BAID - China is dedicated to addressing the increasingly severe issue of
microplastic contamination in bottled water and beverages. We have developed
an eco-friendly and efficient biobased filtration membrane using synthetic
biology methods, which can achieve over 90% microplastic removal. This
groundbreaking filtration device is specially designed to fit onto
environmentally friendly and renewable materials used in bottle caps. It is
expected to be available for mass production at a price not exceeding $0.25
per unit, with an estimated reuse capacity of 20-30 times.
In addition, we have introduced a calculator program to help consumers
estimate their daily intake of microplastics. This tool aims to raise
awareness about microplastic ingestion, encouraging individuals to reduce
their reliance on plastic products in their daily lives.
For the biobased filtration membrane, we employ bacterial cellulose as the
cellulose matrix. To enhance adsorption efficiency, we first engineer oat
proteins into the cellulose matrix using cellulose-binding modules (CBMs). We
have created a triblock structure component called "CBM3-Globulin-CBM3" to
strengthen the binding between cellulose and oat proteins. This combination
forms the foundational membrane for filtering microplastics, along with
CBM3-OP-CBM3 composite proteins. Furthermore, we tested the addition of
substances like APT, tannic acid, and catechins to increase microplastic
adsorption sites on the membrane. In microplastic removal efficiency tests, we
utilize a microscopic Raman spectrometer to characterize the composition
(types) of microplastics in water. We have pioneered an AI-based algorithm for
high-precision microplastic counting in drinking water.
For the bottle cap structure, we experimented with using a common agricultural
waste, sugarcane bagasse. We combined cellulose microfibers and lignin
extracted from sugarcane bagasse to create an alternative material for bottle
caps, replacing traditional plastic materials. Surface treatment with sodium
alginate and calcium lactate made the bottle caps waterproof and resistant to
deformation. We manufactured the mentioned bottle cap structures using 3D
printing technology and mold methods, reducing individual bottle cap
production costs to only 0.2% of traditional machining methods.
We hope our product will become an effective alternative to plastic bottle
caps in the bottled water market, potentially reducing the production and
usage of billions of plastic bottle caps each year and lowering consumer
microplastic ingestion by 40%-60%.
Target 1: Production of Oat Protein
Design
Oat protein is a globulin extracted from byproducts of processing oat
β-glucans. In recent years, oat β-glucans have gained prominence due to
their health benefits in reducing blood cholesterol and regulating blood
sugar levels. Consequently, they have been incorporated into 76 different
health-related components in food and cosmetics. Oat protein is favored
for its low cost and environmental sustainability.
The decision of taking oat protein as an additive is grounded in the
research conducted by Wang and colleagues in 2021. Their study reported
that oat protein sponges exhibited a removal efficiency of 75% to 82% for
PS particles (a form of microplastic). Their model indicated that the
binding sites for these microplastics on the sponges are likely
hydrophobic interactions between protein side chains and the phenyl rings
on PS. Considering that they primarily produced oat protein hydrogels
through chemical cross-linking and subsequently created oat protein
sponges through liquid nitrogen freezing and freeze-drying, a process that
minimally affects the protein's side chain groups, we theorize that oat
protein possesses the necessary characteristics for adsorbing
microplastics. Therefore, we have chosen to incorporate it into our
biomaterials.
Build
Using the method proposed by Wu et al. in 1977, oat flour, which had been
defatted using n-hexane and sifted to remove bran, was subjected to multiple
centrifugation cycles and freeze-dried to obtain oat protein powder (as
elaborated in the notebook).
Test
We conducted SDS-PAGE experiments on the extracted proteins, with results
shown in the figure above. The result revealed prominent bands at 22kDa,
32kDa, and 55kDa, which is consistent with the research conducted by
Shotwell et al. in 1900. Their research identified that oat protein 12S
comprises two subunits of 22kDa and 32kDa, which would be separated during
electrophoresis. The presence of a band near 55kDa suggests the existence of
7S proteins, while other bands correspond to other proteins. Consequently,
it can be inferred that the extracted oat protein exhibits a purity ranging
from 60% to 70%, which is within the normal and slightly higher range.
