All over the world today there is a shortage of clean water due to rapid population growth, environmental degradation, uncontrolled disposals from industrial enterprises and the widespread introduction of chemical technologies in agriculture. Despite the widespread construction of modern treatment facilities, it is not possible to achieve complete wastewater treatment. This is due to the presence of difficult-to-oxidize organic pollutants, the most common of which are phenol-containing substances and antibiotics. Traditional treatment methods include mainly biological treatment and a number of physicochemical methods such as adsorption, ion exchange and reverse osmosis. The disadvantages of these methods include the non-destructive nature of cleaning, high energy and operating costs, low efficiency and the generation of large amounts of waste. In recent years, environmentally friendly and energy-efficient advanced oxidation technologies have been actively developed, among which photo-catalysis (PC) occupies an important place [
1,
2]. An important advantage of PC is the possibility of oxidation at relatively low concentrations of pollutants [
3], which is important for the mineralization of toxic organic pollutants with low maximum permissible concentrations. The efficiency of PC is determined by the efficiency of formation and separation of photo-charges. For a long time, the main photo-catalyst produced on an industrial scale was titanium dioxide (TiO
2) from Degussa (P-25) [
4]. The disadvantage of TiO
2 is its significant band gap (Eg = 3.2 eV) and its maximum photo-catalytic activity when irradiated with ultraviolet (UV) light. Ultraviolet radiation takes up only 5-7% of solar radiation. At the same time, visible radiation makes up about 45% and the search for photo-catalysts active in the visible region is very relevant. A huge number of works are devoted to heterostructural and composite photo-catalysts exhibiting activity in the visible region [
5,
6,
7,
8,
9,
10]. Despite individual studies demonstrating the effectiveness of hybrid photo-catalysts, the traditionally used TiO
2 still remains the most popular. This is due to the lack of economically accessible technology for mass production of hybrid photo-catalysts. As an alternative to TiO
2, ZnO [
11,
12], which is not inferior in efficiency and availability, has recently been actively studied. Despite the similarity of the band gap of ZnO (3.37 eV) with TiO
2 (3.2 eV), a distinctive feature of the band structure of ZnO is the presence of isolated energy levels in the band gap associated with point defects, mainly oxygen vacancies [
13]. With a significant increase in the concentration of vacancies, photosensitivity can expand into the visible region of the spectrum. An additional source of levels in the forbidden zone are dislocations. The band structure is distorted around the dislocation core and a level is introduced closer to the center of the band gap. In n-type crystals, which include ZnO, dislocations can capture electrons and prevent their recombination. The highest concentration of defects is observed in crystals synthesized under conditions that are far from ideal: high saturation, unstable temperature gradient, chaotic influx of atoms. Such conditions can be created using plasma synthesis of metal oxide structures [
14]. Plasma synthesis using gas-discharge plasma is not only energy efficient, but also has a high productivity. Of greatest interest is the microwave (MW) discharge of atmospheric pressure, which has a much higher charge density and, as a consequence, greater reactivity compared to other discharges at the same power. Note also that in some types of atmospheric pressure discharges (corona, spark and arc), the plasma is “contaminated” by the material of the internal discharge electrodes. This can be avoided by investing energy in a microwave discharge excited in discharge chambers (for example, dielectric tubes) in the absence of direct contact with metal electrodes. This property is of fundamental importance for creating high-purity plasma. It should be noted that the possibility of using microwave plasma for the synthesis of photocatalytically active ZnO tetrapods was previously studied in [
15]. However, the authors pay attention only to plasma regions in which the conditions for the formation of ZnO tetrapods are realized. This approach generally limits the performance of the photoactive ZnO catalyst. It seems to us that loading zinc metal powder directly into the gas transportation system is an important technological solution. Thus, the residence time of zinc metal in the plasma increases. Taking into account the plasma temperature of 5000-6000 K, one can expect instantaneous evaporation of zinc and the formation of individual ZnO elements with a wide range of sizes and different micromorphologies. It should be noted that micron-sized particles injected into a gas-discharge plasma become centers of recombination of plasma electrons and ions (sometimes a source of electrons owing to thermo-, photo-, and secondary electron emissions) and acquire a negative electric charge because of the greater mobility of electrons. In this case, the particle charge can reach significant values of up to 10
3-10
5 electron charges [
16,
17]. Owing to electrostatic interaction, particles of the same charge sign experience mutual Coulomb repulsion, which prevents them from sticking together and forming agglomerates. As a result, the form of individual ZnO elements with a large variation in size and different micromorphology with a developed surface can be expected. In order to enhance the photosensitivity of ZnO powder in the visible region, one can resort to nitridation of ZnO [
18]. For this purpose, it is possible to use nitrogen as a buffer plasma-forming gas.
In the presented work, the processes of synthesis of nitrogen-containing ZnO structures using microwave plasma were studied and their photocatalytic activity in the processes of degradation of 2,4-dinitrophenol and the antibiotic ciprofloxacin under irradiation with sunlight was investigated.