of regulatory proteins from other diverse groups have been reported.These factors might be either integrated in the main pathways of environmental adaptation,likely under control of the key regulatory TFs,or they might have functions in regulating sub-networks of adaptation to drought and salt stress and in linking these stress adapta-tions to other stresses,developmental and hormonal responses.Thus,dual roles in both biotic and abiotic stress responses have been demonstrated for AP2/ERF proteins as soybean GmERF3and the ABA-responsive RAP2.6from A.thaliana(Zhang et al.2009;Zhu et al.2010b).Over-expression of Arabidopsis light and drought responsive RAP2.4led to defects in multiple developmental processes regulated by light and ethylene as well as drought tolerance (Lin et al.2008).Complementary to these observations, overexpression of AP2/ERF GmERF3in tobacco induced the expression of PR genes and of osmotin accompanied by enhanced accumulation of free proline and soluble carbo-hydrates(Zhang et al.2009).Members of the DREB/CBF subfamily of the AP2/ERF TFs have been recognized for a decade for their roles in stress tolerance via ABA-depen-dent and-independent pathways and for their regulation of a stress-response sub-transcriptome with more than hun-dred target genes inclusive regulatory factors as ZAT12 and RAP2.1(Shinozaki and Yamaguchi-Shinozaki2000). However,constitutive overexpression of the DREB/CBF pathway led to serious developmental defects of transgenic plants although accompanied by increased tolerance to drought,salt,and cold(Kasuga et al.1999).These data clearly demonstrate complexity of the stress adaptive net-work that requires major control points of the multiple transcriptional sub-regulons as well as cooperative and integrative function of the different stress sub-clusters to prevent impairing side effects.Nevertheless,members of the AP2/ERF TF family are integrated as a hub in signaling interconnections of complex biotic and abiotic environ-mental cues.Supporting the undeniable key function of AP2/ERF in terms of drought and salt tolerance the picture of integrative function of these factors in plant develop-mental processes as well as biotic and/or abiotic stress signaling in an interconnecting and linking way is,how-ever,only emerging.As another example for multi-functional regulations,the R2R3-MYB TF AtMYB41is transcriptionally induced in response to ABA,drought,salinity,and cold(Lippold et al. 2009).In addition,the factor influences cell expansion and cuticle deposition suggesting a linking function in abioticstress response and cell wall modifications(Cominelli et al. 2008).Interaction and competition of complex signaling pathways infine-tuning cellular responses is further illustrated by the A.thaliana basic-helix-loop helix TF bHLH92.The factor regulates only the expression of a subset of salt-and drought-responsive genes(Jiang et al. 2009).However,different peroxidases are down-stream targets of the factor and bHLH92might have a function in the control of ROS-mediated signaling thus linking salt and drought adaptation to ROS signaling(Fig.2). Here,more detailed work will be necessary to elucidate the precise integration of the diverse TFs in the cellular network of stress adaptation and to understand their potential in genetic engineering of improved stress tol-erance,probably via targeted engineering of defined subsets of stress adaptive mechanisms or sub-pathways of signaling to customize specific features of stress adaptation.NAC-triggered gene expression and miRNANAC type proteins are not only involved in diverse pro-cesses as developmental programs,defense,and biotic stress responses(Olsen et al.2005)but they also have a key function in abiotic stress tolerance inclusive drought and salinity.Thus,in rice ONAC5and ONAC6are transcrip-tionally induced by ABA,drought,and salt stress(Rabbani et al.2003;Takasaki et al.2010).ONAC5and ONAC6 transcriptionally activate stress-inducible genes as OsLEA3 by direct binding to the promoter and they interact in vitro suggesting functional dimerization of these TFs(Takasaki et al.2010).Interestingly,overexpression of the Arabid-opsis factors ANAC019,ANAC055,and ANAC072caused increased drought tolerance of transgenic plants but they only changed transcription of a limited number of non-particularly salt-and drought-responsive genes(Tran et al. 2004).These important results strongly suggest interaction or co-regulation of NAC factors with other regulatory pathways or subsets of stress-inducible molecular mecha-nisms for achieving the significant increased stress toler-ance that was observed(Tran et al.2004).Improved drought and salt tolerance could also be achieved by transgenic overexpression of diverse NAC factors in spe-cies ranging from A.thaliana and rice to chickpea,wheat, and tomato(Peng et al.2009;Yokotani et al.2009;Xia et al.2010;Yang et al.2011).Interestingly,in tomato two NAC TFs were salt-inducible in a salt-tolerant cultivar but showed different expression in salt-sensitive tomato plants (Yang et al.2011).These data indicate that differences in plant salt tolerance might be due to different and specific transcriptional activation of NAC-dependent regulatory pathways.As important examples for conferring increased stress tolerance underfield conditions,in rice transgenic over-expression of SNAC1enhanced salt and drought tolerance and OsNAC10improved drought tolerance and grain yield (Hu et al.2006;Jeong et al.2010).OsNAC10-regulated target genes mainly included protein kinases and TFs of AP2,WRKY,LRR,NAC,and Zn-finger types as well as the stress-responsive genes cytochrome P450and the potassium transporter HAK5(Jeong et al.2010).These results support the view that NAC type TFs might be part of the general frameworks of drought and salt adaptation by connecting or regulating subsets of linear adaptive pathways but the NAC factors themselves are likely to be controlled by global regulatory factors of the network of stress adaptive transcription and metabolism.Thus, important evidence for cooperative regulation of stress responses by members of different TF families was pro-vided by the study of Tran et al.(2007)that showed interaction and co-function of the drought,salt,and ABA inducible zincfinger protein ZFHD1and a NAC factor.As it was recognized recently,members of the CCAAT-HAP TF family also have a potential key function in conferring stress tolerance to crops.Transgenic maize plants with increased expression of the CCAAT-HAP-type factor ZmNF-YB2showed improved drought tolerance underfield conditions(Nelson et al.2007).This effect was achieved by mechanisms independent of ABA and DREB/ CBF pathways supporting the hypothesis of concerted action of different TF families within subsets of regulatory modules in the cellular stress-response network.Interestingly,members of the NAC TF family are potential regulatory targets of the small RNA(miRNA) posttranscriptional silencing machinery(Rhoades et al. 2002;Guo et al.2005).As an example,recently a NAC domain containing TF was identified as a target of miR164 in switchgrass(Matts et al.2010).Thus,regulation of NAC TFs by miRNA-mediated cleavage of mRNAs together with data showing differential regulation of NAC factors in response to drought and salt stress indicate that these TFs might participate in the regulation of environmental adaptation through miRNA pathways.Next to NAC pro-teins,TFs e.g.of SCL,MYB,and TCP types were iden-tified as targets of drought and salt inducible miRNAs as miR159,miR168,miR171,and miR396(Liu et al.2008). Accordingly,it might be hypothesized that the cellular networks of drought-and salt-stress tolerance are regulated by miRNA-mediated targeting of convergent and divergent adaptive pathways under control of different stress-specific TFs.Accordingly,relevance of modification of drought and salt stress-specific signaling pathways via the miRNA machinery in a biotechnological context might be a pow-erful approach for genetic engineering of improved toler-ance but remains to be discovered.Epigenetics:what is next in terms of biotechnological application?Next to transcriptional regulations of abiotic stress responses,epigenetic processes are becoming a new and current chapter in plant environmental adaptation.Effi-ciency of gene expression is highly influenced by chro-matin structure that might be modulated epigenetically by processes as DNA methylation and posttranslational mod-ifications of histones.The histone-mediated structure of nucleosomes in the chromatin might be posttranslationally modified at the N-terminal tails of the core histone com-plexes(H2A,H2B,H3,H4)and thus influence nucleosome density,binding efficiency of TFs,and transcriptional activity(Chinnusamy and Zhu2009;Kim et al.2010).In addition to methylations of histones,also acetylations and phosphorylations as well as other posttranslational modi-fications of histones as ubiquitination,biotinylation,and sumoylation might have a modulating impact on the reg-ulation of stress-specific gene expression(Chinnusamy et al.2008).Meanwhile,it is accepted knowledge that phenotypes within one species may transmit different epigenetic information based on covalent modifications of DNA or histones(Fazzari and Greally2004).Thus,plant popula-tions from stress exposed habitats may carry inherited memories of stress adaptation and transfer this epigeneti-cally to next generations.As an example,the desert shrub Zygophyllum dumosum was posttranslationally methylated at histone H3under wet but less under dry growth condi-tions indicating posttranslational regulation of gene expression activity(Granot et al.2009).As it was also reported recently,natural populations of mangroves were DNA hypomethylated when grown under saline conditions in contrast to populations from non-saline sites(Lira-Medeiros et al.2010).Based on these results,it seems obvious to think on simulation of inherited memories of stress adaptation in biotechnological applications to confer increased drought and salt tolerance to naturally sensitive species.However,in contrast to the detailed knowledge on influences of epigenetic mechanisms on developmental processes,information on epigenetic regulation of abiotic stress resistance is still rare.As a few examples,salinity-induced phosphorylation of histone H3and acetylation of histone H4in A.thaliana and tobacco have been reported(Sokol et al.2007).In addition, altered acetylation as well as trimethylation of histone H3 under drought stress in drought-responsive genes of A. thaliana have been observed(Kim et al.2008).In rice, expression of cytosine DNA methyltransferases was mod-ified by salt stress indicating functional importance of epigenetic modulation of genome activity also in monocot species(Sharma et al.2009).Detailed knowledge on the specific mechanisms that underlay epigenetic regulation under environmental expo-sure is,however,only slowly emerging.Thus,trans-gen-erational modifications of stress adaptations as salt stress include altered genomic DNA methylation as well as function of Dicer-like proteins suggesting involvement of small RNA pathways in epigenetic regulations(Boyko et al.2010).Interestingly,in barley expression of Poly-comb proteins with function in histone methylation was influenced by abscisic acid(ABA)suggesting involvement of ABA-mediated pathways in epigenetic modifications (Kapazoglou et al.2010).Thus,according to the current knowledge,an applica-tion of epigenetic processes to improve the stress-regulat-ing function of TFs will be a challenging and novel biotechnological approach for the engineering of plant tolerance to drought and salinity,however,many detailed information are still missing.Particularly,despite the importance of elucidating epigenetic mechanisms in model plants,it will be obligatory to extend investigations to systematic and comprehensive comparisons of stress rele-vant epigenetics in sensitive-and naturally tolerant species. Linking epigenetic processes to the key regulatory com-ponents of the general stress adaptive frameworks will be essential to further support the feasibility of epigenetics in the customized engineering of stress adaptation. Conclusion and perspectivesCellular effects of environmental stresses as drought and salinity are not only imbalances of ionic and osmotic homeostasis but also impaired photosynthesis,cellular energy depletion,and redox imbalances.Regulatory sys-tems inclusive TFs that link sensing and signaling of the environmental conditions and the cellular adaptive responses are emerging but are not well understood yet.As a next step,it will be important to identify master regula-tors and master pathways of stress adaptation in naturally stress-tolerant species as well as integration of the diverse regulatory factors in the network of intracellular stress adaptation pathways(Fig.2).Within this hierarchical net-work,cellular stress responses might befine tuned by interaction and competition of TFs that regulate sub-clus-ters of the stress transcriptome.Here,systematic and comprehensive data on the timing of all stress responsive TFs upon stress will be indispensable for detailed hierar-chical linking of all regulatory factors.In addition,more detailed understanding of shared and competing transcrip-tional regulation as well as modulated intramolecular interactions of different factors and epigenetic processes will be essential for targeted and efficient genetic engi-neering of improved drought and salt tolerance in plants.。
γ-氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化
㊀Guihaia㊀Dec.2023ꎬ43(12):2338-2351http://www.guihaia-journal.comDOI:10.11931/guihaia.gxzw202211003林欣琪ꎬ魏茜雅ꎬ梁腊梅ꎬ等ꎬ2023.γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化[J].广西植物ꎬ43(12):2338-2351.LINXQꎬWEIQYꎬLIANGLMꎬetal.ꎬ2023.EffectsofGABAseedprimingonalleviatingsaltstressandphysiologicalandbiochemicalchangesinCapsicumannuum[J].Guihaiaꎬ43(12):2338-2351.γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化林欣琪ꎬ魏茜雅ꎬ梁腊梅ꎬ秦中维ꎬ李映志∗(广东海洋大学滨海农业学院ꎬ广东湛江524088)摘㊀要:种子引发是提高作物生长期耐盐性的有效方法ꎬ而γ ̄氨基丁酸(GABA)种子引发对辣椒(Capsicumannuum)耐盐性的效果和作用机制尚不清楚ꎮ该研究以 茂蔬360 朝天椒为材料ꎬ分析了不同浓度γ ̄氨基丁酸(0㊁1.0㊁2.0㊁4.0㊁6.0㊁8.0μmol L ̄1)种子引发对4~6叶期100mmol L ̄1NaCl胁迫下的植株生物量㊁渗透调节物质㊁抗氧化能力㊁光合作用系统及钾钠离子吸收的影响ꎮ结果表明:(1)种子引发能显著增加盐胁迫下辣椒植株的生物量ꎬ以6.0μmol L ̄1GABA引发处理的效果最佳ꎮ(2)种子引发处理增加盐胁迫下植株可溶性糖㊁可溶性蛋白㊁脯氨酸的含量ꎬ同时ꎬO2-和MDA的含量下降ꎬ抗氧化酶(SOD㊁POD㊁CAT和APX)活性增强ꎬ叶片叶绿素含量增加ꎬ叶片叶绿素荧光参数受胁迫影响程度低ꎬ叶绿素荧光指标包括Fvᶄ/Fmᶄ㊁qP_Lss㊁QY_Lss㊁NPQ_Lss和Rfd均有所上升ꎮ根㊁茎中的K+含量和K+/Na+比值下降ꎮ(3)灰色关联度分析表明ꎬGABA种子引发主要通过提高POD㊁CAT的活性和渗透调节物质含量来缓解盐胁迫对辣椒植株的伤害ꎮ综上所述ꎬ6.0μmol L ̄1GABA种子引发可有效提高辣椒苗期的耐盐性ꎬ其作用机制可能是提高了盐胁迫下辣椒植株的抗氧化能力和渗透调节能力ꎮ关键词:γ ̄氨基丁酸(GABA)ꎬ辣椒ꎬ种子引发ꎬ耐盐性ꎬ灰色关联度分析中图分类号:Q945㊀㊀文献标识码:A㊀㊀文章编号:1000 ̄3142(2023)12 ̄2338 ̄14EffectsofGABAseedprimingonalleviatingsaltstressandphysiologicalandbiochemicalchangesinCapsicumannuumLINXinqiꎬWEIQianyaꎬLIANGLameiꎬQINZhongweiꎬLIYingzhi∗(CollegeofCoastalAgriculturalSciencesꎬGuangdongOceanUniversityꎬZhanjiang524088ꎬGuangdongꎬChina)收稿日期:2023-05-15基金项目:广东省科技厅科技计划项目(2016A020210116ꎬ2012A020602051)ꎻ广东海洋大学创新强校项目(GDOU2013050217ꎬGDOU2016050256)ꎮ第一作者:林欣琪(1997-)ꎬ硕士研究生ꎬ研究方向为热带园艺作物栽培生理ꎬ(E ̄mail)134****2564@163.comꎮ∗通信作者:李映志ꎬ博士ꎬ教授ꎬ研究方向为热带园艺植物栽培与育种ꎬ(E ̄mail)liyz@gdou.edu.cnꎮAbstract:Seedprimingisprovedtobeanefficientwaytoimprovecropsalttoleranceꎬwhichisameasureofpre ̄treatingseedwithvariousagentswhileobtainingenhancementtocropperformanceatgrowingstage.Gammaaminobutyricacid(GABA)isanon ̄proteinaminoacidinvolvedinvariousmetabolicprocessesꎬandpartiallyprotectsplantsfromenvironmentalstress.EnhancingeffectsofGABAprimingongerminationcharacteristicsandabioticstresshavebeenestablishedinseveralcrops.HoweverꎬtheeffectandmechanismofGABAseedprimingonsalttoleranceofpepper(Capsicumannuum)arestillunknown.Inthisstudyꎬahybridpeppervarietyof Maoshu360 ChaotianpepperwasusedasmaterialꎬtheeffectsofseedprimingwithvariousconcentrationsofGABA(0ꎬ1.0ꎬ2.0ꎬ4.0ꎬ6.0ꎬ8.0μmol L ̄1)onplantbiomassꎬleafosmoticregulatingsubstanceꎬleafantioxidantcapacityꎬleafphotosynthesissystemꎬpotassiumandsodiumionuptakeanddistributionbetweenleavesandshootsofpepperplantsunder100mmol L ̄1NaClstressappliedat4-6leafstagewereinvestigated.Theresultswereasfollows:(1)FromthepointofplantgrowthundersaltstressꎬthebestconcentrationofGABAforseedprimingofpepperwas6.0μmol L ̄1ꎬwhichgreatlyboostedthebiomassofpepperplantsundersaltstress.(2)ThemechanismsofGABAseedprimingpromotingsalttoleranceofpepperwerefurtheranalyzed.SeedprimingincreasedtheleafcontentsofsolublesugarꎬsolubleproteinꎬchlorophyllandprolineꎬdecreasedtheleafcontentsofO2-andmalondialdehyde(MDA)ꎬenhancedtheleafactivitiesofantioxidantenzymesꎬincludingsuperoxidedismutase(SOD)ꎬperoxidase(POD)ꎬcatalase(CAT)andascorbateperoxidase(APX)ꎬandraisedseveralchlorophyllfluorescencemetricsꎬincludingFvᶄ/FmᶄꎬqP_LssꎬQY_LssꎬNPQ_LssandRfdꎬreducedtheK+contentandK+/Na+ratioinrootsandstems.(3)ForacomprehensiveunderstandingofthemechanismsofGABAseedprimingpromotingsalttoleranceofpepperꎬgreycorrelationanalysiswascarriedout.BasedonresultsofgreycorrelationanalysisꎬseedprimingwithGABAsignificantlyalleviatedsaltstresstopepperplantsbyboostingtheactivitiesoftheantioxidantenzymesPODandCATaswellasincreasingthelevelsofosmoticregulators.Inconclusionꎬseedprimingwith6.0μmol L ̄1GABAsignificantlyincreasessalttoleranceofpepperseedlingsꎬprobablybyimprovingantioxidantandosmoticregulatingcapacitiesofpepperplants.Keywords:γ ̄aminobutyricacid(GABA)ꎬCapsicumannuum(pepper)ꎬseedprimingꎬsalttoleranceꎬgreycorrelationanalysis㊀㊀近年来ꎬ全球已有1.1ˑ109hm2陆地表面受到盐渍化的影响ꎬ我国盐渍土总面积达3.69ˑ107hm2ꎬ盐渍化已成为农业可持续生产的重要障碍(杨劲松等ꎬ2022)ꎮ土壤盐分作为一种非生物胁迫因子ꎬ主要通过降低种子萌发率㊁影响植株活力㊁细胞离子稳态和代谢途径来对作物产量产生不利影响(Shabalaetal.ꎬ2016ꎻElbadrietal.ꎬ2021)ꎮ辣椒(Capsicumannuum)是重要的茄果类蔬菜ꎬ在我国的种植面积超过2.1ˑ106hm2(邹学校等ꎬ2020)ꎮ辣椒对盐度敏感或中等敏感ꎬ生长发育过程中受到的盐胁迫会导致产量降低和果实品质下降(胡华冉等ꎬ2022)ꎮ国内外学者对盐逆境的作用机制进行了广泛研究ꎬ目前主要认为盐分会直接或间接地引起活性氧(reactiveoxygenspeciesꎬROS)的过量积累和氧化胁迫(AbdelLatef&Heꎬ2014)ꎬ造成离子毒性和营养失衡ꎬ限制水分吸收㊁降低光合效率ꎬ最终导致生长发育不良或植株死亡(Cuarteroetal.ꎬ2006ꎻAfzaletal.ꎬ2008ꎻNoumanetal.ꎬ2014)ꎮ植物可采用多种机制应对盐胁迫ꎬ如调节气孔㊁维持细胞膜的完整性㊁改变激素平衡㊁激活抗氧化系统㊁调节渗透势以及排斥有毒离子等(Netoetal.ꎬ2005ꎻAbdelLatefetal.ꎬ2019)ꎮ种子引发是一种新兴的㊁提高植株生长发育期逆境抗性的种子处理技术ꎬ其作用机制目前尚不清楚ꎬ可能是通过控制种子的有限活化或逆境驯化ꎬ改变基因的表达模式ꎬ使之处于耐受逆境的准备状态(李洁等ꎬ2016)ꎮ种子引发可激活应激反应系统ꎬ使种子在暴露于未来的胁迫时ꎬ具有 交叉耐受性 (Bhanuprakash&Yogeeshaꎬ2016)ꎮ目前ꎬ种子引发作为一种实用㊁经济㊁低风险㊁无生物安全风险的栽培措施ꎬ不但能够改善逆境下种子的萌发和出苗(Migahidetal.ꎬ2019)ꎬ而且可通过记忆效应提高植株生长发育期的逆境抗性ꎬ这种记忆效应甚至可遗传(Margareteetal.ꎬ2019)ꎮγ ̄氨基丁酸(γ ̄aminobutyricacidꎬGABA)是一种非蛋白四碳氨基酸ꎬ由谷氨酸脱羧或二胺氧化酶降解多胺产生的新型植物生长调节物质(Wangetal.ꎬ2014)ꎮ植株在逆境胁迫时ꎬGABA可在细胞中快速积累ꎬ通过提高抗氧化应激反应ꎬ调节碳933212期林欣琪等:γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化氮代谢和细胞质pH值ꎬ以及参与渗透调节和信号转导等途径提高植株对逆境的适应能力(贾琰等ꎬ2014ꎻ张海龙等ꎬ2020)ꎮ在盐胁迫中ꎬGABA作为信号物质或临时氮库ꎬ通过调节植株的抗氧化能力和改善叶片的光合特性ꎬ对植物的耐盐性产生重要影响(Lietal.ꎬ2016ꎻRameshetal.ꎬ2017ꎻKaspaletal.