orale acuto
|
|
topo
|
mammiferi
|
LD50
|
766 mg/kg bw
|
|
|
1969
|
grado purezza >= 98 %
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC10
|
3 mg/l
|
96h
|
UBA Verfahrensvorschlag "Hemmung der Zellvermehrung bei der Gruenalge Scenedesmus subspicatus" (EC 10; EC50; 72 Stunden; statisches System (01,02,1984)
|
ND
|
grado purezza 98%
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC50
|
18,9 mg/l
|
96h
|
UBA Verfahrensvorschlag "Hemmung der Zellvermehrung bei der Gruenalge Scenedesmus subspicatus" (EC 10; EC50; 72 Stunden; statisches System (01,02,1984)
|
ND
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC10
|
2,22 mg/l
|
96h
|
UBA Verfahrensvorschlag "Hemmung der Zellvermehrung bei der Gruenalge Scenedesmus subspicatus" (EC 10; EC50; 72 Stunden; statisches System (01,02,1984)
|
ND
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC50
|
8,4 mg/l
|
96h
|
UBA Verfahrensvorschlag "Hemmung der Zellvermehrung bei der Gruenalge Scenedesmus subspicatus" (EC 10; EC50; 72 Stunden; statisches System (01,02,1984)
|
ND
|
grado purezza 98%
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC50
|
1,4 mg/l
|
96h
|
OECD Guide–line 201 "Algae, Growth Inhibition Test"
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC0
|
1,4 mg/l
|
96h
|
OECD Guide–line 201 "Algae, Growth Inhibition Test"
|
ND
|
|
|
acuto
|
acquatico
|
Aplexa hypnorum
|
invertebrati acquatici
|
EC50
|
3,16 mg/l
|
96h
|
Stephan, C,E, et al; Guidelines for deriving numerical national water quality criteria for the protection of aquatic organisms and theit uses, NTIS, PB85–227049 (1985)
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC50
|
36,7 mg/l
|
96h
|
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
0,45 mg/l
|
14g
|
OECD Guide–line 202, part 2 "Daphnia sp,, Reproduction Test"
|
ND
|
|
|
|
|
fanghi attivi
|
microrganismi
|
EC50
|
500 mg/l
|
3h
|
Activated Sludge, Respiration Inhibition Test, OECD Guideline 209, 4,04,1984, modified
|
ND
|
|
|
|
acquatico
|
Selenastrum capricornutum
|
alghe
|
EC100
|
4,9 mg/l
|
96h
|
OECD Guide–line 201 "Algae, Growth Inhibition Test"
|
ND
|
|
|
|
acquatico
|
Ankistrodesmus falcatus
|
alghe
|
EC50
|
6 mg/l
|
4h
|
|
ND
|
|
|
dermale acuto
|
|
topo
|
mammiferi
|
LD50
|
305 mg/kg bw
|
|
|
1978
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
0,27 mg/l
|
16g
|
NEN Reports 6501, 6502 GLP no data
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
0,1 mg/l
|
16g
|
NEN Reports 6501, 6502
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
3,4 mg/l
|
14g
|
OECD Guide–line 202, part 2 "Daphnia sp,, Reproduction Test"
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC16
|
0,32 mg/l
|
14g
|
OECD Guide–line 202, part 2 "Daphnia sp,, Reproduction Test"
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
0,56 mg/l
|
14g
|
NEN Reports 6501, 6502 GLP no data
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
0,32 mg/l
|
14g
|
NEN Reports 6501, 6502
|
ND
|
|
|
|
|
fanghi attivi
|
microrganismi
|
EC50
|
35 mg/l
|
12h
|
Respirometer test run on a Comput–OX Respirometer (N–CON Corporation, NY)
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
0,4 mg/l
|
21g
|
EEC Directive 79/831, Annex V, Part C: Methods for the Determination of Ecotoxicity
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1107 mg/kg bw
|
|
OECD Guide–line 401 (draft)
|
1979
|
grado purezza 98 %
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
0,36-0,6 mg/l
|
28g
|
|
ND
|
|
|
dermale acuto
|
|
topo
|
mammiferi
|
LD50
|
300 mg/kg bw
|
|
|
1978
|
|
|
dermale acuto
|
|
ratto
|
mammiferi
|
LD50
|
6139 mg/kg bw
|
|
|
1969
|
grado purezza 98 %
|
|
dermale acuto
|
|
ratto
|
mammiferi
|
LD50
|
11356,8 mg/kg bw
|
|
OECD Guide–line 401 (draft)
|
1979
|
grado purezza 98 %
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC0
|
418 ppm
|
4h
|
|
1982
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1421 mg/kg bw
|
|
|
1980
|
grado purezza 98 %
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
855 mg/kg bw
|
|
|
ND
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID prescribed by 1,1 –
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
756 mg/kg bw
|
|
|
1969
|
grado purezza 98 %
