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Many plant species can be induced to flower by responding to stress factors. The short-day plants Pharbitis nil and Perilla frutescens var. crispa flower under long days in response to the stress of poor nutrition or low-intensity light. Grafting experiments using two varieties of P. nil revealed that a transmissible flowering stimulus is involved in stress-induced flowering. The P. nil and P. frutescens plants that were induced to flower by stress reached anthesis, fruited and produced seeds. These seeds germinated, and the progeny of the stressed plants developed normally. Phenylalanine ammonialyase inhibitors inhibited this stress-induced flowering, and the inhibition was overcome by salicylic acid (SA), suggesting that there is an involvement of SA in stress-induced flowering. PnFT2, a P. nil ortholog of the flowering gene FLOWERING LOCUS T (FT) of Arabidopsis thaliana, was expressed when the P. nil plants were induced to flower under poor-nutrition stress conditions, but expression of PnFT1, another ortholog of FT, was not induced, suggesting that PnFT2 is involved in stress-induced flowering.Key words: flowering, stress, phenylalanine ammonia-lyase, salicylic acid, FLOWERING LOCUS T, Pharbitis nil, Perilla frutescensFlowering in many plant species is regulated by environmental factors, such as night-length in photoperiodic flowering and temperature in vernalization. On the other hand, a short-day (SD) plant such as Pharbitis nil (synonym Ipomoea nil) can be induced to flower under long days (LD) when grown under poor-nutrition, low-temperature or high-intensity light conditions.19 The flowering induced by these conditions is accompanied by an increase in phenylalanine ammonia-lyase (PAL) activity.10 Taken together, these facts suggest that the flowering induced by these conditions might be regulated by a common mechanism. Poor nutrition, low temperature and high-intensity light can be regarded as stress factors, and PAL activity increases under these stress conditions.11 Accordingly, we assumed that such LD flowering in P. nil might be induced by stress. Non-photoperiodic flowering has also been sporadically reported in several plant species other than P. nil, and a review of these studies suggested that most of the factors responsible for flowering could be regarded as stress. Some examples of these factors are summarized in 1214

Table 1

Some cases of stress-induced flowering
Stress factorSpeciesFlowering responseReference
high-intensity lightPharbitis nilinduction5
low-intensity lightLemna paucicostatainduction29
Perilla frutescens var. crispainduction14
ultraviolet CArabidopsis thalianainduction23
droughtDouglas-firinduction30
tropical pasture Legumesinduction31
lemoninduction3235
Ipomoea batataspromotion36
poor nutritionPharbitis nilinduction3, 4, 13
Macroptilium atropurpureumpromotion37
Cyclamen persicumpromotion38
Ipomoea batataspromotion36
Arabidopsis thalianainduction39
poor nitrogenLemna paucicostatainduction40
poor oxygenPharbitis nilinduction41
low temperaturePharbitis nilinduction9, 12
high conc. GA4/7Douglas-firpromotion42
girdlingDouglas-firinduction43
root pruningCitrus sp.induction44
Pharbitis nilinduction45
mechanical stimulationAnanas comosusinduction46
suppression of root elongationPharbitis nilinduction7
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Brassinosteroids (BRs) are perceived by Brassinosteroid Insensitive 1 (BRI1), that encodes a leucine-rich repeat receptor kinase. Tomato BRI1 has previously been implicated in both systemin and BR signalling. The role of tomato BRI1 in BR signalling was confirmed, however it was found not to be essential for systemin/wound signalling. Tomato roots were shown to respond to systemin but this response varied according to the species and growth conditions. Overall the data indicates that mutants defective in tomato BRI1 are not defective in systemin-induced wound signalling and that systemin perception can occur via a non-BRI1 mechanism.Key words: tomato BRI1, brassinosteroids, systemin, wound signallingBrassinosteroids (BRs) are steroid hormones that are essential for normal plant growth. The most important BR receptor in Arabidopsis is BRASSINOSTERIOD INSENSITIVE 1 (BRI1), a serine/threonine kinase with a predicted extracellular domain of ∼24 leucine-rich repeats (LRRs).1,2 BRs bind to BRI1 via a steroid-binding domain that includes LRR 21 and a so-called “island” domain.2,3 In tomato a BRI1 orthologue has been identified that when mutated, as in the curl3 (cu3) mutation, results in BR-insensitive dwarf plants.4 Tomato BRI1 has also been purified as a systemin-binding protein.5 Systemin is an eighteen amino acid peptide, which is produced by post-translational cleavage of prosystemin. Systemin has been implicated in wound signalling and is able to induce the production of jasmonate, protease inhibitors (PIN) and rapid alkalinization of cell suspensions (reviewed in ref. 6).To clarify whether tomato BRI1 was indeed a dual receptor it was important to first confirm its role in BR signalling. Initially this was carried out by genetic complementation of the cu3 mutant phenotype.7 Overexpression of tomato BRI1 restored the dwarf phenotype and BR sensitivity and normalized BR levels (
35S:TomatoBRI1 complemented lineWt*cu3*
6-deoxocathasterone566964676
6-deoxoteasteronend4748
3-dehydro-6-deoxoteasterone876269
6-deoxotyphasterolnd588422
6-deoxocastasterone1,7556,24726,210
castasterone25563717,428
brassinolidendndnd
Open in a separate windowBR content ng/kg fw.*Montoya et al.4 nd, not detected.To show the role of tomato BRI1 in systemin signalling tomato BR mutants and the complemented line were tested for their systemin response. Tomato cu3 mutants were shown not to be defective in systemin-induced proteinase inhibitor (PIN) gene induction, nor were they defective in PIN gene induction in response to wounding. Cell suspensions made from cu3 mutant tissue exhibited an alkalinization of culture medium similar to wild-type cell suspension. These data taken together indicated that BRI1 was not essential for systemin signalling. However, Scheer et al.8 demonstrated that the overexpression of tomato BRI1 in tobacco suspension cultures results in an alkalinization in response to systemin, which was not observed in untransformed cultures. This suggests that BRI1 is capable of eliciting systemin responsiveness and that in tomato BRI1 mutants another mechanism is functioning to enable systemin signalling.Root elongation is a sensitive bioassay for BR action with BRs inhibiting root growth. Solanum pimpinellifolium roots elongate in response to systemin, in a BRI1-dependent fashion. In Solanum lycopersicum root length was reduced in response to systemin and BR and jasmonate synthesis mutants indicated that the inhibition did not require jasmonates or BRs. Normal ethylene signalling was required for the root response to systemin. When a tobacco, Nicotiana benthamiana, BRI1 orthologue was transformed into cu3 both the dwarfism and systemin-induced root elongation was restored to that of wild type. Tobacco plants however do not respond to systemin. This is puzzling as the introduction of tomato BRI1 into tobacco enabled systemin responsiveness.8 Further investigation as to how tomato BRI1 elicits this response is therefore required.Systemin has been demonstrated to bind to two tomato proteins BRI1/SR1605 and SBP50.9 The data presented by Holton et al.7 indicates that tomato BRI1 is not essential for systemin-induced wound responses and that a non-BRI1 pathway is present that is able to facilitate a systemin response. Whether this is via a related LRR receptor kinase or by another protein remains to be elucidated.  相似文献   

