Correction: Gasperi et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394
Reference
- Gasperi, J.; Le Roux, J.; Deshayes, S.; Ayrault, S.; Bordier, L.; Boudahmane, L.; Budzinski, H.; Caupos, E.; Caubrière, N.; Flanagan, K.; et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394. [Google Scholar] [CrossRef]
Substance | Abbv. | EQS 1 | n | Quantif. | Q10 | Median | Q90 | Literature 2 | |
---|---|---|---|---|---|---|---|---|---|
Phtalates (µg/L) | dimethyl phthalate | DMP | 38 | 55% | 0.1 | 0.3 | 0.8 | <0.01–0.08 | |
diisobutyl phthalate | DiBP | 36 | 100% | 1.1 | 3.3 | 8.3 | |||
dibutyl phthalate | DBP | 10 | 38 | 100% | 0.6 | 1.3 | 2.8 | <0.05–0.96 | |
dimethoxyethyl phthalate | DMEP | 25 | 76% | 0.1 | 0.8 | 3.7 | |||
di-4-methyl-2-pentyl phthalate | DMPP | 25 | 96% | 0.2 | 0.5 | 4.4 | |||
diethoxyethyl phthalate | DEEP | 25 | 76% | 0.04 | 0.3 | 1.4 | |||
di-n-pentyl phthalate | DPP | 25 | 68% | 0.02 | 0.2 | 2.6 | |||
butylbenzyl phthalate | BBP | 7.5 | 25 | 80% | 0.1 | 0.3 | 0.7 | <0.01–0.08 | |
di-n-hexyl phthalate | DNHP | 25 | 84% | 0.1 | 1.3 | 2.1 | |||
di-2-butoxyethyl phthalate | DBEP | 18 | 94% | 0.1 | 0.7 | 3.5 | |||
dicyclohexyl phthalate | DCHP | 25 | 100% | 0.6 | 1.8 | 6.4 | |||
di-2-ethylhexyl phthalate | DEHP | 1.3 | 37 | 100% | 4.2 | 11.9 | 53.5 | 0.38–78 | |
di-n-octyl-phthalate | DNOP | 23 | 78% | 0.2 | 1.5 | 5.1 | <0.01–1.1 | ||
dinonyl phtalate | DNP | 38 | 74% | 0.1 | 0.5 | 2.4 | |||
Total hydrocarbons (ng/L) | THC | 35 | 100% | 0.2 × 106 | 0.7 × 106 | 2.9 × 106 | |||
PAHs (ng/L) | Naphthalene | Nap | 2000 | 35 | 100% | 10 | 34 | 152 | |
1-methylnaphtalene | 1MN | 35 | 89% | 2 | 9 | 54 | |||
2-methylnaphtalene | 2MN | 35 | 97% | 5 | 18 | 78 | |||
Acenaphthylene | Acyl | 35 | 100% | 10 | 32 | 140 | |||
Acenaphthene | Acen | 35 | 74% | 4 | 11 | 37 | |||
Fluorene | F | 35 | 97% | 5 | 17 | 59 | |||
Anthracene | A | 100 | 35 | 100% | 12 | 45 | 143 | ||
Phenanthrene | PHEN | 35 | 100% | 65 | 162 | 522 | |||
Pyrene | PY | 35 | 100% | 128 | 404 | 1573 | |||
Fluoranthene | Fluo | 6.3 | 35 | 100% | 75 | 302 | 1368 | ||
Benzo(a)anthracene | BaA | 35 | 100% | 24 | 127 | 390 | |||
Chrysene | Chry | 35 | 100% | 39 | 159 | 690 | |||
Benzo(a)pyrene | BaP | 0.17 | 35 | 100% | 23 | 91 | 282 | ||
Benzo(k)fluoranthene | BkF | 35 | 100% | 19 | 68 | 219 | |||
Benzo(b)fluoranthene | BbF | 35 | 100% | 56 | 213 | 837 | |||
Benzo(ghi)perylene | Bper | 35 | 100% | 37 | 166 | 665 | |||
Indeno(1,2,3-cd)pyrene | IP | 35 | 100% | 25 | 113 | 329 | |||
Dibenzo(ah)anthracene | DahA | 35 | 97% | 8 | 47 | 115 | |||
Coronene | Cor | 35 | 100% | 15 | 51 | 429 | |||
∑16 PAH | ∑16 PAH | 35 | 100% | 604 | 2068 | 7481 | 300–6000 | ||
Alkylphenols (ng/L) | Bisphenol A | BPA | 1600 | 38 | 100% | 148 | 513 | 1657 | <200–2500 |
4-tert-octylphenol | OP | 100 | 38 | 100% | 56 | 197 | 780 | 110–1900 | |
Octylphenol-mono-ethoxylate | OP1EO | 38 | 79% | 12 | 31 | 159 | |||
Octylphenol-di-ethoxylate | OP2EO | 38 | 79% | 3 | 8 | 70 | |||
Nonylphenol | NP | 300 | 38 | 100% | 99 | 699 | 3375 | 170–3600 | |
Nonylphenol-mono-ethoxylate | NP1EO | 38 | 100% | 34 | 125 | 668 | |||
Nonylphenol-di-ethoxylate | NP2EO | 38 | 89% | 40 | 141 | 719 | |||
Nonylphenoxy acetic acid | NP1EC | 38 | 100% | 25 | 82 | 447 |
Family | Substance | Acronym | EQS 1 | N | Quantif. | C10 | Median | C90 |
---|---|---|---|---|---|---|---|---|
hexabromocyclododecane (ng/L) | a-hexabromocyclododecane | a-HBCDD | 11 | 91% | 0.9 | 1.4 | 11 | |
b-hexabromocyclododecane | b-HBCDD | 11 | 91% | 0.1 | 0.3 | 1.6 | ||
