Progress on Pit Foaming (what we know, what we dont know, what were - - PowerPoint PPT Presentation

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Progress on Pit Foaming (what we know, what we dont know, what were - - PowerPoint PPT Presentation

Progress on Pit Foaming (what we know, what we dont know, what were doing) 2015 Iowa Pork Congress Dan Andersen, PhD Steve Hoff, PhD Dept. of Ag & Biosystems Engineering Iowa State University Brian Kerr, PhD Steve Trabue, PhD


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SLIDE 1

Progress on Pit Foaming

(what we know, what we don’t know, what we’re doing)

2015 Iowa Pork Congress

Dan Andersen, PhD Steve Hoff, PhD

  • Dept. of Ag & Biosystems Engineering

Iowa State University Brian Kerr, PhD Steve Trabue, PhD USDA-ARS National Center for Agriculture and the Environment Ames, Iowa January 28, 2015

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SLIDE 2

Objectives for Today

Update on IPPA-funded Pit Foaming Research Summarize Results Precautionary Measures

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SLIDE 3

Overall Foaming Requirements

Three-phase Process:

  • 1. Gas generation (i.e. methane, hydrogen sulfide),
  • 2. Surface tension reduction (surfactants; bio- or otherwise),
  • 3. Bubble support structure (i.e. small fibers).

H2S CH4 CH4 CH4 H2S H2S

A surfactant causes surface to “elasticize” Gases otherwise naturally escaping at very low concentrations are trapped Foam supported by bacteria

  • r fine fibers or ??
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SLIDE 4

Photo courtesy of Dr. Larry Jacobson, UMN Foam Creeping Through Slats (4 ft of foam case)

In-field Foaming

Foam Into Animal Occupied Zone Photo courtesy of Dave Preisler, MPB;

  • Dr. Larry Jacobson, UMN
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SLIDE 5

Curious Nature of Foaming

  • Has occurred in one pit of side-by-side rooms

with equalizing channel.

  • Commonly found in one barn of multi-barn sites

with common genetics, feed, management, etc.

  • Attempts at correlating foaming vs non-foaming

barns with multiple factors has been elusive.

Photo courtesy of Dr. Larry Jacobson, UMN

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SLIDE 6

IPPA Funded Research Project

GOAL: Finding and Correcting the Mechanisms of Foaming

Photo courtesy of Dr. Larry Jacobson, UMN

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SLIDE 7

IPPA Funded Research Effort

  • Multi-state effort (ISU, UMN, UILL) involving 20+ academic

professionals with expertise in manure management, chemistry, microbiology, feed rations, and digestibility

  • $1M investment over three years (we are finishing YR2)
  • Project managed by Iowa State University
  • Our team is working diligently to solve this problem
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SLIDE 8

Multi-state Research Collaboration

  • Feed trials
  • Chemical composition

analysis

  • Methane production
  • Foaming potential

testing

ISU/USDA-ARS UMN

  • Extensive producer

survey

  • Microbial analysis
  • Foaming potential

testing

UILL

  • Organize all manure

sampling and distribution

  • Microbial analysis

Dan Andersen Brian Kerr Steve Trabue Chuck Clanton Larry Jacobson Bo Hu Brian Hetchler Rich Gates, Angela Kent, Laura Pepple

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SLIDE 9

Theory

  • Biogas

Generation of methane, CO2 and hydrogen sulfide.

  • Surfactants

Materials that significantly change the surface tension.

  • Stabilizer

Increases the stability of foam bubbles, like small fibers and

  • ther hydrophobic particles.
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SLIDE 10

Hypotheses - Mechanism

(1) Increased prevalence of foaming is due to increased biogas/methane production from the manure (2) Elevated concentrations of surface active agents in foaming manures are causing greater gas capture (3) Foam is being stabilized by small particles/proteins (4) Differing physical, chemical, and biological properties are related to dietary inputs.

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SLIDE 11

Hypotheses - Microbial

  • Brief Background
  • ARISA & Sequencing
  • Site, Management, and Environmental Factor Database
  • Objective 1 – Microbial community differences
  • Objective 2 – Identify relevant microbes using sequencing
  • Objective 3 – Use relational database with Obj’s 1 and 2
  • Methanogen Sequencing
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SLIDE 12

Manure Sampling SOP

A B C D foam/crust transition slurry sludge Samples were collected from discrete depths in the manure storage pit. Samples from 2 Integrators Over 60 Sites Generated more than 2000 manure samples