7.
What Makes each Aux/IAA Gene Unique in its Gene Family,Expression Pattern or Properties of the Gene Product?     
Hideki Muto  Masaaki K Watahiki  Kotaro T Yamamoto 《Plant signaling & behavior》2007,2(5):390-392
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8.
Indirect effects of tending ants on holm oak volatiles and acorn quality     
Carolina I Paris  Joan Llusia  Josep Pe?uelas 《Plant signaling & behavior》2011,6(4):547-550
The indirect effect of ants on plants through their mutualism with honeydew-producing insects has been extensively investigated. Honeydew-producing insects that are tended by ants impose a cost on plant fitness and health by reducing seed production and/or plant growth. This cost is associated with sap intake and virus transmissions but may be overcompesated by tending ants if they deter or prey on hebivorous insects. The balance between cost and benefits depends on the tending ant species. In this study we report other indirect effects on plants of the mutualism between aphids and ants. We have found that two Lasius ant species, one native and the other invasive, may change the composition of volatile organic compounds (VOCs) of the holm oak (Quercus ilex) blend when they tend the aphid Lachnus roboris. The aphid regulation of its feeding and honeydew production according to the ant demands was proposed as a plausible mechanism that triggers changes in VOCs. Additionally, we now report here that aphid feeding, which is located most of the time on acorns cap or petiole, significantly increased the relative content of linolenic acid in acorns from holm oak colonized by the invasive ant. This acid is involved in the response of plants to insect herbivory as a precursor or jasmonic acid. No effect was found on acorn production, germination or seedlings quality. These results suggest that tending-ants may trigger the physiological response of holm oaks involved in plant resistance toward aphid herbivory and this response is ant species-dependent.Key words: tended aphid, invasive ants, linolenic acid, jasmonic acid, monoterpene emissionsTo achieve an indirect effect it is necessary to have a minimun of three species, two focal species that interact directly and an associate species whose presence promotes an indirect effect on one or both focal species. In general, indirect effects of a third species are defined by how and to what degree a pairwise species interaction is influenced by the presence and density of this third species.1 There are several examples of interactions presenting indirect effects: apparent competition,1 facilitation,2 tri-trophic level interactions,3 cascading effects4 and exploitative competition. 5 But, indirect effects have been studied most extensively in the context of trophic cascades when top predators are removed6 or added7 and in the context of mutualisms.810 Usually, indirect effects are investigated as changes in abundance of the focal species occur. However, indirect effects may result in biologically significant changes in a species that are not reflected only to its abundance.11 There are many examples of changes in physiology, behavior, morphology and/or genotypic composition of the focal species.11,12 These changes on density and/or morphological, physiological and behavioral traits of the focal species are not mutually exclusive, and all can act at the same time.13 The magnitude and direction of both direct and indirect effects should influence the relative resilience of communities to perturbation, which in turn will affect species coexistence and community evolution.14 In this regard, indirect effects had been postulated as one of the main forces structuring communities2 and shaping the evolution of communities.14In terrestrial communities ants interact with plants both directly and indirectly. They can disperse or consume seeds, feed from specialized plant structures such as food bodies and extrafloral nectaries, act as or deter pollinitators, prey on herbivorous insects and/or develop mutualisms with honeydew-producing insects indirectly modifying plant fitness.1517 Additionally, through their nesting activities in soil, ants increase soil nutrient content available to plants, may change water infiltration and soil holding-capacity and modify biodiversity and abundance of soil organisms related to the decomposition process.18,19 As a consequence of their activities, ants may thus change behavior, density, physiology or fitness of other species.12,22,23 In the case of ants that tend honeydew-producing insects, evidence shows that their attention may change some traits of insect life history, 22 their abundance or physiology.18 For the plant, the net outcome of the mutualism between ants and honeydew-producing insects will depend on the balance between the costs for plant fitness via consumption of plant sap and transmission of plant pathogens and the benefit of ants deterring herbivorous insects.18,23 As a consequence, plant seed production, pod production or even plant growth may decrease when the cost of honeydew-producing insects exceed the benefit provided by tending ants.18,23Recently, we have described the changes that two tending ant species may exert indirectly on monoterpene emissions of holm oak (Quercus ilex) saplings through its mutualism with Lachnus roboris aphids.24 One of these tending ant species was Lasius neglectus, an invasive ant species that displaces the local ant Lasius grandis. We found that aphids feeding on holm oak increased the emission of total volatile organic carbon (VOCs) by 31%. In particular, aphids feeding elicited the emission of a new monoterpene, Δ3-carene, and increased the emission of myrcene (mean ± SE; sapling alone: 0.105 ± 0.011 µg g−1 h−1; sapling plus not tended aphid: 0.443 ± 0.057 µg g1 h1) and γ-terpinene (sapling alone: 0.0013 ± 0.0001; sapling plus not tended aphid: 0.0122 ± 0.0022 µg g1 h1) (Mann-Whitney, sapling alone vs. sapling plus not tended aphids, U4,4 = 0, p < 0.05 for both compounds). Changes of VOC emission in response to aphid infestation were noticed also in boreal trees.24 When the aphids became tended by the invasive ant, L. neglectus, VOCs emissions increased only 19% because myrcene, the main compound of the blend, decreased significantly (25 When our data was recalculated on leaf area basis (nmol m−2 s−1), the general pattern was the same independently of the units, but the differences among treatments were not statistically significant (26 These slight differences in the statitiscal significance of the differences of VOC emissions depending on the reference unit may be due to differences in leaf morphology, i.e., changes of leaf area and mass. However, in our study, all holm oaks showed a similar leaf morphology among treatments (Kruskal-Wallis, leaf mass: H3,20 = 2.16, p = 0.53; leaf area: H3,20 = 2.64, p = 0.45) (24,27 This lack of consistence of aphid effect on leaf area and mass limits the development of a clear pattern linking aphids feeding, leaf area or mass and VOC emissions. On the other hand, to achieve statistical significance of emitted VOCs among treatments, values should differ strongly given the high variability of VOC emission within treatments.26 Under this scenario, we recommend giving the values of leaf morphology and to give VOC emissions on both unit bases to facilite comparisons among different studies.

