菲、芘、1,2,4-三氯苯对土壤高等植物根伸长抑制的生态毒性效应

测定了草甸棕壤条件下,菲、芘、１,２,４—三氮苯对高等植物（小麦、白菜、西红柿）根伸长抑制串以及复合污染毒性效应。结果表明,菲、芘、１,２,４—三氮苯浓度与植物根伸长抑制串呈显著线性或对数相关（ｐ＝０．０５）。３种化学品对植物根伸长抑制的强弱顺序为１,２,４—三氮苯＞菲＞芘。这与３种化学品的水中溶解度大小显著相关。小麦是３种供试植物中对有机污染物最敏感植物。菲、芘、１,２,４—三氮苯复合污染主表现为协同作用。     

重金属对土壤中小麦种子发芽与根伸长抑制的生态毒性

测定了4种土壤（红壤、草甸棕壤、暗棕壤和栗钙土）条件下,Cu,Zn,Pb和Cd单一污染对小麦种子发芽与根伸长抑制主及其复合污染效应（暗棕壤条件下）。结果表明,同一浓度下,重金属对小麦根伸长抑制率均明显大于对种子发芽抑制率,植物根对金属污染的生态毒性比种子发芽敏感,土壤有机质和土壤N含量与Cu,Zn,Pb和Cd污染对小麦根伸长抑制率显著负相关（R^2OR=0.91,R^2K-N=0.92),土壤PH和阳离子交换量与Cu,Zn,Pb和Cd污染对小麦根伸长抑制率的相关性不显著（R^2PH=0.62,R^2CEC=0.60),在单一污染对小麦根伸长为刺激作用浓度（较低浓度）或为抑制作用浓度下（较高浓度）,复合污染均表现为协同作用。^     

重金属对土壤中萝卜种子发芽与根伸长抑制的生态毒性

高等植物是生态系统中的基本组成部分。一个平衡、稳定的生态系统生产健康、优良的高等植物。反之 ,一个不稳定或受到外来污染的生态系统 ,对高等植物的生长可带来不利和可见的负面影响。因此 ,利用高等植物的生长状况监测土壤污染程度 ,是从生态学角度衡量土壤健康状况 ,评价土壤质量的重要方法之一[4 ,6] 1) 。土壤生态毒理学评价方法是对化学分析方法的重要补充。目前已建立的高等植物毒理试验有三种方法 ,即 1根伸长试验 ;2种子发芽试验 ;3早期植物幼苗生长试验[3 ,5,6,10 ] 。最初 ,这类试验主要用于纯化学品的毒性检验 ,但随着对土壤…     

植物对水中菲和芘的吸收

以菲和芘为多环芳烃（PAHs）代表物,采用水培体系研究了黑麦草（Lolium multiflorum Lam）对水中PAHs的吸收作用,重点研究了植物吸收菲和芘的时间动态.水中菲和芘起始浓度分别为1.00mg/L和0.12mg/L.0～288h内,黑麦草根和茎叶中菲和芘含量均先快速增加而后降低,积累量不断增大,植物根系和茎叶富集系数则先快速升高而后趋于稳定.茎叶中菲和芘含量、茎叶对菲和芘的富集系数比根低1～3数量级,积累量也明显小于根系.黑麦草根系对水中芘有更强的富集能力,其根系富集系数比菲大85%～179%;而其茎叶对菲的富集作用则略强.菲和芘在植物体内有明显的传导作用.0～288h,传导系数（TF）先显著升高而后趋于恒定;但实验条件下,菲和芘的TF值均很小,分别不高于0.031和0.009,且芘的TF值明显小于菲,表明供试植物对芘的传导能力更弱.     

植物CytP450和抗氧化酶对土壤低浓度菲、芘胁迫的响应

以小麦(Triticum acstivnm)为供试植物,草甸棕壤为供试土壤,以微粒体细胞色素P450及抗氧化酶SOD、POD和CAT酶活性为指标,进行了土壤中菲、芘单一及复合胁迫响应研究.结果初步表明,菲、芘胁迫引起植物体内解毒代谢和抗氧化防御酶反应.菲、芘单一胁迫浓度为1mg kg-1时对细胞色素P450产生显著诱导;4 mg kg-1时P450酶含量明显被抑制,表明低浓度菲、芘单一胁迫对植物代谢解毒系统产生损伤;而菲、芘复合1mg kg-1时P450酶含量明显被抑制,说明菲、芘复合胁迫对植物的代谢解毒具有协同毒性效应.土壤中菲、芘单一胁迫未引起SOD酶活性的明显改变,复合胁迫下SOD酶活性出现微弱下降;菲、芘单一胁迫对CAT和POD酶活性具有显著抑制作用;复合胁迫对CAT产生抑制作用,而POD酶活性并未对菲、芘复合产生增强毒性响应.研究从代谢解毒和抗氧化防御酶系统两方面,为土壤低浓度PAHs污染诊断提供了实验依据.     

