environmental nanotechnology research at ndsu feb 7 2013-final.pdfharjyoti kalita michael quamme...
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Harjyoti Kalita
Michael Quamme
Department of Civil Engineering North Dakota State University, Fargo, ND
Environmental Nanotechnology Research at
NDSU
Nanoenvirology Research Group
1
Student (2006-1012) Project MS PhD
Jay Thompson √ √
Sita Krajangpan √ √
Harjyoti Kalita √ √
Rabiya Shabanam √ √
Dhritikshama Roy √ ----
Christopher Capecchi √ ----
Sharanya Shanbhogue √ ----
Michael Quamme √ √
2
Source: NSF
US $ in Billion
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70
100
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0 100 200 300 400
Tools
Health Care
Sustainability
Aerospace
Chemicals
Phamaceutical
Electronics
Materials
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Late 1990s: rash of
research in NZVI
Laboratory results were
outstanding
Field studies have shown
moderate success
Image Credit: Zhang, W-X., 2003. J. Nanopart. Res. 5, 323-332.
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6
1. Will nanoparticles work for our contaminants?
2. Can we make them work better?
3. Will our new products be biocompatible?
4. Are nanoparticles harmful to microorganisms?
5. What other innovations possible with nanoparticles?
Funding: NDWRRI and Civil Eng
Herbicide for the control of grasses/weeds in corn and soybeans
Maximum Contaminant Level (MCL) = 2 ppb
Jay Thompson
0
5
10
15
20
25
30
35
40
0 6 12 18 24 30 36 42 48 54 60 66 72
C, m
g/L
Time, hr
Objective: To modify nanoscale
zero-valent iron (NZVI) particle
surface using APGC for effective
groundwater remediation
Hypothesis: APGC provide the
colloidal stability and improve
capabilities to NZVI for
groundwater contaminant removal
Bezbaruah et al., J. Hazard. Mater.,2009, 166,
1339-1343.
Oxidation rate↑, Dispersibility ↓,
and Reactive surface area ↓
Krajangpan et al., ASCE, 2009, pp 191-212.
Krajangpan et al., Polymer Preprint, 2008, 49, 921-922.
Coated Feo Nanoparticle
Dispersed in the Aqueous Phase
Coated Feo Nanoparticle
at the Aqueous/Organic Interface
Aqueous
Phase
Organic
Phase
Coated Feo Nanoparticle
Dispersed in the Aqueous Phase
Coated Feo Nanoparticle
at the Aqueous/Organic Interface
Aqueous
Phase
Organic
Phase
Coated Feo Nanoparticle
Dispersed in the Aqueous Phase
Coated Feo Nanoparticle
at the Aqueous/Organic Interface
Aqueous
Phase
Organic
Phase
Coated Feo Nanoparticle
Dispersed in the Aqueous Phase
Coated Feo Nanoparticle
at the Aqueous/Organic Interface
Aqueous
Phase
Organic
Phase
APGC synthesis
A schematic representation of APGC
coated NZVI (CNZVI)
SiO
SiO
SiO
Si
H
x y
+
O
O +O
On
SiO
SiO
SiO
SiO
a b
Si
c
O
O
nO
O
SiO
SiO
SiO
SiO
a b
Si
c
HO
O
nO
O
Pt
Hydrolysis
0.0
0.2
0.4
0.6
0.8
1.0
20 40 60N
orm
ali
zed
In
ten
sity
Time (min)
Bare nZVI CnZVIBare NZVI CNZVI
CNZVI has significantly higher colloidal
stability than bare NZVI
U.S
. P
ate
nt
11
Initial concentration of TCE and
As(V): 1, 15, and 30 mg/L
TCE batch study: 1.5 g/L of NZVI