Table 1

Means and standard error of the emission rates of the main compounds emitted by Quercus ilex saplings (n = 4 for T1 and T2 and n = 8 for T3) infested with untended aphids (T1) or infested with aphids tended by the native ant Lasius grandis (T2) or by the invasive ant Lasius neglectus (T3)
Emission rates: µg g−1 h−1 above and nmol m−2 s−1 below
CompoundT1T2T3
Non tendedTended by native antTended by invasive ant
α-Thujene0.007 ± 0.004a0.015 ± 0.005a0.005 ± 0.001a
0.006 ± 0.004a0.006 ± 0.003a0.009 ± 0.008a
α-Pinene0.391 ± 0.182a2.072 ± 0.033b0.551 ± 0.105a
0.244 ± 0.139a0.532 ± 0.082a0.244 ± 0.127a
Camphene0.007 ± 0.003a0.047 ± 0.014b0.012 ± 0.004ab
0.005 ± 0.003a0.014 ± 0.004a0.007 ± 0.004a
Sabinene0.084 ± 0.042a0.387 ± 0.045b0.075 ± 0.017a
0.100 ± 0.076a0.210 ± 0.097a0.128 ± 0.107a
β-Pinene0.227 ± 0.105a1.454 ± 0.269b0.306 ± 0.075a
0.159 ± 0.097a0.322 ± 0.134a0.179 ± 0.097a
Myrcene0.443 ± 0.057a0.482 ± 0.044a0.093 ± 0.020b
0.101 ± 0.034a0.119 ± 0.026a0.060 ± 0.034a
Δ3-Carene0.003 ± 0.002a0.018 ± 0.001b0.010 ± 0.003ab
0.001 ± 0.001a0.004 ± 0.001a0.002 ± 0.001a
α-Terpine0.004 ± 0.001a0.003 ± 0.001a0.001 ± 0.000a
0.001 ± 0.000a0.004 ± 0.003a0.001 ± 0.001a
γ-Terpinene0.012 ± 0.002a0.011 ± 0.004a0.013 ± 0.005a
0.003 ± 0.001a0.013 ± 0.010a0.006 ± 0.003a
Terpinolene0.001 ± 0.000a0.002 ± 0.001a0.005 ± 0.002a
0.001 ± 0.000a0.002 ± 0.001a0.001 ± 0.001a
Leaf mass (g)0.001 ± 0.000a0.002 ± 0.001a0.005 ± 0.002a
Leaf area (m2)0.104 ± 0.005a0.146 ± 0.026a0.113 ± 0.006a
Open in a separate windowThe emission rate were compared first by Kruskal-Wallis test. Values given above were calculated as µg g−1 h−1, while values below were calculated as nmols m−2 s−1. At the last row, leaf morphology is shown for each treatment. Different letters indicate statistical differences of multiple non parametrical post hoc comparisons (Dunn''s test, p < 0.05).The tended aphid, Lachnus roboris, feed most of the time on the petiole or on the cap of acorns of holm oaks.28 Therefore, acorn quantity and quality (lipid content) and seedlings quality could be affected by tending ants through their mutualism with aphids. We analyzed lipid content as an estimator of acorn quality. Lipids and starches are synthetized in acorns from carbohydrates translocated from leaves.29 However, before being used for metabolic functions, lipid content of acorns must be transformed into glucids and then can be used as respiratory substrate during germination.29 As a consequence, when aphids suck sap from acorns they may act as a sink of translocated carbohydrates, thus decreasing the amount that reaches the seeds.30During two consecutive years, we counted all acorns from one branch (8–11 cm diameter) for each one of 6 holm oaks colonized by L. neglectus and 6 holm oaks colonized by L. grandis that we studied. We followed them at different stages of their development (July, September and December). Among holm oaks, the loss of acorn production varied between 87.9–96.8%. Acorn production (acorns that started to develop and reached maturity) did not differ between the tree colonized by one or another ant species (mean number of acorns per branch ± SE, 2003: L. neglectus trees: 2.67 ± 1.38, L. grandis trees: 2.67 ± 2.01; Mann Whitney, U = 15, p = 0.69; 2004: L. neglectus trees: 35.83 ± 19.23, L. grandis trees: 49.80 ± 27.99; Mann Whitney, U = 12, p = 0.66). The only work in which researchers evaluated the effect of ants on acorn production was conducted by Ito and Higashi.31 These authors showed that the acorn production of Quercus dentata in the presence of the tending ant Formica yessensis did not differ either. However, there was a significantly lower proportion of infested acorns with weevil larvae when Formica yessensis were tending aphids.31 So, ants may indirectly increase the probability that acorns reach the maturity in healthy conditions, improving in this way one component of the fitness of the oak. In the case of the larvae of weevils, wasps and moth species that infest holm oak acorns32 during their development, they do not move to other acorn as in the case reported by Ito and Higashi.31 This behavior prevents ant predation during the move from one acorn to another.Lipid content of acorn cotyledons was analyzed by gas cromatography-flame ionization detector (FID) after performing the derivatization of lipid acids to methyl esters with BF3 in methanol.33 Acorn quality only differed in the content of linolenic acid, which was significantly higher in acorns from oaks colonized by the invasive ant Lasius neglectus (Fig. 1). Linolenic acid acts as a precursor for the synthesis of jasmonic acid,34 a signaling molecule involved in responses associated with insect herbivory.35 The increase of linolenic acid suggests that a local response to aphid feeding was triggered during acorn development. In boreal trees, aphid feeding increased up to 50% the emission of methyl salicylate, a defence compound of plants, that acts as aphid repellent and an attractor of foraging predators and parasitoids.24Open in a separate windowFigure 1Mean (±SE) of the percentage of each fatty acid relative to the total amount of fatty acids of acorns from holm oaks colonized by invasive ants L. neglectus (in grey) or by native ants L. grandis (in white). Asterisk shows significant differences of linolenic content (Mann Whitney, U = 7.5, p = 0.026).We then performed a germination test at the second year when enough acorns reached maturity. We picked mature acorns from trees colonized by the invasive or by the native ant. Those acorns with visual evidence of being infested by insect larvae were discarded as non-viable. From the group of healthy acorns, we chose randomly between 6 to 18 acorns per tree comprising in total 94 or 97 acorns for holm oaks colonized by L. neglectus or L. grandis, respectively. We performed a laboratory germination test at 20–25°C under natural light conditions. Acorns were planted in nursery flats of 300 cc filled with commercial compost (70% organic matter, pH = 6.5), watered twice a week and inspected daily from January to April until emergency. After 90 days, acorn viability (germination + seedling emergence) was 89% and 87% for acorns from holm oaks colonized by the invasive or by native ant, respectevily. Puerta-Piñeiro et al. obtained a 90% acorn viability when acorns where sown in sterilized river sand. On the other hand, Leiva and Fernαndez-Alés37 sowed 20 acorns per 7l pots filled with peat and obtained 59% of acorn viability. In our test, we sowed acorns in separate flats under a less competitive environment. The mean time of seedling emergence was 47.8 ± 13.1 days for acorns from holm oaks colonized by L. neglectus and 47.3 ± 14.1 days for acorns from holm oaks colonized by L. grandis. We randomly chose 10 one-month-old seedlings to calculate their quality using the Dickson index.38 This index indicates the potentiality of a seedling to survive and to grow by combining the ratio between root biomass and total biomass with the height and the diameter of the sapling. Seedlings with a higher quality have a higher index. Seedlings showed a very low and similar Dickson index (Mann-Whitnney, L. neglectus: 0.072 ± 0.015; L. grandis: 0.075 ± 0.015, U = 44, p = 0.68, n = 10 seedlings). The low values of Dickson index of the two treatments suggest that from the chosen acorns, emerged seedlings had, per se, a low quality. Only a long term experiment, i.e., at least 10 years to achieve at least two masting years with reproductive holm oaks that never had been infested with aphids, and another group that was infested, could reveal if the effect of aphid feeding on acorns really affect holm oak fitness.We conclude that ants, through their mutualism with tended aphids, may promote considerable changes of holm oaks VOCs emission and acorn quality. However, there was no effect on seedling quality in spite of the decrease of linolenic acid content of acorns from holm oaks where aphids were tended by the invasive ant. These results indicate that the physiological response of acorns to aphid feeding tended by invasive or local ants does not necessary imply a low quality of seedlings as we previously expected. Under natural conditions, the emission of mature holm oak doubled those of saplings from a plantation.39 So considering that we performed our experiment using 4-year-old saplings, it is probable that the indirect effect of ants on VOCs emissions and acorn quality could be magnified when aphid outbreaks occur in mature holm oak forest. Taking into account the contribution of monoterpenes and isoprene emitted by mediterranean and boreal forests to atmospheric VOC pools40 and the species richness of aphids in the north hemisphere,41 we suggest, in agreement with Blande et al., that aphid infestations should be considered in future models of biogenic VOC emissions from forests.  相似文献   

9.
Lessons from investigation of regulation of APS reductase by salt stress     
Anna Koprivova  Stanislav Kopriva 《Plant signaling & behavior》2008,3(8):567-569
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10.
Gene silencing to investigate the roles of receptor-like proteins in Arabidopsis     
Ursula Ellendorff  Zhao Zhang  Bart PHJ Thomma 《Plant signaling & behavior》2008,3(10):893-896
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11.
Genome-wide analysis of lipoxygenase gene family in Arabidopsis and rice     
Pavan Umate 《Plant signaling & behavior》2011,6(3):335-338
The enzymes called lipoxygenases (LOXs) can dioxygenate unsaturated fatty acids, which leads to lipoperoxidation of biological membranes. This process causes synthesis of signaling molecules and also leads to changes in cellular metabolism. LOXs are known to be involved in apoptotic (programmed cell death) pathway, and biotic and abiotic stress responses in plants. Here, the members of LOX gene family in Arabidopsis and rice are identified. The Arabidopsis and rice genomes encode 6 and 14 LOX proteins, respectively, and interestingly, with more LOX genes in rice. The rice LOXs are validated based on protein alignment studies. This is the first report wherein LOXs are identified in rice which may allow better understanding the initiation, progression and effects of apoptosis, and responses to bitoic and abiotic stresses and signaling cascades in plants.Key words: apoptosis, biotic and abiotic stresses, genomics, jasmonic acid, lipidsLipoxygenases (linoleate:oxygen oxidoreductase, EC 1.13.11.-; LOXs) catalyze the conversion of polyunsaturated fatty acids (lipids) into conjugated hydroperoxides. This process is called hydroperoxidation of lipids. LOXs are monomeric, non-heme and non-sulfur, but iron-containing dioxygenases widely expressed in fungi, animal and plant cells, and are known to be absent in prokaryotes. However, a recent finding suggests the existence of LOX-related genomic sequences in bacteria but not in archaea.1 The inflammatory conditions in mammals like bronchial asthama, psoriasis and arthritis are a result of LOXs reactions.2 Further, several clinical conditions like HIV-1 infection,3 disease of kidneys due to the activation of 5-lipoxygenase,4,5 aging of the brain due to neuronal 5-lipoxygenase6 and atherosclerosis7 are mediated by LOXs. In plants, LOXs are involved in response to biotic and abiotic stresses.8 They are involved in germination9 and also in traumatin and jasmonic acid biochemical pathways.10,11 Studies on LOX in rice are conducted to develop novel strategies against insect pests12 in response to wounding and insect attack,13 and on rice bran extracts as functional foods and dietary supplements for control of inflammation and joint health.14 In Arabidopsis, LOXs are studied in response to natural and stress-induced senescence,15 transition to flowering,16 regulation of lateral root development and defense response.17The arachidonic, linoleic and linolenic acids can act as substrates for different LOX isozymes. A hydroperoxy group is added at carbons 5, 12 or 15, when arachidonic acid is the substrate, and so the LOXs are designated as 5-, 12- or 15-lipoxygenases. Sequences are available in the database for plant lipoxygenases (EC:1.13.11.12), mammalian arachidonate 5-lipoxygenase (EC:1.13.11.34), mammalian arachidonate 12-lipoxygenase (EC:1.13.11.31) and mammalian erythroid cell-specific 15-lipoxygenase (EC:1.13.11.33). The prototype member for LOX family, LOX-1 of Glycine max L. (soybean) is a 15-lipoxygenase. The LOX isoforms of soybean (LOX-1, LOX-2, LOX-3a and LOX-3b) are the most characterized of plant LOXs.18 In addition, five vegetative LOXs (VLX-A, -B, -C, -D, -E) are detected in soybean leaves.19 The 3-dimensional structure of soybean LOX-1 has been determined.20,21 LOX-1 was shown to be made of two domains, the N-terminal domain-I which forms a β-barrel of 146 residues, and a C-terminal domain-II of bundle of helices of 693 residues21 (Fig. 1). The iron atom was shown to be at the centre of domain-II bound by four coordinating ligands, of which three are histidine residues.22Open in a separate windowFigure 1Three-dimensional structure of soybean lipoxygenase L-1. The domain I (N-terminal) and domain II (C-terminal) are indicated. The catalytic iron atom is embedded in domain II (PDB ID-1YGE).21This article describes identification of LOX genes in Arabidopsis and rice. The Arabidopsis genome encodes for six LOX proteins23 (www.arabidopsis.org) (LocusAnnotationNomenclatureA*B*C*AT1G55020lipoxygenase 1 (LOX1)LOX185998044.45.2049AT1G17420lipoxygenase 3 (LOX3)LOX3919103725.18.0117AT1G67560lipoxygenase family proteinLOX4917104514.68.0035AT1G72520lipoxygenase, putativeLOX6926104813.17.5213AT3G22400lipoxygenase 5 (LOX5)LOX5886101058.86.6033AT3G45140lipoxygenase 2 (LOX2)LOX2896102044.75.3177Open in a separate window*A, amino acids; B, molecular weight; C, isoelectric point.Interestingly, the rice genome (rice.plantbiology.msu.edu) encodes for 14 LOX proteins as compared to six in Arabidopsis (and22). Of these, majority of them are composed of ∼790–950 aa with the exception for loci, LOC_Os06g04420 (126 aa), LOC_Os02g19790 (297 aa) and LOC_Os12g37320 (359 aa) (Fig. 2).Open in a separate windowFigure 2Protein alignment of rice LOXs and vegetative lipoxygenase, VLX-B,28 a soybean LOX (AA B67732). The 14 rice LOCs are indicated on left and sequence position on right. Gaps are included to improve alignment accuracy. Figure was generated using ClustalX program.

