Scottish Marine and Freshwater Science Volume 3 Number 5: SOTEAG Rocky Shore Monitoring Programme. TBT Contamination in Sullom Voe, Shetland. 2011 Dogwhelk Survey
This report provides the results and assessment of a survey carried out by Marine Scotland Science, Marine Laboratory, Aberdeen as part of a rocky shore monitoring programme undertaken by Aquatic Survey and Monitoring Limited, commissioned by the Shetland
Results of the 2011 survey of imposex in dogwhelks ( Nucella lapillus) in Sullom Voe and Yell Sound.
Site No | Site Name | Size | Incidence of Occurrence % | % RPSI | VDSI | No. Females | No. Males |
---|---|---|---|---|---|---|---|
1 | Easterwick | 10‑15 | 0 | 0.00 | 0.00 | 5 | 5 |
15‑21 | 0 | 0.00 | 0.00 | 8 | 8 | ||
21‑26 | 18 | 0.00 | 0.18 | 11 | 7 | ||
26‑35 | 13 | <0.01 | 0.25 | 8 | 2 | ||
Adults | 14 | <0.01 | 0.21 | 28 | 12 | ||
2 | Burgo Taing | Adults | 21 | <0.01 | 0.31 | 29 | 9 |
3 | Billia Skerry | 10‑15 | 50 | 0.01 | 0.67 | 6 | 4 |
15‑21 | 50 | <0.01 | 0.57 | 6 | 1 | ||
21‑26 | 50 | 0.00 | 0.50 | 10 | 9 | ||
26‑35 | 60 | <0.01 | 1.00 | 5 | 5 | ||
Adults | 38 | 0.00 | 0.38 | 8 | 32 | ||
4 | Scarf Stane | Adults | 67 | 0.00 | 0.67 | 3 | 7 |
5 | East of Ollaberry | 10‑15 | 36 | 0.05 | 0.45 | 11 | 3 |
15‑21 | 22 | 0.01 | 0.33 | 9 | 11 | ||
21‑26 | 7 | 0.00 | 0.07 | 14 | 5 | ||
26‑35 | 11 | 0.00 | 0.11 | 9 | 11 | ||
Adults | 13 | 0.00 | 0.13 | 15 | 22 | ||
6 | Grunn Taing | Adults | 67 | <0.01 | 1.44 | 18 | 20 |
7 | Tivaka Taing | Adults | 86 | 0.07 | 2.05 | 22 | 8 |
8 | Noust of Burraland | Adults | 88 | 0.11 | 2.19 | 16 | 13 |
9 | Mavis Grind | 10‑15 | 100 | 0.46 | 1.33 | 3 | 1 |
15‑21 | 63 | 0.27 | 1.13 | 8 | 11 | ||
21‑26 | 57 | <0.01 | 0.86 | 7 | 11 | ||
26‑35 | 50 | 0.01 | 0.90 | 10 | 9 | ||
Adults | 87 | 0.17 | 2.4 | 15 | 23 | ||
10 | Voxter Ness | Adults | 56 | 0.02 | 1.25 | 16 | 14 |
11 | Northward | Adults | 86 | 0.31 | 2.73 | 22 | 13 |
12 | Kames | 10‑15 | NA | NA | NA | 0 | 0 |
15‑21 | 50 | 1.10 | 1.00 | 12 | 6 | ||
21‑26 | 70 | 0.23 | 1.70 | 10 | 10 | ||
26‑35 | 70 | 0.15 | 1.70 | 10 | 11 | ||
Adults | 88 | 0.17 | 2.25 | 16 | 17 | ||
13 | Skaw Taing | Adults | 70 | 0.07 | 1.6 | 20 | 20 |
14 | Grunna Taing | Adults | 19 | 0.00 | 0.19 | 16 | 22 |
15 | Orfassary | Adults | 22 | <0.01 | 0.26 | 23 | 17 |
16 | Samphrey/The Helliach | Adults | 7 | <0.01 | 0.14 | 14 | 18 |
17 | Uynarey | Adults | 23 | <0.01 | 0.27 | 22 | 18 |
18 | Little Roe | Adults | 46 | <0.01 | 0.62 | 13 | 18 |
19 | The Brough | Adults | 4 | <0.01 | 0.08 | 24 | 15 |
22 | Sweinna Stack | Adults | 6 | 0.00 | 0.06 | 17 | 20 |
Summary of sampling carried out at sites 1-21 in Yell Sound and Sullom Voe for imposex development in toothed adult (*) and juvenile/sub-adult un-toothed adult (J) dogwhelks ( Nucella lapillus). Data taken from Bailey and Davies (1991), Harding et al. (1997), Minchin and Davies (2000), Gubbins et al (2005, 2008), Gubbins (2010) and the present survey.
