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Background
Bees (Hymenoptera: Apoidea: Anthophila) are the most important group of pollinators with about 20,507 known species worldwide. Despite the critical role of bees in providing pollination services, studies aiming at understanding which species are present across disturbance gradients are scarce. Limited taxononomic information for the existing and unidentified bee species in Tanzania make their conservation haphazard. Here, we present a dataset of bee species records obtained from a survey in nothern Tanzania i.e. Kilimanjaro, Arusha and Manyara regions. Our findings serve as baseline data necessary for understanding the diversity and distribution of bees in the northern parts of the country, which is a critical step in devising robust conservation and monitoring strategies for their populations.
New information
In this paper, we present information on 45 bee species belonging to 20 genera and four families sampled using a combination of sweep-netting and pan trap methods. Most species (27, ~ 60%) belong to the family Halictidae followed by 16 species (35.5%) from the family Apidae. Megachilidae and Andrenidae were the least represented, each with only one species (2.2%). Additional species of Apidae and Megachilidae sampled during this survey are not yet published on Global Biodiversity Information Facility (GBIF), once they will be available on GBIF, they will be published in a subsequent paper. From a total of 953 occurrences, highest numbers were recorded in Kilimanjaro Region (n = 511), followed by Arusha (n = 410) and Manyara (n = 32), but this pattern reflects the sampling efforts of the research project rather than real bias in the distributions of bee species in northern Tanzania.
1. Pollination of sexually reproducing plants requires pollen transfer agents, which can be biotic, abiotic or a combination of biotic and abiotic agents. The dominance of one of pollination system in wild plant communities depends on climatic factors and/or degrees of anthropogenic influences, which have effects on pollinator diversity and pollination function. Anthropogenic activities and climate change are also considered as main causes of ongoing invasion of invasive species into wild and managed habitats which can bring up competition for pollinators with possible negative consequences for the reproduction of co-occurring native plant species.
2. The study aimed to determine pollination systems and pollination limitation of invasive and native plant communities in natural savannah between 870 – 1130 m and semi-natural (managed) grassland between 1300 – 1750 m above sea level; effects of flower density and pollinator abundance on seed production of cross-pollinated and self-pollinated plants; and relationships of bee abundance and the proportion of cross- pollinated plants at the southern slope of Mount Kilimanjaro, Tanzania.
3. Pollinator-exclusion, open pollination and supplemental hand-pollination treatments were applied to 27 plant species in savannah and grassland habitats. Flowers were counted in each clusters based upon their species. Pollinators were sampled by using pan traps. Information-theory-based multi-model averaging and generalized linear mixed effects models were used to identify and analyze the effects of flower density, pollinator abundance, pollination treatments and habitat types on seed production. Regression models were used to determine relationships of altitude with bee abundance, and with proportion of cross-pollinated plants.
4. My results show that mean seed numbers of native plants were significantly lower in pollinator-exclusion treatments than in open-pollination treatments, indicating their reliance on pollinators for reproductive success. In contrast, seed numbers of invasive plants were similar in pollinator-exclusion and open-pollination treatments, demonstrating an ability of reproduction without pollinators. Despite of higher levels of self-pollination in invasive plants, supplemental hand-pollination treatments revealed pollen limitation in grassland and marginally in savannah habitats. There were no significant difference in seed numbers between supplemental hand pollination and open pollination treatments of native plant communities in savannah and grassland, which indicates no pollination limitation in the studied ecological system for native communities. Besides, grassland plants produced comparatively more seeds than savannah plants, however seeds in grasslands were lighter than those of the savannah which may be due to nutrient limitation in grassland.
5. I found 12 cross-pollinated and 15 self-pollinated plants along altitudinal gradient after comparing seeds from pollinator-excluded and open-pollinated experiments. I also found that proportions of cross-pollinated plants and bee abundance simultaneously decreased with increasing altitude. All cross-pollinated plants were native and grew in savannah habitats, with an exception of one species.
