Influence of Incubation Temperature on the Microbial Reductive Dechlorination of 2,3,4,6-Tetrachlorobiphenyl in Two Freshwater Sediments

We studied the impact of incubation temperatures on the dechlorination of 2,3,4,6-tetrachlorobiphenyl (2346-CB) in two sediments from different climates: polychlorinated biphenyl (PCB)-free sediment from Sandy Creek Nature Center Pond (SCNC) in Athens, Ga., and PCB-contaminated sediment from Woods Pond (WP) in Lenox, Mass. Sediment slurries were incubated anaerobically with 350 (mu)M 2346-CB for 1 year at temperatures ranging from 4 to 66(deg)C. Most of the 2346-CB was dechlorinated between 12 and 34(deg)C in both sediments and, unexpectedly, between 50 and 60(deg)C in WP sediment. This is the first report of PCB dechlorination at thermobiotic temperatures. The data reveal profound differences in dechlorination rate, extent, and products as a function of sediment and temperature. The highest observed rate of dechlorination of 2346-CB to trichlorobiphenyls occurred at 30(deg)C in both sediments, but the rate was higher for WP than for SCNC sediment (46 versus 16 (mu)mol liter(sup-1) day(sup-1)). For SCNC sediment the rate of dechlorination dropped sharply below 30(deg)C, but for WP sediments it was near optimal from 20 to 34(deg)C and then dropped sharply below 20(deg)C. In WP sediment most of the meta chlorines were removed between 8 and 34(deg)C and between 50 and 60(deg)C. para dechlorination was restricted from 18 to 34(deg)C and was optimal at 20(deg)C. ortho dechlorination occurred between 8 and 30(deg)C, with optima around 15 and 27(deg)C, but the extent was highly variable. In SCNC sediment complete meta dechlorination occurred from 12 to 34(deg)C and para dechlorination occurred from 18 to 30(deg)C; both were optimal at 30(deg)C. No ortho dechlorination was observed. Dechlorination products were 246-CB, 236-CB, and 26-CB (both sediments) and 24-CB, 2-CB, and 4-CB (WP sediment). The data suggest that in SCNC sediment similar factors controlled meta and para PCB dechlorination over a broad temperature range (18 to 30(deg)C) but that in WP sediment there were multiple temperature-dependent changes in the factors controlling ortho, meta, and para dechlorination. We attribute the differences observed in the two sediments to differences in their PCB-dechlorinating communities.     

Effect of Incubation Temperature on the Route of Microbial Reductive Dechlorination of 2,3,4,6-Tetrachlorobiphenyl in Polychlorinated Biphenyl (PCB)-Contaminated and PCB-Free Freshwater Sediments

We studied the influence of temperature (4 to 66(deg)C) on the microbial dechlorination of 2,3,4,6-tetrachlorobiphenyl (2,3,4,6-CB) incubated for 1 year in anaerobic sediments from Woods Pond in Lenox, Mass., and Sandy Creek Nature Center Pond (SCNC) in Athens, Ga. Seven discrete dechlorination reactions were observed, four of which occurred in both sediments. These were 2,3,4,6-CB (symbl) 2,4,6-CB, 2,3,4,6-CB (symbl) 2,3,6-CB, 2,4,6-CB (symbl) 2,6-CB, and 2,3,6-CB (symbl) 2,6-CB. Three additional reactions occurred only in Woods Pond sediment. These were 2,4,6-CB (symbl) 2,4-CB, 2,4-CB (symbl) 2-CB, and 2,4-CB (symbl) 4-CB. The dechlorination reactions exhibited at least four different temperature dependencies in SCNC sediment and at least six in Woods Pond sediment. We attribute the discrete dechlorination reactions to different polychlorinated biphenyl (PCB)-dechlorinating microorganisms with distinct specificities. Temperature influenced the timing and the relative predominance of parallel pathways of dechlorination, i.e., meta versus para dechlorination of 2,3,4,6-CB and ortho versus para dechlorination of 2,4,6-CB and 2,4-CB. meta dechlorination of 2,3,4,6-CB to 2,4,6-CB dominated at all tested temperatures except at 18 and 34(deg)C, where para dechlorination to 2,3,6-CB dominated in some replicates. The dechlorination of 2,4,6-CB was restricted to (symbl)15 to 30(deg)C in both sediments. Temperature affected the lag time preceding the dechlorination of 2,4,6-CB in both sediments and affected the preferred route of its dechlorination in Woods Pond sediment. para dechlorination dominated at 20(deg)C, and ortho dechlorination dominated at 15(deg)C, but at 18 and 22 to 30(deg)C the relative dominance of ortho versus para dechlorination of 2,4,6-CB varied. These data indicate that field temperatures play a significant role in controlling the nature and the extent of the PCB dechlorination that occurs at a given site.     

