Molybdenum toxicological studies with fish
Transformation of microbiota of fish intestines and gills against the background of molybdenum oxide nanoparticles in environment
This work is aimed at the evaluation of transformation of microbiota of Danio rerio intestines and gills under the impact of MoO3NPs, which corresponds to the existing level of studies using this model. The composition of the microbial community of Danio rerio was studied after nanoparticles of MoO3 (MoO3NPs) were administered into the environment in amount of 0.2 mg/dm3 within 7 days (Group II), in amount of 0.4 mg/dm3 within 14 days (Group III) in the form of lyosols with fish feed. MoO3NPs were not added to the reference group I; the procedure was comprised of the following: sampling, isolation, cleaning, measurement of DNA concentrations, polymerase chain reaction, validation and normalization of libraries with subsequent sequencing on the basis of high-performance sequenator (MiSeq Illumina, USA). Dose-dependent influence of MoO3NPs on microbiota transformation of intestines and gills has been estimated. Nanoparticles modify the composition of the microbiota by reducing the amount of symbionts participating in vital activity of macro-organism. Gills' microbiota is modified to a greater extent, and the increased occurrence of Actinobacteria phylum has been detected with significant difference in Group III. In fish intestines of Group II Cetobacterium somerae is the significant species. In Group III, representatives of Acinetobacter and Staphylococcus genuses have been identified, and the increase in fraction of Gram-positive microflora has been observed. The results evidence the violation of equilibrium in microbiota of intestines and gills and suppression of protecting mechanisms which usually prevent colonization by foreign microflora. Penetration of MoO3NPs into organism can influence the fish intestinal and respiratory systems and health.
E. Aleshina, E. Miroshnikova, and E. Sizova, Transformation of microbiota of fish intestines and gills against the background of molybdenum oxide nanoparticles in environment, International Journal of Environmental Science and Technology, 2020, 17, 721-732.
Fish
An Evaluation of Molybdenum Toxicity to the Oligochaete, Tubifex tubifex, and Early-Life Stages of Brown Trout, Salmo trutta
Limited data are available describing the aquatic toxicity of molybdenum in freshwater environments, making it difficult to assess the aquatic risk to freshwater organisms. In order to increase available information on the aquatic toxicity of molybdenum, a 96-h LC50 test with the oligochaete Tubifex tubifex and an 85-day development test using brown trout, Salmo trutta, were conducted. The T. tubifex test resulted in an LC50 value of 2782 mg/L. No adverse effects were observed on brown trout survival or length in the concentrations tested, however an IC10 value for growth (wet weight) was determined to be 202 mg/L. Whole body fish tissue concentrations for molybdenum increased in all treatment concentrations tested, although bioconcentration factors decreased at greater exposure concentrations, and ranged from 0.13 at an exposure concentration of 20 mg/L to 0.04 at an exposure of 1247 mg/L. A body burden of 26.0 mg/kg was associated with reduced wet weight.
Lucas, B. T., Quinteros, C., Burnett-Seidel, C., and Elphick, J. R.,An Evaluation of Molybdenum Toxicity to the Oligochaete, Tubifex tubifex, and Early-Life Stages of Brown Trout, Salmo trutta, Bulletin of Environmental Contamination and Toxicology, 2017, 98, 747-752.
Toxicological Testing Programme: Aquatic organisms
IMOA Toxicological Testing Programme: Aquatic organisms
Substance | Toxicity/ mg/l |
acute fisha | acute daphnidsb | algal growthc |
96 h LC50 |
48 h EC50 |
72 h IC50 |
Molybdenum trioxide (pure) |
130 |
150 |
100 |
Molybdenum trioxide (tech)d |
77 |
88 |
100 |
Ammonium dimolybdatee |
420 |
140 |
41 |
Sodium molybdate |
7600 |
330 |
>100 |
Risk phrase required if: |
<100 |
<100 |
< 100 |
Notes
a Acute fish toxicity is representive of relative toxicity to aquatic vertebrates. Trout used because of large data base and sensitivity. Rainbow trout (10/concentration) exposed to various concentrations under semi-static conditions for 96 hours.
b Acute daphnia toxicity is representative of relative toxicity to aquatic invertebrates. Dapnids are ubiquitous thoughout the world in fresh water ponds and lakes, important link in food chain. Daphnids (20/concentation) exposed to various concentrations under static conditions for 48 hours. Daphnids observed for immobilization and Effective Concentration, EC50 calculated.
