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Anaerobic Digestion of Finishing
Cattle Manure
A.K. Watson, S.C. Fernando, G.E. Erickson, T.J. Klopfenstein
University of Nebraska, Lincoln, NE
Integrated BioRefinery
Feedlot Ethanol Plant
Anaerobic Digester
Distillers Grains
Manure
Crop
Production
Grain
Integrated BioRefinery
Feedlot Ethanol Plant
Anaerobic Digester
Distillers Grains
Manure
Crop
Production
Grain
Integrated BioRefinery
Feedlot Ethanol Plant
Anaerobic Digester
Distillers Grains
Manure
Crop
Production
Grain
Objectives
Trial 1
• Impact of cattle diet on manure quality
Trial 2
• Impact of cattle housing and ash contamination
Materials and Methods
• Seven, 1 L digesters
– Turnover every 20 days (sample
and feed 1/20th every day)
– 9% DM
– 37° C
– pH 7.00 (sodium hydroxide)
– Anaerobic conditions, constant
flow of N2 gas
0.00
0.05
0.10
0.15
0.20
0.25
0.30
30 35 40 45 50 55 60 65
Methaneproduction,L/gOMfed
C
3 d
9 d
18 d
37 C
20 d RT
Mesophilic Thermophilic
Varel et al. 1980. Effect of temperature and retention time on methane production from
beef cattle waste. Applied and Environmental Microbiology 40:217-222.
Materials and Methods
• Methane Production
– Methane Detector
• RKI instruments
– Concentration & flow rate
= methane production
• DM and OM degradation
– Feed 9.0% DM
– Measure DM and OM of
effluent
Impact of Diet
• Control Cattle
– 82.5% DRC
– 5% Molasses
– 7.5% Alfalfa
– 5% Supplement
• 0.986% urea
• WDGS Cattle
– 47.5% DRC
– 40% WDGS
– 7.5% Alfalfa
– 5% Supplement
Impact of Diet
• Complete collection in cement gutter
– 4 steers on each diet
– 3 d
– Manure slurry analyzed and weighed into individual
feeding allotments
• Switchback design
– 7 digesters
– Digesters on trt for 42 d (2 complete turnovers)
– Measurements made last 5 d
Cattle Performance
0.150
0.155
0.160
0.165
0.170
0.175
0 10 20 30 40 50
G:F
Corn DGS Inclusion, % of diet DM
Bremer et al. 2011. Effect of distillers grains moisture and inclusion level in livestock
diets on greenhouse gas emissions in the corn-ethanol-livestock life cycle. Prof. Anim.
Sci. 27:449-455.
Linear Quad
WDGS < 0.01 < 0.01
MDGS < 0.01 0.05
DDGS < 0.01 0.45
Digestibility
0
20
40
60
80
100
0 40
TotalTractDigestibility,%
Corn WDGS Inclusion, % of diet DM
Corrigan et al. 2009. Effect of corn processing method and corn wet distillers grains plus
solubles inclusion level in finishing steers. J. Anim. Sci. 87:3351-3362.
P-value
Starch 0.92
OM 0.05
DM 0.08
NDF 0.72
Digestibility
0.0
0.5
1.0
1.5
2.0
2.5
0
20
40
60
80
100
0 15 30 45 60
FecalOM,kg/d
TotalTractDigestibility,%
Corn/Sorghum WDGS Inclusion, % of diet DM
Luebbe et al. 2012. Wet distillers grains plus solubles concentration in steam-flaked-
corn-based diets: Effects on feedlot cattle performance, carcass characteristics, nutrient
digestibility, and ruminal fermentation characteristics. J. Anim. Sci. 90:1589-1602.
Linear Quad
Starch < 0.01 < 0.01
OM < 0.01 0.99
NDF < 0.01 0.89
Fecal OM 0.04 0.32
Impact of Diet
% of DM CONT
Manure
CONT
Effluent
WDGS
Manure
WDGS
Effluent
Total N 3.95a 6.93d 3.79a 6.02c
P 1.88a 4.40c 2.64b 4.82d
S 0.45a 0.83c 0.51b 0.75c
Mg 0.48a 1.08c 0.65b 1.19c
a,b,c,d Means within a row without a common superscript differ (P<0.05).