Temperature determines the pattern of anaerobic microbial dechlorination of Aroclor 1260 primed by 2,3,4,6-tetrachlorobiphenyl in Woods Pond sediment.

Reductive dechlorination of the Aroclor 1260 residue in Woods Pond (Lenox, Mass.) sediment samples was investigated for a year at incubation temperatures from 4 to 66 degrees C. Sediment slurries were incubated anaerobically with and without 2,3,4,6-tetrachlorobiphenyl (2346-CB; 350 microM) as a primer for dechlorination of the Aroclor 1260 residue. Dechlorination of the Aroclor residue occurred only in live samples primed with 2346-CB and only at 8 to 34 degrees C and 50 to 60 degrees C. The extent and pattern of polychlorinated biphenyl (PCB) dechlorination were temperature dependent. At 8 to 34 degrees C, the dechlorination resulted in 28 to 65% decreases of the hexathrough nonachlorobiphenyls and corresponding increases in the tri- and tetrachlorobiphenyls. At 12 to 30 degrees C, 30 to 40% of the hexa- through nonachlorobiphenyls were dechlorinated in just 3 months. The optimal temperature for overall chlorine removal was 20 to 27 degrees C. We observed four different microbial dechlorination processes with different but partially overlapping temperature ranges, i.e., Process N (flanked meta dechlorination) at 8 to 30 degrees C, Process P (flanked para dechlorination) at 12 to 34 degrees C, Process LP (unflanked para dechlorination) at 18 to 30 degrees C, and Process T (a very restricted meta dechlorination of specific hepta- and octachlorobiphenyls) at 50 to 60 degrees C. These temperature ranges should aid in the development of strategies for the enrichment and isolation of the microorganisms responsible for each dechlorination process. The incubation temperature determined the relative dominance of the four PCB dechlorination processes and the extent and products of dechlorination. Hence, understanding the effects of temperature on PCB dechlorination at contaminated sites should assist in predicting the environmental fate of PCBs or planning bioremediation strategies at those sites.     

Particularites biologiques et ecologiques du Rotifere Sinantherina socialis (Linne)

Resume Le Rotifère épiphyte et colonial Sinantherina socialis (Linné) prolifère dans la Loire depuis quelques années. Ses caractéristiques biologiques et écologiques ont été étu-diées au laboratoire et sur le terrain.Malgré une répartition des pontes régulière dans le temps, les éclosions manifestent une rythmicité liée a la photopériode. La determination des durées de dévelop-pement embryonnaire et post-embryonnaire, du rythme de ponte, de la dúree de la période de sénilité et de la durée de vie à différentes températures montrent que cette espèce se développe entre 18 et 34°C, avec un optimum à 27°C.Le cycle sexué se caractérise par l'existence de femelle amphoteres, capables d'émettre des oeufs femelles, apparemment amictiques, après avoir produit des oeufs mâles. L'apparition de la micticité est Re aux photopériodes courtes et aux fortes densités de population. Des températures suffisamment élevées (plus de 18°C) ont permis d'obtenir au laboratoire jusqu'à 80% d'éclosions parmi les oeufs de duree.

