Molybdenum in Human Health
Industrial and Environmental Exposure of Humans
Humans are exposed to molybdenum compounds in industrial operations and in the environment. As with other elements maximum exposure limits for molybdenum are laid down in government legislation and regulatory controls. The limits may vary from country to country and are not always consistent. The basis for the limits is not always clear. Here we list the regulatory limits, the natural levels of molybdenum and the levels derived from industrial activity including mining.
Mo uptake from industrial sources
Average daily intakes of Mo 0.1 – 0.5 mg Mo increasing to 1 mg if contamination from industrial sources
Friberg, L., Lener, J., Molybdenum, in Handbook on the Toxicology of Metals Vol II, Friberg, L., Nordberg, G.F., and Vouk, V.B., eds., Elsevier, 1986, 446 – 461.
56 adults in Germany 47 – 89 microg
Anke, M., Groppel, B., Krause, U., Arnhold, W., Langer, M., Trace element intake of humans , J. Trace Elemen. Electrolytes Health Dis., 1991, 5, 69 – 74.
Adults in Denver 120 – 240 microg Mo/d av 180
Tsongas, T.A., Meglen, R.R., Walravens, P.A., Chappell W.R., Molybdenum in the diet, Am. J. Clin. Nutr., 1980, 33, 1103 –1107.
NE US 74 – 126 microg Mo/d
Pennington, J.A.T., Young, B.E., Wilson, D., Nutritional elements in US diets, J. Am. Diet. Assoc., 1989, 89, 659 – 664.
For guinea pigs exposed to the dust or fumes of molybdenum trioxide (150-300 mg/m3) for 1 h per day, 5 times per week, for 5 weeks [Fairhall et al., 1945]. Low concentrations of molybdenum (20-270 microg/10g fresh tissue) were found in the lungs, liver, kidneys, spleen and bone. The molybdenum concentrations in these tissues decreased after exposure was stopped to 20% of the original level after 2 weeks. After an oral gavage dose of 50 mg molybdenum trioxide was administered to guinea pigs, molybdenum was distributed to the kidneys, spleen, blood, bile, liver, and lungs within 4 h. The concentrations of molybdenum in the organs decreased, whereas in the blood and bile molybdenum titres were higher at 48 h. Bone retained molybdenum longer than any other tissues [Fairhall et al., 1945]. Based on the amount recovered in faeces for up to 48 h, Fairhall et al. (1945) calculated that 85 % of the oral dose was absorbed. Excess hexavalent forms of molybdenum are excreted rapidly through the kidneys and the bile. Twice as much molybdenum is eliminated in urine as in the faeces. The urinary and faecal concentrations of molybdenum returned to normal after an oral dose of molybdenum trioxide was administered to guinea pigs [Fairhall et al., 1945]. The predominant urinary metabolite of molybdenum was in the form of molybdate complexes [Venugopal and Luckey, 1978].
Fairhall, L. T., Dunn, R. C., Sharpless, N. E. and Pritchard, E. A., U. S. Public Health Bull., 1945, 293, 1.
Venugopal, B. and Luckey, T. D., Metal Toxicity in Mammals, 1978, Vol. 2, Chemical Toxicity of Metals and Metalloids, Plenum Press, New York.
Regulatory controls and legislation
| Metal |
TLV/mg Mo/m3 |
|
| |
soluble |
insoluble |
| molybdenum |
5 |
10 |
| tungsten |
1 |
5 |
| iron oxide |
|
5 |
| tantalum |
|
5 |
| nickel |
0.1 |
1 |
| copper dust |
1 |
1 |
| copper fume |
|
0.2 |
| chromium |
|
0.5 |
| lead |
0.15 |
0.15 |
| cobalt |
0.02 |
0.02 |
| chromium(VI) |
0.05 |
0.01 |
| cadmium |
0.01 |
0.01 |
| arsenic |
0.01 |
0.01 |
TLV, threshold limit value
International Molybdenum Association (IMOA), Report 1995, p. 5
| Process or material |
Limit |
Units |
Averaging period |
Source of limit |
Air emission |
||||
| Dust collectors |
15 |
mg Mo dust/m3 |
|
Holland-permit |
| Calciner dust collector |
0.126 |
kg Mo oxide/h |
|
Holland-permit |
| Dryer dust collector |
0.024 |
kg ADM/h |
|
Holland-permit |
| As dust |
10 |
mg/m3 |
|
NER (Dutch emission guidelines) |
| Soluble compounds |
5 |
mg Mo/m3 |
|