6. Neither effects of focal flower density nor a significant interaction between focal flower densities and bee abundance for self-pollinated plants were observed. However, there were effects of focal flower densities and interactions of flower density with bee abundance for cross-pollinated plants. Non-focal flower density has no significant effects on seed production of cross-pollinated and self-pollinated plants.
7. The results show that native plants depend more on cross-pollination than invasive plants, despite of most native plants in managed habitat (grassland) rely on self-pollination for reproduction. The tendency of having more cross-pollinated plants in natural savannah which are in low altitude coincides with other finding that the cross-pollinated plants and bee abundance simultaneously decrease with increasing altitude. Therefore, our findings support the hypotheses that self-fertilization of flowering plants increases with increasing altitude, and pollinator limitation is most pronounced in managed or disturbed habitats. Despite of reduction of pollinators in grassland, only invasive plants experience pollen limitation, which may be due to poor integration with available pollinator networks.
8. I also found bee abundance and flower density are not the main pollination factors required by self-pollinated plants during reproduction. However, focal flower density, which influences pollinator diversity, is more applicable to cross-pollinated plants. Climate change and anthropogenic activities in natural habitats are factors that influence pollinator abundance and functioning, which lead to a shift of mating systems in plant communities so as to assure their reproduction.
Background
The World Health Organization (WHO) has recommended guidelines for a HIV drug resistance (HIVDR) survey for resource-limited countries. Eligibility criteria for patients include age below 25 years in order to focus on the prevalence of transmitted HIVDR (tHIVDR) in newly-infected individuals. Most of the participating sites across Africa have so far reported tHIVDR prevalences of below 5%. In this study we investigated whether the rate of HIVDR in patients <25 years is representative for HIVDR in the rest of the therapy-naïve population.
Methods and Findings
HIVDR was determined in 88 sequentially enrolled ART-naïve patients from Mwanza, Tanzania (mean age 35.4 years). Twenty patients were aged <25 years and 68 patients were aged 25–63 years. The frequency of HIVDR in the study population was 14.8% (95%; CI 0.072–0.223) and independent of NVP-resistance induced by prevention of mother-to-child transmission programs. Patients >25 years had a significantly higher HIVDR frequency than younger patients (19.1%; 95% CI 0.095–0.28) versus 0%, P = 0.0344). In 2 out of the 16 patients with HIVDR we found traces of antiretrovirals (ARVs) in plasma.
Conclusions
ART-naïve patients aged over 25 years exhibited significantly higher HIVDR than younger patients. Detection of traces of ARVs in individuals with HIVDR suggests that besides transmission, undisclosed misuse of ARVs may constitute a significant factor in the generation of the observed high HIVDR rate. The current WHO tHIVDR survey that is solely focused on the transmission of HIVDR and that excludes patients over 25 years of age may therefore result in substantial underestimation of the prevalence of HIVDR in the therapy-naïve population. Similar studies should be performed also in other areas to test whether the so far reported optimistic picture of low HIVDR prevalence in young individuals is really representative for the rest of the ART-naïve HIV-infected population.
The StrongPaed study in the paediatric ward of a referral hospital in Mwanza in the lake region of Tanzania showed the prevalence of S. stercoralis, G. lamblia, E. histolytica and E. dispar as well as of other intestinal parasites with various diagnostic methods.
The prevalence of S. stercoralis was 2-10 % depending on the diagnostic methods used. There were no symptomatic infections but only carriage of the nematode. The positive results differed greatly depending on the performed diagnostic methods. None of the diagnostics showed satisfying results, neither in sensitivity and specificity nor in feasibility for this population in an endemic region in sub-Saharan Africa. PCR and microscopy were limited by the low amount of examined stool samples and by the resulting lack of sensitivity. Stool cultures were limited by time-consuming procedures and mainly by the problem of differentiation from hookworm and the resulting lack of specificity. ELISA was limited by the need of blood samples and also by poor specificity in the ELISA used.
The prevalence of G. lamblia was high, but mostly only carriage and not symptomatic infections was seen. No E. histolytica was detected, but 8.5 % samples were positive for E. dispar. Among the performed diagnostics, the rapid test showed sufficient results. It showed better sensitivity than microscopy and is cheaper and more feasible than PCR. Differentiation between E. histolytica and E. dispar was only possible with qPCR performed in Germany.
