The present work is dedicated to the characterization of Moroccan cactus juice, which shows encouraging performance in wastewater treatment. Various techniques were used to highlight the chemical and physical properties of this natural product. Elemental analysis of cactus juice using inductively coupled plasma emission spectroscopy revealed the presence of numerous minerals. Fourier Transform Infrared, ultraviolet, and nuclear magnetic spectroscopies demonstrate the presence of many carbohydrate components. Identification of volatile compounds by gas chromatography reveals the presence of Gibb-3-ene-1,10-dicarboxylic acid, ethyl gallate, 3TMS derivative, ethyl ester and 1-(2-Isopropyl-phenyl)-3,6,6-trimethyl-1,5,6,7-tetrahydro–indazol. Thermogravimetric analysis indicates three peaks at 100, 200 and 600 °C, corresponding to the mass loss of water, polysaccharides, and organic matter, respectively. The rheological characterization of cactus juice suggests that this liquid exhibits shear-thinning behavior, which is governed by the Casson model. The results of the Zeta potential measurement demonstrate the anionic character of cactus juice as a flocculant, with −25 mV as a value of zeta potential. Its use as a flocculant in organic matter removal shows that the chemical oxygen demand decreases significantly with the increase of the added cactus juice dose, confirming, therefore, its flocculating behavior.

  • Cactus juice was extracted from Moroccan Opuntia Ficus Indica.

  • Physical and chemical properties of Moroccan cactus were investigated.

  • Flocculatory behaviours of cactus juice were discussed.

  • Encouraging performances on chemical oxygen demand removal of wastewater were obtained.

Chemical flocculants play an important role in different industrial sectors. In the mineral industry, the selective flocculation technique has been used for more than 30 years. It can be considered as one of the most widely used techniques in ore beneficiation (Brostow et al. 2007). This technique is also widely used in wastewater and drinking water treatment (Lee et al. 2014; Ma et al. 2019). In the last decades, the use of coagulation-flocculation processes has increased considerably. The success of these processes is due to the flocculants' properties, which contains monomers of acrylamide and acrylic acid (Benda et al. 1997) or ionic groups (Ma et al. 2013; Zheng et al. 2014) that contribute to the elimination of suspended particles in water (Nougbodé et al. 2013). The flocculation mechanism is governed by electrostatic interactions between the polymer functional groups (flocculants) and the surface of the particles (pollutants). Other factors such as the particle size and the intrinsic polymer flexibility play an important role in improving flocculation efficiency (Gregory & O'Melia 1989; Walker & Grant 1996; Thomas et al. 1999). Nevertheless, the use of synthetic chemical flocculants raises several questions about their impact on human health and environment safety (Harford et al. 2011; Okaiyeto et al. 2016). Alternatively, several research works have focused on the development of green and sustainable flocculants derived from plants, opening a new way for the use of green products without harmful effects on health and the environment. Pallavi et al. have used Moringa oleifera powder to treat dairy wastewater (Pallavi & Mahesh 2013). In the other work, the ability of the mucilaginous, an extract of Salvia hispanica seeds, to treat compost leachate wastewater was investigated (Tawakkoly et al. 2019). In addition, the suitability of mango kernels as a bioflocculant for the treatment of sewage wastewater has been studied (Das et al. 2021). On the other hand, Betatache et al. (2014), as well as other works (Zhang et al. 2006; Sellami et al. 2014; Ennawaoui et al. 2022), demonstrate that the juice of Opuntia Ficus Indica, a species of cactus, has the same flocculating effect as those of the industrial flocculants. Other studies have focused on the use of cactus juice for the removal of heavy metals and organic matter (Amari et al. 2019; El Bouaidi et al. 2020; El Mansouri et al. 2023). Pichler et al. showed that the treatment of drinking water by mucilage from a common cactus induces a decrease in turbidity. Such treatment provokes the removal of more than 83.3% of suspended solids and 59.1% of the chemical oxygen demand (Pichler et al. 2012).

