Upload
tranthuan
View
213
Download
0
Embed Size (px)
Citation preview
IONIZING RADIATION INDUCED DECOMPOSITION OF ANTIBIOTICS IN WASTEWATER
Erzsébet Takács, László Szabó, Tünde Tóth, Csilla Mohácsi-Farkas,
László Wojnárovits
Wide varieties of toxic organic compounds are entering the aquatic environment. The main sources of these impurities are the wastewater treatment plants for domestic sewage. The co-occurrence of sublethal antibiotic concentration and high dense of microbial population provides ideal condition for facilitating the selection and propagation of resistant bacteria in sewage treatment plants. Conventional methods in sewage treatment plants are not able to completely eliminate the antibiotics. The effluent emitted to the surface waters contains pharmaceuticals and bacteria.
Pharmaceuticals in the aquatic environment
Test compound Concentration
µg ml-1
Biodegradation
after 28 days, %
Biodegradation
after 40 days, %
Cefotiam
dihydrochloride 4.8 7 10
Ciprofloxacin 3.5 0 0 Metropenem 2.5 7 7 Penicillin G 3.0 27 36 Sulfamethoxazole 3.8 0 0
Biodegradation of antibiotics. Results of closed bottle test.a)
a) Al-Ahmad, A., Dashner, F.D., Kummerer, K., Biodegradability of cefotiam,
ciprofloxacin, meropenem, penicillin G and sulfamethoxazole and inhibition of waste bacteria. Archiv. Environ. Contam. Toxicol. 37, 158 (1999)
Pharmaceuticals in the aquatic environment
How to solve this problem?
Post treatment of the wastewater treatment plant effluent by ionizing radiation.
Elimination of the antimicrobial activity and deactivation of the
bacteria in one step.
H2O H, eaq, OH, H+, OH, H2O2, H2
G (H) = 0.06 µm J-1; G(OH) = 0.28 µm J-1; G(eaq) = 0.28 µm J-1
The purpose of our work is:
• To describe degradation mechanisms and determine rate constants for the reactions of the water radiolysis intermediates with the pollutant molecules.
• To suggest the dose necessary to eliminate the toxicity and biological (e.g. antimicrobial) activity of pharmaceuticals.
Radiolysis in aqueous solutions
Mechanism of free-radical induced oxidation
• Pulse radiolysis – Tesla Linac LPR-4 accelerator (4 MeV)
– Pulse width 800 ns
– Dose/pulse 20-40 Gy
• Final product analysis
– 60Co facility with 11.5 kGy h1 dose rate
• LC/ESI-MS analysis
– Agilent 1200 liquid chromatograph
– Agilent 6410 triple quadrupole MS/MS with electrospray ionization (ESI) interface
• CO2-release using a Shimadzu TOC-L equipment
Decomposition kinetics and mechanism of free-radical induced degradation
0 20 40 60
-0.01
0.00
0.01
0.02
0.03
0.04
0.05
0.06
0 2 4
-0.005
0.000
0.005
0.010
0.015
0 10 20 30
-0.02
0.00
0.02
0.04
0.06
0.08
0.10
0.12
0 400 800 1200
-0.002
-0.001
0.000
0.001
0.002
0.003
0.004
DC
B
MV.+
A
bso
rban
ce
Time (s)
A
= 415 nm
ABTS.+
= 600 nm
A
bso
rban
ce
Time (s)
= 415 nm
A
bso
rban
ce
Time (s)
k' = 1.78 x 10
5 s
-1
= 430 nm
Q.-
A
bso
rban
ceTime (s)
250 300 350 400 450 500 550
0.000
0.005
0.010
0.015
0.020
0.025
0.030
0.02 0.04 0.06 0.08 0.1000
1
2
3
4
5
0 2 4 6 8 10 12
0.000
0.005
0.010
0.015
0.020
0.025
0.030
0.035
A
bso
rban
ce
Wavelength (nm)
a
b
c0.0 0.5 1.0 1.5
-6
-5
-4
B
ln(
A)
Time (ms)
Fitting at 325 nm
k' (
s-1)
Concentration (10-3 mol dm
-3)
x 105
A
CKinetic trace at 485 nm
A
bso
rban
ceTime (s)
Decomposition kinetics of penicillin derivative (-lactam) antibiotics
Transient absorption spectra of intermediates in eaq
reaction in N2 saturated AMX solution
Reaction of eaq
10 μs
80 μs
580 μs
250 300 350 400 450 500
0.000
0.005
0.010
0.015
0.020
0.025
0 2 4 6 8 10 12-0.004
-0.002
0.000
0.002
0.004
0.006
0.008
0.010
0.012
0.014
0.016
0.0 0.5 1.0 1.5 2.0 2.5 3.0-0.005
0.000
0.005
0.010
0.015
0.020
0 1 2 3 4 5 6-0.002
-0.001
0.000
0.001
0.002
0.003
0.004
0.005
B
A
bso
rban
ce
Wavelength (nm)
a
b
250 300 350 400 450 500
0.000
0.005
0.010
0.015
0.020
0.025
d
c
A
bso
rban
ce
Wavelength (nm)
E
D
C
e290 nm
f260 nm
A
bso
rban
ce
Time (ms)
e
f
350 nm
A
bso
rban
ce
Time (ms)
405 nm
A
bso
rban
ce
Time (ms)
A
Decomposition kinetics of penicillin derivative (-lactam) antibiotics
Transient absorption spectra observed of 0.1 mM amoxicillin solution saturated with N2O (A), and in the same solution containing 0.1 mM K3Fe(CN)6.
