|
acquatico
|
Skeletonema costatum
|
alghe
|
EC50
|
49,6 mg/l
|
96h
|
Wachstumshemmtest statisch
|
ND
|
|
|
acuto
|
acquatico
|
Mysidopsis bahia
|
invertebrati acquatici
|
LC50
|
2,85 mg/l
|
96h
|
|
ND
|
|
|
|
acquatico
|
Ankistrodesmus falcatus
|
alghe
|
EC50
|
2,9 mg/l
|
4h
|
Bestimmung der Photosynthesehemmung
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC50
|
179 mg/l
|
96h
|
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC50
|
149 mg/l
|
96h
|
Wachstumstest
|
ND
|
|
|
|
acquatico
|
Chlorella vulgaris
|
alghe
|
EC50
|
35-38 mg/l
|
6h
|
Wachstumstest gemaess Boehm et al, (1972): DD–Pat, 94234
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
0,54 mg/l
|
21g
|
Verlaengerter Toxizitaetstest bei Daphnia magna (Bestimmung der NOEC fuer Reproduktionsrate, Mortalitaet und den Zeitpunkt des ersten Auftretens von Nachkommen, 21 d), Stand: 01,01,1984
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
LOEC
|
1,5 mg/l
|
21g
|
ASTM (1978): Proposal standard practice for conducting renewal life cycle toxicity tests with the daphnid Daphnia magna, Draft No, 4
|
ND
|
|
|
acuto
|
acquatico
|
Chironomus riparius
|
invertebrati acquatici
|
NOEC
|
0,367 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Mysidopsis bahia
|
invertebrati acquatici
|
NOEC
|
<1,3 mg/l
|
96h
|
|
ND
|
|
|
|
acquatico
|
Skeletonema costatum
|
alghe
|
NOEC
|
7,3 mg/l
|
96h
|
|
ND
|
|
|
|
|
microrganismi anaerobi
|
microrganismi
|
EC0
|
50 mg/l
|
193h
|
Bioassay for Monitoring Biochemical Methane Potential and Anaerobic Toxicity nach Owen et al, (1979): Water Res, 13, 485
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
LC50
|
28 mg/l
|
48h
|
US–EPA (1975): Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians (EPA–660/3–75–009)
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
0,69 mg/l
|
21g
|
ASTM (1978): Proposal standard practice for conducting renewal life cycle toxicity tests with the daphnid Daphnia magna, Draft No, 4
|
ND
|
|
|
|
|
batteri metanogeni
|
microrganismi
|
EC50
|
250 mg/l
|
24h
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
>17,6 mg/l
|
4h
|
OECD Guide–line 403 "Acute Inhalation Toxicity"
|
1992
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
ca, 580 mg/kg bw
|
|
other: Versuchsdurchfuehrung nach internen Richtlinien der Hoechst AG
|
1980
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
ca, 2300 mg/kg bw
|
|
other: Versuchsdurchfuehrung nach internen Richtlinien der Hoechst AG
|
1979
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
|
|
non riportata
|
microrganismi
|
EC50
|
5,1 mg/l
|
30min
|
microtox
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
1,4 mg/l
|
16g
|
Dutch Standard Organisation (1980): NEN 6502, 6501;
|
ND
|
|
|
|
|
microrganismi anaerobi
|
microrganismi
|
EC15
|
ca, 100 mg/l
|
193h
|
Bioassay for Monitoring Biochemical Methane Potential and Anaerobic Toxicity nach Owen et al, (1979): Water Res, 13, 485
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
NOEC
|
41,8 mg/l
|
96h
|
|
ND
|
|
|
|
|
microrganismi aerobi
|
microrganismi
|
EC100
|
>=20 mg/l
|
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
6 mg/l
|
48h
|
US–EPA (1975): Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians (EPA–660/3–75–009)
|
ND
|
|
|
|
acquatico
|
Cyclotella meneghiniana
|
alghe
|
EC50
|
51,88 mg/l
|
48h
|
Bestimmung der Abnahme des DNA–Gehalts
|
ND
|
|
|
|
|
batteri aerobi eterotrofi
|
microrganismi
|
EC50
|
687 mg/l
|
24h
|
|
ND
|
|
|
|
|
Tetrahymena pyriformis
|
microrganismi
|
EC50
|
130 mg/l
|
24h
|
|
ND
|
|
|
|
|
Photobacterium phosphoreum
|
microrganismi
|
EC50
|
3,29 mg/l
|
15min
|
microtox
|
ND
|
|
|
|
|
Photobacterium phosphoreum
|
microrganismi
|
EC50
|
4,2 mg/l
|
10min
|
microtox
|
ND
|
|
|
|
|
Photobacterium phosphoreum
|
microrganismi
|
EC50
|
2,9 mg/l
|
5min
|
microtox
|
ND
|
|
|
|
acquatico
|
non riportata
|
alghe
|
EC50
|
31 mg/l
|
96h
|
OECD proposal (1979): short–term toxicity test
|
ND
|
grado di purezza 99,4 %
|
|
|
|
batteri anaerobi da impianti di trattamento di tipo domestico
|
microrganismi
|
EC0
|
ca, 40 mg/l
|
24h
|
ETAD Fermentation tube method "Determination of damage to effluent bacteria by the Fermentation Tube Method"
|
ND
|
|
|
acuto
|
acquatico
|
Brachydanio rerio
|
pesci
|
LC50
|
3,15-6,3 mg/l
