|
| Forside | | Indhold | | Forrige | | Næste |
Brug af regnvand opsamlet fra tage og befæstede arealer
Bilag B
Karakteristik af opsamlet regnvand (tabeller)
Dette bilag indeholder resultatet af litteraturundersøgelsen med henblik på at finde parametre, der er målt i opsamlet regnvand. Resultatet præsenteres på de
følgende sider i tabeller. Parametrene er opdelt i stofgrupper efter princippet i NOVA 2003, samt nogle ekstra tabeller for andre parametre og mikroorganismer. I
tabellerne angives parametrene i første kolonne og i tabellens anden og tredje kolonner oplyses henholdsvis intervallet for de målte værdier (oftest koncentrationer)
og antallet af forskellige lokaliteter hvor parameteren er undersøgt. Hvis der er foretaget målinger af et stof uden at stoffet har kunne detekteres angives
koncentrationen som <detektionsgrænsen, hvis denne er oplyst, ellers angives værdien som ”nd” (not detected). Hvis stoffet er fundet i en undersøgelse, hvor
koncentrationen ikke er oplyst angives værdien for stoffet som ”d” (detected). I sidste kolonne angives et nummer, der henviser til referencerne under tabellerne.
Parametrene er grupperet i 8 tabeller ved følgende indhold:
Tabel B1: Fysiske parametre
Tabel B2: Kemiske parametre
Tabel B3: Tungmetaller og overgangselementer
Tabel B4: Miljøfremmede organiske stoffer
Tabel B5: Cytotoksicitet, genotoksicitet og mutagenicitet af afstrømningsvand fra motorveje
Tabel B6: Toksicitet af regnvand
Tabel B7. Generelle mikrobielle parametre i opsamlet regnvand fra tage
Tabel B8. Indikatororganismer i opsamlet regnvand
Tabel B1. Fysiske parametre.
| Partikelkarakteristik |
Interval (mg/L) |
Antal
lokaliteter |
Referencer |
| D <100 µm (%) |
76-85 |
2 |
1 |
| D10 (µm) |
5,7-180 |
5 |
1, 4, 5, 6 |
| D30 (µm) |
200-450 |
3 |
4, 5, 6 |
| D50 (µm) |
29-785 |
5 |
1, 4, 5, 6 |
| D60 (µm) |
480-1200 |
3 |
4, 5, 6 |
| D90 (µm) |
265-1375 |
2 |
1 |
| Dn (µm) |
0, 10-0, 95 |
21 |
7 |
| Dv (µm) |
28,22-147,97 |
21 |
7 |
| |
|
|
|
| Specific mass of part <100µm (g/cm³) |
2,36-2,57 |
2 |
1 |
| Specific mass of part >100µm (g/cm³) |
1,38-2,54 |
2 |
1 |
| Specific mass of part Total (g/cm³) |
2,19-2,56 |
2 |
1 |
| |
|
|
|
| Filtrable solids |
49-64 |
1 |
41 |
| Residue filterable |
88-283 |
10 |
43 |
| Residue suspended |
65-3861 |
10 |
43 |
| SS (suspended solids) |
0,5-5700 |
125 |
3, 9, 10, 11, 12, 13, 16, 20, 21, 22, 23, 25, 26, 37, 38, 39, 40, 44, 45,
46, 47, 48, 49, 50, 51, 52, 53, 54, 55, 56, 57, 58, 59, 60, 61, 62, 63, 64, 65,
66, 67, 68, 69, 70, 99 |
| SS ≥1,0µm |
18-230 |
2 |
71 |
| SS ≥1,6µm |
18-220 |
2 |
71 |
| TDR (total dried residue) |
240-5500 |
1 |
18 |
| TS (total solids) |
47-81728 |
16 |
3,31,40,45 |
| TSS (total suspended solids) |
<3-9880 |
70 |
2, 3, 4, 5, 6, 7, 8, 14, 15, 18, 19, 27, 31, 34, 35, 42, 56, 72, 73, 74, 75,
76, 77, 78 |
| TVS (total volatile solids) |
0,5-2300 |
1 |
31 |
| VSS (volatile suspended solids) |
2-490 |
20 |
4, 5, 6, 20, 38, 49, 72, 74 |
| Ionindhold |
Interval (mg/L) |
Antal
lokaliteter |
Referencer |
| EC (mS) |
0,053-0,317 |
21 |
7 |
| Electrical conductivity (µS/cm) |
0-110000 |
67 |
2, 3, 8, 9, 10, 11, 12, 13, 14, 15, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25,
26, 27, 28, 30, 31, 32, 33, 34, 35, 36, 37, 38, 39, 40 |
| TDS (total dissolved solids) |
13-81700 |
17 |
2, 3, 4, 5, 6, 14, 27, 31, 34, 40, 64, 72, 73 |
| VDS (volatile dissolved solids) |
12,6-204,3 |
3 |
4, 5, 6 |
| SSdiss |
16 |
1 |
54 |
| Mineral matters (%) |
52-92 |
1 |
42 |
| Soluble substances |
50, 0-10930 |
1 |
10 |
| Andre fysiske parametre |
Interval |
Antal
lokaliteter |
Referencer |
| Colour (mg/L or Pt) |
66-279 |
1 |
2 |
| Colour (Colour Unit) |
50-20000 |
1 |
3 |
| Turbidity (NTU) |
1,5-400 |
19 |
2, 3, 14, 20, 24, 28, 31 |
| Temperature (°C) |
1,0-31 |
19 |
3, 13, 20, 24, 28, 30, 40 |
| Generel vandkemi |
Interval (mg/L) |
Antal
lokaliteter |
Referencer |
| Cl |
0,7-46000 |
46 |
3, 10, 11, 12, 18, 20, 21, 23, 27, 28, 31, 32, 34, 35, 37, 41, 46, 47, 48,
52, 55, 56, 79, 91, 92, 99 |
| Dissolved oxygen |
0,0-14,8 |
19 |
3, 11, 15, 20, 24, 28, 30 |
| F |
0,1-0,2 |
4 |
91 |
| FR |
27-3700 |
13 |
82 |
| Hardness |
3,47-800 |
14 |
28, 30, 83, 84 |
| Hardness (as CaCO3) |
1,5-880 |
6 |
8, 15, 19, 23 |
Tabel B2. Kemiske parametre (fortsat).
