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Environmental monitoring

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Title: Environmental monitoring


1
Environmental monitoring
  • Dr. William Stafford
  • wstafford_at_uwc.ac.za

2
Human health..
Is tightly linked to the Health of the
environment
3
Pollution
  • Pollution is the introduction into the
    environment of substances or energy liable to
    cause hazards to human health, harm to living
    resources and ecological damage, or interference
    with legitimate uses of the environment.
  • The changes that are occurring in the environment
    caused by either natural processes or human
    activities, involve many large parameters and
    range from a slow increase in global temperature
    over years to the rapid accumulation of heavy
    metals and xenobiotics.
  • Some of the changes may require careful
    monitoring over long time periods. Some of the
    elements and compounds that accumulate in the
    environment are present in concentrations so low
    that they are close to the limits of detection.

4
Causes?
  • The first major human influence on the
    environment was perhaps agriculture, and later
    the industrial revolution
  • Many countries have a legacy of pollution and
    polluted sites.

5
Sources
  • The main groups of environmental pollutants which
    can contaminate land, water, and air are
  • Inorganic compounds such as metals
  • Organic compounds such as sewage, petrochemicals
  • Synthetic xenobiotic compounds such as phenol
  • Micro-organisms such as pathogens and genetically
    engineered organisms (GMOs).
  • The environmental pollutants can originate from
    contaminated sites of defunct industries such as
    gasworks, from existing domestic and industrial
    sources such as sewage and metals from industries
    like electroplating, from accidents, and illegal
    dumping.

6
What are dangerous levels?
  • The permissible levels and type of environmental
    contaminant are regulated by environmental
    legislation.
  • National laws are normally associated with a
    number of acts covering many types of pollutants,
    industries, and conditions (McEldowney and
    McEldowney, 1996).

7
Air pollution from coal oil
  • Use of coal by South Africa's industrial sector
    is the primary source of the country's air
    pollution- 90 of South Africa's electricity is
    generated from the combustion of coal, which
    contains approximately 1.2 sulfur and up to 45
    ash. Coal combustion can lead to particulate
    matter in the air, as well as contribute to acid
    rain. Despite harmful environmental effects,
    coal-fired power stations are not required to use
    coal scrubbers to remove sulfur, as use of
    clean-coal technology would significantly raise
    the cost of electricity for consumers.
  • Vehicular emissions also contribute to air
    pollution in urban centers. The effects of
    pollution caused by use of leaded gasoline use of
    older vehicles and lack of emissions control
    technology has been compounded by the historical
    absence of vehicle emissions legislation.
  • South Africa's four oil refineries are another
    major contributor to energy-related air
    pollution. The refineries, located in the
    northern suburbs of Cape Town and in the
    southeastern coastal city of Durban, emit high
    levels of sulfur dioxide and several other
    chemicals known to cause health problems.
    According to UNICEF, in 2000, respiratory
    infections from air pollution were the
    fourth-largest cause of death in children under
    five in South Africa (more than 6,000 deaths per
    year).

8
Air pollution-legal status
  • Though most townships have high levels of air
    pollution, South Africa has long lacked legally
    binding air pollution regulations on a national
    level, with only non-binding guidelines and no
    enforcement authority.
  • In order to address this problem, in April 2003,
    the Department of Environmental Affairs and
    Tourism proposed draft legislation for new
    ambient air quality standards for industries. The
    National Air Quality Management Bill, which
    replaces the outdated 1965 Atmospheric Pollution
    Prevention Act (APPA), aims to control air
    pollution, emission of greenhouse gases, and
    ozone-depleting pollutants by setting permissible
    concentrations of several polluting substances as
    well as total emissions levels.
  • Atmospheric emission licenses will be used to
    regulate firm-level emissions. This proposed
    legislation aims to make polluters accountable by
    applying the "polluter-pays" principle,

