Member State report / Art8-2024 / 2024 / D8 / Slovenia / Mediterranean: Adriatic Sea
| Report type | Member State report to Commission |
| MSFD Article | Art8 |
| Report due | 2024-10-15 |
| GES Descriptor | D8 Contaminants |
| Member State | Slovenia |
| Region/subregion | Mediterranean: Adriatic Sea |
| Report date | 2026-04-03 07:57:04 |
MAD-SI-MS-1
Regional assessment area |
|
|---|---|
Component MRUs |
|
GES component |
D8
|
Feature |
Acute pollution events
|
Element |
|
Element extent |
|
Trend element |
|
Element 2 |
|
Element source |
|
Criterion |
D8C3
|
Parameter |
Extent
|
Threshold value upper |
7.0 |
Threshold value lower |
|
Threshold value operator |
< |
Threshold qualitative |
|
Threshold value source |
Other (specify)
|
Value achieved upper |
|
Value achieved lower |
|
Value unit |
tonne
|
Proportion threshold value |
|
Proportion value achieved |
|
Proportion threshold value unit |
|
Trend parameter |
Stable |
Parameter achieved |
Yes |
Description parameter |
Za mejo pojava znatnih akutnih onesnaženj smo upoštevali klasifikacijo za razlitja večjih razsežnosti po ITOPF-u, to je razlitje nafte ali drugih nevarnih snovi v količini >7 t.
V obravnavanem obdobju ni prišlo do znatnih akutnih onesnaženj, prišlo je le do manjših operativnih onesnaženj, kjer je prišlo do izlitja nafte. Največji takšen dogodek v obravnavanem obdobju je predstavljalo izlitje 50 litrov oljnih snovi.
|
Related indicator |
|
Criteria status |
Good |
Description criteria |
V obravnavanem obdobju ni prišlo do znatnih akutnih onesnaženj, prišlo je le do manjših operativnih onesnaženj, kjer je prišlo do izlitja nafte. Največji takšen dogodek v obravnavanem obdobju je predstavljalo izlitje 50 litrov oljnih snovi.
|
Element status |
|
Description element |
|
Source assessment feature |
|
Reporting method feature |
Type D |
Trend feature |
Stable |
Integration rule type parameter |
Not relevant
|
Integration rule description parameter |
|
Integration rule type criteria |
Not relevant
|
Integration rule description criteria |
|
GES extent threshold |
|
GES extent achieved |
100.00 |
GES extent unit |
Proportion of area in good status |
GES achieved |
GES achieved by 2018 |
Description overall status |
V obravnavanem obdobju ni prišlo do znatnih akutnih onesnaženj, prišlo je le do manjših operativnih onesnaženj, kjer je prišlo do izlitja nafte. Največji takšen dogodek v obravnavanem obdobju je predstavljalo izlitje 50 litrov oljnih snovi.
|
Assessments period |
2016-2021 |
Related pressures |
|
Related targets |
|
Test TV |
NA |
Test results |
False |
MAD-SI-MS-11
Regional assessment area |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Component MRUs |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES component |
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
Feature |
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Element |
1,2,3-Trichlorobenzene |
1,2,4-Trichlorobenzene |
1,2-Dichloroethane |
1,3,5-Trichlorobenzene |
Aclonifen |
Alachlor |
Aldrin |
Anthracene |
Anthracene |
Antimony |
Arsenic and its compounds |
Atrazine |
Benzene |
Beta-HCH |
Bifenox |
Bisphenol A |
Cadmium and its compounds |
Cadmium and its compounds |
Carbon tetrachloride |
Chlorfenvinphos |
Chloroalkanes C10-13 |
Chlorpyrifos |
Chromium and its compounds |
Cobalt and its compounds |
Copper and its compounds |
Cybutryne |
Cypermethrin |
Delta-HCH |
Di(2-ethylhexyl)phthalate (DEHP) |
Dibutylphthalate |
Dibutyltin |
Dichloromethane |
Dichlorvos |
Dicofol |
Dieldrin |
Dieldrin |
Diuron |
Endrin |
Fluoranthene |
Fluoranthene |
Fluoranthene |
Gamma-HCH (Lindane) |
Gamma-HCH (Lindane) |
