ethanol co-product utilization and its impact on the environment -beef cattle

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thanol Co-Product Utilizatio and its impact on the environment -beef cattle Rick Koelsch & Galen Erickson

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Ethanol Co-Product Utilization and its impact on the environment -beef cattle Rick Koelsch & Galen Erickson. Manure P vs. Crop Land P Use. < 25% 25 - 50% 50 - 100% >100%. < 25% 25 - 50% 50 - 100% >100%. One-Way Flow of Nutrients Is Underlying Cause. Public Policy Response. - PowerPoint PPT Presentation

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Page 1: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Ethanol Co-Product Utilization and its

impact on the environment-beef cattle

Rick Koelsch & Galen Erickson

Page 2: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 2

Manure P vs. Crop Land P Use

< 25%25 - 50%50 - 100%>100%

Page 3: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 3

One-Way Flow of NutrientsIs Underlying Cause

< 25%25 - 50%50 - 100%>100%

Page 4: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 4

Public Policy Response• Nutrient Management Plan

– Use manure nutrients efficiently within the land base managed by the livestock operation.

• Phosphorus Risk Assessment – – Potential for P to move from land application site– Based upon “source” and “transport” factors

• Preference to imported commercial nutrients over recycled manure nutrients.

Page 5: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Ethanol Plants & Fed Cattle Population

Page 6: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

DRY MILLING-WDG(+S)GRAIN

GRIND, WET, COOK

FERMENTATION

YEAST, ENZYMES

STILL ALCOHOL & CO2

STILLAGE

DISTILLERS GRAINSWDG, DDG

DISTILLERS SOLUBLESWDGSDDGS

Abengoa Bioenergy, York, NE

Page 7: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

y = -0.0007x2 + 0.043x + 3.6604

R2 = 0.914

y = 0.0005x2 - 0.0406x + 6.5271

R2 = 0.8867

2.53.03.54.04.55.05.56.06.57.0

0 10 20 30 40 50

Level of diet DM (WDG)

Per

form

ance

ADGF:G

Performance for DGS

Vander Pol et al., 2006 Nebraska Beef Rep. and 2005 Midwest ASAS

Page 8: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Economics for WDGS

0

10

20

30

40

50

0 10 20 30 40 50WDGS Level

Re

turn

($

/hd

)

0 miles30 miles60 miles100 miles

Corn at $3.50/bu; WDGS at 95% of corn price; miles are distance from ethanol plant to feedlot

-$143.19

Page 9: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle
Page 10: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Beef Extension Pagehttp://beef.unl.edu

Beef Reports

Page 11: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Intake

Excretion

Intake-Retention=Excretion

Excretion in feces & urine

Retained nutrients

10-15%

Page 12: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

• Excretion numbers using ASABE std approach

AVG MIN MAXDiet P, % 0.31 0.25 0.50*

P Excretion 7.0 lb 4.6 lb 14.1 lb“old” std 13.9 lb

Diet CP, % 13.3 12.0 20.5*

N Excretion 64 lb 57 lb 104 lb

150 days fed for an "average" steer

Impact of DGS on excretion

Page 13: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

0

20

40

60

80

100

120

N intake N excrete N manure N volatilize

lb p

er a

nim

al

0 WDGS30 WDGS

P<0.01

P<0.01

P<0.01

P=0.07

Impact of DGS on N challenge

N mass balance

Page 14: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

.27

.35

.52

.59

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

85% corn 85% corn +supplement

byproduct byproduct +supplement

% d

iet P

(D

M-b

asi

s)

mineral P

base diet

NRC

Dietary P in Feedlot Diets

Impact of DGS on P challenge

Page 15: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

.27

.35

.52

.59

0

0.1

0.2

0.3

0.4

0.5

0.6

0.7

85% corn 85% corn +supplement

byproduct byproduct +supplement

% d

iet P

(D

M-b

asi

s)

mineral P

base diet

NRC

Our data

Impact of DGS on P challenge

Dietary P in Feedlot Diets

Page 16: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Relationship between P intake and manure harvested P (kg/hd/d) for cattle lots.

y = 1.03x - 0.011

R2 = 0.31

0.000

0.010

0.020

0.030

0.040

0.050

0.060

0.070

0.000 0.010 0.020 0.030 0.040 0.050 0.060 0.070

P Intake (kg/hd/d)

Ma

nu

re P

(k

g/h

d/d

)

