Effects of exogenous glycinebetaine and trehalose on lead accumulation in an aquatic plant (Lemna gibba L.)

This study was aimed at investigating and comparing the effects of exogenous glycinebetaine (GB) and trehalose (TR) on lead (Pb) accumulation in Lemna gibba. Two-way ANOVA showed that both GB and TR had significant effects on Pb accumulation. However, TR seemed to be more effective than GB. It was determined that 5 mM GB application decreased Pb accumulation whereas 0.5 mM TR increased and 2 and 5 mM decreased Pb accumulation. The results obtained from this study will be useful for examining the phytoremediation of polluted water using aquatic plants.     

Influence of nutrient addition on growth and accumulation of cadmium and copper in Lemna gibba

Abstract

Aquatic plants have been identified as potentially useful for accumulating and bioconcentrating heavy metals. This study was developed to test the hypothesis that nutrient enrichment enhances the metal tolerance of floating macrophytes. Relative growth rates (RGR), photosynthetic pigments (chlorophyll a, b and carotenoid), malondialdehyde (MDA) content, and electrical conductivity (EC) were measured in Lemna gibba exposed to different cadmium and copper concentrations in laboratory conditions. Relative growth rates were negatively correlated with metal exposure, but nutrient addition suppressed this effect. Photosynthetic pigment levels were negatively correlated with metal exposures, and nutrient addition attenuated chlorophyll decrease in response to metal exposures. MDA content and EC also showed sharp increases at higher concentrations, indicating oxidative stress. This study indicates that nutrient enrichment increases the tolerance of Lemna gibba to metals, and that Lemna gibba is a suitable candidate for the phytoremediation of low-level copper and cadmium pollution.     

The accumulation of arsenic,uranium, and boron in Lemna gibba L. exposed to secondary effluents

Aquatic plants are used as a practical and effective method to remove toxic elements from secondary-treated municipal wastewater. In this study, Lemna gibba was investigated for its capacity to remove uranium, arsenic, and boron from secondary effluents. L. gibba was collected from a natural lake in Elaz??, Turkey, then acclimatized to the effluent in situ. The concentration of toxic elements in the plant material was monitored as a function of time for 7 days. L. gibba significantly accumulated the toxic elements, particularly in the first 2 days. Arsenic, uranium, and boron were accumulated in the highest concentrations (133%, 122%, and 40%, respectively). However, in the following days, accumulation levels showed both increases and decreases, most probably due to L. gibba reaching saturation levels.     

Genetic transformation of duckweed Lemna gibba and Lemna minor

Summary We developed efficient genetic transformation protocols for two species of duckweed, Lemna gibba (G3) and Lemna minor (8627 and 8744), using Agrobacterium-mediated gene transfer. Partially differentiated nodules were co-cultivated with Agrobacterium tumefaciens harboring a binary vector containing β-glucuronidase and nptII expression cassettes. Transformed cells were selected and allowed to grow into nodules in the presence of kanamycin. Transgenic duckweed fronds were regenerated from selected nodules. We demonstrated that transgenic duckweed could be regenerated within 3 mo. after Agrobacterium-mediated transformation of nodules. Furthermore, we developed a method for transforming L. minor 8627 in 6 wk. These transformation protocols will facilitate genetic engineering of duckweed, ideal plants for bioremediation and large-scale industrial production of biomass and recombinant proteins.     

Spectral dependences of flowering in Lemna perpusilla and L. gibba

Floral induction in Lemna perpusilla and L. gibba was determinedunder continuous irradiation with monochromatic light in spectralranges from 396 to 765 nm. In the former it was induced underwavelengths from about 400 to 550 nm and longer than 700 nm,while in the latter with wavelengths near 400 nm and from about550 to 650 nm. The patterns of these spectral dependences werenearly mirror images and corresponded to the P_fr level in thephotostationary states of phytochrome. (Received December 3, 1974; )     

