Alleviation of drought stress of marigold plants by using arbuscular mycorrhizal fungi

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解决干旱问题英文作文

解决干旱问题英文作文

解决干旱问题英文作文英文:As someone who has experienced the effects of drought firsthand, I understand the importance of finding solutions to this issue. Drought can lead to crop failure, water shortages, and even famine, so it is crucial that we address it as soon as possible.One solution is to invest in water conservation and management. This can include using drip irrigation systems, which deliver water directly to the roots of plants, reducing water waste. We can also implement rainwater harvesting systems to collect and store rainwater for later use. Additionally, we can encourage individuals to conserve water by fixing leaks, taking shorter showers, and using water-efficient appliances.Another solution is to promote sustainable agriculture practices. This can involve using drought-resistant cropsthat require less water, practicing crop rotation to maintain soil health, and reducing the use of chemical fertilizers and pesticides that can harm the environment. By promoting sustainable agriculture, we can not only conserve water but also ensure food security for future generations.中文:作为一个亲身经历过干旱影响的人,我理解解决这个问题的重要性。

顾建光:《公共管理英语》(修订版)--词汇汇总

顾建光:《公共管理英语》(修订版)--词汇汇总

Lesson 1citizen 公民 municipal government 市政府 administrative affairs 行政事务transparency 透明度 accomplishment 成就,成绩 financial budget 财政预算implementation 实施,实行 obligation 义务,责任 lag behind 落后于bulletin 公告,公报 natural disaster 自然灾害 to grant 授予,认可license 许可证 booth 货摊,小摊 civil affairs 国内事务domicile registration 居民登记 matrimonial registration 婚姻注册e-government 电子政府 to facilitate 使更容易 regulation 规章制度,条例healthcare 医疗卫生 Handling Affairs Online 在线事务办理to retain 保留,保存Lesson 2bureaucracy 官僚机构,官僚作风 bureaucratic constrain 官僚式约束to inhibit 抑制,约束 citizenry 平民,公民 to espouse 信奉cynic 愤世嫉俗者 to render 表现,使成为 quasi-market 准市场to streamline 使简化,使有效率,使现代化 slacken off 放慢,放缓in conjunction with 与......结合起来 status quo 现状reward and appraisal system 奖励与褒扬制度 to reshuffle 改组commitment 承诺Lesson 3public administration 公共管理,公共行政decentralization 分权化liberalization 自由化 thrust 冲击 centralization 权力集中化diagnosis 诊断,判断 impetus 推动力,刺激 permanent tension 长期的压力revenue 财政收入 revival 复兴,恢复 consolidation 联合,统一autonomy 自治,自治权 infrastructure 基础设施 jurisdiction 司法权,裁判权innovation 创新,革新 responsiveness 回应 interdependence 互相依赖remit 汇出 at odds 争议,争吵 local authority 地方政府central authority 中央政府 ceiling 上限,天花板 performance 绩效,成就emergence 出现 statute 条例,法令Lesson 4private sector 私营部门,民营部门 to generate 产生,造成judicial services 法律服务 know-how 技术秘诀 regulation 管制oversight 疏忽,失察 entrepreneur 企业家gross national income〔GNI〕国民总收入Euromoney 欧洲货币creditworthiness 信贷价值public sector 公共部门vibrant 充满活力的,活跃的 to levy 征税 progressivity 进步 incentive 动机monopoly 垄断 budget 预算 accessibility 可达性,可获得性affordability 可承担,可负担性 stark 完全的,巨大的Lesson 5community 社区 interpersonal 人与人之间的 predisposition 倾向to embody 使具体化,具体表现 indelible 不可或缺的,永恒的to exile 放逐,流散 to transcend 超越 static 静止的,静态的heritage 遗产,继承物Lesson 6performance management 绩效管理to forge 打造,锤炼diagnostic 诊断的integrative 综合的,一体化的 holistic 总体的,全部的 mission 使命unitarist 一元论的 a logical progression 一种逻辑级数performance appraisal 绩效评估 diagnosis 诊断Lesson 7indicator 指标 in aggregate 总起来看,总起来说system of national accounts 国民账户体系 statistics 统计,统计数据currency 流通货币 gross national income〔GNI〕国民总收入unincorporated business 综合经营的商业 multiple exchange rate 多重汇率Lesson 8disparity 不同,差距 coastal 沿海的 interior 内陆的financial sector 经济部门 surge 波动,汹涌 drought 干旱housing mortgage loan 住宅抵押贷款 disposable income 税后收入,可支配收入to trigger 引发,引起 state-owned enterprises 国有企业fiscal revenue 财政收入expenditure 支出,花费allowance 津贴,补助extra-budgetary funds 预算外资金 unauthorized spending 未授权的花费treasury bond 国库券 stock market 股票市场 A-share A股Indices〔index的复数〕指标,指示物 quota 配额 to rebound 反弹tandem 纵列的 consecutive fiscal stimulus 连续的财政鼓励 rebate rate 折扣率aggravate deflationary 加重通货紧缩 phytosanitary 植物检疫的,控制植物病害的Lesson 9well-off 小康的,富裕的 incomprehensive X围有限的 to shake off 摆脱,甩掉to illustrate 例示,说明 multiplication scenario 乘法情境division scenario 除法情境 to conform to the tide of the times 符合时代潮流to endeavor to foster 努力培育 household contract system 家庭联产承包责任制initiative 进取性 to usher in 引进 wrestling 对抗,斗争resource shortage 资源短缺 positive factor 积极因素,有利因素 hegemony 霸权unswervingly boost 坚定不移地推进Lesson 10recipient 接受者 foreign direct investment〔FDI〕外商直接投资momentum 动力,势头 be attributed to 归因于,由于......引起的to lure 吸引,诱惑 conglomerates 联合企业Build-Operate-Transfer model 建设-经营-移交模式〔BOT模式〕securities 有价证券the Global Venture Investor Association 国际风险投资者协会transaction 交易,业务Lesson 11scar 创伤,伤痕 premise 前提,基础 to be embedded in 深植入......,嵌入maldistribution 分配不当 change agents 变革者 ecosystem 生态系统destiny 命运 rational 理性的,合理的 to infuse 注入,灌输integrity 正直,诚实 disguised 伪装的 dysfunctional 功能不良的,功能紊乱的paternalism 家长政治 social betterment 社会改良Lesson 12battered 憔悴的,消瘦的 hospice 收容所social production organization 社会生产组织community development corporations〔CDCs〕社区发展合作组织 empowerment 授权to rekindle 重新燃起,使复苏 to monitor 检测,监督appropriateness 适当,适合Lesson 13unprecedented 史无前例的 to trigger 引发,引起 demographic 人口统计学的fertility 人口出生率 gross domestic product〔GDP〕国民生产总值enhancing security 提高保障水平 household income 家庭收入impoverishing effect 贫困效应 vulnerability 弱点 economic shock 经济冲击human capital 人力资本 enrollment 入学 public sector 公共部门immunization 预防,免疫 sanitation 卫生,卫生设施 public health 公共健康Lesson 14personnel policy 人事政策 personnel manual 人事手册governing board 政府公告 verbal 口头上的 memo 备忘录 variation 差别,差距specificity 特征,特性 to surf 冲浪,浏览〔网页〕 sexual harassment 性骚扰 Court 美国最高法院 to codify 整理,系统化,编成法典overwhelming 至关重要的,势不可当的 timeframe 时间表,进度表periodic review of policies 对政策的定期评估Lesson 15HRD〔human resource development〕人力资源开发 professional 专业人员,行家alien 完全不同的,相异的 assignment 指派,分配,委任 talent 才干,才能consultant 顾问,咨询者 clue 线索 human resource 人力资源physical resource 物力资源 financial resource 财力资源liquid asset 流动资产 liabilities 债务,负债 debt 债务 to hire 雇用to relocate 重组,重新部署 intangible 无形的 to manifest 表明,证明performance improvement 业绩提高,业绩改进Lesson 16to diversify 使多样化public ownership 公有制productivity 生产力malpractice 玩忽职守 reorganization 重组 merger 合并 to lease 批租to contract 制定合同,签订契约 scale 规模,X围 shareholding 股权asset 资产,财产 limited liability company mainstay 支柱to propel 推进 personnel arrangement 人事安排 income distribution 收入分配to embody 实现,体现,使具体化 to be conducive to 对......有帮助,有助于ensure preservation 保值 appreciation 升值 joint-stock 合资clear-cut equity structure 清晰的资产结构 equity transfer 资产转移stagnant 呆滞的 ambiguous interests 模糊的利益 supervision 监督restraint 限制Lesson 17cultivated land 可耕地 coinciding approximately with 大致与......相同arable area 可用于耕作的地域 surplus labor 剩余劳动力 to thrive 繁荣发展vitality 生机,活力 to outstrip 超过,超越 prominent 突出的,显眼的to omit 忽视,忽略 off-payroll 额外收入,隐形收入 to impede 妨碍lay-off 下岗,失业 hukou 户口 to tighten 加强,加紧excessive 过度的,过分的 social security 社会保障Lesson 18pack of 一群,一批 severe acute respiratory syndrome 严重急性呼吸综合症sign 迹象,征兆 capital influx 资本流入 giant 巨头〔本课最后一个单词〕investment liberalization 投资自由化 preferential policies 优惠政策banking 银行业 insurance 保险 wholesale 批发 retail 零售apparatus 仪器,设备 hotspot 热点,焦点 tariff 关税transnational mergers and acquisitions〔TMA〕跨国兼并收购 to plummet 暴跌intermediary agencies 中介机构 to promulgate 公布,颁布solely foreign-funded 外商独资的 joint ventures 合资企业cooperative corporation 合作企业 transnational corporation 跨国公司market-oriented 以市场为导向的 to radiate 辐射,扩散 to cancel 取消Lesson 19transformation 转型,转变 well-off 小康的,富裕的 promise 承诺,许诺to quadruple 增长三倍,达到四倍量 proficient 成熟的,精通的industrialization 工业化 complementarity 互补 to marginalize 使处于边缘economic aggregate 经济总量 integration 一体化,整合 euro zone 欧元区sluggish 缓慢的,迟缓的 superiority 杰出,优越 elasticity 弹性structural adjustment 结构调整 per-capita GDP 人均国内生产总值economic entity 经济体 annual growth rate 年增长率Lesson 20to cluster 集聚,丛生,类聚 proximate 最近的 tannery 制革厂quantifiable 可以计量的 spillover 溢出 metropolitan area 都市区economies of scale 规模经济 spatial configuration 空间结构agglomeration economies 集聚经济Lesson 21measure 量度标准 consumption 消费 to disaggregate 分解 literature 文献gender 性别 imputation 归咎 well-being 康乐,福利 to pursue 追求,追赶WHO〔World Health Organization〕世界卫生组织Lesson 22linear 线的,线性的 lateral 旁边的,侧面的 dome 圆顶 node 交点,交叉点foci 〔focus的复数〕 epitome 梗概,摘要 to partake 分担,分享,参与junction 连接,接合Lesson 23to stimulate 刺激 inter alia 在其他因素中的 sustainable manner 可持续的方式exponentially 指数的 high fertility 高生育率 high mortality 高死亡率vector 遗传媒介 prenatal 出生前的,天生的 maternal 母亲的deficiency 缺陷,缺乏environmental 环境的degradation 恶化,退化indigenous 当地的,本土的domain 领域poverty alleviation 缓解贫困reduction of poverty 贫困程度的降低 quality of life 生活质量client 客户,委托人 lending operation 借贷操作 public policy 公共政策facet 方面Lesson 24indicator 指标 to hamper 妨碍,限制 shrinking 收缩的,减少的biodiversity 生物多样性timber 木材,木料mammal species 哺乳类动物terrestrial 陆地的 aquatic 水生的,水栖的 scarcity 匮乏,短缺millennium 一千年 carbon dioxide 二氧化碳 anthropogenic 人类造成的hazard 冒险,危险 stock 贮备 emission 释放,散发。

