Geometric means and (range) of sum polybrominated diphenyl ethers (∑PBDEs) and 5 congeners in nestling bald eagle (Haliaeetus leucocephalus) plasma from 2006 to 2017 at 12 study areas and 3 waterbody types in Wisconsin and Minnesota (sorted by ∑PBDE)
Geometric means and (range) in µg/La | |||||||
Study area (waterbody type) | No. | ∑PBDE | BDE‐47 | BDE‐99 | BDE‐100 | BDE‐153 | BDE‐154 |
MISS (river) | 139 | 10.8E (3.23–48.7) | 6.10H (1.20–29.0) | 1.47E (0.230–6.60) | 1.37E (0.250–6.80) | 0.590C (<LOQ–2.70) | 0.570DE (<LOQ–2.40) |
Pools3+4 (river) | 33 | 9.72DE (6.31–20.6) | 5.56H (3.30–11.0) | 1.31E (0.480–3.40) | 1.21CDE (0.830–2.40) | 0.500BC (<LOQ–1.40) | 0.500CD (<LOQ–1.10) |
GBLM (Great Lake) | 30 | 7.62CDE (2.25–31.1) | 1.99DE (0.620–5.30) | 1.07D (<LOQ–6.50) | 0.810C (<LOQ–2.70) | 0.550BC (<LOQ–4.20) | 0.470BC (<LOQ–3.64) |
LSSS (Great Lake) | 16 | 8.36CDE (4.28–45.5) | 3.25FG (1.10–10.0) | 1.63E (0.420–15.0) | 1.58E (0.420–6.80) | 0.610BC (<LOQ–9.50) | 0.700EF (<LOQ–2.20) |
APIS (Great Lake) | 58 | 7.86CD (3.38–37.2) | 2.51EF (0.860–8.60) | 1.52E (0.440–9.20) | 1.21DE (0.330–6.60) | 0.590C (<LOQ–5.60) | 0.780F (<LOQ–2.80 |
LSACN (river) | 65 | 7.79CD (3.18–23.7) | 3.66G (0.820–14.0) | 0.830D (LOQ–2.60) | 0.900CD (LOQ–3.60) | 0.400B (<LOQ–0.960) | 0.410C (<LOQ–0.970) |
FRGBb (river/Great Lake) | 16/7 | 5.88BC (2.70–16.2) | 1.46CD (0.580–5.20) | 0.490C (<LOQ–1.40) | 0.480B (<LOQ–1.70) | 0.210A (<LOQ–1.40) | 0.140A (<LOQ–2.10) |
UPWR (river) | 8 | 4.79ABCD (1.51–15.2) | 1.40C (0.320–7.60) | 0.430BC (<LOQ–1.20) | 0.380AB (<LOQ–1.40) | 0.240A (<LOQ–0.780) | 0.260AB (<LOQ–1.10) |
MDWR (river) | 7 | 4.61ABC (2.78–6.71) | 1.30BC (0.490–3.80) | 0.260AB (<LOQ–0.490) | 0.190A (<LOQ–0.730) | 0.110A (<LOQ–0.410) | 0.230A (<LOQ–0.480) |
NHEL (inland lake) | 25 | 4.02AB (0–9.15) | 0.830AB (<LOQ–3.40) | 0.350AB (>LOQ–1.40) | 0.270A (<LOQ–1.10) | 0.100A (<LOQ–0.890) | 0.150A (<LOQ–0.840) |
LWSR (river) | 5 | 2.98AB (2.27–3.08) | 0.830ABC (0.670–0.960) | 0.250ABC (LOQ–0.360) | 0.180A (<LOQ–0.230) | <LOQ (<LOQ–0.150) | 0.150A (<LOQ–0.480) |
USACN (river) | 65 | 2.88A (1.36–8.10) | 0.630A (0.190–2.20) | 0.240A (<LOQ–0.630) | 0.230A (<LOQ–0.620) | 0.150A (<LOQ–0.620) | 0.180A (<LOQ–0.580) |
Waterbody type: | |||||||
Great Lakes | 111 | 7.18B (2.25–45.5) | 2.35B (0.620–10.0) | 1.08C (LOQ–15.0) | 0.940C (LOQ–6.80) | 0.450C (LOQ–9.50) | 0.540C (LOQ–3.64) |
