ADSORPTION KINETICS OF LOW MOLECULAR WEIGHT POLYCYCLIC AROMATIC HYDROCARBONS ONTO PHENYL ACETIC ACID MODIFIED BIOSILICA FROM CYCLOTELLA STRIATA TBI DIATOM
Low molecular weight (LMW) polycyclic aromatic hydrocarbons (PAHs), such as phenanthrene, anthracene, and fluorene, are volatile, carcinogenic, and highly toxic. One of the methods to concentrate and purify LMW PAHs as a pre-concentration stage of samples from polluted environments is the adso...
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Format: | Final Project |
Language: | Indonesia |
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Online Access: | https://digilib.itb.ac.id/gdl/view/81568 |
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Institution: | Institut Teknologi Bandung |
Language: | Indonesia |
Summary: | Low molecular weight (LMW) polycyclic aromatic hydrocarbons (PAHs), such as
phenanthrene, anthracene, and fluorene, are volatile, carcinogenic, and highly toxic. One of
the methods to concentrate and purify LMW PAHs as a pre-concentration stage of samples
from polluted environments is the adsorption method. Biosilica is a biosorbent from
diatomaceous microalgae that has the potential to be used as a PAH adsorbent because it has
a large surface area and can be modified with hydrophobic groups that can interact with LMW
PAH. In this study, biosilica was extracted from the diatom Cyclotella striata from Teluk
Bidadari Indonesia (TBI), and then activated to add silanol groups on its surface, and
subsequently modified with phenyl acetic acid as a hydrophobic compound that can interact
with LMW PAH. Furthermore, phenyl acetic acid-modified biosilica was characterized and
evaluated in terms of adsorption performance as anthracene, phenanthrene, and fluorene
adsorbent. Extraction of biosilica from biomass by nitric acid oxidation followed by
calcination at 550 °C resulted in pure biosilica. Biosilica extraction was successfully carried
out with a productivity of 2 grams of biosilica for every 100 grams of Cyclotella striata
biomass. The FTIR spectrum of activated biosilica showed an increase in the intensity of the
Si-OH peak at wavenumber 960 cm-1
. Meanwhile, the FTIR spectrum of phenyl acetic acidmodified biosilica indicates the presence of new groups in the sample, compared to pure
biosilica, namely the C=O group absorbing at 1700 cm-1 and C-H at 1400 cm-1
. This indicates
that the modification of biosilica with phenyl acetic acid has been successfully carried out.
The adsorption kinetics study of anthracene, phenanthrene, and fluorene on pure biosilica and
phenyl acetic acid modified biosilica followed a pseudo second-order kinetics model. Based
on the kinetic model, the modified biosilica had higher adsorption capacity compared to pure
biosilica towards anthracene (73.7 vs. 60.6 mg/g), phenanthrene (66.7 vs. 51.6 mg/g), and
fluorene (57.7 vs. 40.2 mg/g). Phenyl acetic acid modification slowed down the adsorption
process of anthracene and fluorene on biosilica, indicated by a smaller initial adsorption rate
compared to pure biosilica. Despite the decrease in adsorption rate, the adsorption half-time
of modified biosilica is still quite low, indicating that adsorption still occurs rapidly (3.5–6.5
minutes). Adsorption kinetics modeling with the Weber-Morris intraparticle diffusion model
shows that the LMW PAH adsorption process on pure biosilica is limited by three rate-limiting
steps, in contrast to modified biosilica which is only limited by two rate-limiting steps. |
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