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Amendments and Feed Through Amendments and FeedThrough Additive for Gas and Odor Emission Reduction from Dairy Manure Eileen Fabian Wheeler Eileen Fabian Wheeler Professor of Agricultural Engineering Pennsylvania State University, USA American Chemical Society 242 nd National Meeting & Expo AGRO Division Denver Colorado 2011
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Amendments and Feed ThroughAmendments and Feed‐Through Additive for Gas and Odor Emission 

Reduction from Dairy ManureEileen Fabian WheelerEileen Fabian Wheeler

Professor of Agricultural Engineering

Pennsylvania State University, USA

American Chemical Society 242nd National Meeting & ExpoAGRO Division

Denver Colorado 2011

The SituationThe Situation

• An inexpensive and popular air qualityAn inexpensive and popular air quality mitigation strategy in the USA is the use of manure amendmentsmanure amendments

• Additives in dairy diets to modulate rumen fermentation and subsequent gas formationfermentation and subsequent gas formation

The ProblemThe Problem

• Evaluations of manure amendments underEvaluations of manure amendments under controlled conditions often indicate limited effectiveness despite on‐farm testimonials ofeffectiveness despite on farm testimonials of success

• A need for simultaneous• A need for simultaneous assessment of odor and pollutant gasand pollutant gas

Objective 1Objective 1

To evaluate performance of dairy manureTo evaluate performance of dairy manure amendments in reducing odor, ammonia, hydrogen sulfide and/or greenhouse gashydrogen sulfide and/or greenhouse gas emissions after short, medium and long storage periodsstorage periods.

Objective 2Objective 2

To evaluate different amendment modes ofTo evaluate different amendment modes of action on emissions

Digestive / Microbial 

Di i f iDisinfecting

Oxidizing

Adsorbents

Masking 

Chemical (pH)

Objective 3Objective 3

To characterize odor descriptors using humanTo characterize odor descriptors using human panel observations

MethodMethodScreening Study

Twenty‐Two Manure Amendments (n=1)7 i bi l/di t7 microbial/digest6 oxidizing/chemical3 di i f3 disinfectants6 masking agents1 adsorbentOdor and gas evaluations at 3 d and 30 dStorage at 20oC

Method 1/2Method 1/2Main Study

• Seven Manure Amendments (n=2 to 4)

2 microbial/digest‐MBR liquid & MPG powder/ g q p

oxidizing‐ Abandoned (acid) mine drainage

chemical CGE liquid chemical‐ CGE liquid

disinfectant‐ oxychlorine liquid

2 masking essential oils‐ peppermint & Hyssopus

Method 2/2Method 2/2Main Study

Plus one feed‐through essential oil additiveeugenol (28%) + cinnamaldehyde (17%) @ 525 mg/cow/d

Odor and gas evaluations at 3 d, 30 d and 94 dStorage at 10oC and 20oCg

MethodMethodManure Preparation

Manure collected during a Feed Additive trial

Urine: feces collected & combined 1:1 7Urine: feces collected & combined 1:1.7

MethodMethodManure Preparation

Stored @ 4oC for at least 2 wk to stabilize feedstock

Average pH 7.86

total solids 12 0%total solids 12.0%

total N 50.6 g kg‐1

No bedding

MethodMethodManure Storage & Study

2 kg Dairy Manure into 3.8L glass jars with d ( l)amendment (or Control)

5 batches with Control 

Walk‐in incubator

MethodMethodGas Measurement

Multi‐chamber steady‐state gas emission h i i f d i ( )Photoacoustic infrared gas monitor (Innova)Ammonia

b d dCarbon dioxideNitrous oxideM thMethane

Pulsed fluorescence (TEI)  H d lfidHydrogen sulfide

Methodsl l d lCalculate Steady‐State Flux

)(sf CiCo )(A

f CiCo

f = gas flux (mg cm‐2 min‐1)s = sweep air flow rate (m min‐1)s = sweep air flow rate (m min )Co = exhaust gas concentration (mg/m3)Ci = ambient gas concentration (mg/m3)iA = surface area of manure each chamber (cm2)

MethodOdor Emission

Olfactometer with qualified human panelists using Triangular Forced Choice method‐Detection threshold

‐Recognition threshold

Plus Odor QualityHedonic toneIntensityCharacter

CEN.2003. Air quality – Determination of odour concentration by dynamic olfactometry. EN. 13725 European Committee for Standardization (CEN), Management Centre: Rue de Stassart 36, B‐1050 Brussels.