解决干旱问题英文作文

解决干旱问题英文作文

解决干旱问题英文作文英文:As a resident of a region that has been affected by drought, I understand the importance of finding solutions to this problem. Here are some ways we can address the issue of drought:1. Water conservation: We can reduce our water usage by taking shorter showers, fixing leaks, and using water-efficient appliances. This will help us conserve water and reduce our overall demand for it.2. Rainwater harvesting: We can collect rainwater and use it for non-potable purposes such as watering plants, flushing toilets, and cleaning. This will help us reduce our reliance on groundwater and surface water.3. Desalination: We can use desalination technology to extract salt and other minerals from seawater, making itsafe for human consumption. This will help us increase our water supply and reduce our dependence on freshwater sources.4. Crop rotation: Farmers can rotate their crops to reduce soil erosion and improve soil fertility. This will help them conserve water and increase crop yields.5. Drought-resistant crops: Farmers can grow crops that are adapted to dry conditions and require less water. This will help them maintain their livelihoods even during periods of drought.中文:作为一个居住在受干旱影响地区的居民,我理解找到解决这个问题的重要性。

干旱胁迫对中粒种咖啡幼苗膜脂过氧化_抗氧化酶活性和渗透调节物质含量的影响

干旱胁迫对中粒种咖啡幼苗膜脂过氧化_抗氧化酶活性和渗透调节物质含量的影响

水分亏缺是影响咖啡生产的主要环境胁迫因子[1]。

干旱不仅影响咖啡的生长发育,还会造成咖啡的大幅度减产及品质下降,给生产带来重大损失。

据报道,2010年4月下旬,由于严重干旱,有近1.60万hm 2的咖啡树受害,约占云南当年咖啡种植面积的60%,造成的经济损失近6亿元[2]。

冬春干旱和热带作物学报2014,35(5):944-949Chinese Journal of Tropical Crops收稿日期2013-11-06修回日期2014-01-09作者简介杨华庚(1966年—),男,硕士,副教授;研究方向:热带作物栽培与生理生态。

E-mail :hg-yang@ 。

干旱胁迫对中粒种咖啡幼苗膜脂过氧化、抗氧化酶活性和渗透调节物质含量的影响杨华庚1,颜速亮1,陈慧娟1,邓志声21海南大学农学院,海南海口5702282中国热带农业科学院科技信息研究所,海南儋州571737摘要以苗龄约8个月的中粒种咖啡袋育苗为材料,测定3种干旱胁迫强度下咖啡幼苗叶片的生理指标变化,旨在了解其对干旱胁迫的生理响应。

结果表明:在轻度干旱胁迫下(土壤相对含水量为55%~60%),与对照相比,中粒种咖啡幼苗叶片的可溶性蛋白、可溶性糖、脯氨酸含量、超氧化物歧化酶(SOD )、过氧化物酶(POD )、过氧化氢酶(CAT )活性极显著增加,而丙二醛(MDA )含量和相对电导率没有显著变化。

但在中度干旱或重度干旱胁迫下(土壤相对含水量为40%~45%或25%~30%),可溶性蛋白含量、SOD 、POD 、CAT 活性显著或极显著减少,而可溶性糖、脯氨酸的积累减缓,MDA 含量和相对电导率迅速上升。

在适度干旱胁迫下,中粒种咖啡幼苗可通过提高抗氧化酶活性和渗透调节能力来增强其对干旱胁迫的耐性。

关键词中粒种咖啡;干旱胁迫;抗氧化作用;渗透调节;膜脂过氧化;质膜透性中图分类号S571.2文献标识码AEffects of Drought Stress on Lipid Peroxidation,AntioxidantEnzyme Activities and Osmolyte Content in Leaves of Coffea canephora SeedlingsYANG Huageng 1,YAN Suliang 1,CHEN Huijuan 1,DENG Zhisheng 21College of Agronomy,Hainan University,Haikou,Hainan 570228,China 2Institute of Information and Technology,Chinese Academy of Tropical Agricultural Sciences,Danzhou,Hainan 571737,ChinaAbstract Coffea canephora seedlings were used for the experiment at the age of about 8months.Three levels ofdrought stress were applied in the present experiment,and the physiological indices of coffee leaves were measured to understand the physiological responses to drought stress.Experimental results showed that when coffee seedlings were exposed to mild drought stress (relative soil water content of 55%to 60%),compared with the control group,soluble protein,soluble sugar and proline contents,SOD,POD and CAT activities increased significantly,while MDA contents and relative electrical conductivity had no significant change.But under moderate or severe drought stress (relative soil water content of 40%to 45%or 25%to 30%),soluble protein content,SOD,POD and CAT activities reduced significantly,while soluble sugar and proline accumulated relatively slowly,and MDA content,relative electrical conductivity increase rapidly.These results show that Coffea canephora seedlings have improved drought tolerance by increasing antioxidant enzyme activities and osmoregulation ability under suitable drought stress conditions.Key word Coffea canephora ;Drought stress ;Antioxidation action ;Osmoregulation ;Lipid peroxidation ;Membranepermeabilitydoi 10.3969/j.issn.1000-2561.2014.05.019第5期杨华庚等:干旱胁迫对中粒种咖啡幼苗膜脂过氧化、抗氧化酶活性和渗透调节物质含量的影响cCcBC bBaA对照轻度干旱中度干旱重度干旱水分处理MDA含量/(μmol/g)108642柱上不同大写字母表示0.01水平上的差异显著性,不同小写字母表示0.05水平上的差异显著性。

云南旱灾英文作文

云南旱灾英文作文

云南旱灾英文作文The drought in Yunnan has caused a serious shortage of water for drinking and irrigation. Farmers are struggling to keep their crops alive, and many are facing the prospect of losing their livelihoods. The government has been providing assistance, but it may not be enough to alleviate the widespread impact of the drought.The lack of water has also led to a decline in hydropower production, further exacerbating the energy crisis in the region. With power outages becoming more frequent, businesses are suffering and people are finding it difficult to meet their basic needs. The situation is becoming increasingly dire, and there is no quick solution in sight.In addition to the immediate effects on agriculture and energy, the drought is also taking a toll on the local ecosystem. Rivers and lakes are drying up, and wildlife is struggling to survive. The loss of biodiversity and naturalhabitats is a cause for concern, and the long-term effects of the drought on the environment are yet to be fully understood.The people of Yunnan are resilient, but the ongoing drought is testing their endurance. Many are having to make difficult decisions about their future, and the uncertainty is taking a toll on their mental and emotional well-being. It is a challenging time for the community, and the needfor support and solidarity is greater than ever.Despite the hardships, there are signs of hope as people come together to support each other and find innovative ways to cope with the crisis. Communities are sharing resources, and organizations are working to provide aid to those in need. The spirit of resilience and cooperation is a source of inspiration in the face of adversity.。

drought 英语介绍

drought 英语介绍

drought 英语介绍What is Drought?Drought is a prolonged period of abnormally dry weather, resulting in a shortage of water supply for various uses such as irrigation, household consumption, and industrial processes. It is a natural disaster that can have severe impacts on ecosystems, agriculture, economies, and human lives. Droughts can occur in any climate zone and can range in duration, severity, and geographic extent. In this article, we will delve deeper into the causes, effects, and strategies for mitigating the impacts of drought.Causes of DroughtSeveral factors contribute to the onset of drought, including natural variability in climate patterns and anthropogenic activities. Natural causes of drought include weather patterns like El Niño and La Niña, which can disrupt rainfall patterns and lead to prolonged dry periods. Climate change also plays a role in increasing the frequency and intensity of droughts, altering precipitation patterns and exacerbating water scarcity in certain regions.Human activities can also contribute to the occurrence of drought. Deforestation, for instance, reduces the capacity of forests to retain water, leading to decreased water availability in adjacent areas. Additionally, excessive water consumption by agriculture and industrial sectors can deplete water sources, exacerbating drought conditions. Poor water management practices, such as inefficient irrigation methods and inadequate water storage infrastructure, can further amplify the impacts of drought.Effects of DroughtDrought can have extensive impacts on various sectors and ecosystems. The agricultural sector is particularly susceptible, as crops and livestock depend heavily on water for growth and sustenance. Droughts can lead to crop failures, reduced agricultural yields, and livestock deaths, causing food shortages and price hikes. In addition to the immediate economic consequences, the longterm effects of drought on agriculture can include soil degradation, reduced soil fertility, and loss of vegetation cover.Ecosystems also suffer during droughts, with decreased water availability disrupting natural processes and habitats. Rivers, lakes, and groundwaterreservoirs can dry up, threatening the survival of aquatic species and diminishing biodiversity. Forests become vulnerable to wildfires, as dry vegetation becomes highly flammable. Moreover, droughts can lead to ecological imbalances, such as invasive species proliferation, which can further harm native flora and fauna.Droughts also impact human lives and economies. Water scarcity affects human health and hygiene, with a higher risk of waterborne diseases. Indigenous communities and disadvantaged populations are particularly vulnerable, as they often lack access to alternative water sources or means to cope with the impacts of drought. Economic sectors such as energy production, manufacturing, and tourism can also suffer as water scarcity hampers operations, increases costs, and decreases productivity.Mitigation and Adaptation StrategiesTo mitigate the impacts of drought, a combination of preventive measures, water management strategies, and adaptive practices are necessary. Integrated water resources management (IWRM) plays a crucial role in drought mitigation by balancing water supply and demand. This involves improving water efficiency, implementing water conservation practices, and promoting sustainable water use across sectors.Investing in water storage infrastructure, such as dams and reservoirs, increases water availability during dry periods. Implementing watersaving technologies and encouraging practices like rainwater harvesting and wastewater reuse also contribute to mitigating the impacts of drought. Moreover, enhancing soil conservation practices, such as afforestation and conservation agriculture, can improve soil moisture retention and reduce the effects of drought on agriculture.In terms of adaptive measures, enhancing early warning systems, drought monitoring, and forecasting can enable timely preparedness and response actions. Government agencies, in collaboration with local communities, should develop drought contingency plans that outline water allocation priorities, emergency response measures, and alternative water sources. Diversifying water sources through investment in desalination plants, interbasin water transfers, and water recycling can help alleviate the impacts of drought.Building resilience to drought also requires raising awareness and educating the public about water conservation practices and sustainable water use. Encouraging behavioral changes and promoting watersaving habits at home, schools, and workplaces can contribute to longterm watersecurity. Additionally, supporting research and innovation in waterrelated technologies and practices can lead to more efficient and sustainable solutions for drought management.ConclusionDrought is a complex phenomenon that poses significant challenges to ecosystems, economies, and human wellbeing. Addressing the causes and impacts of drought requires a multidimensional approach that involves climate change mitigation, water management strategies, and adaptive measures. By implementing comprehensive and integrated solutions, societies can build resilience and ensure water security in the face of future drought events.。