In fact, due to the importance of water for human survival and environmental sustainability, water treatment continues to attract great interest. Recently, several investigations have been conducted to promote the use of natural materials for water treatment, such as cactus plants, which show promising performance as flocculant agents (Rachdi et al. 2017; Rebah & Siddeeg 2017). In order to understand the origin of flocculation induced by cactus, some studies have been dedicated to the identification of the chemical composition of cactus mucilage. Madera-Santana et al. (2018) reported that the mucilage of cactus is a heteropolysaccharide composed of galactose, arabinose, xylose, rhamnose and galacturonic acid. In addition to polysaccharides, cactus mucilage contains other components such as fibers, potassium and calcium (Sepúlveda et al. 2007).

All published works have focused on the use of cactus as a flocculant. Its characterization was in most cases limited to FTIR analysis. The aim of this work resumes in the in-depth analytical characterization of cactus juice, in order to understand its physical behavior, as well as the mechanisms responsible for its flocculating effect. To achieve this goal, many analytical techniques have been used. Optical inductively coupled plasma spectrometer (ICP-AES), Attenuated Total Reflection Fourier Transform Infrared spectrometry (ATR-FTIR), Nuclear magnetic resonance spectroscopy (NMR), and Gas Chromatography coupled with Mass spectrometry (GC-MS) were used to determine the chemical properties of cactus juice, while thermogravimetric analysis, Zeta potential and viscosity measurements were employed to study the physical properties. In addition, an application of cactus juice for the removal of chemical oxygen demand (COD) in wastewater by the coagulation/flocculation process was tested to confirm the cactus's efficiency as a natural flocculant in water treatment.

Sample preparation

The cactus leaves were collected from an agricultural field surrounding El Jadida town (Morocco). After washing, the cactus leaves were divided into two parts: the first part was cut and squeezed to extract the juice in a liquid state, and the second part was cut, dried, and crushed to a powder of less than 0.5 mm. Figure 1 shows the preparation steps.

Chemical properties

Elemental analysis of the extracted juice was carried out by an optical inductively coupled plasma spectrometer ICP-AES (PerkinElmer AVIO 500). The maximum absorbance of cactus juice was determined using a Shimadzu UV-1900 series spectrophotometer in the range of 200 to 800 nm, and the spectrum obtained is shown in Figure SI.1 (Supplementary file). Attenuated Total Reflection Fourier Transform Infrared (ATR-FTIR) spectrometry was performed to identify the functional groups in dried cactus and extracted juice using a Spectrometer BX-1000 FTIR (Perkin Elmer, Überlingen, Germany). The FTIR spectra were recorded in the range of 450–4,000 cm−1. The 1H, 13C, 13C DEPT, 2D 1H-13C HSQC NMR spectra of cactus juice after extraction in ethanol solvent were performed on a Bruker Avance 400 MHz spectrometer (Bruker, Germany) at 25 °C and D2O as solvent.

Gas Chromatography-Mass Spectrometry (GC-MS) analysis was performed on a GC TRACE 1300 TSQ 8000 evo, after treatment of the sample with ethanol, equipped with a TR 35MS (30 m × 0,25 mm × 0,25 μm) column. The injection volume was fixed at 0.5 μl in split mode with a flow of 1.5 ml/min and an injection temperature of 250 °C. Spectra were indexed using a NIST/EPA/NIH MASS SPECTRAL LIBRARY Version 2011.

Physical properties

Thermogravimetric analysis was conducted on raw cactus in the range of 20–900 °C with a heating rate of 5 °C/min under an inert atmosphere of N2 at a flow rate of 60 mL/min using the Q50 TGA (TA instrument). The rheological behavior of the cactus juice was determined using an Anton Paar MCR 72 rheometer with an MS CC39 parallel plate measuring system at room temperature. The viscosity was measured as a function of shear rate ranging from 1,000 to 10 s−1. On the other hand, the measurement of zeta potential (ζ) and particle size in cactus juice was carried out from a dilute solution of 10% and analyzed at 25 °C by using a Zetasizer Ultra zettameter (Malvern Panalytical, UK), equipped with a capillary cell (DTS 1070), and ZS XPLORER software (V 3.2.2.5).