and CNZVI
As(V) batch study: 1 g/L of NZVI
and CNZVI
Controls and blanks were ran
simultaneously
Aliquots withdrawn at definite
time intervals
TCE and As(V) were analyzed
using GC-MS and ICP-AES
0
0.2
0.4
0.6
0.8
1
0 2 4 6 8 10 12
TC
E N
orm
ali
ze
d
Co
nc
en
tra
tio
n
Time (h)
CNZVIBare NZVIBlankControl
TCE kinetic study
As
(V)
No
rma
lize
d
Co
nc
en
tra
tio
n
CNZVI(Aerobic)
Bare NZVI
Blank
Control
CNZVI (Anarobic)
12
0.0
0.2
0.4
0.6
0.8
1.0
0 20 40 60 80 100 120
Norm
ali
zed
In
ten
sity
Time (min)
CNZVI sedimentation studies:12 month-
period
0
5
10
15
20
25
30
0 2 4 6 8 10 12
TC
E C
on
cen
tra
tio
n
(mg
/L)
Time (h)
CNZVI-TCE kinetic studies: 6 month-
period
Sedimentation studies:
Batch studies: 3 g/L of NZVI and 15
g/L of APGC
30 min sonication and 72 hr of 28
rpm rotation
UV-VIS spectrophotometer
TCE kinetic studies:
1.5 g/L of NZVI and CNZVI
30 mg/L of TCE initial concentration
TCE was analyzed using GC-MS
13
Funding: NDWRRI & ND Soybean Council
Objectives:
1. Development of novel ion imprinted polymer
for arsenic removal
2. Synthesis of biodegradable amphiphilic
copolymer from soybean oil
Harjyoti Kalita
SHAs(III), As(V)5 AsS
S
S SS
AsS
S
S
+
AsS
S
S
Polymerization
60 oC, 24 hr
+
AsS
S
SLeaching1:1 HCl
Monomer Crosslinker
Thiol -arsenic complex
Thiol -arsenic complex
February 11, 2013 14
Sample
Theoretical value(ppm)
Experimental value (ppm)
Thiol- arsenic complex
143.98 138.61
Elution of arsenic and preparation of IIP
10 ml HCL 150.85 147.67
20 ml HCL 150.85 145.38
30 ml HCL 150.85 149.74
Binding & Elution of As: IIP-As Synthesis
February 11, 2013
Weight of IIP-As (g)
Extraction (%)
Preconcentration time
(hr)
Extraction (%) Elution time ( hr)
Extraction (%)
0.05 > 87 1 >97 0.5 >98
0.1 >96 2 >99 1 >99
0.15 >98 3 >99 1.5 >99
0.2 >96 4 >99
0.25 >97 5 >99
0.3 >97
Influence of Various Parameters on As
Extraction
February 11, 2013
18
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
n
C6H17Al2Cl3
Toluene, N2, 8hr
O
O
O
O
O
O
O
O
O
O
n
ab
c
d
f
g
h
i
j
e
k
l
m
n
o
p
q
r
s
t
u
v
O
x
w
y
z
19
O
O
O
O
O
O
O
n
ab
c
d
f
g
h
i
j
e
k
l
m
n
o
p
q
r
s
t
u
v
O
x
w
y
z
HS OH
O
Benzophenone
UV , 3hr
O
O
O
O
O
O
O
n
ab
c
d
f
g
h
i
j
e
k
lm
n
o
p
q
r
s
t
u
v
O
x
w
y
z
S
HOOC
S
COOH
V-15/T-85:C20
where V-15 represent VOES 15wt%; T-15 represent TGEVE 85wt%
C represent – carboxilic acid & 20 represent 20 g/L polymer solution
0
0.2
0.4
0.6
0.8
1
1.2
0 20 40 60 80 100 120
Ab
sorp
tio
n (
I/I
0)
Time minute)
V-15/T-85: C20
V-15/T-85: C15
V-15/T-85: C10
V-15/T-85: C5
Bare NZVI
Time - 0 m
Time - 1h
Time - 15m
Time - 2 h
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Funding : NDWRRI & ECS Program
Objective: To understand microorganism-NZVI
interactions
Hypothesis: Microorganisms can establish a
“symbiotic relationship” with NZVI
Rabiya Shabnam
24
Bactericidal effects: NZVI
concentration dependent
Physical condition of the cell membrane
Growth phase of the bacteria
E. coli 8739, Jm109 and Pseudomonas putida F1 show similar effects with NZVI
Inactivation of E. coli 8739 in buffer