Plant Adaptations to Drought Stress

Plant Adaptations to Drought Stress

Plant Adaptations to Drought StressPlants have evolved various adaptations to cope with drought stress, which is one of the most important environmental factors limiting plant growth and productivity. Drought stress is caused by a lack of water availability, which can be due to low rainfall, high temperatures, or low soil moisture. In response to drought stress, plants have developed a range of mechanisms to mitigate the effects of water deficit and maintain their physiological functions.One of the most common adaptations of plants to drought stress is the regulation of water uptake and loss. Plants can reduce water loss by closing their stomata, which are tiny pores on the leaves that allow for gas exchange. When water is scarce, plants can close their stomata to conserve water, but this also limits their ability to photosynthesize and grow. Some plants have developed specialized stomata that can remain open even under water deficit conditions, allowing for gas exchange while minimizing water loss.Another adaptation of plants to drought stress is the development of deeper root systems. Plants with deep roots can access water from deeper soil layers, where water is less likely to be depleted by evaporation or plant uptake. Some plants also have the abilityto adjust their root growth in response to water availability, growing more roots in wet conditions and fewer roots in dry conditions.In addition to regulating water uptake and loss, plants can also produce compounds that help them tolerate drought stress. For example, some plants produce osmoprotectants, such as proline and glycine betaine, which help maintain cell turgor and protect against damage from dehydration. Other plants produce antioxidants, such as ascorbic acid and glutathione, which help protect against oxidative stress caused by drought.Plants can also alter their metabolism in response to drought stress, shifting from growth and development to stress tolerance. This involves changes in gene expression and protein synthesis, as well as the accumulation of stress-responsive metabolites. For example, some plants produce abscisic acid (ABA) in response to drought stress, which helps regulatestomatal closure and water uptake. ABA also triggers the synthesis of protective proteins and enzymes that help plants cope with drought stress.Finally, some plants have evolved specialized structures to cope with drought stress. For example, succulent plants, such as cacti and succulents, have thick, fleshy leaves and stems that can store water for extended periods of time. Some plants also have specialized tissues, such as the water storage tissue in the stems of baobab trees, that can store large amounts of water and help the plant survive extended periods of drought.In conclusion, plants have evolved a range of adaptations to cope with drought stress, including the regulation of water uptake and loss, the development of deeper root systems, the production of osmoprotectants and antioxidants, the alteration of metabolism, and the evolution of specialized structures. These adaptations allow plants to maintain their physiological functions and survive in environments with limited water availability. As climate change continues to alter global weather patterns, understanding these adaptations will be crucial for developing strategies to mitigate the effects of drought stress on plant growth and productivity.。

