Water relations of Robinia pseudoacacia L- are R-shaped vulnerability curves invalid in Robinia
天津滨海绿地的植物种类及其应用研究
Botanical Research 植物学研究, 2017, 6(5), 317-324Published Online September 2017 in Hans. /journal/brhttps:///10.12677/br.2017.65042Study on Plant Species and Its Applicationin Tianjin Costal GreenlandMeixian WangBeijing Laboratory of Urban and Rural Ecological Environment, College of Landscape Architecture,Beijing Forestry University, BeijingReceived: Sep. 8th, 2017; accepted: Sep. 22nd, 2017; published: Sep. 27th, 2017AbstractTianjin coastal area is seawater impregnated, seriously affecting plant growth and have a lot of salt and alkali wasteland, vegetation ecological restoration is particularly important. Therefore, it is important to study the plant species, plant growth potential and application status of Tianjin coastal green land, and to select the plant species suitable for ecological restoration in Tianjin coastal area. The research on plant species and spontaneous growth plants of Tianjin coastal green space was carried out. The plant species and their growth potential, frequency and degree of occurrence were analyzed, and the important values were calculated, to provide reference for ve-getation selection and restoration in Tianjin coastal area. The results showed that there were 129 species (including cultivation), belonging to 45 families and 102 genera. Among them, seven kinds of growth potentials such as: Pinus bungeana, Pinus tabulaeformis and Albizia julibrissin were poor. Trees such as Sophora japonica, Amygdalus persica, Malusmicromalus, Fraxinus velutina, Prunus cerasifera, etc. were more widely used; Shrubs such as Euonymus japonicas, Ligustrum vi-caryi, Hibiscus syriacus, Amorpha fruticosa, Rhustyphina, etc. were more widely used; Herbs such as Phragmites australis, Festucaelata, Medicago sativa, L epidium apetalum, Irislactea etc. were more widely used.KeywordsTianjin Coastal Greenland, Plant Species, Growth Potential, Important Value天津滨海绿地的植物种类及其应用研究王美仙北京林业大学园林学院,城乡生态环境北京实验室,北京收稿日期:2017年9月8日;录用日期:2017年9月8日;发布日期:2017年9月27日王美仙摘 要天津滨海区域长期受海水浸渍拥有大量的盐碱荒地,植物生长受到严重影响,植被生态恢复尤为重要。
水位梯度对湿地植物生长、繁殖和生物量分配的影响
植物生态学报ACTA PHYTOECOLOGICA SINICA1999年5月 第23卷 第3期 Vol.23 No.31999水位梯度对湿地植物生长、繁殖和生物量分配的影响王海洋 陈家宽 周 进摘 要:本文考察了水位梯度对武夷慈姑(Sagittaria wuyiensis)、小慈姑(S. potamogetifolia)、野荸荠(Eleocharis plantagineiformis)和锐棱荸荠(E. acutangula)植物幼苗生长、繁殖器官干重、生物量及其分配式样的影响。
实验表明:植物高度、生物量及其分配对水位梯度的反应在种间有一定差异,而慈姑属植物的叶数、荸荠属植物的秆数、繁殖器官干重等对水位梯度处理的反应在种间有一定相似性。
综合植物生物量和繁殖的反应特点,可以认为武夷慈姑和锐棱荸荠适宜生长在0~5cm水深处,小慈姑在20cm水深处生长较佳,而野荸荠适宜于0~20cm范围。
结果提示:湿地植物的空间分布与其对水位反应的差异性有一定关系。
关键词:水位梯度 反应 湿地植物INFLUENCE OF WATER LEVEL GRADIENT ON PLANT GROWTH,REPRODUCTION AND BIOMASS ALLOCATIONOF WETLAND PLANT SPECIESWang Haiyang Chen Jiakuan and Zhou JinSchool of Life Science,Wuhan University,Wuhan 430072Abstract:The effects of water level gradient on the growth,reproduction and biomass allocation of the four wetland plant species:Sagittaria wuyiensis, S. potamogetifolia,Eleocharis plantagineiformis and E.acutagula, were studied with cultivated population.Seedlings of four species were cultivated in four water level treatments, i.e. 40cm, 20cm,0~5cm water depth and 5cm below the substrate surface. The four wetland plant species showed significant response to the gradient, and for these species, S.wuyiensis and B.acutangula preferred the treatment of 0~5cm water depth, S.potamogetifolia preferred 20cm and B.plantgineiformis 0~20cm. The distinct response patterns might explain the spatial distribution of the wetland plants to some extent.Key words:Water level gradient, Responses,Wetland plants 湿地植物沿环境梯度而发生的物种组成变化一直是生态学家感兴趣的一个重要问题,但关于其变化机制还有争论(Gopal,1990),争论的焦点之一在于:植物对环境梯度的反应是共同反应(Shared responses),还是差异反应(Distinct responses)(Keedy &Ellis,1985)?如果是差异反应,即不同的植物由于适应环境梯度中的不同位置而具有相异的反应特征,那么物种组成的变化就可视为植物适应性不同的结果(van der Valk,1981);如果是共同反应,即这些植物适应相同的位置而具有相似的反应特征,则需要其它机制(如竞争)来解释之(Wilson & Keedy,1985)。
水生生物学1-蓝藻
§⑥ 束球藻属
每个细胞和 一条胶质柄 相连,2个或 4个细胞为一 组,每组的 胶质柄又互 相连接,组 成一个由中 心发出的放 射状系统。
§⑦ 腔球藻属
细胞群体作 辐射状排列。 绿色。营浮 游生活。繁 殖为细胞分 裂或群体断 裂方式。
§⑧ 平裂藻属
细胞规律排列,常两两成双, 两对一组,集合成平板状。多 为浮游性种类。
个新的植物体。 两个 有性繁殖: 配子 结合 新个体 合子 孢子 新个体
同配:2个配子形态、生理相同 异配:2个配子形态结构不同 大、较不活动-雌配子 小、较活动-雄配子 卵配:2个配子形态差异明显 大、不动-卵 小、游动-精子
孢子:是植物所产生的一种有繁殖或休
眠作用的细胞,能直接发育成新个体。
不需和其他细胞结合,即可萌发成新的植物体。 一般微小,单细胞。通常为无性生殖过程所产生的
定义:
一群具有叶绿素,营自养生活, 没有真正的根、茎、叶分化,以 单细胞的孢子或合子进行繁殖的 低等植物,又叫孢子植物 (spore plant)、叶状体植物、 自养原植体植物。
藻类特点
① 藻体各式各样。有单细胞、群体、丝状体、
囊状体、叶状体、枝状体等各种类型。
②个体大小相差悬殊。绝大多数藻类植物微
红海束毛藻
埃及红海
§③ 颤藻属
单条藻丝,或由许多藻 丝组成皮壳状、块状。 藻丝不分枝,直或扭曲, 能颤动。以段殖体繁殖。 分布很广。
The Formation of Coral Reefs and Atolls
The Formation of Coral Reefs and Atolls Coral reefs and atolls are some of the most fascinating and diverse ecosystems on the planet. They are formed from the accumulation of calcium carbonate exoskeletons of coral polyps, which are tiny, invertebrate animals that live in colonies. These structures provide a habitat for a wide variety of marine life, including fish, invertebrates, and algae. The formation of coral reefs and atolls is a complex process that involves geological, biological, and environmental factors.One of the key factors in the formation of coral reefs and atolls is the presence of suitable substrate for coral growth. Coral polyps require a hard surface on which to attach and grow, and they typically thrive in warm, shallow, clear waters. As the polyps grow and reproduce, they form colonies that eventually build up into large, solid structures. Over time, the accumulation of coral skeletons creates the framework for a reef or atoll.The geological processes that contribute to the formation of coral reefs and atolls are also important to consider. Reefs often form along the edges of continents or around volcanic islands, where the ocean floor is relatively shallow. As the Earth's tectonic plates shift and move, these areas can experience changes in sea level and land elevation, which can impact the growth and development of coral reefs. Additionally, the presence of ocean currents and wave action can influence the shape and structure of reefs, as well as the distribution of coral species.In addition to geological factors, biological processes play a crucial role in the formation of coral reefs and atolls. Coral polyps rely on a symbiotic relationship with photosynthetic algae called zooxanthellae, which live within their tissues and provide them with essential nutrients. This relationship allows corals to thrive in nutrient-poor waters, but it also makes them sensitive to environmental stressors such as changes in temperature and water quality. When corals are stressed, they can expel their zooxanthellae, a process known as coral bleaching, which can have devastating effects on reef ecosystems.The environmental conditions in which coral reefs and atolls form and grow are also significant. These ecosystems are typically found in tropical and subtropical regions, wherethe water is warm and clear. The availability of sunlight is crucial for the photosynthetic processes of both corals and their symbiotic algae, so reefs are most commonly found in shallow waters where light can penetrate. Additionally, the stability of water temperature and chemistry is important for the health and growth of coral reefs, as they are sensitive to changes in conditions such as ocean acidification and pollution.Human activities also play a role in the formation and degradation of coral reefs and atolls. Overfishing, destructive fishing practices, coastal development, and pollution can all have negative impacts on reef ecosystems. Additionally, climate change is a major threat to coral reefs, as rising sea temperatures and ocean acidification are causing widespread coral bleaching and mortality. Conservation efforts, such as marine protected areas and sustainable fishing practices, are essential for the preservation of these valuable and vulnerable ecosystems.In conclusion, the formation of coral reefs and atolls is a complex and dynamic process that involves a combination of geological, biological, and environmental factors. These ecosystems are not only incredibly diverse and beautiful, but they also provide important ecological and economic benefits. Understanding the processes that shape coral reefs and atolls is crucial for their conservation and management, especially in the face of growing threats from human activities and climate change. As stewards of the natural world, it is our responsibility to protect and preserve these irreplaceable ecosystems for future generations.。
水污染英文版
artificially supplemented results in an abnormal increase in the growth of water plants
The pollutants include grit, asbestos石棉, phosphates and nitrates, mercury, lead, caustic soda and other sodium compounds, sulfur and sulfuric acid, oils, and petrochemicals.
