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Визначено технологiчнi ршення для зниження концентраци сполук нтрогену на 75 % в процеы очищення стiчноi води з метантен^в тсля зброджування послиду птахiв. Показано вплив структури косуб-страту на змту вм^ту сполук ттрогену у стiчнiй водi в процеЫ отримання бюгазу з послиду. Визначено технологiчнi параметри (час гiдравлiчного утримання, спiввiдно-шення пототв) анаеробно-аеробного про-цесу очищення сто^в
Ключовi слова: зброджування послиду, косубстрат, стiчна вода, ттрифжащя-
деттрифкащя, анаеробно-аеробний процес
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Определены технологические решения для снижения концентрации соединений азота на 75 % в процессе очистки сточной воды из метантенков после сбраживания помета птиц. Показано влияние структуры косубстрата на изменение содержания соединений азота в сточной воде в процессе получения биогаза из помета. Определены технологические параметры (время пребывания воды в системе, соотношения потоков) анаэробно-аэробного процесса очистки стоков
Ключевые слова: сбраживание помета, косубстрат, сточная вода, нитри-фикация-денитрификация, анаэробно-
аэробный процес -□ □-
UDC 620.92
[doi: 10.15587/1729-4061.2016J2336|
TECHNOLOGY OF ANAEROBIC-AEROBIC PURIFICATION OF WASTEWATER FROM NITROGEN COMPOUNDS AFTER OBTAINING BIOGAS
N. Golub
Doctor of Technical Sciences, Professor* E-mail: [email protected] O. Kozlovets
Engineer LLC Envitec
Chervonozoryany ave., 6А, Kyiv, Ukraine, 03037 Е-mail: [email protected] D. Voyevoda Postgraduate Student* E-mail: [email protected] *Department of environmental biotechnology and bioenergetics National Technical University of Ukraine "Kyiv Polytechnic Institute" Peremogy ave., 37, Kyiv, Ukraine, 03056
1. Introduction
In the anaerobic utilization of the waste of livestock breeding, especially of poultry breeding, there is a problem of wastewater utilizing after the separation of the solid phase in the separator at the outlet of a methane tank [1]. In the course of processing the waste of the biogas production, while loading the methane tank with 5 % of the dry substance at the volume of a methane tank of 3000 m3 and with keeping raw materials there for 24 days, 90 m3/day of wastewater are produced [2]. Wastewaters are highly concentrated and have a high content of nitrogen and ammonium nitrogen (up to 180 mg/dm3), which complicates the technology of their purification and makes their dumping into natural bodies of water impossible. Therefore, the development of the technological solutions of the purification of the wastewater with the high concentration of ammonium ions is an urgent problem.
2. Analysis of scientific literature and the problem statement
To reduce the content of the ammonium compounds in the fermenter and in wastewater, the co-fermentation is used with adding to the remainder the crop wastes [3] (corn,
cane, beet pulp [4], sparging and paper waste) or the food production wastes [5] in various ratios depending on the raw materials that are used as co-substrate. In this case, the remainder concentration makes about 30 % [6].
According to this approach, while increasing the population of birds, it is necessary to increase the amount of the agricultural wastes, the delivery of which increases the cost of biogas. Therefore, determining a co-substrate composition, the use of which reduces the content of nitrogen ions in the environment and increases the content of the remainder, is an important problem [7].
The technologies that are used for the utilization of ammonium ions in wastewater, various modifications of the biological methods are used [8]: sequential anaerobic-aerobic, or with the return of the wastewater into the anaerobic reactor, unoxidic processes and their combinations [9]. The methods are hardly effective, because reducing the concentrations of the nitrogen compounds mainly occurs at the expense of increasing the biomass of the microorganisms, but not due to the formation of the molecular N2 [10], which is released into the atmosphere. Moreover, high concentration of ammonium ions can cause the death of the microorganisms or inhibiting their life processes.
One of the new methods is the use of anammox-bacteria [11]. Such technology with using special carriers for the immobilization of the microorganisms allows purifying the
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wastewater with ammonium nitrogen with the efficiency of 97 % [11] while using the ammonium nitrogen concentration of 150 mg/dm3 [12]. Using sequentially a series of reactors with anaerobic, aerobic and unoxide conditions of the flow of biological processes, the authors of the work [13] managed to reach indicators of 2 mg/dm3 at the outlet of wastewater constructions while purifying the wastewaters with ammonium nitrogen concentration of 20-50 mg/dm3 at the inlet. It should be noted that in the offered decisions of purifying the wastewater from nitrogen compounds, the ammonium ion concentration up to 70 mg/dm3 is used, which is much lower than in the wastewater after the fermentation of the remainder [14].
