Microsoft word - fluoxetine research.doc
Photodecomposition of Fluoxetine
St. John’s University/College of St. Benedict
Fluoxetine, also known as Prozac, is a widely marketed selective serotonin
reuptake inhibitor, used to fight depression and anxiety. Recently, it has been observed
that high levels of this pharmaceutical have been found in water sources prone to
contamination. This is a concern for environmental reasons because of the negative
effects that it can have on aquatic organisms, including fertility and reproductive
problems. In further studies, it has been found that fluoxetine reacts in light, breaking
down into various molecules via direct and indirect photolysis, with a half life of 55.2 ±
3.6 hours.7 It was my goal in this study to investigate whether fluoxetine would indeed
break down. High performance liquid chromatography and mass spectrometry were used
to determine a half life of 66.896 hours in East Gemini Lake water, compared to much
higher half lives in buffered solutions. This was evidence that fluoxetine broke down via
indirect and/or direct photodecomposition versus simply just direct photodecomposition.
Additionally, trials were run in isopropyl alcohol and DABCO to find a mechanism by
means of hydroxyl radical or singlet oxygen, respectively.
Fluoxetine, also known as Prozac, is categorized as a selective serotonin reuptake
inhibitor (SSRI) with the chemical structure seen in Figure 1
. SSRIs selectively inhibit
the reuptake of serotonin at the presynaptic neuronal membrane. This could be a result of
fluoxetine’s electron withdrawing effect and its lipophilicity. Fluoxetine is used
primarily in the treatment of depression and obsessive compulsive disorder.
: Fluoxetine or N
-methyl-8-[4-(trifluoromethyl) phenoxy] benzene propanamine
When fluoxetine is metabolized in the body via demethylation, norfluoxetine is
formed, which may contribute to the long duration of the action of fluoxetine in the body.
Findings indicate that 2.5% of the metabolites analyzed in excreted urine were fluoxetine
and 10% norfluoxetine.12 Because this metabolization takes place, as seen in Figure 3
both structures need to be taken into consideration when analyzing for environmental
: Fluoxetine and its demethylized metabolite, norfluoxetine 12
There have been very few studies done on the environmental effects of non-
steroidal pharmaceuticals, much less anti-depressants. One study done on the toxicity of
fluoxetine on select organisms, including aquatic biota such as Ceriodaphnia dubia
, and Pimephales promelas
was conducted. In these experiments,
organisms were treated with fluoxetine treatments at various concentrations. Cell
deformities occurred, especially seen in algae. Cells appeared shriveled and frequently
were not crescent shaped, a normal characteristic of the particular cell being observed. 1
Results also showed that this exposure resulted in fertility problems. In fish,
serotonin stimulates the release of gonadotropin in some species, which stimulates sex
steroid synthesis and controls the development of oogenesis, including vitellogenesis.1
Other studies have verified that anti-depressants have been found to have the same effect
on fish that they do people, they cause aquatic life to be more relaxed. This would
suggest that smaller fish would become easier prey for larger fish. This also suggests that
if concentrations of drugs, and in particular fluoxetine, are high enough they could cause
In this study, the goal was to see if fluoxetine would break down in water with the
understanding that it is present currently in many bodies of water throughout the United
States as well as Canada. Previous studies indicated that fluoxetine broke down in sunlit
water, resulting in a half life of 55.2 ± 3.6 hours7. Finding out whether fluoxetine
decomposed via direct and indirect photolysis was the primary goal. Direct photolysis is
when a compound absorbs light, becomes unstable, and decomposes. Indirect photolysis
occurs when a reactive intermediate is generated by another light absorbing material and
then causes a compound to decompose. Using this information, the objective was to find
a half life of fluoxetine and if possible, a mechanism for decomposition.
A 10 mM solution of fluoxetine·HCl from the National Science Foundation was
prepared using E.Pure water and 3 mL acetonitrile to dissolve. Formate, acetate and
ethanolamine buffers were prepared at pH 3, 5 and 9, respectively again using E.Pure
water. East Gemini Lake (EGL) water was filtered using 0.45 µm filter paper.
Solutions were also made of 100 µM fluoxetine in an ethanolamine buffer of pH
8.5, EGL water, EGL water with isopropyl alcohol (IPA) at a concentration of 10-2 M and
EGL water with DABCO (1,4-Diazabicyclo[2.2.2]-octane) at a concentration of 10-3 M.
Duplicate samples of 100 µM fluoxetine in the respective pH 3, 5, 9 and EGL
lake water were prepared and put into quartz test tubes. Similar samples were wrapped in
aluminum foil to serve as controls for the experiment. The photoreacter was comprised
of a 450 W UV immersion lamp from Ace Glass Incorporated surrounded by quartz
immersion lamp well that continuously had cold water running through it. The samples
were run around the lamp powered by a generator. A diagram of this setup can be seen in
. Aliquots of 750 µL were taken from the test tubes at various time intervals for
Samples were run under the previous conditions; however the solutions of 100
µM fluoxetine were in the ethanolamine buffer of pH 8.5, EGL water, EGL water with
isopropyl alcohol and EGL water with DABCO at concentrations previously specified.
Controls of the same nature were also provided.
