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
Always quote citation above when using data! You can download the citation in several formats below.
Published: 2011 (exact date unknown) • DOI registered: 2013-07-25
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