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SLIDE 13

Sample Summary: Cases

CLASSIFICATION INTEGRATOR A

  • INTEGRATOR

B #

OF

SAMPLES #

OF

SAMPLES

  • NON-FOAMING

250

  • 183

FOAMING 255

  • 362

NOT TREATED 178

  • 163

TREATED 327

  • 362

PREVIOUS PUMP OUT 24

  • 18

FALL 2012 337

  • 460

SPRING 2013 142

  • 38

FALL 2013 2

  • 9

CASE 1 (FOAMING) 115

  • 76

CASE 2 (NON-FOAMING) 85

  • 258

CASE 3 (TRANSITION) 157

  • 111

CASE 4 (UNSTABLE) 148

  • 80

TOTAL 505

  • 525
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SLIDE 14

Why Foam? Why Now? Diet composition and particle size effects on nutrient excretion

Diet ID Diet Composition Digestion/Excretion Coefficient Output, kg1 Output difference, kg Estimated C Equivalence, kg2

C-SBM 4.6% EE 63% (37%) 6,592 7.0% NDF 66% (34%) 9,223 17% CP 88% (12%) 7,905 45% Carbon 91% (9%) 15,694 C-SBM + FIBER 6.2% EE 63% (37%) 8,889 2,297 (+35%) 28% 13.8% NDF 68% (32%) 17,112 7,889 (+85%) 55% 17% CP 85% (15%) 9,881 1,976 (+25%) 17% 46% Carbon 87% (13%) 23,291 7,597 (+48%)

1Output based upon 310 kg feed/pig from wean-to-finish and 1,250 pigs/barn. 2Lipid = 76% carbon; Protein = 53% carbon; Fiber = 45% carbon.

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SLIDE 15

Dietary Tidbits

  • Averaged across 3 trials in our metabolism/tank studies, high fiber diets increased

manure carbon by approximately 40%.

  • Intact fats are less digestible than ‘added’ fats (e.g., 65% versus 85%,

respectively).

  • We do not know any interactive effects between fiber and lipid type, or between

fiber and lipid level.

  • On average, grinding to a finer particle size, 374 vs 631 m, improved FAT

, FIBER, CP , and C digestibility by 30, 8, 3, and 3%, respectively. In general, finer grinding improves digestibility of low-digestible ingredients more than high-digestible ingredients.

  • DDGS of 340 μm exhibited an FAT digestibility of 75% compared to 57% for DDGS of

650 μm

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SLIDE 16

Diets in Practice:

More C in manure, more methane potential

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SLIDE 17

How do you study the gas phase?

MPR L L ∗ day = (Methane % 1 100)(Biogas Produced mL + Vheadspace) × ρmanure( g mL) Mass of sample g × incubation period(minutes) × 1440 minutes day

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SLIDE 18

Methane Production Rates

  • Methane production rate was higher in foaming barn than non-foaming barns.
  • Why?
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SLIDE 19

What would cause this difference?

  • Quantity of carbon inputs?
  • TS, VS, VFA
  • Source of carbon?
  • BMP

, VFA

  • Differences in microbes?
  • Degraders, methanogens, sulfate reducers
  • Microbial community structure
  • Response to different carbon substrates?
  • Differences in pathways/response to substrate?
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SLIDE 20

Quantity of Food?

2 4 6 8 10 12 A B C D

Total Solids (%) Sample Depth

Foaming Non-Foaming A D E B C A A 1 2 3 4 5 6 7 8 9 A B C D

Volatile Solids (%) Sample Depth

Foaming Non-Foaming A C D B B A A

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SLIDE 21

Quality of Food?

  • Difference between foaming and non-foaming, but non-foaming is better and driven by VFA’s
  • More solids deeper in the manure, but quality of those solids is lower
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SLIDE 22

Microbial Data – What your looking at

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SLIDE 23

Microbial Differences?

  • Foaming and non-foaming

sites have distinct microbial communities

  • Sequencing Data
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SLIDE 24

Microbial Richness (Diversity)

Integrator A Integrator B

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SLIDE 25

So which microbes are these?

  • Differences in relative abundance of dominant taxa are associated with

foaming—but no new microbes.

0% 2% 4% 6% 8% 10% 12% 14% 16% 18% 20%

non.foaming foaming

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SLIDE 26

So can these microbes be related to management practices?

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SLIDE 27

So what is influencing these microbes?

Integrator B

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SLIDE 28

Is this related to functionality?

Integrator B

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SLIDE 29

So do they like a certain food better?

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SLIDE 30

What about surfactants?

Difference between F and NF – driven by VFA concentrations Difference between B and C&D driven by ??? (oil/long chain fatty acids) What is role of particles/proteins?

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SLIDE 31

Surfactant should drive capacity to foam

Generally small differences in ability of manure to foam.