Site | 1987 | 1990 | 1991 | 1993 | 1995 | 1997 | 1999 | 2001 | 2004 | 2007 | 2009 | 2011 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | - | - | *J | *J | *J | *J | *J | *J | *J | *J | *J | *J |
2 | - | - | * | * | * | * | * | * | * | * | * | * |
3 | * | * | *J | *J | *J | *J | *J | *J | *J | *J | *J | *J |
4 | * | * | * | * | * | * | * | * | * | * | * | * |
5 | * | *J | *J | *J | *J | *J | *J | *J | *J | *J | *J | *J |
6 | * | *J | * | * | * | * | * | * | * | * | * | * |
7 | * | * | * | * | * | * | * | * | * | * | * | * |
8 | * | *J | * | * | * | * | * | * | * | * | * | * |
9 | * | *J | *J | *J | *J | *J | *J | *J | *J | *J | *J | *J |
10 | * | * | * | * | * | * | * | * | * | * | * | * |
11 | * | *J | * | * | * | * | * | * | * | * | * | * |
12 | * | *J | * | *J | *J | * | *J | *J | *J | *J | *J | *J |
13 | * | * | * | * | * | * | * | * | * | * | * | * |
14 | - | - | * | * | * | * | * | * | * | * | * | * |
15 | - | - | * | * | * | * | * | * | * | * | * | * |
16 | - | - | * | * | * | * | * | * | * | * | * | * |
17 | * | * | * | * | * | * | * | * | * | * | * | * |
18 | * | * | * | * | * | * | * | * | * | * | * | * |
19 | - | - | * | * | * | * | * | * | * | - | * | * |
20 | - | - | * | * | * | * | * | * | * | - | * | - |
21 | - | - | - | - | - | *J | * | - | - | - | - | - |
22 | - | - | - | - | - | - | - | - | - | - | - | * |
Data from surveys undertaken in 1987-2011. Numbers of toothed dogwhelk ( Nucella lapillus) individuals, percentage of females (%F) and percentage of sterile females (%FS) at each site.
- = No sampling; 0 = No sterile females found.
Site | Site name | 1987 | 1990 | 1991 | 1993 | 1995 | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Total | %F | %FS | Total | %F | %FS | Total | %F | %FS | Total | %F | %FS | Total | %F | %FS | ||
1 | Easterwick | - | - | - | - | - | - | 48 | 60 | 0 | 40 | 45 | 0 | 41 | 56 | 0 |
2 | Burgo Taing | - | - | - | - | - | - | 40 | 73 | 0 | 40 | 43 | 0 | 41 | 20 | 0 |
3 | Billia Skerry | 41 | 54 | 0 | 41 | 56 | 0 | 40 | 50 | 0 | 40 | 43 | 0 | 40 | 48 | 0 |
4 | Scarf Stane | 40 | 63 | 0 | 41 | 46 | 0 | 38 | 45 | 0 | 40 | 40 | 19 | 40 | 43 | 0 |
5 | East of Ollaberry | 40 | 50 | 0 | 42 | 55 | 5 | 37 | 62 | 0 | 40 | 50 | 5 | 40 | 38 | 0 |
6 | Grunn Taing | 40 | 45 | 0 | 40 | 58 | 0 | 39 | 49 | 0 | 36 | 42 | 0 | 40 | 60 | 13 |
7 | Tivaka Taing | 40 | 45 | 22 | 39 | 41 | 71 | 39 | 44 | 29 | 38 | 42 | 19 | 40 | 30 | 25 |