That is why this work is dedicated to the solution of the problem of the utilization of the nitrogen compounds in wastewater from the methane tank after the fermentation of the remainder with the view to its reusing.
3. The purpose and objectives of the study
The aim of the work is to develop a technological solution of reducing the concentration of nitrogen compounds in the wastewater from methane tanks.
To achieve this aim, the following tasks were solved:
- researching the influence of co-substrate structure regarding the content of ammonium ions in the wastewater from the methane tank;
- determining the time of hydraulic retention of waste-water in an aerobic reactor, depending on the concentration of ammonium ions and COD;
- establishing the ratio between the aerated and anaer-ated streams of wastewater for the implementation of the anammox-process.
4. Materials and methods of studying the way of purifying wastewater from the methane tank from the nitrogen compounds
4. 1. The studied materials and the equipment for determining the influence of co-substrate on the contents of ammonium ions in wastewater from a methane tank
The main substrate was the remainder of chickens with the humidity of 32 %. Paper (cellulose - 98 %, lignin - 2 %) [15], reed (cellulose - 43.5 %, lignin - 37 %) [16], hemp (cellulose - 34-48 %, hemicellulose - 21-37 %, lignin - 16-28 % depending on the grade) [17] were used as the co-substrate.
The choice of the co-substrates was based on:
- global increase in the use of paper as packing material;
- increase in the agricultural areas under hemp, the sorts of which do not contain any narcotic substances and are used for the production of paper and other substances, the wastes of which need recycling;
- reed overgrowth on the river banks of Ukraine and cheap methods of its collection and delivery;
- the largest output of biogas in the process of fermentation.
The fermentation of the remainder was carried out in the reactors, the volume of which is 1.8 dm3, at the temperature of 36±2 °C for 21 days.
For the measurement of the ion concentration NH4+, NO3-,NO2-, the PH-meter I-160MI was used. The analysis is carried out by standard methods [18].
4. 2. Materials and equipment for studying the method of purifying waste water from nitrogen compounds
The installation with the volume 1,8 dm3 where the process of the denitrification took place, has a mechanic stirrer in its set-up for the intensification of the mass exchange processes, and synthetic carriers for the immobilization of microorganisms association enriched with anammox-bacte-ria. The concentration of the biomass in an anaerobic reactor reaches 9-10 g/dm3. The speed of stirring was 50-60 r/m.
The composition of the biogas that was obtained in the process of denitrification was determined with the help of the gas chromatographer LCM-8-MD (1987) by a standard method [19]. The chromatograph contains two columns, one for determining H2, 02, CH4, N2, the other - for determining C02. The column temperature is 50 °C, the temperature of the evaporator is 50 °C, the temperature of the detector is 50 °C, the detector current is 50 mA. The gas - carrier is argon, the gas flow speed is 30 cm3/min. The volume of the gas sample on the first column is 2.5 cm3, on the second one it is 1 cm3.
The percentage content of gases - H2, C02, N2, CH4 i 02 in the gas mixture
C=KSM, (1)
where C is the percentage content of a certain gas component in a mixture; K is the coefficient of the gas component (according to Table 1); S is the area of the triangle on the chromatogram.
Table 1
The coefficients of gas components after the denitrification
Gas component Coefficient, K
N2 0,0069
O2 0,0052
H2 0,0016
CO2 0,0217
CH4 0,0024
Aeration was carried out in rectangular tanks, at the bottom of which there were two aerators with the size of pores of 0.4 mm. The air consumption accounted for 3.5 dm3/min. The concentration of the biomass in the aerobic reactor reaches 6-7 g/dm3.
Chemical oxygen comsumption was determined by a standard method [20].
4. Results of studying the method of purifying wastewater from the methane tank after fermentation of the remainder
To determine the influence of the structure of cellulose-containing raw materials on the process of utilization of the ammonium ions in methane fermentation and the reduction of its concentration in wastewater, three types of co-substrate were used: paper, reed, hemp, which gave the highest yield of biogas with the ratio of the components remainder/co-substrate 1:1. The content of nitrogen compounds and COD in wastewater after the fermentation (21 days) is listed in Table 2. Nitrates were not formed in the process of methanogenesis. It should be noted that the biogas contained up to 9 % of nitrogen with
the use of hemp, and 7 % with the use of other co-substrates.