Reaction of OH radical
sulfuranyl radical
10 s
400 s
2 s
10 s
K3Fe(CN)6
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 150
1
2
3
4
Ab
un
da
nce
Time (min)
x 106
Mechanism of free-radical induced oxidation of AMX LC-MS/MS
100 300 500 700200 400 600 800
0.2
0.4
0.6
0.8
1.0
1.2
1.4
1.6
0
Abundance
m/z
366
731
349
208160114
+ Scan (6.279 min) x10
6
A
100 300 500 700200 400 600 800
0.4
0.8
1.2
1.6
2.0
2.4
2.8
0
B
- Scan (6.311 min) x105
Abundance
m/z
729
364
320
223
Total ion chromatogram
Mass spectra of AMX in positive mode (A) and in negative mode (B)
Final products of
amoxicillin (P9) exposed
to oxidative stress.
Structures suggested based
on LC-MS/MS analysis
Mechanism of free-radical
induced oxidation
Elimination of the toxicity and antibacterial activity
Microbiology
• Biological assays • Acute and chronic effects toward bacteria
• Vibrio fischeri bioluminescence inhibition assay • Vibrio fischeri growth inhibition assay
• Bacterial susceptibility tests • Agar diffusion test
• Staphylococcus aureus • Bacillus subtilis • Eschericia coli
• Broth macrodilution test • Staphylococcus aureus • Eschericia coli
Elimination of the antibacterial activity Tracking the elimination of the pharmacophore
0 2 4 6 80
20
40
60
80
100
Gro
wth
inh
ibit
ion
(%
)
Dose (kGy)
Growth inhibition of Vibrio fischeri in amoxicillin (■), cloxacillin (●) and ampicillin (▲) samples as a function of absorbed dose.
2200 2000 1800 1600 1400 1200 1000 800 600
B
2240 M .OH
280 M .OH
Ab
sorb
ance
Wavenumber (cm-1)
168 M .OH
(d)
1768 cm-12067 cm
-1
(c)
(b)
(a)
A
0 2 4 6 8
0.00
0.05
0.10
0.15
0.20
0.25
0.30
0.35
0.40
0.45
0.50
-l
acta
m c
on
ten
t (m
M)
Am
ou
nt
of
. OH
in
ject
ed (
M)
Dose (kGy)
0
500
1000
1500
2000
2500
(A) FTIR spectra of amoxicillin, (B) Quantitative FTIR analysis of the β-lactam content in the case of amoxicillin (■), cloxacillin (●) and ampicillin (▲) as a function of absorbed dose.
0.6 kGy
1 kGy
0 kGy
Elimination of the antibacterial activity of penicillin derivative (β-lactam) antibiotics
8 kGy
Agar diffusion is a routine method in clinical microbiology to assess bacterial susceptibility to certain antibiotics. It is based on the formation of inhibition zones in the vicinity of the antibiotic solution diffusing in agar media seeded with a certain microorganism.
Agar diffusion test of amoxicillin solutions, treated with increasing dose, on agar plates seeded with B. subtilis (A) and E. coli (B).
Elimination of the antibacterial activity in purified water
Agar diffusion test using S. aureus B.01755 for erythromycin dissolved in the synthetic effluent wastewater matrix received increasing absorbed dose.
Elimination of the antibacterial activity of erythromycin in a complex synthetic wastewater matrix by EB treatment
Sample 0 kGy 4 kGy 8 kGy 12
kGy
16
kGy
20
kGy
24
kGy
28
kGy
1. 21.5 16.0 14.0 12.0 12.5 11.5 - 10.0
2. 21.0 16.0 15.0 14.0 12.5 12.0 11.0 -
Sample 32
kGy 36 kGy
40
kGy
60
kGy
80
kGy
100
kGy
200
kGy
1. 12.0 10.0 - - - - -
2. 10.0 10.0 - - - - -
The absorbed doses should be divided by 500.
80 Gy
humic acid, inorganic salts
SUMMARY
• Based on pulse radiolysis combined with final products analysis degradation mechanism was suggested
• It is important to follow the change in toxicity and in antibacterial activity
• A mild treatment (80 Gy) was just enough to eliminate antimicrobial activity of a complex matrix.
THANK YOU FOR YOUR ATTENTION