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1 Authors: Tobias Gienau, M. Sc. Dipl.-Biologe Ulrich Brüß Prof. Dr.-Ing. Matthias Kraume Prof. Dr.-Ing. Sandra Rosenberger Project time: January 2014 – November 2017 “Nutrient recovery from biogas digestate in semi- technical scale in Northern Germany” ATHENS 2017

ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Page 1: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Authors: Tobias Gienau, M. Sc.

Dipl.-Biologe Ulrich Brüß

Prof. Dr.-Ing. Matthias Kraume

Prof. Dr.-Ing. Sandra Rosenberger

Project time: January 2014 – November 2017

“Nutrient recovery from biogas digestate in semi-technical scale in Northern Germany”

ATHENS 2017

Page 2: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Motivation Biogas plants in Germany

• In 2016 about 31.7 % of electricity consumption in Germany is based on renewable energies, 7 % on biomass energy

• Biogas plants in Germany constantly increased in number and electriccapacity

• 9.000 plants with 4.200 MWe installed power (2016)

• Development driven by“German Renewable Energy Sources Act”

Fig. 1: Development of German biogas plants, Fachagentur Biogas e.V. (July 2016)

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Number of biogas plants in Germany

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Page 3: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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[1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrient availability and crop growth: A review. Eng. Life Sci. 12, 242–257.[2] Nutrient report, Germany, Lower Saxony 2013/2014

• In 2011, about 65,5 million m³ ofanaerobic sludge from biogas plants

was ejected [1]

20000 – 25000 t/a sludge per MWe

• Nutrients are highly recommendedfor manuring processes [1]

Nitrogen 1.2 – 9.1 kg/t Ammonia 1.5 – 6.8 kg/tPhosphorus 0.4 – 2.6 kg/tPotassium 1.2 – 11.5 kg/t

But: Local usage is limited (excess)Costs for transport (50-150 km):• 10 – 17 €/m³ digestate (N-Germany)

Nitrogen load

Motivation Biogas plants in Germany

Fig. 2: Nitrogen load on agricultural fields, Lower Saxony [2]

Page 4: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Table of content

Motivation

Separation technology

Experimental set-up

Results

Conclusion and outlookFig. 3: Ultrafiltration plant Inwil- Switzerland

Page 5: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Separation technologyMembrane based

Fig. 4: Process scheme of the membrane based total conditioning process

Screw press separator

Decanter centrifugeUltrafiltration

Reverse osmosis

Page 6: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Process targets:

• Energy efficient separation

• Stable process during unstable condition

• Transport worthy nutrient production

• Reduction of transport effort

Fig. 4: Process scheme of the membrane based total conditioning process

1. Liquid fertiliser:particle free, high amount ofnitogen+potassium

2. Solid fertilser: TS > 20 %, org. nitrogen andphosphorus

3. Process water in high quality

Separation technologyMembrane based

UF: 50 % of invest costs50-60 % of energy costs

Page 7: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Experimental set-upScreening

0,5 t/h

Analysed parameters:

• Viscosity of digestate and centrate (supernatant)• Density of digestate and centrate• Polysaccharides and proteins• FOS/TAC value• Ntotal, NH4-N, K+, P2O5, • Membrane performance with 40 nm ultrafiltration

(Amicon)• TS, VS…

digestate, centrate, retentate UF, filtrate UF

Fig. 5: Ultrafiltration test- Amicon 8200

Fig. 6: Centrifuge, 2200 g, CEPA

Page 8: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Experimental set-upBiogas plant

Biogas plant Northwest Germany

• 2 MWel and 2 MWth power

• Feed: 50 t/d cattle manure, 50 t/d maize silage, 50 t/d crops

• Digestate output: 35,000 – 45,000 t/a

Problems:

• Local fields are limited

• Nitrate Groundwater

• Further Phosporusseparation required

Page 9: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Experimental set-upSeparation units

Container decanter centrifuge

Container membranetreatment0,5 t/h

Screw press separator0,5 mm mesh6-7 m³/h

5-6 m³/hZ=3.500 g

Solid fertiliser

0,5-1 t/h

Page 10: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Experimental set-upSeparation units

Ultrafiltration unit Reverse osmosis unit

• Ceramic Al2O3 membranes (50 nm)• 7,3 m² active membrane area• High cross-flow velocity 3 – 5 m/s