ꎬ2021)ꎮ本研究以种子引发和辣椒耐盐性为研究要点ꎬ采用生物量和生理生化分析方法ꎬ通过研究GABA种子引发处理对盐胁迫下辣椒植株生长和生理生化的影响ꎬ拟探讨:(1)GABA种子引发处理对辣椒植株耐盐性的影响ꎻ(2)GABA种子引发处理提高辣椒植株耐盐性的最佳处理浓度ꎻ(3)GABA种子引发处理提高辣椒植株耐盐性的作用机制ꎮ1㊀材料与方法1.1材料和处理供试材料为 茂蔬360 朝天椒ꎬγ ̄氨基丁酸(GABA)购于上海生工商贸有限公司ꎮ1.1.1种子引发处理㊀γ ̄氨基丁酸(GABA)引发处理设置0(蒸馏水ꎬT0)㊁1.0(T1)㊁2.0(T2)㊁4.0(T4)㊁6.0(T6)㊁8.0(T8)μmol L ̄16个浓度ꎮ选取大小一致㊁籽粒饱满的辣椒种子1.8g(约100粒)置于不同浓度的GABA溶液中ꎬ种子质量(g)与溶液体积(mL)比为1ʒ5(吴凌云等ꎬ2017)ꎬ在20ħ黑暗条件下引发24hꎮ引发结束后ꎬ用蒸馏水洗净种子残余的GABAꎬ吸干表面水分ꎬ置于鼓风干燥箱中28ħ回干至原始质量ꎮ重复3次ꎮ1.1.2盐胁迫处理㊀将引发和未引发的种子在正常基质内催芽后ꎬ播种至15孔盘穴中ꎬ正常管理ꎬ以未进行种子引发处理的植株为对照(CK)ꎮ待植株长至4~6叶时ꎬ每两天每株用50mLNaCl溶液(100mmol L ̄1)浇灌ꎬ14d后取样分析ꎮ每处理20株ꎬ重复3次ꎮ1.2方法1.2.1植株生长情况㊀每个处理随机选取5株辣椒植株ꎬ测定每株植株的株高和根㊁茎和叶的鲜重及干重ꎮ1.2.2酶活性及代谢物质含量的测定㊀每处理随机选取5株ꎬ取植株上部完全展开叶用于分析ꎮ可溶性蛋白含量的测定参考Bradford(1976)的方法ꎻ采用蒽酮比色法测定可溶性糖含量ꎬ硫代巴比妥酸法测定丙二醛(malondialdehydeꎬMDA)含量李合生(2012)ꎻ抗坏血酸过氧化物酶(ascorbateperoxidaseꎬAPXꎬU g ̄1 min ̄1FW)的测定参照Nakano和Asada(1981)的方法ꎻ还原型抗坏血酸(ascorbicacidꎬAsA)㊁脱氢抗坏血酸(dehydroascorbateꎬDHA)的含量测定参照杨颖丽等(2018)的方法ꎻ脯氨酸(prolineꎬPro)㊁过氧化氢(hydrogenperoxideꎬH2O2)㊁超氧阴离子(superoxideanionꎬO2-)的含量和超氧化物歧化酶(superoxidedismutaseꎬSODꎬU g ̄1FW)㊁过氧化物酶(peroxidaseꎬPODꎬU g ̄1FW)㊁过氧化氢酶(catalaseꎬCATꎬU g ̄1FW)㊁谷胱甘肽还原酶(glutathionereductaseꎬGRꎬU g ̄1FW)的活性测定均采用试剂盒法(索莱宝科技有限公司)ꎬ酶活性U指在最适条件下1min催化1μmol底物转化的酶量ꎮ1.2.3叶绿素含量的测定㊀每处理随机选取5株ꎬ选距生长点第2~5片完全展开叶ꎬ使用SPAD ̄502仪(柯尼卡美能达)测定叶绿素含量(Wakiyamaꎬ2016)ꎮ1.2.4叶绿素荧光参数的测定㊀叶绿素荧光参数值采用FluorPen叶绿素荧光分析仪(CzechRepublicꎬPhotonSystemsInstruments)测定ꎬ每处理随机选择6株ꎬ每株选取植株顶端完全展开叶片测定Fv/Fmꎬ植株暗室放置20min后测定其他叶绿素荧光参数值ꎬ即潜在最大量子产量(Fvᶄ/Fmᶄ)㊁稳态光化学淬灭(qP_Lss)㊁稳态非光化学淬灭(NPQ_Lss)㊁稳态光量子效率(QY_Lss)和荧光衰减率(Rfd)ꎮ1.2.5Na+、K+的含量测定㊀每处理随机选取5株ꎬ蒸馏水清洗后ꎬ分别取烘干后的根㊁茎㊁叶进行分析ꎮ采用浓硫酸-H2O2消煮法(鲍士旦ꎬ2000)消解干样ꎬ滤液采用火焰原子吸收法(鲍士旦ꎬ2000)测定K+㊁Na+的含量ꎮ1.3数据分析在Excel2019软件中进行数据常规处理ꎬ用SPSS25.0软件对数据进行单因素方差分析ꎬ采用Duncan s法进行多重比较ꎬ运用SPASSAU在线平台进行灰色关联度分析ꎮ2㊀结果与分析2.1不同浓度GABA种子引发处理对盐胁迫下辣椒生长的影响不同浓度GABA种子引发处理对盐胁迫下辣0432广㊀西㊀植㊀物43卷椒植株生长的影响见图1ꎮ由图1可知ꎬGABA种子引发处理可提高辣椒植株的根㊁茎㊁叶的鲜重㊁干重及株高ꎮ不同浓度GABA种子引发的效果不同ꎬT6处理(6.0μmol L ̄1GABA)的效果最佳ꎬ其次为T4和T2处理ꎬ三者除茎干重与株高无显著差异外ꎬ其余均显著高于未引发处理(CK)ꎮ根㊁茎㊁叶的鲜重分别比CK增加72.4%㊁163.9%㊁94.3%ꎬ根㊁茎㊁叶的干重分别比CK增加1.20倍㊁2.22倍㊁1.56倍ꎬ株高增高0.92倍ꎻ根㊁茎㊁叶的鲜重分别比T0处理增加了62.2%㊁138.5%㊁88.3%ꎬ根㊁茎㊁叶的干重分别比T0增加1.03倍㊁2.14倍㊁1.28倍ꎬ株高增高0.86倍ꎮ这表明盐胁迫条件下ꎬGABA种子引发处理的辣椒植株长势更好ꎬ根㊁茎㊁叶的生物量积累更多ꎮ2.2不同浓度GABA种子引发处理对盐胁迫下辣椒植株相关酶活性及代谢物质含量的影响2.2.1对盐胁迫下辣椒叶片可溶性糖㊁可溶性蛋白㊁脯氨酸含量的影响㊀不同浓度GABA种子引发处理对盐胁迫下辣椒植株叶片可溶性糖㊁可溶性蛋白和脯氨酸含量的影响见图2ꎮ由图2可知ꎬGABA种子引发处理可不同程度增加盐胁迫下叶片3种物质的含量ꎮ当GABA浓度为6.0μmol L ̄1时各值达到最大ꎬ显著高于未引发植株ꎬ可溶性糖含量增加1.28倍ꎬ可溶性蛋白含量增加1.72倍ꎬ脯氨酸含量增加1.04倍ꎻ与T0相比ꎬ可溶性糖含量增加0.94倍ꎬ可溶性蛋白的含量增加0.97倍ꎬ脯氨酸含量增加0.79倍ꎮ其中T4处理的可溶性糖㊁可溶性蛋白的含量与T6处理无显著差异ꎬ较降低0.83%㊁11.8%ꎬT6处理脯氨酸的含量是T4处理的1.27倍ꎬ与其他处理组差异显著ꎮ这表明GABA种子引发处理可促进盐胁迫下辣椒植株的生理活动和渗透调节物质的积累ꎮ2.2.2对盐胁迫下辣椒叶片H2O2㊁O2-和MDA含量的影响㊀由图3可知ꎬ与未进行种子引发的植株相比ꎬGABA种子引发处理可提高叶片H2O2含量ꎬ降低O2-含量和MDA含量ꎮ盐胁迫下辣椒植株叶片H2O2含量以T6处理最高ꎬ与其他处理组间存在显著差异ꎬ与未进行种子引发处理的植株相比ꎬ增加2.1倍ꎬ比T0处理增加1.04倍ꎻO2-㊁MDA含量以T6处理最低ꎬ分别较未引发处理下降63.6%㊁73.6%ꎬ与T0相比ꎬ分别降低73.0%㊁68.8%ꎬ与GABA引发处理组T1㊁T2㊁T4㊁T8之间无显著差异ꎮ可见GABA种子引发处理能有效缓解盐胁迫下辣椒植株叶片的活性氧积累和细胞膜的氧化损伤ꎮ2.2.3对盐胁迫下辣椒植株叶片SOD㊁POD㊁CAT㊁APX㊁GR活性的影响㊀由图4可知ꎬ盐胁迫下ꎬGABA种子引发处理可显著提高叶片SOD㊁POD㊁CAT和APX的活性ꎬ均在6.0μmol L ̄1GABA处理中达到峰值ꎬ但对GR活性影响不明显(图4:E)ꎮ除T4处理的POD活性外ꎬ其他GABA引发处理的SOD㊁POD㊁CAT和APX活性与T6处理间均存在显著差异ꎮ与CK相比ꎬT6处理的SOD㊁POD㊁CAT和APX活性分别增加了0.44倍㊁4.09倍㊁7.22倍和1.35倍ꎻ比T0处理的SOD㊁POD㊁CAT和APX活性分别增加了0.32倍㊁3.30倍㊁1.13倍和1.04倍ꎮGR活性在未引发㊁水引发与GABA引发处理间没有规律性差异ꎮ可见GABA种子引发处理提高了盐胁迫下辣椒植株叶片由SOD㊁POD㊁CAT㊁APX酶介导的抗氧化能力ꎮ2.2.4对盐胁迫下辣椒植株叶片AsA㊁DHA的含量及两者比值的影响㊀由图5可知ꎬGABA种子引发处理可提高叶片AsA含量和AsA/DHA比值ꎬ降低DHA含量ꎮ其中AsA含量以T8处理最高ꎬ与T4处理间存在显著差异ꎬ是T4处理的1.40倍ꎮ相比未引发处理的叶片ꎬ增加了62.3%ꎬ比T0处理增加2.02倍ꎮGABA种子引发处理的抗坏血酸(AsA)含量高和氧化产物(DHA)含量低ꎬ这表明引发处理后的叶片抗氧化能力增强或自由基胁迫较低ꎮ2.3不同浓度GABA种子引发对盐胁迫下辣椒植株叶片叶绿素含量的影响不同浓度GABA种子引发处理对盐胁迫下辣椒植株叶片叶绿素含量的影响见图6ꎮ由图6可知ꎬ只有6.0μmol L ̄1GABA种子引发的叶片叶绿素含量与CK㊁T0有显著差异ꎬ含量分别提高了8.78%㊁8.41%ꎻ当GABA浓度达到8.0μmol L ̄1时ꎬ与T6处理存在显著差异ꎬ降低了16.0%ꎮ这说明适当浓度的GABA引发处理能缓解盐胁迫下辣椒植株叶片叶绿素的降解ꎮ2.4不同浓度GABA种子引发对盐胁迫下辣椒植株叶片叶绿素荧光特性的影响不同浓度GABA引发处理对盐胁迫下辣椒植株叶片叶绿素荧光特性的影响见图7ꎮ由图7可知ꎬ与CK㊁T0相比ꎬGABA种子引发处理的叶片Fo下降ꎬFv/Fm无显著差异ꎬFvᶄ/Fmᶄ㊁qP_Lss㊁NPQ_143212期林欣琪等:γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化不同字母表示差异显著(P<0.05)ꎮ下同ꎮDifferentlettersinthesamecolumnrepresentsignificantdifferences(P<0.05).Thesamebelow.图1㊀不同浓度GABA种子引发对盐胁迫下辣椒植株根鲜重(A)㊁茎鲜重(B)㊁叶鲜重(C)㊁根干重(D)㊁茎干重(E)㊁叶干重(F)和株高(G)的影响Fig.1㊀EffectsofdifferentconcentrationsofGABAseedprimingonrootfreshweight(A)ꎬstemfreshweight(B)ꎬleaffreshweight(C)ꎬrootdryweight(D)ꎬstemdryweight(E)ꎬleafdryweight(F)andplantheight(G)ofpepperplantsundersaltstressLss㊁QY_Lss和Rfd均显著上升ꎮ与CK相比ꎬT6处理的Fo最低ꎬ降低5.04%ꎻFvᶄ/Fmᶄ㊁qP_Lss㊁NPQ_Lss㊁QY_Lss和Rfd最高ꎬ分别增加10.5%㊁22.3%㊁40.0%㊁14.5%和36.1%ꎻ相较T0处理ꎬFo下降14.6%ꎬFvᶄ/Fmᶄ㊁qP_Lss㊁NPQ_Lss㊁QY_Lss和Rfd分别增加了5.47%㊁29.5%㊁10.4%㊁26.0%和27.0%ꎮ这表明GABA种子引发处理能使光合系统保持相对稳定的状态ꎬ促进光合作用的正常进行ꎮ2.5不同浓度GABA种子引发对盐胁迫下辣椒植株Na+㊁K+的含量及K+/Na+比值的影响不同浓度GABA种子引发处理对盐胁迫下辣椒根㊁茎和叶K+㊁Na+含量的影响见图8ꎮ由图82432广㊀西㊀植㊀物43卷图2㊀不同浓度GABA种子引发对盐胁迫下辣椒植株叶片可溶性糖含量(A)㊁可溶性蛋白含量(B)和脯氨酸含量(C)的影响Fig.2㊀EffectsofdifferentconcentrationsofGABAseedprimingonsolublesugarcontent(A)ꎬsolubleproteincontent(B)andprolinecontent(C)inleavesofpepperplantsundersaltstress图3㊀不同浓度GABA种子引发对盐胁迫下辣椒植株叶片H2O2含量(A)㊁O2-含量(B)和丙二醛含量(C)的影响Fig.3㊀EffectsofdifferentconcentrationsofGABAseedprimingonH2O2content(A)ꎬO2-content(B)andMDAcontent(C)inleavesofpepperplantsundersaltstress可知ꎬ辣椒植株的根㊁茎㊁叶的K+含量依次增加ꎻNa+含量在根㊁茎㊁叶间无显著差异ꎮGABA种子引发处理可降低根和茎中K+含量ꎬ对叶中K+含量无显著影响ꎻ对根中Na+含量无显著影响ꎬ部分处理可提高茎和叶中Na+含量(分别为T0和T8处理)ꎻT1处理降低了根和茎的K+/Na+比值ꎬ对叶的K+/Na+比值无显著影响ꎮ2.6不同浓度GABA种子引发处理对盐胁迫下辣椒植株生理指标的灰色关联度分析将38个生理指标看作一个灰色系统ꎬ其中不同处理作为参考序列ꎬ生理指标作为比较序列ꎬ使用初值化量纲处理方式ꎬ综合分析两者的关联度ꎮ由表1可知ꎬ关联度介于0.556~0.755ꎬ该值越大表示评价项与 参考值 相关性越强ꎮ其中POD活性的综合评价最高(关联度为0.755)ꎬ其次为CAT活性(关联度为0.692)和可溶性蛋白含量(关联度为0.688)ꎮ这说明GABA种子引发处理主要通过增加POD㊁CAT的活性和可溶性蛋白含量等途径来缓解盐胁迫对辣椒植株的伤害ꎮ343212期林欣琪等:γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化图4㊀不同浓度GABA种子引发对盐胁迫下辣椒植株叶片SOD活性(A)㊁POD活性(B)㊁CAT活性(C)㊁APX活性(D)和GR活性(E)的影响Fig.4㊀EffectsofdifferentconcentrationsofGABAseedprimingonactivitiesofSOD(A)ꎬPOD(B)ꎬCAT(C)ꎬAPX(D)andGR(E)inleavesofpepperplantsundersaltstress图5㊀不同浓度GABA种子引发对盐胁迫下辣椒植株叶片还原型抗坏血酸含量(A)㊁脱氢抗坏血酸含量(B)和AsA/DHA(C)的变化Fig.5㊀EffectsofdifferentconcentrationsofGABAseedprimingoncontentsofAsA(A)ꎬDHA(B)andAsA/DHA(C)inleavesofpepperplantsundersaltstress4432广㊀西㊀植㊀物43卷图6㊀不同浓度GABA种子引发对盐胁迫下辣椒植株叶片叶绿素含量的影响Fig.6㊀EffectsofdifferentconcentrationsofGABAseedprimingonchlorophylcontentinleavesofpepperplantsundersaltstress3㊀讨论与结论已有研究表明ꎬ种子引发处理可提高作物在生长发育期对盐胁迫的耐受性(Chenetal.ꎬ2021ꎻZafaretal.ꎬ2022ꎻAdhikarietal.ꎬ2022)ꎮ在辣椒中ꎬ氯化钾㊁过氧化氢㊁5-氨基乙酰丙酸等被用于种子引发处理来提高生长发育期植株对干旱㊁盐碱或低温的耐受性(Korkmaz&Korkmazꎬ2009ꎻRinezetal.ꎬ2018ꎻGammoudietal.ꎬ2020ꎻSolichatunetal.ꎬ2022ꎻ)ꎮGABA被认为是一种与植物逆境适应有关的新型植物生长调节物质(贾琰等ꎬ2014ꎻ张海龙等ꎬ2020)ꎮGABA用于白三叶草(Trifoliumrepens)㊁黑胡椒(Pipernigrum)种子引发处理时ꎬ可提高其在水分或渗透胁迫下的生物量(Vijayakumari&Puthurꎬ2016ꎻZhouetal.ꎬ2021)ꎮ将GABA添加到水培营养液中能促进盐胁迫下玉米幼苗的生长ꎬ提高株高和根㊁茎㊁叶的鲜重和干重(王泳超ꎬ2016)ꎻ能促进盐胁迫下番茄(Lycopersiconesculentum)根㊁茎和叶的生长(罗黄颖等ꎬ2011)ꎮGABA种子引发处理在辣椒上的应用尚未见报道ꎮ本研究表明不同浓度的GABA种子引发处理能有效地改善盐胁迫下辣椒植株的生长状况ꎬ增加株高以及根㊁茎㊁叶的鲜重和干重ꎬ以6.0μmol L ̄1GABA(T6)种子引发处理的效果最好ꎮ表1㊀不同浓度GABA种子引发处理对盐胁迫下辣椒植株生理指标的灰色关联度分析Table1㊀GreycorrelationanalysisofphysiologicalindexesofpepperplantsundersaltstressprimedwithdifferentGABAconcentrations指标Index关联度Correlation排名Rank根鲜重Rootfreshweight0.62214茎鲜重Stemfreshweight0.63110叶鲜重Leaffreshweight0.63012根干重Rootdryweight0.6478茎干重Stemdryweight0.6477叶干重Leafdryweight0.6586株高Height0.61315可溶性糖含量Solublesugarcontent0.6665可溶性蛋白含量Solubleproteincontent0.6883脯氨酸含量Prolinecontent0.60819过氧化氢含量H2O2content0.6794超氧阴离子含量O2-content0.57934丙二醛含量MDAcontent0.55638SOD活性SODactivity0.60222POD活性PODactivity0.7551CAT活性CATactivity0.6922APX活性APXactivity0.6349GR活性GRactivity0.61216AsA含量AsAcontent0.60321DHA含量DHAcontent0.58532AsA/DHA0.63111叶绿素含量Chlorophyllcontent0.59528初始荧光Fo0.59727光化学最大量子产量Fv/Fm0.59329潜在最大量子产量Fvᶄ/Fmᶄ0.59925稳态光化学淬灭qP_Lss0.59726稳态非光化学淬灭NPQ_Lss0.62313稳态光量子效率QY_Lss0.59231荧光衰减率Rfd0.61017根K+含量K+contentinroot0.57935茎K+含量K+contentinstem0.58533叶K+含量K+contentinleaf0.60223根Na+含量Na+contentinroot0.61018茎Na+含量Na+contentinstem0.60620叶Na+含量Na+contentinleaf0.60024根K+/Na+K+/Na+inroot0.56937茎K+/Na+K+/Na+instem0.57636叶K+/Na+K+/Na+inleaf0.59230543212期林欣琪等:γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化㊀㊀渗透胁迫是作物处于盐胁迫时的最直接反映ꎬ表现为作物吸水能力下降ꎬ叶片萎蔫ꎮ可溶性糖和可溶性蛋白既是植株生理活动的反映ꎬ也可与脯氨酸一起作为叶片的渗透调节物质(薛腾笑等ꎬ2018ꎻLietal.ꎬ2021)ꎮ在本研究中ꎬ所有GABA种子引发处理的叶片可溶性糖含量和可溶性蛋白质含量均显著高于未引发处理或蒸馏水引发处理ꎬ表明GABA种子引发处理提高了盐胁迫下辣椒植株的生理活动ꎻT4和T6浓度种子引发处理的叶片脯氨酸含量高于未引发㊁蒸馏水引发和其他浓度的引发处理ꎬ但高浓度(T8)处理的叶片脯氨酸含量显著低于未引发或蒸馏水引发处理ꎬ这与根据生物量衡量出的最佳引发处理浓度一致ꎬ同时也表明ꎬ较高浓度的GABA种子引发处理可能对辣椒植株的生理代谢有不利影响ꎮ已有研究表明ꎬGABA可直接作为渗透保护剂或通过提高渗透调节物质含量维持植株渗透势的稳定(白明月等ꎬ2022)ꎮ在培养基中添加0.5g L ̄1GABA可以提高越橘(Vacciniumcorymbosum)试管苗的可溶性糖㊁可溶性蛋白和游离脯氨酸的含量ꎬ进而缓解玻璃化现象的发生(张换换等ꎬ2021)ꎮGABA种子引发处理可增加白三叶草(Trifoliumrepens)水胁迫下的可溶性糖㊁可溶性蛋白和脯氨酸的含量(Zhouetal.ꎬ2021)ꎮ叶面喷施GABA可促进盐碱胁迫下西伯利亚白刺(Nitrariasibirica)脯氨酸的积累ꎬ进而提高其对盐胁迫的耐受性(王贺ꎬ2021)ꎻGABA诱导匍匐翦股颖(Agrostisstolonifera)耐盐性提高的同时ꎬ促进了可溶性糖和多胺的积累(Lietal.ꎬ2020)ꎻ但也有研究表明ꎬGABA种子引发处理降低了水稻(Oryzasativa)逆境胁迫下的脯氨酸含量(Sheteiwyetal.ꎬ2019)ꎮ因此ꎬGABA种子引发处理能提高辣椒植株渗透调节物质的含量ꎬ维持细胞的渗透调节平衡ꎬ从而降低盐胁迫对辣椒植株的影响ꎮ活性氧的积累是植物处于盐胁迫时的反应之一ꎬ对其的清除能力可反映作物对盐胁迫的耐受性(AbdelLatefetal.ꎬ2014)ꎮ在本研究中ꎬGABA种子引发处理后ꎬ盐胁迫下辣椒植株叶片的O2-含量和MDA含量下降ꎬ说明植株的氧化胁迫程度轻㊁细胞膜完整ꎻ虽然叶片的H2O2含量增加ꎬ但SOD㊁POD㊁CAT和APX等抗氧化酶活性增强ꎬ对过氧化物和氧自由基进行了及时清除ꎬ减轻了氧化应激ꎬ提高了辣椒的耐盐性ꎮ李师翁等(2007)研究表明ꎬH2O2可作为植物细胞的信号分子ꎬ参与系统获得抗性(SAR)和高度敏感抗性(HR)等诸多生理过程ꎬ因此ꎬGABA种子引发处理后ꎬ可能通过促进H2O2的积累ꎬ激活了植物的抗氧化系统ꎬ进而提高了辣椒植株对盐胁迫的抗性ꎮ此外ꎬGABA本身也具有清除ROS的能力(Dengetal.ꎬ2010ꎻLiuetal.ꎬ2011)ꎮ外施GABA可以促进抗氧化酶相关基因的转录(Lietal.ꎬ2017ꎻZhangetal.ꎬ2022)ꎬ提高水稻㊁黑胡椒和多年生黑麦草(Loliumperenne)中的SOD㊁POD㊁CAT㊁APX等酶活性(Krishnanetal.ꎬ2013ꎻNayyaretal.ꎬ2014ꎻVijayakumari&Puthurꎬ2016)ꎮGABA水稻种子引发处理可通过诱导逆境胁迫下的抗氧化酶活性及其基因的转录来控制氧自由基的水平(Sheteiwyetal.ꎬ2019)ꎮ作为末端氧化酶ꎬ抗坏血酸氧化酶可通过催化抗坏血酸氧化生成脱氢抗坏血酸的方式清除活性氧(李泽琴等ꎬ2013)ꎬ同时AsA还可作为非酶抗氧化剂来清除氧自由基(Akashietal.ꎬ2004)ꎮ在本研究中ꎬGABA种子引发处理提高了APX酶活性和AsA含量ꎬ但其氧化产物(DHA)含量并未增加ꎬ说明植株耐盐性的提高可能与该途径无关或DHA下游途径参与了活性氧的清除ꎮLi等(2016)研究表明ꎬ叶片喷施GABA可显著提高高温胁迫下匍匐翦股颖叶片中的AsA含量和AsA/DHA的比值ꎮ因此ꎬGABA种子引发处理可能以类似的机制提高了辣椒植株盐胁迫下的氧自由基清除能力ꎮ逆境下植物光合能力的改变是反映植物对逆境耐受性的指标之一ꎮ非生物胁迫可影响植物的光合性能㊁叶绿素荧光参数和叶绿素含量(Brugnoli&Lauteriꎬ1991ꎻGargetal.ꎬ2002)ꎮ在本研究中ꎬGABA种子引发处理可影响盐胁迫下辣椒植株叶片的叶绿素含量ꎬ但仅T6浓度处理显著高于未引发和蒸馏水引发处理ꎬ而最高浓度处理(T8)则显著低于其他处理ꎮ与本研究结果类似ꎬ叶面喷施GABA可增加盐胁迫下西伯利亚白刺的叶绿素含量(王馨等ꎬ2019)ꎮ在叶绿素荧光参数方面ꎬGABA种子引发处理的植株在盐胁迫下均不低于或优于未引发处理的植株ꎬ说明GABA种子引发处理能缓解盐胁迫对辣椒植株光合系统的损伤ꎮ有关GABA种子引发处理影响植物光合系统的报道还较少ꎬ但已有研究表明ꎬ在浇灌营养液中6432广㊀西㊀植㊀物43卷图7㊀不同浓度GABA种子引发对盐胁迫下辣椒植株叶片初始荧光(A)㊁光化学最大量子产量(B)㊁潜在最大量子产量(C)㊁稳态光化学淬灭(D)㊁稳态非光化学淬灭(E)㊁稳态光量子效率(F)和荧光衰减率(G)的影响Fig.7㊀EffectsofdifferentconcentrationsofGABAseedprimingonFo(A)ꎬFv/Fm(B)ꎬFvᶄ/Fmᶄ(C)ꎬqP_Lss(D)ꎬNPQ_Lss(E)ꎬQY_Lss(F)andRfd(G)inleavesofpepperplantundersaltstress添加GABA可使盐胁迫下番茄幼苗的Fv/Fm㊁ETR㊁ΦPSⅡ和qP增加(罗黄颖ꎬ2011)ꎻGABA引发蚕豆(Viciafaba)种子后ꎬ增加了盐胁迫下叶片的Fv/FmꎬNPQ下降ꎬ缓解了盐胁迫对光合作用系统的不利影响(Shomalietal.ꎬ2021)ꎮ盐胁迫会引起植株Na+的积累和Na+/K+的比例失衡(Flowers&Colmerꎬ2015)ꎬ植物可通过Na+的选择性吸收或外排来提高耐盐性(Niuetal.ꎬ2018)ꎮ本研究表明ꎬ盐胁迫下ꎬK+在辣椒植株的叶片中积累最多ꎬ其次是茎ꎬ根中的K+积累较少ꎬ这与正常生长环境中的辣椒植株钾积累状况类似(伍国强等ꎬ2019)ꎮGABA种子引发处理后ꎬ根和茎中K+含量有所下降ꎬ但对叶中K+含量无显著影响ꎻ对根和茎中Na+含量无显著影响ꎬ仅高浓度处理743212期林欣琪等:γ ̄氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化图8㊀不同浓度GABA种子引发对盐胁迫下辣椒植株K+含量(A)㊁Na+含量(B)和K+/Na+比值(C)的变化Fig.8㊀EffectsofdifferentconcentrationsofGABAseedprimingonK+content(A)ꎬNa+content(B)andK+/Na+ratio(C)inpepperplantsundersaltstress(T8)的叶Na+含量显著高于未引发处理ꎮWu等(2020)研究表明ꎬ营养液中添加GABA能降低番茄植株Na+通量和含量ꎬGABA种子引发处理能促进白三叶幼苗Na+/K+的转运和Na+/K+的积累(Cheng8432广㊀西㊀植㊀物43卷etal.ꎬ2018)ꎬ但本研究结果表明ꎬGABA种子引发处理提高辣椒植株的耐盐性可能与Na+/K+的选择性吸收或转运无关ꎮ灰色关联法作为综合评价方法被广泛用于作物抗性研究(高安静等ꎬ2021)ꎮ由于GABA对植物的生理活动影响比较复杂ꎬ本研究根据灰色关联度法对GABA种子引发处理影响辣椒植株耐盐性的机制进行了分析ꎬ发现GABA引发处理主要通过提高抗氧化酶POD㊁CAT的活性和渗透调节物质含量等途径来减缓盐胁迫的伤害ꎮ综上所述ꎬ6.0μmol L ̄1GABA种子引发处理可有效促进辣椒植株在盐胁迫下的生长ꎬ可作为生产用种子处理方法ꎮGABA种子引发处理提高辣椒植株耐盐性的作用机制可能包括:促进植株的生理代谢ꎬ提高可溶性糖㊁可溶性蛋白及渗透调节物质脯氨酸的含量ꎬ增强植株的抗氧化能力ꎬ降低活性氧水平和膜脂过氧化损伤ꎬ维持光合作用系统的正常运行ꎮ参考文献:ABDELLATEFAAHꎬHECXꎬ2014.DoesinoculationwithGlomusmosseaeimprovesalttoleranceinpepperplants? 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̄dependentH2O2productionconferssalttoleranceonagraftedcucumberbycontrollingNa+exclusionandstomatalclosure[J].JExpBotꎬ69(14):3465-3476.NOUMANWꎬBASRASMAꎬYASMEENAꎬetal.ꎬ2014.SeedprimingimprovestheemergencepotentialꎬgrowthandantioxidantsystemofMoringaoleiferaundersalineconditions[J].PlantGrowthRegulꎬ73(3):267-278.RAMESHSAꎬTYERMANSDꎬGILLIHAMMꎬetal.ꎬ2017.γ ̄aminobutyricacid(GABA)signallinginplants[J].CellMolLifeSciꎬ74(9):1577-1603.RINEZIꎬGHEZALNꎬRINEZAꎬetal.ꎬ2018.Improvingsalttoleranceinpepperbybio ̄primingwithPadinapavonicaandJaniarubensaqueousextracts[J].IntJAgricBiolꎬ20(3):513-523.SHABALALꎬZHANGJYꎬPOTTOSINIꎬetal.ꎬ2016.Cell ̄type ̄specificH+ ̄ATPaseactivityinroottissuesenablesK+retentionandmediatesacclimationofbarley(Hordeumvulgare)tosalinitystress[J].PlantPhysiolꎬ172(4):0532广㊀西㊀植㊀物43卷。
γ-氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化
γ-氨基丁酸(GABA)种子引发缓解辣椒盐胁迫的效果及生理生化的变化作者:林欣琪魏茜雅梁腊梅秦中维李映志来源:《广西植物》2023年第12期摘要:种子引发是提高作物生长期耐盐性的有效方法,而γ-氨基丁酸(GABA)种子引发对辣椒(Capsicum annuum)耐盐性的效果和作用机制尚不清楚。
该研究以‘茂蔬360’朝天椒为材料,分析了不同浓度γ-氨基丁酸(0、1.0、2.0、4.0、6.0、8.0 μmol·L-1)种子引发对4~6叶期100 mmol·L-1 NaCl胁迫下的植株生物量、渗透调节物质、抗氧化能力、光合作用系统及钾钠离子吸收的影响。
结果表明:(1)种子引发能显著增加盐胁迫下辣椒植株的生物量,以6.0 μmol·L-1 GABA引发处理的效果最佳。
(2)种子引发处理增加盐胁迫下植株可溶性糖、可溶性蛋白、脯氨酸的含量,同时,O2-和MDA的含量下降,抗氧化酶(SOD、POD、CAT和APX)活性增强,叶片叶绿素含量增加,叶片叶绿素荧光参数受胁迫影响程度低,叶绿素荧光指标包括Fv ′/Fm ′、qP_Lss、QY_Lss、NPQ_Lss和Rfd均有所上升。
根、茎中的K+含量和K+/Na+比值下降。
(3)灰色关联度分析表明,GABA种子引发主要通过提高POD、CAT的活性和渗透调节物质含量来缓解盐胁迫对辣椒植株的伤害。
综上所述,6.0 μmol·L-1 GABA种子引发可有效提高辣椒苗期的耐盐性,其作用机制可能是提高了盐胁迫下辣椒植株的抗氧化能力和渗透调节能力。
关键词:γ-氨基丁酸(GABA),辣椒,种子引发,耐盐性,灰色关联度分析中图分类号: Q945文献标识码: A文章编号: 1000-3142(2023)12-2338-14收稿日期: 2023-05-15基金项目:广东省科技厅科技计划项目(2016A020210116, 2012A020602051); 广东海洋大学创新强校项目(GDOU2013050217, GDOU2016050256)。
Salt Stress Tolerance of Plants(植物耐盐胁迫)
Introduction Soil salinity is a major constraint to food production because it limits crop yield and restricts use of land previously uncultivated. The United Nations Environment Program estimates that approximately 20% of agricultural land and 50% of cropland in the world is salt-stressed (Flowers and Yeo, 1995). Natural boundaries imposed by soil salinity also limit the caloric and the nutritional potential of agricultural production. These constraints are most acute in areas of the world where food distribution is problematic because of insufficient infrastructure or political instability. Water and soil management practices have facilitated agricultural production on soils marginalized by salinity but additional gain by these approaches seems problematic. On the horizon are crop improvement strategies that are based on the use of molecular marker techniques and biotechnology, and can be used in
水稻耐盐分子机制研究进展
广东农业科学 2023,50(12):29-42Guangdong Agricultural Sciences DOI:10.16768/j.issn.1004-874X.2023.12.003陈思蓉,李晨,孙炳蕊. 水稻耐盐分子机制研究进展[J]. 广东农业科学,2023,50(12):29-42.水稻耐盐分子机制研究进展陈思蓉,李 晨,孙炳蕊〔广东省农业科学院水稻研究所/农业农村部华南优质稻遗传育种实验室(部省共建)/广东省水稻育种新技术重点实验室/广东省水稻工程实验室,广东 广州 510640〕摘 要:水稻是世界上重要的粮食作物之一,对盐胁迫比较敏感,土壤盐碱化对水稻的安全生产造成潜在风险。
盐胁迫会引起水稻的渗透胁迫和离子毒害,还会在植株中引起氧化胁迫,导致水稻品质和产量下降。
由于水稻根系能吸收盐分分泌有机酸,同时具有田间持水和排水晒田的生长特性,因此水稻也是一种改良盐渍土的优良作物。
因此培育耐盐水稻新品种,提高水稻耐盐性,可有效提高盐渍化耕地的生产潜力,对保障我国乃至全球粮食安全具有重要意义。
近年来,数量遗传学和分子标记技术不断发展,通过遗传、生化及分子生物学等手段,挖掘出大量耐盐相关QTL和基因,对于解析水稻耐盐分子机制,利用分子标记辅助选择、基因编辑等提高耐盐水稻育种效率,均具有非常重要的意义。
但目前克隆的耐盐相关基因大多采用反向遗传学方法获得,且大多是在过表达条件下表现出耐盐性,或者耐盐基因为隐性,难以在耐盐水稻育种中应用。
总结近年来水稻耐盐相关基因的鉴定和挖掘研究中所取得的进展,从有机物渗透调节、离子吸收转运调节、抗氧化系统清除活性氧调节、激素调节4个方面综述水稻耐盐分子机制的研究进展,并探讨未来水稻耐盐性研究面临的挑战,为开展水稻耐盐分子育种提供建议。
关键词:水稻;盐胁迫;耐盐性;QTL;耐盐基因;分子机制中图分类号:S511 文献标志码:A 文章编号:1004-874X(2023)12-0029-14Research Progress on Molecular Mechanism ofSalt Tolerance in RiceCHEN Sirong, LI Chen, SUN Bingrui〔Rice Research Institute, Guangdong Academy of Agricultural Sciences / Key Laboratory of Genetics and Breeding of High Quality Rice in Southern China (Co-construction by Ministry and Province),Ministry of Agriculture and Rural Affairs / Guangdong Key Laboratory of New Technology in Rice Breeding /Guangdong Rice Engineering Laboratory, Guangzhou 510640, China〕Abstract: Rice is one of the important grain crops in the world and is sensitive to salt stress. The increasingly serious salinization of paddy soils is becoming a potential risk to the safe production of rice. Salt stress can cause osmotic stress, ion toxicity and oxidative stress in rice plant, ultimately leading to a decrease in rice quality and yield. Due to the ability of rice roots to absorb salt and secrete organic acids as well as the growth characteristics of water holding in the early stage and drainage in rice paddies in the later stage, rice is also an excellent crop for improving saline soil. Therefore, cultivating new rice varieties of salt tolerant and improving rice salt tolerance can effectively enhance the production potential of saline收稿日期:2023-10-30基金项目:广东省自然科学基金(2021A1515011226);广东省农业科学院水稻研究所“优谷计划”(所长基金)(2021YG02);广东省财政厅提升广东省稻种资源考察与保护精深鉴评与创新利用产业科技能力水平项目(粤财农〔2023〕145号);广东省水稻育种新技术重点实验室项目(2023B1212060042)作者简介:陈思蓉(1998-),女,硕士,研究实习员,研究方向为水稻种子活力,E-mail:*****************通信作者:孙炳蕊(1980-),女,博士,副研究员,研究方向为作物遗传育种,E-mail:**********************30水稻是全世界一半以上人口的主食,是最重要的谷类作物之一,但其对盐分胁迫较为敏感[1-2]。
农作物耐盐碱机制解析及应用
农作物耐盐碱机制解析及应用## Crop Salt and Alkali Tolerance Mechanisms and Applications.### English Answer:Salt and alkali stress are major environmental challenges that restrict crop growth and productivity in many regions worldwide. To cope with these stresses, crops have evolved various mechanisms to maintain cellular homeostasis and mitigate the toxic effects of salt and alkali ions. Understanding these mechanisms is crucial for developing effective strategies to improve crop salt and alkali tolerance.One of the primary mechanisms of salt and alkali tolerance in crops is ion exclusion. Ion exclusion prevents the influx of harmful ions, such as sodium (Na+) and chloride (Cl-), into the plant roots and shoots. This is achieved through various ion transporters and channelspresent in the root cell membranes. For example, salt overly sensitive 1 (SOS1) is a critical sodium/hydrogen antiporter that pumps Na+ out of the root cells, maintaining a low cytoplasmic Na+ concentration.Another important mechanism is tissue tolerance. Tissue tolerance involves the compartmentalization and detoxification of salt and alkali ions that have entered the plant tissues. This includes the sequestration of ions into vacuoles, where they are stored and prevented from causing damage to cellular components. Additionally, crops may accumulate compatible solutes, such as proline and glycine betaine, which help maintain cell turgor and protect enzymes and proteins from salt and alkali stress.Molecular and genetic approaches have been employed to identify genes and pathways involved in salt and alkali tolerance in crops. Several quantitative trait loci (QTLs) and candidate genes have been identified that control ion exclusion and tissue tolerance mechanisms. Genetic engineering techniques are being used to introgress these salt tolerance genes into elite cultivars to enhance theirperformance in saline and alkaline soils.### 中文回答:农作物耐盐碱机制解析及应用。
盐碱胁迫对植物的影响及抗性机制研究进展
盐碱胁迫对植物的影响及抗性机制研究进展作者:贾秀苹王莹卯旭辉柳延涛王兴珍来源:《寒旱农业科学》2024年第07期摘要:盐碱胁迫是仅次于干旱胁迫抑制植物生长发育的主要非生物胁迫之一,不仅影响植物的生长发育,而且对农业生产和生态环境造成严重威胁。
研究植物的耐盐碱机制,对耐盐碱作物选育及盐碱地的开发利用具有重要的现实意义。
结合近年来国内外的相关研究总结性阐述了盐碱胁迫对植物代谢的伤害(包括离子伤害、膜系统伤害、诱导渗透伤害等)机制,并从膜系统保护以及诱导基因表达方面综述了植物对盐碱胁迫的缓解机制,进而提出外源物质的导入、生物技术手段、耐盐碱品种培育是解决植物抗盐碱的主要手段。
最后就植物适应盐碱胁迫方面的研究进行了展望,指出了当前研究者需要解决的问题和突破口,旨在为提高植物耐盐碱能力、增加作物产量提供一定的理论依据。
关键词:盐碱胁迫;植物;伤害;抗盐碱机制;技术手段中图分类号:S184;Q945.78 文献标志码:A 文章编号:2097-2172(2024)07-0593-07doi:10.3969/j.issn.2097-2172.2024.07.002Research Progress on Effects of Saline-alkali Stress on Plants andTheir Resistance MechanismsJIA Xiuping 1, WANG Ying 2, MAO Xuhui 1, LIU Yantao 3, WANG Xinzhen 1(1. Institute of Crop, Gansu Academy of Agriculture Sciences, Lanzhou Gansu 730070,China; 2. Jiuquan Academy of Agricultural Sciences, Jiuquan Gansu 735000, China; 3. Crop Research Institute of Xinjiang Agricultural ReclamationAcademy of Sciences, Shihezi Xinjiang 832000, China)Abstract: Salt-alkali stress is one of the main abiotic stresses that inhibit plant growth and development, second only to drought stress. It not only affects plant growth and development but also poses a serious threat to agricultural production and the ecological environment. Studying the mechanisms of plant salt-alkali tolerance has significant practical implications for the breeding of salt-alkali tolerant crops and the development and utilization of salt-alkali land. Based on recent domestic and international research, this paper summarizes the mechanisms of salt-alkali stress on plant metabolism, including ion damage, membrane system damage, and induced osmotic damage. It reviews the mechanisms by which plants mitigate salt-alkali stress, focusing on membrane systemprotection and induced gene expression. It further suggests that the introduction of exogenous substances, biotechnological methods, and the cultivation of salt-alkali tolerant varieties are the main strategies to address plant salt-alkali resistance. Finally, the paper looks forward to research on plant adaptation to salt-alkali stress, pointing out the issues and breakthroughs that current researchers need to address. The aim is to provide a theoretical basis for improving plant salt-alkali tolerance and increasing crop yields.Key words: Salt-alkali stress; Plant; Damage; Salt-alkali resistance mechanism; Technical method土壤鹽碱化是世界性的资源和生态环境问题,对保证粮油安全及有效耕地面积造成严重影响。