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The periphytic and colonial Rotifer Sinantherina socialis is a thermophile species living between 18 and 34°C. The hatching of its eggs takes place daily with a rhythm linked to the photoperiod. The sexual cycle is characterized by the existence of amphoteric females producing two kinds of eggs. The occurence of mictic eggs appeared to be significantly related to short photoperiods and great densities of population.Summary The periphytic and colonial Rotifer Sinantherina socialis has been swarming in the river Loire every summer for some years. Its biological and ecological characteristics have been studied in the laboratory and in the field.Although the eggs are laid regularly in time, the hatching occurs daily with a rhythm linked to the photoperiod. It occurs about 10 hours after the beginning of the light-period with a 16–8 (LD) photoperiod, 11 hours with a 14–10 photoperiod and 12 hours with a 12–12 photoperiod. To explain this hatching synchronisation and shift in time, the existence of a substance synthesized in the egg by night and destroyed by light might be assumed. The mature eggs would be sensitive to this substance, which would have the effect of delaying the hatching.Measurements of the duration of embryonic and post-embryonic development, of the frequency of laying eggs, of the duration of the senility period and of the duration of life, show that this species can grow between 18 and 34°C, the optimum being 27°C.The sexual cycle is characterized by the existence of amphoteric females, capable to emit apparently amictic eggs, after having produced male eggs. The occurrence of mictic reproduction appeared to be significantly related to short photoperiods and great densities of population. Sufficiently high temperatures (more than 18°C) allowed 80 per cent of hatching among the resting eggs in laboratory cultures.

     

Cloning of a gene encoding a thermo-stable endo-beta-1,4-glucanase from Thermoascus aurantiacus and its expression in yeast

A gene encoding a thermo-stable endo--1,4-glucanase was isolated from the thermophilic fungus, Thermoascus aurantiacusIFO9748, and designated as eg1. Induction of this gene expression at 50°C was stronger than at 30°C. The deduced amino acid sequence encoded by eg1 showed that it belongs to the glycoside hydrolase family 5. The cloned gene was expressed in Saccharomyces cerevisiae and the gene product was purified and characterized. No significant activity loss was detected over 2 h at 70°C and the product was stable from pH 3–10. The enzyme was optimally active at 70°C over 20 min and the optimal pH was 6.     

Detection of a Single Viable Cryptosporidium parvum Oocyst in Environmental Water Concentrates by Reverse Transcription-PCR

Volume 62, no. 9, p. 3386, column 1, last line: "(specific gravity, 2.10) and centrifuging the mixture at 2,000 x g for 10 min" should read "(specific gravity, 1.10) and centrifuging the mixture at 1,050 x g for 10 min." Page 3387, column 1, line 16: "25 cycles at 90(deg)C for 5 min" should read "25 cycles at 90(deg)C for 5 s." [This corrects the article on p. 3385 in vol. 62.].     

Ca2+-Dependent and Ca2+-Independent [3H]GABA Release from Rat Brain Synaptosomes: the Effect of Temperature

The main inhibitory neurotransmitter GABA in the mammalian brain is distributed in the nerve terminals between two pools, vesicular (synaptic vesicles) and cytosolic. GABA is released from these pools by different mechanisms; there are calcium-activated exocytotic release and calcium-independent sodium-dependent release from the cytosolic pool (resulting from the membrane GABA transporter reversal). We investigated the influence of temperature on [³H]GABA release from rat brain synaptosomes, which was induced by stimulation of both these processes. In addition, we used -latrotoxin as a stimulant of [³H]GABA release. Synaptosomes from the rat brain were used in the experiments. 4-Aminopyridine (4-AP) and high [KCl] were applied to stimulate calcium-activated and calcium-independent [³H]GABA release, respectively. 4-AP-evoked [³H]GABA release was of the same intensity at 37 and 25°C (10.1 ± 1.2 and 10.1 ± 0.8% of total [³H]GABA incorporated into the synaptosomes, respectively). The effect of 4-AP on the ⁴⁵Ca²⁺ influx into synaptosomes was also temperature-independent: 0.775 ± 0.075 and 0.725 ± 0.100 nmol/min/mg of protein at 37 and 25°C, respectively. A drop in the effect of 4-AP was observed only at 15°C. When synaptosomes were depolarized with 50 mM KCl, a temperature decrease from 37°C to 25°C resulted in a twofold drop in the [³H]GABA release, from 20.5 ± 1.4 to 10.3 ± 0.7%; at 15°C [³H]GABA release dropped to less than one-third of the norm (6.0 ± 0.5%). -Latrotoxin-stimulated [³H]GABA release was diminished from 32.5 ± 2.5 at 37°C to 17.2 ± 1.3 at 25°C and 5.9 ± 0.4% at 15°C and was not affected by the presence or absence of calcium in the medium. It seems likely that the observed effect of temperature can be interpreted as based on the temperature dependence of the -latrotoxin insertion into the membrane. It is suggested that the pattern of the temperature sensitivity of GABA release from the synaptosomes can be used as a criterion for identification of the mode of neurotransmitter release.     

