Gudkov Sergey V, Shafeev Georgy A, Glinushkin Alexey P, Shkirin Alexey V, Barmina Ekaterina V, Rakov Ignat I, Simakin Alexander V, Kislov Anatoly V, Astashev Maxim E, Vodeneev Vladimir A, Kalinitchenko Valery P
Prokhorov General Physics Institute RAS, 38 Vavilova Street, Moscow 119991, Russia.
National Research Nuclear University MEPhI (Moscow Engineering Physics Institute), 31 Kashirskoe sh., Moscow 115409, Russia.
ACS Omega. 2020 Jul 10;5(28):17767-17774. doi: 10.1021/acsomega.0c02448. eCollection 2020 Jul 21.
The synergy problem was discussed linking Se nanoparticles and different soil fertility agents. Se zero-valent-state nanoparticles were investigated as fertilizers and antioxidants. A technology was proposed for producing Se zero-valent-state nanoparticles. Se nanoparticles were obtained by laser ablation of Se in water using a fiber ytterbium laser, with a wavelength between 1060 and 1070 nm, a pulse repetition rate of 20 kHz, a pulse duration of 80 ns, and an average power of 20 W, and a copper vapor laser with wavelengths of 510.6 and 578.2 nm and an average power of 8 W. The main particle mass part shifted from 800 nm to a size less than 100 nm, corresponding to the increase in the laser fragmentation time. The resulting nanoparticles were monodisperse in size and mass. The Se nanoparticle water suspension was introduced into the soil. The soil Se nanoparticle concentrations were about 1, 5, 10, and 25 μg kg. An experiment was carried out in a climate chamber in two series: (1) growing plants in soil imitating the standard organogenesis environment conditions such as illumination of 16 h per day, temperature of 22 °C, soil humidity of 25% SDW, and an experiment duration of 30 days and (2) growing plants in soil under changing environmental conditions of organogenesis. The standard environmental conditions for the first 10 days are illumination of 16 h day, temperature of 22 °C, and soil humidity of 25% SDW. The plant stress for 5 days is hyperthermia of 40 °C. The standard environmental conditions for the next 15 days are illumination of 16 h day, temperature of 22 °C, and soil humidity of 25% SDW. At standard organogenesis, the plant leaf plate surface area was 30 ± 2 cm in the control option, and the Se nanoparticle doses were correspondingly 1 μg kg for 32 ± 3 cm, 5 μg kg for 37 ± 2 cm, 10 μg kg for 38 ± 3 cm, and 25 μg kg for 28 ± 4 cm. Hyperthermia stressed plant growth was studied. The highest plant growth rate was in Se nanoparticle concentrations of 5 and 10 μg kg. The eggplant growth on the soil with the Se nanoparticle addition at a concentration of 10 μg kg of leaf plate surface area was twice compared to the eggplant growth in untreated soil. The same was for tomato plants. The leaf plate surface area of the cucumber plant grown using Se nanoparticles was 50% higher compared to the control option. The Biogeosystem technique methodology of 20-45 cm soil-layer intrasoil milling for soil multilevel aggregate system formation and intrasoil pulse continuous-discrete watering for soil water regime control was proposed for the Se nanoparticles for better function in the real soil, providing a synergy effect of soil mechanical processing, nanoparticles, humic substances, and polymicrobial biofilms on soil fertility.
讨论了硒纳米颗粒与不同土壤肥力因子的协同作用问题。研究了零价态硒纳米颗粒作为肥料和抗氧化剂的性能。提出了一种生产零价态硒纳米颗粒的技术。通过在水中用光纤镱激光器(波长在1060至1070nm之间,脉冲重复频率为20kHz,脉冲持续时间为80ns,平均功率为20W)和铜蒸气激光器(波长为510.6和578.2nm,平均功率为8W)对硒进行激光烧蚀来制备硒纳米颗粒。主要颗粒质量部分从800nm转移到小于100nm的尺寸,这与激光破碎时间的增加相对应。所得纳米颗粒在尺寸和质量上是单分散的。将硒纳米颗粒水悬浮液引入土壤中。土壤中硒纳米颗粒的浓度约为1、5、10和25μg/kg。在气候箱中进行了两个系列的实验:(1)在模拟标准器官发生环境条件的土壤中种植植物,如每天光照16小时、温度22°C、土壤湿度25%SDW,实验持续30天;(2)在器官发生环境条件变化的土壤中种植植物。前10天的标准环境条件是每天光照16小时、温度22°C、土壤湿度25%SDW。植物胁迫5天为40°C高温。接下来15天的标准环境条件是每天光照16小时、温度22°C、土壤湿度25%SDW。在标准器官发生条件下,对照选项中植物叶片表面积为30±2cm,硒纳米颗粒剂量分别为1μg/kg时为32±3cm、5μg/kg时为37±2cm、10μg/kg时为38±3cm、25μg/kg时为28±4cm。研究了高温胁迫下的植物生长。硒纳米颗粒浓度为5和10μg/kg时植物生长速率最高。在添加浓度为10μg/kg硒纳米颗粒的土壤上茄子的生长,其叶片表面积是未处理土壤中茄子生长的两倍。番茄植株也是如此。使用硒纳米颗粒种植的黄瓜植株的叶片表面积比对照选项高50%。为使硒纳米颗粒在实际土壤中发挥更好作用,提出了20 - 45cm土层土壤内研磨以形成土壤多级团聚体系统和土壤内脉冲连续 - 离散浇水以控制土壤水分状况的生物地球系统技术方法,从而实现土壤机械处理、纳米颗粒、腐殖质和多微生物生物膜对土壤肥力的协同效应。