Hexachlorobenzene |
Hexachlorobenzene |
Hexachlorobutadiene |
Hexachloroethane |
Isodrin |
Isoproturon |
Lead and its compounds |
Lead and its compounds |
Meta xylene + para xylene |
Metolachlor |
Mineral oil index |
Molybdenum and its compounds |
Naphthalene |
Naphthalene |
Nickel and its compounds |
Nickel and its compounds |
Nitrite |
Nonylphenol |
Octylphenol |
Pentachlorobenzene |
Pentachlorophenol |
Phenol |
Quinoxyfen |
Selenium and its compounds |
Simazine |
Terbuthylazine |
Terbutryn |
Tetrachloroethylene |
Toluene |
Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') |
Trichloroethylene |
Trichloromethane |
Trifluralin |
Zinc and its compounds |
alpha-Endosulfan |
alpha-HCH |
beta-Endosulfan |
o-Xylene |
BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether) |
BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether) |
BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether) |
BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether) |
BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether) |
BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether) |
BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether) |
BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether) |
BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether) |
BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether) |
BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether) |
Benzo(a)pyrene |
Benzo(a)pyrene |
Benzo(a)pyrene |
Benzo(b)fluoranthene |
Benzo(g,h,i)perylene |
Benzo(g,h,i)perylene |
Benzo(k)fluoranthene |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Heptachlor |
Indeno(1,2,3,-cd)pyrene |
Indeno(1,2,3,-cd)pyrene |
Mercury and its compounds |
Mercury and its compounds |
Mercury and its compounds |
Tributyltin compounds |
Element extent |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend element |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Element 2 |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Element source |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
National |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
Criterion |
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
Parameter |
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in sediment
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in biota
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
|
Threshold value upper |
0.4 |
0.4 |
10.0 |
0.4 |
0.012 |
0.3 |
0.005 |
0.085 |
0.1 |
3.2 |
7.0 |
0.6 |
8.0 |
0.002 |
0.0012 |
1.6 |
1.2 |
0.2 |
12.0 |
0.1 |
0.4 |
0.03 |
12.0 |
0.3 |
8.2 |
0.0025 |
8e-06 |
0.002 |
1.3 |
10.0 |
0.02 |
20.0 |
6e-05 |
3.2e-05 |
0.002 |
0.005 |
0.2 |
0.005 |
30.0 |
0.6 |
0.0063 |
0.003 |
0.002 |
0.02 |
0.05 |
0.6 |
24.0 |
0.005 |
0.3 |
47.0 |
1.3 |
185.0 |
0.3 |
0.05 |
24.0 |
0.16 |
2.0 |
21.0 |
8.6 |
0.3 |
0.01 |
0.0007 |
0.4 |
7.7 |
0.015 |
6.0 |
1.0 |
0.5 |
0.0065 |
10.0 |
74.0 |
0.025 |
10.0 |
2.5 |
0.03 |
52.0 |
0.0005 |
0.002 |
0.0005 |
185.0 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.014 |
5.0 |
0.43 |
0.00017 |
0.00017 |
0.085 |
0.00017 |
0.00017 |
0.0065 |
1e-08 |
0.24 |
0.00017 |
20.0 |
0.15 |
0.07 |
0.0002 |
|
Threshold value lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value operator |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
|
Threshold qualitative |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
OSPAR Convention
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
|
Value achieved upper |
0.04 |
0.04 |
0.2 |
0.04 |
0.02 |
0.01 |
0.001 |
0.01 |
0.005 |
1.0 |
2.8 |
0.01 |
0.3 |
0.001 |
0.01 |
0.21 |
0.22 |
0.097 |
0.2 |
