Epon-Embedded Tissue Stained with Aldehyde-Fuchsin for Radioautography

Four-week-old Holtzman rats were injected intraperitoneally with 20 μCi ¹²⁵I. Six or eight weeks later, they were killed by intracardiac perfusion with glutaraldehyde; thyroid and adrenal glands were excised, postfixed in osmic acid, and embedded in Epon. Steps in the staining procedure of 0.5-1 μm thick sections are: oxidation in 0.3% potassium permanganate in 0.625% sulfuric acid, 2-5 min at 70 C; brief rinse; bleaching with 2.5% NaHSO₃, 4-5 min; brief r-utse; let dry completely; aldehydefuchsm, 15-20 min at 50 C; 95% alcohol; rinse in absolute alcohol; let dry completely. seaions were coated with Kodak NTB2 emulsion and exposed for 3 to 8 weeks. Results indicate that (1) tissues are well stained even after an 8-week exposure, (2) aldehyde-fuchsin pduces no chemographic effect, and (3) structures underneath the emulsion are easily identified.     

Detection of Plutonium Contamination in Humans by the Autoradiographic Method

The autoradiographic technique, using 5 μ paraffin sections in contact with 5 μ NTA emulsion for 10 hr. and similar sections of sputum for 3 days, was found to be more sensitive for detecting contamination with Pu²³⁹ than tests with a scintillation counter. Both human and pig skin were tested. The autoradiograms showed characteristic alpha tracks in the emulsion at sites of Pu deposition following its uptake either in solution or in particulate form. Autoradiography is recommended as a routine method to supplement information gained from chemical analyses and counting procedures.     

Combination of u.v.-B. and ozone reduces pollen tube growth more than either stress alone

The rate of in vitro Nicotiana tabacum L. “Bel-W3” pollen tube growth was reduced 62 and 44%, respectively, when pollen tubes were exposed to 120 ppb ozone (O₃) for 3 hr or 300 μW/cm² ultraviolet-B (u.v.-B) radiation for 30 min. Petunia hybrida Vilm. “White Cascade” pollen tube growth was reduced 34 and 59%, respectively, upon exposure to O₃ or u.v.-B at the above doses. The combination of u.v.-B at 300 μW/cm² for 30 min, followed by O₃ at 120 ppb for 3 hr, reduced pollen tube growth by 79% for “Bel-W3” and 75% for “White Cascade”. The effect appeared to be additive, implying that different target areas may be affected by the two stressors. In the Northeast, plants are exposed to both u.v.-B and O₃ during the normal growing season. This may result in an unexpectedly higher stress on the reproductive system than had been previously suspected based on these two stressors acting individually.     

The response of intact Strongyloides ratti infective (L3) larvae to substrates and inhibitors of respiratory electron transport.

Live, intact third-stage larvae (L3s) of Strongyloides ratti in the absence of exogenous substrates consumed oxygen at a rate (E-QO₂) of 181.8 ± 12.4 ng atoms min⁻¹ mg dry weight⁻¹ at 35°C. Respiratory electron transport (RET) Complex I inhibitor rotenone (2 μ ) produced 33 ± 6.5% inhibition of the E-QO₂. Unusually the rotenone-induced inhibition was not relieved by 5 μ -succinate. The E-QO₂ of intact L3s was refractory to RET Complex III inhibitor antimycin A at 2 μ ; 4 μ -antimycin inhibited ≤ 10% of the E-QO₂. The electron donor couple ascorbate/TMPD augmented the E-QO₂ in the presence of rotenone (2 μ ) and antimycin A (4 μ ) by 110%. Azide (1 m ) stimulated the antimycin A refractory QO₂ by 36.6 ± 7.2% which was only partially inhibited by 1.0 m -KCN ( ). The data suggest the presence of classical (CPW) and alternate (APW) electron transport pathways in S. ratti L3s.     