Antioxidant capacity of Lemna gibba L. exposed to wastewater treatment

In this study, the amounts of antioxidant vitamins (A, E and C), selenium (Se), reduced glutathione (GSH)/oxidized glutathione (GSSG) ratio and malondialdehyde (MDA) that is the indicator of lipid peroxidation were determined in Lemna gibba L. plants placed in the secondary clarifier and grown in natural water. The amounts of antioxidant vitamins (A, E and C), GSH, GSSG and MDA were determined with HPLC (high performance liquid chromatography) and the amounts of Se were determined fluorimetrically. While significant decrease in amounts of antioxidant vitamins (A, E and C) and Se takes place between the first and the second or third day depending on species and insignificant decrease takes place after that day, the amount of GSH/GSSG ratio decreases until the second day (p < 0.05) and insignificantly increases after that day. Amounts of vitamins (A, E and C), Se and GSH/GSSG ratio for the plants placed in the secondary clarifier are much less than that for control group while an opposite trend was observed in MDA level. The MDA for the plants placed in secondary clarifier has maximum value at the second day, which can be considered as the maximum stress occurring at that day. Consequently, the first two days of treatment time can be taken as acclimation time and after the acclimation time the plant lives in the hostile environmental condition with the certain amount of oxidative stress. As a result, it is determined that wastewater decreases the lifetime of plant by causing metabolic stress on it and affects antioxidant capacity. The lifetime of the plants in the secondary clarifier was determined to be five days since fading toward yellow color (necrosis) in the plants was observed at the fifth day.     

Oxygen and Hydrogen Isotope Fractionation during Cellulose Metabolism in Lemna gibba L

Lemna gibba L. B3 was grown under heterotrophic, photoheterotrophic, and autotrophic conditions in water having a variety of hydrogen and oxygen isotopic compositions. The slopes of the linear regression lines between the isotopic composition of water and leaf cellulose indicated that under the three growth conditions about 40, 70, and 100% of oxygens and carbon-bound hydrogens of cellulose exchanged with those of water prior to cellulose formation. Using the equations of the linear relationships, we estimated the overall fractionation factors between water and the exchanged oxygen and carbon bound-hydrogen of cellulose. At least two very different isotope effects must determine the hydrogen isotopic composition of Lemna cellulose. One reflects the photosynthetic reduction of NADP, while the second reflects exchange reactions that occur subsequent to NADP reduction. Oxygen isotopic composition of cellulose apparently is determined by a single type of exchange reaction with water. Under different growth conditions, variations in metabolic fluxes affect the hydrogen isotopic composition of cellulose by influencing the extent to which the two isotope effects mentioned above are recorded. The oxygen isotopic composition of cellulose is not affected by such changes in growth conditions.     

Persistence of the Potassium Uptake Rhythm in the Presence of Exogenous Sucrose in Lemna gibba G3

The potassium uptake rhythm in a flow medium culture of Lemnagibba G3 persisted in darkness for 3 days, when the flow mediumcontained sucrose (1%). The rhythm was damped out after thatin darkness but it persisted longer when the plants were keptunder continuous weak light (80 lux). The rhythm was not dampedout when a daily light pulse (4,200 lux for 15 min) was applied.A single light pulse (4,200 lux for 15 min) at hour 48 of theprolonged dark period caused the rhythm to start again. DCMU(1 µM) slightly reduced the amplitude of the rhythm butdid not nullify the effect of the inserted light pulse. (Received September 16, 1981; Accepted February 2, 1982)     

Test system stability and natural variability of a Lemna gibba L. bioassay

Background

In ecotoxicological and environmental studies Lemna spp. are used as test organisms due to their small size, rapid predominantly vegetative reproduction, easy handling and high sensitivity to various chemicals. However, there is not much information available concerning spatial and temporal stability of experimental set-ups used for Lemna bioassays, though this is essential for interpretation and reliability of results. We therefore investigated stability and natural variability of a Lemna gibba bioassay assessing area-related and frond number-related growth rates under controlled laboratory conditions over about one year.

Methology/Principal Findings

Lemna gibba L. was grown in beakers with Steinberg medium for one week. Area-related and frond number-related growth rates (r_(area) and r_(num)) were determined with a non-destructive image processing system.To assess inter-experimental stability, 35 independent experiments were performed with 10 beakers each in the course of one year. We observed changes in growth rates by a factor of two over time. These did not correlate well with temperature or relative humidity in the growth chamber.In order to assess intra-experimental stability, we analysed six systematic negative control experiments (nontoxicant tests) with 96 replicate beakers each. Evaluation showed that the chosen experimental set-up was stable and did not produce false positive results. The coefficient of variation was lower for r_(area) (2.99%) than for r_(num) (4.27%).

