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P. Comba et al. / Journal of Inorganic Biochemistry 159 (2016) 70–75
4. Experimental section
All solvents and reagents (absolute, p.a. grade and purum grade) were
obtained commercially and used without further purification. Dry
solvents were kept above molecular sieves. MilliQ water (R N 18MΩ)
was used for the kinetic assays.
4.1. Ligands and complexes
The cyclic pseudo-peptides were prepared according to [4,6,19].
4.2. Hydrolase assays
4.2.1. Preparation of the multicomponent buffer solutions
Fig. 5. pH profile of the [CuII2(H4pat1)(OH)]+ (3) nitrocefin hydrolysis (c = 25 μM; the
solid line is a basis spline function and not fit to a kinetic model).
The aqueous buffer consisted of CAPS, N-cyclohexyl-3-amino-
propanesulfonic acid, pKa = 10.40, CHES, 2-(N-cyclohexylamino)
ethanesulfonic acid, pKa = 9.30, HEPES, 4-(2-hydroxyethyl)-1-
piperazinylethanesulfonic acid, pKa = 7.55 and MES, 2-(N-morpholino)
ethanesulfonic acid, pKa = 6.15. Lithium perchlorate was added to
achieve a constant ionic strength of μ = 0.45. Each component was
dissolved in Milli-Q water. A standard solution with 55.56 mM of the
buffer components and 277.8 mM lithium perchlorate was prepared.
Aliquotes of 45 mL of the standard buffer were adjusted to the desired
pH value by addition of 2 M NaOH. A Metrom 713 pH meter which is
equipped with a KCl electrode was used to adjust pH values at 25 °C.
The pH-meter was calibrated with pH standard solutions at pH values
of 4, 7 and 9. Subsequently the aliquotes were filled up to 50 mL leading
to a final buffer concentration of 50 mM and 250 mM lithium perchlorate.
Metal ions were removed by stirring adjusted buffers over night with
Chelex 100, which was afterwards filtered off by using 45 μm syringe
filters. Finally all buffers were degassed by flushing N2 through the
solution in an ultrasonic bath for 3 h in order to remove potentially dis-
solved CO2.
Table 2
Kinetic data from pH-profiles of [Cu2(H2pat1)(OH)]+ (3) for the hydrolysis of nitrocefin
and the corresponding Michaelis–Menten parameters determined at pH 11.5.
Catalyst pHmax v0,max ∙10−9 pKa1
kcat × 10−4
[s−1
KM
[μM]
kcat/KM
[M/s]
]
[M−1 s−1
]
3
11.50
3.82 0.03
≈11.3 11.34 ( 0.91) 22.47 50.47
shown in Fig. 5 and the resulting kinetic parameters and pKa values are
summarized in Table 2 (see Supporting Information for a plot of the sub-
strate concentration dependent kinetic data). β-lactamase activity
is observed at approx. pH 11 with resulting kcat/KM = 50.5 M−1 s−1
,
and this is consistent with similar dinuclear model complexes [7].
The uncatalyzed background rate constant for β-lactam hydrolysis is
kuncat = 0.025ˑ10−4 s−1 [24], and the rate enhancement therefore is
kcat/kuncat = 454. The kinetic Michealis Menten data reported for natural
β-lactamase activity is reported to be in the range of KM = 16–100 μM
and kcat = 0.3–200 s−1 for Bacteroides fragilis and Aeromonas hydrophila
respctively (substrate nitrocefin) [25].
4.2.2. Glycosidase-like activity
The glycosidase-like activity was determined by measuring the hy-
drolysis of 4-nitrophenyl-α-D-glucopyranoside and 4-nitrophenyl-β-
D-glucopyranoside hydrolysis. The hydrolysis product 4-nitrophenole
was produced which could be detected by monitoring the increase of
an strong absorbance at 410 nm (ε is pH dependent).
3. Conclusions
The patellamide-dicopper(II) complexes are among the few exam-
ples of dinuclear copper(II) complexes acting as glycosidase-like
model compounds. Taking into account the broad reactivity pattern of
these compounds with respect to hydrolysis reactions, namely phos-
phatase, carboanhydrase, glycosidases as well as β-lactamase, several
questions emerge. First and probably foremost, it is uncertain whether
the catalytic activities observed for the dinuclear copper(II) complexes
can be associated with the function of the cyclic peptides in Prochloron
or Lissoclinum patellum. Currently, we are therefore carrying out in
vivo studies towards an understanding of the stability of dinuclear
copper(II) complexes with these naturally occurring ligands. Second
and not less important is the question, whether all of the hydrolyses
are of importance for the symbiosis partners. Is each of the reactions
happening in a separate compartment in the cyanobacterium, providing
the optimum pH value? Or is none of these reactions observed in the
test tube actually metabolically relevant for the ascidians?
These questions are in the focus of ongoing research. If glycosidase as
well as carboanhydrase activity in the cell were mediated by the same
dinuclear copper(II) patellamide complexes, this would indicate that
the same enzyme is capable of fixing carbon from CO2 as well as to
catabolize the products from the assimilation (Calvin cycle). Here,
research has to be carried out as to where which reaction takes place.
Prochloron might be responsible for the fixation, whereas the ascidian
might require the catabolic glycosidase activity.
Initially, the extinction coefficients of the product formation of
4-nitrophenolate in a multicomponent buffer were calculated by cali-
bration curves for each pH value (pH = 5.5–11.5) using Lambert Beer's
law (Table 1). The extinction coefficients of pH = 8.7–11.5 are similar to
those determined for 4-nitrophenolate in CAPS buffer (ε = 16,190 M-
1 cm-1) [10]. The obtained extinction coefficients (see Supporting Infor-
mation) were used to convert the absorbance of the reaction product
into molar amounts.
UV–Vis-spectra data were recorded on a Jasco V-570 spectropho-
tometer equipped with a Jasco ETC-505 T cryostat at 25 °C and in a
0.3: 1.3: 1 MeCN:buffer:MeOH solution. Using time-course measure-
ments at fixed wavelengths (λmax = 410 nm), spectrophotometric
titrations were performed with a cyclic pseudo-peptide concentra-
tion of 1 mM (MeOHdry). CuII(CF3SO3)2 (25 mM, MeOHdry) and
base (n-Bu4N)(OMe) (25 mM, MeOHdry) were added to different
pH-samples. The final concentrations of dicopper(II) complexes
of H4pat1 and H4pat2 in the cuvette were 40 μM. All solutions were
degassed and kept under argon at 7 °C. Blank tests, the auto-
hydrolysis of 4-nitrophenyl-α-D-glucopyranoside or 4-nitrophenyl-β-
D-glucopyranoside respectively, were subtracted from the reported
kinetic rates. For the determination of pH dependent reaction velocities
the substrate concentration of 30 mM (MeOHdry) was chosen. For
substrate dependency measurements at constant pH the substrate
concentration was varied between 1 and 50 mM.