Purifying Arsenic Polluted Water with Engineered Yeast Matthew Alpert Shailendra Singh Shen-Long...
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Purifying Arsenic Purifying Arsenic Polluted Water with Polluted Water with Engineered Yeast Engineered Yeast Matthew Alpert Matthew Alpert Shailendra Singh Shailendra Singh Shen-Long Tsai Shen-Long Tsai Dr. Ashok Mulchandani Dr. Ashok Mulchandani Dr. Wilfred Chen Dr. Wilfred Chen
Purifying Arsenic Polluted Water with Engineered Yeast Matthew Alpert Shailendra Singh Shen-Long Tsai Dr. Ashok Mulchandani Dr. Wilfred Chen
Purifying Arsenic Polluted Water with Engineered Yeast Matthew
Alpert Shailendra Singh Shen-Long Tsai Dr. Ashok Mulchandani Dr.
Wilfred Chen
Slide 2
Arsenic Toxicity Common as As(V) and As(III) Common as As(V)
and As(III)
Slide 3
Arsenic Toxicity Common as As(V) and As(III) Common as As(V)
and As(III) As(V) can be substituted for phosphate in the citric
acid cycle, interfering with: As(V) can be substituted for
phosphate in the citric acid cycle, interfering with:
Slide 4
Arsenic Toxicity Common as As(V) and As(III) Common as As(V)
and As(III) As(V) can be substituted for phosphate in the citric
acid cycle, interfering with: As(V) can be substituted for
phosphate in the citric acid cycle, interfering with: The reduction
of NAD + ATP synthesis Mitochondrial respiration
Slide 5
Arsenic Toxicity As(III) acts as an endocrine disruptor by
binding to hormone receptors As(III) acts as an endocrine disruptor
by binding to hormone receptors
Slide 6
Arsenic Toxicity As(III) acts as an endocrine disruptor by
binding to hormone receptors As(III) acts as an endocrine disruptor
by binding to hormone receptors Disrupting the endocrine system has
a serious impact on: Disrupting the endocrine system has a serious
impact on:
Slide 7
Arsenic Toxicity As(III) acts as an endocrine disruptor by
binding to hormone receptors As(III) acts as an endocrine disruptor
by binding to hormone receptors Disrupting the endocrine system has
a serious impact on: Disrupting the endocrine system has a serious
impact on: Metabolism Tissue function Growth and development
Arsenic Pollution Herbicide Herbicide Insecticide Insecticide
Pesticide Pesticide Brain damage has been found in those working
the sprayers
Slide 13
Arsenic Pollution Herbicide Herbicide Insecticide Insecticide
Pesticide Pesticide Brain damage has been found in those working
the sprayers Kingicide Kingicide
Slide 14
Arsenic Pollution Herbicide Herbicide Insecticide Insecticide
Pesticide Pesticide Brain damage has been found in those working
the sprayers Kingicide Kingicide King George III of Great Britain
Francesco I de' Medici, Grand Duke of Tuscany
Arsenic Pollution Chromated copper arsenate (CCA) (Tanalith
brand) Chromated copper arsenate (CCA) (Tanalith brand) Protects
wood from various forms of decay The arsenic acts as an
insecticide
Slide 17
Arsenic Pollution Chromated copper arsenate (CCA) (Tanalith
brand) Chromated copper arsenate (CCA) (Tanalith brand) Protects
wood from various forms of decay The arsenic acts as an insecticide
Depending on application and environment, the amount of chemical
leaching varies Depending on application and environment, the
amount of chemical leaching varies
Slide 18
Arsenic Pollution Arsenic is a waste product of some mining and
smelting activities Arsenic is a waste product of some mining and
smelting activities Coal, gold, etc. Poor handing leads to various
forms of pollution, including arsenic in groundwater Poor handing
leads to various forms of pollution, including arsenic in
groundwater
Slide 19
Arsenic Pollution Arsenic is found in various geological
formations Arsenic is found in various geological formations
Granites containing cooper and tin
Slide 20
