16 research outputs found
Coconut Shell Activated Carbon Supported Quaternary Ammonium for Continuous Cycloaddition of CO<sub>2</sub> and Biogas Upgrading in a Packed Bed
Quaternary ammonium was successfully
prepared on coconut shell
activated carbon (CSAC) granules. The samples were characterized by
FT-IR, N<sub>2</sub> adsorption–desorption, XPS, TG, and EA.
The immobilized quaternary ammonium was thermally stable below 320
°C. The amount of immobilized quaternary ammonium on the CSAC
was 0.957 mmol/g. Continuous cycloaddition of CO<sub>2</sub> to epichlorohydrin
(ECH) was carried out in a packed-bed reactor without using solvent
or cocatalyst. When the reaction conditions were 130 °C and 1.4
MPa, the conversion of ECH and the corresponding turnover frequency
(TOF) were 43.5% and 64.6 h<sup>–1</sup>, respectively. The
selectivity to epichlorohydrin carbonate (ECHC) reached ∼100%.
In biogas upgrading, grafting of quaternary ammonium was demonstrated
to enhance CO<sub>2</sub> capture capacity of the CSAC. The saturated
CO<sub>2</sub> capture capacities of the CSAC and the quaternary ammonium
functionalized CSAC were 1.82 and 2.40 mmol/g at 20 °C and 0.5
MPa, respectively. The adsorption selectivities of CO<sub>2</sub> over
CH<sub>4</sub> were ∼67% and 85% for the CSAC and the supported
quaternary ammonium, respectively. The adsorption heat was 20–30
kJ/mol for the adsorbents. The supported quaternary ammonium also
exhibited a relatively stable cyclability in a packed bed
Development of Coconut Shell Activated Carbon-Tethered Urease for Degradation of Urea in a Packed Bed
Coconut shell activated
carbon (AC)-tethered urease (from jack
bean) was successfully developed to degrade urea in a packed bed reactor.
The loading capacity of urease in AC was 78.8 mg/g. The tethered enzyme
showed a maximum activity at 70 °C and pH 7.2. For higher than
75% of the maximum activity, the tethered urease showed a broader
temperature range of 42–80 °C compared to 45–75
°C for the free enzyme. Similarly, the tethered urease had an
increased stability against the changes of pH. The <i>K</i><sub>m</sub> value of the free urease was 0.271 mol/L and 0.345 mol/L
for the tethered one. This may be caused by the conformational changes
of the enzyme. The <i>V</i><sub>max</sub> values were 0.215
and 0.110 mol/min for the tethered and free ureases, respectively,
which is reflected by an increase in catalytic activity. The catalytic
degradation of urea was performed in a packed bed reactor. The remaining
activity of the tethered urease was over 80% after 50 h of operation
Acute toxicity-associated pathological changes in Wistar rats manifested as atelectasis.
<p>A) The group receiving deltamethrin degradation mixture; B) The control group receiving residual deltamethrin.</p
Delayed toxicity-associated pathological changes occurred mainly in the spleen, including fibrosis and lymphoid tissue hyperplasia.
<p>A) The group receiving deltamethrin degradation mixture; B) The control group receiving residual deltamethrin.</p
One of the main deltamethrin degradation products with the molecular formula of C<sub>13</sub>H<sub>10</sub>O<sub>2</sub>.
<p>One of the main deltamethrin degradation products with the molecular formula of C<sub>13</sub>H<sub>10</sub>O<sub>2</sub>.</p
The survival and death of Wistar rats after treatment of deltamethrin or its degradation products.
<p>√ survival, × death.</p
Percentage of deltamethrin degraded in trypsin-catalyzed reactions.
<p>Percentage of deltamethrin degraded in trypsin-catalyzed reactions.</p
<i>Culex pipiens pallens</i> mosquito mortality rate in standard WHO deltamethrin resistance bioassay.
<p><i>Culex pipiens pallens</i> mosquito mortality rate in standard WHO deltamethrin resistance bioassay.</p
Values of 50% lethal concentration (LC<sub>50</sub>) in Tangkou population of <i>Culex pipiens pallens</i> in response to deltamethrin selection.
<p>*Resistance ratio is the ratio of LC<sub>50</sub> of the test population to LC<sub>50</sub> of the initial parental (G<sub>0</sub>) population.</p
Dynamics of <i>kdr</i> allele frequency in response to deltamethrin selection.
<p><b>A</b>: wildtype L1014 allele frequency was significantly decreased under deltamethrin selection, but significantly increased in the absence of selection; <b>B</b>: L1014F allele frequency was significantly increased under selection, but significantly decreased when no insecticide selection pressure was available; and <b>C</b>: L1014S allele frequency was decreased regardless of deltamethrin selection.</p