8 | Noust of Burraland/ Blanches Geo | 40 | 35 | 21 | 28 | 32 | 33 | 38 | 30 | 91 | 40 | 33 | 15 | 40 | 43 | 59 |
9 | Mavis Grind | 40 | 48 | 21 | 43 | 49 | 55 | 29 | 28 | 63 | 26 | 15 | 50 | 40 | 43 | 35 |
10 | Voxter Ness | 30 | 57 | 65 | 40 | 75 | 77 | 39 | 26 | 60 | 40 | 25 | 60 | 40 | 35 | 57 |
11 | Northward | 40 | 40 | 44 | 36 | 28 | 30 | 40 | 28 | 91 | 41 | 32 | 77 | 40 | 25 | 40 |
12 | The Kames | 38 | 42 | 93 | 40 | 50 | 95 | 39 | 44 | 100 | 40 | 30 | 92 | 40 | 30 | 83 |
13 | Skaw Taing | 40 | 50 | 0 | 37 | 43 | 69 | 39 | 44 | 35 | 40 | 45 | 62 | 40 | 33 | 39 |
14 | Moss Bank/ Grunna Taing | - | - | - | - | - | - | 40 | 50 | 15 | 40 | 33 | 0 | 40 | 33 | 0 |
15 | Orfasay | - | - | - | - | - | - | 40 | 48 | 0 | 40 | 45 | 0 | 40 | 58 | 0 |
16 | Samphrey/The Helliack | - | - | - | - | - | - | 40 | 48 | 0 | 40 | 38 | 0 | 40 | 60 | 0 |
17 | Uynarey | 34 | 56 | 0 | 40 | 53 | 0 | 40 | 53 | 0 | 40 | 50 | 0 | 40 | 48 | 0 |
18 | Little Roe | 38 | 55 | 0 | 42 | 60 | 4 | 39 | 54 | 14 | 38 | 63 | 13 | 40 | 40 | 6 |
19 | Brough | - | - | - | - | - | - | 40 | 53 | 0 | 40 | 28 | 0 | 41 | 46 | 0 |
20 | Norther Geo | - | - | - | - | - | - | 40 | 43 | 0 | 40 | 23 | 0 | 38 | 63 | 0 |
21 | Breiwick | - | - | - | - | - | - | - | - | - | - | - | - | - | - | - |
Table 3 (continued)
Site | Site name | 1997 | 1999 | 2001 | 2004 | 2007 | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Total | %F | %FS | Total | %F | %FS | Total | %F | %FS | Total | %F | %FS | Total | %F | %FS | ||
1 | Easterwick | 40 | 40 | 0 | 40 | 45 | 0 | 40 | 60 | 0 | 39 | 56 | 0 | 40 | 65 | 0 |
2 | Burgo Taing | 40 | 63 | 0 | 40 | 40 | 0 | 40 | 50 | 0 | 40 | 63 | 0 | 40 | 50 | 0 |
3 | Billia Skerry | 40 | 58 | 0 | 40 | 50 | 0 | 40 | 43 | 0 | 40 | 35 | 0 | 39 | 38 | 0 |
4 | Scarf Stane | 40 | 53 | 0 | 40 | 45 | 6 | 39 | 44 | 59 | 38 | 37 | 7 | 40 | 58 | 0 |
5 | East of Ollaberry | 38 | 40 | 0 | 40 | 48 | 0 | 40 | 38 | 0 | 39 | 59 | 0 | 40 | 50 | 0 |
6 | Grunn Taing | 39 | 33 | 0 | 40 | 58 | 0 | 40 | 48 | 0 | 39 | 62 | 0 | 40 | 45 | 0 |
7 | Tivaka Taing | 39 | 54 | 10 | 40 | 65 | 10 | 40 | 48 | 0 | 39 | 72 | 0 | 40 | 48 | 0 |
8 | Noust of Burraland/ Blanches Geo | 40 | 43 | 24 | 40 | 55 | 9 | 40 | 40 | 25 | 39 | 46 | 6 | 40 | 68 | 11 |
9 | Mavis Grind | 40 | 28 | 27 | 40 | 20 | 13 | 40 | 30 | 42 | 39 | 46 | 22 | 40 | 23 | 11 |
