| Forside | | Indhold | | Tilbage | | Udskriftsvejledning |
Organiske miljøfremmede stoffer og tungmetaller i havsedimenter
Tabel 2 Koncentrationer af organiske miljøfremmede stoffer beregnet på tørstof
Havsedimenter |
Kattegat st. 905 |
Øresund st.431 |
Mecklenburg Bugt - st. M2 |
Smålands- farvandet - Skellerev |
Karrebæks- minde Bugt |
Roskilde Fjord |
Nibe Bredning |
Marselisborg Lystbådehavn¹ |
Odense Fjord |
Øresund Konge- dybet |
Horsens Fjord |
Enhed: µg/kg ts
Parameter |
O-71-1 |
O-71-2a |
O-71-3 |
O-71-4 |
O-71-6 |
O-71-7 |
O-71-8 |
140-15 (99) |
O-72-2 |
O-72-3 |
O-72-6 |
Blødgørere |
2000 |
1999 |
|
Di-iso-nonylphthalat |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
i.a. |
<5 |
<5 |
<5 |
Di(2-ethylhexyl)adipat |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
i.a. |
<5 |
<5 |
<5 |
Di(2-ethylhexyl)phthalat |
< 10 |
< 10 |
< 10 |
< 10 |
< 10 |
< 10 |
< 10 |
91 |
850 |
< 10 |
< 10 |
< 10 |
Butylbenzylphthalat |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<40 |
<5 |
<5 |
<5 |
Diethylphthalat |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<40 |
<5 |
<5 |
<5 |
Dimethylphthalat |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<40 |
<5 |
<5 |
<5 |
Di-n-butylphthalat |
< 10 |
< 10 |
15 |
< 10 |
< 10 |
17 |
< 10 |
< 10 |
87 |
< 10 |
< 10 |
< 10 |
Di-n-octylphthalat |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<5 |
<40 |
<5 |
<5 |
<5 |
Nonylphenoler |
4-Octylphenol |
<20 |
<20 |
<20 |
<20 |
<20 |
<20 |
<20 |
<20 |
i.a. |
<20 |
<20 |
<20 |
Bisphenol A |
<10 |
<10 |
<10 |
<10 |
<10 |
<10 |
<10 |
<10 |
i.a. |
<10 |
<10 |
<10 |
Nonylphenol (+EO1 og EO2) |
<10 |
<10 |
<10 |
<10 |
<10 |
17 |
<10 |
41 |
170 |
<10 |
11 |
32 |
P-triestere |
Tributylphosphat |
<5 |
<5 |
<5 |
5.7 |
5.2 |
<5 |
<5 |
28.6 |
<35 |
5.7 |
18 |
5.4 |
Tricresylphosphat |
<5 |
<5 |
<5 |
<5 |
<5 |
370 |
<5 |
<5 |
<35 |
<5 |
<5 |
<5 |
Triphenylphosphat |
<10 |
<10 |
<10 |
<10 |
<10 |
<10 |
<10 |
<10 |
<35 |
<10 |
<10 |
<10 |
Tris-1.3-dichlorisopropylphosphat |
<20 |
<20 |
<20 |
<20 |
<20 |
<20 |
<20 |
<20 |
i.a. |
32 |
17 |
7.2 |
PAH |
Naphthalen |
39 |
5.8 |
18 |
7.5 |
3.4 |
4.4 |
<3 |
34 |
24 |
4.7 |
11 |
8.9 |
2-Methylnaphthalen |
57 |
6.8 |
16 |
6.2 |
3.1 |
3.9 |
<3 |
31 |
i.a. |
4.0 |
11 |
7.6 |
1-Methylnaphthalen |
37 |
4.7 |
9.4 |
4.2 |
<3 |
3.1 |
<3 |
25 |
i.a. |
<3 |
6.7 |
7.3 |
Biphenyl |
18 |
3.1 |
7.4 |
3.2 |
<3 |
<3 |
<3 |
11 |
i.a. |
<3 |
4.2 |
4.1 |
1.5-Dimethylnaphthalen |
32 |
4.7 |
8.0 |
4.8 |
<3 |
<3 |
<3 |
24 |
i.a. |
<3 |
3.1 |
4.0 |
Acenaphthylen |
5.3 |
3.1 |
6.2 |
5.2 |
4.8 |
5.6 |
<3 |
60 |
58 |
11 |
6.9 |
8.2 |
Acenaphthen |
12 |
5.2 |
7.8 |
5.8 |
<3 |
<3 |
<3 |
31 |
18 |
3.8 |
6.8 |
11 |
Dibenzofuran |