Sources of water pollution
The used water of a community is called wastewater, or sewage. If it is not treated before being discharged into waterways, serious pollution is the result.
Example: Chrome plating on bumpers, grills, and ornaments is a source of pollution
Pollutants from various industries
The textile industry dumps conditioners, dyes, bleaches, and water effluents containing oils, dirt, and other organic debris.
对水的研究英文作文
对水的研究英文作文英文:I have always been fascinated by the study of water. Water is essential for all living organisms, and it plays a crucial role in the Earth's ecosystems. From a scientific perspective, water has unique properties that make it a fascinating subject of study. For example, its ability to exist in three states – solid, liquid, and gas – is quite remarkable. The way water molecules form hydrogen bondswith each other also contributes to its unique properties, such as its high surface tension and ability to dissolve a wide range of substances.In addition to its chemical properties, water also hasa profound impact on human culture and society. For example, many ancient civilizations were built around bodies of water, and water has been a central theme in art,literature, and religion throughout history. Even today, water continues to play a significant role in our lives,from providing a source of recreation and relaxation to serving as a means of transportation and trade.From a personal perspective, my interest in water stems from my own experiences and observations. I grew up near a lake, and I have always been drawn to the calming effect of water. Whether it's taking a peaceful walk along the shore or simply listening to the sound of waves, I find water to be incredibly soothing. Additionally, I have always been fascinated by the diverse marine life that inhabits oceans, rivers, and lakes. The way different species interact with their aquatic environment is truly remarkable.In conclusion, the study of water is a multifaceted and fascinating field that encompasses scientific, cultural, and personal perspectives. Whether it's exploring the chemical properties of water, studying its cultural significance, or simply enjoying its calming effects, water is a topic that never fails to captivate me.中文:水一直是我着迷的研究课题。
植物生理学英语_Plant Physiology English
植物生理学词汇植物生理学 plant physiology message transportation 信息传递signal transduction 信号转导water potential 水势solute potential 溶质势osmotic potential 渗透势matric potential 衬质势diffusion 扩散osmosis 渗透plasmolysis 质壁分离deplasmolysis 质壁分离复原pressure potential 压力势turgor pressure 膨压bulk flow 集流aquaporin 水孔蛋白active absorption of water 主动吸水root pressure 根压blooding 伤流blooding sap 伤流液guttation 吐水apoplast 质外体symplast 共质体passive absorption of water 被动吸水transpiration pull 蒸腾拉力bound water 束缚水gravitational water 重力水cappilary water 毛细管水permanent wilting coefficient 永久萎蔫系数accumulation 积累性lenticular transpiration 皮孔蒸腾cuticular transpiration 角质层蒸腾stomatal transpiration 气孔蒸腾transpiration rate 蒸腾速率transpiration ratio 蒸腾效率transpiration coefficient 蒸腾系数small pore diffusion law 小孔扩散律feed back manner 反馈调节feed forward manner 前馈调节vapor pressure difficiency 叶片-大气水气压亏缺cohesion theory 内聚力学说mineral nutrition 矿质营养ash 灰分ash element 灰分元素mineral element 矿质元素essential element 必需元素solution culture method 溶液培养法water culture method 水培法sand culture method 沙基培养法balance solution 平衡溶液major element 大量元素minor element 微量元素nutrient deficiency symptom 营养缺乏症calcium binding proteins 钙结合蛋白calmodulin 钙调素beneficial elements 有益元素rare earth element 稀土元素selective absorption 选择吸收physiologically acid salt 生理酸性盐physiologically alkaline salt 生理碱性盐physiologically neutral salt 生理中性盐toxicity of single salt 单盐毒害ino antagonism 离子拮抗ion transporter 离子运载体ion channel 离子通道ion carrier 离子载体ion pump 离子泵voltage sensor 电压感受器permease 透过酶transport enzyme 运输酶ATPase ATP酶electrogenic pump 致电离子泵electroneutral pump 中性离子泵masterenzyme 主宰酶pinocytosh 胞饮作用simple diffusion 单纯扩散facilitated diffusion 协助扩散primary active transport 初始主动运输secondary active transport 次级主动运输co-transport 协同转运,共转运secondary co-transport 次级共转运proton mative force 跨膜质子电动势symport 同向转运antiport 反向转运ATP-binding complex ATP结合复合体contact exchange 接触交换foliar nutrition 叶片营养ectodesmata 外连丝nitrate reductase ,NR 硝酸还原酶induced enzyme 诱导酶adaptive enzyme 适应酶nitrite reductase 亚硝酸还原酶glutamine synthetase 谷氨酰胺合成酶glutamate synthase 谷氨酸合成酶carbon assimilation 碳素同化作用photosynthesis 光合作用chlorophyll 叶绿素phytol 植醇carotenoid 类胡萝卜素carotene 胡萝卜素lutein 叶黄素pigment protein complex 色素蛋白复合体phycobillin 藻胆素photon 光子quantum 光量子ground state 基态excited state 激发态light reaction 光反应dark reaction 暗反应reaction centre pigments 反应中心色素light-harvesting pigments 聚光色素antenna pigments 天线色素reaction center 反应中心photosynthetic unit 光合单位exciton transfer 激子传递resonance transfer 共振传递primary electron donor 原初电子供体primary electron acceptor 原初电子受体secondary electron donor 次级电子供体trap 陷阱red drop 红降现象Emerson effect 爱默生效应PSII light harvesting complex,LHC II : PSII 的捕光色素复合体pheo 去镁叶绿素plastoquinone 质体醌reductive pentose phosphate pathway,RPPP 还原戊糖磷酸途径GAP 甘油醛-3-磷酸z scheme z方案cytochrome,Cyt 细胞色素ferrdoxin,Fd 铁氧还蛋白plastocyanin,PC 质蓝素water photolysis 水的光解Hill reaction 希尔反应oxygen-evolving complex,OEC 放氧复合体manganese stablizing protein 锰稳定蛋白water oxidizing clock 水氧化钟noncyclic electron transport 非环式电子传递cyclic electron transport 环式电子传递pseudocyclic electron transport 假环式电子传递water-water cycle 水-水循环photosynthetic phosphorylation 光合磷酸化DNP 二硝基苯酚(解偶联剂)crassulacean acid metabolism,CAM 景天酸代谢the Calvin cycle 卡尔文循环oxaloacetic acid 草酰乙酸malic acid,Mal 苹果酸aspartic acid ,Asp天冬氨酸bundle sheath