Learn
Through this engineering cycle, a convenient method for oat protein
extraction has been successfully proposed and validated using readily
available materials. Additionally, the corresponding part, BBa_K4714002, have been created, allowing future teams to easily choose different
methods for oat protein extraction as per their experimental requirements.
Notably, oat protein has remained unexplored in previous iGEM teams. Owing
to its pertinent attributes and straightforward extraction, oat protein
holds great potential as a research focus for future teams in the fields of
nutrition, agriculture, and related disciplines.
Target 2: Oat Protein as an Additive to the Base
Target 2.1 Maillard reaction
Design
To assess the impact of oat protein(OP) on the filtration efficiency and
determine the optimal ratios, the following experimental groups were
established. This section will focus on the first five groups.
Index
Base
Additive
1
BC Only
2
OP only
3
BC
OP concentration 1
4
BC
OP concentration 2
5
BC
OP concentration 3
6
BC
CBM3-CBM3
7
BC
CBM3-OP-CBM3
Table 1: Experimental groups for the Maillard reaction
The first and second groups serve as control groups. BC membranes were
prepared by vacuum filtering BC suspensions in the first group. The second
group, on the other hand, involved the production of a hydrogel using oat
protein powder and then freeze-dried, creating a structure akin to the oat
protein sponge mentioned prior in the work of Wang et al, 2021.
The Maillard reaction occurs when proteins and carbohydrates are mixed at
elevated temperatures (Kim & Lee, 2008). For instance, Lii, Chen, Lu, and
Tomasik (2003) reported the formation of covalently bonded CMC-casein
complexes via electrosynthesis. These complexes exhibit exceptional stability
in response to changes in pH and ionic strength, alongside excellent
emulsification properties and thermal stability. Hence, the approach taken
here involves the incorporation of oat protein into BC through the Maillard
reaction, using a simple blending process. Blending is an effective method for
polymer modification, with strong economic incentives, as it imparts enhanced
properties to polymers through conventional processing techniques. After
pouring the blended solution onto stainless-steel plates coated with an
anti-sticking agent, then drying at 50 degrees Celsius for 5 hours in a drying
oven, the membrane can be readily separated from the stainless-steel plate.
Build
To determine the optimal dosage of oat protein, a ratio gradient was set
while preparing the oat protein solution: 5 wt%, 10 wt%, and 15 wt%. The
first five groups were prepared based on the experimental process detailed
in the notebook.
Test
The experimental groups with varying concentrations of oat protein were
tested for their microplastic filtration ability using the method described
on our measurement page (link). A microplastic suspension for standardizing
the filtration efficiency test was prepared by diluting PS microspheres with
diameters of 100nm, 1μm, 5μm, and 10μm. Following measurements, it was
determined that the optimal ratio for oat protein was 15wt%.
Learn
[Technical Iteration]
Maillard Reaction Round 1
Problem 1: There’re visible cavities on the protein membrane surface, suspected
to be a result of bubbles introduced during the stirring process, becoming
apparent during pouring. This phenomenon undoubtedly compromises the filtration
effectiveness of the membrane.
Problem 2: The mechanical properties of the protein membrane are
suboptimal. While it can withstand the pressure exerted by water flow, it
is relatively fragile, posing challenges in industrial operational
settings.
Maillard Reaction Round 2
Problem 1 Resolved: Vacuum degassing was performed before pouring the solution
onto stainless steel plates. In cases where this process proved inefficient,
brief ultrasonication (10-20 minutes) was introduced. As a result, no longer
were holes observed on the second batch of membranes due to bubble formation.
Problem 2 Resolved: By incorporating some AR (analytical reagent) level
glycerol into the membrane, substantial enhancements were achieved in the
mechanical properties of the membrane, particularly in terms of increased
tensile strength.
