Reversible Aggregation of Molecular-Like Fluorophores Driven by Extreme pH in Carbon Dots

The origin of carbon-dots (C-dots) fluorescence and its correlation with the dots structure still lack a comprehensive model. In particular, the core-shell model does not always fit with the experimental results, which, in some cases, suggest a molecular origin of the fluorescence. To gain a better insight, we have studied the response of molecular-like fluorophores contained in the C-dots at extreme pH conditions. Citric acid and urea have been employed to synthesize blue and green-emitting C-dots. They show a different emission as a function of the pH of the dispersing media. The photoluminescence has been attributed to molecular-like fluorophores: citrazinic acid and 4-hydroxy-1H-pyrrolo[3,4-c]-pyridine-1,3,6-(2H,5H)-trione. 3D and time-resolved photoluminescence, ultraviolet–visible (UV–vis) spectroscopy, and dynamic light scattering have been used to determine the aggregation state, quantum yield and emission properties of the C-dots. The dependence of the C-dots blue and green components on the chemical environment indicates that the origin of fluorescence is due to molecular-like fluorophores.


Introduction
Carbon dots (C-dots) are luminescent materials whose potential applications span different fields: lasing, photocatalysis, chemical and biological sensing and bioimaging [1,2]. Many synthesis methods have been developed so far, in particular bottom-up routes based on the polymerization and carbonization of the molecular precursors [3]. Several syntheses employ citric acid as a precursor [4,5], which has the advantage of being highly biocompatible [6]. The quantum yield (QY) of the product is in general in the range of 5-15%, which is quite low in comparison to C-dots obtained with other precursors [7]. A better QY is achieved by adding a nitrogen-source as a precursor, such as urea [8,9]. In a recent work [10], we have reported the high fluorescence tunability C-dots synthesized by carbonization of citric acid and urea. A marked blue to green shift has been obtained as a function of the precursors molar ratio.
Although a substantial number of works have been already published on the topic, a controversial debate about the origin of C-dots fluorescence is still ongoing. Some authors attribute the C-dots emission properties to the functional groups on the dot surface, others to molecular-like fluorophores, which form during the thermal degradation process [11][12][13]. Conventionally, carbon dots can be divided into four classes [14]. Graphene quantum dots (GQDs) are small fragments of one or a few layers of graphene displaying a size-dependent fluorescence originating from quantum confinement effects. Carbon quantum dots (CQDs) present quantum confinement effects as well. CQDs have a graphitic core with several functional groups at the surfaces. Carbon nanodots (CNDs) typically do not show a well-defined crystal lattice and tend to display a molecular fluorescence, although many papers of a porous polyvinylidene difluoride (PVDF) membrane having a pore size of 0.20 µm were used for filtration.

Synthesis of Citric Acid-Urea C-Dots
C-dots were prepared by following an already published synthesis [10]. Briefly, blue-and green-emitting C-dots were prepared by using two precursors: citric acid (CA) and urea, with molar ratios 1:2 (sample CU2) and 1:25 (sample CU25), respectively. CA and urea were put in an open round bottomed flask, dissolved in 10 mL of mQ water, and heated in an oil bath at 190 • C for 2 h. To remove large aggregates from the C-dots, the black powders obtained from the process were at first dissolved in water and then centrifuged at 12,000 rpm for 20 min. After this, the supernatants were filtered with a syringe filter. Finally, the water solutions containing the CU2 and CU25 samples were evaporated to obtain a solid product. The optical properties of CU2 and CU25 were investigated in water as a reference at the concentration of 1, 10, and 100 mg·L -1 . The corresponding pH values varied from 6.3 (1,10 mg L −1 ) to 6.0 (100 mg L −1 ) for CU2 and 6.3 (1,10 mg L −1 ) to 6.2 (100 mg L −1 ) for CU25, respectively.

Study of the Fluorescence of C-Dots Dissolved in Strong Acid and Base
CU2 and CU25 in the form of powders were dissolved in solutions of sulfuric acid at different dilutions (40, 20, and 10% (v/v) aqueous solutions). In particular, the CU2 C-dots dissolved in sulfuric acid at pH 1 (10% dilution) have been compared with the C-dots dissolved in aqueous sodium hydroxide solutions at pH 14, with a final concentration of 10 mg L −1 . C-dots in water were used as a reference and were analyzed at a concentration of 1 mg L −1 for ultraviolet-visible (UV-Vis) and for photoluminescence (PL) analysis. A neutralization reaction was carried out adding NaOH pellets until reaching pH 7 to a solution of CU2 C-dots in H 2 SO 4 10% with a concentration of 10 mg L −1 . 0.1 and 1 mg L −1 was considered for neutralization experiments, as well.