cell 维管束鞘细胞pyruvic acid 丙酮酸photo respiration 光呼吸light compensation point 光补偿点light saturation 光饱和现象photoinhibition of photosynthesis 光抑制midday depression 午睡现象aerobic respiration 有氧呼吸anaerobic respiration 无氧呼吸respiratory substrate 呼吸底物fermentation 发酵respiratory rate 呼吸速率respiratory quotient 呼吸商glycolysis 糖酵解tricarboxylic acid cycle 三羧酸循环elicitor 激发子biological oxidation 生物氧化barbital acid 巴比妥酸rotenone 鱼藤酮positive effector 正效应物negative effector 负效应物Pasteur effect 巴斯德效应maintenance respiration 维持呼吸growth respiration 生长呼吸confocal laser canning microscope 共聚集激光扫描显微镜empty seed coat technique 空种皮杯技术symplastic phloem loading 共质体装载apoplasmic phloem loading 质外体装载first messenger 第一信使chemical signal 化学信号positive chemical signal 正化学信号negative chemical signal 负化学信号physiocal signal 物理信号action potentials 动作电位variation potentials 变异电位receptor 受体blue light recepter 隐花色素,蓝光受体protein kinase 蛋白激酶phosphorlation 磷酸化作用transcription factor 转录因子plant growth substance 植物生长物质phytohormones 植物激素plant growth regulators 植物生长调节剂auxin 生长素IAA 吲哚乙酸hormone receptor 激素受体acid-growth theory 酸生长学说Gibberellins 赤霉素Gibberellic acid,GA 赤霉酸zeatin 玉米素cytokinin,CTK 细胞分裂素cytokinin oxidase,CKO 细胞分裂素氧化酶abscisin II 脱落素IIdormin 休眠素abscisic acid,ABA 脱落酸terpenoid pathway 类萜途径carotenoid pathway 类胡萝卜素途径xanthoxin 黄质醛lutein 叶黄素neoxanthix 新黄质brassinolide 油菜素内酯brassinosteroide 油菜素甾体类化合物bean bioassay 生物鉴定法jasmonates 茉莉酸Jasmonic acid methyl ester 茉莉酸甲酯linolenic acid α-亚麻酸cyclic fatty acid 环脂肪酸aspirin 阿司匹林salicylic acid ,SA 水杨酸polyamines,PA 多胺putrescine,Put 腐胺cadaverine,Cad 尸胺spermidine,Spd 亚精胺spermine,Spm 精胺CEPA 乙烯利NAA 萘乙酸NAD 萘乙酰胺6-BA 6-苄基腺嘌呤CCC 矮壮素PP333 多效唑growth 生长differentiation 分化development 发育chemical creep 化学滑行totipotency 细胞全能性polarity 极性explant 外植体tissue culture 组织培养primary culture 初代培养subculture 继代培养redifferentiation 再分化embryoid 胚状体somatic embryo 体细胞胚adventitious embryo 不定胚virus-free plants 无病毒植株light seed 需光种子dark seed 需暗种子seed longevity 种子寿命seed vigor 种子活力seed viability 种子生活力seed aging 种子老化determinate 有限性meristem 分生组织initial cell 原细胞seed deterioration 种子劣变indeterminate 无限性self-perpetuating 自我留存stem cell 干细胞quiescent center 静止中心tunica 原套corpus 原体central zone 中央区peripheral zone 周缘区vegetative meristem 营养分生组织floral meristem 成花分生组织growth periodicity 生长的周期性grand period of growth 生长大周期lagphase 停滞期logarithmic growth phase 指数期linear growth phase 线性期senescence phase 衰减期daily periodicity 昼夜周期性correlation 相关性apical dominance 顶端优势primigenic dominance 原发优势autoinhibition 自动抑制allelopathy 它感作用autotoxicity 自毒photomorphogenesis 光形态建成photoreceptor 光敏受体photosensor 光敏受体phytochrome 光敏色素thermoperiodicity of growth 生长的温周期现象tropic movement 向性运动nastic movement 感性运动phototropism 向光性geotropism 向地性gravitropism 向重力性positive/negative gravitropism 正/负向重力性diagravitropism 横向重力性statolith 平衡石amyloplast 淀粉体chemotropism 向化性hydrotropism 向水性turgor movement 紧张性运动nyctinasty 感夜性thermonasty 感温性seismonasty 感震性action potential 动作电位circadian rhythm 近似昼夜节律ripeness to flower state 花熟状态floral induction 成花诱导floral evocation 成花启动initiation of flower 花的发端floral development 花发育vernalization 春化作用devernalization 去春化作用revernalization 再春化作用vernalin 春化素bolting 抽薹photoperiod 光周期photoperiodism 光周期现象photoperiodic induction 光周期诱导critical dark period 临界暗期critical night 临界夜长florigen 成花素floral determinated state 成花决定态flower bud differentiation 花芽分化hermaphroditic plants 雌雄同株同花植物dioecious plants 雌雄异株植物androecious line 雄性系gynoecious line 雌性系fertility change 育性转化pollenin 花粉素recognition 识别group effect 集体效应parthenocarpy 单性结实phyrin 非丁respiratory climacteric 呼吸跃变dormancy 休眠epistotic dormancy 强迫休眠physiological dormancy 生理休眠after-ripening 后熟stratification 层积处理copigmentation 协同关系作用free radical 生物自由基programmed cell death 程序性细胞死亡apoptosis 细胞凋亡abscission 脱落stress 逆境,胁迫stress physiology 逆境生理strain 胁变escape 避性avoidance 御性tolerance 耐性hydraulic signal 水信号water mass flow 水流hydraustatic pressure 水压chemical signal 化学信号aquaporin 水孔蛋白proteinase inhibitor 蛋白酶抑制剂systemin 系统素electrical signal 电信号osmotin 渗调蛋白chaperone 分子伴侣water stress protein 水分胁迫蛋白heat shock protein 热激蛋白late embryogenesis abundant protein 胚胎发生晚期丰富蛋白lipid transfer protein 类脂转移蛋白kinase-regulated protein 激酶调节蛋白biotic stress 生物逆境pathogenesis-related protein 病程相关蛋白heavy metal binding protein 重金属结合蛋白phytochelatin 植物螯合肽cold-acclimation-induced protein 冷驯化诱导蛋白anaerobic stress protein 厌氧蛋白cross adaptation 交叉适应。
【生理学课外读物】细胞膜水通道的发现
【生理学课外读物】细胞膜水通道的发现细胞膜水通道的发现(一)2003 年 10 月 8 日,瑞典皇家科学院将 2003 年诺贝尔化学奖授予时为 The Johns Hopkins University School of Medicine 生物化学系(现为 Duke University 医学中心副主任)的 Peter Agre 教授,以表彰他发现细胞膜水通道并证明其功能这一开创性贡献。
Agre 教授 1949 年出生于美国,他的祖父辈们在 19 世纪末从瑞典和挪威移民到了美国。
其父Courtland Agre 毕业于 University ofMinnesota ,并获得了化学学士和博士学位。
二战期间曾是 3M company 即明尼苏达矿务及制造业公司的化学专家,负责实验室合成多聚物。
二战后先后成为St. Olaf ColIege 和 Augsberg College 化学系的一位教师。
Peter Agre 教授能从事基础研究,与从小受其父影响不无关系。
身为细胞生物学的教授,Peter 教授并非科班出身于分子生物学。
1967 年至 1970 年,他就读于 Minneapois , Augsburg college 的化学专业,并获得学士学位。
1970 年至1974 年,进入Johns Hopkins Uuniversity school of Medicine 获医学博士学位,并在1981 年获得医师执照。
1974 年至 1975 年, Peter A gre 在 Johns Hopkins 药理学系Pedro Cuatrecasas 的实验室进行博士后的研究。
1984 年, Peter 在The Johns Hopklns University 的 the old Blalock Building 建立了第一个自己的实验室。
当时作为血液学家,Peter 和助手Andy Asimos 开始研究球形红细胞增多症( spherocytosis ),并分别与1985 年和 1986 年在 Nature 和 New England Journal of Medicine 上发表了相关文章,证明血影蛋白( spectrin )缺乏与临床上球形细胞增多症( spherocytosis )的严重程度有关。
Water
Water by Robert Bly
水
罗伯特•布莱冯默谌 译作者简介:罗伯特•布莱(Robert Bly,1926—2021)是美国“深度意象派”的代表诗人,已出版十多部诗集、三十多部译诗集。
主要诗集有《五十年代》
《身体周围的光》《从两个世界爱一个女人》等。
12The bird dips to take some water in its bill .You know we do not drink only with our hands.
