The recycling of post-industrial waste poly(lactic acid)
(PI-PLA)
from coffee machine pods into electroanalytical sensors for the detection
of caffeine in real tea and coffee samples is reported herein. The
PI-PLA is transformed into both nonconductive and conductive filaments
to produce full electroanalytical cells, including additively manufactured
electrodes (AMEs). The electroanalytical cell was designed utilizing
separate prints for the cell body and electrodes to increase the recyclability
of the system. The cell body made from nonconductive filament was
able to be recycled three times before the feedstock-induced print
failure. Three bespoke formulations of conductive filament were produced,
with the PI-PLA (61.62 wt %), carbon black (CB, 29.60 wt %), and poly(ethylene
succinate) (PES, 8.78 wt %) chosen as the most suitable for use due
to its equivalent electrochemical performance, lower material cost,
and improved thermal stability compared to the filaments with higher
PES loading and ability to be printable. It was shown that this system
could detect caffeine with a sensitivity of 0.055 ± 0.001 μA
μM–1, a limit of detection of 0.23 μM,
a limit of quantification of 0.76 μM, and a relative standard
deviation of 3.14% after activation. Interestingly, the nonactivated
8.78% PES electrodes produced significantly better results in this
regard than the activated commercial filament toward the detection
of caffeine. The activated 8.78% PES electrode was shown to be able
to detect the caffeine content in real and spiked Earl Grey tea and
Arabica coffee samples with excellent recoveries (96.7–102%).
This work reports a paradigm shift in the way AM, electrochemical
research, and sustainability can synergize and feed into part of a
circular economy, akin to a circular economy electrochemistry.
day life. However, managing the endof-life of plastic materials has become an increasingly urgent topic due to the reliance of most virgin plastics production on non-renewable resources like oil, and the significant, harmful effects that environmentally persistent waste plastic can have on the natural world. [1] Limiting these effects requires consumption of virgin plastic to be reduced wherever possible, and where not possible, plastic waste should be recycled into new products such that it does not enter traditional waste streams (e.g., by being sent to landfill). With regards to plastics recycling, the ideal situation is one in which innovation facilitates "upcycling" of plastic waste into products that retain high value and longevity, such that the material flow from raw material to waste product is slowed significantly. [2] Seeking upcycling in this way can be especially effective when incorporated into Circular Economy (CE) practices; [2] while the precise definition of CE has not been formalized, in broad terms, it is a new economic model intended to cause a sea change in the way society approaches sustainable development. [3] Additive Manufacturing (AM), otherwise known as 3D
The production of electrically conductive additive manufacturing feedstock from recycled poly(lactic acid) (rPLA), carbon black (CB), and bio-based plasticiser castor oil is reported herein. The filament was used to print...
Changing the connection length of an additively manufactured electrode (AME) has a significant impact on the electrochemical and electroanalytical response of the system. In the literature, many electrochemical platforms have been produced using additive manufacturing with great variations in how the AME itself is described. It is seen that when measuring the near-ideal outer-sphere redox probe hexaamineruthenium (III) chloride (RuHex), decreasing the AME connection length enhances the heterogeneous electrochemical transfer (HET) rate constant (k0) for the system. At slow scan rates, there is a clear change in the peak-to-peak separation (ΔEp) observed in the RuHex voltammograms, with the ΔEp shifting from 118 ± 5 mV to 291 ± 27 mV for the 10 and 100 mm electrodes, respectively. For the electroanalytical determination of dopamine, no significant difference is noticed at low concentrations between 10- and 100-mm connection length AMEs. However, at concentrations of 1 mM dopamine, the peak oxidation is shifted to significantly higher potentials as the AME connection length is increased, with a shift of 150 mV measured. It is recommended that in future work, all AME dimensions, not just the working electrode head size, is reported along with the resistance measured through electrochemical impedance spectroscopy to allow for appropriate comparisons with other reports in the literature. To produce the best additively manufactured electrochemical systems in the future, researchers should endeavor to use the shortest AME connection lengths that are viable for their designs.
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