|
acquatico
|
Chlorella emersonii
|
alghe
|
EC50
|
5-10 mg/l
|
2g
|
|
ND
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC10
|
0,92 mg/l
|
72h
|
|
ND
|
|
|
|
acquatico
|
Pseudomonas putida
|
microrganismi
|
TT
|
100 mg/l
|
16h
|
|
ND
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC50
|
2,8 mg/l
|
72h
|
|
ND
|
|
|
|
acquatico
|
fanghi attivi
|
microrganismi
|
EC50
|
300 mg/l
|
3h
|
ISO 8192 "Test for inhibition of oxygen consumption by activated sludge"
|
1985
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC50
|
4,4 mg/l
|
96h
|
|
ND
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC50
|
1,1 mg/l
|
72h
|
|
ND
|
|
|
acuto
|
acquatico
|
Gammarus pseudolimnaeus
|
invertebrati acquatici
|
LC50
|
1,7 mg/l
|
96h
|
Methods for Acute Toxicity Tests with Fish, Macroinvertebrates and Amphibians, 795,120 of the Federal Register Guideline "Gammarid Acute Toxicity Test" and Standard Methods for Examination of Water and Wastewater (flow–through bioassay) Length: 2 – 3 mm M
|
ND
|
|
|
|
acquatico
|
fanghi attivi di prevalente origine domestica
|
microrganismi
|
EC50
|
100 mg/l
|
3h
|
OECD Guide–line 209 "Activated Sludge, Respiration Inhibition Test"
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
NOEC
|
2,2 mg/l
|
96h
|
|
ND
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC10
|
0,37 mg/l
|
72h
|
|
ND
|
|
|
|
acquatico
|
Scenedesmus quadricauda
|
alghe
|
TT
|
3,2 mg/l
|
8g
|
|
ND
|
|
|
|
acquatico
|
Microcystis aeruginosa
|
alghe
|
TT
|
4,1 mg/l
|
8g
|
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
1,3 mg/l
|
21g
|
"Verlaengerter Toxizitaetstest bei Daphnia magna (Bestimmung derNOEC fuer Reproduktionsrate, Mortalitaet und den Zeitpunkt des erstenAuftretens von Nachkommen; 21 d) Stand: 01,01,1984"
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia pulex
|
invertebrati acquatici
|
EC50
|
93 mg/l
|
6h
|
|
ND
|
|
|
acuto
|
acquatico
|
Gammarus pseudolimnaeus
|
invertebrati acquatici
|
NOEC
|
0,52 mg/l
|
96h
|
Methods for Acute Toxicity Tests with Fish, Macroinvertebrates and Amphibians, 795,120 of the Federal Register Guideline "Gammarid Acute Toxicity Test" and Standard Methods for Examination of Water and Wastewater (flow–through bioassay) Length: 2 – 3 mm M
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia pulex
|
invertebrati acquatici
|
EC50
|
68 mg/l
|
24h
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1552 mg/kg bw
|
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
28 mg/l
|
1h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
35 mg/l
|
24h
|
|
ND
|
|
|
|
acquatico
|
Chlorella vulgaris
|
alghe
|
EC50
|
5 mg/l
|
7g
|
OECD Guide–line 201 "Algae, Growth Inhibition Test"
|
ND
|
|
|
orale acuto
|
|
topo
|
mammiferi
|
LD50
|
1240 mg/kg bw
|
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
35 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
TC
|
8,3 mg/l
|
50g
|
|
ND
|
|
|
dermale acuto
|
|
guinea pig
|
mammiferi
|
LD50
|
9700 – 19400 mg/kg bw
|
|
|
ND
|
|
|
dermale acuto
|
|
coniglio
|
mammiferi
|
LD50
|
>10000 mg/kg bw
|
|
|
ND
|
|
|
dermale acuto
|
|
coniglio
|
mammiferi
|
LD50
|
>3100 mg/kg bw
|
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
<200 mg/l
|
1h
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
>4,242 mg/l
|
4h
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
<2000 mg/l
|
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
>42 mg/l
|
6h
|
|
ND
|
|
|
orale acuto
|
|
topo
|
mammiferi
|
LD50
|
900 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1600 – 3200 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
topo
|
mammiferi
|
LD50
|
1189 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
topo
|
mammiferi
|
LD50
|
400 – 800 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
<20000 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
11265 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1530 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1390 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
3350 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1400 mg/kg bw
|
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
3000 mg/kg bw
|
|
|
ND
|
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC0
|
1,5 mg/l
|
6h
|
|
ND
|
|
|
acuto
|
acquatico
|
Carassius auratus
|
pesci
|
LC50
|
8,8 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
18 mg/l
|
48h
|
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
14,2 mg/l
|
48h
|
Japanese Industrial Standard (JIS K 0102–1986–71) "Testingmethods for industrial waste water"
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
