Abstract
A soil arthropod community was studied in a dry evergreen forest over a 3-year period from May 1998 to April 2001. Population abundance, species composition, and community structure were investigated over the 3-year study period. The soil arthropods consisted of Acari (75.38%), Collembola (16.11%), and others (8.51%), and their abundances showed a clear difference between the rainy and dry seasons. Population abundance of Collembola and Acari were low during drought conditions. The humidity was the most important factor determining distribution, abundance, and survival of soil Collembola in this tropical forest. High predation and low accumulation of organic matter caused low population abundance of Collembola in the tropical habitat. The collembolan community was dominated by a few dominant species over the study period. The pattern of seasonal changes in numbers of Collembola was similar over the 3-year study period. The species composition of the collembolan community was constant and persistent throughout a 3-year study period. Thus, the collembolan community showed constancy in its species composition with seasonal variability over the 3-year study period.
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Acknowledgements
We would like to thank the students of the Forest Entomology Laboratory, Faculty of Forestry, Kasetsart University for their assistance in the sampling of soil arthropods and to Drs. M. Hasegawa and Barclay Hugh (Pacific Forestry Center, Canada) for their helpful comments on the manuscript.
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Appendix
Appendix
The abundance of collembolan species; density is expressed as numbers per m2. The mean densities are calculated over the 3 years
Species | First year Mean±S.E. | Second year Mean±S.E. | Third year Mean±S.E. | Mean | Relative abundance (%) |
|---|---|---|---|---|---|
1. Isotomiella minor | 1,858±479 | 1,293±177 | 1,193±230 | 1,448±295 | 26.45 |
2. Sminthurides spp. | 849±271 | 702±221 | 951±314 | 834±267 | 15.23 |
3. Proisotoma sp. | 884±324 | 282±79 | 1,189±325 | 785±243 | 14.34 |
4. Pseudosinella spp. | 524±101 | 222±50 | 511±137 | 419±96 | 7.66 |
5. Megalothorax sp. | 153±80 | 451±145 | 638±184 | 414±136 | 7.56 |
6. Lepidocyrtus spp. | 333±65 | 293±57 | 193±32 | 273±51 | 4.99 |
7. Folsomides parvulus | 256±70 | 227±84 | 291±103 | 258±86 | 4.71 |
8. Cryptopygus sp. | 287±133 | 49±14 | 49±19 | 128±55 | 2.34 |
9. Sinella spp. | 211±81 | 129±48 | 38±14 | 126±48 | 2.30 |
10. Pseudachorutes sp. | 107±31 | 140±81 | 102±22 | 116±45 | 2.12 |
11. Brachystomella sp. | 31±19 | 147±59 | 158±48 | 112±42 | 2.04 |
12. Tullbergia sp. | 64±26 | 42±18 | 191±60 | 99±35 | 1.81 |
13. Hypogastrura sp. | 42±24 | 118±52 | 84±34 | 82±37 | 1.49 |
14. Entomobrya sp. | 89±31 | 140±87 | 7±3 | 79±40 | 1.43 |
15. Dicyrtoma sp. | 76±38 | 47±16 | 47±15 | 56±23 | 1.03 |
16. Anurida sp. | 0±0 | 84±21 | 76±36 | 53±19 | 0.97 |
17. Onychiurus sp. | 42±15 | 71±25 | 29±8 | 47±16 | 0.87 |
18. Friesea sp. | 9±7 | 60±21 | 53±22 | 41±17 | 0.74 |
19. Sminthurinus spp. | 0±0 | 13±8 | 104±33 | 39±14 | 0.72 |
20. Neanura sp. | 62±28 | 0±0 | 2±2 | 22±10 | 0.39 |
21. Sminthurus sp. | 29±11 | 9±6 | 9±7 | 16±6 | 0.28 |
22. Callyntrura sp. | 11±4 | 7±2 | 13±8 | 10±5 | 0.19 |
23. Arrhopalites sp. | 7±4 | 2±2 | 11±9 | 7±5 | 0.12 |
24. Salina sp. | 0±0 | 18±8 | 2±2 | 7±3 | 0.12 |
25. Odontella sp. | 2±2 | 0±0 | 5±3 | 2±2 | 0.04 |
26. Microparonella sp. | 2±2 | 0±0 | 0±0 | 1±1 | 0.01 |
27. Anurophorus sp. | 0±0 | 2±2 | 0±0 | 1±1 | 0.01 |
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| Total | 5,475 | 100 |
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Wiwatwitaya, D., Takeda, H. Seasonal changes in soil arthropod abundance in the dry evergreen forest of north-east Thailand, with special reference to collembolan communities. Ecol Res 20, 59–70 (2005). https://doi.org/10.1007/s11284-004-0013-x
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DOI: https://doi.org/10.1007/s11284-004-0013-x