| Generel vandkemi (fortsat) |
Interval (mg/L) |
Antal lokaliteter |
Referencer |
| ICH2 |
2,02-34,00 |
1 |
42 |
| NFR |
4-3600 |
13 |
82 |
| ORP (mV) |
+158-+267 |
2 |
4, 5 |
| pH |
3,81-9,8 |
104 |
2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14, 15, 16, 17, 19, 20, 21, 22, 23,
24, 25, 26, 27, 28, 30, 31, 33, 34, 35, 36, 39, 41, 46, 55, 61, 62, 69, 79, 83,
89, 90 |
| SAR |
0,58-18 |
1 |
33 |
| SO42- |
0,04-680 |
28 |
3, 10, 12, 20, 21, 27, 28, 31, 34, 63, 82, 93, 99 |
| S-SO4diss |
2-79 |
1 |
42 |
| Sulfides (S2-) |
0,0-15,0 |
1 |
10 |
| Pufferkapacitet |
Interval (mg/L) |
Antal lokaliteter |
Referencer |
| Acid capacity (mmol/L) |
0,94-1,98 |
1 |
41 |
| Acidity |
1,1-55,6 |
3 |
3, 30 |
| Alkalinity (CaCO3) |
11-520 |
14 |
15, 19, 20, 21, 23, 30, 34, 79 |
| Alkalinity total |
1,4-326,2 |
9 |
2, 3, 28, 32 |
| Sumparametre for organisk materiale |
Interval (mg/L) |
Antal lokaliteter |
Referencer |
| Aliphatic compunds particulate |
0,18-28,83 |
1 |
14 |
| Aliphatic compunds soluble |
0,090-1,870 |
1 |
14 |
| Aliphatic hydrocarbons |
0,00005-2,179 |
9 |
68,93,97,98 |
| AOX |
0,0015-0,1972 |
1 |
17 |
| Aromatic hydrocarbons (µg/L) |
nd |
1 |
93 |
| Aromatic hydrocarbons (µg chrysene eqv./L) |
20-64 |
1 |
59 |
| DOC |
0,3-331 |
20 |
12, 16, 17, 22, 25, 27, 39, 70, 74 |
| DOC (mM) |
0,5-3 |
2 |
79 |
| Hydrocarbons |
0,037-4,032 |
5 |
51 |
| Mineral oil |
0,23-7,02 |
4 |
37, 41 |
| MOTH, mineral oil type hydrocarbons |
0,7-18,5 |
4 |
85 |
| n-Hexane extracts |
1,0-825,8 |
6 |
58 |
| NVOC |
4,5-14 |
2 |
11 |
| Oil & grease |
<0,1-161 |
36 |
2, 3, 15, 20, 34, 43, 46, 69, 71, 73, 74, 76, 86, 87, 88 |
| Oil & grease on SS ≥1,0µm |
0,5-3,5 |
1 |
71 |
| Oil & grease on SS ≥1,6µm |
0,3-3,4 |
1 |
71 |
| Particulate polar compounds |
0,22-9,81 |
1 |
14 |
| Particulate aromatic compunds |
0,18-2,10 |
1 |
14 |
| POC |
28,9-53,0 |
1 |
39 |
| Soluble aromatic compunds |
0,11-2,44 |
1 |
14 |
| Soluble polar compounds |
0,15-5,630 |
1 |
14 |
| TC |
20-46 |
3 |
74 |
| TEO (Total Extractable Organics) |
4,07-9,42 |
1 |
14 |
| TEOparticulate |
1,64-6,71 |
1 |
14 |
| TEOsoluble |
2,71-3,66 |
1 |
14 |
| TOC |
<0,7-390 |
36 |
2, 9, 14, 18, 20, 27, 31, 34, 63, 75, 82, 87, 93 |
| Tot Petroleum Hydrocarbons (TPH) |
<0,05-12,6 |
6 |
7, 72 |
| Total aromatic hydrocarbons |
0,0151-0,0355 |
5 |
97 |
| Total hydrocarbons |
0,081 -400 |
14 |
11, 19, 26, 35, 44, 47, 55 |
| Total hydrocarbons particulate |
1,040 |
1 |
94 |
| Total hydrocarbons soluble |
0,0954 |
1 |
94 |
| UCM (Unresolved complex mixtures) |
0,450-1,926 |
5 |
97 |
Tabel B2. Kemiske parametre (fortsat).
| Iltforbrug |
Interval (mg/L) |
Antal lokaliteter |
Referencer |
| BOD |
1-6700 |
18 |
15, 34, 46, 47, 66, 74, 76, 80 |
| BOD5 |
0,9-324 |
65 |
2, 3, 10, 30, 31, 43, 49, 50, 51, 57, 58, 69, 78, 81, 82 |
| COD |
2-270000 |
101 |
2, 3, 4, 5, 6, 9, 10, 11, 15, 18, 19, 21, 23, 26, 27, 31, 34, 35, 37, 38,
41, 42, 43, 44, 46, 49, 50, 51, 52, 54, 55, 56, 57, 58, 59, 60, 66, 69, 73, 74,
76, 81 |
| CODdiss |
4,4-84 |
4 |
42, 54 |
| Næringsstoffer |
Interval (mg/L) |
Antal lokaliteter |
Referencer |
| KJD-N |
0,3-39 |
15 |
31, 46, 82 |
| N inorg. |
0,637-0,870 |
1 |
64 |
| N org. |
0,377-6,9 |
4 |
38, 64 |
| N susp. |
1,282-1,951 |
1 |
64 |
| NH3 |
0,05-23 |
3 |
15, 30, 43 |
| NH3-N |
0,009-6,6 |
19 |
70, 73, 82 |
| NH3unionized |
0,001-0,010 |
1 |
84 |
| NH4+ |
0,011-4,88 |
11 |
3, 35, 38, 79, 99 |
| NH4-N |
0,1-4,2 |
12 |
10, 11, 20, 34, 37, 41, 57, 90 |
| NH4-Ndiss |
<0,01-1,01 |
1 |
42 |
| NO2 |
0,01-1,2 |
5 |
3, 28 |
| NO2-N |
0,003-10,60 |
13 |
10, 28, 34, 41, 82 |
| NO3- |
0,01-77,4 |
23 |
3, 9, 10, 28, 35, 38, 79-91, 99 |
| NO3 & NO2 |
0,08-5 |
11 |
31,43 |
| NO3 & NO2 as N |
<0,01-13,37 |
10 |
20, 34, 46, 73, 90 |
| NO3-N |
0,004-23,0 |
25 |
32, 41, 58, 74, 82, 100 |
| NO3-Ndiss |
0,30-1,70 |
1 |
42 |
| Ntot |
0,18-39,72 |
27 |
9, 20, 31, 34, 38, 47, 52, 54, 55, 56, 59, 66, 79, 81, 90 |
| Ntotdiss |
0,68-21,65 |
2 |
54 |
| Organic N as N |
0,842-2,3 |
3 |
20, 90 |
| P ortho |
<0,01-2,2 |
17 |
23,73,79,82,90 |
| Pdiss |
<0,001-1,45 |
27 |
20, 38, 43, 45, 64 |
| Phosphates total |
0,008-2,580 |
2 |
2, 3 |
| PO4 |
0,01-22,6 |
9 |
10, 28, 30 |
| PO4-P |
0,07-7,02 |
8 |
32, 58, 100 |
| PO4-Pdiss |
<0,01-0,38 |
2 |
20, 42 |
| Psusp |
0,413-0,697 |
1 |
64 |
| Ptot |
<0,005-13 |
109 |
7, 15, 20, 23, 28, 31, 34, 37, 38, 42, 43, 45, 52, 54, 55, 56, 57, 58, 59,
60, 66, 73, 77, 82, 90, 101, 102 |
| Ptotdiss |
<0,01-3,49 |
3 |
54, 57 |
| TKN |
0,04-7,1 |
53 |
7, 15, 26, 35, 43, 58, 60, 65, 73, 76 |
| TKN-N |
<1,0-400 |
4 |
20, 34, 42 |
| TKN-Ndiss |
<0,02-1,31 |
1 |
42 |
Tabel B3. Tungmetaller og overgangselementer
| Tungmetaller og uorganiske sporstoffer |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| Ag |