Target 2.2 Cellulose Binding Module (CBM)
Design
Wet Lab Design
The cellulose-binding module (CBM) is a specific region on certain
cellulase enzymes comprised of amino acids with aromatic residues
(tyrosine or tryptophan). These residues establish firm bonds with
cellulose chains through van der Waals interactions (Perez & Samain,
2010). CBMs have found extensive and enduring application in the design
and modification of protein-polysaccharide composites (Lapidot et al.,
2012). In our experiment, we employed CBM3 from Ruminiclostridium
thermocellum (Protein Data Bank (PDB) accession: 1NBC). This component was
initially proposed by LinksChina 2021. Previously, the Imperial College
2014 team used the cellulose-binding domain, BBa_K1321356, individually as an additive to enhance the adsorption of heavy metal
pollutants by bacterial cellulose membranes. Moreover, research by
Mohammadi et al. in 2019 indicated that CBM3-CBM3 dimers, when binding to
cellulose, exhibited greater mechanical strength and pressure tolerance
compared to CBM3 monomers combined with cellulose. Therefore, CBM3-CBM3
was designed and expressed for testing CBM3's adsorption capabilities.
Furthermore, due to the special structure of CBM3 - featuring regions with
affinity for both cellulose and proteins, it can emulate the function of
natural cellulose cross-linkers. This ability ensures them to secure
various proteins onto cellulose to produce cellulose-CBM and fusion
protein composites. The "triblock protein architecture" model proposed by
Mohammadi et al., involving CBM, functional proteins, and bacterial
cellulose, provides a pathway for manufacturing highly adjustable
composite materials. In our project, we adapted this binding pattern,
substituting spider silk proteins with oat proteins. This approach retains
the adsorption sites on oat protein side chains while introducing the CBM3
component, thereby maximizing the efficiency of microplastic adsorption.
In the study, we designed the amino acid sequences of CBM3-CBM3 and
CBM3-Globulin-CBM3 fusion proteins, and reverse-translated and
codon-optimized their expression sequences based on the Escherichia coli
codon usage. Prior to assembling the expression sequences, we conducted
transmembrane region prediction, hydrophobicity analysis, and disorder
analysis on the designed sequences. After confirming that the designed
sequences met the desired criteria, the sequences were synthesized. The
synthetic sequences were then introduced into the pET28a vector using
BamHI-HindIII restriction ss sites for plasmid construction. The
constructed plasmid was subsequently introduced into Escherichia coli
strains for induction expression.
Following the completion of plasmid assembly, we performed protein
purification using a His tag and conducted preliminary analysis of
expression results through SDS-PAGE electrophoresis. Furthermore, although
CBM3 has been confirmed for soluble expression in Escherichia coli on
multiple occasions, the solubility expression of oat 11S globulin, which
has been less studied, remains unknown. Even if the oat 11S globulin
itself exhibits good solubility expression, it is uncertain whether the
fusion protein will alter this desirable characteristic. Therefore, we
induced expression in modified bacterial strains and conducted soluble
expression analysis on their protein products, obtaining a solubility
result of 0.8504. This further confirms the utility of the designed fusion
protein.
Build
Tsingke Biotech used Escherichia coli TOP10 to synthesize the designed
plasmid, and helped us with protein expression and purification. The
obtained proteins were used for further experimental analysis.
Test
The experimental group that only contains CBM3-CBM3 and BC achieved a
removal efficiency of 79.77% for the microplastic mixture. In the group
containing OP (CBM3-OP-CBM3), the removal efficiency increased to 91.70%.
This result aligns with the outcomes of computer simulations, suggesting
that specific functional groups on the target protein's side chains, as well
as its isoelectric characteristics, may facilitate electrostatic and
hydrophobic interactions with microplastics, enhancing the adsorption of
composites to microplastics. The increase in adsorption efficiency proves
the effectiveness of our system.
