The effects of prolonged emersion and submersion by tidal manipulation on marine macrobenthos

Effects of tidal manipulation, resulting in prolonged periods of emersion and submersion or in protracted tidal cycles, on estuarine benthic animals are reviewed.Prolonged submersion periods did not show effects on mortality of most benthic animals tested, with the exception of the crumb-of-bread sponge Halichondrea panicea, which, at low water-flow rates, was covered with a layer of bacteria and subsequently died.Protracted low-water periods of 18 hours during several weeks hardly caused any mortality. However, protracted low-water periods of 30 hours during some weeks or emersion during several days caused a strong increase in mortality, depending on: the duration of emersion, temperature, condition of the animals, species and age. At temperatures below –1 °C and above 24 °C mortality was generally high. Animals with a low glycogen content were more sensitive to emersion than those with a high content. Species with a shell and those that are relatively big were less sensitive than those without a shell or of small size.The reproductive cycle of benthic animals could be delayed or accelerated by both emersion and submersion.     

Sensitivity to stress in the bivalve Macoma balthica from the most northern (Arctic) to the most southern (French) populations: low sensitivity in Arctic populations because of genetic adaptations?

The stress sensitivity, determined in copper exposureexperiments and in survival in air tests, and thegenetic structure, measured by means of isoenzymeelectrophoresis, were assessed in populations of theBaltic clam Macoma balthica (L.) from itssouthern to its northern distribution limit, in orderto test the hypotheses that near the distributionlimit the clams would be more stress sensitive andwould have a lower genetic variability. Thepopulations in west and north Europe show a stronggenetic resemblance. The populations in the sub-ArcticWhite Sea are genetically slightly different, and showa low stress sensitivity. The populations in theArctic Pechora Sea are genetically very distant fromthe other populations, and show the lowest stresssensitivity. Near the southern distribution limit, inagreement with the hypotheses, genetic variability islow and stress sensitivity high. On the other hand, incontrast to expectation, near the northerndistribution limit, in the populations of the PechoraSea, the genetic variability was higher, thus notreduced, and the stress sensitivity was low comparedto all other populations. Yet, it remains a questionif such is due to gradual physiologicalacclimatization (and ongoing differential selection)or to genetic adaptation.     

Hypophysectomy increases the sensitivity of rats to naloxone-induced hypothermia

Three experiments were done to explore the role of pituitary endorphins in thermoregulation. Hypophysectomized rats were found to be hypothermic when compared to intact rats, but to show a hyperthermic response to handling-induced stress of equal magnitude to that seen in intact animals. In unstressed intact and hypophysectomized animals, the specific opiate antagonist, naloxone, produced a dose-dependent hypothermia, but hypophysectomized animals were found to be ten times more sensitive to naloxone than were the intact animals. In contrast, short-term blockade of pituitary endorphins by dexamethasone had no effect on the magnitude of the naloxone-inducted hypothermia. It was concluded that endorphins of pituitary origin play a long-term tonic role in the modulation of the sensitivity of the brain opioid systems.     

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.     

Measurement of biologically available naphthalene in gas and aqueous phases by use of a Pseudomonas putida biosensor

Genetically constructed microbial biosensors for measuring organic pollutants are mostly applied in aqueous samples. Unfortunately, the detection limit of most biosensors is insufficient to detect pollutants at low but environmentally relevant concentrations. However, organic pollutants with low levels of water solubility often have significant gas-water partitioning coefficients, which in principle makes it possible to measure such compounds in the gas rather than the aqueous phase. Here we describe the first use of a microbial biosensor for measuring organic pollutants directly in the gas phase. For this purpose, we reconstructed a bioluminescent Pseudomonas putida naphthalene biosensor strain to carry the NAH7 plasmid and a chromosomally inserted gene fusion between the sal promoter and the luxAB genes. Specific calibration studies were performed with suspended and filter-immobilized biosensor cells, in aqueous solution and in the gas phase. Gas phase measurements with filter-immobilized biosensor cells in closed flasks, with a naphthalene-contaminated aqueous phase, showed that the biosensor cells can measure naphthalene effectively. The biosensor cells on the filter responded with increasing light output proportional to the naphthalene concentration added to the water phase, even though only a small proportion of the naphthalene was present in the gas phase. In fact, the biosensor cells could concentrate a larger proportion of naphthalene through the gas phase than in the aqueous suspension, probably due to faster transport of naphthalene to the cells in the gas phase. This led to a 10-fold lower detectable aqueous naphthalene concentration (50 nM instead of 0.5 micro M). Thus, the use of bacterial biosensors for measuring organic pollutants in the gas phase is a valid method for increasing the sensitivity of these valuable biological devices.