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1.
Sameh S. Ali Maria-Cecilia Garibaldi Marcondes Hilda Bajova Laura L. Dugan Bruno Conti 《The Journal of biological chemistry》2010,285(42):32522-32528
Temperature (T) reduction increases lifespan, but the mechanisms are not understood. Because reactive oxygen species (ROS) contribute to aging, we hypothesized that lowering T might decrease mitochondrial ROS production. We measured respiratory response and ROS production in isolated mitochondria at 32, 35, and 37 °C. Lowering T decreased the rates of resting (state 4) and phosphorylating (state 3) respiration phases. Surprisingly, this respiratory slowdown was associated with an increase of ROS production and hydrogen peroxide release and with elevation of the mitochondrial membrane potential, ΔΨm. We also found that at lower T mitochondria produced more carbon-centered lipid radicals, a species known to activate uncoupling proteins. These data indicate that reduced mitochondrial ROS production is not one of the mechanisms mediating lifespan extension at lower T. They suggest instead that increased ROS leakage may mediate mitochondrial responses to hypothermia. 相似文献
2.
Kiyoon Kang Kyungjin Lee Sangkyu Park Sungbeom Lee Young Soon Kim Kyoungwhan Back 《Journal of Plant Biology》2010,53(4):291-296
Protoporphyrin IX is a photosensitizer and a causative agent of rice membrane lipid peroxidation in plant cells. Protoporphyrinogen
IX oxidase (PPO) is the molecular target of PPO-inhibiting herbicides, which trigger a massive increase in protoporphyrin
IX. Thus, any possible method to decrease the levels of protoporphyrin IX upon challenge with PPO-inhibiting herbicides could
be employed to generate plants resistant to such herbicides. We generated transgenic rice plants overexpressing rice ferrochelatase
isogenes encoding ferrochelatase enzymes, which convert protoporphyrin IX into protoheme, to see whether the transgenic plants
have phenotypes resistant to PPO-inhibiting herbicides. The resulting transgenic rice plants were all susceptible to oxyfluorfen
(a diphenyl-ether-type PPO-inhibiting herbicide), as judged by cellular damage with respect to cellular leakage, chlorophyll
loss, and lipid peroxidation. In particular, the transgenic plants expressing rice ferrochelatase II without its plastid targeting
sequence showed higher transgene expression and oxyfluorfen susceptibility than lines expressing the intact ferrochelatase
II. Possible susceptibility mechanisms to oxyfluorfen herbicide in the transgenic rice plants are discussed. 相似文献
3.
Mitochondria of Isolated Plant Cells (Acer pseudoplatanus L.): II. Copper Deficiency Effects on Cytochrome C Oxidase and Oxygen Uptake 下载免费PDF全文
The effects of copper deficiency on cell culture growth, cell respiration, mitochondrial oxidative properties, and electron transport chain have been studied with suspension-cultured sycamore cells (Acer pseudoplatanus L.). Within the range of the copper concentration studied (0.1-25 μg/1 of culture medium), the mean rate of cell division is independent of copper concentration. An initial copper concentration lower than 2 μg/1 limited the maximum density of population reached at the stationary phase of growth. 相似文献
4.
Amit Pal Rama Kumari Badyal Rakesh Kumar Vasishta Savita Verma Attri Babu Ram Thapa Rajendra Prasad 《Biological trace element research》2013,153(1-3):257-268
Animal models of copper toxicosis rarely exhibit neurological impairments and increased brain copper accumulation impeding the development of novel therapeutic approaches to treat neurodegenerative diseases having high brain Cu content. The aim of this study was to investigate the effects of intraperitoneally injected copper lactate (0.15 mg Cu/100 g body weight) daily for 90 days on copper and zinc levels in the liver and hippocampus, on biochemical parameters, and on neurobehavioral functions (by Morris water maze) of male Wistar rats. Copper-administered animals exhibited significantly decreased serum acetylcholinesterase (AChE) activity and impaired neuromuscular coordination and spatial memory compared to control rats. Copper-intoxicated rats showed significant increase in liver and hippocampus copper content (99.1 and 73 % increase, respectively), 40.7 % reduction in hepatic zinc content, and interestingly, 77.1 % increase in hippocampus zinc content with concomitant increase in copper and zinc levels in serum and urine compared to control rats. Massive grade 4 copper depositions and grade 1 copper-associated protein in hepatocytes of copper-intoxicated rats were substantiated by rhodanine and orcein stains, respectively. Copper-intoxicated rats demonstrated swelling and increase in the number of astrocytes and copper deposition in the choroid plexus, with degenerated neurons showing pyknotic nuclei and dense eosinophilic cytoplasm. In conclusion, the present study shows the first evidence in vivo that chronic copper toxicity causes impaired spatial memory and neuromuscular coordination, swelling of astrocytes, decreased serum AChE activity, copper deposition in the choroid plexus, neuronal degeneration, and augmented levels of copper and zinc in the hippocampus of male Wistar rats. 相似文献
5.