Learn
To evaluate the interaction between proteins and membranes, an Energy Dispersive
Spectrometer (EDS) analysis was conducted on samples containing BC+Oat membrane,
BC membrane, and BC+CBM-Globulin-CBM+APT membrane. The obtained results demonstrated
the occurrence of nitrogen in both BC+Oat membrane and BC+CBM-Globulin-CBM+APT
membrane, with a measured nitrogen content of 10.8%wt. In contrast, the absence
of nitrogen in the BC membrane confirmed the successful binding of proteins to
the membrane.
Target 3: APT as an Additive to the Base
Design
Attapulgite (APT), a low-cost and abundant clay mineral, exhibits a porous,
rod-shaped crystalline structure, a large surface area, and high cation adsorption
capacity. It is frequently employed in anti-diarrheal medications (Haden et
al., 1967). Research has demonstrated that BC-APT membranes (BAM) produced
by combining APT with bacterial cellulose possess excellent microplastic adsorption
capabilities (Zhang et al., 2023). The irregular, randomly distributed clusters
formed by BC nanofibers crosslinked with APT bundles increase water flux, generating
an abundant and uniform pore structure ideal for microplastic filtration (see
figure). Furthermore, microplastics in water experience a repulsive effect
with APT as they pass through the membrane due to their weak negative charge,
preventing PS particles from entering the membrane pores. This allows the solvent
in the filtrate to pass through, maintaining a high flux for BAM during water
filtration.
Therefore, we aimed to add APT as an additive to the base membrane for its
superior effect. Since a relatively toxic crosslinking agent was used
during the production process of BAM, 3-aminopropyl triethoxysilane, the
actual application of APT as a necessary component is still under
consideration. However, the wide-spread application of 3-aminopropyl
triethoxysilane in tissue engineering and other areas that requires no
toxicity and the toxicity test performed in both literature and our wet
lab proves the little effect of APT under the BAM circumstance.
Build
BAM membranes were fabricated using the method described by Jiang et al.,
2023. In essence, they were prepared through vacuum filtration of a
mixture of BC and APT, followed by in-situ crosslinking.
Firstly, a pre-treatment of APT was conducted. APT was placed in ultrapure
water, stirred, and allowed to settle for 8 hours, resulting in the
collection of fine particles in the intermediate layer. The obtained APT
was then acidified in HCl, and the mixture was subjected to
ultrasonication for 30 minutes to ensure the removal of any internal
organic matter. Subsequently, the APT was ultrasonically washed in
ultrapure water until the wash solution reached a neutral pH. Finally, it
was dried and sieved.
The BC-APT membrane was prepared by vacuum-assisted filtration of a BC/APT
suspension onto a PVDF membrane. Typically, a specific quantity of APT
powder and 3-aminopropyltriethoxysilane were added to the BC suspension,
and the mixture was sonicated for 30 minutes. The suspension was then
vacuum-filtered, and the resulting composite membrane was dried at ambient
temperature with an APT weight ratio of 5% to the BC.
Test
Characterization
Characterization of BAM was conducted using scanning electron microscopy
(SEM). Fiber structures highly resembling those reported by Jiang et al.
were observed, providing partial confirmation of the successful production
of BAM.
Toxicity Test
Due to the addition of 3-aminopropyltriethoxysilane in the production of
BAM, a commonly used chemical cross-linker in tissue engineering and
materials science, it can immobilize functional molecules on various
materials but carries some toxicity and environmental impact. In order to
investigate the potential toxicity of MPs/NPs on water quality after
filtration, acute toxicity tests were conducted using D. magna Straus as a
model organism. D. magna Straus was cultured for 1 to 3 generations, and
individuals aged between 6 hours and 24 hours were selected for the
experiment, with 10 water fleas in each group. Filtrate from BAM
filtration was used for the toxicity tests, and water was used as a
control. Each group was exposed in triplicate, and the water fleas were
maintained under starvation conditions during the experiment. Monitoring
was carried out at 24 and 48 hours to determine the number of water fleas
exhibiting activity inhibition (including mortality) as an indicator of
the toxicity of the experimental solution.
The data from the four experimental groups were analyzed, and the results
are presented in the table and graph.
