Literature DB >> 31061859

A comprehensive dataset on anaerobic digestion of cattle manure, source separated organics, and municipal sludge using different inoculum sources.

E Hosseini Koupaie1, A Azizi1, A A Bazyar Lakeh1, H Hafez1,2, E Elbeshbishy1.   

Abstract

The dataset reported in this article provides quantitative data on anaerobic digestion of cattle manure, source separated organics (SSO), primary sludge (PS), and thickened waste activated sludge (TWAS) using different inoculum sources. The discussion and interpretation of the data are provided in another publication entitled "Comparison of liquid and dewatered digestate as inoculum for anaerobic digestion of organic solid wastes" [1]. The data presented in this article include 1) the gas chromatography (GC) procedure of determining the biogas composition, 2) the procedure of converting the daily biogas/methane production data from the experimental condition (mesophilic temperature of 38 °C and room pressure) to the standard temperature (0 °C) and pressure (1 atm) condition, 3) the specific methanogenic activity data, and 4) the methane daily production rate data, and 5) the organics biodegradation kinetic rates.

Entities:  

Year:  2019        PMID: 31061859      PMCID: PMC6488733          DOI: 10.1016/j.dib.2019.103913

Source DB:  PubMed          Journal:  Data Brief        ISSN: 2352-3409


Specifications table To understand the details on translating the parameters measured under specific laboratory conditions (temperature and pressure) into the standard condition which makes the data easily comparable with other researchers' findings. The kinetic data would be useful to compare the digestion rate of various organic waste with respect to the type of inoculum used. The data provides comprehensive information on the application of two different inoculum sources on anaerobic digestion of synthetic (acetic acid and glucose) and real organic waste The dataset presents the procedure of the analytical method with GC to analyze the biogas composition as well as the detailed information on several measured AD parameters. The dataset provided in this article suggests that the startup (seeding) of industrial-scale anaerobic digestion plants can be done using dewatered digestate cake, reducing the transportation volume up to 90% compared to the application of liquid digestate.

Data

The measured biogas production data during the SMA, BHP, and BHP experiments are presented in Table 1, Table 2, and Table 3, respectively. The converted values to the standard temperature (°C) and pressure (1 atm) condition are shown in Table 4, Table 5, Table 6, respectively. Table 7 presents the daily methane production rate of the SMA digesters at the standard temperature and pressure condition. Fig. 1 illustrates the cumulative methane production of the SMA digesters during the initial operation period along with the linear regression equation of the best-fitted line to each graph. The slope of the linear regression was used to determine the specific methanogenic activity illustrated in Fig. 2. Fig. 3 shows the first-order specific TCOD removal rate constant of the BMP digesters.
Table 1

Daily biogas production data from the SMA reactors at a temperature of 38 °C (mL).

DayF/M = 0.25
F/M = 0.5
AD digestateSTDEVAD cakeSTDEVAD digestateSTDEVAD cakeSTDEV
000000000
1162193205242
22523293143412
336450641115917
4501257449108615
55765911561410414
88311948791216420
9961311618931218513
1110811144111111622717
121241416371381526710
151549208181912136512
1615919220202191840616
1818819253192602448014
192052127092911451628
2022117284173181154425
2124018293173451757027
2226313306213931458819
2327916309194362159922
2429411314144852761024
2530416316145262162217
2631718318205553462719
2732331321175813163316
2832919323245931663615
2933423325246082264123
3034023328186182764319
3134220332236262164423
3234210332256271864618
3334317333236281464717
3434322334136292264720
3534420335236302064720
Table 2

Daily biohydrogen production data from the BHP reactors at a temperature of 38 °C (mL).

Time (h)DigestateSTDEVDigestate cakeSTDEV
00000
11021
21121
31121
41131
51141
62162
73062
84184
963105
1099104
111311112
121810143
13268192
143620272
155028375
167027504
16.58124568
179321624
17.5104296911
1811825787
18.5132239616
191482212220
19.51632314923
201791717914
20.51972120919
212162323522
21.52362725416
222582327132
22.52832928825
233062130522
23.53162331937
243322933133
24.53462733843
253541934553
25.53622535024
263672735441
26.53702335750
273722535934
27.53752736034
283782536243
28.53803136338
293812936434
303822536643
313823136743
323822736834
333823136834
343822936826
353822536834
363822536826
Table 3

Daily biogas production data from the BMP reactors at a temperature of 38 °C (mL).

