Table 5.
Comparison between the results of this study and other studies (MPs abundance, dominant MPs, and MPs type).
References | Origin | Salt type | No of salt brand | MP abundance (MP/kg) | MP identification technique |
Filter pore size (μm) |
Dominant MP types |
Human intake (MPs capita− 1 Salt yr− 1) |
|
---|---|---|---|---|---|---|---|---|---|
Shape | Polymer | ||||||||
(Yang et al., 2015) | China | Sea salt Lake salt Rock/well salt |
5 | 550–681 | Visual/FTIR | 100–200 | Fiber | PET > PE > cellophane | - |
(Karami et al., 2017) | 6 countries | Sea salt | 15 | 0–10 | Raman | 149 | Fragment | PP, PE, poly-acrylonitrile | 37 |
2 countries | Lake salt | 2 | 0 | ||||||
(Renzi et al., 2019) | Italy, Croatia | Sea salt | 11 | 1570–39,800 | Visual | 0.45 | Fragment for Italy Fiber for Croatia |
- | 36.5–36,172 |
(Seth and Shriwastav, 2018) | India | Sea salt | 8 | 56–103 | μ-FTIR | 0.45 | Fragment | PES, PE, PA | 188 |
(Kim et al., 2018) | 16 countries | Sea salt | 28 | 0–13,629 | 0–13,629 | 100–500 | Fragment | PE > PP > PET | - |
(Lee et al., 2019) | 6 countries | Sea salt | 10 | 2.5–20 | μ-FTIR | 5 | Fragment | PP, PE, PS | 35.8 |
Thailand | Rock salt | 1 | 12.5 | Fragment | PP | ||||
(Lee et al., 2021) | Korea | Sea salt | 1 | 2395 | μ-FTIR | 20 | Fragment | PP, PE | 12,000 |
(Sharifi and Movahedian Attar, 2021) | Iran | Crystallized salt | - | 151.4 ± 48.8 | Micro-Raman | 0.45 | Fiber, Fragment | PP, PE, PET | - |
Refined sea salt | 406.7 ± 93.3 | ||||||||
Unrefined sea salt | 1288.6 ± 184.9 | ||||||||
Rock salt | 283.4 ± 97 | ||||||||
(Nakat et al., 2023) | Lebanon | 16 | 0–635.2 | FTIR | 0.7 | - | PP, PS, PE, thermoplastic elastomers | 2372 | |
(Özçifçi et al., 2023) | Turkey | Sea salt Lake salt Rock salt |
36 | 39 ± 30 | FTIR | fiber, granulated, film | CPE | 150 | |
This study | Iran | Sea salt | 13 | 700–4248 | > 100 (FTIR) < 100 (Micro-Raman) |
0.45 | Fragment, Fiber | CA, PE, PS, PP, ABS, PET | - |
Rock salt | 13 | 760–2368 | |||||||
Bulk salt | 8 | 726–2196 | |||||||
Non-standard | 6 | 720–5470 |