水稻根表铁膜吸附镉及植株吸收镉的动态

采用营养液培养法研究了Cd处理时间对有铁膜和无铁膜水稻根表吸附Cd及植株吸收Cd动态变化的影响.水稻根表铁膜由50 mg·L^-1 Fe^2＋（Fe₅₀）诱导形成.供试植株在含10 μmol·L^-1Cd的营养液中生长不同时间后收获.结果表明, 随Cd处理时间的延长,无铁膜和有铁膜处理水稻根表DCB-Cd含量均为先增加后减少,Cd处理2 h达到最高,之后逐渐下降并趋于稳定. 根系和地上部Cd含量均持续上升,Cd处理8 h前增加缓慢,8 h后增加幅度加大.有铁膜水稻根系和地上部Cd含量增加幅度均低于无铁膜水稻.有铁膜处理DCB-Cd含量、根系和地上部Cd含量均低于无铁膜处理.表明铁膜不影响水稻各部分Cd含量随时间的变化趋势;不同Fe处理之间根系和地上部Cd含量的差异可能与根系含Fe量有关.     

根区通氧状况对水稻幼苗生长及吸收镉的影响

采用水培的方法研究了根区通氧状况对水稻根系结构、根系泌氧、根表铁膜生成以及水稻耐受、吸收Cd的影响.水培条件下,根区氧处理对水稻幼苗的生长产生了一定的影响,缺氧条件下的水稻根的伸长量降低,生物量增加,直径增粗,根系泌氧量增加,并降低幼苗对Cd的吸收.当培养溶液Cd2+浓度为1.0 mg/L时,缺氧处理相对于通氧处理,根表吸附的Cd降低了85 5%,地下部分吸收的Cd降低了35%,转运到地上部分的Cd降低了58%.根表铁膜对Cd的吸收和转运也有一定的抑制作用,但其作用因环境中Cd2+浓度和根区通氧状况而异.在根区通氧充分的培养条件下,水稻幼苗铁膜对较高浓度Cd2+(1.0 mg/L)的吸收和转运起着重要的作用,DCB-Cd占根系吸收Cd的50%,茎叶对Cd的吸收显著降低(p<0.05).研究表明在缺氧胁迫下,根系结构本身(如根表通透性降低)是影响水稻吸收Cd的重要因素.     

不同耐性水稻幼苗根系对镉胁迫的形态及生理响应

采用水培试验,以两个耐镉性不同的水稻品种为材料,研究了不同浓度镉胁迫对水稻幼苗根系形态、根系活力、游离脯氨酸含量及抗氧化酶活性的影响。结果表明:低于5 μmol/L Cd胁迫对2个水稻品种总根长、根表面积、根体积、根干重、根系活力无明显影响,在1 μmol/L Cd时,甚至起促进作用。随Cd浓度增加表现出一定的抑制效应,秀水63在10 μmol/L Cd胁迫下根系形态、根系活力明显受到抑制,而秀水09在25 μmol/L Cd胁迫下明显受抑。随Cd胁迫浓度的增加,游离脯氨酸含量、丙二醛(MDA)含量、超氧化物歧化酶(SOD)、过氧化物酶(POD)活性均呈上升趋势,两品种相比,秀水09的游离脯氨酸含量、SOD和POD增幅大于秀水63,而MDA含量增幅小于秀水63;过氧化氢酶(CAT)活性变化表现为先上升后下降,10-100 μmol/L Cd胁迫下秀水63根系中CAT活性明显低于秀水09。总之,水稻对Cd毒害响应存在明显的品种差异,且Cd胁迫下根系生理响应的差异是品种间耐性差异的重要原因之一。     

铁镉互作对水稻脂质过氧化及抗氧化酶活性的影响

利用营养液培养方法,以‘沈农265’为供试品种,研究不同Fe(0、0.1、0.25、0.5 mmol Fe²⁺·L^-1 )、Cd(0、0.1、1.0 μmol Cd²⁺·L^-1)处理对水稻植株体内脂质过氧化及抗氧化酶活性的影响.结果表明： 单独供应Fe显著降低了水稻地上部和根系生物量,同时供应Cd后生物量不再下降;单独供应Cd降低了根系中丙二醛(MDA)和可溶性蛋白含量,而同时供应Fe时这种降低作用消失.Fe处理降低了水稻地上部和根系Cd含量,Cd处理也降低了Fe含量,两者表现出明显的相互抑制作用.高Cd(1.0 μmol·L^-1)和Fe互作,增加了水稻根系中MDA和可溶性蛋白含量,降低了超氧化物岐化酶(SOD)和过氧化氢酶(CAT)活性.表明在低Cd环境中为水稻提供一定数量的外源Fe能降低植株Cd含量;但高Cd胁迫将降低水稻对Fe的吸收,并导致植株体内产生脂质过氧化.     