Characterization Methods
UV-Vis measurements were performed in absorbance, using a Nicolet Evolution 300 spectrophotometer (ThermoFisher Scientific, Waltham, Massachusetts, USA) from 200 to 600 nm.
Fluorescence spectroscopic measurements were taken using a Horiba Jobin Yvon FluoroMax-3 spectrofluorometer (Rome, Italy). For three-dimensional mapping (excitation-intensity-emission), a 450 W Xenon lamp was used as the excitation source. The maps were collected with an excitation range of 200-700 nm and an emission range of 200-700 nm with a 2 nm slit for excitation and emission in water and 5 nm slit for acidic and basic solutions. Solutions of C-dots at 100 mg L −1 were analyzed with the particle size analyzer DLS (dynamic light scattering) Horiba LB-550. Time-resolved fluorescence measurements (TR) in the nanosecond time domain were performed using the TBX picosecond detection module connected to a Nanolog spectrometer (Horiba Jobin Yvon, Rome, Italy). The samples were excited with a 340 nm light-emitting diode (LED) source (1 MHz repetition rate and pulse width <1.2 ns) and with a 405 nm laser diode (1 MHz repetition rate and pulse width <0.2 ns). Data were collected immediately after laser decay. The acquisition time resolution is 0.11 ns.
Absolute photoluminescence quantum yield (AQY) measurements were performed using the quanta-φ (Horiba) integrating sphere accessory, attached to the "NanoLog" spectrofluorometer (Rome, Italy). Water was used as a blank reference exciting at 350 nm for blue-emitting dots and 420 nm for green-emitting C-dots.
Transmission electron microscopy (TEM) images were acquired by using a FEI TECNAI 200 microscope (ThermoFisher Scientific, Waltham, MA, USA) working with a field emission gun operating at 200 kV. The samples were dropped onto a carbon-coated grid and dried for observations.

Results and Discussion
The optical response of C-dots prepared from citric acid and urea in acid and alkaline solutions have been systematically studied to reveal the dependence of fluorescence properties on the variations of the fluorophore protonation and deprotonation. Water-dissolved C-dots were used as a reference.

C-Dots Reference Samples
Transmission electron microscopy (TEM), UV-Vis absorption and photoluminescence spectra were used to characterize the CU2 and CU25 samples and confirm their respective morphological and spectral features. Transmission electron microscopy images of as-prepared C-dots ( Figure S1) confirm that both samples do not show a crystalline structure in accordance with our previous work [10].
The UV-Vis absorption spectrum of the CU2 C-dots in water (Figure 1a) shows the characteristic UV absorption bands peaking at 234 nm and 345 nm. Citric acid and urea derived C-dots are known to exhibit these bands [12]. Nevertheless, they are also detected in the absorption spectrum of citrazinic acid dissolved in water [27]. Correspondingly, the CU2 C-dots absorption spectrum is mainly identified by molecular origin, as a result of the formation of citrazinic acid molecule by citric acid and urea reaction at high temperature (190 • C).