Actual and potential dark respiration rates and different electron transport pathways in freshwater aquatic plants

The rates of respiratory O₂ uptake have been studied in leaves, stems and whole shoots of several freshwater plants: 6 angiosperms, 2 bryophytes and one alga. For angiosperm leaves, rates varied widely with species (30–142 μmol O₂ (gDW)⁻¹ h⁻¹), were correlated with chlorophyll content and were higher than those of the stems (13–71 μmol O₂ (gDQ)⁻¹ h⁻¹). The rates for the shoots of bryophytes (53–66 μmol O₂ (gDW)⁻¹ h⁻¹) and for the alga Cladophora glomerata (L.) Kütz. (96 μmol O₂ (gDW)⁻¹ h⁻¹) were slightly higher than those of most angiosperm stems, but lower than those for most leaves.

These plants had a significant cyanide-resistant respiration, suggesting the existence of an alternative pathway to the “classic” cytochrome system. This pathway was found to be active in all the species studied, as judged by responses to a specific inhibitor, SHAM (salicylhydroxamic acid). Measurement of electron-transport system (ETS) activity showed that there is a large electron-transport capacity which is not normally used by respiration in vivo.     

PAH-DNA adducts in environmentally exposed population in relation to metabolic and DNA repair gene polymorphisms

Epidemiologic studies indicate that prolonged exposure to particulate air pollution may be associated with increased risk of cardiovascular diseases and cancer in general population. These effects may be attributable to polycyclic aromatic hydrocarbons (PAHs) adsorbed to respirable air particles. It is expected that metabolic and DNA repair gene polymorphisms may modulate individual susceptibility to PAH exposure. This study investigates relationships between exposure to PAHs, polymorphisms of these genes and DNA adducts in group of occupationally exposed policemen (EXP, N = 53, males, aged 22–50 years) working outdoors in the downtown area of Prague and in matched “unexposed” controls (CON, N = 52). Personal exposure to eight carcinogenic PAHs (c-PAHs) was evaluated by personal samplers during working shift prior to collection of biological samples. Bulky-aromatic DNA adducts were analyzed in lymphocytes by ³²P-postlabeling assay. Polymorphisms of metabolizing (GSTM1, GSTP1, GSTT1, EPHX1, CYP1A1-MspI) and DNA repair (XRCC1, XPD) genes were determined by PCR-based RFLP assays. As potential modifiers and/or cofounders, urinary cotinine levels were analyzed by radioimmunoassay, plasma levels of vitamins A, C, E and folates by HPLC, cholesterol and triglycerides using commercial kits. During the sampling period ambient particulate air pollution was as follows: PM10 32–55 μg/m³, PM2.5 27–38 μg/m³, c-PAHs 18–22 ng/m³; personal exposure to c-PAHs: 9.7 ng/m³ versus 5.8 ng/m³ (P < 0.01) for EXP and CON groups, respectively. The total DNA adduct levels did not significantly differ between EXP and CON groups (0.92 ± 0.28 adducts/10⁸ nucleotides versus 0.82 ± 0.23 adducts/10⁸ nucleotides, P = 0.065), whereas the level of the B[a]P-“like” adduct was significantly higher in exposed group (0.122 ± 0.036 adducts/10⁸ nucleotides versus 0.099 ± 0.035 adducts/10⁸ nucleotides, P = 0.003). A significant difference in both the total (P < 0.05) and the B[a]P-“like” DNA adducts (P < 0.01) between smokers and nonsmokers within both groups was observed. A significant positive association between DNA adduct and cotinine levels (r = 0.368, P < 0.001) and negative association between DNA adduct and vitamin C levels (r = −0.290, P = 0.004) was found. The results of multivariate regression analysis showed smoking, vitamin C, polymorphisms of XPD repair gene in exon 23 and GSTM1 gene as significant predictors for total DNA adduct levels. Exposure to ambient air pollution, smoking, and polymorphisms of XPD repair gene in exon 6 were significant predictors for B[a]P-“like” DNA adduct. To sum up, this study suggests that polymorphisms of DNA repair genes involved in nucleotide excision repair may modify aromatic DNA adduct levels and may be useful biomarkers to identify individuals susceptible to DNA damage resulting from c-PAHs exposure.     