镉对水稻种子萌发的影响

以不同类型的319个水稻品种为研究对象,研究了10 mg·L^-1 Cd²⁺处理对水稻种子萌发的影响.结果表明:Cd²⁺对种子发芽率影响较小,对根系生长的影响显著,且大于对芽生长的影响;不同类型水稻种子萌发对Cd的响应差异较大,敏感顺序为粳稻>籼稻>杂交稻;两系不育系根系长度和根系数量受Cd的抑制程度显著高于三系.应用快速聚类方法,可以将参试品种划分为耐受型、中间型和敏感型3种不同的敏感类型.     

铁镉互作对水稻脂质过氧化及抗氧化酶活性的影响

利用营养液培养方法,以‘沈农265’为供试品种,研究不同Fe(0、0.1、0.25、0.5mmolFe2+·L-1)、Cd(0、0.1、1.0μmolCd2+·L-1)处理对水稻植株体内脂质过氧化及抗氧化酶活性的影响.结果表明:单独供应Fe显著降低了水稻地上部和根系生物量,同时供应Cd后生物量不再下降;单独供应Cd降低了根系中丙二醛(MDA)和可溶性蛋白含量,而同时供应Fe时这种降低作用消失.Fe处理降低了水稻地上部和根系Cd含量,Cd处理也降低了Fe含量,两者表现出明显的相互抑制作用.高Cd(1.0μmol·L-1)和Fe互作,增加了水稻根系中MDA和可溶性蛋白含量,降低了超氧化物岐化酶(SOD)和过氧化氢酶(CAT)活性.表明在低Cd环境中为水稻提供一定数量的外源Fe能降低植株Cd含量;但高Cd胁迫将降低水稻对Fe的吸收,并导致植株体内产生脂质过氧化.     

不同性别桑树幼苗对镉与酸雨复合处理的生长响应及镉积累差异

为研究不同性别桑树在镉(Cd)与酸雨(AR)复合处理条件下的生长与镉积累差异,本试验以‘强桑1号’(雌株)和‘农桑14号’(雄株)两种不同性别桑树为材料,研究重金属镉(100 mg·kg^-1干土)和模拟酸雨(pH 3.0)处理下,两者生物量积累和分配、最大净光合速率(A_max)和叶绿素荧光参数,以及Cd积累与分配的差异.试验共设置无Cd和AR(对照)、单独Cd、单独AR、Cd+AR复合4个处理.结果表明:单独Cd处理虽然显著增加了雌株和雄株根茎叶中Cd含量,而且雌株各部分Cd含量显著高于雄株,但是只有雄株根、茎和总生物量、最大净光合速率显著下降,而雌株除了A_max显著下降外,各部分生物量积累下降均不显著,且两者的最大光化学效率(F_v/F_m)、光化学淬灭系数(q_P)和非光化学淬灭系数(q_N)均未发生显著变化.复合处理下,雄株和雌株的总生物量、A_max均显著降低,与单独镉处理相比,雌株根和叶中的Cd含量显著升高,但雄株没有明显变化,两者的F_v/F_m、q_P没有显著变化,但q_N均显著降低.短时间处理下桑树雌株对单独镉胁迫的耐受性高于雄株,但是酸雨的加入会降低雌株对镉的耐受性,可能是因为酸雨促进雌株根系对镉的吸收,并导致叶片积累了更多的镉.     

