RhoA regulates peroxisome association to microtubules and the actin cytoskeleton

The current view of peroxisome inheritance provides for the formation of new peroxisomes by both budding from the endoplasmic reticulum and autonomous division. Here we investigate peroxisome-cytoskeleton interactions and show by proteomics, biochemical and immunofluorescence analyses that actin, non-muscle myosin IIA (NMM IIA), RhoA, Rho kinase II (ROCKII) and Rab8 associate with peroxisomes. Our data provide evidence that (i) RhoA in its inactive state, maintained for example by C. botulinum toxin exoenzyme C3, dissociates from peroxisomes enabling microtubule-based peroxisomal movements and (ii) dominant-active RhoA targets to peroxisomes, uncouples the organelles from microtubules and favors Rho kinase recruitment to peroxisomes. We suggest that ROCKII activates NMM IIA mediating local peroxisomal constrictions. Although our understanding of peroxisome-cytoskeleton interactions is still incomplete, a picture is emerging demonstrating alternate RhoA-dependent association of peroxisomes to the microtubular and actin cytoskeleton. Whereas association of peroxisomes to microtubules clearly serves bidirectional, long-range saltatory movements, peroxisome-acto-myosin interactions may support biogenetic functions balancing peroxisome size, shape, number, and clustering.     

pH regulation in apoplastic and cytoplasmic cell compartments of leaves

 The regulation of pH in the apoplast, cytosol and chloroplasts of intact leaves was studied by means of fluorescent pH indicators and as a response of photosynthesis to acid stress. The apoplastic pH increased under anaerobiosis. Aeration reversed this effect. Apoplastic responses to CO₂, HCl or NH₃ differed considerably. Whereas HCl and ammonia caused rapid acidification or alkalinization, the return to initial pH values was slow after cessation of fumigation. Addition of CO₂ either did not produce the acidification expected on the basis of known apoplastic buffering or even caused some alkalinization. Removal of CO₂ shifted the apoplastic pH into the alkaline range before the pH returned to initial steady-state levels. In the presence of vanadate, the alkaline shift was absent and the apoplastic pH returned slowly to the initial level when CO₂ was removed from the atmosphere. In contrast to the response of the apoplast, anaerobiosis acidified the cytosol or, in some species, had little effect on its pH. Acidification was rapidly reversed upon re-admission of oxygen. The CO₂-dependent pH changes were very fast in the cytosol. Considerable alkalinization was observed after removal of CO₂ under aerobic, but not under anaerobic conditions. Rates of the re-entry of protons into the cytosol during recovery from CO₂ stress increased in the presence of oxygen with the length of previous exposure to high CO₂. Effective pH regulation in the chloroplasts was indicated by the recovery of photosynthesis after the transient inhibition of photosynthetic electron flow when CO₂ was increased from 0.038% to 16% in air. As photosynthesis became inhibited under high CO₂, reduction of the electron transport chain increased transiently. The time required for recovery of photosynthesis from inhibition during persistent CO₂ stress was similar to the time required for establishing steady-state pH values in the cytosol under acid stress. The high capacity of leaf cells for the rapid re-attainment of pH homeostasis in the apoplast and the cytoplasm under acid or alkaline stress suggested the rapid activation or deactivation of membrane-localised proton-transporting enzymes and corresponding ion channel regulation for co-transport of anions or counter-transport of cations together with proton fluxes. Acidification of the cytoplasm appeared to activate energy-dependent proton export primarily into the vacuoles whereas apoplastic alkalinization resulted in the pumping of protons into the apoplast. Proton export rates from the cytosol into the apoplast after anaerobiosis were about 100 nmol (m² leaf area)⁻¹ s⁻¹ or less. Proton export under acid stress into the vacuole was about 1200 nmol m⁻² s⁻¹. The kinetics of pH responses to the addition or withdrawal of CO₂ indicated the presence of carbonic anhydrase in the cytosol, but not in the apoplast. Received: 19 July 1999 / Accepted: 29 December 1999     

