Dynamics of glutathione-S-transferases in Mytilus galloprovincialis exposed to toxic Microcystis aeruginosa cells, extracts and pure toxins

Molluscs and especially bivalves are able to accumulate dinoflagelates, diatoms and cyanobacteria toxins, and, being vectors for these toxins, transfer them along food chains. The data obtained from laboratory experiments showed that bivalve molluscs are resistant to cyanobacteria toxins. In this work, we wanted to test if Mytilus galloprovincialis organs react to microcystins and other cyanobacteria compounds by inducing or decreasing its GST activity. Acclimated mussels M. galloprovincialis were exposed to the toxic Microcystis aeruginosa M13 strain. Exposure of mussels to toxins was done in three ways: living Microcystis cells, crude Microcystis extracts and pure toxins. The measurement of soluble and microsomal GST activity in the different mussel organs was done by using the substrates 1-chloro-2,4-dinitrobenzene (CDNB) and 2,4-dichloro-1-nitrobenzene (DCNB). Analysis of the GST activity of the control mussels using CDNB as a substrate showed that cytosolic activity is much more significant than microsomal. Intact M. aeruginosa cells did not induce any significant response from the mussels, showing that these animals are quite resistant to the cyanobacteria if they are intact. On the other hand, cell extracts caused an important effect in the gut, in the gills and in the labial palps, although in different ways. There was an increase in GST activity in the gut and gills of mussels exposed to Microcystis extracts, showing a response of this detoxication pathway, but in the labial palps a severe reduction in GST activity occurred. Pure MC LR+YR induced an increase in GST activity in all organs but the labial palps. The results showed that other substances apart from microcystins may cause stress to mussels and affect detoxication enzymes such as GST.

Ecotoxicological effects of selected cyanobacterial secondary metabolites: a short review

Cyanobacteria are one of the most diverse groups of gram-negative photosynthetic prokaryotes. Many of them are able to produce a wide range of toxic secondary metabolites. These cyanobacterial toxins can be classified in five different groups: hepatotoxins, neurotoxins, cytotoxins, dermatotoxins, and irritant toxins (lipopolysaccharides). Cyanobacterial blooms are hazardous due to this production of secondary metabolites and endotoxins, which could be toxic to animals and plants. Many of the freshwater cyanobacterial blooms include species of the toxigenic genera Microcystis, Anabaena, or Plankthotrix. These compounds differ in mechanisms of uptake, affected organs, and molecular mode of action. In this review, the main focus is the aquatic environment and the effects of these toxins to the organisms living there. Some basic toxic mechanisms will be discussed in comparison to the mammalian system.

Direct and interacting toxicological effects on the waterflea (Daphnia magna) by natural organic matter, synthetic humic substances and cypermethrin

Humic substances are the main component of dissolved organic matter in all aquatic ecosystems, comprising a variety of molecular structures and functional groups. They bind organic pollutants and metals, thereby decreasing the bioavailability and consequently the toxicity of these substances in most instances. Recent studies also describe direct interactions and effects on organisms. Current studies also show that in some cases mitigation effects are stronger at lower concentrations of natural organic matter (NOM) and that toxicity increases with increased NOM concentrations. We hypothetise that at higher concentrations the mitigating effects are overlayed by direct effects of NOM themselves, thus these aspects were investigated in combination. So, on the one hand, this study demonstrates direct effects on toxicological parameters and activities of transformation enzyme systems of Daphnia magna, provoked by two NOM and one synthetic humic-like substance, HS1500. On the other hand, capacities of NOM and synthetic HS1500 to mitigate effects of the insecticide cypermethrin were investigated. Taken together, mitigation effects were overlayed by direct own effects of the NOM and HS1500. The NOM used were isolates from Suwannee River (XAD, Spring 2000) and from streams of the Svartberget forest (reverse osmosis, Spring 2000). The HS1500 was synthetically produced by radicalic autoxidation of hydroquinones. Suwannee River NOM at concentrations between 50 and 100 mg/l, and HS1500 (10-50 mg/l), but not Svartberget NOM increased immobility and lethality of the daphnids. All elevated the activity of the soluble glutathione S-transferase from 0.5 mg/l (HS1500), 1.0 mg/l (Suwannee River NOM) and 10 mg/l (Svartberget NOM) onwards, the microsomal glutathione S-transferase did not react. The glutathione peroxidase tended to increase. In the single exposure, the insecticide cypermethrin increased all toxicological parameters, elevated soluble and tendentially microsomal glutathione S-transferase activity between 0.001 and 1.0 microg/l and tendentially increased glutathione peroxidase. In contrast to that, 50 mg/l of the NOM and HS1500 did not mitigate toxicological effects. HS1500 in combination with cypermethrin even increased immobility, compared to cypermethrin alone. Increase of the NOM or HS1500 concentrations in combination with cypermethrin did not increase mitigation as seen in the activity of soluble glutathione S-transferases, activities of microsomal glutathione S-transferase and glutathione peroxidase even decreased, relative to control, which can be a hint of enzyme disfunction or further damages in the cell. An increase of concentration did not increase mitigation. Mitigation was higher at lower NOM or HS1500 concentration, probably as a consequence of the direct effects caused by themselves. Consequently, direct effects are relevant for analysing the mitigation qualities.

