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Bechshøft, Thea Ø; Rigét, Frank F; Sonne, Christian; Letcher, Robert J; Muir, Derek C G; Novak, M A; Henchey, E; Meyer, J S; Eulaers, I; Jaspers, Veerle LB; Eens, Marcel; Covaci, Adrian; Dietz, Rune (2012): (Table 1) Concentration of pollutants in hair of East Greenland polar bears (Ursus maritimus) [dataset]. PANGAEA, https://doi.org/10.1594/PANGAEA.807320, Supplement to: Bechshøft, TØ et al. (2012): Measuring environmental stress in East Greenland polar bears, 1892-1927 and 1988-2009: What does hair cortisol tell us? Environment International, 45, 15-21, https://doi.org/10.1016/j.envint.2012.04.005

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Abstract:
Hair sampled from 96 East Greenland polar bears (Ursus maritimus) over the periods 1892-1927 and 1988-2009 was analyzed for cortisol as a proxy to investigate temporal patterns of environmental stress. Cortisol concentration was independent of sex and age, and was found at significantly higher (p<0.001) concentrations in historical hair samples (1892-1927; n = 8) relative to recent ones (1988-2009; n = 88). In addition, there was a linear time trend in cortisol concentration of the recent samples (p< 0.01), with an annual decrease of 2.7%. The recent hair samples were also analyzed for major bioaccumulative, persistent organic pollutants (POPs). There were no obvious POP related time trends or correlations between hair cortisol and hair POP concentrations. Thus, polar bear hair appears to be a relatively poor indicator of the animal's general POP load in adipose tissue. However, further investigations are warranted to explore the reasons for the temporal decrease found in the bears' hair cortisol levels.
Coverage:
Latitude: 74.000000 * Longitude: -20.000000
Event(s):
East_Greenland * Latitude: 74.000000 * Longitude: -20.000000 * Location: East Greenland
Comment:
All concentrations per g hair, dry weight. Data extracted in the frame of a joint ICSTI/PANGAEA IPY effort, see http://doi.pangaea.de/10.1594/PANGAEA.150150
Parameter(s):
#NameShort NameUnitPrincipal InvestigatorMethod/DeviceComment
Polychlorinated biphenyl 138PCB_138µg/gBechshøft, Thea Ømean; n = 68
Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB68
Polychlorinated biphenyl 138PCB_138µg/gBechshøft, Thea Ømin
Polychlorinated biphenyl 138PCB_138µg/gBechshøft, Thea Ømax
Polychlorinated biphenyl 153PCB_153µg/gBechshøft, Thea Ømean; n = 69
Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB69
Polychlorinated biphenyl 153PCB_153µg/gBechshøft, Thea Ømin
Polychlorinated biphenyl 153PCB_153µg/gBechshøft, Thea Ømax
Polychlorinated biphenyl 156PCB_156µg/gBechshøft, Thea Ømean; n = 65
10 Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB65
11 Polychlorinated biphenyl 156PCB_156µg/gBechshøft, Thea Ømin
12 Polychlorinated biphenyl 156PCB_156µg/gBechshøft, Thea Ømax
13 Polychlorinated biphenyl 170PCB_170µg/gBechshøft, Thea Ømean; n = 69
14 Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB69
15 Polychlorinated biphenyl 170PCB_170µg/gBechshøft, Thea Ømin
16 Polychlorinated biphenyl 170PCB_170µg/gBechshøft, Thea Ømax
17 Polychlorinated biphenyl 180PCB_180µg/gBechshøft, Thea Ømean; n = 69
18 Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB69
19 Polychlorinated biphenyl 180PCB_180µg/gBechshøft, Thea Ømin
20 Polychlorinated biphenyl 180PCB_180µg/gBechshøft, Thea Ømax
21 Polychlorinated biphenyl 183PCB_183µg/gBechshøft, Thea Ømean; n = 65
22 Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB65
23 Polychlorinated biphenyl 183PCB_183µg/gBechshøft, Thea Ømin
24 Polychlorinated biphenyl 183PCB_183µg/gBechshøft, Thea Ømax
25 Polychlorinated biphenyl 187PCB_187µg/gBechshøft, Thea Ømean; n = 66
26 Polychlorinated biphenyl, standard deviationPCB std dev±Bechshøft, Thea ØPCB66
27 Polychlorinated biphenyl 187PCB_187µg/gBechshøft, Thea Ømin
28 Polychlorinated biphenyl 187PCB_187µg/gBechshøft, Thea Ømax
29 para,para-Dichlorodiphenyldichloroethylenepp-DDEµg/gBechshøft, Thea Ømean, n = 67
30 Dichlorodiphenyldichloroethylene, standard deviationDDE std dev±Bechshøft, Thea Ø
31 para,para-Dichlorodiphenyldichloroethylenepp-DDEµg/gBechshøft, Thea Ømin
32 para,para-Dichlorodiphenyldichloroethylenepp-DDEµg/gBechshøft, Thea Ømax
33 Oxychlordaneoxy-CHLµg/gBechshøft, Thea Ømean, n = 69
34 Standard deviationStd dev±Bechshøft, Thea ØOxyCHL
35 Oxychlordaneoxy-CHLµg/gBechshøft, Thea Ømin
36 Oxychlordaneoxy-CHLµg/gBechshøft, Thea Ømax
37 trans-Nonachlort-Nonachlorµg/gBechshøft, Thea Ømean, n = 69
38 Standard deviationStd dev±Bechshøft, Thea Øtrans-Nonachlor
39 trans-Nonachlort-Nonachlorµg/gBechshøft, Thea Ømin
40 trans-Nonachlort-Nonachlorµg/gBechshøft, Thea Ømax
41 Polybrominated diphenyl ethers, congener BDE-47BDE-47µg/gBechshøft, Thea Ømean, n = 69
42 Polybrominated diphenyl ethers, standard deviationPBDE std dev±Bechshøft, Thea Ø
43 Polybrominated diphenyl ethers, congener BDE-47BDE-47µg/gBechshøft, Thea Ømin
44 Polybrominated diphenyl ethers, congener BDE-47BDE-47µg/gBechshøft, Thea Ømax
Size:
44 data points