Su R Wang R Guo S Cao H Pan J Li C Shi D Tang Z 《Biological trace element research》2011,144(1-3):668-677
This study is to examine if Cu(2+) can act directly on mitochondria or indirectly by producing reactive oxygen species (ROS), isolated broiler hepatic mitochondria were exposed to different concentrations of Cu(2+) (10, 30, 50?μM). Respiratory chain complex activities, ROS generation, respiratory control ratio (RCR) and mitochondrial membrane potential were investigated. Dose-dependent inhibition of respiratory chain complexes and induction of ROS were observed, which coincided with decreasing RCR both with glutamate?+?malate or succinate. Further investigation indicated that the membrane potential determined by rhodamine 123 release decreased after CuCl(2) exposure at 30 and 50?μM. In addition, the effects of the antioxidants NAC (200?μM) and GSH (200?μM) were studied at 50?μM Cu(2+). The results indicate that Cu can induce mitochondrial dysfunction in excessive dose and the effect of Cu(2+) exposure on respiratory chain is not site-specific, and antioxidants can protect the mitochondrial function by reducing the formation of free radicals. 相似文献
6.
7.
Effect of Synthetic Detergents on the Swelling and the ATPase of Mitochondria Isolated from Rat Liver 下载免费PDF全文
A study was made of the effects of various types of detergents on the swelling of isolated mitochondria and on mitochondrial ATPases which are activated by Mg or DNP respectively. The rate of swelling was measured in the Beckman spectrophotometer by following the decrease in turbidity of dilute suspensions of these organelles. It was found that non-ionic detergents containing a nonyl phenoxy side chain or anionic detergents caused swelling of the mitochondria and activation of Mg-ATPase. On the other hand, cationic detergents promoted the clumping of mitochondria and did not activate Mg-ATPase. DNP-ATPase was inhibited by all of the detergents tested. It would appear from these observations that the inhibition of DNP-ATPase is not related to a gross change in the morphology of the organelles; in contrast, the activation of Mg-ATPase definitely is correlated with swelling of the isolated mitochondria. These data also suggest that the ionic detergents combine with charged sites on the protein moiety of the lipoprotein in the mitochondrial surface, whereas the non-ionic detergents form inclusion compounds with the lipide moiety, thereby altering the mitochondrial structure and permeability. 相似文献
8.
Mahmood Ul-Hassan Andrea Scozzafava Zahid H. Chohan 《Journal of enzyme inhibition and medicinal chemistry》2013,28(6):499-505
Metal complexes of aromatic/heterocyclic sulfonamides act as stronger inhibitors of the zinc enzyme carbonic anhydrase (CA, EC 4.2.1.1) as compared to the uncomplexed sulfonamides from which they are derived. Here we report the synthesis and inhibition studies against the physiologically relevant isozymes CA I, CA II and CA IV, of a series of metal complexes (Co(II), Ni(II) and Cu(II) derivatives) of a Schiff-base ligand, obtained from sulfanilamide and salicylaldehyde. The best activity was observed for the Cu(II) and Co(II) complexes, against CA II and CA IV, for which inhibition constants in the range of 15-39 and 72-108 nM, respectively, were seen. The enhanced efficacy in inhibiting the enzyme may be due to a dual mechanism of action of the metal complexes, which interact with CA both by means of the sulfonamide moieties as well as the metal ions present in their molecule. 相似文献
9.