Removal of organic matter from wastewater

The samples tested were taken from the municipal wastewater of the city of El Jadida (Morocco). The samples were collected, stored at 4 °C to minimize bacterial activity, and transported immediately to the laboratory. The coagulant was 10% (w/v) aluminum sulphate prepared by dissolving 10 g of aluminum sulphate ((Al2(SO4)3,18H2O), SOLVAPUR) in 100 mL of distilled water and stirring until complete dissolution. Cactus juice at 10% (v/v) (10 mL of the cactus juice solution in 100 mL of distilled water) was used as a flocculant. Turbidity was measured using a HACH LANGE 2100Q IS turbidimeter. The chemical oxygen demand (COD) was determined according to the ISO 15705:2002 standard (ISO 2002).

The extracted cactus juice, obtained by squeezing the leaves, has a green color and is very miscible in water. It contains about 95% humidity and less than 5% of dry residue. The liquid pH was 4.25, its conductivity was 6.36 mS/cm and its density was 0.95.

The elemental analysis of the cactus juice revealed the presence of six major elements as shown in Table 1. The content of these elements varies from 1 ppm (manganese) to 2,650 ppm (potassium). The presence of these elements explains the conductivity value mentioned above. In addition, the presence of aluminum ions is interesting because they are widely used as a flocculants in water treatment (Zouboulis et al. 2008; Bo et al. 2012; Betatache et al. 2014).

Table 1

Results of ICP-OES analysis

ElementsContent in ppm
Calcium 486 
Magnesium 336 
Potassium 2,652 
Sodium 1,810 
Manganese 1.14 
Aluminium 1.94 
ElementsContent in ppm
Calcium 486 
Magnesium 336 
Potassium 2,652 
Sodium 1,810 
Manganese 1.14 
Aluminium 1.94 

Thermogravimetric investigation

Thermogravimetric analysis was performed to evaluate the thermal decomposition of the raw cactus and to understand its behavior with increasing temperature. Figure 2 shows the TG decomposition profile (green curve) and DTA curve (blue curve). Two main peaks were identified; the first was around 120 °C with 78% of mass loss. This endothermic peak is related to the evaporation of water involved in the composition of cactus and the water involved in dehydration of polysaccharide (Madera-Santana et al. 2018). It should be noted that the loss of moisture in some families of polysaccharides is observed at temperatures above 100 °C (Bothara & Singh 2012). The second peak is around 600 °C with a mass loss of 17%. This exothermic peak could be attributed to the total decomposition of the polysaccharides (Otálora et al. 2021). The residue observed after 600 °C is certainly due to inorganic compounds.
Figure 1

(a) Opuntia Ficus Indica in an agricultural field close to the town of El Jadida (Morocco), (b) (c) (d) steps of preparation of cactus juice.

Figure 1

(a) Opuntia Ficus Indica in an agricultural field close to the town of El Jadida (Morocco), (b) (c) (d) steps of preparation of cactus juice.

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Fourier Transform Infrared (FTIR) characterization