g-hexabromocyclododecane | g-HBCDD | 11 | 91% | 0.3 | 1.1 | 2.4 | ||
Sum | HBCDD | 1.6 | 11 | 91% | 1.5 | 2.9 | 14 | |
Tetrabromobisphenol A (ng/L) | TBBPA | 260 | 11 | 91% | 0.1 | 0.5 | 1.7 | |
Polybrominated biphenyl ethers (ng/L) | BDE 28 | BDE 28 | Σ6BDE 0.5 | 14 | 79% | 0.02 | 0.05 | 0.1 |
BDE 47 | BDE 47 | 14 | 100% | 0.05 | 0.2 | 0.4 | ||
BDE 100 | BDE 100 | 14 | 93% | 0.02 | 0.1 | 0.1 | ||
BDE 99 | BDE 99 | 14 | 100% | 0.08 | 0.3 | 0.7 | ||
BDE154 | BDE154 | 14 | 71% | 0.02 | 0.1 | 0.1 | ||
BDE 153 | BDE 153 | 14 | 79% | 0.03 | 0.1 | 0.3 | ||
BDE 209 | BDE 209 | 14 | 93% | 3.0 | 20 | 72 | ||
Perfluoroalkyl carboxylic acids (ng/L) | perfluoropentanoic acid | PFPeA | 15 | 40% | 0.40 | 17 | 81 | |
perfluorohexanoic acid | PFHxA | - | 15 | 100% | 0.03 | 0.5 | 22 | |
perfluoroheptanoic acid | PFHpA | 15 | 73% | 0.002 | 0.04 | 15 | ||
perfluorooctanoc acid | PFOA | 15 | 100% | 0.20 | 1.9 | 34 | ||
perfluoronoanoic acid | PFNA | 15 | 67% | 0.05 | 0.2 | 5.4 | ||
perfluorodecanoique acid | PFDA | 15 | 100% | 0.18 | 0.6 | 8.4 | ||
perfluoroundecanoic acid | PFUnA | 15 | 80% | 0.02 | 0.2 | 1.0 | ||
perfluorododecanoic acid | PFDoA | 15 | 93% | 0.10 | 0.4 | 1.4 | ||
Perfluoroalkylsulfonic acids (ng/L) | perfluorobutane sulfonic acid | PFBS | 15 | 20% | 0.01 | 0.05 | 0.41 | |
perfluorohexane sulfonic acid | PFHxS | 15 | 7% | 0.02 | 0.02 | 0.02 | ||
perfluorooctane sulfonic acid, linear isomer | L-PFOS | 0.65 | 15 | 100% | 0.15 | 0.55 | 2.73 | |
perfluorooctane sulfonic acid, sum of branched isomer | Br-PFOS | 15 | 80% | 0.06 | 0.28 | 0.93 | ||
perfluorodecane sulfonic acid | PFDS | 15 | 60% | 0.02 | 0.05 | 0.09 | ||
Perfluorooctane sulfonamide (ng/L) | FOSA | 15 | 80% | 0.02 | 0.1 | 0.6 | ||
Fluorotelomere sulfonates (ng/L) | 4:2 fluorotelomere sulfonate | 4:2 FTSA | 15 | 7% | 0.1 | 0.1 | 0.1 | |
6:2 fluorotelomere sulfonate | 6:2 FTSA | 15 | 80% | 0.6 | 1.8 | 4.0 | ||
8:2 fluorotelomere sulfonate | 8:2 FTSA | 15 | 33% | 0.0 | 0.1 | 0.3 | ||
Benzotriazoles (µg/L) | 1H-Benzotriazole | BT | 7 | 100% | 0.5 | 1.4 | 2.2 | |
4-Methyl- 1H-benzotriazole | 4mBT | 7 | 100% | 0.2 | 1.0 | 1.4 | ||
5-Methyl- 1H-benzotriazole | 5mBT | 7 | 86% | 0.2 | 0.8 | 1.2 |
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Gasperi, J.; Le Roux, J.; Deshayes, S.; Ayrault, S.; Bordier, L.; Boudahmane, L.; Budzinski, H.; Caupos, E.; Caubrière, N.; Flanagan, K.; et al. Correction: Gasperi et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394. Water 2022, 14, 2215. https://doi.org/10.3390/w14142215
Gasperi J, Le Roux J, Deshayes S, Ayrault S, Bordier L, Boudahmane L, Budzinski H, Caupos E, Caubrière N, Flanagan K, et al. Correction: Gasperi et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394. Water. 2022; 14(14):2215. https://doi.org/10.3390/w14142215
Chicago/Turabian StyleGasperi, Johnny, Julien Le Roux, Steven Deshayes, Sophie Ayrault, Louise Bordier, Lila Boudahmane, Hélène Budzinski, Emilie Caupos, Nadège Caubrière, Kelsey Flanagan, and et al. 2022. "Correction: Gasperi et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394" Water 14, no. 14: 2215. https://doi.org/10.3390/w14142215
APA StyleGasperi, J., Le Roux, J., Deshayes, S., Ayrault, S., Bordier, L., Boudahmane, L., Budzinski, H., Caupos, E., Caubrière, N., Flanagan, K., Guillon, M., Huynh, N., Labadie, P., Meffray, L., Neveu, P., Partibane, C., Paupardin, J., Saad, M., Varnede, L., & Gromaire, M.-C. (2022). Correction: Gasperi et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394. Water, 14(14), 2215. https://doi.org/10.3390/w14142215