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Water Quality

Ambient Water Quality Criteria for Fluoride


Table 5.3 Effects of Fluoride on Aquatic Organisms other than Fish


F **

Freshwater Algae

mg/L

Salt

Organisms

Effects

Reference

2

-

Chlorella pyrendoidosa

37% decrease in growth rate

Smith & Woodson, 1965; Groth, 1975a; Groth, 1975b

10

NaF

Synechococcus leopoliensis

no effect on growth

Hekman et al., 1984

43

NaF

Scenedesmus sp.

4-day, 24°C
toxic threshold

Bringmann & Kuhn, 1959a; Bringmann & Kuhn, 1959c

52

NaF

Synechococcus leopoliensis

13% decrease in log phase of growth

Hekman et al., 1984

52

NaF

Oscillatoria limnetica,
Cyclotella meneghiniana,
Ankistrodesmus braunii,
Scenedesmus quadricauda
Stephanodiscus minutus

no effect on: growth, dark O2 uptake, F uptake, light O2 evolution

Hekman et al., 1984

F **

Bacteria

mg/L

Salt

Organisms

Effects

Reference

81

NaF

Escherichia coli

toxic threshold
27°C

Bringmann & Kuhn, 1959a; Bringmann & Kuhn, 1959c

544

NaF

Escherichia coli
Pseudomonas fluorescens
Enterococcus sp.

no effect after 48-h culture or 4 months in storage

Vajdic, 1966

F **

Protozoans

mg/L

Salt

Organisms

Effects

Reference

102.2

NaF

Microregma

toxic effect threshold,

Bringmann & Kuhn, 1959a; Bringmann & Kuhn, 1959c

1000

NaF

free-living protozoans and rotifers

no effect on reproduction

Wantland, 1956

1700

NaF

free-living protozoans and rotifers

lethal

Wantland, 1956

F **

Marine Invertebrates

mg/L

Salt

Organisms

Effects

Reference

1.0

NaF

Portunus depurator (crab)

not lethal in 90-days

Wright & Davidson, 1975

1.0

NaF

Cancer pagurus (crab)

not lethal in 90-days

Wright & Davidson, 1975

1.0

NaF

Carcinus maenas (crab)

not lethal in 90-days

Wright & Davidson, 1975

2.4

NaF

Portunus depurator (crab)

not lethal in 90-days

Wright & Davidson, 1975

2.4

NaF

Cancer pagurus (crab)

not lethal in 90-days

Wright & Davidson, 1975

2.4

NaF

Carcinus maenas (crab)

not lethal in 90-days

Wright & Davidson, 1975

2.4

NaF

Mytilus edulis (mussel)

not lethal in 42-days

Wright & Davidson, 1975

5.5

NaF

Penaeus indicus (prawn)

increased body weight and survival over controls @ 0.95 mg/L fluoride for 113 days

Hemens et al., 1975

5.5

NaF

Tylodisplax blephariskios
(crab)

no survival effect over controls @ 0.95 mg/L fluoride for 113 days

Hemens et al., 1975

5.9

NaF

Penaeus indicus (prawn)

no growth or survival effects in 68-days

Hemens et al., 1975

5.9

NaF

Tylodisplax blephariskios
(crab)

no survival effects in 68-days

Hemens et al., 1975

10

NaF

Penaeus indicus (prawn)

no mortality in 96-h @20°C

Hemens & Warwick 1972

10

NaF

Penaeus monodon (prawn)

no mortality in 96-h @20°C

Hemens & Warwick 1972

10

NaF

Portunus depurator (crab)

not lethal in 90-days

Wright & Davidson, 1975

10

NaF

Cancer pagurus (crab)

not lethal in 90-days

Wright & Davidson, 1975

10

NaF

Carcinus maenas (crab)

not lethal in 90-days

Wright & Davidson, 1975

10

NaF

Mytilus edulis (mussel)

75% mortality in 30-d, 100% by 36-days

Wright & Davidson, 1975

20

NaF

Callinectus sapidus (crab)

4.5% reduction in growth per moult

Moore, 1971

30

NaF

Portunus depurator (crab)

not lethal in 90-days

Wright & Davidson, 1975

30

NaF

Cancer pagurus (crab)

not lethal in 90-days

Wright & Davidson, 1975

30

NaF

Carcinus maenas (crab)

not lethal in 90-days

Wright & Davidson, 1975

30

NaF

Mytilus edulis (mussel)

75% mortality in 14-d, 100% by 21-days

Wright & Davidson, 1975

32-128

_

(oysters)

100% mortality in 60-days

Connell & Miller, 1984

52

_

Palaemon pacificus (shrimp)

23-45% mortality in 72-days

Connell & Miller, 1984

52

NaF

Tylodisplax blephariskios
(crab)

72-day survival rate is 32% of the controls @ l mg/L F, 25°C

Hemens & Warwick 1972

52

NaF

Palaemon pacificus
(shrimp)

72-day survival rate is 71% of the controls @ 1 mg/L F, 25°C

Hemens & Warwick 1972

52

NaF

Paenaeus indicus (prawn)

no effect on survival to 72-days @ 25°C

Hemens & Warwick 1972

100

NaF

Paenaeus indicus (prawn)

no 96-h mortality @ 20°C

Hemens & Warwick 1972

100

NaF

Penaeus monodon (prawn)

no 96-h mortality @ 20°C

Hemens & Warwick 1972

F **

Species: Daphnia and other Cladocerans

mg/L

Salt

Organisms/Conditions

Effects

Ref.