We receive what nothing else can give.
3
We are thirsty for the heron and the lake, the touch of bill on the water.
Notes :
欣赏
诗歌
1. dip [ ] v . 浸,蘸
2. bill [ ] n . 喙
3. heron [ ] n . 鹭,苍鹭
鸟儿低头用喙饮水。
你知道我们仅用双手无法饮水。
我们的所得,别人难以给予。
我们渴望着苍鹭和湖,
轻触后的波纹。
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ICM_2009翻译
2009ICM:交叉学科建模竞赛创建食物系统:调整人类影响的生态系统平衡技术背景只有不到1%的海底被珊瑚覆盖。
然而,25%的海洋生物多样性需要在这样的环境下生存。
因此,自然资源保护论者担心一旦珊瑚消失,该地区的生物多样性也会随之消失。
例如位于菲律宾的吕宋岛和圣地亚哥岛之间的一条狭长的海峡,过去那里充满了珊瑚礁,而且有大量不同品种的生物(图1)。
随着20世纪90年代引入了商业化遮目鱼(Milkfish)养殖业以后,这个曾经拥有大量的物种的地区产生了戏剧性的物种下降的情况。
曾经生活着活珊瑚的地方都变成了泥地,野生鱼都因为过度捕捞和丧失生存环境而濒临灭绝。
虽然为该地区的提供足够的食物很重要,但找到一个可以使自然生态系统继续繁荣的创新的方法同样重要,也就是建立一个理想的混养系统,可以取代目前单一的遮目鱼养殖。
最终的目标是发展一套水产养殖方法,不仅支持当地居民的经济需求和营养需求,同时也改善当地的水质,使得活珊瑚可以重新回到这个区域的海底并且与养殖厂和谐相处。
一个理想的混养方案是多种经济作物一起养殖,并且一种物种产生的废物是另一种物种的食物。
例如Finfish产生的废物可以被Filter Feeder(滤食动物)吃掉,并且他们(fish&filter feeders)产生的额外的废物也可以被海藻吸收,海藻也是可以被出售的。
这不仅减少在鱼类养殖中对周围水域的营养物质输入,也可以通过利用鱼的排泄物产生更大数量的可利益化产品(贻贝,海带等)。
为了建模的目的,在这个动物多样性的环境中,可以将这些生物有机体划分为掠食性鱼类(脊索动物门,脊椎动物亚门);草食性鱼类(脊索动物门,脊椎动物亚门),软体动物(如贻贝,牡蛎,蛤蜊,蜗牛等);甲壳类动物(如螃蟹,龙虾,藤壶,虾等,节肢动物门,甲壳动物亚门);棘皮类动物(如星鱼,海参,海胆等;门棘皮动物门);和藻类(软体动物门)。
喂养结构:有初级生产者(光合作用,可以是单细胞浮游藻类,蓝藻,多细胞藻类);滤食性生物(应变浮游生物,有机颗粒,有时是水体之外的细菌); 沉积物摄食者(吃泥土和消化的有机分子和营养物质的);食草动物(吃初级生产者)和捕食者(食肉动物)。
(植物的含水量及水分存在状态)概要
Section1 Role of water in plant life
• 1.1 Structure and .2 Water content and status in plant (植物的含水量及水分存在状态)
2.13植物细胞是一个渗透系统
2.1.4 Water potential consist of the plant cell
• Ψw=Ψs+Ψp+Ψm…… 。 Ψs--solute potential。它取决于细胞内溶质 颗 粒 ( 分 子 或 离 子 ) 总 和 。 植物叶Ψs为-1~-2 MPa,旱生植物叶片达 10MPa 。 Ψs还存在着日变化和季节变化。
• 吸胀作用的动力为Ψm,因为Ψs=0,Ψp=0,Ψw=Ψm。
2.4 Water channel proteins or aquaporins (水通道蛋白或水孔蛋白)
• 指细胞膜或液泡膜上,可减少水分跨膜运 输阻力,加快水分进出生物膜的一类蛋白 质。
• Aquaporins的可能生理功能: 生殖生长、细胞伸长、保卫细胞和叶枕运 动、细胞膨压和体积调节、蒸腾流和栓塞 去除,木质部和韧皮部水分循环、矿质营 养吸收、对旱和盐胁迫的响应。
4.1 Organs for transpiration
• Lenticular transpiration (皮孔蒸腾)约0.1% 植物的蒸腾作用绝大部分是经过叶片进行 的,称Leaf transpiration(叶片的蒸腾)。 叶片的蒸腾 • 叶片的蒸腾 角质层蒸腾 气孔蒸腾
4.2 Stomatal transpiration
• 内皮层细胞向外侧质外体吸收离子,离子 最终被转移到中柱导管,导管的离子浓度 增高而水势下降,结果水分通过内皮层细 胞渗透到中柱导管,使导管产生静水压力 即根压。 试验证明,根系高水势溶液中,伤流快; 低水势溶液中,伤流速度慢或甚至到流。
植物叶表面的润湿性及其生态学意义
Abstract: Leaf wettability,indicating the affinity for water on the leaf surface,is a common phenomenon for plants in a solid and liquid interface is an index wide variety of habitats. The contact angle ( θ) of water on leaves measured at the gas, of surface wettability,θ < 110° for hydrophilic and θ > 130° for hydrophobic. The main factors affecting leaf wettability include the wax content and crystal forms,the number and distribution of trichomes,and the shape and size of stomata and epidermal cells. The chemical composition and structure of leaf surfaces are internal causes,but the external environment can also influence wettability by affecting the structure and composition of the surface. The main ecological functions affected by leaf wettability are photosynthetic rate,interception of precipitation,pathogen infection and environmental quality. Precipitation interception on foliage surfaces is affected by high wettabilty as water droplets form a layer of film on the surface that is relatively easy retained on leaves. For low wettability or water - repellent leaves,water on the surface produces droplets that are more easily removed by wind and gravity. The spreading water film on leaves with high wettability can decrease photosynthesis due to high CO2 diffusion resistance through water to stomata. Differences in leaf wettability can influence the amount of air pollutants that can be captured,absorbed ,and filtrated by leaf surfaces; however,if air pollutants injure the leaf surface,a dramatic change in leaf surface wettability may result. For bacterial pathogens,a completely wettable leaf surface can make the leaf more susceptible to infection. Once the bacteria are disseminated,leaf
国槐花叶病
国槐花叶病
【国槐花叶病分布及危害】北京及山东颇为常见。
对幼树影响生长,导致矮生。
【国槐花叶病症状】叶面呈现不规则线条斑块,分布无定位,图案美丽。
部分叶片变小,叶色变浅。
如不细细观察,易被疏忽。
叶腋不定芽萌发时,产生弱枝及小枝叶呈丛生状。
发生在东欧,中欧或美国的,叶片变小,脉明,叶柄短,植株易受冻害,且常有多枝、黄化现象。
发生于英国的花叶,呈斑驳状,叶扭曲,木材弯曲。
病苗矮小,仅及健株一半。
寄主为国槐(Robiniapseudoacaci)及粘国槐(R.viscosa),发病率约10%。
【国槐花叶病病原】洋槐花叶病毒(RoMV)的病毒粒子最早是1961年在匈牙利分离到。
后来在南斯拉夫也有记录,认为属黄瓜花叶病毒CMV。
报道的病毒粒子大小为40nm。
用特殊方法纯化时,粒子圆形,直径27~28nm。
可由蚜虫传毒。
国内1981年有报道,病毒粒子直径为34nm。
接种苋色藜,苗叶出现圆形、褪绿晕斑;在豇豆苗,则表现系统花叶。
病毒钝化温度66~68℃,体外存活期57天,稀释终点10-4~10-5。
病毒可机械接种。
土壤不传毒。
昆虫是介体。
蚜虫(Aphiscraccivora)、桃蚜(Myzuspersicae)能非持久性带毒。
此病毒的寄主范围甚广,在10科以上。
在被子植物的自然感染症状,为系统花叶及叶片扭曲。
苋色藜、茴藜、菜豆、番茄等可作为诊
断寄主。
繁殖寄主有心叶烟及普通烟。
【国槐花叶病的防治措施】消灭蚜虫能减轻发病。
森林水文学翻译
森林水文学1.水作为生命的重要组成部分,人类不仅在水草丰美的区域放牧、在冲积平原种植作物、在主要河流和港口附近建造城市,更是在气候适宜和水资源丰富的地区孕育文明。
由此,尼罗河被称为“生命之泉”,黄河也被誉为“中华文明的摇篮”。
然而地球水资源的分布并不均匀,因此纵观历史和近代史,水资源是各国间、各国内以及群体间的主要争议。
2.的确,水资源是人类社会的关注要点。
人们担心洪涝和干旱、用水安全问题、用水权利缺乏和水资源分配状况。
大多数大学都开设了关于水资源的学科。
例如,德克萨斯州州立的16所四年制大学都开设了相关课程。
掌握关于水体性质、水环境问题和重要性以及水资源管理的知识对有效利用这种重要的自然资源是十分必要的。
3.森林的分布显著体现了森林与水分的相关性。
森林通常生长发育在年降水量≥500mm的地区,这样的区域同样适宜一定的农业活动。
土地的森林覆盖率达30%时,这30%的林地能够产生占总径流量60%的径流。
换言之,大部分饮用水源于林区。
故林区的任何活动、开发和利用都不可避免地在一定程度上破坏和扰乱了林冠和森林的枯枝落叶层。
这些行为可能通过对蒸腾作用、林冠截留损失、入渗速率、持水量和地表径流流速的作用来影响水量。
同时雨滴对裸露矿质土的直接击溅作用、根系对土壤固持作用的丧失、坡面径流的增加以及有机物的加速分解也都对水质产生了影响。
所有这些因素可能加剧土壤侵蚀和养分流失。
林地规划应考虑到森林对水资源的作用,这样才能合理保护和利用水资源。
许多问题与水和森林有关,但本书的重点是研究二者间的关系,书的开始是对水和水资源的诠释,之后陆续介绍森林和森林各项活动产生的影响。
我们都认识到这两种资源的合理管理对人类福祉极其重要,但没有基础知识、足够的研究和丰富的信息,也无法做出合理的管理。
4.调节气候:大气中的水蒸气在白天吸收和反射部分入射太阳辐射,晚上又以长波的形式为地球提供热能。
此外,由于水具有高热容和高潜热,气温高时是储存热能的良好媒介,气温低时水中储存的热能又能释放出来。
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Original ArticleWater relations of Robinia pseudoacacia L.:do vessels cavitate and refill diurnally or are R-shaped curves invalid in Robinia?Ruiqing Wang,Lingling Zhang,Shuoxin Zhang,Jing Cai&Melvin T.TyreeCollege of Forestry,Northwest A&F University,Yangling712100,ChinaABSTRACTSince2005,an unresolved debate has questioned whether R-shaped vulnerability curves(VCs)might be an artefact of the centrifuge method of measuring VCs.VCs with R-shape show loss of stem conductivity from approximately zero tension,and if true,this suggests that some plants either refill embolized vessels every night or function well with a high percentage of vessels permanently embolized.The R-shaped curves occur more in species with vessels greater than half the length of the segments spun in a centrifuge.Many have hypothesized that the embolism is seeded by agents(bubbles or particles)entering the stem end and travelling towards the axis of rotation in long vessels,causing premature cavi-tation.VCs were measured on Robinia pseudoacacia L.by three different techniques to yield three different VCs; R-shaped:Cavitron P50=0.30MPa and S-shaped:air injec-tion P50=1.48MPa and bench top dehydration P50= 3.57MPa.Stem conductivity measured in the Cavitron was unstable and is a function of vessel length when measured repeatedly with constant tension,and this observation is dis-cussed in terms of stability of air bubbles drawn into cut-open vessels during repeated Cavitron measurement of conductiv-ity;hence,R-shaped curves measured in a Cavitron are prob-ably invalid.Key-words:Cavitron;centrifuge method;exponential curves; vulnerability curve.INTRODUCTIONPlants transport metastable water(tensile water)under nega-tive pressure(Tyree&Zimmermann2002).The transport system is vulnerable to embolisms because if an air bubble enters a conduitfilled with tensile