• No results found

Appendix 1. Time trends for contaminant concentrations in herring, guillemot, grey seal, and white-tailed sea eagle.

N/A
N/A
Info
Download
Protected

Academic year: 2021

Share "Appendix 1. Time trends for contaminant concentrations in herring, guillemot, grey seal, and white-tailed sea eagle."

Copied!
44
0
0

Loading.... (view fulltext now)

Download now ( 44 Page )

Full text

(1)

Appendix 1. Time trends for contaminant concentrations in herring, guillemot, grey

seal, and white-tailed sea eagle.

Fig. 1. Condition factor for herring from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 2. Fat percentage in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(2)

Siloxanes

Fig. 3. Siloxane D5 (ng/g lw) in herring muscle from the Bothnian Bay and the north Baltic Proper.

Phenols

Fig. 4. 2,4,6-Bromophenol (ng/g lw) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(3)

.

Fig. 5. 2’OH-BDE68 (ng/g lw) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

.

Fig. 6. 6’OH-BDE47 (ng/g lw) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(4)

.

Fig. 7. PCP (Pentachlorophenol) (ng/g lw). Herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(5)

Fig. 8. BDE-47 (ng/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 9. BDE-99 (ng/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 10. BDE-100 (ng/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(6)

Fig. 11. BDE-153 (ng/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 12. BDE-154 (ng/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(7)

Fig. 13. HBCDD (ng/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 14. HBCDD (ng/g lipid weight) in guillemot eggs from Stora Karlsö.

n(tot)=227,n(yrs)=37 0 50 100 150 200 250 300 350 70 75 80 85 90 95 00 05 10 t(2)=27 yrs (42,20) y(10)=166 (134,205) r2=.47, p<.001 * t(1/2)=22 yrs (8.3,-) r2=.20, p<.199 Source: NRM 12.10.26 10:48, G-HBCD

(8)

Fig. 15. BDE-47 (ng/g lw) in grey seals (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(9)

Fig. 17. BDE-100 (ng/g lw) in grey seals (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(10)

Fig. 19. BDE-154 (ng/g lw) in grey seals (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(11)

Fig. 21. BDE-47 (ng/g lw) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(12)

Fig. 23. BDE-100 (ng/g lw) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(13)

Fig. 25. BDE-154 (ng/g lw) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Fig. 26. HBCDD (ng/g lw) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(14)

Fig. 27. DDE (ug/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 28. DDE (ug/g lw) in Guillemot eggs at Stora Karlsö.

G-DDE 0 100 200 300 400 500 600 700 800 900 1000 1100 70 75 80 85 90 95 00 05 10 n(tot)=567,n(yrs)=43 t(1/2)=6.7 yrs (6.3,7.2) y(10)=7.52 (6.31,8.95) r2=.95, p<.001 * t(1/2)=8.1 yrs (5.1,19) r2=.67, p<.004 * Source: NRM 12.10.24 13:32, G-DDE

(15)

Fig. 29. DDT (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(16)

Fig. 31. DDD (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(17)

Fig. 33. DDE (ug/g lw) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Polychlorinated biphenyls (PCBs)

Fig. 34. CB-118 (ug/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(18)

Fig. 35. CB-153 (ug/g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig. 36. CB-153 (ug/g lw) in Guillemot eggs from Stora Karlsö.

G-CB153 n(tot)=246,n(yrs)=23 0 5 10 15 20 25 90 95 00 05 10 t(1/2)=8.8 yrs (7.7,10) y(10)=1.66 (1.43,1.93) r2=.90, p<.001 * t(1/2)=6.7 yrs (4.4,14) r2=.71, p<.002 * Source: NRM 12.10.24 13:27, G-153

(19)

Fig. 37. totPCB (ug/g lw) in Guillemot eggs from Stora Karlsö.

Fig. 38. CB-52 (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

G-totPCB 0 100 200 300 400 500 600 70 75 80 85 90 95 00 05 10 n(tot)=586,n(yrs)=43 t(1/2)=6.8 yrs (6.5,7.2) y(10)=6.84 (6.01,7.78) r2=.97, p<.001 * t(1/2)=7.6 yrs (5.0,16) r2=.72, p<.002 * Source: NRM 12.10.24 10:45, G-SPCB

(20)

Fig. 39. CB-101 (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(21)

Fig. 41. CB-118 (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(22)

Fig. 43. CB-153 (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(23)

Fig. 45. CB-180 (ug/g lw) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia.

(24)

Fig. 47. totPCB (ug/g lw) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Polychlorinated dioxins

Fig. 48. PCDD/F (pg TCDD-eqv /g lw) in herring muscle from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(25)

Fig. 49. PCDD, PCDF (pg TCDD-eqv/g fat) and PCDD/F (ng TCDD-eqv/g fat) concentrations in guillemot eggs from Stora Karlsö.