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SLIDE 32

What stabilizes foam?

1 2 3 4 5 6 7 8 9 A B C D

Volatile Solids (%) Sample Depth

Foaming Non-Foaming A C D B B A A

  • What did we notice about samples that stabilized
  • Solids rich, but finer looking solids, not big chunks
  • Liquid drained more slowly from the foam
  • Sort of set up, with solids in bubble matrix
  • Good foams grey/brown (protein), bad foams were white/clear (fats/oils)
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SLIDE 33

Foam is really stable

200 400 600 800 1000 1200 1400 1600 1800 A B C D Foam Half-Life (Minutes) Sample Depth Foaming Non-Foaming

A B B B B B

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SLIDE 34

The foam stays wet - viscous

2 4 6 8 10 12 Foam Foaming Manure Non-Foaming Manure

Viscosity (cP)

As Is Centrifuged Filtered

A B B a b b 1 2 2

Its not just the solids, something else is giving us viscosity in the foam.

  • sugar, oil, lipopolysaccharides, proteins? Microbial goo
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SLIDE 35

but… Particles hold it together

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 0.01 0.1 1 10 100 1000

Fraction of Particles Finner Particle Size (um)

Foam Foaming Manure Non-foaming Manure

20 40 60 80 100 120 140 160 180 200 Foam Foaming Manure Non-foaming Manure

Averag Particle Size (um)

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SLIDE 36

Does diet influence these particles?

0.00 0.04 0.08 0.12 0.16 0.20 0.0 0.3 2.0 16.0 128.0 1,024.0

Fraction of Particles in Size Class Particle Size (μm)

C-SBM-C C-DDGS-C C-SH-C C-SBM-F C-DDGS-F C-SH-F

Greater percent of particles were fine silt particles from inoculated manure (p < 0.05) & courser grind (p = 0.1254)

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SLIDE 37

If you add these particles will make foam?

Yes…. But they have to interact with proteins Add moving particles from foaming manure to non- foaming manure will make it foam.

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SLIDE 38

So Proteins then?

5000 10000 15000 20000 25000 30000 35000 40000 Foam Foaming Manure Non-foaming Manure

Protein Conent (ug/mL)

As Is Centrifuged A B B a a a

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SLIDE 39

So remove proteins, stop foam?

  • Removal of protein strongly reduces foaming capability and stability
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SLIDE 40

What’s holding the proteins together?

Total Carbohydrates mg g

  • 1 manure

0.0 0.5 1.0 1.5 2.0 2.5 Foam Foam Manure C Non-Foam Manure C

Total Hemicellulose g g

  • 1 manure

200 400 600 800 1000

Foam

Foam Manure C

Non-Foam Manure C

0.977 0.798 0.783

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SLIDE 41

So what do we know now?

  • High fiber feed ingredients have reduced nutrient digestibility increasing

levels of C reaching the pit.

  • Efficiencies in both the processing of these new C inputs and

fermentation of fatty acid material have resulted in increased levels of methane production.

  • Higher levels of methane production have resulted in separation (i.e.,

translocation) and concentration of biological material into a foam layer.

  • The foam layer itself showed unique characteristics:
  • Solids Enriched with Fine Particles (Proteins)
  • Enhanced Foam Stability
  • Higher Total Carbohydrates
  • Liquid is viscous
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SLIDE 42

Precautionary Measures

  • Any attempt to break-up foam WILL release

explosive levels of methane. Therefore….

  • 1. All ignition sources OFF (i.e. pilot lights, welding),
  • 2. Set ventilation at 30 cfm/pig space minimum,
  • Use open curtains if ≥ 10 mph wind, OR,
  • Use fans* + ceiling inlets if calm
  • 3. Make sure ceiling inlets operational,
  • 4. Vacate barn, then finally,
  • 5. Foam/pit can be disturbed.

* In a 1000-hd barn, equates to 2-48” or 3-36” or 6-24” fans

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SLIDE 43

Ventilation Strategies

(1000-hd Finisher) 6-24” fans or 3-36” fans or 2-48” fans + operational ceiling inlet system + curtains closed OR Curtains Open with Wind of ≥ 10 mph But NOT Curtains Open, Calm Conditions Reliance on Fans

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SLIDE 44

Precautionary Measures (NPB)

http://www.pork.org/filelibrary/November2009%20PCRSE.pdf

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SLIDE 45

Precautionary Measures (ISU)

http://www.agronext.iastate.edu/immag/

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SLIDE 46

Precautionary Measures (UMN)

http://www1.extension.umn.edu/agriculture/manure-management-and-air-quality/

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SLIDE 47

Questions, comments, discussion?