Leat, Eliza HK; Bourgeon, Sophie; Borgå, Katrine; Strøm, Hallvard; Hanssen, Sveinn Are; Gabrielsen, Geir W; Petersen, Ævar; Olafsdottir, Kristin; Magnusdottir, Ellen; Fisk, Aaron T; Ellis, Sandra; Bustnes, Jan Ove; Furness, Robert W (2011): (Table 1) Concentration of organochlorines in Great skua eggs (Stercorarius skua) from Shetland in 1980 and 2008 [dataset]. PANGAEA, https://doi.org/10.1594/PANGAEA.815231, In supplement to: Leat, EHK et al. (2011): Effects of environmental exposure and diet on levels of persistent organic pollutants (POPs) in eggs of a top predator in the North Atlantic in 1980 and 2008. Environmental Pollution, 159(5), 1222-1228, https://doi.org/10.1016/j.envpol.2011.01.036
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Coverage:
Latitude: 60.373000 * Longitude: -1.233000
Date/Time Start: 1980-05-15T00:00:00 * Date/Time End: 2008-06-01T00:00:00
Event(s):
Comment:
All concentrations per (kilo)gram wet weight; ng/g = µg/kg; µg/g = 1/1000 µg/kg. Toxaphenes : N = 10 for both years.
Parameter(s):
# | Name | Short Name | Unit | Principal Investigator | Method/Device | Comment |
---|---|---|---|---|---|---|
1 | DATE/TIME | Date/Time | Geocode | |||
2 | Sample amount | N | # | no. of Great skua eggs | ||
3 | Pentachlorobenzene | PeCB | µg/g | QCB; median | ||
4 | Pentachlorobenzene | PeCB | µg/g | QCB; min | ||
5 | Pentachlorobenzene | PeCB | µg/g | QCB; max | ||
6 | Pentachlorobenzene | PeCB | µg/g | QCB; mean | ||
7 | Pentachlorobenzene, standard deviation | PeCB std dev | ± | |||
8 | Hexachlorobenzene | HCB | µg/g | median | ||
9 | Hexachlorobenzene | HCB | µg/g | min | ||
10 | Hexachlorobenzene | HCB | µg/g | max | ||
11 | Hexachlorobenzene | HCB | µg/g | mean | ||
12 | Hexachlorobenzene, standard deviation | HCB std dev | ± | |||
13 | Octachlorostyrene | OCS | ng/g | median | ||
14 | Octachlorostyrene | OCS | ng/g | min | ||
15 | Octachlorostyrene | OCS | ng/g | max | ||
16 | Octachlorostyrene | OCS | ng/g | mean | ||
17 | Octachlorostyrene, standard deviation | OCS st dev | ± | |||
18 | para,para-Dichlorodiphenyldichloroethylene | pp-DDE | µg/g | median | ||
19 | para,para-Dichlorodiphenyldichloroethylene | pp-DDE | µg/g | min | ||
20 | para,para-Dichlorodiphenyldichloroethylene | pp-DDE | µg/g | max | ||
21 | para,para-Dichlorodiphenyldichloroethylene | pp-DDE | µg/g | mean | ||
22 | Dichlorodiphenyldichloroethylene, standard deviation | DDE std dev | ± | |||
23 | para,para-Dichlorodiphenyldichloroethane | pp-DDD | µg/g | median | ||
24 | para,para-Dichlorodiphenyldichloroethane | pp-DDD | µg/g | min | ||
25 | para,para-Dichlorodiphenyldichloroethane | pp-DDD | µg/g | max | ||
26 | para,para-Dichlorodiphenyldichloroethane | pp-DDD | µg/g | mean | ||
27 | Dichlorodiphenyldichloroethane, standard deviation | DDD std dev | ± | |||
28 | para,para-Dichlorodiphenyltrichloroethane | pp-DDT | µg/g | median | ||
29 | para,para-Dichlorodiphenyltrichloroethane | pp-DDT | µg/g | min | ||
30 | para,para-Dichlorodiphenyltrichloroethane | pp-DDT | µg/g | max | ||
31 | para,para-Dichlorodiphenyltrichloroethane | pp-DDT | µg/g | mean | ||