Alterations of Red Cell Membrane Properties in Nneuroacanthocytosis

Neuroacanthocytosis (NA) refers to a group of heterogenous, rare genetic disorders, namely chorea acanthocytosis (ChAc), McLeod syndrome (MLS), Huntington’s disease-like 2 (HDL2) and pantothenate kinase associated neurodegeneration (PKAN), that mainly affect the basal ganglia and are associated with similar neurological symptoms. PKAN is also assigned to a group of rare neurodegenerative diseases, known as NBIA (neurodegeneration with brain iron accumulation), associated with iron accumulation in the basal ganglia and progressive movement disorder. Acanthocytosis, the occurrence of misshaped erythrocytes with thorny protrusions, is frequently observed in ChAc and MLS patients but less prevalent in PKAN (about 10%) and HDL2 patients. The pathological factors that lead to the formation of the acanthocytic red blood cell shape are currently unknown. The aim of this study was to determine whether NA/NBIA acanthocytes differ in their functionality from normal erythrocytes. Several flow-cytometry-based assays were applied to test the physiological responses of the plasma membrane, namely drug-induced endocytosis, phosphatidylserine exposure and calcium uptake upon treatment with lysophosphatidic acid. ChAc red cell samples clearly showed a reduced response in drug-induced endovesiculation, lysophosphatidic acid-induced phosphatidylserine exposure, and calcium uptake. Impaired responses were also observed in acanthocyte-positive NBIA (PKAN) red cells but not in patient cells without shape abnormalities. These data suggest an “acanthocytic state” of the red cell where alterations in functional and interdependent membrane properties arise together with an acanthocytic cell shape. Further elucidation of the aberrant molecular mechanisms that cause this acanthocytic state may possibly help to evaluate the pathological pathways leading to neurodegeneration.     

Population dynamics of an introduced bacterium degrading chlorinated benzenes in a soil column and in sewage sludge

The capacity of the -Proteobacterium Pseudomonas sp. strain P51, which degrades chlorinated benzenes, to metabolize 1,2,4-trichlorobenzene (TCB) under environmental conditions was tested by its release into two experimental systems. The first system consisted of laboratory scale microcosms which were operated with and without the addition of TCB and which were inoculated with sludge from a wastewater treatment plant. The second system consisted of a non sterile, water saturated soil column. We determined survival of strain P51 after its introduction and its ability to degrade TCB. The population dynamics was followed by selective plating and applying the polymerase chain reaction (PCR) to detect strain P51 and the chlorobenzene ( tcb) genes on catabolic plasmid pP51. The results showed a completely different behaviour of strain P51 in the two habitats under the applied conditions. In the soil column the P51 bacteria inoculated the entire area and their population reached 2 × 10⁶ cells/g soil. The population remained active since TCB was degraded to concentrations below the detection limit of 30 g/l. In the sludge microcosms, the number of strain P51 cells immediately decreased from 4 × 10⁷ cells/ml to 10⁵ cells/ml over a period of 2 days after inoculation, and then the strain disappeared to levels below our detection limit (10³–10⁴ cells/ml). In the reactor without TCB the population of P51 maintained a stable value of 10⁵ cells/ml during 8 days but then also decreased to levels below the detection limit. In addition, no significant TCB degradation was found in the sludge reactors. The influence of presence of TCB on maintenance of strain P51 in the two habitats is discussed. This work demonstrates the possibility to successfully apply preselected strains to degrade otherwise poorly degradable substances in complex mixed microbial communities. However, survival and activity may depend strongly on the type of system into which the strain is introduced.     

Cleavage of Zearalenone by Trichosporon mycotoxinivorans to a Novel Nonestrogenic Metabolite