Measurement of glomerular filtration rate by low-dose iopromide plasma clearance

PURPOSE

Glomerular filtration rate (GFR) can be measured by iopromide plasma clearance. As an injection of 120 ml nonionic contrast medium is expensive and especially in patients with nephropathy potentially nephrotoxic, we investigated whether iopromide plasma clearance could be measured using a tenth of that dose as 'low-dose' clearance.

MATERIAL AND METHODS

Fifty adult patients scheduled for CT were recruited. Iopromide 300 mg I/ml was used for GFR measurement. Prior to CT, low-dose clearance was measured by injecting 12 ml iopromide per 75 kg b.w. At 3, 4 and 5 h after injection, plasma samples were obtained and the iodine concentration was measured by X-ray fluorescence analysis. Immediately after the last blood sample, CT was again performed following injection of 120 ml iopromide per 75 kg b.w. A further 3 plasma samples were then obtained 3, 4, and 5 h after CT and used for the determination of high-dose clearance.

RESULTS

Low-dose clearance ranged from 20 ml/min to 141 ml/min (mean 78.3 ml/min). High-dose and low-dose clearance correlated excellently, with clearance (high-dose) = 1.4 + 0.994 clearance (low-dose); the correlation coefficient was r = 0.944, the standard deviation SDxy= 9.3 ml/min.

CONCLUSION

Plasma clearance of iopromide is dose-independent on use of iodine amounts of 3.6 g and 36 g I/75 kg b.w. The GFR can be determined by high-dose and low-dose iopromide plasma clearance with identical accuracy.

Measurement of glomerular filtration rate by low-dose iopromide plasma clearance

PURPOSE

Glomerular filtration rate (GFR) can be measured by iopromide plasma clearance. As an injection of 120 ml nonionic contrast medium is expensive and especially in patients with nephropathy potentially nephrotoxic, we investigated whether iopromide plasma clearance could be measured using a tenth of that dose as 'low-dose' clearance.

MATERIAL AND METHODS

Fifty adult patients scheduled for CT were recruited. Iopromide 300 mg I/ml was used for GFR measurement. Prior to CT, low-dose clearance was measured by injecting 12 ml iopromide per 75 kg b.w. At 3, 4 and 5 h after injection, plasma samples were obtained and the iodine concentration was measured by X-ray fluorescence analysis. Immediately after the last blood sample, CT was again performed following injection of 120 ml iopromide per 75 kg b.w. A further 3 plasma samples were then obtained 3, 4, and 5 h after CT and used for the determination of high-dose clearance.

RESULTS

Low-dose clearance ranged from 20 ml/min to 141 ml/min (mean 78.3 ml/min). High-dose and low-dose clearance correlated excellently, with clearance (high-dose) = 1.4 + 0.994 clearance (low-dose); the correlation coefficient was r = 0.944, the standard deviation SDxy= 9.3 ml/min.

CONCLUSION

Plasma clearance of iopromide is dose-independent on use of iodine amounts of 3.6 g and 36 g I/75 kg b.w. The GFR can be determined by high-dose and low-dose iopromide plasma clearance with identical accuracy.

