PEER REVIEW DRAFT. DO NOT CITE OR QUOTE
\vEPA
United States Office of Chemical Safety and
Environmental Protection Agency Pollution Prevention
Draft Risk Evaluation for
Perchloroethylene
(Ethene, 1,1^2,2-Tetrachloro)
Systematic Review Supplemental File: Data Extraction Tables for
Environmental Hazard Studies
CASRN: 127-18-4
CI CI
CI CI
April 2020
1
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Environmental Hazard Data Extraction Table for Perchloroethylene (PCE)
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Fish
Rainbow trout
Fresh
96-hour
LCso -
Not reported
Flow-
Mortality
Shubat et
High
(Oncorhynchu
s mvkiss)
5.84 mg
AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
96-hour
LCso =
Not reported
Flow-
Mortality
Shubat et
High
('Oncorhynchu
s mvkiss)
4.99 mg
AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
1-hour
LCso =
Not reported
Flow-
Mortality
Shubat et
High
('Oncorhynchu
s mvkiss)
-15 mg
AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
3-hour
LCso =
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
>11, <12
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
6-hour
LCso = ~7
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
12-hour
LCso = ~6
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
24-hour
LCso = ~5
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
48-hour
LCso = ~5
mg AI/L
Not reported
Flow-
through,
Measured
Mortality
Shubat et
al„ 1982
High
Rainbow trout
Fresh
72-hour
LCso = ~5
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
1-hour
LCso =
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
>11, <12
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
3-hour
LCso = >8,
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
6-hour
LCso = >7,
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
<8 mg
AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
12-hour
LCso = ~7
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
mg AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
24-hour
LCso = >6,
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
<7 mg
AI/L
through,
Measured
al„ 1982
Rainbow trout
Fresh
48-hour
LCso = >6,
Not reported
Flow-
Mortality
Shubat et
High
{Oncorhynchu
s mvkiss)
<7 mg
AI/L
through,
Measured
al„ 1982
2
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INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Rainbow trout
(Oncorhynchu
s mvkiss)
Fresh
72-hour
LCso = >6,
<7 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Shubat et
al„ 1982
High
Rainbow trout
Fresh
24-hour
LCso =
Not reported
Flow-
Mortality
Call et al„
High
('Oncorhynchu
s mvkiss)
4.99 mg
AI/L
through,
Measured
1983
Rainbow trout
Fresh
48-hour
LCso =
Not reported
Flow-
Mortality
Call et al„
High
('Oncorhynchu
s mvkiss)
4.99 mg
AI/L
through,
Measured
1983
Rainbow trout
Fresh
72-hour
LCso =
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
4.99 mg
AI/L
through,
Measured
1983
Rainbow trout
Fresh
24-hour
LCso =
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
6.31 mg
AI/L
through,
Measured
1983
Rainbow trout
Fresh
48-hour
LCso =
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
5.95 mg
AI/L
through,
Measured
1983
Rainbow trout
Fresh
72-hour
LCso =
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
5.81 mg
AI/L
through,
Measured
1983
Rainbow trout
Fresh
96-hour
ECso =
Not reported
Flow-
Equilibrium
Call et al„
High
{Oncorhynchu
s mvkiss)
5.38 mg
AI/L
through,
Nominal
1979
Rainbow trout
Fresh
96-hour
ECso =
Not reported
Flow-
Equilibrium
Call et al„
High
{Oncorhynchu
s mvkiss)
4.68 mg
AI/L
through,
Nominal
1979
Rainbow trout
Fresh
<20-hour
LCso = >9,
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
<12 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
<20-hour
LCso = >6,
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
<20-hour
LCso = >6,
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
>20-<
LCso = ~6
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
40-hour
mg AI/L
through,
Measured
1979
Rainbow trout
Fresh
>40-,
LCso = >3,
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
<60-hour
<6 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
>60-,
LCso = >3,
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
<80-hour
<6 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
96-hour
LCso = >3,
Not reported
Flow-
Mortality
Call et al„
High
{Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
<20-hour
LCso = >6,
Not reported
Flow-
Mortality
Call et al..
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
1979
3
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INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Duration
End-point
Concentration(s)
Test
Effect(s)
References
Data Quality
Salt
Analysis
Evaluation
Water
Rainbow trout
Fresh
<20-hour
LCso = >3,
Not reported
Flow-
Mortality
Ca
et al..
High
(Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
LCso = >3,
Not reported
Flow-
Mortality
Ca
et al..
High
('Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>20-,
LCso = >3,
Not reported
Flow-
Mortality
Ca
et al..