c Algal growth inhibition is representative of relative toxicity to aquatic plants. Algae are primary producers in the food chain. Inhibition can alter food web and reduce productivity of ecosystems. Stimulation may cause algal blooms, causing anoxic conditions, negative anaesthetic effects, etc. Test cultures of algae were prepared and added to solutions of test material and incubated for 72 hours. Growth was monitored by measuring the absorbance of each culture at 665 nm. The median effective concentration for inhibition of growth (IC50 ) after 72 hours was calculated.
d The aquatic toxicity of technical oxide varied with the level of impurities, particularly copper. High copper content samples gave lower results in the daphnia studies.
e The toxicity of ammonium molybdate to algae is not unexpected considering the the known toxicity of ammonia, which is commonly used as a bactericide and disinfectant.
Acute toxicities of molybdenum compounds towards fish
Acute toxicities of molybdenum compounds towards fish
LD50/mg/l |
Compound | Species | 24h | 48h | 96h | No effect Level |
MoO3[1] |
bluegill |
87-120 |
87-120 |
87 |
75 |
|
rainbow trout |
102 |
65-87 |
65-87 |
65 |
Ammonium dimolybdate[2] |
bluegill |
166 |
157 |
157 |
140 |
|
rainbow trout |
138 |
135 |
120 |
87 |
Sodium molybdate [2] |
bluegill |
> 10,000 |
- |
6,790 |
2,400 |
|
rainbow trout |
> 10,000 |
- |
7,340 |
3,200 |
|
channel catfish |
> 10,000 |
- |
> 10,000 |
7,500 |
|
fathead minnow |
> 10,000 |
- |
7,630 |
5,600 |
Sodium molybdate [3] |
shrimp |
3997 |
- |
- |
- |
|
minnow |
6590 |
- |
- |
- |
|
American oyster (EC50) |
3526 |
- |
- |
- |
[1] Bentley, R. E., Acute Toxicity of Ammonium Molybdate and Molybdic Trioxide to Bluegill (Lepomis macrochirus) and Rainbow Trout (Salmo gairdneri),Bionomics, Wareham, Massachusetts, 1975, January
[2] Bentley, R. E., Acute Toxicity of Sodium Molybdate to Bluegill (Lepomis macrochirus), Rainbow Trout (Salmo gairdneri), Fathead Minnow (Pimephales promeals), Channel Catfish (Ictalurus punctatus), Water Flea (Daphnia magna) and Scud (Gammarus fasciatus),Bionomics, Wareham, Massachusetts, 1973, December.
[3] Knothe, D. W. and van Riper, G. G., Bull. Environ. Contam. and Toxicol., 1988, 40, 785.
Sodium molybdate was found to be significantly less toxic to several varieties of fish than either molybdic oxide or ammonium dimolybdate [ Bentley, 1973; 1975].
Bentley, R. E., Acute Toxicity of Sodium Molybdate to Bluegill (Lepomis macrochirus), Rainbow Trout (Salmo gairdneri), Fathead Minnow (Pimephales promeals), Channel Catfish (Ictalurus punctatus), Water Flea (Daphnia magna) and Scud (Gammarus fasciatus), Bionomics, Wareham, Massachusetts, 1973.
Bentley, R. E., Acute Toxicity of Ammonium Molybdate and Molybdic Trioxide to Bluegill (Lepomis macrochirus) and Rainbow Trout (Salmo gairdneri), Bionomics, Wareham, Massachusetts, 1975.
The purpose of the study was to resolve inconsistencies in reported bioassays of the toxicity of molybdenum (as sodium molybdate in water) to fertilized rainbow trout eggs and alevins (EA) for which a wide toxicity range (LC50 0.73 to >90 mg/L Mo) has been reported. Molybdenum was not acutely toxic to the early life stages of rainbow trout (32 d, maximum molybdenum concentration 400 mg l-1). When early life stages of rainbow trout were exposed to a maximum molybdenum concentration of 1500 mg l-1 for 32 d there was not sufficient mortality for an LC50 to be calculated. The importance of careful control of the water chemistry in the bioassay was emphasized.
Davies, T. D., Pickard, J., and Hall, K. J., Acute molybdenum toxicity to rainbow trout and other fish, Journal of Environmental Engineering and Science, 2005, 4, 481-485.
