Bioindicator
14/07/2024 Views : 143
I K. Putra Juliantara
Bioindicators
Monitoring changes in aquatic environments can
be detected using bioindicators—organisms that serve as biological indicators
of environmental quality. Their presence can provide insights into the
resources within their habitat, reflecting past, present, and future ecological
conditions (Swasta, 2003; Kopciuch et al., 2004; Sudarso, 2009; Bellinger &
Sigee, 2010; Samways et al., 2010).
Certain guidelines for using ecological
bioindicators include preferring stenotopic species (those with narrow
environmental tolerance limits) over eurytopic species (those with wide
tolerance limits), using adult species rather than juveniles, and ensuring the
presence of definitive limiting factors before designating a species as a
bioindicator (Odum, 1993). When using a single species as a bioindicator, the
species should respond quickly to environmental changes, be stenotopic, have
well-known taxonomy, possess reliable identification characteristics, and have
a wide geographic distribution (Bellinger & Sigee, 2010).
Bioindicator species can be classified into
five categories: sentinel species, which are highly sensitive to pollutants and
often introduced to a habitat to provide early warnings of pollution; detector
species, which are native to a habitat and can indicate measurable
environmental changes (e.g., behavioral changes, mortality, morphological
changes); exploiter species, which thrive in polluted environments due to
reduced competition; accumulator species, which uptake and accumulate
measurable chemical compounds; and bioassay species, which are used in
laboratory tests to detect and quantify pollutants and rank pollutant toxicity
levels (Spellerberg, 2005; Samways et al., 2010).
Examples of bioindicator use include lichens
for air pollution monitoring (Wolterbeek et al., 2003; Das et al., 2011);
Hydra, plankton, macroinvertebrates, and macrozoobenthos for water quality
assessment (Handayani et al., 2001; Sekiranda et al., 2004; Suwondo et al.,
2004; Setiawan, 2009; Huarachi & Gonzales, 2012); algae for identifying
eutrophic status of water bodies (Dokulil, 2003; Bellinger & Sigee, 2010);
and birds as bioindicators of chemical pollution and climate change (Becker,
2003; Dzugan, 2012).
The most efficient organisms for use as
bioindicators in freshwater bodies are benthic macroinvertebrates
(macrozoobenthos). Their abundance from upstream to downstream, ease of
collection and identification, relatively long lifespan in various water conditions,
limited mobility, and habitat preference make them ideal indicators (Wardhana,
1999; Handayani et al., 2001; Suwondo et al., 2004; Tjokrokusumo, 2006;
Wijayanti, 2007).
Many researchers use macroinvertebrates to
indicate pollution in freshwater bodies (Handayani et al., 2001; Sekiranda et
al., 2004; Suwondo et al., 2004; Tjokrokusumo, 2006; Yimer & Mengistou,
2009). Insects, worms, snails, and crustaceans are particularly effective due
to their high natural abundance, limited distribution, the simplicity of
collection without special tools, short life cycles (≤1 year), and ease of
observation (Tjokrokusumo, 2006).
The benefits of using insects to monitor
aquatic environmental changes include their high abundance, significant
ecological roles, lack of ethical issues in sampling, suitability for habitat
monitoring, cost-effectiveness compared to other bioindicators due to passive
trap sampling methods, ease of identification, and predictable responses to
environmental changes (Shahabuddin, 2004; Gullan & Cranston, 2005).
Compared to physical and chemical parameters,
bioindicators offer several advantages in monitoring water quality: they
reflect overall water quality (integrating impacts of various environmental
factors over time), provide direct measures of ecological impact, and offer
reliable, quick, and inexpensive information to record conditions across
aquatic environments (Bellinger & Sigee, 2010). The benefits of
bioindicators include detecting environmental changes, serving as metrics or models
for characterizing ecosystem quality, monitoring the negative impacts of
industrial activities on the environment, and contributing to sustainable
development by ensuring minimal industrial impact on the environment (Sauvolic
et al., 2007).
References
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Bellinger, E.G.,
and D.C. Sigee. 2010. Fresh
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