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