Temporal pattern in swimming activity of two fish species (Danio rerio and Leucaspius delineatus) under chemical stress conditions

Circadian periodicity of swimming activity was investigated in two fish species, the zebrafish (Danio rerio) and the sunbleak (Leucaspius delineatus) under sublethal long-term exposure to the cyanobacteria toxin microcystin-LR (nominal concentrations of 0.5 μg l^- 1, 5 μg l^- 1, 15 μg l^- 1, 50 μg l^- 1) in 15-litre tanks. Swimming activity of fish was monitored continuously by using an automated video-monitoring and object-tracing system over a period of 17 days. Influenced by long-term exposure to microcystin-LR, Leucaspius delineatus reversed their significant diurnal swimming activity and the fish became statistically significant nocturnal. Danio rerio remained diurnal active, but a significant phase shift was registered. In both Danio rerio and Leucaspius delineatus analysis of time series by cosinor regression revealed microcystin-LR induced dose-dependent alterations of the mean of oscillation, amplitude, acrophase and period length in a different extent. For Danio rerio the periodogram analysis revealed a significant circadian component of swimming activity for control as well as exposure groups, whereby the spectral amplitude clearly decreased at microcystin-LR concentrations of 15 and 50 μg l^- 1. For Leucaspius delineatus the amplitude of circadian rhythm was decreased at all exposure concentrations of MC-LR. Furthermore the dominance of circadian rhythm was clearly reduced, whereas the rate of ultradian rhythms increased at elevated MC-LR concentrations of 5 μg l^- 1, 15 μg l^- 1 and 50 μg l^- 1. The studied temporal aspects of behaviour clearly indicated stress symptoms in both fish species, therefore it proved to be a relevant method to characterise the impact of toxic substances in the environment and for biomonitoring.     

Effect of glutamate on extracellular potassium activity in isolated retina of cyprinid fish

The effect of ( -)glutamate on extracellular K⁺ activity of the isolated retina of the cyprinid fish, roach, was investigated using double-barrelled K⁺-sensitive micro-electrodes. Application of μM-mM glutamate to the retina as a “puff” from an atomizer induced a transient rise in extracellular K⁺ activity, which was maximal 50–100 μm below the photoreceptor surface. The effect was concentration-dependent, but not related to the state of light adaptation of the retina. In the presence of dinitrophenol or ouabain, the glutamate-induced increase in extracellular K⁺ activity was maintained.

The following conclusions are made. (1) The most likely cellular origin(s) of the glutamate-induced rise in extracellular K⁺ activity are the photoreceptors and/or the Muller (glial) cells. (2) The mechanism responsible for returning the extracellular K⁺ activity to normal depends strongly on metabolic, Na⁺, K⁺ pump activity. (3) The effect parallels the action of endogenous glutamate, and may be important for modulation of neurotransmission in the intact retina.     

Quantification of some active compounds in air samples at pharmaceutical workplaces by HPLC

Workers involved in the manufacture of drug substances may be exposed to active pharmaceuticals by inhalation of drug dusts or droplets which has been considered the main exposure route. The proposed HPLC method allowed to determine sulpiryde, hydroxyurea and dyprophylline in the concentration range of 0.01–0.187 mg/m³, 0.001–0.08 mg/m³ and 0.01–0.40 mg/m³ for sulpiryde, hydroxyurea and dyprophylline, respectively, when 480 L of air sample was collected on the glass fibre filters. Sulpiryde was extracted with a solvent system consisting of acetonitrile–phosphate buffer at pH 3 (85:15, v/v), while the best efficiency of extraction for hydroxyurea and dyprophylline was achieved using water. HPLC analysis of sulpiryde with fluorescence detection was more sensitive (LOD = 3.1 μg/L) in comparison with UV detection (LOD = 84.4 μg/L).     

The response of sweet corn to HF and SO2 under field conditions

“Marcorss” sweet corn plants grown in field plots were exposed continuously in open-top chambers for 32 days to ambient air, charcoal-filtered air or charcoal-filtered air containing HF (ca. 0.5 μgF m⁻³), SO₂ (ca. 235 μg m⁻³), or the two pollutants combined. Elliptical chlorotic leasions appeared after 23 days on leaves of plants exposed to SO₂/HF, and shortly thereafter on plants exposed to all other treatments. At harvest, the number of plants with lesions was significantly greater in chambers supplied with SO₂/HF than in chambers with SO₂, HF, or filtered air.