植物根际促生菌提高植物耐盐性研究进展
收稿日期:2023-02-13作者简介:陈梦霞(1997—),女,四川富顺人,在读硕士,研究方向为植物微生物。
E-mail :******************。
陈梦霞.植物根际促生菌提高植物耐盐性研究进展[J ].南方农业,2023,17(13):17-21.植物根际促生菌提高植物耐盐性研究进展陈梦霞(吉林师范大学,吉林四平136000)摘要盐胁迫是限制农业生产力的主要因素之一,土壤盐分已成为影响农业发展的一个重大阻碍。
植物根际促生菌(PGPR )是附着在植物根部或者土壤的有益菌类,它既可促进植物生长、提高吸收和利用矿物质的效率、抵抗病原菌的侵害,又可增强植物的耐盐性。
为改善盐渍土环境,促进植物生长,提高作物产量提供参考,主要论述了盐胁迫环境对植物、土壤微生物的影响,以及PGPR 诱导植物耐盐性的相关机制,并对今后PGPR 的发展进行了展望。
关键词盐胁迫;植物根际促生菌(PGPR );耐盐性;研究进展中图分类号:S154.38+1文献标志码:CDOI :10.19415/ki.1673-890x.2023.13.004目前,全球盐碱土分布范围与占地面积越来越大,面积已超过8.33亿hm 2,其中大多分布在非洲、亚洲和拉丁美洲的自然干旱或半干旱地带。
我国盐渍土面积约为0.99亿hm 2,占全球1/10以上,这对我国粮食和生态安全造成了严重的影响。
土壤盐渍化形成的原因有很多种,比如海平面上升和热带风暴潮导致的气候变化会增加土壤和水中盐分[1],地底深部含盐地下水中的岩盐和石膏的溶解导致地下水盐度增加[2],人为活动可以将土壤盐浓度提高到影响土壤质量、微生物、植物和动物生命的水平[3]。
此外,堆肥中含有较高浓度的可溶性盐,也可导致土壤盐分含量偏高[4]。
研究表明,植物根际促生菌(PGPR )与植物根系相互作用,可以减轻盐分胁迫以提高作物生产力[5]。
PGPR 也被用作生物接种剂,用于提高作物产量、防治植物病原体和改善土壤健康[6]。
1盐胁迫下的生理生化检测
Physiological Mechanisms for High Salt Tolerance in Wild Soybean (Glycine soja) from Yellow River Delta, China: Photosynthesis, Osmotic Regulation, Ion Flux and antioxidant CapacityPeng Chen1, Kun Yan1,3*, Hongbo Shao1,2*, Shijie Zhao31 Key Laboratory of Coastal Biology & Bioresources Utilization and Key Laboratory of Coastal Zone Environmental Processes, Yantai Institute of Coastal Zone Research (YIC), Chinese Academy of Sciences (CAS), Yantai, China, 2Institute for Life Sciences, Qingdao University of Science & Technology (QUST), Qingdao, China, 3 State Key Laboratory of Crop Biology, Shandong Agriculture University, Tai’an, ChinaIntroductionAt present, more than 800 million hectares of lands are affected by salinity in the world and in particular, farmland salinity has become a severe agricultural problem due to unreasonable irrigation and fertilization [1,2]. Soil salinity inhibits plant growth and decreases crop yield, and it is a feasible way to meet the challenge of farmland salinity by enhancing crop salt tolerance [3]. Halophyte can survive and evolve in saline lands because of some special physiological adaptive mechanisms [4], and it is a primary work to explore these adaptive mechanisms before genefor stress, ion toxicity and oxidative stress [1,5]. Upon salinity exposure, osmotic stress often firstly occurs because water absorption by plant roots becomes hard, and many osmotic regulation substances may be accumulated to increase their hyperosmotic tolerance for avoiding water loss from the cells. Proline and glycinebetaine are the most widely reportedosmotic regulation substances, and theirrole in resistingsalt stress also has been recognized to reduce water loss under saline condition, down regulate leaf stomatal conductance to reduce water evaporation, but photosynthesis is concomitantly affected, as CO 2 flux into leaf is also inhibited. Photosynthesis is closely related with plant growth and crop yield and is also very sensitive to environmental stress. Depression of photosynthetic rate can be usually found in plants under salt stress, but the underlying reasons remain to be ascertained [7-9]. Initial negative effect of salt stress on photosynthesis may be due to the decreased CO 2 availability as a result of the diffusion limitations of stomata [7,10]. Rubisco is the key enzyme in CO 2fixation process, and rubisco activity is liable to be suppressed under salt stress, however, decreased rubisco activity stems from different aspects such as decreased rubisco content and inhibited rubisco activation [8,11]. Photosystem II (PSII) plays an important role in plant photosynthesis, but its tolerance to salt stress still remains to be defined. PSII was proved to be sensitive to salt stress in some studies [9,12,13], whereas high salt-resistance was demonstrated in other studies [10,14,15].Salt stress about oxidative stress on plants by inducing excess generation of reactive oxygen species (ROS)in plant tissues [16]. Antioxidant system including antioxidant enzymes such as superoxide dismutase (SOD) and ascorbate peroxidase (APX), and antioxidants such as ascorbic acid (AsA) and glutathione (GSH) to scavenge excess ROS, and the antioxidant capacity are often used for differentiating the salt tolerance in crop varieties [17,18]. Na + and Cl - are the origins exerting toxic effects on physiological metabolisms and plant growth in saline condition. Except the succulent species such as Suaeda salsa , salt-tolerant plants often have high extraction capacity of Na + and Cl - in roots, and then maintain lower Na + and Cl - in the tissue. Sun et al. [19] reported that salt-tolerant Populus euphratica exhibited a higher capacity to extrude Na + than salt-sensitive Populus popularis under NaCl stress, and Na +/H + antiporter played a crucial role in ion homeostasis. Luo et al. [20] reported that G. soja had higher salt tolerance than G. max due to less accumulation of Na + and Cl -. Zhang et al. [21] revealed that G. soja had higher Na + and Cl - extrusion in roots in contrast to G. max .Soybean is rich in proteins and necessary for the diet of Human beings. There is a great of demand for soybean in the international market. However, cultivated soybean species are usually sensitive to soil salinity, and farmland salinity can lead to the loss of soybean yield. Glycine soja (BB52) is a wild soybean cultivar grown in coastal saline land in Yellow River Delta, China. G. soja is the near relative ancestor of cultivated soybean species, and they have high gene homology [22,23].In addition, as a salt-born soybean species, G. soja should have unique physiological mechanisms for adapting to salinity stress in contrast to cultivated soybean. Therefore, G. soja can be considered as a valuable genomic resource for improving salt tolerance of cultivated soybean species by molecular biology means. Up to now, it has been reported about the salt tolerance in G. soja with higher root extrusion and less accumulation in tissues of Na + and Cl - [21], however, thesystematic salt-adaption physiological mechanisms have not been comprehensively studied in G. soja . In this study, we intended to systematically diagnose these mechanisms in G.soja from the aspects of root ions flux, antioxidant system,osmotic regulation and photosynthesis, and the results can enrich the knowledge of plant salt tolerance and may provide a reference for genetic improvement of salt tolerance in cultivated soybean.Materials and Methods"I state clearly that no specific permissions were required for these locations/activities, which are concerned about scientific study in the region in China. I confirm that the field studies did not involve endangered or protected species".Plant material and treatmentG. soja (BB52) is a wild soybean cultivar grown in coastal saline land in Yellow River Delta. The area belongs to temperate humid continental monsoon climate. G. max (ZH13)is a widely planted soybean cultivar in China, and it has high yield. The seeds of BB52 were collected in Yellow River Delta in October, 2012, while the seeds of ZH13 were obtained from Shandong Academy of Agricultural Science. The seeds of ZH13 were fully soaked in distilled water for 8 h, while the seeds of BB52 were soaked in concentrated sulfuric acid for 10min to remove the hard shell over the seeds. Then, the seeds were placed in petri dishes in the dark between two sheets of filter paper at 25 °C to germinate, and the filter paper was kept wet by spraying Hoagland nutrient solution (pH 5.7). After 5days, the germinated seeds were transferred to plastic pots filled with vermiculite and grown in artificial climatic chambers (Huier, China). The vermiculite was kept wet by watering also with Hoagland nutrient solution every day. Light time was 12hours in each day. Day/night temperature and humidity were respectively controlled at 25/18 °C and 65% in the chambers.After 20 days, seedlings with uniform growth pattern were selected for salt treatment. NaCl was added to nutrient solution to provide final concentrations of 0 (control), 50, 100, 200 and 300 mM. The higher NaCl concentrations (>50 mM) were imposed incrementally by 50 mM step every day until final concentrations were reached. There were twenty replicate seedlings in each salt treatment, and each parameter was measured for five times respectively by using five replicate seedlings 7 days after the final concentrations were reached.Photosynthetic, fluorescent, water potential and relative water content measurements were conducted on the newest fully expanded leaves, and this kind of leaves were sampled, frozen in liquid nitrogen and stored at -80 °C in a freezer for measuring other parameters such as antioxidant,osmoregulation substance and malondialdehyde (MDA)contents, antioxidant enzymes and rubisco activities, and western blotting. The roots and leaves (the newest fully expanded) were harvested from five replicate seedlings and dried at 70 °C for 48 h. The dried samples were ground to powder and used for measuring Na + and Cl - contents.Measurements of gas exchange and modulated chlorophyll fluorescenceGas exchange and modulated chlorophyll fluorescence weresimultaneously detected using an open photosynthetic system (LI-6400XT, Li-Cor, USA) equipped with a fluorescence leaf chamber (6400-40 LCF, Li-Cor, USA). The leaves were dark-adapted for 30 min before the measurements. The minimal fluorescence level in the dark-adapted state (Fo) was measured using a modulated pulse (< 0.05 µmol photons m-2 s-1for 1.8 s). Maximal fluorescence (Fm) was measured after applying a saturating actinic light pulse of 8000 µmol photons m-2 s-1 for 0.7 s. Subsequently, actinic light intensity was altered to 1000 µmol photons m-2s-1in leaf cuvette and then maintained for about 30 min. The temperature, carbon dioxide concentration and relative humidity in the leaf cuvette depended on ambient conditions. Stomatal conductance (Gs), intercellular CO2concentration (Ci) and transpiration rate (E) were recorded simultaneously with Pn. In addition, steady-state fluorescence yield (Fs) was also recorded. A saturating actinic light pulse of 8000 µmol photons m-2 s-1 for 0.7 s was then used to produce maximum fluorescence yield (Fm’) by temporarily inhibiting photosystem II (PSII) photochemistry, and then the actual photochemical efficiency of PSII (ΦPSII) were calculated [24].For the measurement of carboxylation efficiency (CE), photon flux density and temperature were set at 1000 µmol photons m-2 s-1 and 25 °C in the leaf cuvette, respectively. Pnwas measured under CO2concentrations in a sequence of 600, 500, 400, 300, 200, 150, 100, and 50 µmol mol-1. The leaveswere kept under each level of CO2concentration for 5 min to let leaves reach steady photosynthesis, the Pn and Ci were then recorded. The correlation curve of Pn related to Ci was established. CE was calculated from the linear portion of the Pn-Ci curve according to Chen et al. [25].Measurement of chlorophyll contentLeaf samples (0.2 g) were soaked in 20 ml 95% (v/v) ethanol at 4 °C in darkness until the tissues became totally white. Extracts were used to measure the absorbance at 649 nm and 665 nm, the chlorophyll content was calculated according to Lichtenthaler and Wellburn [26].Measurement of rubisco activity and activation state Rubisco activity was measured according to Wang et al. [27] with slight modifications. Leaf samples (0.2 g) were frozen in liquid nitrogen and homogenized to fine powder with mortar and pestle. Rubisco was extracted by grinding the fine powder in 1 ml extraction buffer containing 100 mM HEPES-KOH (pH8.0), 10 mM MgCl2, 0.5 mM ethylene diaminetetraacetic acid (EDTA), 1% (w/v) polyvinylpolypyrrolidone (PVPP) and 0.06 ml b-mercaptoethanol. After centrifugation at 16000 g for 15 min, the supernatant was used in the measurement of initial activity of rubisco. Extract supernatant (0.1 ml) was added to 0.4 ml of activation solution (33 mM HEPES-KOH (pH 8.0), 33 mMMgCl2, 0.67 mM EDTA, 10 mM NaHCO3as finalconcentration). After incubated at 30 °C for 10 min, the solution was used for measurement of total activity of rubisco.The activity of rubisco was determinedspectrophotometrically by measuring the disappearance rate of NADH. To determine the initial and total activity of rubisco, the reaction was initiated by adding 60 µl 10 mM ribulose-1,5-diphosphate (RuDP) and 0.1 ml extract immediately after mixing the desalted sample solution containing 50 mM HEPES-KOH (pH 8.0), 20 mM MgCl2, 1 mM EDTA, 2.5 mM DTT, 2.5mM NADH, 5 mM ATP, 10 mM NaHCO3, 5 mM phosphocreatin, 10 U/ml of phosphocreatine kinase, 10 U/ml of phosphoglyceric kinase and 10 U/ml of glyceraldehyde-3-phosphate dehydrogenase. The changes in the absorption were recorded and the activation state of rubisco was calculated as the ratio of initial activity to total activity of this enzyme.Western blotting of rubiscoactivaseLeaf samples (0.5 g) were ground in liquid nitrogen with mortar and pestle. Total proteins were firstly extracted with 1 ml buffer I (acetone containing 10% (W/V) TCA and 0.07% (V/V) b-mercaptoethanol). After incubated at -20 °C for 1 h, the mixture was centrifugated for 30 min (4 °C, 15000 g). Equal volume of buffer II (acetone containing 0.07% (V/V) b-mercaptoethanol) was added and the mixture was incubated and centrifugated as above after vortexing for 1min. Repeat this step twice to remove salt ion and organic admixture like pigmentum and polyphenol. The protein pellets were vacuum-dried, recovered in lysis buffer and centrifugated for 30 min (4°C, 15000 g). The upper phase protein concentrations were quantified using the Bradford assay [28].For western-blotting, the same quantityprotein of BB52 and ZH13 was separated by SDS-PAGE using 12% (w/v) acrylamide gels and electrically transferred onto polyvinylidene fluoride (PVDF) membranes (Clontech, China) using a semi-dry transfer system (BIO-RAD, USA). The protein blot was probed with a primary antibody of the rubisco activase (Agrisera, Sweden, dilution of 1:5000) for 2 h at 37 °C with agitation and then incubated with the secondary antibody (peroxidase-babeled affinity purified antibody, KPL, USA, dilution of 1:1000) for 2 h at 37 °C. The blots were finally developed with a peroxidase substrate kit (KPL, USA).Measurement of water potential (ψw) and relative water content (RWC)Leaf samples were placed in a sample cup, and the cup bottom should be completely covered. Then, water potential was measured using chilled-mirror dewpoint technique with a WP4-T Dewpiont Potentia Meter (USA). Fresh leaves were harvested and weighed (fresh weight, FW), and then soaked in deionized water for 24 h at 4 °C and weighed (called saturated fresh weight, SFW). Finally, the leaves were dried completely in an oven and weighed (dry weight, DW). RWC was calculated as: RWC= (FW-DW) / (SFW-DW).Measurement of glycinebetaine contentLeaf samples (0.2 g) were ground under liquid nitrogen andhomogenized in 3 ml methanol-chloroform-KHCO3solution(methanol: chloroform: 0.2 mM KHCO3= 12:5:1). The mixture was incubated at 60 °C in water bath for 20 min and thencentrifugated at 10000 g for 10 min. The supernatant was transferred to another tube and the precipitate was washed twice (firstly with 1 ml of the same extract solution, secondly with 1 ml of methanol- H2O (1:1) solution, and all transferred to the above tube). After 2 ml chloroform and 3 ml distilled water were subsequently added, the mixture was vortexed and centrifugated at 10000 g for 10 min. The upper phase was used for glycine betaine content measurement by TSQ Quantum Access MAX triple stage quadrupole mass spectrometer (Thermo, USA) with Hypersil ODS column (5 µm particles size, 4.6×250 mm, USA). The glycinebetaine content was calculated from a standard curve prepared with pure glycinebetaine (Sigma, USA) solutions.Measurement of proline contentLeave samples (0.2 g) were homogenized using pestle and mortar with 3ml of 5% (w/v) sulphosalicylic acid and incubated at 100 °C for 10 min. After centrifugation at 13000 g for 10 min, 2 ml glacial acetic acid and 3 ml ninhydrin reagent were added to 2 ml of the supernatant and incubated at 100 o Cfor 40 min. After cooling, 5 ml toluene was added to the mixture and the absorbance at 520 nm of the toluene phase was recorded [10]. The standard curve was plotted according to the proline solution of known concentration.Measurement of Na+ and Cl- contentThe extraction of Na+and Cl-were performed according toLuo et al. [20]. Deionized H2O (15 ml) was added to 100 mg of dried plant powder and boiled for 2 h. After centrifugation at 10000 g for 20 min, the supernatant was used for measurement of Cl-content and diluted 100 times withdeionized H2O for Na+content. The atomic absorption spectrophotometer (PAS-990, PERSEE, China) was used for measurement of Na+content while Cl-content was analyzed with a Cl-electrode (Leici, China). The amount of these three ions was calculated from a standard curve prepared with pure NaCl (for Na+ and Cl-) solutions.Measurements of net Na+ and Cl- fluxesNet fluxes of Na+ and Cl- were measured using Non-invasive Micro-test Technique (NMT-YG-100, Younger, USA). The concentration gradients of the target ions were measured by moving the ionselective microelectrode repeatedly between two points close to the plant material. The ion fluxes were calculated based on the Fick’s law of diffusion.Prepulled and silanized glass micropipettes (Xuyue Sci. and Tech., China) were firstly filled with a backfilling solution (Na+: 100 mM NaCl; Cl-: 100 mM KCl) to a length of approximately 1 cm from the tip. Then the micropipettes were front filled with selective liquid ion-exchange cocktails (LIXs, Xuyue Sci. and Tech., China). An Ag/AgCl wire electrode holder (Xuyue Sci. and Tech., China) was then inserted in the back of the electrode to make electrical contact with the electrolyte solution. DRIREF-2 (World Precision Instruments) was used as the reference electrode.Ion-selective electrodes were firstly calibrated before flux measurements using the following solutions: (1) Na+: 5 mM, 2 mM, 1 mM (2 mM in measuring solution); (2) K+: 1 mM, 0.5mM, 0.1 mM (0.5 mM in measuring solution); (3) H+: pH 5, 6, 7(6 in measuring solution); (4) Cl-: 2 mM, 0.5 mM, 0.25 mM (0.5 mM in measuring solution). Only electrodes with Nernstian slopes >50 mV/decade (< -50 mV/decade for Cl-electrodes) were used.Root segments with 3 cm apices were immobilized on the bottom of measuring dish, rinsed