Fourier Transform Infrared (FTIR) spectroscopy is a powerful technique often used to identify functional groups of materials and to study intermolecular interactions. Figure 3(a) shows the global FTIR spectra of cactus juice (red line) and cactus powder (black line), while Figure 3(b) introduces the interval between 800 and 1,800 cm−1. The strong bands around 3,600–3,200 cm−1 in cactus juice (red line) and cactus powder (black line) shown in Figure 3(a), can be attributed to hydroxyl group (-OH) (El Bouaidi et al. 2020). The wide band around 1,650–1,600 cm−1 in Figure 3(b) was observed in cactus juice (red line) and in cactus powder (black line) and was attributed to C-C and H-O-H vibrations (Haxaire et al. 2003). The absorption bands at 1,040 cm−1 observed in cactus juice (red line) and in cactus powder (black line) as shown in Figure 3(b) were attributed to polysaccharides of pectins (Pereira et al. 2016). The bands at 1,320 and 1,500 cm−1 observed in cactus powder (black line) but not in cactus juice (red line) were assigned to C-H methyl vibration of polysaccharides and aromatic group (Matsuhiro et al. 2006; El Bouaidi et al. 2020). However, according to Trachtenberg and Mayer (Trachtenberg & Mayer 1980, 1981, 1982), cactus is mainly composed of different amounts of saccharides such as d-galactose, l-rhamnose, d-xylose, l-arabinose, and galacturonic acid, in addition to other mineral elements such as potassium and calcium. It also contains dietary fibers, which explains the gelatinous properties of cactus juice (Sepúlveda et al. 2007). Finally, the large band at 1,000 cm−1 that was observed in the cactus powder (black line) but not in the cactus juice (red line) has been attributed to cellulose (Hospodarova et al. 2018).
Figure 2

TGA (green line) and DTA (blue line) curves of raw cactus.

Figure 2

TGA (green line) and DTA (blue line) curves of raw cactus.

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1H NMR & 13C NMR spectroscopies characterization

The cactus extract was characterized by nuclear magnetic resonance spectroscopies 1H and 13C NMR. 1H NMR, shown in Figure 4(a), revealed the presence of aromatic ring protons (chemical shift around 7 ppm), CH protons at the chemical shift around 4.5 ppm, CH2 protons at the chemical shift of 3.75 ppm, and C-CH3 groups at chemical shift around 1.25 ppm (Petera et al. 2015; Madera-Santana et al. 2018). The identified functional groups were confirmed by the DEPT 13C NMR as shown in Figure 4(b). The obtained spectrum shows the aromatic carbons in the region of 115–135 ppm, the CH carbons at 70 ppm, the CH2 carbons around 64 ppm, and the CH3 carbons at 20 ppm. Peaks related to the quaternary carbons were identified in the spectrum of normal 13C compared to that of DEPT13C (Figure 4(c)), which appeared in the region of 150–190 ppm. Since cactus juice is composed of several very complicated molecules, and to try to get closer to its structure, we performed 2D NMR experiments. As shown in Figure 4(d), and according to the heteronuclear single quantum coherence between 1H and 13C (HSQC), we can identify the corresponding proton in the 1H to 13C, thus confirming the correlation between each proton and carbons of the previously identified functional groups by 1D NMR. Then, the main proton signals identified at 1.30 ppm, 3.5–4 ppm, 6.75 ppm and 7.10 ppm in the 1H spectrum were assigned to 20 ppm, 60–80 ppm, 115 ppm, and 131 ppm in the 13C spectrum, respectively. This phenomenon can be explained by the presence of various polysaccharides in the cactus juice, which have not been taken into account in this article.
Figure 3

(a) Global FTIR spectra of Cactus juice (Red line) and cactus powder (Black line) and (b) FTIR spectra in the interval between 800 and 1,800 cm−1.

Figure 3

(a) Global FTIR spectra of Cactus juice (Red line) and cactus powder (Black line) and (b) FTIR spectra in the interval between 800 and 1,800 cm−1.

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GC-MS analysis

GC-MS analysis of cactus juice revealed the presence of many compounds as shown in Figure 5. Table 2 summarizes the main compounds found, indexed in the NIST/EPA/NIH MASS SPECTRAL LIBRARY Version 2011 database. As we can see from this table, the two major compounds were the Steroid Androstane and Gibberellin. Figure 5(b) and 5(c) show their MS spectra, respectively. It is reported in the literature that Steroid Androstane is considered as a reproductive hormonal compound in plants (Sultan 2015). In addition, the Gibberellin molecule is considered as a growth hormone in the flowering mechanisms of plants (Boyle et al. 1994; Abo-El-Ez et al. 2023). Other minor molecules were observed in the chromatogram, such as 1-Diphenyl (methyl) silyloxy-cyclohexane, gallic acid, classified as an antioxidant agent (Balaji et al. 2022), and 1-(2-Isopropyl-phenyl)-3,6,6-trimethyl-1,5,6,7-tetrahydro-indazol, classified in the family of Phenylpyrazols (antioxidants), and analgesics used in the pharmacological industry (Nagai et al. 1979; Karrouchi et al. 2018). Thus, the presence of the last two compounds considered as antioxidants can explain the stability of cactus juice as a flocculant. It has been observed that the storage of cactus juice, at room temperature, for a long time (6 months) does not change its flocculant properties.
Table 2

