dermale acuto
|
|
ratto
|
mammiferi
|
LD50
|
>3450 mg/kg bw
|
|
|
ND
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
inalatorio acuto
|
|
ratto
|
mammiferi
|
LC50
|
>2,6 mg/l mg/l
|
4h
|
|
ND
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|
acuto
|
acquatico
|
Salmo gairdneri
|
pesci
|
LC50
|
14 mg/l
|
96h
|
APHA, Standard Methods for the Examination of Water and Waste Water, 14th edition, American Public Health Assoc,, Washington,
|
1975
|
|
|
acuto
|
acquatico
|
Daphnia magna
|
invertebrati acquatici
|
EC50
|
110 mg/l
|
48h
|
Finney, D,J,, Probit Analysis, Cambridge University Press, 3rd Edition, p,333,
|
1971
|
|
|
acuto
|
acquatico
|
Acartia tonsa
|
invertebrati acquatici
|
EC50
|
0,06-1,3 mg/l
|
48h
|
U,S, EPA, Methods for acute toxicity testing with fish, macro–invertebrates and amphibians, EPA–660/3–75–009,
|
1975
|
|
|
|
acquatico
|
Scenedesmus subspicatus
|
alghe
|
EC50
|
26 mg/l
|
96h
|
Finney, D,J,, Probit Analysis, Cambridge University Press, 3rd Edition, p,333,
|
1971
|
|
|
|
|
Pseudomonas putida
|
microrganismi
|
NOEC
|
>= 100 mg/l
|
6h
|
TNO, Degradability, Ecotoxicity, and Bioaccumulation, Delft, The Netherlands,
|
1977
|
|
|
orale acuto
|
|
ratto
|
mammiferi
|
LD50
|
>8850 mg/kg bw
|
|
|
ND
|
sostanza conforme a quanto riportato nei par. 1.1 -1.4 del dossier IUCLID
|
|