Idham Sakti’s scientific contributions

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Figure 1. Biomass of termites in each of the different types of land use in ESMS. The value shown is the average value (x) with standard errors. 
Table 1 . Descriptions of each type of habitat of study sites.
Table 2 . Relative abundance of species of termites in five different types of land use in ESMS.
Figure 3. RDA ordination between levels of habitat disturbance (TG), types of land use (PL) with species evenness (E), biomass (BM), relative abundance (KR) and species diversity (H) and species richness (S) termites in five types of usage different land in ESMS. Description: The long arrows indicate the strength of correlation between parameters. Parameters with the same direction arrows mean positive correlation, whereas in the opposite direction of arrows means negative correlation and the direction perpendicular arrows between the parameter mean not correlated. The smaller the angle formed between two parameters means that the higher correlation (Braak & Smilauer 2002). 
Termites community as environmental bioindicators in highlands: a case study in eastern slopes of Mount Slamet, Central Java
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October 2011

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215 Reads

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15 Citations

Biodiversitas Journal of Biological Diversity

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Idham Sakti

Pribadi T,Raffiudin R,HarahapIS (2011)Termites community as environmental bioindicators in highlands: a case study in eastern slopes of Mount Slamet, Central Java. Biodiversitas 12: 235-240. Termites ecological behaviour is much affected by land use change and disturbance level. Their variation in diversity can be used as bioindicator of environmental quality. However, termite community response to land use changes and habitat disturbance in highland ecosystems remains poorly understood. This study was conducted to investigate the response of termite community to land use intensification and to explore their role as environmental bioindicator in Mount Slamet. A standard survey protocol was used to collect termites in five land use typesof various disturbance levels,i.e. protected forest, recreation forest, production forest,agroforestry, and urban area. It was found two termite families i.e. Rhinotermitidae and Termitidae with seven species, i.e Schedorhinotermes javanicus, Procapritermes sp, Pericapritermes semarangi, Macrotermes gilvus, Microtermes insperatus, Nasutitermes javanicus, and N. matanganensis. Termite species' richness and evenness, Shannon-Wiener index, relative abundance, and biomass of termite were declined along with the land use types and disturbance level from protected forest to urban area. Habitat disturbance was the main declining factor of termite diversity. Termite composition changed along with the land use disturbance level. Soil feeding termites were sensitive to the disturbance – they were not found in urban area. Hence, their presence or absence can be used as environmental bioindicator to detect habitat disturbance.

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... This is indicating that there was a decrease in termite species in disturbed habitats compared to undisturbed primary ones. Similar findings were reported by Pribadi et al. (2011), who found that the conversion of natural forest land into forests developed for tourism, production forests, agroforestry, and settlements reduced termite species richness. Gillison et al. (2003) found that the number of termite species was around 34 in primary forests, falling to only one in monoculture-type gardens. ...

Reference:

Response of termite communities to natural forest conversion
Termites community as environmental bioindicators in highlands: a case study in eastern slopes of Mount Slamet, Central Java

Biodiversitas Journal of Biological Diversity