Automated system for cleaning liquid waste products for closed ecosystems for space purposes

Capa

Citar

Resumo

Ensuring human life activity for several years in isolated conditions of future Martian and lunar bases is possible with the organization of a circular process of converting organic waste, including human exometabolites (cal, urin), into the products he needs: water, oxygen and food. A promising way to organize such a circular process is to create a three–link closed ecosystem (CES): a person, a link for obtaining fertilizers from organic waste and plants - where plants synthesize the products necessary for a person. The paper considers the original scheme of a complex installation for the purification of liquid products of processing of human exometabolites from pollutants in the process of obtaining nutrient solutions for growing plants in a CES. The processing of human exometabolites was carried out in a device for physicochemical oxidation of hydrogen peroxide in an aqueous medium under the action of alternating electric current – in a “wet” combustion reactor. Peripheral equipment was selected for the organization of the automatic control system of the cleaning plant, problems were identified and approaches were developed in the automation of technological processes and the creation of software for human interaction with the proposed installation. Experiments on the cultivation of lettuce plants have been carried out, confirming the effectiveness of the proposed processes of purification of liquid products of processing of human exometabolites. It is concluded that the created integrated cleaning plant, equipped with the proposed software, can be used for scientific research in relation to the subject of CES, including space purposes.

Texto integral

Introduction

The problem of creating closed ecosystems (CES) to ensure human life during long-term space flight and stay on celestial bodies (Moon, Mars, asteroids, etc.) is currently receiving increasing attention from leading space agencies and other major research centers  [1; 2]. In Russia, the Institute of Biophysics SB RAS(Siberian Branch of Russia Academy of Science) is actively engaged in the development of closed ecosystems for space purposes [3]. At the same time, much attention is paid to the creation of models of closed ecosystems. Various patterns of circular processes are worked out on their basis, which can then be the basis for the creation of full-scale closed ecosystems with humans. Future closed ecosystems should include both biological and physico-chemical methods of waste oxidation for their subsequent inclusion in cycling processes  [4–17]. To ensure the effective operation of the physical and chemical processes of oxidation of organic and inorganic waste in CES, it is extremely important to create and sustainably operate a set of necessary instruments and equipment. An integral part of such equipment is an installation for the purification of liquid products of human waste processing (feces, urine), since the process of waste oxidation produces pollutants that inhibit plant growth.  The Institute of Biophysics of the SB RAS is conducting research on the creation of such cleaning methods in relation to closed ecosystems. In particular, software is being developed to automate cleaning processes  [17; 18].

The purpose of this work is biotesting of solutions obtained after purification and the development of a digital automated control system for the installation of physical and chemical purification of mineralized human exometabolites.

Methods and approaches

Long-term daily direct application of mineralized exometabolites into the irrigation solution will cause its salinity due to the high NaCl content in human urine [19; 20]. In addition, the “wet” combustion method is practically unable to utilize urea, which increases the risk of the development of opportunistic urobacteria in the system [21] and reduces the availability of nitrogen for the plant CES link. Therefore, the complex of physical and chemical processing of organic waste includes, in addition to “wet” combustion, several more sequential processes for purifying solutions of mineralized exometabolites, for each of which a reactor has been developed [18]: 1) decomposition of urea; 2) release of Cl2; 3) synthesis of HCl; 4) release of alkali; 5) release of Na2CO3; 6) synthesis of NaCl. Together, these 6 reactors are a plant for the purification of liquid products of physical and chemical processing of human waste products.

To assess the influence of liquid products of the physicochemical oxidation of human exometabolites on plants, we used previously developed methodological approaches for preparing nutrient solutions on this basis for their subsequent use in an experimental model of a closed ecosystem, subject to regular (once every 7 days) replacement of 1/8 of the nutrient solution with water. That is, in 8 weeks there was a complete change of solution [22].

Studying the influence of possible pollutants in a nutrient solution required testing the possibility of long-term use of permanent solutions prepared on the basis of liquid products of the mineralization of human exometabolites for growing plants. The object of research was the “Moscow Greenhouse” variety lettuce. Plants in an experimental model of a closed ecosystem were grown using hydroponics on expanded clay. The technology and growing conditions are similar to those described earlier.  [22; 23]. The duration of cultivation from germination to technical maturity is 21 days. In the experimental version, the solution was prepared based on liquid mineralization products. Control options – standard Knop solution: control 1 – permanent solution with correction, control 2 – every 7 days the solution was changed to a freshly prepared one. During plant growth, correction of permanent irrigation solutions was carried out with initial solutions based on the content of available forms of nitrogen.