0.6

NaF

D. magna
20°C, hardness 250 mg/L

affects long term reproduction

Dave, 1984

2.7

Na3AlF6

D. pulex
soft water

48-h EC50

Sanders & Cope, 1966

3.7

NaF

D. magna
20°C, hardness 250 mg/L

7 and 21-day growth inhibition threshold

Dave, 1984

3.7

NaF

D. magna
20°C, hardness 250 mg/L

parthenogenesis is stimulated below and inhibited above

Dave, 1984

4.4

NaF

D. magna
20°C, hardness 250 mg/L

breakeven point for 21-day rate of reproduction

Dave, 1984

5.4

Na3AlF6

Simocephalus serrulatus

48-h EC50

Sanders & Cope, 1966

8.9

NaF

D. magna
20°C, hardness 250 mg/L

reduced median time of survival for fed neonates

Dave, 1984

10.0

NaF

D. magna
20°C, hardness 250 mg/L

reduced median time of survival for unfed neonates

Dave, 1984

10.0

NaF

D. magna
20°C, hardness 169 mg/L

approximate lower threshold for reduced egg hatchability

Fieser et al., 1986

26

NaF

D. magna
20°C, hardness 169 mg/L

21-day impaired reproduction threshold

Fieser et al., 1986

29

NaF

D. magna
20°C, hardness 169 mg/L

reproduction breakeven (increasing egg production and decreasing hatching)

Fieser et al., 1986

35

NaF

D. magna
20°C, hardness 169 mg/L

21-day reduced neonate production to 44% of controls

Fieser et al., 1986

49

NaF

D. magna
20°C, hardness 169 mg/L

21-day 98% decrease in live young

Fieser et al., 1986

52

NaF

D. magna
25°C, hardness 169 mg/L

mortality threshold

Fieser et al., 1986

65

NaF

D. magna
20°C, hardness 169 mg/L

threshold for increasing egg production

Fieser et al., 1986

84-142

NaF-

D. magna
20°C, hardness 169 mg/L

no live young

Fieser et al., 1986

93

NaF

D. magna
20°C, hardness 169 mg/L

mortality threshold

Fieser et al., 1986

98

NaF

D. magna
20°C, hardness 250 mg/L

48-h EC50 for immobilization

Dave, 1984

110

NaF

D. magna
hard water

no discernible effect

LeBlanc, 1980

122

NaF

Daphnia sp
23°C

mortality threshold

Bringmann & Kuhn, 1959a; Bringmann & Kuhn 1959c

124

NaF

D. magna
15°C, hardness 169 mg/L

2-day toxic threshold

Fieser et al., 1986

180

NaF

D. magna
25°C, hardness 169 mg/L

48-h LC50

Fieser et al., 1986

295

NaF

D. magna
20°C, hardness 250 mg/L

24-h EC50 for immobilization

Dave, 1984

247

NaF

D. magna
20°C, hardness 169 mg/L

48-h LC50

Fieser et al., 1986

270

NaF

D. magna, hard water

48-h EC50

Bringmann & Kuhn, 1959a

340

NaF

D. magna, hard water

48-h EC50

Leblanc, 1980

350

NaF

D. magna
15°C, hardness 169 mg/L

48-h LC50

Fieser et al., 1986

680

NaF

D. magna, hard water

24-h EC50

Leblanc, 1980

F **

Species: Rana (frogs)

mg/L

Salt

Organisms

Effects

Reference

1.0

NaF

Rana pipiens

slows embryo growth rate

Cameron, 1940

1-10

NaF

Rana temporaria

delayed metamorphosis and histological changes in the thyroid gland

Kuusisto & Telkka, 1961

5-40

NaF

Rana pipiens *

no deaths in 30 days

Kaplan et al., 1964

50

NaF

Rana pipiens *

5% deaths in 30 days

Kaplan et al., 1964

100

NaF

Rana pipiens *

25% deaths in 30 days

Kaplan et al., 1964

150

NaF

Rana pipiens *

35% deaths in 30 days

Kaplan et al., 1964

200

NaF

Rana pipiens *

63% deaths in 30 days

Kaplan et al., 1964

250

NaF

Rana pipiens *

all died in 30 days

Kaplan et al., 1964

300

NaF

Rana pipiens *

all died in 24 days

Kaplan et al., 1964

1000

NaF

Rana pipiens *

lethal in 72 hours

Kaplan et al., 1964

1500

NaF

Rana pipiens *

lethal in 72 hours

Kaplan et al., 1964

2200

NaF

Rana pipiens *

lethal in 50 hours

Kaplan et al., 1964

2500

NaF

Rana pipiens *

lethal in 18 hours

Kaplan et al., 1964

2800

NaF

Rana pipiens *

lethal in 15 hours

Kaplan et al., 1964

3500

NaF

Rana pipiens *

lethal in 2 hours

Kaplan et al., 1964

* Estimated value, see Table 5.4; 25°C, hardness 12.

** The values are usually expressed as concentration of fluoride only, not the molecule used, but in some references it is not clear what is meant so some may actually be the molecular concentration. Where a range is given the values are the 95% confidence limits around the mean.



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