Anaerobic ortho Dechlorination of Polychlorinated Biphenyls by Estuarine Sediments from Baltimore Harbor

Reductive dechlorination of the ortho moiety of polychlorinated biphenyls (PCBs) as well as of meta and para moieties is shown to occur in anaerobic enrichments of Baltimore Harbor sediments. These estuarine sediments ortho dechlorinated 2,3,5,6-chlorinated biphenyl (CB), 2,3,5-CB, and 2,3,6-CB in freshwater or estuarine media within a relatively short period of 25 to 44 days. ortho dechlorination developed within 77 days in marine medium. High levels of ortho dechlorination (>90%) occurred when harbor sediments were supplied with only 2,3,5-CB. Incubation with 2,3,4,5,6-CB or 2,3,4,5-CB resulted in the formation of the ortho dechlorination product 3,5-CB; however, para dechlorination of these congeners always preceded ortho chlorine removal. ortho dechlorination of PCBs is an exceedingly rare event that has not been reported previously for marine or estuarine conditions. The activity was reproducible and could be sustained through sequential transfers. In contrast, freshwater sediments incubated under the same conditions exhibited only meta and para dechlorinations. The results indicate that unique anaerobic dechlorinating activity is catalyzed by microorganisms in the estuarine sediments from Baltimore Harbor.     

Two anaerobic polychlorinated biphenyl-dehalogenating enrichments that exhibit different para-dechlorination specificities.

Two anaerobic polychlorinated biphenyl (PCB)-dechlorinating enrichments with distinct substrate specificities were obtained: a 2,3,4,6-tetrachlorobiphenyl (2346-CB) para-dechlorinating enrichment derived from Aroclor 1260-contaminated Woods Pond (Lenox, Mass.) sediment and a 2,4,6-trichlorobiphenyl (246-CB) unflanked para-dechlorinating enrichment derived from PCB-free Sandy Creek Nature Center (Athens, Ga.) sediment. The enrichments have been successfully transferred to autoclaved soil slurries over 20 times by using 300 to 350 microM 2346-CB or 246-CB. Both enrichments required soil for successful transfer of dechlorination activity. The 2346-CB enrichment para dehalogenated, in the absence or presence of 2346-CB, only 4 of 25 tested para halogen-containing congeners: 234-CB, 2345-CB, 2346-CB, and 2,4,6-tribromobiphenyl (246-BrB). In the presence of 246-CB, the 246-CB enrichment para dehalogenated 23 of the 25 tested congeners. However, only three congeners (34-CB, 2346-CB, and 246-BrB) were dehalogenated in the absence of 246-CB, indicating that these specific congeners initiate dehalogenation in this enrichment culture. The addition of the 2346-CB (para)-dechlorinating enrichment did not further stimulate the 2346-CB-primed dechlorination of the Aroclor 1260 residue in Woods Pond sediment samples. Compared to the addition of the primer 246-CB or the 246-CB unflanked para-dechlorinating enrichment alone, the addition of both 246-CB (300 microM) and the 246-CB enrichment stimulated the unflanked para dechlorination of the Aroclor 1260 residue in Woods Pond sediments. These results indicate that the two enrichments contain different PCB-dechlorinating organisms, each with high substrate specificities. Furthermore, bioaugmentation with the enrichment alone did not stimulate the desired dechlorination in PCB-contaminated Woods Pond sediment.     

„Room temperature“ incubation for chlamydospore production by Candida albicans

Summary Occasional failure ofCandida albicans to produce chlamydospores on potato-carrot chlamydospore agar could not be attributed to variations in the preparation of the medium including autoclaving and lyophilization. Chlamydospore production was, however, very sensitive to temperature. 104 strains ofC. albicans were grown for 3 days on potato-carrot agar at 16, 20, 25, 30, and 37° C. While at 25° C (the optimal temperature) 93 % of the strains sporulated, a variation of only 5° C either way caused a serious reduction in the performance and only 43 % of the strains sporulated. Sporulation at both extremes of temperature was negligible. A check of temperature variations in the laboratory over a 24 week period during winter months showed that for almost half that period, as expressed in total hours, the temperature remained below 21.1° C (70° F.). Thus room temperature incubation for chlamydospore production inC. albicans may not be sufficient in many cases. Production of chlamydospores on potato-carrot agar was also found to be much superior to that on corn meal agar.     