Results‐Screening ExampleResults Screening Example Ammonia Measurement

A0.20

PAIRS of Treated manure + Control

m-2

hr-1

0.120.140.160.180.20

Treated with Microbial digestTreated with ChemicalTreated with DisinfectantTreated with Masking AgentTreated with AdsorbentControl

30D***

*** *** ***

NH

3 mg

cm

0 020.040.060.080.10

****** ************ ** *** **

Digestive MBR

Digestive MUN

Digestive MAE

Digestive MAC

Digestive MAF

Chemical CSE

ainage sediment

Chemical CBP

Chemical CBS

Chemical CGE

Chemical CAS

Chemical CPRBorax

drogen peroxide

chlorine solution

rvacrol + pineneEugenol

Glycerol

cimum basilicum

t black mitcham

Hyssopus oilZeolite

0.000.02

D D D

Acid mine drain CHydro

OxychlCarv Ocim

Peppermint b

Results‐Screening ExampleResults Screening Example Ammonia Measurement

A0.20

Reduction in Treated manure pH explains much of the improvementCircled amendments significantly reduced NH3 at 3 d and 30 d.

m-2

hr-1

0.120.140.160.180.20

Treated with Microbial digestTreated with ChemicalTreated with DisinfectantTreated with Masking AgentTreated with AdsorbentControl

30D***

*** *** ***

NH

3 mg

cm

0 020.040.060.080.10

****** ************ ** *** **

Digestive MBR

Digestive MUN

Digestive MAE

Digestive MAC

Digestive MAF

Chemical CSE

ainage sediment

Chemical CBP

Chemical CBS

Chemical CGE

Chemical CAS

Chemical CPRBorax

drogen peroxide

chlorine solution

rvacrol + pineneEugenol

Glycerol

cimum basilicum

t black mitcham

Hyssopus oilZeolite

0.000.02

D D D

Acid mine drain CHydro

OxychlCarv Ocim

Peppermint b

Results‐Screening Example Ammonia Measurement

• Products that reduced ammonia flux by atProducts that reduced ammonia flux by at least 10% for both 3 d and 30 d storage at 20oC included:– MBR, proprietary aerobic/facultative microbes– Acid mind drainage,– CAS, a Chemical proprietary liquid mix– Glycerol– Hyssopus oil– Peppermint black mitcham oil– Zeolite clinoptilolite

Full Results‐Screening: 2010 ASABE American Society of 

Agricultural & Biological EngineersAgricultural & Biological Engineers

Wheeler, E.F., M.A.A. Adviento‐Borbe, R.C. Brandt, P. A. Topper, D. A. Topper H A Elliott R E Graves A N Hristov V A Ishler and M ATopper, H. A. Elliott, R. E. Graves, A. N. Hristov, V. A. Ishler and M.A. Bruns. 2010. Amendments for mitigation of dairy manure ammonia and greenhouse gas emissions: Preliminary screening. ASABE Paper No. 1008662. ASABE, St. Joseph, MI.00866 . S , St. Josep , .

Wheeler, E.F., M.A.A. Adviento‐Borbe, R.C. Brandt, P. A. Topper, D. A. Topper, H. A. Elliott, R. E. Graves, A. N. Hristov, V. A. Ishler and M.A. Bruns. 2010. Amendments for mitigation of odor emissions from dairy manure: Preliminary screening. ASABE Paper No. 1008658. ASABE, St. Joseph, MI.