旱_盐复合胁迫对玉米种子萌发和生理特性的影响_姚海梅

旱_盐复合胁迫对玉米种子萌发和生理特性的影响_姚海梅

旱-盐复合胁迫对玉米种子萌发和生理特性的影响姚海梅李永生张同祯赵娟王婵王汉宁方永丰*(甘肃农业大学农学院/甘肃省作物遗传改良与种质创新重点实验室/甘肃省干旱生境作物学重点实验室,兰州730070)摘要分别用15%PEG 、100mmol ·L -1NaCl 及其混合溶液模拟干旱(D )、盐(S )及旱-盐复合胁迫(D +S )对玉米种子萌发及幼苗生长的影响.结果表明:3种胁迫处理均明显抑制了种子萌发、幼芽、幼根的伸长及生物量的积累,且影响程度为D>D +S>S ;幼芽及幼根中过氧化氢(H 2O 2)、超氧阴离子(O -·2)等活性氧含量及丙二醛(MDA )含量明显升高,质膜相对透性增大,脯氨酸、可溶性糖和可溶性蛋白等生理渗透调节物质含量显著增加,且幼芽中含量高于幼根,积累程度均为D>D +S>S.3种胁迫处理均使幼芽、幼根中的超氧化物歧化酶(SOD )、过氧化氢酶(CAT )、过氧化物酶(POD )及抗坏血酸过氧化物酶(APX )等抗氧化酶活性增强;其中,SOD 和APX 活性表现为复合胁迫介于单一胁迫之间,而POD 和CAT 活性表现为复合胁迫大于单一胁迫;说明旱-盐复合逆境胁迫对玉米种子萌发及幼苗生理特性的影响并不是单一胁迫的简单叠加,与单一干旱胁迫相比,旱-盐复合胁迫在一定程度上能够缓解干旱胁迫对玉米种子萌发及幼苗生长的影响.关键词玉米;复合胁迫;种子萌发;生理特性Effects of combined drought and salinity stress on germination and physiological characteris-tics of maize (Zea mays ).YAO Hai-mei ,LI Yong-sheng ,ZHANG Tong-zhen ,ZHAO Juan ,WANG Chan ,WANG Han-ning ,FANG Yong-feng *(Gansu Key Laboratory of Crop Improvementand Germplasm Enhancement /Gansu Key Laboratory of Aridland Crop Science ,College of Agronomy ,Gansu Agricultural University ,Lanzhou 730070,China ).Abstract :In this study ,15%PEG ,100mmol ·L -1NaCl and PEG-NaCl mixed solution were em-ployed to respectively simulate the drought (D ),salinity (S )and the combined stress (D +S ),and effects of these three stresses on the seed germination and the physiological characteristics of seed-lings were investigated.The results showed that seed germination ,seedling growth and biomass ac-cumulation were significantly inhibited by these three stresses ,and the impact of stress ranked asD>D +S>S.The content of reactive oxygen species like H 2O 2and O -·2,as well as malondialdehyde (MDA )and membrane permeability were increased under these stresses ,meanwhile ,proline (Pro ),soluble sugar and soluble proteins contents were significantly improved ,which were higher in seedlings than in roots with a rank of D>D +S>S.The activities of antioxidant enzymes such as su-peroxide dismutase (SOD ),peroxide (POD ),catalase (CAT )and ascorbate peroxide (APX )were also obviously increased.In addition ,SOD and APX induced by PEG-NaCl mixed solutionwere ranked in the middle compared to those induced by their single stress ,but POD and CAT were more induced by PEG-NaCl mixed solution than their single stress.It was demonstrated that effect ofdrought-salinity combined adverse condition on maize seed germination and seedlings physiologicalcharacteristics were not simply additive of their single stress ,compared with their single stress ,drought-salinity combined adverse condition could reduce the effects of drought stress on maize see-ding to a certain extent.Key words :maize ;combined stress ;seed germination ;physiological characteristics.本文由国家重点基础研究发展计划前期研究专项(2012CB722902)、甘肃省财政厅科研业务费(035041046)和甘肃省干旱生境作物学重点实验室开放基金(GSCS-2012-10)资助This work was supported by the Pilot Study Project of National Basic Research Program of China (2012CB722902),Gansu Provincial Department of Finance Research Operating Expense (035041046)and Open Fund of Gansu Key Laboratory of Aridland Crop Science(GSCS-2012-10).2015-10-30Received ,2016-04-26Accepted.*通讯作者Corresponding author.E-mail :fangyf@gsau.edu.cn应用生态学报2016年7月第27卷第7期http ://www.cjae.netChinese Journal of Applied Ecology ,Jul.2016,27(7):2301-2307DOI :10.13287/j.1001-9332.201607.023在全球气候变化背景下,各种非生物胁迫因子(干旱、盐渍、高温、低温、水涝等)成为影响作物生产的主要限制因素,导致植株生长缓慢、产量下降甚至绝收[1].玉米(Zea mays)是我国重要的粮食及饲料作物,近年来播种面积持续增加,在2014年已超过3690ˑ104hm2,成为第一大粮食作物.但是,我国干旱、半干旱地区的面积约占国土面积的52.5%[2],旱地玉米播种面积占种植面积的三分之二,主要分布于东北、西北、华北及西南地区,同时,由于近年来过量施肥造成土壤盐渍化现象加重,使玉米在生长发育过程中可能会遭受干旱-高盐的复合逆境,对玉米生产造成严重影响.因此研究玉米在复合胁迫下的生理生化机制,对干旱、半干旱地区玉米生产具有重要的理论意义及实际价值.目前,国内外学者在玉米响应单一干旱或盐胁迫方面做了大量工作.研究表明,干旱胁迫使玉米种子萌发活性受到抑制[3],并造成根系活力下降[4]、膜脂过氧化程度加剧[5]、光合速率变小[6]、生长发育减缓[6],严重时造成产量下降[7].与干旱胁迫类似,盐胁迫使玉米发芽势、发芽指数、活力指数、苗高和根长等指标下降[8],膜系统严重受损[9],叶绿素含量、根系活力、生物量降低[9],生长发育受到抑制[9-10],产量减少[10].近年来,国内外学者对复合逆境方面进行了一些研究,刘瑞侠等[11]研究了干旱-高温复合胁迫对玉米幼苗抗氧化防护系统的影响,表明干旱-高温复合胁迫对玉米幼苗保护酶活性的影响大于单一胁迫.Javadmanesh等[12]研究了紫外(UV-B)辐射与高盐、干旱及其复合胁迫对玉米幼苗生理特性的影响,发现单一盐渍、干旱胁迫处理比UV-B辐射和盐、UV-B辐射和干旱复合处理对玉米生理特性的影响更显著,表明UV-B辐射在一定程度上可以缓解土壤干旱及盐渍对玉米幼苗的伤害效应.Sun等[13]基于氢核磁共振(1H-NMR)的代谢组学技术,研究了单一干旱胁迫、盐胁迫以及干旱-盐复合胁迫下玉米叶片内代谢物的响应特征,发现复合胁迫下玉米代谢响应机制是一种不同于单一胁迫的新模式.另外,关于复合胁迫对水稻(Oryza sati-va)[14]、棉花(Gossypium hirsutum)[15]、芝麻(Sesa-mum indicum)[16]等植物生长发育的影响研究表明,植物对复合胁迫的响应机制较为复杂,与单一胁迫有所不同.为了阐明干旱-盐复合胁迫对玉米种子萌发及幼苗生长的影响,以及单一胁迫与复合胁迫之间的差异,本研究采用15%PEG、100mmol·L-1NaCl以及二者的混合溶液分别模拟干旱(D)、盐(S)及二者的复合胁迫(D+S)环境,研究了3种胁迫处理对玉米种子萌发以及生理生化特性的影响,以期为玉米响应复合胁迫的生理机制及抗逆育种研究提供一定的理论参考.1材料与方法1.1供试材料供试材料为玉米杂交种郑单958,由甘肃农业大学玉米育种课题组提供.1.2种子消毒与试验处理选取籽粒饱满、大小一致的干净玉米种子,经0.5%的次氯酸钠消毒10min,灭菌蒸馏水冲洗3遍后,用滤纸吸干附着水后,将50粒种子均匀播于以双层滤纸作为发芽床的发芽盒内.向发芽盒中分别加入30mL15%PEG-6000溶液、100mmol·L-1 NaCl溶液以及二者的混合溶液分别模拟干旱、盐及复合胁迫环境,同时以无菌水作为对照,试验设3次重复.将发芽盒置于25ħ恒温培养箱中黑暗培养,从第3天开始每天统计发芽种子数,7d后结束发芽试验,并取样进行各项指标测定.1.3测定项目与方法1.3.1萌发指标及生物量发芽率、发芽势、发芽指数、活力指数的计算参照彭云玲等[17]的方法,其中发芽率=第7天的发芽种子数/供试种子数ˑ100%,发芽势=第4天的发芽种子数/供试种子数ˑ100%,发芽指数(G)=∑G t/D t;活力指数(VI)=∑(G t/D t)ˑS=GIˑS,其中,Gt为t日的发芽数,D t为相应的发芽日数,S为平均胚芽质量.随机取10株测量胚芽、胚根长度及鲜质量,随后置于80ħ烘箱烘干至恒量,测定组织干质量.1.3.2MDA含量与质膜相对透性组织中的丙二醛(MDA)含量测定采用硫代巴比妥酸比色法[18];相对电导率(REC)测定参照张蜀秋等[18]的方法.1.3.3活性氧(ROS)及渗透调节物质含量测定O2-·含量测定参照田景花等[19]的方法;H2O2含量参照沙爱华等[20]的方法;脯氨酸含量测定采用3%黄基水杨酸法[18];可溶性糖含量测定采用蒽酮比色法[21];可溶性蛋白含量测定采用考马斯亮蓝染色法[21].1.3.4抗氧化酶活性超氧化物岐化酶(SOD)活性测定采用氮蓝四唑光化还原法[18],以抑制NBT光化还原50%所需酶量为1个酶活单位(U·g-1 FM);过氧化物酶(POD)活性测定采用愈创木酚2032应用生态学报27卷法[18],以每分钟OD值变化0.01为1个酶活性单位(U·min-1·g-1FM);过氧化氢酶(CAT)活性测定采用紫外分光光度计法[18],以每分钟OD值变化0.01为1个酶活性单位(U·min-1·g-1FM);抗坏血酸过氧化物酶(APX)活性测定参考张亚宏等[22]的方法,以OD290每分钟氧化1μmol AsA的酶量为1个酶活单位(U獉min-1獉g-1FM).1.4数据处理采用SPSS16.0统计分析软件对数据进行方差分析及最小显著差异性检验(Duncan新复极差法,α=0.05),采用Excel2013和Origin8.5软件进行数据处理和绘图.2结果与分析2.1种子萌发及生物量干旱、盐及二者的复合胁迫处理显著抑制了玉米种子的萌发及生物量的积累.由表1可见,3种胁迫处理后玉米种子发芽率、发芽势、发芽指数、活力指数与对照相比均明显下降(P<0.05),其中,干旱处理下发芽率、发芽势、发芽指数、活力指数分别下降了22.5%、24.3%、15.4%和56.9%;盐处理下分别下降了8.3%、10.1%、4.2%和42.5%;复合胁迫下分别下降了16.3%、18.7%、11.1%和65.9%.由此可见,表1干旱-盐复合胁迫对玉米种子萌发的影响Table1Effects of combined drought and salinity stress on germination of maize seeds处理Treatment发芽率Germinationrate(%)发芽势Germinationenergy(%)发芽指数Germinationindex活力指数VigorindexCK96.3ʃ1.5a89.3ʃ2.1a35.05ʃ0.39a15.24ʃ0.80aD74.7ʃ2.1d67.7ʃ3.1d29.65ʃ0.53d6.56ʃ0.34cS88.3ʃ2.5b80.3ʃ2.1b33.58ʃ0.53b8.76ʃ0.84bD+S80.7ʃ1.5c72.7ʃ1.2c31.19ʃ0.46c5.18ʃ0.19d CK:对照Control;D:干旱胁迫Drought stress;S:盐胁迫Salinity stress;D+S:干旱-盐复合胁迫Drought and salinity stress.同列不同小写字母表示处理间差异显著(P<0.05)Different small letters in the same column indicated significant difference among treatments at0.05 level.