Data

Download dataset as tab-delimited text — use the following character encoding:


PCB_138 [µg/g]
(mean; n = 68)

PCB std dev [±]
(PCB68)

PCB_138 [µg/g]
(min)

PCB_138 [µg/g]
(max)

PCB_153 [µg/g]
(mean; n = 69)

PCB std dev [±]
(PCB69)

PCB_153 [µg/g]
(min)

PCB_153 [µg/g]
(max)

PCB_156 [µg/g]
(mean; n = 65)
10 
PCB std dev [±]
(PCB65)
11 
PCB_156 [µg/g]
(min)
12 
PCB_156 [µg/g]
(max)
13 
PCB_170 [µg/g]
(mean; n = 69)
14 
PCB std dev [±]
(PCB69)
15 
PCB_170 [µg/g]
(min)
16 
PCB_170 [µg/g]
(max)
17 
PCB_180 [µg/g]
(mean; n = 69)
18 
PCB std dev [±]
(PCB69)
19 
PCB_180 [µg/g]
(min)
20 
PCB_180 [µg/g]
(max)
21 
PCB_183 [µg/g]
(mean; n = 65)
22 
PCB std dev [±]
(PCB65)
23 
PCB_183 [µg/g]
(min)
24 
PCB_183 [µg/g]
(max)
25 
PCB_187 [µg/g]
(mean; n = 66)
26 
PCB std dev [±]
(PCB66)
27 
PCB_187 [µg/g]
(min)
28 
PCB_187 [µg/g]
(max)
29 
pp-DDE [µg/g]
(mean, n = 67)
30 
DDE std dev [±]
31 
pp-DDE [µg/g]
(min)
32 
pp-DDE [µg/g]
(max)
33 
oxy-CHL [µg/g]
(mean, n = 69)
34 
Std dev [±]
(OxyCHL)
35 
oxy-CHL [µg/g]
(min)
36 
oxy-CHL [µg/g]
(max)
37 
t-Nonachlor [µg/g]
(mean, n = 69)
38 
Std dev [±]
(trans-Nonachlor)
39 
t-Nonachlor [µg/g]
(min)
40 
t-Nonachlor [µg/g]
(max)
41 
BDE-47 [µg/g]
(mean, n = 69)
42 
PBDE std dev [±]
43 
BDE-47 [µg/g]
(min)
44 
BDE-47 [µg/g]
(max)
0.00790.0190.00020.14360.02940.07860.00040.61620.0010.00190.00020.01390.01390.02910.00020.20660.02580.05920.00020.43570.00080.00180.00010.01370.00060.00130.00010.00950.00220.0050.00010.0360.00580.02080.00020.17130.00220.00560.00020.04430.00050.00080.00010.0058