Effects of enteric bacterial and cyanobacterial lipopolysaccharides, and of microcystin-LR, on glutathione S-transferase activities in zebra fish (Danio rerio)

Cyanobacteria (blue-green algae) can produce a variety of toxins including hepatotoxins e.g. microcystins, and endotoxins such as lipopolysaccharides (LPS). The combined effects of such toxins on fish are little known. This study examines the activities of microsomal (m) and soluble (s) glutathione S-transferases (GST) from embryos of the zebra fish, Danio rerio at the prim six embryo stage, which had been exposed since fertilisation to LPS from different sources. A further aim was to see how activity was affected by co-exposure to LPS and microcystin-LR (MC-LR). LPS were obtained from Salmonella typhimurium, Escherichia coli, a laboratory culture of Microcystis CYA 43 and natural cyanobacterial blooms of Microcystis and Gloeotrichia. Following in vivo exposure of embryos to each of the LPS preparations, mGST activity was significantly reduced (from 0.50 to between 0.06 and 0.32 nanokatals per milligram (nkat mg(-1)) protein). sGST activity in vivo was significantly reduced (from 1.05 to between 0.19 and 0.22 nkat mg(-1) protein) after exposure of embryos to each of the cyanobacterial LPS preparations, but not in response to S. typhimurium or E. coli LPS. Activities of both m- and sGSTs were reduced after co-exposure to MC-LR and cyanobacterial LPS, but only mGST activity was reduced in the S. typhimurium and E. coli LPS-treated embryos. In vitro preparations of GST from adult and prim six embryo D. rerio showed no significant changes in enzyme activity in response to the LPS preparations with the exception of Gloeotrichia bloom LPS, where mGST was reduced in adult and embryo preparations. The present study represents the first investigations into the effects of cyanobacterial LPS on the phase-II microcystin detoxication mechanism. LPS preparations, whether from axenic cyanobacteria or cyanobacterial blooms, are potentially capable of significantly reducing activity of both the s- and mGSTs, so reducing the capacity of D. rerio to detoxicate microcystins. The results presented here have wide ranging implications for both animal and human health.

Toxicokinetics of atrazine in embryos of the zebrafish (Danio rerio)

Atrazine (2-chloro-4-ethylamino-6-isopropylamine-s-triazine) is a widely used selective herbicide. Due to its persistence, it is present in many surface waters, contaminating nontarget organisms such as fish. Teratogeny of atrazine was examined during the first 48 h of zebrafish development (embryo test) and correlated to effects on the microsomal and soluble glutathione S-transferases (m-/sGST; EC 2.5.1.18). Atrazine at 4 mg/L disturbed the normal development to long pec stage, at concentrations between 10 and 20 mg/L it caused retardations in organogenesis, a slowdown of movements, and functional disturbances of heart and circulatory system. m- and sGST activities were affected by atrazine in all investigated developmental stages. Atrazine elevated the mGST activity dose dependently up to a concentration of 5 mg/L, and the sGST up to 1 mg/L. Higher atrazine concentrations caused a decrease of GST activity, especially of the sGST of the younger stages, 32 cells and 75% epiboly. This might indicate that the detoxication system itself is affected, which then gives rise to morphological abnormalities during fish development. In vitro tests were performed to purify and characterize GST-formed atrazine metabolites by the use of ESI--HPLC--MS. mGST showed higher conversion rates compared to sGST.

Mutants of tobacco mosaic virus with temperature-sensitive coat proteins induce heat shock response in tobacco leaves

We analyzed, with respect to heat shock proteins (HSPs), systemically reacting tobacco leaves inoculated with Tobacco mosaic virus (TMV), wild-type vulgare, and temperature-sensitive coat protein (CP) mutants Ni 118 (P20L) and flavum (D19A), kept at 23 or 30 degrees C. HSP18 and HSP70 mRNAs and proteins were induced with temperature-sensitive CP mutants after 1 to 2 days at 30 degrees C. After 4 to 6 days, HSP70 was also induced at 23 degrees C. The induction of HSPs paralleled the amount of insoluble TMV CP in leaf extracts, indicating that denatured TMV CP by itself induces a heat-shock response.

