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33 results for “Bactrocera carambolae”
Fig. 2 in Biology and fertility life table of Bactrocera carambolae on grape and acerola
Fig. 2. Survival curves of Bactrocera carambolae adults grown on grapes (Vitis vinifera) and acerola (Malpighia emarginata) in laboratory (26 ± 2 ◦C; 60 ± 10% RH; photophase 12 h).
Fig. 3 in Biology of Bactrocera carambolae (Diptera: Tephritidae) on four hosts
Fig. 3. Survival curve of males of Bactrocera carambolae: Treatment A (Averrhoa carambola), Treatment B (Psidium guajava), Treatment C (Spondias mombin) and Treatment D (Eugenia stipitata). The arrows indicate the mean survival time (Tms).
Fig. 2 in Biology of Bactrocera carambolae (Diptera: Tephritidae) on four hosts
Fig. 2. Survival curve of females of Bactrocera carambolae: Treatment A (Averrhoa carambola), Treatment B (Psidium guajava), Treatment C (Spondias mombin) and Treatment D (Eugenia stipitata). The arrows indicate the mean survival time (Tms).
Fig. 1 in Biology of Bactrocera carambolae (Diptera: Tephritidae) on four hosts
Fig. 1. Daily rate of oviposition of Bactrocera carambolae reared on fruits of carambola (Averrhoa carambola), araza (Eugenia stipitata), guava (Psidium guajava) and yellow mombin (Spondias mombin).
Figure 6 in Effect of soil class and moisture on the depth of pupation and pupal viability of Bactrocera carambolae Drew & Hancock (1994)
Figure 6 Effect of time and moisture on the emergence of flies from three soil types (sandy, sandy clay loam and clay loam).The lines in the graphs of the relation between the number of flies emerged and time (a-c) represent nonlinear models with a quadratic term [a) y = 4.12***-0.94***x+0.04x^2, b)y = 0.81*+0.5*x-0.098***x^2 and c) y = 2.47***-0.26x-0.02x^2], while the lines in the graphs of the relation between number of flies emerged and moisture (d-f) represent linear models with Poisson distributions [d) y = 0.11+0.0016x, e) y = -0.69***+0.01***x and f) y = -0.37***+0.008***x]. *:P<0.05; *** P<0.001.
Figure 5 in Effect of soil class and moisture on the depth of pupation and pupal viability of Bactrocera carambolae Drew & Hancock (1994)
Figure 5 Effect of soil depth and moisture on the number of pupae in three soil types (sandy, sandy clay loam and clay loam). The lines in the graphs of the relation between the number of pupae and depth (a-c) represent exponential models [a) y=exp(1.58-1.24***x), b) y=exp(1.42-0.21***x) and c) y=exp(1.18-0.16***x)], while the lines in the graphs of the relation between number of pupae and moisture (d-f) represent linear models with Poisson distributions [d) y = 0.56-0.0006x, e) y = 0.55-0.0017x and f) y = 0.55-0.0025x].*** P<0.001.
Figure 4 in Effect of soil class and moisture on the depth of pupation and pupal viability of Bactrocera carambolae Drew & Hancock (1994)
Figure 4 Number of pupae per centimeter for each treatment (T1 to T4 with sandy soil, T5 to T8 with sandy clay loam and T9 to T12 with clay loam) in combination with different moisture levels (0%, 30%, 60% and 90% for T1 to T4, T5 to T8 and T9 to T12, respectively). Treatments: T1 = sandy × 0% moisture, T2 = sandy x 30% moisture, T3 = sandy x 60% moisture, T4 = sandy x 90% moisture, T5 = sandy clay loam x 0% moisture, T6 = sandy clay loam x 30% moisture, T7 = sandy clay loam x 60% moisture, T8 = sandy clay loam x 90% moisture, T9 = clay loam x 0% moisture, T10 = clay loam x 30% moisture, T11 = clay loam x 60% moisture, and T12 = clay loam x 90% moisture.
Figure 3 in Effect of soil class and moisture on the depth of pupation and pupal viability of Bactrocera carambolae Drew & Hancock (1994)
Figure 3 Illustration of the steps of the experiment: A) Larvae on the soil surface; B) Containers used in the experiment; C) Removal of a 1 cm ring; D) Transfer of the soil to a plastic tray; E) Sorting and counting of the pupal cases; and F) Insects that were unable to rupture the soil layer. Photos: Eric Joel Ferreira do Amaral.
