Therefore, stable
isotope labeled products will have an indefinitely long
shelf life: significantly longer than competing labeling methods.
Stable-isotope labeled microspheres serving as identifying markers cannot be assured to be emplaced in explosives save those legitimately produced, and then only under mandate of law or regulation.
Of course, to remove the microspheres, and markers, requires destruction of the compound.
Moreover, such explosion and attendant molecular dissociation does not truly get rid of the elemental markers, which remain (and will remain, short of atomic transmutation) as residue.
However, direct measurement of fluid(s) flow(s), such as within the
blood stream of a living animal, is often impossible.
Moreover, direct quantitative analysis of the constituent components of complex, or extensive, mixtures of fluids is often prohibitively difficult or expensive.
The expense is magnified if many samples must be taken, and analyzed, over time.
The blood, and the organs and tissues receiving blood, within a living animal present a
system that is very complex in its fluid flow patterns and dynamics, and that is difficult of direct access and measurement.
Previous systems developed for medical
blood flow analysis--discussed in greater detail hereafter--have proven to be both complex and expensive.
Because of their cost and complexity, such systems have not been found suitable for use in routine industrial or environmental fluid flow and mixing measurement problems.
However, it should be recognized that the flow of blood, or blood components, within the arteries and veins of a living animal is only different in complexity, and not in the essential nature of fluid flow dynamics, from the flows of fluids occurring within factories, ecosystems, and the like.
The main (but not the only) problem with radioisotope-labeled microspheres is
shelf life.
Radioactive microspheres thus have a time limited
shelf life, which adds a cost factor to their use.
Care must also be taken not to let too much time go by before harvesting and analyzing the tissue samples or there may be insufficient activity to determine low fluid flows due to the `
noise` threshold of a typical gamma counter used for measurement of radioactivity.
If not performed diligently experimental schedules may be disrupted.
Although due precautions are taken in transport and storage of radioactive microspheres, the constant flux of newly produced radioisotopes from manufacturer to laboratory, the controlled storage of radioisotopes still suitable for experimental use, and the long term of radioisotopes no longer suitable for use but still sufficiently radioactive so as to be unsuitably released into the environment, all involve a
biohazard.
There is typically a high minimum "per order" cost of equipments from manufacturers.
These high costs severely limit the use of radioisotope-labeled microspheres in
blood flow measurement, generally restricting its use to large laboratories and medical centers.
Second, because of the half-lives of their contained radioisotopes, radioactively-labeled microspheres have a limited shelf life typically
ranging from weeks to several months.
Third, because of the short half-lives of many radioisotopes, radioactively-labeled microspheres are typically
usable only in experiments of durations that are no more than a few weeks or months.
Sodium-
iodine (NaI) crystals provide a low-cost, sensitive gamma-
ray counting
system with intrinsically poor spacial resolution.
As a result, researchers are limited in the number of different radioactive microspheres that can be accurately measured per sample, due to overlap between the emission energies of available radiolabels.
Increasing the number of radiolabels measurements is done only at a significant loss in sensitivity and specificity.
These techniques are similar to the spectrographic analysis of a palette of dye-
colored microspheres.) p Fifth, laboratory workers using radioactively-labeled microspheres are exposed to
radiation danger.
Accordingly, the costs, and risks, involved in minimizing
radiation exposure can be substantial.
Finally, and perhaps most critically, disposal of the experimental animals poses significant problems, both logistically and financially.
The cost of disposal is becoming prohibitively high, recently
ranging to as high as $750 U.S. or more per animal.
However, due to the precautionary measures needed to minimize
radiation exposure, use of R M is restricted to specially licensed laboratories.
There are, however, significant limitations to these previous counting techniques.
First, RMBF is extrapolated from only a small aliquot of the dye-
colored microspheres (CM) actually trapped within the sample, thereby entailing a substantial
statistical error in RMBF calculations.
Third, there was considerable variation in the
diameter of the CM used in previous studies, as admitted by Hale et al.
Fourth, the prior methods require substantial time for the tedious counting of individual dye-
colored microspheres.
Automation for optical counting is expensive, typically $40-50K U.S. circa 1993 .
The method of Morita, et al. could be hampered by leaching of the
label from the microspheres over time.
Another
disadvantage is the need of a sophisticated and extremely expensive equipment for X-
ray excitation and
fluorescence detection which is not commercially available.
Because the numbers of microspheres introduced within the blood [typically five to ten million (5-10.times.10.sup.6)], and captured within the capillaries of the tissue, are large in the counting techniques, the actual numbers are commonly only estimated by statistical sampling, which induces measurement error.
Worse, even the determination of the numbers of dye-colored microspheres that are within minute sub-samples is tedious and expensive, involving in the methods of Shell, et al., and of Hale, et al., manual or semi automated observations through a
microscope.
However, with existing
spectrometer sensitivities, and with analytical
software programs of tractable size and execution times, which, most importantly, produce accurate quantitative results in the analysis of the individual spectral outputs of several different dyes (derived from species of CM) mixed together, it has, to date simply not been possible, to identify compatible dyes, and families of dyes, that number more than approximately one dozen.
Of these three additional steps, the second is by far the most labor intensive, and is therefore the most expensive.