C-Dots Reference Samples
Transmission electron microscopy (TEM), UV-Vis absorption and photoluminescence spectra were used to characterize the CU2 and CU25 samples and confirm their respective morphological and spectral features. Transmission electron microscopy images of as-prepared C-dots ( Figure S1) confirm that both samples do not show a crystalline structure in accordance with our previous work [10].
The UV-Vis absorption spectrum of the CU2 C-dots in water (Figure 1a) shows the characteristic UV absorption bands peaking at 234 nm and 345 nm. Citric acid and urea derived C-dots are known to exhibit these bands [12]. Nevertheless, they are also detected in the absorption spectrum of citrazinic acid dissolved in water [27]. Correspondingly, the CU2 C-dots absorption spectrum is mainly identified by molecular origin, as a result of the formation of citrazinic acid molecule by citric acid and urea reaction at high temperature (190 °C). The CU2 C-dots are characterized by a blue fluorescence (Figure 1b,c) peaking at 450 nm, which corresponds to the characteristic citrazinic acid emission in water [27]. The C-dots show also a weaker green component assigned to the formation of a fluorophore identified with HPPT. The presence of this compound has been already observed in C-dots synthesized by citric acid and urea with an excess of urea and in anhydrous conditions [24].
Green emitting C-dots (CU25) were synthesized by increasing the urea content, according to a previous work [10]. The CU25 UV-Vis spectra (Figure 1d) display the UV absorption bands that are attributed to π-π* of HPPT [24]. The latter is already observed in CU2 dots. The UV-Vis absorption bands peaking at 425 nm (CU2) and 415 nm (CU25) can be attributed to the formation of aggregates of molecular-like fluorophores into the carbon dots. This peculiar optical response of citrazinic acid has also been observed in another experiment by Reckmeier et al. [2]. The origin of the green emission for CU25 C-dots was attributed to the formation of the HPPT molecular compounds. The 3D spectra of CU25 dots (Figure 1f) mainly show a single-emission pattern peaking at 510 nm (λex = 420 nm) ( Figure 1e). The CU2 C-dots are characterized by a blue fluorescence (Figure 1b,c) peaking at 450 nm, which corresponds to the characteristic citrazinic acid emission in water [27]. The C-dots show also a weaker green component assigned to the formation of a fluorophore identified with HPPT. The presence of this compound has been already observed in C-dots synthesized by citric acid and urea with an excess of urea and in anhydrous conditions [24].
Green emitting C-dots (CU25) were synthesized by increasing the urea content, according to a previous work [10]. The CU25 UV-Vis spectra (Figure 1d) display the UV absorption bands that are attributed to π-π* of HPPT [24]. The latter is already observed in CU2 dots. The UV-Vis absorption bands peaking at 425 nm (CU2) and 415 nm (CU25) can be attributed to the formation of aggregates of molecular-like fluorophores into the carbon dots. This peculiar optical response of citrazinic acid has also been observed in another experiment by Reckmeier et al. [2]. The origin of the green emission for CU25 C-dots was attributed to the formation of the HPPT molecular compounds. The 3D spectra of CU25 dots (Figure 1f) mainly show a single-emission pattern peaking at 510 nm (λ ex = 420 nm) ( Figure 1e). Therefore, two main emissions, with maxima in the blue (λ ex = 350 nm, λ em = 450 nm) and green (λ ex = 420 nm, λ em = 510 nm) regions (Figure 1c), characterize the CU2 C-dots fluorescence spectra in water. The blue emission is the most intense ( Figure 1b). By contrast, the green component results were enhanced in CU25 (Figure 1e), for the excess of urea.

Effect of Sulfuric Acid
The CU2 C-dots have been dispersed in aqueous solutions of sulfuric acid using different concentrations (40, 20, and 10% (v/v)).
By dissolving the CU2 C-dots in sulfuric acid 40% (v/v) (5.31 M) (Figure 2b), a quenching of the blue fluorescence was observed while the green one was still detected (intensity of 2 × 10 6 CPS). The dissociation maximum of H 2 SO 4 (aq) occurs between 5 M and 7 M where the highest concentration of protons and counter-ions in the solution can be observed [28]. This maximum acid concentration corresponds to a solution of sulfuric acid 40% (v/v). It is worth noting that the citrazinic acid in analogous acidic conditions undergoes a luminescence quenching ( Figure S2). This correspondence supports the hypothesis that the blue emission is originated by citrazinic acid and its derivatives. Therefore, two main emissions, with maxima in the blue (λex = 350 nm, λem = 450 nm) and green (λex = 420 nm, λem = 510 nm) regions (Figure 1c), characterize the CU2 C-dots fluorescence spectra in water. The blue emission is the most intense (Figure 1b). By contrast, the green component results were enhanced in CU25 (Figure 1e), for the excess of urea.