Hendrik Küpper Birgit G?tz Ana Mijovilovich Frithjof C. Küpper Wolfram Meyer-Klaucke 《Plant physiology》2009,151(2):702-714
The amphibious water plant Crassula helmsii is an invasive copper (Cu)-tolerant neophyte in Europe. It now turned out to accumulate Cu up to more than 9,000 ppm in its shoots at 10 μm (=0.6 ppm) Cu2+ in the nutrient solution, indicating that it is a Cu hyperaccumulator. We investigated uptake, binding environment, and toxicity of Cu in this plant under emerged and submerged conditions. Extended x-ray absorption fine structure measurements on frozen-hydrated samples revealed that Cu was bound almost exclusively by oxygen ligands, likely organic acids, and not any sulfur ligands. Despite significant differences in photosynthesis biochemistry and biophysics between emerged and submerged plants, no differences in Cu ligands were found. While measurements of tissue pH confirmed the diurnal acid cycle typical for Crassulacean acid metabolism, Δ13C measurements showed values typical for regular C3 photosynthesis. Cu-induced inhibition of photosynthesis mainly affected the photosystem II (PSII) reaction center, but with some unusual features. Most obviously, the degree of light saturation of electron transport increased during Cu stress, while maximal dark-adapted PSII quantum yield did not change and light-adapted quantum yield of PSII photochemistry decreased particularly in the first 50 s after onset of actinic irradiance. This combination of changes, which were strongest in submerged cultures, shows a decreasing number of functional reaction centers relative to the antenna in a system with high antenna connectivity. Nonphotochemical quenching, in contrast, was modified by Cu mainly in emerged cultures. Pigment concentrations in stressed plants strongly decreased, but no changes in their ratios occurred, indicating that cells either survived intact or died and bleached quickly.Heavy metals such as cadmium (Cd), copper (Cu), manganese, nickel (Ni), and zinc (Zn) are well known to be essential microelements for the life of plants (for Cd, see Lane and Morel, 2000). On the other hand, elevated concentrations of these metals induce inhibition of various processes in plant metabolism (for review, see Prasad and Hagemeyer, 1999; Küpper and Kroneck, 2005). Cu can occur in very high concentrations that are detrimental or even lethal to most plants. It is widely used as a pesticide in agriculture, and field runoff may easily reach concentrations of several micromolar (Gallagher et al., 2001). Photosynthetic reactions, both photochemical and biochemical ones, belong to the most important sites of inhibition by many heavy metals and in particular Cu. In the thylakoids, PSII has frequently been identified to be the main target. The exact location of its damage, however, strongly depends on the irradiance conditions, as shown originally by Cedeno-Maldonado et al. (1972) and later by Küpper et al. (1996b, 1998, 2002). The latter authors found that in low irradiance including a dark phase, the inhibition of PSII is largely due to the impairment of the correct function of the light-harvesting antenna; this mechanism was termed “shade reaction.” It results from the substitution by heavy metals of the Mg2+ ion in the chlorophyll (Chl) molecules of the light-harvesting complex II. In high irradiance, direct damage to the PSII reaction center (RC) occurs instead, which most likely involves insertion of Cu2+ into the Pheo a of the PSII RC. This was named “sun reaction” (Küpper et al., 1996b, 1998, 2002). Also, oxidative stress has often been described as a result of Cu stress; recent data have shown that in photosynthetic organisms, it is mainly a consequence of an inhibition of the photosynthetic light reactions (Rocchetta and Küpper, 2009).Plants developed a number of strategies to resist the toxicity of heavy metals, as reviewed by Cobbett and Goldsbrough (2002) and Küpper and Kroneck (2005). Such strategies include efflux pumps, sequestration in cells and intracellular compartments where metals do least harm, and binding of heavy metals inside the cells by strong ligands like phytochelatins or free amino acids. A majority of the heavy metal-resistant plants, called “excluders,” prevent the accumulation of heavy metals inside their tissues (Baker, 1981). Other resistant plants actively take up heavy metals, translocate them into the shoot, and sequester them to certain parts of the plant, where they are stored in a harmless state. These plants, which accumulate up to several percent of heavy metals in the dry mass of their aboveground parts, are called “hyperaccumulators” (Brooks et al., 1977). In their natural habitats, metal-rich soils in many parts of the world, this type of heavy metal accumulation serves as a defense against pathogens and herbivores (Boyd and Martens, 1994; Martens and Boyd, 1994; Boyd et al., 2002; Hanson et al., 2003; Jhee et al., 2005). They can now be used for the decontamination (“phytoremediation”) of anthropogenically heavy metal-contaminated soils and in some cases also for the commercial extraction (“phytomining”) of high-value metals (mainly Ni) from metal-rich soils (Baker et al., 1994; McGrath and Zhao, 2003; Chaney