10.1002/anie.201811067
Angewandte Chemie International Edition
COMMUNICATION
benzoic acid can be obtained by recrystallization from hexane.
The filtrate contains the unreacted benzaldehyde and a little
mount of benzoic acid, which can be reused for the next cycle of
reaction. Through each cycle, 6~6.5 g of benzoic acid can be
obtained, if we keep 10 g of benzaldehyde at the feed. Meanwhile,
the catalytic activity of CPTF was also tested (Figure S19). After
10 cycles, the activity of CPTF was about 85% as that for the first
run. As such, the reaction can be driven by sunlight without any
solvent in a large scale, and the product can be easily purified. In
addition, the catalyst of CPTF and unreacted reactant can be
easily recycled, which meet all the requirements of green
reactions.
under AM1.5G irradiation. As shown in Figure S20, once the
bacteria were treated with CPTF under AM1.5G irradiation for 1
h, serious collapse and merge in membranes were observed.
After the same irradiation for 2 h, some holes were observed in
the bacteria. In contrast, the morphologies of bacteria exhibited
clear edges and smooth bodies for the control group (bacteria
without CPTF treatment). The positive results on organic waste
decomposition and bacterial killing indicated good performance of
CPTF in sunlight-induced wastewater treatment.
In conclusion, a cross-linked porous conjugated polymer PS of
CPTF was designed and synthesized via A3+B2 Suzuki
polymerization. CPTF shows good 1O2 generation efficiency
under sunlight irradiation, excellent photostability, and large
specific surface area for photooxidation. Meanwhile, its excellent
photostability and poor solubility endow it with good recyclability.
Under simulated AM1.5G irradiation, the light-induced organic
synthesis by using oxidation of aldehyde to acid as the example,
and light-induced wastewater treatment by using organic waste
decomposition and bacterial killing as the example indicate that
CPTF is an excellent photocatalyst for sunlight-induced
photooxidation. These results will open up new opportunities for
green chemistry.
Figure 4. (A) The degradation rates of Rhodamine 6G (1×10-4 M) by CPTF and
Rose Begal (0.1 mg/mL); A0 and A are the absorbance of Rhodamine 6G in
the presence of the CPTF and Rose Begal at 530 nm before and after AM1.5G
irradiation, respectively. (B) Photos of Rhodamine 6G solutions with CPTF
before and after AM1.5G irradiation for 2h. From left to right: before irradiation;
after irradiation; after irradiation and then filtration. (C) The killing efficiency of
CPTF (0.1 mg/mL) to S. aureus (1×107 counts/mL) under AM1.5G irradiation for
different times. (D) Plate photographs for S. aureus on LB agar plate
supplemented with CPTF with AM1.5G irradiation for different times and then
grew overnight. From left to right: 0 h, 1 h, and 2 h.
Acknowledgements
We thank the Singapore NRF Competitive Research Program
(R279-000-483-281), NRF Investigatorship (R279-000-444-281),
and National University of Singapore (R279-000-482-133) for
financial support.
Keywords: photosensitizers • singlet oxygen • photooxidation •
sunlight-induced organic synthesis • sunlight-induced
wastewater treatment
Besides organic synthesis, another photooxidation application is
photo-induced wastewater treatment. Under light irradiation, the
generated 1O2 by PSs can ablate commonly seen
microorganisms (such as bacteria, molds and fungi) and
decompose organic waste in water to realize wastewater
treatment.[9] Herein, Rhodamine 6G, and staphylococcus aureus
(S. aureus, ATCC 6538, one of Gram-positive bacteria) were used
as the examples of organic waste, and microorganism,
respectively, to demonstrate the sunlight-induced wastewater
treatment ability and the results are presented in Figure 4. In the
presence of CPTF (0.1 mg/mL), nearly all the Rhodamine 6G
(1×10-4 M) can be decomposed under simulated AM1.5G
irradiation for 2h (Figure 4A). As a reference, only 25% of
Rhodamine 6G was decomposed by RB under the same
condition. In addition, CPTF can be recovered by filtration easily
(Figure 4B). The bacterial killing efficiency of CPTF was then
performed to determine the percentage of live cells by a traditional
colony counting method. After AM1.5G irradiation for 1h, the
percentage of living cells decreased sharply and the relative
viability of S. aureus was lower than 5% (Figures 4C and 4D, initial
concentration: 1×107 counts/mL), and after 2 h irradiation, nearly
all the S. aureus can be killed by the generated 1O2 from CPTF.
To obtain further evidence for the antimicrobial activity of CPTF,
field emission SEM was employed to monitor the morphological
changes of the bacteria before and after treatment with CPTF
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