<0,2-4 |
13 |
28, 43, 96 |
| Al |
5,0-71300 |
26 |
31, 61, 63, 91, 103, 119 |
| As |
0,1-340 |
26 |
28, 31, 34, 43, 86, 91, 95, 96, 103, 108, 109 |
| Ba |
40-120 |
9 |
75,91,103 |
| Be |
<0,2-49 |
8 |
91, 95, 96 |
| Ca (mg/L) |
0,131-480 |
36 |
2, 12, 18, 21, 24, 27, 30, 32, 34, 41, 59, 62, 79, 91, 92, 99 |
| Cd |
<0,1-700 |
141 |
2, 9, 11, 12, 15, 18, 21, 22, 25, 26, 27, 30, 31, 34, 37, 38, 39, 41, 43,
46, 48, 49, 50, 51, 55, 56, 59, 61, 63, 64, 67, 73, 77, 81, 82, 84, 86, 91, 92,
95, 96, 102, 105, 106, 107, 108, 109, 110, 111, 112 |
| Cd (ppm dry wt) |
0,003-0,795 |
5 |
113 |
| Cddiss |
<0,01-12 |
38 |
16, 23, 35, 45, 53, 79, 107, 113, 114, 115, 116 |
| Cdpart |
<0,01-7,2 |
8 |
35, 53, 79, 115 |
| Cdtot |
0,04-30 |
25 |
3, 20, 23, 45, 62, 101, 103, 114 |
| Cdtot (µg/g) |
0,07-26,7 |
21 |
23, 35, 70, 117 |
| Co |
1,3-6,7 |
9 |
91, 103, 105, 108 |
| Cr |
<0,5-4200 |
99 |
2, 11, 15, 18, 31, 34, 37, 38, 41, 43, 46, 55, 61, 63, 64, 73, 82, 84, 86,
90, 91, 95, 96, 105, 108, 109, 110, 112, 119, 123 |
| Crdiss |
0,2-2,6 |
4 |
79, 114 |
| Crpart |
0,1-9,6 |
2 |
78 |
| Crtot |
0,44-230 |
23 |
3, 20, 27, 45, 70, 101, 103, 114 |
| 137Cs (Bq/L) |
3-268000 |
1 |
104 |
| Cu |
<0,5-6800 |
150 |
2, 8, 11, 12, 15, 18, 21, 22, 25, 26, 27, 28, 30, 31, 34, 37, 38, 39, 41,
43, 46, 48, 49, 51, 52, 55, 56, 59, 61, 63, 64, 67, 73, 74, 77, 80, 81, 82, 84,
86, 90, 91, 92, 95, 96, 102, 105, 106, 107, 108, 110, 111, 112, 118, 119 |
| Cu (ppm dry wt) |
0,52-0,55 |
2 |
113 |
| Cu acid extr |
30-305 |
21 |
7 |
| Cudiss |
1,0-248 |
48 |
16, 23, 35, 45, 53, 76, 79, 83, 89, 107, 114, 115, 116, 120 |
| Cupart |
0,1-145 |
8 |
35, 53, 79, 115 |
| Cutot |
1,9-1120 |
54 |
3, 20, 23, 35, 45, 47, 62, 76, 83, 89, 101, 103, 114, 120, 121 |
| Cutot (µg/g) |
5-842 |
18 |
23, 35, 70, 117 |
| Cyanides |
2-33 |
4 |
95, 96 |
| Fe |
0,5-78600 |
51 |
2, 16, 18, 21, 27, 28, 31, 37, 38, 41, 63, 64, 74, 75, 90, 91, 92, 119 |
| Fe (ppm dry wt) |
14-38 |
4 |
113 |
| Fetot |
29-81290 |
8 |
3, 20, 70, 103 |
| Hg |
<0,2-24,0 |
47 |
27, 31, 34, 43, 55, 82, 95, 96, 103, 108, 109, 112 |
| K (mg/L) |
0,1-13,7 |
12 |
2, 21, 32, 34, 79, 91, 92, 99 |
| Mg (mg/L) |
0,056-39,7 |
23 |
2, 24, 32, 34, 41, 59, 79, 91, 92, 99 |
| Mn |
0,5-1647 |
29 |
2, 21, 38, 63, 64, 91, 92, 103, 105, 106 |
| Mn (ppm dry wt) |
0,05-0,56 |
4 |
113 |
| Mo |
2,4-20 |
4 |
103,105 |
| Na (mg/L) |
0,46-67000 |
15 |
2, 20, 21, 31, 32, 34, 79, 91, 92, 99 |
| Ni |
5-580 |
95 |
11, 15, 18, 27, 31, 34, 38, 43, 46, 55, 61, 63, 73, 80, 82, 84, 86, 90, 91,
95, 96, 102, 105, 106, 108, 110, 112, 118, 119 |
| Ni tot |
1-30 |
7 |
20, 101, 103, 114 |
| Nidiss |
1,1-4,1 |
2 |
114 |
| Pb |
<0,5-2764 |
168 |
2, 8, 9, 11, 15, 18, 21, 22, 25, 26, 27, 28, 30, 31, 34, 37, 38, 39, 40, 41,
43, 44, 46, 48, 49, 51, 52, 55, 56, 58, 59, 61, 63, 64, 65, 67, 69, 73, 74, 77,
80, 81, 82, 84, 86, 90, 91, 92, 95, 96, 100, 102, 105, 106, 107, 108, 109, 110,
111, 112, 118, 119, 122, 123 |
| Pb (ppm dry wt) |
0,23-3,18 |
5 |
113 |
| Pb acid extr |
50-575 |
21 |
7 |
| Pbdiss |
<0,01-120 |
54 |
16, 23, 35, 42, 45, 53, 72, 76, 79, 83, 89, 107, 113, 114, 115, 116, 120,
124 |
| Pbpart |
0,04-482 |
8 |
35, 53, 79, 115 |
| Pbtot |
0,5-2410 |
61 |
3, 20, 23, 35, 45, 47, 62, 70, 72, 76, 83, 89, 101, 102, 103, 114, 121 |
| Pbtot (µg/g) |
5-1233 |
11 |
117 |
| Pb tot organic (diss) |
0,037-1,30 |
1 |
53 |
| Tetramethyllead (pg Pb/L) |
<20 |
1 |
122 |
| TMEL (pg Pb/L) |
<2,8 |
1 |
122 |
| DMDEL (pg Pb/L) |
<3,5-24 |
1 |
122 |
| MTEL (pg Pb/L) |
<3,3-18 |
1 |
122 |
Tabel B3. Tungmetaller og overgangselementer (fortsat).
| Tungmetaller og uorganiske sporstoffer (fortsat) |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| Tetraethyllead (pg Pb/L) |
<4,2-29 |
1 |
122 |
| Trimethyllead (pg Pb/L) |
<2,5-117 |
1 |
122 |
| Triethyllead (pg Pb/L) |
<4,4-61 |
1 |
122 |
| Dimethyllead (pg Pb/L) |
<20 |
1 |
122 |
| Diethyllead (pg Pb/L) |
<50 |
1 |
122 |
| Sb |
<2-23 |
21 |
28, 43, 91, 95, 96, 105 |
| Se |
<0,5-77 |
23 |
28, 43, 91, 95, 96, 103, 108, 109 |
| Sr |
70-230 |
4 |
75 |
| Tl |
<1-14 |
14 |
43, 95, 96 |
| V |
7,2-29 |
6 |
91, 105 |
| Zn |
0-38061 |
149 |
2, 8, 9, 11, 12, 15, 18, 25, 26, 27, 30, 31, 34, 37, 38, 39, 40, 41, 43, 44,
46, 48, 49, 51, 52, 55, 56, 59, 61, 63, 64, 65, 67, 69, 74, 75, 77, 81, 82, 84,
90, 91, 95, 96, 102, 105, 106, 107, 108, 109, 110, 111, 112, 118, 119, 123 |
| Zn (ppm dry wt) |
0,38-18,5 |
5 |
113 |
| Zn acid extr |
160-1120 |
21 |
7 |
| Zndiss |
<0,05-38267 |
51 |
16, 23, 35, 42, 45, 72, 76, 79, 83, 89, 107, 113, 114, 120 |
| Znpart |
<0,05-98 |
7 |
35, 48, 79 |
| Zntot |
4-43942 |
62 |
3, 20, 23, 35, 45, 47, 62, 70, 72, 76, 83, 89, 101, 103, 114, 120, 121 |
| Zntot (µg/g of dry solids) |
11-2691 |
11 |
117 |
Table B4. Miljøfremmede organiske stoffer.