Uptake, effects, and metabolism of cyanobacterial toxins in the emergent reed plant Phragmites australis (cav.) trin. ex steud

The commonly occurring cyanobacterial toxin microcystin-LR (MC-LR) was rapidly taken up by the emergent reed plant Phragmites australis with clear distribution in the different cormus parts of the plant. Highest uptake was detected in the stem, followed by the rhizome. Enzyme extracts of the rhizome system, the stem, and the leaf revealed the presence of soluble glutathione S-transferases (sGST) measured with the model substrate 1-chloro-2,4-dinitrobenzene. A significant elevation of sGST activity in the rhizome and stem parts of P. australis was detected after a 24-h exposure to 0.5 microg/L MC-LR. Rhizome, stem, and leaf tissues were also able to conjugate several microcystin toxins. However, no conjugation, either chemical nor enzymatic, was detected using the related cyanobacterial toxin nodularin as substrate. Highest glutathione S-transferase activity for the toxin substrates was detected in the pkat/mg range in the stem of P. australis. For MC-LR, a complete metabolism from the formation of a glutathione conjugate to the degradation of a cysteine conjugate in all cormus parts of the plant is reported. The stepwise degradation of the MC-LR-glutathione conjugate to a gamma-glutamylcysteine and a cysteine conjugate was demonstrated by comparison with chemically formed reference compounds and by matrix-assisted laser desorption/ionization time-of-flight mass spectrometry. This is the first evidence for the uptake and metabolism of cyanobacterial toxins by an emergent aquatic macrophyte.

The human dopamine transporter gene: the 5'-flanking region reveals five diallelic polymorphic sites in a Caucasian population sample

The 5'-flanking region of the human dopamine transporter (hDAT) was systematically screened for variants by single strand conformation analysis (SSCA) between -1586 and +97 basepair (bp) relative to the transcription start site. Five diallelic polymorphisms were found, which were shown to be due to single base substitutions: T-67A, G-660C, C-839T, C-1169G, T-1476G. In a population sample of 119 unrelated Caucasians, allele frequencies of the rarer allele were 47% for -67T, 3% for -660C, 45% for -839T, 50% for -1169G, and 8% for -1476G, respectively. Among 15 observed haplotypes, seven haplotypes collected a frequency of about 96% in our sample. T-67A, C-839T, C-1169G, T-1476G were related to potential transcriptional recognition sites. These findings and the occurrence of distinct haplotypes at the hDAT promoter locus in a Caucasian population sample make this region a promising target in the context of linkage and association studies in certain diseases.

The effects of a cyanobacterial crude extract on different aquatic organisms: evidence for cyanobacterial toxin modulating factors

In an aquatic ecosystem, during cyanobacterial bloom lysis, a mixture of toxins and other cyanobacterial and bacterial components will be present in the water, acting on aquatic organisms. Most of the research into toxic effects of cyanobacteria has involved the use of purified toxins. In this study, the "real-life" situation of a cyanobacterial lysis event was investigated. For this purpose, intact cells from a natural cyanobacterial bloom from Lake Müggelsee, Berlin, were taken and the cells were broken by repeated freeze/thaw cycles. This crude extract was used to expose several aquatic organisms ranging from microalgae (Scenedesmus armatus), macrophyte (Ceratophyllum demersum), invertebrate (Chaoborus crystallinus) up to fish eggs (Danio rerio) to look at several physiological parameters such as detoxication enzyme activity and, in the case of the microalgae and the macrophyte, also the effect on activity of photosynthesis. In all the tests, the cyanobacterial crude extract caused stronger effects than the pure cyanobacterial toxins used in equivalent concentrations.

