Annex B Derivation of Toxicity Reference Value for Aquatic Life
TRVs of Contaminants of Potential Concern (COPC) for aquatic life were evaluated to determine the Concentration of Interest (COI) for COC selection and the risk calculation for COCs. TRVs were derived from the following sources of toxicity values, listed in order of preference:
· Toxicity values developed and/or adopted by regulatory agencies; generally provided in the form of standards, criteria, guidance or benchmarks
· Toxicity values published in scientific literature
Water quality criteria/standards of the USA (federal and state level), the United Kingdom, Canada, Australia, China and Hong Kong were reviewed. Criteria/standards for some COCs were not identified. For the COCs with available criteria/standards, the following rules were adopted to derive the TRV:
· Rule 1: Criteria from Hong Kong are adopted when available and suitable
· Rule 2: Criteria/standards for protection of marine water/saltwater biota are preferred to that of freshwater or that without clear specification (e.g. protection of aquatic environment)
· Rule 3: Chronic criteria/standards specified with averaging time period are preferred and adopted whenever possible. For chronic criteria/standards without specified averaging time, annual averaging time is adopted
· Rule 4: National criteria/standards are preferred to local criteria/standards
· Rule 5: If more than one criteria/standards for the same COC meet the above criteria, criterion/standard with the lower value would be adopted to provide conservatism
The identified relevant criteria/standards were presented in Table 1; the adopted values based on the above rules were typed in bold.
Table 1 Water Quality Criteria/Standards
|
|
US Nationala |
US Statesb |
Australiac |
Canadad |
UKe |
Chinaf |
Hong Kongg |
|
TRC |
7.5 (saltwater, 4-day average) |
Criteria search not needed |
3 (freshwater, protection level to 95% species) |
N/A |
N/A |
N/A |
8 (at edge of mixing zone, daily max.) 13 (at edge of ZID, daily max.) |
|
Bromodichloromethane |
N/A |
22 (marine water, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
Bromoform |
N/A |
360 (marine water, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
Chloroform |
N/A |
470.8 (marine water, annual avg.), Florida |
N/A |
1.8 (freshwater) |
12 (marine water, annual avg.) |
N/A |
N/A |
|
Dibromochloromethane |
N/A |
34 (marine water, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
Bromoacetic acid |
N/A |
||||||
|
Chloroacetic acid |
N/A |
||||||
|
Dibromoacetic acid |
N/A |
||||||
|
Dichloroacetic acid |
N/A |
||||||
|
Trichloroacetic acid |
N/A |
||||||
|
Methylene chloride |
N/A |
1,580 (marine water, annual avg.), Florida |
N/A |
98.1 (freshwater) |
N/A |
N/A |
N/A |
|
Carbon tetrachloride |
N/A |
Criteria search not needed |
N/A |
N/A |
12 (marine, annual avg.) |
N/A |
N/A |
|
Chlorobenzene |
N/A |
Criteria search not needed |
N/A |
25 (marine water) |
N/A |
N/A |
N/A |
|
1,1-dichloroethane |
N/A |
||||||
|
1,2-dichloroethane |
N/A |
Criteria search not needed |
N/A |
N/A |
10 (marine, annual avg.) |
N/A |
N/A |
|
|
US Nationala |
US Statesb |
Australiac |
Canadad |
UKe |
Chinaf |
Hong Kongg |
|
1,1-dichloroethylene |
N/A |
3.2 (marine, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
1,2-dichloropropane |
N/A |
||||||
|
Tetrachloroethylene |
N/A |
8.85 (marine, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
1,1,1-trichloroethane |
N/A |
Criteria search not needed |
N/A |
N/A |
100 (marine annual avg.) |
N/A |
N/A |
|
1,1,2-trichloroethane |
N/A |
Criteria search not needed |
1,900 (marine water) |
N/A |
100 (marine annual avg.) |
N/A |
N/A |
|
Trichloroethylene |
N/A |
Criteria search not needed |
N/A |
N/A |
10 (marine annual avg.) |
N/A |
N/A |
|
2-chlorophenol |
N/A |
Criteria search not needed |
N/A |
N/A |
50 (marine annual avg.) |
N/A |
N/A |
|
2,4-dichlorophenol |
N/A |
Criteria search not needed |
N/A |
N/A |
20 (marine annual avg.) |
N/A |
N/A |
|
p-chloro-m-cresol |
N/A |
Criteria search not needed |
N/A |
N/A |
40 (marine annual avg.) |
N/A |
N/A |
|
Pentachlorophenol |
7.9 (marine water, 4-day avg.) |
Criteria search not needed |
22 (marine water) |
N/A |
N/A |
N/A |
N/A |
|
2,4,6-trichlorophenol |
N/A |
||||||
|
Bis(2-chloroethoxy)methane |
N/A |
||||||
|
1,4-dichlorobenzene |
N/A |
||||||
|
Hexachlorobenzene |
N/A |
Criteria search not needed |
N/A |
N/A |
0.03 (marine, annual avg.) |
N/A |
N/A |
|
Hexachlorocyclopentadiene |
N/A |
||||||
|
Hexachloroethane |
N/A |
||||||
|
1,2,4-trichlorobenzene |
N/A |
Criteria search not needed |
80 (marine water) |
5.4 (marine water) |
N/A |
N/A |
N/A |
|
Alpha-BHC |
N/A |
||||||
|
|
US Nationala |
US Statesb |
Australiac |
Canadad |
EUe |
Chinaf |
Hong Kongg |
|
Beta-BHC |
N/A |
0.046 (marine, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
Gamma-BHC |
N/A |
0.063 (marine, annual avg.), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
Aluminium |
87 (freshwater, 4-day average) |
1,500 (marine water), Florida |
55 (freshwater) |
5-100 (freshwater) |
N/A |
N/A |
N/A |
|
Antimony |
N/A |
4,300 (marine water), Florida |
N/A |
N/A |
N/A |
N/A |
N/A |
|
Barium |
N/A |
||||||
|
Chromium (III) |
74 (freshwater water, 4-day average) |
Criteria search not needed |
27.4 (marine water) |
56 (marine water) |
15 (marine water, annual avg.), in terms of total chromium |
N/A |
50 (at least 90% occasion), in terms of total chromium |
|
Copper |
3.1 (marine water, 4-day avg.) |
Criteria search not needed |
1.3 (marine water) |
2-4 (freshwater) |
5 (marine water, annual avg.) |
N/A |
5 (at least 90% occasion) |
|
Lead |
8.1 (marine water, 4-day avg.) |
Criteria search not needed |
N/A |
1-7 (freshwater) |
25 (marine, annual avg.) |
N/A |
N/A |
|
Nickel |
8.2 (marine water, 4-day avg.) |
Criteria search not needed |
70 (marine water) |
25-150 (freshwater) |
30 (marine, annual avg.) |
N/A |
5 (at least 90% occasion) |
|
Selenium |
71 (marine water, 4-day avg.) |
Criteria search not needed |
1 (freshwater) |
11 (freshwater) |
N/A |
N/A |
N/A |
|
Silver |
N/A |
Criteria search not needed |
1.4 (marine water) |
1 (freshwater) |
N/A |
N/A |
N/A |
|
Tin |
N/A |
||||||
|
Vanadium |
N/A |
Criteria search not needed |
N/A |
100 (marine water) |
100 (marine, annual avg.) |
N/A |
N/A |
|
Zinc |
81 (marine water, 4-day average) |
Criteria search not needed |
15 (marine water) |
30 (freshwater) |
40 (marine, annual avg.) |
N/A |
20 (at least 90% of occasions) |
|
Ammonia, total |
pH and Temp. dependent |
Criteria search not needed |
910 (marine water) |
N/A |
N/A |
N/A |
N/A |
|
Sulphideh |
2 (marine water, 4-day average) – hydrogen sulfide |
Criteria search not needed |
1 (freshwater) – in terms of hydrogen sulfide |
N/A |
N/A |
N/A |
20 (at least 90% of occasions) |
|
Dioxins and Furans (TEQ) |
N/A |
||||||
|
Toluene |
N/A |
Criteria search not needed |
0.05 (freshwater) |
N/A |
40 (marine, annual average) |
N/A |
N/A |
|
Diazinon |
N/A |
Criteria search not needed |
0.01 (freshwater) |
N/A |
N/A |
N/A |
N/A |
|
Malathion |
0.1 (marine water, 4-day avg.) |
Criteria search not needed |
0.05 (freshwater) |
N/A |
0.02 (marine, annual average) |
N/A |
N/A |
Note: N/A = Not Available; all concentration units in µg/L; bolded values were adopted as TRV.
