A green approach in the frame of circular economy: robocasted photocatalysts for wastewater treatment and use of reclaimed water in agriculture


Project Director: Dr. Irina ZGURA


Project ID: WaterGreenTreat

Project Director: Dr. Irina Zgura

Project Type: International

Project Program: COFUND-WATER4ALL

Funded by: Romanian National Authority for Scientific Research, UEFISCDI

Contractor: National Instiute of Materials Physics

Start Date: 1 April, 2024

End Date: 31 March, 2027

Project Abstract: 

The aim of this proposal consists in the obtaining macroporous photocatalysts based on ecogenic metal oxides (ecoMO) (ZnO/CuO) composites through the robocasting technique, but also the evaluation the synergistic effect induced by the presence of microalgae in the removal of specific pollutants for wastewater treatment and the use of regenerated water in agriculture. The main objectives of the project are the following: (i) green synthesis of photo-catalysts based on metal oxides (ZnO, CuO) nanoparticles (NPs), (ii) 3D-printing structures based on ecogenic metal oxides by robocasting, (iii) the use of the obtained 3D photocatalytic structures based on metal oxides NPs to remove contaminants such as antibiotics or dyes from the wastewater generated by pharmaceutical/textile industry, (iv) the use of the microalgae to reduce the pollutant species generated during the photocatalysis process, and (v) the assessment of the synergistic effect induced by the 3D photocatalytic structures and microalgae at laboratory/semi-industrial/greenhouse level on synthetic wastewater (by adding drugs/dyes) and in real wastewater (treatment plants). This project has the following specific objectives: 1) Phytosynthesis and characterization of metal oxide, metallic NPs and their composites. 2) The use of ecoMO to treat, in laboratory, various synthetic wastewaters (containing organic dyes, drugs, etc.). 3) In vitro biological investigations [cytotoxicity evaluation by acute and chronic Aliivibrio fischeri assays (ISO 11348), acute algae (OECD 201) and Daphnia (OECD 202), and zebrafish embryo toxicity assay (OECD 236)]; and the ecoMO bio-impact on terrestrial and aquatic media will be tested. 4) The synthetic/real wastewaters (before and after the treatment with robocasted photocatalysts based on ecoMO composites) will be tested as follows: (i) in vivo on plants grown in the greenhouse (didactic and scientific research resort); (ii) in vitro on Aliivibrio fischeri for acute cytotoxicity (ISO 11348 standard) and for chronic toxicity in a high throughput assay adapted to microplates; Daphnia acute tests; and acute toxicity measurement on zebrafish eggs for wastewater qualification (ISO 15088). 5) Evaluation of the detoxification efficiency of different composite samples based on ecological metal oxide (ecoMO) nanoparticles and their robocasted photocatalysts by microalgae culture in a treated wastewater environment, but also of the synergistic effect induced by the presence of microalgae on the ecological composite of metal oxide nanoparticles or their robocasted photocatalysts based on ecoMO composites for the removal of certain pollutants. Upon our knowledge, there are no reports regarding robocasted photocatalysts based on ecoMO composites (ZnO/CuO). In the frame of circular economy, it is necessary to identify and develop efficient technologies for treatment of the residual waters generated by pharmaceutical, textile, etc. industries in order to use the reclaimed water for agriculture. The elimination of the pharmaceutically active compounds (PhACs) and dyes from water generated from pharmaceutical and textile industry is vital for using the reclaimed water in other fields such as agriculture. Thus, reclaimed water obtained through a synergistic effect induced by 3D-printed photocatalytic structures and microalgae can be used in agriculture activities. Moreover, taking into account that the increase of periods with high temperature has the direct effect of decreasing the flow of surface water, which also influences the flow of shallow underground water, the population can be constrains to reduce the crop irrigation. This impediment can be mitigated by reusing treated wastewater in agriculture. Consequently, the outcome of our proposal can improve the resilience and adaptation capacity of wastewater treatment facilities within the frame of hydroclimatic extreme events.