Riversc | 338 | 5.85B (1.36–48.7) | 2.38B (0.190–29.0) | 0.750B (0.120–7.0) | 0.610B (0.100–6.80) | 0.320B (LOQ–2.70) | 0.330B (LOQ–2.40) |
Inland lakes | 25 | 0.920A (0–9.15) | 0.030A (0.150–3.40) | 0.240A (LOQ–1.40) | 0.200A (LOQ–1.10) | 0.090A (LOQ–0.890) | 0.140A (LOQ–0.840) |
Geometric means and (range) in µg/La | |||||||
Study area (waterbody type) | No. | ∑PBDE | BDE‐47 | BDE‐99 | BDE‐100 | BDE‐153 | BDE‐154 |
MISS (river) | 139 | 10.8E (3.23–48.7) | 6.10H (1.20–29.0) | 1.47E (0.230–6.60) | 1.37E (0.250–6.80) | 0.590C (<LOQ–2.70) | 0.570DE (<LOQ–2.40) |
Pools3+4 (river) | 33 | 9.72DE (6.31–20.6) | 5.56H (3.30–11.0) | 1.31E (0.480–3.40) | 1.21CDE (0.830–2.40) | 0.500BC (<LOQ–1.40) | 0.500CD (<LOQ–1.10) |
GBLM (Great Lake) | 30 | 7.62CDE (2.25–31.1) | 1.99DE (0.620–5.30) | 1.07D (<LOQ–6.50) | 0.810C (<LOQ–2.70) | 0.550BC (<LOQ–4.20) | 0.470BC (<LOQ–3.64) |
LSSS (Great Lake) | 16 | 8.36CDE (4.28–45.5) | 3.25FG (1.10–10.0) | 1.63E (0.420–15.0) | 1.58E (0.420–6.80) | 0.610BC (<LOQ–9.50) | 0.700EF (<LOQ–2.20) |
APIS (Great Lake) | 58 | 7.86CD (3.38–37.2) | 2.51EF (0.860–8.60) | 1.52E (0.440–9.20) | 1.21DE (0.330–6.60) | 0.590C (<LOQ–5.60) | 0.780F (<LOQ–2.80 |
LSACN (river) | 65 | 7.79CD (3.18–23.7) | 3.66G (0.820–14.0) | 0.830D (LOQ–2.60) | 0.900CD (LOQ–3.60) | 0.400B (<LOQ–0.960) | 0.410C (<LOQ–0.970) |
FRGBb (river/Great Lake) | 16/7 | 5.88BC (2.70–16.2) | 1.46CD (0.580–5.20) | 0.490C (<LOQ–1.40) | 0.480B (<LOQ–1.70) | 0.210A (<LOQ–1.40) | 0.140A (<LOQ–2.10) |
UPWR (river) | 8 | 4.79ABCD (1.51–15.2) | 1.40C (0.320–7.60) | 0.430BC (<LOQ–1.20) | 0.380AB (<LOQ–1.40) | 0.240A (<LOQ–0.780) | 0.260AB (<LOQ–1.10) |
MDWR (river) | 7 | 4.61ABC (2.78–6.71) | 1.30BC (0.490–3.80) | 0.260AB (<LOQ–0.490) | 0.190A (<LOQ–0.730) | 0.110A (<LOQ–0.410) | 0.230A (<LOQ–0.480) |
NHEL (inland lake) | 25 | 4.02AB (0–9.15) | 0.830AB (<LOQ–3.40) | 0.350AB (>LOQ–1.40) | 0.270A (<LOQ–1.10) | 0.100A (<LOQ–0.890) | 0.150A (<LOQ–0.840) |
LWSR (river) | 5 | 2.98AB (2.27–3.08) | 0.830ABC (0.670–0.960) | 0.250ABC (LOQ–0.360) | 0.180A (<LOQ–0.230) | <LOQ (<LOQ–0.150) | 0.150A (<LOQ–0.480) |
USACN (river) | 65 | 2.88A (1.36–8.10) | 0.630A (0.190–2.20) | 0.240A (<LOQ–0.630) | 0.230A (<LOQ–0.620) | 0.150A (<LOQ–0.620) | 0.180A (<LOQ–0.580) |
Waterbody type: | |||||||
Great Lakes | 111 | 7.18B (2.25–45.5) | 2.35B (0.620–10.0) | 1.08C (LOQ–15.0) | 0.940C (LOQ–6.80) | 0.450C (LOQ–9.50) | 0.540C (LOQ–3.64) |