Effect of Sulfuric Acid
The CU2 C-dots have been dispersed in aqueous solutions of sulfuric acid using different concentrations (40, 20, and 10% (v/v)). By dissolving the CU2 C-dots in sulfuric acid 40% (v/v) (5.31 M) (Figure 2b), a quenching of the blue fluorescence was observed while the green one was still detected (intensity of 2 × 10 6 CPS). The dissociation maximum of H2SO4 (aq) occurs between 5 M and 7 M where the highest concentration of protons and counter-ions in the solution can be observed [28]. This maximum acid concentration corresponds to a solution of sulfuric acid 40% (v/v). It is worth noting that the citrazinic acid in analogous acidic conditions undergoes a luminescence quenching ( Figure S2). This correspondence The results suggest the presence of two fluorophores, which have specific optical responses to a change of the chemical environment. In a recent work [25] it has been shown that the citrazinic acid can form aggregates with a weak green emission, if dissolved in acidic solutions ( Figure S2b). This phenomenon is explained with the protonation of the citrazinic acid molecules, associated with a blueshift and a weakening of the band at 275 nm. In accordance with the citrazinic acid response, CU2 C-dots exhibit the disappearance of the 275 nm band as an effect of the protonation. As illustrated in a recent article by Sakar et al. [29] the most stable specie of the citrazinic acid in strong acidic conditions is the imine form with the protonated carbonyl-, carboxyl-and nitrogen groups. In strong acidic conditions, the aggregation is favored due to the formation of intermolecular H-bonds and π-π stacking of the pyridone units [2].
The emission of CU25 C-dots is differently affected by the solution acidity (Figure 3). At increasing acidity concentration, we observe both a decrease of the green contribution and the blue component (attributed to the residual amount of citrazinic acid). The PL response confirms the assumption of a different emission source for the CU25 sample, i.e., HPPT fluorophore. The results suggest the presence of two fluorophores, which have specific optical responses to a change of the chemical environment. In a recent work [25] it has been shown that the citrazinic acid can form aggregates with a weak green emission, if dissolved in acidic solutions ( Figure S2b). This phenomenon is explained with the protonation of the citrazinic acid molecules, associated with a blueshift and a weakening of the band at 275 nm. In accordance with the citrazinic acid response, CU2 C-dots exhibit the disappearance of the 275 nm band as an effect of the protonation. As illustrated in a recent article by Sakar et al. [29] the most stable specie of the citrazinic acid in strong acidic conditions is the imine form with the protonated carbonyl-, carboxyl-and nitrogen groups. In strong acidic conditions, the aggregation is favored due to the formation of intermolecular H-bonds and π-π stacking of the pyridone units [2].
The emission of CU25 C-dots is differently affected by the solution acidity ( Figure S3). At increasing acidity concentration, we observe both a decrease of the green contribution and the blue component (attributed to the residual amount of citrazinic acid). The PL response confirms the assumption of a different emission source for the CU25 sample, i.e., HPPT fluorophore.

Reversibility of the Quenching Effect
To verify if the emission quenching is reversible, CU2 C-dots dissolved in sulfuric acid (10%) have been neutralized with NaOH and the 3D spectra have been recorded. Figure 4 shows the PL and the 3D fluorescence maps of C-dots upon excitation at 350 (black) and 420 nm (red) in acid and after neutralization. As a result of the neutralization, an intense blue emission appears, and, correspondingly, the green contribution decreases. A broadening of the green emission nm is also visible. This effect is attributed to the merging of the PL with the water Raman vibration, which is

Reversibility of the Quenching Effect
To verify if the emission quenching is reversible, CU2 C-dots dissolved in sulfuric acid (10%) have been neutralized with NaOH and the 3D spectra have been recorded. Figure 4 shows the PL and the 3D fluorescence maps of C-dots upon excitation at 350 (black) and 420 nm (red) in acid and after neutralization. As a result of the neutralization, an intense blue emission appears, and, correspondingly, the green contribution decreases. A broadening of the green emission nm is also visible. This effect is attributed to the merging of the PL with the water Raman vibration, which is located at 491 nm under excitation at 420 nm. To confirm this attribution, we have measured the CU2 sample at lower concentrations ( Figure S3). The PL spectra show a strong contribution of the Raman signal of water which becomes prominent as the CU2 concentration decreases. The reversibility of the quenching effect suggests that aggregation is a reversible process and the pristine emissions of the CU2 sample can be easily restored (see Figure 1b).
Materials 2020, 13, x FOR PEER REVIEW 7 of 13 sample at lower concentrations ( Figure S3). The PL spectra show a strong contribution of the Raman signal of water which becomes prominent as the CU2 concentration decreases. The reversibility of the quenching effect suggests that aggregation is a reversible process and the pristine emissions of the CU2 sample can be easily restored (see Figure 1b).  Figure 5 shows the absorption spectra of CU2 ( Figure 5a) and CU25 (Figure 5b) in water (black), acid (red), and basic (blue) solutions. The overall spectra of both CU2 and CU25 in basic conditions appear very similar. The visible component at λ > 400 nm decreases for both samples at pH 14, up to a complete disappearance for CU25 dots. A blue shift of the 345 nm band in water is also observed for CU2 dots. Moreover, the rise of a new one at 328 nm is detected in the CU25 sample.   At pH 14, the molecular-like fluorophores are in a de-protonated form [25,28] which inhibits the formation of hydrogen bonds between fluorophores and avoids aggregation. This is in agreement with the disappearance of the absorption bands at 425 nm for CU2 ( Figure 5a) and 410 nm for CU25 (Figure 5b) attributed to the aggregates [2].