Perfluoroalkylated substances (PFASs)

(26)

Fig. 50. PFHxS (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig 51. PFHxS (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

(27)

Fig. 52. PFHxS (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Fig. 53. PFOS (

ng/g ww)

in herring liver from the south Bothnian Sea, the north Baltic Proper and the south

Baltic Proper.

(28)

Fig. 54. PFOS (ng/g fresh weight) in guillemot eggs from Stora Karlsö.

Fig 55. PFOS (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

n(tot)=83,n(yrs)=25 0 200 400 600 800 1000 1200 70 75 80 85 90 95 00 05 10 t(2)=9.9 yrs (13,7.9) y(10)=1325 (907,1935) r2=.74, p<.001 * t(1/2)=19 yrs (4.4,-) r2=.06, p<.519

(29)

Fig. 56. PFOS (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Fig. 57. PFDS (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(30)

Fig 58. PFDS (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

Fig. 59. PFDS (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(31)

Fig. 60. FOSA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig 61. linFOSA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

(32)

Fig. 62. FOSA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Perfluoroalkyl carboxylic acids (PFCAs)

Fig. 63. PFOA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(33)

Fig. 64. PFOA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

Fig. 65. PFOA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(34)

Fig. 66. PFNA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig 67. PFNA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

(35)

Fig. 68. PFNA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Fig. 69. PFDA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(36)

Fig. 70. PFDA (ng/g ww) in grey seal blubber (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

Fig. 71. PFDA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(37)

Fig. 72. PFUnDA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig 73. PFUnDA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

(38)

Fig. 74. PFUnDA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Fig. 75. PFDoDA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(39)

Fig 76. PFDoDA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

Fig. 77. PFDoDA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(40)

Fig. 78. PFTrDA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(41)

Fig 79. PFTrDA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

Fig. 80. PFTrDA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

(42)

Fig. 81. PFTeDA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

Fig 82. PFTeDA (ng/g ww) in grey seal liver (1-3 years old) from the Baltic Proper and the Gulf of Bothnia. Data are taken from Kratzer et al. (2011).

(43)

Fig. 83. PFTeDA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

Fig. 84. PFPeDA (ng/g ww) in herring liver from the south Bothnian Sea, the north Baltic Proper and the south Baltic Proper.

(44)

Fig. 85. PFPeDA (ng/g corrected wet weight) in WTSE egg from the Baltic Proper, the Gulf of Bothnia, Inland and Lapland.

References

Download now ( PDF - 44 Page - 6.04 MB )

Related documents

Silicon cycling in the Baltic Sea: Trends and budget of dissolved silica

In Paper III, data on the DSi concentrations in the water column, estimates of riverine DSi loads and accumulation rates of BSi in sediments are used to evaluate the state of

Silicon cycling in the Baltic Sea: Trends and budget of dissolved silica

While DSi concentrations are still high in the northern regions of the Baltic, other areas may be at risk of developing Si limitation if the decrease in DSi concentrations

Ancient genomics of Baltic seals : Insights on the past Baltic grey seal and harp seal populations

Based on an outstanding zooarchaeological collection of seal bones from across the Baltic Basin, ancient DNA was extracted from harp seal and grey seal bones, ranging in age from

Appendix III Nutrient content per basin in the Baltic Sea and the Gulf of Bothnia

In Bornholm Basin, Arkona Basin, Bothnian Sea and Bothnian Bay the average concentration of two stations is used for the calculation, assuming little horizontal variations in

Grey seal Halichoerus grypus recolonisation of the southern Baltic Sea, Danish Straits and Kattegat

Solid line, round markers (left axis): total number of grey seals counted on haul-outs in the southern Baltic, Danish Straits and Kattegat (southern Sweden, Denmark, Germany

Clupea harengus ) in the Baltic Sea. Temporal, seasonal and spatial variation in dioxins and dioxin-like PCBs from Baltic herring (

environmental conditions appear to have affected herring biology, which in turn played a role in the observed slowing of temporal decreases, seasonal observations of

Contaminant profiles in female eelpout (Zoarces viviparus) and larvae from the Baltic Sea area

Six groups of environmental contaminants i.e., dioxins and dl-PCBs, polybrominated diphenyl ethers, organotins, heavy metals, perfluorinated substances, and phenolics, were

Development and multiplex PCR amplification of novel microsatellite markers in the White-tailed Sea Eagle, Haliaeetus albicilla (Aves: Falconiformes, Accipitridae)

Of these markers, two were impossible to score unambiguously (Hal 11 and Hal 21; clone and primer sequences were deposited in GenBank with Accession numbers AY817050 and