Riversc | 338 | 5.85B (1.36–48.7) | 2.38B (0.190–29.0) | 0.750B (0.120–7.0) | 0.610B (0.100–6.80) | 0.320B (LOQ–2.70) | 0.330B (LOQ–2.40) |
Inland lakes | 25 | 0.920A (0–9.15) | 0.030A (0.150–3.40) | 0.240A (LOQ–1.40) | 0.200A (LOQ–1.10) | 0.090A (LOQ–0.890) | 0.140A (LOQ–0.840) |
Geometric means with the same capital letter within columns are not significantly different (Tukey‐adjusted comparisons). All comparisons for ∑PBDE were significant at p < 0.01; for congeners BDE‐47, ‐99, and ‐100, they were significant at p < 0.001.
For the FRGB study area, 16 samples were categorized as river samples for analysis by waterbody type.
∑PBDE = sum polybrominated diphenyl ether; APIS = Apostle Islands; LSSS = Lake Superior southern shore; USACN = Upper St. Croix River; LSACN = Lower St. Croix River; MISS = Mississippi River; Pools 3 + 4 = Pools 3 and 4 of the Mississippi River; FRGB = Fox River/Green Bay; GBLM = Green Bay/Lake Michigan; UPWR = Upper Wisconsin River; MDWR = Mid‐Wisconsin River; LWSR = Lower Wisconsin River; NHEL = Northern Highlands; LOQ = limits of quantification.
Geometric means and (range) of sum polybrominated diphenyl ethers (∑PBDEs) and 5 congeners in nestling bald eagle (Haliaeetus leucocephalus) plasma from 2006 to 2017 at 12 study areas and 3 waterbody types in Wisconsin and Minnesota (sorted by ∑PBDE)
Geometric means and (range) in µg/La | |||||||
Study area (waterbody type) | No. | ∑PBDE | BDE‐47 | BDE‐99 | BDE‐100 | BDE‐153 | BDE‐154 |
MISS (river) | 139 | 10.8E (3.23–48.7) | 6.10H (1.20–29.0) | 1.47E (0.230–6.60) | 1.37E (0.250–6.80) | 0.590C (<LOQ–2.70) | 0.570DE (<LOQ–2.40) |
Pools3+4 (river) | 33 | 9.72DE (6.31–20.6) | 5.56H (3.30–11.0) | 1.31E (0.480–3.40) | 1.21CDE (0.830–2.40) | 0.500BC (<LOQ–1.40) | 0.500CD (<LOQ–1.10) |
GBLM (Great Lake) | 30 | 7.62CDE (2.25–31.1) | 1.99DE (0.620–5.30) | 1.07D (<LOQ–6.50) | 0.810C (<LOQ–2.70) | 0.550BC (<LOQ–4.20) | 0.470BC (<LOQ–3.64) |
LSSS (Great Lake) | 16 | 8.36CDE (4.28–45.5) | 3.25FG (1.10–10.0) | 1.63E (0.420–15.0) | 1.58E (0.420–6.80) | 0.610BC (<LOQ–9.50) | 0.700EF (<LOQ–2.20) |
APIS (Great Lake) | 58 | 7.86CD (3.38–37.2) | 2.51EF (0.860–8.60) | 1.52E (0.440–9.20) | 1.21DE (0.330–6.60) | 0.590C (<LOQ–5.60) | 0.780F (<LOQ–2.80 |