Impact of Diet
• Two 6-week periods (switchback design)
CONT WDGS SEM P-value
DMD 42.7 44.9 1.1 0.05
OMD 51.0 52.9 1.1 0.10
Impact of Diet
• Two 6-week periods (switchback design)
CONT WDGS SEM P-value
Methane,
L/d
0.551 0.634 0.05 0.10
Methane,
L/g OM fed
0.116 0.137 0.01 0.05
Impact of Diet
CONT WDGS SEM P-value
OMD 51.0 52.9 1.1 0.10
Methane,
L/g OM fed
0.116 0.137 0.01 0.05
Methane,
L/g OM
degraded
0.237 0.261 0.03 0.44
• Samples taken from digesters on each
treatment at 4 time points
• Started with 100,000 sequences and 10,000
OTUs
– Data analyzed represents 3,500 OTUs
– Ribosomal Database Project (Michigan State
University)
Microbial Community Analysis
Effluent
Sample
DNA PCR
454
Sequencing
Diversity
Identity
Effluent Samples-Eubacteria at Phylum Level
Fibrobacteres
Firmicutes
Tenericutes
Actinobacteria
Synergistetes
Chloroflexi
Bacteriodetes
Proteobacteria
Verrucomicrobia
Unclassified
WDGS
CONT
Thermoprotei
Thermoplasmata
Methanomicrobia
Methanobacteria
WDGS
CONT
Effluent Samples-Archaea at Class Level
Microbial Community Analysis
-0.5
-0.4
-0.3
-0.2
-0.1
0
0.1
0.2
0.3
0.4
0.5
-0.5 -0.4 -0.3 -0.2 -0.1 0 0.1 0.2 0.3 0.4
PC2(15.5%-Bacteria,14.0%-Archaea)
PC1 (23.6% - Bacteria, 53.9% - Archaea)
Bacteria-WDGS Bacteria-CONT
Archaea-WDGS Archaea-CONT
Species Diversity
• Eubacteria populations
– WDGS 177 OTUs common to all 4 samples
– CONT 47 OTUs common to all 4 samples
• Homova P < 0.001
• Amova P < 0.001
• Archaea populations
– WDGS 137 OTUs common to all 4 samples
– CONT 87 OTUs common to all 4 samples
• Homova P = 0.019
• Amova P < 0.001
Impact of Housing
• Open lot manure quality affected by
– Cattle ration
– Environmental conditions
• season
– Animal stocking density
– Pen cleaning frequency
– Distance from the feed bunk
Feedlot Pen Surface
0
5
10
15
20
25
0 5 10 15 20 25 30
Depth,cm
Organic Matter, %
Organic Layer
Interface Layer
Soil Layer
Mielke et al. 1974. Soil profile conditions of cattle feedlots. J. Environ.
Quality 3:14-17.
Feedlot Pen Surface
0
5
10
15
20
25
0 5 10 15 20 25 30
Depth,cm
Organic Matter, %
Organic Layer
Interface Layer
Soil Layer
Mielke et al. 1974. Soil profile conditions of cattle feedlots. J. Environ.
Quality 3:14-17.
Impact of Housing
• Complete confinement
manure, 88% OM (CONF)
• Open feedlot manure, 26% OM
(FDLT)
• One 6-week period
– 3 digesters on CONF
– 4 digesters on FDLT (3 failed due
to ash buildup)
Impact of Housing
CONF FDLT SEM P-value
OMD, % 46.7 24.8 3.11 < 0.01
Methane,
L/d
0.478 0.229 0.07 < 0.01
Methane,
L/g OM fed
0.103 0.189 0.03 0.01
• 4 remaining digesters
Next Steps
• New design
– 45 L, ash removal
• Varying levels of ash contamination
– “Pure” manure 80% OM
– Soil surface of pen 10% OM
– Stockpiled 20% OM
– Fresh 25% OM
– Cement pad 50% OM
Frequency and area of pen cleaning
Summary
• Feeding WDGS to cattle
– Improves cattle performance
– Decreases digestibility in cattle
– Enhances digestibility and methane production
• Changes in OM composition of manure
• Changes in microbial community
• Open lot manure can be used as anaerobic digester
feedstock if ash buildup is avoided
– 95% of feedlot cattle in open lot soil based pens
Questions??