Monoclonal antibody MS13 identifies a plasmatocyte membrane protein and inhibits encapsulation and spreading reactions of Manduca sexta hemocytes

Lepidopterans generally can successfully defend themselves against a variety of parasites or parasitoids. One mechanism they use is to encapsulate the invader in many layers of hemocytes. For encapsulation to occur, the hemocytes must attach to the foreign material, spread, and adhere to each other. The molecules that mediate these processes are not known. One method to identify proteins potentially necessary for adhesion, spreading, and, thus, encapsulation is to use monoclonal antibodies that interfere with these functions. In this paper, we report that a monoclonal antibody against Manduca sexta plasmatocytes effectively inhibited encapsulation of synthetic beads in vitro and in vivo. Furthermore, it inhibited plasmatocyte spreading in vitro. Other anti-hemocyte antibodies did not have these effects. The plasmatocyte-specific monoclonal antibody, mAb MS13, recognized a protein of approximately 90,000 daltons as indicated by Western blot analysis of hemocyte lysate proteins. The epitope recognized by mAb MS13 was present on the exterior surface of plasmatocytes. Using indirect immunohistochemistry with hemocyte-specific antibodies, we also determined that during encapsulation plasmatocytes were the first cells bound to latex beads and later layers consisted of both plasmatocytes and granular cells. Arch.

Uptake, toxicity, and effects on detoxication enzymes of atrazine and trifluoroacetate in embryos of zebrafish

The uptake, toxicity, and elimination of atrazine and trifluoroacetate (TFA) were studied in early life stages of the zebrafish (Danio rerio). Furthermore, the effects of these xenobiotics on soluble (s) and microsomal (m) glutathione S-transferases (GST) of zebrafish embryos were investigated using 1-chloro-2,4-dinitrobenzene (CDNB), 1,2-dichloro-4-nitrobenzene (DCNB), and [(14)C]atrazine. [(14)C]Atrazine was taken up by the embryos within seconds, unhindered by the chorions. It accumulated in the embryos by a factor of 19 after 24 h of exposure time. LC(50) (48 h) was determined at 36.8 mg/L. At a level of 5 mg/L atrazine, activities of s and m GSTs were elevated in most stages, especially in prim 6 and long pec stage (24, 48 h after fertilization, respectively). GST activity toward atrazine was detectable only in untreated D. rerio eggs, increasing with developmental time. [(14)C]Atrazine was eliminated from the embryos between 24 and 48 h, indicating a possible metabolism to a more hydrophilic GSH conjugate. [(14)C]TFA was taken up by embryos, reaching at maximum fivefold the concentration of the incubation medium after 10 h. The chorions served no physiological protection. TFA (1 g/L) caused low elevation of the GST activity. No acute toxic effects (48 h) were observed up to 4 g/L TFA.

Identification of an enzymatically formed glutathione conjugate of the cyanobacterial hepatotoxin microcystin-LR: the first step of detoxication

Cyanobacterial toxins have adverse effects on mammals, birds and fish and are being increasingly recognised as a potent stress factor and health hazard factor in aquatic ecosystems. Microcystins, cyclic heptapeptides and a main group of the cyanotoxins are mainly retained within the producer cells during cyanobacterial bloom development. However, these toxins are released into the surrounding medium by senescence and lysis of the blooms. Any toxin present could then come into contact with a wide range of aquatic organisms including phytoplankton grazers, invertebrates, fish and aquatic plants. Recent studies showed the conversion of microcystin in animal liver to a more polar compound in correlation with a depletion of the glutathione pool of the cell. The present study shows the existence of a microcystin-LR glutathione conjugate formed enzymatically via soluble glutathione S-transferase in various aquatic organisms ranging from plants (Ceratophyllum demersum), invertebrates (Dreissena polymorpha, Daphnia magna) up to fish eggs and fish (Danio rerio). The main derived conjugate was characterized by matrix-assisted laser desorption/ionization time-of-flight mass spectrometry yielding a mass of m/z 1302, which is equivalent to the mass assumed for a glutathione microcystin-LR conjugate. This conjugate appears to be the first step in the detoxication of a cyanobacterial toxin in aquatic organisms.

The 46/50 kDa phosphoprotein VASP purified from human platelets is a novel protein associated with actin filaments and focal contacts