10 | Voxter Ness | 40 | 38 | 7 | 40 | 25 | 0 | 40 | 53 | 5 | 40 | 53 | 10 | 40 | 23 | 0 |
11 | Northward | 40 | 35 | 7 | 40 | 35 | 0 | 40 | 23 | 0 | 40 | 43 | 18 | 37 | 35 | 8 |
12 | The Kames | 23 | 13 | 67 | 40 | 40 | 19 | 40 | 50 | 25 | 37 | 41 | 33 | 40 | 48 | 21 |
13 | Skaw Taing | 40 | 48 | 16 | 40 | 48 | 0 | 40 | 43 | 29 | 39 | 39 | 0 | 40 | 38 | 0 |
14 | Moss Bank/ Grunna Taing | 40 | 40 | 0 | 41 | 41 | 0 | 40 | 40 | 0 | 40 | 60 | 0 | 40 | 30 | 0 |
15 | Orfasay | 40 | 60 | 0 | 40 | 58 | 0 | 40 | 40 | 0 | 40 | 60 | 0 | 38 | 63 | 0 |
16 | Samphrey/ The Helliack | 40 | 38 | 0 | 40 | 45 | 0 | 40 | 35 | 0 | 40 | 38 | 0 | 40 | 50 | 0 |
17 | Uynarey | 40 | 45 | 0 | 40 | 40 | 0 | 40 | 45 | 0 | 39 | 46 | 0 | 40 | 43 | 0 |
18 | Little Roe | 40 | 38 | 0 | 40 | 45 | 0 | 39 | 41 | 6 | 42 | 57 | 0 | 40 | 45 | 0 |
19 | Brough | 40 | 35 | 0 | 40 | 45 | 0 | 40 | 48 | 0 | 39 | 46 | 0 | - | - | - |
20 | Norther Geo | 40 | 58 | 0 | 40 | 48 | 0 | 40 | 58 | 0 | 40 | 63 | 0 | - | - | - |
21 | Breiwick | 20 | 30 | 50 | 40 | 43 | 12 | - | - | - | - | - | - | - | - | - |
Table 3 (continued)
Site | Site name | 2009 | 2011 | ||||
---|---|---|---|---|---|---|---|
Total | %F | %FS | Total | %F | %FS | ||
1 | Easterwick | 40 | 55 | 0 | 40 | 70 | 0 |
2 | Burgo Taing | 40 | 65 | 0 | 38 | 76 | 0 |
3 | Billia Skerry | 40 | 58 | 0 | 40 | 20 | 0 |
4 | Scarf Stane | 40 | 50 | 0 | 10 | 30 | 0 |
5 | East of Ollaberry | 40 | 53 | 0 | 37 | 41 | 0 |
6 | Grunn Taing | 40 | 43 | 0 | 38 | 47 | 0 |
7 | Tivaka Taing | 38 | 58 | 0 | 30 | 73 | 0 |
8 | Noust of Burraland/ Blanches Geo | 39 | 49 | 0 | 29 | 55 | 0 |
9 | Mavis Grind | 40 | 40 | 0 | 38 | 39 | 0 |
10 | Voxter Ness | 39 | 31 | 0 | 30 | 53 | 0 |
11 | Northward | 39 | 56 | 0 | 35 | 63 | 0 |
12 | The Kames | 40 | 35 | 0 | 33 | 48 | 0 |
13 | Skaw Taing | 40 | 43 | 0 | 40 | 50 | 0 |
14 | Moss Bank/ Grunna Taing | 39 | 44 | 0 | 38 | 42 | 0 |
15 | Orfasay | 39 | 38 | 0 | 40 | 58 | 0 |
16 | Samphrey/ The Helliack | 40 | 45 | 0 | 32 | 44 | 0 |
17 | Uynarey | 40 | 53 | 0 | 40 | 55 | 0 |
18 | Little Roe | 40 | 48 | 0 | 31 | 42 | 0 |
19 | Brough | 38 | 58 | 0 | 39 | 62 | 0 |
20 | Norther Geo | 39 | 64 | 0 | - | - | - |
21 | Breiwick | - | - | - | - | - | - |
22 | Sweinna Stack | - | - | - | 37 | 46 | 0 |
RPSI and VDSI in adult dogwhelks ( Nucella lapillus) from populations in Sullom Voe and Yell Sound surveyed between 1987 and 2011.
