Development and localization of microsatellite markers for the sibling species Chironomus riparius and Chironomus piger (Diptera: Chironomidae)

Five variable microsatellite loci are reported for the nonbiting midge species Chironomus riparius and Chironomus piger. All loci show considerable intraspecific variation and species‐specific alleles, which allow to discriminate among the two closely related species and their interspecific hybrids, and to estimate genetic diversity within and between populations. Additionally, the loci were localized on C. riparius polytene chromosomes to verify their single copy status and investigate possible chromosomal linkage. The described markers are used in different studies with regard to population and ecological genetics and evolutionary ecotoxicology of Chironomus.     

In Vitro Studies on the Biosynthesis of the Surface Glycoprotein of Trypanosoma congolense1,2

Tritiated leucine, glucosamine, mannose, and galactose were incorporated into the variant specific surface glycoprotein (VSG) of Trypanosoma congolense in vitro. The uptake of the precursors is shown by SDS-polyacrylamide electrophoresis and fluorography, by assay of the radioactivity in immunoprecipitates obtained with specific antisera, and by the isolation of the labeled antigens by affinity chromatography on concanavalin A-sepharose and isoelectric focusing. The in vitro labeled VSG exhibits the same degree of microheterogeneity as that observed in the VSG isolated from trypanosomes grown in animals. Analysis of the incorporated sugars after hydrolysis of the glycoprotein showed that glucosamine and mannose were utilized in biosynthesis of the carbohydrate moiety directly whereas galactose was converted possibly to other intermediates before being incorporated into the antigen. Tunicamycin completely prevented the incorporation of the radiolabeled sugars into the surface glycoprotein. The unglycosylated VSG with a molecular weight of 47 kDa had completely lost its size heterogeneity.     

The Lipid Requirement of the Ciliated Protozoon Tetrahymena patula

ABSTRACT. The ciliated protozoon Tetrahymena patula can be grown in a chemically defined medium supplemented with a suitable lipid. High purity natural phosphoiipids; mono-, di-, and triglycerides: and free fatty acids are suitable lipids. The more complete lipids appear to serve simply as nutritionally convenient sources of fatty acids. T. patula can also be grown in the synthetic medium supplemented with cholesterol or other sterols in lieu of fatty acid containing lipids. Supplementation with either ethanolamine or choline permits suboptimal growth of the ciliate in a lipid-free synthetic medium. No other water soluble compound, of a variety that were tested, permitted growth of the ciliate in the lipid-free medium.     

Isolation of a Stearoyl CoA Desaturase from Tetrahymena thermophila

Cell free preparations of Tetrahymena thermophila contain an enzyme that catalyzes the direct desaturation of stearoyl CoA to octadecenoic acid. The enzyme is associated with the microsomal fraction of the ciliate. Substrate for the enzyme consists of either free stearic acid or stearoyl CoA. Both ATP and CoA are required when free stearate is the substrate and are also highly stimulatory when stearoyl CoA is the substrate. With stearoyl CoA as the substrate, either NADH or NADPH are required for desaturase activity. In the presence of ATP and CoA, either NAD or NADP can replace NADH and NADPH. Desaturase activity is optimal when the enzyme is incubated at a pH of 7.2 and a temperature of 30–35°C. Highest levels of the stearoyl CoA desaturase are found in stationary phase ciliates grown at 35°C.     

Agra, arboreal beetles of Neotropical forests: mixta group, virgata group, and ohausi group systematics (Carabidae)

Abstract. This paper is the fifth in a series designed to cover taxono-mically all species-groups of the lebiine genus Agra , whose cumulative ranges extend from southernmost Texas to northernmost Argentina. The mixta, virgata, feisthameli and ohausi groups constitute Section Feisthameli of the genus, and a key to these groups is provided. The mixta group consists of two species which have a composite range extending from southeastern Brazil to middle Mexico; the virgata group consists of nine species which have a composite range extending from southeastern Brazil to Guatemala; and the ohausi group consists of four species which have a composite range restricted to southeastern Brazil. The speciose feisthameli group is covered in a separate paper.
Among the three groups in the present paper, eleven new species are described from the following type localities: perkinsorum (MEXICO, Nayarit, 17.6 km southwest of Compostela), vate (MEXICO, Veracruz, Los Tuxtlas, La Playa Escondida), nola (REPUBLIC OF PANAMA, Panama, Cerro Campana), cadabra (EQUADOR, Pichincha, 47 km south of Santo Domingo de los Colorados, Rio Palenque Station), chocha (WEST INDIES, Trinidad, Arima Valley), phainops (FRENCH GUIANA, Pariacabo), imaginis (BRAZIL, Goias, Jatahy), inca (PERU, Madre de Dios, Rio Tambopata Reserve, 30 km (air) southwest of Puerto Maldonado), itatiaya (BRAZIL, Rio de Janeiro, Parque Nacional Itatiaya), calamitas (BRAZIL, Bahia, Itamaraju), anthrax (BRAZIL, Espirito Santo, Parque Socretama). A dot map illustrates the range of each taxon.
Distribution and relationships are discussed in general, but detailed cladistic and biogeographic analysis is deferred until taxonomy of the four groups of Section Feisthameli is completed. Species distribution correspond to Pleistocene refuges suggested by other authors based on other groups and classes of organisms.     

WHY COMPENSATING WILDLIFE DAMAGES MAY BE BAD FOR CONSERVATION

Abstract: In an effort to attenuate human-wildlife conflict and promote conservation of charismatic megafauna, compensation programs for wildlife damages have been implemented in many countries. Compensating pastoralists and farmers for damage caused by wildlife reduces hunting pressure on wild animal populations. However, it can also lead to a decrease in efforts to prevent damage and exacerbate conflicts with wildlife. Furthermore, compensation programs increase the return to agriculture and can therefore be viewed as a subsidy toward crop and livestock production. Such subsidies can trigger agricultural expansion (and habitat conversion), an inflow of agriculture producers, and intensification of agricultural production. Each of these impacts is shown to have potentially adverse effects on the wildlife population that compensation intends to favor. In some circumstances, the net effect on the wildlife stock could be negative. This calls for a careful assessment of local ecological and economic conditions before compensation is implemented. Incentive mechanisms that are directly tied to conservation outcomes (e.g., payments to locals based on the size of the wildlife population) should be considered instead of compensation programs.