0.01 |
0.05 |
0.009 |
3.5 |
6.0 |
3.0 |
0.0025 |
0.0002 |
0.001 |
0.62 |
0.1 |
0.00749 |
2.0 |
0.003 |
0.001 |
0.01 |
0.001 |
0.01 |
0.001 |
10.4 |
0.11 |
0.007 |
0.01 |
0.001 |
0.005 |
0.0005 |
0.03 |
0.04 |
0.001 |
0.01 |
37.0 |
0.35 |
0.4 |
0.018 |
0.02 |
15.0 |
0.05 |
0.016 |
93.0 |
6.0 |
0.05 |
0.03 |
0.001 |
0.05 |
0.27 |
0.01 |
1.8 |
0.01 |
0.018 |
0.01 |
0.1 |
0.3 |
0.002 |
0.1 |
0.1 |
0.009 |
30.0 |
0.001 |
0.001 |
0.001 |
0.2 |
0.019 |
5e-05 |
0.0022 |
5e-05 |
0.0057 |
5e-05 |
0.096 |
6e-05 |
0.045 |
9e-05 |
7e-05 |
2.0 |
0.059 |
0.004 |
0.005 |
0.045 |
0.004 |
0.004 |
0.496 |
0.001 |
0.038 |
0.004 |
38.0 |
0.65 |
0.025 |
0.00052 |
|
Value achieved lower |
0.04 |
0.04 |
0.2 |
0.04 |
0.02 |
0.01 |
0.001 |
0.01 |
0.005 |
1.0 |
1.0 |
0.01 |
0.3 |
0.001 |
0.01 |
0.03 |
0.1 |
0.06 |
0.2 |
0.01 |
0.04 |
0.009 |
3.5 |
6.0 |
2.5 |
0.0025 |
0.0002 |
0.001 |
0.1 |
0.1 |
0.00025 |
2.0 |
0.003 |
0.001 |
0.01 |
0.001 |
0.01 |
0.001 |
2.0 |
0.011 |
0.002 |
0.01 |
0.001 |
0.005 |
0.0005 |
0.03 |
0.04 |
0.001 |
0.01 |
19.0 |
0.3 |
0.4 |
0.01 |
0.015 |
3.2 |
0.05 |
0.005 |
42.0 |
6.0 |
0.03 |
0.01 |
0.001 |
0.05 |
0.05 |
0.01 |
1.8 |
0.01 |
0.01 |
0.01 |
0.1 |
0.3 |
0.002 |
0.1 |
0.1 |
0.009 |
30.0 |
0.001 |
0.001 |
0.001 |
0.2 |
0.019 |
5e-05 |
0.0022 |
5e-05 |
0.0057 |
5e-05 |
0.096 |
5e-05 |
0.045 |
5e-05 |
5e-05 |
2.0 |
0.015 |
0.004 |
0.005 |
0.012 |
0.004 |
0.004 |
0.001 |
0.012 |
0.004 |
13.0 |
0.059 |
0.01 |
0.00022 |
||
Value unit |
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
milligram per kilogram
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per kilogram of wet weight
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
|
Proportion threshold value |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend parameter |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Not assessed |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Not assessed |
Stable |
Stable |
|
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
No |
Not assessed |
Yes |
No |
|
Description parameter |
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK).
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK).
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata seštevek polovičnih vrednosti LOQ DDT izomerov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov. Vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata isto meritev.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov. Vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata isto meritev.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov. Vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata isto meritev.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov. Vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata isto meritev.
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ValueAchievedLower predstavlja vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov. Vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata isto meritev.
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ValueAchievedLower predstavlja vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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ValueAchievedLower predstavlja vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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ValueAchievedUpper predstavlja vsoto izmerjenih vrednosti. Ta element je bil izmerjen samo v enem vzorcu v presojanem obdobju. Večina izmerjenih vrednosti, ki sestavljajo ta element, je bila pod LOQ, zaradi česar privzemamo, da element ne poslabšuje stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK).