硅素对水稻幼苗镉积累及抗胁迫应答的调节效应

施硅(Si)可以显著缓解镉(Cd)胁迫对水稻生长发育的毒害效应。本研究通过水培分根试验,研究了Si对水稻幼苗Cd积累及胁迫应答的调节效应。结果表明: Cd胁迫下水稻幼苗的生物量显著降低,加Si可以显著缓解Cd对水稻幼苗生长的抑制效应。水稻幼苗对Cd的吸收、转运和积累明显受到Si的影响,单侧根系Cd胁迫下加Si(Si-Cd+Si,Si-Cd)使根系对Cd的滞留系数达83.3%～83.6%,限制了Cd从根向地上部转移。单侧根系Cd胁迫下非胁迫侧加Si(Si-Cd)处理的植株对Cd的吸收和累积明显增加,尤其是根中Cd的积累量较单侧根系Cd胁迫下无Si(CK-Cd)处理增加了48.2%;而单侧根系Cd胁迫下双侧加Si(Si-Cd+Si)处理则显著降低了根和地上部对Cd的吸收,较CK-Cd处理分别降低了36.7%和54.9%。双侧Cd胁迫下单侧加Si(Cd-Cd+Si)则使根和地上部对Cd的吸收量显著减少,较双侧根Cd胁迫(Cd-Cd)处理分别降低了57.8%和46.5%。Cd胁迫下水稻幼苗根中含较高浓度的Si,加Si则使Cd胁迫下根和地上部积累更多的Si。加Si也影响了水稻幼苗对其他金属元素如钙(Ca)、镁(Mg)、锰(Mn)的吸收,Cd-Cd+Si处理显著增加了根系和地上部的Ca、Mg浓度,但Mn浓度的变化则因Cd胁迫程度而表现不同。加Si对Cd胁迫下根系超氧化物歧化酶(SOD)和过氧化物酶(POD)活性有一定的影响,尤其是Si-Cd处理的胁迫侧POD和非胁迫侧SOD活性显著上升,有利于清除Cd胁迫产生的氧自由基。总之,Si对Cd胁迫下水稻幼苗生长、Cd和Si等的吸收及根系的抗氧化反应有一定的调节效应,植株体内较高的Si浓度有利于增强植株对Cd的耐受性。     

不同有机肥对土壤镉锌生物有效性的影响

在南方典型稻田设置连续4年施用猪粪、鸡粪、稻草的定位试验,监测施用不同有机肥条件下土壤及水稻植株镉(Cd)、锌(Zn)含量的变化,研究有机肥对土壤Cd、Zn活性及其交互作用的影响.结果表明: 施用有机肥(猪粪、鸡粪、稻草)对土壤全Cd、有效态Cd含量及Cd活性皆无显著影响,但有增加土壤Cd全量的趋势,且显著增加土壤全Zn、有效态Zn含量及Zn活性.施用猪粪、鸡粪、稻草皆可降低稻米Cd含量,降Cd效果为猪粪>鸡粪>稻草,猪粪处理水稻稻米、茎、叶Cd含量分别比对照下降37.5%、44.0%、36.4%;鸡粪处理水稻米、茎、叶Cd含量分别比对照下降22.5%、33.8%、22.7%;而稻草处理水稻米Cd含量比对照下降7.5%,但茎、叶Cd含量比对照分别增加8.2%、22.7%;施用猪粪、鸡粪降低稻米Cd含量主要是降低了水稻植株对土壤Cd的富集,而施用稻草则主要是降低了水稻茎Cd向稻米的转运.施用有机肥还增加了水稻茎Zn含量,施用猪粪、鸡粪、稻草的水稻茎Zn含量比单施化肥分别增加53.4%、41.2%、13.9%,但对水稻稻米、叶Zn含量无显著影响.Zn、Cd在土壤、植株茎中皆表现出显著的拮抗作用,土壤及水稻茎Zn含量的增加显著抑制了水稻米、茎、叶对Cd的吸收积累,且随土壤有效态Zn/Cd含量比值的增加,Zn、Cd竞争土壤吸附不是抑制水稻吸收积累Cd的主控因子,而Zn、Cd竞争吸收才是影响水稻吸收积累Cd的主控因子.     