a USEPA (2004).
b USEPA. www.epa.gov/waterscience/standards/states
c ANZECC (2000).
d CCME (2005).
e WRc Swindon (1999).
f PRC National Guideline – Environmental Quality Standards for Surface Water.
g CDM (2002).
h According to CDM (2002), using the TRV based on the criterion of 20mg/L would overestimate the risks to aquatic biota. Therefore, the criterion for sulphide was not adopted to derive TRV.
For COPCs without relevant criteria/standards adopted by agencies, TRVs were derived from toxicity data in scientific literature, based on the guidance provided by USEPA (1999b). ECOTOX database maintained by USEPA and OECD Screening Information DataSet (SIDS) by ICPS INCHEM were reviewed for toxicity data of HAAs on aquatic life, which are summarized at the end of this Annex.
The ECOTOX database is a source for locating single chemical toxicity data from three USEPA ecological effects databases: AQUIRE, TERRETOX and PHYTOTOX. Relevant literature for ECOTOX is retrieved using a comprehensive search strategy to locate worldwide aquatic and terrestrial ecological effects literature. The majority of literature reviewed for ECOTOX is from 1972 through to present, which literature acquisition, data entry and data abstraction are continually conducted by USEPA who maintains the database. In the ECOTOX database, all the available toxicity data of a particular chemicals in the database can be retrieved by performing query, which is conducted by entering the chemical name or CAS number of the chemicals.
According to USEPA (1999b), the following rules are adopted to derive COC-specific TRV from the toxicity data:
l Rule 1: Toxicity data shall be ecologically relevant to the Study
o Biota of concern: toxicity data for saltwater species is preferred to freshwater species
o Ecological endpoint: ecologically relevant endpoint such as growth, reproduction and survival shall be used
l Rule 2: The following hierarchy, in terms of decreasing preference, shall be followed for the exposure duration and study endpoint selection:
o Chronic NOEC (No Observable Effect Concentration)
o Subchronic NOEC
o Chronic LOEC (Lowest Observed Effect Concentration)
o Subchronic LOEC
o Acute median lethality point estimate (LC50)
o Single dose toxicity value
l Rule 3: Uncertainty Factor (UF) shall be applied to convert toxicity test endpoint to TRV (which is equivalent to a chronic NOEC), if the toxicity test endpoint is not a chronic NOEC
o Chronic LOEC should be multiplied by a UF of 0.1
o Subchronic LOEC should be multiplied by a UF of 0.1
o Acute lethal value (such as LC50) should be multiplied by an UF of 0.01
The following guidelines were adopted to generally determine exposure duration:
l For fish:
o A chronic test lasts for more than 90 days
o A subchronic test lasts from 14 to 90 days
o An acute test lasts less than 14 days
l For other marine organisms:
o A chronic test lasts for 7 or more days
o A subchronic test lasts from 3 to 6 days
o An acute test lasts less than 3 days
The derived TRVs for COCs without relevant criteria/standards are presented in Table 2.
Table 2 Toxicity Reference Values Derived
|
COC |
Toxicity Data Adopted |
UF Used |
TRV Derived |
|
Bromoacetic acid |
1.6mg/L, chronic NOEC for water flea |
- |
1.6mg/L |
|
Dibromoacetic acid |
69.0mg/L, acute LC50 for fish |
0.01 |
0.69mg/L |
|
Chloroacetic acid |
32.0 mg/L, chronic NOEC for water flea |
- |
32.0mg/L |
|
Dichloroacetic acid |
23.0mg/L, subchronic LC50 for copecod (an invertebrate) |
0.01a |
0.23mg/L |
|
Trichloroacetic acid |
9300.0mg/L, acute LC50 for fish |
0.01 |
93.0mg/L |
|
Chlorobenzene |
8.9mg/L, acute LC50 for fish |
0.01 |
0.089mg/L |
|
1,1-dichloroethane |
No toxicity data available |
||
|
1,2-dichloropropane |
61mg/L, acute LC50 for fish |
0.01 |
0.61mg/L |
|
2,4,6-trichlorophenol |
1.21mg/L, subchronic LC50 for shrimp |
0.01a |
0.0121mg/L |
|
Bis(2-chloroethoxy)methane |
184mg/L, acute LC50 for fish |
0.01 |
1.84mg/L |
|
1,4-dichlorobenzene |
7.4mg/L, acute LC50 for fish |
0.01 |
0.074mg/L |
|
Hexachlorocyclopentadiene |
0.009mg/L, chronic NOEC for water flea |
- |
0.009mg/L |
|
Hexachloroethane |
2.4mg/L, acute LC50 for fish |
0.01 |
0.024mg/L |
|
1,2,4-trichlorobenzene |
0.09mg/L, subchronic LC50 for shrimp |
0.01a |
0.0009mg/L |
|
Alpha-BHC |
0.5mg/L, subchronic LC50 for shrimp |
0.01a |
0.005mg/L |
|
Barium |
500mg/L, acute LC50 for fish |
0.01 |
5mg/L |
|
Tin |
8.16mg/L, subchronic LC50 for fish |
0.01 |
0.0816mg/L |
|
Sulphide |
10mg/L, subchronic EC50 for algae |
0.01 |
0.1mg/L |
|
2,3,7,8-TCDD |
3.8E-8mg/L, chronic NOEC for fish |
- |
3.8E-8mg/L |
a No recommended UF factor to convert subchronic lethal level to chronic NOEC; the adopted UF of 0.01 was considered to be conservative.