Vasoactive agents which elevate either cGMP or cAMP inhibit platelet activation by pathways sharing at least one component, the 46/50 kDa vasodilator-stimulated phosphoprotein (VASP). VASP is stoichiometrically phosphorylated by both cGMP-dependent and cAMP-dependent protein kinases in intact human platelets, and its phosphorylation correlates very well with platelet inhibition caused by cGMP- and cAMP-elevating agents. Here we report that in human platelets spread on glass, VASP is associated predominantly with the distal parts of radial microfilament bundles and with microfilaments outlining the periphery, whereas less VASP is associated with a central microfilamentous ring. VASP is also detectable in a variety of different cell types including fibroblasts and epithelial cells. In fibroblasts, VASP is concentrated at focal contact areas, along microfilament bundles (stress fibres) in a punctate pattern, in the periphery of protruding lamellae, and is phosphorylated by cGMP- and cAMP-dependent protein kinases in response to appropriate stimuli. Evidence for the direct binding of VASP to F-actin is also presented. The data demonstrate that VASP is a novel phosphoprotein associated with actin filaments and focal contact areas, i.e. transmembrane junctions between microfilaments and the extracellular matrix.

The upright position of brush border-type microvilli depends on myosin filaments

We have studied the correlation between the actomyosin organization and microvillar position in an epithelial cell line derived from the proximal pig kidney tubule (LLC-PK1). When grown on glass, these cells are approximately 5–6 microns in height and develop numerous microvilli that project from the dorsal membrane. A fairly homogeneous distribution of microvilli was achieved by synchronization of the cell cycle. These microvilli are of the brush border type, as defined by their content of villin and their anchorage in a myosin-rich terminal web-like structure. When LLC-PK1 cells were injected with two monoclonal antibodies against pig brain nonmuscle myosin, in concentrations yielding a 1:1 ratio of antibody to myosin, neither microvillar number nor length was affected. However, when we examined the cells by scanning electron microscopy 1–3 h after microinjection, we found that one of the antibodies (a-PBM 4) had a profound effect on microvillar position: more than 50% were seen tilted or lying prone on the plasma membrane. The microvilli of cells injected with the other antibody (a-PBM 9) were not significantly different from those of cells injected with control antibodies. This difference correlates with in vitro properties of the antibodies: a-PBM 4 decreases the actin-activated Mg(2+)-ATPase of pig brain nonmuscle myosin quite substantially, while a-PBM 9 affects it only moderately. These differential effects are probably a consequence of the different epitope location as determined for both antibodies, not of differences in antibody affinity. Our data are compatible with the hypothesis that a-PBM 4 also interferes with the actomyosin interaction in situ, thus decreasing the effective cross-linking of microvillar rootlets by myosin filaments in the terminal web. On the basis of this model, we suggest that myosin filaments are essential for the upright position of brush-border type microvilli.

[Fulminant malignant hyperthermia during the 6th general anesthesia using volatile anesthetics]

We report on the fulminant crisis of malignant hyperthermia occurring in a 30-year-old female during kidney transplantation. In the past, she had been anaesthetised repeatedly without complications. Anaesthesia was induced with thiopental and vecuronium and continued with isoflurane/N2O/O2. After an initially normal course of anaesthesia, the patient developed symptoms of a fulminant malignant hyperthermia (MH) including excessive increase in end expiratory CO2, hyperkalaemia, tachycardia and hyperpyrexia. The patient was saved by the timely administration of dantrolene. A surgical revision required the next day because of bleeding was done under dantrolene cover and took an uncomplicated course. The patient was extubated 7.5 hours after the second intervention and transferred to a normal ward after 4 days. A subsequently performed in vitro contracture test clearly revealed susceptibility to malignant hyperthermia.

Characterization of the coated vesicle uncoating ATPase: tissue distribution, association with and activity on intact coated vesicles

We have analyzed the uncoating process of clathrin-coated vesicles (CV) performed by an ATPase (UA; apparent molecular mass 70 kDa) prepared from various mammalian tissues. Our data show that this enzyme removes the clathrin coat from isolated, intact coated vesicles, as seen by sedimentation analysis on gels and also by electron microscopy. The isolated UA does not discriminate between CV from homologous or heterologous tissues. This finding implies that the brain-specific insertion in clathrin light chains cannot be essential for the binding of brain UA to target vesicles. Polyclonal antibodies were raised against UA and were found to inhibit UA activity. Immunoblotting of purified CV and immunoblotting of CV in situ indicate that a subpopulation of CV contains bound UA. However, most of the uncoating enzyme is not associated with coated structures in mammalian tissue culture cells. Our data support the hypothesis that the 70 kDa uncoating ATPase is responsible for the in vivo uncoating of coated vesicles.