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Reporting method feature |
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Trend feature |
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Integration rule type parameter |
OOAO
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OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent threshold |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent achieved |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
GES extent unit |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
GES achieved |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
Description overall status |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
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|
|
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|
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|
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|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|
|
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|
|
|
|
|
|
|
|
|
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|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Test TV |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
NA |
Yes |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
No |
No |
Yes |
No |
No |
No |
No |
Yes |
No |
No |
No |
Yes |
No |
Test results |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Correct |
False |
Correct |
Correct |
MAD-SI-MS-12
Regional assessment area |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Component MRUs |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES component |
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
D8
|
Feature |
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - UPBT substances
|
Element |
1,2,3-Trichlorobenzene |
1,2,4-Trichlorobenzene |
1,2-Dichloroethane |
1,3,5-Trichlorobenzene |
Aclonifen |
Alachlor |
Aldrin |
Anthracene |
Anthracene |
Antimony |
Arsenic and its compounds |
Atrazine |
Benzene |
Beta-HCH |
Bifenox |
Bisphenol A |
Cadmium and its compounds |
Cadmium and its compounds |
Carbon tetrachloride |
Chlorfenvinphos |
Chloroalkanes C10-13 |
Chlorpyrifos |
Chromium and its compounds |
Cobalt and its compounds |
Copper and its compounds |
Cybutryne |
Cypermethrin |
Delta-HCH |
Di(2-ethylhexyl)phthalate (DEHP) |
Dibutylphthalate |
Dibutyltin |
Dichloromethane |
Dichlorvos |
Dicofol |
Dicofol |
Dieldrin |
Dieldrin |
Diuron |
Endrin |
Fluoranthene |
Fluoranthene |
Fluoranthene |
Gamma-HCH (Lindane) |
Gamma-HCH (Lindane) |
Hexachlorobenzene |
Hexachlorobenzene |
Hexachlorobenzene |
Hexachlorobutadiene |
Hexachlorobutadiene |
Hexachloroethane |
Isodrin |
Isoproturon |
Lead and its compounds |
Lead and its compounds |
Meta xylene + para xylene |
Metolachlor |
Mineral oil index |
Molybdenum and its compounds |
Naphthalene |
Naphthalene |
Nickel and its compounds |
Nickel and its compounds |
Nitrite |
Nonylphenol |
Octylphenol |
Pentachlorobenzene |
Pentachlorophenol |
Phenol |
Quinoxyfen |
Selenium and its compounds |
Simazine |
Terbuthylazine |
Terbutryn |
Tetrachloroethylene |
Toluene |
Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') |
Trichloroethylene |
Trichloromethane |
Trifluralin |
Zinc and its compounds |
alpha-Endosulfan |
alpha-HCH |
beta-Endosulfan |
o-Xylene |
BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether) |
BDE 100 (2,2’,4,4’,6-pentabromodiphenyl ether) |
BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether) |
BDE 153 (2,2’,4,4’,5,5’-hexabromodiphenyl ether) |
BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether) |
BDE 154 (2,2’,4,4’,5,6’-hexabromodiphenyl ether) |
BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether) |
BDE 47 (2,2’,4,4’-tetrabromodiphenyl ether) |
BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether) |
BDE 99 (2,2’,4,4’,5-pentabromodiphenyl ether) |
BDE-183 (2,2',3,4,4',5',6-heptabromodiphenyl ether) |
Benzo(a)pyrene |
Benzo(a)pyrene |
Benzo(a)pyrene |
Benzo(b)fluoranthene |
Benzo(g,h,i)perylene |
Benzo(g,h,i)perylene |
Benzo(k)fluoranthene |
Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) |
Heptachlor |
Heptachlor |
Indeno(1,2,3,-cd)pyrene |
Indeno(1,2,3,-cd)pyrene |
Mercury and its compounds |
Mercury and its compounds |
Tributyltin compounds |
Element extent |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend element |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Element 2 |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Element source |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
National |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