Toxicity Data Reviewed
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
Bromoacetic acid |
||||||
|
Daphnia magna |
FW |
R |
24hr |
EC0 (ability to maintain balance) |
34 |
ECOTOX
|
|
Daphnia magna |
FW |
R |
24hr |
EC50 (ability to maintain balance) |
65 |
|
|
Daphnia magna |
FW |
R |
21d |
NOEC (ability to maintain balance) |
3.2 |
|
|
Daphnia magna |
FW |
S |
24hr |
EC50 (immobile) |
65.0 |
|
|
Daphnia magna |
FW |
R |
21d |
NOEC (reproduction) |
1.6 |
|
|
Scenedesmus subspicatus |
FW |
S |
48hr |
EC50 (biomass) |
0.34 |
|
|
Scenedesmus subspicatus |
FW |
S |
72hr |
EC50 (biomass) |
0.2 |
|
|
Scenedesmus subspicatus |
FW |
S |
96hr |
EC50 (biomass) |
0.22 |
|
|
Scenedesmus subspicatus |
FW |
S |
48hr |
EC50 (population change) |
2.3 |
|
|
Scenedesmus subspicatus |
FW |
S |
72hr |
EC50 (population change) |
1.4 |
|
|
Tinca tinca |
FW |
NR |
96hr |
LC50 |
3420.0 |
|
Note: Bolded value was used to derive
toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
Dibromoacetic acid |
||||||
|
Pimephales promelas |
FW |
S |
24hr |
LC50 |
160.0 |
ECOTOX |
|
Pimephales promelas |
FW |
S |
48hr |
LC50 |
107.0 |
|
|
Pimephales promelas |
FW |
S |
72hr |
LC50 |
81.0 |
|
|
Pimephales promelas |
FW |
S |
96hr |
LC50 |
69.0 |
|
Note: Bolded value was used to derive
toxicity reference value
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
Chloroacetic acid |
||||||
|
Daphnia magna |
FW |
S |
24hr |
EC50 (ability to maintain balance) |
79 |
ECOTOX |
|
Scenedesmus subspicatus |
FW |
S |
7d |
EC03 (proliferation) |
0.13 |
|
|
Brachionus calyciflorus |
FW |
S |
48hr |
EC50 (progeny) |
68.9 |
|
|
Brachionus calyciflorus |
FW |
S |
48hr |
NOEC (progeny) |
40 |
|
|
Daphnia magna |
FW |
S |
24hr |
EC50 (immobile) |
99.0 |
|
|
Daphnia magna |
FW |
S |
48hr |
EC50 (immobile) |
77.0 |
|
|
Daphnia magna |
FW |
R |
21d |
NOEC (reproduction) |
32.0 |
|
|
Scenedesmus subspicatus |
FW |
S |
48hr |
EC50 (biomass) |
0.028 |
|
|
Scenedesmus subspicatus |
FW |
S |
48hr |
EC50 (population change) |
0.07 |
|
|
Pimephales promelas |
FW |
R |
96hr |
LC50 |
145 |
OECD SIDS
|
|
Brachydanio rerio (Zebra Fish) |
FW |
S |
96hr |
LC50 |
370 |
|
|
Poecillia reticulata (Guppy, fish) |
FW |
S |
96hr |
LC50 |
369 |
|
|
Scenedesmus quadricauda (Green algae) |
FW |
NR |
8d |
EC3 (biomass) |
0.13 |
|
|
Scenedesmus quadricauda (Green algae) |
FW |
NR |
48hr |
EC10 (biomass) |
0.007 |
|
|
Branchydanio reiro (Zebrafish) |
FW |
R |
12d |
NOEC (egg and fish development) |
320 |
|
Note: Bolded value was used to derive
toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
Dichloroacetic acid |
||||||
|
Daphnia magna |
FW |
S |
24hr |
EC50 (ability to maintain ability) |
106 |
ECOTOX |
|
Scenedesmus subspicatus |
FW |
S |
7d |
EC03 (proliferation) |
1485 |
|
|
Nitocra spinipes |
SW |
S |
96hr |
LC50 |
23.0 |
|
Note: Bolded value was used to derive
toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Trichloracetic acid |
||||||
|
Daphnia magna |
FW |
NR |
24hr |
EC0 (ability to maintain balance) |
2500 |
ECOTOX
|
|
Daphnia magna |
FW |
NR |
24hr |
EC50 (ability to maintain balance) |
8370 |
|
|
Leuciscus idus melanotus |
FW |
NR |
48hr |
LC50 |
>10000 |
|
|
Alburnus alburnus |
SW |
S |
96hr |
LC50 |
9300.0 |
|
|
Carassius sp. |
FW |
NR |
96hr |
LC50 |
3420.0 |
|
|
Cyprinus carpio (Carp, fish) |
FW |
NR |
96hr |
LC50 |
2500.0 |
|
|
Daphnia magna |
FW |
S |
24hr |
EC50 (immobile) |
164.0 |
|
|
Daphnia magna |
FW |
S |
48hr |
EC50 (immobile) |
146.0 |
|
|
Daphnia magna |
FW |
NR |
96hr |
LC50 |
3100.0 |
|
|
Nitocra spinipes |
SW |
S |
96hr |
LC50 |
4800 |
|
|
Pimephales promelas |
FW |
S |
96hr |
LC50 |
2000.0 |
|
|
Salmonidae |
FW |
NR |
96hr |
LC50 |
1050.0 |
|
|
Streptocephalus proboscideus |
FW |
S |
24hr |
LC50 |
1.2 |
|
|
Tinca tinca |
FW |
NR |
96hr |
LC50 |
3420.0 |
|
Note: Bolded value was used to derive
toxicity reference value
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Carassius auratus |
FW |
S |
24 h |
LC50 |
73.03 |
ECOTOX |
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
S |
48 h |
LC50 |
56 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
S |
96 h |
LC50 |
51.62 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
84 h |
LC50 |
4.38 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
7.5 d |
LC50 |
0.88 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
84 h |
LC50 |
4.08 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
7.5 d |
LC50 |
1.04 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
96 h |
LC50 |
3.48 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
8 d |
LC50 |
0.88 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
96 h |
LC50 |
2.37 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
8 d |
LC50 |
1.04 |
|
|
(Goldfish) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
R |
7 - 10 d |
EC50 (reproduction) |
14 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
R |
7 - 10 d |
EC50 (reproduction) |
26 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
R |
7 - 10 d |
EC50 (reproduction) |
22 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Ceriodaphnia dubia |
FW |
S |
24 h |
LC50 |
7.6 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
7.9 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
7.9 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
11.4 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
8.9 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
11 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
11.8 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
10.4 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
11.1 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
LC50 |
47 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
R |
168 h |
LC50 |
24 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
7 - 10 d |
NOEC |
3.89 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
R |
7 - 10 d |
NOEC (reproduction) |
19 |
|
|
(Water flea) |
|
|
|
|||
|
Ceriodaphnia dubia |
FW |
R |
7 - 10 d |
NOEC (reproduction) |
19 |
|
|
(Water flea) |
|
|
|
|||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Ceriodaphnia dubia |
FW |
R |
7 - 10 d |
NOEC (reproduction) |
12 |
ECOTOX |
|
(Water flea) |
|
|
|
|||
|
Cyprinodon variegatus |
SW |
S |
24 h |
LC50 |
>20 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
48 h |
LC50 |
8.9 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
LC50 |
10 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
NOEC (mortality) |
6.2 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Danio rerio |
FW |
R |
28 d |
LC50 |
10.3 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
S |
48 h |
LC50 |
10.5 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
R |
7 d |
NOEC (reproduction) |
8.5 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
R |
14 d |
NOEC (reproduction) |
8.5 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
R |
21 d |
NOEC (reproduction) |
8.5 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
R |
28 d |
NOEC (reproduction) |
8.5 |
|
|
(Zebra danio) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
4.3 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
EC50 (reproduction) |
15 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
EC50 (reproduction) |
19 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
EC50 (reproduction) |
16 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
14 d |
EC50 (reproduction) |
2.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
140 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
86 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
310 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
13 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
10.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
15.4 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
12.9 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