National Institute of Materials Physics (NIMP), Romania – Project Coordinator: Dr. Irina Zgura

Universitatea Bucuresti, Romania – Partner Leader: Conf. Univ. Dr. Marcela-Elisabeta Bărbînţă-Pătraşcu

MAGYAR AGRAR- ES ELETTUDOMANYI EGYETEM, Institute of Aquaculture and Environmental Safety, Hungary – Partner Leader: Dr. Judit Hahn

UNIVERSIDAD DE EXTREMADURA, Spain – Partner Leader: Dr. Antonia Pajares

CENTRE NATIONAL DE LA RECHERCHE SCIENTIFIQUE CNRS, GEPEA UMR6144, France – Partner Leader: Dr. Pascale Gillon

NIMP’s team members:

Dr. Irina Zgura

Dr. Nicoleta Preda

Dr. Monica Enculescu

Dr. George Stan

Dr. Liviu Nedelcu

Dr. Oana Rasoga

Dr. Carmen Breazu

Dr. Paul Constantin Ganea

PostDoc Monica Dinescu

PhD student Madalina Chivu

Open-position

Open-position

Year 2024

During the implementation period (2024), activities were carried out regarding the preparation and characterization of the commercial metal oxide–based samples, evaluated in terms of morphological, structural and optical properties, both as monocomponent systems (ZnO, CuO) and as composites (ZnO–CuO). Structural characterization by X-ray diffraction (XRD) confirmed that the commercial powders exhibited diffraction peaks corresponding to hexagonal wurtzite ZnO and monoclinic CuO phases. The morphological properties were assessed through scanning electron microscopy (SEM), the images revealing particles with sizes below 100 nm, a result consistent with the partner’s DLS measurements.

Optical measurements (reflectance spectra and FTIR spectra) highlighted the optical signature of both ZnO and CuO components in the composite materials. Eco-impact (eco-toxicological) evaluation, including greenhouse/laboratory plant assays, urease activity testing, and photosynthesis/respiration measurements, indicated that:
i) the tested powder samples did not exhibit urease inhibition activity at 1 g/L concentration (due to the absence of bioactive surface compounds), and
ii) the samples did not present antioxidant properties (due to the lack of bioactive compounds capable of scavenging and neutralizing free radicals).
These results, together with the urease inhibition assays, demonstrate the necessity of using metal oxide nanoparticles obtained through ecological (plant-extract-based) synthesis, since phytoderived oxides possess surface phytomolecules that may induce relevant bioactivities.

Regarding the photocatalytic activity of commercial nanometric metal oxide powders, composite samples displayed better photocatalytic performance than monocomponent ZnO or CuO. The highest degradation efficiency was observed for the composite containing 3% CuO. At the optimum concentration, CuO acts as an electron trap, reducing electron–hole recombination and thus significantly enhancing photocatalytic performance.

Synthetic wastewater treated with commercial metal oxide powders prior to photocatalytic degradation (performed by the partner) caused deterioration of photosynthesis and respiration processes in plants, leading to premature plant death due to the presence of RhB in the water. After photocatalytic treatment using commercial metal oxide powders, the treated water showed a stimulatory effect on plant development, improving photosynthesis and respiration rates.

In the evaluation of RhB photodegradation using 3D-printed structures, longer irradiation times and significantly higher photocatalyst loadings (approximately 100-fold) were required. This is attributed to the substantially lower specific surface area of 3D-printed structures compared to commercial metal oxide powders. However, despite the increased irradiation time and catalyst quantity, the photocatalytic effect obtained with 3D structures was comparable to that of powdered catalysts, with several key advantages:
i) elimination of the filtration step, which is difficult to perform;
ii) easy separation and reuse of printed structures;
iii) production of treated water free of particulate impurities.
Composite-based 3D structures exhibited better photocatalytic behavior than monocomponent ZnO or CuO 3D samples, with improved degradation efficiency observed in structures containing 1% and 3% CuO.

Water treated with robocasted structures showed beneficial effects on plants, as confirmed by photosynthesis and respiration measurements, which were similar to the control samples. Among all robocast structures, the 3D ZnO97%–CuO3% composite displayed the highest RhB photodegradation efficiency. Based on these results, this composite was further selected for urease activity and ecotoxicity assessment. In treatments using water decontaminated with 3D_ZnO97%–CuO3%NPs, ecotoxicity studies indicated two essential aspects: lack of toxicity and potential applicability in agriculture.