C-Dots in Highly Basic Solutions
The analysis of the CU2 3D PL map (Figure 5c) in NaOH (aq) shows two different residual bands, which can be attributed to citrazinic acid for the blue emission and, in a small amount, to HPPT for the green component. The CU25 3D PL map shows similar emissions in the blue and the green with a shift in the maximum excitation of the blue component (Figure 5d). This can be due to the dissolution of green-emitting aggregates of citrazinic acid in strong basic conditions, which causes a blue shift of the C-dots emission. Figure 6a shows the UV-Vis spectra of CU25 dots at the increase of pH values. At high pH, the deprotonation of the fluorophores [25,29] and the subsequent formation of carbonyl groups determine the rise of the absorption band at around 328 nm, assigned to the n-π* electron transitions of C=O bonds [30]. This process affects the emission yield with a gradual quenching of the green component and the appearance of the blue one (Figure 6b-d). At pH 14, the molecular-like fluorophores are in a de-protonated form [25,28] which inhibits the formation of hydrogen bonds between fluorophores and avoids aggregation. This is in agreement with the disappearance of the absorption bands at 425 nm for CU2 ( Figure 5a) and 410 nm for CU25 (Figure 5b) attributed to the aggregates [2].
The analysis of the CU2 3D PL map (Figure 5c) in NaOH (aq) shows two different residual bands, which can be attributed to citrazinic acid for the blue emission and, in a small amount, to HPPT for the green component. The CU25 3D PL map shows similar emissions in the blue and the green with a shift in the maximum excitation of the blue component (Figure 5d). This can be due to the dissolution of green-emitting aggregates of citrazinic acid in strong basic conditions, which causes a blue shift of the C-dots emission. Figure 6a shows the UV-Vis spectra of CU25 dots at the increase of pH values. At high pH, the deprotonation of the fluorophores [25,29] and the subsequent formation of carbonyl groups determine the rise of the absorption band at around 328 nm, assigned to the n-π* electron transitions of C=O bonds [30]. This process affects the emission yield with a gradual quenching of the green component and the appearance of the blue one (Figure 6b-d). DLS measurements provide new insight into the mechanism of pH-induced aggregation. Table  1 shows the C-dots hydrodynamic radii at different pH. The radius in water and NaOH solutions for CU2 and CU25 C-dots is very similar while there is a sensitive aggregation in acidic solutions, especially for the CU25 sample. The particles tend to agglomerate and to form clusters with a Gaussian distribution peaking around 0.6 μm ( Figure S5). CU25/NaOH 6.5 The C-dots aggregation measured by DLS can be correlated with the AQY values summarized in Table 2. The acidic conditions cause a consistent decrease of the quantum yield, in particular for the CU25 sample. This strong quenching in emission is therefore due either to the aggregation of the fluorophores and the C-dots at low pH. DLS measurements provide new insight into the mechanism of pH-induced aggregation. Table 1 shows the C-dots hydrodynamic radii at different pH. The radius in water and NaOH solutions for CU2 and CU25 C-dots is very similar while there is a sensitive aggregation in acidic solutions, especially for the CU25 sample. The particles tend to agglomerate and to form clusters with a Gaussian distribution peaking around 0.6 µm ( Figure S5). CU25/NaOH 6.5 The C-dots aggregation measured by DLS can be correlated with the AQY values summarized in Table 2. The acidic conditions cause a consistent decrease of the quantum yield, in particular for the CU25 sample. This strong quenching in emission is therefore due either to the aggregation of the fluorophores and the C-dots at low pH.  Figure 7 shows the fluorescence decays of the CU2 (Figure 7a) and CU25 (Figure 7b) excited at two different wavelengths (340 and 405 nm). In general, the decay profiles can be fitted by a two-exponential law. As already reported, the different chemical environments affect the mechanism of de-excitation. The various fluorophores in the C-dots undergo protonation, followed by aggregation in acidic conditions, and deprotonation in alkaline media. In general, it is observed that the samples in water (pH ≈ 6) exhibit a longer average lifetime with respect to highly acidic and basic conditions (Table  S1). In particular, due to the formation of large aggregates in acid, the non-radiative recombination channels favor a drastic reduction in lifetime. By contrast, in aqueous and alkaline solutions the C-dots show similar lifetime decays as a result of a more effective dispersion.  Figure 7 shows the fluorescence decays of the CU2 (Figure 7a) and CU25 (Figure 7b) excited at two different wavelengths (340 and 405 nm). In general, the decay profiles can be fitted by a two-exponential law. As already reported, the different chemical environments affect the mechanism of de-excitation. The various fluorophores in the C-dots undergo protonation, followed by aggregation in acidic conditions, and deprotonation in alkaline media. In general, it is observed that the samples in water (pH ≈ 6) exhibit a longer average lifetime with respect to highly acidic and basic conditions (Table S1). In particular, due to the formation of large aggregates in acid, the non-radiative recombination channels favor a drastic reduction in lifetime. By contrast, in aqueous and alkaline solutions the C-dots show similar lifetime decays as a result of a more effective dispersion. As shown in Figure S1, the C-dots obtained by carbonization in anhydrous conditions lack detectable crystalline structures. The characteristic lattice spacing of about 0.24 nm, corresponding to the in-plane spacing of graphite (100) [31] is not measurable in this case. Nonetheless, the optical properties of C-dots herein presented have been measured for QCDs as well [31], although they differ in structural and morphological features. This agrees with the fluorophore-like origin of the emission. In particular, the C-dots reproduce the fluorescence of molecular fluorophores and the response under extreme pH conditions. For citric acid and urea-derived C-dots, the graphitic core and surface states model does not properly explain the effect of chemical surrounding variations on the luminescence properties. Indeed, the C-dots can be considered as permeable nanostructures of carbon, which include fluorophores sensitive to the external environment. The molecular units can As shown in Figure S1, the C-dots obtained by carbonization in anhydrous conditions lack detectable crystalline structures. The characteristic lattice spacing of about 0.24 nm, corresponding to the in-plane spacing of graphite (100) [31] is not measurable in this case. Nonetheless, the optical properties of C-dots herein presented have been measured for QCDs as well [31], although they differ in structural and morphological features. This agrees with the fluorophore-like origin of the emission. In particular, the C-dots reproduce the fluorescence of molecular fluorophores and the response under extreme pH conditions. For citric acid and urea-derived C-dots, the graphitic core and surface states model does not properly explain the effect of chemical surrounding variations on the luminescence properties. Indeed, the C-dots can be considered as permeable nanostructures of carbon, which include fluorophores sensitive to the external environment. The molecular units can affect the overall luminescence signal by promoting the aggregation and disaggregation of carbonaceous superstructure through the protonation and deprotonation process.