21.3 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
8.6 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
11.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
12.8 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
31 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Daphnia magna |
FW |
S |
240 h |
LC50 |
16 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
14.2 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
13.9 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
13 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
10.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
15.4 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
NOEC (mortality) |
<1.4 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
NOEC (reproduction) |
11 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
NOEC (reproduction) |
11 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
9 - 11 d |
NOEC (reproduction) |
6.5 |
|
|
(Water flea) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
24 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
48 h |
LC50 |
24 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
24 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
17 |
|
|
(Bluegill) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
16 |
ECOTOX |
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
4.5 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
48 h |
LC50 |
4.5 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
72 h |
LC50 |
4.5 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
4.5 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
24 h |
LC50 |
8 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
48 h |
LC50 |
7.7 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
72 h |
LC50 |
7.4 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
96 h |
LC50 |
7.4 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
1 h |
LC50 |
12 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
2 h |
LC50 |
6.8 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
4 h |
LC50 |
6 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
8 h |
LC50 |
6 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
16 h |
LC50 |
6 |
|
|
(Bluegill) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Lepomis macrochirus |
FW |
F |
24 h |
LC50 |
6 |
ECOTOX |
|
(Bluegill) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
60 h |
LC50 |
0.66 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
6.5 d |
LC50 |
0.05 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
60 h |
LC50 |
0.71 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
6.5 d |
LC50 |
0.06 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
84 h |
LC50 |
0.34 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
7.5 d |
LC50 |
0.05 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
84 h |
LC50 |
0.39 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
F |
7.5 d |
LC50 |
0.06 |
|
|
(Largemouth bass) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
16 d |
LC50 |
<0.09 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
16 d |
LC50 |
<0.09 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
4.7 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
7.46 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
48 h |
LC50 |
4.1 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
16.9 |
ECOTOX |
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
29.12 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
29.12 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
29.12 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
33.93 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
33.93 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
33.93 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
39.19 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
34.98 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
33.93 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
7.7 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
22.3 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
35.4 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
22.2 |
|
|
(Fathead minnow) |
|
|
||||
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Chlorobenzene |
||||||
|
Poecilia reticulata |
FW |
S |
24 h |
LC50 |
45.53 |
ECOTOX |
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
S |
48 h |
LC50 |
45.53 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
S |
96 h |
LC50 |
45.53 |
|
|
(Guppy) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2-Dichloropropane |
||||||
|
Chlamydomonas reinhardtii |
FW |
F |
4d |
EC50 (population change) |
83 |
ECOTOX |
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
7d |
EC50 (population change) |
62 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
10d |
EC50 (population change) |
50 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
4d |
EC50 (population change) |
83 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
7d |
EC50 (population change) |
62 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
10d |
EC50 (population change) |
50 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
4d |
NOEC (population change) |
38 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
7d |
NOEC (population change) |
31.5 |
|
|
(Green algae) |
|
|
||||
|
Chlamydomonas reinhardtii |
FW |
F |
10d |
NOEC (population change) |
29 |
|
|
(Green algae) |
|
|
||||
|
Crangon crangon |
SW |
R |
48hr |
LC50 |
>100 |
|
|
(Common shrimp, sand shrimp) |
|
|
||||
|
Daphnia magna |
FW |
S |
24hr |
LC50 |
99 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48hr |
LC50 |
52 |
|
|
(Water flea) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
86hr |
LC50 |
320 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24hr |
LC50 |
360 |
|
|
(Bluegill) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2-Dichloropropane |
||||||
|
Lepomis macrochirus |
FW |
S |
96hr |
LC50 |
280 |
ECOTOX |
|
(Bluegill) |
|
|
||||
|
Menidia beryllina |
SW |
S |
96hr |
LC50 |
240 |
|
|
(Inland silverside) |
|
|
||||
|
Pimephales promelas |
FW |
F |
24hr |
LC50 |
194 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
48hr |
LC50 |
154 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
72hr |
LC50 |
141 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96hr |
LC50 |
140 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96hr |
LC50 |
127 |
|
|
(Fathead minnow) |
|
|
||||
|
Pleuronectiformes |
SW |
F |
96hr |
LC50 |
61 |
|
|
(Sole order) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
<=96hr |
EC50 (population change) |
194 |
|
|
(Green algae) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
<=96hr |
EC50 (population change) |
123 |
|
|
(Green algae) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
2,4,6-Trichlorophenol |
||||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
EC50 (mortality) |
4 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Chlorella vulgaris |
FW |
S |
96 h |
EC50 (general growth) |
10 |
|
|
(Green algae) |
|
|
||||
|
Chlorella vulgaris |
FW |
S |
96 d |
EC50 (general growth) |
10 |
|
|
(Green algae) |
|
|
||||
|
Crangon septemspinosa |
SW |
R |
96 h |
LC50 |
2.7 |
|
|
(Bay shrimp, Sand shrimp) |
|
|
||||
|
Daphnia carinata |
FW |
S |
24 h |
EC50 (immobile) |
7.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
F |
48 h |
EC50 (immobile) |
3.34 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
3.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
EC50 (immobile) |
2.2 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
1.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
5.47 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
15 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
6 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
13.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
13 d |
LC50 |