WaterFD |
Criterion |
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
D8C1
|
Parameter |
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in sediment
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in biota
|
Concentration in sediment
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in biota
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
Concentration in biota
|
Concentration in biota
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in sediment
|
Concentration in water
|
Concentration in water
|
|
Threshold value upper |
0.4 |
0.4 |
10.0 |
0.4 |
0.012 |
0.3 |
0.005 |
0.085 |
0.1 |
3.2 |
7.0 |
0.6 |
8.0 |
0.002 |
0.0012 |
1.6 |
1.2 |
0.2 |
12.0 |
0.1 |
0.4 |
0.03 |
12.0 |
0.3 |
8.2 |
0.0025 |
8e-06 |
0.002 |
1.3 |
10.0 |
0.02 |
20.0 |
6e-05 |
33.0 |
3.2e-05 |
0.002 |
0.005 |
0.2 |
0.005 |
30.0 |
0.6 |
0.0063 |
0.003 |
0.002 |
10.0 |
0.02 |
0.05 |
55.0 |
0.6 |
24.0 |
0.005 |
0.3 |
47.0 |
1.3 |
185.0 |
0.3 |
0.05 |
24.0 |
0.16 |
2.0 |
21.0 |
8.6 |
0.3 |
0.01 |
0.0007 |
0.4 |
7.7 |
0.015 |
6.0 |
1.0 |
0.5 |
0.0065 |
10.0 |
74.0 |
0.025 |
10.0 |
2.5 |
0.03 |
52.0 |
0.0005 |
0.002 |
0.0005 |
185.0 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.0085 |
0.014 |
0.014 |
5.0 |
0.43 |
0.00017 |
0.00017 |
0.085 |
0.00017 |
0.00017 |
0.0065 |
0.0067 |
1e-08 |
0.24 |
0.00017 |
0.15 |
0.07 |
0.0002 |
|
Threshold value lower |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value operator |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
< |
|
Threshold qualitative |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
OSPAR Convention
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
OSPAR Convention
|
National
|
National
|
National
|
National
|
National
|
OSPAR Convention
|
National
|
OSPAR Convention
|
National
|
National
|
||
Value achieved upper |
0.04 |
0.04 |
0.2 |
0.04 |
0.02 |
0.01 |
0.001 |
0.01 |
0.005 |
1.0 |
2.0 |
0.01 |
0.3 |
0.001 |
0.01 |
0.18 |
0.1 |
0.06 |
0.2 |
0.01 |
0.04 |
0.009 |
3.5 |
6.0 |
3.8 |
0.0025 |
0.0002 |
0.001 |
0.18 |
0.1 |
0.00291 |
2.0 |
0.003 |
20.0 |
0.001 |
0.01 |
0.001 |
0.01 |
0.001 |
2.0 |
0.017 |
0.003 |
0.01 |
0.001 |
3.0 |
0.005 |
0.0005 |
15.0 |
0.03 |
0.04 |
0.001 |
0.01 |
40.0 |
0.3 |
0.4 |
0.01 |
0.015 |
15.0 |
0.05 |
0.008 |
63.0 |
6.0 |
0.09 |
0.01 |
0.001 |
0.05 |
0.23 |
0.01 |
1.9 |
0.01 |
0.01 |
0.01 |
0.1 |
0.3 |
0.002 |
0.1 |
0.1 |
0.009 |
30.0 |
0.001 |
0.001 |
0.001 |
0.2 |
0.071 |
5e-05 |
0.028 |
5e-05 |
0.039 |
5e-05 |
0.174 |
7e-05 |
0.013 |
5e-05 |
5e-05 |
2.0 |
0.026 |
0.004 |
0.005 |
0.022 |
0.004 |
0.004 |
4.819 |
2.0 |
0.001 |
0.017 |
0.004 |
1.4 |
0.059 |
0.0003 |
|
Value achieved lower |
0.04 |
0.04 |
0.2 |
0.04 |
0.02 |
0.01 |
0.001 |
0.01 |
0.005 |
1.0 |
1.1 |
0.01 |
0.3 |
0.001 |
0.01 |
0.04 |
0.1 |
0.06 |
0.2 |
0.01 |
0.04 |
0.009 |
3.5 |
6.0 |
2.4 |
0.0025 |
0.0002 |
0.001 |
0.1 |
0.1 |
0.00028 |
2.0 |
0.003 |
20.0 |
0.001 |
0.01 |
0.001 |
0.01 |
0.001 |
2.0 |
0.046 |
0.003 |
0.01 |
0.001 |
3.0 |
0.005 |
0.0005 |
15.0 |
0.03 |
0.04 |
0.001 |
0.01 |
28.0 |
0.3 |
0.4 |
0.01 |
0.015 |
11.0 |
0.05 |
0.005 |
45.0 |
6.0 |
0.03 |
0.01 |
0.001 |
0.05 |
0.05 |
0.01 |
1.8 |
0.01 |
0.01 |
0.01 |
0.1 |
0.3 |
0.002 |
0.1 |
0.1 |
0.009 |
30.0 |
0.001 |
0.001 |
0.001 |
0.2 |
0.04 |
5e-05 |
0.0039 |
5e-05 |
0.006 |
5e-05 |
0.13 |
5e-05 |
0.0018 |
5e-05 |
5e-05 |
2.0 |
0.01 |
0.004 |
0.005 |
0.012 |
0.004 |
0.004 |
1.149 |
2.0 |
0.001 |
0.01 |
0.004 |
0.8 |
0.01 |
0.0002 |
|
Value unit |
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
milligram per kilogram
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per kilogram of wet weight
|
milligram per kilogram
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
microgram per kilogram of wet weight
|
microgram per kilogram of wet weight
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
milligram per kilogram
|
microgram per litre
|
microgram per litre
|
|
Proportion threshold value |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend parameter |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Not assessed |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Deteriorating |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Not assessed |
Stable |
Stable |
Stable |
Stable |
Stable |
Not assessed |
Stable |
Not assessed |
Stable |
Stable |
|
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
No |
|
Description parameter |
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
|
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ. ValueAchievedUpper predstavlja izmerjeno vrednost, ki je bila izmerjena nad LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK).