Table 2

Genes encoding lipoxygenases in rice
ChromosomeLocus IdPutative functionA*B*C*
2LOC_Os02g10120lipoxygenase, putative, expressed9271035856.0054
2LOC_Os02g19790lipoxygenase 4, putative29733031.910.4799
3LOC_Os03g08220lipoxygenase protein, putative, expressed9191019597.4252
3LOC_Os03g49260lipoxygenase, putative, expressed86897984.56.8832
3LOC_Os03g49380lipoxygenase, putative, expressed87898697.57.3416
3LOC_Os03g52860lipoxygenase, putative, expressed87197183.56.5956
4LOC_Os04g37430lipoxygenase protein, putative, expressed79889304.610.5125
5LOC_Os05g23880lipoxygenase, putative, expressed84895342.97.6352
6LOC_Os06g04420lipoxygenase 4, putative12614054.76.3516
8LOC_Os08g39840lipoxygenase, chloroplast precursor, putative, expressed9251028196.2564
8LOC_Os08g39850lipoxygenase, chloroplast precursor, putative, expressed9421044947.0056
11LOC_Os11g36719lipoxygenase, putative, expressed86998325.45.3574
12LOC_Os12g37260lipoxygenase 2.1, chloroplast precursor, putative, expressed9231046876.2242
12LOC_Os12g37320lipoxygenase 2.2, chloroplast precursor, putative, expressed35940772.78.5633
Open in a separate window*A, amino acids; B, molecular weight; C, isoelectric point.

Table 3

Percent homology of rice lipoxygenases against Arabidopsis
Loci (Os)Homolog (At)Identity/similarity (%)No. of aa compared
LOC_Os02g10120LOX260/76534
LOC_Os02g19790LOX554/65159
LOC_Os03g08220LOX366/79892
LOC_Os03g49260LOX556/73860
LOC_Os03g49380LOX560/75861
LOC_Os03g52860LOX156/72877
LOC_Os04g37430LOX361/75631
LOC_Os05g23880LOX549/66810
LOC_Os06g04420LOX549/62114
LOC_Os08g39840LOX249/67915
LOC_Os08g39850LOX253/70808
LOC_Os11g36719LOX552/67837
LOC_Os12g37260LOX253/67608
LOC_Os12g37320LOX248/60160
Open in a separate windowOs, Oryza sativa L.; At, Arabidopsis thaliana L.; aa, amino acids.In plants, programmed cell death (PCD) has been linked to different stages of development and senescence, germination and response to cold and salt stresses.24,25 To conclude, this study indicates that rice genome encodes for more LOX proteins as compared to Arabidopsis. The LOX members are not been thoroughly investigated in rice. The more advanced knowledge on LOXs function might spread light on the significant role of LOXs in PCD, biotic and abiotic stress responses in rice.  相似文献   

12.
Sources of floral scent variation: Can environment define floral scent phenotype?     
Cassie J Majetic  Robert A Raguso  Tia-Lynn Ashman 《Plant signaling & behavior》2009,4(2):129-131
Studies of floral scent generally assume that genetic adaptation due to pollinator-mediated natural selection explains a significant amount of phenotypic variance, ignoring the potential for phenotypic plasticity in this trait. In this paper, we assess this latter possibility, looking first at previous studies of floral scent variation in relation to abiotic environmental factors. We then present data from our own research that suggests among-population floral scent variation is determined, in part, by environmental conditions and thus displays phenotypic plasticity. Such an outcome has strong ramifications for the study of floral scent variation; we conclude by presenting some fundamental questions that should lead to greater insight into our understanding of the evolution of this trait, which is important to plant-animal interactions.Key words: abiotic factors, aromatics, floral scent, GxE interaction, phenotypic plasticity, pollination, terpenoids, volatilesFloral scent is thought to function as a major non-visual attractive cue for many pollinators in a large number of plant systems1,2 and therefore most research on this plant trait has proceeded in the context of pollination ecology. Such studies have revealed the physiological and behavioral responses of pollinators to various floral volatiles (reviewed in refs. 3 and 4), convergent evolution of odor phenotypes attractive to specific pollinator classes (reviewed in refs. 5 and 6), reproductive isolation of plant species due to differences in pollinator attraction by scent,7 and instances of deception in which flowers mimic insect pheromones to effect pollination.8 Together, this body of evidence suggests that specific floral scent profiles can have important implications for the reproductive potential of many plant species.This pollinator-centered viewpoint has carried through to research on floral scent variation, including our most recent work on the insect-pollinated species Hesperis matronalis (Brassicaceae).9 Such studies usually suggest that the floral scent variation commonly found within and among individuals, populations and species (reviewed in ref. 2) is due to genetic differentiation as a result of selection by pollinators over time (reviewed in ref. 10). But an organism''s genes are only one factor determining phenotype. Both biotic (living) and abiotic (non-living) environmental conditions can profoundly affect phenotype expression, leading to significant variation. For plants, abiotic factors such as climate and soil chemistry can have particularly strong effects on phenotypes. When these environmental conditions cause changes in phenotype, we would say that a trait displays phenotypic plasticity.1113 A number of studies have uncovered phenotypic plasticity for many different plant traits.12 However, while phenotypic variation in floral scent has been well-documented1,2 and correlated with variation in biotic factors like pollinator behavior,1417 these studies were decidedly focused on natural selection, rather than phenotypic plasticity, as an organizational framework.However, in examining the scientific literature on floral scent, we found four studies in which the effects of naturally variable abiotic factors on floral scent profiles were examined, three of which were performed by the same research group (1821 (21). Moreover, these studies are decidedly not analyzed and interpreted using standard protocols for phenotypic plasticity studies.13

