4 research outputs found
End-Capping Effect of Quinoxalino[2,3‑<i>b</i>′]porphyrin on Donor–Acceptor Copolymer and Improved Performance of Polymer Solar Cells
A series of end-capped donor–acceptor
copolymers, PÂ(BT-DPP)-T,
PÂ(BT-DPP)-QP, and PÂ(BT-DPP)-QPZn, were synthesized by Stille coupling
of 2,2′-bithiophene (BT) and diketopyrrolopyrrole (DPP) with
end-caps of thiophene (T), quinoxalinoÂ[2,3-<i>b</i>′]Âporphyrin
(QP), and quinoxalinoÂ[2,3-<i>b</i>′]Âporphyrinatozinc
(QPZn), respectively. Compared with the counterpart, PÂ(BT-DPP), which
contains no end-caps, PÂ(BT-DPP)-QP and PÂ(BT-DPP)-QPZn showed remarkably
enhancement of light absorption in the range of <i>ca</i>. 400–550 nm resulted from the end-capping effect of porphyrins.
Bulk heterojunction polymer solar cells (PSCs) based on these polymers
were fabricated and the results showed significant improvement of
power conversion efficiencies (PCEs) of the end-capped polymers. Especially,
ligand addivie, 4,4′-bipyridine (Bipy), was applied to the
PSCs based on polymers end-capped by porphyrins and the PCE of the
photovoltaic device based on PÂ(BT-DPP)-QPZn significantly improved
from 2.92% to 4.45% with the comprehensive benefits of optimization
strategies such as using additives and thermal annealing. Furthermore,
thermal aging experiments showed increased stability of the optimal
morphology of PÂ(BT-DPP)-QPZn:PC<sub>71</sub>BM blend film after the
use of Bipy. This study provides a promising strategy to design donor–acceptor
copolymers with multifunctional end-caps and to use ligand additives
for achieving PSCs with both high-efficiency and long-term stability,
which are critical for the devices to be commercially useful
Assessment of the Air–Soil Partitioning of Polycyclic Aromatic Hydrocarbons in a Paddy Field Using a Modified Fugacity Sampler
Rice, one of the most widely cultivated
crops, has received great
attention in contaminant uptake from soil and air, especially for
the special approaches used for its cultivation. The dry–wet
alternation method can influence the air–soil partitioning
of semivolatile organic compounds (SVOCs) in the paddy ecosystem.
Here, we modified a fugacity sampler to investigate the air–surface
in situ partitioning of ubiquitous polycyclic aromatic hydrocarbons
(PAHs) at different growth stages in a suburban paddy field in South
China. The canopy of rice can form a closed space, which acts like
a chamber that can force the air under the canopy to equilibrate with
the field surface. When we compared the fugacities calculated using
a fugacity model of the partition coefficients to the measured fugacities,
we observed similar trends in the variation, but significantly different
values between different growing stages, especially during the flooding
stages. However, the measured and calculated fugacity fractions were
comparable when uncertainties in our calculations were considered,
with the exception of the high molecular weight (HMW) PAHs. The measured
fugacity fractions suggested that the HMW PAHs were also closed to
equilibrium between the paddy field and atmosphere. The modified fugacity
sampler provided a novel way of accurately determining the in situ
air–soil partitioning of SVOCs in a wet paddy field
Organochlorine Pesticides in the Atmosphere and Surface Water from the Equatorial Indian Ocean: Enantiomeric Signatures, Sources, and Fate
Nineteen
pairs of gaseous and surface seawater samples were collected along
the cruise from Malaysia to the south of Bay of Bengal passing by
Sri Lanka between April 12 and May 4, 2011 on the Chinese research
vessel Shiyan I to investigate the latest OCP pollution status over
the equatorial Indian Ocean. Significant decrease of α-HCH and
γ-HCH was found in the air and dissolved water phase owing to
global restriction for decades. Substantially high levels of <i>p,p</i>′-DDT, <i>o,p</i>′-DDT, trans-chlordane
(TC), and cis-chlordane (CC) were observed in the water samples collected
near Sri Lanka, indicating fresh continental riverine input of these
compounds. Fugacity fractions suggest equilibrium of α-HCH at
most sampling sites, while net volatilization for DDT isomers, TC
and CC in most cases. Enantiomer fractions (EFs) of α-HCH and <i>o,p</i>′-DDT in the air and water samples were determined
to trace the source of these compounds in the air. Racemic or close
to racemic composition was found for atmospheric α-HCH and <i>o,p</i>′-DDT, while significant depletion of (+) enantiomer
was found in the water phase, especially for <i>o,p</i>′-DDT
(EFs = 0.310 ± 0.178). 24% of α-HCH in the lower air over
the open sea of the equatorial Indian Ocean is estimated to be volatilized
from local seawater, indicating that long-range transport is the main
source
Source Apportionment Using Radiocarbon and Organic Tracers for PM<sub>2.5</sub> Carbonaceous Aerosols in Guangzhou, South China: Contrasting Local- and Regional-Scale Haze Events
We
conducted a source apportionment and investigated the atmospheric
behavior of carbonaceous aerosols during hazy and normal days using
radiocarbon (<sup>14</sup>C) and biomass burning/secondary organic
aerosol (SOA) tracers during winter in Guangzhou, China. Haze episodes
were formed either abruptly by local emissions or through the accumulation
of particles transported from other areas. The average contributions
of fossil carbon to elemental carbon (EC), water-insoluble organic
carbon, and water-soluble organic carbon were 71 ± 10%, 40 ±
6% and 33 ± 3%, respectively. High contributions of fossil carbon
to EC (80–90%) were observed for haze samples that were substantially
impacted by local emissions, as were the highest (lowest) ratios for
NO<sub>3</sub><sup>–</sup>/SO<sub>4</sub><sup>2–</sup> (OC/EC), which indicates that these particles mainly came from local
vehicle exhaust. Low contributions of fossil carbon to EC (60–70%)
were found for haze particles impacted by regional transport. Secondary
organic carbon (SOC) calculated using SOA tracers accounts for only
∼20% of the SOC estimated by <sup>14</sup>C, which is probably
because some important volatile organic carbons are not taken into
account in the SOA tracer calculation method and because of the large
discrepancy in ambient conditions between the atmosphere and smog
chambers. A total of 33 ± 11% of the SOC was of fossil origin,
a portion of which could be influenced by humidity