J = sites at which juvenile/subadult surveys were carried out; - = No sampling.
RPSI
Site No | Site name | 1987 | 1990 | 1991 | 1993 | 1995 | 1997 | 1999 | 2001 | 2004 | 2007 | 2009 | 2011 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 J | Easterwick | - | - | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 1.43 | <0.01 | <0.01 | 0.00 | <0.01 |
2 | Burgo Taing | - | - | 3.37 | <0.01 | <0.01 | 0.02 | <0.01 | 0.03 | <0.01 | <0.01 | <0.01 | <0.01 |
3 J | Billia Skerry | 0.64 | 1.45 | 0.24 | 0.06 | 0.02 | 0.02 | 0.05 | 0.16 | 0.27 | <0.01 | 0.13 | 0.00 |
4 | Scarf Stane | 2.16 | 1.67 | 3.76 | 4.38 | 2.69 | 15.24 | 22.29 | 28.81 | 8.69 | 0.14 | <0.01 | 0.00 |
5 J | East of Ollaberry | 2.41 | 7.51 | 3.53 | 0.31 | 0.23 | 0.94 | 0.39 | 0.09 | 0.12 | <0.01 | <0.01 | 0.00 |
6 | Grunn Taing | 12.71 | 13.52 | 15.00 | 4.92 | 7.33 | 7.18 | 4.69 | 6.20 | 4.62 | 0.95 | 0.00 | <0.01 |
7 | Tivaka Taing | 58.85 | 34.19 | 23.72 | 14.06 | 20.34 | 19.90 | 21.52 | 14.21 | 10.55 | 3.45 | 0.54 | 0.07 |
8 | Noust of Burraland | 54.50 | 45.59 | 50.75 | 39.39 | 21.44 | 21.88 | 24.26 | 18.06 | 11.00 | 1.73 | 0.41 | 0.11 |
9 J | Mavis Grind | 40.91 | 30.24 | 30.15 | 23.19 | 11.63 | 24.11 | 21.33 | 28.61 | 20.33 | 4.29 | 1.08 | 0.17 |
10 | Voxter Ness | 58.54 | 39.59 | 41.32 | 32.38 | 27.65 | 28.05 | 24.27 | 27.65 | 12.63 | 2.69 | 0.01 | 0.02 |
11 | Northward | 34.03 | 30.54 | 42.57 | 31.37 | 26.70 | 36.70 | 40.26 | 30.71 | 14.73 | 7.86 | 0.31 | 0.31 |
12 J | The Kames | 56.78 | 69.44 | 54.93 | 37.49 | 31.32 | 73.12 | 35.65 | 34.03 | 16.99 | 0.90 | 0.26 | 0.17 |
13 | Skaw Taing | 42.46 | 32.34 | 45.00 | 18.26 | 20.59 | 27.16 | 20.02 | 23.61 | 14.43 | 2.59 | 0.26 | 0.07 |
14 | Moss Bank/ Grunna Taing | - | - | 5.04 | 0.18 | 0.37 | 0.76 | 0.64 | 0.50 | 0.07 | 0.01 | 0.67 | 0.00 |
15 | Orfassary | - | - | 0.54 | 0.05 | 0.09 | 0.01 | 0.59 | 0.02 | <0.01 | <0.01 | <0.01 | <0.01 |
16 | Samphrey/ The Helliack | - | - | 1.30 | <0.01 | 0.01 | 0.02 | <0.01 | 0.00 | <0.01 | <0.01 | <0.01 | <0.01 |
17 | Uynarey | 0.99 | 1.25 | 0.18 | 0.01 | 0.02 | 0.11 | 0.03 | 0.02 | 0.02 | <0.01 | <0.01 | <0.01 |
18 | Little Roe | 13.46 | 9.69 | 18.89 | 14.10 | 5.30 | 12.00 | 5.81 | 8.91 | 3.76 | 1.62 | 0.03 | <0.01 |
19 | The Brough | - | - | 0.63 | <0.01 | <0.01 | 0.00 | <0.01 | 0.00 | 0.01 | - | 0.01 | <0.01 |
20 | Norther Geo | - | - | 0.13 | 0.01 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | - | 0.00 | - |
21 | Breiwick | - | - | - | - | - | 38.89 | 33.51 | - | - | - | - | - |
22 | Sweinna Stack | - | - | - | - | - | - | - | - | - | - | - | 0.00 |
Table 4 (Continued)
VDSI