As it can be seen from the data of Table 2, with the use of paper and cane waste (example 1, 2) as co-substrate, the content of COD at the outlet from the methane tank by 1.5 times lower than with the use of hemp. At the same time, the concentration of ammonium ions with the use of hemp and paper waste (sample 1, 3) is 2 times lower than with the use of reed as a co-substrate in fermentation of the remainder. The composition of the co-substrate does not influence the concentration of nitrite ions. It should be noted that the nitrate ions during the fermentation of the remainder with any co-substrate are not formed.
For purifying wastewater from nitrogen, it is supposed to divide the decant into two streams. In one stream, the purification of the wastewa-ter occurs in aerobic conditions, in the second one - in anaerobic. Fig. 1 shows the dynamics of the changes in the concentration of ammonium ions in wastewater depending on the period of water retention in the aerobic reactor.
and for 2 hours for chart c. The change in the concentration of ammonium ions in the reactor after bringing the aerobic stream was not taken into consideration.
Fig. 1. Change of the concentration of ammonium nitrogen C (NH4+) depending on the time of hydraulic water retention (t) for various co-substrates: 1 — paper waste, 2 — reed, 3 — hemp (systems are listed in accordance with Table 2)
Table 2
Contents of nitrogen and COD in the wastewater from methane tank
Indicator 1. Remainder -paper wastes (1:1) 2. Remainder -reed (1:1) 3. Remainder -hemp (1:1)
COD, mg 02/dm3 1200±50 1040±50 1800±100
NO2-, mg/dm3 2,0±0,04 1,4±0,03 1,6±0,03
NH4+mg/dm3 74±3,5 138±7 69±3,5
As it can be seen from Fig. 1, the oxidation of ammonium ions occurs in a different time interval depending on the composition of wastewater. So, in the systems with fewer organic compounds (1 and 2), the ammonium utilization starts earlier: in 45 minutes for system 1, and in 1 hour for system 2. With the concentration of COD 1800 mg 02/dm3 (system 3), the oxidation of ammonium ions begins in 2 hours and lasts for a longer period of time. From Fig. 1, it can be seen that the lower the concentration of COD, the faster the process of oxidation of ammonium nitrogen is (2).
To determine the maximum reduction of the concentration of the ammonium ions and the formation of nitrogen (N2) in the anaerobic reactor, the ratio of the volumes of aerobic and anaerobic streams was investigated. The wastewater after the aeration process was settled and directed to the anaerobic reactor-denitrificator, in which there was the anaerobic purification of the other part of the wastewater after the separation. The microbial destruction of an organic substance and the reduction of the COD value took place in the reactor before the aerated water arrival. The time of retaining water in aerobic and anaerobic reactors is the same. The reactor contains fibrous carrier, on which the hydrobionts, enriched with anammox-bacteria, are immobilized.
Fig. 2 shows the change in the concentration of ammonium ions depending on the ratio of the streams that are directed to the aerobic reactor with a period of wastewater retaining for 1 hour for chart a; for 1.5 hours for chart b;
C (NH,+),
mg/dm3
160
140
120
100
SO
60
40
20
0
I After purification
2 3
Ratio
O Before purification
Fig. 2. Change of the concentration of ammonium ions (C (NH4+) at the outlet depending on the ratio of aerobic and anaerobic streams: a — 1:1, b — 2:1; c — 3:1, respectively
a
b
c
As it can be seen from Fig. 2, the largest reduction of the initial concentration of ammonium ions occurs while using the ratio of aerobic and anaerobic flows 2:1. According to the chromatographic analysis, the nitrogen content in biogas reaches 30 % while using the ratio of the streams from the aerobic and the anaerobic reactors for all systems 2:1. When one changes the ratio of the flows, the nitrogen content in biogas is reduced to 25 %±3 % with the use of the ratio of 1:1, and to 22 %±2 % with the use of the ratio of 3:1.
The degree of the purification of wastewater by the suggested method is listed in Fig. 3.
COD, mg02/dm3
2500 i-
C (NH4), mg/dm3
2000 1500 -1000 500 0
±
a
m
tation of the remainder it is necessary to use cellulose-containing raw materials which are low in lignin.
Based on the data in Fig. 2, the ratio of flows during decant splitting after the separation depends on the concentration of the ammonium ions and COD. With the increase in COD and in ammonium ions, the part of the water that is directed to the aerobic reactor, is larger than the other part which is directed to the anaerobic reactor. In the aerobic reactor, the utilization of organic substances is the first to occur, followed by the oxidation of nitrogen to NO2- [15]:
NH4+ ^NH2OH^(NOH)^NO2.