The different treatments had no effect on fresh or dry weights of leaves, husks, or tassels, height of plants, or number of kernels per ear. Exposure to SO₂/HF reduced the fresh and dry weights of stalks. There were fewer mature ears in the SO₂/HF and unfiltered air treatments than in the others. The reduction in yield from SO₂/HF was about the same as that ascribed to ambient photochemical oxidants in the unfiltered air treatment.

HF combined with SO₂ had no effect on accumulation of S as compared with SO₂ alone, but there was a striking reduction in accumulation of foliar F in plants exposed to SO₂/HF as compared with HF alone.     

Basic Dye Counterstaining of Sections Impregnated by the Golgi-Cox Method

Celloidin blocks of Golgi-Cox impregnated material are cut at 50 μ, the sections collected in 70% alcohol, transferred to a 3:1 mixture of absolute alcohol and chloroform for 2 min, and then stored in xylene or toluene for at least 3 min, or up to 2 wk until processed further. Mounting is done on glass slides which have been coated with fresh egg albumen diluted in 0.2% ammonia water (or a 0.5% solution of dry powdered egg albumen) and then dried at 60°C overnight. For attachment to these coated slides, sections are first soaked for 2-3 min in a freshly prepared mixture of methyl benzoate, 50 ml; benzyl alcohol, 200 ml; chloroform, 150 ml; and then transferred quickly to the slides by means of a brush. After 2-3 min the chloroform evaporates and the celloidin softens. The slides are then immersed in toluene which hardens the celloidin and anchors the sections to the slides. Alcohols of descending concentrations to 40% are followed by alkalinizations, first in: absolute alcohol, 40 ml; strong ammonia water 60 ml, for 2 min, then in: absolute alcohol, 70 ml; strong ammonia water, 30 ml, for 1 hr. Excess alkali is then removed by 70% and 40% alcohol, 2 min each, and a 10 min wash in running tap water. Bleaching in 1% Na₂S₂O₃, for 10 min and washing again in tap water for 10 min completes the process preliminary to staining. The preparations are then stained for 90 min in an aqueous solution of either 0.5% cresylecht violet, neutral red, or Darrow red, buffered at pH 3.6. Dehydration and differentiation in ascending grades of alcohol, clearing with toluene or xylene, and applying a cover glass with a mounting medium having a refractive index of about 1.61 completes the process.     

Zooplankton feeding ecology: bacterivory by metazoan microzooplankton

Bacterivory by the rotifer Brachionus plicatilis Müller, nauplii and copepodites of the copepods Centropages Krøyer sp. and Acartia tonsa Dana, and the tintinnid Favella panamensis Kofoid & Campbell was examined using fluorescently labelled bacteria (FLB) and epifluorescence microscopy. FLB were < 1 μm in diameter, and were offered at environmental concentrations (1.47−9.08 × 10⁶ cells·ml⁻¹). FLB were visible within rotifers, nauplii, copepodites, and tintinnids, confirming ingestion. Rotifer clearance rates (32–418 μl·animal⁻¹·h⁻¹) exhibited no relation with FLB concentration. In some cases rates of clearance of FLB by rotifers were different with alternative phytoplankton food (Nanochloris Naumann sp.) than in replicates with FLB alone, whereas in other cases presence of alternative food exhibited no clear effects on rates of ingestion of FLB. Clearance rates for all six naupliar stages of A. tonsa nauplii (0–320 μl·animal⁻¹·h⁻¹) were stage-related, with higher rates by NIII-VI nauplii than NI-II nauplii. Nauplii had higher rates of clearance of FLB in the absence of alternative phytoplankton food (Isochrysis Parke sp.). Clearance rates of FLB by a single stage of Centropages sp. nauplii, A. tonsa CI copepodites and F. panamensis (each obtained at only a single food concentration of either 1.5 or 5.0 × 10⁶ cells·ml⁻¹) were within the range of 85–142 μl·animal⁻¹·h⁻¹. These ranges were similar to those of rotifers and A. tonsa nauplii. This is the first report of FLB ingestion by metazoan marine microzooplankton. Although rotifers and ciliates might be expected to ingest small particles such as FLB using ciliary induced feeding currents, the means by which nauplii and copepodites eat FLB is less clear. We propose that they may “eat” bacteria as they “drink” to osmoregulate.     