下同The same below.单一干旱处理对种子萌发的抑制作用明显大于盐处理(P<0.05),而复合胁迫对玉米种子萌发的影响介于单一胁迫之间.生物量是植物对逆境胁迫的综合体现,植物在胁迫环境下生长受抑程度可以最直观地反映植物的受伤害程度.经3种胁迫处理后,玉米根长、芽长以及干、鲜质量均显著降低(P<0.05,表2),其中,在干旱胁迫下根长、芽长、芽干质量、根干质量、芽鲜质量、根鲜质量与对照相比分别减少了42.4%、46.3%、38.1%、34.9%、61.8%、18.1%;在盐处理下分别减少了25.4%、27.3%、22.1%、14.1%、39.9%、8.8%;在复合胁迫下分别减少了34.4%、35.5%、29.7%、24.3%、50.9%、13.6%.与盐处理相比,干旱处理对芽、根的伸长及生物量积累的影响更大,而复合胁迫并没有加重单一胁迫的影响,影响程度介于两种单一胁迫之间.2.2H2O2和O2-·含量逆境胁迫能迅速诱导植物体内产生活性氧(re-active oxygen species,ROS),打破植物体内ROS的动态平衡,对脂类、蛋白质以及核酸产生氧化损伤,进而导致细胞膜系统受到破坏,蛋白质及核酸等生物大分子变性,酶活性丧失,新陈代谢受阻[23].由图1可知,3种胁迫处理下玉米幼芽、幼根中H2O2含量及O2-·含量与对照相比显著增加(P<0.05),并且幼芽中H2O2和O2-·含量明显大于幼根.其中,干旱、盐及复合胁迫处理后幼芽中H2O2含量分别为对照的2.14、1.41和1.70倍,幼根中H2O2含量分别为对照的2.17、1.48和1.74倍;幼芽中O2-·含量分别为对照的1.44、1.14和1.35倍,幼根中O2-·含量分别为对照的1.42、1.20和1.32倍.由此可见,干旱胁迫对植物体内ROS积累的影响明显高于盐胁迫,而复合胁迫并没有加重这一影响,其H2O2和O2-·含量介于两种单一胁迫处理之间,表明复合胁迫对植物体内ROS积累的影响不是单一胁迫的简单叠加,在干旱表2干旱-盐复合胁迫对玉米幼苗芽、根生长及生物量积累的影响Table2Effects of combined drought and salinity stress on growth of shoots and roots and accumulation of biomass in maize seedlings处理Treatment根长Root length(cm)芽长Shoot length(cm)干质量Dry mass(g·10plants-1)芽Shoot根Root鲜质量Fresh mass(g·10plants-1)芽Shoot根RootCK12.05ʃ0.34a7.11ʃ0.29a0.38ʃ0.02a0.21ʃ0.02a4.35ʃ0.26a1.54ʃ0.05a D6.95ʃ0.29d3.81ʃ0.33d0.23ʃ0.01d0.13ʃ0.01d1.66ʃ0.06d1.25ʃ0.02d S8.99ʃ0.40b5.17ʃ0.30b0.29ʃ0.02b0.18ʃ0.01b2.61ʃ0.25b1.40ʃ0.03b D+S7.91ʃ0.31c4.59ʃ0.22c0.26ʃ0.01c0.16ʃ0.01c2.13ʃ0.13c1.33ʃ0.03c 30327期姚海梅等:旱-盐复合胁迫对玉米种子萌发和生理特性的影响图1不同胁迫处理对玉米幼苗H 2O 2和O 2-·含量的影响Fig.1Effects of combined drought and salinity stress on H 2O 2and O 2-·contents in maize seedlings.CK :对照Control ;D :干旱胁迫Drought stress ;S :盐胁迫Salinity stress ;D +S :干旱-盐复合胁迫Drought and salinity stress.不同小写字母表示处理间差异显著(P <0.05)Different small letters indicated sig-nificant difference among treatments at 0.05level.下同The same below.处理的同时进行盐处理反而缓解了干旱导致的活性氧的积累.2.3MDA 含量和细胞质膜相对透性MDA 含量和电解质渗透率可以反映植物在逆境胁迫下的受伤害程度,MDA 是膜质过氧化的主要产物,指示着膜脂过氧化程度,膜脂过氧化程度越高,电解质外渗越严重,导致电导率(REC )升高[24].3种胁迫处理使玉米幼芽及幼根中MDA 含量显著升高(P <0.05)、细胞质膜相对透性显著增大(P <0.05),并且幼根中的MDA 含量和REC 大于幼芽(图2).其中,幼芽中MDA 含量较对照分别增加了38.3%、14.9%和25.2%,幼根中MDA 含量分别增加了31.4%、20.9%和20.9%;幼芽中REC 较对照分别上升了26.8%、10.3%和17.7%,幼根中REC 分别上升了24.7%、7.6%和15.7%.以上结果说明单一干旱处理对膜脂过氧化及质膜透性的影响明显高于盐处理,而复合胁迫介于单一胁迫之间.2.4渗透调节物质含量脯氨酸、可溶性糖和可溶性蛋白是重要的渗透调节剂,能降低细胞的渗透势,维持细胞质和液泡间的渗透平衡,提高植物组织的持水力,保护细胞膜结构的完整性,逆境下植物体内积累的渗透调节物质在一定程度上有助于增强植物抗逆性,也是评价植图2干旱-盐复合胁迫对玉米幼苗MDA 含量和相对电导率的影响Fig.2Effects of combined drought and salinity stress on MDA contents and relative electrical conductivity in maize seedlings.物抗逆性的重要生化指标[25].由图3可知,3种胁迫处理下,玉米幼芽、幼根中脯氨酸、可溶性糖和可溶性蛋白含量与对照相比显著升高(P <0.05),且幼根中脯氨酸含量高于幼芽,而可溶性糖和可溶性蛋白含量低于幼芽.干旱处理下幼芽中脯氨酸、可溶性糖和可溶性蛋白含量分别为对照的4.01、1.69和2.86倍,幼根中分别为对照的2.21、1.52和2.74倍;盐处理下幼芽中脯氨酸、可溶性糖和可溶性蛋白含量分别为对照的3.07、1.12、2.08倍,幼根中分别为对照的1.82、1.13、1.88倍;复合胁迫下,幼芽中脯氨酸、可溶性糖和可溶性蛋白含量分别为对照的3.61、1.34、2.44倍,幼根中分别为对照的2.02、1.28、2.24倍.以上结果表明单一干旱胁迫下渗透调节物质的积累量明显高于盐胁迫,复合胁迫下的积累量居于二者之间,可见复合胁迫下植物的受伤害程度小于干旱胁迫,在干旱处理的同时进行盐处理反而对干旱胁迫造成的影响具有一定缓解作用.2.5抗氧化酶活性增强抗氧化防御系统是植物适应逆境的重要机制,为保护自身免受伤害,植物形成了SOD 、POD 、CAT 和APX 等抗氧化酶系统,SOD 把O 2-·转化成H 2O 2,H 2O 2又可被CAT 、POD 和APX 降解为H 2O 和O 2,从而有效清除植物体内积累的ROS 和氧自由基,确保体内活性氧的产生和清除处于动态平衡状态[26].由图4可知,3种胁迫处理使参与ROS 清4032应用生态学报27卷图3干旱-盐复合胁迫对玉米幼苗脯氨酸、可溶性蛋白和可溶性糖含量的影响Fig.3Effects of combined drought and salinity stress on contents of proline ,soluble protein and soluble sugar in maizeseedlings.图4干旱-盐复合胁迫处理对玉米幼苗超氧化物岐化酶(SOD )、过氧化氢酶(CAT )、过氧化物酶(POD )和抗坏血酸过氧化物酶(APX )活性的影响Fig.4Effects of combined drought and salinity stress on superoxide dismutase (SOD ),catalase (CAT ),peroxide (POD )and ascor-bate peroxide (APX )activities in maize seedlings.除的保护酶活性显著增强(P <0.05),且幼芽SOD 和CAT 活性高于幼根,而POD 和APX 活性低于幼根.3种胁迫处理后幼芽中SOD 活性分别为对照的1.45、2.06和1.84倍,幼根SOD 活性分别为对照的1.56、2.26和1.97倍;幼芽中POD 活性分别为对照的1.32、1.17和1.71倍,幼根中POD 活性分别为对照的1.27、1.14和1.43倍;幼芽中CAT 活性分别为对照的1.34、1.69和2.37倍,幼根中CAT 活性分别为对照的1.15、1.35和1.58倍;幼芽中APX 活性分别为对照的1.95、1.30和1.70倍,幼根中APX 活性分别为对照的1.59、1.19和1.38倍.以上结果表明,单一盐处理后SOD 和CAT 活性高于干旱处理,而POD 和APX 活性低于干旱处理,复合胁迫与单一胁迫相比明显增强了POD 和CAT 活性,而SOD 和APX 活性居于两者之间.由此可见,复合胁迫对4种抗氧化酶活性的影响表现出不同的变化趋势,也说明了复合胁迫对玉米种子萌发及生理特性的影响机制相对复杂,不具备单一胁迫的累加效应.3讨论干旱是限制作物生长发育的主要环境因子,在干旱、半干旱地区由于土壤水分蒸发量远大于降雨量,造成土壤溶液浓缩、盐分浓度升高,形成旱、盐双重胁迫,对植物生长发育造成严重影响[27].胁迫环境下植物的外部形态及萌发率是作物受胁迫影响的直接体现,受影响程度越大,萌发率越低,导致出苗不齐,影响作物产量.本研究发现,干旱、盐及二者的复合胁迫均对玉米种子萌发、伸长及生物量积累产50327期姚海梅等:旱-盐复合胁迫对玉米种子萌发和生理特性的影响生了明显的抑制作用,影响程度大小为干旱胁迫>复合胁迫>盐胁迫,说明在干旱胁迫条件下,适量的盐离子可以使植物消耗较少的能量吸收盐离子产生膨压,从而降低渗透势,提高根系从外界吸收水分的能力,改善植株的供水和生长状况,缓解干旱胁迫对植物生长的抑制作用,Slama等[28]的研究也证实了这一点,这可能与盐分在植物干物质的积累中起着积极的营养作用有关.逆境胁迫能破坏植物细胞中ROS产生与清除之间的平衡,使ROS积累,导致植物细胞膜遭受氧化胁迫,引起膜脂过氧化、蛋白质变性、核酸链断裂等多种有害反应.植物为适应逆境,主动积累细胞溶质,提高脯氨酸、可溶性糖、可溶性蛋白等渗透调节物质含量增加,清除过多的活性氧自由基,减轻细胞膜的伤害程度,但由于其调节能力有限,因而积累了过剩的氧自由基,从而引起膜脂过氧化及质膜相对透性的增大,产生了大量的MDA[29].本研究结果发现,15%PEG溶液使玉米幼芽、幼根中H2O2、O2-·、MDA、REC、脯氨酸、可溶性糖及可溶性蛋白含量显著增加,在加入100mmol·L-1NaCl溶液后玉米幼芽、幼根中相应指标含量降低,说明加入适量盐分可通过清除ROS的积累,减轻膜脂过氧化程度,维持了细胞膜的完整性;并且由于蛋白质降解速度大于合成的速度,引起可溶性蛋白含量的降低,保证了充足的酶合成,同时可溶性糖及脯氨酸含量降低.由此表明,盐胁迫在一定程度上缓解了干旱胁迫对玉米造成的伤害,这与陈成升等[30]的研究结果类似,但并不完全一致,他们的研究结果得出,在干旱胁迫的基础上,一定量盐分的加入能够增加可溶性糖及脯氨酸含量,这可能是由于所设置的试验条件与所研究的植物材料不同而导致的.植物在进化过程中形成了完善的抗氧化防御体系,通过调节SOD、POD、CAT及APX等抗氧化酶活性的变化,避免植物细胞遭受胁迫伤害.本研究发现,3种胁迫对抗氧化酶活性的影响并不一致,其中干旱胁迫对POD、APX活性的影响大于盐胁迫,对SOD、CAT活性的影响小于盐胁迫,复合胁迫对POD、CAT活性的影响最大,对SOD、APX活性的影响小于干旱胁迫,说明单一盐胁迫对干旱胁迫下POD、SOD、CAT及APX酶活性的影响不尽一致,这与Ahmed等[31]研究干旱-盐复合胁迫下大麦的抗氧化酶活性结果类似.单一干旱、盐对抗氧化酶活性影响不一致,使得复合胁迫下抗氧化酶活性变化趋势不同,这可能是由于单一胁迫间的互作效应及冲突性所引起的.由此可见,植物对复合逆境的响应模式不同于单因子逆境,取决于单一胁迫在环境中的影响.Mittler[32]的研究结果也表明,植物对复合胁迫的响应机制是独特的,不能依据单一胁迫进行简单推理.本研究结果发现,15%PEG和100mmol·L-1 NaCl及其复合胁迫均显著抑制了种子的萌发、伸长及生物量的积累,且干旱胁迫影响最大.干旱、盐单一及复合胁迫均显著增加了H2O2及O2-·含量,提高了MDA含量、增大了细胞质膜透性,使渗透调节物质脯氨酸、可溶性糖及可溶性蛋白含量明显升高,而复合胁迫的增加幅度介于单一胁迫之间.另外,3种胁迫处理显著增强了SOD、POD、CAT及APX活性,其中SOD和APX活性表现为复合胁迫介于单一胁迫之间,而POD和CAT活性表现为复合胁迫大于单一胁迫,进一步说明了复合胁迫逆境响应机制的复杂性.总之,植物受到多因子逆境时,在对单因子胁迫做出响应的同时,有可能还需要调节和补偿多因子胁迫的冲突.与单一胁迫相比,复合胁迫作为一种新的胁迫状态,植物对其响应模式可能存在特异性,而且对这种胁迫状态需要做出新的适应或防御反应[33].由于干旱-盐复合胁迫更能代表旱作农业区作物的生长环境,因此,本研究通过对玉米抗旱耐盐生理特性的分析,为干旱、半干旱地区玉米新品种的选育提供新的方向,为植物耐复合胁迫的生理生化机制提供理论参考.