CG-MS molecular identification of cactus juice

50RTAreaArea 100%Compound NameMol. FormulaMWSIRSIProb.N° CasLibrary
20.05 427802 100.00 Androstane-11,17-dione,3 [(trimethyl)oxy]-, 17[O,(phenylmethyl)oxime],3à 5à- C29H43NO3Si 481 488 634 16.98 mainly1-0 Mainlib 
20.05 427802 100.00 Gibb-3-ene-1,10-dicarboxylic acid, 2,4a-dihydroxy-1-methyl-8-methylene-, 1,4a-lactone, 10-methyl ester, (1à,2á,4aà,4bá,10á)- C20H24O5 344 487 591 16.32 5508-47-4 Mainlib 
20.05 427802 100.00 Ethyl gallate, 3TMS derivative C18H34O5
Si3 
414 457 524 4.53 Na Mainlib 
20.05 427802 100.00 1-Diphenyl (methyl) silyloxycyclohexane C19H24OSi 296 452 591 3.65 20466-56-2 Mainlib 
20.05 427802 100.00 1-(2-Isopropyl-phenyl)-3,6,6-trimethyl-1,5,6,7-tetrahydro-indazol-4-one C19H24N2O 296 450 570 3.37 NA Mainlib 
50RTAreaArea 100%Compound NameMol. FormulaMWSIRSIProb.N° CasLibrary
20.05 427802 100.00 Androstane-11,17-dione,3 [(trimethyl)oxy]-, 17[O,(phenylmethyl)oxime],3à 5à- C29H43NO3Si 481 488 634 16.98 mainly1-0 Mainlib 
20.05 427802 100.00 Gibb-3-ene-1,10-dicarboxylic acid, 2,4a-dihydroxy-1-methyl-8-methylene-, 1,4a-lactone, 10-methyl ester, (1à,2á,4aà,4bá,10á)- C20H24O5 344 487 591 16.32 5508-47-4 Mainlib 
20.05 427802 100.00 Ethyl gallate, 3TMS derivative C18H34O5
Si3 
414 457 524 4.53 Na Mainlib 
20.05 427802 100.00 1-Diphenyl (methyl) silyloxycyclohexane C19H24OSi 296 452 591 3.65 20466-56-2 Mainlib 
20.05 427802 100.00 1-(2-Isopropyl-phenyl)-3,6,6-trimethyl-1,5,6,7-tetrahydro-indazol-4-one C19H24N2O 296 450 570 3.37 NA Mainlib 
Figure 4

NMR spectra of cactus juice. (a) 1H NMR, (b) DEPT 13C NMR, (c) normal 13C NMR spectrum, and (d) 2D NMR.

Figure 4

NMR spectra of cactus juice. (a) 1H NMR, (b) DEPT 13C NMR, (c) normal 13C NMR spectrum, and (d) 2D NMR.

Close modal

Rheological behavior

A rheological test was performed on the cactus juice at constant temperature (20 °C) and under increasing shear rate from 10 to 1,000 l/s. The results show a decrease in viscosity with increasing shear rate as shown in Figure 6.
Figure 5

GC-MS analysis of cactus juice. (a) chromatogram of cactus juice with is related MS spectrum, (b) MS specta of Steroid Androstane, and (c) MS spectra of Gibberellin.

Figure 5

GC-MS analysis of cactus juice. (a) chromatogram of cactus juice with is related MS spectrum, (b) MS specta of Steroid Androstane, and (c) MS spectra of Gibberellin.