(2)
180 160 140 120 100 80 60 40 20 0
1. Remainder - 2. Remainder - reed 3. Remainder -paper waste (50:50) (50:50) hemp (50:50)
□ COD, before purification
□ COD, after purification
□ Ammonium nitrogen, before purification
Fig. 3. Indicators of wastewater COD and C(NH4+) before and after the purification by the aerobic-anaerobic method with dividing the flows by the ratio of 2:1 with different hydraulic retention of the wastewater depending on the COD and the ammonium ion concentrations. The time of the retention: system 1 — 1 h; system 2 — 1,5 h; system 3 — 2 hrs
The set parameters of the process, which are listed in Fig. 3, allow significantly reducing the ammonium ions content in wastewater, which makes it possible to reuse it in the technological process of obtaining biogas from the poultry remainder.
5. Discussion of the results of reducing the concentration of nitrogen compounds in the wastewater from a methane tank
Based on the data of Table 2, we can state that the use of cellulose-containing raw materials with the low content of lignin (samples 1 and 3) reduces the content of the ammonium ions in wastewater by means of the primary destruction of hydrocarbon compounds, but not proteins, contained in the remainder, because the formation of ammonium ions (sample 2) occurs as a result of their destruction. The increase in lignin in the co-substrate to 37 % (sample 2) slows down the speed of the destruction of reeds, which leads to a decrease in the COD content in wastewater in relation to raw materials, containing less lignin (hemp 16-28 %).
The increased content of lignin also influences the development of the microorganisms contained in biocenose of a fermenter, because it makes the access to the biomass difficult and reduces the speed of the increase in the biomass. This leads to the increased content of the ammonium ions, which are formed through the decomposition of urea.
Thus, to reduce the content of the ammonium ions in wastewater from methane tanks in the process of the fermen-
Under these conditions, the formation of NO3- takes place in the process of nitrification.
According to the received data (Fig. 2), the ratio 2:1 of the aerobic and anaerobic flows is appropriate.
The time of the hydraulic retention of wastewater in the aero tank depends primarily on the concentration of COD. As it can be seen from Fig. 1, the rational time of the water retention in the aero tank is, h: in the first one - 1-2 hours; in the second one - 1.5-2.5 hours; in the third one - 2-4 hours. The reduction of the COD content in the anaerobic process is slower than in the aerobic one, because the metabolism speed of aerobes is 3-6 times as high. So, the time of the hydraulic retention of water will be determined by the decrease in the value of COD in the anaerobic reactor.
When mixing the streams by using anammox-bacteria, formation of molecular nitrogen occurs according to the scheme:
NH4+ +NO2- ^ N2+2H2O.
(3)
Molecular nitrogen also forms during the life of the other kinds of microorganisms with the consumption of the ions of ammonium and nitrate. In addition to molecular nitrogen in anaerobic reactor (denitrificator), the products of the methane fermentation (CH4, H2, CO2) are also formed. However, unlike the biogas that is produced in a methane tank, the biogas from the denitrificator is low in calories due to the high content (30 %) of the molecular nitrogen (not flammable component) and C02 and can be used to remove oxygen from the water before stilling it after the aerobic reactor.
6. Technological process of purification of the wastewater from methane tank from the ammonium ions for its reusing
On the basis on the obtained data, the technological solutions of the anaerobic-aerobic purification of waste-water with the high content of ammonium nitrogen after the fermentation process of obtaining methane from the remainder were developed. The principle of technology lies in dividing the flow after the separation into two. The first is directed to the aerobic additional purification, where the process of nitrification simultaneously takes place. The second is directed to denitrificator, which contains the association of microorganisms enriched with anammox-bac-teria. During the streams joining, the process of forming molecular nitrogen from ammonium and nitrite takes place in the denitrificator by equation (3). The scheme of the purification of wastewater from the organic compounds and the nitrogen compounds after the formation of biogas in the process of the fermentation of the remainder process is shown in Fig. 4.