Zearalenone (ZON) is a potent estrogenic mycotoxin produced by several Fusarium species most frequently on maize and therefore can be found in food and animal feed. Since animal production performance is negatively affected by the presence of ZON, its detoxification in contaminated plant material or by-products of bioethanol production would be advantageous. Microbial biotransformation into nontoxic metabolites is one promising approach. In this study the main transformation product of ZON formed by the yeast Trichosporon mycotoxinivorans was identified and characterized by liquid chromatography-tandem mass spectrometry (LC-MS/MS) and LC-diode array detector (DAD) analysis. The metabolite, named ZOM-1, was purified, and its molecular formula, C₁₈H₂₄O₇, was established by time of flight MS (TOF MS) from the ions observed at m/z 351.1445 [M-H]⁻ and at m/z 375.1416 [M+Na]⁺. Employing nuclear magnetic resonance (NMR) spectroscopy, the novel ZON metabolite was finally identified as (5S)-5-({2,4-dihydroxy-6-[(1E)-5-hydroxypent-1-en-1-yl]benzoyl}oxy)hexanoic acid. The structure of ZOM-1 is characterized by an opening of the macrocyclic ring of ZON at the ketone group at C6′. ZOM-1 did not show estrogenic activity in a sensitive yeast bioassay, even at a concentration 1,000-fold higher than that of ZON and did not interact with the human estrogen receptor in an in vitro competitive binding assay.Zearalenone (ZON) is the main member of a growing family of biologically important “resorcylic acid lactones” (RALs), which have been found in nature. ZON is produced by several Fusarium species, which colonize maize, barley, oat, wheat, and sorghum and tend to develop ZON during prolonged cool, wet growing and harvest seasons (38). Maize is the most frequently contaminated crop plant, and therefore, ZON can be found frequently in animal feeding stuff. Occurrence, toxicity, and metabolism data of ZON were summarized by the European Food Safety Authority (EFSA) (5) and in recent reviews (12, 38).The potent xenohormone ZON leads to hyperestrogenism symptoms and in extreme cases to infertility problems, especially in pigs (15). Ovarian changes in pigs have been noted with toxin levels as low as of 50 μg/kg in the diet (1). Ruminants are more tolerant to ZON ingestion; however, hyperestrogenic syndrome, including restlessness, diarrhea, infertility, decreased milk yields, and abortion, have been well documented with cattle and sheep (4, 29).Because widespread ZON contamination in feed can occur in problematic years, efficient ways to detoxify are desirable. The transformation of mycotoxins to nontoxic metabolites by pure cultures of microorganisms or by cell-free enzyme preparations (3) is an attractive possibility. Microbial metabolization of ZON to alpha-ZOL and beta-ZOL cannot be regarded as detoxification, because both ZOL products are still estrogenic (14). Also, formation of ZON-glucosides and -diglucosides (8, 17) and ZON-sulfate (7) cannot be considered true detoxification but rather formation of masked mycotoxins, because the conjugates may be hydrolyzed during digestion (11, 23), releasing ZON again (2).As the estrogenic activity of ZON and its derivates can be explained by its chemical structure, which resembles natural estrogens (20), it can be expected that cleavage of the lactone undecyl ring system of ZON results in permanent detoxification.El-Sharkawy and Abul-Hajj (9) were the first to report inactivation of ZON after opening of the lactone ring by Gliocladium roseum. This filamentous fungus was capable of metabolizing ZON in yields of 80 to 90%. Also Takahashi-Ando et al. (31) described the degradation reaction of ZON with Clonostachys rosea (synonym of G. roseum). A hydrolase (encoded by a gene designated ZHD101) cleaves the lactone ring, and as recently proved (37; unpublished data) by subsequent decarboxylation of the intermediate acid, the compound 1-(3,5-dihydroxyphenyl)-10′-hydroxy-1′E-undecene-6′-one is formed. In contrast to ZON and 17β-estradiol, which showed potent estrogenic activity, this cleavage product did not show any estrogenic activity in the human breast cancer MCF-7 cell proliferation assay (16). Further details, e.g., on the conditions of the maximum activity of ZHD101 and its exploitation in genetically modified grains, can be found in later published work of this research group (32, 33).Only a few authors reported the loss of estrogenicity in microbial metabolites of ZON, which are based on reactions other than cleavage of the lactone undecyl ring system. El-Sharkawy and Abul-Hajj demonstrated (10) that binding to rat uterine estrogen receptors requires a free 4-OH phenolic group (devoid of methylation or glycosylation). Loss of estrogenicity was, for instance, observed with 2,4-dimethoxy-ZON, one of the metabolites produced by Cunninghamella bainieri ATCC 9244B. Nevertheless, this rule cannot be generalized, as 8′-hydroxyzearalenone formed by Streptomyces rimosus NRRL 2234, despite having a free 4-phenolic hydroxyl group, did not bind to the estrogen receptor. Also, other authors reported that 8′-hydroxyzearalenone and 8′-epi-hydroxyzearalenone are nonestrogenic (13). However, so far, no practical application in feed or food detoxification has been found for the microorganisms producing these compounds.It has been shown previously that the yeast Trichosporon mycotoxinivorans has a very high capability to degrade both ochratoxin A (OTA) and ZON (22, 26, 27). When T. mycotoxinivorans is used as a feed additive preparation, microbial degradation of the mycotoxins is assumed to take place in the gastrointestinal tract of the animal after consumption of contaminated feed. The protective effect of T. mycotoxinivorans against OTA toxicity has already been shown with broiler chicken (24).In the present study we report the isolation, analytical characterization, and structure elucidation, as well as the evaluation, of the estrogenic activity of the main degradation product of ZON produced by T. mycotoxinivorans.     