High
('Oncorhynchu
s mvkiss)
<40-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>40-,
LCso = >3,
Not reported
Flow-
Mortality
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<60-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>60-,
LCso = >3,
Not reported
Flow-
Mortality
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<80-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
ECso = >6,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
ECso = >6,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
ECso = >6,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<9 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>20-,
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<40-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>40-,
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<60-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>60-,
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<80-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
96-hour
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
<20-hour
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>20-,
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<40-hour
<6 mg
AI/L
through,
Measured
979
Rainbow trout
Fresh
>40-,
ECso = >3,
Not reported
Flow-
Equilibrium
Ca
et al..
High
{Oncorhynchu
s mvkiss)
<60-hour
<6 mg
AI/L
through,
Measured
1979
4
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Rainbow trout
(Oncorhynchu
s mvkiss)
Fresh
>60-,
<80-hour
ECso = >3,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al„
1979
High
Rainbow trout
('Oncorhynchu
s mvkiss)
Fresh
<20-hour
LCso = >8,
<10 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
('Oncorhynchu
s mvkiss)
Fresh
<20-hour
LCso = >8,
<10 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
<20-hour
LCso = >6,
<8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
<20-hour
LCso = >6,
<8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
<20-hour
LCso = >6,
<8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>20-,
<40-hour
LCso = ~6
mg AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>20-,
<40-hour
LCso = >6,
<8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>40-,
<60-hour
LCso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>40-,
<60-hour
LCso = >6,
<8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>60-,
<80-hour
LCso = >6,
<8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>60-,
<80-hour
LCso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>60-,
<80-hour
ECso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>60-,
<80-hour
ECso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>40-,
<60-hour
ECso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>40-,
<60-hour
ECso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al„
1979
High
Rainbow trout
{Oncorhynchu
s mvkiss)
Fresh
>20-,
<40-hour
ECso = ~6
mg AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al.,
1979
High
5
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INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Rainbow trout
(Oncorhynchu
s mvkiss)
Fresh
>20-,
<40-hour
ECso = >4,
<6 mg
AI/L
Not reported
Flow-
through,
Measured
Equilibrium
Call et al„
1979
High
Rainbow trout
Fresh
<20-hour
m
p
o
II
ck
Not reported
Flow-
Equilibrium
Call et al„
High
('Oncorhynchu
s mvkiss)
mg AI/L
through,
Measured
1979
Rainbow trout
Fresh
<20-hour
m
p
o
II
V
p
Not reported
Flow-
Equilibrium
Call et al„
High
('Oncorhynchu
s mvkiss)
<8 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
<20-hour
m
p
o
II
V
p
Not reported
Flow-
Equilibrium
Call et al„
High
{Oncorhynchu
s mvkiss)
<8 mg
AI/L
through,
Measured
1979
Rainbow trout
Fresh
<20-hour
m
p
o
II
V
00
Not reported
Flow-
Equilibrium
Call et al„
High
{Oncorhynchu
s mvkiss)
<10 mg
