ABSTRACT
Studies based on the bacterial diversity present in Mansonia spp. are limited; therefore, the aim of this study was to investigate the bacterial diversity in females and larvae of Mansonia spp., describe the differences between the groups identified, and compare the microbiota of larvae from different collection sites. Sequences of the 16S rRNA region from the larvae and females of Mansonia spp. were analyzed. Diversity analyzes were performed to verify the possible bacterial differences between the groups and the collection sites. The results showed Pseudomonas was the most abundant genus in both females and larvae, followed by Wolbachia in females and Rikenellaceae and Desulfovibrio in larvae. Desulfovibrio and Sulfurospirillum, sulfate- and sulfur-reducing bacteria, respectively, were abundant on the larvae. Aminomonas, an amino acid-degrading bacterium, was found only in larvae, whereas Rickettsia was identified in females. Bacterial diversity was observed between females and larvae of Mansonia and between larvae from different collection sites. In addition, the results suggest that the environment influenced bacterial diversity.
Subject(s)
Culicidae , Female , Animals , Larva/microbiology , Brazil , RNA, Ribosomal, 16S/genetics , Culicidae/genetics , Bacteria/geneticsABSTRACT
In the Amazon rainforest, methylmercury (MeHg) is easily biomagnified and bio-accumulated in the aquatic food chain. This unique biome has been studied for occupational and environmental issues related to human health and contamination through fish consumption; however, wildlife studies have not yet addressed fish-eating birds. Different species of birds categorized by foraging strategies and life-stages were studied in the Madeira River Basin (Western Amazon rainforest). Feather and tissue (muscle, liver, kidneys, lungs, heart, brain, and blood) samples were collected opportunistically from six bird species feeding on fish and aquatic fauna and a scavenger (a saprophagous species) during the low-water season (July 2017). All collected samples were analyzed for total Hg (THg); methyl-Hg (MeHg) was determined only in feathers. The mean THg concentrations in feathers (dw) were as follows: Ardea cocoi (4.05 µg g-1, n = 51) > Egretta thulla (3.94 µg g-1, n = 5) > Ardea alba (3.80 µg g-1, n = 61) > Anhinga anhinga (3.69 µg g-1, n = 8) > Nannopterum brasilianus (3.07 µg g-1, n = 10). The scavenger Coragyps atratus showed mean THg in feathers (9.93 µg g-1, n = 30) to be significantly higher than in fish-eating birds. Across species, THg levels in feathers correlated significantly with THgmuscle (p = 0.022) and THgbrain (p = 0.002). THg concentrations varied in tissues (feather > liver > kidneys > lungs > heart > muscle > blood > brain). The Hgbrain:Hgfeather, Hgbrain:Hgmuscle, and Hgbrain:Hgblood ratios were 0.031, 0.503 and 0.516, respectively. The mean [MeHg:THg] ratio in feathers from aquatic birds varied between species from 14 to 74% with a mean of 38%. Scavenger birds that forage in the terrestrial Amazonian environments concentrate more THg than species that forage in the aquatic environment. None of the aquatic species showed THg concentration in internal organs that were above threshold for risk of Hg toxicity; additionally, they are not listed in the categories of threat by the International Union for Conservation of Nature (IUCN).
Subject(s)
Mercury , Animals , Birds , HumansABSTRACT
BACKGROUND: The Madeira River (Amazon Basin) has been impacted by activities related to artisanal and small-scale gold mining (ASGM), deforestation and burning (for timber, agriculture, and hydroelectric dam projects). All these activities contribute to environmental mercury (Hg) release and cycling into the Amazon ecosystem and thus to changing lifestyles. METHOD: We assessed exposure to total and MeHg in two small riverine communities of the Madeira River (Amazon): Lago Puruzinho (LP, nâ¯=â¯26 families) and São Sebastião do Tapurú (SST, nâ¯=â¯31 families). Samples of human hair (nâ¯=â¯137), blood (nâ¯=â¯39), and feces (nâ¯=â¯41) were collected from adults and children (0-15 years of age). RESULTS: In women of childbearing age from LP village, the mean blood total-Hg (THg) (45.54⯱â¯24.76⯵g.L-1) and MeHg (10.79⯱â¯4.36⯵g.L-1) concentrations were significantly (pâ¯=â¯0.0024; pâ¯<â¯0.0001, respectively) higher than in women from SST village (THg: 25.32⯱â¯16.75⯵g.L-1; MeHg: 2.32⯱â¯1.56⯵g.L-1) village; the trend in hair-Hg persisted but was statistically significant (pâ¯<â¯0.0145) only for THg (LP, 11.34⯱â¯5.03 µg.â¯g-1; SST, 7.97⯱â¯3.51 µg.â¯g-1). In women, the median hair:blood ratio of total Hg was 269. In children, the mean hair THg concentrations were 6.07⯱â¯3.60 µg.â¯g-1 and 6.47⯱â¯4.16 µg.â¯g-1 in LP and SST; thus, not significantly different (pâ¯=â¯0.8006). There was a significant association (pâ¯<â¯0.001) between hair-Hg concentrations of mothers and their respective children. The excretion of Hg in feces of women (0.52 µg.â¯g-1 dw) was not significantly different from children (0.49 µg.â¯g-1 dw). The only statistically significant correlation between Hg in feces and in hair was found in children, (nâ¯=â¯16, rsâ¯=â¯0.38, pâ¯=â¯0.005). Significant relationship was seen between the levels of THg in blood and hair of women from LP and SST. Based on hair-Hg concentrations, fish consumption rate ranged from 94.5 to 212.3â¯g.day-1. CONCLUSION: Women and children excrete THg in feces in comparable concentrations. However, the mean fish consumption rate and blood MeHg are higher in the most remote villagers. Mother`s hair-Hg concentration is a good predictor of children's hair-Hg.