Table 1

A survey of previous studies examining changes in floral scent phenotype due to abiotic factors
StudySpeciesEnvironmental characteristicPlant materialStudy locationChange in volatile emissions?Direction of change
Loper and Berdel 1978Medicago sativa L.IrrigationClonesExperimental farmNon/a
CuttingClonesExperimental farmNon/a
Hansted et al. 1994Ribes nigrumTemperatureTwo varietiesGrowth chamberYes+ temperature, + ER*
Jakobsen and Olsen 1994Trifolium repens L.TemperatureCultivarGrowth chamberYes+ temperature, + ER
IrradianceCultivarGrowth chamberYes+ irradiance, + ER
Air HumidityCultivarGrowth chamberYes+ humidity, − ER
Nielsen et al. 1995Hesperis matronalis L.TemperatureWild seedsGrowth chamberYes+ temperature,
+ monoterpene ER
This study, 2009Hesperis matronalisGrowingWild plantsWild vs.YesWild—different ER,
EnvironmentCommon GardenSC between populations;
Garden—similar ER,
SC between populations
Open in a separate window*Plus signs indicate a numerical increase, minus signs indicate a decrease; ER = floral scent emission rate, SC = scent composition.Research we have conducted in conjunction with our recently published work on the floral scent of H. matronalis9 suggests that some of the natural variation in the odor of this species may be attributable to phenotypic plasticity. We reared potted H. matronalis rosettes from two populations (PA1 and PA2) in northwestern Pennsylvania in a common garden environment and upon flowering, collected scent from these individuals using dynamic headspace extractions (reviewed in ref. 9). We then compared floral scent composition and emission rates of potted plants with each other (between populations in a common garden), as well as with the floral scent profiles of plants reared in their source population (i.e., between individuals from the same population reared in different environments). The results were striking. Analysis of scent composition using non-metric multidimensional scaling and analysis of similarity (NMDS and ANOSIM, respectively: reviewed in ref. 9) suggested that the scent composition of plant populations reared in their native environments differ significantly from each other in terms of two major biosynthetic classes of volatiles—aromatics and terpenoids (Fig. 1, filled symbols only). This was especially true for the aromatic eugenol and derivatives of the terpenoid linalool (furanoid linalool oxides and linalool epoxide). In contrast, common-garden reared plants from different populations did not differ in floral scent composition, regardless of their original source population. Perhaps even more interestingly, while both populations showed changes due to rearing environment, the degree of change differed: in only one population (PA1) did scent composition change significantly between native and garden reared plants (Fig. 1).Open in a separate windowFigure 1NMDS (non-metric multidimensional scaling) plots of scent composition for purple morphs from two populations of Hesperis matronalis—(A) Aromatics and (B) Terpenoids. Filled symbols represent scent from home environment in situ plants, which are significantly different from one another as determined by analysis of similarity (ANOSIM: aromatics—p = 0.03, R = 0.22; terpenoids—p = 0.01, R = 0.25). Open symbols represent scent from plants reared in a common environment. Population PA1 is represented by triangles and population PA2 is represented by squares. Arrows indicate the direction of shift from home environment to common garden floral scent composition; black arrows represent a significant difference between groups determined by ANOSIM (Aromatics—p = 0.01, R = 0.30; Terpenoids—p = 0.06; R = 0.20) and gray arrows represent a non-significant difference.Floral scent emission rate also showed environmentally induced differences. While wild plants from our two populations differed significantly in the amount of scent emitted in situ, with PA1 emitting more total scent, total aromatics and total terpenoids,9 we found that rearing plants from these sites in a common garden environment either significantly reverses the direction of differences in emission rates seen between natural populations, with PA2 now emitting more aromatic scent (Analysis of Variance: F = 4.09; p = 0.05; Fig. 2A), or homogenizes the quantity of scent emitted (i.e., no significant differences in emission rates between populations; Fig. 2B and C).Open in a separate windowFigure 2Box plots of scent emission rates for purple Hesperis matronalis plants grown in common garden environments in terms of (A) Aromatics, (B) Terpenoids and (C) Total Scent. The edges of each box represent the range of data between the 25th percentile and the 75th percentile, while the horizontal bar indicates the median for each population. The error bars on each box extend to the 5th and 95th percentile of the data range respectively. To the right of each box plot, the mean is presented as a horizontal line, with standard error bars. Mean values not sharing letters are significantly different as determined by analysis of variance (ANOVA).Together, these results suggest that rearing environment can have a profound effect on floral scent composition and emission rate, such that plants from the same maternal environment can have radically different floral scent phenotypes in response to differential growing conditions. If our work effectively incorporates a random genetic sample from each population into each growing environment, then at least some of the phenotypic variation we describe here could be interpreted as phenotypic plasticity. This experiment does not allow us to pinpoint the exact environmental conditions associated with phenotypic differences in floral scent (although variation in nutrient or water availability between wild and common-garden settings is likely), nor does it completely conform to the traditional “reactionnorm” studies associated with plasticity research which would allow detection of genetic variation in scent plastiticy.12,13 However, our results suggest that floral scent of plants grown in wild populations may be plastic, which provides some additional insight into our recently published work uncovering significant among-population variation in floral scent.9 For researchers that study phenotypic plasticity, such an outcome is probably not a surprise, nor is our finding that populations respond differently to environmental conditions (i.e., potential GxE interaction, reflecting genetic variability in plasticity).However, if floral scent can be plastic, this raises a number of biologically relevant questions that should be addressed in floral scent research, including: (1) Is there truly a canonical floral scent blend that can be attributed to a given plant species, as is normally supposed by those studying floral scent from an evolutionary perspective? (2) Which environmental conditions exert the strongest influence on floral scent profiles in a species? (3) How do such conditions interact with genetic variation in the factors responsible for scent biosynthesis and emission? (4) Are floral scent profiles plastic within a single flowering period; if so, what impact does this have on pollinator behavior and therefore plant fitness? (5) At what scale do biotic agents such as pollinators and herbivores respond to quantitative and qualitative variation in floral scent? Studies that address these questions should lead us to a more mature understanding of the causes and consequences of natural variation in floral scent.  相似文献   

13.
De novo mammalian prion synthesis     
Federico Benetti  Giuseppe Legname 《朊病毒》2009,3(4):213-219
Prions are responsible for a heterogeneous group of fatal neurodegenerative diseases. They can be sporadic, genetic, or infectious disorders involving post-translational modifications of the cellular prion protein (PrPC). Prions (PrPSc) are characterized by their infectious property and intrinsic ability to convert the physiological PrPC into the pathological form, acting as a template. The “protein-only” hypothesis, postulated by Stanley B. Prusiner, implies the possibility to generate de novo prions in vivo and in vitro. Here we describe major milestones towards proving this hypothesis, taking into account physiological environment/s, biochemical properties and interactors of the PrPC.Key words: prion protein (PrP), prions, amyloid, recombinant prion protein, transgenic mouse, protein misfolding cyclic amplification (PMCA), synthethic prionPrions are responsible for a heterogeneous group of fatal neurodegenerative diseases (1 They can be sporadic, genetic or infectious disorders involving post-translational modifications of the cellular prion protein (PrPC).2 Prions are characterized by their infectious properties and by their intrinsic ability to encipher distinct biochemical properties through their secondary, tertiary and quaternary protein structures. In particular, the transmission of the disease is due to the ability of a prion to convert the physiological PrPC into the pathological form (PrPSc), acting as a template.3 The two isoforms of PrP appear to be different in terms of protein structures, as revealed by optical spectroscopy experiments such as Fourier-transform infrared and circular dichroism.4 PrPC contains 40% α-helix and 3% β-sheet, while the pathological isoform, PrPSc, presents approximately 30% α-helix and 45% β-sheet.4,5 PrPSc differs from PrPC because of its altered physical-chemical properties such as insolubility in non-denaturing detergents and proteinases resistance.2,6,7

