The current, ongoing, intensive development of the international phosphate industry is destined to impinge onto at least two major aspects of nuclear energy in the immediate future. The first contact will come in the evaluation of the economic viability and potential sustainability of sedimentary phosphorites as a secondary source for uranium. The second impact will be in the determination of whether or not there exists significant uranium contamination in the utilization of phosphate fertilizers on agricultural systems. There are no adequate substitutes for phosphatic fertilizers. Phosphorous derived from these fertilizers is absolutely essential for the maintenance, growth, and yield of crop plants as well as the survival of all living systems. If the current (6.748 billion), let alone projected, global population (±9 billion, 2040) is without a continuing, uninterrupted, and increasing supply of this ubiquitous commodity for the agricultural system, the world will face certain global famine. The most severely impacted will be those emerging and third world tropical nation-states with phosphate-poor soil systems. The fundamental reason we have been able to feed the bulk of humanity today and avoid a predicted Malthusian future famine is in large part due to the use of phosphate fertilizers. Accompanying the benefits of phosphate-based fertilizers are potentially serious side effects that need to be examined. Phosphate based fertilizers contain heavy metals, led by uranium. Some of the resulting problems are the questions of: the quantitative dimensions of uranium contained in phosphate fertilizers that is lost into the environment (soil and aqueous systems) and how, whether, and under what conditions does the metal enter the biosphere’s food chain (animals, plants, and water). Therefore, the downside to the use of phosphate fertilizers is that the uranium in those fertilizers can be transferred to agricultural systems and subsequently to ground- and running-water systems. The potential resultant impact of this on plant life systems is and will continue to be subject to continuing research. In view of the environmental consequences of continued reliance on fossil fuels, the shift to the extensive development of nuclear power seems inevitable. Given the current national and international conditions, it’s necessary to carefully examine the political and economic ramifications of such a shift. Competing alternatives of wind (cost and reliability), solar (cost and size), and hydro (at near capacity) will not even
[1]
T. Bituh,et al.
Radioactive contamination in Croatia by phosphate fertilizer production.
,
2009,
Journal of hazardous materials.
[2]
E. Schnug,et al.
Uranium balances in agroecosystems
,
2008
.
[3]
D. Manning.
Phosphate Minerals, Environmental Pollution and Sustainable Agriculture
,
2008
.
[4]
Franz J. Dahlkamp,et al.
Uranium Ore Deposits
,
1993
.
[5]
F. H. Attix.
Introduction to Radiological Physics and Radiation Dosimetry
,
1991
.
[6]
E. Schnug,et al.
Loads and Fate of Fertilizer-derived Uranium
,
2008
.
[7]
J. Pasteris,et al.
Bone and Tooth Mineralization: Why Apatite?
,
2008
.
[8]
E. Oelkers,et al.
Phosphate Mineral Reactivity and Global Sustainability
,
2008
.
[9]
F. Khan.
The physics of radiation therapy
,
1985
.
[10]
I. Iiyama,et al.
Distribution of uranium in soil components of agricultural fields after long-term application of phosphate fertilizers.
,
2009,
The Science of the total environment.
[11]
D. Leikam,et al.
Phosphate Fertilizers: Production, Characteristics, and Technologies
,
2015
.
[12]
S. J. van Kauwenbergh,et al.
Cadmium and Other Minor Elements in World Resources of Phosphate Rock
,
1997
.
[13]
E. Schnug,et al.
A critical evaluation of phytoextraction on uranium-contaminated agricultural soils
,
2008
.