When creating an automated control system and software for a treatment plant, a uniform approach is desirable, thanks to which the same type of process parameters and reactor programming menus will be displayed in the same way, and the same type of automatic control algorithm for all reactors will be used. This is important, since the reactors are different, and it is more convenient for the operator to control and configure them with a uniform interface display. In addition, the automation system and software being developed should be easily adaptable to connecting possible new reactors to the structure of the treatment plant. Following this logic, the automation and software must be adaptable to connecting the “wet” combustion reactor and other reactors of the physicochemical waste mineralization subsystem [17]. This seems possible, since the program interaction scheme that meets the specified requirements for the automation and software of the treatment plant is the same for the “wet” combustion reactor (Fig. 1).

 

Рис. 1. Схема взаимодействия программ

Fig. 1. Scheme of program interaction

 

In order to ensure interaction with peripheral devices, including sensors, relays, servos and others, it was decided to use the Arduino platform due to its ease of programming, wide support for hardware modules and sensors. The Arduino IDE development environment is chosen for Arduino programming. For software development, with a focus on creating a convenient interface for the end user, an additional development environment was added – Visual Studio using a programming language C#.

Methods and approaches

A study of the influence of pollutants in a nutrient solution showed that the biomass of lettuce plants grown in non-replaceable solutions of the experimental and control variants did not differ significantly, just as there were no significant differences from the biomass of plants grown in control solutions that were regularly replaced (see table).

 

Dry weight (g) per plant of lettuce variety “Moscow Greenhouse”, grown on solutions prepared on the basis of liquid products mineralization of human exometabolites

Type of nutrient solution

Total biomass

Leaf biomass

Permanent solution of exometabolites

3.3±0.4

2.9±0.3

Non-replaceable Knop solution

(control 1)

2.8±0.5

2.4±0.5

Replaceable Knop solution

(control 2)

2.7±0.9

2.1±0.4

 

Thus, the fundamental possibility of long-term use of nutrient solutions prepared on the basis of liquid products of the mineralization of human exometabolites for growing plants of the phototrophic link of a closed ecosystem has been experimentally demonstrated.

Based on the analysis of the processes of the physico-chemical unit for processing human waste, the automatic reactor control algorithm was taken as the basis for logical control [18, Fig. 2, B)], the logic of which is to maintain the parameters of the technological process conditions in the specified ranges and stop the process when the target parameter reaches the specified value.  The work [18] does not disclose the operating principle of the unit for adjusting the conditions parameters, which is a problematic point when trying to create a unified structure of the automatic control algorithm for the treatment plant. This is due to the fact that the processes in the reactors of the installation are varied: they occur in the liquid and gaseous phase, have one or several stages, and may require partial operator intervention. Therefore, maintaining certain condition parameter values ultimately requires different hardware and logic solutions. As a result, despite the possibility of uniformly displaying the parameters of technological processes, the software settings for the operation of different reactors and control algorithms will differ from each other.

The need for an individual approach to settings for each reactor of a treatment plant indicates the possibility of using common software for all reactors of the physico-chemical mineralization subsystem of waste [17], including a “wet” combustion reactor, the operating algorithm of which differs from the operating algorithm of the treatment plant (Fig. 2)

 

Рис. 2. Алгоритмы работы реакторов: А – без контроля параметров условий процесса; Б – с контролем параметров условий процесса

Fig. 2. Reactor operation algorithms: A – without control of the parameters of the process conditions; Б – with control of the parameters of the process conditions

 

As a result, software was developed in which, for user convenience, the operator’s workspace is divided into tabs, where each tab has its own reactor (Fig. 3). Each tab has fields for displaying indicators in text format, buttons for reactor control, fields for plotting graphs based on measurement results, as well as operating time and current date.

By pressing the “Start” button, a signal is sent to the connection port, then the Arduino begins to transmit readings of the running process. The data is displayed in the appropriate fields, and based on this data, the construction of the graphs presented in Fig. begins. 3, where each tab corresponds to a reactor/process of physical and chemical processing of human waste products. Four-color tab marking is proposed to indicate the state of processes:

state 1 – the process is not running, not the current tab;

state 2 – process not running, current tab;

state 3 – the process is running, not the current tab;

state 4 – process running, current tab.

Reactor operation settings allow you to enter parameter values for each purification process to automatically maintain and adjust the conditions for its occurrence.