water,the bubble(or vacuum void)will expand tofill the entire conduit,rendering it incapable of further transport of tensile water until it can be refilled by some mechanism.Transport of tensile water is possible because of the unique structure of xylem conduits, which tend to be numerous for pathway redundancy and separated from each other by pit membranes that prevent passage of air from an embolized to water-filled conduit. Different species have different conduit structures,which confer different vulnerabilities to cavitation events.Smaller vessels tend to be safer than large vessels(Cai&Tyre2010), but it is the porosity of the pit membranes between adjacent vessels that seems to be of paramount importance because the surface tension of water acting at the pit membrane site prevents bubble propagation between adjacent vessels(Tyree &Zimmermann2002).A vulnerability curve(VC)is a plot of the percentage loss of hydraulic conductivity(PLC)in stems as a function of tension(minus xylemfluid pressure).A large number of articles have revealed two kinds of VCs classified by their shape:R-shaped(or exponential)curves tend to increase in PLC from zero tension,whereas S-shaped(or sigmoid)curves tend to be at zero PLC for a range of tensions to a critical tension(T crit),beyond which PLC increases rapidly to100%following a sigmoid curve as tension increases. Plants with S-shaped curves are conservative because their stomata remain partly open,permitting carbon gain and tran-spiration until xylem tension reaches T crit and then the stomata close to prevent excessive embolism in the stems.In contrast,plants with R-shaped curves suffer substantial PLC every day,but keep their stomata open while the stems lose 50–90%of their water conductivity.These plants seem to survive day to day by having a mechanism to refill conduits every night(Cochard et al.2013)or by surviving with only a small percentage of functional vessels.Species that refill diur-nally are relatively rare but increasing numbers have been reported[see,e.g.Vitis(Brodersen et al.2010),Acer and Fraxinus(Zwieniecki&Holbrook1998),Quercus(Taneda& Sperry2008;Sperry et al.2012),Laurus(Salleo et al.1996), Taxus(Zhang&Richter1996)and Robinia(An et al.2006)]. Recently,Sperry(2013)and Wheeler et al.(2013)have questioned the veracity of evidence for refilling in many species.Refilling is usually measured by observing diurnal changes in native PLC(NPLC),but these measurements are subject to error if stem segments are harvested while still under tension.Cutting stems under tension seems to induce extra embolisms not present before the cutting.Because air bubbles take hours to days to dissolve once tension is relieved(Tyree&Yang1992;Yang&Tyree1992),it is rec-ommended that stems be harvested and rehydrated prior toCorrespondence:J.Cai.Fax:+8602987080363;e-mail:cjcaijing@;and M.T.Tyree.Fax:+8602987080363;e-mail:mel.tyree@Plant,Cell and Environment(2014)doi:10.1111/pce.12315©2014John Wiley&Sons Ltd1excising the stem segments used to measure NPLC.Still,any species with an R-shaped curve is a candidate for a species that might cavitate and refill diurnally.Much debate in the literature has been directed also to the veracity of R-shaped VCs measured by some centrifuge tech-niques(particularly the Cochard Cavitron).If R-shaped curves are an artefact of measuring technique,then the number of potential candidates for diurnal refilling can be dramatically reduced.In a critical review of methods of measuring VCs,Cochard et al.(2013)showed that R-shaped curves are more common in species with long vessels and the percentage of species with R-shaped vessels seems to be a function of the method used to measure VCs.When a Sperry-type centrifuge is used,85%of long-vessel(ring porous) species appear to have R-shaped curves versus<25%when measured by more traditional methods(bench top dehydra-tion and air injection).Given the concerns regarding the above methodological techniques of measuring NPLC and VCs,all species that have been reported in the past to have R-shaped curves or reported to refill diurnally have to be re-examined.The aims of this article are(1)to re-examine Robinia pseudoacacia and(2)to gain further insights into the cause of R-shaped curves in species measured in the Cochard Cavitron.It has been suggested,for example,that R-shaped curves are the result of pre-mature embolism caused in long-vessel species because air bubbles or solid particles can travel to the centre of the axis of rotation in a centrifuge where the highest tension exists,and hence,the bubbles or particles can expand to seed embolisms.In contrast,in short-vessel species,such particles arefiltered out by pit membranes and do not induce cavitation near the centre.Our hypothesis is that air bubbles,if present,ought to induce cavitation at a very small tension(T≤0.1MPa)because the critical tension for bubble expansion=2τ/r,whereτis the surface tension of air–water interface and r is the radius of the bubble.An air bubble is‘more vulnerable’than a solid particle because it will expand tofill the entire conduit even before tension exceeds the pressure equivalent of a perfect vacuum(about 0.1MPa),whereas a solid particle might not seed a cavita-tion until much larger tensions.Therefore,if you simply spin stems with long vessels at T≤0.1MPa long enough,then substantial increases in PLC are ought to be observed due to air bubbles.MATERIALS AND METHODSPlant materialExperiments were conducted from May to December in2013 on R.pseudoacacia L.trees growing about5m above the water level on the bank of the Weihe River in Yangling, Shaanxi,China(34°16′N108°4′E,457m a.s.l.).Most samples were collected from four trees of5–7m tall.All of the meas-urements were carried out on current-year stems harvested from the southern crown of the trees.For laboratory experi-ments,shoots of1.4–2m long were excised because prelimi-nary air injection experiments indicated that maximum vessel length was<1m.After spraying leaves with water,branches were enclosed in humidified black plastic bags before excising to retard water loss.The shoots were brought to the laboratory within half an hour after excision and sub-merged in water for at least30min to release the xylem tension.Length of vesselsVessel length was measured by the‘air method’as described by Cohen et al.