n plants
2 photo-
such
jara
lants
lumines-
lity in
sS, but
re most
r were
and
ted
Fluoride
intra-
1ical and
arge
ted to
69,
er in
i,
was
tes
eed
nolyb-
pm
S :that
f lead
from
rences
ally
terial
)spect-
-eveals
1atic
| to
ing
imited
«the
To assess the application of the FLD in prospecting for phosphate
rocks, the luminescence of ten samples of phosphate rocks from several
geographic locations were measured with the laboratory fluorescence
spectrometer at the 486.1 nm Fraunhofer line. All samples luminesced
within the sensitivity range of the FLD. That the FLD is sensitive to
luminescing phosphate rock was later confirmed in an airborne test over
a sedimentary phosphate area in southern California. Although both
gypsum and phosphatic soils luminesced at approximately equivalent
values, it was possible to distinguish them from remote positions
because of their significantly different reflectance.
In order to quantify the luminescence of selected oils in terms
of rhodamine WI equivalence, the excitation spectra of 29 crude oils
and 20 refined oils were measured with the laboratory fluorescence
spectrometer by Watson and others (1974). The results of these studies
suggest:
1. The luminescence of the 3 um and 10 um films of the lower
specific gravity oils (0.7317 to 0.8327) is significantly less than that
of the bulk oil.
2. At specific gravities of 0.8752 or greater, luminescence of the
films approaches that of the bulk oil.
3. The peak luminescence of the 3 um and 10 ym films shows a
spectral shift toward the blue end of the wavelength spectrum for the
low specific gravity oils and toward the red end of the spectrum for the
higher specific gravity oils.
4. Comparison of luminescence of the 3 um and 10 um films at the
six Fraunhofer wavelengths suggest that the thickness of an oil film can
be determined for specific gravities of 0.8327 and lower.
5. For oils of specific gravity of 0.9752 and heavier, the
difference in luminescence between the film and bulk oil is negligible.
In an airborne test, the FLD successfully discriminated natural
seeps of oil from apparently uncontaminated seawater in the Santa
Barbara Channel, California.
Spent sulfite liquor is produced as a waste material in the process
of making paper from wood pulp. Disposal of the material into rivers
and estuaries constitutes a severe water pollution problem in areas
where numerous paper mills are located. The spent sulfite liquors are
injurious to fish due to the high oxygen demand of the liquors (Almgren
and Josefsson, 1973).