Photosynthetic response of Myriophyllum salsugineum A.E. orchard to photon irradiance, temperature and external free CO2

The photosynthetic capacity of Myriophyllum salsugineum A.E. Orchard was measured, using plants collected from Lake Wendouree, Ballarat, Victoria and grown subsequently in a glasshouse pond at Griffith, New South Wales. At pH 7.00, under conditions of constant total alkalinity of 1.0 meq dm⁻³ and saturating photon irradiance, the temperature optimum was found to be 30–35°C with rates of 140 μmol mg⁻¹ chlorophyll a h⁻¹ for oxygen production and 149 μmol mg⁻¹ chlorophyll a h⁻¹ for consumption of CO₂. These rates are generally higher than those measured by other workers for the noxious Eurasian water milfoil, Myriophyllum spicatum L., of which Myriophyllum salsugineum is a close relative. The light-compensation point and the photon irradiance required to saturate photosynthetic oxygen production were exponentially dependent on water temperature. Over the temperature range 15–35°C the light-compensation point increased from 2.4 to 16.9 μmol (PAR) m⁻² s⁻¹ for oxygen production while saturation photon irradiance increased from 41.5 to 138 μmol (PAR) m⁻² s⁻¹ for oxygen production and from 42.0 to 174 μmol (PAR) m⁻² s⁻¹ for CO₂ consumption. Respiration rates increased from 27.1 to 112.3 μmol (oxygen consumed) g⁻¹ dry weight h⁻¹ as temperature was increased from 15 to 35°C. The optimum temperature for productivity is 30°C.     

“Survival in air” of the blue mussel Mytilus edulis L. as a sensitive response to pollution-induced environmental stress

Mussels, Mytilus edulis, were exposed for periods of 6 weeks at various locations in Dutch coastal waters during 1989 and 1990. “Survival in air” showed to be a sensitive response parameter for indicating pollution induced environmental stress in transplanted mussels sampled from eight field sites. Increased tissue contaminant levels, especially PCBs and PAHs, correlated with a reduced survival time during aerial exposure. Three weeks exposure of mussels in the laboratory to 1 μg · 1⁻¹ PCBs affected the aerial survival time negatively. Laboratory experiments did not indicate that lowered salinity influences the “Survival in air” response after sufficient acclimation (15 days), facilitating the use of this response parameter in both marine and estuarine waters.     

Photosynthetic photon flux effects on bean response to nitrogen dioxide

Phaseolus vulgaris L. cv. Kinghorn Wax seedlings, supplied with nutrient solution containing either 0 or 5 mM nitrate as sole N source, were exposed to 0.25 μl/l NO₂ for 6 hr each day for 10 days at continuous photosynthetic photon flux (PPF) of 100, 300, 500 or 700 μmol m⁻² sec⁻¹. There was a significant interaction of PPF and nitrate. Shoot and root dry weights increased with increasing PPFs only when nitrate was supplied. The main effects of NO₂ on plant growth were significant; none of the interactions involving NO₂ were significant. Exposure to NO₂ decreased shoot and root dry weight in both the presence and absence of nutrient N and at all PPF levels. All interactions were significant for in vitro leaf nitrate reductase activity (NRA), which increased markedly at PPFs above 100 μmol m⁻² sec⁻¹ when nitrate was supplied. Treatment with NO₂ strongly inhibited enzyme activity in the presence of nitrate, particularly at the 300 μmol m⁻² sec⁻¹ PPF level. These experiments demonstrated that PPF level does not modify the effect of NO₂ on growth but does have a major effect on NRA and on NO₂ effects on NRA in the presence of nutrient nitrate.     