A two-way ANOVA analysis was conducted on the data related to D. magna
Straus activity inhibition. The analysis revealed a p-value of 0.896 for
the interaction between D. magna Straus activity and BAM filtrate
treatment. This p-value does not reach statistical significance at the
alpha level of 0.05. Therefore, there is no statistically significant
difference in the activity of D. magna Straus between the two groups,
confirming that BAM filtrate is not toxic or exhibits minimal toxicity.
Removal Efficiency
The measured removal efficiency of BAM for the MP mixture was 96.17%,
while Jiang et al. reported an efficiency of 99.81%. The discrepancy
between these results may stem from slight human errors, or it could also
be attributed to the use of a broader range of PS microspheres in our MP
suspension (Jiang et al. employed 100nm, 0.5μm, and 1μm PS microspheres,
whereas we used microspheres with diameters of 100nm, 1μm, 5μm, and 10μm).
However, overall, the observed filtration effectiveness of BAM for
microplastics is excellent. This suggests that APT, as the sole additive
on the BC membrane, plays a primary role in enhancing filtration
performance.
Learn
Toxicity Testing Round 1
Problem: D. magna Straus, when cultured under normal conditions, did not survive
for unknown reasons.
Toxicity Testing Round 2
Problem Resolved: By introducing a culture medium for green microalgae and
regularly changing the culture medium, there was a significant increase in
the reproduction rate of D. magna Straus. From 3 newborn D. magna Straus individual
per day for every 10 individual group, to up to 15 newborn D. magna Straus
individual per day for every 10 individual group.
Toxicity Testing Round 3
Reflection: D. magna Straus, as a simple planktonic crustacean, have limited
representativeness in toxicity tests. In the future, it will be necessary to
conduct toxicity testing using human tissue cells or other models that better
mimic real-life scenarios. The reason for not using these cells is the lack
of suitable laboratory conditions and animal testing certification.
Target 4: Production of the Support structure
4.1 Composition of the Support Structure-- Cellulose-Lignin Reinforced
Composites
Design
Inspired by the principle of cellulose and lignin reinforcement found in
natural wood, we developed all-natural, biodegradable, strong, and
water-stable cellulose-lignin reinforced composites by integrating lignin
into micro-nanocellulose fibers as a replacement for plastic. Following
the method described in [Reference], the cellulose-lignin composite
consists of approximately 74 wt% cellulose fibers (a blend of cellulose
microfibers and nanofibrillated cellulose (NFC) for cost-efficiency and
mechanical performance balance) and approximately 26 wt% uniformly mixed
lignin powder, forming a wet film. The lignin content closely resembles
that of natural wood. The untreated fragments of natural wood still
maintain the intrinsic bonding between lignin and cellulose, which is
somewhat unfavorable for achieving high mechanical performance and water
resistance. Therefore, the use of commercially available cellulose
microfibers, nanofibers, and lignin components allows us to chemically
process and rebuild the cellulose-lignin reinforced composite structure,
thus achieving high mechanical performance and water stability in the
resulting support structure.
Left: extracted cellulose microfibers
Right: water stability experiment of composite (Wang et al, 2021)
To demonstrate the superior mechanical strength and water stability of
cellulose-lignin reinforced composite materials, we further fabricated
drinking straws from this wet film, followed by baking in an oven at
150°C. Due to the abundant hydroxyl groups in cellulose molecular chains
and lignin, hydrogen bonds are readily formed between cellulose fibers and
lignin during the drying process. Consequently, the newly formed hydrogen
bonds between cellulose fibers and lignin effectively adhere to the edges
of the film without the need for additional additives. Baking at
temperatures higher than the glass transition temperature of lignin allows
molten lignin to penetrate the pores of cellulose fibers, forming a
permeable and dense structure.
Outstanding mechanical performance due to crosslinking between cellulose
and lignin.
High water stability resulting from the hydrophobic nature of lignin.
Cost-effectiveness.
Biodegradability, offering potential as an environmentally friendly
alternative to petroleum-derived plastic straws.