(2003),with some modification.Briefly,long shoots were cut with a sharp razor blade and injected with compressed air(0.15MPa)from the distal side of6-mm-diameter stems while the basal end was immersed in water. Stem segments(2cm long)were sequentially excised until bubbling was observed,and the length of remaining stem was recorded as the maximum length of the vessel.The bubblesflowing out from the basal end were collected in a volumetric cylinder by the water displacement method, and the volume of air was determined when the water surface inside and outside the cylinder were at the same level in order to be sure that the air volume was measured at atmos-pheric pressure.The gravimetric water displacement method was used to measure air volume since this allowed more precision than reading the scale on the volumetric cylinder. Firstly,the cylinder wasfilled to the top with water,and then the water was delivered to a balance to measure the maximum water content(W i).After measuring the air dis-placement for a measured time interval(ΔT),the cylinder was held at a shallow angle with the open end below the water and the air/water interface at the water level.The end of the cylinder was covered to avoid spilling of water and the cylinder was lifted out of the water.The water remaining in the cylinder was again delivered to a balance and measured (W f).The airflow rate[Q(mL/min)]was computed from (W i−W f)/(ΔTρ),whereρis the density of water displaced by the air.The airflow rate[Q(mL/min)]was measured at different stem lengths with the air pressure at the inlet and outlet ends being held constant.Under such conditions of constant air pressure drop,the hydraulic conductivity of the cut-open vessels to the air(C)should be proportional to Qx(see eqn 4in Cohen et al.2003),where x is the stem length at which the airflow rate(Q)was ing the theory of Cohen et al.(2003),we assume thatC C kx Qx Q x kx=−()=−()000exp expor(1)where C0is the limiting conductivity as x approaches zero,k is an extinction coefficient and x is the stem length.A plot of natural log of C versus x resulted in a linear plot,from which k was evaluated from the slope.According to the theory,the most common or mode vessel length(L mode)equals−1/k. Mean vessel length was calculated from L mean=2L mode. Similar measurements were carried out on other shoots,with the difference that air was injected from the basal end of the stem segment,and we found no significant difference in the computed mean and mode vessel lengths.2R.Wang et al.©2014John Wiley&Sons Ltd,Plant,Cell and EnvironmentKeeping solutions cleanOur laboratory started doing repeated cycles of embolism and flushing on the same stem and we discovered that extraordinary steps had to be taken to prevent plugging in long stem segments (0.274m)and to achieve the same K max after each cycle.An ultra-pure water system (model GYJ1-10L-S;Huachuang Inc.,Chongqing,China)was used to make water with particles <10nm in diameter (guaranteed to produce <1particle/mL)and the ultra-purer water was used to make 0.1m KCl solution.Flushing was carried out with degassed KCl solution stored in a stainless steel captive air tank (model 3400-002;SHURflo Inc.,Cypress,CA,USA).Even stainless steel rusts a little when in contact with KCl,so to eliminate plugging rust particles,the tank was disassem-bled and cleaned two to three times per week.Stainless steel surfaces remain shiny because the rust particles easily fall off the surface of stainless steel;other metallic tanks should be avoided.Post-filtering of flushing solution was carried out through an in-line filter (0.3μm porousity,model 9933-05-AAQ;Parker Hannifin Corp.,Rochester,NY,USA).Further-more,the water in the captive air tank needs to be left unpressurized when not used for flushing;otherwise,air migrates through the rubber bag in sufficient quantity to supersaturate the water with air,which effervesces like flat soda water when depressurized.All of the above steps are necessary for consistent results.Vulnerability curvesVCs were measured by the Cochard Cavitron technique (Cochard 2002;Cochard et al .2005)using a custom-modified centrifuge.Details about the construction and use of the Cochard Cavitron are described in Cai &Tyree (2010).Briefly,the Cavitron allows measurement of stem-segment hydraulic conductivity while the stems are spinning in a cen-trifuge.The maximum conductivity (K max )was measured at a slow spin rate,which causes little or no embolism.Increasing the spin rate increased the tension (T )and the stem conduc-tivity K h declined.Percentage loss conductivity was com-puted fromPLC K K =−()1001h max (2)at each T .VCs were measured on stem segments that are 27.4cm long,and the typical curve contained 30–50points of PLC versus T .Each point in the VC was the mean of 5–8measurements of PLC at any given T and the VCs were fitted to a single Weibull curve (Eqn 3a)or a dual Weibull curve (Eqn 3b)using the software (CavAnal)written by MTT:PLC T B C1001=−−()⎡⎣⎤⎦exp (3a)PLC T B T B C C 1001111122=−−()⎡⎣⎤⎦{}+−()−−()⎡⎣⎤⎦{}ααexp exp (3b)where the Weibull constants were obtained by minimizingroot mean square error (RMS error ).Typical fitted VCs had anRMS error of 2–4%.The value of T at 50%PLC (P 50)was then computed fromP B C5012=()[]ln (4)VCs were measured on both flushed and unflushed stems (with native embolism of about 30%).Preliminary experi-ments revealed that a flush time of 4min at 150kPa pressure was adequate to reverse embolism because of the long vessels in our species.In contrast,flush times of 30min are needed for species with short vessels (6cm long),based upon other experiments carried out at the same time on a Populus clone.VC measurements and flushing were carried out with the ultra-pure water used to make 0.1m m KCl.Diurnal variation of native xylem tensionNative xylem tensions (T nx )were measured by the bagged-leaf technique using a portable pressure chamber (model 1515D;PMS Instruments Co.,Corvallis,OR,USA).T nx was determined by sealing a leaf in a Ziploc bag covered with aluminium foil bag in order to stop transpiration from the bagged leaf.Leaves remained in the shaded bags >1h prior to harvest for pressure chamber measurement,at which point the leaves are in equilibrium with T nx in stems.Measurements were conducted on 3hot and sunny days from 0530h (pre-dawn)to 2030h (after the sunset)at 1h intervals each day.Generally,6–10replicate measurements of T nx were per-formed at each hour.The time of maximum T nx value also was used for the sampling time determination in NPLC measurements.Pre-dawn and midday NPLCThis experiment was conducted in May 2013.Pre-dawn samples were collected before sunrise between 0530and 0600h on sunny days.Midday samples were collected between 1400and 1500h on the same day with the pre-dawn PLC test.PLC s of pre-dawn and midday stems were assessed by low pressure flow meter (LPFM)as described by Tyree et al .(1993),with some modification.Shoots were sprayed with water,enclosed in a black plastic bag,excised and then returned to the laboratory within 30min.Whole shoots were placed under water for at least 30min to release tension,and then leaves were excised under water to further release tension.These steps were designed to avoid embolism induced by cutting before relaxation of native tension (Wheeler et al .2013).Approximately 2-cm-long stem seg-ments with a diameter about 6.5mm were excised under water,then mounted on a conductivity system filled with ultra-pure,degassed 0.1m KCl solution pre-filtered to 10nm and post-filtered to 0.3μm.Initial conductivity (K h =K i )was measured by flowing KCl solution from a reservoir through the segment and onto a computer-interfaced balance with a pressure difference of about 3kPa.The stems were then flushed with a pressure of 150kPa for 1min to remove air bubbles.The hydraulic conductivity was determined again and the flushing was repeated until attaining a maximumRobinia water relations 3©2014John Wiley &Sons Ltd,Plant,Cell and Environmentconductivity (K max ).PLC was calculated from Eqn 