中性环境中铝盐絮凝剂对典型作物的生态毒性效应

采用种子发芽和根伸长抑制的陆生生态毒理方法,在中性条件(pH=7.0)下对铝盐絮凝剂(AlCl₃)的生态毒性效应进行了研究.结果表明,AlCl₃溶液在pH=7.0时,与其酸性条件(pH=4.0)相比对萝卜、白菜和小麦等受试作物种子发芽和根伸长均表现出抑制作用,且发芽抑制率和根伸长抑制率与铝浓度均呈极显著相关(P＜0.01).尽管在酸性条件下AlCl₃对白菜和小麦根伸长抑制效应比相同浓度中性条件更为强烈,但对萝卜根伸长的抑制程度在相同铝浓度条件下则是pH=7.0时明显大于pH=4.0时,在低浓度时萝卜发芽抑制率也是中性条件明显高于酸性条件.同时,铝盐在中性条件下对萝卜、白菜的发芽和根伸长产生明显抑制效应的起始浓度低于酸性条件(＜2.0 mg·L^-1).     

玉米幼苗根际土壤微生物活性对芘污染的响应

用根际袋法土培试验研究了玉米幼苗根际与非根际土壤微生物量碳、微生物熵、代谢熵和土壤酶活性对不同芘污染水平(50、200、800mg·kg-1,记为T1、T2、T3)的响应差异。结果表明,较低浓度芘可适当的刺激玉米幼苗的生长,而较高浓度芘则抑制幼苗生长,其抑制作用随芘处理浓度的提高而增强;芘对玉米根系的影响要大于对茎叶的影响。玉米幼苗能够明显促进土壤中芘的去除。根际和非根际土壤中芘的去除率分别为56.67%-76.18%和32.64%-70.44%,根际土壤中芘的平均去除率比非根际土壤高16.06%。同处理中根际土壤芘含量显著低于非根际土壤,随着芘处理浓度的提高其差异更加显著。根际土壤微生物量碳、微生物熵、多酚氧化酶活性、脱氢酶活性和磷酸酶活性均高于非根际土壤,代谢熵低于非根际土壤,且其差异随芘处理浓度的提高而增大。在不同芘污染水平下,微生物量碳、微生物熵和脱氢酶活性根际和非根际土壤为T1T2T3,代谢熵为T3T2T1;多酚氧化酶活性根际土壤为T2T1T3,非根际土壤为T1T2T3;磷酸酶活性根际土壤为T3T1T2,非根际土壤为T1T2T3。土壤中残余芘含量与土壤微生物量碳、微生物熵、多酚氧化酶、脱氢酶和磷酸酶活性呈显著负相关,与代谢熵呈显著正相关。     

土壤重金属污染对蚯蚓的急性毒性效应研究

测定了草甸棕壤条件下 ,Cu、Zn、Pb、Cd单一 /复合污染对蚯蚓的急性致死及亚致死效应 .结果表明 ,Cu、Pb浓度与蚯蚓死亡率显著相关 (α=0 .0 5 ,RCu=0 .86 ,RPb=0 .87) ,Cu浓度与生长抑制率显著相关 (α=0 .0 5 ,RCu=0 .84) ,其他供试重金属浓度与蚯蚓死亡率和生长抑制率相关性不显著 .蚯蚓个体对重金属毒性的耐受程度差别较大 .其毒性阈值 (引起个体蚯蚓死亡浓度 )分别为 :Cu 30 0mg·kg-1,Zn 130 0mg·kg-1,Pb 170 0mg·kg-1,Cd 30 0mg·kg-1.LC50 分别为 :Cu 40 0～ 45 0mg·kg-1,Zn15 0 0～ 190 0mg·kg-1,Pb2 35 0～ 2 40 0mg·kg-1,Cd 90 0mg·kg-1.在Cu、Zn、Pb、Cd单一污染引起 >10 %蚯蚓死亡的浓度下 ,复合污染导致 10 0 %蚯蚓死亡 ,表明复合污染极强的协同效应 .     