AI/L
through,
Measured
1979
Bluegill
Fresh
24-hour
LCso = 46
Not reported
Static,
Mortality
Buccafusco
Medium
{Lepomis
macrochirus)
mg AI/L
Nominal
etal., 1981
Bluegill
Fresh
96-hour
LCso = 13
Not reported
Static,
Mortality
Buccafusco
Medium
{Lepomis
macrochirus)
mg AI/L
Nominal
etal., 1981
Bluegill
Fresh
1-21 day
BCF = 49
0.00343 mg AI/L
Flow-
Bioconcentratio
Barrows et
Medium
{Lepomis
macrochirus)
through,
Measured
n
al„ 1978
Fathead
Fresh
32-day
NOAF.L =
Not reported
Flow-
Mortality
Ahmad et
High
minnow
{Pimephales
promelas)
1.4 mg
AI/L
through,
Measured
al„ 1984
Fathead
Fresh
32-day
MATC =
Not reported
Flow-
Growth: Wet
Alunad et
High
minnow
{Pimephales
promelas)
0.5, 1.4
mg AI/L
through,
Measured
weight
al„ 1984
Fathead
Fresh
32-day
NOAF.L =
Not reported
Flow-
Growth: Wet
Alunad et
High
minnow
{Pimephales
promelas)
0.5 mg
AI/L
through,
Measured
weight
al„ 1984
Fathead
Fresh
32-day
LOAEL =
Not reported
Flow-
Growth: Wet
Alunad et
High
minnow
{Pimephales
promelas)
1.4 mg
AI/L
through,
Measured
weight
al„ 1984
Fathead
Fresh
32-day
LCioo =
Not reported
Flow-
Mortality
Alunad et
High
minnow
{Pimephales
promelas)
4.1 mg
AI/L
through,
Measured
al„ 1984
Fathead
Fresh
96-hour
r
p
o
II
Not reported
Flow-
Mortality
Geiger et
High
minnow
{Pimephales
promelas)
13.4 mg
AI/L
through,
Measured
al„ 1985
6
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Fathead
minnow
(Pimephales
promelas)
Fresh
96-hour
LCso =
20.3 mg/L
Not reported
Flow-
through,
Measured
Mortality
Geiger et
al„ 1985
High
Fathead
Fresh
96-hour
LCso =
Not reported
Flow-
Mortality
Broderius
High
minnow
23.8 mg
through,
and Kahl,
(Pimephales
promelas)
AI/L
Not
reported
1985
Fathead
Fresh
96-hour
LCso =
Not reported
Static,
Mortality
Brooke,
High
minnow
10.8 mg
Measured
1987
(Pimephales
promelas)
AI/L
Fathead
Fresh
32-day
LCioo =
Not reported
Flow-
Mortality
De Foe,
Medium
minnow
(Pimephales
promelas)
4.1 mg
AI/L
through,
Measured
1980
rFathead
Fresh
24-hour
LCso =
Not reported
Flow-
Mortality
Alexander
High
minnow
(Pimephales
promelas)
23.5 mg
AI/L
through,
Measured
et al„ 1978
Fathead
Fresh
48-hour
LCso =
Not reported
Flow-
Mortality
Alexander
High
minnow
(Pimephales
promelas)
19.6 mg
AI/L
through,
Measured
et al„ 1978
Fathead
Fresh
72-hour
LCso =
Not reported
Flow-
Mortality
Alexander
High
minnow
(Pimephales
promelas)
18.9 mg
AI/L
through,
Measured
et al„ 1978
Fathead
Fresh
96-hour
LCso =
Not reported
Flow-
Mortality
Alexander
High
minnow
(Pimephales
promelas)
18.4 mg
AI/L
through,
Measured
et al„ 1978
Fathead
Fresh
96-hour
LCso =
Not reported
Static,
Mortality
Alexander
High
minnow
21.4 mg
Nominal
et al„ 1978
(Pimephales
promelas)
AI/L
Fathead
Fresh
24-hour
ECso =
Not reported
Flow-
Immobilization
Alexander
High
minnow
(Pimephales
promelas)
14.4 mg
AI/L
through,
Measured
et al„ 1978
Fathead
Fresh
48-hour
ECso =
Not reported
Flow-
Immobilization
Alexander
High
minnow
(Pimephales
promelas)
14.4 mg
AI/L
through,
Measured
et al„ 1978
Fathead
Fresh
72-hour
ECso =
Not reported
Flow-
Immobilization
Alexander
High
minnow
(Pimephales
promelas)
14.4 mg
AI/L
through,
Measured
et al„ 1978
7
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Fathead
minnow
(Pimephales
promelas)
Fresh
96-hour
ECso =
14.4 mg
AI/L
Not reported
Flow-
through,
Measured
Immobilization
Alexander
et al„ 1978
High
Fathead
minnow
(Pimephales
promelas)
Fresh
96-hour
LCso =
23.8 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Envtl
Research
Laboratory,
1985
High
Flagfish
(Jordanella
floridae)
Fresh
96-hour
LCso =
8.43 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Smith et
al„ 1991
High
Flagfish
(Jordanella
floridae)
Fresh
10-day
LOEC =
3.1 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Smith et
al„ 1991
High
Flagfish
(Jordanella
floridae)
Fresh