Himark BioGas
Vegreville, AB, Canada

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Anaerobic Digestion of Finishing Cattle Manure

  • 1. Anaerobic Digestion of Finishing Cattle Manure A.K. Watson, S.C. Fernando, G.E. Erickson, T.J. Klopfenstein University of Nebraska, Lincoln, NE
  • 2. Integrated BioRefinery Feedlot Ethanol Plant Anaerobic Digester Distillers Grains Manure Crop Production Grain
  • 3. Integrated BioRefinery Feedlot Ethanol Plant Anaerobic Digester Distillers Grains Manure Crop Production Grain
  • 4. Integrated BioRefinery Feedlot Ethanol Plant Anaerobic Digester Distillers Grains Manure Crop Production Grain
  • 5. Objectives Trial 1 • Impact of cattle diet on manure quality Trial 2 • Impact of cattle housing and ash contamination
  • 6. Materials and Methods • Seven, 1 L digesters – Turnover every 20 days (sample and feed 1/20th every day) – 9% DM – 37° C – pH 7.00 (sodium hydroxide) – Anaerobic conditions, constant flow of N2 gas
  • 7. 0.00 0.05 0.10 0.15 0.20 0.25 0.30 30 35 40 45 50 55 60 65 Methaneproduction,L/gOMfed C 3 d 9 d 18 d 37 C 20 d RT Mesophilic Thermophilic Varel et al. 1980. Effect of temperature and retention time on methane production from beef cattle waste. Applied and Environmental Microbiology 40:217-222.
  • 8. Materials and Methods • Methane Production – Methane Detector • RKI instruments – Concentration & flow rate = methane production • DM and OM degradation – Feed 9.0% DM – Measure DM and OM of effluent
  • 9. Impact of Diet • Control Cattle – 82.5% DRC – 5% Molasses – 7.5% Alfalfa – 5% Supplement • 0.986% urea • WDGS Cattle – 47.5% DRC – 40% WDGS – 7.5% Alfalfa – 5% Supplement
  • 10. Impact of Diet • Complete collection in cement gutter – 4 steers on each diet – 3 d – Manure slurry analyzed and weighed into individual feeding allotments • Switchback design – 7 digesters – Digesters on trt for 42 d (2 complete turnovers) – Measurements made last 5 d
  • 11. Cattle Performance 0.150 0.155 0.160 0.165 0.170 0.175 0 10 20 30 40 50 G:F Corn DGS Inclusion, % of diet DM Bremer et al. 2011. Effect of distillers grains moisture and inclusion level in livestock diets on greenhouse gas emissions in the corn-ethanol-livestock life cycle. Prof. Anim. Sci. 27:449-455. Linear Quad WDGS < 0.01 < 0.01 MDGS < 0.01 0.05 DDGS < 0.01 0.45
  • 12. Digestibility 0 20 40 60 80 100 0 40 TotalTractDigestibility,% Corn WDGS Inclusion, % of diet DM Corrigan et al. 2009. Effect of corn processing method and corn wet distillers grains plus solubles inclusion level in finishing steers. J. Anim. Sci. 87:3351-3362. P-value Starch 0.92 OM 0.05 DM 0.08 NDF 0.72
  • 13. Digestibility 0.0 0.5 1.0 1.5 2.0 2.5 0 20 40 60 80 100 0 15 30 45 60 FecalOM,kg/d TotalTractDigestibility,% Corn/Sorghum WDGS Inclusion, % of diet DM Luebbe et al. 2012. Wet distillers grains plus solubles concentration in steam-flaked- corn-based diets: Effects on feedlot cattle performance, carcass characteristics, nutrient digestibility, and ruminal fermentation characteristics. J. Anim. Sci. 90:1589-1602. Linear Quad Starch < 0.01 < 0.01 OM < 0.01 0.99 NDF < 0.01 0.89 Fecal OM 0.04 0.32
  • 14. Impact of Diet % of DM CONT Manure CONT Effluent WDGS Manure WDGS Effluent Total N 3.95a 6.93d 3.79a 6.02c P 1.88a 4.40c 2.64b 4.82d S 0.45a 0.83c 0.51b 0.75c Mg 0.48a 1.08c 0.65b 1.19c a,b,c,d Means within a row without a common superscript differ (P<0.05).