2.The tubing and valves of the LPFM were cleaned weekly by filling tubing and valves with Clorox bleach (2%)and allowing it to stand for 24h (or 4%bleach overnight).VCs by bench top dehydrationVCs by bench top dehydration (Tyree &Dixon 1986;Sperry et al .1988)were constructed by plotting stem PLC s against corresponding xylem tension values measured on bagged leaves.Shoots were sampled in the morning and dehydrated on a bench in the laboratory at room temperature to obtain a series of xylem tensions covering a range of PLCs .Dehy-dration times never exceeded 24h and usually took less than 6h.The whole shoot was tightly wrapped in a black plastic bag once the shoot had reached the desired tension.After a minimum of 1h of equilibration,three leaves were excised from the shoot,and the leaf balance pressure was measured with pressure chamber (model 1505D;PMS Instruments Co)and the balance pressure equated to T nx .Soon after excising the leaves,PLC due to embolism was measured with the LPFM technique (measured on six 2-cm-long stem segments harvested under water from each shoot)as described before.Traditionally,stems are not flushed when VCs are measured by the bench top dehydration method;hence,native PLC was factored out of the bench top dehydration VCs using Eqn 5:AdjPLC T PLC T NPLC NPLC ()=()−[]=−()100100(5)where AdjPLC (T )is the adjusted PLC at xylem tension (T )and PLC (T )is the PLC measured by the bench top method at any given T before correction for NPLC .Equation 5basi-cally re-scales the uncorrected VC by a constant factor of [100/(100−NPLC )],which starts at the NPLC at low tension and increases to PLC (T )=100%at maximum tension.VCs by air injection using a pressure collarA pressure collar (model 1505D-EXP;PMS,Albany,OR,USA)was used to measure VCs according to Cochard et al .(1992)and Ennajeh et al .(2011).Briefly,stem segments of 15or 27.4cm long were harvested as above and flushed to achieve maximum hydraulic conductivity;the bark was removed from the central portion of the segment equal to the length of the pressure collar (8cm),and mounted on the collar.The segment,while mounted on the collar,was con-nected to a LPFM for the measurement of K max ,as described earlier,and then removed from the LPFM and immersed in water while still connected to the collar.Segments were exposed to each test pressure for 10min.At all times,the segment ends were immersed in water to observe bubbling of air that resulted from embolism under positive pressure.After the 10min exposure,the pressure was returned to atmospheric and we waited until the bubbles had stopped flowing out of the ends (for 30min or more)and then the K h of the stem segment was measured in the LPFM.PLC was calculated from Eqn 2.Measured and predicted NPLCNPLC measurements were conducted in August on sunny days with maximum temperature above 31°C.Shoots were sampled in the afternoon between 1400and 1500h.Leaf balance pressure =the native xylem tension (T nx )was meas-ured by the pressure chamber method prior to excising shoots.NPLC was computed from K h measured on 27.4-cm-long segments by two techniques:the LPFM technique and the Cavitron technique.In the Cavitron technique,the cen-trifuge was used to measure K i and K max before and after flushing at 500r.p.m.(T =0.022MPa at the centre).The K h values were also measured by the LPFM technique.The dif-ference between techniques is the tension.K h was measured at either positive pressure or a small sub-atmospheric pres-sure.The process for LPFM test was similar to the pre-dawn PLC test,with the difference that 27.4cm stems were used.K i and K max measurements were made at 500r.p.m.(tension =0.022MPa)after spinning for 40min.Predicted NPLC was calculated from VCs measured on flushed samples in the Cavitron using the native tension T nx measured in the field at the time of collection.Stomatal conductanceStomatal conductance (g s )was measured using a Li-6400XT portable photosynthesis system (Li-Cor Inc.,Lincoln,NE,USA)in a sunny day in August.Ten leaves from the four sample trees were tagged and measured from 0700to 2000h at 1h intervals.Leaves were measured with natural sunlight,air temperature and ambient CO 2while keeping the leaves in their native growing position during the measurement.Anatomical observations and stainingStem segments were stained to determine the diameter of conducting (stained)and embolized (unstained)vessels by a technique,as described in Cai et al .(2014).Shoots (>1.4m in length)were collected in the afternoon between 1400and 1500h.Four stem segments 2cm long and 6.5mm in diameter were excised under water.Then,the segments were perfused with 0.02%(w/v)dying solution (basic fuchsin +0.1m KCl)at a pressure of 3kPa.Four segments were perfused for 15min,30min,1h and 2h,respectively.Then,segments were flushed with 0.1m KCl at 130kPa for 5min to remove excess stain.A microtome (Leica RM 2235,Nussloch,Germany)was used to cut 18-μm-thick cross sec-tions from the middle of the 2cm segments.Four sections were washed in graded ethanol (35,50,75and 95%)for ≥4s and mounted in glycerin on glass slides.Cross sections were photographed under a microscope (Zeiss,Imager A2,Göttingen,Germany)at 100×magnification with a digital camera (Infinity1-5C,Lumenera Corporation Ottawa,Canada).The RGB colour values,exposure,gamma and colour saturation were adjusted to yield suitable image quality using the software called Infinity Capture Application (Version 6.0.0,Lumenera Corporation Ottawa,Canada).Stained and unstained vessel areas (A )were measured with4R.Wang et al .©2014John Wiley &Sons Ltd,Plant,Cell and EnvironmentWinCell Pro version2012a(Regent Instruments Inc.,Quebec City,Canada)and equivalent diameters(D)were computed from D=2(A/π)1/2.RESULTSDiameter and length of vesselsThe frequency distribution of vessel diameter–percentage of vessels versus bin diameter size class(D)–is shown in Fig.1a together with the hydraulic weight of the size classes.The hydraulic weight of each size classes is defined as% vessels×D4in each diameter size class.The fourth power is used to weigh the hydraulic conductivity of each bin size class according to the Hagen–Poiseuille law.It can be seen that large-diameter vessels have a disproportionate hydraulic weight relative to the percentage of each bin diameter size class.Staining was used to determine which vessels were embolized(unstained)in the native state;the number of embolized vessels was269compared to the total vessels measured,1239(stained and unstained).In terms of hydrau-lic weight,the embolized vessels tended to be a little smaller, where the mode diameter of embolized vessels was about 60μm versus75μm for all vessels.We chose to measure vessel length by the air injection technique(Cohen et al.2003)because it also averages (weighs)the vessel length towards the more conductive con-duits.In the air injection technique,one can plot ln(C/C0) versus distance from the air injection surface,where C is the pneumatic conductivity of the stem at distance x and C0is C at x=0.The use of C for pneumaticflow is similar to water flow,which,like the Hagen–Poisseuille law,weighs airflow by the fourth power of the diameter of the conduit through which the airflows.According to Cohen et al.