Close modal

It is well known that a shear-thinning fluid is characterized by a decrease in apparent viscosity as the velocity gradient increase (Perrin et al. 2006). Therfore, the observed behavior may be due to the fact that the time required for the rearrangement of the chains exceeds the time scale of deformation. Hence the elastic deformation of the entangled network becomes progressively larger and the system behaves like an elastic solid, exhibiting a nonlinear model that characterizes non-Newtonian fluids (Denn 2004). This behavior can be attributed to the disorder of the macromolecules, which are mainly composed of D-xylose, D-galactose, L-arabinose, L-rhamnose and D-galacturonic acid (Cárdenas et al. 1997; Pichler et al. 2012).

According to the obtained results, the rheological behavior of cactus juice is in perfect agreement with Casson's model (Nazeer et al. 2021; Verma & Mondal 2021). Several industrial flocculants used to remove suspended matter from water or to condition sludge show identical behavior (Nasser & James 2007; Feng et al. 2020).

Zeta potential and size distribution measurements of cactus juice

Zeta potential is a technique that measures the total surface charge of particles present in a liquid sample. Its principle is based on measuring the velocity of particles when they are subjected to an electric field and become charged, migrating towards electrodes of opposite polarity in proportion to the intensity of the field and the zeta potential (Bean et al. 1964; Pestana et al. 2015). This technique can be used to distinguish between cationic and anionic flocculants.

According to Figure 7(a), the zeta potential of cactus juice as a flocculant tends towards a negative charge of approximately −25 mV. It should be noted that all the tests were carried out on cactus juice in its natural state, at a pH of 4.7 and under ambient conditions. These results could explain the anionic charge of cactus juice and can justify its affinity with the usual coagulants used in coagulation-flocculation techniques, as discussed in the paragraph below. In addition, the size distribution of the cactus juice shown in Figure 7(b) shows two persistent grain size slices, a first and small population with a diameter size of 25 nm and a second large population with a diameter size of 250 nm.
Figure 6

Rheological behaviour of cactus juice.

Figure 6

Rheological behaviour of cactus juice.

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Application for removal of organic matter in domestic wastewater

The objective of this section is to provide an application of cactus juice in order to confirm its flocculant activity as suggested by the characterization discussed above. As previously reported elsewhere (Bouaouine et al. 2018; Othmani et al. 2020), the presence of neutral sugars and uronic acids are assumed to be the active flocculating agents in cactus juice. Polygalacturonic acid, consisting of a long polymer chain containing functional groups, mainly carboxyl (-COO)-/-COOH) and hydroxyl (-OH), provides both positively and negatively charged adsorption sites that interact electrostatically to create charge neutrality between the flocculant and the cationic pollutant. For anionic particles that carry the same charge as the flocculant, flocculation mechanisms do not operate in the same way as for cationic pollutants, but rather through an adsorption and bridging mechanism between the particles and the flocculant (Bouaouine et al. 2018; Choudhary et al. 2019).

In the experimental part, a series of experiments were carried out for the removal of chemical oxygen demand (COD) from wastewater by coagulation/flocculation process using aluminum sulphate as a coagulant and cactus juice as a bioflocculant. The effect of aluminum sulfate and catus juice doses, as well as pH on the coagulation/flocculation process were investigated. The efficiency of the treatment was based on the COD removal. Table 3 shows the characteristics of the wastewater used and the coagulated wastewater after treatment.

Table 3

Results of analysis of raw wastewater and coagulated wastewater in the optimized conditions

UnitRaw wastewaterCoagulated wastewater
Ph – 7.32 7.06 
Conductivity μS/cm 1,718 1,810 
COD mg/L 930 21 
Turbidity NTU 76.5 
UnitRaw wastewaterCoagulated wastewater
Ph – 7.32 7.06 
Conductivity μS/cm 1,718 1,810 
COD mg/L 930 21 
Turbidity NTU 76.5 

