TABLE II. Abundance and distribution of sandflies captured from September 2013 to January 2015 in Brasiléia, Acre, Brazil.
| Genera | Species | Forest environment | TF | Peridomicile environment | TP | OP % | |||||
| A1R4 | A3R13 | A4R18 | A5R59 | A2R5 | A6R69 | A7R74 | |||||
| Nyssomyia | Ny. shawi | 823 | 89 | 34 | 254 | 1,200 | 26.83 | ||||
| Ny. whitmani | 143 | 28 | 8 | 31 | 210 | 0.46 | |||||
| Ny. antunesi | 72 | 74 | 19 | 28 | 193 | 6 | 6 | 4.45 | |||
| Ny. umbratilis | 8 | 68 | 42 | 3 | 121 | 2.57 | |||||
| Ny. yuilli yuilli | 8 | 21 | 9 | 2 | 40 | 0.89 | |||||
| Nyssomyia sp. | 164 | 28 | 32 | 27 | 251 | 14 | 14 | 5.92 | |||
| Lutzomyia | Lu. sherlocki | 22 | 36 | 38 | 5 | 101 | 2.26 | ||||
| Lu. flabellata | 2 | 2 | 4 | 0.08 | |||||||
| Lutzomyia sp. | 11 | 34 | 7 | 0 | 52 | 1.16 | |||||
| Psychodopygus | Ps. davisi | 276 | 115 | 32 | 119 | 542 | 12.12 | ||||
| Ps. carrerai carrerai | 152 | 8 | 3 | 130 | 293 | 8.47 | |||||
| Ps. llanosmartinsi | 4 | 163 | 167 | 6.55 | |||||||
| Ps. amazonensis | 27 | 12 | 13 | 46 | 98 | 2.19 | |||||
| Ps. hirsutus hirsutus | 32 | 13 | 2 | 39 | 86 | 1.92 | |||||
| Ps. paraensis | 6 | 10 | 10 | 25 | 51 | 1.14 | |||||
| Ps. geniculatus | 6 | 2 | 23 | 31 | 0.69 | ||||||
| Ps. lainsoni | 21 | 6 | 27 | 0.60 | |||||||
| Ps. chagasi | 11 | 11 | 0.24 | ||||||||
| Ps. claustrei | 1 | 2 | 3 | 1 | 1 | 0.08 | |||||
| Ps. bispinosus | 1 | 1 | 0.02 | ||||||||
| Ps. complexus | 1 | 1 | 0.02 | ||||||||
| Ps. dorlinsis | 1 | 1 | 0.02 | ||||||||
| Psychodopygus sp. | 29 | 8 | 5 | 12 | 54 | 1.21 | |||||
| Trichopygomyia | Ty. dasypodogeton | 1 | 2 | 3 | 6 | 0.13 | |||||
| Trichopygomyia sp. | 3 | 1 | 4 | 0.08 | |||||||
| Trichophoromyia | Th. octavioi | 47 | 18 | 22 | 118 | 205 | 4.58 | ||||
| Th. auraensis | 47 | 3 | 8 | 54 | 112 | 1 | 4 | 5 | 2.62 | ||
| Th. ubiquitalis | 5 | 2 | 7 | 0.15 | |||||||
| Th. clitella | 1 | 1 | 0.02 | ||||||||
| Trichophoromyia sp. | 25 | 7 | 19 | 139 | 190 | 4.25 | |||||
| Evandromyia | Ev. saulensis | 4 | 13 | 40 | 4 | 61 | 4 | 5 | 9 | 1.56 | |
| Ev. bacula | 4 | 2 | 2 | 8 | 1 | 1 | 0.08 | ||||
| Ev. infraspinosa | 1 | 3 | 4 | 1 | 1 | 0.11 | |||||
| Ev. termitophila | 1 | 3 | 4 | 1 | 1 | 0.11 | |||||
| Ev. monstruosa | 2 | 1 | 3 | 0.06 | |||||||
| Ev. walkeri | 2 | 2 | 0.04 | ||||||||
| Ev. cortelezzii | 1 | 1 | 0.02 | ||||||||
| Ev. williamsi | 2 | 2 | 0.04 | ||||||||