LSACN (river) | 65 | 7.79CD (3.18–23.7) | 3.66G (0.820–14.0) | 0.830D (LOQ–2.60) | 0.900CD (LOQ–3.60) | 0.400B (<LOQ–0.960) | 0.410C (<LOQ–0.970) |
FRGBb (river/Great Lake) | 16/7 | 5.88BC (2.70–16.2) | 1.46CD (0.580–5.20) | 0.490C (<LOQ–1.40) | 0.480B (<LOQ–1.70) | 0.210A (<LOQ–1.40) | 0.140A (<LOQ–2.10) |
UPWR (river) | 8 | 4.79ABCD (1.51–15.2) | 1.40C (0.320–7.60) | 0.430BC (<LOQ–1.20) | 0.380AB (<LOQ–1.40) | 0.240A (<LOQ–0.780) | 0.260AB (<LOQ–1.10) |
MDWR (river) | 7 | 4.61ABC (2.78–6.71) | 1.30BC (0.490–3.80) | 0.260AB (<LOQ–0.490) | 0.190A (<LOQ–0.730) | 0.110A (<LOQ–0.410) | 0.230A (<LOQ–0.480) |
NHEL (inland lake) | 25 | 4.02AB (0–9.15) | 0.830AB (<LOQ–3.40) | 0.350AB (>LOQ–1.40) | 0.270A (<LOQ–1.10) | 0.100A (<LOQ–0.890) | 0.150A (<LOQ–0.840) |
LWSR (river) | 5 | 2.98AB (2.27–3.08) | 0.830ABC (0.670–0.960) | 0.250ABC (LOQ–0.360) | 0.180A (<LOQ–0.230) | <LOQ (<LOQ–0.150) | 0.150A (<LOQ–0.480) |
USACN (river) | 65 | 2.88A (1.36–8.10) | 0.630A (0.190–2.20) | 0.240A (<LOQ–0.630) | 0.230A (<LOQ–0.620) | 0.150A (<LOQ–0.620) | 0.180A (<LOQ–0.580) |
Waterbody type: | |||||||
Great Lakes | 111 | 7.18B (2.25–45.5) | 2.35B (0.620–10.0) | 1.08C (LOQ–15.0) | 0.940C (LOQ–6.80) | 0.450C (LOQ–9.50) | 0.540C (LOQ–3.64) |
Riversc | 338 | 5.85B (1.36–48.7) | 2.38B (0.190–29.0) | 0.750B (0.120–7.0) | 0.610B (0.100–6.80) | 0.320B (LOQ–2.70) | 0.330B (LOQ–2.40) |
Inland lakes | 25 | 0.920A (0–9.15) | 0.030A (0.150–3.40) | 0.240A (LOQ–1.40) | 0.200A (LOQ–1.10) | 0.090A (LOQ–0.890) | 0.140A (LOQ–0.840) |
Geometric means and (range) in µg/La | |||||||
Study area (waterbody type) | No. | ∑PBDE | BDE‐47 | BDE‐99 | BDE‐100 | BDE‐153 | BDE‐154 |
MISS (river) | 139 | 10.8E (3.23–48.7) | 6.10H (1.20–29.0) | 1.47E (0.230–6.60) | 1.37E (0.250–6.80) | 0.590C (<LOQ–2.70) | 0.570DE (<LOQ–2.40) |
Pools3+4 (river) | 33 | 9.72DE (6.31–20.6) | 5.56H (3.30–11.0) | 1.31E (0.480–3.40) | 1.21CDE (0.830–2.40) | 0.500BC (<LOQ–1.40) | 0.500CD (<LOQ–1.10) |
GBLM (Great Lake) | 30 | 7.62CDE (2.25–31.1) | 1.99DE (0.620–5.30) | 1.07D (<LOQ–6.50) | 0.810C (<LOQ–2.70) | 0.550BC (<LOQ–4.20) | 0.470BC (<LOQ–3.64) |
LSSS (Great Lake) | 16 | 8.36CDE (4.28–45.5) | 3.25FG (1.10–10.0) | 1.63E (0.420–15.0) | 1.58E (0.420–6.80) | 0.610BC (<LOQ–9.50) | 0.700EF (<LOQ–2.20) |
APIS (Great Lake) | 58 | 7.86CD (3.38–37.2) | 2.51EF (0.860–8.60) | 1.52E (0.440–9.20) | 1.21DE (0.330–6.60) | 0.590C (<LOQ–5.60) | 0.780F (<LOQ–2.80 |
