1. PROMPT LEAD EXPOSURE OF AQUEOUS
ENVIRONMENT BIOMONITORED BY
PHOTOSYNTHETIC BACTERIA
Saed AL-Atawneh
Department of Medical Physics and Informatics
University of Szeged
October
2018
2. - Toxic heavy metals: mercury, lead, chrome
Introduction
Heavy metal contamination in Drinking Water
Source:http://www.epa.gov/sites/production/files/styles/large/publi
c/2017-08/pbinfographic_thumbnail_0.png
-The permissible level of lead
contamination in drinking water
(World Health Organization limit) is
as low as 10 µg/l ≈ 50 nM.
Source:http://www.epa.gov/sites/production/files/styles/larg
e/public/2017-08/pbinfographic_thumbnail_0.png
3. Why photosynthetic purple bacteria?
Photosynthetic apparatus
Kis M.,et al. , Photobiology. B. Biology, 2015.
LH2
(peripheral antenna)
LH1
(core antenna)
Reaction
center
TEM picture of Rhodobacter sphaeroides
Advantages:
1. Varied habitat and metabolisms
2. Relatively short generation time
3. Excellent model system
4. Easily adapts
5. Monitoring environmental pollution
6. Bioremediation
500 fs
5 ps
100 fs
4. Bacterial Biosorption
Prasad et al. 2006
Main types of Bacterial Biosorption
Ions adsorb to the cell
surface groups and
they diffuse through
the cell membrane
Ions can use other non
toxic metal channels
Ions bind to the negatively charged
phosphate, sulfate and carboxylic
acid groups.
6. Results and Discussion
Steady-state absorption spectrum.
-The absorption spectra of intact cells were
measured by dual beam spectrophotometer
-Both red absorption bands characteristic of
the peripheral (808 nm) and core (870 nm)
antenna complexes demonstrate prompt
decomposition after treatment with lead
acetate in the few mM concentration range
Fig. 1. Steady state red absorption spectra of
intact cells of photosynthetic bacteria
Rubrivivax gelatinosus after prompt addition
of Pb(II) acetate to the culture.
LH2
LH1
LH2
LH2
LH1
7. Results and Discussion
Fig. 2. Kinetics (inset) and lead(II)-dependent
amplitude of flash-induced electrochromic
response of the carotenoids.
Flash-induced absorption change kinetics.
- The flash-induced absorption change indicating
that the magnitude of the membrane potential was
changed
- whole cells of Rubrivivax gelatinosus upon
treatment with 0-4 mM Pb(II) measured by
absorption change at 530 nm (vs. 510 nm).
https://www.promegaconnections.com
8. Fig. 3. BChl fluorescence (F) induction kinetics
(inset) and lead-dependent changes of the
maximum fluorescence (Fmax).
Results and Discussion
Induction and relaxation of bacteriochlorophyll (BChl)
fluorescence.
-The induction and decay were measured by a home built
fluorometer .
-The light source was a laser diode (808-nm wavelength
and 2W light power).
9. Results and Discussion
Fig. 4. Relaxation of the BChl
fluorescence after flash excitation
- BChl fluorescence gives information about the
pathways of re-opening of the closed reaction
centers in the dark.
- The prompt effect of lead(II) ions is expressed as
significant decrease of the maximum fluorescence
.
Closed R.C
Open R.C
Reaction
center
10. Conclusion
- Photosynthetic Purple bacteria are sensitive bioindicators of lead(II) contamination of
aqueous cultures.
- The absorption spectrum was decreased by 62.5% with 3mM of lead-acetate
contamination.
- The absorption Amplitude (A530-510) of carotenoid was decreased by 50.0% with 4mM of
lead- acetate.
- The Fluorescence–Induction was decreased by 27% with 6mM of Lead–acetate and also
the Relaxation Fluorescence was decreased by 48.7% with 4mM of lead-acetate.
- The Pb(II) ions cause prompt and detectable physiological changes by disconnection and
damage of the antenna pigments, LHCs.
`- The human Activities like industries and the natural sources like volcanoes are the main source of heavy metal ions such as (mercury, lead and cadmium) , where the concentration of these metals are increased today to alarming levels.
Out of these non-biodegradable pollutants, the lead (II) ions have a special significance because of their wide use in various human activities including glass, metal ,batteries and paints industries.
In addition to Copper pipe with lead solder, Galvanized pipe, and lead service unit which represent a main source of lead contamination in drinking water.
- Where the high concentration of lead in water caused physiological disorders and toxicological effects to humans as you see over their , for these reasons the lead concentration in drinking water was determined by WHO
- Different chemical methods including reduction, ion-exchange, electrolysis have been used for the removal of lead ions from water. In addition to the chemical methods, biological techniques are also available to detect and to remove the toxic heavy metal pollutants , where the Photosynthetic bacteria successfully used for this purpose.
-The chromatophores was magnified and you can see the LHCs
-Cell surface interaction, this kind of diffusion will be very slow due to electrostatic interaction between heavy metal ions “lead” and ions that's already surrounded the membrane
Bacterial strains and growth conditions
The photosynthetic purple bacterium Rubrivivax (Rvx.) gelatinosus were grown in Siström’s medium (photoheterotrophic and anaerobic growth).
The medium was illuminated by tungsten lamps that assured 13 Wm-2 irradiance on the surface of the vessel.
Chemicals
-The cells were harvested and bubbled by nitrogen for 15 min before measurements.
-Variable amounts of Pb(CH3COO)2*3H2O (Pb(II)-acetate) were added to the bacterial culture for heavy metal ions treatment .
Optical
-consist of three different measurments Techniques, the steady , Flash , and the Fluoresence.
-The absorption spectra were measured by dual beam spectrophotometer as you see over their the LHCs in Fig1
-The absorption decrease which demonstrate a prompt decomposition after treatment with lead acetate in the few mM concentration .
-You can see over their in the lower corner of the right side of slid
-The reaction center including to carotenoid were irradiated by flash and the membrane was charged as a capacitor and then the carotenoid absorption amplitude was measured by home constructed spectrophotometer , you can see in figure2 over their the black line which represent an absorption amplitude of carotenoid at 0mM of acetate.
-then, when the lead acetate ions were added , the absorption amplitude was decreased as you see in the red line over their from 1.3 to be around 0.6 ,
-And again, you can see the exponential decay of absorption amplitude with lead-acetate concentrations.
- In conclusion , the flash induction absorption change its just indication on membrane potential change due to lead-actate pollutants.
-The difference in fluorescence- induction value between controlled and uncontrolled sample demonstrate the prompt effect of lead- acetate , I mean ,the lead acetate ions were promptly attacked the RCs and reduce the max value of fluorescence induction
-the first line represent to the relaxation part of untreated sample were most of the reaction centres were equipped with photons so we can call it as a closed reaction centre
Where the reaction centres are going to decay within few mSec in dark and then we can say that its an open reaction centres.
-compare to second line which represent the treated sample with 4mM of lead acetate , you can see decrease in the initial value of fluorescence induction was decreased by 48% and this demonstrate the prompt effect of lead ions where most of R.C in this case are not equipped.