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Speciation-Driven Toxicity and Remediation of Mercury: Mechanistic Insights and Policy Implications
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Mercury is a worldwide spread pollutant whose effects are more related
to chemical speciation rather than concentration. Changes between
elemental mercury (Hg
0
), inorganic mercury (Hg
2+
) and organomercury species, including methylmercury
(CH
3
Hg
+
), Dimethyl mercury (CH
3
)
2
Hg
+
) and
ethylmercury (EtHg), determine the mobility, bioavailability, and
toxicity of mercury in soil, water, sludge, and air. These dynamic
changes are caused by factors such as pH, redox potential, organic
matter and microbial activity. Elemental mercury (Hg
0
) causes inhalation toxicity, considered relatively
less toxic but can be oxidized to inorganic mercury (Hg
2+
), which has higher affinity for sulfhydryl groups
in protein and enzymes, leading to cellular dysfunction and kidney
damage. The most hazardous form is organic mercury, particularly
methylmercury which easily crosses biological membranes, including the
blood brain and placental barrier. Once inside the body, methyl mercury
bind to thiol containing molecules contains molecules, cause sever
disproportionate neurodevelopmental damage by food webs. Dimethyl
mercury is even more toxic, penetrate skin and tissue rapidly, resulting
in acute poisoning at extremely low exposure level. Mercury speciation
has a significant impact on plant uptake, cross-species toxicity and
remediation. The risks can be alleviated by phytoremediation, microbial
transformation, sludge treatment, and thermal or chemical stabilization,
and mitigated or inadvertently increased by specification-conscientious
planning. Detection is improved by the development of analytical
methods, such as HPLC-ICP-MS, CVAFS, X-ray absorption spectroscopy, and
biosensors, but in situ and real time monitoring is still problematic.
Speciation metrics should replace bulk mercury levels, which should be
incorporated in policy systems, including the Minamata Convention. In
the future, the integration of mechanistic models and field data, the
creation of AI-based speciation prediction, and the implementation of
low-cost biosensors are important, especially in
poorly-infrastructure-equipped regions. Sustainable mercury management
should be based not only on reduction of the total amount but also on
conversion of mercury into less toxic and mobile states.
Title: Speciation-Driven Toxicity and Remediation of Mercury: Mechanistic Insights and Policy Implications
Description:
Mercury is a worldwide spread pollutant whose effects are more related
to chemical speciation rather than concentration.
Changes between
elemental mercury (Hg
0
), inorganic mercury (Hg
2+
) and organomercury species, including methylmercury
(CH
3
Hg
+
), Dimethyl mercury (CH
3
)
2
Hg
+
) and
ethylmercury (EtHg), determine the mobility, bioavailability, and
toxicity of mercury in soil, water, sludge, and air.
These dynamic
changes are caused by factors such as pH, redox potential, organic
matter and microbial activity.
Elemental mercury (Hg
0
) causes inhalation toxicity, considered relatively
less toxic but can be oxidized to inorganic mercury (Hg
2+
), which has higher affinity for sulfhydryl groups
in protein and enzymes, leading to cellular dysfunction and kidney
damage.
The most hazardous form is organic mercury, particularly
methylmercury which easily crosses biological membranes, including the
blood brain and placental barrier.
Once inside the body, methyl mercury
bind to thiol containing molecules contains molecules, cause sever
disproportionate neurodevelopmental damage by food webs.
Dimethyl
mercury is even more toxic, penetrate skin and tissue rapidly, resulting
in acute poisoning at extremely low exposure level.
Mercury speciation
has a significant impact on plant uptake, cross-species toxicity and
remediation.
The risks can be alleviated by phytoremediation, microbial
transformation, sludge treatment, and thermal or chemical stabilization,
and mitigated or inadvertently increased by specification-conscientious
planning.
Detection is improved by the development of analytical
methods, such as HPLC-ICP-MS, CVAFS, X-ray absorption spectroscopy, and
biosensors, but in situ and real time monitoring is still problematic.
Speciation metrics should replace bulk mercury levels, which should be
incorporated in policy systems, including the Minamata Convention.
In
the future, the integration of mechanistic models and field data, the
creation of AI-based speciation prediction, and the implementation of
low-cost biosensors are important, especially in
poorly-infrastructure-equipped regions.
Sustainable mercury management
should be based not only on reduction of the total amount but also on
conversion of mercury into less toxic and mobile states.
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