| Alifatiske kulbrinter |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| Alkane n-C13 |
0,001-0,28 |
1 |
36 |
| Alkane n-C14 |
0,002-0,66 |
1 |
36 |
| Alkane n-C15 |
0,01-3,7 |
1 |
36 |
| Alkane n-C16 |
0,02-1,4 |
1 |
36 |
| Alkane n-C17 |
0,02-9,9 |
6 |
36, 97 |
| Alkane n-C18 |
0,03-9,7 |
6 |
36, 97 |
| Alkane n-C19 |
0,02-12 |
6 |
36, 97 |
| Alkane n-C20 |
0,04-3,9 |
1 |
36 |
| Alkane n-C21 |
0,2-5,0 |
1 |
36 |
| Alkane n-C22 |
0,03-8,5 |
1 |
36 |
| Alkane n-C23 |
0,02-8,3 |
1 |
36 |
| Alkane n-C24 |
0,02-5,7 |
1 |
36 |
| Alkane n-C25 |
0,01-3,4 |
1 |
36 |
| Alkane n-C26 |
0,01-1,4 |
1 |
36 |
| Alkane n-C27 |
0,01-7,9 |
6 |
36, 97 |
| Alkane n-C28 |
0,003-4,8 |
6 |
36, 97 |
| Alkane n-C29 |
3,2-20,7 |
5 |
97 |
| Alkanes (Total linear) |
24,8-167 |
5 |
97 |
| Aromatiske kulbrinter |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 1,2,3,4-Tetrahydronaphthalene |
nd |
1 |
108 |
| 1-Methylnaphthalene |
d-9 |
2 |
94, 108 |
| 2-Etylnaphthalene |
d |
1 |
94 |
| 2-Methylnaphthalene |
d-0,95 |
2 |
94, 108 |
| Benzene |
0,017-13 |
8 |
11, 55, 87, 95, 96 |
| Dimethylnaphthalenes |
0,1-0,35 |
4 |
55, 103 |
| Ethylbenzene |
<0,2-2 |
3 |
11, 95 |
| Ethylbenzene + xylenes |
0,21-0,23 |
2 |
11 |
| Methylnaphthalenes |
<0,05-0,20 |
4 |
55, 101 |
| Naphthalene |
0,006-49 |
16 |
17, 55, 61, 63, 88, 94, 95, 101, 103, 110 |
| Naphthalene (µg/g) |
0,06-1272 |
2 |
17, 13 |
| Nitrobenzene |
nd |
1 |
95 |
| Toluene |
0,028-9 |
14 |
11, 43, 55, 97, 95 |
| Trimethylnaphthalenes |
0,57-3,6 |
4 |
55, 103 |
| Xylene |
<0,2-18 |
11 |
11, 28, 43 |
Table B4. Miljøfremmede organiske stoffer (fortsat).
| Blødgørerer |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| Butylbenzylphthalate |
0,20-130 |
7 |
55, 61, 95, 110 |
| Di(2-ethylhexyl) adipate |
0,04-1,8 |
5 |
55, 103 |
| Di(2-ethylhexyl) phthalate |
3,0-44 |
11 |
34, 55, 95, 98, 103, 110 |
| Diethylphthalate |
0,06-10 |
7 |
95, 98, 103 |
| Di-n-butylphthalate |
0,19-11 |
9 |
55, 95, 98, 103 |
| Di-n-octylphthalate |
0,1-2,1 |
9 |
55, 95, 96, 103 |
| Dimethyl phthalate |
<0,2-0,4 |
3 |
95, 103 |
| Misc. phthalates |
<0,2 |
2 |
103 |
| Dioxiner og furaner |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 1,2,3,4,6,7,8-HpCDD |
<1,4-1300 |
9 |
135, 136, 137 |
| 1,2,3,4,6,7,8-HpCDF |
1,4-350 |
9 |
135, 136, 137 |
| 1,2,3,4,7,8,9-HpCDF |
<0,1-20 |
9 |
135, 136, 137 |
| 1,2,3,4,7,8/9-HxCDF |
<0,5-5,8 |
3 |
135, 136 |
| 1,2,3,4,7,8-HxCDD |
<0,2-43 |
9 |
135, 136, 137 |
| 1,2,3,4,7,8-HxCDF |
<1,4-26 |
6 |
137 |
| 1,2,3,4/7,8-PCDF |
<0,2-5,7 |
3 |
135, 136, 137 |
| 1,2,3,6,7,8-HxCDD |
<0,2-86 |
9 |
135, 136, 137 |
| 1,2,3,6,7,8-HxCDF |
<0,5-47 |
9 |
135, 136, 137 |
| 1,2,3,7,8,9-HxCDD |
<0,5-83 |
9 |
135, 136, 137 |
| 1,2,3,7,8,9-HxCDF |
<0,5-10 |
9 |
135, 136, 137 |
| 1,2,3,7,8-PCDD |
<0,4-15 |
9 |
135, 136, 137 |
| 1,2,3,7,8-PCDF |
1,2-8,0 |
6 |
137 |
| 2,3,4,6,7,8-HxCDF |
<0,6-49 |
9 |
135, 136, 137 |
| 2,3,4,7,8-PCDF |
<0,5-61 |
9 |
135, 136, 137 |
| 2,3,4,8/2,3,7,8-TCDF |
2,3 |
1 |
136 |
| 2,3,7,8-TCDD |
<0,5-4,5 |
10 |
95, 135, 136, 137 |
| 2,3,7,8-TCDF |
0,9-8,6 |
8 |
135, 137 |
| OCDD |
50-420 |
4 |
135, 136 |
| OCDF |
3,2-52 |
3 |
135, 136 |
| TEQ |
<1,7-<11 |
4 |
135, 136 |
| Tot-HpCDD |
<1,4-3100 |
9 |
135, 136, 137 |
| Tot-HpCDF |
<1,4-970 |
9 |
135, 136, 137 |
| Tot-HxCDD |
<1,4-460 |
9 |
135, 136, 137 |
| Tot-HxCDF |
<1,4-870 |
8 |
135, 136, 137 |
| Tot-OCDD |
5,8-12000 |
6 |
137 |
| Tot-OCDF |
3-930 |
6 |
137 |
| Tot-PCDD |
1,3-57 |
9 |
135, 136, 137 |
| Tot-PCDDs |
<1,41-15512 |
7 |
136, 137 |
| Tot-PCDF |
<1,4-940 |
9 |
135, 136, 137 |
| Tot-PDCFs |
<1,4-3070 |
7 |
136, 137 |
| Tot-TCDD |
0,9-15 |
9 |
135, 136, 137 |
| Tot-TCDF |
0,9-250 |
9 |
135, 136, 137 |
| Tot-TEQ |
0,1-73 |
6 |
137 |
Table B4. Miljøfremmede organiske stoffer (fortsat).