Table 1

The prion diseases
Prion diseaseHostMechanism
iCJDhumansinfection
vCJDhumansinfection
fCJDhumansgenetic: octarepeat insertion, D178N-129V, V180I, T183A, T188K, T188R-129V, E196K, E200K, V203I, R208H, V210I, E211Q, M232R
sCJDhumans?
GSShumansgenetic: octarepeat insertion, P102L-129M, P105-129M, A117V-129V, G131V-129M, Y145*-129M, H197R-129V, F198S-129V, D202N-129V, Q212P, Q217R-129M, M232T
FFIhumansgenetic: D178-129M
Kurufore peopleinfection
sFIhumans?
Scrapiesheepinfection
BSEcattleinfection
TMEminkinfection
CWDmule deer, elkcontaminated soils?
FSEcatsinfection
Exotic ungulate encephalopathygreater kudu, nyala, oryxinfection
Open in a separate windowi, infective form; v, variant; f, familial; s, sporadic; CJD, Creutzfeldt-Jakob disease; GSS, Gerstmann-Straüssler-Sheinker disease; FFI, fatal familial insomnia; sFI, sporadic fatal insomnia; BSE, bovine spongiform encephalopathy; TME, transmissible mink encephalopathy; CWD, chronic wasting disease; FSE, feline spongiform encephalopathy.73,78The prion conversion occurring in prion diseases seems to involve only conformational changes instead of covalent modifications. However, Mehlhorn et al. demonstrated the importance of a disulfide bond between the two cysteine residues at position 179 and 214 (human (Hu) PrP numbering) to preserve PrP into its physiological form. In the presence of reducing conditions and pH higher than 7, recombinant (rec) PrP tends to assume high β-sheet content and relatively low solubility like PrPSc.8  相似文献   

14.
Low temperature-induced necrosis shows phenotypic plasticity in wheat triploid hybrids     
Shigeo Takumi  Nobuyuki Mizuno 《Plant signaling & behavior》2011,6(10):1431-1433
  相似文献   

15.
Heritability and role for the environment in DNA methylation in AXL receptor tyrosine kinase     
Carrie V Breton  Muhammad T Salam  Frank D Gilliland 《Epigenetics》2011,6(7):895-898
  相似文献   

16.
Natural Infection of Burkholderia pseudomallei in an Imported Pigtail Macaque (Macaca nemestrina) and Management of the Exposed Colony     
Crystal H Johnson  Brianna L Skinner  Sharon M Dietz  David Blaney  Robyn M Engel  George W Lathrop  Alex R Hoffmaster  Jay E Gee  Mindy G Elrod  Nathaniel Powell  Henry Walke 《Comparative medicine》2013,63(6):528-535
Identification of the select agent Burkholderia pseudomallei in macaques imported into the United States is rare. A purpose-bred, 4.5-y-old pigtail macaque (Macaca nemestrina) imported from Southeast Asia was received from a commercial vendor at our facility in March 2012. After the initial acclimation period of 5 to 7 d, physical examination of the macaque revealed a subcutaneous abscess that surrounded the right stifle joint. The wound was treated and resolved over 3 mo. In August 2012, 2 mo after the stifle joint wound resolved, the macaque exhibited neurologic clinical signs. Postmortem microbiologic analysis revealed that the macaque was infected with B. pseudomallei. This case report describes the clinical evaluation of a B. pseudomallei-infected macaque, management and care of the potentially exposed colony of animals, and protocols established for the animal care staff that worked with the infected macaque and potentially exposed colony. This article also provides relevant information on addressing matters related to regulatory issues and risk management of potentially exposed animals and animal care staff.Abbreviations: CDC, Centers for Disease Control and Prevention; IHA, indirect hemagglutination assay; PEP, postexposure prophylacticBurkholderia pseudomallei, formerly known as Pseudomonas pseudomallei, is a gram-negative, aerobic, bipolar, motile, rod-shaped bacterium. B. pseudomallei infections (melioidosis) can be severe and even fatal in both humans and animals. This environmental saprophyte is endemic to Southeast Asia and northern Australia, but it has also been found in other tropical and subtropical areas of the world.7,22,32,42 The bacterium is usually found in soil and water in endemic areas and is transmitted to humans and animals primarily through percutaneous inoculation, ingestion, or inhalation of a contaminated source.8, 22,28,32,42 Human-to-human, animal-to-animal, and animal-to-human spread are rare.8,32 In December 2012, the National Select Agent Registry designated B. pseudomallei as a Tier 1 overlap select agent.39 Organisms classified as Tier 1 agents present the highest risk of deliberate misuse, with the most significant potential for mass casualties or devastating effects to the economy, critical infrastructure, or public confidence. Select agents with this status have the potential to pose a severe threat to human and animal health or safety or the ability to be used as a biologic weapon.39Melioidosis in humans can be challenging to diagnose and treat because the organism can remain latent for years and is resistant to many antibiotics.12,37,41 B. pseudomallei can survive in phagocytic cells, a phenomenon that may be associated with latent infections.19,38 The incubation period in naturally infected animals ranges from 1 d to many years, but symptoms typically appear 2 to 4 wk after exposure.13,17,35,38 Disease generally presents in 1 of 2 forms: localized infection or septicemia.22 Multiple methods are used to diagnose melioidosis, including immunofluorescence, serology, and PCR analysis, but isolation of the bacteria from blood, urine, sputum, throat swabs, abscesses, skin, or tissue lesions remains the ‘gold standard.’9,22,40,42 The prognosis varies based on presentation, time to diagnosis, initiation of appropriate antimicrobial treatment, and underlying comorbidities.7,28,42 Currently, there is no licensed vaccine to prevent melioidosis.There are several published reports of naturally occurring melioidosis in a variety of nonhuman primates (NHP; 2,10,13,17,25,30,31,35 The first reported case of melioidosis in monkeys was recorded in 1932, and the first published case in a macaque species was in 1966.30 In the United States, there have only been 7 documented cases of NHP with B. pseudomallei infection.2,13,17 All of these cases occurred prior to the classification of B. pseudomallei as a select agent. Clinical signs in NHP range from subclinical or subacute illness to acute septicemia, localized infection, and chronic infection. NHP with melioidosis can be asymptomatic or exhibit clinical signs such as anorexia, wasting, purulent drainage, subcutaneous abscesses, and other soft tissue lesions. Lymphadenitis, lameness, osteomyelitis, paralysis and other CNS signs have also been reported.2,7,10,22,28,32 In comparison, human''s clinical signs range from abscesses, skin ulceration, fever, headache, joint pain, and muscle tenderness to abdominal pain, anorexia, respiratory distress, seizures, and septicemia.7,9,21,22

Table 1.

Summary of reported cases of naturally occurring Burkholderia pseudomalleiinfections in nonhuman primates
CountryaImported fromDate reportedSpeciesReference
AustraliaBorneo1963Pongo sp.36
BruneiUnknown1982Orangutan (Pongo pygmaeus)33
France1976Hamlyn monkey (Cercopithecus hamlyni) Patas monkey (Erythrocebus patas)11
Great BritainPhilippines and Indonesia1992Cynomolgus monkey (Macaca fascicularis)10
38
MalaysiaUnknown1966Macaca spp.30
Unknown1968Spider monkey (Brachytelis arachnoides) Lar gibbon (Hylobates lar)20
Unknown1969Pig-tailed macaque (Macaca nemestrina)35
Unknown1984Banded leaf monkey (Presbytis melalophos)25
SingaporeUnknown1995Gorillas, gibbon, mandrill, chimpanzee43
ThailandUnknown2012Monkey19
United StatesThailand1970Stump-tailed macaque (Macaca arctoides)17
IndiaPig-tailed macaque (Macaca nemestrina)
AfricaRhesus macaque (Macaca mulatta) Chimpanzee (Pan troglodytes)
Unknown1971Chimpanzee (Pan troglodytes)3
Malaysia1981Pig-tailed macaque (Macaca nemestrina)2
Wild-caught, unknown1986Rhesus macaque (Macaca mulatta)13
Indonesia2013Pig-tailed macaque (Macaca nemestrina)Current article
Open in a separate windowaCountry reflects the location where the animal was housed at the time of diagosis.Here we describe a case of melioidosis diagnosed in a pigtail macaque (Macaca nemestrina) imported into the United States from Indonesia and the implications of the detection of a select agent identified in a laboratory research colony. We also discuss the management and care of the exposed colony, zoonotic concerns regarding the animal care staff that worked with the shipment of macaques, effects on research studies, and the procedures involved in reporting a select agent incident.  相似文献   