|
48h
|
AFNOR–T90–303
|
1979
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
acuto
|
acquatico
|
Leuciscus idus
|
pesci
|
LC50
|
13,9 mg/l
|
96g
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
1980
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
acuto
|
acquatico
|
Leuciscus idus
|
pesci
|
NOEC
|
<4 mg/l
|
96g
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
1980
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
acuto
|
acquatico
|
Lepomis macrochirus
|
pesci
|
NOEC
|
1,7 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Lepomis macrochirus
|
pesci
|
LC50
|
5,02 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Lepomis macrochirus
|
pesci
|
LC50
|
5 mg/l
|
96h
|
US–EPA (1975): Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians
|
ND
|
|
|
acuto
|
acquatico
|
Leuciscus idus melanotus
|
pesci
|
LC50
|
3,15-6,3 mg/l
|
48h
|
other: DIN 38412; L15
|
1979
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
acuto
|
acquatico
|
Cyprinodon variegatus
|
pesci
|
LC50
|
7,8 mg/l
|
96h
|
US–EPA (1975): Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
7,8 mg/l
|
96h
|
Acute Toxizitaet gegenueber Fischen
|
ND
|
|
|
acuto prolungato
|
acquatico
|
Poecilia reticulata
|
pesci
|
LC50
|
7,37 mg/l
|
14g
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
LC50
|
6,8 mg/l
|
24h
|
OECD proposal (1979): short–term toxicity test
|
ND
|
grado purezza 99,4 %
|
|
|
acquatico
|
Skeletonema costatum
|
alghe
|
EC50
|
52,8 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
7,36 mg/l
|
96h
|
Committee on Methods for toxicity Tests with aquatic Organisms (1975): EPA–660/3–75–009
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
9,12 mg/l
|
96h
|
ASTM (1980): Standard practice for conducting acute toxicity tests with fishes, macroinvertebrates, and amphibians (E729–80)
|
ND
|
grado purezza 99 %
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
8,03 mg/l
|
96h
|
APHA (1980): Standard Methods for the examination of water and wastewater
|
1985
|
grado purezza 98 %
|
|
acuto
|
acquatico
|
Cyprinodon variegatus
|
pesci
|
NOEC
|
4,2 mg/l
|
96h
|
US–EPA (1975): Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC10
|
0,95 mg/l
|
16g
|
Dutch Standard Organisation (1980): NEN 6502, 6501
|
ND
|
|
|
acuto
|
acquatico
|
Leuciscus idus melanotus
|
pesci
|
LC50
|
13,9 mg/l
|
96h
|
Interne Richtlinie der Hoechst AG
|
1980
|
m–Dichlorobenzole distillato
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
1,2 mg/l
|
24h
|
OECD proposal (1979): short–term toxicity test
|
ND
|
grado purezza 99,4 %
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
EC50
|
4,89 mg/l
|
96h
|
APHA (1980): Standard Methods for the examination of water and wastewater
|
1985
|
grado purezza 98 %
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
LC50
|
1,7 mg/l
|
16g
|
Dutch Standard Organisation (1980): NEN 6502, 6501;
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
0,3 mg/l
|
16g
|
Dutch Standard Organisation (1980): NEN 6502, 6501
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
5,5 mg/l
|
48h
|
DIN 38412 Teil 11
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
7 mg/l
|
48h
|
DIN 38412 Teil 11
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
LC50
|
7,4 mg/l
|
48h
|
ASTM (1980): Standard E 729–80
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
4,22 mg/l
|
48h
|
ASTM (1980): Standard E 729–80
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
6 mg/l
|
24h
|
AFNOR (1974): Determination de L’inhibition de mobilite de Daphnia magna Straus (crustace cladocere), Norme experimentale T 90–301, Avril 1974 GLP no data
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
9 mg/l
|
48h
|
Japanese Industrial Standard (JIS K 0102–1986–71) "Testing methods for industrial waste water"
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
7,7 mg/l
|
96h
|
APHA (1980): Standard Methods for the examination of water and wastewater
|
ND
|
grado purezza 98 %
|
|
acuto
|
acquatico
|
Leuciscus idus melanotus
|
pesci
|
LC100
|
25 mg/l
|
96h
|
Interne Richtlinie der Hoechst AG
|
1980
|
m–Dichlorobenzole distillato
|
|
acuto
|
acquatico
|
Leuciscus idus melanotus
|
pesci
|
LC0
|
10 mg/l
|
96h
|
Interne Richtlinie der Hoechst AG
|
1980
|
m–Dichlorobenzole distillato
|
|