0.77 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
2,4,6-Trichlorophenol |
||||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
0.33 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
0.27 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
21 d |
NOEC (progeny) |
0.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia pulex |
FW |
S |
24 h |
EC50 (immobile) |
3.9 |
|
|
(Water flea) |
|
|
||||
|
Fundulus heteroclitus |
SW |
S |
48 h |
LC50 |
2.3 |
|
|
(Mummichog, fish) |
|
|
||||
|
Jordanella floridae |
FW |
R |
96 h |
LC50 |
2.26 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
12 h |
LC50 |
2.972 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
24 h |
LC50 |
2.541 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
36 h |
LC50 |
2.292 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
48 h |
LC50 |
2.207 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
72 h |
LC50 |
2.207 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
96 h |
LC50 |
2.207 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
10 d |
LOEC |
>1.76 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
28 d |
LOEC |
1.335 |
|
|
(Flagfish) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
2,4,6-Trichlorophenol |
||||||
|
Jordanella floridae |
FW |
F |
28 d |
LOEC (general growth) |
0.75 |
ECOTOX |
|
(Flagfish) |
|
|
||||
|
Lemna minor |
FW |
S |
72 h |
LC50 |
5.9 |
|
|
(Duckweed) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
0.72 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
0.32 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
96 h |
LC50 |
0.41 |
|
|
(Bluegill) |
|
|
||||
|
Mya arenaria |
SW |
R |
96 h |
LC50 |
3.9 |
|
|
(Sand gaper, soft shell clam) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
R |
48 h |
LC50 |
2.786 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
0.73 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
24 h |
LC50 |
3.304 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
R |
72 h |
LC50 |
2.249 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
R |
96 h |
LC50 |
1.991 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oryzias latipes |
FW |
S |
48 h |
LC50 |
0.18 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
S |
96 h |
LC50 |
2.3 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Palaemonetes pugio |
SW |
S |
48 h |
LC50 |
5.6 |
|
|
(Daggerblade grass shrimp) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
2,4,6-Trichlorophenol |
||||||
|
Palaemonetes pugio |
SW |
R |
96 h |
LC50 |
1.21 |
ECOTOX |
|
(Daggerblade grass shrimp) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
2.8 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
9.7 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
8.6 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
8 d |
LC50 |
5.8 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
8 d |
LC50 |
6.4 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
2.74 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
9.16 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
4.55 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
4.55 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
0.1-1 |
|
|
(Fathead minnow) |
|
|
||||
|
Platichthys flesus |
SW |
R |
96 h |
LC50 |
1.4 |
|
|
(European flounder, fish) |
|
|
||||
|
Poecilia reticulata |
FW |
R |
96 h |
LC50 |
2.2 |
|
|
(Guppy) |
|
|
||||
|
Pseudokirchneriella subcapitata |
FW |
S |
96 h |
EC50 (general growth) |
3.5 |
|
|
(Green algae) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
2,4,6-Trichlorophenol |
||||||
|
Pseudokirchneriella subcapitata |
FW |
S |
96 d |
EC50 (general growth) |
3.5 |
ECOTOX |
|
(Green algae) |
|
|
||||
|
Salmo trutta |
FW |
S |
24 h |
LC50 |
11 |
|
|
(Brown trout) |
|
|
||||
|
Scenedesmus abundans |
FW |
S |
96 h |
EC50 (general growth) |
5.6 |
|
|
(Green algae) |
|
|
||||
|
Spirostomum teres |
FW |
S |
24 h |
LC50 |
2 |
|
|
(Ciliated protozoa) |
|
|
||||
Note: Bolded value was used to derive toxicity refernce value
|
Test Species |
Media Type |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Bis(2-chloroethoxy)methane |
||||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
201 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
184 |
|
|
(Fathead minnow) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Danio rerio |
FW |
F |
48 h |
LC50 |
4.8 |
ECOTOX |
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
F |
96 h |
LC50 |
2.1 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
F |
14 d |
NOEC (general behavioral changes) |
0.44 |
|
|
(Zebra danio) |
|
|
||||
|
Daphnia magna |
FW |
R |
24 h |
EC0 (equilibrium) |
1.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
24 h |
EC50 (equilibrium) |
3.2 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
21 d |
NOEC (equilibrium) |
0.5 |
|
|
(Water flea) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
24 h |
LC50 |
>7.5-10 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
48 h |
LC50 |
7.2 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
72 h |
LC50 |
7.4 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
LC50 |
7.4 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Danio rerio |
FW |
R |
28 d |
LC50 |
2.7 |
|
|
(Zebra danio) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Danio rerio |
FW |
S |
48 h |
LC50 |
4.25 |
ECOTOX |
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
S |
24 h |
LC50 |
4.2 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
R |
7 d |
NOEC (reproduction) |
2.1 |
|
|
(Zebra danio) |
|
|
|
|||
|
Danio rerio |
FW |
R |
14 d |
NOEC (reproduction) |
2.1 |
|
|
(Zebra danio) |
|
|
|
|||
|
Danio rerio |
FW |
R |
21 d |
NOEC (reproduction) |
2.1 |
|
|
(Zebra danio) |
|
|
|
|||
|
Danio rerio |
FW |
R |
28 d |
NOEC (reproduction) |
2.1 |
|
|
(Zebra danio) |
|
|
|
|||
|
Daphnia magna |
FW |
S |
48 h |
EC50 (immobile) |
0.0007 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
1.6 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
1.6 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
3.2 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
F |
96 h |
EC50 (immobile) |
1.35 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Daphnia magna |
FW |
R |
14 d |
EC50 (reproduction) |
0.93 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
42 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
11 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
11.2 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
21.4 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
16.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
10.9 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
13.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
10.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
2.2 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
21 d |
NOEC |
0.3 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Daphnia magna |
FW |
R |
21 d |
NOEC (reproduction) |
0.4 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Jordanella floridae |
FW |
R |
96 h |
LC50 |
4.48 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
12 h |
LC50 |
3.069 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
24 h |
LC50 |
3.069 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
36 h |
LC50 |
3.069 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
48 h |
LC50 |
2.11 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
72 h |
LC50 |
2.053 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
96 h |
LC50 |
2.053 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
10 d |
LOEC |
0.263 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
28 d |
LOEC |
>0.349 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
28 d |
LOEC (general growth) |
>0.349 |
|
|
(Flagfish) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
4.5 |
ECOTOX |
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