| Halogenerede alifatiske kulbrinter |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 1,1,1-Trichloroethan |
0,025-10 |
4 |
55, 95 |
| 1,1,2,2-Tetrachloroethane |
2-3 |
1 |
95 |
| 1,1,2-Trichloroethane |
2-3 |
1 |
95 |
| 1,1-Dichloroethane |
1,5-3 |
1 |
95 |
| 1,1-Dichloroethene |
1,5-4 |
1 |
95 |
| 1,2-Dichloroethane |
4 |
1 |
95 |
| 1,2-Dichloropropane |
3 |
1 |
95 |
| 1,2-Transdichloroethene |
1-3 |
1 |
95 |
| 1,3-Dichloropropane |
1-2 |
1 |
95 |
| Bromomethane |
nd |
1 |
95 |
| Chlorodibromomethane |
2 |
1 |
95 |
| Chloroethane |
nd |
1 |
95 |
| Chloroethene |
nd |
1 |
95 |
| Chloroform |
<0,1-12 |
3 |
55, 95, 96 |
| Chloromethane |
nd |
1 |
95 |
| Dichlorodifluoromethane |
nd |
1 |
95 |
| Dichloromethane |
5-14,5 |
9 |
43, 95 |
| Hexachlorobutadiene |
nd |
1 |
95 |
| Hexachloroethane |
nd-d |
2 |
95, 98 |
| Tetrachloroethylene |
0,058-25 |
10 |
43, 55 |
| Tetrachloromethane |
<0,02-2 |
2 |
55, 95 |
| Tribromomethane (Bromoform) |
1 |
1 |
95 |
| Trichloroethylene |
0,036-7 |
10 |
43, 55 |
| Trichlorofluoromethane |
0,6-27 |
1 |
95 |
| Trihalomethanes |
161 |
1 |
80 |
| Halogenerede aromatiske kulbrinter |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 1,2,3,4-Tetrachlorobenzene |
<0,005-0,02 |
3 |
55, 95, 98 |
| 1,2,3-Trichlorobenzene |
nd |
1 |
95 |
| 1,2,4,5 + 1,2,3,5-Tetrachlorobenzene |
nd |
1 |
95 |
| 1,2,4-Trichlorobenzene |
0,0015-0,02 |
3 |
55, 95, 108 |
| 1,2-Dichlorobenzene |
nd-0,0390 |
2 |
95, 108 |
| 1,3,5-Trichlorobenzene |
0,00099 |
1 |
108 |
| 1,3-Dichlorobenzene |
0,0074-103 |
11 |
61, 95, 108, 110 |
| 1,4-Dichlorobenzene |
nd-0,0089 |
4 |
55, 95, 108 |
| 2,4-Dinitrotoluene |
nd |
1 |
95 |
| 2,6-Dinitrotoluene |
nd |
1 |
95 |
| 2-Chloronaphthalene |
nd-0,97 |
2 |
95, 108 |
| Chlorobenzenes |
<0,05-10 |
3 |
95, 103 |
| Hexachlorobenzene |
nd 0,00073-0,016 |
4 |
55, 95, 108 |
| Pentachlorobenzene |
0,0010-0,0092 |
3 |
55,108 |
| Pesticider |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 2,4,5-T |
<0,006 |
1 |
125 |
| 2,4,5-TP |
<3,2-d |
2 |
28, 125 |
| 2,4-D |
0,010-276,0 |
7 |
28, 55, 125 |
| 2,4-D (normalised to rainload)* |
0,8 |
1 |
126 |
| 2,4-DP Dichlorprop |
<0,01-4,64 |
4 |
55, 126, 127 |
| (R,S)-Dichlorprop (normalised to rainload)* |
0,9 |
1 |
126 |
| 2,6-Dichlorbenzamid (BAM) |
<0,05-0,35 |
2 |
55 |
| Acetochlor |
<0,0018? |
1 |
125 |
| α-HCB |
0,0027-20 |
6 |
17, 95, 96, 108 |
| Acrolein |
nd-240 |
7 |
43 |
| Alachlor |
0,019 |
1 |
125 |
| Alachlor (normalised to rainload)* |
1,0 |
1 |
126 |
| Aldrin |
0,0006 (aldrien+dieldrin)-6 |
11 |
43, 95, 108, 109 |
Table B4. Miljøfremmede organiske stoffer (fortsat).
| Pesticider (fortsat) |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| Aldrin, Dieldrin and Endrin |
<0,01-<0,2 |
5 |
103 |
| Atraton |
<0,0014 |
1 |
125 |
| Atrazine |
0,015-0,551 |
3 |
125, 126 |
| Atrazine (normalised to rainload)* |
0,04-1,2 |
5 |
126 |
| β-HCB |
0,1-5 |
2 |
95 |
| Chlordane |
0.00121 -10 |
9 |
61, 95, 99, 108, 109, 110 |
| δ-BHC (-Hexachlorocyclohexane) |
0,006-6 |
3 |
95, 96 |
| DDD |
nd-0,00053 |
2 |
95, 108 |
| DDE |
nd-0,00038 |
2 |
95, 108 |
| DDT |
0,00036-1 |
6 |
17, 95, 96, 108, 109 |
| DDT, o,p'- |
0,00032 |
1 |
108 |
| DDX |
nd-d |
2 |
28,55 |
| Deisopropylatrazine |
0,029 |
1 |
125 |
| Deisopropylatrazine (normalised to rainload)* |
0,10-1,07 |
4 |
126 |
| Desethylatrazine |
0,037 |
1 |
125 |
| Desethylatrazine (normalised to rainload)* |
0,08-1,2 |
4 |
126 |
| Dichlobenil |
<0,05-0,28 |
2 |
55 |
| Dieldrin |
0,00051-2 |
4 |
95, 96, 108 |
| Dimethenamid |
<0,003 |
1 |
125 |
| Diuron |
0,25-238,4 |
2 |
128 |
| DNOC (2-Methyl-4,6-dinitrophenol) |
<0,1-1,6 |
2 |
55 |
| Endosulfan |
0,0011-0,2 |
2 |
96, 109 |
| Endosulfan α- |
0,00041-13 |
3 |
95, 108 |
| Endosulfan β- |
nd-0,00060 |
2 |
95, 108 |
| Endosulfan sulfate |
nd |
1 |
95 |
| Endrin |
0,00077-0,05 |
7 |
28, 95, 108, 109 |
| Endrin aldehyde |
nd |
1 |
95 |
| HCB |
0,00046-0,0985 |
4 |
55, 102 |
| Heptachlor |
<0,0004-5 |
4 |
95, 96, 108 |
| Heptachlor epoxide |
0,0011-1 |
4 |
95, 108, 109 |
| Isodrin |
<0,01-<0,1 |
5 |
103 |
| Isophorone |
4-10 |
2 |
95 |
| Isoproturon |
<0,05-0,079 |
2 |
55 |
| Lindane |
0,002-11 |
17 |
17, 22, 28, 48, 67, 95, 96, 98, 108, 109, 110, 123 |
| MCPA |
0,009-0,13 |
3 |
55, 125 |
| MCPA (normalised to rainload)* |
1,0 |
1 |
126 |
| MCPP (R,S)-Mecoprop (normalised to rainload)* |
0,6-41,0 |
2 |
126 |
| MCPP Mecoprop |
0,012-~500 |
5 |
55, 126, 127, 129 |
| Metalaxyl |
0,005 |
1 |
125 |
| Metazachlor |
0,007 |
1 |
125 |
| Methoxychlor |
0,0015-1,21 |
6 |
28, 108, 109 |
| Metolachlor |
~0,036 |
1 |
125 |
| Metolachlor (normalised to rainload)* |
1,1 |
1 |
126 |
| Mirex |
0,0002 |
1 |
108 |
| Propachlor |
0,106 |
1 |
125 |
| Propazine |
0,044 |
1 |
125 |
| Simazine |
0,006-2,23 |
5 |
22,125,128 |
| Simazine (normalised to rainload)* |
0,03-0,9 |
3 |
126 |
| Terbuthylazin |
0,017-0,16 |
3 |
55,126 |
| Terbuthylazine (normalised to rainload)* |
0,6-2,59 |
4 |
126 |
| Toxaphene |
nd |
1 |
95 |
| Chlorinated pesticides and PCBs (20) |
<0,2 |
2 |
103 |
| Non-chlorinated pesticides (29) |
<0,1 |
2 |
103 |
| Pesticides indiv. comp. |
nd->100 |
2 |
70 |
*normalised to rainload = (ng/m² runoff) / (ng/m² rainwater)
Table B4. Miljøfremmede organiske stoffer (fortsat).