: Diagram of the photoreactor used for photolysis of fluoxetine
Analysis was performed using liquid chromatography/mass spectrometry
(LC/MS). This instrument was a Surveyor photodiode array (PDA) Detector,
Autosampler, LC Pump, followed by an LCQ Advantage mass spectrometer, all produced
by Thermo Finnigan. The conditions of the LC were as follows: a stationary phase of
Synergi 4u MAX-RP 80A 150x4.6 mm column was used with a mobile phase of 60%
acetonitrile and 40% pH 5 acetate buffer. An electron Spray Ionization (ESI) source was
Results and Discussion
: Results of the photodecomposition of fluoxetine at pH 3 using, resulting in a half life of 150.515 hours
: Results of the photodecomposition of fluoxetine at pH 5, resulting in a half life of 136.832 hours
: Results of the photodecomposition of fluoxetine at pH 9, resulting in a half life of 107.511 hours
: Results of the photodecomposition of fluoxetine in East Gemini Lake water, resulting in a half life of 66.896 hours
In order to find the half life of fluoxetine in the various conditions, a line of best
fit was found for each set of data, as seen in Figures 5
. From this data, the
slope of the line represented the negative of the rate constant. Using the rate constant, the
half life was found from the following equation: -log(1/2) = -kt. The data used to find
this information was found using the analysis method of mass spectrometry (MS)
chromatograms instead of the photodiode array (PDA) chromatograms. The reasoning
for this was that the MS analysis provided much better quantitation for fluoxetine. The
PDA chromatograms were not as precise and therefore not used.
Half Life (hours)
: Half lives (in hours) of fluoxetine based on the solution they were in during photodecomposition
These half lives provided valuable information. The primary purpose of the
experiment was to find out whether fluoxetine photodecomposed via direct or indirect
photolysis. From the information seen in Table 1
, one can see that there was a trend in
the photodecomposition as the pH of the buffer used became more basic, indicating that
there was a possible dependence on pH. Another similarity shows that the pH of EGL
water is approximately at a pH of 8.5, showing a direct correlation between the pH 9
buffer and EGL water. Another deduction that can be made from the combined results in
is that photolysis occurred much faster in the EGL water, with a half life of
66.896 hours. This signifies that fluoxetine did not break down solely by direct
decomposition; there must have been a mixture of direct and indirect decomposition.
Again, during indirect photolysis there are organic molecules in solution that are excited
by light absorption and thus cause the breakdown of fluoxetine versus direct photolysis
where fluoxetine absorbs light and breaks down directly.
After finding that although fluoxetine decomposes at a rather slow rate, it does
indeed decompose. Another goal of the experiment was to propose a mechanism by
which fluoxetine photodecomposed. Two very common mechanisms of indirect
photodecomposition include photodecomposition by hydroxyl radical (●OH) and singlet
oxygen (1O2). Trials run with isopropyl alcohol will cause the consummation of any
hydroxyl radical in solution. If indirect photolysis occurs by hydroxyl radical, the
fluoxetine will not decompose in trials ran in the presence of isopropyl alcohol. Trials
run with DABCO will similarly consume any singlet oxygen present in solution and if
indirect photolysis occurs by singlet oxygen, the fluoxetine will not decompose in the
presence of DABCO. These two chemicals and the mechanism by which they prevent
photodecomposition are termed “scavengers.”
Half Life (hours)
: Half lives (in hours) of fluoxetine based on the solution they were in during photodecomposition
Preliminary results of the investigation of the mechanism by which fluoxetine
photodecomposes have shown that a mechanism via singlet oxygen is possibly favorable.
This can be seen in the results found in Table 2
, where the EGL water with IPA produced
a half life of 125.429 hours and EGL water with DABCO produced a half life of 301.030
hours. As previously stated before, fluoxetine would not decompose in the presence of a
certain scavenger (IPA or DABCO) if fluoxetine photodecomposed via that mechanism.
However, because these are strictly introductory studies, further research needs to be
performed in order to solidify these results.
There are many other future areas of research that could be explored using
fluoxetine. There are possibilities of more trials run with IPA and DABCO that could be
performed in order to see if singlet oxygen is indeed a true mechanism. If neither of the
two scavengers proposed are the cause of photodecomposition, other possible organic
molecules could be in solution acting as reactive intermediates causing the
Another trend that was seen was the dark (control) for all of the different solutions
of buffer as well as the EGL water also decomposed. Running trials where fluoxetine
would not be exposed to any sort of light and not put into the photoreactor could be tried
to see if there is some other mechanism other than one involving light absorption that
Environmentalists are concerned because of the immediate effects that fluoxetine
has on the environment that have already been researched. Additionally, another concern
is to identify the exact photodecomposed products because it is possible that these
byproducts could be harmful to the environment and aquatic life as well.
Lastly, norfluoxetine, the metabolite that fluoxetine forms in the body by a
demethylation, could be researched under all of the same conditions as above since it is
present in higher concentrations in the urine of patients taking fluoxetine.
The half life of fluoxetine was found to be 66.896 hours in East Gemini Lake
water. A proposed mechanism via singlet oxygen is in the beginning stages of research
and other avenues of research are proposed for the study of the photodecomposition
There are special acknowledgements to Dr. Michael Ross for expertise advise
during this research project, as well as the College of Saint Benedict/Saint John’s
University Chemistry Department for additional support.
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9 Streater, S., Drug found in area fish stirs concern.
17 October 2003. Star-Telegram.
10 Walton, M., Frogs, fish and pharmaceuticals a troubling brew
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Cable News Network LP, LLLP. www.cnn.com
11 Wirth, D.D., Miller, M.S., Bioni, S.K., Koenig, T.M., Identification and comparison
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12 Wong, S.H.Y., Dellafera, S.S., Fernandes, R., Kranzler, H., Determination of
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. 1990. Journal of Chromatography 499, p. 601-608.
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