32 | Dichlorodiphenyltrichloroethane, standard deviation | DDT std dev | ± | |||
33 | Mirex | Mirex | ng/g | median | ||
34 | Mirex | Mirex | ng/g | min | ||
35 | Mirex | Mirex | ng/g | max | ||
36 | Mirex | Mirex | ng/g | mean | ||
37 | Mirex, standard deviation | Mirex std dev | ± | |||
38 | beta-Hexachlorocyclohexane | b-HCH | µg/kg | median | ||
39 | beta-Hexachlorocyclohexane | b-HCH | µg/kg | min | ||
40 | beta-Hexachlorocyclohexane | b-HCH | µg/kg | max | ||
41 | beta-Hexachlorocyclohexane | b-HCH | µg/kg | mean | ||
42 | beta-Hexachlorocyclohexane, standard deviation | b-HCH std dev | ± | |||
43 | gamma-Hexachlorocyclohexane | g-HCH | µg/kg | min | ||
44 | gamma-Hexachlorocyclohexane | g-HCH | µg/kg | max | ||
45 | trans-Chlordane | trans-CHL | µg/g | min | ||
46 | trans-Chlordane | trans-CHL | µg/g | max | ||
47 | trans-Chlordane | trans-CHL | µg/g | mean | ||
48 | Chlordane, standard deviation | CHL std dev | ± | trans-CHL | ||
49 | cis-Chlordane | cis-CHL | µg/g | median | ||
50 | cis-Chlordane | cis-CHL | µg/g | min | ||
51 | cis-Chlordane | cis-CHL | µg/g | max | ||
52 | cis-Chlordane | cis-CHL | µg/g | mean | ||
53 | Chlordane, standard deviation | CHL std dev | ± | cis-CHL | ||
54 | trans-Nonachlor | t-Nonachlor | µg/g | median | ||
55 | trans-Nonachlor | t-Nonachlor | µg/g | min | ||
56 | trans-Nonachlor | t-Nonachlor | µg/g | max | ||
57 | trans-Nonachlor | t-Nonachlor | µg/g | mean | ||
58 | Nonachlor, standard deviation | Nonachlor std dev | ± | t-Nonachlor | ||
59 | cis-Nonachlor | cis-Nonachlor | µg/g | median | ||
60 | cis-Nonachlor | cis-Nonachlor | µg/g | min | ||
61 | cis-Nonachlor | cis-Nonachlor | µg/g | max | ||
62 | cis-Nonachlor | cis-Nonachlor | µg/g | mean | ||
63 | Nonachlor, standard deviation | Nonachlor std dev | ± | cis-Nonachlor | ||
64 | Oxychlordane | oxy-CHL | µg/g | median | ||
65 | Oxychlordane | oxy-CHL | µg/g | min | ||
66 | Oxychlordane | oxy-CHL | µg/g | max | ||
67 | Oxychlordane | oxy-CHL | µg/g | mean | ||
68 | Chlordane, standard deviation | CHL std dev | ± | Oxy-CHL | ||
69 | Heptachlor epoxide | HC epox | ng/g | median | ||
70 | Heptachlor epoxide | HC epox | ng/g | min | ||
71 | Heptachlor epoxide | HC epox | ng/g | max | ||
72 | Heptachlor epoxide | HC epox | ng/g | mean | ||
73 | Heptachlor epoxide, standard deviation | HC epox std dev | ± | |||
74 | Dieldrin | Dieldrin | ng/g | median | ||
75 | Dieldrin | Dieldrin | ng/g | min | ||
76 | Dieldrin | Dieldrin | ng/g | max | ||
77 | Dieldrin | Dieldrin | ng/g | mean | ||
78 | Dieldrin, standard deviation | Dieldrin std dev | ± | |||
79 | Polychlorinated biphenyl | PCB | µg/g | group I median; sum of PCB153,187,183,180,191,201,194,205,206,209 | ||
80 | Polychlorinated biphenyl | PCB | µg/g | group I min; sum of PCB153,187,183,180,191,201,194,205,206,209 | ||
81 | Polychlorinated biphenyl | PCB | µg/g | group I max; sum of PCB153,187,183,180,191,201,194,205,206,209 | ||
82 | Polychlorinated biphenyl | PCB | µg/g | group I mean; sum of PCB153,187,183,180,191,201,194,205,206,209 | ||