with deionized water and immediately incubated in the measuring solution to equilibrate for 20 min. The measuring site was 500µm from the root apex, in which a vigorous flux of Na+ or Cl- was usually observed. The measuring solutions were as follows: (1) Na+: 0.1 mM KCl, 0.1 mM CaCl2, 0.1 mM MgCl2, 2 mM NaCl, 0.3 mM MES, pH 6.0, adjusted with choline and HCl; (2) Cl-: 0.05 mMKCl, 0.05 mMCaCl2, 0.05 mM MgCl2, 0.25 mM NaCl, pH 6.0, adjusted withcholine and H3PO3. The miro-volts differences were then imported and converted into net ion fluxes using the JCal V3.0 (Xuyue Sci. and Tech., China).Measurement of MDA contentThe lipid peroxidation level was determined in terms of MDA content by the thiobarbituric acid reaction method [29]. Leaf tissues (0.2 g) were ground under liquid nitrogen and then homogenized in 3.5 ml 200 mM potassium phosphate buffer (pH 7.6) containing 1 mM EDTA, 2% (w/v) PVPP and 1 mM ascorbate. After centrifugation at 4 °C and 13000 g for 10 min, the supernatant was prepared for the measurement. The reaction mixture containing 1 ml of extract supernatant and 4 ml of 0.5% thiobarbituric acid in 20% trichloroacetic acid (TCA) was incubated in water bath at 95 °C for 30 min, and then transferred to ice bath to stop the reaction. After centrifugation at 10000 g for 10 min, the absorbance of supernatant was measured at 532 nm, 600 nm and 450 nm. The concentrationof MDA was calculated as: MDA content (µM) = 6.45(A532–A600)–0.56 A450.Measurement of total phenolics contentTotal phenolics were extracted from 0.1 g of dry leaf powder by homogenization in 8 ml methanol for 2 h. The mixture was centrifuged for 5 min at 10000 g and the supernatant was diluted ten times with methanol before the Folin–Ciocalteu assay [30]. A 0.1 ml aliquot of supernatant was mixed with 0.15ml 1M Folin–Ciocalteu reagent, 0.15 ml 10% (W/V) Na2CO3 and 4.6 ml distilled water. The reaction mixture was incubated in water bath at 25 °C for 90 min and the absorbance was measured at 760 nm. Total phenolics content was calculated by comparison with the standard curve obtained with gallic acid.Measurement of AsA contentLeaf samples (0.2 g) were ground under liquid nitrogen and homogenized in 5ml 6% (w/v) metaphosphoric acid (MPA) containing 2 mM EDTA and 1% (w/v) PVPP. The homogenate was centrifuged at 13000 g for 20 min and the supernatant was used for measurement by liquid chromatography method [31]. The analysis was performed in a Surveyor Plus high performance liquid chromatography system (Thermo, USA) with a Polaris C18-A column (5.0 µm particles size, 4.6×150 mm). AsA was detected at 243 nm and the content wascalculated from a standard curve prepared with pure AsA (Sigma, USA) solutions.Measurement of GSH contentGSH was measured according to the method reported by Li et al. [32] with a slight modification. Leave samples (0.2 g) were homogenized using pestle and mortar with 3 ml 5% (w/v) sulphosalicylic acid, the homogenate was then centrifuged at 13000 g for 20 min. A 1 ml aliquot of the supernatant was neutralized with 1.5 ml 0.05 M K-phosphate buffer (pH 7.5) containing 5 mM EDTA, this sample was used for the assay of total glutathione. Another 1 ml aliquot of the supernatant was also neutralized with 1.5 ml 0.05 M K-phosphate buffer (pH 7.5) containing 5 mM EDTA, and then 0.2 ml 2-vinylpyridine was added. The tube was mixed until an emulsion formed and then incubated at 25 °C for 1 h, this sample was used for the assay of oxidized glutathione (GSSG).The reaction mixture contained: 0.3 ml 2 mM 5,5’-dithiobis-(2-nitrobenzoic acid) (DTNB), 0.5 ml 0.42 mM NADPH, 0.1 ml (1 U) of yeast glutathione reductase (GR, Sigma, USA) (DTNB, NADPH and GR were all dissolved in phosphate buffer (pH 7.5) containing 6 mM EDTA). The reaction was initiated by the addition of 0.1 ml GSH standard or extract. The absorbance change within 2min was recorded and the GSH concentration was proportional to the slope.Enzyme extraction and activity assayLeaf tissues (0. 2g) were ground under liquid nitrogen and then homogenized in 5 ml of 200 mM potassium phosphate buffer (pH 7.8) containing 1 mM EDTA, 2% (w/v) PVPP. After centrifugation at 4 °C and 13000 g for 10 min, the supernatant was prepared for SOD activity assay. By the same procedure, the enzyme extracts for APX activity assay were prepared in 5 ml 200 mM (pH 7.6) potassium phosphate buffer containing 1 mM EDTA, 2% (w/v) PVPP, and 1mM ascorbate.The assay of SOD activity was based on the method described by Beyer and Fridovich [33]. One unit of enzymatic activity was defined as the amount of enzyme required to bring about a 50% inhibition of the rate of nitro blue tetrazolium (NBT) reduction measured at 560 nm. APX activity was respectively calculated by the rate of AsA consumption and monitored by the change of absorbance at 290 nm [34].The reaction solution compositions for enzyme activity assay are as follows: (1) SOD: 0.3 ml 13 µM riboflavin, 0.3 ml 130 mM L-methionine (L-Met), 0.3 ml 63 µM NBT and 2.1 mlextract. (2) CAT: 2 ml 15 mM H2O2and 1 ml extract. (3) APX:0.8 ml 0.5m MAsA, 0.1 ml 2m M H2O2and 0.1 ml extract (4).DHAR: 0.7 mlpotassium phosphate buffer (pH 7.0), 0.1 ml 50mM reduced glutathione, 0.1 ml 2mM dehydroascorbic acid and 0.1 ml extract.Statistical analysisOne-way ANOVA was carried out by using SPSS 16.0 (SPSS Inc., Chicago, IL, USA) for all sets of data. The values presented are the means of all measurements, and comparisons of means were determined through LSD test among the different salt treatments in a cultivar and between the two soybean cultivars under the same salt treatment. Difference was considered significant at P< 0.05.ResultsEffects of salt stress on chlorophyll content and parameters of gas exchange and chlorophyll fluorescenceChlorophyll content and Fv/Fm were not significantly affected by salt stress in ZH13 and BB52 (Figure 1A-H). Upon salt stress exposure, Pn, Gs, CE, E and ΦPSII decreased with increasing NaCl concentration in ZH13 and BB52, and they were higher in BB52 than in ZH13. In ZH13 and BB52, Ci gradually decreased with increasing NaCl concentration up to 200 mM (Figure 1D). At 300 mM NaCl concentration, Ci increased significantly in ZH13, whereas it increased to the control level in BB52 (Figure 1D).Effects of salt stress on rubisco activity and expression of rubisco activaseInitial rubisco activity was decreased by salt stress in ZH13 and BB52, and the decrease was greater in ZH13 (P< 0.05) (Figure 2A-C). Salt stress had no significant effect on total rubisco activity in BB52, but when NaCl concentration rose to 200 mM, significant decrease in total rubisco activity appeared in ZH13 (P< 0.05) (Figure 2B). Rubisco activation state decreased with increasing NaCl concentration and it was significantly higher in BB52 than in ZH13 (Figure 2C). Western blotting showed that rubisco activase content was pronouncedly declined upon 300 mM NaCl exposure, but this enzyme was not affected in BB52 (Figure 2A).Effects of salt stress on water potential, relative water content, glycinebetaine content and proline content With increasing NaCl concentration, Ψw and RWC decreased in ZH13 and BB52, while glycinebetaine and proline contents increased (Figure 3A-D). Ψw, RWC and contents of glycinebetaine and proline were higher in BB52 than in ZH13 under salt stress, and the difference in RWC between BB52 and ZH13 was not significant (Figure 3C,B).Effects of salt stress on Na+and Cl- contents and ion flux in the root surfaceIn ZH13 and BB52, Na+ and Cl- content in leaves and roots increased significantly with increasing NaCl concentration (Figure 4A, B). Under salt stress, BB52 could maintain lower Na+ and Cl- contents in leaves and roots. NMT results showed that Na+and Cl-were excluded by roots. Na+efflux of ZH13 was not affected under salt stress, and Cl-efflux of ZH13 remained at a lower level and decreased dramatically under 300 mM NaCl. (Figure 4C, D). Na+and Cl-effluxes of BB52 were significantly increased by 50 mM NaCl, and their effluxes level was not changed significantly with increasing NaCl (Figure 4C, D). Under salt stress, effluxes of Na+and Cl-in BB52 were significantly higher than those in ZH13 (Figure 4C, D).Figure 1.Changes in chlorophyll content (A), photosynthetic rate (Pn, B), stomatal conductance (Gs, C), intercellular CO2 concentration (Ci, D), carboxylation efficiency (CE, E), transpiration rate (E, F), maximal photochemical efficiency of PSII (Fv/Fm, G) and actual photochemical efficiency of PSII (ΦPSII, H) under salt stress for 7 days. DW indicates dry weight. Data in the figure indicate mean of five replicates (±SD). Significant difference between G. max (ZH13) and G. soja (BB52) is indicated by asterisks: * P< 0.05, ** P < 0.01.doi: 10.1371/journal.pone.0083227.g001Figure 2.Western-blotting of rubisco activase (A) and changes in rubisco activity (B) and rubisco activation state (C) under salt stress for 7 days.DW indicates dry weight. Data in the figure indicate mean of five replicates (±SD). Significant difference between G. max (ZH13) and G. soja (BB52) is indicated by asterisks: * P< 0.05, ** P < 0.01.doi: 10.1371/journal.pone.0083227.g002Effects of salt stress on MDA content, total phenolics content and antioxidant systemWhen NaCl treatment was over 100 mM, MDA content increased significantly in the leaves of ZH13. Salt-induced increase in MDA content also appeared in leaves of BB52, but the increase was lower than that in ZH13 (Figure 5A-F). Under salt stress, BB52 maintained significantly higher total phenolics, GSH and AsA contents in the leaves in contrast to ZH13 (Figure 5B-D). Under salt stress, SOD and APX activities were stimulated in BB52 and ZH13 leaves, and they were significantly higher in BB52 than in ZH13 (Figure 5E, F).DiscussionSalt-induced decrease of Pn in BB52 and ZH13 indicated that photosynthesis was negatively affected by salt stress (Figure 1B). Under salt stress, Pn was significantly higher in BB52 than in ZH13, suggesting the stronger salt tolerance of photosynthesis in BB52 (Figure 1B). According to the theory of Farquhar and Sharkey [35], salt-induced decrease in Pn wasmainly due to stomatal limitation in BB52 and ZH13 before NaCl concentration reached 300 mM, as G s and Ci decreased simultaneously (Figure 1C, D). The salt-induced stomatal limitation of Pn, as a common result, has been observed in other crops such as sorghum, rice and maize [10,11,36], and the decrease in Gs also can reduce water loss from leaf transpiration (Figure 1F). Under 300 mM NaCl, increase in Ci along with decrease in Gs appeared in BB52 and ZH13 (Figure 1D), and thus, the main limitation of Pn derived from non-stomatal factor. In our opinion, decreased Pn resulted from the depressed carboxylation process at 300 mM NaCl, as significant decrease in CE appeared (Figure 1E). ΦPSII also was significantly decreased at 300 mM NaCl, indicating photosynthetic electron transport rate was declined, but we did not believe that the decreased ΦPSII was the underlying cause for the decreased Pn. Fv/Fm is a classic parameter reflecting PSII stability. Unlike Fv/Fm, ΦPSII reflects PSII photochemical efficiency after photosynthetic initiation. Fv/Fm and chlorophyll content was not affected by salt stress (Figure 1 A, G), and therefore, the decreased ΦPSII did not result fromPSIIFigure 3. Changes in water potential (ψw , A), relative water content (RWC, B), glycinebetaine (C) and proline (D) contents under salt stress for 7 days. DW indicates dry weight. Data in the figure indicate mean of five replicates (±SD). Significant difference between G . max (ZH13) and G . soja (BB52) is indicated by asterisks: * P < 0.05, ** P < 0.01.doi: 10.1371/journal.pone.0083227.g003。
植物耐盐生理机制及耐盐性研究进展
Journal of Agricultural Catastrophology 2023, Vol.13 No.7植物耐盐生理机制及耐盐性研究进展蒋宇杰山东师范大学,山东济南 250000摘要 盐胁迫会对作物的生长造成一定的影响,从而造成产量下降。
阐述了盐胁迫对植物的影响,并综述了植物耐盐机理的研究、植物的耐盐性等。
通过对国内外有关文献的分析,提出了一些可以改善作物耐盐性的方法,进一步研究植物的抗盐性,给选育和生产奠定了基础。
关键词 盐胁迫;植物生长机理;抗盐性中图分类号:Q945.78 文献标识码:B 文章编号:2095–3305(2023)07–0020-031 盐胁迫对植物的影响 盐胁迫对植物生长和发育等方面都有明显的影响。
究其原因,主要有以下2点:第一,盐胁迫会使植株的水分吸收能力下降,从而使植株的生长受到抑制,这就是所谓的渗透胁迫[1]。
如果过量的盐分进入植株,就会对植株的细胞产生损伤,进而对植株的生长产生更大的影响。
第二,离子毒性在盐的浓度到达临界点后会出现,导致植物无法保持离子平衡,从而导致二次伤害。
结果表明,盐胁迫对植物的萌发、生长、光合色素、光合作用、离子平衡、养分平衡等都有影响。
1.1 盐分对植物生长发育的影响种子发芽是植物生命活动的基础和关键环节,是影响植物生长发育和繁殖的重要因素。
研究观察到,光果甘草和胀果甘草在400 mmol/L NaCl条件下的萌发率、根长、根鲜重等均显著降低。
有研究表明,盐害对松果菊种子发芽有显著的抑制作用,对发芽、发芽指数等都有明显的抑制作用,会延迟种子萌发时间,使其萌发周期拉长[2]。
总之,盐分胁迫对种子萌发有一定的抑制作用。
盐害对植株的表现效应主要有:新枝生长缓慢,植株高度下降,叶片枯黄、枯萎等,而与生理变化相比,植株生长速度较慢。
植物受到盐害的第一个征兆是老叶,然后是新叶。
植物老叶的盐害表现为:叶片边缘和叶片尖端先枯萎,接着变为黄绿色,再到凋谢,最终叶片发黑,叶片枯死。
understanding and improving salt tolerance in plants
R e p r o d u c e d f r o m C r o p S c i e n c e . P u b l i s h e d b y C r o p S c i e n c e S o c i e t y o f A m e r i c a . A l l c o p y r i g h t s r e s e r v e d .Understanding and Improving Salt Tolerance in PlantsViswanathan Chinnusamy,Andre ´Jagendorf,and Jian-Kang Zhu*ABSTRACTeven when ECe is Ͻ3.0dS m Ϫ1(Table 1),which in terms of osmotic potential is less than –0.117MPa (osmotic One-fifth of irrigated agriculture is adversely affected by soil salin-potential ϭϪ0.39ϫECe).At these salinity levels,the ity.Hence,developing salt-tolerant crops is essential for sustainingpredominant cause of crop susceptibility appears to be food production.Progress in breeding for salt-tolerant crops has been hampered by the lack of understanding of the molecular basis of salt ion toxicity rather than osmotic stress.Ion cytotoxicity tolerance and lack of availability of genes that confer salt tolerance.is caused by replacement of K ϩby Na ϩin biochemical Genetic evidence suggests that perception of salt stress leads to a reactions and conformational changes and loss of func-cytosolic calcium-signal that activates the calcium sensor protein tion of proteins as Na ϩand Cl Ϫions penetrate the hydra-SOS3.SOS3binds to and activates a ser/thr protein kinase SOS2.tion shells and interfere with noncovalent interactions The activated SOS2kinase regulates activities of SOS1,a plasma between their amino acids.Metabolic imbalances caused membrane Na ؉/H ؉antiporter,and NHX1,a tonoplast Na ؉/H ؉anti-by ionic toxicity,osmotic stress,and nutritional defi-porter.This results in Na ؉efflux and vacuolar compartmentation.ciency under salinity may also lead to oxidative stress A putative osmosensory histidine kinase (AtHK1)-MAPK cascade (Zhu,2002).Hence,engineering crops that are resistant probably regulates osmotic homeostasis and ROS scavenging.Os-to salinity stress is critical for sustaining food production motic stress and ABA (abscisic acid)-mediated regulation of LEA (late-embryogenesis-abundant)-type proteins also play important and achieving future food security.Understanding the roles in plant salt tolerance.Genetic engineering of ion transporters molecular basis of salt-stress signaling and tolerance and their regulators,and of the CBF (C-repeat-binding factor)regu-mechanisms is essential for breeding and genetic engi-lons,holds promise for future development of salt-tolerant crops.neering of salt tolerance in crop plants.Here,we discuss the molecular basis of cellular ion homeostasis,osmotic homeostasis,stress damage control and repair under Salinity is one of the major abiotic stresses that ad-salt stress,and their exploitation for genetic engineering versely affect crop productivity and quality.About of salt-tolerant crop plants.20%of irrigated agricultural land is adversely affected by salinity (Flowers and Yeo,1995).The problem of soil Sensors of Salt Stresssalinity is further increasing because of the use of poor Plants sense salt stress through both ionic (Na ϩ)and quality water for irrigation and poor drainage.In clay osmotic stress signals.Excess Na ϩcan be sensed either soils,improper management of salinity may lead to soil on the surface of the plasma membrane by a transmem-sodicity whereby sodium binds to negatively charged clay brane protein or within the cell by membrane proteins causing clay swelling and dispersal that makes the soil or Na ϩsensitive enzymes (Zhu,2003).In addition to less fit for crop growth.According to the USDA salinity its role as an antiporter,the plasma membrane Na ϩ/H ϩlaboratory,saline soil can be defined as soil having an antiporter SOS1(S alt O verly S ensitive 1),having 10to electrical conductivity of the saturated paste extract (EC e )12transmembrane domains and a long cytoplasmic tail,of 4dS m Ϫ1(4dS m Ϫ1≈40m M NaCl)or more.Most may act as a Na ϩsensor (Zhu,2003).This dual role would grain crops and vegetables are glycophytes and are highly be analogous to the sugar permease BglF in Escherichia susceptible to soil salinity even when the soil EC e is Ͻ4coli and the yeast ammonium transporter Mep2p.When dS m Ϫ1.Different threshold tolerance EC e and different expressed in Xenopus laevis oocytes Na ϩ–K ϩcotrans-rate of reduction in yield beyond threshold tolerance porters from Eucalyptus camaldulensis Dehnh.show in-EC e indicate variation in mechanisms of salt tolerance creased ion uptake under hypoosmotic conditions while,among crop species (Table 1).their Arabidopsis homolog do not show this osmosen-Soil type and environmental factors,such as vapor sing capacity (Liu et al.,2001).Entry of Na ϩthrough pressure deficit,radiation,and temperature may further nonspecific ion channels under salinity may cause mem-alter salt tolerance.Adverse effects of salinity on plant brane depolarization that activates Ca 2ϩchannels (Sand-growth may be due to ion cytotoxicity (mainly due toers et al.,1999),and thus generates Ca 2ϩoscillations,Na ϩ,Cl Ϫ,and SO Ϫ4),and osmotic stress (reviewed by and signals salt stress.Cell volume decreases because Zhu,2002).Most crop plants are susceptible to salinityof turgor loss under salinity-induced hyperosmotic stress may lead to retraction of the plasma membrane from Viswanathan Chinnusamy,Water Technology Centre,Indian Agricul-the cell wall,which is probably sensed by both stretch-tural Research Institute,New Delhi,India;Andre´Jagendorf,Depart-activated channels and transmembrane protein kinases,ment of Plant Biology,Cornell University,Ithaca,NY14853;Jian-such as two component histidine kinases and wall-asso-Kang Zhu,Institute for Integrative Genome Biology and Department ciated kinases (Urao et al.,1999;Kreps et al.,2002;Seki of Botany and Plant Sciences,University of California,Riverside,Cali-fornia 92521.Received 3Dec.2003.Symposia.