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  "alternate_identifier": "DOI: 10.1016/j.marpolbul.2021.112407",
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  "author": "Leon, Victor M., Moreno-Gonzalez, R., Besada, V., 
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  "author": "Leon, Victor M., Moreno-Gonzalez, R., Besada, V., 
            
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Martinez, F., Ceruso, C., Garcia, V., Schultze, F. y Campillo, J.A.",
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  "author_name": "Leon, Victor M., Moreno-Gonzalez, R., Besada, V., 
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  "author_name": "Leon, Victor M., Moreno-Gonzalez, R., Besada, V., 
            
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Martinez, F., Ceruso, C., Garcia, V., Schultze, F. y Campillo, J.A.",
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      "name": "Leon, Victor M., Moreno-Gonzalez, R., Besada, V., 
            
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  "notes": "The seasonal bioaccumulation of trace metals, polycyclic 
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  "notes": "The seasonal bioaccumulation of trace metals, polycyclic 
            
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aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs) and 
111
aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs) and 
            
102
organochlorinated pesticides (OCPs) in sea snail (Hexaplex trunculus) 
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organochlorinated pesticides (OCPs) in sea snail (Hexaplex trunculus) 
            
103
and sea cucumber (Holothuria polii) from Mar Menor lagoon were 
113
and sea cucumber (Holothuria polii) from Mar Menor lagoon were 
            
104
characterised. The highest concentrations of p,p'-DDE were detected in 
114
characterised. The highest concentrations of p,p'-DDE were detected in 
            
105
the central and south part of Mar Menor lagoon. However, the highest 
115
the central and south part of Mar Menor lagoon. However, the highest 
            
106
concentrations of metals in sea snail and holothurians were detected 
116
concentrations of metals in sea snail and holothurians were detected 
            
107
in the influence area of El Beal wadi. Biomagnification factors (BMF) 
117
in the influence area of El Beal wadi. Biomagnification factors (BMF) 
            
108
in sea snail from cockle (sea snail-cockle concentration ratio) were 
118
in sea snail from cockle (sea snail-cockle concentration ratio) were 
            
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higher than 5 for metal and organochlorinated compounds. However, 
119
higher than 5 for metal and organochlorinated compounds. However, 
            
110
similar concentrations were observed in both species for PAHs due to 
120
similar concentrations were observed in both species for PAHs due to 
            
111
gastropods capability of metabolising these pollutants. Consequently, 
121
gastropods capability of metabolising these pollutants. Consequently, 
            
112
sea snail is proposed as a sentinel for trace metals, PCBs and OCPs in 
122
sea snail is proposed as a sentinel for trace metals, PCBs and OCPs in 
            
113
the coastal lagoons, not only due to its bioaccumulation and 
123
the coastal lagoons, not only due to its bioaccumulation and 
            
114
biomagnification capacity but also the easy sampling and amply 
124
biomagnification capacity but also the easy sampling and amply 
            
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distribution in many coastal areas.",
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distribution in many coastal areas.",
            
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  "notes_translated": {
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    "es": "The seasonal bioaccumulation of trace metals, polycyclic 
127
    "es": "The seasonal bioaccumulation of trace metals, polycyclic 
            
118
aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs) and 
128
aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs) and 
            
119
organochlorinated pesticides (OCPs) in sea snail (Hexaplex trunculus) 
129
organochlorinated pesticides (OCPs) in sea snail (Hexaplex trunculus) 
            
120
and sea cucumber (Holothuria polii) from Mar Menor lagoon were 
130
and sea cucumber (Holothuria polii) from Mar Menor lagoon were 
            
121
characterised. The highest concentrations of p,p'-DDE were detected in 
131
characterised. The highest concentrations of p,p'-DDE were detected in 
            
122
the central and south part of Mar Menor lagoon. However, the highest 
132
the central and south part of Mar Menor lagoon. However, the highest 
            
123
concentrations of metals in sea snail and holothurians were detected 
133
concentrations of metals in sea snail and holothurians were detected 
            
124
in the influence area of El Beal wadi. Biomagnification factors (BMF) 
134
in the influence area of El Beal wadi. Biomagnification factors (BMF) 
            
125
in sea snail from cockle (sea snail-cockle concentration ratio) were 
135
in sea snail from cockle (sea snail-cockle concentration ratio) were 
            
126
higher than 5 for metal and organochlorinated compounds. However, 
136
higher than 5 for metal and organochlorinated compounds. However, 
            
127
similar concentrations were observed in both species for PAHs due to 
137
similar concentrations were observed in both species for PAHs due to 
            
128
gastropods capability of metabolising these pollutants. Consequently, 
138
gastropods capability of metabolising these pollutants. Consequently, 
            
129
sea snail is proposed as a sentinel for trace metals, PCBs and OCPs in 
139
sea snail is proposed as a sentinel for trace metals, PCBs and OCPs in 
            
130
the coastal lagoons, not only due to its bioaccumulation and 
140
the coastal lagoons, not only due to its bioaccumulation and 
            
131
biomagnification capacity but also the easy sampling and amply 
141
biomagnification capacity but also the easy sampling and amply 
            
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distribution in many coastal areas."
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distribution in many coastal areas."
            
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