不同有机肥对土壤镉锌生物有效性的影响

在南方典型稻田设置连续4年施用猪粪、鸡粪、稻草的定位试验,监测施用不同有机肥条件下土壤及水稻植株镉(Cd)、锌(Zn)含量的变化,研究有机肥对土壤Cd、Zn活性及其交互作用的影响.结果表明:施用有机肥(猪粪、鸡粪、稻草)对土壤全Cd、有效态Cd含量及Cd活性皆无显著影响,但有增加土壤Cd全量的趋势,且显著增加土壤全Zn、有效态Zn含量及Zn活性.施用猪粪、鸡粪、稻草皆可降低稻米Cd含量,降Cd效果为猪粪>鸡粪>稻草,猪粪处理水稻稻米、茎、叶Cd含量分别比对照下降37.5%、44.0%、36.4%;鸡粪处理水稻米、茎、叶Cd含量分别比对照下降22.5%、33.8%、22.7%;而稻草处理水稻米Cd含量比对照下降7.5%,但茎、叶Cd含量比对照分别增加8.2%、22.7%;施用猪粪、鸡粪降低稻米Cd含量主要是降低了水稻植株对土壤Cd的富集,而施用稻草则主要是降低了水稻茎Cd向稻米的转运.施用有机肥还增加了水稻茎Zn含量,施用猪粪、鸡粪、稻草的水稻茎Zn含量比单施化肥分别增加53.4%、41.2%、13.9%,但对水稻稻米、叶Zn含量无显著影响.Zn、Cd在土壤、植株茎中皆表现出显著的拮抗作用,土壤及水稻茎Zn含量的增加显著抑制了水稻米、茎、叶对Cd的吸收积累,且随土壤有效态Zn/Cd含量比值的增加,Zn、Cd竞争土壤吸附不是抑制水稻吸收积累Cd的主控因子,而Zn、Cd竞争吸收才是影响水稻吸收积累Cd的主控因子.     

CO2浓度升高对不同品种水稻镉吸收和根形态的影响

为了探讨CO2浓度升高下不同水稻品种荣优398 (RY)和粤杂889(YZ)吸收重金属Cd差异性的原因,利用水培试验研究了不同浓度Cd处理下两种水稻吸收Cd的差异及根形态的变化特征.结果表明:低Cd处理(5、10、20 μmol·L-1)显著增加水稻生物量;当Cd浓度高于50 μmol·L-1时,Cd胁迫效果开始显现,水稻生物量减少.CO2浓度升高显著增加了水稻的生物量,增加了YZ茎Cd含量而降低了RY茎Cd含量.在5～200 μmol·L-1的Cd浓度下,CO2浓度升高增加了YZ活性根在总根长中的比例,降低了RY活性根的比例.CO2浓度升高下不同水稻品种根形态的变化是导致其对Cd吸收差异性的原因之一.     

Fe对不同品种水稻吸收Cd的影响

1引言在农作物重金属污染中,Cd是一个毒性较强的元素,不仅对植物产生毒害引起产量下降[1,4],而且还会残留在植物可食部分,通过食物链进入人体,危害人体健康[2]。减少Cd进入食物链的可能途径之一是调节土壤中Cd的生物有效性;二是利用或培育吸Cd童少或Cd优先吸附保留在报中的植物品种水稻对土壤中Cd吸收量较大,通过第一种途径改良比较困难,因此利用植物自身的调控机制减少对Cd的吸收及其转移尤为重要Cd很容易被吸收并分配到植物的各个部位,为了减少它在食物链中的官集,有必要了解植物对它的吸收机制和在体内的分配过程本文研究…     

Effect of acidulation of high cadmium containing phosphate rocks on cadmium uptake by upland rice

Little information is available in literature on Cd uptake by crops from either phosphate rock (PR) or partially acidulated PR (PAPR). The purpose of this greenhouse experiment was to study the effect of acidulation of two PRs having high Cd content (highly reactive North Carolina PR and low-reactive Togo PR) on Cd uptake by upland rice. The degrees of acidulation with H₂SO₄ were 100% for North Carolina PR (NC-single superphosphate [SSP]) and 50% or 100% for Togo-PR (i.e., Togo PAPR or Togo-SSP). Separation of the confounding effect between P uptake and Cd uptake from various P sources was made by adding 200 mg P/kg as KH₂PO₄ to all the treatments. Rates of Cd added from various P sources were 50–400 µg Cd/kg. Upland rice (Oryza sativa L.) was grown on two acid soils (Hartsells, pH 5.0 and Waverly, pH 5.6) to maturity.The results show that Cd uptake by rice grains followed the order of NC-SSP> NC-PR and Togo SSP> Togo PAPR> Togo PR. The results also showed that most of the Cd uptake was retained in rice roots and straw. Total uptake of Cd, Ca, and P by rice plant (root, straw, and grain) was higher from NC-PR than from Togo-PR. Cd concentration in rice grains showed no significant difference between NC-PR and Togo-PR, whereas Cd concentrations in root and straw were higher with NC-PR than that with Togo-PR. There was a significant relationship between total Cd uptake by rice plant and Cd extracted by DTPA from soils treated with various P sources at 400 µg Cd/kg.     