9
Discharge into seas
  • Pipelines Over 60 licensed pipelines discharge
    effluent along the South African coast one third
    discharge domestic sewage - about 66 million
    litres per day (66ML/d), half discharge
    industrial wastes and the remainder discharge
    mixed effluent. These pipelines operate via
    exemption permits' administered by the
    Department of Water Affairs, and both the
    effluent and environmental effects are monitored
    and controlled.
  • South Africa is especially vulnerable to oil
    spills due to the high volume of oil transported
    around the country's coasts by ships en route
    from the Middle East to Europe and the Americas.
    In June 2000, a tanker sank off of the coast of
    Cape Town, rupturing two fuel tanks. The spill
    threatened the South African penguin population
    and damaged tourist areas including the World
    Heritage site of Robben Island.
  • Lastly, small waste coal dumps and other
    hazardous waste from energy-related industries
    cause both pollution and safety problems. Waste
    coal may spontaneously ignite, while runoff from
    mining can contaminate groundwater.

10
The fate of pollutants
in the environment depends on the properties of
the compound and the environmental conditions.
11
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12
Monitoring
  • Monitoring must take into consideration the type
    or types of contaminants present (biological and
    chemical), their availability and the possibility
    of biomagnification and bioaccumulation.
  • The environmental monitoring must be able to
    detect with accuracy and consistency pollutants
    present at very low levels.
  • A range of chemical analyses is used to determine
    the concentrations and type of pollutants- HPLC,
    GC, NMR, MS ,IR etc..
  • This does not determine the real effect on the
    environment as the effects can be modified by
    availability, degradation, and transport of the
    pollutants. An alternative is to use a
    biological system to measure the pollutant..

13
Bioindicators, Biomarkers, Test organisms
  • The effects of pollutants on whole organisms
    representative of the environment, known as
    bioindicators.
  • The effects of pollutants on physiological,
    biochemical, and molecular characteristics of
    organisms in the environment, known as
    biomarkers.
  • The effect of the pollutant on test organisms in
    the laboratory.
  • Bioindicators and biomarkers have the advantage
    that they measure the action of the pollutants in
    the real and complex environment where there may
    be many and complex interactions at sublethal
    levels.

14
BIOINDICATORS
  • Bioindicator organisms are those that can be used
    to identify and quantify the effects of
    pollutants on the environment.
  • Lichens are a symbiotic relationship between an
    alga and fungus and are particularly sensitive to
    air pollutants and have been used widely used as
    bioindicators of air quality (Conti and
    Cecchetti, 2001)
  • Honey bees have been used as a bioindicator for
    the contamination of the atmosphere by heavy
    metals (cadmium, chromium, and lead).
  • The filter-feeding mussels are known to
    accumulate heavy metals, making them ideal for
    the monitoring of coastal waters eg.
    Mediterranean mussel Myttlus galloprovincialis
    (Regioli and Principato, 1995).
  • Frogs, fish eggs as a measure of water quality

15
BIOMARKERS
  • Biomarkers can be defined as quantitative
    measures of changes in the biological system in
    response to pollutant exposure.
  • Biomarkers can be placed into three groups
    biochemical, immunochemical, and genetic.

16
Biochemical biomarkers
  • Based on the ability of the pollutant to generate
    a response at the gene level, inducing or
    increasing specific enzymes involved with
    detoxification of contaminants.
  • The detoxification of xenobiotics often involves
    one of three detoxification strategies
  • cytochrome P450,
  • conjugation with glutathione and
  • chelation by proteins (Metallothioneines).

17
s
EROD, ethoxyresorufin-o-dethylase. AHH, aryl
hydrocarbon hydroxylase. GSH, glutathione.polyaro
matic hydrocarbon.
18
Immunochemical biomarkers
  • The specific reaction between antigens and
    antibodies can be used to determine the presence
    of xenobiotics in environmental samples.
  • Antibodies against PCBs (polychlorinated
    biphenyls), PCDDs (polychlorinated
    dibenzo-p-dioxins), and PCDFs (polychlorinated
    dibenzofurans) have been developed and used in an
    ELISA system to determine PCBs in samples (Hahn,
    2002).