SITE NO. | SITE NAME | 1987 | 1990 | 1991 | 1993 | 1995 | 1997 | 1999 | 2001 | 2004 | 2007 | 2009 | 2011 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 J | Easterwick | - | - | 0.26 | 0.05 | 0.04 | 0.06 | 0.33 | 0.17 | 0.36 | 0.15 | 0.46 | 0.21 |
2 | Burgo Taing | - | - | 1.72 | 1.13 | 1.00 | 0.92 | 1.125 | 0.25 | 0.28 | 0.50 | 0.58 | 0.31 |
3 J | Billia Skerry | 2.32 | 2.35 | 2.30 | 2.06 | 1.11 | 1.04 | 1.25 | 1.76 | 1.79 | 1.20 | 1.50 | 0.38 |
4 | Scarf Stane | 3.44 | 3.42 | 3.53 | 3.75 | 3.82 | 3.67 | 4.06 | 4.59 | 4.07 | 2.56 | 0.95 | 0.67 |
5 J | East of Ollaberry | 3.21 | 3.95 | 3.39 | 2.55 | 2.47 | 2.33 | 2.68 | 1.60 | 1.57 | 0.70 | 0.38 | 0.13 |
6 | Grunn Taing | 4.00 | 4.00 | 4.00 | 3.73 | 4.13 | 4.00 | 4.00 | 4.00 | 3.46 | 3.50 | 0.59 | 1.44 |
7 | Tivaka Taing | 4.22 | 4.93 | 4.41 | 4.19 | 4.25 | 4.09 | 4.00 | 4.00 | 4.00 | 3.58 | 2.64 | 2.05 |
8 | Noust of Burraland | 4.21 | 4.33 | 5.00 | 4.15 | 4.65 | 4.24 | 4.09 | 4.31 | 4.05 | 4.00 | 3.53 | 2.19 |
9 J | Mavis Grind | 4.26 | 4.64 | 4.75 | 4.50 | 4.35 | 4.27 | 4.125 | 4.42 | 4.25 | 4.11 | 3.67 | 2.4 |
10 | Voxter Ness | 4.71 | 4.83 | 4.80 | 4.60 | 4.57 | 4.07 | 4.00 | 4.05 | 4.10 | 3.78 | 1.30 | 1.25 |
11 | Northward | 4.44 | 4.87 | 5.18 | 4.77 | 4.40 | 4.07 | 4.07 | 4.33 | 4.18 | 4.08 | 3.14 | 2.73 |
12 J | The Kames | 5.27 | 5.33 | 5.59 | 5.08 | 5.17 | 4.67 | 4.19 | 4.25 | 4.33 | 3.89 | 3.00 | 2.25 |
13 | Skaw Taing | 4.00 | 4.69 | 4.41 | 4.61 | 4.31 | 4.16 | 4.00 | 4.29 | 4.00 | 3.33 | 2.77 | 1.60 |
14 | Moss Bank/ Grunna Taing | - | - | 4.05 | 1.77 | 2.46 | 2.13 | 2.65 | 1.88 | 1.47 | 1.08 | 3.24 | 0.19 |
15 | Orfassary | - | - | 2.74 | 1.78 | 1.04 | 0.88 | 1.65 | 0.81 | 1.12 | 0.83 | 0.40 | 0.26 |
16 | Samphrey/ The Helliack | - | - | 2.32 | 0.53 | 0.63 | 0.87 | 0.72 | 0.43 | 0.40 | 0.20 | 0.33 | 0.14 |
17 | Uynarey | 2.58 | 2.86 | 2.05 | 1.20 | 0.90 | 1.56 | 1.375 | 0.78 | 1.17 | 0.82 | 0.38 | 0.27 |
18 | Little Roe | 4.00 | 4.04 | 4.14 | 4.13 | 4.06 | 3.93 | 3.94 | 2.19 | 3.63 | 3.56 | 1.95 | 0.62 |
19 | The Brough | - | - | 2.57 | 1.09 | 1.16 | 0.43 | 0.83 | 0.61 | 0.89 | - | 0.38 | 0.08 |
20 | Norther Geo | - | - | 1.35 | 0.56 | 0.00 | 0.30 | 0.43 | 0.17 | 0.08 | - | 0.20 | - |
21 | Breiwick | - | - | - | - | - | 4.50 | 4.10 | - | - | - | - | - |
22 | Sweinna Stack | - | - | - | - | - | - | - | - | - | - | - | 0.06 |
Oslo and Paris Commission biological effects assessment criteria for imposex in Nucella lapillus, based on VDSI ( OSPAR, 2004) and amended to show which classes exceed Background Assessment Criteria ( BAC) and Environmental Assessment Criteria ( EAC).