17.
Induction of systemic resistance in rice by leaf extracts of Zizyphus jujuba and Ipomoea carnea against Rhizoctonia solani     
Sateesh Kagale  Thambiayya Marimuthu  Jayashree Kagale  Balsamy Thayumanavan  Ramasamy Samiyappan 《Plant signaling & behavior》2011,6(7):919-923
Plants accumulate a great diversity of natural products, many of which confer protective effects against phytopathogenic attack. Earlier we had demonstrated that the leaf extracts of Zizyphus jujuba and Ipomoea carnea inhibit the in vitro mycelial growth of Rhizoctonia solani, and effectively reduce the incidence of sheath blight disease in rice.7 Here we demonstrate that foliar application of the aqueous leaf extracts of Z. jujuba and I. carnea followed by challenge inoculation with R. solani induces systemic resistance in rice as evident from significantly increased accumulation of pathogenesis-related proteins such as chitinase, β-1,3-glucanase and peroxidase, as well as defense-related compounds such as phenylalanine ammonia-lyase and phenolic substances. Thin layer chromatographic separation of secondary metabolites revealed presence of alkaloid and terpenoid compounds in the leaf extracts of Z. jujuba that exhibited toxicity against R. solani under in vitro condition. Thus, the enhanced sheath blight resistance in rice seedlings treated with leaf extracts of Z. jujuba or I. carnea can be attributed to the direct inhibitory effects of these leaf extracts as well as their ability to elicit systemic resistance against R. solani.Key words: sheath blight, Zizyphus jujuba, Ipomoea carnea, Rhizoctonia solani, induced systemic resistance, antimicrobial compoundsSheath blight disease of rice, caused by Rhizoctonia solani, has become a major production constraint in intensive rice cropping systems where semi-dwarf, nitrogen-responsive and high-yielding rice cultivars are grown. The disease causes an annual yield loss of upto 50%.1 R. solani is both soil- and water-borne, and can infect more than 27 families of both monocot and dicot species.2 Natural host genetic resistance to R. solani has not been recorded in cultivars or wild relatives of rice.3 Several broad spectrum fungicides have been recommended for control of sheath blight, however, chemical method of disease management is neither practical due to high cost of fungicides nor sustainable as it can affect the balance of ecosystem by destroying beneficial microbial population. In addition, the environmental pollution problems associated with indiscriminate use of synthetic pesticides have prompted investigations on exploiting bio-pesticides of plant and microbial origin.Plants accumulate an enormous variety of over 100,000 secondary metabolites,4 which can act as pre-existing chemical inhibitors to invading pathogens and/or help strengthen defense response of host plant. The pre-formed infectional barriers in plants are generally referred to as “phytoanticipins;” whereas, the antimicrobial compounds that are synthesized de novo in response to pathogen attack are referred to as “phytoalexins.”5 Because of years of selective breeding leading to removal of natural products, the endogenous levels of phytoanticipins in commonly cultivated crop species are generally low and often not sufficient to fight pathogen attack, effectively.4 Various weed species and wild relatives of crop plants that are not subjected to selective breeding are believed to contain higher levels of antimicrobial compounds, consistent with their ability to fight invading pathogens more effectively than cultivated crop species. Identification of such weed/plant species that are enriched with antimicrobial principles, isolation of bio-active compounds from them, and application in the form of concentrated formulations to crop plants can augment their disease resistance capability by directly inhibiting the growth of pathogen and inducing defense responses. Indeed, the antimicrobial properties of tissue extracts of several weed/plant species have been reported by a number of research groups world-wide, especially in Asia and Latin America.613Earlier, we had evaluated the antimicrobial activity of leaf extracts of 16 different plant species belonging to 16 different families and demonstrated that leaf extracts of most of these plant species exhibit growth-inhibitory activities against R. solani and Xanathomoas oryzae pv. oryzae (Xoo).7 Among these, the leaf extracts of Datura metel were found to be the most effective in inhibiting the mycelial growth and sclerotia formation of R. solani, and the growth of Xoo, as well as in reducing the incidence of sheath blight and bacterial blight diseases caused by these pathogens, respectively, under greenhouse condition.7 We further demonstrated that rice seedlings treated with leaf extracts of D. metel accumulated significantly higher levels of pathogenesis-related (PR) proteins and other defense related compounds following challenge inoculation with R. solani or Xoo.7 Our attempts to identify biologically active compounds from D. metel revealed the presence of a withanolide compound “daturilin” that exhibited remarkable antibacterial activity against Xoo.7Apart from D. metel, two other plants species, Zizyphus jujuba and Ipomoea carnea, were found to possess remarkable antifungal activity against R. solani.7 Z. jujuba is a thorny rhamnaceous plant that is widely distributed in Europe and South-eastern Asia. I. carnea of convolvulaceae family, commonly known as morning glory, is a toxic weed found in abundance in India, Brazil, the United States and other countries.14 Both of these plant species have allelopathic effect and are commonly used in folklore medicine for curing multiple diseases.1518 The aqueous and methanol leaf extracts of Z. jujuba and I. carnea have been found to be highly effective in reducing in vitro mycelial growth, and therefore, sclerotia production of R. solani.7 In the greenhouse experiments, rice seedlings sprayed with leaf extracts of Z. jujuba and I. carnea exhibited 44 and 34% reduction in severity of sheath blight disease over the control, respectively.7 While these findings are encouraging, the mechanisms by which the leaf extracts of Z. jujuba and I. carnea modulate defense responses in rice have not yet been explored.Plants are endowed with defense genes which remain quiescent or are expressed at basal levels in healthy plants. Activation of defense genes results in induction of systemic resistance in host plant; this defense response, designated as induced systemic resistance (ISR), plays an important role in development of disease resistance.19 The onset of ISR in plants correlates with accumulation of phytoalexins and increased activity of PR proteins such as chitinases, β-1,3-glucanases and peroxidases;2023 consequently, PR proteins are generally used as ISR markers.19 The classical inducers of ISR include both biotic and abiotic factors, including disease causing microorganisms themselves,24,25 plant growth promoting rhizobacteria,22,26 chemicals27,28 and natural plant products.7,10,12,13,29,30 Plant products have been considered as one of the major groups of compounds that induce ISR. To date, extracts of at least a few plant species have been reported to contain allelopathic substances which can act as elicitors and induce systemic resistance in host plants resulting in reduction or inhibition of disease development.7,10,12,13In the present study, with the objective of understanding the mechanisms of disease suppression by leaf extracts of Z. jujuba and I. carnea, we investigated their ability to induce ISR in rice by analyzing the activities of ISR markers including PR-proteins and other defense enzymes involved in phenylpropanoid metabolism. The changes in activities of chitinase, β-1,3-glucanase, peroxidase, phenylalanine ammonia-lyase (PAL) and phenolic compounds induced in rice seedlings that were elicited with leaf extracts (at 1:10 dilution; w/v) of Z. jujuba or I. carnea and infected with R. solani were analyzed, and compared to changes in non-elicited and uninfected seedlings. Rice seedlings that were both elicited with leaf extracts of Z. jujuba or I. carnea and infected with R. solani accumulated significantly higher levels (2–5-fold) of ISR markers as compared to non-elicited and/or uninfected seedlings (Fig. 1). About two-fold increase in activities of ISR markers was also observed in seedlings that were either infected but not elicited or elicited but not infected; however, this increase was significantly lower than the changes in seedlings that were both elicited and infected (Fig. 1). Although the activity of all ISR markers began to increase around or after 24 h post-infection, at least two distinct induction patterns were observed. For instance, the activities of chitinase and phenolic substances gradually increased to reach maximum levels at 164 h post-infection (Fig. 1A and E); whereas, the activities of β-1,3-glucanase, peroxidase and PAL reached maximum levels at 72 to 96 h post-infection and decreased thereafter (Fig. 1B–D). The leaf extracts of Z. jujuba were found slightly more effective in inducing ISR markers than the leaf extracts of I. carnea. There was no significant change in the activity of ISR markers in control seedlings sprayed with sterile distilled water (Fig. 1). Collectively, these results suggested that the leaf extracts of Z. jujuba and I. carnea have the ability to induce systemic resistance in rice seedlings infected with R. solani. The fungitoxicity of the leaf extracts of Z. jujuba and I. carnea 7 combined with their ability to elicit ISR is possibly responsible for low sheath blight disease incidence observed in rice seedlings treated with these leaf extracts.7Open in a separate windowFigure 1Activity of ISR markers and defense-related compounds in rice seedlings elicited with the leaf extracts of Zizyphus jujuba or Ipomoea carnea and challenge inoculated with Rhizoctonia solani. Total activity of chitinase (A), β-1,3-glucanase (B), peroxidase (C) phenylalanine ammonia-lyase (PAL; D) and phenolic substances (E) was analyzed in rice seedlings. The inoculation of rice seedlings with R. solani was performed 45 days after planting. Spraying of leaf extracts (1:10 dilution; w/v) of Z. jujuba or I. carnea was performed two days prior to inoculation. Tissue samples (sheath) from elicited and/or infected seedlings were collected for analysis at various time intervals.The in vitro antimicrobial and in vivo disease inhibitory effects of natural plant products are generally attributed to the allelopathic substances present in them. However, very few attempts have been made to purify and characterize active principles from bio-active natural plant products. We have previously identified a withanolide compound from leaf extracts of D. metel which exhibited antibacterial activity against Xoo.7 Both Z. jujuba and I. carnea are rich source of secondary metabolites including alkaloids, terpenoids, flavonoids and phenolic compounds.3135 To determine the composition of bio-active ingredients within the leaf extracts of Z. jujuba and I. carnea, we performed thin layer chromatographic separation of alkaloid, terpenoid and phenolic compounds. The partially purified compounds, as reported in Leaf extractRf valueAnti-fungal activity against R. solani*VisibleIodine vaporsUV-lightSpray reagentPhenolic substances1Z. jujuba0.6960.696-0.696-I. carnea-0.807-0.807-Terpenoid compounds2Z. jujuba---0.189-0.3580.3580.3580.3585.1 mm---0.4463.7 mmI. carnea-0.5900.5900.590-Alkaloid compounds3Z. jujuba-0.784-0.7845.1 mmI. carnea-0.806-0.806-Open in a separate window*Inhibition zone diameter (mm) as mean of triplicate tests.1Solvent-acetic acid:chloroform (1:9); Spray reagent-Diazotised sulphanilic acid.2Solvent-methanol:chloroform (2:9); Spray reagent-10% vanillin-sulphuric acid.3Solvent-methanol:chloroform (1:1); Spray reagent-Drag endorffs reagent.In conclusion, our results together with several other reports in the literature have established that natural plant products possess antimicrobial substances that can inhibit the growth of the pathogens and augment disease resistance capability of plants by eliciting ISR in host plants. In the immediate future, identification and characterization of additional novel bio-active compounds from natural plant products is essential for developing commercial formulations of potential use in controlling pathogenic diseases in crop plants.Rice cultivar, IR-50 (susceptible to sheath blight) and virulent isolate of R. solani (RS7 Anastamosis group AG1),36 were used in all experiments. The leaf tissues of Z. jujuba and I. carnea were collected from local areas around Coimbatore, India and aqueous extracts were prepared, as described previously in reference 7. Forty-five-day-old rice seedlings were sprayed with either aqueous leaf extracts (1:10 dilution) or sterile distilled water, two-days prior to inoculation with sclerotia of R. solani.37 Sheath tissues from infected seedlings were collected at various time intervals, including 0, 24, 48, 72, 96 and 164 h after pathogen inoculation. The changes in the chitinase and peroxidase activities were determined by colorimetric assays, as described previously by Boller and Mauch,38 and Hammerschmidt et al.39 respectively. β-1,3-glucanase activity was assayed by the laminarin-dinitrosalicylic acid method.40 PAL activity was determined as the rate of conversion of L-phenylalanine to trans-cinnamic acid at 290 nm as described by Dickerson et al.41 The amount of trans-cinnamic acid synthesized was calculated using its extinction coefficient of 9,630 M−1. Estimation of phenolic substances was carried out as described previously in reference 7.TLC was carried out on 20 × 20 cm glass plate coated with0.5 mm thickness silica gel. Twenty microliters of Z. jujuba and I. carnea leaf extracts (1 g/ml) were spotted on each plate. The mixture of solvents comprising acetic acid:chloroform (1:9), methanol:chloroform (2:9) or methanol:chloroform (1:1) were used to develop the chromatograms for detection of phenolic, terpenoid or alkaloid compounds, respectively. The developed chromatograms were observed under visible, UV light and after exposing to iodine vapours. Additionally, the chemical class specific visualization spray reagents were used for detection of phenolic substances (Diazotized sulphanilic acid), terpenoids (10% vanillin-sulphuric acid) and alkaloids (Dragendorffs reagent). Preparative TLC was carried out using 2 mm thickness silica gel. The Rf value of each spot detected on the chromatogram was recorded. The silica gel corresponding to each spot was scraped off and the chemical compound was eluted using sterile water. The eluted compound was tested for its antimicrobial activity using the inhibition zone technique.42  相似文献   