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
550 mg/kg bw
|
|
OECD Guide–line 402
|
1982
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
1019 mg/kg bw
|
|
|
1979
|
grado purezza 98 %
|
|
|
|
Photobacterium phosphoreum
|
microrganismi
|
EC50
|
2,3 mg/l
|
5min
|
microtox
|
ND
|
|
|
|
terrestre
|
Lactuca sativa Ravel R2
|
piante terrestri
|
EC50
|
0,6 mg/l soluz, nutritiva
|
16-21g
|
Steiner, A,A,: Soilless culture, Proceedings, Sixth Colloquium of the International Potash Institute, Florence, Italy, 324–341 (1968)
|
ND
|
grado purezza >= 95 %
|
|
|
terrestre
|
Avena sativa
|
piante terrestri
|
EC50
|
240 mg/kg
|
14g
|
OECD Guide–line 208 "Terrestrial Plants, Growth Test"
|
ND
|
|
|
|
terrestre
|
Brassica rapa
|
piante terrestri
|
EC50
|
110 mg/kg
|
14g
|
OECD Guide–line 208 "Terrestrial Plants, Growth Test"
|
ND
|
|
|
|
terrestre
|
Lactuca sativa Ravel R3
|
piante terrestri
|
EC50
|
48 mg/g soil
|
14g
|
OECD Guide–line 208 "Terrestrial Plants, Growth Test"
|
ND
|
grado purezza >= 95 %
|
|
|
terrestre
|
Lactuca sativa Ravel R2
|
piante terrestri
|
EC50
|
56 mg/g soil
|
7g
|
OECD Guide–line 208 "Terrestrial Plants, Growth Test"
|
ND
|
grado purezza >= 95 %
|
|
cronico
|
terrestre
|
Eisenia foetida
|
invertebrati terrestri
|
LC50
|
250-500 mg/kg
|
28g
|
Richtlinie zur Pruefung der Toxizitaet von Chemikalien und Pflanzenbehandlungsmitteln an Regenwuermern (Eisenia foetida) der BBA; OECD Chemicals Testing Programme, Ecotoxicology Group, June 1982
|
ND
|
|
|
|
acquatico
|
Nitrosomonas
|
microrganismi
|
IC50
|
2120 mg/l
|
24h
|
simile a ISO/DIS 9509
|
ND
|
|
|
|
|
Tetrahymena pyriformis
|
microrganismi
|
EC50
|
0,91 mg/l
|
24h
|
|
ND
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
930 mg/kg bw
|
|
|
1982
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
4,2 mg/l
|
96h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
1,95 mg/l
|
48h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
12 mg/l
|
48h
|
|
ND
|
|
|
|
|
Pseudomonas putida
|
microrganismi
|
EC10
|
>30 mg/l
|
30min
|
Bewertung toxischer Wasserinhaltsstoffe aus ihrer Inhibitorwirkung auf die Substratoxydation von Pseudomonas Stamm Berlin mit Hilfe polarographischer Sauerstoffmessungen, Robra, K,H,: gwf wasser/abwasser 117 (2), 80–86 (1976)
|
ND
|
|
|
acuto
|
acquatico
|
Lepomis macrochirus
|
pesci
|
LC50
|
3,4 mg/l
|
96h
|
Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians", U,S, EPA 1975
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
12,3 mg/l
|
96h
|
Japanese Industrial Standard (JIS K 0102–1986–71) "Testing methods for industrial waste water"
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
4,8 mg/l
|
96h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Oryzias latipes
|
pesci
|
LC50
|
4,9 mg/l
|
48h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Lepomis macrochirus
|
pesci
|
LC50
|
3,02 mg/l
|
96h
|
Stephan, C,E, et al,; Guidelines for deriving numerical national water quality criteria for the protection of aquatic organisms and their uses, NTIS, PB85–227049 (1985)
|
ND
|
|
|
acuto
|
acquatico
|
Cyprinodon variegatus
|
pesci
|
LC50
|
21 mg/l
|
96h
|
U,S, EPA: Methods for acute toxicity tests with fish, macroinvertebrates , and amphibians, Ecological Research Series (EPA–660/3–75–009), 61 pp, (1975)
|
ND
|
grado purezza >= 80%
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
1,3 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Leuciscus idus
|
pesci
|
LC50
|
0,7 mg/l
|
48h
|
Bestimmung der Wirkung von Wasserinhaltsstoffen auf Fische, DIN 38412 Teil 15
|
ND
|
|
|
acuto
|
acquatico
|
Cyprinodon variegatus
|
pesci
|
LC0
|
15 mg/l
|
96h
|
U,S, EPA: Methods for acute toxicity tests with fish, macroinvertebrates , and amphibians, Ecological Research Series (EPA–660/3–75–009), 61 pp, (1975)
|
ND
|
grado purezza >= 80%
|
|
acuto
|
acquatico
|
Lepomis macrochirus
|
pesci
|
LC50
|
109 mg/l
|
24h
|
Methods for acute toxicity tests with fish, macroinvertebrates, and amphibians", U,S, EPA 1975
|
ND
|
grado purezza >= 80%
|
|
acuto
|
acquatico
|
Brachydanio rerio
|
pesci
|
LC50
|
6,57 mg/l
|
96h
|
Bestimmung der Wirkung von Wasserinhaltsstoffen auf Fische, DEV, L15 (1979)