4.3 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
6.4 |
|
|
(Bluegill) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
EC50 (equilibrium) |
1.1 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
48 h |
LC50 |
1.18 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
24 h |
LC50 |
1.37 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
48 h |
LC50 |
1.24 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
72 h |
LC50 |
1.24 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
1.12 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
24 h |
LC50 |
1.2 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
14 d |
LC50 |
0.8 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
1.12 |
ECOTOX |
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
24 h |
LC50 |
0.88 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
96 h |
LC50 |
0.88 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Palaemonetes pugio |
SW |
S |
48 h |
LC50 |
129.2 |
|
|
(Daggerblade grass shrimp) |
|
|
||||
|
Palaemonetes pugio |
SW |
S |
96 h |
LC50 |
60 |
|
|
(Daggerblade grass shrimp) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
34 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
34 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
34.5 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
2.4 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
35.4 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
35.4 |
|
|
(Fathead minnow) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
33.7 |
ECOTOX |
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
30 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
4 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
3.6 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
14.2 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
11.7 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
4.2 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
32 d |
LOEC |
1 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
32 d |
NOEC |
0.57 |
|
|
(Fathead minnow) |
|
|
||||
|
Pseudokirchneriella subcapitata |
FW |
S |
96 h |
EC50 (general growth) |
1.6 |
|
|
(Green algae) |
|
|
||||
|
Pseudokirchneriella subcapitata |
FW |
S |
3 h |
EC50 (photosynethesis) |
5.2 |
|
|
(Green algae) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,4-Dichlorobenzene |
||||||
|
Salvelinus fontinalis |
FW |
S |
96 h |
LC50 |
1.67 |
ECOTOX |
|
(Brook trout) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
48 h |
EC50 |
28 |
|
|
(Green algae) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
48 h |
EC50 |
38 |
|
|
(Green algae) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
|
Hexachlorocyclopentadiene |
|||||||
|
Daphnia magna |
FW |
R |
24 h |
EC0 (ability to maintain balance) |
0.19 |
ECOTOX |
|
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
R |
24 h |
EC50 (ability to maintain balance) |
0.21 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
R |
21 d |
NOEC (ability to maintain balance) |
0.009 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
0.21 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
0.0522 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
0.093 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
0.13 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
0.039 |
||
|
(Water flea) |
|
|
|||||
|
Daphnia magna |
FW |
R |
21 d |
NOEC (reproduction) |
0.009 |
||
|
(Water flea) |
|
|
|||||
|
Ictalurus punctatus |
FW |
S |
24 h |
LC50 |
0.19 |
||
|
(Channel catfish) |
|
|
|||||
|
Ictalurus punctatus |
FW |
S |
48 h |
LC50 |
0.15 |
||
|
(Channel catfish) |
|
|
|||||
|
Ictalurus punctatus |
FW |
S |
96 h |
LC50 |
0.097 |
||
|
(Channel catfish) |
|
|
|||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
>500 |
||
|
(Bluegill) |
|
|
|||||
|
Lepomis macrochirus |
FW |
S |
48 h |
LC50 |
30 |
||
|
(Bluegill) |
|
|
|||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachlorocyclopentadiene |
||||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
25 |
ECOTOX |
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
0.17 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
48 h |
LC50 |
0.15 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
0.13 |
|
|
(Bluegill) |
|
|
||||
|
Micropterus salmoides |
FW |
S |
24 h |
LC50 |
>500 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
S |
48 h |
LC50 |
35 |
|
|
(Largemouth bass) |
|
|
||||
|
Micropterus salmoides |
FW |
S |
96 h |
LC50 |
20 |
|
|
(Largemouth bass) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
0.007 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
30 d |
LC50 |
0.0067 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
0.078 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
0.059 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
72 h |
LC50 |
0.059 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
0.059 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
0.115 |
|
|
(Fathead minnow) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachlorocyclopentadiene |
||||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
0.11 |
ECOTOX |
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
72 h |
LC50 |
0.107 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
0.104 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
0.093 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
0.078 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
72 h |
LC50 |
0.078 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
0.078 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
0.0139 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
24 h |
LC50 |
0.24 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
48 h |
LC50 |
0.21 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
S |
96 h |
LC50 |
0.18 |
|
|
(Fathead minnow) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
48 h |
EC50 (biomass) |
0.08 |
|
|
(Green algae) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
48 h |
EC50 (population change) |
0.24 |
|
|
(Green algae) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachloroethane |
||||||
|
Arbacia punctulata |
SW |
S |
48 h |
EC50 (general growth) |
9.32 |
ECOTOX |
|
(Purple-spined sea urchin) |
|
|
||||
|
Arbacia punctulata |
SW |
S |
48 h |
EC50 (general growth) |
8.51 |
|
|
(Purple-spined sea urchin) |
|
|
||||
|
Carassius auratus |
FW |
F |
96 h |
LC50 |
>2.1 |
|
|
(Goldfish) |
|
|
||||
|
Carassius auratus |
FW |
F |
96 h |
LC50 |
1.42 |
|
|
(Goldfish) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
EC50 (mortaility) |
4.3 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia reticulata |
FW |
S |
48 h |
EC50 (immobile) |
6.8 |
|
|
(Water flea) |
|
|
||||
|
Ceriodaphnia reticulata |
FW |
S |
48 h |
LC50 |
3.3 |
|
|
(Water flea) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
24 h |
LC50 |
3.1 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
48 h |
LC50 |
2.8 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
72 h |
LC50 |
2.4 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
LC50 |
2.4 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
EC50 (immobile) |
10 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
EC50 (immobile) |
2.1 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
EC50 (immobile) |
1.8 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachloroethane |
||||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
26 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
8.1 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
2.9 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
2.4 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
2.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
1.36 |
|
|
(Water flea) |
|
|
||||
|
Daphnia pulex |
FW |
S |
48 h |
EC50 (immobile) |
13 |
|
|
(Water flea) |
|
|
||||
|
Daphnia pulex |
FW |
S |
48 h |
LC50 |
>10 |
|
|
(Water flea) |
|
|
||||