Evidence for the identity of P430 of Photosystem I and chloroplast-bound iron-sulfur protein

The EPR spectrum of Photosystem-I subchloroplast particles, which had been pre-illuminated in the presence of methyl viologen, showed a large P700⁺ signal whereas bound iron-sulfur proteins were not detected. This observation is consistent with a “one-way” electron discharge by the primary electron acceptor, P430⁻, subsequent to the primary photochemical charge separation, and an accumulation of photooxidized P700⁺. Subsequent illumination of the same sample at 77 °K did not change the EPR spectrum. However, if the pre-illuminated subchloroplast particles were allowed to recover at room temperature by standing in the dark for 10 min or by addition of a chemical reductant, subsequent illumination of the sample at 77 °K yielded an EPR spectrum consisting of signals due to both P700⁺ and reduced iron-sulfur protein.     

Validation of urinary thiocyanate as a biomarker of tobacco smoking

Thiocyanate ion (SCN) is the major detoxication product of cyanide, which is converted to SCN by a thiosulphate sulphurtransferase, mainly in hepatic mitochondria. Low-level cyanide exposure for man is caused by factors such as dietary intake of cyanogenic glucosides, tobacco smoking, drug administration and occupational exposure to organic nitriles. Urinary SCN concentration was determined through a commercial kit for the analysis of cyanide in water. Spot urine samples were collected at 7:30 h and 12:30 h, from 99 healthy male white-collar office workers (non-smokers n=72, smokers n=27). Comparison of SCN excretion values did not show any difference between the morning and midday samples. The SCN median value of non-smokers was 24 μmol l^-1 (range 9-24 μmol l^-1) and was statistically different from that of smokers (SCN = 92 μmol l^-1, range 33-275 μmol l^-1) (     

Autoradiography of Water-Soluble Materials in Plant Tissues

Samples of tissue with water-soluble substances are lyophilized and doubly-infiltrated with parlodion and paraffin. Sections are mounted on an adhesive-coated cover slip with chloroform. The reverse side of the cover slip is coated successively with a thin layer of Harleco resin and a thick layer of Kodak “Opaque”. A corner of the cover slip is broken off as a marker. The cover slip is assembled with a covering glass slide on a nuclear track plate (Kodak NTB-2) with protective coating, the section being in contact with the emulsion, and held in place during radioactive exposure. Before development, the cover slip and plate are exposed briefly to light and then disassembled. Following development of the plate and removal of the layer of resin and opaque from the cover slip, staining of the section is optional. Lining up of the section with its autoradiograph can be accurate within 1-5μ.     

Réoxydation du quencher de fluorescence “Q” en présence de 3-(3,4-dichlorophényl)-1,1-diméthylurée

Reoxidation of the fluorescence quencher “Q” in the presence of 3-(3,4-dichlorophenyl)-1,1-dimethylurea

Reoxidation of the fluorescence quencher Q in the presence of 3-(3,4-dichlorophenyl)-1,1-dimethylurea shows the following properties:

It is sensitive to very low concentrations of hydroxylamine (a few μM).

It corresponds to a back reaction between Q⁻ and the primary oxidant Z⁺ formed in the light. A part of this back reaction gives rise to luminescence emission.

Within the range we studied the kinetic of reoxidation is second order with regards to Q⁻.     

Determination of bacterial cell number and cell volume by means of flow cytometry, transmission electron microscopy, and epifluorescence microscopy

Comparative measurements of bacterial total counts and volumes of flow cytometry (FCM), transmission electron (TEM), and epifluorescence microscopy (EFM), were undertaken during a four week mesocosm experiment. Total counts of bacteria measured by TEM, EFM, and FCM were in the range of 1 · 10⁶−6 cells ml⁻¹, 1 · 10⁶−3 · 10¹⁶ cells ml⁻¹, and 5 · 10⁵ cells ml⁻¹ respectively. The mean volume of the bacterial community, measured by means of EFM and TEM, increased from 0.12–0.15 μm³ at the start of the experiment to 0.39–0.53 μm³ at the end. Generally, there was good agreement between the two methods and regression analyses gave r = 0.87 (p < < 0.01) for cell volume and r = 0.97 (p < < 0.01) for cell number. DAPI stained bacteria with volumes less than 0.2 μm³ were not detected by flow cytometry and these were generally an order of magnitude lower than counts made by TEM and EFM. For samples where the mean bacterial cell volume was longer than 0.3 μm³, all three methods were in agreement both with respect to counts and volume estimates.