Conclusions/Significance

It is hypothesised that the variations in growth rates over time under controlled conditions are partly due to endogenic periodicities in Lemna gibba. The relevance of these variations for toxicity investigations should be investigated more closely. Area-related growth rate seems to be more precise as non-destructive calculation parameter than number-related growth rate. Furthermore, we propose two new validity criteria for Lemna gibba bioassays: variability of average specific and section-by-section segmented growth rate, complementary to average specific growth rate as the only validity criterion existing in guidelines for duckweed bioassays.     

Effect of L-Pipecolic Acid on Flowering in Lemna paucicostata and Lemna gibba

L-Pipecolic acid was found to be effective in inducing floweringof Lemna paucicostata 151, 381, 441 and 6746, and of Lemna gibbaG3. When the plants were grown on half-strength Hutner's medium,L-pipecolic acid caused profuse flowering of L. paucicostata151 maintained under 9 and 10 h of light daily. In L. paucicostata441 and 6746, L-pipecolic acid had a strong flower-promotingeffect under a near critical photoperiod. In L. paucicostata381, by contrast, L-pipecolic acid had only a very small effecton flowering. In L. gibba G3 substantial promotion of floweringwas observed under continuous light. When one-twentieth-strengthHutner's medium was used as the basic medium, L-pipecolic acidstimulated flowering in all strains of Lemna examined, evenunder continuous light. When L. paucicostata 151 was grown on one-tenth-strength M mediumor one-twentieth-strength Hutner's medium, the flower-inducingactivity of L-pipecolic acid was greatly enhanced by cytokininunder continuous light. However, when this strain was grownwith 9 h of illumination daily, this synergistic effect of cytokininwas only slight. A short-term (even 1-h) treatment with L-pipecolicacid resulted in flowering, suggesting that L-pipecolic acidis involved in the induction of flowering, rather than its evocation.D-Pipecolic acid also had flower-inducing activity, but itsactivity was 50 times lower than that of the L-isomer. (Received January 23, 1992; Accepted March 9, 1992)     

Nickel-induced changes in lipid peroxidation, antioxidative enzymes, and metal accumulation in Lemna gibba

In this study, an experiment was carried out to study the process of stress adaptation in Lemna gibba grown under nickel stress (0-20 mg Ni L(-1)). The results showed that Ni concentrations in plants increased with increasing Ni supply levels and reached a maximum of 142.82 mg.kg1 DW at 0.5 mg x L(-1) Ni treatments. The level of photosynthetic pigments (Chl a, Chi b, and total Chl) and soluble proteins increased upon exposure to high Ni concentrations. At the same time, the level of malondialdehyde (MDA) increased with increasing Ni concentration. These results suggested an alleviation of stress that was presumably the results of antioxidants such as superoxide dismutase (SOD), catalase (CAT) which generally increased linearly with increasing Ni levels. In addition, the proline content in L. gibba increased with increasing nickel levels. Our present work concluded that Lemna gibba has a high level of nickel tolerance and accumulation. We also found that moderate nickel treatment (0.05-5 mg x L(-1)) alleviated oxidative stress in plants, while the addition of higher amounts of nickel (10-20 mg x L(-1)) could cause an increasing generation of ROS, which was effectively scavenged by the antioxidative system. Therefore, L. gibba may be used as a phytoremediator in moderately polluted aquatic ecosystems.     

The nature and localization of superoxide dismutase in fronds of Lemna gibba L. and the effect of copper and zinc deficiency on its activity

Superoxide dismutase (SOD) is present in the fronds of Lemna gibba L. Differential centrifugation showed that ca. 90% of the enzyme is present in the 140,000 g soluble cell fraction. Lemna SOD is sensitive to cyanide and is probably a Cu-Zn metallo-protein. Gel filtration showed the SOD to have a mass of 31,000 daltons. In Zn-defizient culture media, the activity of Lemna SOD was less than in fronds grown in complete nutrient media whereas in Cu-deficient media little change was found in the enzyme activity. The SOD activity in Zn-deficient plants could be partly restored to the level of Zn-sufficient fronds by adding Zn²⁺ to the enzyme assay solution.     