|
Gambusia affinis |
FW |
F |
96 h |
LC50 |
1.38 |
|
|
(Western mosquitofish) |
|
|
||||
|
Ictalurus punctatus |
FW |
F |
48 h |
LC50 |
1.93 |
|
|
(Channel catfish) |
|
|
||||
|
Ictalurus punctatus |
FW |
F |
72 h |
LC50 |
1.6 |
|
|
(Channel catfish) |
|
|
||||
|
Ictalurus punctatus |
FW |
F |
96 h |
LC50 |
1.52 |
|
|
(Channel catfish) |
|
|
||||
|
Ictalurus punctatus |
FW |
F |
96 h |
LC50 |
2.36 |
|
|
(Channel catfish) |
|
|
||||
|
Ictalurus punctatus |
FW |
F |
96 h |
LC50 |
1.77 |
|
|
(Channel catfish) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachloroethane |
||||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
1.8 |
ECOTOX |
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
0.98 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
24 h |
LC50 |
1.82 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
48 h |
LC50 |
1.6 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
72 h |
LC50 |
1.13 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
96 h |
LC50 |
0.97 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
96 h |
LC50 |
0.856 |
|
|
(Bluegill) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
EC50 (ability to maintain balance) |
0.84 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
EC50 (mortaility) |
0.87 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
192 h |
EC50 (mortaility) |
0.6 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
0.84 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
24 h |
LC50 |
1.8 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
48 h |
LC50 |
1.17 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
72 h |
LC50 |
1.05 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachloroethane |
||||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
0.94 |
ECOTOX |
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
192 h |
LC50 |
0.77 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
24 h |
LC50 |
1.51 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
48 h |
LC50 |
0.97 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
72 h |
LC50 |
0.97 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
0.97 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
1.18 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
0.98 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
192 h |
LC50 |
0.76 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Orconectes immunis |
FW |
F |
96 h |
LC50 |
>2.1 |
|
|
(Crayfish) |
|
|
||||
|
Orconectes immunis |
FW |
F |
96 h |
LC50 |
2.7 |
|
|
(Crayfish) |
|
|
||||
|
Pimephales promelas |
FW |
F |
24 h |
LC50 |
1.74 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
48 h |
LC50 |
1.44 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
72 h |
LC50 |
1.29 |
|
|
(Fathead minnow) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Hexachloroethane |
||||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
1.23 |
ECOTOX |
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
24 h |
LC50 |
1.8 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
48 h |
LC50 |
1.55 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
72 h |
LC50 |
1.55 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
1.51 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
1.32 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
1.53 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
1.39 |
|
|
(Fathead minnow) |
|
|
||||
|
Pimephales promelas |
FW |
F |
96 h |
LC50 |
1.1 |
|
|
(Fathead minnow) |
|
|
||||
|
Simocephalus vetulus |
FW |
S |
48 h |
LC50 |
5.8 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2,4-Trichlorobenzene |
||||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (equilibrium) |
5.4 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
7 d |
EC03 (proliferation) |
>24 |
|
|
(Green algae) |
|
|
||||
|
Acartia tonsa |
SW |
S |
96 h |
LC50 |
2.1 |
|
|
(Calanoid copepod) |
|
|
||||
|
Armandia maculata |
SW |
F |
96 h |
LC50 |
0.93 |
|
|
Polychaete or Opheliid worm |
|
|
||||
|
Branchiostoma caribaeum |
SW |
F |
96 h |
LC50 |
>1.5 - <10 |
|
|
(Caribbean lancelet) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
EC50 (immobile) |
F 3.9, 2.7 - 5.6 umol/L |
|
|
(Water flea) |
|
|
||||
|
Corophium acherusicum |
SW |
F |
96 h |
LC50 |
1.1 |
|
|
(Scud) |
|
|
||||
|
Crangon septemspinosa |
SW |
S |
96 h |
LC50 |
0.09 |
|
|
(Bay shrimp, Sand shrimp) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
24 h |
LC50 |
>47 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
48 h |
LC50 |
>47 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
72 h |
LC50 |
>4 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
LC50 |
21 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
NOEC |
15 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Danio rerio |
FW |
S |
48 h |
LC50 |
6.3 |
|
|
(Zebra danio) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
1.2 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2,4-Trichlorobenzene |
||||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (equilibrium) |
5.4 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Scenedesmus subspicatus |
FW |
S |
7 d |
EC03 (proliferation) |
>24 |
|
|
(Green algae) |
|
|
||||
|
Acartia tonsa |
SW |
S |
96 h |
LC50 |
2.1 |
|
|
(Calanoid copepod) |
|
|
||||
|
Armandia maculata |
SW |
F |
96 h |
LC50 |
0.93 |
|
|
Polychaete or Opheliid worm |
|
|
||||
|
Branchiostoma caribaeum |
SW |
F |
96 h |
LC50 |
>1.5 - <10 |
|
|
(Caribbean lancelet) |
|
|
||||
|
Ceriodaphnia dubia |
FW |
S |
48 h |
EC50 (immobile) |
F 3.9, 2.7 - 5.6 umol/L |
|
|
(Water flea) |
|
|
||||
|
Corophium acherusicum |
SW |
F |
96 h |
LC50 |
1.1 |
|
|
(Scud) |
|
|
||||
|
Crangon septemspinosa |
SW |
S |
96 h |
LC50 |
0.09 |
|
|
(Bay shrimp, Sand shrimp) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
24 h |
LC50 |
>47 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
48 h |
LC50 |
>47 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
72 h |
LC50 |
>4 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
LC50 |
21 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
S |
96 h |
NOEC |
15 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Danio rerio |
FW |
S |
48 h |
LC50 |
6.3 |
|
|
(Zebra danio) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2,4-Trichlorobenzene |
||||||
|
Daphnia magna |
FW |
S |
24 h |
EC50 (immobile) |
1.2 |
ECOTOX |
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
F |
48 h |
EC50 (immobile) |
3.39 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
14 d |
EC50 (reproduction) |
0.45 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
24 h |
LC50 |
110 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
50 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
2.1 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
1.7 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
S |
48 h |
LC50 |
7.69 |
|
|
(Water flea) |
|
|
||||
|
Gammarus annulatus |
SW |
S |
96 h |
LC50 |
0.5 |
|
|
(Scud) |
|
|
||||
|
Gammarus minus |
FW |
S |
96 h |
LC50 |
3.9 |
|
|
(Scud) |
|
|
||||
|
Hydra oligactis |
FW |
F |
96 h |
LC50 |
>3.37 |
|
|
(Hydra) |
|
|
||||
|
Jordanella floridae |
FW |
R |
96 h |
LC50 |
4 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
R |
24 h |
LC50 |
2.672 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
R |
36 h |
LC50 |
2.318 |
|
|
(Flagfish) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2,4-Trichlorobenzene |
||||||
|
Jordanella floridae |
FW |
R |
48 h |
LC50 |
1.494 |
ECOTOX |
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
72 h |
LC50 |
1.285 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
96 h |
LC50 |
1.217 |
|
|
(Flagfish) |
|
|
||||
|
Jordanella floridae |
FW |
F |
10 d |
LOEC |
1.13 |
|
|
(Flagfish) |
|
|
||||
|
Laevicardium mortoni |
SW |
F |
96 h |
LC50 |
0.89 |
|
|
(Morton's egg cockle) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
24 h |
LC50 |