83 | Polychlorinated biphenyl, standard deviation | PCB std dev | ± | group I | ||
84 | Polychlorinated biphenyl | PCB | µg/g | group II median; sum of PCB99,138,128,177,170 | ||
85 | Polychlorinated biphenyl | PCB | µg/g | group II min; sum of PCB99,138,128,177,170 | ||
86 | Polychlorinated biphenyl | PCB | µg/g | group II max; sum of PCB99,138,128,177,170 | ||
87 | Polychlorinated biphenyl | PCB | µg/g | group II mean; sum of PCB99,138,128,177,170 | ||
88 | Polychlorinated biphenyl, standard deviation | PCB std dev | ± | group II | ||
89 | Polychlorinated biphenyl | PCB | µg/g | group III median; sum of PCB74,118,158 | ||
90 | Polychlorinated biphenyl | PCB | µg/g | group III min; sum of PCB74,118,158 | ||
91 | Polychlorinated biphenyl | PCB | µg/g | group III max; sum of PCB74,118,158 | ||
92 | Polychlorinated biphenyl | PCB | µg/g | group III mean; sum of PCB74,118,158 | ||
93 | Polychlorinated biphenyl, standard deviation | PCB std dev | ± | group III | ||
94 | Polychlorinated biphenyl | PCB | µg/g | group IV median; sum of PCB18/17,33,52,49,44,70,101,110 | ||
95 | Polychlorinated biphenyl | PCB | µg/g | group IV min; sum of PCB18/17,33,52,49,44,70,101,110 | ||
96 | Polychlorinated biphenyl | PCB | µg/g | group IV max; sum of PCB18/17,33,52,49,44,70,101,110 | ||
97 | Polychlorinated biphenyl | PCB | µg/g | group IV mean; sum of PCB18/17,33,52,49,44,70,101,110 | ||
98 | Polychlorinated biphenyl, standard deviation | PCB std dev | ± | group IV | ||
99 | Polychlorinated biphenyl 149 | PCB_149 | µg/g | median | ||
100 | Polychlorinated biphenyl 149 | PCB_149 | µg/g | min | ||
101 | Polychlorinated biphenyl 149 | PCB_149 | µg/g | max | ||
102 | Polychlorinated biphenyl 149 | PCB_149 | µg/g | mean | ||
103 | Polychlorinated biphenyl, standard deviation | PCB std dev | ± | PCB149 | ||
104 | Polychlorinated biphenyl | PCB | µg/g | total median | ||
105 | Polychlorinated biphenyl | PCB | µg/g | total min | ||
106 | Polychlorinated biphenyl | PCB | µg/g | total max | ||
107 | Polychlorinated biphenyl | PCB | µg/g | total mean | ||
108 | Polychlorinated biphenyl, standard deviation | PCB std dev | ± | total | ||
109 | Toxaphene 26 | Toxaphene 26 | µg/g | median | ||
110 | Toxaphene 26 | Toxaphene 26 | µg/g | min | ||
111 | Toxaphene 26 | Toxaphene 26 | µg/g | max | ||
112 | Toxaphene 26 | Toxaphene 26 | µg/g | mean | ||
113 | Toxaphene, standard deviation | Toxaphene std dev | ± | T 26 | ||
114 | Toxaphene 50 | Toxaphene 50 | µg/g | median | ||
115 | Toxaphene 50 | Toxaphene 50 | µg/g | min | ||
116 | Toxaphene 50 | Toxaphene 50 | µg/g | max | ||
117 | Toxaphene 50 | Toxaphene 50 | µg/g | mean | ||
118 | Toxaphene, standard deviation | Toxaphene std dev | ± | T 50 | ||
119 | Toxaphene 62 | Toxaphene 62 | µg/g | median | ||
120 | Toxaphene 62 | Toxaphene 62 | µg/g | min | ||
121 | Toxaphene 62 | Toxaphene 62 | µg/g | max | ||
122 | Toxaphene 62 | Toxaphene 62 | µg/g | mean | ||
123 | Toxaphene, standard deviation | Toxaphene std dev | ± | T 62 |
License:
Creative Commons Attribution 3.0 Unported (CC-BY-3.0)
Size:
244 data points