Arsenic Pollution Arsenic is found in various geological
formations Arsenic is found in various geological formations
Granites containing cooper and tin Natural wearing can lead to its
release Natural wearing can lead to its release
Slide 21
Arsenic Pollution Arsenic is found in various geological
formations Arsenic is found in various geological formations
Granites containing cooper and tin Natural wearing can lead to its
release Natural wearing can lead to its release Wells may tap into
polluted ground water Wells may tap into polluted ground water
Wells are commonly used as a source of microbiologically safe
drinking water without much though to possible chemical
dangers
Slide 22
Arsenic Pollution Worldwide Source: World Bank
Slide 23
Arsenic Pollution United States For decades the regulatory
limit for arsenic was set to 50 g/L (ppb) For decades the
regulatory limit for arsenic was set to 50 g/L (ppb)
Slide 24
Arsenic Pollution United States For decades the regulatory
limit for arsenic was set to 50 g/L (ppb) For decades the
regulatory limit for arsenic was set to 50 g/L (ppb) Recently the
U.S. Environmental Protection Agency lowered the limit to only 10
g/L (ppb) Recently the U.S. Environmental Protection Agency lowered
the limit to only 10 g/L (ppb)
Slide 25
Arsenic Pollution United States For decades the regulatory
limit for arsenic was set to 50 g/L (ppb) For decades the
regulatory limit for arsenic was set to 50 g/L (ppb) Recently the
U.S. Environmental Protection Agency lowered the limit to only 10
g/L (ppb) Recently the U.S. Environmental Protection Agency lowered
the limit to only 10 g/L (ppb) Many sites which previously had safe
levels of arsenic are now over the limit by as much as five times
Many sites which previously had safe levels of arsenic are now over
the limit by as much as five times
Slide 26
Arsenic Pollution United States
Slide 27
Cleanup An inexpensive and efficient method for arsenic
remediation is needed An inexpensive and efficient method for
arsenic remediation is needed
Slide 28
Cleanup Most existing methods are impractical Most existing
methods are impractical
Slide 29
Cleanup An inexpensive and efficient method for arsenic
remediation is needed An inexpensive and efficient method for
arsenic remediation is needed Most existing methods are impractical
Most existing methods are impractical They lack specificity Are
small scale Require alteration of water chemistry Fail to remove
trace quantities Or are completely ineffective against As(III)
which is uncharged at natural pH
Slide 30
Yeast Yeast has defense mechanisms to protect itself from heavy
metals and metalloids Yeast has defense mechanisms to protect
itself from heavy metals and metalloids
Slide 31
Yeast As(III) As(III) Transported back out of the yeast cells
Bound by glutathione and stored in vacuoles Bound by phytochelatins
and sulfides forming various complexes
Slide 32
Yeast Yeast has defense mechanisms to protect itself from heavy
metals and metalloids Yeast has defense mechanisms to protect
itself from heavy metals and metalloids As(III) As(III) Transported
back out of the yeast cells Bound by glutathione and stored in
vacuoles Bound by phytochelatins and sulfides forming various
complexes As(V) As(V) Reduced to As(III) and dealt with
accordingly
Slide 33
Phytochelatin
Slide 34
Cysteine
Slide 35
Cysteine As(III) has an affinity for thiol groups As(III) has
an affinity for thiol groups
Slide 36
Cysteine This is why it binds to proteins, wreaking havoc on
various organisms This is why it binds to proteins, wreaking havoc
on various organisms
Slide 37
Cysteine As(III) has an affinity for thiol groups As(III) has
an affinity for thiol groups This is why it binds to proteins,
wreaking havoc on various organisms This is why it binds to