NOTE: Both articles “in press” for  Agricultural Engineering International: CIGR Journal 

Results‐Replicated Main Experiment Methane 3 d Storage

0.5

0.6Treated; 10oCControl; 10oCTreated; 20oCControl; 20oC

3D

d‐1 No significant improvements

0.3

0.4

Control; 20 C

**

H4cm

‐2d

0.1

0.2

mg CH

0.0

Digestive MBRDigestive MPG

id mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oil

Peppermint black mitchamFeed additive

0.0

Acid min Peppe

Results Methane 94 d Storage

C

0.6 94DTreated; 10oCControl; 10oC No significant improvements

0 3

0.4

0.5

cm‐2d‐

1

Control; 10 CTreated; 20oCControl; 20oC

No significant improvements

0 1

0.2

0.3

**

mg CH

4c

igestive MBRigestive MPG

e sedimentChemical CGE

ine solutionHyssopus oil

ck mitchamFeed additive

0.0

0.1*** ******

m

Digestiv Digestiv

Acid mine drainage sedChemic

Oxychlorine so Hyssop

Peppermint black mi Feed a

Results 0.5

0.6Treated; 10oCControl; 10oCTreated; 20oCControl; 20oC

3D

Methane0 1

0.2

0.3

0.4

**

0.0

0.1

CH

4 cm

-2 d

-1

0 4

0.5

0.6 30D

emis

sion

s, m

g C0.1

0.2

0.3

0.4

** ** *** *

Reduced CH with

CH

4 e

0.0

0 4

0.5

0.6 94D

*** ** * *

Reduced CH4 with longer storage

0.1

0.2

0.3

0.4

**

*** ******

Digestive MBRDigestive MPG

Acid mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oil

Peppermint black mitchamFeed additive

0.0

Results d dOdor Emission 3 d Storage

140 3DTreated; 10oCC t l 10oC1 Acid mine drainage reduced odor 

80

100

120Control; 10oCTreated; 20oCControl; 20oC

cm‐2d‐

1 gemission at 20oC

40

60

80

*OUE

0

20

1

i e MBRi e MPG diment

al CGEolution pus oil

itcham dditive0.0

Digestive MBDigestive MP

Acid mine drainage sedimeChemical CG

Oxychlorine solutioHyssopus o

Peppermint black mitchaFeed additi

Results Odor Emission 94 d Storage

140 94D

1 Treated; 10oC Significant reduction but generally

80

100

120

cm‐2d‐

1 ;Control; 10oCTreated; 20oCControl; 20oC

Significant reduction but generally small improvements

40

60

80

***

OUE

MBR MPG iment l CGE lution us oil t ham dditive0

20 ** *** ****** * **

Digestive MBRDigestive MPG

Acid mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oi

Peppermint black mitchamFeed additive

Results 100

120

140 3DTreated; 10oCControl; 10oCTreated; 20oCControl; 20oC

Odor Emission 20

40

60

80

100 ;

*

Emission0

20

OU

E cm

-2 d

-1

100

120

140 30D

or e

mis

sion

s, O

20

40

60

80

** ***

*

Odor emission was 

Odo

0

0

100

120

140 94D

reduced with longer storage time

20

40

60

80

** *** ******

*** * **

Digestive MBRDigestive MPG

Acid mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oil

Peppermint black mitchamFeed additive

0

Results Ammonia 3 d Storage

2.8 Treated; 10oC 3D

d‐1

2.0

2.4Control; 10oCTreated; 20oCControl; 20oC

H3cm

‐2d

No significant reductions

0.8

1.2

1.6

mg NH

0 0

0.4

MBR MPG ent CGE tion s oil ham ditive0.0

Digestive MBRDigestive MPG

Acid mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oil

Peppermint black mitchamFeed additive

Results Ammonia 94 d Storage

Treated; 10oC

N 0.02.8 94D

**

Several amendments and the feed additive reduced emissions

Treated; 10 CControl; 10oCTreated; 20oCControl; 20oC

2.0

2.4 **

m‐2d‐

1

0.8

1.2

1.6

*** *****

*

g NH3cm

MBR MPG nt CGE tion oil m itive0.0

0.4***

mg

Digestive MBRDigestive MPG

Acid mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oil

Peppermint black mitchamFeed additive

Results  2.4

2.8 Treated; 10oCControl; 10oCTreated; 20oC

3D

Ammonia0.8

1.2

1.6

2.0

;Control; 20oC

Long‐term storage, promising results:

0.0

0.4

H3 c

m-2

d-1

2.4

2.8 30D

(Digestive MPG) Digestive MBR A id i i em

issi

ons,

mg

N0 4

0.8

1.2

1.6

2.0

** *

Acid Mine Drainage Hyssopus oil

(Feed additive)

NH

3 e0.0

0.4

2.0

2.4

2.8 94D

****

(Feed additive)

Longer storage did not reduce NH3

0.4

0.8

1.2

1.6

***

*** *****

*

not reduce NH3emission

Digestive MBRDigestive MPG

Acid mine drainage sedimentChemical CGE

Oxychlorine solutionHyssopus oil

Peppermint black mitchamFeed additive

0.0 ***

Overall Correlations dGas & Odor Emissions

Odor/ Gas Odor Ammonia Methane Carbon

dioxideNitrous oxide

Hydrogen sulfide

coeff1 P coeff P coeff P coeff P coeff P coeff P

NH3 -0.43 **CH4 0.76 ** -0.22 **CO2 0.18 * 0.42 ** 0.35 **N2O 0.08 ns 0.21 ** 0.26 ** 0.53 **H2S 0.54 ** -0.25 * 0.20 * 0.25 * 0.08 ns

Odor 0.16 * 0.18 * 0.26 ** 0.29 ** 0.07 ns -0.05 ns

1Coefficient of Correlation*P< 0.05**P<=0.001ns = not significant

Conclusionsd d lManure Amendment Odor Control

Essential oils, Hyssopus and Peppermint black mitcham,Essential oils, Hyssopus and Peppermint black mitcham, were effective for long‐term odor control.

They reduced odor emission by 25 to 50% and H2S by y y 2 y80% (20oC after 94 d).  However, at 10oC  after 30 d they increased odor and H2S.

Under long‐term cool (10oC) conditions, typical of storage, digest MBR and chemical CGE were effective 

d d lin odor and H2S control.

Acid mine drainage was effective in short‐term odor t l (20oC) ff i l d li ti t ti lcontrol (20oC) offering pre‐land‐application potential

Conclusionsd lManure Amendment Gas Control

Storing manure, treated or not, reduced greenhouseStoring manure, treated or not, reduced greenhouse gas (and odor) emissions about 90%

Acid mine drainage reduced ammonia emission by 40‐g y80% after medium and long‐term storage under both cool and warm conditions

Two digestive amendments significantly reduced ammonia emissions at 30 d & 94 d storage

Feed‐through additive not efficient method for odor emission control, but showed promise for ammonia 

t l t 20oCcontrol at 20oC.

Co‐Authorsl l l lAgricultural & Biological Engineering

• Patrick Topper – Senior Research Technologist

• Robin Brandt – Lecturer– Director Penn State Odor Assessment Laboratory

• Arlene Adviento‐Borbe – Post‐Doctorate Scholar

• Deborah Topper – Research Technologist

• Hershel “Chip” Elliottp– Professor

• Robert Graves – Professor

• Roderick Thomas– Instrumentation Instructor

Co‐AuthorslDairy & Animal Science

• Virginia IshlerVirginia Ishler– Nutrient Management Extension Specialist 

– Manager Penn State Dairy Production Research and Teaching Center

• Alex Hristov– Associate Professor

G b i ll V• Gabriella Varga– Professor

C d S il S iCrop and Soil Science• Mary Ann Bruns

– Associate Professor

FundingFunding

• USDA Special GrantUSDA Special Grant– Improved Dairy Management Practices


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