Figure 1 in Effect of soil class and moisture on the depth of pupation and pupal viability of Bactrocera carambolae Drew & Hancock (1994)
Figure 1 Representation of the steps for rearing B. carambolae: A) Oviposition container; B) Cage with adults; C) Eggs; D) Feed based on carrots in a plastic tray containing larvae; E) Paper envelope containing the plastic tray with larvae. Photos: Eric Joel Ferreira do Amaral.
Supplementary material 2 from: Aketarawong N, Isasawin S, Sojikul P, Thanaphum S (2015) Gene flow and genetic structure of Bactrocera carambolae (Diptera, Tephritidae) among geographical differences and sister species, B. dorsalis, inferred from microsatellite DNA data. In: De Meyer M, Clarke AR, Vera MT, Hendrichs J (Eds) Resolution of Cryptic Species Complexes of Tephritid Pests to Enhance SIT Application and Facilitate International Trade. ZooKeys 540: 239-272. https://doi.org/10.3897/zookeys.540.10058
Component data at the four successive thresholds used to illustrate Figure 5: Explanation note: Component data are used to illustrate the structure of the subset of Bactrocera carambolae and Bactrocera dorsalis populations. The highest Betweenness-centrality is highlighted in blue.
Supplementary material 1 from: Aketarawong N, Isasawin S, Sojikul P, Thanaphum S (2015) Gene flow and genetic structure of Bactrocera carambolae (Diptera, Tephritidae) among geographical differences and sister species, B. dorsalis, inferred from microsatellite DNA data. In: De Meyer M, Clarke AR, Vera MT, Hendrichs J (Eds) Resolution of Cryptic Species Complexes of Tephritid Pests to Enhance SIT Application and Facilitate International Trade. ZooKeys 540: 239-272. https://doi.org/10.3897/zookeys.540.10058
Component data at the five successive thresholds used to illustrate Figure 4: Explanation note: Component data are used to illustrate the structure of the subset of Bactrocera carambolae populations. The Highest Betweenness-centrality is highlighted in blue.
Supplementary material 4 from: Aketarawong N, Isasawin S, Sojikul P, Thanaphum S (2015) Gene flow and genetic structure of Bactrocera carambolae (Diptera, Tephritidae) among geographical differences and sister species, B. dorsalis, inferred from microsatellite DNA data. In: De Meyer M, Clarke AR, Vera MT, Hendrichs J (Eds) Resolution of Cryptic Species Complexes of Tephritid Pests to Enhance SIT Application and Facilitate International Trade. ZooKeys 540: 239-272. https://doi.org/10.3897/zookeys.540.10058
Comparisons among three different the individual admixture plots: Explanation note: Comparisons among the individual admixture plots of 289 individuals, for K = 3, considering correlated allele frequency, uncorrelated allele frequency, and missing data as recessive homozygotes for the null alleles, respectively.
Supplementary material 3 from: Aketarawong N, Isasawin S, Sojikul P, Thanaphum S (2015) Gene flow and genetic structure of Bactrocera carambolae (Diptera, Tephritidae) among geographical differences and sister species, B. dorsalis, inferred from microsatellite DNA data. In: De Meyer M, Clarke AR, Vera MT, Hendrichs J (Eds) Resolution of Cryptic Species Complexes of Tephritid Pests to Enhance SIT Application and Facilitate International Trade. ZooKeys 540: 239-272. https://doi.org/10.3897/zookeys.540.10058
Component data at the four successive thresholds used to illustrate Figure 6: Explanation note: Component data are used to illustrate the structure of the subset of the Salaya5 strain and wild populations. The highest Betweenness-centrality is highlighted in blue.