The benthic [sediment] organismsChironomus plumosus larvae andTubifex tubifex worms may be used as aquatic toxicity indicators of metals which may accumulate in freshwater sediments as a consequence of heavy metal contamination of water. The LC50 values after 96 h are given in the Table. The tests were carried out in boiled tap water (20 C, pH 7 - 8, calcium carbonate hardness 80 mg l-1). Molybdate (supplied as ammonium hepatamolybdate) is the least toxic of the metals on both a mass and molar basis and is non-toxic, its LC50 value being less than concentrations found in the environment.
Toxicities of metals towards aquatic organisms
| C. plumosus | T. tubifex |
Compound |
103LC50/mg l-1 |
103LC50/ mol l-1 |
103LC50/mg l-1 |
103LC50/ mol l-1 |
V2O5 |
218 |
4.28 |
211 |
4.14 |
(NH4)6Mo7O24.4H2O |
455 |
4.74 |
4563 |
47.6 |
MnSO4.H2O |
68 |
1.24 |
295 |
5.37 |
NiSO4.7H2O |
266 |
4.53 |
537 |
9.15 |
CuSO4.5H2O |
0.105 |
0.00165 |
2 |
0.0315 |
Cu2Cl2 |
0.927 |
0.0146 |
6 |
0.0945 |
Fargasova, A, Comparative acute toxicity of Cu2+, Cu+, Mn2+, Mo6+, Ni2+ and V5+ to Chironomus plumosus larvae and Tubifex tubifex worms, Biologia, 1998, 53, 315-319.
Mo toxicity towards flannelmouth sucker
Larval flannelmouth sucker (Catostomus latipinnis) were exposed to inorganics which simulated environmental ratios reported for sites along the San Juan River. The toxicity rank order was copper > zinc >vanadium > selenite > selenate > arsenate > uranium > boron > molybdenum.
Hamilton, S.J., Buhl, K.J., Hazard evaluation of inorganics, singly and in mixtures, to flannelmouth sucker Catostomus latipinnis in the San Juan River, New Mexico, Ecotoxicology And Environmental Safety, 1997, 38, 296-308.
Molybdates are alternatives to toxic chromates in industrial applications, e.g. passivation of zinc coatings in the automobile industry. Molybdates are much less toxic than chromates although both molybdenum and chromium and their compounds are included in th List II of European dangerous substances directive (Council of the European Communities (1976). Directive of 4 May 1976 on Pollution Caused by Certain Dangerous Substances and Discharged into the Aquatic Environment of the Community (76/464/EEC, OJL 129, 18 May). The purpose of the work described in this paper was to compare the aquatic acute and chronic toxicity of Mo and Cr in standard tests with the organism Daphnia magna, and in acetylcholinesterase inhibition.
Acute toxicity towardsDaphnia magnain ASTM hard water
Chemical | 48 h LC50/mg L-1 | 95% confidence limit |
Sodium dichromate |
0.29 |
0.269-0.315 |
Sodium molybdate |
2848 |
2839-2857 |
Chronic toxicity towardsDaphnia magnain ASTM hard water
Chemical | Total growth | Reproduction | Mortality |
NOEC /mg L-1 | LOEC /mg L-1 | EC50 /mg L-1 | NOEC /mg L-1 | LOEC /mg L-1 | EC50 /mg L-1 | NOEC /mg L-1 | LOEC /mg L-1 | EC50 /mg L-1 |
Sodium dichromate |
0.0125 |
0.025 |
0.233 |
0.0125 |
0.025 |
0.047 |
0.075 |
0.01 |
0.524 |
Sodium molybdate |
50 |
75 |
204 |
50 |
75 |
102 |
75 |
100 |
255 |
Daphnia magnaacetylcholinesterase inhibition in vivoa
Chemical | NOEC/mg L-1 | LOEC/mg L-1 | EC50 /mg L-1 |
Sodium dichromate |
0.075 |
0.15 |
0.632 |
Sodium molybdate |
750 |
1500 |
26.5 |
a No inhibition in vitro
The study shows that sodium molybdate is much less toxic towardsDaphnia magna than is sodium dichromate.
Diamantino, T.C., Guilhermino, L., Almeida, E., and Soares, A. M. V. M., Toxicity of sodium molybdate and sodium dichromate to Daphnia magna Straus evaluated in acute, chronic, and acetylcholinesterase inhibition tests, Ecotoxicology and Environmental Safety, 2000, 45, 253-259.