Fig. 4. Scheme of purification of the wastewater after methanogenesis: 1 — methane tank; 2 — filter for biogas purification; 3 — gas holder for accumulating purified biogas; 4 — compressor of the biogas supply for cogeneration; 5 — cogeneration plant; 6 — separator; 7 — aero tank; 8 — pump for wastewater pumping from the methane tank to denitrificator; 9 — pump of wastewater supply from the aero tank to denitrificator via the ejection system; 10 — pump for the supply of the gas formed in a methane tank for bubbling; 11 — denitrificator; 12 — pump for the purified water supply for reusing
Wastewater after separator 6, where the solid fraction is removed, is divided into two streams in the ratio of the aerobic: anaerobic purification (1.5-2): 1 and is supplied to aerobic 7 and anaerobic 11 reactors. A greater part of the wastewater arrives in aero tank 7, where its purification from organic compounds takes place and there is the process of nitrification with the formation of NO3- and NO2-. Another part, which is enriched with ammonium nitrogen NH4+, arrives in the anaerobic reactor 11, where it is purified from organic compounds and biogas is formed. Biogas with the help of the pump 10 is pumped for bubbling in the main methane tank 1.
After the process of aeration, the wastewater is pumped 9 to ejection, where the air is removed and its stilling takes place. The wastewater from the aero tank arrives in the anaerobic reactor 11, to which the water from the methane tank was directed 1. In anaerobic reactor 11, the process of de-nitrification takes place with the course of reactions (4) and:
NO3-+organic substances=N2+C02+H20. (4)
Reactor 11 is equipped with inert carriers to increase the number of microorganisms and hydrobionts, as well as to intensify the process of purifying wastewater. The anaerobic reactor 11 is also equipped with the special loading stirrer to intensify the process of the formation of molecular nitrogen.
After being purified from organic substances and the nitrogen compounds, the wastewater returns to the methane tank 1, where once again takes part in methane fermentation. The suggested technological solution allows using wastewater of methane tanks after purifying as circulating, which reduces the biogas costs and reduces the anthropo-
genic load on the environment. In addition to the positive environmental effect, the use of such technologies allows additional receiving biological fertilizers which contain all of the necessary components for the development of plants.
8. Conclusions
1. The concentration of ammonium ions and COD in the wastewater after the process of methanogenesis from the remainder is influenced by the component composition of the used co-substrate. Co-substrate, which has higher lignin content, contributes to increasing ammonium ions content twice in relation to the substrates, the lignin content of which does not exceed 25 %; besides, it does not increase the content of organic compounds in wastewater. Lower lignin content leads to increasing the content of organic substances in wastewater by 70 %.
2. With dividing the flow, the time of the hydraulic retention of wastewater in the aerobic reactor depends on the concentration of organic substances and ammonium ions. With the concentration of COD up to 1200 mg 02/dm3 and the concentration of ammonium ions up to 70 mg/dm3, 1-2 hours is the rational time of the hydraulic retention of the wastewater in the aero tank, with increasing the concentration of ammonium ions up to 130 mg/dm3 the rational time is 1.5-2.5 hours, with increasing the COD up to 1800 mg/dm3 the rational time is 2-4 hours.
3. The suggested technology allows reducing the concentration of ammonium ions by 75 % by dividing the wastewater to conduct processes of nitrification and de-nitrification (1,5-2):1.
References
1. Geletukha, G. Sovremennoe sostoyanie i perspektivy bioenergetiki v Ukraine [Text] / G. Geletukha, T. Zheleznaya, P. Kucheruk, E. Oleinik // Analiticheskaya zapyska BAU. - 2013. - Vol. 9. - P. 25.
2. Li, X. Development of Bioelectrochemical Systems to Promote Sustainable Agriculture [Text] / X. Li, I. Abu-Reesh, Z. He // Agriculture. - 2015. - Vol. 5, Issue 3. - P. 367-388. doi: 10.3390/agriculture5030367
3. Kozlovets, O. Technology of anaerobic-aerobic treatment wastewaters from nitrogen compounds after biogas production [Text] / O. Kozlovets, D. Voyevoda, N. Golub // Agroinkom. - 2015. - Vol. 6, Issue 4. - P. 43-46.