0.0E+00
2.0E-01
4.0E-01
6.0E-01
8.0E-01
1.0E+00
1.2E+00
1.4E+00
0 10 20 30 40 50 60 70
Ce
lls/m
L
Time, min
90 mg/L 200 mg/L500 mg/L 800 mg/L1000 mg/L
25 25
Findings:
Bacteria in a lag or early
exponential phase are
affected by NZVI
Actively growing bacteria are
not effected by NZVI
Non-replicating bacteria are
more susceptible to NZVI
toxicity
1.0E+05
1.0E+06
1.0E+07
1.0E+08
1.0E+09
0 2 4 6 8 10
Ce
lls/m
L
Time, h
10 mg NZVI 10 mg NZVI 10 mg NZVI
1.0E+05
1.0E+06
1.0E+07
1.0E+08
1.0E+09
0 2 4 6 8 10
Ce
lls/m
L
Time, h
10 mg NZVI
Funding: NDWRRI and NSF
Objective: Entrapment of NZVI in alginate beads for effective
treatment of selenium from contaminated waters
26
Michael Quamme and Bryant Feist
28
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
1.1
0 2 4 6 8 10 12 14 16 18 20 22 24
Norm
ali
zed
Se
Con
cen
trati
on
Time, h
0.5 mg/L
5 mg/L
10 mg/L
0.5 mg L-1
5 mg L-1
10 mg L-1
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
1.1
0 1 2 3 4 5 6
Norm
ali
zed
Se
Con
cen
trati
on
Time, h
0.5 mg/L
5 mg/L
10 mg/L
0.5 mg L-1
5 mg L-1
10 mg L-1
Entrapped NZVI Bare NZVI
Bare and entrapped equally effective
Slower reaction rate for entrapped NZVI
Possible use in surface, ground and tap water
Ongoing and Future Work
Growth of microbes on PDMS need further study
Growth study on copolymer added mineral media is underway
Need to analyze PEG and AA degradation study along with PDMS
Isolation of fungi from the composting is in progress
Isolation of microorganisms from batch reactors is in progress
Iron polymer for metals removal
29
Funding: Civil Engineering
Objective: Entrapment of NZVI in alginate beads for effective
treatment of arsenic contaminated groundwater
Chris Capecchi Bezbaruah et al., J. Haz. Mat., 2009
30
Arsenic (IV) Batch Studies:
After 45-60 minutes entrapped
NZVI out performs bare NZVI
Blank and control show
negligible concentration
change
Entrapped beads can be used
in PRB’s
32
33
Funding: Civil Engineering
Objectives: NZVI and
microorganism Co-entrapment in
alginate beads for groundwater
TCE degradation
Shanaya Shanbhogue
34
Encapsulation of NZVI
Encapsulated NZVI
TCE degradation using Encapsulated NZVI
0
5
10
15
20
25
30
35
40
0 20 40 60 80 100 120
Co
nce
ntr
atio
n (
mg/
L)
Time, min
30 mg/L
BLANK
Control
Avg TCE Conc
Bare NZVI
35
1. Chisholm, B.J.; Kalita, H.; Bezbaruah, A. (2012), “ Vegetable Oil-Based Polymers for
Nanoparticle Surface Modification”, Provisional patent. (Patent)
2. Chisholm, B.J.; Kalita, H. (2013), RFT-438, “Plant Oil based Diluent”, Provisional
patent. (Patent)
3. Almeelbi T, Quamme M, Bezbaruah AN (2012), RFT-419A, “Aqueous Phosphate
Removal using Iron Cross-lined Alginate”, Patent Filed. Patent)
4. Almeelbi T, Quamme M, Khan E, Bezbaruah AN (2012), RFT-419B, “Selenium
Removal from Surface Waters: Exploratory Research with Iron Nanoparticles”, Patent
Filed. Patent)
5. Krajangpan, S., Chishlom, B., Bezbaruah, A. (2010), RFT-247 & RFT-247A, Novel
Polymer Modified Iron Nanoparticles for Environmental Remediation, US Patent.
