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  "alternate_identifier": "DOI: 10.3389/fmars.2021.697424",
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  "author": "Vega-Herrera, A., Llorca, M., Savva, K., Le\u00f3n, V.M., 
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  "author": "Vega-Herrera, A., Llorca, M., Savva, K., Le\u00f3n, V.M., 
            
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Abad, E. y Farr\u00e9, M.",
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Abad, E. y Farr\u00e9, M.",
            
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  "author_name": "Vega-Herrera, A., Llorca, M., Savva, K., Le\u00f3n, 
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V.M., Abad, E. y Farr\u00e9, M.",
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  "name": "c3f97a92-52ca-5296-b1db-8b8ce95e66e6",
            
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  "notes": "In this work a suspect-screening approach was employed to 
103
  "notes": "In this work a suspect-screening approach was employed to 
            
94
assess the polymers and plastic additives of micro(nano)plastics 
104
assess the polymers and plastic additives of micro(nano)plastics 
            
95
(NPL/MPLs) of size ranges from the nm range to 20 \u03bcm present in 
105
(NPL/MPLs) of size ranges from the nm range to 20 \u03bcm present in 
            
96
seawater from the top 5 cm of the Mar Menor lagoon during two sampling 
106
seawater from the top 5 cm of the Mar Menor lagoon during two sampling 
            
97
campaigns (summer and winter), as well of other potentially adsorbed 
107
campaigns (summer and winter), as well of other potentially adsorbed 
            
98
compounds onto the plastic particles surfaces and suspended material. 
108
compounds onto the plastic particles surfaces and suspended material. 
            
99
The identification of NPL/MPLs has been based on characteristic 
109
The identification of NPL/MPLs has been based on characteristic 
            
100
Kendrick Mass Defect analysis for each polymer type in mass spectra. 
110
Kendrick Mass Defect analysis for each polymer type in mass spectra. 
            
101
The applied methodology allowed to identify NPLs/MPLs of polystyrene 
111
The applied methodology allowed to identify NPLs/MPLs of polystyrene 
            
102
(PS), polyethylene (PE), polyisoprene (PI), polybutadiene (PBD), 
112
(PS), polyethylene (PE), polyisoprene (PI), polybutadiene (PBD), 
            
103
polypropylene (PP), polyamides (PA), polyvinylchloride (PVC), 
113
polypropylene (PP), polyamides (PA), polyvinylchloride (PVC), 
            
104
n-isopropylacrylamide (PNIPAm), and polydimethylsiloxanes. In 
114
n-isopropylacrylamide (PNIPAm), and polydimethylsiloxanes. In 
            
105
addition, PS, PE, PI, PBD, PP, PA, and PVC were confirmed with 
115
addition, PS, PE, PI, PBD, PP, PA, and PVC were confirmed with 
            
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standards, and the equivalent concentrations were quantified.",
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standards, and the equivalent concentrations were quantified.",
            
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  "notes_translated": {
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  "notes_translated": {
            
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    "es": "In this work a suspect-screening approach was employed to 
118
    "es": "In this work a suspect-screening approach was employed to 
            
109
assess the polymers and plastic additives of micro(nano)plastics 
119
assess the polymers and plastic additives of micro(nano)plastics 
            
110
(NPL/MPLs) of size ranges from the nm range to 20 \u03bcm present in 
120
(NPL/MPLs) of size ranges from the nm range to 20 \u03bcm present in 
            
111
seawater from the top 5 cm of the Mar Menor lagoon during two sampling 
121
seawater from the top 5 cm of the Mar Menor lagoon during two sampling 
            
112
campaigns (summer and winter), as well of other potentially adsorbed 
122
campaigns (summer and winter), as well of other potentially adsorbed 
            
113
compounds onto the plastic particles surfaces and suspended material. 
123
compounds onto the plastic particles surfaces and suspended material. 
            
114
The identification of NPL/MPLs has been based on characteristic 
124
The identification of NPL/MPLs has been based on characteristic 
            
115
Kendrick Mass Defect analysis for each polymer type in mass spectra. 
125
Kendrick Mass Defect analysis for each polymer type in mass spectra. 
            
116
The applied methodology allowed to identify NPLs/MPLs of polystyrene 
126
The applied methodology allowed to identify NPLs/MPLs of polystyrene 
            
117
(PS), polyethylene (PE), polyisoprene (PI), polybutadiene (PBD), 
127
(PS), polyethylene (PE), polyisoprene (PI), polybutadiene (PBD), 
            
118
polypropylene (PP), polyamides (PA), polyvinylchloride (PVC), 
128
polypropylene (PP), polyamides (PA), polyvinylchloride (PVC), 
            
119
n-isopropylacrylamide (PNIPAm), and polydimethylsiloxanes. In 
129
n-isopropylacrylamide (PNIPAm), and polydimethylsiloxanes. In 
            
120
addition, PS, PE, PI, PBD, PP, PA, and PVC were confirmed with 
130
addition, PS, PE, PI, PBD, PP, PA, and PVC were confirmed with 
            
121
standards, and the equivalent concentrations were quantified."
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standards, and the equivalent concentrations were quantified."
            
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