Data from: Tracking the origins of fly invasions; using mitochondrial haplotype diversity to identify potential source populations in two genetically intertwined fruit fly species (Bactrocera carambolae and Bactrocera dorsalis [Diptera: Tephritidae])
Bactrocera carambolae Drew and Hancock and B. dorsalis (Hendel) (Diptera: Tephritidae) are important pests of many fruits. These flies have been spread across the world through global travel and trade, and new areas are are at risk of invasion. Whenever new invasive populations are discovered, quick and accurate identification is needed to mitigate the damage they can cause. Determining invasive pathways can prevent further spread of pests as well as subsequent reinvasions through the same pathway. Molecular markers can be used for both species identification and pathway analysis. We analyzed 1601 individuals from 18 populations using 765 base pairs of the mitochondrial cytochrome oxidase I (COI) gene to infer the haplotype diversity and population structure within these flies from across their native and invasive ranges. We analyzed these samples by either grouping by species or geographic populations due to the genetic similarity in the mitochondrial genome. We found no genetic structure between B. dorsalis and B. carambolae and our findings suggest recent and most likely ongoing, genetic exchange between these two species in the wild. Hyper-diverse mitochondrial genetic diversity in the native range suggests large population sizes and relatively high mutation rates. Only 52% of the haplotypes found in the trap captures from California are shared with haplotypes from flies found in our global survey, indicating significant genetic diversity in the native range that is missing from our samples. However, these results provide a foundation for the accurate determination of the provenance of invasive populations around the world.
Supplementary material 2 from: Leblanc L, Hossain MA, Doorenweerd C, Khan SA, Momen M, San Jose M, Rubinoff D (2019) Six years of fruit fly surveys in Bangladesh: a new species, 33 new country records and discovery of the highly invasive Bactrocera carambolae (Diptera, Tephritidae). ZooKeys 876: 87-109. https://doi.org/10.3897/zookeys.876.38096
: Data type: statistical data
Supplementary material 1 from: Leblanc L, Hossain MA, Doorenweerd C, Khan SA, Momen M, San Jose M, Rubinoff D (2019) Six years of fruit fly surveys in Bangladesh: a new species, 33 new country records and discovery of the highly invasive Bactrocera carambolae (Diptera, Tephritidae). ZooKeys 876: 87-109. https://doi.org/10.3897/zookeys.876.38096
: Data type: statistical data
Figure 5 from: Leblanc L, Hossain MA, Doorenweerd C, Khan SA, Momen M, San Jose M, Rubinoff D (2019) Six years of fruit fly surveys in Bangladesh: a new species, 33 new country records and discovery of the highly invasive Bactrocera carambolae (Diptera, Tephritidae). ZooKeys 876: 87-109. https://doi.org/10.3897/zookeys.876.38096
Figure 5 Maximum likelihood tree of COI-3P sequences of Zeugodacus madhupuri sp. nov. and its closest relatives in COI. Taxa names include UHIM 'ms' molecular voucher numbers, GenBank accessions and ISO three letter country codes. The record of Zeugodacus hengsawadae was published as Zeugodacus nr. tau in San Jose et al. (2018a). The scale bar indicates substitutions per site; values on the branches indicate ultrafast bootstrap support values and Sh-aLRT bootstrap values, respectively.
Figure 4 from: Leblanc L, Hossain MA, Doorenweerd C, Khan SA, Momen M, San Jose M, Rubinoff D (2019) Six years of fruit fly surveys in Bangladesh: a new species, 33 new country records and discovery of the highly invasive Bactrocera carambolae (Diptera, Tephritidae). ZooKeys 876: 87-109. https://doi.org/10.3897/zookeys.876.38096
Figure 4 Bactrocera carambolae collected in Bangladesh A head B head and scutum C abdomen D wing E lateral view.
Figure 1 from: Leblanc L, Hossain MA, Doorenweerd C, Khan SA, Momen M, San Jose M, Rubinoff D (2019) Six years of fruit fly surveys in Bangladesh: a new species, 33 new country records and discovery of the highly invasive Bactrocera carambolae (Diptera, Tephritidae). ZooKeys 876: 87-109. https://doi.org/10.3897/zookeys.876.38096
Figure 1 Distribution of Bactrocera dorsalis and B. carambolae in Asia, including the new records of B. carambolae in Bangladesh and range expansion recorded in San Jose et al. (2018b).
Figure 3 from: Leblanc L, Hossain MA, Doorenweerd C, Khan SA, Momen M, San Jose M, Rubinoff D (2019) Six years of fruit fly surveys in Bangladesh: a new species, 33 new country records and discovery of the highly invasive Bactrocera carambolae (Diptera, Tephritidae). ZooKeys 876: 87-109. https://doi.org/10.3897/zookeys.876.38096
Figure 3 Species accumulation curves for species collected in the rural and forest sites through the whole sampling period (2013–2018) (A) and for the individually surveyed protected forest areas (B). Estimates of species numbers based on the Chao 2 estimator, with the 95% confidence interval ranges). Data used to generate these curves and estimates include two species not yet definitely identified and not included on Table 1.
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