More children were positive for intestinal parasites from rural than from urban areas. The profession of the parents working as farmers was a risk factor for intestinal parasitic infections. Hygienic living conditions such as access to tap water and flush toilets at home were preventive for intestinal parasitic infections in children.
The acquired immunodeficiency syndrome (AIDS) is currently the most infectious disease worldwide. It is caused by the human immunodeficiency virus (HIV). At the moment there are ~33.3 million people infected with HIV. Sub-Saharan Africa, with ~22.5 million people infected accounts for 68% of the global burden. In most African countries antiretroviral therapy (ART) is administered in limited-resource settings with standardised first- and second-line ART regimens. During this study I analysed the therapy-naïve population of Cape Town, South Africa and Mwanza, Tanzania for any resistance associated mutations (RAMs) against protease inhibitors, nucleoside reverse transcriptase inhibitors and non-nucleoside reverse transcriptase inhibitors. My results indicate that HIV-1 subtype C accounts for ~95% of all circulating strains in Cape Town, South Africa. I could show that ~3.6% of the patient derived viruses had RAMs, despite patients being therapy-naïve. In Mwanza, Tanzania the HIV drug resistance (HIVDR) prevalence in the therapy-naïve population was 14.8% and significantly higher in the older population, >25 years. Therefore, the current WHO transmitted HIVDR (tHIVDR) survey that is solely focused on the transmission of HIVDR and that excludes patients over 25 years of age may result in substantial underestimation of the prevalence of HIVDR in the therapy-naïve population. Based on the prevalence rates of tHIVDR in the study populations it is recommended that all HIV-1 positive individuals undergo a genotyping resistance test before starting ART. I also characterized vif sequences from HIV-1 infected patients from Cape Town, South Africa as the Vif protein has been shown to counteract the antiretroviral activity of the cellular APOBEC3G/F cytidine deaminases. There is no selective pressure on the HIV-1 Vif protein from current ART regimens and vif sequences was used as an evolutionary control. As the majority of phenotypic resistance assays are still based on HIV-1 subtype B, I wanted to design an infectious HIV-1 subtype C proviral molecular clone that can be used for in vitro assays based on circulating strains in South Africa. Therefore, I characterized an early primary HIV-1 subtype C isolate from Cape Town, South Africa and created a new infectious subtype C proviral molecular clone (pZAC). The new pZAC virus has a significantly higher transient viral titer after transfection and replication rate than the previously published HIV-1 subtype C virus from Botswana. The optimized proviral molecular clone, pZAC could be used in future cell culture and phenotypic HIV resistance assays regarding HIV-1 subtype C.
The present study investigates the infection rates of parasites, morbidity, and the living conditions of street children and orphans in Mwanza city, northern Tanzania. A high percentage of orphans and street children in Mwanza city is infected with one or more parasites. A significantly higher rate of infections with S. mansoni in street children as compared with orphans could be observed. The prevalence of S. mansoni determined by POC CCA test was 65.9% for orphans and 94.5% for street children. 19.2% of the orphans tested positive for S. mansoni in Kato Katz. Of the street children, 77.1% showed positive test results in Kato-Katz. Only 1.3% of the orphans stated in the questionnaire that they use the lake to wash, whereas 91.1% of the street children named the lake as at least one of their options for washing. Protozoal infections used as a marker for hygiene were at a comparable level for both groups. Microscopy showed positive results for G. intestinalis in 8.2% and for E. histolytica/dispar in 23% of orphans and 8.1% for G. intestinalis, and 23.8% for E. histolytica/dispar in street children. Through ultrasonography, we observed no signs of severe PPF and only a few mild PPF patterns. Most street children use the lake to wash and often do not have access to adequate sanitation. However, everyone in the study group indicated having access to safe drinking water. Overall, we found the general hygienic conditions for both groups to be inadequate. With the help of simple public health measures, like improve sanitation and regular mass drug administration, the overall situation would likely be considerably improved.