28-day
LOEC =
3.69 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Smith et
al„ 1991
High
Flagfish
(Jordanella
floridae)
Fresh
28-day
LOEC
>9.3 mg
AI/L
Not reported
Flow-
through,
Measured
Growth: general
Smith et
al„ 1991
High
Japanese
medaka
(Oryzias
latipes)
Fresh
10-day
LCso = 25
mg AI/L
Not reported
Renewal,
Nominal
Mortality
Schell,
1987
High
Japanese
medaka
(Oryzias
latipes)
Fresh
10-day
LCioo = 40
mg AI/L
Not reported
Renewal,
Nominal
Mortality
Schell,
1987
High
Japanese
medaka
(Oryzias
latipes)
Fresh
10-day
NOEC =
17 mg
AI/L
Not reported
Renewal,
Nominal
Mortality
Schell,
1987
High
Japanese
medaka
(Oryzias
latipes)
Not
reporte
d
96-hour
NOEL =
2.19 mg
AI/L
LOEL =
4.37 mg
AI/L
0, 20, 40, 60, 80
mg/L
Renewal,
Measured
Mortality
Spencer et
al„ 2002
High
Japanese
medaka
(Oryzias
latipes)
Not
reporte
d
96-hour
LC50 =
26.8 mg
AI/L
0, 20, 40, 60, 80
mg/L
Renewal,
Measured
Mortality
Spencer et
al„ 2002
High
Japanese
medaka
(Oryzias
latipes)
Not
reporte
d
96-hour
LC95 =
96.53 mg
AI/L
0, 20, 40, 60, 80
mg/L
Renewal,
Measured
Mortality
Spencer et
al„ 2002
High
Japanese
medaka
(Oryzias
latipes)
Not
reporte
d
<17 days
LOAEL =
1.5 mg
AI/L
0, 1.5,3,6, 12, 25
mg/L
Static,
Nominal
Reproduction:
Hatch
Spencer et
al„ 2002
unacceptable
8
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Japanese
medaka
Fresh
96-hour
LOAEL =
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Japanese
medaka
Fresh
96-hour
LOAEL=
10 mg
0, 10 mg/L
Static,
Nominal
Growth: Weight
Spencer et
al„ 2006
unacceptable
(Orvzias
latipes)
AI/L
Molly
(Poecilia
sphenops)
Not
reporte
d
59-day
LCioo =
0.005 mg
AI/L
Not reported
Renewal,
Nominal
Mortality
Loekle et
al„ 1983
Unacceptable
Sheepshead
minnow
Salt
24-hour
LCso >52
mg AI/L
Not reported
Static,
Nominal
Mortality
Heitmuller
etal., 1981
Unacceptable
(Cvprinodon
variegatus)
Sheepshead
minnow
Salt
48-hour
LCso >52
mg AI/L
Not reported
Static,
Nominal
Mortality
Heitmuller
etal., 1981
Unacceptable
(Cvprinodon
variegatus)
Sheepshead
minnow
Salt
96-hour
LCso =
>29, <52
Not reported
Static,
Nominal
Mortality
Heitmuller
etal., 1981
Unacceptable
(Cvprinodon
variegatus)
mg AI/L
Sheepshead
minnow
Salt
96-hour
NOEC =
29 mg
Not reported
Static,
Nominal
Mortality
Heitmuller
etal., 1981
Unacceptable
(Cvprinodon
variegatus)
AI/L
9
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Sheepshead
minnow
Salt
24-hour
LCioo =
31.63 mg
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
(Cvprinodon
variegatus)
AI/L
Sheepshead
minnow
Salt
24-hour
LCioo =
31.63 mg
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
(Cvprinodon
variegatus)
AI/L
Sheepshead
minnow
Salt
96-hour
LCso = 9.8
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
(Cvprinodon
variegatus)
Inland
silverside
Salt
96-hour
LCso =
28.1 mg
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
(Menidia
bervllina)
AI/L
Aquatic Invertebrates
Water flea
Fresh
48-hour
LCso = 18
Not reported
Static,
Mortality
Richter et
High
(Daphnia
mg AI/L
Measured
al„ 1983
magna)
Water flea
Fresh
48-hour
LCso = 9.1
Not reported
Static,
Mortality
Richter et
High
(Daphnia
mg AI/L
Measured
al„ 1983
magna)
Water flea
Fresh
48-hour
EC5o=8.5
Not reported
Static,
Immobilization
Richter et
High
(Daphnia
mg AI/L
Measured
al„ 1983
magna)
Water flea
Fresh
48-hour
EC5o=7.5
Not reported
Static,
Immobilization
Richter et
High
(Daphnia
mg AI/L
Measured
al„ 1983
magna)
Water flea
Fresh
24-hour
LCso =
Not reported
Static,
Mortality
LeBlanc,
High
(Daphnia
magna)
14.4 mg
AI/L
Nominal
1980
Water flea
Fresh
48-hour
LCso =
Not reported
Static,
Mortality
LeBlanc,
High
(Daphnia
magna)
14.4 mg
AI/L
Nominal
1980
Water flea
Fresh
48-hour
NOEC = 8
Not reported
Static,
Mortality
LeBlanc,
High
(Daphnia
mg AI/L
Nominal
1980
magna)
Water flea
Fresh
28-day
NOEC =