*Corresponding author et al.,2002).Salinity up-regulates the biosynthesis of (jian-kang.zhu@).the plant stress hormone ABA (Jia et al.,2002;Xiong and Zhu,2003),and causes accumulation of reactive Published in Crop Sci.45:437–448(2005).oxygen species (ROS)(Smirnoff,1993;Hernandez et al.,©Crop Science Society of America677S.Segoe Rd.,Madison,WI 53711USA2001).ABA and ROS also regulate ionic and osmotic 437Published online January 31, 2005R e p r o d u c e d f r o m C r o p S c i e n c e . P u b l i s h e d b y C r o p S c i e n c e S o c i e t y o f A m e r i c a . A l l c o p y r i g h t s r e s e r v e d .438CROP SCIENCE,VOL.45,MARCH–APRIL 2005Table 1.Many important crops are susceptible to soil salinity†(Maas,1990).CropThreshold salinityDecrease in yield dS m Ϫ1Slope %per dS m Ϫ1Bean (Phaseolus vulgaris L.)1.019.0Eggplant (Solanum melongena L.) 1.1 6.9Onion (Allium cepa L.)1.216.0Pepper (Capsicum annuum L.) 1.514.0Corn (Zea mays L.)1.712.0Sugarcane (Saccharum officinarum L.) 1.7 5.9Potato (Solanum tuberosum L.)1.712.0Cabbage (Brassica oleracea var.capitata L.) 1.89.7Tomato (Lycopersicon esculentum Mill.) 2.59.9Rice,paddy (Oryza sativa L.)3.012.0Peanut (Arachis hypogaea L.) 3.229.0Soybean [Glycine max (L.)Merr.] 5.020.0Wheat (Triticum aestivum L.) 6.07.1Sugar beet (Beta vulgaris L.)7.0 5.9Cotton (Gossypium hirsutum L.)7.7 5.2Barley (Hordeum vulgare L.)8.05.0†Lack of a direct correlation between the threshold salinity and yield decrease per unit increase in salinity may be attributed to the differences in salt exclusion,uptake,compartmentation and other mechanisms of salt tolerance among these crop species.homeostasis as well as stress damage control and re-1997).Silica deposition and polymerization of silicate in the endodermis and rhizodermis blocks Na ϩinflux pair processes.Regulation of K ϩuptake and/or prevention of Na ϩthrough the apoplastic pathway in roots of rice (Yeo et al.,1999).Restriction of sodium influx either into the entry,efflux of Na ϩfrom the cell,and utilization of Na ϩfor osmotic adjustment are strategies commonly used root cells or into the xylem stream is one way of main-taining the optimum cytosolic K ϩ/Na ϩratio of plants by plants to maintain desirable K ϩ/Na ϩratios in the cytosol.Osmotic homeostasis is established either by Na ϩunder salt stress.The hkt1mutation suppresses the salt hypersensitivity and K ϩ-deficient phenotype of the Ara-compartmentation into the vacuole or by biosynthesis and accumulation of compatible solutes.ROS detoxifi-bidopsis S alt O verly S ensitive 3(sos3)mutant (Rus et al.,2001a).Antisense expression of wheat HKT1in cation systems as well as stress proteins belonging to the LEA protein family contribute to prevention of salt-transgenic wheat causes significantly less 22Na uptake and enhances growth under salinity when compared stress damage (Zhu,2002).In addition to these mecha-nisms,Na ϩsecretion is a strategy used by some halo-with control plants (Laurie et al.,2002).These results suggest that either inactivation of the low affinity Na ϩphytic plants.Thus,precise regulation of ion transport systems is critical for salt tolerance.Important insights transporter (HKT)activity or suppression of its expres-sion can considerably improve plant salt tolerance.into ion homeostasis under salt stress have emerged from the molecular genetic analysis of s alt o verly s ensi-In saline conditions,cellular potassium levels can be maintained by activity or expression of potassium-spe-tive (sos )mutants of Arabidopsis (Fig.1;Zhu,2003).cific transporters.In Mesembryanthemum crystallinum L.,high affinity K ϩtransporter–K ϩuptake genes are Sodium Influx and K ؉/Na ؉Balanceup-regulated under NaCl stress (Su et al.,2002).In yeast,A high K ϩ/Na ϩratio in the cytosol is essential for HAL1and HAL3regulate K ϩuptake and Na ϩefflux.normal cellular functions of plants.Na ϩcompetes with Overexpression of the Arabidopsis HAL3a gene en-K ϩuptake through Na ϩ–K ϩcotransporters,and may hances salt tolerance of transgenic Arabidopsis (Es-also block the K ϩ-specific transporters of root cells un-pinosa-Ruiz et al.,1999).Similarly,transgenic tomato der salinity (Zhu,2003).This results in toxic levels of plants overexpressing yeast HAL1gene show a higher sodium as well as insufficient K ϩconcentration for enzy-K ϩ/Na ϩratio and improved salt tolerance than control matic reactions and osmotic adjustment.Under salinity,plants.Transgenic tomato plants exhibit lower reduction sodium gains entry into root cell cytosol through cation in fruit yield than that of control plants when irrigated channels or transporters (selective and nonselective)or with 35m M NaCl (Rus et al.,2001b).Signaling events into the root xylem stream via an apoplastic pathway that regulate the potassium-specific transporters under depending on the plant species.In Arabidopsis (Uozumi salinity should be understood.et al.,2000),Eucalyptus (Liu et al.,2001),and wheat,it has been shown that high affinity K ϩtransporters Sodium Efflux(HKT)act as low affinity Na ϩtransporters (Rubio et al.,1995;Gorham et al.,1997)under salinity.The HKT Sodium efflux from root cells prevents accumulation of toxic levels of Na ϩin the cytosol and transport of transporters of Eucalyptus camaldulensis are more per-meable to Na ϩthan they are to K ϩwhen extracellular Na ϩto the shoot.Molecular genetic analysis in Arabi-dopsis sos mutants have led to the identification of a concentrations of Na ϩand K ϩare equal (Liu et al.,2001).Hence,under salinity HKT homologs may con-plasma membrane Na ϩ/H ϩantiporter,SOS1,which plays a crucial role in sodium extrusion from root epider-tribute to Na ϩinflux.However,in rice,sodium influx into the xylem through the apoplastic pathway appears mal cells under salinity.The SOS1transcript level is up-regulated under salt stress.The sos1mutant plants showto be more significant (Yadav et al.,1996;Garcia et al.,R e p r o d u c e d f r o m C r o p S c i e n c e . P u b l i s h e d b y C r o p S c i e n c e S o c i e t y o f A m e r i c a . A l l c o p y r i g h t s r e s e r v e d .CHINNUSAMY ET AL.:SALT STRESS SIGNALING AND SALT TOLERANCE439Fig.1.SOS signaling pathway for ion homeostasis under salt stress in Arabidopsis .Salt stress elicited Ca 2؉signals are perceived by SOS3,which activates the protein kinase SOS2.Activated SOS2phosphorylates SOS1,a plasma membrane Na ؉/H ؉antiporter,which then transports Na ؉out of the cytosol.The transcript level of SOS1is regulated by the SOS3-SOS2kinase complex.SOS2also activates the tonoplast Na ؉/H ؉antiporter that sequesters Na ؉into the vacuole.Na ؉entry into the cytosol through the Na ؉transporter HKT1may also be restricted by SOS2.ABI1regulates the gene expression of NHX1,while ABI2interacts with SOS2and negatively regulates ion homeostasis either by inhibiting SOS2kinase activity or the activities of SOS2targets.Double arrow indicates SOS3-independent and SOS2-dependent pathway.hypersensitivity to salt stress (100m M NaCl),and accu-ing EF hands and an N-myristoylation motif (Liu and Zhu,1998;Ishitani et al.,2000).Mutations that disrupt mulate more Na ϩin shoots than wild-type plants.So-dium efflux by SOS1is also vital for salt tolerance of either calcium binding (sos3-1)or myristoylation (G2A)of SOS3cause salt-stress hypersensitivity in Arabidopsis meristem cells such as growing root-tips and shoot apex as these cells do not have large vacuoles for sodium plants (Ishitani et al.,2000).The SOS3gene product transduces a salt stress-elicited calcium signal by activat-compartmentation (Shi et al.,2000&2002).Isolated plasma membrane vesicles from sos1mutants show ing SOS2,a ser/thr protein kinase with an N-terminal kinase catalytic domain that is similar to that of yeast significantly less inherent as well as salt stress-induced Na ϩ/H ϩantiporter activity than vesicles from wild-type SNF1and animal AMP-activated kinase,and a unique C-terminal regulatory domain.The C-terminal regula-plants (Qiu et al.,2002).The expression of SOS1is ubiquitous,but stronger in epidermal cells surrounding tory domain of SOS2consists of an autoinhibitory FISL motif (Liu et al.,2000),deletion of which results in the root-tip,as well as parenchyma cells bordering the xylem.Thus,SOS1functions as a Na ϩ/H ϩantiporter constitutive activation of SOS2(Guo et al.,2001).Under salt stress,SOS3binds to the FISL motif of SOS2and on the plasma membrane and plays a crucial role in sodium efflux from root cells and the long distance Na ϩactivates its substrate phosphorylation (protein kinase)activity (Halfter et al.,2000).Activated SOS2then phos-transport from root to shoot (Shi et al.,2002).Indeed,transgenic Arabidopsis plants overexpressing SOS1phorylates SOS1,and results in activation of antiporter activity of SOS1.The Na ϩ–H ϩexchange activity of iso-have lower Na ϩin the xylem transpirational stream and in shoots compared with wild-type plants.These plants lated plasma membranes vesicles from sos3and sos2mutants is significantly less than that of wild-type plants.also show enhanced salt tolerance,measured in terms of their growth,ability to bolt and flower at increasing Consistent with this finding,these mutants also accumu-late higher levels of Na ϩ,similar to those accumulated concentrations of salt stress (50–200m M NaCl);while,control plants became necrotic and have failed to bolt by the sos1mutant (Quintero et al.,2002).Overexpres-sion of an active form of SOS2could overcome the salt (Shi et al.,2003).Sodium efflux through SOS1under salinity is regu-hypersensitivity of sos2and sos3mutants and enhanced the salt tolerance of transgenic Arabidopsis (Guo et al.,lated by SOS3–SOS2kinase complex (Fig.1).In Arabi-dopsis ,salt-stress induced calcium signatures are sensed 2004).The SOS1up-regulation under salt stress is also impaired in sos2and sos3mutants.Hence,the SOS3–by SOS3,a Ca 2ϩsensor protein with three calcium bind-R e p r o d u c e d f r o m C r o p S c i e n c e . P u b l i s h e d b y C r o p S c i e n c e S o c i e t y o f A m e r i c a . A l l c o p y r i g h t s r e s e r v e d .440CROP SCIENCE,VOL.45,MARCH–APRIL 2005SOS2signaling pathway positively regulate salt-stress proteins such as SOS3,SCaBP1(SOS3-like calcium-binding proteins 1),SCaBP3,SCaBP5,and SCaBP6.induced SOS1gene expression and/or transcript stabil-ity as well as SOS1transporter activity (Shi et al.,2003).One of these SCaBPs may signal SOS2to regulate the tonoplast Na ϩ/H ϩ-exchange activity (Fig.1;Qiu et al.,In addition to increasing cytosolic calcium,salt-stress induced ABA accumulation also appears to regulate 2003).Transgenic Arabidopsis plants overexpressing AtNHX1the SOS pathway through the ABA insensitive 2(ABI2)protein phosphatase 2C.ABI2interacts with the protein have showed significantly higher salt (200m M NaCl)tolerance than wild-type plants (Apse et al.,1999).Since phosphatase interaction (PPI)motif of SOS2.This inter-action is abolished by the abi2-1mutation,which en-tomato is a highly salt-sensitive crop (Table 1),an effort has been made to improve its salt tolerance by overex-hances tolerance of seedlings to salt shock (150m M NaCl)and causes ABA insensitivity.Hence,the wild-pressing AtNHX1.These tomato transgenics grow and produce fruits in the presence of very high salt concen-type ABI2may negatively regulate salt tolerance either by inactivating SOS2,or the SOS2regulated Na ϩ/H ϩtrations (200m M NaCl).Yield and fruit quality of trans-genic tomato plants under salinity are equivalent to antiporters such as SOS1or NHX1(Fig.1;Ohta et al.,2003).those of control plants grown under nonstress conditions (Zhang and Blumwald,2001).Similar results have been reported for transgenic canola (Brassica napus L.)over-Sodium Compartmentationexpressing AtNHX1(Zhang et al.,2001).A positive turgor is indispensable for expansion growth of cells and stomatal openings in plants.A de-Compatible Osmolytescrease in water potential due to soil salinity causes os-motic stress that leads to turgor loss.Plants have evolved Although use of ions for osmotic adjustment may be energetically more favorable than biosynthesis of organic an osmotic adjustment (active solute accumulation)mechanism that maintains water uptake and turgor un-osmolyte under osmotic stresses,many plants accumulate organic osmolytes to tolerate osmotic stresses.These os-der osmotic stress conditions.For osmotic adjustment,plants use inorganic ions such as Na ϩand K ϩand/or molytes include proline,betaine,polyols,sugar alcohols,and soluble sugars.Glycine betaine and trehalose act as synthesize organic compatible solutes such as proline,betaine,polyols,and soluble sugars.Vacuolar seques-osmoprotectants by stabilizing quaternary structures of proteins and highly ordered states of membranes.Manni-tration of Na ϩis an important and cost-effective strategy for osmotic adjustment that also reduces the Na ϩcon-tol serves as a free-radical scavenger.Proline serves as a storage sink for carbon and nitrogen and a free-radical centration in the cytosol.Na ϩsequestration into the vacu-ole depends on expression and activity of Na ϩ/H ϩanti-scavenger.It also stabilizes subcellular structures (mem-branes and proteins),and buffers cellular redox potential porters as well as on V-type H ϩ-ATPase and H ϩ-PPase.These phosphatases generate the necessary proton gra-under stress.Hence,these organic osmolytes are known as osmoprotectants (Bohnert and Jensen,1996;Chen and dient required for activity of Na ϩ/H ϩantiporters.Overexpression of AVP1,a vacuolar H ϩ-pyrophos-Murata,2000).Genes involved in osmoprotectant biosyn-thesis are up-regulated under salt stress,and concentra-phatase in Arabidopsis enhanced sequestration of Na ϩinto the vacuole and maintained higher relative water tions of accumulated osmoprotectants correlate with os-motic stress tolerance (Zhu,2002).Analysis of the content in leaves.These plants also show higher salt-and drought-stress tolerance than that of wild type Arabidopsis t365mutant supports the involvement of os-moprotectants in salt tolerance.The t365mutant is im-(Gaxiola et al.,2001).The tonoplast Na ϩ/H ϩantiporter NHX1gene is induced by both salinity and ABA in paired in the S -adenosyl-L-methionine phosphoethano-lamine N -methyltransferase (PEAMT )gene.The PEAMT Arabidopsis (Shi and Zhu,2002)and rice (Fukuda et al.,1999).The AtNHX1promoter contains putative ABA enzyme catalyzes conversion of phosphoethanolamine to phosphocholine,which is a precursor of glycinebetaine responsive elements (ABRE)between –736and –728from the initiation codon.AtNHX1expression under biosynthesis (Mou et al.,2002).Salt tolerance of transgenic tobacco engineered to salt stress is partially dependent on ABA biosynthesis and ABA signaling through ABI1.Salt-stress induced over-accumulate mannitol was first demonstrated by Tarczynski et al.(1993).Genetically engineered over-up-regulation of AtNHX1expression is lower in ABA deficient mutants (aba2-1and aba3-1)and in the ABA production of compatible osmolytes in transgenic plants such as Arabidopsis ,rice,wheat,and Brassica has also insensitive mutant,abi1-1(Shi and Zhu,2002).Compar-ing tonoplast Na ϩ/H ϩ-exchange activity (mainly due to been shown to enhance stress tolerance as measured by germination,seedling growth,survival,recovery,pho-AtNHX1)between wild type and mutants (sos1,sos2,and sos3)shows that SOS2also regulates the tonoplast tosystem II yield,and seed production under very high salt and osmotic stresses.The observed salt tolerance exchange.The impaired tonoplast Na ϩ/H ϩ-exchange activity in vitro from isolated sos2tonoplasts could be was attributed to the osmoprotectant effect of compati-ble osmolytes rather than their contribution to osmotic restored to levels in wild type by adding activated SOS2protein.Since the tonoplast Na ϩ/H ϩ-exchange activity adjustment (Table 2).It is interesting to note that gly-cine betaine-(Kishitani et al.,2000)and trehalose-(Garg is not affected in the sos3mutant,the tonoplast Na ϩ/H ϩ-exchange activity is not regulated by SOS3.SOS2et al.,2002)overproducing transgenic rice plants accu-mulated fewer Na ϩions,and maintained K ϩuptake,has been found to interact with plant calcium sensorR e p r o d u c e d f r o m C r o p S c i e n c e . P u b l i s h e d b y C r o p S c i e n c e S o c i e t y o f A m e r i c a . A l l c o p y r i g h t s r e s e r v e d .CHINNUSAMY ET AL.:SALT STRESS SIGNALING AND SALT TOLERANCE441Table 2.Salt-stress tolerance of transgenic plants over-producing compatible osmolytes.Gene and sourceTransgenic plantsStress tolerant traitsReference MannitolE.coli mt1D (mannitol-1-phosphate tobacco fresh weight,plant height and flowering underTarczynski et al.,1993dehydrogenase)salinity stressE.coli mt1D Arabidopsis germination at 400m M NaCl Thomas et al.,1995E.coli mt1D tobacco salt-stress tolerance;mannitol contributed only toKarakas et al.,199730-40%of the osmotic adjustmentE.coli mt1Dwheat (Triticum aestivum L.)only 8%biomass reduction when compared toAbebe et al.,200356%reduction in control plants in 150m M NaCl stressD-OnonitolIMT1(myo-inositol O -methyl trans-tobacco drought and salinity stressSheveleva et al.,1997ferase)of common ice plant SorbitolStpd1(sorbitol-6-phosphate dehy-Japanese persimmon tolerance in Fv/Fm ratio under NaCl stress Gao et al.,2001drogenase)of apple,driven by CaMV 35S promoterGlycine betaineArthrobacter globiformis CodA Arabidopsis germination at 300m M NaCl;seedling growth Hayashi et al.,1997(choline oxidase)at 200m M NaCl;retention of PSII activity at 400m M NaClA.globiformis CodA targeted to the ricefaster recovery after 150m M NaCl stress Sakamoto et al.,1998;chloroplasts or cytosol Mohanty et al.,2002A.globiformis CodABrassica juncea (L.)Czernj.germination in 100–150m M NaCl;seedling Prasad et al.,2000growth in 200m M NaClE.coli choline dehydrogenase (betA )tobaccobiomass production of greenhouse grown plants Holmstrom et al.,2000and betaine aldehyde dehydroge-under salt stress;faster recovery from photo nase (betB )genesinhibition under high light,salt stress and cold stressesAtriplex hortensis betaine aldehyde wheat (Triticum aestivum L.)seedling growth in 0.7%(ϭ120m M )NaCl Guo et al.,2000dehydrogenase (BADH )gene under maize ubiquitin promoter Barley peroxisomal BADH genericestability in chlorophyll fluorescence under Kishitani et al.,2000100m M NaCl stress;accumulates less Na ؉and Cl Ϫions but maintained K ؉uptake ProlineVigna aconitifolia L.P5CS (⌬1]-tobacco root growth;flower developmentKishor et al.,1995pyrroline-5-carboxylate synthe-tase)geneVigna aconitifolia L.P5CS gene rice faster recovery after a short period of salt stress Zhu et al,1998under barley HVA22promoter Mutated gene of Vigna aconitifolia L.tobaccoimproved seedlings tolerance and low free radical Hong et al,2000P5CS which encode P5CS enzyme levels at 200m M NaClthat lacks end product (proline)inhibitionAntisense proline dehydrogenase Arabidopsis tolerant to high salinity (600m M NaCl);constitu-Nanjo et al.,1999genetive freezing tolerance (Ϫ7؇C)TrehaloseE.coli otsA (Trehalose-6-phosphate rice root and shoot growth at 4wk of 100m M NaCl Garg et al.,2002synthase)and otsB (Trehalose-stress;survival under prolonged salt stress;6-phosphate phosphatase)bi-func-maintenance of high K ؉/Na ؉ratio;Low Na ؉tional fusion gene (TPSP )under accumulation in the shoot;maintained high the control of ABA responsive PSII activity and soluble sugar levelspromoter or Rubisco small subunit (rbcS )promoterE.coli TPSP under maize ubiquitin rice better seedling growth and PSII yield under salt,Jang et al.,2003promoterdrought and cold stressesThus,these plants retained optimal K ϩ/Na ϩratios nec-component hybrid histidine kinase,ATHK1,from Ara-bidopsis is implicated in osmosensing under salt stress essary for cellular functions.Whether ion homeostasis in these transgenics was either due to direct regulation based on induced expression and ability to complement the yeast double mutant lacking both osmosensors of ion transporters or to maintenance of cellular integ-rity by protecting membranes and proteins from oxida-(sln1⌬sho1⌬).By analogy to SLN1of yeast,the Arabi-dopsis