Conclusions
C-dots prepared from citric acid and urea show a different response as a function of the pH and relative concentration of their precursors. The CU25 sample in water shows only a green component while the CU2 exhibits both blue and green emissions. The photoluminescence of CU2 and CU25 has been attributed to molecular-like fluorophores: citrazinic acid and HPPT.
In extreme acidic conditions, CU2 dots show a quenching of the blue emission while the green component remains detectable. This response, which is reversible with the pH, is explained with the formation of citrazinic acid aggregates in the C-dots structure. The aggregates emit in the green, as confirmed by the experiments on pure citrazinic acid in solution. The emission of CU25 dots, which is mainly attributed to HPPT, shows small changes in an acidic solution, indicating that the green fluorophore is less sensitive to the pH of the medium.
In extreme basic conditions, the molecular-like fluorophores are in a de-protonated form. This state favors the disaggregation of the fluorescent molecules. The CU2 C-dots show two different emission bands attributed to citrazinic acid and HPPT monomers. In contrast, the CU25 C-dots, beside the HPPT green emission, display a blue component correlated to the dissolution of citrazinic acid aggregates.
Considering the whole photoluminescence fingerprint of both CU2 and CU25, it can be inferred that the reported C-dots contain fluorophores that aggregate as a function of the dispersing medium pH. The fluorophores strongly interact with the external environment and evaluation of the emission properties in different media has to be, therefore, carefully considered. The high sensitivity to the chemical environment opens new scenarios for future applications in the field of sensing and diagnostics.

Conflicts of Interest:
The authors declare no conflict of interest.