Not reported
Renewal,
Growth: Length
Call et al„
High
(Daphnia
magna)
0.505 mg
AI/L
Measured
1980
Water flea
(Daphnia
magna)
Fresh
28-day
NOEC =
0.505 mg
AI/L
Not reported
Renewal,
Measured
Reproduction:
Reproductive
success
(general)
Call et al„
1980
High
Water flea
Fresh
48-hour
LCso =
Not reported
Static,
Mortality
Call et al„
High
(Daphnia
magna)
18.1 mg
AI/L
Measured
1980
Water flea
Fresh
48-hour
ECso = 8.5
Not reported
Static,
Immobilization
Call et al„
High
(Daphnia
mg AI/L
Measured
1980
magna)
10
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Water flea
(Daphnia
magna)
Fresh
48-hour
LCso =
9.09 mg
AI/L
Not reported
Static,
Measured
Mortality
Call et al„
1980
High
Water flea
Fresh
48-hour
ECso =
Not reported
Static,
Immobilization
Call et al„
High
(Daphnia
magna)
7.49 mg
AI/L
Measured
1980
Water flea
Fresh
2-day
LCso =
0,0.17, 0.33,0.66,
Renewal,
Mortality
Niederlehn
High
{Ceriodaphnia
dubia)
2.48751
mg AI/L
0.99, 1.5 mg/L
Measured
eret al.,
1998
Water flea
Fresh
7-day
LCso =
0,0.17, 0.33,0.66,
Renewal,
Mortality
Niederlehn
High
{Ceriodaphnia
dubia)
0.82917
mg AI/L
0.99, 1.5 mg/L
Measured
er et al.,
1998
Water flea
Fresh
7-day
NOEL =
0,0.17, 0.33,0.66,
Renewal,
Reproduction:
Niederlehn
High
('Ceriodaphnia
dubia)
0.331668
mg AI/L
LOEL =
0.663336
mg AI/L
0.99, 1.5 mg/L
Measured
Progeny
counts/numbers
er et al.,
1998
Water flea
Fresh
7-day
IC50 =
0,0.17, 0.33,0.66,
Renewal,
Reproduction:
Niederlehn
High
{Ceriodaphnia
dubia)
0.663336
mg AI/L
0.99, 1.5 mg/L
Measured
Progeny
counts/numbers
er et al.,
1998
Brine shrimp
{Artemia
Salt
24-hour
LCso =
23.21676
Not reported
Aquatic-
not
Mortality
Sanchez-
Fortun et
Low
salina)
mg AI/L
reported.
Nominal
al., 1997
Brine shrimp
{Artemia
Salt
24-hour
LCso =
6.63336
Not reported
Aquatic-
not
Mortality
Sanchez-
Fortun et
Low
salina)
mg AI/L
reported.
Nominal
al., 1997
Brine shrimp
{Artemia
Salt
24-hour
LCso =
0.331668
Not reported
Aquatic-
not
Mortality
Sanchez-
Fortun et
Low
salina)
mg AI/L
reported.
Nominal
al., 1997
Opossum
shrimp
{Americamysis
bahia)
Salt
96-hour
LC50 =
2.85 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Hollister et
al., 1968
High
Opossum
shrimp
{Americamysis
bahia)
Salt
6-day
NOAF.L =
1.4 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Hollister et
al., 1968
High
Opossum
shrimp
{Americamysis
bahia)
Salt
7-day
LOAEL =
1.4 mg
AI/L
Not reported
Flow-
through,
Measured
Mortality
Hollister et
al., 1968
High
Opossum
shrimp
{Americamysis
bahia)
Salt
28-day
NOAF.L =
0.37 mg
AI/L,
LOAEL=
0.67 ppm
Not reported
Flow-
through,
Measured
Mortality
Hollister et
al., 1968
High
11
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Opossum
shrimp
(Americamvsis
bahia)
Salt
28-day
NOAF.L =
1.39 mg
AI/L
Not reported
Flow-
through,
Measured
Reproduction:
progeny counts/
numbers
Hollister et
al„ 1968
High
Opossum
shrimp
(Americamvsis
bahia)
Salt
28-day
MATC =
>0.3,
<0.67 mg
AI/L
Not reported
Flow-
through,
Measured
Endpoint
reported
without a
specific effect
Hollister et
al„ 1968
High
Scud
(Gammarus
minus)
Fresh
24-hour
LCioo= 60
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Scud
('Gammarus
minus)
Fresh
96-hour
LCo =
21.6 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Stonefly
(Tallaperia
maria)
Fresh
96-hour
LCso = 3.6
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Pond snail,
pneumonate
snail (Phvsa
heterostropha)
Fresh
96-hour
LCso =
93.4 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Scud
(Gammarus
minus)
Fresh
96-hour
LCso =
28.6 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Scud
(Gammarus
annulatus)
Salt
24-hour
LCioo = 21
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Scud
(Gammarus
annulatus)
Salt
24-hour
LCioo =
24.7 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Scud
(Gammarus