(Patent)
6. Kalita, H, Chishlom, B., Bezbaruah, A. (2010), Soybean-based Copolymer, to be filled
(Patent)
7. Alam, S.; Kalita, H.; Jayasooriya, A.; Chisholm, B.J. (2012), “Coatings Derived from
Novel Plant Oil-Based Polymers”, Submitted to ACS, 2012
8. Kalita, H.; Kudina, O.; Popadyuk, A.; Chishola, B.; Voronov, A. (2013), “Soy-Based
Surface Active Copolymers as Safer Replacement for Low Molecular Weight
Surfactants.” ACS Sustainable Chemistry & Engineering, 1, 19-22
36
9. Krajangpan, S.; Kalita, H.; Chisholm, B.J.; Bezbaruah, A.N. (2012), “Iron Nanoparticles
Coated with Amphiphilic Polysiloxane Graft Copolymers Coated Iron
Nanoparticles: Dispersibility and Contaminant Treatability.” Environmental Science and
Technology, 2012, 46, 10130–10136
10. Thompson, J.M., Chisholm, B.J., Bezbaruah, A.N. (2010). Reductive Dechlorination of
Chloroacetanilide Herbicide (Alachlor) Using Zero-valent Iron Nanoparticles,
Environmental Engineering Science, 27, 227-232.
11. Bezbaruah, A.N., Shanbhogue, S.S., Simsek and S., Khan, E. (2011), Encapsulation of
iron nanoparticles in alginate biopolymer for trichloroethylene remediation, Journal of
Nanoparticle Research, 13, 6673–6681.
12. Bezbaruah, A.N. and Kalita, H. (2010) Sensors and Biosensors for Endocrine
Disrupting Chemicals State-of-the-art and Future Trends in Treatment of
Micropollutants in Water and Wastewater (Eds: Virkutyte, J., Varma, R.S.,
Jegatheesan, V.), International Water Association, London,, U.K., ISBN:
9781843393160, pp.92-128. (Book Chapter)
13. Krajangpan, S., Chisholm, B.J., Kalita, H., Bezbaruah, A.N. (2009). Challenges in
Groundwater Remediation with Iron Nanoparticles: Enhancement Colloidal Stability
(Chapter 8) in Nanotechnologies for Water Environment Applications (Eds: Zhang,
T.C., Surampalli, R.Y., Lai, K.C.K., Hu, Z., Tyagi, R.D., Lo, I.M.C.), American Society for
Civil Engineers, pp 191-212. (Book Chapter)
14. Kalita, H., Chisholm, B., Bezbaruah, A. (2009) Effects of different graft copolymer
constituent groups on sedimentation characteristics of coated iron nanoparticles,
PSME Preprints, 100:683-685.
15. Bezbaruah, A.N., Thompson, J.M., Chisholm, B.J. (2009) Remediation of alachlor
and atrazine contaminated water with zero-valent iron nanoparticles, Journal of
Environmental Science and Health Part B Pesticides, Food Contaminants, and
Agricultural Wastes, 44:518-524.
16. Thompson, J.M., Bezbaruah, A.N. Selected Pesticide Remediation with Iron
Nanoparticles: Modeling and Barrier Applications. Technical Report No. ND08-04.
North Dakota Water Resources Research Institute, Fargo, ND, 2008. Krajangpan, S.,
Jarabek, L., Jepperson, J., Chisholm, B., Bezbaruah, A. (2008). Polymer Modified
Iron Nanoparticles for Environmental Remediation, Polymer Preprint, 49, 921-922.
17. Bezbaruah, A.N., Krajangpan, S., Chisholm, B.J., Khan, E., Bermudez, J.J.E., (2009).
Entrapment of Iron Nanoparticles in Calcium Alginate Beads for Groundwater
Remediation Applications, Journal of Hazardous Materials, 166, 1339-1343.
37