109 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
S |
96 h |
LC50 |
3.4 |
|
|
(Bluegill) |
|
|
||||
|
Lepomis macrochirus |
FW |
F |
96 h |
LC50 |
3.02 |
|
|
(Bluegill) |
|
|
||||
|
Leptosynapta inhaerens |
SW |
F |
96 h |
LC50 |
2.4 |
|
|
(Sea cucumber) |
|
|
||||
|
Lumbriculus variegatus |
FW |
F |
96 h |
LC50 |
>3.37 |
|
|
(Oligochaete, worm) |
|
|
||||
|
Menidia beryllina |
SW |
S |
96 h |
LC50 |
2.5 |
|
|
(Inland silverside) |
|
|
||||
|
Neanthes arenaceodentata |
SW |
S |
96 h |
LC50 |
4.7 |
|
|
(Polychaete worm) |
|
|
||||
|
Nitocra spinipes |
SW |
S |
96 h |
LC50 |
2.6 |
|
|
(Harpacticoid copepod) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 d |
EC50 (equilibrium) |
1.27 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
1,2,4-Trichlorobenzene |
||||||
|
Oncorhynchus mykiss |
FW |
S |
48 h |
LC50 |
1.95 |
ECOTOX |
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
24 h |
LC50 |
2.3 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
48 h |
LC50 |
2 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
72 h |
LC50 |
1.73 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
1.53 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
192 h |
LC50 |
1.28 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
96 h |
LC50 |
4.04 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
S |
96 h |
LC50 |
4.33 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
1.32 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oncorhynchus mykiss |
FW |
F |
96 h |
LC50 |
1.52 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Orconectes immunis |
FW |
F |
96 h |
LC50 |
3.02 |
|
|
(Crayfish) |
|
|
||||
|
Oryzias latipes |
FW |
S |
48 h |
LC50 |
1.1 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Palaemonetes pugio |
SW |
F |
96 h |
LC50 |
0.54 |
|
|
(Daggerblade grass shrimp) |
|
|
||||
|
Palaemonetes pugio |
SW |
S |
96 h |
LC50 |
0.9 |
|
|
(Daggerblade grass shrimp) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Alpha-BHC |
||||||
|
Artemia salina |
SW |
R |
96 h |
LC50 |
0.5 |
ECOTOX |
|
(Brine shrimp) |
|
|
||||
|
Chlorella pyrenoidosa |
FW |
R |
96 h |
EC50 (general growth) |
>10 |
|
|
(Green algae) |
|
|
||||
|
Danio rerio |
FW |
S |
24 h |
LC50 |
1.41 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
S |
48 h |
LC50 |
1.11 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
S |
72 h |
LC50 |
1.11 |
|
|
(Zebra danio) |
|
|
||||
|
Danio rerio |
FW |
S |
96 h |
LC50 |
1.11 |
|
|
(Zebra danio) |
|
|
||||
|
Daphnia magna |
FW |
R |
48 h |
EC50 (immobile) |
0.8 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
25 d |
EC50 (reproduction) |
0.1 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
1 wk |
LC50 |
0.37 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
2 wk |
LC50 |
0.48 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
3 wk |
EC50 (general growth) |
>8.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
19 d |
EC50 (reproduction) |
1.36 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
1 wk |
LC50 |
>8.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
2 wk |
LC50 |
>8.5 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
R |
3 wk |
LC50 |
2.1 |
|
|
(Water flea) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Alpha-BHC |
||||||
|
Microhyla ornata |
FW |
R |
96 h |
LC50 |
7.27 |
ECOTOX |
|
Oncorhynchus mykiss |
FW |
D |
48 h |
EC50 (immobile) |
1.05 |
|
|
(Rainbow trout,donaldson trout) |
|
|
||||
|
Oryzias latipes |
FW |
R |
24 h |
EC50 (immobile) |
>10 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
48 h |
EC50 (immobile) |
8 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
72 h |
EC50 (immobile) |
8 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
96 h |
EC50 (immobile) |
5.6 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
24 h |
LC50 |
>10 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
48 h |
LC50 |
>10 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
72 h |
LC50 |
8.5 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
96 h |
LC50 |
8 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
9 d |
LC50 |
>10 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
9 d |
LC50 |
>10 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
16 d |
LC50 |
>10 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
23 d |
LC50 |
2.8 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Oryzias latipes |
FW |
R |
30 d |
LC50 |
2.3 |
|
|
(Medaka, high-eyes) |
|
|
||||
|
Test Species |
Medium |
Exposure Type |
Duration |
Endpoint |
Concentration (mg/L) |
Source |
|
Alpha-BHC |
||||||
|
Oryzias latipes |
FW |
R |
37 d |
LC50 |
1.2 |
ECOTOX |
|
(Medaka, high-eyes) |
|
|
||||
|
Paracheirodon axelrodi |
FW |
S |
24 h |
LC50 |
1.64 |
|
|
Paracheirodon axelrodi |
FW |
S |
48 h |
LC50 |
1.52 |
|
|
Paracheirodon axelrodi |
FW |
S |
72 h |
LC50 |
1.52 |
|
|
Paracheirodon axelrodi |
FW |
S |
96 h |
LC50 |
1.52 |
|
|
Poecilia reticulata |
SW |
R |
48 h |
EC50 (immobile) |
1.38 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
SW |
R |
96 h |
EC50 (immobile) |
1.31 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
R |
48 h |
EC50 (immobile) |
0.8 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
S |
24 h |
LC50 |
2.65 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
S |
48 h |
LC50 |
1.95 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
S |
72 h |
LC50 |
1.58 |
|
|
(Guppy) |
|
|
||||
|
Poecilia reticulata |
FW |
S |
96 h |
LC50 |
1.49 |
|
|
(Guppy) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Duration |
Exposure Type |
Endpoint |
Concentration (mg/L) |
Source |
|
Barium |
||||||
|
Americamysis bahia |
SW |
96 h |
|
LC50 |
>500 |
ECOTOX |
|
(Opossum shrimp) |
|
|
||||
|
Cyprinodon variegatus |
SW |
24 h |
S |
LC50 |
>500 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
48 h |
S |
LC50 |
>500 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
72 h |
S |
LC50 |
>500 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
96 h |
S |
LC50 |
>500 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Cyprinodon variegatus |
SW |
96 h |
S |
NOEC |
500 |
|
|
(Sheepshead minnow) |
|
|
||||
|
Daphnia magna |
FW |
24 h |
S |
LC50 |
>530 |
|
|
(Water flea) |
|
|
||||
|
Daphnia magna |
FW |
48 h |
S |
LC50 |
410 |
|
|
(Water flea) |
|
|
||||
|
Lemna minor |
FW |
4 d |
S |
EC50 |
26 |
|
|
(Duckweed) |
|
|
||||
|
Myriophyllum spicatum |
FW |
32 d |
S |
EC50 |
41.2 |
|
|
(Eurasian watermilfoil) |
|
|
||||
|
Myriophyllum spicatum |
FW |
32 d |
S |
EC50 |
103 |
|
|
(Eurasian watermilfoil) |
|
|
||||
|
Test Species |
Medium |
Duration |
Exposure Type |
Endpoint |
Concentration (mg/L) |
Source |
|
Barium |
||||||
|
Myriophyllum spicatum |
FW |
32 d |
S |
EC50 |
113 |
ECOTOX |
|
(Eurasian watermilfoil) |
|
|
||||
|
Myriophyllum spicatum |
FW |
32 d |
S |
EC50 |
83.8 |
|
|
(Eurasian watermilfoil) |
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Duration |
Exposure |
Endpoint |
Concentration (mg/L) |
Source |
|
|
Tin |
|||||||
|
Oncorhynchus mykiss |
FW |
28 d |
R |
LC50 |
>0.17-<15.61 |
ECOTOX |
|
|
(Rainbow trout,donaldson trout) |
|
|
|
||||
Note: Bolded value was used to derive toxicity reference value
|
Test Species |
Medium |
Duration |
Exposure |
Endpoint |
Concentration (mg/L) |
Source |
|
|
Sulphide |
|||||||
|
Pseudokirchneriella subcapitata |
FW |
96 h |
|
EC50 |
10 |
ECOTOX |
|
|
(Green algae) |
|
|
|
|
|
||
|
Cyprinodon variegatus |
FW |
24 h |
|
NR-ZERO |
4.5 – 5.0 |
||
|
(Sheepshead minnow) |
|
|
|
|
|
||
|
Fundulus grandis |
FW |
24 h |
|
NR-ZERO |
4.5 – 5.0 |
||
|
(Gulf killifish) |
|
|
|
|
|
||
|
Fundulus similis |
FW |
24 h |
|
NR-ZERO |
4.5 – 5.0 |
||
|
(Longnose killifish) |
|
|
|
|
|
||
|
Gambusia affinis |
FW |
24 h |
|
NR-ZERO |
4.5 – 5.0 |
||
|
(Western mosquitofish) |
|
|
|
|
|
||
|
Lucania parva |
FW |
24 h |
|
NR-ZERO |
4.5 – 5.0 |
||
|
(Rainwater Killifish) |
|
|
|
|
|
||