(2003),the slope of ln(C/C0)versus distance x from the injection surface can be used to calculate vessel length.Three representative plots out of12experiments in which air was injected from the apical or basal end of six stems each are shown in Fig.1b. Other advantages of the air injection technique are that it is faster than other standard techniques(Cai et al.2010)and has a high R2(≥0.99)for the regression of the plot of ln(C/C0) versus x used to determine mean vessel length.Afinal advan-tage of normalizing the plot of C to C0,that is,ln(C/C0),is that the anti-log directly yields the fraction of vessels still open at any given distance x from the injection surface(see right axis values in%in Fig.1b).There was no significant difference between vessel length computed whether air was injected from the apex or base of stems,so the values were pooled to yield a mean vessel lengthof20±1.9cm(n=12);all errors in this article are standard errors of the mean,unless otherwise stated.However,there was a large variation in the mean vessel length between stems between a maximum and minimum of30.0and12.7cm, respectively.The length of stem segments used in our Cavitron is27.4cm,the mean vessel length and percentage of vessels still open at the length and half-length of these seg-ments are given in Table1for each segment as well as the overall means.VCs measured by three methodsThe VCs of Robinia measured by the Cavitron technique exhibited‘R’-shaped curves(Fig.1a).The curves werefitted by both single and dual Weibullfits(Eqn3a and3b);the dual Weibull functionfitted significantly better than thatfitted by a single Weibull function(Table2).The PLC rose fast with the increase of tension(induced by centrifuge)from0%at 0.022MPa to about78%at0.599MPa.The increase ofPLC Figure1.(a)Frequency distribution of vessel diameters plottedas percentage of vessels(y-axis)in each bin diameter size class(x-axis).Diamond points are a plot of the percentage of vessels in each diameter size class on the x-axis.The hydraulic weight(%ineach class)is defined as y D y Di i i i44∑(),where y i is the percentage value on the y-axis of the diamond points and D i is the diameter size class on the x-axis for the diamond points.The solid squares are the hydraulic weight of all vessels(n=1239vessels)and open squares are the hydraulic weight of embolized vessels in the native state(n=269vessels).(b)Three examples of air injection data for the determination of vessel length.Each data set contains at least 7points,but some points used in the regression are beyond the maximum value of x(distance from the air injection surface).The y-axis is the natural log of C[pneumatic conductivity divided by C0 (the limiting value of C as x approaches zero)];C0is derived from the y-intercept of the regression of ln(C)versus x.The advantage of normalizing the plot to C0is that the anti-log(shown on the left axis)equals the fraction of vessels still open at distance x;theanti-log is given as a percentage on the right-hand vertical axis.A1 and A2are branches injected from the apex and B1was injected from the base.The slopes of the regressions are given in thefigure and mean vessel length=−2/slope.Robinia water relations5©2014John Wiley&Sons Ltd,Plant,Cell and Environmentslowed down as the tension grew higher than0.599MPa and reached95%at2.947MPa.The shapes of VCs were not dramatically changed regardless of whether there isflushing (Fig.2a)or not(Fig.2b)prior to the VC measurements,and the P50values were not significantly different(P=0.941), with the values of0.319and0.323MPa forflushed and unflushed stems,respectively.The VC constructed by the bench top dehydration tech-nique is shown in Fig.2b,which displayed an S-shaped curves.The PLC stayed at low levels(<10%)until tension exceeded2.9MPa.PLC dramatically increased from6.39to 97.27%as xylem tension rose from2.9to4.6MPa.The P50 equalled3.57MPa for bench top dehydration,which was about11times the P50value calculated from Cavitron VCs. The VCs obtained by the air injection technique were also of S-shaped but intermediate between the R-shaped Cavitroncurves and the S-shaped curves obtained by bench top dehy-dration(see Table2for parameters and statistics).The ques-tion is which VC is correct?Some clues can be gained byexamining the water relations of the species below. Diurnal water relations and native PLCof RobiniaThe diurnal variation of the water relations of Robinia on3sunny days in August is shown in Fig.3a.The balance pres-sure of transpiring leaves provides an undefined estimate ofminus leaf water potential(P b,leaf≅−Ψleaf).The estimate is undefined because a transpiring leaf has a water potentialgradient that disappears when the leaf is enclosed in a pres-sure chamber;after the leaf is equilibrated in the pressurechamber,the balance pressure equals the xylem tension,which,in turn,equals the water potential minus the xylemosmotic pressure.The balance pressure of bagged leaves istraditionally taken as a measure of the native tension of stemxylemfluid(T nx).From Fig.3a,we can conclude that stemsand leaves rehydrate to a balance pressure<0.3MPa over-night and rise to approximately1.6and1.8MPa by midday,respectively.In contrast,stomatal conductance(g s)peaks at0800h when stem and leaf balance pressures are about0.8and 1.1MPa,respectively.Partial or complete stomatalclosure is often viewed as a mechanism to avoid excessiveembolism in stems,and in most cases,the minimum g s occursquite near the inflection point of the VC of the species inquestion,that is,when PLC≤10%(Cochard et al.1996).Inthis context,the stomatal behaviour seems tofit superficiallybest with the air injection VC,which reaches10%PLC atabout1MPa(Fig.2b).However,it couldfit with the benchtop dehydration VC if we argue that Robinia is very con-servative in its water relations(see the Discussion section formore details).On the contrary,Robinia has been described asTable1Shown are vessel lengths of n=12stems injected with air from the apex or baseMethod Vessel length(cm)%>27.4cmlong%>13.7cmlongLongestvessel(cm)Apex injection17.2 4.1%20.3%61Apex injection32.0(max)18.0%42.5%59Apex injection19.2 5.8%24.0%57Apex injection16.8 3.8%19.5%54Apex injection15.9 3.2%17.8%56Apex injection27.914.1%37.5%58Base injection14.9 2.6%16.0%32Base injection29.015.1%38.9%53Base injection22.18.3%28.9%46Base injection12.7(min) 1.3%11.6%44Base injection16.3 3.4%18.5%51Base injection16.1 3.3%18.2%42Mean20.0 6.9%24.5%SD 6.3 5.7%10.1%SE 1.9 1.7% 3.0%Maximum and minimum values are indicated in the table;however,in Fig.4b,we report a mean vessel length of5.2cm in one stem segment.The longest vessel length has a resolution of2cm(=length of segments excised).Table2Shown are the parameters from the single and dualWeibullfits(WF)in Eqns3a and3b,respectivelyDual WFMean SD SE P1/2B10.2800.0810.0220.223C1 1.5950.7170.199B2 1.695 1.0370.288 1.261C2 1.2400.7310.203α68.210.389 2.881RMS error 2.3930.8540.237Single WFMean SD SE P50B0.4360.1240.0340.295C0.9390.2330.065RMS error 5.516 1.0270.285The RMS error of thefits are significantly different(P<10−8),n=14.6R.Wang et al.©2014John Wiley&Sons Ltd,Plant,Cell and Environment。