Water quality can be described in terms of physical, chemical and biological characteristics. Bioindicator organisms are those that can be used to identify and quantify the effects of pollutants on the environment. The presence, condition and numbers of certain species of fishes, insects, algae and plants can provide accurate information about the health of a specific river, stream, lake, wetland or estuary. Biological methods are inexpensive and data can be obtained by periodic (e.g.monthly or yearly) visits to the sites. The data is unambiguously related to pollutional impact and scientifically credible. Since pollution is a threat to the biological components of the ecosystem, the assessment of biological variables is the most appropriate. Biological monitoring can indicate past and ongoing pollution events. The reactions of individual organisms, such as behavioural, physiological or morphological changes, can also be studied as responses to pollutant stress. Certain contaminants, particularly metals and organic compounds, may be accumulated in the tissues of organisms. The chemical analysis of the appropriate biological tissues can be used to show that the organism has been exposed to contaminants. The biological approaches can be cheaper than chemical methods in terms of manpower and equipment.
Pros and cons of biomonitoring
Monitoring of biological variables can be cheaper, precise, rapid, easy to perform, require less sophisticated instruments and reflect the integrated expression of pollution load. Biological indicators could identify the possible environmental problems before the health of the aquatic system is seriously altered. Since there is no instrument devised by man to measure toxicity of chemical pollutants, a living organism is a most ‘sensitive sensor’ to evaluate the relative toxicity of pollutants. However the biological approach suffers from the problems posed by the extreme complexity of organisms and ecosystems, endless form of interactions and the non-specific nature of population and community responses.Biological monitoring is an important tool for water quality management.
Biological monitoring measures the cumulative effect of all the pollutants and overall health of the aquatic ecosystems. Biological can integrate all environmental variables over long periods of time. Generally biological effects occur at concentrations below the analytical capabilities. Toxicity is a property that can be measured only by an organism’s response(Mount,1980).Definition of biological monitoring
Biomonitoring is the introduction of biological variables for the assessment of the structural and functional aspects of ecosystems. Biological variables are most sensitive to stress which can be easily measured and quantified.A bioindicator is an organism (or community of organisms) that contains information on the quality of the environment. Organisms which are used as indicators of water quality are called sentinel organisms or biological litmus paper or pollution thermometer. The indicator organisms are either plants or animals which show clear symptoms of the possible presence of pollutants. e.g. macroinvertebrates in general( caddis fly larva, may fly larva, stone fly larva etc.), bivalve molluscs (clams, mussels, oysters) and microcrustaceans.Bioindicators
Indicator organisms may be true indicators or scale indicators.
In true indicators, the degree of pollution- induced damage is related to morphological and/or physical symptoms in one single species.
In scale indicators, the degree of pollutional stress is related to the presence or absence of a sensitive species in a community.
Active bioindication is meant when bioindicators bred in laboratories are exposed in a standardized form in the field for a defined period of time. At the end of the exposure, the reactions provoked in the organisms are analysed.
Passive bioindication organisms already occurring naturally in the ecosystem are examined for their actions.
Accumulation indicators / monitors are organisms that accumulate one or more elements or compounds from their environment. e.g. fresh water mussels.
Effect or impact indicators / monitors are organisms that demonstrate specific or unspecific effects in response to exposure to a certain element or compound or a number of substances.
2. Widely distributed in many habitats.
3. Taxonomically stable and well known.
4. Low genetic and biological variability
5. Well known natural history with abundant ecological and physiological data .
6. Ready and easy to be sampled, surveyed and manipulated.
7. Economically/ biologically important species.
8. Easily held or cultured in the laboratory for experimental ecotoxicological procedures.
Biomarkers reflect pollution – induced effects at several levels of biological organization. Biomarkers are measurable biological parameters at the genetic, enzymatic, physiological and morphological levels which indicate qualitative and quantitative aspects of environmental pollution.
Biomarkers can be divided in to markers of exposure and toxic effects.
In true indicators, the degree of pollution- induced damage is related to morphological and/or physical symptoms in one single species.
In scale indicators, the degree of pollutional stress is related to the presence or absence of a sensitive species in a community.
Active bioindication is meant when bioindicators bred in laboratories are exposed in a standardized form in the field for a defined period of time. At the end of the exposure, the reactions provoked in the organisms are analysed.