Glycolate and glyoxylate stimulation of growth in Lemna gibba

A 10 to 20% stimulation of growth in Lemna gibba L. G3 occurred following the addition of 0.5 to 3 mM glycolate or glyoxylate, although concentrations of 5 mM or higher were inhibitory. Glyoxylate gave a higher stimulation than glycolate. The stimulating effect on growth was obtained in media with or without 2% added sucrose. A higher stimulation was obtained when the plants were cultivated in open flasks in comparison to cultivation in flasks plugged with cellulose stoppers, which presumably retarded gas exchange.     

Influence of nutrients on the development of gibbosity in fronds of the duckweed Lemna gibba L.

The duckweeds Lemna gibba L. and Lemna minor L. only grew wellin undisturbed culture under axenic conditions in low lightintensity when provided with a suitable energy source such asglucose. In media containing N0₃-N gibbosity (a convex ventralsurface) was induced in the presence of the chelating agentethylene-diamine-di-o-hydroxyphenylacetic acid (EDDHA). In nutrientsolutions containing NO₃-N as the only N source, but withoutEDDHA, L. gibba occasionally exhibited gibbosity in culturesolutions of 40 cm³ volumes. More fronds were induced to exhibitgibbosity when the volume of the culture medium was increasedfrom 40 cm³ to 200 cm³. Gibbosity was never induced in L. minor,neither was it induced in L. gibba in media containing NH₄-N,even in the presence of NO₃-N. There was no direct correlationbetween the occurrence of gibbosity and frond growth rate, butgibbosity occurred only when there was good frond growth. In the absence of a sugar, frond growth was enhanced by bubblingair through the culture solution in the light. Increasing theCO₂ concentration in the air up to 1% enhanced growth and inducedgibbosity. Carbon dioxide did not induce gibbosity in mediacontaining NH₄-N. Key words: Ammonium-N, carbon dioxide, gibbosity, Lemna, nitrate-N     

Flowering Responses of the Long-day Plant Lemna gibba G3

Lemna gibba L., strain G3, exhibits a qualitative long-day flowering response with a critical daylength on a 24-hour cycle of about 10 hours. Evidence is presented that the onset of daughter frond formation in a given frond inhibits the activity of the flowering meristem. Consequently, flower induction can only occur in fronds smaller than about 0.05 to 0.07 mm long. Although a minimum of 1 long day seems to be sufficient to induce the formation of flower primordia, at least 6 long days are required to obtain mature flowers since long days are also required for the early stages of flower development. The critical night length on 24, 48 and 72-hour cycles is respectively 14, 16, and 18 to 22 hours. The close similarity between the critical night length for the different cycle lengths is explained in terms of an inhibitory effect of darkness both on flower initiation and flower development. A 10-hour dark period is more inhibitory to flowering on a 36-hour cycle than on 24, 48, 60 or 72-hour cycles. It is suggested that darkness inhibits flowering through the formation of a light-labile flower inhibitor which acts to inhibit the functioning of the flowering stimulus.     

Short term exposure of Lemna minor and Lemna gibba to mercury, cadmium and chromium

The effects of mercury (Hg), cadmium (Cd) and chromium (Cr) in concentrations ranging from 0.02 to 20 mg L^?1 applied for 24 h were assessed in Lemna minor and Lemna gibba by measuring changes in protein concentration, ascorbic acid, phenolics, malondialdehyde (MDA), hydrogen peroxide (H₂O₂), the activity of guaiacol peroxidase (G-POX) and catalase (CAT). Ascorbic acid, phenolics, catalase and guaiacol peroxidase played a key role in the antioxidative response of L. gibba. Inadequate activity of antioxidant enzymes in the L. minor resulted in MDA and H₂O₂ accumulation. In both used species, Hg treatment decreased protein content and increased CAT and G-POX activity, but decreased MDA and H₂O₂ levels. Cadmium and chromium had opposite impacts on two used Lemna species on almost all observed parameters. Enhanced antioxidative responses of L. gibba to lower concentrations of Hg, Cd and Cr indicated greater abiotic stress tolerance than L. minor.     

