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A population of Tubifex tubifex in an organically rich stream was found to have an annual life-cycle with a prolonged period of reproductive activity throughout the winter and spring. Cocoons were produced mainly during the late winter and early spring. No cocoons were found during August and September, and there were few mature worms at this time. The population density ranged between 5420 m-2 in mid-September and 613000 m-2 in mid-May. The maximum population biomass (Bmax) recorded was 106 g dry wt m-2 (March) and the minimum was 10 g dry wt m-2 (September), Total annual production (P) was 139 g dry wt m-2 and the average annual biomass (B) was 46 g dry wt m-2 giving an annual P/B ratio of 3.0, and a P/Bmax ratio of 1.3. [ABSTRACT FROM AUTHOR]

The acute toxicity of phenol and ammonia, singly and in combination,to larvae of the ephemeropteran, Baetis rhodani, was examined using a computerized continuous flow system in the laboratory. The 24 h LC50 values (with 95% confidence intervals) were calculated to be 29.9 (17.3-51.5) mg phenol liter-1 and 8.2 (2.0-33.0)mg un-ionized ammonia liter-1. When phenol and ammonia were together in low concentration (< 20 mg liter-1 and < 3 mg liter-1 [un-ionized], respectively), they expressed their toxicity additively, but at higher concentrations they behaved in a greater-than-additive manner. When the 24 h LC50 values were used to predict the toxicity of a coking plant effluent, containing principally ammonia and phenol, it was found that the B. rhodani larvae died quicker than expected indicating the presence of other toxic chemicals. This exemplifies the value of using direct toxicity assessments to detect the presence of unknown toxicants. [ABSTRACT FROM AUTHOR]

The environmental plasmid pQKH6 was transferred conjugatively between strains of Pseudomonas putida at mean frequencies of up to 8.4x10(-4) within pilot-scale sewage filter beds. This frequency was 10-fold higher than that reported previously for this environment and was probably due to seasonal temperature changes. Many (45%) of the plasmids isolated subsequently from the filter beds had restriction fragment length polymorphism (RFLP) profiles that differed from that expected for pQKH6. RFLP analysis revealed structural rearrangements occurring within a particularly restriction-site-rich region of the plasmid. Although no evidence was obtained showing the indigenous invertebrate populations within the filter beds to influence the rate of gene transfer, pQKH6 was transferred with frequencies of up to 1.6x10(-2) within the guts of the filter-bed-dwelling Sylvicola fenestralis larvae during laboratory experiments. This transfer was strongly influenced by donor to recipient ratios. Laboratory experiments also showed that Serratia fonticola survived better within invertebrate guts than P. putida. This evidence, along with experiments showing that S. fonticola could participate in pQKH6 transfer within filter-bed biofilm, identify this bacterium as a better model than P. putida for examining the effect of invertebrates on gene transfer.

The acute toxicity of phenol and ammonia, singly and in combination, to larvae of the ephemeropteran, Baetis rhodani, was examined using a computerized continuous flow system in the laboratory. The 24 h LC50 values (with 95% confidence intervals) were calculated to be 29.9 (17.3-51.5) mg phenol litre(-1) and 8.2 (2.0-33.0) mg un-ionized ammonia litre(-1). When phenol and ammonia were together in low concentration (< 20 mg litre(-1) and < 3 mg litre(-1) [un-ionized], respectively), they expressed their toxicity additively, but at higher concentrations they behaved in a greater-than-additive manner. When the 24 h LC50 values were used to predict the toxicity of a coking plant effluent, containing principally ammonia and phenol, it was found that the B. rhodani larvae died quicker than expected indicating the presence of other toxic chemicals. This exemplifies the value of using direct toxicity assessments to detect the presence of unknown toxicants.