  • 15. Impact of Diet • Two 6-week periods (switchback design) CONT WDGS SEM P-value DMD 42.7 44.9 1.1 0.05 OMD 51.0 52.9 1.1 0.10
  • 16. Impact of Diet • Two 6-week periods (switchback design) CONT WDGS SEM P-value Methane, L/d 0.551 0.634 0.05 0.10 Methane, L/g OM fed 0.116 0.137 0.01 0.05
  • 17. Impact of Diet CONT WDGS SEM P-value OMD 51.0 52.9 1.1 0.10 Methane, L/g OM fed 0.116 0.137 0.01 0.05 Methane, L/g OM degraded 0.237 0.261 0.03 0.44
  • 18. • Samples taken from digesters on each treatment at 4 time points • Started with 100,000 sequences and 10,000 OTUs – Data analyzed represents 3,500 OTUs – Ribosomal Database Project (Michigan State University) Microbial Community Analysis Effluent Sample DNA PCR 454 Sequencing Diversity Identity
  • 19. Effluent Samples-Eubacteria at Phylum Level Fibrobacteres Firmicutes Tenericutes Actinobacteria Synergistetes Chloroflexi Bacteriodetes Proteobacteria Verrucomicrobia Unclassified WDGS CONT
  • 21. Microbial Community Analysis -0.5 -0.4 -0.3 -0.2 -0.1 0 0.1 0.2 0.3 0.4 0.5 -0.5 -0.4 -0.3 -0.2 -0.1 0 0.1 0.2 0.3 0.4 PC2(15.5%-Bacteria,14.0%-Archaea) PC1 (23.6% - Bacteria, 53.9% - Archaea) Bacteria-WDGS Bacteria-CONT Archaea-WDGS Archaea-CONT
  • 22. Species Diversity • Eubacteria populations – WDGS 177 OTUs common to all 4 samples – CONT 47 OTUs common to all 4 samples • Homova P < 0.001 • Amova P < 0.001 • Archaea populations – WDGS 137 OTUs common to all 4 samples – CONT 87 OTUs common to all 4 samples • Homova P = 0.019 • Amova P < 0.001
  • 23. Impact of Housing • Open lot manure quality affected by – Cattle ration – Environmental conditions • season – Animal stocking density – Pen cleaning frequency – Distance from the feed bunk
  • 24. Feedlot Pen Surface 0 5 10 15 20 25 0 5 10 15 20 25 30 Depth,cm Organic Matter, % Organic Layer Interface Layer Soil Layer Mielke et al. 1974. Soil profile conditions of cattle feedlots. J. Environ. Quality 3:14-17.
  • 25. Feedlot Pen Surface 0 5 10 15 20 25 0 5 10 15 20 25 30 Depth,cm Organic Matter, % Organic Layer Interface Layer Soil Layer Mielke et al. 1974. Soil profile conditions of cattle feedlots. J. Environ. Quality 3:14-17.
  • 26. Impact of Housing • Complete confinement manure, 88% OM (CONF) • Open feedlot manure, 26% OM (FDLT) • One 6-week period – 3 digesters on CONF – 4 digesters on FDLT (3 failed due to ash buildup)
  • 27. Impact of Housing CONF FDLT SEM P-value OMD, % 46.7 24.8 3.11 < 0.01 Methane, L/d 0.478 0.229 0.07 < 0.01 Methane, L/g OM fed 0.103 0.189 0.03 0.01 • 4 remaining digesters
  • 28. Next Steps • New design – 45 L, ash removal • Varying levels of ash contamination – “Pure” manure 80% OM – Soil surface of pen 10% OM – Stockpiled 20% OM – Fresh 25% OM – Cement pad 50% OM Frequency and area of pen cleaning
  • 29. Summary • Feeding WDGS to cattle – Improves cattle performance – Decreases digestibility in cattle – Enhances digestibility and methane production • Changes in OM composition of manure • Changes in microbial community • Open lot manure can be used as anaerobic digester feedstock if ash buildup is avoided – 95% of feedlot cattle in open lot soil based pens

Editor's Notes

  1. Changes in manure quality due to addition of distillers grains to the diet
  2. 95%+ of Nebraska feedlots have open lot soil based pens
  3. OM = VS and DM = TS
  4. Manure slurry = feces and urine, fresh
  5. Meta analysis of 20 WDGS (3,365 steers); 4 MDGS (680 steers); 4 DDGS (581 steers) studies All corn DGS replacing DRC, HMC or blend of two
  6. Within 3 corn types (DRC, HMC, SFC) no interactions
  7. 6 ruminally and duodenallycannulated steers in SFC diets
  8. Anaerobic digester performance
  9. For digester not animal
  10. Principal coordinate analysis plots or clusters microbial community based on species composition/who is there how abundant they are phylogenic relationshipActually many of the same species are present in both digesters (previous slides) but how abundant they are differ by trt
  11. Very difficult to collect only the top 8 cm of high OM material with this size of equipment
  12. Approximately 70% less OM in FDLT manure compared to CONFCONF manure is urine and feces, freshFDLT was urine and feces deposited onto pen surface at one time, undergoes changes over 150 d before collected, stockpiled and then utilized