18.
Aluminum induced proteome changes in tomato cotyledons     
Suping Zhou  Roger Sauve  Theodore W Thannhauser 《Plant signaling & behavior》2009,4(8):769-772
Cotyledons of tomato seedlings that germinated in a 20 µM AlK(SO4)2 solution remained chlorotic while those germinated in an aluminum free medium were normal (green) in color. Previously, we have reported the effect of aluminum toxicity on root proteome in tomato seedlings (Zhou et al.1). Two dimensional DIGE protein analysis demonstrated that Al stress affected three major processes in the chlorotic cotyledons: antioxidant and detoxification metabolism (induced), glyoxylate and glycolytic processes (enhanced), and the photosynthetic and carbon fixation machinery (suppressed).Key words: aluminum, cotyledons, proteome, tomatoDifferent biochemical processes occur depending on the developmental stages of cotyledons. During early seed germination, before the greening of the cotyledons, glyoxysomes enzymes are very active. Fatty acids are converted to glucose via the gluconeogenesis pathway.2,3 In greening cotyledons, chloroplast proteins for photosynthesis and leaf peroxisomal enzymes in the glycolate pathway for photorespiration are metabolized.24 Enzymes involved in regulatory mechanisms such as protein kinases, protein phosphatases, and mitochondrial enzymes are highly expressed.3,5,6The chlorotic cotyledons are similar to other chlorotic counterparts in that both contains lower levels of chlorophyll, thus the photosynthetic activities are not as active. In order to understand the impact of Al on tomato cotyledon development, a comparative proteome analysis was performed using 2D-DIGE following the as previously described procedure.1 Some proteins accumulated differentially in Al-treated (chlorotic) and untreated cotyledons (Fig. 1). Mass spectrometry of tryptic digestion fragments of the proteins followed by database search has identified some of the differentially expressed proteins (Open in a separate windowFigure 1Image of protein spots generated by Samspot analysis of Al treated and untreated tomato cotyledons proteomes separated on 2D-DIGE.

Table 1

Proteins identified from tomato cotyledons of seeds germinating in Al-solution
Spot No.Fold (treated/ctr)ANOVA (p value)AnnotationSGN accession
12.340.00137412S seed storages protein (CRA1)SGN-U314355
22.130.003651unidentified
32.00.006353lipase class 3 familySGN-U312972
41.960.002351large subunit of RUBISCOSGN-U346314
51.952.66E-05arginine-tRNA ligaseSGN-U316216
61.950.003343unidentified
71.780.009219Monodehydroascorbate reductase (NADH)SGN-U315877
81.780.000343unidentified
91.754.67E-05unidentified
121.700.002093unidentified
131.680.004522unidentified
151.660.019437Glutamate dehydrogenase 1SGN-U312368
161.660.027183unidentified
171.622.01E-08Major latex protein-related, pathogenesis-relatedSGN-U312368
18−1.610.009019RUBisCo activaseSGN-U312543
191.610.003876Cupin family proteinSGN-U312537
201.600.000376unidentified
221.590.037216unidentified
0.003147unidentified
29−1.560.001267RUBisCo activaseSGN-U312543
351.520.001955unidentified
401.470.007025unidentified
411.470.009446unidentified
451.450.001134unidentified
59−1.405.91E-0512 S seed storage proteinSGN-U314355
611.391.96E-05MD-2-related lipid recognition domain containing proteinSGN-U312452
651.370.000608triosephosphate isomerase, cytosolicSGN-U312988
681.360.004225unidentified
811.320.001128unidentified
82−1.310.00140833 kDa precursor protein of oxygen-evolving complexSGN-U312530
871.300.002306unidentified
89−1.30.000765unidentified
921.290.000125superoxide dismutaseSGN-U314405
981.280.000246triosephosphate isomerase, cytosolicSGN-U312988
Open in a separate window  相似文献   

19.
Interactions of meniscal cells with extracellular matrix molecules: Towards the generation of tissue engineered menisci     
Guak-Kim Tan  Justin J Cooper-White 《Cell Adhesion & Migration》2011,5(3):220-226
  相似文献   

20.
Are loline alkaloid levels regulated in grass endophytes by gene expression or substrate availability?     
Dong-Xiu Zhang  Padmaja Nagabhyru  Jimmy D Blankenship  Christopher L Schardl 《Plant signaling & behavior》2010,5(11):1419-1422
  相似文献   

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