芘对苦草的生物毒性效应

通过静态模拟实验,研究了不同浓度(0.01、0.02、0.05、0.07和0.1 mg·L^-1)芘暴露10 d后,芘在苦草中的富集,以及芘对苦草茎叶中自由基含量、抗氧化系统以及叶绿素、可溶性糖等的影响.结果表明: 芘能够大量富集在苦草叶部;自由基信号强度、过氧化物酶(POD)活性和脂质过氧化产物丙二醛(MDA)含量持续升高;当污染加重时,这种升高现象有减弱的趋势,且三者有较好的相关性;谷胱甘肽S转移酶(GST)活性和氧化型谷胱甘肽(GSSG)含量持续增加,而还原型谷胱甘肽(GSH)含量持续降低;随着芘浓度的增加,叶绿素含量降低,而可溶性糖含量升高.苦草对芘暴露比较敏感,0.01 mg·L^-1即已显示胁迫效应.     

AMF和PGPR联合修复菲和芘污染土壤的效应

丛枝菌根真菌（arbuscular mycorrhizal fungi,AMF）与根围促生细菌（plant growth-promoting rhizobacteria,PGPR）联合降解有毒有机物、修复污染土壤和促进植物生长的作用倍受关注。本试验旨在探究AMF与PGPR联合降解土壤中菲和芘的效应,以菲和芘1:1混合处理浓度各0、50mg/kg、100mg/kg和150mg/kg下对高羊茅Festuca elata接种AMF根内根孢囊霉Rhizophagus intraradices（Ri）、变形球囊霉Glomus versiforme（Gv）、PGPR荧光假单胞菌Pseudomonas fluorescens Ps2-6、芽孢杆菌Bacillus velezensis Ps3-2、Ri+Ps2-6、Ri+Ps3-2、Gv+Ps2-6、Gv+Ps3-2和不接种对照共36个处理。结果表明,供试AMF增加了PGPR的定殖数量;接种PGPR则显著提高AMF的侵染率。AMF、PGPR或AMF+PGPR处理均显著降低土壤中菲和芘含量,促进植物对土壤中菲和芘的吸收,显著提高高羊茅根系和叶片内的菲和芘含量。在土壤中菲和芘100mg/kg和150mg/kg水平下,Gv与Ps2-6及Ri与Ps2-6能相互促进对土壤中菲和芘的去除效应,其中接种Gv+Ps2-6组合处理的去除率最高,达到95%-98%,土壤中多酚氧化酶、脱氢酶和过氧化氢酶活性显著高于单接种处理和不接种对照,而酸性磷酸酶活性变化则表现为相反趋势。其中以Gv+Ps2-6组合处理的多酚氧化酶活性最高,为0.17mg/g,是不接种对照的1.9倍;脱氢酶和过氧化氢酶活性分别达到1.32µg/(g·h)和1.81mL/g;酸性磷酸酶活性则比不接种对照土壤降低27%-45%;易提取球囊霉素相关土壤蛋白含量和总球囊霉素相关土壤蛋白含量分别是不接种对照的1.6倍和1.5倍。     

The effect of inorganic and organic supplements on the microbial degradation of phenanthrene and pyrene in soils

The effects of several bioremediation stimulants, including potentialmetabolism pathway inducers, inorganic/organic nutrients, and surfactants onthe metabolism of phenanthrene and pyrene, as well as the populationdynamics of PAH degrading microorganisms was examined in five soils withdiffering background PAH concentrations, exposure histories and physicalproperties. Most of the supplements either had no significant effect ordecreased the mineralization of [¹⁴C]-phenanthrene and[¹⁴C]-pyrene in soil slurry microcosms. The effect of aparticular supplement, however, was often not uniform within or acrosssoils. Decreased mineralization of [¹⁴C]-phenanthrene and[¹⁴C]-pyrene was usually due to either preferential use of thesupplement as carbon source and/or stimulation of non-PAH degradingmicroorganisms. Many of the supplements increased populations ofheterotrophic microorganisms, as measured by plate counts, but did notincrease populations of phenanthrene degrading microorganisms, as measuredby the [¹⁴C]-PAH mineralization MPN analysis or cellularincorporation of [¹⁴C]-PAH. These results suggest that the PAHdegrading community at each site may be unique in their response tomaterials added in an attempt to stimulate PAH degradation. Thecharacteristics of the site, including exposure history, soil type, andtemporal variation may all influence their response.     