参考文献[1]Wang Z-H(王铸豪).Plant and Environment.Beijing:Science Press,1986(in Chinese)[2]Song J-Z(宋家壮),Li P-P(李萍萍),Fu W-G(付为国).Effect of water stress and rewatering on the phy-siological and biochemical characteristics of Phalarisarundinacea.Acta Prataculturae Sinica(草业学报),2012,21(2):62-69(in Chinese)[3]Liu M,Li M,Liu K,et al.Effects of drought stress on seed germination and seedling growth of different maizevarieties.Journal of Agricultural Science,2015,7:231-240[4]Qi W(齐伟),Zhang J-W(张吉旺),Wang K-J (王空军),et al.Effects of drought stress on the grainyield and root physiological traits of maize varieties withdifferent drought tolerance.Chinese Journal of AppliedEcology(应用生态学报),2010,21(1):48-52(inChinese)[5]Wang J-H(王军辉),Zha X-Q(查学强),Luo J-P (罗建平),et al.Effect of drought stress on lipid peroxi-dation and activity of cell defense enzyme in maize seed-ling.Journal of Anhui Agricultural Sciences(安徽农业科学),2006,34(15):3568-3571(in Chinese)[6]ZhangR-H(张仁和),Zheng Y-J(郑友军),Ma G-S (马国胜),et al.Effects of drought stress on photosyn-thetic traits and protective enzyme activity in maize see-6032应用生态学报27卷ding.Acta Ecologica Sinica (生态学报),2011,31(5):1303-1311(in Chinese )[7]Zhang Y-J (张彦军),Xue J-Q (薛吉全),Zhang R-H(张仁和),et al .The effect of water stress in maize ear-lier-period on photosynthesis characteristic at spinning stage.Acta Agriculturae Boreali-Occidentalis Sinica (西北农业学报),2008,17(3):135-138(in Chinese )[8]Carpycy EB ,Celyk N ,Bayram G.Effects of salt stress on germination of some maize (Zea mays L.)cultivars.African Journal of Biotechnology ,2009,8:4918-4922[9]Zhang H-Y (张海艳),Zhao Y-M (赵延明).Effects of NaCl stress on seed germination and seedling growth ofwaxy corn.Plant Physiology Communications (植物生理学通讯),2010,46(3):291-293(in Chinese )[10]Zheng S-Y (郑世英),Shang X-F (商学芳),Wang L-Y (王丽燕),et al .Changes of physiological character-istics and yield of different salt-sensitive maize undersalt stress.Agricultural Research in the Arid Areas (干旱地区农业研究),2010,28(2):109-112(in Chi-nese )[11]Liu R-X (刘瑞侠),Li Y-H (李艳辉),Chen S-N (陈绍宁),et al .Effects of collaborative stress of drought and high temperature on antioxidant defense system in maize.Journal of Henan Agricultural University (河南农业大学学报),2008,42(4):363-366(in Chinese )[12]Javadmanesh S ,Rahmani F ,Pourakbar L.UV-B radia-tion ,soil salinity ,drought stress and their concurrent effects on some physiological parameters in mize plant.American-Eurasian Journal of Toxicological Sciences ,2012,4:154-164[13]Sun CX ,Gao XX ,Fu JQ ,et al .Metabolic response of maize (Zea mays L.)plants to combined drought and salt stress.Plant and Soil ,2015,388:99-117[14]Gao H-Y (高焕晔),Wang S-G (王三根),Zong X-F (宗学凤),et al .Effects of combined high temperatureand drought stress on amylose and protein contents at rice grain-filling stage.Chinese Journal of Eco-Agricul-ture (中国生态农业学报),2012,20(1):40-47(inChinese )[15]Luo Z (罗振),Dong H-Z (董合忠),Li W-J (李维江),et al .Combined effects of water logging and salini-ty on plant growth and some physiological parameters incotton seedling leaves.Cotton Science (棉花科学),2008,20(3):203-206(in Chinese )[16]Xu F-F (徐芬芬).Effect of drought and salt compound stress on seed germination and seedling growth of sesa-me.Journal of Jilin Agricultural Sciences (吉林农业科学),2013,38(4):15-17(in Chinese )[17]Peng Y-L (彭云玲),Li W-L (李伟丽),Wang K-Z (王坤泽),et al .Effects of salt stress on seed germina-tion and seedlings growth of salt-tolerant line and salt-sensitive line of maize.Acta Prataculturae Sinica (草业学报),2012,21(4):62-71(in Chinese )[18]Zhang S-Q (张蜀秋),Li Y (李云),Wu W-H (武维华).Experimental Technology of Plant Physiology.Beijing :Science Press ,2011(in Chinese )[19]Tian J-H (田景花),Wang H-X (王红霞),Zhang Z-H (张志华),et al.Effects of chilling stress on antioxi-dant system and ultrastructure of walnut cultivars.Chi-nese Journal of Applied Ecology (应用生态学报),2015,26(5):1320-1326(in Chinese )[20]Sha A-H (沙爱华),Huang J-B (黄俊斌),Lin X-H(林兴华),et al .The change in hydrogen peroxide con-tent and enzyme activity related to adult plant resistanceto rice bacterial blight.Acta Phytopathologica Sinica (植物病理学报),2004,34(4):340-345(in Chinese )[21]Zou Q (邹琦).The Experimental Guide for Plant Physiology.Beijing :China Agriculture Press ,2000(in Chinese )[22]Zhang Y-H (张亚宏),Sun W-C (孙万仓),Wei W-H(魏文慧),et al .Changes of SOD ,CAT and APX of Brassica napus infected by selfing in total growth period.Acta Agriculturae Boreali-Sinica (华北农学报),2008,23(1):105-108(in Chinese )[23]Li JT ,Qiu ZB ,Zhang XW ,et al .Exogenous hydrogen peroxide can enhance tolerance of wheat seedlings to salt stress.Acta Physiologiae Plantarum ,2011,33:835-842[24]Du R-F (杜润峰),Hao W-F (郝文芳),Wang L-F (王龙飞).Dynamic responses on anti-oxidative defense system and lipid peroxidation of Lespedeza davurica todrought stress and re-watering.Acta Prataculturae Sinica(草业学报),2012,21(2):51-61(in Chinese )[25]Mahajan S ,Tuteja N.Cold ,salinity and drought stres-ses :An overview.Archives of Biochemistry and Biophy-sics ,2005,444:139-158[26]Asada K.Production and scavenging of reactive oxygen species in chloroplasts and their functions.Plant Phy-siology ,2006,141:391-396[27]Xie W-H (解卫海),Ma S-J (马淑杰),Qi L (祁琳),et al .The mitigating effects of Na +accumulation on the drought-induced damage to photosynthetic appara-tus in cotton seedlings.Acta Ecologica Sinica (生态学报),2015,35(19):6549-6556(in Chinese )[28]Slama I ,Ghnaya T ,Messedi D ,et al .Effect of sodium chloride on the response of the halophyte species Sesuvi-um portulacastrum grown in mannitol-induced waterstress.Journal of Plant Research ,2007,120:291-299[29]Zhang Y-B (张远冰),Liu A-R(刘爱荣),Fang R(方蓉).Effect of exogenous nitric oxide on the growth and antioxidant enzyme activities of Lolium pe-renne under Cd stress.Acta Prataculturae Sinica (草业学报),2008,17(4):57-64(in Chinese )[30]Chen C-S (陈成升),Xie Z-X (谢志霞),Liu X-J (刘小京).Interactive effects of drought and salt stresses on winter wheat seedlings growth and physiological charac-teristics of stress resistance.Chinese Journal of Applied Ecology (应用生态学报),2009,20(4):811-816(in Chinese )[31]Ahmed IM ,Dai H ,Zheng W ,et al .Genotypic differ-ences in physiological characteristics in the tolerance to drought and salinity combined stress between Tibetan wild and cultivated barley.Plant Physiology and Bio-chemistry ,2013,63:49-60[32]Mittler R.Abiotic stress ,the field environment and stress combination.Trends in Plant Science ,2006,11:15-19[33]Manivannan P ,Jaleel CA ,Sankar B ,et al .Growth ,bi-ochemical modifications and proline metabolism in Heli-anthus annuus L.as induced by drought stress.Colloids and Surfaces B :Biointerfaces ,2007,59:141-149作者简介姚海梅,女,1989年生,硕士研究生.主要从事玉米抗逆生理及分子生物学研究.E-mail :yhm@st.gsau.edu.cn 责任编辑张凤丽姚海梅,李永生,张同祯,等.旱-盐复合胁迫对玉米种子萌发和生理特性的影响.应用生态学报,2016,27(7):2301-2307Yao H-M ,Li Y-S ,Zhang T-Z ,et al .Effects of combined drought and salinity stress on germination and physiological characteristics ofmaize (Zea mays ).Chinese Journal of Applied Ecology ,2016,27(7):2301-2307(in Chinese )70327期姚海梅等:旱-盐复合胁迫对玉米种子萌发和生理特性的影响。