Assessment class | Nucella VDSI | Effects and impacts |
---|---|---|
A (< BAC) | VDSI = <0.3 | The level of imposex in the more sensitive gastropod species is close to zero (0 - ~30% of females have imposex) indicating exposure to TBT concentrations close to zero, which is the objective in the OSPAR strategy of hazardous substances. |
B (> BAC < EAC) | VDSI = 0.3 - <2.0 | The level of imposex in the more sensitive gastropod species (~30 - ~100 % of the females have imposex) indicates exposure to TBT concentrations below the EAC derived for TBT. E.g. adverse effects in the more sensitive taxa of the ecosystem caused by long-term exposure to TBT are predicted to be unlikely to occur. |
C (> EAC) | VDSI = 2.0 - <4.0 | The level of imposex in the more sensitive gastropod species indicates exposure to TBT concentrations higher than the EAC derived for TBT. E.g. there is a risk of adverse effects, such as reduced growth and recruitment, in the more sensitive taxa of the ecosystem caused by long-term exposure to TBT. |
D (> EAC) | VDSI = 4.0 - 5.0 | The reproductive capacity in the populations of the more sensitive gastropod species, such as Nucella lapillus, is affected as a result of the presence of sterile females, but some reproductively capable females remain. E.g. there is evidence of adverse effects, which can be directly associated with the exposure to TBT. |
E (> EAC) | VDSI = > 5.0 | Populations of the more sensitive gastropod species, such as Nucella lapillus, are unable to reproduce. The majority, if not all females within the population have been sterilized. |
F (> EAC) | VDSI = - | The populations of the more sensitive gastropod species, such as Nucella lapillus and Ocinebrina aciculata, are absent/expired. |
Temporal changes in OSPAR imposex classes at sites in Sullom Voe and Yell Sound. See Table 5 for key to OSPAR classes (A: VDSI<0.3; E: VDSI>5.0).
Site | 1987 | 1990 | 1991 | 1993 | 1995 | 1997 | 1999 | 2001 | 2004 | 2007 | 2009 | 2011 |
---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | - | - | A | A | A | A | B | A | B | A | B | A |
2 | - | - | B | B | B | B | B | A | A | B | B | B |
3 | C | C | C | C | B | B | B | B | B | B | B | B |
4 | C | C | C | C | C | C | D | D | D | C | B | B |
5 | C | C | C | C | C | C | C | B | B | B | B | A |
6 | D | D | D | C | D | D | D | D | C | C | B | B |
7 | D | D | D | D | D | D | D | D | D | C | C | C |
8 | D | D | D | D | D | D | D | D | D | D | C | C |
9 | D | D | D | D | D | D | D | D | D | D | C | C |
10 | D | D | D | D | D | D | D | D | D | C | B | B |
11 | D | D | E | D | D | D | D | D | D | D | C | C |
12 | E | E | E | E | E | D | D | D | D | C | C | C |
13 | D | D | D | D | D | D | D | D | D | C | C | B |
14 | - | - | D | B | C | C | C | B | B | B | C | A |
15 | - | - | C | B | B | B | B | B | B | B | B | A |
16 | - | - | C | B | B | B | B | B | B | A | B | A |
17 | C | C | C | B | B | B | B | B | B | B | B | A |
18 | D | D | D | D | D | C | C | C | C | C | B | B |
19 | - | - | C | B | B | B | B | B | B | - | B | A |
20 | - | - | B | B | A | A | B | A | A | - | A | - |
22 | - | - | - | - | - | - | - | - | - | - | - | A |
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