Development, survival and reproduction of Euseius finlandicus (Acari: Phytoseiidae) at different constant temperatures

Development, survival and reproduction of Euseius finlandicus Oudemans were studied at seven constant temperatures (15, 20, 25, 27, 30, 32 and 34°C) in the laboratory. Within the temperature range tested, developmental period from egg to adult varied from 148 to 360.5h and 133.7 to 336.5h for females and males, respectively. The lower thermal threshold for immature development for females and males was 8.9 and 6.4°C, respectively. Survival during immature development exceeded 90% at all the temperatures from 15 to 32°C, but at 34°C an abrupt decline was recorded. Female longevity decreased gradually from 82.7d at 15°C to 12.2 d at 34°C. The mean generation time ranged from 44.3d at 15°C to 15.9d at 32°C. The highest r _m value (0.2817) was obtained at 30°C and the lowest at 15°C (0.0976). Temperatures above 30°C had an adverse effect on population increase.     

Regiospecificity of chlorophenol reductive dechlorination by vitamin b(12s)

Vitamin B(12), reduced by titanium (III) citrate to vitamin B(12s), catalyzes the reductive dechlorination of chlorophenols. Reductive dechlorination of pentachlorophenol and of all tetrachlorophenol and trichlorophenol isomers was observed. Reaction of various chlorophenols with vitamin B(12) favored reductive dechlorination at positions adjacent to another chlorinated carbon, but chlorines ortho to the hydroxyl group of a phenol were particularly resistant to reductive dechlorination, even if they were also ortho to a chlorine. This resulted in a reductive dechlorination pattern favoring removal of para and meta chlorines, which differs substantially from the pattern exhibited by anaerobic microbial consortia.     

Bud dormancy and vegetative growth in Salix polaris as affected by temperature and photoperiod

Summary Vegetative growth of two ecotypes (lat. 78° 15N and 69°37N) of Salix polaris L. was studied in phytotron experiments. Dormancy of the winter buds was broken by chilling at 0.5°C for 14 to 42 days. Chilling requirement increased with decreasing growth temperature. The optimum temperature for bud break and shoot growth was about 15°C for both ecotypes. Cessation of apical shoot growth and abscission of shoot tip was not prevented by long photoperiods. However, at high temperature, 15°C or more, and in 18 to 24 h photoperiod, two or three growth flushes occurred frequently in both ecotypes. Leaf abscission in the arctic ecotype from lat. 78°N was not affected by photoperiod when grown at 6°C, but was stimulated by short photoperiod when grown at 15°C. In the ecotype from lat. 69°N leaf abscission was enhanced by short photoperiod even at 6°C.     

Effect of Thermal Acclimation on the Expression of Gene Coding for Lactate Dehydrogenase A4 in Loach Skeletal Muscle

Acclimation of Misgurnus fossilis to 5 and 18°C induced considerable changes in LDH-A gene expression in white skeletal muscle. Qualities of total and messenger RNA isolated from weighted portions of muscle are considerably higher after acclimation to 18°C as compared to 5°C. However, a PCR assay of cDNA synthesized from these mRNA and equalized by optical density demonstrated that the level of LDH-A gene expression was indistinguishable for high and low acclimation temperatures, while expression of other genes (glyceraldehyde-3-phosphate dehydrogenase and -actin) considerably increased at 18°C as compared to 5°C. The specific enzymatic activity of LDH from white skeletal muscle of the fish acclimated to low temperature is by 20% higher than that for high-temperature acclimation. Structural analysis of the PCR products synthesized on cDNA-5°C and cDNA-18°C has revealed no differences. However, there are indirect indications of the differences in the C-thermal region of the LDH-A molecule. Northern hybridization reveals the differences at the RNA level: one (1400 bp) or two (about 1600 and 1400 bp) hybridization signals have been found in mRNA-5°C and mRNA-18°C, respectively. The presence of two fractions in the mRNA-18°C indicates alternative splicing.     