| Evandromyia sp. | 1 | 7 | 9 | 1 | 18 | 8 | 4 | 12 | 0.67 | ||
| Pintomyia | Pi. serrana | 29 | 10 | 11 | 11 | 61 | 1 | 1 | 1.39 | ||
| Pi. nevesi | 5 | 3 | 4 | 2 | 14 | 1 | 1 | 2 | 0.35 | ||
| Pintomyia sp. | 2 | 2 | 1 | 1 | 0.06 | ||||||
| Bichromomyia | Bi. flaviscutellata | 1 | 1 | 20 | 22 | 0.51 | |||||
| Bi. olmeca nociva | 7 | 1 | 8 | 1 | 1 | 0.20 | |||||
| Bi. olmeca bicolor | 2 | 2 | 0.04 | ||||||||
| Bichromomyia sp. | 2 | 1 | 3 | 0.06 | |||||||
| Psathyromyia | Pa. aragaoi | 9 | 5 | 3 | 1 | 18 | 1 | 1 | 2 | 0.44 | |
| Pa. dendrophyla | 7 | 2 | 3 | 12 | 1 | 1 | 0.29 | ||||
| Pa. bigeniculata | 5 | 5 | 0.11 | ||||||||
| Pa. lutziana | 3 | 1 | 4 | 1 | 1 | 0.11 | |||||
| Pa. abonnenci | 2 | 1 | 3 | 0.06 | |||||||
| Pa. campbelli | 2 | 1 | 3 | 0.06 | |||||||
| Pa. scaffi | 1 | 1 | 1 | 3 | 0.06 | ||||||
| Pa. abunaensis | 1 | 1 | 0.02 | ||||||||
| Pa. punctigeniculata | 1 | 1 | 0.02 | ||||||||
| Psathyromyia sp. | 4 | 7 | 3 | 5 | 19 | 1 | 1 | 0.44 | |||
| Viannamyia | Vi. furcata | 3 | 7 | 2 | 12 | 0.26 | |||||
| Pressatia | Pr. choti | 3 | 3 | 0.06 | |||||||
| Pr. duncanae | 2 | 1 | 3 | 0.06 | |||||||
| Pr. calcarata | 1 | 1 | 0.02 | ||||||||
| Pr. triacantha | 1 | 1 | 0.02 | ||||||||
| Pressatia sp. | 7 | 1 | 8 | 2 | 2 | 0.22 | |||||
| Brumptomyia | Br. galindoi | 1 | 1 | 0.02 | |||||||
| Br. mangabeirai | 1 | 1 | 0.02 | ||||||||
| Br. avellari | 8 | 8 | 0.17 | ||||||||
| Brumptomyia sp. | 5 | 5 | 0.11 | ||||||||
| Sciopemyia | Sc. sordellii | 2 | 3 | 5 | 0.11 | ||||||
| Sc. servulolimai | 1 | 2 | 3 | 0.06 | |||||||
| Sciopemyia sp. | 2 | 1 | 3 | 1 | 1 | 0.08 | |||||
| Migonemyia | Mg. migonei | 1 | 1 | 2 | 0.04 | ||||||
| Migonemyia sp. | 1 | 1 | 0.02 | ||||||||
| Micropygomyia | Mi. longipennis | 3 | 3 | 0.06 | |||||||
| Mi. trinidadensis | 1 | 1 | 0.02 | ||||||||
| Mi. micropyga | 1 | 1 | 0.02 | ||||||||
| Micropygomyia sp. | 1 | 1 | 0.02 | ||||||||
| Total | 2,022 | 664 | 425 | 1,278 | 4,389a | 62 | 13 | 9 | 84a | 100 | |
a: comparison for the abundance of sandflies in the forest and peridomicile environments. A: area; OP %: overall percentage; R: Ramal (defined by the distance in kilometres along the Trans Pacific Federal Highway BR 317); TF: total forest environment; TP: total peridomicile environment. Kruskal-Wallis test. H = 36.6, degrees of freedom (df) = 14, p = 0.001.