Table 1.
Overview of reports utilizing surface‐enhanced Raman spectroscopy (SERS) to detect (spiked) nanoplastics (NPs).
NP types[a] |
Sample |
SERS substrate |
Enhancement factor |
Ref. |
---|---|---|---|---|
PS |
Spiked water |
Ag nanoparticles on Si wafer |
Uneven |
|
|
Spiked lake water |
Ag nanoparticles with KI |
2.30×104 [b] |
|
|
Spiked water and sea water |
Ag nanoparticles with NaCl |
4×104 [b] |
|
|
Spiked bottled, tap, and river water |
Nanowell patterned Ag film on SiO2 substrate |
2.3×108 [c] |
|
|
Spiked water |
Ag nanowires on regenerated cellulose |
1.8×107 |
|
PS/PMMA |
Spiked water |
Klarite substrate |
172[b] |
|
PS/PET |
Air |
Klarite substrate |
|
|
PS/PET |
Spiked water |
Au nanoparticles on glass |
445.7[b] |
|
PE |
Bottles and cups under irradiation |
CuO/Ag nanoparticles |
– |
|
PS[d] |
Exposed bivalves |
PS‐coated Au nanostars[d] |
– |
[a] Key: polystyrene (PS), polymethylmethacrylate (PMMA), polyethylene terephthalate (PET). [b] The highest reported, but for one specific particle size. Other particle sizes had lower enhancement factors. [c] Calculated on measurements performed on p‐ATP molecules instead of on the NPs themselves. [d] The plastic and metal particle are the same: PS is grown around a SERS nanostar.