Nanosized Iron Oxide Colloids Strongly Enhance Microbial Iron Reduction

Microbial iron reduction is considered to be a significant subsurface process. The rate-limiting bioavailability of the insoluble iron oxyhydroxides, however, is a topic for debate. Surface area and mineral structure are recognized as crucial parameters for microbial reduction rates of bulk, macroaggregate iron minerals. However, a significant fraction of iron oxide minerals in the subsurface is supposed to be present as nanosized colloids. We therefore studied the role of colloidal iron oxides in microbial iron reduction. In batch growth experiments with Geobacter sulfurreducens, colloids of ferrihydrite (hydrodynamic diameter, 336 nm), hematite (123 nm), goethite (157 nm), and akaganeite (64 nm) were added as electron acceptors. The colloidal iron oxides were reduced up to 2 orders of magnitude more rapidly (up to 1,255 pmol h⁻¹ cell⁻¹) than bulk macroaggregates of the same iron phases (6 to 70 pmol h⁻¹ cell⁻¹). The increased reactivity was not only due to the large surface areas of the colloidal aggregates but also was due to a higher reactivity per unit surface. We hypothesize that this can be attributed to the high bioavailability of the nanosized aggregates and their colloidal suspension. Furthermore, a strong enhancement of reduction rates of bulk ferrihydrite was observed when nanosized ferrihydrite aggregates were added.Dissimilatory iron reduction is an important anaerobic respiration process in anoxic subsurface environments. However, the reactivity of ferric iron is mostly limited by the reduction kinetics of the poorly soluble, extracellular iron minerals. Electron transfer from microorganisms to iron oxides can occur via direct contact or by electron shuttling compounds (46). Transport of the electron shuttle between the redox partners is then assumed to occur via diffusion. For example, humic substances can serve as natural electron shuttles that can be reduced by microorganisms and subsequently chemically oxidized by the ferric oxide (18). Shewanella oneidensis excretes a flavin to stimulate hematite reduction, functioning in a similar manner (27). As another option, formation of conductive pili serving as nanowires was described as a possible way of transferring electrons to the oxide surface (15, 34). Nevertheless, direct attachment has been recognized as a major mode of accessing iron oxides as electron acceptors (12). Direct transfer between microbial outer membrane reductases and the ferric minerals, however, requires close contact of less than 14 Å between the terminal iron reductase on the cell surface and the iron oxide molecule at the mineral surface (19, 25), limiting the rates of electron transfer between cell and mineral.Several parameters have been discussed in this context as being decisive for the bioavailability and reactivity of iron oxides, such as, e.g., the mineral surface area (8, 41). Larger surface areas have been shown to be accompanied by higher initial reduction rates. Another parameter that might determine reactivity is the low solubility of ferric iron in water at neutral pH (20). Low solubility entails high crystallinity, which reduces reaction rates (4). Therefore, crystalline bulk iron phases such as goethite or hematite (9) are poorly reducible by microorganisms, in contrast to amorphous ferrihydrite (41). Naturally, well crystalline minerals have lower surface areas, and the effects of surface area and solubility cannot be distinguished sharply. Cell density, initial oxide and substrate concentrations, and ferrous iron adsorbed to the bulk mineral surface were also reported to control microbial reduction rates by exhibiting mutual saturation behavior in Michaelis-Menten-type kinetics (3, 22, 40).The latter studies also considered particle sizes, a parameter that has often been overlooked so far. All concepts mentioned above generally assumed a bulk state of the electron-accepting iron oxide. Indeed, iron oxides used in microbiological experiments appear mainly as coarse, flocculating macroaggregates, visible to the naked eye as sludge-like precipitates. In nature, however, nanosized iron oxides are abundant (32, 45) and play a vital role in many biogeochemical processes (2, 16, 28). Such nanoparticles may appear in stable colloidal suspension, even if aggregated as a stable cluster of multiple particles (13). Ferric oxide particles can appear in colloidal suspensions of different aggregate sizes and densities.Different particle aggregate sizes might influence the bioavailability of iron oxides in microbial reduction. Nanosized aggregates appearing in colloidal suspensions might be spatially more accessible for microorganisms than large aggregates flocculating as bulk phases. Therefore, the present study aims at assessing the reactivity and putative role of aggregate sizes of iron oxides in dissimilatory iron reduction. A set of ferrihydrite, hematite, goethite, and akaganeite colloids was compared to their respective noncolloidal bulk phases to evaluate this effect.