4. Eusebi, A. L. Nitrogen removal from temperate anaerobic-aerobic two-stage biological systems: impact of reactor type and wastewater strength [Text] / A. L. Eusebi, N. Martin-Garcia, E. J. McAdam, B. Jefferson, J. N. Lester, E. Cartmell // Journal of Chemical Technology and Biotechnology. - 2013. - Vol. 88, Issue 11. - P. 2107-2114. doi: 10.1002/jctb.4102
5. Sgroi, F. Economic evaluation of biogas plant size utilizing giantreed [Text] / F. Sgroi, M. Fodera, A. M. Di Trapani, S. Tudisca, R. Testa // Renewable and Sustainable Energy Reviews. - 2015. - Vol. 49. - P. 403-409. doi: 10.1016/j.rser.2015.04.142
6. Igwe J. Production of Biogas from Paper Waste Blended With Cow Dung [Text] / J. Igwe // IOSR Journal of Environmental Science, Toxicology and Food Technology. - 2014. - Vol. 8. - P. 58-68. doi: 10.9790/2402-081025868
7. Shved, O. M. Current technologies of ammonium withdrawal from wastewater [Text] / O. M. Shved // Biotechnologia acta. -2014. - Vol. 7, Issue 5. - P. 108-113. doi: 10.15407/biotech7.05.108
8. Zhu, G. Anammox bacterial abundance, biodiversity and activity in a constructed wetland [Text] / G. Zhu, S. Wang, X. Feng // Environmental science & technology. - 2011. - Vol. 45, Issue 23. - P. 9951-9958. doi: 10.1021/es202183w
9. Strous, M. The sequencing batch reactor as a powerful tool for the study of slowly growing anaerobic ammonium-oxidizing microorganisms [Text] / M. Strous, J. J. Heijnen, J. G. Kuenen, M. S. M. Jetten // Applied Microbiology and Biotechnology. -1998. - Vol. 50, Issue 5. - P. 589-596. doi: 10.1007/s002530051340
10. Shved, O. Anammox enrichment and constructed wetland inoculation for improvement of wastewater treatment performance [Text] / O. Shved, S. Dehestaniathar, V. Novikov // J Adv Environ Health Res. - 2014. - Vol. 2, Issue 3. - P. 189-195.
11. Graaf, A. A. Van de Autotrophic growth of anaerobic ammonium-oxidizing microorganisms in a fluidized bed reactor [Text] / A. A. Van de Graaf, P. De Bruijn, L. A. Robertson et al. // Microbiology. - 1996. - Vol. 142. - P. 2187-2196.
12. Luesken, F. A. Simultaneous nitrite-dependent anaerobic methane and ammonium oxidation processes [Text] / F. A. Luesken, J. Sanchez, T. A. van Alen, J. Sanabria, H. J. M. Op den Camp, M. S. M. Jetten, B. Kartal // Applied and Environmental Microbiology. - 2011. - Vol. 77, Issue 19. - P. 6802-6807. doi: 10.1128/aem.05539-11
13. Sabliy, L. A. Vpliv anaerobnih umov of biologichne ochishtennya gospodarsyko-pobutovih stichnih vod [Text] / L. A. Sabliy // Visnik NUVGP. - 2012. - Vol. 2, Issue 57. - P. 24-29.
14. Mendes, C Modeling simultaneous carbon and nitrogen removal (SCNR) in anaerobic/anoxic reactor treating domestic wastewater [Text] / C. Mendes, K. Esquerre, L. M. Queiroz // Journal of Environmental Management. - 2016. - Vol. 177. - P. 119-128. doi: 10.1016/j.jenvman.2016.04.016
15. Amon, Th. Biogas production from maize and dairy cattle manure-Influence of biomass composition on the methane yield [Text] / Th. Amona, B. Amona, V. Kryvoruchkoa, W. Zollitschb, K. Mayerc, L. Gruberd // Agriculture, Ecosystems & Environment. -2007. - Vol. 118, Issue 1-4. - P. 173-182. doi: 10.1016/j.agee.2006.05.007
16. Corno, L. New energy crop giant cane (Arundo donax L.) can substitute traditional energy crops increasing biogas yield and reducing costs [Text] / L. Cornoa, R. Pilub, F.Tambonea, B. Scagliaa, F. Adania // Bioresource Technology. - 2015. - Vol. 191. -P. 197-204. doi: 10.1016/j.biortech.2015.05.015
17. Kreuger, E. Biogas production from hemp - evaluation of the effect of harvest time on methane yield [Text] / E. Kreuger, F. Escobar, S.-E. Svensson, L. Bjornsson // Biomass and bioenergy. - 2011. - Vol. 35. - P. 893-900.
18. Ionomer laboratornyy i-160mi [Text]. - Obschtstvo s ogranichennoy otvetstvennostyyu «Izmeritelynaya tehnika», 2007. - 69 p.
19. Leybnits, E. Rukovodstvo po gazovoy chromatographii. Part 1 [Text] / E. Leybnits, H. G. Shtruppe. - Moscow: Myr, 1988. - 480 p.
20. KND 211.1.4.021-95 [Text]. - Metodika viznachennya himichnogo spozhivannya (HSC) in poverhnevih i stichnih vodah, 1995.