Time (d)
024578101113141719222528313542
TWASDigestateAverage0417595115127146170196233406547762856885896897898
STDEV061591610142317223845393434384042
Digestate cakeAverage087126149178201235274314370580707853884922945945950
STDEV0469517141824354839265860717173
PSDigestateAverage02439103151179203210235249308344425595869101510281046
STDEV21317483124202327314038193748202530
Digestate cakeAverage051751232012322643083353745576818589801055108410841084
STDEV212132067181316223747525561676767
SSODigestateAverage0769135183204222241271334657807102011461234128013001300
STDEV60815181921161116175166496252575454
Digestate cakeAverage4184144206239259307394503606872986112812151265126512651265
STDEV171520212433455256797896111109109109109
ManureDigestateAverage0124077137182243307370434589640720785833854856863
STDEV2617253246514366647445845636405950
Digestate cakeAverage03287166288382488551605643722750786804815827831835
STDEV248121826354453597074778183888888
Table 4

Converted daily biogas production data from the SMA reactors to the standard temperature and pressure condition (mL).

DayF/M = 0.25
F/M = 0.5
AD digestateSTDEVAD cakeSTDEVAD digestateSTDEVAD cakeSTDEV
000000000
1142173185212
22322882833010
332344536105215
444105034397614
5515531050139213
87410837701114518
9851110316821116411
1196101289981420115
12110131446123132369
151368184161701932410
1614117195181941636014
1816717224172312142612
191821823982581245725
2019615252152821048222
2121216260153061550624
2223312271193481252117
2324714274163861953119
2426010278134302454121
2526914280124661955115
2628116282184923055517
2728628285155152856114
2829217286215261556413
2929621288225392056820
3030120291165472457017
3130317294205551857120
323049295225561657216
3330415295205571257315
3430420296115582057418
3530417297205581857418
Table 5

Converted daily biohydrogen production data from the BHP reactors to the standard temperature and pressure condition (mL).

Time (h)DigestateSTDEVDigestate cakeSTDEV
00000
10011
21121
31121
41131
51131
62152
72062
83174
95385
108894
111210102
12169122
13237172
143218242
154425334
166224444
16.57121507
178219554
17.592256110
1810423696
18.5117208514
191312010817
19.51452013220
201591515913
20.51751918517
211912020819
21.52092422514
222282024028
22.52512525523
232711927020
23.52802028333
242952529329
24.53072430038
253141730647
25.53212231021
263252431436
26.53282031645
273302231830
27.53332432030
283352232138
28.53372732234
293372532331
303382232438
313382732538
323382432631
333382732631
343382532623
353382232631
363382232623
Table 6

Converted daily biogas production data from the BMP reactors to the standard temperature and pressure condition (mL).

Time (d)
024578101113141719222528313542
TWASDigestateAverage0366684102112129151174207360485675759785794795796
STDEV05138149122015193340353030343538
Digestate cakeAverage077112132158178208243278328514626756783817838838842
STDEV0458415121621314235235153636364
PSDigestateAverage0213491134158180186208221273304376528770899911927
STDEV11215432821182124283633173343182227
Digestate cakeAverage04566109178205234273297332494603760869935960960960
STDEV111121856161215193342464854595959
SSODigestateAverage066112016218019621424029658271590410161094113511521152
STDEV53713161719141014154558435547514747
Digestate cakeAverage3774127182212230272349445537773874100010771121112111211121
STDEV1613181921304046507069859996969696
ManureDigestateAverage0103669121161216272328385522567638696739757759765
STDEV1515222940453858576640754932355344
Digestate cakeAverage02977147255338433488536570640665697712723733736740
STDEV147111623313947536266697274787878
Table 7

Daily methane production rate of the SMA digesters at the standard temperature and pressure condition (mL/g TCODadded.d).