19
Genetic biomarkers
  • Ames test
  • The Ames test was developed to test substances
    for their ability to produce mutations in
    bacteria. The test consists of the treatment of a
    Salmonella typhimurium histidine auxotroph
    (His-). The test compound is added to the
    Salmonella typhimurium His- in an extract of rat
    liver.
  • If the compound is a mutagen then mutations will
    cause revertants- colonies will form on a medium
    lacking histidine. The number of colonies will
    give a measure of the mutagenic potential.

20
Molecular biology biomarkers
  • Another development using genetic manipulation of
    biological material for the estimation of
    toxicity has been the generation of a transgenic
    strain of the nematode Caenorhabditis elegans .
  • The lacZ gene from E. coli is fused to the hsp16
    gene.
  • When the nematode is stressed the enzyme is
    induced in the worm. The enzyme can be detected
    by the addition of a substrate such as
    o-nitrophenyl-p-galactopyranoside (ONPG), which
    will produce a blue colour when cleaved by the
    enzyme.

21
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22
BIOSENSORS
  • A biosensor can be defined as a device that
    incorporates a biological sensing element in
    close proximity or integrated with a signal
    transducer in order to quantify a compound or
    conditions.
  • Thus the biosensor can give an online, continuous
    determination of the compound present. The
    biological material carrying out the reaction can
    be enzymes, antibodies, hormone receptors,
    proteins, organelles, lectins, DNA, and whole
    cells.
  • To function correctly the biological material has
    to be kept in close contact with the transducer
    and this is often achieved by immobilizing the
    biological material.

23
Biosensors for environmental monitoring
  • The oxygen demand of wastewaters and effluents
    has been determined traditionally by measuring
    the BOD5 value -5 days are required to obtain a
    result. With a BOD biosensor a fast, online
    determination is possible.
  • BOD biosensors can be either of the biofilm or
    respirometer type. In a biofilm BOD biosensor a
    microbial film is sandwiched between a porous
    membrane and the oxygen permeable membrane of a
    Clark oxygen electrode- A change in oxygen levels
    in the microbial culture will be proportional to
    the metabolizable content of the material to be
    measured.
  • In some cases the electrical signal from the
    oxygen electrode has been replaced by optical
    signals using the luminous bacterium Vibrio
    phosphoreum.

24
Pesticide biosensors
  • Biosensors that can measure pesticide
    concentrations have been developed using the
    enzyme acetylcholinesterase combined with choline
    oxidase.
  • Acetylcholinesterase converts acetylcholine to
    choline and choline oxidase converts the choline
    to betain and hydrogen peroxide.
  • The H2O2 can be measured with an oxygen
    electrode. Pesticides inhibit the action of
    acetylcholinesterase and therefore produce a
    reduction in peroxide formation.

25
Other biosensors
  • The oxidation of phenols to catechols and
    quinones by the enzyme tyrosinase requires
    oxygen. If the enzyme tryosinase is linked to an
    oxygen electrode levels down to about 50 parts
    per billion (ppb) could be detected.
  • Metals such as lead and cadmium can be detected
    by their inactivation of oxidases and
    dehydrogenases linked again to an oxygen
    electrode.
  • Thus biosensors can provide cheap, reliable, and
    accurate monitoring of the environment which will
    also give real-time analysis.

26
  • Biotechnology will influence the monitoring of
    the environment in the following areas.
  • Microbial diversity. The culture-independent
    study of microbial populations in situ.
  • Biomarkers using microorganisms with the
    fluorescent protein (gfp) gene inserted will be
    used to monitor pollution in situ.
  • Molecular biology techniques to follow the
    introduction of genetically modified
    micro-organisms released into the environment.
  • Biosensors will be able to determine the levels
    of contaminants in the environment and perhaps
    provide real-time online monitoring.
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