ATHK1is also probably active at low osmolarity.tive damage was not known and needs to be determined.Although enhanced synthesis and accumulation of Active ATHK1may inactivate a response regulator by phosphorylation.Inactivation of ATHK1under high compatible solutes under osmotic stresses are well docu-mented,little is known about the signaling cascades that osmolarity may result in the accumulation of nonphos-phorylated active form of the response regulator,which regulate the compatible solute biosynthesis in higher plants.A signaling cascade similar to that of the yeast then stimulates osmolyte biosynthesis in plants by acti-vating a MAPK pathway(s)(Urao et al.,1999).Tran-Mitogen Activated Protein Kinase-High Osmotic Glyc-erol 1(MAPK-HOG1)pathway may regulate osmolyte scriptome analyses also show induction of receptor-like kinase genes in Arabidopsis under salt stress (Krepsbiosynthesis (Zhu,2002).A putative osmosensory two-R e p r o d u c e d f r o m C r o p S c i e n c e . P u b l i s h e d b y C r o p S c i e n c e S o c i e t y o f A m e r i c a . A l l c o p y r i g h t s r e s e r v e d .442CROP SCIENCE,VOL.45,MARCH–APRIL 2005et al.,2002;Seki et al.,2002).However,genetic and by both ABA-dependent and independent signaling molecular evidences to support the role of these proteins pathways (Fig.2).Promoters of LEA-like genes contain in osmotic stress sensing and compatible osmolyte bio-dehydration responsive elements/C-Repeat (DRE/CRT),synthesis are lacking.ABA-responsive elements (ABREs),and/or MYB/MYC ABA may also regulate osmolyte biosynthesis in recognition elements.The DRE/CRT elements regulate plants under salt stress.Osmotic stress-induced ABA gene expression in response to dehydration (salt,drought,accumulation has been shown to regulate the P5CS gene and cold stresses);while,ABRE and MYB/MYC ele-involved in proline biosynthesis (Xiong et al.,2001a).ments control gene expression in response to ABA un-Proline induces the expression of salt-stress responsive der abiotic stresses (Thomashow,1999;Shinozaki and genes,which have proline responsive elements (PRE ,Yamaguchi-Shinozaki,2000).ACTCAT)in their promoters (Satoh et al.,2002;Oono Genetic analysis of ABA-deficient Arabidopsis mu-et al.,2003).Better understanding of the salt-stress sig-tants,los5and los6,has revealed that ABA is necessary naling pathway that regulates compatible osmolyte bio-for the salt-stress induced expression of some Arabi-synthesis will help to devise better breeding and genetic dopsis LEA genes (Xiong et al.,2001a;Xiong et al.,2002).engineering strategies.Ca 2ϩand/or H 2O 2act as second messengers of ABA induced stomatal closure and gene expression under LEA-Type Proteinsabiotic stresses (Leung and Giraudat,1998;Schroeder et al.,2001).Transient expression analysis has revealed Osmotic stresses induce late-embryogenesis-abun-that IP 3and cADPR-gated calcium channels are in-dant (LEA)proteins in vegetative tissues,which impart volved in ABA induced Ca 2ϩconcentration changes,dehydration tolerance to vegetative tissues of plants.and these Ca 2ϩtransients regulate expression of LEA-These LEA-type proteins are encoded by RD (respon-type genes,such as RD29A and KIN2(Wu et al.,1997).sive to dehydration),ERD (early responsive to dehydra-Genetic evidence from the fry1(fiery 1)mutant,defec-tion),KIN (cold inducible),COR (cold regulated),and tive in inositol polyphosphate 1-phosphatase,has dem-RAB (responsive to ABA)genes in different plant spe-onstrated that IP 3metabolism is critical for ABA and cies (Shinozaki and Yamaguchi-Shinozaki,2000;Zhu,abiotic stress signaling (Xiong et al.,2001b).Salt-stress/2002).Accumulation levels of these proteins correlate ABA induced Ca 2ϩsignals are at least partially transduced with stress tolerance in various plant species suggesting through calcium-dependent protein kinases (CDPKs).protective roles under osmotic stress.Transgenic rice Transient expression analyses in maize protoplasts have plants engineered to overexpress a barley LEA gene,shown that an increase in cytosolic Ca 2ϩconcentration HVA1,under control of the rice actin 1promoter exhibit activates CDPKs,which in turn induce the stress respon-better stress tolerance under 200m M NaCl and drought sive HVA1promoter.Moreover,expression of CDPKs stress than wild-type plants (Xu et al.,1996).Expression of LEA-type genes under osmotic stresses is regulatedis under the negative control of ABI1proteinphospha-Fig.2.LEA-type gene transcription under abiotic stresses in Arabidopsis .ABA-independent DREB2and ABA-dependent CBF4transcription factors transactivate DRE/CRT cis-elements in the promoters of LEA type genes.ABA-dependent pathways regulate LEA type genes through MYC/MYB and bZIP type transcription factors.ABA-dependent signaling is mediated through IP3and Ca 2؉.FRY1negatively regulates IP3levels.ABA induced Ca 2؉signaling is negatively regulated by ABI1/2protein phosphatase 2C.Low temperature stress activates ICE1a myc-like bHLH transcription factor,which binds to myc type cis-elements of CBF3promoter and induces CBF3expression.CBFs bind to the CRT/DRE cis-elements on the promoter of LEA-type genes and induce expression of these genes.。
冰叶日中花耐盐机制的研究进展
冰叶日中花耐盐机制的研究进展丰宇凯;李飞飞;王华森【摘要】Mesembryanthemum crystallinum L. is a halophyte with high resistance to salt stress. The salt tolerance mechanism of M. crystallinum was summarized from the osmotic adjustment, aquaporin regulation and reactive oxygen scavenging, to provide the theoretically basis for M. crystallinum planting and extension, improvement of saline land.%冰叶日中花 (Mesembryanthemum crystallinum L.) 是一种耐盐性极强的盐生植物.该研究从冰叶日中花的渗透调节、水通道蛋白调控以及活性氧清除等方面综述了其耐盐机制, 旨在为冰叶日中花的种植推广、盐碱地的改良提供理论依据.【期刊名称】《湖北农业科学》【年(卷),期】2018(057)023【总页数】5页(P15-18,147)【关键词】冰叶日中花 (Mesembryanthemum crystallinum L.);耐盐机制;盐生植物【作者】丰宇凯;李飞飞;王华森【作者单位】浙江农林大学农业与食品科学学院,浙江临安 311300;浙江农林大学农业与食品科学学院,浙江临安 311300;浙江农林大学农业与食品科学学院,浙江临安 311300【正文语种】中文【中图分类】S636.9盐胁迫是影响作物产量主要的非生物胁迫之一。
盐胁迫会影响作物对水分的吸收,影响作物体内离子的平衡,还会导致膜透性的改变以及生理生化代谢的紊乱,进而影响作物的生长甚至导致死亡[1]。
科技改良草场盐碱化的英语作文题目
科技改良草场盐碱化的英语作文题目全文共3篇示例,供读者参考篇1Using Technology to Improve Salinization of RangelandsSalinization is a major issue impacting rangelands aroundthe world. As a student studying environmental science, I've learned about the detrimental effects soil salinization can haveon ecosystems and agricultural productivity. However, emerging technologies offer promising solutions to monitor, mitigate and remediate this complex challenge.Salinization refers to the buildup of salts in soils and waters. While low levels occur naturally, human activities like irrigation, land clearing, and groundwater overexploitation can exacerbate the problem. Excess salts make it difficult for plants to absorb water and essential nutrients from the soil. This inhibits growth, reduces yields, and can eventually render land unsuitable for cultivation or grazing.The impacts are far-reaching - salinization threatens food security, economic livelihoods, and biodiversity in affected regions. An estimated 20% of the world's cultivated lands and 33%of irrigated farmlands are salt-affected. Rangelands, which provide grazing areas for livestock, are particularly vulnerable due to sparse vegetation cover and arid conditions.As our global population continues growing, there is an urgent need to rehabilitate degraded lands and make efficient use of available resources. This is where technology can play a pivotal role in tackling salinization through precise monitoring, targeted interventions, and sustainable land management practices.Remote Sensing for Soil MappingOne of the greatest challenges in addressing salinization is obtaining accurate data on its spatial extent and severity over vast areas. Thanks to advances in remote sensing, we can now map soil conditions across entire landscapes in remarkable detail.Multispectral and hyperspectral imaging sensors mounted on satellites, aircraft or drones can detect unique spectral signatures of surface salts and salt-affected vegetation. Software algorithms then process this data into high-resolution salinization maps. These cutting-edge tools allow researchers and land managers to rapidly identify hotspots, quantify areas impacted, and prioritize sites for remediation.Precision AgricultureWith detailed soil data in hand, technological solutions in precision agriculture can be deployed to better manage salinization. Precision ag uses site-specific data to optimize farm inputs like water, fertilizers and soil amendments.Variable rate technology (VRT) enables inputs to be applied at different prescribed rates across a field based on soil properties mapped using GPS coordinates. In salt-affected areas, farmers can use VRT to precisely target gypsum, organic matter or other amendments to displace sodium and improve soil structure.Smart irrigation systems that automatically adjust water volumes based on soil moisture sensor data can also help reduce waterlogging that concentrates salts. Overall, precision ag reduces costs, minimizes environmental impacts from excess inputs, and boosts productivity on saline lands.Rehabilitation Using HalophytesA nature-based approach for remediating salt-affected rangelands involves cultivating salt-tolerant plants called halophytes. Certain grasses, shrubs and trees can thrive inhigh-saline conditions using special adaptations.Researchers are exploring how to introduce native halophytes on degraded sites to lower water tables that draw up salts. As the plants establish root systems, excess salts get absorbed into their biomass. This revegetation reduces salt loads while providing nutritious fodder for livestock. Halophyte crops are even being investigated as potential biofuel feedstocks.Some forward-thinking projects are utilizing biotech tools to develop halophyte cultivars with enhanced traits like higher yields, greater salt tolerance, enhanced nutritional profiles, and resistance to pests or diseases. Gene editing techniques could potentially accelerate the breeding process.Engineered AmendmentsIn severe cases where soils have become inhospitable to most plants, geo-engineering solutions may be required. One emerging technology uses industrially produced mineral amendments to sequester salts and improve soil properties.Mineral polymers like polyacrylic acids and polyacrylamides have a high binding affinity for salt ions. When applied to soils, they enmesh salt molecules into stable cross-linked hydrogel solids, preventing those salts from dissolving into soil water and affecting plants.These engineered amendments also help bind soil particles together into stable aggregates that improve water infiltration, aeration and overall soil workability. Scientists are continually testing and refining these synthetic products to optimize performance, cost-effectiveness and environmental impacts.As we look ahead, innovative technologies will likely play an expanding role in detecting, managing and rehabilitatingsalt-affected lands. Precision data systems, smart ag machinery, biological solutions, and new soil amendments offer powerful tools in our arsenal.However, technology alone cannot solve the salinization crisis. Integrated approaches combining these innovations with improved irrigation practices, vegetation buffers, drainage systems and sustainable farming methods will be crucial. There must also be policy support through funding, extension services and incentives for land stewardship.Salinization is a complex, multifaceted issue tied to unsustainable land use, groundwater depletion, climate change and poor management practices. But by harnessingcutting-edge technologies in concert with ecological principles, we can monitor and mitigate salt buildup while restoring productivity to degraded rangelands. As future environmentalprofessionals, my classmates and I have a major role to play in realizing these solutions for long-term food and water security.篇2Title: Harnessing Technology to Tackle Salt-Alkalized GrasslandsAs a student deeply concerned about environmental issues, I have become increasingly aware of the pressing problem of salt-alkalized grasslands. These degraded landscapes, once lush and verdant, have been ravaged by excessive soil salinity and alkalinity, leaving them barren and inhospitable to plant growth. However, amid this bleak scenario, I firmly believe that modern technology holds the key to revitalizing these neglected ecosystems.Salt-alkalized grasslands are a global phenomenon, affecting vast swaths of land across various regions. The root cause of this issue lies in a combination of natural processes and human activities. Climate change, coupled with unsustainable agricultural practices and improper irrigation techniques, has led to the accumulation of salts and alkaline compounds in the soil. As a result, these areas have become increasingly unproductive, posing significant challenges to local communities that rely onthese grasslands for grazing livestock and sustaining their livelihoods.Fortunately, the rapid advancements in technology have opened up new avenues for combating this environmental challenge. One promising approach lies in the realm of remote sensing and Geographic Information Systems (GIS). By leveraging satellite imagery and advanced mapping techniques, researchers can precisely identify and monitor the extent of salt-alkalized areas. This data can then be used to develop targeted strategies for remediation and restoration.Moreover, precision agriculture technologies, such asGPS-guided machinery and variable-rate application systems, offer tremendous potential for mitigating soil salinity and alkalinity. These advanced systems allow for precise and controlled application of soil amendments, such as gypsum or organic matter, which can help neutralize the adverse effects of salts and alkaline compounds. By tailoring the treatment to specific areas within the grasslands, we can optimize resource utilization and minimize environmental impact.Another exciting development is the use of biotechnology in developing salt-tolerant plant varieties. Through genetic engineering and selective breeding techniques, scientists areworking to create crop and forage species that can withstand the harsh conditions of salt-alkalized soils. These resilient plants not only have the potential to restore vegetation cover but also provide valuable resources for livestock and local communities.In addition to these cutting-edge technologies, traditional methods of soil remediation should not be overlooked. Techniques such as phytoremediation, which involves using certain plant species to absorb and remove salts from the soil, can be coupled with modern monitoring and management strategies for enhanced effectiveness.Furthermore, the integration of advanced computational models and decision support systems can aid in developing comprehensive management plans for salt-alkalized grasslands. These tools can simulate various scenarios, taking into account factors such as climate patterns, soil characteristics, and vegetation dynamics, allowing for informed decision-making and adaptive management strategies.However, the successful implementation of these technological solutions hinges on collaborative efforts among researchers, policymakers, and local communities. It is imperative to foster knowledge-sharing platforms and facilitate capacity-building initiatives to ensure that these technologiesare accessible and effectively utilized by those most affected by salt-alkalized grasslands.As a student passionate about sustainable solutions, I am excited by the potential of technology to address this pressing environmental issue. By embracing innovative approaches and combining them with traditional knowledge, we can pave the way for the restoration of these degraded landscapes, ensuring a resilient and productive future for grasslands globally.In conclusion, the challenge of salt-alkalized grasslands may seem daunting, but it is not insurmountable. Through the judicious application of cutting-edge technologies, coupled with traditional methods and collaborative efforts, we can reclaim these once-thriving ecosystems. It is our responsibility as stewards of the environment to harness the power of science and innovation to create a sustainable future for our planet's precious resources.篇3Technology Improving Salinization in GrasslandsSalinization is a major issue that plagues grasslands around the world, causing soil degradation, reduced plant growth, and overall ecosystem decline. As a student passionate aboutenvironmental conservation, I find the topic of using technology to mitigate salinization in grasslands fascinating and worthy of exploration. In this essay, I will delve into the causes and effects of salinization, current technological approaches to combat it, and potential future advancements that could revolutionize the way we tackle this pressing issue.Causes and Effects of Salinization in GrasslandsSalinization, or the accumulation of salts in soil, can occur due to various natural and human-induced factors. Natural causes include weathering of parent rock materials, deposition of oceanic salt spray, and the intrusion of saline groundwater. However, human activities such as improper irrigation practices, deforestation, and climate change have exacerbated the problem significantly.The effects of salinization on grasslands are far-reaching and detrimental. High salt concentrations in the soil can disrupt the water uptake and nutrient absorption processes of plants, leading to stunted growth, reduced productivity, and even plant death. This, in turn, can lead to a loss of biodiversity, as only the most salt-tolerant species can survive in such conditions. Furthermore, salinization can alter soil structure, reducing waterinfiltration and increasing erosion, ultimately leading to desertification.Current Technological ApproachesIn recent years, several technological solutions have been proposed and implemented to combat salinization in grasslands. One approach is the use of remote sensing and Geographic Information System (GIS) technologies. These tools allow for the accurate mapping and monitoring of saline-affected areas, enabling targeted interventions and efficient resource allocation.Another promising technology is the use of subsurface drainage systems. These systems involve the installation of perforated pipes or tile drains below the soil surface to remove excess water and salts from the root zone. This approach has proven effective in reclaiming saline-affected areas and improving soil conditions for plant growth.Phytoremediation, the use of salt-tolerant plants to remove salts from the soil, is another innovative solution. Certain plant species, such as halophytes, have the ability to accumulate and metabolize salts, making them valuable tools in the remediation process. This approach not only addresses salinization but also promotes biodiversity and provides additional ecosystem services.Future Advancements and Potential SolutionsWhile current technological approaches have shown promise, there is still room for further advancements and innovative solutions. One area of potential exploration is the use of nanotechnology for soil remediation. Nanoparticles and