DayF/M = 0.25
F/M = 0.5
AD digestateSTDEVAD cakeSTDEVAD digestateSTDEVAD cakeSTDEV
00.00.00.00.00.00.00.00.0
114.03.817.05.49.14.610.72.2
29.01.611.97.04.91.24.53.1
310.32.217.34.04.92.712.17.0
410.85.15.60.73.21.410.83.9
58.21.62.71.03.81.99.42.6
87.72.010.11.63.41.08.92.2
912.93.423.7a7.27.41.911.21.6
115.61.212.91.94.01.29.61.4
1211.02.512.91.19.82.114.01.0
159.21.113.72.38.11.815.11.0
165.61.312.72.314.02.320.4a1.6
1812.72.514.32.19.01.616.30.9
1915.63.115.61.013.71.316.01.8
2014.02.112.41.512.10.912.71.2
2116.82.58.10.912.51.211.91.1
2221.1a2.111.81.621.31.57.80.5
2314.11.63.10.419.51.95.10.4
2413.81.03.90.422.4a2.55.10.4
258.90.92.00.218.31.55.20.3
2611.71.31.80.213.11.62.20.1
275.81.12.90.311.81.32.70.1
285.60.71.30.25.50.31.70.1
294.40.62.40.46.70.52.20.2
305.00.72.90.34.40.40.70.0
312.10.23.00.43.80.30.60.0
320.40.00.60.10.40.00.60.0
330.40.00.70.10.50.00.60.0
340.40.00.70.10.50.00.10.0
350.30.00.70.10.30.00.10.0

The maximum daily methane production rate values are highlighted in blue.

Fig. 1

Cumulative methane production of the SMA digesters during the initial operation period.

Fig. 2

The specific methanogenic activity of the SMA digesters (determined via the slope of the best-fitted line to the Fig. 1 graphs).

Fig. 3

First-order specific TCOD removal rate constant of the BMP digesters.

Daily biogas production data from the SMA reactors at a temperature of 38 °C (mL). Daily biohydrogen production data from the BHP reactors at a temperature of 38 °C (mL). Daily biogas production data from the BMP reactors at a temperature of 38 °C (mL). Converted daily biogas production data from the SMA reactors to the standard temperature and pressure condition (mL). Converted daily biohydrogen production data from the BHP reactors to the standard temperature and pressure condition (mL). Converted daily biogas production data from the BMP reactors to the standard temperature and pressure condition (mL). Daily methane production rate of the SMA digesters at the standard temperature and pressure condition (mL/g TCODadded.d). The maximum daily methane production rate values are highlighted in blue. Cumulative methane production of the SMA digesters during the initial operation period. The specific methanogenic activity of the SMA digesters (determined via the slope of the best-fitted line to the Fig. 1 graphs). First-order specific TCOD removal rate constant of the BMP digesters.

Experimental design, materials, and methods

Data analysis procedures

The conversion of measured biogas volume data from the experimental conditions to the standard temperature and pressure condition was done using Eq. (1).where. : Biogas volume at the standard temperature and pressure condition (mL). : Measured biogas volume (mL). : Standard temperature (273.15). : Digester temperature (273.15 + 38 = 311.15). : Pressure at the time of measuring the biogas volume (atm). : Standard pressure (1 atm). The daily methane production rate was determined via Eq. (2) : Daily methane production rate (mL/g TCODadded.d). : Cumulative biogas production yield until ith measurement (mL/g TCODadded). : Cumulative biogas production until (i+1)th measurement (mL/g TCODadded). : Time difference between the ith and (i+1)th biogas measurement (d). Previous studies have proven that the first-order reaction model can represent the biogas production as well as the organics removal during the AD process [2], [3], [4], [5], [6]. Eq. (3) shows the first-order reaction model that was utilized to calculate the specific reaction rate constant of the BMP digesters.in which rsu, C and k are TCOD removal rate (mg/L.d), TCOD concentration (mg/L) and first-order specific rate constant (1/d), respectively. Eq. (4) is derived after integration and rearrangement of Eq. (3).in which Lt, Lu and t are TCOD concentration in the digester at time t (mg/L), ultimate biodegradable TCOD (mg/L) and digestion time, respectively.

Analytical procedure

The methane content of the produced biogas was measured with a Thermo Scientific Trace 1310 gas chromatograph (GC). The GC had a TG-Bond Msieve 5A packed column with diameter and length of 0.53 mm and 30 m, respectively. It was also equipped with a thermal conductivity detector running at the oven, detector, and filament temperatures of 80, 100, and 250 °C, respectively. The chemical oxygen demand (COD), carbohydrate, and protein contents of the samples were determined calorimetrically using a DR3900 Hach spectrophotometer. The volume of the biogas produced throughout the biochemical methane potential (BMP) test was measured with a 100 mL air-tight glass syringe (Poulten & Graf Fortuna™). The production of biogas during the biohydrogen potential test was monitored using an AMPTS II gas-measuring device (Bioprocess Control, Lund, Sweden). The analysis of variance (ANOVA) was performed using Minitab Software 17. The COD analysis was carried out using the closed reflux colorimetric method described by the Standard Methods [7]. The analyses of carbohydrate and protein were performed according to the colorimetric methods developed by Dubios et al. (1956) and Frolund et al. (1995), respectively [8], [9].