Characterization of the requirements and substrates for reductive dehalogenation by strain DCB-1

Summary An obligately anaerobic bacterium known as strain DCB-1 was grown under a variety of conditions to determine the requirements for dehalogenation as well as factors which stimulated or inhibited the process. Dechlorination was obligately anaerobic since introduction of O₂ immediately inhibited the reaction. Sulfuroxy anions, which also serve as electron acceptors for DCB-1, inhibited dechlorination but NO₃ ^– and fumarate did not. The optimum growth medium for dechlorination was 0.2% Na pyruvate and 20% rumen fluid in basal salts. Media with either pyruvate or rumen fluid alone did not support dechlorination. DCB-1 also consumed H₂ but typical substrate concentrations of H₂ (80 kPa) delayed dechlorination. Once the H₂ concentration was reduced to <20 M (2.67 kPa), dechlorination resumed. Dehalogenation by DCB-1 was restricted to the meta substituted benzoates as halogens in other positions and chloroaromatic compounds with other functional groups were not dechlorinated.     

Analysis of the deep chlorophyll maximum across the Azores Front

Physical, chemical and biological observations made in late July and August 1997 across the Azores Front (37° N, 32°W to 32° N, 29°W) are presented. The objectives of the study were: (1) to analyse horizontal and vertical profiles of temperature, salinity, density, nutrients and chlorophyll-a (Chl a) of the top 350 m; (2) to identify the main differences in the deep Chl a Maximum (DCM) and hydrographic structure between the water masses that pass north and south of the Azores Front; and (3) to estimate phytoplankton primary production in these water masses. Horizontal and vertical profiles of salinity, temperature, density, nutrients and phytoplankton pigments in the top 350 m were analysed. The Front separates two distinct water types: the 18°C Mode Water (18 MW) of sub-tropical origin, and the 15°C Mode Water (15 MW) of sub-polar origin. Differences in the DCM and hydrographic structure between 18 MW and 15 MW were observed in the contour plots of each section. The average Chl a concentration between 5 and 200 m depth decreased significantly from 15 MW to 18 MW. The same pattern was observed for the Chl a concentration at the DCM depth. A vertical one-dimensional model was used to estimate the phytoplankton primary production in the 15 MW and 18 MW and led to an estimated water column average gross primary productivity (GPP) between 1.08 and 2.71 mg C m^–3 d^–1 for the 15 MW and about half of these values for the 18 MW. These results indicate that the typical south–north positive slope on DCM depth parallels a latitudinal increase on GPP, suggesting that the location of the Azores Front may have a significant regional impact on GPP.     

Overproduction of an acetylxylan esterase from the extreme thermophile “Caldocellum saccharolyticum” in Escherichia coli

Summary The xynC gene coding for an acetylxylan esterase from the extreme thermophile Caldocellum saccharolyticum was overexpressed in Escherichia coli strain RR28 by cloning the gene downstream from the lacZ promoter region of pUC18 (pNZ1447) or downstream from the temperature-inducible p _r p _l promoters of pJLA602 (pNZ1600). The protein formed high molecular weight aggregates in induced cells of RR28/pNZ1600 but not in RR28/pNZ1447. The enzyme constituted up to 10% of the total cell protein and was located in the cytoplasmic fraction of RR28/pNZ1447. The acetyl esterase was most active at pH 6.0 and 70–75° C with a half-life of 64 h at 70° C and 30 h at 80° C, respectively.Offprint requests to: P. L. Bergquist     

Microbial reductive dechlorination of PCBs

Reductive dechlorination is an advantageous process to microorganisms under anaerobic conditions because it is an electron sink, thereby allowing reoxidation of metabolic intermediates. In some organisms this has been demonstrated to support growth. Many chlorinated compounds have now been shown to be reductively dechlorinated under anaerobic conditions, including many of the congeners in commercial PCB mixtures. Anaerobic microbial communities in sediments dechlorinate Aroclor at rates of 3 µg Cl/g sediment × week. PCB dechlorination occurs at 12° C, a temperature relevant for remediation at temperate sites, and at concentrations of 100 to 1000 ppm. The positions dechlorinated are usually meta > para > ortho. The biphenyl rings, and the mono-ortho- and diorthochlorobiphenyls were not degraded after a one year incubation. Hence subsequent aerobic treatment may be necessary to meet regulatory standards. Reductive dechlorination of Arochlors does reduce their dioxin-like toxicity as measured by bioassay and by analysis of the co-planar congeners. The most important limitation to using PCB dechlorination as a remediation technology is the slower than desired dechlorination rates and no means yet discovered to substantially enhance these rates. Long term enrichments using PCBs as the only electron acceptor resulted in an initial enhancement in dechlorination rate. This rate was sustained but did not increase in serial transfers. Bioremediation of soil contaminated with Aroclor 1254 from a transformer spill was dechlorinated by greater than 50% following mixing of the soil with dechlorinating organisms and river sediment. It is now reasonable to field test reductive dechlorination of PCBs in cases where the PCB concentration is in the range where regulatory standards may be directly achieved by dechlorination, where a subsequent aerobic treatment is feasible, where any co-contaminants do not pose an inhibitory problem, and where anaerobic conditions can be established.This paper was presented at the Pacific Basin Conference on Hazardous Waste, April, 1992, Bangkok, Thailand. Published by permission of the Pacific Basin Consortium for Hazardous Waste Research, East-West Center, Honolulu, HI     