nanomaterials could be engineered to selectively remove or immobilize salts in the soil, offering a more targeted and efficient approach to salinization mitigation.Another exciting prospect is the development ofsalt-tolerant crop varieties through genetic engineering or selective breeding. By introducing genes that confer salt tolerance, researchers could create plant varieties that can thrive in saline conditions, ensuring food security and sustainable agricultural practices in affected areas.Additionally, the integration of artificial intelligence (AI) and machine learning algorithms could revolutionize the way we monitor and manage salinization. AI systems could analyze vast amounts of data from remote sensing, soil sampling, and environmental variables to predict areas at risk of salinization and recommend targeted interventions.Challenges and ConsiderationsWhile technological advancements offer promising solutions, it is crucial to acknowledge and address potential challenges and considerations. One significant challenge is the cost and scalability of implementing certain technologies, particularly in resource-limited regions. Developing affordable and accessible solutions should be a priority to ensure widespread adoption and impact.Environmental and ecological impacts must also be carefully evaluated. Any technological intervention should prioritize sustainability and minimize potential negative consequences on the broader ecosystem. Comprehensive environmental impact assessments and long-term monitoring should be conducted to ensure the safety and efficacy of proposed solutions.Furthermore, stakeholder engagement and community involvement are essential for the successful implementation of any technological solution. Local communities, indigenous populations, and grassland managers should be actively involved in the decision-making process, as their traditional knowledge and practices can complement and enhance technological interventions.ConclusionSalinization in grasslands is a complex and pressing issue that requires multifaceted solutions. Technology offers a range of promising approaches, from remote sensing and subsurface drainage systems to phytoremediation and nanotechnology. However, future advancements, such as the development of salt-tolerant crop varieties and the integration of AI and machine learning, hold even greater potential for transformative solutions.As a student passionate about environmental conservation, I am excited about the possibilities that technology presents in mitigating salinization and preserving the integrity of grassland ecosystems. However, it is crucial to address challenges related to cost, scalability, environmental impacts, and stakeholder engagement to ensure the successful and sustainable implementation of these solutions.By embracing technological innovations while considering local contexts and prioritizing sustainability, we can pave the way for a future where salinization is effectively managed, and grasslands can thrive, supporting biodiversity, ecosystem services, and the well-being of communities that depend on these vital landscapes.。
氟苯尼考的功能主治的英文
氟苯尼考的功能主治的英文简介氟苯尼考(Flufeniconazole)是一种广谱菌剂,属于三唑类杀菌剂。
它具有抗真菌活性,并在农业上广泛应用。
本文将介绍氟苯尼考的功能和主治,并提供其对应的英文表达。
功能与主治氟苯尼考作为一种广谱菌剂,具有多种功能和主治,主要包括:1.杀菌作用:氟苯尼考对多种真菌有明显的杀菌作用,可以有效控制农作物病害的发生和传播。
2.防治功能:它可以预防和治疗多种农作物病害,包括叶斑病、锈病、黑穗病等。
3.提高作物产量:氟苯尼考的使用可以显著提高作物产量,改善农作物的质量和品质。
4.增强植物抗逆性:通过应用氟苯尼考,植物的抗逆性可以得到增强,从而提高农作物对环境压力的适应能力。
英文表达以下是氟苯尼考的功能和主治的英文对应表达:1.杀菌作用:Fungicidal activity2.防治功能:Preventive and curative effect3.提高作物产量:Increase crop yield4.增强植物抗逆性:Enhanced plant stress tolerance使用注意事项在使用氟苯尼考时,需要注意以下事项:1.使用剂量:根据具体作物和病害情况,按照产品使用说明进行正确的剂量使用。
2.施用时机:选择适当的施用时机,一般在病害初期或病害预测模型指导下进行施用。
3.施用方法:根据农作物的生长状况和病害特点,选择适当的施用方法,如喷雾、浸种等。
4.安全使用:使用前需仔细阅读产品标签和使用说明,遵守安全使用规定,避免对人体和环境造成危害。
总结氟苯尼考作为一种广谱菌剂,在农业生产中发挥着重要的功能和主治。
通过其抗真菌活性和多种杀菌机制,氟苯尼考能够有效控制农作物病害,并提高作物产量和质量。
同时,使用氟苯尼考还能增强植物的抗逆性,提高对环境压力的适应能力。
需要注意的是,在使用氟苯尼考时应遵循正确的使用方法和安全规定,以确保其有效性和安全性。
以上就是氟苯尼考的功能主治的英文表达和使用注意事项的介绍。
关于蔬菜研究的作文英语
关于蔬菜研究的作文英语Title: Exploring the Fascinating World of Vegetable Research。
Vegetables play a crucial role in our daily lives, providing essential nutrients and contributing to ouroverall health and well-being. Over the years, extensive research has been conducted to understand the various aspects of vegetables, ranging from their nutritional content to their cultivation techniques. In this essay, we will delve into the realm of vegetable research, exploring its significance, recent advancements, and future prospects.First and foremost, vegetable research encompasses a wide array of disciplines, including agriculture, nutrition, biology, and environmental science. Researchers investigate different aspects of vegetables, such as their genetic makeup, physiological processes, and interactions with the environment. By gaining insights into these areas,scientists aim to enhance crop yield, improve nutritionalquality, and develop sustainable farming practices.One of the key focuses of vegetable research is understanding the nutritional composition of various vegetables and their impact on human health. Studies have shown that vegetables are rich sources of vitamins, minerals, antioxidants, and dietary fiber, all of which are essential for maintaining optimal health. Research has also highlighted the role of vegetables in preventing chronic diseases such as heart disease, diabetes, and certain types of cancer. By identifying the specific nutrients and bioactive compounds present in different vegetables, researchers can recommend dietary guidelines to promote better health outcomes.In addition to nutritional studies, vegetable research also encompasses agronomic practices aimed at improving crop productivity and resilience. This includes exploring innovative cultivation techniques, optimizing irrigation and fertilization practices, and developing disease and pest management strategies. With the growing global population and the increasing pressure on agriculturalresources, there is a need to maximize the efficiency of vegetable production while minimizing its environmental impact. Through research, scientists strive to address these challenges and ensure food security for future generations.Advancements in technology have revolutionized thefield of vegetable research, allowing scientists to explore new frontiers and tackle complex challenges. For example, genomic tools enable researchers to unravel the genetic basis of traits such as yield, disease resistance, and nutritional quality in vegetables. This knowledge can then be leveraged to develop improved cultivars throughselective breeding or genetic engineering. Similarly, precision agriculture technologies, such as remote sensing and data analytics, enable farmers to monitor crop health and optimize resource use with unprecedented accuracy. By harnessing these technological advancements, vegetable research continues to push the boundaries of innovation and sustainability.Looking ahead, the future of vegetable research holdsimmense promise and potential. With advances in biotechnology, such as gene editing and synthetic biology, researchers can develop novel crop varieties with enhanced nutritional profiles, improved stress tolerance, and better flavor. Furthermore, interdisciplinary collaborations between scientists from different fields will foster a holistic approach to addressing complex challenges in vegetable production and consumption. By integrating knowledge from genetics, agronomy, food science, and public health, researchers can develop comprehensive solutionsthat promote both human health and environmental sustainability.In conclusion, vegetable research plays a vital role in ensuring food security, promoting human health, and sustaining the environment. From understanding the nutritional composition of vegetables to optimizing cultivation practices, researchers continue to make significant strides in this field. With ongoing advancements in technology and increasing collaboration among scientists, the future of vegetable research looks promising. By harnessing the power of innovation andinterdisciplinary cooperation, we can pave the way for a healthier and more sustainable future for generations to come.。
大豆出苗期耐盐性鉴定方法建立及耐盐种质筛选
作物学报ACTA AGRONOMICA SINICA 2020, 46(1): 1-8 / ISSN 0496-3490; CN 11-1809/S; CODEN TSHPA9E-mail: zwxb301@DOI: 10.3724/SP.J.1006.2020.94062大豆出苗期耐盐性鉴定方法建立及耐盐种质筛选刘谢香常汝镇关荣霞*邱丽娟*中国农业科学院作物科学研究所 / 国家农作物基因资源与遗传改良重大科学工程 / 农业部种质资源利用重点实验室, 北京 100081 摘要: 土壤盐渍化是影响农业生产的重要问题, 筛选耐盐大豆资源对于大豆主产区盐渍化土壤的利用具有重要意义。
以中黄35、中黄39、Williams 82、铁丰8号、Peking和NY27-38为供试材料, 以蛭石为培养基质, 设0、100和150 mmol L-1 NaCl 3个处理, 进行出苗期耐盐性鉴定, 分析与生长相关的6个指标, 旨在明确大豆出苗期耐盐性鉴定指标和评价方法。
结果表明, 150 mmol L-1 NaCl处理显著降低大豆的成苗率、株高、地上部鲜重、根鲜重、地上部干重和根干重, 并且不同材料间差异显著。
基于幼苗生长发育状况的耐盐指数方法与耐盐系数方法对6份种质耐盐性评价结果显著相关。
耐盐指数法对植株无损坏、可省略种植对照, 节约人力和物力, 提高种质鉴定的效率。
因此,以150 mmol L-1 NaCl作为出苗期耐盐鉴定浓度, 以耐盐指数作为大豆出苗期耐盐鉴定评价指标, 鉴定27份大豆资源,获得出苗期高度耐盐大豆(1级) 3份、耐盐大豆(2级) 7份, 其中4份苗期也高度耐盐(1级), 分别为运豆101、郑1311、皖宿1015和铁丰8号。
本研究建立了一种以蛭石为基质, 利用150 mmol L-1 NaCl处理, 以耐盐指数作为评价指标的大豆出苗期耐盐性鉴定评价的简便方法, 并筛选出4份出苗期和苗期均耐盐的大豆, 对耐盐大豆种质资源的高效鉴定和耐盐大豆新品种培育具有重要意义。
盐碱地 英语表达
盐碱地英语表达
盐碱地是一种土地类型,其土壤中含有过多的盐分和碱性物质,导致植物生长的困难。
为了更好地了解这种土地类型,以下是一些关于盐碱地的英语表达:
1. Saline-alkali land: 盐碱地
2. High salinity: 高盐度
3. Alkaline soil: 碱性土壤
4. Salt-affected land: 受盐碱化影响的土地
5. Salinity tolerance: 耐盐性
6. Soil remediation: 土壤修复
7. Soil amendment: 土壤改良
8. Irrigation management: 灌溉管理
9. Crop selection: 作物选择
10. Soil drainage: 土壤排水
以上这些表达可以帮助人们更好地理解盐碱地及其相关的问题。
在研究和处理盐碱地问题时,这些表达也可以帮助人们进行交流和合作。
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DOI:10.1093/jxb/erh003Advanced Access publication 12January,2004FOCUS PAPERImproving crop salt toleranceT.J.Flowers*School of Biological Sciences,University of Sussex,Falmer,Brighton,Sussex BN19QG,UK School of Plant Biology,35Stirling Highway,Crawley,Western Australia 6009,AustraliaReceived 20March 2003;Accepted 3July 2003AbstractSalinity is an ever-present threat to crop yields,especially in countries where irrigation is an essential aid to agriculture.Although the tolerance of saline conditions by plants is variable,crop species are generally intolerant of one-third of the concentration of salts found in seawater.Attempts to improve the salt tolerance of crops through conventional breeding programmes have met with very limited success,due to the complexity of the trait:salt tolerance is complex genetically and physiologically.Tolerance often shows the charac-teristics of a multigenic trait,with quantitative trait loci (QTLs)associated with tolerance identi®ed in barley,citrus,rice,and tomato and with ion trans-port under saline conditions in barley,citrus and rice.Physiologically salt tolerance is also complex,with halophytes and less tolerant plants showing a wide range of adaptations.Attempts to enhance tolerance have involved conventional breeding pro-grammes,the use of in vitro selection,pooling physiological traits,interspeci®c hybridization,using halophytes as alternative crops,the use of marker-aided selection,and the use of transgenic plants.It is surprising that,in spite of the com-plexity of salt tolerance,there are commonly claims in the literature that the transfer of a single or a few genes can increase the tolerance of plants to saline conditions.Evaluation of such claims reveals that,of the 68papers produced between 1993and early 2003,only 19report quan-titative estimates of plant growth.Of these,four papers contain quantitative data on the response of transformants and wild-type of six species with-out and with salinity applied in an appropriate manner.About half of all the papers report dataon experiments conducted under conditions where there is little or no transpiration:such experiments may provide insights into components of tolerance,but are not grounds for claims of enhanced toler-ance at the whole plant level.Whether enhanced tolerance,where properly established,is due to the chance alteration of a factor that is limiting in a complex chain or an effect on signalling remains to be elucidated.After ten years of research using transgenic plants to alter salt tolerance,the value of this approach has yet to be established in the ®eld.Key words:Halophytes,salt tolerance,transgenic plants.Why should we want to improve crop salt tolerance?Earth is a salty planet,with most of its water containing about 30g of sodium chloride per litre.This salt solution has affected,and continues to affect,the land on which crops are,or might be,grown.Although the amount of salt-affected land (about 900Q 106ha)is imprecisely known,its extent is suf®cient to pose a threat to agriculture (Flowers and Yeo,1995;Munns,2002)since most plants,and certainly most crop plants,will not grow in high concen-trations of salt:only halophytes (by de®nition)grow in concentrations of sodium chloride higher than about 400mM.Consequently,salinity is a threat to food supply.Although there is currently food enough for the world population,more than 800million people are chronically undernourished (Conway,1997).Growth of the human population by 50%,from 6.1billion in mid-2001to 9.3billion by 2050(/swp/2001/),means that crop production must increase if food security is to*To whom correspondence should be addressed (Brighton,UK).Fax:+44(0)1273678433.E-mail:t.j.¯owers@ Journal of Experimental Botany ,Vol.55,No.396,ãSociety for Experimental Biology 2004;all rightsreservedbe ensured,especially for those who live on about$1per day.Approximately half of the world's land surface is `perennial desert or drylands'(United Nations Development Programme,see /seed/ unso/pub-htm/dryland-population.pdf).These areas can only be made more productive by irrigation(and irrigation increased by almost one-third between1979and1999, from207to274million hectares;/page/ collections?subset=agriculture).Unfortunately,a strong link with salinization(Ghassemi et al.,1995),throws an immediate question over the sustainability of using irrigation to increase food production and it has been argued elsewhere(Shannon and Noble,1990;Flowers and Yeo,1995)that the primary value of increasing the salt tolerance of crops will be to the sustainability of irrigation. Given the amount by which food production will have to be increased,it seems reasonable to predict that changing the salt tolerance of crops will be an important aspect of plant breeding in the future,if global food production is to be maintained.Historical perspectiveThe need to produce salt-tolerant crops was evident in ancient times(Jacobsen and Adams,1958)and the possible ways to increase tolerance have been extensively rehearsed.Epstein et al.(1980)described technical and biological`®xes'to the problem of salinity.The`bio-logical®x'was founded on salt tolerance having a genetic basis,for which the evidence(Epstein et al.,1980)was the existence of a salt-tolerant¯ora(halophytes)and differ-ences in salt tolerance between genotypes within species. Varietal differences in salt tolerance have been known since the1930s(Epstein,1977)and intraspeci®c selection for salt tolerance was,by the1980s,shown to be possible with rice(Akbar and Yabuno,1977)and barley(Epstein et al.,1980).In spite of early promise,the`biological®x'has been slow in arriving.In1993,Flowers and Yeo (1995)reviewed the evidence for the paucity of new salt-tolerant cultivars and concluded that the number was likely to be fewer than30.Since1993,there have been just three registrations of salt-resistant cultivars in Crop Science(Owen et al.,1994;Al-Doss and Smith, 1998;Dierig et al.,2001)and one patent registered in the US(Dobrenz,1999);one other patent claims a method to increase tolerance in cereals by the incorp-oration of a late embryogenesis abundant(LEA) protein(Wu and Ho,1996).Flowers and Yeo(1995) concluded that,although salinity might be of profound local importance,it had not yet had suf®cient impact on regional agricultural production to warrant the effort necessary to produce new salt-tolerant cultivars.The complexity of salt toleranceAssessment of toleranceUltimately,salt tolerance of crops is tested as yield from farmers'®elds.However,evaluating®eld performance under saline conditions is notoriously dif®cult because of the variability of salinity within®elds(Richards,1983; Shannon and Noble,1990;Daniells et al.,2001)and the enormous potential for interactions with other environ-mental factors,ranging from gaseous pollutants,soil fertility and drainage to temperature,light¯ux density and transpirational water loss.Consequently,prediction of `®eld'performance is commonly carried out in trial plots, or using a solution-based method where the salinity of the medium can be readily adjusted to required values(Maas and Hoffmann,1977;Francois and Maas,1994).The latter often precludes measuring yield through lack of space and estimates of tolerance obtained from such experiments may not always be borne out by the response of plants in the®eld(Rowland et al.,1989;Daniells et al.,2001). Evaluating tolerance is made more complex by variation in sensitivity to salt during the life cycle.For example,it has long been known that grain yield in rice is much more depressed by salt than is vegetative growth(Khatun and Flowers,1995):germination is relatively salt resistant.In tomato,tolerance at germination is not correlated with the ability to grow under salt stress:both are controlled by different mechanisms(Foolad and Lin,1997),although it is possible to®nd genotypes with similar tolerance at germination and during vegetative growth(Foolad and Chen,1999).Genetics of salt tolerancePerhaps the®rst attempt to evaluate the inheritance of salt tolerance was made by Lyon(1941).An interspeci®c cross of Lycopersicon esculentum and L.pimpinellifolium showed fruit yield of the hybrid was more sensitive to increasing salt(sodium sulphate)than that of either parent. Other crosses of wild and cultivated tomato also suggested a complex genetics.Heterosis was apparent under saline (NaCl)conditions in the elongation of stems in hybrids of L.esculentum produced with three wild species (L.cheesmanii,L.peruvianum,and L.pennellii =Solanum pennellii)by Tal and Shannon(1983).Stem elongation was a dominant trait in hybrids with S.pennellii, but not with L.cheesmanii as the parent.Total dry matter production of another F1hybrid,between L.esculentum and L.pennellii,showed hybrid vigour(Saranga et al., 1991)under saline conditions.Analysis of other species has also suggested that the genetics of salt tolerance is complex.In rice,sterility,an important factor in yield under saline conditions,is determined by at least three genes(Akbar et al.,1972;Akbar and Yabuno,1977).In diallel analysis the effects of salinity on the seedling stage and on sterility308Flowerssuggested both additive and dominance effects,some with high heritability²(Moeljopawiro and Ikehashi,1981; Akbar et al.,1986).Evidence of dominance of tolerance is also seen with pigenopea(Cajanus cajan),where a cross with Atylosia albicans(one of the most salt-tolerant relatives of pigeonpea)produced intergeneric hybrids that behaved as the wild parent,indicating dry weight produc-tion was determined by a dominant genetic factor (Subbarao et al.,1990).There is also evidence of dominance in the salt tolerance of sorghum.Diallel