UK Health and Safety Executive |
| Insoluble compounds |
10 |
mg Mo/m3 |
|
UK Health and Safety Executive |
| Exhaust air from production plants |
5 |
mg Mo/m3 |
0.5 - 3 h total |
Austria |
| For non-ferrous metals after filter stations |
0.2 |
mg Mo/m3 |
0.5 - 3 h |
Austria-regional authority |
| Soluble Mo TLV |
5 |
mg Mo/m3 |
0.5 - 3 h |
Austria |
| Insoluble Mo TLV |
15 |
mg Mo/m3 |
0.5 - 3 h |
Austria |
Water quality |
||||
| Drinking |
0.07 |
mg/l |
|
Austria-WHO guideline |
| |
0.01 |
mg/l |
|
Chile-N Ch 1333 - 1978 |
| Industrial |
1 - 2 |
kg/day |
|
Holland-permit |
| |
5 |
mg/l |
|
Austria-country |
| |
5 |
mg/l |
2 h average |
Germany-municipal authorities |
| Ground |
300 |
mg/l |
|
Holland-intervention values |
| |
5 |
ppm |
|
Holland-authorisation |
| |
none |
|
|
Belgium-80/68/EEC |
| |
0.1 |
mg/l |
|
US EPA |
| |
0.07 |
mg/l |
|
Japan |
| target limit |
5 |
mg/l |
|
Belgium-MILBOWA (DBO 07494013) |
| intervention limit |
300 |
mg/l |
|
Belgium-MILBOWA (DBO 07494013) |
Soil |
||||
| soil sanitation |
200 |
mg/kg |
|
Holland-intervention values |
| arableland pastures |
10 |
mg/kg dry |
|
Austria-TLV |
| |
30 |
kg/ha |
|
Austria-TLV |
| |
3 |
g/m2 |
|
Austria-TLV |
| target limit |
10 |
mg/kg dry |
|
Belgium-MILBOWA (DBO 0749013) |
| intervention limit |
200 |
mg/kg dry |
|
Belgium-MILBOWA (DBO 0749013) |
| emission limit |
150 |
mg/kg dry |
|
Belgium-MILBOWA (DBO 0749013) |
Solid waste |
||||
| waste |
5000 |
mg/kg |
|
Holland-(BAGA) |
| to landfill |
50 |
mg/l |
|
Germany-approval DIN 38414 |
| landfill leachate limit |
125 |
mg/kg dry |
|
OVAM proposals to Belgium Government |
| leachate limit |
35 |
mg/m2 |
|
OVAM proposals to Belgium Government |
| |
150 |
mg/m3/100y |
|
Belgium-NEM 7340 Decision 23/11/95 |
| sludge from dredging |
10 |
mg/kg dry |
|
Belgium-Decision 25/11/93 |
| fly ash leachate limit |
3 |
mg/kg |
|
Belgium- NEM 7343 Decision 20/1/93 |
Sewage sludge |
||||
| agricultural disposal |
20 |
mg/kg dry |
|
Austria |
| |
0.5 |
mg/l |
|
Chile |
| land application ceiling concentration |
75 |
mg/kg |
|
US EPA |
Milk |
||||
| |
0.2 |
mg/kg |
|
Austria |
Data assembled by IMOA Health and Safety Committee, 1999.
| Country |
MAC Limit (mg/m3) |
|
Insoluble molybdenum compounds |
||
| Holland |
10 (mean) |
|
| Romania |
5 (mean) |
|
| Germany |
15 (mean) |
|
| Russia (USSR), Hungary, Bulgaria |
6 (peak) |
|
| USA |
20 (peak) |
10 as TWA |
Soluble molybdenum compounds |
||
| Holland |
5 (mean) |
|
| Romania |
2 (mean) |
|
| Germany, USA, Austria, Belgium, Italy |
5 (mean) |
|
| Russia (USSR), Bulgaria, Poland |
4 (peak) |
|
| Romania, USA |
10 (peak) |
5 as TWA |
ILO, Occupational Exposure Limits, 2nd (revised) Ed., Occupational Safety and Health Series, 1980, 37, ILO Geneva.
| Material |
TLV-TWA /mg m-3 |
Soluble Morespirable particulate |
0.5 |
Insoluble Moinhalable particulate |
10 |
Threshold Limit Values and Biological Exposure Indices for 2001: American Conference of Governmental Industrial Hygienists (ACGIH), Cincinatti, Ohio, 2001.
The number of workers in the United States potentially exposed to molybdenum trioxide during the years 1981 to 1983 was approximately 17,072
National Occupational Exposure Survey (NOES): National Institute for Occupational Safety and Health (NIOSH), 1995.
Occupational standards of exposure established by the Occupational Safety and Health Administration (OSHA) are 5 mg/m3 for soluble molybdenum compounds and 15 mg/m3 for insoluble molybdenum compounds
Hammond, P.B. and Beliles, R.P. Metals. In Casarett and Doull's Toxicology:The Basic Science of Poisons ,ed. Doull, J., Klaasen C. D. and Amdur, M. O., Macmillan, New York, 2nd Ed. 1980, 409.
The American Conference of Governmental Industrial Hygienists [ACGIH, 1995, 2001] recommends a threshold limit value-time-weighted average of 5 mg/m3 for soluble molybdenum compounds and 10 mg/m3 for insoluble molybdenum.