Specifications table

Subject areaEnvironmental Engineering
More specific subject areaAnaerobic digestion, organic solid waste treatment, biological treatment, bioenergy recovery
Type of dataTable, figures
How data was acquiredThe biogas methane content was measured via gas chromatography (GC). The chemical oxygen demand (COD), carbohydrate, and protein contents of the samples were determined calorimetrically using a DR3900 Hach spectrophotometer. The volume of the biogas produced throughout the biochemical methane potential (BMP) test was measured manually. The production of biogas during the biohydrogen potential test was instantly monitored throughout 72 h. The Minitab Software 17 was used for the statistical analysis.
Data formatRaw, analyzed
Experimental factorsTo analyze the soluble content, the sample was first centrifuged using a Fisher Scientific Sorvall Legend XT centrifuge at 90000 rpm for 30 min. Afterwards, the centrate (permeate) of the centrifuged samples was filtered through 0.45 μm microfiber filters.
Experimental featuresThree sets of experiment including SMA, BMP, and BHP were conducted. The acetic acid was used as a substrate for the SMA assay. The BMP test was performed with four different organic solid waste including cattle manure, SSO, PS, and TWAS. The substrate for the BHP experiment was glucose. All the experiments were done in triplicates.
Data source locationToronto, Canada
Data accessibilityData are presented in this article
Related research article[1] E. Hosseini Koupaie, A. Azizi, A.A. Bazyar Lakeh, H. Hafez, E. Elbeshbishy, Comparison of liquid and dewatered digestate as inoculum for anaerobic digestion of organic solid wastes, Waste Manage., 87 (2019) 228–236.
Value of the Data

To understand the details on translating the parameters measured under specific laboratory conditions (temperature and pressure) into the standard condition which makes the data easily comparable with other researchers' findings.

The kinetic data would be useful to compare the digestion rate of various organic waste with respect to the type of inoculum used.

The data provides comprehensive information on the application of two different inoculum sources on anaerobic digestion of synthetic (acetic acid and glucose) and real organic waste

The dataset presents the procedure of the analytical method with GC to analyze the biogas composition as well as the detailed information on several measured AD parameters.

The dataset provided in this article suggests that the startup (seeding) of industrial-scale anaerobic digestion plants can be done using dewatered digestate cake, reducing the transportation volume up to 90% compared to the application of liquid digestate.

  6 in total

1.  Characterization of soluble organic matter of waste activated sludge before and after thermal pretreatment.

Authors:  Cigdem Eskicioglu; Kevin J Kennedy; Ronald L Droste
Journal:  Water Res       Date:  2006-10-09       Impact factor: 11.236

2.  Evaluation of continuous mesophilic, thermophilic and temperature phased anaerobic digestion of microwaved activated sludge.

Authors:  Nuno Miguel Gabriel Coelho; Ronald L Droste; Kevin J Kennedy
Journal:  Water Res       Date:  2011-03-12       Impact factor: 11.236

3.  Comparison of liquid and dewatered digestate as inoculum for anaerobic digestion of organic solid wastes.

Authors:  E Hosseini Koupaie; A Azizi; A A Bazyar Lakeh; H Hafez; E Elbeshbishy
Journal:  Waste Manag       Date:  2019-02-10       Impact factor: 7.145

4.  Hydrothermal pretreatment of source separated organics for enhanced solubilization and biomethane recovery.

Authors:  A S Razavi; E Hosseini Koupaie; A Azizi; H Hafez; E Elbeshbishy
Journal:  Bioresour Technol       Date:  2018-12-10       Impact factor: 9.642

5.  Enzymatic activity in the activated-sludge floc matrix.

Authors:  B Frølund; T Griebe; P H Nielsen
Journal:  Appl Microbiol Biotechnol       Date:  1995 Aug-Sep       Impact factor: 4.813

6.  Comparison of Different Electricity-Based Thermal Pretreatment Methods for Enhanced Bioenergy Production from Municipal Sludge.

Authors:  E Hosseini Koupaie; T Johnson; C Eskicioglu
Journal:  Molecules       Date:  2018-08-11       Impact factor: 4.411

  6 in total

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