annulatus)
Salt
96-hour
LCso = 9.1
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Daggerblade
grass shrimp
(Palaemonetes
pugio)
Salt
24-hour
LCo = 2.5
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Daggerblade
grass shrimp
(Palaemonetes
pugio)
Salt
24-hour
LCo = 2.5
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Daggerblade
grass shrimp
(Palaemonetes
pugio)
Salt
24-hour
LCioo =
18.85 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Calanoid
copepod
(Acartia tonsa)
Salt
96-hour
LCso =
13.2 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
12
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Bay shrimp,
sand shrimp
(Cragnon
septemspinosa
)
Salt
96-hour
LCso =
17.4 mg
AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Daggerblade
grass shrimp
(Palaemonetes
pugio)
Salt
96-hour
LCso= 1.3
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Polychaete
wo mi
(Neanthes
arenaceodenta
ta)
Salt
96-hour
LCso= 1.3
mg AI/L
Not reported
Static,
Nominal
Mortality
Home et
al„ 1983
High
Flatworm
(Dugesia
japonica)
Fresh
7-day
LCso= 1.4
mg AI/L
Not reported
Renewal,
Nominal
Mortality
Yosliioka et
al„ 1986
Low
Flatworm
(Dugesia
japonica)
Fresh
7-day
ECso = 0.9
mg AI/L
Not reported
Renewal,
Nominal
Limb/body part
regeneration
Yosliioka et
al„ 1986
Low
Ciliate
(Tetrahymena
pvriformis)
Not
reporte
d
24-hour
ECso =
100 mg
AI/L
Not reported
Static,
Nominal
Population
growth rate
Yosliioka et
al„ 1985
Unacceptable
Midge
(Tany tarsus
dissimilis)
Fresh
24-hour
LCso =
54.6 mg
AI/L
Not reported
Static,
Measured
Mortality
Call et al„
1983
High
Midge
(Tany tarsus
dissimilis)
Fresh
48-hour
LCso =
30.8 mg
AI/L
Not reported
Static,
Measured
Mortality
Call et al„
1983
High
Midge
(Tany tarsus
dissimilis)
Fresh
48-hour
ECso = 7
mg AI/L
Not reported
Aquatic-
not
reported.
Nominal
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>0, <10-
hour
LCso =
>60, <80
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>0, <10-
hour
LCso =
>60, <80
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>0, <10-
hour
LCso =
~60 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>10,
<20-hour
LCso =
~60 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
13
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Midge
(Tany tarsus
dissimilis)
Fresh
>20,
<30-hour
LCso =
>40, <60
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>20,
<30-hour
LCso =
>40, <60
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>30-,
<40-hour
LCso =
>40, <60
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>30-,
<40-hour
LCso =
>20, <40
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>30-,
<40-hour
ECso = >0,
<20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>30-,
<40-hour
ECso = >0,
<20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>20,
<30-hour
ECso = >0,
<20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>20,
<30-hour
ECso = >0,
<20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>10,
<20-hour
ECso = >0,
<20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>10,
<20-hour
ECso = >0,
<20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>0, <10-
hour
ECso =
~20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
>0, <10-
hour
ECso =
~20 mg
AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al.,
1979
High
14
-------
INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Midge
(Tany tarsus
dissimilis)
Fresh
>0, <10-
hour
ECso =
>20, <40
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
9-hour
LCioo =
101.8
mg/AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
<10 hour
LCso =
>60, <80
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Mortality
Call et al„
1979
High
Midge
(Tany tarsus
dissimilis)
Fresh
<10 hour
ECso =
>20, <40
mg AI/L
Not reported
Aquatic-
not
reported.
