Correction: Gasperi et al. Micropollutants in Urban Runoff from Traffic Areas: Target and Non-Target Screening on Four Contrasted Sites. Water 2022, 14, 394
by
, , , ,
Johnny Gasperi
1,2
,
Julien Le Roux
2
,
Steven Deshayes
3,
Sophie Ayrault
4,
Louise Bordier
4,
Lila Boudahmane
2,
Hélène Budzinski
5,
Emilie Caupos
2,
Nadège Caubrière
1,
Kelsey Flanagan
3,6,
Martin Guillon
1,
Nina Huynh
2,
Pierre Labadie
5,
Laurent Meffray
7,8,
Pascale Neveu
9,
Chandirane Partibane
3,
Julien Paupardin
10,
Mohamed Saad
3,
Lucie Varnede
7,11 and
Marie-Christine Gromaire
3,* 1
GERS-LEE, Université Gustave Eiffel, IFSTTAR, F-44344 Bouguenais, France
2
Leesu, Université Paris Est Creteil, Ecole des Ponts, F-94010 Creteil, France
3
Leesu, Ecole des Ponts, Université Paris Est Creteil, F-77455 Marne-la-Vallee, France
4
LSCE-IPSL, UMR 8212 (CEA/CNRS/UVSQ), Université Paris-Saclay, F-91191 Gif-sur-Yvette, France
5
UMR 5805 EPOC, CNRS, Université de Bordeaux, F-33400 Talence, France
6
Urban Water Engineering, Department of Civil, Environmental and Natural Resources Engineering, Luleå University of Technology, S-971 87 Luleå, Sweden
7
CEREMA, Equipe de Recherche Team, 12 Rue Teisserenc de Bort, F-78190 Trappes, France
8
Aquatycia 7/9ter Rue Parmentier, F-94140 Alfortville, France
9
STEA, Ville de Paris, F-75000 Paris, France
10
DEA, Conseil Départemental de la Seine St Denis, F-93110 Rosny-sous-Bois, France
11
Ecovegetal, Les Grandes Pieces, F-28410 Broue, France
*
Author to whom correspondence should be addressed.
Water 2022, 14(14), 2215; https://doi.org/10.3390/w14142215
Submission received: 14 June 2022
/
Accepted: 22 June 2022
/
Published: 14 July 2022
(This article belongs to the Special Issue Research on Urban Runoff Pollution)
In the original publication [1], there were mistakes in Tables 6 and 7 as published. In Table 6, the values given in the table for Q10, the median and Q90 of alkylphenols (last seven lines of the tables) were shifted by one line and, thus, were not associated with the right compound. In Table 7, the values given in the table for Q10 of polybrominated biphenyl ethers (BDE 28 to BDE 153) were shifted by one line and, thus, were not associated with the right compound. The corrected Table 6 and Table 7 appear below.
The authors apologize for any inconvenience caused and state that the scientific conclusions are unaffected. This correction was approved by the Academic Editor. The original publication has also been updated.
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]
Table 6.
Organic micropollutants (group 3) analyzed in the runoff, quantification frequency and range of quantified total EMC concentrations.
Table 6.
Organic micropollutants (group 3) analyzed in the runoff, quantification frequency and range of quantified total EMC concentrations.
| 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 | |||
1 EQS: Environmental Quality Standard, annual average value for the total phase, European regulatory value 2013/39/UE or–in italics-INERIS calculated guidance value for the protection of freshwater pelagic organisms from chronic ecotoxicity (https://substances.ineris.fr, accessed on 16 December 2021), 2 Literature = range of EMCs measured in roads and parking lots [20,22,29,31].
Table 7.
Organic micropollutants (groups 4 and 5) analyzed in the runoff, quantification frequency and EMC total concentrations.
Table 7.
Organic micropollutants (groups 4 and 5) analyzed in the runoff, quantification frequency and EMC total concentrations.
| 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 | ||
1 EQS: Environmental Quality Standard, annual average value for the total phase, European regulatory value 2013/39/UE (2008/105/UE for Σ6BDE) or—in italics—INERIS calculated guidance value for the protection of freshwater pelagic organisms from chronic ecotoxicity (https://substances.ineris.fr, accessed on 16 December 2021).
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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
AMA Style
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
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