Passive bioindication organisms already occurring naturally in the ecosystem are examined for their actions.
Biomonitors
A biomonitor is an organism (or community of organisms) that contains information on the quantitative aspects of the quality of the environment.Accumulation indicators / monitors are organisms that accumulate one or more elements or compounds from their environment. e.g. fresh water mussels.
Effect or impact indicators / monitors are organisms that demonstrate specific or unspecific effects in response to exposure to a certain element or compound or a number of substances.
Criteria for a bioindicator species
1. Highly susceptible to pollutant stress.2. Widely distributed in many habitats.
3. Taxonomically stable and well known.
4. Low genetic and biological variability
5. Well known natural history with abundant ecological and physiological data .
6. Ready and easy to be sampled, surveyed and manipulated.
7. Economically/ biologically important species.
8. Easily held or cultured in the laboratory for experimental ecotoxicological procedures.
Criteria for
selecting a bioindicator species
1.
Relevance – causal
relationship to ecologically significant endpoints
2. Sensitivity –
dose responsiveness to specific
stressors.
3. Specificity –
responds to specific stressors.
4.
Broad applicability – over temporal and spatial scales.
5. Representatives
– role as surrogate for other
responses.
6.
Variability – low
variability relative to noise in a ecosystem.
7. Cost – reasonable for available resources and scope of study.
Benthic macroinvertebrates as good bioindicators
Benthic macroinvertebrates are small animals that live on the bottom of a pond, lake, stream or river for at least part of their lives. E.g. aquatic insects – may flies, damsel flies, dragon flies, stone flies, caddies flies, Dobson flies, true flies and beetles.EPT index is a measure of total number 3 aquatic insect orders such as Ephemeroptera, Placoptera and Trichoptera.
Properties of benthic macroinvertebrates
1. Live in water for all or most of their life with
limited mobility.
2. Stay in areas suitable for their survival.
3. Easy to identify, sample or survey
4. Differ in the range of tolerance to amount and types
of pollution.
5. Are integrators of environmental conditions.
Biomarkers
Biomarkers can be divided in to markers of exposure and toxic effects.
Biomarkers of exposure represent responses such as induction or inhibition of
specific enzymes involved in biotransformation and detoxification as a result
of chemical exposure. These biomarkers show early response at the molecular or
cellular level and specific in their reaction.
Biomarkers of toxic effects reflect pathological endpoints and are determined at
each level of biological organization. These biomarkers serve as integrative
markers of complex toxicities and ecologically relevant indicating
environmental health at higher levels of biological organization( individual,
population, and community level).
Molecular level biomarkers – The activity of cytochrome p 450-dependent
monooxygenase system can be analysed as a biomarker of organic chemical
pollutant exposure e.g. PCBs, PAHs, dioxins, furans.
Subcellular level biomarkers – the integrity of lysosomal system is analysed to find
out the influence of PAHs, heavy metals and organochlorines.
Cellular level biomarkers – the accumulation of neutral lipids in fish
hepatocytes is analysed for toxicity induced liver fat metabolism.
Individual level biomarkers – the macrophage aggregate activity is analysed as a
marker of pollution induced changes of cellular immune responses.
A biosensor is a measuring device that produces a signal in
proportion to the concentration of a xenobiotic substance in a biological
system. E.g enzyme, antibody, membrane, organelle, cell, or tissue.
Biological indicators of water quality
Saprobic index(S.I) – a measure of level of organic pollution(Pantle and Buck 1955).
Nyggard’s algal index (Nyggard 1949) and Palmer’s algal index(Palmer 1969) – pollution index using algal species.
Biological index of pollution – BIP
Shannon – Weiner index (Shannon – Weiner 1949)
Biological index of pollution – BIP
Shannon – Weiner index (Shannon – Weiner 1949)
Potential uses of bioindicators
1. Indicate pollutant exposure
2. Help identify mechanisms of toxicity
3. Provide early warning of impending ecological damage
4. Reveal early indication of environmental recovery or remediation.
5. Important in linking cause/ effect relationship.
6. Can be included in ecological risk assessment.
3. Provide early warning of impending ecological damage
4. Reveal early indication of environmental recovery or remediation.
5. Important in linking cause/ effect relationship.
6. Can be included in ecological risk assessment.
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