根表铁锰氧化物胶膜对不同品种水稻吸镉的影响

采用土培方法,研究了不同品种水稻吸镉的差异及其与根表铁锰氧化物胶膜的关系,结果表明：不同品种水稻其根膜,根部及地上部含镉量均存在显著性差异,且镉在不同水稻植株体内运输转移能力不同,不同水稻其根表淀积的铁锰氧化物数量也存在显著性差异,根膜及地上部的含镉量与极膜的含铁量均未达到显著性相关,但与根膜的含锰量相关性显著。     

Arsenic mitigates cadmium toxicity in rice seedlings

Two contrasting rice (Oryza sativa L.) cultivars, i.e. Wuyujing 3 (WYJ3, Cd-tolerant) and Shanyou 63 (SY63, Cd-sensitive), were grown on a red soil (Ultisol) to study both individual and combined phytotoxicity of arsenic (As) and cadmium (Cd) in terms of Cd and As availability, their uptake and accumulation, antioxidant defense activity and oxidative damage. The antioxidant defense system examined in this study included enzymatic and non-enzymatic molecular antioxidants such as superoxide dismutase (SOD), peroxidase (POD), glutathione (GSH) and ascorbic acid (AsA). Results showed that As or Cd treatment decreased root and shoot biomass in both cultivars compared with their corresponding control (no Cd or As treatment), although less severe inhibition of plant growth was observed in WYJ3 than in SY63. Moreover, rice growth was inhibited more severely by Cd treatment than by As treatment, which could be explained by the higher amount of available Cd (60%) (0.1 M HCl-extractable Cd) compared to the lower amount of available As (15%) (0.5 M NaH₂PO₄-extractable As) in their postharvest soils. However, shoot biomass in cultivar SY63, and root and shoot biomass in cultivar WYJ3 were significantly higher in the As plus Cd treatment than in the Cd treatment alone, showing that the combined toxicity of these two heavy metals was not additive and on the contrary, As mitigated Cd-induced growth inhibition. The As plus Cd treatment also significantly decreased As or Cd concentrations both in roots and in shoots of the two rice cultivars compared with the As or Cd treatment alone, respectively. On the other hand, treatment with As or Cd alone significantly decreased the SOD and POD activities, and GSH and AsA concentrations, while the activities of these enzymes and the concentrations of GSH and AsA were significantly higher in the As plus Cd treatment than in the Cd treatment alone, resulting in less severe oxidative damage as indicated by the lower concentration of MDA in the As plus Cd treatment (P < 0.05). However, no significant difference was observed in the antioxidant defense activity between the As plus Cd treatment and the As treatment alone. These results suggest that the combined toxicity of As and Cd in rice is lower than that of individual Cd or As, which might be attributed to the decreased uptake and accumulation of Cd and As, and the less oxidative stress caused by the interactive effects of As with Cd both in rhizosphere and in plants.     