Measured
Equilibrium
Call et al„
1979
High
Algae
Green algae
(Chlamvdomo
nas
reinhardtii)
Fresh
2-hour
EC20 = 8.1
mg AI/L
Not reported
Static,
Nominal
Fluorescence
Brack and
Frank,
1980
Unacceptable
Green algae
(Chlamvdomo
nas
reinhardtii)
Fresh
72-hour
ECso =
3.64 mg
AI/L
Not reported
Static,
Nominal
Biomass
Brack and
Rottler,
1994
High
Green algae
(Chlamvdomo
nas
reinhardtii)
Fresh
72-hour
EC10 =
1.77 mg
AI/L
Not reported
Static,
Nominal
Biomass
Brack and
Rottler,
1994
High
Green algae
(Pseudokirchn
eriella
subcapitata)
Fresh
48-hour
ECso =
10.54 mg
AI/L
Not reported
Static,
Nominal
Population
growth rate
Tsai and
Chen, 2007
High
Green algae
(Pseudokirchn
eriella
subcapitata)
Fresh
24-hour
NOAF.L =
0.01 mg
AI/L
LOAEL =
0.02 mg
AI/L
0, 0.01, 0.02, 0.05,
0.2, 0.5 mg/L
Static,
Nominal
Abundance
Labra et al.,
2010
Medium
Green algae
(Pseudokirchn
eriella
subcapitata)
Fresh
48-hour
NOAF.L =
0.01 mg
AI/L
LOAEL=
0.02 mg
AI/L
0, 0.01, 0.02, 0.05,
0.2, 0.5 mg/L
Static,
Nominal
Abundance
Labra et al.,
2010
Medium
Green algae
(Pseudokirchn
eriella
subcapitata)
Fresh
72-hour
NOAF.L =
0.01 mg
AI/L
LOAEL=
0.02 mg
AI/L
0, 0.01, 0.02, 0.05,
0.2, 0.5 mg/L
Static,
Nominal
Abundance
Labra et al.,
2010
Medium
15
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INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies
that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Green algae
Fresh
72-hour
NOAEL =
0, 0.01, 0.02, 0.05,
Static,
Damage
Labra et al..
Medium
(Pseudokirchn
eriella
0.02 mg
AI/L
0.2, 0.5 mg/L
Nominal
2010
subcapitatd)
LOAEL =
0.05 mg
AI/L
Green algae
Fresh
48-hour
NOAEL=
0, 0.01, 0.02, 0.05,
Static,
Damage
Labra et al..
Medium
(Pseudokirchn
eriella
0.02 mg
AI/L
0.2, 0.5 mg/L
Nominal
2010
subcapitatd)
LOAEL=
0.05 mg
AI/L
Green algae
Fresh
24-hour
NOAEL=
0, 0.01, 0.02, 0.05,
Static,
Damage
Labra et al..
Medium
(Pseudokirchn
eriella
0.02 mg
AI/L
0.2, 0.5 mg/L
Nominal
2010
subcapitatd)
LOAEL=
0.05 mg
AI/L
Blue-green
Fresh
24-hour
LOAEL=
0, 23 |iL
Static,
Peroxidase
Bacsi et al..
Unacceptable
algae
(Synechococcu
s elongatus)
23 |iL
Nominal
activity
2013
Blue-green
Fresh
24-hour
LOAEL=
0, 23 |iL
Static,
Abundance
Bacsi et al..
Unacceptable
algae
23 |iL
Nominal
2013
(Synechococcu
s elongatus)
Blue-green
Fresh
4-hour
LOAEL=
0, 23 |iL
Static,
Chlorophyll A
Bacsi et al..
Unacceptable
algae
23 |iL
Nominal
concentration
2013
(Synechococcu
s elongatus)
Blue-green
Fresh
24-hour
NOAEL=
0, 23 |iL
Static,
Chlorophyll A
Bacsi et al..
Unacceptable
algae
23 |iL
Nominal
concentration
2013
(Synechococcu
s elongatus)
Blue-green
Fresh
4-hour
NOAEL=
0, 23 |iL
Static,
Peroxidase
Bacsi et al..
Unacceptable
algae
(Synechococcu
s elongatus)
23 |iL
Nominal
activity
2013
Blue-green
Fresh
8-hour
LOAEL=
0, 23 |iL
Static,
Peroxidase
Bacsi et al..
Unacceptable
algae
(Synechococcu
s elongatus)
23 |iL
Nominal
activity
2013
Blue-green
Fresh
12-hour
LOAEL=
0, 23 |iL
Static,
Peroxidase
Bacsi et al..
Unacceptable
algae
(Synechococcu
s elongatus)
23 |iL
Nominal
activity
2013
Blue-green
Fresh
24-hour
LOAEL=
0, 23 |iL
Static,
Thiobarbituric
Bacsi et al..