| PCB'er |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| PCB |
nd-2,6 |
7 |
55,67,102,108,123 |
| PCBs; PCB-28, -52, -101, -138, -153, -180 |
d |
1 |
98 |
| PCB-1016 |
nd |
1 |
95 |
| PCB-1221 |
nd |
1 |
95 |
| PCB-1232 |
nd |
1 |
95 |
| PCB-1242 |
nd |
1 |
95 |
| PCB-1248 |
nd |
1 |
95 |
| PCB-1254 |
nd |
1 |
95 |
| PCB-1260 |
0,03 |
1 |
95 |
| Phenoler |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 2,3,4,6-Tetrachlorophenol |
0,0055-0,014 |
2 |
55 |
| 2,3,5-Trimethyl phenol |
d |
1 |
14 |
| 2,4,6-Trichlorophenol |
0,011-0,017 |
3 |
55, 95 |
| 2,4-Dichlorophenol |
0,007-0,040 |
3 |
55, 95 |
| 2,4-Dimethylphenol |
10 |
1 |
95 |
| 2,4-Dinitro-o-cresol |
nd |
1 |
95 |
| 2,4-Dinitrophenol |
0,02-35,0 |
4 |
17, 25, 39, 95 |
| 2,6-Dimethyl-4-nitrophenol |
0,02-13,7 |
1 |
17 |
| 2,6-Dinitro-4-methylphenol |
0,05-7,8 |
1 |
17 |
| 2,6-Dinitro-6-methylphenol |
0,10-42,7 |
1 |
17 |
| 2-Chlorophenol |
d |
1 |
98 |
| 2-Nitrophenol |
<0,05-9,5 |
6 |
17, 22, 95, 98, 103 |
| 3,4-Xylenol |
d |
1 |
14 |
| 3,5-Xylenol |
d |
1 |
14 |
| 3-Methyl-4-nitrophenol |
0,02-3,4 |
1 |
17 |
| 4-Chloro-3-methyl-phenol |
<0,01-1,5 |
7 |
55, 95, 103 |
| 4-Methyl-2-nitro-phenol |
0,008-6,69 |
1 |
17 |
| 4-Nitrophenol |
0,01-25,2 |
4 |
17, 22, 25, 39, 95 |
| Bisphenol A |
<0,01-0,17 |
3 |
103 |
| Chloro- and nitrophenols (8) |
<0,05 |
2 |
103 |
| Di- and trichlorophenols (3) |
<0,01-<0,05 |
5 |
103 |
| Ethyl phenol |
d |
1 |
14 |
| Guajacol (2-Methoxy-phenol) |
0,43-3,1 |
1 |
17 |
| m,p-Cresol |
0,11-0,30 |
1 |
17 |
| Nonyl phenol |
<0,04-23 |
17 |
112 |
| Nonyl phenol (+NPE 1-2 EO) |
<0,05-5,8 |
7 |
55, 103 |
| o-Cresol |
0,06-1,2 |
1 |
17 |
| Pentachlorophenol (PCP) |
0,044-115 |
14 |
43, 55, 95, 96, 110 |
| Phenol |
<0,01-10 |
8 |
28, 95, 96, 103 |
| Phenols total |
7,00-21,00 |
1 |
34 |
| Phenols; 16 phenols |
d |
1 |
98 |
| Polyaromatiske kulbrinter (PAH'er) |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 2-Methylanthracene |
0,2-1,2 |
6 |
97 |
| 3-4-Benzofluoranthene |
2 |
1 |
96 |
| 9,10 Dimethylanthracene |
0,6-1,2 |
5 |
97 |
| Acenaphthene |
0,002-0,97 |
16 |
14, 17, 36, 55, 88, 95, 101, 103, 108 |
| Acenaphthene (µg/g) |
0,002-140,5 |
2 |
17, 13 |
| Acenaphthylene |
<0,05-0,96 |
11 |
14, 36, 55, 95, 101, 103, 108 |
| Anthracene |
<0,0001-147 |
30 |
17, 36, 53, 55, 63, 95, 96, 101, 103, 131 |
| Anthracene (µg/g) |
0,002-142,9 |
2 |
17, 13 |
| Benzo[a]anthracene |
0,0003-54 |
32 |
17, 36, 55, 61, 63, 95, 96, 97, 101, 103 |
| Benzo[a]anthracene (µg/g) |
0,005-28,7 |
2 |
17, 130 |
| Benzo[a]anthracene/chrysene |
0,070-1,910 |
1 |
53 |
| Benzo[a]pyrene |
0,00015-300 |
44 |
12, 14, 17, 25, 36, 39, 53, 55, 61, 63, 67, 94, 95, 96, 97, 99, 101, 103,
132 |
| Benzo[a]pyrene (µg/g) |
0,02-17,1 |
3 |
17, 130, 133 |
| Benzo[b,j,r]fluoranthene |
1,07 |
1 |
67 |
Table B4. Miljøfremmede organiske stoffer (fortsat).
| Polyaromatiske kulbrinter (PAH'er) (fortsat) |
Interval (µg/L) |
Antal
lokaliteter |
Referencer |
| Benzo[b]fluoranthene |
0,0007-260 |
19 |
17, 36, 48, 53, 61, 63, 95, 99 |
| Benzo[b]fluoranthene (µg/g) |
0,025-23,4 |
2 |
17, 130 |
| Benzo[b]fluorene |
0,2-1,1 |
5 |
97 |
| Benzo[b+j+k]fluoranthene |
<0,01-0,49 |
10 |
55, 101, 103 |
| Benzo[e]pyrene |
0,001-0,6 |
7 |
17, 94, 97 |
| Benzo[e]pyrene µg/g |
0,22-26,7 |
1 |
17 |
| Benzo[ghi]perylene |
<0,01-710 |
37 |
22, 25, 36, 39, 53, 55, 63, 67, 88, 95, 97, 101, 103, 131 |
| Benzo[ghi]perylene (µg/g) |
0,017-39,3 |
2 |
17,130 |
| Benzo[ghi]perylene dissolved |
5,3-130 |
4 |
12, 17 |
| Benzo[k]fluoranthene |
0,0001-61 |
21 |
14, 17, 36, 61, 63, 95, 96, 97 |
| Benzo[k]fluoranthene (µg/g) |
0,001-0,593 |
2 |
17,130 |
| Biphenyl |
d |
1 |
94 |
| Chrysene |
0,0003-10 |
17 |
12, 17, 36, 94, 95, 96, 97, 101 |
| Chrysene (µg/g) |
0,002-158,7 |
2 |
17,130 |
| Chrysene/Triphenylene |
<0,01-2,271 |
13 |
55, 63, 103 |
| Dibenz [a,h] anthracene |
<0,01-83 |
33 |
14, 36, 63, 88, 95, 97, 131 |
| Dibenz [a,h] anthracene (µg/g) |
0,003-9,35 |
2 |
17, 130 |
| Dibenzothiophene |
d |
1 |
94 |
| Flouranthene diss |
0,002-0,80 |
5 |
12, 17, 22 |
| Fluoranthene |
0,009-1958 |
54 |
12, 25, 36, 39, 41, 48, 53, 55, 61, 63, 67, 95, 96, 97, 101, 103, 108, 110, 131 |
| Fluoranthene (µg/g) |
0,08-209,3 |
3 |
17, 130, 133 |
| Fluoranthene particulate |
0,1575 |
2 |
22, 94 |
| Fluoranthene soluble |
0,0034 |
1 |
94 |
| Fluorene |
0,001-74 |
23 |
14, 17, 36, 55, 94, 95, 101, 103, 108, 131 |
| Fluorene (µg/g) |
0,0002-1,87 |
2 |
17, 13 |
| Indene |
nd |
1 |
108 |
| Indeno [1.2.3-cd] pyrene |
<0,01-1080 |
36 |
12, 17, 55, 63, 67, 88, 95, 97, 101, 103, 131 |
| Indeno [1.2.3-cd] pyrene (µg/g) |
0,03-8,4 |
2 |
17, 13 |
| Methylphenanthrenes |
1,3-5,2 |
5 |
97 |
| Perylene |
0,0003-0,8 |
14 |
17, 63, 97 |
| Perylene (µg/g) |
0,02-0,63 |
1 |
17 |
| Phenanthrene |
<0,01-1420 |
43 |
12, 14, 36, 53, 55, 88, 95, 96, 97, 98, 99, 101, 103, 108, 110, 131 |
| Phenanthrene (µg/g) |
0,04-934 |
2 |
17, 13 |
| Phenanthrene particulate |
0,0643 |
1 |
94 |
| Phenanthrene soluble |
0,0263 |
1 |
94 |
| Phenanthrene-Diss |
0,0004-1,6 |
3 |
12, 17, 99 |
| Pyrene |
0,0001-120 |
39 |
14, 17, 36, 53, 55, 61, 63, 95, 96, 97, 101, 103, 108, 110 |
| Pyrene (µg/g) |
0,05-316,1 |
2 |
17, 13 |
| Pyrene particulate |
0,1311 |
1 |
94 |
| Pyrene soluble |
0,0056 |
1 |
94 |
| Quinoline |
nd |
1 |
108 |
| PAH |
<0,011-178 |
29 |
26, 37, 41, 46, 48, 67, 68, 72, 86, 112 |
| PAHs; 16 EPA contr PAHs |
<0,3-5,8 |
3 |
46, 98 |
| PAHtot |
0,360-11,604 |
2 |
27,53 |
| PAHtot(diss) |
0,00036-0,00706 |
1 |
53 |
| Sum of PAH |
<2-3500 |
4 |
55, 88 |
| Ætere |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| Ether, bis(chloromethyl)- |
nd |
1 |
95 |
| Ether, bis(chloroethyl)- |
nd 2,0-87 |
7 |
61, 95, 110 |
| Ether, bis(chloroisopropyl)- |
nd 3,0-400 |
4 |
61, 95 |
| Ether, 2-chloroethyl vinyl- |
nd |
1 |
95 |
| Ether, 4-bromophenyl phenyl |
nd |
1 |
95 |
| Ether, 4-chlorophenyl phenyl |
nd |
1 |
95 |
| Bis(2-chloroethoxy) methane |
nd |
1 |
95 |
| MTBE |
<5-37 |
3 |
43 |
Table B4. Miljøfremmede organiske stoffer (fortsat).