P Intake kg and Manure P kgLinear (P Intake kg and Manure P kg)

Kissinger et al., 2006 NE Beef Report

Dietary P effect on manure

Impact of DGS on P challenge

Page 17: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Traditional Corn Based Diet 10,000 head feedlot 13% CP and 0.29% P Diet

Corn/soybeans crop rotation 40% land availability for spreading

Manure applied at 4-year phosphorus rate Spread with 20 ton truck spreaders

1. Base Scenario (Corn Diet)

Page 18: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

(1)N (#/yr) 1,095,000P (#/yr) 134,000

Acres 5,800Time (hr) 910 Haul (mi) 2.0

Value $108,000Cost $52,000

1. Base Scenario (Corn Diet)

Page 19: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

40% WDGS Scenario

40% WDGS Diet 10,000 head feedlot 18.7% CP and .49% P Diet

Corn/soybeans crop rotation 40% land availability for spreading

Manure applied at 4-year phosphorus rate Spread with 20 ton truck spreaders

Page 20: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

2. 40% WDGS Scenario

(1) (2)N (#/yr) 219,000 331,000P (#/yr) 127,000 243,000

Acres 5,800 11,100Time (hr) 910 1,000 – 1,300Haul (mi) 2.0 2.9

Value $108,000 $192,000Cost $52,000 $59,000

to $72,000

Can I afford100 to 400 hours

added labor?

and $7,000to $23,000

higher costs?

Can I find 5,400 acres?

Page 21: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 21

Summary of Economic Factors…0 vs. 40% Inclusion of DGs

• Costs of DGS use:– $7,000 to $24,000 to manure application costs– 100 to 350 hours to labor & equipment requirements– 5,700 acres to land access requirements

• Benefits of DGS use:– $83,000 in gross manure nutrient value – $150,000 to $300,000 in reduced feed costs

* 10,000 head beef feedlot (40% land available)

Page 22: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Feedlot size (hd): 2500 10,000 25,000

0 byp 0.30 P 1,320 5,300 13,200

20 byp 0.40 P 1,900 7,600 19,000

40 byp 0.50 P 2,500 10,000 25,000

Assumes: 50% of land area accessible185 bu corn, corn-soybean rotation, ~35 lb P per acre (80 lb P2O5)

Land Requirements, 4yr P basis (acres)

Kissinger et al., 2006 NE Beef Report

Impact of DGS on P challenge

Page 23: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Manure P vs Fertilizer P• 79% of corn acres fertilized in 2003

• average = 35 lb/ac

• 8.1 million acres planted

• (141,750 tons P2O5)

• (54,871 tons P at 79% acres)

• 4.5 million feedlot cattle

• Excrete 12 lb = 54 mil. Lb.

• (27,000 tons)http://www.nass.usda.gov/ne/special/agchem04.pdf

Page 24: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 24

Whole Farm P Balance

No DG Inclusion

40% DG Inclusion

Page 25: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 25

Implications of Greater P Inputs

• P Inventory within farm increases at rate of 88,000 vs 180,000 lb P/year faster.

• Short Term - P Risk Assessment will…– Erosion control practices will allow banking of excess

P for some period of time…– Bank will be filled more quickly with DGS.

• Long Term - P Risk Assessment will…– Reduce fields receiving manure to meet N needs– Increase fields receiving manure to meet P needs– Increase fields ineligible for manure application

Page 26: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 26

Summary

• DGS are economical for feeding• DGS supply is dramatically increasing• Feeding DGS increases P excretion (manure)• Feeding DGS increases N volatilization• Use of DGS increases acres and cost• But, manure value increased• Nebraska opportunity (have acres)• Manure distribution challenges

Page 27: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 27

Research Opportunities?

• Remove P from DGS, Remove N from DGS• Value manure over fertilizer nutrients

– Reduce/End N volatilization– Reduce manure nuisance issues– Develop alternative technologies for separating

nutrients

• Reduce bio-availability of P to plants• Low P corn, but mass balance issue

Page 28: Ethanol Co-Product Utilization  and its  impact on the environment -beef cattle

Nebraska CNMP Program 28

Public Policy Needs• Value recycled manure over imported

fertilizer nutrients– Encourage export of manure– Encourage alternative uses of manure– Recognize environmental benefits of manure

• Cautiously apply P-Index triggers for “No Manure” application.

• Recognize critical differences in nutrient plans for cattle operations based upon DGS use.