In order to determine the optimal conditions of the coagulation/flocculation process, we first followed the evolution of COD as a function of varying doses of the coagulation at fixed doses of flocculant. Secondly, we have followed the evolution of COD as a function of varying doses of flocculant at fixed doses of coagulant. For this purpose, varying doses of coagulant (aluminum sulphate), ranging from 32 to 194 mg/L of aluminum, were added to a series of beakers containing 50 ml of wastewater at ambient temperature and stirred for two minutes at a speed of 100 rpm. A dose of 2.85 g/L of flocculant (cactus juice) was then added and the mixture was stirred at 50 rpm for six minutes. Finally, the mixture was allowed to settle for 20 minutes. Figure 8(a) shows the evolution of COD removal yield as a function of coagulant dose. As seen in this figure, the optimum dose was found to be 64.7 mg/L of aluminum. This optimized coagulant dose was used for further optimization. Regarding the optimization of the flocculant dose, after performing the coagulation step described above, different doses of cactus juice, ranging from 0.95 to 6.65 g/L, were added to the beakers and stirred at a speed of 100 rpm for two minutes, and then allowed to settle for 20 minutes. Figure 8(b) shows the evolution of COD removal yield as a function of flocculant dose. The optimized dose of cactus juice was found to be 3.80 g/L. On the other hand, the effect of pH on COD removal was studied from 2 to 12 (Figure 8(c)). pH adjustment was carried out by solutions of 1 M NaOH and 1 M H2SO4. The obtained results show that the best yield of COD elimination was in the pH range of 6–8. For a pH higher than 8 or lower than 4, the surface charge of the coagulants was affected, leading to the destabilization of the suspension (Saritha et al. 2017).
Figure 7

(a) zeta potential measurements and (b) size distribution of cactus juice.

Figure 7

(a) zeta potential measurements and (b) size distribution of cactus juice.

Close modal
Figure 9 illustrates a disturbance in the settling of particles (presence of flotation phenomenon) at pH conditions below 6 or above 8, which justifies the increase in COD in the treated water. Under optimal conditions, large, rigid, and well-settled flocs were obtained in less than 20 minutes.
Figure 8

Optimisation of coagulant/flocculant doses as a function of the yield of COD removal. (a) yield of COD removal as a function of aluminium dose, (b) yield of COD removal as a function of cactus juice dose, and (c) effect of pH.

Figure 8

Optimisation of coagulant/flocculant doses as a function of the yield of COD removal. (a) yield of COD removal as a function of aluminium dose, (b) yield of COD removal as a function of cactus juice dose, and (c) effect of pH.

Close modal
Figure 9

Coagulation-flocculation process: (a) pH 4, (b) pH 10, (c) pH 7 and (d) wastewater before treatment.

Figure 9

Coagulation-flocculation process: (a) pH 4, (b) pH 10, (c) pH 7 and (d) wastewater before treatment.

Close modal

In summary, the removal of organic matter in wastewater is effective with a COD removal of more than 97%. These results are in agreement with several studies carried out on the effectiveness of cactus juice as a green flocculant in the treatment of wastewater such as petrochemical effluent, food industry effluent, and controlled discharge leachate, with 72, 88 and 82% of COD removal, respectively (Rebah & Siddeeg 2017). In addition, the obtained COD removal yield (97%) proves the high flocculating activity of cactus juice, compared to other plant derivatives, such as Moringa oleifera, Salvia hispanica seeds and mango kernels (COD removal yield of 88.76; 39,7 and 33,4%, respectively; Das et al. 2021).

The structural and physicochemical properties of Moroccan cactus juice were investigated in this study. Several powerful techniques such as ICP-AES, FTIR, NMR, GC-MS, TGA, zeta potential, and rheology were used to achieve this objective. The physicochemical characterization of the cactus juice indicated the presence of numerous organic compounds such as polysaccharides and mineral elements (potassium, sodium, calcium, magnesium, aluminum, and manganese), which are considered to be the origin of the significant reduction of the chemical oxygen demand in the wastewater, which decreases drastically with the increase in the added quantity of cactus juice. These results demonstrate the flocculating behavior of cactus juice as a green and sustainable biopolymer.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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