Electron transport across the plasmalemma of Lemna gibba G1

Lemna gibba L., grown in the presence or absence of Fe, reduced extracellular ferricyanide with a V _max of 3.09 mol · g^-1 fresh weight · h^-1 and a K _m of 115 M. However, Fe³⁺-ethylenediaminetetraacetic acid (EDTA) was reduced only after Fe-starvation. External electron acceptors such as ferricyanide, Fe³⁺-EDTA, 2,6-dichlorophenol indophenol or methylene blue induced a membrane depolarization of up to 100 mV, but electron donors such as ferrocyanide or NADH had no effect. Light or glucose enhanced ferricyanide reduction while the concomitant membrane depolarization was much smaller. Under anaerobic conditions, ferricyanide had no effect on electrical membrane potential difference (E_m). Ferricyanide reduction induced H⁺ and K⁺ release in a ratio of 1.16 H⁺+1 K⁺/2 e^- (in +Fe plants) and 1.28 H⁺+0.8 K⁺/2 e^- (in -Fe plants). Anion uptake was inhibited by ferricyanide reduction. It is concluded that the steady-state transfer of electrons and protons proceeds by separate mechanisms, by a redox system and by a H⁺-ATPase.Abbreviations E _m electrical membrane potential difference - EDTA ethylenediaminetetraacetic acid - DCPIP dichlorophenol indophenol - +Fe control plant - -Fe iron-deficient plant - FW fresh weight - H⁺ electrochemical proton gradient     

Flowering responses of Lemna perpusilla and L. gibba in relation to nitrate concentration in the culture medium

Flowering responses of Lemna perpusilla strain 6746, a short-dayplant, and L. gibba strain G3, a long-day plant, to nitrateconcentration in Hoagland's type medium with or without EDTA,were compared. Maximum flowering of L. perpusilla under SD occurredat higher nitrate concentrations than did colony proliferation.Even under CL, L. perpusilla grown at sub-optimal nitrate concentrationsfor colony proliferation, flowered irrespective of the presenceof EDTA which reduces flowering. Unlike L. perpusilla, L. gibba failed to flower under SD atany nitrate concentration whether or not EDTA was added. UnderCL, however, L. gibba flowered at almost any nitrate concentrationwith or without EDTA. Double optima for nitrate concentrationwas exhibited in the presence of EDTA; optimal concentrationfor colony proliferation came between the two optima for flowering. We concluded that the nitrogen level of the medium is importantin regulating flowering of duckweeds, and that the effect ofEDTA, if any, may primarily be on colony proliferation and onlysecondarily or antagonistically on flowering. ¹ Present address: Institute for Agricultural Research, TohokuUniversity, Sendai 980, Japan. (Received September 25, 1971; )     

The Effect of Salicylic Acid on the Growth of Lemna gibba

Salicylic acid added as the iron chelate causes extension ofthe pedicels and distortion in the growth of daughter frondsof Lemna gibba, when included in a nutrient salt medium whichcontains the ammonium ion. The effect is abolished if iron orcopper is omitted from the nutrient solution or if the mediumcontains only nitrate nitrogen. The effect is specific for salicylicacid or acetyl salicylic acid; substituted or analogous compoundsare without effect.     

Giardia and Cryptosporidium removal from waste-water by a duckweed (Lemna gibba L.) covered pond

AIMS: To determine the ability of duckweed ponds used to treat domestic waste-water to remove Giardia and Cryptosporidium. METHODS AND RESULTS: The influent and effluent of a pond covered with duckweed with a 6 day retention time was tested for Giardia cysts, Cryptosporidium oocysts, faecal coliforms and coliphage. Giardia cysts and Cryptosporidium oocysts were reduced by 98 and 89%, respectively, total coliforms by 61%, faecal coliforms by 62% and coliphage by 40%. There was a significant correlation between the removal of Giardia cysts and Cryptospordium oocysts by the pond (P < 0.001). Influent turbidity and parasite removal were also significantly correlated (Cryptosporidium and turbidity, P=0.05; Giardia and turbidity, P=0.01). CONCLUSIONS: The larger organisms (parasites) probably settled to the bottom of the pond, while removal of smaller bacteria and coliphages in the pond was not as effective. SIGNIFICANCE AND IMPACT OF THE STUDY: Duckweed ponds may play an important role in wetland systems for reduction of Giardia and Cryptosporidium.