Resumo Na Amazônia brasileira dois gêneros mono-específicos, Harpia e Morphnus, caracterizam-se por baixa densidade e estão classificados pelo IUCN como Quase Ameaçados, porém ocorrem sobre grande parte do território nacional, suas principais ameaças são a fragmentação florestal, a degradação de hábitat e a caça. Neste estudo avaliamos a abundância destas duas grandes aves de rapina utilizando a base de dados dos programas ambientais da UHE Belo Monte, integrando-se dois métodos para construir um mapa de distribuição ao longo de 245 km do rio Xingu. Os levantamentos terrestres pelo método RAPELD mostraram-se mais eficientes para os registros de grandes águias quando comparado aos esforços padronizados aquáticos, entretanto estes foram complementares na ausência de módulos. Cinquenta e tres por cento foram registros ocasionais durante a supressão da vegetação, afugentamento ou deslocamento. Entre 2012-2014 quatro harpias foram removidas da natureza, dois indivíduos alvo de disparos, uma por colisão com rede elétrica, e outra por atropelamento. Sete ninhos mapeados, a distância média entre os registros de harpia na calha e margens do rio foi de 15 km, 20 km distância média entre ninhos, o que permitiu estimar um total de 20 casais utilizando as florestas aluviais em uma distancia de 270 km, incluindo matas ciliares e os fragmentos fora da margem do rio. Estimamos que territórios de outros 10 casais usando a Volta Grande longe do rio principal também serão afetados pela inundação. A distância média entre os registros de Morphnus foi 16 km ao longo do rio, o único ninho mapeado estava distante 1.3 km do ninho de Harpia. Estes fragmentos florestais estão sendo substituídos por pastagens, ressaltando-se a importância da manutenção das áreas de preservação permanentes (APP) e a proteção destes fragmentos em diversos formatos de áreas de proteção, para diminuir a degradação dos mesmos e garantir a manutenção das populações destes grandes predadores na região do rio Xingu.

Abstract In the Brazilian Amazon, two monospecific genera, the Harpy Eagle and Crested Eagle have low densities and are classified by IUCN as Near Threatened due to habitat loss, deforestation, habitat degradation and hunting. In this study, we evaluate occurrence of these large raptors using the environmental surveys database from Belo Monte Hydroelectric Power Plant. Integrating the dataset from two methods, we plotted a distribution map along the Xingu River, including records over a 276-km stretch of river. Terrestrial surveys (RAPELD method) were more efficient for detecting large raptors than standardized aquatic surveys, although the latter were complementary in areas without modules. About 53% of the records were obtained during activities of wildlife rescue/flushing, vegetation suppression or in transit. Between 2012 and 2014, four Harpy Eagles were removed from the wild; two shooting victims, one injured by collision with power lines and one hit by a vehicle. Also, seven nests were mapped. The mean distance between Harpy Eagle records was 15 km along the river channel, with a mean of 20 km between nests near the channel, which allowed us to estimate 20 possible pairs using the alluvial forest, riverine forest and forest fragments. Territories of another ten pairs will probably be affected by inundation of the Volta Grande channel, which is far from the main river. The average distance between Crested Eagle records was 16 km along the river channel. The only nest found was 1.3 km away from a Harpy Eagle nest. The remnant forests are under threat of being replaced by cattle pastures, so we recommend that permanently protected riparian vegetation borders (APP) be guaranteed, and that forest fragments within 5 km of the river be conserved to maintain eagle populations.

The molecular basis for RHD pseudogene or RHDpsi is a 37-bp insertion in exon 4 of RHD. This insertion, found in two-thirds of D-negative Africans, appears to introduce a stop codon at position 210. The hybrid RHD-CE-Ds, where the 3' end of exon 3 and exons 4 to 8 are derived from RHCE, is associated with the VS+V- phenotype, and leads to a D-negative phenotype in people of African origin. We determined whether Brazilian blood donors of heterogeneous ethnic origin had RHDpsi and RHD-CE-Ds. DNA from 206 blood donors were tested for RHDpsi by a multiplex PCR that detects RHD, RHDpsi and the C and c alleles of RHCE. The RHD genotype was determined by comparison of size of amplified products associated with the RHD gene in both intron 4 and exon 10/3'-UTR. VS was determined by amplification of exon 5 of RHCE, and sequencing of PCR products was used to analyze C733G (Leu245Val). Twenty-two (11%) of the 206 D-negative Brazilians studied had the RHDpsi, 5 (2%) had the RHD-CE-Ds hybrid gene associated with the VS+V- phenotype, and 179 (87%) entirely lacked RHD. As expected, RHD was deleted in all the 50 individuals of Caucasian descent. Among the 156 individuals of African descent, 22 (14%) had inactive RHD and 3% had the RHD-CE-Ds hybrid gene. These data confirm that the inclusion of two different multiplex PCR for RHD is essential to test the D-negative Brazilian population in order to avoid false-positive typing of polytransfused patients and fetuses.