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ORIGINAL ARTICLEAlleviation of drought stress of marigold (Tagetes erecta )plants by using arbuscular mycorrhizal fungiAbdul-Wasea A.Asrar *,Khalid M.ElhindiPlant Production Department,College of Food and Agriculture Sciences,King Saud University,P.O.Box 2460,Riyadh 11451,Saudi ArabiaReceived 3June 2010;revised 23June 2010;accepted 23June 2010KEYWORDSArbuscular mycorrhiza;Glomus constrictum ;Fungus;Drought stress;Marigold;Tagetes erecta ;Growth and floweringAbstract The effect of an arbuscular mycorrhizal fungus ‘‘AMF’’(Glomus constrictum Trappe)on growth,pigments,and phosphorous content of marigold (Tagetes erecta )plant grown under differ-ent levels of drought stress was investigated.The applied drought stress levels reduced growth vigor (i.e.plant height,shoot dry weight,flower diameter as well as its fresh and dry weights)of mycor-rhizal and non-mycorrhizal plant as compared to control plant (non-drought stressed plant).The presence of mycorrhizal fungus,however,stimulated all growth parameters of the treated plant comparing to non-mycorrhizal treated plant.The photosynthetic pigments (carotene in flowers and chlorophylls a and b in leaves)were also stimulated by the mycorrhizal fungi of well-watered as well as of water-stressed plants.The total pigments of mycorrhizal plants grown under well-watered conditions were higher than those of non-mycorrhizal ones by 60%.In most cases,drought-stressed mycorrhizal plants were significantly better than those of the non-mycorrhizal plants.So,the overall results suggest that mycorrhizal fungal colonization affects host plant posi-tively on growth,pigments,and phosphorous content,flower quality and thereby alleviates the stress imposed by water with holding.ª2010King Saud University.All rights reserved.1.IntroductionMarigold (Tagetes erecta L.)belongs to Asteraceae family and is a herbaceous plant with aromatic,pinnately divided leaves and is usually used as a bedding plant,cut flower,or as a col-oring agent in poultry feed to obtain yellow egg yolks (Dole and Wilkins,2005).T.erecta L.has smaller flowers and leaves than those of most other marigolds.The plants brighten up any sunny area in the landscape and attract attention.More-over,marigold plants are considered a very valuable enter crop for controlling plant parasitic nematode as recorded by Basu and Roy (1975).The aerial parts of the plant contain high*Corresponding author.Tel.:+96614678340/4678996;mobile:+9660505452950;fax:+96614678467.E-mail address:aasrar@.sa (Abdul-Wasea A.Asrar).1319-562X ª2010King Saud University.All rights reserved.Peer-review under responsibility of King Saud University.doi:10.1016/j.sjbs.2010.06.007quality of essential oil that can be used for scenting soaps,per-fumery,cosmetic,and pharmaceutical industries.Arbuscular mycorrhizal(AM)fungal symbiosis is widely be-lieved that it protects host plants from detrimental effects of drought(Auge,2001;Abdel-Fattah et al.,2002;Ruiz-Lozano, 2003).Possible mechanisms for improving drought resistance of the mycorrhizal plants could be due to an increased in root hydraulic conductivity(Robert et al.,2008),stomatal regulation or transpiration rate(Allen and Boosalis,1983),enhanced water uptake at low soil moisture levels as a result of extraradical hyphae(Fagbola et al.,2001),osmotic adjustment which pro-motes turgor maintenance even at low tissue water potential (Auge et al.,1986),increased photosynthetic activity,proline and carbohydrate accumulation,and increased nutritional sta-tus in mycorrhizal plants(Scheilenbaum et al.,1999).These mechanisms may be important in adaptation of the mycorrhizal plants to drought conditions.The symbiosis of plant roots with AM fungi is known to be one of the most ancient and wide-spread plant strategies to enhance nutrient acquisition which copes with the environmental stress(Brachmann and Parniske, 2006).The intra-radical mycelium of these soil fungi proliferates in root cortex of the host plant.Extraradical AM hyphae spread in the soil around the root and provide a surface area by which the AM fungus absorbs nutritional elements‘‘such as phospho-rus(P),nitrogen(N),zinc(Zn),or copper(Cu)’’and transports and transfers them to the host plant(Smith and Read,2008).One of the increasing interest and economic importance is the variation of the mycorrhizal responsiveness of a specific fungus by the variations in cultivars of the same host plants. This concept has been reported forfield-grown crops,includ-ing basil(Gupta et al.,2000),grapes(Karagiannidis et al., 1995),onions(Tawaraya et al.,2001),wheat(Zhu et al., 2001),marigold(Robert et al.,2003),Brodiaea laxa(Scagel, 2004),Coriander spp.(Aliabadi et al.,2008),Viola calaminaria (Ferna ndez et al.,2008),Calendula spp.(Rahmani et al.,2008), and medicinal and aromatic plants(Hossein et al.,2009).Marigolds are annual plants that generally respond to mycorrhizal infection,but they do not always exhibit signifi-cant responsiveness under P-limiting conditions(Koide et al., 1999).However,plants of this nature may still benefit from the symbiosis,if not by enhancing growth,and hence increas-ing disease resistance(Linderman,2000),and environmental stress tolerance(Cantrell and Linderman,2001),or other phys-iological changes(Koide,2000).Therefore,the objective of this study was to investigate the effects of arbuscular mycorrhizal fungus(Glomus constrictum) on growth,phosphorus content,andflower quality of marigold plants subjected to various levels of drought stress conditions.2.Materials and methods2.1.Growth conditionsSeeds germination and transplanting of marigold(T.erecta) plants,cultivar‘Jubilee’were carried out in a greenhouse with a temperature of27/18°C day/night,and a supplemental light of750l mol mÀ2sÀ1(at a canopy level)provided by high-vapor pressure sodium lamps for14h dayÀ1,and misted twice daily until transplanted,Plant Production Departments,College of Food and Agricultural Sciences,King Saud University, Riyadh,Saudi Arabia.Seeds were germinated in72-cell plug flats containing a seedling germination mix of50%fine peat moss and50%vermiculite.Seeds were sown on16September, 2009and transplanted2weeks later into plastic pots of25cm diameter with one seedling per pot containing a mixture of one coarse sand:one low P sandy loam soil(v/v)media with a textural analysis of77%sand,9%clay,and14%silt.The sandy loamy soil was collected from the experimental and agricultural research station at Dirab,Riyadh region,Saudi Arabia.Prior to the study,the mix was steam-pasteurized with AM fungal inoc-ulants or non-inoculated controls and then cooled and stored for at least a week prior to use.Soil characteristics were as fol-low:the water pH7.8;23mg phosphorus kgÀ1;17mg nitrogen kgÀ1;28mg potassium kgÀ1,and34mg magnesium kgÀ1soil.2.2.Mycorrhizal fungal inoculum preparationThe mycorrhizal fungus was originally isolated from the Dirab Experimental Station of College of Food and Agricultural Sci-ences,Riyadh region,Saudi Arabia.The fungus was propa-gated in pot culture on roots of bunching onion(Allium cepa L.‘White Lisbon’)grown in loam:sand(1:1)medium for 5months.The non-mycorrhizal control soil had a similar cul-ture,but without AM fungi.Inocula consisted of a mixture of soil medium,extraradical hyphae,and spores,and colonized root segments(62mm in length).The inoculum(5g of soil containing spores of mycorrhizal fungus)was placed3cm be-low the surface of the soil(before sowing)to produce mycor-rhizal pants.The non-mycorrhizal treatment received an equal amount of sterilized soil inoculum to provide the same microflora without mycorrhizal fungi.2.3.Experimental designPots were arranged on a greenhouse bench in a2·4factorial randomized block design included two mycorrhizal treatments (with mycorrhizal fungi‘‘M+’’and non-mycorrhizal fungi ‘‘MÀ’’),and four levels of drought stress(no drought,mild drought,moderate drought,and severe drought).Plants were carefully watered as needed with tap water to maintain soil moisture nearfield capacity for3weeks,and then plants were subjected to eight treatments(five pots were used for each treatment).When seedlings were transplanted,irrigation was given uniformly to all pots.Marigold seedlings were exposed to four levels of drought stresses(100%(D0),75%(D1), 50%(D2),and25%(D3)according to water holding capacity of the soil.Plants were fertilized twice weekly with13N–0.9P–10.8K soluble fertilizer prepared to supply N and K at approximately200mg kgÀ1N,and P at16mg kgÀ1.Each pot received approximately100ml of the fertilizer solution to ensure thought-out saturation of the medium.Growth mea-surements,pigment analysis,and determination of phospho-rous content in both the leaves and theflowers were carried out after6weeks from transplantation.2.4.Seedling measurementsThe following parameters were examined at the end of the experiment(8weeks old):1.Plant height(cm).2.Shoot fresh and dry weights per plant(g).3.Flower fresh and dry weights(g)and diameter(cm)per plant.4.Mineral analysis:oven-dried shoots(leaves andflowers)and samples were ground to pass through0.5mm sieve and then analyzed for P content according to method of Allen(1989).5.Estimation of photosynthetic pigments content:the photo-synthetic pigments(chlorophylls a,b and carotenoids)were extracted and determined in fresh leaves of marigold plants according to the spectrophotometric method recommended by Metzner et al.(1965).2.5.Statistical analysisA randomized complete block design with three replicates was used.Data were subjected to statistical analysis according to (Steel and Torrie,1980).The treatment means were compared using the least significant differences(LSD)test at0.05%level.3.Results and discussion3.1.Growth parameters and plant productivityUnder well-watered conditions,mycorrhizal fungus signifi-cantly increased all the growth attributes such as plant height, shoot dry weight,flower diameter,flower fresh,and dry weights of marigold plants comparing to non-mycorrhizal plants(Table1).The drought stress treatments significantly re-duced the height,shoot dry weight,flower diameter,flower fresh,and dry weights of both the mycorrhizal and the non-mycorrhizal plants.This reduction was greatly offset by the G.constrictum stimulation of growth response of the treated plants comparing to the non-mycorrhizal treated plants (Fig.1).Generally,under drought stress,mycorrhizal fungus stimulated greater growth criteria andflower parameters of treated plants than those of the non-mycorrhizal plants (Fig.2).The enhanced dry weights of AM inoculated plants were5.29,4.12,3.06,and2.62g,while of non-AM inoculated plants were4.44,3.28,2.89,and2g at different levels of water-stressed conditions(well-watered,mild,moderate and severe drought-stressed treatments,respectively).Such pronounced growth response to mycorrhizal colonization was observed by Wu and Xia(2006)and Wu et al.(2008)who noticed that the mycorrhizal(AM)seedlings of Citrus tangerine and Ponci-rus trifoliate had significantly higher shoot and root dry weights,plant height,leaf area,leaf number per plant,and stem diameter under well-watered and water-stressed condi-tions than the corresponding non-AM seedlings.Similar re-sults have been reported for other plant species(Kaya et al., 2003;Wu and Xia,2006).The positive effect was likely attrib-uted to the improvement of phosphorus nutrition(Bethle-nfalvay et al.,1988)and uptake of water by hyphae(FaberEffects of mycorrhizal fungus(Glomus constrictum)on the vegetative growth of marigold plants grown either under (left)or under drought stress condition(right),where M=treated and NM=non-treated mycorrhizal plants.et al.,1991).Dell-Amico et al.(2002)also found that the inoc-ulation of tomato plants with G.clarum encouraged higher growth rates of plants in both well-watered and stressed condi-tions.Drought-stressed non-mycorrhizal plants produced low-er products than mycorrhizal ones at all drought treatments (Table1).These results are in good agreement with Al-Karaki et al.(2004),who observed that the inoculation with AM fungi provided an important enhancement to yield of two wheat cul-tivars.Sorial(2001)also observed increases in straw and grain yield of wheat plants subjected to different levels of water stress and inoculated with arbuscular mycorrhiza when com-pared to non-mycorrhizal plants.The enhancement in mari-gold growth and biomass yields due to AM fungi might be attributed to higher mineral and water uptake.Al-Karaki and Clark(1998)stated that the enhanced plant growth as well as yield following AM inoculation were due to the improved uptake of P and Cu,especially under water-stressed condi-tions.Whereas,M+plants were taller than MÀplants regard-less of levels of drought stress,and the mycorrhizal response was more pronounced in severe drought treatment(D4).3.2.Photosynthetic pigmentsThe content of photosynthetic pigments(chlorophylls a,b in leaves and carotenoids inflowers)of mycorrhizal and non-mycorrhizal marigold plants are presented in Table2and Fig.3.In general,with all treatments,the contents of chloro-phylls a,b and carotenoids in mycorrhizal plants were signifi-cantly greater than those of non-mycorrhizal ones at all stages of plant growth.The total photosynthetic pigments increased due to mycorrhizal colonization by60%at well-watered con-ditions.These results also indicated that the deleterious effect of drought treatment on total pigments was at the severe drought stress of the plants.The decrease of chlorophyll content in marigold plants as a result of water deficit has also been reported by several authors (Dhanda et al.,2004;Shao et al.,2007)and citrus(Wu andXia,2006).Shao et al.