| P-triestere |
Interval (µg/L) |
Antal
lokaliteter |
Referencer |
| Tricresylphosphate |
<0,01-<0,2 |
6 |
55, 103 |
| Tri-n-butyl phosphate |
0,03-0,10 |
7 |
55, 103 |
| Triphenyl phosphate |
<0,01-0,5 |
7 |
55, 103 |
| Andre stoffer |
Interval (µg/L) |
Antal lokaliteter |
Referencer |
| 3,3'-Dichloro-benzidine (µg/L) |
nd |
1 |
95 |
| Acetate |
0,48-8,1 |
2 |
79 |
| Acetone |
0,0123-0,0454 |
1 |
87 |
| Diethylene glycol |
<1-2900 |
2 |
15 |
| Di-n-propyl nitrosamine (µg/L) |
nd |
1 |
95 |
| Ethylene glycol |
nd-98000 |
2 |
15 |
| Fatty acids; C6-C18, 2 decenoic acids |
d |
1 |
98 |
| Formate |
0-2,9 |
2 |
79 |
| Hexadecene |
<0,0015 |
1 |
98 |
| MEK (methyl ethyl ketone) |
0,00281-0,00839 |
1 |
87 |
| Nonanol |
d |
1 |
14 |
| Octanol |
d |
1 |
14 |
| Oleic acid |
0,0015-0,009 |
1 |
98 |
| Oxalate |
0,27-1,5 |
2 |
79 |
| Phytane |
0,00091-0,007 |
5 |
97 |
| Pristane |
0,00077-0,0072 |
5 |
97 |
| Propylene glycol |
nd-130000 |
2 |
15 |
| Tetradecanol |
d |
1 |
14 |
| Total glycol |
nd-230900 |
2 |
15 |
| Tridecanol |
d |
1 |
14 |
1) Chebbo og Bachoc, 1992. 2) Chui, 1993. 3) de Luca et al., 1991. 4) Sansalone et al., 1996. 5) Sansalone et al., 1998. 6) Sansalone, 1998. 7) Drapper et al.,
2000. 8) Barbosa og Hvitved-Jacobsen, 1999. 9) Barraud et al., 2000. 10) Bartkowska og Królikowski, 1996. 11) Kjølholt et al., 2001. 12) Daub et al., 1994.
13) Deletic og Maksimovic, 1998. 14) Fam et al., 1987. 15) Fisher et al., 1995. 16) Förster, 1990. 17) Förster, 1993. 18) Gjessing et al., 1984. 19) Hall og
Anderson, 1988. 20) Harned, 1988. 21) Harrison og Wilson, 1985B. 22) Herrmann et al., 1994. 23) Hvitved-Jacobsen et al., 1987. 24) Karouna-Renier og
Sparling, 2001. 25) Kern et al., 1992. 26) Legret et al., 1999B. 27) Lygren, 1984. 28) McGehee Marsh, 1993. 30) Medeiros et al., 1984. 31) Moxness, 1987.
32) Nightingale, 1988. 33) Norrström og Bergstedt, 2001. 34) Sieber, 1995. 35) Pagotto et al., 2000. 36) Shu og Hirner, 1997. 37) Stotz, 1987. 38) Williamson,
1986. 39) Wüst et al., 1994. 40) Yaziz etal., 1989. 41) Stotz og Krauth, 1994. 42) Montrejaud-Vignoles et al., 1996. 43) Line et al., 1996. 44) Balades et al,.
1984. 45) Bannerman et al., 1993. 46) Berbee et al., 1999. 47) Ellis og Rewitt, 1991. 48) Förster, 1999. 49) Gromaire et al., 2001. 50) Gromaire-Mertz et al.,
1998. 51) Gromaire-Mertz et al., 1999. 52) Grønning et al., 1998. 53) Hewitt og Rashed, 1992. 54) Johansen, 1985. 55) Kjølholt et al., 1997. 56) Koop og
Kaarup, 1992. 57) Lammersen, 1993. 58) Lee og Bang, 2000. 59) Maltby et al., 1995A. 60) PH-consult ApS, 1990. 61) Pitt et al., 1995. 62) Quek og Förster,
1993. 63) Shinya et al., 2000. 64) Simpson og Stone, 1988. 65) Strecker et al., 1987. 66) Uchimura et al., 1996. 67) Xanthopoulos og Hahn, 1990. 68) Yamane
et al., 1990. 69) Zhao et al., 1999. 70) Zobrist et al., 2000. 71) Henze og Munk Nielsen, 1997. 72) Stephenson et al., 1999. 73) Wu et al., 1998. 74) Barrett et
al., 1998. 75) Characklis og Wiesner, 1997. 76) Duke et al.,1999. 77) Lloyd og Wong, 1999. 78) Whiteley et al., 1993. 79) Mason et al., 1999. 80) Shutes et
al., 1997. 81) Hvitved-Jacobsen et al., 1994. 82) Walker et al., 1981. 83) Good, 1993. 84) Skinner et al., 1999. 85) Hahn og Pfeifer, 1995. 86) Anderson et al.,
1991. 87) Lopes et al., 2000. 88) Smith et al., 2000. 89) Lau et al., 2000. 90) Yousef etal., 1987. 91) Dannecker et al., 1990. 92) Harrison og Wilson, 1985A.
93) Telang, 1990. 94) Hoffman et al., 1984. 95) Cole et al.,1984. 96) Gavin og Moore, 1982. 97) Bomboi og Hernández, 1991. 98) Shu og Hirner, 1998. 99)
Förster, 1998. 100) Cutbill, 1993. 101) Dannisøe og Krogsgaard Jensen, 2000. 102) Marsalek, 1991. 103) Lehmann et al., 2001. 104) Halldin et al., 1990. 105)
Hares og Ward, 1999. 106) Jirik et al., 1998. 107) Legret et al., 1999A. 108) Marsalek og Schroeter, 1988. 109) Marsalek, 1986. 110) Pitt et al., 1994. 111)
Siverth, 1995. 112) Storhaug, 1996. 113) Flores-Rodríguez et al., 1993. 114) Legret et al., 1995. 115) Mesuere og Fish, 1989. 116) Morrison et al., 1990. 117)
Sansalone og Buchberger, 1997. 118) Leschber og Pernak, 1995. 119) Maltby et al., 1995B. 120) Novotny et al., 1998. 121) Mungur et al., 1995. 122)
Harrison et al., 1986. 123) Granier et al., 1990. 124) Flores-Rodríguez et al., 1994. 125) Bucheli et al., 1997. 126) Bucheli et al., 1998A. 127) Felding et al.,
1995. 128) Revitt et al., 1999. 129) Bucheli et al., 1998B. 130) Xanthopoulos og Hahn, 1993. 131) Krein og Schorer, 2000. 132) Jensen, 1984. 133) Hoffman
et al., 1985. 135) Horstmann og McLachlan, 1995. 136) Näf et al., 1990. 137) Wenning et al., 1999. 138) Hatch og Burton, 1999. 139) Marsalek et al.,
1999.