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK).
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata seštevek polovičnih vrednosti LOQ DDT izomerov.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
|
Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Vrednost v TresholdValueUpper se nanaša na vsoto koncentracij izomerov HCH.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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ValueAchievedLower predstavlja vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Navedena vrednost TresholdValueUpper se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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ValueAchievedLower predstavlja vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK). Le-ta se nanaša na vsoto koncentracij sorodnih bromiranih difenil etrov.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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ValueAchievedUpper predstavlja vsoto izmerjenih vrednosti. Večina izmerjenih vrednosti, ki sestavljajo ta element, je bila pod LOQ, zaradi česar privzemamo, da element ne poslabšuje stanja.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Obe navedeni vrednosti ValueAchievedUpper in ValueAchievedLower predstavljata vrednost LOQ za ta parameter. Meritve niso nikoli presegale te vrednosti. To pomeni, da se je pri presoji upoštevala polovična vrednost LOQ. Privzema se, da izmerjene vrednosti v povprečju ne presegajo zastavljene mejne vrednosti, saj gre za omejitev pri merilni metodi, uporabljeni za ta parameter. Za skupino poliaromatskih ogljikovodikov (PAH) se mejna vrednost v TresholdValueUpper nanaša na koncentracijo benzo(a)pirena, saj temelji na njegovi toksičnosti.
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Ker trenutno v nacionalni zakonodaji še ni določenih mejnih vrednosti za koncentracije onesnaževal v sedimentu, smo vrednosti za nekatera onesnaževala, izmerjena v sedimentu, orientacijsko primerjali z ERL (ang. Effects Range Low) vrednostmi iz literature po zgledu nekaterih drugih organizacij (OSPAR/US EPA). Te mejne vrednosti ne predstavljajo nacionalno predpisanih mejnih vrednosti in zaradi tega niso bile upoštevane pri presoji stanja.
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Navedena vrednost TresholdValueUpper je najvišja dovoljena koncentracija (NDK-OSK).
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ValueAchievedLower predstavlja izmerjeno vrednost, ki je bila izmerjena pod LOQ.
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Related indicator |
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Criteria status |
Not good |
Not good |
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Not good |
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Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Description criteria |
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Element status |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not good |
Not good |
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Not good |
Not good |
Not good |
Not good |
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Not good |
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Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
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Good |
Good |
Good |
Not good |
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Description element |
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Source assessment feature |
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Reporting method feature |
Type D |
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Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
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Stable |
Stable |
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Stable |
Stable |
Stable |
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Stable |
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Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
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Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Integration rule type parameter |
OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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Integration rule description parameter |
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Integration rule type criteria |
OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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Integration rule description criteria |
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GES extent threshold |
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GES extent achieved |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
98.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
62.50 |
GES extent unit |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
Proportion of substances in good status |
GES achieved |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
GES later than 2024, Art14ExceptionReported |
Description overall status |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
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Related targets |
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|
Test TV |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
NA |
Yes |
No |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
No |
No |
Yes |
No |
No |
No |
No |
No |
Yes |
No |
No |
Yes |
No |
Test results |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Correct |
Correct |