Life cycle and population dynamics of Pycnogonum litorale (Pycnogonida) in a natural habitat

A natural population of Pycnogonum litorale Ström was examined every 4 weeks over a period of 15 months and thereafter at yearly intervals for 15 years. Adult pycnogonids – mating couples and males carrying egg batches – and freshly hatched protonymphon larvae within these egg batches were found throughout the year. The second, third, and fourth instar larvae were only found from April to July, during the vegetation period of their hydroid host Clava multicornis. After metamorphosis to the fifth instar (first juvenile instar) the pycnogonids have a significantly larger proboscis than during the larval period, and they feed on the sea anemone Metridium senile. First juvenile instars were found on M. senile from May to August. Older and larger juvenile stages were found over longer time spans throughout the year, and the maximum number of successive instars shifted slowly from June to December. Freshly moulted adults occurred throughout the year. Males, which on the average are smaller, usually reach the adult stage during late autumn of the first year and females, at the end of the following spring. We conclude that in nature the development from egg to adult stage is completed within one year. Continuous reproduction and asynchronous embryonic development provide offspring throughout most of the year. The annual cycle is synchronized by the vegetation period of C. multicornis, the only host of these pycnogonid larvae in the investigated habitat, and by the arrest of growth during low winter temperatures. The low level of locomotory activity of P. litorale probably requires an environment in which both host species coexist. The abundance of C. multicornis, M. senile, and juvenile pycnogonids decreased from 1990 to 1996, maybe due to hydrographic conditions.     

Photodegradation of PCDD/Fs adsorbed on spruce (Picea abies (L.) Karst.) needles under sunlight irradiation

Spruce (Picea abies (L.) Karst.) needles were exposed to exhaust gas containing polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) generated by combustion of polyvinyl chloride, wood, high-density polyethylene, and styrene. Photodegradation of PCDD/Fs adsorbed on spruce needles under sunlight irradiation was studied. The photodegradation of PCDD/Fs follows pseudo-first-order reaction kinetics, with photolysis half-lives ranging between 40 and 100 h. The photolysis rates of PCDF congeners are higher than PCDD congeners with the same chlorinated substitutions. Higher chlorinated PCDD/Fs tend to photolyze slowly. The wax components in spruce needles may act as proton donors and accelerate the photolysis rate. C-Cl cleavage through the addition of protons to PCDD/F molecules may be an important route for PCDD/Fs photodegradation.     

Nitrifying community analysis in a single submerged attached-growth bioreactor for treatment of high-ammonia waste stream.

This study investigated the nitrifying community structure in a single-stage submerged attached-growth bioreactor (SAGB) that successfully achieved stable nitrogen removal over nitrite of a high-strength ammonia wastewater. The reactor was operated with intermittent aeration and external carbon addition (methanol). With influent ammonia and total Kjeldahl nitrogen ranging from 537 to 968 mg/L and 643 to 1510 mg/L, respectively, 85% nitrogen removal was obtained, and effluent was dominated by nitrite (NO2-/NOx > 0.95). Nitrifying community analysis using fluorescence in situ hybridization (FISH), with a hierarchical set of probes targeting known ammonia-oxidizing bacteria (AOB) within beta-proteobacteria, showed that the AOB community of the biofilter consists almost entirely of members of the Nitrosomonas europaea/eutropha and the Nitrosococcus mobilis lineages. Image analysis of FISH pictures was used to quantify the identified AOB, and it was estimated that Nitrosomonas europaea/eutropha-like AOB accounted for 4.3% of the total volume of the biofilm, while Nitrosococcus mobilis-like AOB made up 1.2%; these numbers summed up to a total AOB fraction of 5.5% of the total volume on the biofilm. Nitrite-oxidizing bacteria (NOB) were not detectable in the biofilm samples with probes for either Nitrospira sp. or Nitrobacter sp., which indicated that NOB were either absent from the biofilters or present in numbers below the detection limit of FISH (< 0.1% of the total biofilm). Nitrite oxidizers were likely outcompeted from the system because of the free ammonia inhibition and the possibility that the aeration period (from intermittent aeration) was not sufficiently long for the NOB to be released from the competition for oxygen with heterotrophs and AOB. The nitrogen removal via nitrite in a SAGB reactor described in this study is applicable for high-ammonia-strength wastewater treatment, such as centrate or industrial wastes.