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 DO NOT CITE OR QUOTE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 DO NOT CITE OR QUOTE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


-------
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


-------
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


-------
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


-------
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


-------
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


-------
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


-------