Tabel B5. Cytotoksicitet, genotoksicitet og mutagenicitet af afstrømningsvand fra motorveje.
| Testsystem |
Prøvebeskrivelse |
Effekt |
Antal lokaliteter |
Referencer |
Cytotoksicitet
(Sub-mitrochondrial particle) |
Opkoncentreret prøve (10x) |
90 % hæmning |
1 |
139 |
| Genotoksicitet (SOS-chromo test, Escherichia coli) |
Opkoncentreret prøve (10x) |
ikke genotoksisk |
1 |
139 |
| Mutagenicity (Ames test, Salmonella typhimurium) |
Filtreret vandprøve |
påvist mutagen aktivitet
|
1 |
63 |
63) Shinya et al. ,2000. 139) Marsalek et al., 1999.
Tabel B6. Toksicitet af regnvand målt på forskellige organismer.
| Fisk |
Effektparameter |
Effektværdi |
Antal
lokaliteter |
Referencer |
Fathead minnow
(Pimephales promelas) |
Akut toks., LC50, 96h (% prøve) |
3-100 |
4 |
28,29 |
Fathead minnow
(Pimephales promelas) |
Akut toks., % overlevelse (48 h field test) |
60-100 |
2 |
139 |
Fathead minnow
(Pimephales promelas) |
Længde af fisk, EC50 (% prøve)1 |
72-91 |
2 |
30 |
| Regnbueørred |
Akut toks., % overlevelse ved 32 % prøve |
0-100 |
5 |
83 |
| Regnbueørred |
Akut toks., % overlevelse ved 65 % prøve |
0-90 |
5 |
83 |
| Regnbueørred |
Akut toks., % overlevelse ved 100 % prøve |
0-60 |
5 |
83 |
| Krebsdyr |
Effektparameter |
Effektværdi |
Antal
lokaliteter |
Referencer |
| Ceriodaphnia dubia |
Akut toks., LC50, 96h (% prøve) |
10-25 |
1 |
86 |
| Daphnia Magna |
Akut toks., % overlevelse (48 h field/lab) |
0/15 |
1 |
138 |
| Daphnia Magna |
Akut toks., EC50, 48h (% prøve) |
70 |
1 |
139 |
| Daphnia Magna |
Akut toks., LC50, 48h (% prøve) |
1,7- non toxic |
2 |
15 |
| Daphnia Magna |
Akut toks., LC10/LC50 (% prøve) |
6,2- >90/17- >90 |
2 |
11 |
| Alger |
Effektparameter |
Effektværdi |
Antal
lokaliteter |
Referencer |
| Pseudokirchneriella subcapiata |
Sub-kronisk, EC10/EC50 (% prøve) |
6,7-58/>99,9 |
2 |
11 |
| Testkits |
Effektparameter |
Effektværdi |
Antal
lokaliteter |
Referencer |
IQ Toxicity Test
D. magna H. azteca |
IC50 (% sample) |
18-96/37-63 |
1 |
138 |
Microtox
(Vibrio fischeri) |
Akut toks., EC10/EC50 (% prøve) |
57->75/>75 |
2 |
11 |
Microtox
(Vibrio fischeri) |
Akut toks., EC50, 10x opkonc. prøve (% hæmn.) |
52,4 |
1 |
139 |
| Øvrige organismer |
Effektparameter |
Effektværdi |
Antal
lokaliteter |
Referencer |
| Søpindsvin (Purple Sea Urchin) |
Reproduktion, EC50 (% prøve) |
12-20 |
1 |
106 |
Bundlevende krebsdyr
(Hyalella azteca) |
Akut toks., 48 h |
påvirket ved 100% prøve |
1 |
138 |
1 Estimeret værdi på baggrund af oplysninger i Medeiros
et al., 1984.
11) Kjølholt et al., 2001. 15) Fisher et al., 1995. 28)
McGehee og Marsh, 1993. 30) Medeiros et al., 1984. 63) Shinya et al., 2000. 83)
Good, 1993. 86) Anderson et al., 1991. 106) Jirik et al., 1998. 138) Hatch og
Burton, 1999. 139) Marsalek et al., 1999.
Tabel B7. Generelle mikrobielle parametre i opsamlet regnvand fra tage.
| Parameter |
Tagvand |
Referencer |
Interval
(CFU/mL) |
Antal
lokaliteter |
| Kimtal (~21°C) |
1-2×109 |
315 |
1, 2, 3, 5, 6, 8, 9 |
| Kimtal (~37°C) |
5-7×106 |
176 |
1, 3, 8, 9 |
| DEFT(celler/mL) |
3×104-6×106 |
3 |
1 |
| Svampe |
0.06-26 |
7 |
1 |
1) Albrechtsen, 1998. 2) Yaziz et al., 1989. 3) Holländer et al., 1996. 5) Crabtree et al., 1996. 6) Simmons et al., 2001. 8) Lye, 1987. 9) Lorch, 1996.
Tabel B8. Indikatororganismer i opsamlet regnvand.
| Parameter |
Tagvand |
Befæstede arealer |
Referencer |
Interval
(CFU/100mL) |
Hyppighed |
Antal
lokali-
teter |
Interval
(CFU/100mL) |
Antal lokali-
teter |
| Total coliforme |
<1-1,9×104 |
535/1149 |
47% |
309 |
10-2×105 |
4 |
2,3,5,6,8,9,11 |
| Fækale coliforme |
<1-3500 |
120/292 |
41% |
224 |
55-9×104 |
39 |
2, 4, 5, 6, 7, 8, 9, 10 |
| Escherichia coli |
<1-5,4×104 |
135/993 |
14% |
109 |
10-1.2×104 |
2 |
1, 3, 10 |
| Fækale streptococcer |
<99->104 |
243/969 |
25% |
102 |
99-6×104 |
2 |
3, 10 |
| Enterococcer |
<1-4900 |
ikke oplyst |
- |
125 |
- |
- |
6 |
| Gær |
<0,01-100 |
17/448 |
3,8% |
44 |
- |
- |
1,3 |
1) Albrechtsen, 1998. 2) Yaziz et al., 1989. 3) Holländer et al., 1996. 4) Thomas og Greene, 1993. 5) Crabtree et al., 1996. 6) Simmons et al., 2001. 7)
Bannerman et al., 1993. 8). Lye, 1987. 9) Lorch, 1996. 10) Young og Thackston, 1999. 11) Lim og Lim, 1999.
Tabel B9. Potentielt patogene mikroorganismer i opsamlet regnvand fra tage.
| Parameter |
Tagvand |
Referencer |
Interval
(CFU/mL) |
Hyppighed |
Antal
lokali-
teter |
| Pseudomonas aeruginosa |
<1-870 |
3/21 |
14% |
7 |
1 |
| Mycobacterium avium |
Påvist (1) |
1/21 |
4,8% |
7 |
1 |
| Staphylococcus aureus |
Ikke påvist |
0/782 |
0% |
79 |
3 |
| Yersinia spp. |
Ikke påvist |
0/338 |
0% |
79 |
3 |
| Salmonella spp. |
Påvist (3,6) |
2/913 |
0,22% |
208 |
3,6 |
| Shigella spp. |
Ikke påvist |
0/342 |
0% |
34 |
3 |
| Legionella spp. |
Påvist (1) |
10/462 |
2.2% |
68 |
1,3,6 |
| Legionella pneumophila |
Ikke påvist |
0/21 |
0% |
7 |
1 |
| Campylobacter spp. |
Påvist (1) |
4/284 |
1,4% |
156 |
1,3,6 |
| Aeromonas spp. |
<10-4.4×103 |
25/146 |
17% |
132 |
1,6 |
| Giardia spp.* |
<1-3,8 (5) |
10/122 |
8,2% |
70 |
1,5,6 |
| Cryptosporidium spp.* |
<1-5×104 (1,5) |
29/122 |
24% |
70 |
1,5,6 |
1) Albrechtsen, 1998. 3) Holländer et al., 1996. 5) Crabtree et al., 1996. 6) Simmons et al., 2001.
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