37 |
6.9 |
20 |
11.3 |
4.4 |
4.4 |
<3 |
29 |
i.a. |
3.8 |
6.8 |
15 |
2.3.5-trimethylnaphthalen |
37 |
5.2 |
9.5 |
9.5 |
4.1 |
4.8 |
<3 |
41 |
i.a. |
4.1 |
6.8 |
14 |
Fluoren |
14 |
5.7 |
12 |
6.9 |
<3 |
<3 |
<3 |
38 |
31 |
4.6 |
4.9 |
14 |
1-Methylfluoren |
<3 |
3.4 |
3.5 |
<3 |
<3 |
<3 |
<3 |
11 |
i.a. |
<3 |
14 |
4.6 |
Dibenzothiophen |
7.5 |
3.1 |
5.9 |
6.1 |
<3 |
3.1 |
<3 |
31 |
i.a. |
3.3 |
3.1 |
6.4 |
Phenanthren |
67 |
25 |
62 |
54 |
32 |
28 |
<3 |
360 |
300 |
50 |
38 |
62 |
Anthracen |
11 |
11 |
14 |
12 |
6.7 |
7.5 |
<3 |
64 |
81 |
13 |
10 |
18 |
Carbazol |
5.4 |
<3 |
6.6 |
<3 |
<3 |
<3 |
<3 |
41 |
i.a. |
5.4 |
6.3 |
5.7 |
2-Methylphenanthren |
23 |
7.3 |
19 |
15 |
11 |
12 |
<3 |
80 |
i.a. |
14 |
9.1 |
12 |
2-Methylanthracen |
<3 |
<3 |
3.9 |
3.1 |
<3 |
<3 |
<3 |
16 |
i.a. |
4.1 |
3.5 |
6.5 |
1-Methylphenanthren |
12 |
5.8 |
9.5 |
10.1 |
5.4 |
6.8 |
<3 |
35 |
i.a. |
6.1 |
3.8 |
8.8 |
3.6-Dimethylphenanthren |
7.1 |
<3 |
3.7 |
4.5 |
<3 |
<3 |
<3 |
13 |
i.a. |
4.2 |
<3 |
3.5 |
Fluoranthen |
120 |
49 |
140 |
270 |
140 |
120 |
<3 |
940 |
960 |
120 |
72 |
140 |
Pyren |
100 |
49 |
140 |
240 |
120 |
110 |
<3 |
840 |
850 |
100 |
67 |
120 |
1-Benzofluoren |
23 |
11 |
24 |
44 |
25 |
19 |
<3 |
110 |
i.a. |
19 |
12 |
26 |
1-Methylpyren |
8.6 |
4.6 |
9.8 |
10 |
5.0 |
6.5 |
<3 |
49 |
i.a. |
6.2 |
3.9 |
7.1 |
Benz(a)anthracen |
110 |
34 |
100 |
130 |
80 |
70 |
<3 |
410 |
420 |
67 |
43 |
89 |
Chrysen/Triphenylen |
150 |
42 |
130 |
140 |
80 |
60 |
<3 |
450 |
490 |
70 |
45 |
110 |
Benzo(b+k+j)flouranthen |
600 |
130 |
560 |
570 |
200 |
170 |
6.9 |
1100 |
920 |
170 |
115 |
425 |
Benz(e)pyren |
260 |
51 |
220 |
230² |
80² |
78 |
4.8 |
460 |
i.a. |
70 |
47 |
175 |
Benz(a)pyren |
81 |
39 |
120 |
|
|
14 |
<3 |
300 |
620 |
76 |
50 |
130 |
Perylen |
20 |
12 |
14 |
<3 |
<3 |
<3 |
<3 |
75 |
i.a. |
30 |
20 |
32 |
Indeno(1.2.3-cd)pyren |
170 |
49 |
280 |
390 |
13 |
29 |
3.3 |
320 |
300 |
73 |
54 |
145 |
Dibenzo(a,h)anthracen |
17 |
5.2 |
14 |
130 |
6.7 |
10 |
<3 |
95 |
57 |
7.3 |
5.5 |
13 |
Benzo(ghi)perylen |
160 |
49 |
240 |
320 |
7.0 |
27 |
<3 |
343 |
270 |
62 |
47 |
110 |
Sum PAH |
2241 |
628 |
2234 |
2643 |
832 |
797 |
15 |
6467 |
5399 |
1007 |
737 |
1741 |
Individuel chlorbiphenyler (PCB) |
CB#28 |
0.61 |
0.2 |
0.25 |
0.32 |
0.12 |
0.48 |
<0.1 |
0.36 |
<10 |
0.13 |
0.27 |
0.75 |
CB#52 |
0.61 |
0.16 |
0.19 |
0.46 |
<0.1 |
0.59 |
0.39 |
1.3 |
<10 |
0.16 |
0.18 |
0.18 |
CB#101 |
0.56 |
0.36 |
0.66 |
0.38 |
0.17 |
0.94 |
<0.1 |
2.1 |
<10 |
0.14 |
0.44 |
0.86 |
CB#118 |
0.68 |
0.38 |
0.58 |
0.57 |
0.19 |
1.3 |
<0.1 |
2.0 |
<10 |
0.21 |
0.45 |
0.66 |
CB#138 |
0.78 |
0.57 |
1.7 |
0.79 |
0.41 |
2.0 |
<0.1 |
4.5 |
<10 |
0.68 |
1.1 |
3.8 |
CB#153 |
0.81 |
