
PHOSPHORITES
519
Dullien, F.A.L., 1979. Porous Media: Fhdd Transport and
Pore
Struc-
ture, 2nd edn, Academie Press.
Ehrlieh, R., Crabtree, S.J., Kennedy, S.K., and Cannon, R.L., 1984.
Petrographic image analysis I—analysis of reservoir pore com-
plexes. Journal of Sedimentary Petrology, 54 (4): 1365-1376.
Ehrlich, R., Horkowitz, K.O., Horkowitz, J.P., and Crabtree, S.J.,
1991a. Petrography and reservoir physies 1: objective elassification
of reservoir porosity. American Association of Petroleum Geologists
Bulletin, 75 (10): 1547-1562.
Ehrlich, R., Etris, E.L., Brumfield, D., and Yuan, L.P., 1991b.
Petrography and reservoir physies III: physical models for
permeability and formation factor. American Association of
Petro-
leum Geologists Bulletin, 75 (10): 1579-1592.
Etris,
E.L., Brumfield, D.S., and Egrlich, R., 1989. Petrographic
insights into the relevance of Archie's Equation: formation factor
without "M" and "A". SPWLA Journal Thirtieth Annual Logging
Symposium, June, 1989, I (F): pp. 1-18.
Ferm, J.B., Ehrlich, R., Kranz, R.L., and Park, W.C., 1990. The
relationship between petrographie image analysis data and fracture
toughness. Association of Engineering Geologists Bulletin, 27 (3):
327-339.
Graton, L.C., and Fraser, H.J., 1935. Systematic packing of spheres
with particular relation to porosity and permeability. Journal of
Geology, 43: 785-909.
Johnson, G.W., Ehrlich, R., and Full, W., 2001. Prineipal component
and receptor models. In Murphy, and Morrison (eds.). Introduc-
tion to Environmental
Eorensics.
Academic Press, Chapter 12 pp
46i-51fi.
MeCreesh, C.A., Ehrlich, R., and Crabtree, S.J., 1991. Petrography
and reservoir physics II: relating thin section porosity to capillary
pressure: the association between pore types and throat size.
American Association of Petroleum Geologists Bulletin, 75 (10)-
1563-1578.
Prince, C.R., Ehrlich, R., and Anguy, Y., 1995. Analysis of spatial
order in sandstones II: grain clusters, packing flaws, and the small-
scale structure of sandstones. Journal of Sedimentary Research,
A65:
13-2^8.
Prince, CM., and Ehriich, R., 2000. A test of hypotheses regarding
quartz cementation in sandstones: a quantitative image analysis
approach. In Worden, R. (ed.). Quartz Cementation in Sandstones,
IAS Special Publication, 29.
Seheidegger, A.E., 1974. The Physics of FlowThrough
Porous
Media, 3rd
edn. University of Toronto Press, 353pp.
Cross-references
Fabric, Porosity, and Permeability
Sands, Gravels and their Lithifled Equivalents
PHOSPHORITES
Introduction
Phosphorites are rocks enriched in phosphorus relative to
average erustal abundances, an enhancement usually expressed
in terms of P2O5 concentrations. Whereas the average P2O5
content of condnental crustal rocks is esdmated as 0.23
percent (Ronov and Yaroshevsky, 1969) and sedimentary
rocks average 0.03-0.16 percent (McKelvey, 1973), rocks
typically designated as phosphorites have 15-37 percent P2O5
(Bentor, 1980). Phosphorites thus have phosphate contents
that are 60 to 160 times greater than the crustal average and
on the order of 100 to over 1,000 times greater than the
averages for common sedimentary rocks. The most conten-
tious issues concerning phosphorites center on the mechanism
or mechanisms by which this enrichment has taken place in
the geologic past and whether formation of phosphorites
represents a significant perturbation of the biogeochemical
cycle for phosphorus, questions discussed below.
The element phosphorus averages about 70 ppb
(~ 2.3 umol/L) in seawater, is a limiting nutrient to biological
productivity on geological dmescales, and regulates the global
carbon cycle and climate. Because of its low abundance and
because it is closely tied to short-lived biological-chemical
cycles of growth and decay, phosphorus has a relatively brief
residence time in the ocean, estimated for the surface ocean by
Mackenzie etal. (1993) as 0.07 years based on phytoplankton
uptake. The overall oceanic residence time for phosphorus is
estimated to range between ca. 10,000 years and 40,000 years
(Delaney, 1998; Colman and Holland, 2000; Guidry et al.,
2000).
Initial interest in phosphorites stemmed from their impor-
tance as a raw material for the production of fertilizer
phosphate. Along with potassium and nitrogen, phosphorus
is critical for plant growth; but, whereas K and N are readily
available from several sources (seawater, evaporite deposits,
the atmosphere), phosphorus can only be obtained in large
quantities from phosphorite deposits. Following the discovery
in the mid-19th Century of the role of mineral nutrition in
plant metabolism by the German chemist Justus von Liebig,
phosphorite deposits began to be exploited after more readily
available P sources such as guano, manure, and crushed bones
became inadequate to support expanding agricultural systems.
Phosphorites are now the main source of fertilizer P, and
mining of phosphorites is a world-wide enterprise, with major
eenters of production in the USA, Morocco, and several
countries in the Middle East. Excluding China, global
production in 2000 was close to 92,200 thousand metric tons
(IFA, 2001).
The main mineral in phosphorites is carbonate fluorapatite
(CFA) or francolite, which according to Slansky (1986) has the
simplified general formula Caio[(P04)6_x(C03)JF2+x, with
numerous substitutions of both cations and anions (Nathan,
1984;
Jarvis etal., 1994). The most important ancient deposits
are marine, granular phosphorites that formed in continental
margin or epeiric sea settings (Figure P5). Two of the key
questions about this kind of phosphorite concern: (1) phos-
phogenesis: how do CFA particles initially form in marine
environments? (2) concentration: how do such particles become
dominant in granular phosphorites?
Phosphogenesis
Studies in modern environments in which CFA forms have
demonstrated that this rnineral commonly precipitates during
early diagenesis in the upper few tens of centimeters of
sediment. The most notable of these environments are the
continental margins of Peru, Baja California [Mexico], south-
west Africa, and eastern Australia. Whereas the first three of
these are regions of pronounced eastern boundary currents,
strong coastal upwelling, prominent oxygen minimum zones,
and organic-rich sedimentation (1-20 percent organic carbon),
the eastern Australia margin is an area of low productivity,
oxygen-rich bottom waters, and sediments low in organic
matter (<0.5 percent organic carbon). These differences
suggest that CFA may form in different ways, depending
upon the environmental conditions. Studies of Peru margin
sediments, for example, have linked phosphogenesis with high
organic carbon burial rates and anoxie diagenesis (Burnett,
1977).
In this setting, microbial degradation of organic matter