Role of cytoskeleton in gravisensing of the root elongation zone in Arabidopsis thaliana plants

In order to reveal the involvement of tubulin microtubules and actin microfilaments in gravisensing reactions in the distal elongation zone of root, Arabidopsis thaliana plants stably transformed with MAP4-GFP construct were grown under slow clinorotation. Experiments have shown that stabilization of cell growth in the distal elongation zone of Arabidopsis seedling root is provided by common structural organization of microtubules and microfilaments, and interrelations between microtubules and microfilaments is highly dependent upon the type of cell differential growth. Less pronounced effect of microfilament disruption on microtubule organization has been observed under clinorotation and it suggests the existence of complex mechanism of cooperation between microtubules and microfilaments which is probably, masked on earth.     

Light inhibition of internode elongation in green plants

The clongation of the first internode of fully greenVigna sinensis L. is inhibited by white light (W). This inhibition is fluence-rate dependent between 0 and 70 Wm^–2. The kinetics of elongation rate in the light after darkness were investigated with linear displacement transducers. The internode elongation rate does not exhibit any endogenous rhythm. A rapid inhibition occurs during the first 2 or 3 h after the onset of light, and a second type of inhibition (slow reaction) increases from the beginning to the 8th hour of light. The rapid inhibition is not fluence-rate dependent between 20 and 70 Wm^–2, but the slow reaction is. There is no rapid inhibition in a low fluence rate white light to high fluence rate white light transition, only the slow reaction is observed. The responses to different wavebands, i.e., blue light (B), yellow and green light (YG), and red light (R), are the same for the two inhibition reactions. Each waveband used separately does not reproduce the full effect observed in W. Results show a stimulation with B, a greater inhibition activity with YG than with R, and a synergistic action of B and R which when given together lead to an inhibition similar to that obtained in W. Plants returned from the light to darkness progressively recover a high elongation rate without any latent period. The W light regulating internode elongation rate is mainly perceived by the growing internode itself.Abbreviations B blue light - D darkness - F far-red light - HW high fluence rate white light - LW low fluence rate white light - R red light - W white light - YG yellow and green light     

Relationship between root elongation rate and diameter and duration of growth of lateral roots of maize

The objective of this work was to describe the relationship between elongation rate and diameter of maize roots and to estimate the length and growth duration of lateral roots of maize. Diameters and elongation rates of roots were measuredin situ on plants grown 5 weeks in small rhizotrons under greenhouse conditions. At the end of the experimental period the roots were harvested and diameters of axile and lateral roots were measured. The frequency distribution of diameters of harvested roots was bimodal with a minimum at 0.6 mm; 97% of axile roots were larger than this value and 98% of the lateral roots were smaller. Root elongation per day increased as diameter increased but the slope of the relationship with lateral roots was about 2.5 times that with axile roots when separate linear regressions were fitted to the two populations. The length of lateral roots found on axillary roots between the base and about 30 cm from the apex was approximately 2.2 cm. All of the data was consistent with the hypothesis that the lateral roots grew for about 2.5 days and then ceased growing. The axillary roots continued to grow throughout the experimental period at a rate of about 3 cm day⁻¹. Contribution from the Department of Agronomy, New York State College of Agriculture and Life Sciences, Cornell University, Ithaca, NY 14853. Agronomy paper No. 1661. This research is part of the program of the Center for Root-Soil Research.     

Factors controlling the timing of root elongation intensity in a mature upland oak stand