et al., 2005).The mechanisms by which hyperaccumulator plants accumulate the enormous amounts of heavy metals in their shoots and prevent phytotoxicity of these metals have been the subject of many studies. Nevertheless, many of these mechanisms are still under debate (Pollard et al., 2002; Küpper and Kroneck, 2005), and a short overview is given in our companion article (Mijovilovich et al., 2009) on Cu in the Cd/Zn model hyperaccumulator plant Thlaspi caerulescens. Studies of arsenic, Cd, Ni, and Zn binding in hyperaccumulators (Krämer et al., 1996; Sagner et al., 1998; Salt et al., 1999, Wang et al., 2002; Küpper et al., 2004) indicated that in such plants most of the metals are coordinated by organic acids, which are commonly found in plant vacuoles. Nonaccumulator plants, in contrast, are well known to bind heavy metals by strong sulfur ligands such as phytochelatins (mainly for Cd) and metallothioneins (mainly for Cu), as reviewed by Cobbett and Goldsbrough (2002).While hundreds of species have been found to hyperaccumulate Ni and about two dozen to hyperaccumulate Zn, true Cu hyperaccumulation in the sense of reaching thousands of ppm in the shoot dry weight has rarely been confirmed. Most species reported to be Cu hyperaccumulators before were later found to be false positives due to Cu adsorption on the leaf surface, et cetera; actually, none of the species recently revisited had a bioaccumulation factor larger than 1, which is commonly regarded as a necessary prerequisite of true hyperaccumulation (Faucon et al., 2007). But it is important in terms of the general understanding of metal metabolism in plants to identify how plants can cope with Cu toxicity other than excluding it from their metabolism and how far the mechanisms of Cu detoxification and Cu stress differ in Cu-resistant and -accumulating plants from Cu excluders and Cu-sensitive plants. Such questions are important also for breeding better Cd/Zn hyperaccumulators, since such plants (e.g. T. caerulescens) turned out to be Cu sensitive, limiting their phytoremediation potential on soils with mixed contamination (Walker and Bernal, 2004). We now analyzed Cu accumulation and Cu stress in a so far not well-characterized species, the amphibious Crassula helmsii, an aggressively invasive plant in Europe (Küpper et al., 1996a). We chose this plant because in a previous study it had turned out to be much more Cu resistant than all other investigated species (Küpper et al., 1996b), but more in summer than in winter. Moreover, preliminary experiments indicated that under high temperatures and salinity, C. helmsii switches to circadian acid metabolism (CAM), which might cause its elevated Cu resistance in summer due to the enhanced availability of malate as a Cu ligand. CAM metabolism was first reported for C. helmsii by Newman and Raven (1995).In this study, we investigated physiological mechanisms of Cu-induced inhibition of photosynthesis, Crassulacean acid metabolism induction, and Cu accumulation and complexation in C. helmsii. The most important method for our investigations of Cu stress was the two-dimensional (imaging) and spectrally resolved microscopic in vivo measurement of the transients of Chl variable fluorescence in the fluorescence kinetic microscope (FKM; Küpper et al., 2000a, 2007a). Cu ligands were investigated via EXAFS (Technical Term Definition/Explanation Antenna connectivity The likelihood of energy transfer between antennae of different photosystems (PSII and/or PSI) CA Component analysis. In this study, we use this term for the fitting of EXAFS spectra with a linear combination of the EXAFS spectra of model compounds. EXAFS Extended x-ray absorption fine structure F0 Minimal fluorescence yield of a dark-adapted sample, fluorescence in nonactinic measuring light Fm Maximum fluorescence yield of a dark-adapted sample after supersaturating irradiation pulse Fm′ Maximum fluorescence yield of a light-adapted sample after supersaturating irradiation pulse Fv/Fm (Fm − F0)/Fm = maximal dark-adapted quantum yield of PSII photochemistry Fp Fluorescence yield at the P level of the induction curve after the onset of actinic light exposure Light saturation Measured by the increased amplitude of Fp relative to Fm after subtraction of F0. (Fp − F0)/(Fm − F0) is mostly dependent on the ratio of functional antenna molecules to functional RCs and electron transport chains. Under constant actinic irradiance for measuring Fp, a large antenna capturing photons and delivering them to its RC will cause more of the “electron traffic jam” that leads to Fp than a small antenna. ΦPSII Φe = (Fm′ − Ft′)/Fm′ = the light-acclimated efficiency of PSII (Genty et al., 1989). In this article, the use of this parameter is extended to the relaxation period after the end of actinic light to analyze the return of the system to its dark-acclimated state as measured by Fv/Fm. NPQ Nonphotochemical quenching, in this article used as an acronym for the name of this phenomenon. In this article, we measure nonphotochemical quenching as qCN = (Fm − Fm′)/Fm = “complete nonphotochemical quenching of Chl fluorescence,” i.e. with normalization to Fm. Pheo Pheophytin XAS X-ray absorption spectroscopy Z Atomic number