Year 2025

During the implementation period (2025), activities were carried out regarding the preparation and characterization of the phytosynthesized metal oxide–based samples, evaluated in terms of morphological, structural, and optical properties, both as monocomponent systems (ZnO, CuO) and as composites (ZnO–CuO). Structural characterization by X-ray diffraction (XRD) confirmed that the phytosynthesized powders exhibited diffraction peaks corresponding to hexagonal wurtzite ZnO and monoclinic CuO phases. The morphological properties were assessed through scanning electron microscopy (SEM), the images showing that the samples consist of particles with an average size of approximately 200 nm, a result consistent with the partner’s DLS measurements.

Optical measurements (reflectance spectra and FTIR spectra) highlighted the optical fingerprints of the two components, ZnO and CuO, in the composite materials. The eco-impact (eco-toxicological) evaluation, including testing on greenhouse/laboratory plants, urease activity assays, and assessment of photosynthesis and respiration, revealed that:
i) among the tested samples (ecoMO and their composites), only two samples (EcoZnO95%–CuO5%NPs and EcoZnO99%–CuO1%NPs) showed a more pronounced urease inhibition activity at a concentration of 1 g/L. The anti-ureolytic activity of EcoZnO95%–CuO5%NPs was 53.902%, while EcoZnO99%–CuO1%NPs was 43.33%. A slight inhibitory effect was also observed for EcoZnO100% and EcoCuO100%.
ii) the samples exhibit antioxidant properties, attributed to the presence of bioactive compounds capable of scavenging and eliminating free radicals from the environment. The highest AA% values were recorded for EcoCuO100%NPs and EcoZnO99%–CuO1%NPs.

Regarding the investigation of the photocatalytic activity of the phytosynthesized metal oxide powders, it was found that the composite samples exhibited superior photocatalytic performance compared to the monocomponent ZnO or CuO powders. The highest degradation efficiency was obtained for the composite containing 3% CuO. When comparing all results obtained on powdered eco-synthesized materials, EcoZnO97%–CuO3%NPs was identified as the most efficient in RhB and paracetamol photodegradation.

Analysis of synthetic wastewater treated with commercial metal oxide powders prior to photocatalytic degradation (performed by the partner) showed that the presence of RhB in the treated water accelerated senescence, ultimately causing premature plant death (similar to Stage I, 2024). Therefore, these plants could not be used for subsequent photosynthesis/respiration evaluation. The photosynthesis process of plants treated with water treated using eco-synthesized metal oxide powders (EcoZnO97%–CuO3%, 400°C, 2.5h) was not inhibited. Meanwhile, basil plants treated with RhB-containing water photocatalytically degraded in the presence of EcoMO powders and their composites exhibited a significant decrease in respiration, particularly for EcoZnO99–CuO1% and EcoZnO97–CuO3%.

For the evaluation of RhB photodegradation in the presence of 3D-printed structures, significantly larger quantities of photocatalyst were required (approximately 20-fold higher). This is attributed to the substantially lower specific surface area of the 3D-printed structures compared to powdered catalysts. Nevertheless, despite the higher catalyst loading, the use of 3D-printed structures in dye-containing wastewater treatment offers several important advantages:
i) elimination of the additional filtration step, which is laborious and challenging to implement;
ii) easy separation and reuse of the printed structures;
iii) obtaining treated water free from particulate impurities.

Composite-based 3D-printed samples exhibited better photocatalytic activity than monocomponent ZnO or CuO 3D samples. The effect of wastewater treated with robocast structures on plants was assessed through photosynthesis and respiration analysis. Results showed that:
i) photosynthesis was not affected by the treatments, and
ii) respiration remained unaffected in plants treated with water decontaminated using 3D EcoCuO100% and 3D EcoZnO99%–CuO1%. For other samples, a slowdown in respiration was observed.

When using water decontaminated with 3D EcoCuO100% and 3D EcoZnO99%–CuO1%, ecotoxicity studies highlighted important aspects, such as lack of toxicity and the potential applicability of these materials in agriculture.

Contact

Project Coordinator: Dr. Irina Zgura

Phone: +40-(0)21-3690185, +40-(0)21-2418100

Fax    : +40-21369 0177

e-mail: irina.zgura@infim.ro


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