U.S. Department of the Interior
U.S. Geological Survey
Vanadium
https://pubs.usgs.gov/pp/1802/u/pp1802u.pdf
An Excerpt:
Vanadium
By Karen D. Kelley, Clinton T. Scott, Désirée E. Polyak, and Bryn E. Kimball
Abstract
Vanadium is used primarily in the production of steel
alloys; as a catalyst for the chemical industry; in the making of
ceramics, glasses, and pigments; and in vanadium redox-flow
batteries (VRBs) for large-scale storage of electricity. World
vanadium resources in 2012 were estimated to be 63 million
metric tons, which include about 14 million metric tons of
reserves. The majority of the vanadium produced in 2012
was from China, Russia, and South Africa.
Vanadium is extracted from several different types of
mineral deposits and from fossil fuels. These deposits include
vanadiferous titanomagnetite (VTM) deposits, sandstonehosted vanadium (with or without uranium) deposits (SSV
deposits), and vanadium-rich black shales. VTM deposits are
the principal source of vanadium and consist of magmatic
accumulations of ilmenite and magnetite containing
0.2 to 1 weight percent vanadium pentoxide (V2
O5). SSV
deposits are another important source; these deposits have
average ore grades that range from 0.1 to greater than 1 weight
percent V2
O5
. The United States has been and is currently the
main producer of vanadium from SSV deposits, particularly
those on the Colorado Plateau. Vanadium-rich black shales
occur in marine successions that were deposited in epeiric
(inland) seas and on continental margins. Concentrations in
these shales regularly exceed 0.18 weight percent V2
O5
and
can be as high as 1.7 weight percent V2
O5
. Small amounts
of vanadium have been produced from the Alum Shale in
Sweden and from ferrophosphorus slag generated during the
reduction of phosphate to elemental phosphorus in ore from
shales of the Phosphoria Formation in Idaho and Wyoming.
Because vanadium enrichment occurs in beds that are typically only a few meters thick, most of the vanadiferous black
shales are not currently economic, although they may become
an important resource in the future. Significant amounts of
vanadium are recovered as byproducts of petroleum refining,
and processing of coal, tar sands, and oil shales may be
important future sources.
Vanadium occurs in one of four oxidation states in nature:
+2, +3, +4, and +5. The V3+ ion has an octahedral radius that
is almost identical to that of Fe3+ and Al3+ and, therefore, it
substitutes in ferromagnesian minerals. During weathering,
much of the vanadium may partition into newly formed clay
minerals, and it either remains in the +3 valence state or
oxidizes to the +4 valence state, both of which are relatively
insoluble. If erosion is insignificant but chemical leaching is
intense, the residual material may be enriched in vanadium,
as are some bauxites and laterites. During the weathering
of igneous, residual, or sedimentary rocks, some vanadium
oxidizes to the +5 valence state, especially in the intensive
oxidizing conditions that are characteristic of arid climates.
The average contents of vanadium in the environment
are as follows: soils (10 to 500 parts per million [ppm]);
streams and rivers (0.2 to 2.9 parts per billion [ppb]); and
coastal seawater (0.3 to 2.8 ppb). Concentrations of vanadium
in soils (548 to 7,160 ppm) collected near vanadium mines in
China, the Czech Republic, and South Africa are many times
greater than natural concentrations in soils. Additionally, if
deposits contain sulfide minerals such as chalcocite, pyrite,
and sphalerite, high levels of acidity may be present if sulfide
dissolution is not balanced by the presence of acid-neutralizing
carbonate minerals. Some of the vanadium-bearing deposit
types, particularly some SSV and black shale deposits, contain
appreciable amounts of carbonate minerals, which lowers the
acid-generation potential.
Vanadium is a micronutrient with a postulated requirement for humans of less than 10 micrograms per day, which
can be met through dietary intake. Primary and secondary
drinking water regulations for vanadium are not currently in
place in the United States. Vanadium toxicity is thought to
result from an intake of more than 10 to 20 milligrams per
day. Vanadium is essential for some biological processes
and organisms. For example, some nitrogen-fixing bacteria
require vanadium for producing enzymes necessary to convert
nitrogen from the atmosphere into ammonia, which is a more
biologically accessible form of nitrogen.
U2 Critical Mineral Resources of the United States—Vanadium
Introduction
Vanadium (V) is a strategic metal that is used principally
in the production of metal alloys, such as high-strength steel
and alloys for use in the aerospace industry. Secondary uses
are as catalysts for the chemical industry, and in ceramics,
glasses, and pigments. In its native state, vanadium is a hard,
silvery gray, ductile, and malleable transition metal. Vanadium
consumption trends are heavily influenced by trends in
steel production.