(2007)reported that chlorophyll was the substantial basis for wheat photosynthesis,so the content of chlorophyll could be one of the indexes for evaluating photosynthesis.Many reports showed that drought could lead to lower photosynthesis and efficiency(Dhanda et al.,2004). However,Moran et al.(1994)stated that the decrease in chlo-rophyll or protein concentrations would be a typical symptom of oxidative stress that had been observed in drought-stressedTable2Chlorophylls a and b for mycorrhizal(M+)and non-mycorrhizal(MÀ)marigold plants exposed to different levels of drought stress(D0no drought,D1mild,D2moderate and D3 severe).Treatments Chlorophylls(mg/g fresh weight) Drought Mycorrhizal Chlorophyll a Chlorophyll b D0M+0.3430.145MÀ0.3350.136D1M+0.3230.127MÀ0.3130.117D2M+0.3030.112MÀ0.2950.104D3M+0.2840.101MÀ0.2700.095LSD5%0.004*0.004*Where M+=mycorrhizal treatment and MÀ=non-mycorrhizal treatment.*Significant difference at p60.05(Steel and Torrie,1980).Mplants.The increase of photosynthetic pigments as a result of mycorrhizal colonization was also supported by Aboul-Nasr (1996)and Wu and Xia(2006).The present results indicate that AM application assist plants to counter photoinhibition and photodestruction of pigments under stressed conditions by increasing the content of carotenoids.It is well known that carotenoids are involved in protecting photosynthetic appara-tus against the photoinhibitory damage by the single oxygen. Therefore,carotenoids can directly deactivate,and can also quench the excited triple state of chlorophyll(Foyer and Harbinson,1994).Moreover,it has been mentioned that the higher chlorophyll content in AM than in non-AM plants has sometimes been associated with a higher rate of photosyn-thesis,or with the increase in nitrogen and magnesium con-tents(major components of chlorophyll molecules)of mycorrhizal plants(Mathur and Vyas,1995).3.3.Phosphorus contentDrought stress levels significantly reduced the phosphorus content of mycorrhizal and non-mycorrhizal marigold plants comparing to well-watered plants(Fig.4).However,the rate of reduction was higher in non-mycorrhizal than in mycor-rhizal plants.These results agreed with thefindings of Al-Karaki et al.(2004)on wheat plants;Auge et al.(2007) on sorghum and squash;Wu and Xia(2006)on citrus. Moreover,Subramanian et al.(2006)also observed that the mycorrhizal tomato plants had significantly higher phos-phorus uptake in both roots and shoots of the plants regardless of the drought stress intensities.Phosphorus concentration may affect host water balance. For instance,stomatal conductance can be influenced by P star-vation.Koide(2000)suggested that the increased stomatal con-ductance and transpiration rate in AM plants could be due to P-mediated improvement in photosynthetic capacity.Phospho-rous concentrations in leaves may affect stomatal response to environmental perturbations,perhaps by affecting the energetic involved in guard cell osmotic potential or wall stiffening gov-erning stomatal movements(Weyers and Meidner,1990).Wu and Xia(2006)reported that under water stress conditions, higher plants accumulate some small molecules including or-ganic solutes and inorganic ions.The accumulation of these molecules in AM seedlings resulted in a greater osmotic adjust-ment,and allowed AM seedlings to accumulate more carbohy-drate and thus higher plant biomass.Davies et al.(1992)found that external hyphal development and soil aggregation of mycorrhizal plants were enhanced by drought acclimation. However,O’Keefe and Sylvia(1993)observed that external hy-phae adhere to soil particles,and improve contact with soil solution.Furthermore,they mentioned that hyphae access smaller pore spaces better than plant roots and root hairs. 4.ConclusionThe results of this study indicated that marigold plants grown under semiarid habitats were affected greatly by water-stressed conditions.The data showed that the mycorrhizal colonization improved drought resistance of the marigold plants as a conse-quence of enhancing nutritional status,especially P and water status of the plants.This enhances plant growth,phosphorous uptake,and plant productivity.Therefore,this study recom-mends farmers in new reclaimed lands to not withhold irriga-tion during heading stage of marigold plants,and suggests adding arbuscular mycorrhizal fungi to arid farms,or to farms suffering from withholding irrigation water at critical growth stages.ReferencesAbdel-Fattah,G.M.,Mighed,F.,Ibrahim,A.H.,2002.Interactive effects of endomycorrhizal fungus Glomus etunicatum and phos-phorous fertilization on growth and metabolic activities of board bean plants under drought stress conditions.Pak.J.Biol.Sci.5(8), 835–841.Aboul-Nasr,A.,1996.Effects of vesicular–arbuscular mycorrhiza on Tagetes erecta and Zinnia elegans.Mycorrhiza6,61–64. Aliabadi,F.,Lebaschi,H.,Hussein,M.,Hussein,S.A.,Reza1,V.A., Jahanfar, D.,2008.Effects of arbuscular mycorrhizal fungi, different levels of phosphorus and drought stress on water use efficiency,relative water content and proline accumulation rate of Coriander(Coriandrum sativum L.).J.Med.Plants Res.2(6),125–131.Al-Karaki,G.N.,Clark,R.B.,1998.Growth,mineral acquisition,and water use by mycorrhizal wheat grown under water stress.J.Plant Nutr.21(2),263–276.Al-Karaki,G.N.,McMichael,B.,Zah,J.,2004.Field response of wheat to arbuscular mycorrhizal fungi and drought stress.Mycor-rhiza14,263–269.Allen,S.E.,1989.Chemical Analysis of Ecological Materials,second ed.Black Well Sci.Pub.Osney,Oxford,London.Allen,M.F.,Boosalis,M.G.,1983.Effect of two species of VA mycorrhizal fungi on drought tolerance of winter wheat.New Phytol.93,67–76.Auge,R.M.,2001.Water relations,drought and vesicular arbuscular mycorrhizal symbiosis.Mycorrhiza11,3–42.Auge,R.M.,Scheikel,K.A.,Warmple,R.L.,1986.Osmotic adjust-ment in leaves of VA-mycorrhiza and non-mycorrhizal rose plants in response to drought stress.Plant Physiol.82,765–770. Auge,R.M.,Toler,H.D.,Moore,J.L.,Cho,K.,Saxton,A.M.,2007.Comparing contributions of soil versus root colonization to variations in stomatal behavior and soil drying in mycorrhizal Sorghum bicolor and Cucurbita pepo.J.Plant Physiol.164,1289–1299.Basu,S.D.,Roy,S.K.,1975.Rotylenchulus sp.a new ecto parasitic nematode in ted soil.Two and Bud(22(1),(17)Em).In:Abst,C.F.H.,Tocklia Experimental Station Horhat,Aaaaem,India,vol.46.Breeding for Resistance to Fungal Pathogens.CanadianJournal of Botany68,1039–1044(1976).Bethlenfalvay,G.J.,Brown,M.S.,Ames,R.N.,Thomas,R.E.,1988.Effects of drought on host and endophyte development inM-mycorrhizal soybeans in relation to water use and phosphate uptake.Physiol.Plant.72,565–571.Brachmann,A.,Parniske,M.,2006.The most important symbiosis on earth.Soil Biol.4,239.Cantrell,I.S.,Linderman,R.G.,2001.Preinoculation of lettuce and onion with VAmycorrhizal fungi reduces deleterious effects of soil salinitx.Plant Soil223,269–281.Davies,F.T.,Potter,J.R.,Linderman,R.G.,1992.Mycorrhiza and repeated drought exposure affect drought resistance and extrarad-ical hyphae development of pepper plants independent of plant size and nutrient content.J.Plant Physiol.139,289–294.Dell-Amico,J.,Torrecillos,A.,Rodriguez,P.,Morte,A.,Sanchez-Blanco,M.J.,2002.Responses of tomato plants associated with the arbuscular mycorrhizal fungus Glomus clarum during drought and recovery.J.Agric.Sci.138,387–393.Dhanda,S.S.,Sethi,G.S.,Behl,R.K.,2004.Indices of drought tolerance in wheat genotypes at early stages of plant growth.J.Agron.Crop Sci.190(1),6–12.Dole,J.M.,Wilkins,H.F.,2005.Floriculture Principles and Species.Prentice-Hall Inc.,USA,p.1023.Faber,B.A.,Zasoki,R.J.,Munns,D.N.,Shackel,K.,1991.A method for measuring hyphal nutrient and water uptake in mycorrhizal plants.Can.J.Bot.69,87–94.Fagbola,O.,Osonubi,O.,Mulongox,K.,Odunfa,S.A.,2001.Effects of drought stress and arbuscular mycorrhiza on the growth of Gliricdia sepium(Jacq).Walp,Leucaenal leucocephala(Lam).De wit.In simulated eroded soil conditions.Mycorrhiza11,215–223. Ferna ndez,O.,Carrillo,R.G.,Vangrosveld,J.,Gonza lez,M.C.,2008.Arbuscular mycorrhizal fungi and Zn accumulation in the metall-ophytic plant Viola calaminaria(Gingins.)Lej.Serie Horticultura 14(3),355–360.Foyer, C.H.,Harbinson,J.,1994.Oxygen metabolism and the regulation of photosynthetic electron transport.In:Foyer,C.H., Mullineausx,P.M.(Eds.),Causes of Photooxidative Stress and Amelioration of Defense System in Plants.CRS Press,Boca Raton, pp.1–4.Gupta,M.L.,Khaliq,A.,Pandey,R.,Shukla,R.S.,Singh,H.K., Kumar,S.,2000.Vesicular–arbuscular mycorrhizal fungi associ-ated with Ocimum spp..J.Herbs Spices Med.Plant7,57–63. Hossein, A.F.,Valadabadi,S.A.,Daneshian,J.,Shiranirad,A.H., Khalvati,M.A.,2009.Medicinal and aromatic plants farming under drought conditions.J.Horti.Forestry6,082–092. Karagiannidis,N.,Nikolaou,N.,Matteou,A.,1995.Influence of three VA-mycorrhiza species on the growth and nutrient uptake of three grapevine rootstocks and one table grape cultivar.Vitis34,85–89. Kaya,C.,Higgs,D.,Kirnak,H.,Tas,I.,2003.Mycorrhizal coloni-zation importoves fruit yield and water use efficiency in water-melon(Citrullus Lanatus Thunb.)grown under well watered and water-stressed conditions.Plant Soil253,287–292.Koide,R.T.,2000.Mycorrhizal symbiosis and plant reproduction.In: Kapulnik,Y.,Douds, D.D.(Eds.),Arbuscular Mycorrhizas: Physiology and Function.Kluwer Academic Publishers,Dordr-echt,pp.19–46.Koide,R.T.,Landherr,L.L.,Besmer,Y.L.,Detweiler,D.M.,Hol-comb, E.J.,1999.Strategies for mycorrhizal inoculation of six annual bedding plant species.HortScience34,1217–1220. Linderman,R.G.,2000.Effects of mycorrhizas on plant tolerance to diseases.In:Kapulnk,Y.,Douds, D.D.(Eds.),Arbuscular Mycorrhizas:Physiology and Function.Kluwer Academic Pub-lishers,Dordrecht,pp.345–365.Mathur,N.,Vyas, A.,1995.Influence of VA mycorrhiza on net photosynthesis and transpiration of Ziziphus mauritiana.J.Plant Physiol.147,328–330.Metzner,H.,Rau,H.,Senger,H.,1965.Untersuchungen zur Synchronnisierbarkeit einzelner pigmentmangel Mutanten von Chlorella.Planta65,186.Moran,J.F.,Becana,M.,Iturbe-Ormaetre,I.,Frechilla,S.,Klucas, R.V.,Aparicio-Tejo,P.,1994.Drought induces oxidative stress in pea plants.Planta194,346–352.O’Keefe,D.M.,Sylvia,D.M.,1993.Chronology and mechanisms of mycorrhizal mediated P uptake in sweet potato plants.New Phytol.122,651–659.Rahmani,N.,Aliabadi,F.H.,Valadabadi,S.A.R.,2008.Effects of nitrogen on oil yield and its component of Calendula(Calendula officinalis L.)in drought stress conditions.Abstracts Book of the World Congress on Medicinal and Aromatic Plants,South Africa, p.364.Robert,G.,Linderman,A.,Davis,E.A.,2003.Varied response of marigold(Tagetes spp.)genotypes to inoculation with different arbuscular mycorrhizal fungi.Sci.Hortic.22,1–14.Robert,M.,Auge,R.M.,Heather,D.,Carl,F.,Sams,E.A.,Ghazala, N.,2008.Hydraulic conductance and water potential gradients in squash leaves showing mycorrhiza-induced increases in stomatal conductance.Mycorrhiza18,115–121.Ruiz-Lozano,J.M.,2003.Arbuscular mycorrhizal symbiosis and alleviation of osmotic stress.New perspectives for molecular studies.Mycorrhiza13Onlinefirst published on April11, doi:10.1007/s00572-003-0237-6.Scagel,C.F.,2004.Soil pasteurization and mycorrhizal inoculation alterflower production and corm composiyion of Brodiaea laxa ‘‘Queen Fabiola’’.HortiScience39(6),1432–1437. Scheilenbaum,L.,Sprenger,N.,Schuepp,H.,Wiemken,A.,Boller,E., 1999.Effect of drought transgenic expression of a fructan synthe-sizing enzyme and of mycorrhizal symbiosis on growth and soluble carbohydrate pools in tobacco plants.New Phytol.142,67–77. Shao,H.B.,Chu,L.Y.,Wu,G.,Zhang,J.H.,Lu,Z.H.,Hu,Y.C., 2007.Changes of some antioxidative physiological indices under soil water deficits among10wheat(Triticum aestivum L.)genotypes at tillering stage.Colloids Surf.B54,143–149.Smith,S.E.,Read, D.J.,2008.Mycorrhizal Symbioses,third ed.Academic Press,UK.Sorial,M.E.,2001.Growth,phosphorus uptake and water relations of wheat infected with an arbuscular mycorrhizal fungus under water stress.Ann.Agric.Sci.-Moshtohor39(2),909–931.Steel,R.C.D.,Torrie,J.M.,1980.Principals and Procedures of Statistics.A Biometrical Approach.Mc Graw-Hill Book Company, NY,USA.Subramanian,K.S.,Santhanakrishnan,P.,Balasubramanian,P.,2006.Responses offield grown tomato plants to arbuscular mycorrhizal fungal colonization under varying intensities of drought stress.Sci.Hort.107,245–253.Tawaraya,K.,Tokairin,K.,Wagatsuma,T.,2001.Dependence of Alliumfistulosum cultivars on the arbuscular three pea cultivars.Plant Soil103,296–298.Weyers,J.D.B.,Meidner,H.,1990.Methods in Research.Longman, London,pp.9–12.Wu,Q.S.,Xia,R.X.,2006.Arbuscular mycorrhizal fungi influence growth,osmotic adjustment and photosynthesis of citrus under well watered and water stress conditions.J.Plant Physiol.163,417–425.Wu,Q.S.,Xia,R.X.,Zou,Y.N.,2008.Improved soil structure and citrus growth after inoculation with three arbuscular mycorrhizal fungi under drought stress.Eur.J.Soil Biol.44,122–128.Zhu,Y.G.,Smith,S.E.,Barritt,A.R.,Smith,F.A.,2001.Phosphorus (P)efficiencies and mycorrhizal responsiveness of old and modern wheat cultivars.Plant Soil237,249–255.。

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