We examined the timing of root elongation intensity (REI) – the production of newly elongating roots measured in length per unit soil volume per unit time – in a mature white oak-chestnut oak forest in Tennessee, USA, over a 4-year period. We used a network of minirhizotrons to (1) examine environmental control of soil moisture and temperature over REI, (2) evaluate the control of phenology over REI (3) develop a multivariate regression equation using the variables of soil temperature, soil water potential and phenology to predict REI, and (4) delineate soil water potentials that were optimum for growth. Fifteen minirhizotron tubes were installed on the upper slope of an upland oak stand on Walker Branch Watershed in Oak Ridge, Tennessee. Measurements of REI were examined over three growing seasons in the upper 30 cm of the soil profile. Composited sets of data on REI, soil water potential, soil temperature and phenology were analyzed to determine the strength of relationships between the latter three variables and REI. There was no statistically significant relationship between REI and soil temperature during the growing season (March–November). The highly significant (p < 0.0001) relationship between soil water potential and REI was best described as log linear, using log₁₀ (-) vs. log₁₀ (REI). The correlation between a phenology index and REI was also highly significant (p < 0.0001), as the 24 highest REI levels occurred between late April and early August. Whereas soil water potential played a major role in controlling REI, our data indicate that at times phenologically related factors appeared to override environmental variables. The fact that REI generally peaked every year following completion of leaf expansion is congruent with the fixed shoot growth pattern of many temperate-zone deciduous tree species. In an attempt to explain the importance of phenology in controlling REI, we refer to the concept of `phenological programming'. This concept contrasts with more environmentally determinant explanations of the timing of root growth. Those theories cannot explain either our data or that of others, wherein, during late summer and early autumn, REI does not return to early summer rates, even though soil moisture and temperature conditions are equally, if not more, favorable. The particular type of `phenological programming' hypothesized in this study may be limited to mature deciduous trees exhibiting a fixed growth pattern of shoot expansion and growing in a temperate climate with a mid-summer drought period.     

Effect of ethylene antagonists on auxin-induced inhibition of intact primary root elongation in maize (Zeamays L.)

We tested that the hypothesis that root elongation might be controlled by altering the level of ethylene in intact primary roots of maize(Zea mays L.). We measured root elongation in a short period using a computerized root auxanometer. Compounds which regulate ethylene production were applied to intact primary roots in different time periods. Root elongation was stimulated by the treatment with ethylene antagonists such as Co²⁺, aminoethoxyvinylglycine (AVG) and L-canaline. This result suggested that root elongation was closely related to ethylene level of intact primary roots. Furthermore, IAA- and 1-aminocyclopropane-1-carboxylic acid (ACC)-induced inhibition of root elongation was reversed by treatment with Co²⁺. The application of ACC to roots which have been exposed to IAA and Co²⁺ have no significant effect on root elongation. However, the inhibition of root elongation by ACC in roots previously treated with IAA and AVG became manifest when the applied IAA concentrations were lower. These results were consistent with the hypothesis that the level of ethylene in intact roots functions to moderate root elongation, and suggested that auxin-induced inhibition of root elongation results from auxin induced promotion of ethylene production.     

Nitric oxide is involved in nitrate-induced inhibition of root elongation in Zea mays

BACKGROUND AND AIMS: Root growth and development are closely dependent upon nitrate supply in the growth medium. To unravel the mechanism underlying dependence of root growth on nitrate, an examination was made of whether endogenous nitric oxide (NO) is involved in nitrate-dependent growth of primary roots in maize. METHODS: Maize seedlings grown in varying concentrations of nitrate for 7 d were used to evaluate the effects on root elongation of a nitric oxide (NO) donor (sodium nitroprusside, SNP), a NO scavenger (methylene blue, MB), a nitric oxide synthase inhibitor (N(omega)-nitro-L-arginine, L-NNA), H(2)O(2), indole-3-acetic acid (IAA) and a nitric reducatse inhibitor (tungstate). The effects of these treatments on endogenous NO levels in maize root apical cells were investigated using a NO-specific fluorescent probe, 4, 5-diaminofluorescein diacetate (DAF-2DA) in association with a confocal microscopy. KEY RESULTS: Elongation of primary roots was negatively dependent on external concentrations of nitrate, and inhibition by high external nitrate was diminished when roots were treated with SNP and IAA. MB and L-NNA inhibited root elongation of plants grown in low-nitrate solution, but they had no effect on elongation of roots grown in high-nitrate solution. Tungstate inhibited root elongation grown in both low- and high-nitrate solutions. Endogenous NO levels in root apices grown in high-nitrate solution were lower than those grown in low-nitrate solution. IAA and SNP markedly enhanced endogenous NO levels in root apices grown in high nitrate, but they had no effect on endogenous NO levels in root apical cells grown in low-nitrate solution. Tungstate induced a greater increase in the endogenous NO levels in root apical cells grown in low-nitrate solution than those grown in high-nitrate solution. CONCLUSIONS: Inhibition of root elongation in maize by high external nitrate is likely to result from a reduction of nitric oxide synthase-dependent endogenous NO levels in maize root apical cells.