Arsenic mitigates cadmium toxicity in rice seedlings

Two contrasting rice (Oryza sativa L.) cultivars, i.e. Wuyujing 3 (WYJ3, Cd-tolerant) and Shanyou 63 (SY63, Cd-sensitive), were grown on a red soil (Ultisol) to study both individual and combined phytotoxicity of arsenic (As) and cadmium (Cd) in terms of Cd and As availability, their uptake and accumulation, antioxidant defense activity and oxidative damage. The antioxidant defense system examined in this study included enzymatic and non-enzymatic molecular antioxidants such as superoxide dismutase (SOD), peroxidase (POD), glutathione (GSH) and ascorbic acid (AsA). Results showed that As or Cd treatment decreased root and shoot biomass in both cultivars compared with their corresponding control (no Cd or As treatment), although less severe inhibition of plant growth was observed in WYJ3 than in SY63. Moreover, rice growth was inhibited more severely by Cd treatment than by As treatment, which could be explained by the higher amount of available Cd (60%) (0.1 M HCl-extractable Cd) compared to the lower amount of available As (15%) (0.5 M NaH₂PO₄-extractable As) in their postharvest soils. However, shoot biomass in cultivar SY63, and root and shoot biomass in cultivar WYJ3 were significantly higher in the As plus Cd treatment than in the Cd treatment alone, showing that the combined toxicity of these two heavy metals was not additive and on the contrary, As mitigated Cd-induced growth inhibition. The As plus Cd treatment also significantly decreased As or Cd concentrations both in roots and in shoots of the two rice cultivars compared with the As or Cd treatment alone, respectively. On the other hand, treatment with As or Cd alone significantly decreased the SOD and POD activities, and GSH and AsA concentrations, while the activities of these enzymes and the concentrations of GSH and AsA were significantly higher in the As plus Cd treatment than in the Cd treatment alone, resulting in less severe oxidative damage as indicated by the lower concentration of MDA in the As plus Cd treatment (P < 0.05). However, no significant difference was observed in the antioxidant defense activity between the As plus Cd treatment and the As treatment alone. These results suggest that the combined toxicity of As and Cd in rice is lower than that of individual Cd or As, which might be attributed to the decreased uptake and accumulation of Cd and As, and the less oxidative stress caused by the interactive effects of As with Cd both in rhizosphere and in plants.     

Root morphology and cadmium uptake kinetics of the cadmium-sensitive rice mutant

To understand the physiological mechanism that confers Cd sensitivity, root morphology and Cd uptake kinetics of the Cd-sensitive mutant and wild type rice were investigated. The root length, root surface area, and root number of mutant rice decreased more significantly with increasing Cd concentration in growth media compared with the wild type rice. The uptake kinetics for ¹⁰⁹Cd²⁺ in roots of both the mutant and wild type rice were characterized by a rapid linear phase during the first 6 h and a slower linear phase during the subsequent period. Concentration-dependent Cd²⁺ influx in both species could be characterized by the Michaelis-Menten equation, with similar apparent K_m values for mutant and wild type rice (2.54 and 2.37 μM, respectively). However, the V_max for Cd²⁺ influx in mutant root cells was nearly 2-fold higher than that for wild type rice, indicating that enhanced absorption into the root is one of the mechanisms involved in Cd sensitivity in mutant rice.     

以回交重组自交系定位水稻萌芽期耐镉胁迫相关QTLs

水稻是世界上最主要的粮食作物之一,目前农用耕地存在土壤重金属污染的问题,而水稻对镉（Cd）等重金属的耐受性较低,进而使水稻产量和质量受到影响。定位稻种耐Cd胁迫相关数量性状基因座(quantitative trait loci, QTLs),对于指导水稻耐Cd育种具有重要意义。为发掘Cd胁迫相关基因,以粳稻02428和籼稻昌恢891衍生的124个回交重组自交系群体（backcross recombinant inbred ines,BILs）为材料,对水稻萌芽期的根长、芽长进行了分析,并对萌芽期与Cd胁迫相关的QTLs进行了定位分析。结果显示：Cd胁迫处理下,02428和昌恢891根长和芽长均受到显著抑制（P＜0.01）,其中Cd对根长的抑制强于芽长;QTL分析共检测到5个萌芽期与Cd胁迫相关的QTLs：qCdBL3、qCdRL7、qCdBL8.1、qCdBL8.2和qCdBL9分别位于水稻第3、7、8、8和9号染色体上,贡献率为6.45%~19.46%。其中,qCdBL3、qCdBL8.1、qCdBL8.2和qCdBL9与芽长相关,qCdRL7与根长相关。同时,检测到2个在对照条件下（水溶液）影响根长和芽长的QTLs：qCKBL8、qCKRL4,分别位于第8和4号染色体上,贡献率为10.53%和10.89%。比较显示,对照和Cd处理条件下控制水稻萌芽期根长或芽长的QTLs均不相同,说明Cd胁迫条件下,控制水稻根长和芽长的遗传机制可能不同于非Cd胁迫条件。研究结果为耐Cd基因的克隆和耐Cd水稻新品种的选育提供了参考。