Cellulose fibers have a high degree of hydrophilicity due to the presence
of numerous active hydroxyl groups on their surfaces. As a result, water
molecules penetrate the dense hydrogen bond network, causing it to expand
and subsequently reducing mechanical strength, resulting in insufficient
wet strength. To improve the user experience, we chose to introduce a thin
layer of sodium alginate to the surface of the support structure, which
was then converted into calcium alginate. As an edible natural
polysaccharide polymer, sodium alginate can infiltrate the pores of the 3D
nanoscale cellulose network. Both cellulose and alginates are
polysaccharides with many hydroxyl groups on their surfaces, which implies
that a considerable number of hydrogen bonds can be formed at the
interface, resulting in a strong connection. The addition of alginates,
along with the penetration of lignin, constitutes two steps that increase
the adhesion at the support structure joints, thus avoiding the use of
chemical adhesives commonly found in other biomaterials like paper straws.
Compared to paper and plastic, cellulose-lignin reinforced composite
materials can simultaneously achieve high water stability and
biodegradability.
Build
According to the designed methods and plans, two components were produced:
Composite material thin rectangular prisms used for performance testing.
Real bottle cap structures prepared using molds and baking.
Test
Due to a lack of the required equipment for mechanical performance
testing, we were unable to conduct three-point bending tests or other
mechanical tests on the support structures. However, literature mentions
that the tensile strength of cellulose-lignin reinforced composite
material (75.2 MPa) is 1.88 times higher than that of plastic straw
materials (40.0 MPa), replacing the original plastic components with the
support structures. Therefore, it is reasonable to assume that the
increased waterproofing, due to the surface treatment, should result in
superior performance compared to the literature.
Learn
Surface Treatment Round 1 Issue: During the first immersion test (without
surface treatment, only baking), we observed noticeable darkening and slight
expansion in the portions of contact with water. After an internal team
discussion, it was unanimously agreed that this may reduce the user's
experience and trust in the product. Surface Treatment Round 2 Issue
Resolved: By conducting further literature research, we discovered a surface
treatment technique originally used for producing BC-based straws. We
applied this technique to our composite materials and achieved positive
results. Surface Treatment Round 3 Reflection: Due to equipment and time
constraints, detailed performance testing has not been conducted yet. This
aspect will need to be addressed in the future.
The production of the Mold
Design
The original plan was to use stainless steel molds for the most precise
control of microplastic contamination. However, due to cost constraints
(creating a stainless steel mold from scratch costs nearly 10,000 RMB or
approximately 1,370 dollars), we decided to use 3D printed heat-resistant
flexible nylon molds to produce the support structures. As shown in the
figure above, the envisioned support structures were modeled using Blender
and SolidWorks, and the initial drawings were used for test printing.
Construction and Testing
Initially, common 3D printing material PLA (in pink) was used to print
plastic support structures to test the size compatibility between
different components. After three rounds of test printing and adjustments,
the dimensions at the bottle neck thread were modified to ensure a perfect
fit with the threads commonly found on bottled water in the Chinese
market, and to prevent water leakage when inverted, ensuring a good seal.
Once the final dimensions for the support structures were confirmed,
SolidWorks was used for the mold design. Elastic molds made of nylon were
then printed to facilitate demolding of threaded structures.
Learning
Mold Design Reflection:
Given the constraints of time, cost, and technical capabilities, the mold
design currently in use is relatively simple and rough. To explore the
industrial application of Plasticlear, it will be essential to investigate
methods for demolding molds with internal threads using stainless steel
molds, which are rigid and lack elasticity.
Summary
Through the engineering cycles described above, we successfully produced all
the components of Plasticlear, assembled them, and ultimately, the
experimental results confirmed the feasibility of our theoretical design and
the outstanding filtration performance of Plasticlear.
It is evident that as a high school student team, there are still many areas
in the industrial application phase that require improvement. However, for
each part involved, we conducted a complete engineering cycle to test the
component's usability and continuously enhance its overall performance.