 

Рис. 3. Окно ПО во время работы: А – отображение параметров текущего процесса (выделение Na2CO3); Б – отображение настроек реактора выделения Na2CO3

Fig. 3. The software window during operation: A – displaying the parameters of the current process (Na2CO3 extraction); Б – displaying the settings of the Na2CO3 extraction reactor

 

When the process is started, in addition to outputting data in the current time, the data is written to a text document. All measurement results are saved in separate folders in the software directory. The file names contain the exact launch date. And the documents themselves describe the number of the launched reactor and the results of measurements over time.

Conclusion

Peripheral equipment for organizing an automatic control system was selected, problems were identified and approaches were developed to automate these processes and create software for human interaction with the proposed installation. Experiments on growing lettuce plants were carried out, confirming the effectiveness of the proposed purification processes for liquid products of the processing of human exometabolites. Thus, the created complex purification installation, equipped with the proposed software, can be used for scientific research in relation to CES topics, including space applications.

×

Sobre autores

Sergei Trifonov

Institute of Biophysics SB RAS; Reshetnev Siberian State University of Science and Technology

Autor responsável pela correspondência
Email: trifonov_sergei@inbox.ru

Ph. D., Head of Laboratory for Problems of Establishing Cycling Processes of Artificial Ecosystems, Institute of Biophysics Siberian Branch of Russian Academy of Sciences; Associate Professor, Department of Closed Ecosystems, Reshetnev Siberian State University of Science and Technology

Rússia, 50/50, Akademgorodok, Krasnoyarsk, 660036; 31, Krasnoyarskii rabochii prospekt, Krasnoyarsk, 660037

Alexander Tikhomirov

Institute of Biophysics SB RAS; Reshetnev Siberian State University of Science and Technology

Email: alex-tikhomirov@yandex.ru

Dr. Sc., Professor, Head of Laboratory of Phototrophic Biosynthesis Control, Institute of Biophysics Siberian Branch of Russian Academy of Sciences; Head of Chair of Closed EcoSystems, Reshetnev Siberian State University of Science and Technology

Rússia, 50/50, Akademgorodok, Krasnoyarsk, 660036; 31, Krasnoyarskii rabochii prospekt, Krasnoyarsk, 660037