LSACN (river) | 65 | 7.79CD (3.18–23.7) | 3.66G (0.820–14.0) | 0.830D (LOQ–2.60) | 0.900CD (LOQ–3.60) | 0.400B (<LOQ–0.960) | 0.410C (<LOQ–0.970) |
FRGBb (river/Great Lake) | 16/7 | 5.88BC (2.70–16.2) | 1.46CD (0.580–5.20) | 0.490C (<LOQ–1.40) | 0.480B (<LOQ–1.70) | 0.210A (<LOQ–1.40) | 0.140A (<LOQ–2.10) |
UPWR (river) | 8 | 4.79ABCD (1.51–15.2) | 1.40C (0.320–7.60) | 0.430BC (<LOQ–1.20) | 0.380AB (<LOQ–1.40) | 0.240A (<LOQ–0.780) | 0.260AB (<LOQ–1.10) |
MDWR (river) | 7 | 4.61ABC (2.78–6.71) | 1.30BC (0.490–3.80) | 0.260AB (<LOQ–0.490) | 0.190A (<LOQ–0.730) | 0.110A (<LOQ–0.410) | 0.230A (<LOQ–0.480) |
NHEL (inland lake) | 25 | 4.02AB (0–9.15) | 0.830AB (<LOQ–3.40) | 0.350AB (>LOQ–1.40) | 0.270A (<LOQ–1.10) | 0.100A (<LOQ–0.890) | 0.150A (<LOQ–0.840) |
LWSR (river) | 5 | 2.98AB (2.27–3.08) | 0.830ABC (0.670–0.960) | 0.250ABC (LOQ–0.360) | 0.180A (<LOQ–0.230) | <LOQ (<LOQ–0.150) | 0.150A (<LOQ–0.480) |
USACN (river) | 65 | 2.88A (1.36–8.10) | 0.630A (0.190–2.20) | 0.240A (<LOQ–0.630) | 0.230A (<LOQ–0.620) | 0.150A (<LOQ–0.620) | 0.180A (<LOQ–0.580) |
Waterbody type: | |||||||
Great Lakes | 111 | 7.18B (2.25–45.5) | 2.35B (0.620–10.0) | 1.08C (LOQ–15.0) | 0.940C (LOQ–6.80) | 0.450C (LOQ–9.50) | 0.540C (LOQ–3.64) |
Riversc | 338 | 5.85B (1.36–48.7) | 2.38B (0.190–29.0) | 0.750B (0.120–7.0) | 0.610B (0.100–6.80) | 0.320B (LOQ–2.70) | 0.330B (LOQ–2.40) |
Inland lakes | 25 | 0.920A (0–9.15) | 0.030A (0.150–3.40) | 0.240A (LOQ–1.40) | 0.200A (LOQ–1.10) | 0.090A (LOQ–0.890) | 0.140A (LOQ–0.840) |
Geometric means with the same capital letter within columns are not significantly different (Tukey‐adjusted comparisons). All comparisons for ∑PBDE were significant at p < 0.01; for congeners BDE‐47, ‐99, and ‐100, they were significant at p < 0.001.
For the FRGB study area, 16 samples were categorized as river samples for analysis by waterbody type.
∑PBDE = sum polybrominated diphenyl ether; APIS = Apostle Islands; LSSS = Lake Superior southern shore; USACN = Upper St. Croix River; LSACN = Lower St. Croix River; MISS = Mississippi River; Pools 3 + 4 = Pools 3 and 4 of the Mississippi River; FRGB = Fox River/Green Bay; GBLM = Green Bay/Lake Michigan; UPWR = Upper Wisconsin River; MDWR = Mid‐Wisconsin River; LWSR = Lower Wisconsin River; NHEL = Northern Highlands; LOQ = limits of quantification.
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