Unacceptable
algae
23 |iL
Nominal
acid reactive
2013
(Synechococcu
s elongatus)
substances
16
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INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Blue-green
algae
{Synechococcu
s elongatus)
Fresh
12-hour
LOAEL =
23 |iL
0, 23 |iL
Static,
Nominal
Thiobarbituric
acid reactive
substances
Bacsi et al.,
2013
Unacceptable
Blue-green
algae
{Synechococcu
s elongatus)
Fresh
8-hour
LOAEL=
23 |iL
0, 23 |iL
Static,
Nominal
Thiobarbituric
acid reactive
substances
Bacsi et al.,
2013
Unacceptable
Blue-green
algae
{Synechococcu
s elongatus)
Fresh
4-hour
LOAEL=
23 |iL
0, 23 |iL
Static,
Nominal
Thiobarbituric
acid reactive
substances
Bacsi et al.,
2013
Unacceptable
Algae (not
reported)
Fresh
24-hour
LOAEL=
92 uL
0, 0, 92 |iL
Lentic,
Nominal
Abundance
Bacsi et al.,
2013
Unacceptable
Algae (not
reported)
Fresh
48-hour
LOAEL=
92 uL
0, 0, 92 |iL
Lentic,
Nominal
Abundance
Bacsi et al.,
2013
Unacceptable
Algae (not
reported)
Fresh
72-hour
LOAEL=
92 uL
0, 0, 92 |iL
Lentic,
Nominal
Chlorophyll A
concentration
Bacsi et al.,
2013
Unacceptable
Algae (not
reported)
Fresh
48-hour
LOAEL=
92 |iL
0, 0, 92 |iL
Lentic,
Nominal
Thiobarbituric
acid reactive
substances
Bacsi et al.,
2013
Unacceptable
Algae (not
reported)
Fresh
1-day
LOAEL=
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Chlorophyll A
concentration
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
2-day
LOAEL=
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Chlorophyll A
concentration
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
3-day
NOAF.L =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Chlorophyll A
concentration
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
3-day
NOAF.L =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Abundance
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
2-day
NOAF.L =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Abundance
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
1-day
LOAEL=
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Abundance
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
1-day
LOAEL=
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Diversity,
evenness
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
2-day
LOAEL=
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Diversity,
evenness
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
3-day
NOAF.L =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Diversity,
evenness
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
1-day
LOAEL=
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Chlorophyll A
concentration
Bacsi et al.,
2015
Unacceptable
17
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INTERAGENCY DRAFT. DO NOT CITE OR QUOTE
Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene
Test Species
Fresh/
Salt
Water
Duration
End-point
Concentration(s)
Test
Analysis
Effect(s)
References
Data Quality
Evaluation
Algae (not
reported)
Fresh
2-day
LOAEL =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Abundance
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
3-day
NOAF.L =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Abundance
Bacsi et al.,
2015
Unacceptable
Algae (not
reported)
Fresh
3-day
NOAF.L =
150 mg
AI/L
0, 150 mg/L
Lentic,
Nominal
Diversity,
Evenness
Bacsi et al.,
2015
Unacceptable
Amphibians
Wood frog
(Lithobates
svlvaticus)
Fresh
96-hour
ECso = 7.8
mg AI/L
0,2.5, 7.5, 12.5,
20, 30, 45 mg/L
Renewal,
Measured
Deformation
McDaniel
et al., 2004
High
Bronze frog
(Lithobates
clamitans ssp.
Clamitans)
Fresh
96-hour
ECso = 7.9
mg AI/L
0,2.5, 7.5, 12.5,
20, 30, 45 mg/L
Renewal,
Measured
Deformation
McDaniel
et al., 2004
High
American toad
(Bufo
americanus)
Fresh
96-hour
ECso >45
mg AI/L
0,2.5, 7.5, 12.5,
20, 30, 45 mg/L
Renewal,
Nominal
Deformation
McDaniel
et al., 2004
High
Spotted
salamander
(Ambvstoma
maculatum)
Fresh
96-hour
ECso =
14.5 mg
AI/L
0,2.5, 7.5, 12.5,
20, 30, 45 mg/L
Renewal,
Measured
Deformation
McDaniel
et al., 2004
Medium
Fungi
Fungi
(Aspergillus
versicolor)
Fresh
~30-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
Fungi
(Aspergillus
cejpii)
Fresh
~20-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
Fungi
(Coniothrium
sp.)
Fresh
~30-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
Fungi
(Acremonium
tubakii)
Fresh
~30-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
Fungi Class:
Basidiomycete
s
Fresh
~20-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
Fungi Class:,
Basidiomycete
s
Fresh
~10-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
Fungi (Phoma
putaminum)
Fresh
~30-hour
LTso =
1,900 mg
AI/L
0, 1,900 mg/L
Static, Not
reported
Mortality
Steiman et
al., 1995
Low
18
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