0.57 |
1.9 |
0.70 |
0.41 |
1.7 |
<0.1 |
4.0 |
<10 |
0.50 |
1.3 |
3.7 |
CB#180 |
0.49 |
<0.1 |
0.73 |
0.59 |
<0.1 |
0.36 |
<0.1 |
2.0 |
<10 |
<0.1 |
0.97 |
1.1 |
Sum CB-7 |
4.54 |
2.23 |
6.01 |
3.81 |
1.3 |
7.37 |
0.39 |
16.26 |
|
1.82 |
4.71 |
11.02 |
Chlorerede pesticider |
Aldrin |
<0.1 |
<0.1 |
<0.1 |
0.16 |
<0.1 |
0.38 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
HCH, alpha- |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
0.4 |
<20 |
<0.1 |
12 |
<0.1 |
HCH, beta- |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
1.2 |
<0.1 |
<0.1 |
<20 |
<0.1 |
12 |
<0.1 |
HCH, delta- |
1.6 |
0.51 |
<0.1 |
0.95 |
0.29 |
0.36 |
<0.1 |
4.3 |
<20 |
<0.1 |
<0.1 |
1.4 |
HCH, gamma- |
5.8 |
2.4 |
4.5 |
3.8 |
2.5 |
1.8 |
<0.1 |
16 |
<20 |
2.8 |
1.3 |
5.2 |
DDD, p,p'- |
0.69 |
0.34 |
1.4 |
1.5 |
0.37 |
1.5 |
<0.1 |
1.3 |
<20 |
<0.1 |
<0.1 |
0.83 |
DDE, p,p'- |
0.82 |
0.37 |
1.8 |
0.88 |
0.52 |
0.61 |
<0.1 |
1.8 |
<40 |
0.14 |
0.18 |
0.7 |
DDT, p,p'- |
1.9 |
0.92 |
2.8 |
1.6 |
1.7 |
3.5 |
3.3 |
23 |
<20 |
2.9 |
2.5 |
1.1 |
Dieldrin |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
0.64 |
<0.1 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Endosulfan I |
2.6 |
1.7 |
3.8 |
2.5 |
1.2 |
2.4 |
<0.1 |
7.5 |
<20 |
1.7 |
1.9 |
<0.1 |
Endosulfan II |
0.69 |
<0.1 |
<0.1 |
4.5 |
1.0 |
1.4 |
0.93 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Endosulfan sulfat |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
0.39 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Endrin |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
2.0 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Endrin Aldehyd |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Endrin Keton |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Heptachlor |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Heptachlorepoxid |
0.34 |
<0.1 |
<0.1 |
0.38 |
<0.1 |
<0.1 |
<0.1 |
0.32 |
<20 |
<0.1 |
<0.1 |
<0.1 |
Methoxychlor |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<0.1 |
<40 |
<0.1 |
<0.1 |
<0.1 |
Sum pesticider |
14.4 |
6.2 |
14.3 |
16.3 |
8.2 |
15.5 |
4.2 |
54.6 |
0.0 |
7.5 |
29.9 |
9.2 |
LAS |
<200 |
<200 |
540 |
<200 |
<200 |
<200 |
<200 |
320 |
300 |
<200 |
<200 |
5500 |
THC mg/kg ts |
14 |
5.2 |
9.3 |
12 |
5.2 |
12 |
3 |
60 |
147 |
7.5 |
16 |
480 |
i.a. = ikke analyseret
1 Marselisborg Lystbådehavn: 2000 data analyseret efter ny metode til sammenligning er anført 1999 data, som er analyseret med en anden GCMS-metode.
2 Der er kun angivet et tal for benz(e) og benz(a), da det ikke var muligt at adskille de to toppe chromatografisk.
| Forside | | Indhold | | Tilbage | | Udskriftsvejledning |
Version 1.0 Januar 2006, © Miljøstyrelsen.
|