Abstract:
Ants are very common in the regions of wet and dry zone but little is known about the
similarities and differences of the ant communities observed in the lands, which are under
different levels of disturbance. A survey in the dry zone was conducted from 3rd to 5111 of
February, 2008, in three types of habitats, a forest (F), Anuradhapura Sanctuary (N 08°
201, E 080° 231 ), a teak cultivation (T ) in M a tale Handiya (N 08° 211, E 080° 261) and
an uncultivated land (U), surrounding area of Nuwara weva (N 08° 211, E 080° 251), in
Anuradhapura by soil and litter sifting, honey baiting, pitfall trapping and manual collection
along five, 100 m transects laid in each type of habitat. Soil and litter sifting were carried out
at 2.5 m intervals along each transect. Honey baits were placed at 2.5 m distance along each
transect and collected into bottles filled with 70% ethanol after an hour. Manual collection
was carried out at five minute intervals along each transect. Honey baited pitfall traps (20)
were placed randomly to cover the whole sampling area and the traps were collected after
five hours. All ants were preserved in the field in 70% ethanol. Worker ants were sorted and
identified to the furthest possible taxonomic levels in the laboratory. Air (F: 29 °C- 31 °C;
T: 29 °C- 30 °C; U: 30 °C- 31 °C) and soil temperatures (F: 28 °C- 31 °C; T: 28 °C- 30
°C; U: 28 °C- 29 °C) and soil moisture content (F: 4% - 8.3%; T: 1% - 3.3%; U: 0.9% -
4.8%) of each habitat were also measured. Dry weather persisted throughout the sampling
period.
Worker ants belonging to seven subfamilies, Aenictinae, Dolichoderinae, Formicinae,
Leptanillinae, Myrmicinae, Ponerinae and Pseudomyrmecinae, and 49 species and
morphospecies of ants were recorded during this survey. Crematogaster sp. 1 (F-1 %, T-
12%, U-1%), Crematogaster sp. 3 (F- 4%, T- 42%, U- 21%), Lepisiota sp. 2 (F- 0.04%,
T- 0.1 %, U- 0.1 %), Meranoplus bicolor (F- 8%, T-10%, U-10%), Monomorium destructor
(F- 0.2%, T- 0.5%, U- 0.7%), Myrmicaria brunnea (F- 0.04%, T- 4%, U-12%), Oecophylla
smaragdina (F- 0.2%, T- 0.4%, U- 0.4%), Pachycondyla sp. 1 (F-0.1%, T- 1%, U- 0.3%),
Paratrechina longicornis (F- 2%, T- 0.1%, U-2%), Paratrechina sp. 2 (F-0.1, T-0.5%, U-
1 %), Pheidole sp. 8 (F-62%, T- 0.2%, U- 13%), Solenopsis geminata (F- 6%, T- 0.2%,
U-1%), Tetramorium sp. 3 (F- 1%, T- 18%, U- 6%), Tetramorium sp. 5 (F- 1%, T- 2%,
U- 0.1 %) and Tetramorium sp. 7 (F- 1%, T- 6%, U-9%) were common to the three types of
habitats (Similarity Co-efficient= 15.8%). Camponotus sp. 2 (0.3%), Crematogaster sp. 5
(0.02%), Crematogaster sp. 6 (0.1 %), Dolichoderus sp. 1 (0.1 %), Lepisiota sp. 3 (0.02%),
Lepisiota sp. 4 (0.02%), Leptanilla sp. 2 (0.02%), Pheidole sp. 5 (0.1 %), Polyrhachis sp. 1
(0.02%), Protanilla sp. 1 (0.02%), Solenopsis sp. 1 (0.02%) Tetraponera rufonigra (0.1 %)
and Tetramorium sp. 10 (0.1%) were restricted to the forest (H1= 0.7 1) while Anochetus sp.
3 (0.03%), Pheidole sp. 11 (0.1 %), Tapinoma sp. 3 (0.4%) and Tetramorium sp. 4 (0.2%) were observed only in the teak cultivation (Hi= 0.81). Anochetus sp. 2 (0.1 %), Aenictus sp.
1 (0.03%), Camponotus sp. 1 (0.1 %) and Harpegnathos sp. 1 (0.03%) were restricted to the
surrounding area ofNuwara weva (Hi = 1). Presence of Leptanilla sp. 2 and Protanilla sp.
1 in a dry zone forest was observed for the first time and, the observation of Aenictus sp.
1 and Harpegnathos sp. 1 in a highly disturbed area was also an important record of this
survey.