4,5 mg/l
|
96h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
4,5 mg/l
|
48h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
11,8 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
8,2 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
9,6 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Leuciscus idus
|
pesci
|
LC100
|
8,7 mg/l
|
48h
|
other: DEV, L 15 (1976)
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
8,18 mg/l
|
96h
|
|
ND
|
grado purezza 99%
|
|
acuto
|
acquatico
|
Leuciscus idus
|
pesci
|
LC0
|
5,8 mg/l
|
48h
|
other: DEV, L 15 (1976)
|
ND
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
4,2 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Brachydanio rerio
|
pesci
|
LC50
|
11,4 mg/l
|
144h
|
ISO 1975
|
ND
|
|
|
acuto prolungato
|
acquatico
|
Brachydanio rerio
|
pesci
|
TC
|
13,5 mg/l
|
10g
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
9,3 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Leuciscus idus
|
pesci
|
LC50
|
7,6 mg/l
|
48h
|
other: DEV, L 15 (1976)
|
ND
|
|
|
acuto
|
acquatico
|
Brachydanio rerio
|
pesci
|
LC100
|
14 mg/l
|
96h
|
Letale Wirkung beim Zebrabaerbling, UBA–Verfahrensvorschlag, Mai1984, Letale Wirkung beim Zebrabaerbling Brachydanio rerio LC0, LC50,LC100, 48–96h
|
1985
|
|
|
acuto
|
acquatico
|
Oncorhynchus mykiss
|
pesci
|
LC0
|
4,3 mg/l
|
96h
|
Methods for Acute Toxicity Tests with Fish, Macroinvertebrates and Amphibians, EPA, Ecological Research Series EPA–660/3–75–009, April 1975, U,S, EPA–TSCA, 40 CFR, Part 797 (1985)
|
ND
|
|
|
acuto
|
acquatico
|
Oncorhynchus mykiss
|
pesci
|
TC
|
19 mg/l
|
96h
|
Methods for Acute Toxicity Tests with Fish, Macroinvertebrates and Amphibians, EPA, Ecological Research Series EPA–660/3–75–009, April 1975, U,S, EPA–TSCA, 40 CFR, Part 797 (1985)
|
ND
|
|
|
acuto
|
acquatico
|
Oncorhynchus mykiss
|
pesci
|
LC50
|
13 mg/l
|
96h
|
Methods for Acute Toxicity Tests with Fish, Macroinvertebrates and Amphibians, EPA, Ecological Research Series EPA–660/3–75–009, April 1975, U,S, EPA–TSCA, 40 CFR, Part 797 (1985)
|
ND
|
|
|
acuto
|
acquatico
|
Brachydanio rerio
|
pesci
|
LC0
|
10 mg/l
|
96h
|
Letale Wirkung beim Zebrabaerbling, UBA–Verfahrensvorschlag, Mai1984, Letale Wirkung beim Zebrabaerbling Brachydanio rerio LC0, LC50,LC100, 48–96h
|
1985
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
33 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
52 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
9,3 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Oncorhynchus mykiss
|
pesci
|
LC50
|
11,5-13,5 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC100
|
58 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
EC50
|
7,79 mg/l
|
96h
|
|
ND
|
grado purezza 99%
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
7 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC100
|
41 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
30 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
5 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
3,1 mg/l
|
14g
|
OECD Guide–line 202, Daphnia sp,, acute immobilization andreproduction test
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
2,5 mg/l
|
24h
|
Daphnien–Schwimmunfaehigkeits–Test, UBA–Verfahrensvorschlag Mai1984, Bestimmung der Schwimmunfaehigkeit beim Wasserfloh Daphnia magna,EC0, EC50, EC100 24h, statisches System Year: 1985 GLP: no
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
11 mg/l
|
96h
|
|
ND
|
grado purezza 99%
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
52 mg/l
|
6h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
2,1 mg/l
|
72h
|
ISO (1975)
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
4,2 mg/l
|
24h
|
OECD Guide–line 202, part 1 "Daphnia sp,, Acute Immobilisation Test"
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
EC50
|
6,56 mg/l
|
96h
|
|
ND
|
grado purezza 99%
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
5,8 mg/l
|
24h
|
Daphnien–Schwimmunfaehigkeits–Test, UBA–Verfahrensvorschlag Mai1984, Bestimmung der Schwimmunfaehigkeit beim Wasserfloh Daphnia magna,EC0, EC50, EC100 24h, statisches System Year: 1985 GLP: no
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC100
|
20 mg/l
|
24h
|
Daphnien–Schwimmunfaehigkeits–Test, UBA–Verfahrensvorschlag Mai1984, Bestimmung der Schwimmunfaehigkeit beim Wasserfloh Daphnia magna,EC0, EC50, EC100 24h, statisches System Year: 1985 GLP: no
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
12,8 mg/l
|
24h
|
ISO (1975)
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
3,65 mg/l
|
48h
|
ISO (1975)
|
ND
|
|
|