analysis,based on assessing tolerance to NaCl as relative root length in salt-treated as compared with control plants, showed that there were both additive and dominance effects of NaCl(Azhar and McNeilly,1988).These examples suggest that while the assessment of tolerance is complicated by changes occurring during the ontogeny of a plant and may be technically dif®cult under®eld conditions,there is evidence of a genetically complex trait (Shannon,1985),showing heterosis,dominance and additive effects.Physiological complexityAs well as the genetic evidence,there is physiological evidence to support the view that salt tolerance is a complex trait.Halophytes show a wide range of adapta-tions from the morphological to the biochemical(Flowers et al.,1986;Leach et al.,1990;Flowers and Dalmond, 1992;Glenn et al.,1999;Tester and Davenport,2003), adaptations that include the ability to remove salt through glandular activity.Although control of ion uptake is exercized at the root,the ability to secrete ions has evolved into a successful strategy for salt tolerance.Some(but by no means all)halophytes utilize salt-secreting glands to remove excess ions from their leaves(Thomson et al., 1988),reducing the need for very tight balancing of ion accumulation and growth(Flowers and Yeo,1988).Within less tolerant species,intraspeci®c variation in tolerance is also associated with variation in a wide variety of physiological traits(Yeo et al.,1990;Cuartero et al., 1992;Foolad,1997;Wahid et al.,1997;Tozlu et al., 1999a,b).Perhaps the best investigated of the traits relating to salt tolerance are those associated with the ion contents of plants grown in the presence of salts.Although there was an early hint that an ability to exclude chloride in Glycine showed simple Mendelian inheritance(Abel,1969),there proved to be complications introduced by interactions with phosphate(Grattan and Maas,1984,1988).In vine, chloride exclusion appeared to be inherited either as a qualitative or a quantitative trait,depending on the parents (Sykes,1992),while in inter-speci®c crosses of Citrus, chloride accumulation showed continuous variation amongst progeny suggesting that this is a polygenic trait, although with a strong heritable basis(see Sykes,1992).In Trifolium repens,heritability of chloride accumulation, estimated from parent±progeny regressions,is only mod-erate(0.24±0.37,Rogers et al.,1997),but suf®cient for net accumulation of chloride to be a useful tool in the selection of salt-tolerant genotypes.For the other dominant ion in saline soils,sodium,there has been considerably more research,often associated with an estimation of the other major monovalent cation in plants,potassium.The tolerance of plants to sodium chloride is commonly,but not uniquely,related to the concentration of sodium in the shoot.For tomato,Foolad (1997)reported,from a parent±progeny comparison,that sodium accumulation under saline conditions was under genetic control,with more than90%of the genetic variation attributable to additive effects:dominance had little in¯uence.Analysis of sodium and potassium accu-mulation between F n and F n+1families of rice growing under saline conditions showed that net accumulation of both sodium and potassium to be heritable(with narrow sense heritabilities of between0.4and0.5),although shoot sodium and potassium concentrations were unrelated, suggesting that the pathways for net accumulation of sodium and potassium in rice are separate(Garcia et al., 1997a).A high degree of heterosis and large environmen-tal effects on Na/K ratios(Gregorio and Senadhira,1993) are characteristic of this aspect of salt tolerance in rice behaving as a quantitative trait.The means by which sodium enters plants is still poorly understood.At low external concentrations,potassium may enter roots through K carriers,while at higher concentrations,non-selective cation channels(Demidchik et al.,2002)are possible means of transport.Channels that are activated when the transmembrane potential is hyperpolarized are highly selective for K;other channels, activated when the membrane potential is depolarized,are less selective and could be one means by which sodium enters cells(Maser et al.,2002b).Sodium can also enter via KUP/HAK/KT potassium transporters,cyclic-nucleo-tide-gated channels,glutamate-activated channels,LCT transporters,and HKT transporters,although the relative roles of each seem likely to vary across species(Maser et al.,2002b;Tester and Davenport,2003).HKT1plays a role in net Na accumulation into wheat(Laurie et al.,2002) and into the distribution of ions between roots and shoots of arabidopsis(Maser et al.,2002a).The rice OsHKT1is down-regulated after osmotic shock(with150mM NaCl) of plants growing in a low(micromolar)potassium²Most estimates of the heritability of complex traits are made from varianceratios.Where genetic and phenotypic variability are estimated simply fromcomparisons of varietal performance,then broad sense heritability isobtained from the ratio of the variance within genotypes to the sum of thegenetic,environmental and genetic Q environmental variances.In experi-ments where a trait is compared in parents and progeny,it is possible to splitthe genetic variance into additive and dominance effects:this allows thecalculation of narrow sense heritability(Simmonds,1979).Improving crop salt tolerance309concentration and more so in a vigorous tolerant landrace than in a sensitive dwarfed variety(Golldack et al.,2002). Much has been written about the importance of the ability of plants to discriminate between sodium and potassium,for which a simple index,the K/Na ratio,can be determined for plants and plant parts.In bread wheat,the discrimination between potassium and sodium in their transport to the shoot,manifested as K/Na ratio in shoot tissue,is apparently determined by a locus described as Kna1and con®rmed by RFLP analysis to be completely linked to®ve markers on the long arm of Chromosome4D (Gorham et al.,1997).That the ratio of K to Na in a plant is determined at a single locus,if proved true,is surprising, given the number of proteins that might contribute to Na and K transport from root to shoot,unless they,or their control,are clustered in a particular chromosomal location. The K/Na discrimination trait can be transferred from durum to bread wheat(Dvorak et al.,1994).However, control of the K/Na discrimination itself cannot be con®ned to the D genome,as in durum wheat(Triticum turgidum L.ssp durum)discrimination equivalent to that found in the hexaploid bread wheat has been found in lines which contain no D genome(Munns et al.,1999).Quantitative trait lociThere is,then,considerable evidence to support the view that salt tolerance and its sub-traits might be determined by multiple gene loci.In an intergeneric cross of tomato, quantitative trait loci(QTL)were found associated with fruit yield in plants growing under saline conditions(Breto et al.,1994),although some of the QTL identi®ed were later shown to be dependent on the parentage of the cross (Monforte et al.,1997a).An important conclusion stem-ming from this work was that QTL are treatment-sensitive. Some QTL associated with aspects of fruit yield were found regardless of whether the plants were grown with or without salt;others were detected only under saline or under non-saline conditions(Monforte et al.,1997b). Other crosses have also identi®ed both stress-(salt and cold)speci®c and stress-non-speci®c QTL:the stress-non-speci®c QTL generally exhibited larger individual effects and accounted for a greater portion of the total phenotypic variation under each condition than the stress-speci®c QTL (Foolad et al.,1999).As for the QTL identi®ed for fruit yield,QTL associated with germination depend upon the conditions under which germination is assessed(Foolad et al.,1999).A similar situation exists for citrus,where about half of the potential QTL identi®ed depended on the presence or absence of salinity(Tozlu et al.,1999a),and in rice(Gong et al.,1999,2001)where less than10%of the QTL were detected both in the presence and absence of salt.Clearly,the major determinants of yield vary with the environmental conditions and quantitative traits typically exhibit a large environment Q genotype interaction.The use of tomato has also been important in establish-ing that QTL associated with tolerance vary with the stage of plant development.The QTL associated with tolerance at germination(Foolad et al.,1997,1998)and vegetative growth(Foolad and Chen,1999;Foolad et al.,2001)differ (Foolad,1999).Such differences are not restricted to tomato and have been demonstrated in arabidopsis (Quesada et al.,2002)and cereals;both barley(Mano and Takeda,1997)and rice(Prasad et al.,2000).QTL associated with aspects of ion transport have also been reported in citrus(Tozlu et al.,1999b)and in rice(Koyama et al.,2001).ConclusionsThere is suf®cient evidence to be con®dent that salt tolerance is a multigenic trait.Research on the physiology of salt tolerance suggests that the overall trait is determined by a number of sub-traits any of which might,in turn,be determined by any number of genes. These sub-traits generally include an ability to minimize the net accumulation of sodium and/or chloride ions and to select potassium from a background of high sodium concentration.Approaches to enhancing toleranceFlowers and Yeo(1995)suggested®ve possible ways, which were appropriate at that time,to develop salt-tolerant crops:(1)develop halophytes as alternative crops;(2)use interspeci®c hybridization to raise the tolerance of current crops;(3)use the variation already present in existing crops;(4)generate variation within existing crops by using recurrent selection,mutagenesis or tissue culture, and(5)breed for yield rather than tolerance.These all remain possible solutions to the problem.Although conventional forms of mutagenesis have not,in general, delivered salt-tolerant genotypes(Flowers and Yeo,1995; but see Tester and Davenport,2003),mutagenesis has unearthed a number of salt-sensitive types(Borsani et al., 2002;Zhu,2002).Bohnert and Jensen(1996)claimed that an important approach had been missed by Flowers and Yeo:they wrote`tolerance breeding must be accompanied by transformation';and that`successful releases of tolerant crops will require large-scale"metabolic engineering" which must include the transfer of many genes'.While such an approach was not feasible in the early1990s (Flowers and Yeo,1996);this approach is now being widely advocated.Some13species(Table1A)have been transformed with nearly40genes in experiments reported between1993and2003(Table1B).The majority of experiments have used rice,tobacco and arabidopsis; transformations involving the synthesis of compatible solutes have been more popular than any other,with those involving glycine betaine the most commonly performed(Table1A).There is an increasing number of310Flowersclaims in this literature that overall tolerance can be manipulated through alteration in the activity of one or two genes(see below),which was not something claimed by Bohnert and Jensen(1996).For a trait as complex as salt tolerance this seems intuitively unlikely.The fundamental issue to be resolved is the importance of individual components or sub-traits of salt tolerance and whether the manipulation of individual or of many genes is required to alter complex traits.If altering a single gene can alter tolerance,this suggests either that changing the concen-tration of a few key components has a substantial effect on a wide range of other processes or that salt tolerance is not as complex as it appears or that a key limit to tolerance might be altered in any given species(or genotype). Substantiating,or otherwise,claims that tolerance is altered by transformation is clearly of major importance both for our understanding of complex traits and for the practicalities of their manipulation.Table1.Species and genes used in the transformation of plants where authors claimed enhancement of salt tolerance(A)Species No.of experiments reported Arabidopsis thaliana14Brassica napus and B.juncea3Citrus(Carrizo citrange)1Cucumis melo(melon)2Diospyros kaki(Japanese persimmon)1Lycopersicon esculentum(tomato)5Medicago sativa(alfalfa)2Nicotiana tabaccum(tobacco)19Oryza sativa(rice)17Solanum melongena(eggplant)1Solanum tuberosum(potato)2Triticum aestivum(wheat)(B)Transformed for No.of experiments Apoplastic invertase,Apo-Inv1Arginine decarboxylase,ADC1Betaine aldehyde dehydrogenase,BADH;betB,choline dehydrogenase(CDH);15choline oxidase,codA(glycinebetaine)Ca2+-dependent protein kinase,CDPK1Ca/H antiporter,CAX11Calcium-binding protein,EhCaBP1Calicneurin;protein kinase,CaN1Ca protein kinase,OsCDPK71Glutathione S-transferase,GST and glutathione peroxidase,GPX1Glyceraldehyde-3-phosphate dehydrogenase,GPD1Glycogen-synthase kinase-3,AtGSK11Glutamine synthetase,GS21Heat shock protein,DnaK/HSP701High-af®nity potassium transporter,*HKT1a3Isopentenyl transferase,ipt(increased cytokinin)1Late embryo abundant protein,HVA1(a LEA)2Mannitol1-phosphate dehydrogenase,mt1D(mannitol)6Myo-inositol O-methyltransferase,IMT1(ononitol)1Omega-3fatty acid desaturase,fad7(fatty acid processing)1Osmotin-like protein1Proline dehydrogenase;Delta(1)-pyrroline-5-carboxylate synthetase(proline)4Proline transporter,AhProT11Proton sodium exchanger,*HNX1a4Putative transcription factor,Al®n12Rare Cold Inducible gene3,RCI31Rice Hal2like,RHL1S-adenosylmethionine decarboxylase,SAMDC(spermine,spermidine)1Serine/threonine kinase,AT-DBF21Sorbitol-6-phosphate dehydrogenase,SPD(sorbitol)1SR-like,putative splicing protein1Transcription factors,DREB1A;AhDREB12Trehalose-6-phosphate synthase/phosphatase,TPSP(trehalose)1Yeast halotolerance gene,Hal23Yeast halotolerance gene,Hal12Yeast mitochondrial superoxide dismutase,Mn-SOD1Vacuolar H+-pyrophosphatase,AVP11a Asterisk indicates a speci®c pre®x,e.g.At.Improving crop salt tolerance311Genetic engineering of salt tolerance:evaluation of successThe evaluation of transgenic material requires some comment.The material to be tested should be genetically stable(it has been suggested that it should be in its fourth or®fth generation by Bajaj et al.,1999)and a comparison of as many transformed lines as possible made with the performance of the parental(wild-type)line under saline and non-saline conditions(Table2).It is important to know whether or not the overall growth of the transgenic plant has been affected,as vigour itself is an important determinant of salt tolerance.For crops,claims of enhanced tolerance should be made on the basis of yield. Unfortunately,there were no such reports by1999(Bajaj et al.,1999)and the situation had changed little by early 2003.Given the paucity of data on crop yield(just®ve reports of estimates of crop yields,Guo et al.,1997;Wang et al.,2000;Zhang and Blumwald,2001;Zhang et al., 2001;Li et al.,2002),the success,or otherwise,of a transformation in altering salt tolerance has generally to be evaluated against the nature of the data that is presented. Those claims based on quantitative estimates of the growth of fourth or®fth generation transgenic lines should be seen as stronger than claims based upon photographic evidence of the performance of plants of the primary transformants grown in salt alone.In the following analysis,papers are allocated to one of®ve categories(Table3).Only those data relating to the growth of plants under conditions in which transpiration occurs have been evaluated:it is transpiration that transports ions to the shoots,where their presence brings about injury and death.Photographs of plants in culture medium are unconvincing as evidence for a successful alteration of crop yield.Quantitative measures of growth are required for plants grown in the presence and absence of salt:the ability to germinate in salt is,in general,a poor indicator of performance in the®eld.It is also important that salt be added in such a way that it is not the effect of water or osmotic stress that is being evaluated and this generally requires an increase of salt concentration of50mM or less per day and determination of the consequences days or weeks later,depending on the salt tolerance of the species(Munns,1993,2002). Analysis of publications to date shows that of the68 reports produced between1993and early2003(Table3; see also supplementary data online)only19describe quantitative estimates of plant growth.Of these,four papers(Table4)contain quantitative data on the response of transformants and wild type of six species without and with salinity applied in an appropriate manner.About half of all the papers(35,Table3and supplementary data online)report data on experiments conducted under conditions where there is little or no transpiration:such experiments may provide insights into components of tolerance,but are not grounds for claims of enhanced tolerance at the whole plant levelÐin such a system,the fern Ceratopteris,where single gene mutants alter the salt tolerance in the gametophytic generation(Warne et al., 1995)might be a useful genetic model.Those experiments where the effects of transformation were determined in saline and non-saline soil or hydro-ponic culture suggest that real changes in salt tolerance can be effected,but generally not without consequences for the growth that occurs in the absence of salt.Over-expression of the gene Al®n1in alfalfa increased its salt tolerance and promoted root growth and shoot growth(Table4A),under normal and saline conditions,producing larger plants than the wild type(Winicov,2000).Al®n1is a putative transcription factor,but its mode of action in altering overall salt tolerance is still unclear.Adding to the uncertainty of how some genes affect overall tolerance is the consequence of transforming tomato with the yeast gene HAL1.HAL1alters the salt tolerance of tomato (Gisbert et al.,2000)and increases the K/Na ratio in transgenic plants.However,these transgenic plants,when grown in the absence of salt,had half the shoot dry weight of the wild type(Table4A).A similar effect of an introduced gene on growth is also seen following the transformation of tobacco with mannitol-1-phosphate dehydrogenase.Here mannitol that accumulated as a consequence of the transformation made only a small contribution to the osmotic potential of the transformedTable2.Possible combinations for experiments reporting the evaluation of transgenic plantsColumn1lists experimental sites and column2the parameters that might be evaluatedÐyielding six possible combinations.In each combination,either quantitative or qualitative date might be reported on transformant and/or wild type,ideally under saline and non-saline conditions,but often only the transformant under saline conditions.Ideally,an experiment evaluating the effects of a transformation would report quantitative data on yield of®eld grown plants of both wild-type and transformant lines in the presence or absence of salinity. Experimental location Parameter evaluated Data Material tested Treatments12345Field Yield Quantitative Transformant lines Plus salinity Greenhouse or other controlled environment Growth Qualitative Wild type Minus salinity`In vitro'(including germination)Plus and minus salinity 312Flowers。