• Polymeric membrane• 138 m² active membrane area• 3-stage reverse osmosis for high water

qualityFouling control

Page 11: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Table of content

Motivation

Separation technology

Experimental set-up

Results

Conclusion and outlookAbb. 4: Ultrafiltrationsanlage in Inwil (Schweiz)

Page 12: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Results Screening

Digestate:

• High viscous, fibre rich, organic material

• TS = 5 – 10 % with ¾ VS

• Water density

Parameter Unit Average

N = 15

TS wt% 7.6 ± 2.4

VS wt% of TS 71.9 ± 5.0

Density kg·m-3 997 ± 28

pH --- 7.8 ± 0.2

Parameter Unit Average

N = 15

TS wt% 3.1 ± 1.2

VS wt% of TS 62.6 ± 7.4

Density kg·m-3 1017 ± 5.0

pH --- 7.8 ± 0.2

Centrifugation

After centrifugation (RZB = 3.500 g):

• moderate viscous, fibre free, organic material

• TS = 2 – 4 % with 2/3 VS

• Water density but not water viscosity

Page 13: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Viscosity-Screening:

• Viscosity after centrifugation is factor 10 – 100 higher than water (Non-Newtonian)

• Water viscosity = 0.001 Pa·s

• Average viscosity after centrifugation (Shear rate =1000 s-1) 0.014 Pa·s

• Strong diviation for the analysed samples feeding strategy is very different

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Viscosity @ 1000 1/s

Fig. 7: Viscosity at 20 °C with double-gap rheometer Anton Paar MCR 101

Results Screening

Page 14: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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• High viscosities correlate with low ultrafiltration flux (1 – 2 L·m-2·h-1)

• Bio-waste digestates are subjected to have higher flux (2.5 – 7.5 L·m-2·h-1) lower TS, lower organic concentration and viscosity

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Membrane-Screening

Fig. 8: Ultrafiltration flux at 20 °C, ∆p = 1 bar, stirrer 120 min-1, Amicon 8200 (40 nm)

Results Screening

Page 15: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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ConclusionScreening

Screening

Fig. 9: Correlation of viscosity and organic concentration

• 32 samples from agricultural biogas plants and 11 samples from bio-waste biogas plants

• Screening is necessary to understand fluid dynamics and the differences in feed and composition

Detailed engineering knowledge of rheological and physical behavior

Scale-Up could be possible!

Page 16: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Results Scale-Up

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Ntotal NH4-N P2O5 K2O

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Solid organic N/P fertiliser Liquid inorganic N/K fertiliser Process water

Digestate

14 mg/L10 mg/L

0.1 mg/L1 mg/L

WWTP effluent quality

Page 17: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Results Scale-Up

0%10%20%30%40%50%60%70%80%90%

100%

SP DEC UF RO

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Water-Energy Nexus:

• Production of clean water and total reduction of organic/inorganic residues

• Production of high concentrated nutrients for direct manuring applications (N/P/K)

• Recycling of limited resources (Phosphorus)

Fig. 10: Concentration based retention of total solids

Costs for manuring procedure and transport• 10 – 17 €/m³ digestate (Northern Germany)

Operation costs incl. investment• 6 – 10 €/m³ digestate

MINUS (3 – 4 €/m³) [3]Price for conc. nutrients

(equivalents of synth. fertilizer) [3] Döhler et al. (2011), Effizente Gärrestaufbereitung und - Verwertung

Page 18: ATHENS 2017 - UESTuest.ntua.gr/athens2017/proceedings/presentations/T_Gienau.pdf3 [1] Möller, K., Müller, T., 2012. Effects of anaerobic digestion on digestate nutrien t availability

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Conclusion and outlook

4 Years of project work…

• 2,5 years of screening and optimisation of digestate and its separated fractions

• 1 year practical tests on site (Northwest Germany)• Separation of 1,500 m³ of digestate• Process water in very high quality (<15 mg/L COD, 10 mg/L NH4

+-N)• Concentrated fractions of liquid and solid fertilisers

• Now: 3 months practical tests on side (West Germany)• Validating experimental results• Optimisation of energy consumption

(Target -50% of ultrafiltration unit)

… 2- 3 months for PhD, publication…

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Thank you very much for your kind attention!

Please feel free to ask any questions…