The emerging need for large-scale electricity storage
makes vanadium redox-flow batteries (VRBs) a major
potential future use of vanadium. Because of their largescale storage capacity, development of VRBs could prompt
increases in the use of wind, solar, and other renewable, intermittent power sources. Lithium-vanadium-phosphate batteries
produce high voltages and high energy-to-weight ratios, which
make them ideal for use in electric cars. Vanadium use in
lithium batteries is expected to increase to 1,700 metric tons
in 2017 from 200 metric tons in 2012 (Perles, 2013).
Vanadium is the 22d most abundant element in Earth’s
crust, and it is an essential constituent of many minerals. A
total of 156 minerals contain vanadium as a major (>10 weight
percent) constituent. Several diverse mineral deposit types
contain vanadium-bearing minerals, and vanadium is a
common component of petroleum and other fossil fuels.
Vanadium deposits are globally distributed (fig. U1) and
comprise four principal deposit types: vanadiferous titanomagnetite (VTM), sandstone-hosted vanadium (SSV),
shale-hosted vanadium, and vanadate deposits (table U1).
Additionally, significant amounts of vanadium are available
for commercial use as a byproduct of petroleum refining, and
processing of coal, tar sands, and oil shales may be important
future sources. World vanadium resources in 2012 were
estimated to be 63 million metric tons of vanadium. Reserves
were estimated to be 14 million metric tons. The majority of
vanadium production in 2012 was from China (37 percent),
South Africa (35 percent), and Russia (25 percent) (fig. U2;
Polyak, 2013).
Uses and Applications
The vanadium market closely follows that of the steel
industry, which in turn follows economic trends. Metallurgical
applications in steel continued to dominate United States
vanadium usage in 2011 (fig. U3), accounting for 93 percent
of reported consumption (Polyak, 2013). Vanadium is used
in steel to impart strength, toughness, and wear resistance.
The formation of vanadium-rich carbides and nitrides imparts
the strength to steel; the addition of only a few kilograms of
vanadium per ton of steel increases the strength of the steel by
as much as 25 percent. Apart from its strengthening characteristic, vanadium also inhibits corrosion and oxidation.
There are many sources of vanadium, and it is used in a
number of common products (fig. U4). Commercial products
developed through the processing of vanadium ores are mainly
ferrovanadium (FeV), which is an iron-vanadium alloy, and
vanadium pentoxide (V2
O5 ). Most vanadium is added to steel
as ferrovanadium. Ferrovanadium is available in compositions containing 45 to 50 percent vanadium and 80 percent
vanadium. The 45- to 50-percent grade is produced from slag
and other vanadium-bearing residues; the 80-percent grade is
produced by the reduction of V2
O5
.
The high-strength, low-alloy (HSLA) steels containing
vanadium are widely used for the construction of auto parts,
buildings, bridges, cranes, pipelines, rail cars, ships, and
truck bodies, including armor plating for military vehicles
(Polyak, 2012). Such HSLA steels are increasingly being
used in the oil and gas industry to meet demand for pipelines
with higher strength and higher low-temperature toughness
(Roskill Information Services, Ltd., 2010, p. 150). Vanadium
is used in tool steels in various combinations with chromium,
niobium (columbium), manganese, molybdenum, titanium,
and tungsten. Only a limited degree of substitution is possible
among these metals, however. Replacement of vanadium with
other mineral commodities requires significant technical adjustments to the steel production process to ensure that product
specifications and quality are not compromised. For example,
use of vanadium generally requires less energy consumption
during production than does niobium to give equivalent steel
properties. Therefore, substitution for vanadium is normally not
considered for short-term changes in market conditions because
of the considerable effort involved in implementing the change.
Vanadium is irreplaceable for its role in aerospace
applications because vanadium-titanium alloys have the
best strength-to-weight ratio of any engineered material
yet discovered. Vanadium, when combined with titanium,
produces a stronger and more stable alloy, and when combined
with aluminum produces a material suitable for jet engines
and high-speed airframes. No acceptable substitutes exist for
vanadium in aerospace titanium alloys.
Nonmetallurgical applications of vanadium include
catalysts, ceramics, electronics, and vanadium chemicals.
For catalytic uses, platinum and nickel can replace vanadium
compounds in some chemical processes. Vanadium dioxide
is used in the production of glass coatings that block
infrared radiation.
Vanadium is becoming more widely used in green
technology applications, especially in battery technology.
One battery technology that continues to show promise in
stabilizing energy distribution in renewable systems is the
VRB, which consists of an assembly of power cells in which
two vanadium-based electrolytes are separated by a proton
exchange membrane. The main advantages of the VRBs are
(a) their nearly unlimited capacity, which is made possible
simply by using sequentially larger storage tanks; (b) their
ability to be left completely discharged for long periods of time
with no detrimental effects; (c) the ease of recharging them
by replacing the electrolyte if no power source is available to
charge it; and (d) their ability to withstand permanent damage
if the electrolytes are accidentally mixed (Polyak, 2012).
Introduction U3
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