proteins, wreaking havoc on various organisms This is also how it
binds to PC and is made harmless within the Yeast This is also how
it binds to PC and is made harmless within the Yeast
Slide 38
Bioremediation Efficiency must be increased Efficiency must be
increased
Bioremediation Efficiency must be increased Efficiency must be
increased Saccharomyces cerevisiae 15616 Acr3 Saccharomyces
cerevisiae 15616 Acr3 The Acr3p membrane transporter is deleted
As(III) is prevented from reentering the water
Slide 41
Bioremediation Efficiency must be increased Efficiency must be
increased Saccharomyces cerevisiae 15616 Acr3 Saccharomyces
cerevisiae 15616 Acr3 The Acr3p membrane transporter is deleted
As(III) is prevented from reentering the water Arabidopsis thaliana
phytochelatin synthase Arabidopsis thaliana phytochelatin
synthase
Slide 42
Bioremediation Efficiency must be increased Efficiency must be
increased Saccharomyces cerevisiae 15616 Acr3 Saccharomyces
cerevisiae 15616 Acr3 The Acr3p membrane transporter is deleted
As(III) is prevented from reentering the water Arabidopsis thaliana
phytochelatin synthase Arabidopsis thaliana phytochelatin synthase
Increase the quantity of available PCs for binding As(III)
Slide 43
Bioremediation MicroorganismYeast E. coli ExpressAtPCSSpPCS
Removal Efficiency LowHigh PC Level HighLow Sulfide Content
LowHigh
Bioremediation Available cysteine are stripped of their thiol
groups, increasing the availability of free sulfides for binding
As(III)
Slide 46
Complexes
Slide 47
Complexes
Slide 48
Complexes
Slide 49
Complexes
Slide 50
Complexes
Slide 51
Complexes
Slide 52
Complexes
Slide 53
Complexes
Slide 54
Complexes
Slide 55
Complexes
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Current Progress Dual plasmid system Dual plasmid system
Slide 81
Current Progress Dual plasmid system Dual plasmid system
Phytochelatin synthase Vector pYES2 (5857 bp) Uracil selection
Slide 82
Current Progress Dual plasmid system Dual plasmid system
Phytochelatin synthase Vector pYES2 (5857 bp) Uracil selection
Cysteine desulfhydrase Vector YEplac181 (5741 bp) Leucine
selection
Slide 83
Current Work Test for effectiveness Test for effectiveness
Slide 84
Current Work Test for effectiveness Test for effectiveness
Phytochelatin levels
Slide 85
Current Work Test for effectiveness Test for effectiveness
Phytochelatin levels Sulfide levels
Slide 86
Current Work Test for effectiveness Test for effectiveness
Phytochelatin levels Sulfide levels Arsenic accumulation
Slide 87
Future Work Experiment with over expression Experiment with
over expression
Slide 88
Future Work Experiment with over expression Experiment with
over expression Phytochelatin levels Sulfide levels Acr2p
levels
Slide 89
Future Work Experiment with over expression Experiment with
over expression Phytochelatin levels Sulfide levels Acr2p levels
Selection media Selection media
Slide 90
Future Work Experiment with over expression Experiment with
over expression Phytochelatin levels Sulfide levels Acr2p levels
Selection media Selection media Plasmid loss
Slide 91
Future Work Experiment with over expression Experiment with
over expression Phytochelatin levels Sulfide levels Acr2p levels
Selection media Selection media Plasmid loss Cysteine levels during
growth Cysteine levels during growth
Slide 92
Acknowledgements This work was supported by grants from NSF
(BES0422791 and BES0329482). This work was supported by grants from
NSF (BES0422791 and BES0329482). Acknowledgements are due for Dr.
Rea and Dr. Keasling for providing pYES3- AtPCS::FLAG and the
cysteine desulfhydrase gene respectively. Acknowledgements are due
for Dr. Rea and Dr. Keasling for providing pYES3- AtPCS::FLAG and
the cysteine desulfhydrase gene respectively. BRITE REU BRITE
REU