|
1980
|
Acetone come solvente
|
|
acuto
|
acquatico
|
Jordanella floridae
|
pesci
|
LC50
|
4000 µg/l
|
96h
|
US Environmental Protection Agency (1975), The Committee on Methods for Toxicity Tests with Aquatic Organisms: Methods for acute toxicity tests with fish, macroinvertebrate and amphibians
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
2,99 mg/l
|
96h
|
|
1985
|
grado purezza 99 %
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
2,9 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
2,76 mg/l
|
96h
|
ASTM (1980): Standard practice for conducting acute toxicity tests with fishes, macroinvertebrates, and amphibians (E729–80)
|
ND
|
|
|
acuto
|
acquatico
|
Jordanella floridae
|
pesci
|
LC50
|
1217 µg/l
|
96h
|
US Environmental Protection Agency (1975), The Committee on Methods for Toxicity Tests with Aquatic Organisms: Methods for acute toxicity tests with fish, macroinvertebrate and amphibians
|
ND
|
|
|
|
acquatico
|
Chlorella vulgaris
|
alghe
|
EC50
|
5,6 mg/l
|
7g
|
OECD Guide–line 201 "Algae, Growth Inhibition Test"
|
ND
|
|
|
acuto
|
acquatico
|
Palaemonetes pugio
|
invertebrati acquatici
|
EC50
|
0,54 mg/l
|
96h
|
|
ND
|
|
|
acuto
|
acquatico
|
Brachydanio rerio
|
pesci
|
LC50
|
6,3 mg/l
|
96h
|
OECD Guide–line 203 "Fish, Acute Toxicity Test"
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
1,4 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC0
|
<2,4 mg/l
|
48h
|
|
ND
|
|
|
acuto
|
acquatico
|
Cyprinodon variegatus
|
pesci
|
LC50
|
>47 mg/l
|
|
U,S, EPA: Methods for acute toxicity tests with fish, macroinvertebrates , and amphibians, Ecological Research Series (EPA–660/3–75–009), 61 pp, (1975)
|
ND
|
grado purezza >= 80%
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
3,4 mg/l
|
48h
|
|
ND
|
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
1,32 mg/l
|
96h
|
|
ND
|
grado purezza 99 %
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
114 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
110 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
21 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
2,5 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
2-2,4 mg/l
|
24h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
2,4 mg/l
|
24h
|
Standard Methods for the Examination of Water and Wastewater, 6th Ed,, APHA, 1960
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
2,7 mg/l
|
48h
|
NEN Reports 6501, 6502
|
ND
|
|
|
cronico
|
acquatico
|
Pimephales promelas
|
pesci
|
NOEC
|
0,5 mg/l
|
32g
|
Methods for acute tests with fish, macroinvertebrates and amphibians, Ecological Research Series EPA–660/3–75–009 (1975), Available from Department of Commerce, National Techn, Information Service, Springfield, VA 22151
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
50 mg/l
|
48h
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
4 mg/l
|
24h
|
Daphnien–Kurzzeittest, DIN 38412 Teil 11, Bestimmung der Wirkung von Wasserinhaltsstoffen auf Kleinkrebse
|
ND
|
|
|
cronico
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
0,5-1 mg/l
|
32g
|
|
ND
|
|
|
acuto prolungato
|
acquatico
|
Pimephales promelas
|
pesci
|
LC50
|
1,8 mg/l
|
8g
|
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
1,7-2,1 mg/l
|
48h
|
ASTM (1980)
|
ND
|
|
|
acuto prolungato
|
acquatico
|
Poecilia reticulata
|
pesci
|
LC50
|
2,4 mg/l
|
14g
|
|
ND
|
|
|
cronico
|
acquatico
|
Pimephales promelas
|
pesci
|
LOEC
|
1 mg/l
|
32g
|
Methods for acute tests with fish, macroinvertebrates and amphibians, Ecological Research Series EPA–660/3–75–009 (1975), Available from Department of Commerce, National Techn, Information Service, Springfield, VA 22151
|
ND
|
|
|
cronico
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
NOEC
|
3,4 mg/l
|
14g
|
Daphnia sp,, Acute Immobilization and Reproduction Test, OECD Guideline 202, 4,04,1984
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
4,1 mg/l
|
24h
|
Daphnia sp,, Acute Immobilization and Reproduction Test, OECD Guideline 202, 4,04,1985
|
ND
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
7,69 mg/l
|
48h
|
Daphnia sp,, Acute Immobilization and Reproduction Test, OECD Guideline 202, 4,04,1985
|
ND
|
|
|