Alexander Murygin

Reshetnev Siberian State University of Science and Technology

Email: avm514@mail.ru

Dr. Sc., Professor, Head of Chair of Information and Management Systems

Rússia, 31, Krasnoyarskii rabochii prospekt, Krasnoyarsk, 660037

Bibliografia

  1. Gitelson J. I., Lisovsky G. M., MacElroy R. D. Manmade Closed Ecological Systems. New York, Taylor and Francis, 2003, 402 p.
  2. Wheeler R. M. Agriculture for space: People and places paving the way. Open agriculture. 2017, Vol. 2 (1), P. 14–32.
  3. Tikhomirov A. A., Ushakova S. A., VelichkoV. V., Tikhomirova N. A., Kudenko Yu. A., Gribovskaya I. V., Gros J.-B., Lasseur Ch. Assessment of the possibility of establishing material cycling in an experimental model of the bio-technical life support system with plant and human wastes included in mass exchange. J. Acta Astronaut. 2011, Vol. 68, P. 1548–1554.
  4. Manukovsky N. S., Kovalev V. S., Rygalov V. Ye., Zolotukhin I. G. Waste bioregeneration in life support CES: development of soil organic substrate. Advances In Space Research. 1997, Vol. 10, P. 1827–1832.
  5. Wenting H., Yidong X., Hong L. A technique for preparing soil-like substrate for bioregenerative life support system. 17th IAA Humans in Space Symposium. Moscow, 2009, P. 53.
  6. Kudenko Yu. A., Pavlenko R. А. Sposob utilizatsii otkhodov zhiznedeyatel'nosti cheloveka i nesjedobnoy biomassy rasteniy, privodyashhiy k polucheniyu iz nih udobreniy [Way of utilization of human wastes and inedible plant biomass, gaining hydroponic fertilizer]. Patent RF, no. 2111939, 1998.
  7. Nelson M., Dempster W. F., Allen J. P. Integration of lessons from recent research for Earth to Mars life support systems. Advances in Space Research. 2008, Vol. 41, P. 675–683.
  8. Bamsey M., Graham T., Stasiak M. et al. Canadian advanced life support capacities and future directions. Advances in Space Research. 2009, Vol. 44, P. 151–161.
  9. Drysdale A. E., Ewert M. K., Hanford A. J. Life support approaches for Mars missions. Advances in Space Research. 2003, Vol. 31, P. 51–61.
  10. Farges B., Poughon L., Creuly C. et al. Dynamic Aspects and Controllability of the MELiSSA Project: A Bioregenerative System to Provide Life Support in Space. Applied Biochemistry and Biotechnology. 2008, Vol. 151, P. 686–699.
  11. Guo S. S., Mao R. X., Zhang L. L. et al. Progress and prospect of research on controlled ecological life support technique. Reach. 2017, Vol. 6, P. 1–10.
  12. Walker J., Granjou C. MELiSSA the minimal biosphere: Human life, waste and refuge in deep space. Futures. 2017, Vol. 92, P. 59–69.
  13. Escobar C., Nabity J. Past, present, and future of closed human life support ecosystems – a review. 47th International Conference on Environmental Systems. Charleston, 2017, P. 18.
  14. Putnam D. F. Composition and Concentrative Properties of Human Urine. NASA contract report. Washington, 1971, 107 p.
  15. Kudenko Yu. A., Gribovskaya I. A., Zolotukchin I. G. Physical-chemical treatment of wastes: A way to close turnover of elements in LSS. Acta Astronautica. 2000, Vol. 46, P. 585–589.
  16. Kudenko Yu. A., Gribovskaya I. A., Pavlenko R. A. Mineralization of wastes of human vital activity and plants to be used in a life support system. Acta Astronautica. 1997, Vol. 41, P. 193–196.
  17. Morozov Ye. A., Trifonov S. V., Saltykov M. Yu. et al. [Physico-chemical waste mineralization reactors subsystem for closed bio technical life support systems for space application]. Siberian Journal of Science and Technology. 2017, No. 3, P. 585–591 (In Russ.).
  18. Tikhomirov А. A., Trifonov S. V., Morozov Ye. A., Murygin A. V. [Development of control principles for the desalination unit for closed life support systems for space purposes]. Siberian Aerospace Journal. 2022, Vol. 23, No. 3, P. 551–560 (In Russ.).
  19. Ushakova S. A., Kovaleva N. P., Gribovskaya I. V. et al. Effect of NaCl concentration on productivity and mineral composition of Salicornia europaea as a potential crop for utilization NaCl in LSS. Adv. Space Res. 2005, Vol. 36 (7), P. 1349–1353.
  20. Ushakova S. A., Kovaleva N. P., Gribovskaya I. V., Dolgushev V. A., Tikhomirova N. A. Effect of NaCl concentration on productivity and mineral composition of Salicornia europaea as a potential crop for utilization NaCl in LSS. Advances in Space Research. 2005, Vol. 36, P. 1349–1353.
  21. Mobley H., Mendz G., Hazell S. Helicobacter pylori: Physiology and Genetics. ASM Press, 2001, 626 p.
  22. Ushakova S. A., Tikhomirov A. A., Tikhomirova N. A. et al. A biological method of including mineralized human liquid and solid wastes into the mass exchange of bio-technical life support systems Advances In Space Research. 2012, Vol. 50, No. 7, P. 932–940. doi: 10.1016/j.asr.2012.05.023.
  23. Morozov Ye. A., Trifonov S. V., Murygin A. V., Tikhomirov A. A. [Automatic Control System of O2 and H2 Concentrations in Technological Gas Circuits of BTLSS Space Application]. Siberian Journal of Science and Technology. 2018, Vol. 19, No. 4, P. 691–697 (In Russ.).

Arquivos suplementares

Arquivos suplementares
Ação
1. JATS XML
2. Fig. 3. The software window during operation: A – displaying the parameters of the current process (Na2CO3 extraction); Б – displaying the settings of the Na2CO3 extraction reactor

Baixar (776KB)
3. Fig. 1. Scheme of program interaction

Baixar (187KB)
4. Fig. 2. Reactor operation algorithms: A – without control of the parameters of the process conditions; Б – with control of the parameters of the process conditions

Baixar (513KB)

Declaração de direitos autorais © Tikhomirov A.A., Trifonov S.V., Murygin A.V., 2023

Creative Commons License
Este artigo é disponível sob a Licença Creative Commons Atribuição 4.0 Internacional.

Este site utiliza cookies

Ao continuar usando nosso site, você concorda com o procedimento de cookies que mantêm o site funcionando normalmente.

Informação sobre cookies