Inhibitory mechanisms of low concentrations of oxidized low-density lipoprotein on platelet aggregation

Summary The intracellular mechanisms underlying oxidized low-density lipoprotein (oxLDL)-signaling pathways in platelets are not yet completely understood. Therefore, the aim of this study was to further examine the effects of oxLDL in prevention of platelet aggregation. In this study, oxLDL concentration-dependently (40–120 g/ml) inhibited platelet aggregation in human platelet-rich plasma stimulated by agonists. Moreover, oxLDL (40 and 80 g/ml) markedly decreased the fluorescence intensity of platelet membranes tagged with diphenylhexatriene. Rapid phosphorylation of a protein of Mr 47,000 (P47), a marker of protein kinase C activation, was triggered by PDBu (150 nM). This phosphorylation was markedly inhibited by oxLDL (40 and 80 g/ml) in phosphorus-32-labeled platelets. In addition, oxLDL (40 and 80 g/ml) markedly increased levels of cyclic AMP and cyclic AMP-induced vasodilator-stimulated phosphoprotein (VASP) Ser¹⁵⁷ phosphorylation. The thrombin-evoked increase in pHi was inhibited in the presence of oxLDL (40 and 80 g/ml). These results indicate that the antiplatelet activity of oxLDL may involve the following pathways. (1) oxLDL may initially induce conformational changes in platelet membranes, leading to inhibition of the activation of protein kinase C, followed by inhibition of P47 protein phosphorylation, and intracellular Ca²⁺ mobilization. (2) oxLDL also activated formation of cyclic AMP and cyclic AMP-induced VASP Ser¹⁵⁷ phosphorylation, resulting in inhibition of the Na⁺/H⁺exchanger; this leads to reduced intracellular Ca²⁺ mobilization, and ultimately to inhibition of platelet aggregation. This study further provides new insights concerning the effects of low concentrations of oxLDL on platelet aggregation.     

Anaerobic dechlorination of polychlorobiphenyls (Aroclor 1242) by pasteurized and ethanol-treated microorganisms from sediments.

A polychlorobiphenyl (PCB)-dechlorinating inoculum eluted from upper Hudson River sediments was treated with either heat or ethanol or both. The treated cultures retained the ability to dechlorinate PCBs (Aroclor 1242) under strictly anaerobic conditions. The dechlorination activity was maintained in serial cultures inoculated with transfers of 1% inoculum when the transferred inoculum was treated each time in the same manner. No methane production was detected in any treated culture, although dechlorination of PCBs in the untreated cultures was always accompanied by methane production. All treated cultures preferentially removed meta chlorines, yielding a dechlorination pattern characterized by accumulation of certain ortho- and para-subsituted congeners such as 2-4-chlorobiphenyl (2-4-CB), 2,4-2-CB, and 2,4-4-CB. In contrast, the untreated cultures showed more extensive dechlorination activities, which almost completely removed both meta and para chlorines from Aroclor 1242. These results suggest that microorganisms responsible for the dechlorination of PCBs in the upper Hudson River sediments can be grouped into two populations according to their responses to the heat and ethanol treatments. Microorganisms surviving the heat and ethanol treatments preferentially remove meta chlorines, while microorganisms lost from the enrichment mainly contribute to the para dechlorination activity. These results indicate that anaerobic sporeformers are at least one of the physiological groups responsible for the reductive dechlorination of PCBs. The selection of a dechlorinating population by such treatments may be an important step in isolation of PCB-dechlorinating microorganisms.