Inventory Gas Rumah Kaca GRK Sektor Peternakan

Perhitungan Emisi Gas Rumah Kaca
Kegiatan Peternakan dan Contoh
Perhitungan

Dr.Ir. Idat Galih Permana, MSc.
Fakultas Peternakan IPB
Email: [email protected]
Telp. 081380263993

Peningkatan Kapasitas - Inventarisasi Gas Rumah Kaca Kegiatan
Pertanian, Kehutanan dan Penggunaan Lainnya
Bogor, 22-24 April 2013

Emisi GRK dari Sektor Pertanian

Source: IPCC (2006)

Emisi GRK dari Sektor Pertanian







Rice Cultivation (CH4)
Cropland Burning (CO2, CH4 , N2O, N2O)
Liming (CO2)
Urea Fertilizer (CO2)
N2O Emission from Managed Soil (N2O)





Direct N2O Soil
Indirect N2O Soil

Livestock




Enteric Fermentation (CH4 )
Manure Management (CH4 and N2O)

Jenis Ternak
 Ruminansia: sapi (sapi perah, sapi potong),
kerbau, domba dan kambing
 Non Ruminansia (Pseudoruminant): kuda
 Unggas: ayam (broiler, petelur, ayam
buras), itik, puyuh dll
 Monogastrik lainnya: babi

Populasi Ternak Nasional
Populasi Ternak di Indonesia (2000-2011)
20,000
18,000

Popilasi (x 1000 ekor)

16,000
14,000


Sapi Potong

12,000

Sapi Perah

10,000

Kerbau
Kuda

8,000

Kambing

6,000

Domba


4,000

Babi

2,000
0
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
Tahun

Populasi Ternak Nasional
Jenis
Ternak
Sapi
Potong
Sapi Perah
Kerbau
Kuda
Kambing

2000


2001

2002

2003

2004

2005

2006

2007

2008

2009

2010


2011

11,008 11,137 11,298 10,504 10,533 10,569 10,875 11,515 12,257 12,760 13,582 14,824
354

347

358

374

364

361

369

374


458

475

488

597

2,405

2,333

2,403

2,459

2,403

2,128


2,167

2,086

1,931

1,933

2,000

1,305

412

422

419

413


397

387

398

401

393

399

419

416

12,566 12,464 12,549 12,722 12,781 13,409 13,790 14,470 15,147 15,815 16,620 17,483

Domba


7,427

7,401

7,641

7,811

8,075

8,327

8,980

9,514

9,605 10,199 10,725 11,372

Babi


5,357

5,369

5,927

6,151

5,980

6,801

6,218

6,711

6,338

6,975

7,477

7,758

Distribusi Emisi Methan berdasarkan dari
Sektor Pertanian berdasarkan Sumbernya

15.5%
43.9%

2.0%

Enteric Fermentation
Manure Management
Cropland Burning
Rice Cultivation

38.7%

Distribusi Emisi Methan dari Fementasi
Enterik berdasarkan Jenis Ternak

10.4%

0.9% 1.2%
Beef Cattle

6.1%

Dairy Cattle
Buffalo
Sheep
Goat

16.0%
2.7%

62.8%

Pig
Horse

Distribusi Emisi Methan dari Manajemen
Manur berdasarkan Jenis Ternak

13.4%

1.7%
0.7%

10.2%
10.3%
4.4%

6.6%
1.1%

1.9%
3.5%
46.1%

Beef Cattle
Dairy Cattle
Buff alo
Sheep
Goat
Pig
Horse
Local Chicken
Broiler
Layer
Duck

Emisi GRK dari Peternakan


Enteric Fermentation




Methan (CH4)

Manure Management




Methan (CH4)
Direct N2O
Indirect N2O

CH4

Enteric Fermentation
 Ternak ruminansia (sapi potong,
sapi perah, kerbau, domba,
kambing), kuda, babi
menghasilkan methan.
 Gas yang dihasilkan ternak
ruminansia adalah CO2, CH4, H2S,
H2O
 Methan dihasilkan dari proses
methanogenesis di dalam rumen
dengan bantuan bakteri
methanogen.
 CO2 + 4H2 ==> CH4 + 2H2O

Manure Management
 Methan:
 Dihasilkan dari proses
penanganan manure (manure
management) pada semua
jenis ternak (sapi perah, sapi
potong, kerbau, domba,
kambing, babi, itik, ayam ras,
ayam kampung, ayam
petelur) secara anaerobik
 Penanganan secara liquid
lebih memungkinkan
terjadinya methanogenesis
dibandingkan penanganan
secara solid.

CH4

Manure Management
 Direct N2O

 Dihasilkan dari proses
kombinasi nitrifikasi dan
detrifikasi N dari manur
selama dalam penyimpanan.
 Proses nitrifikasi adalah
perubahan N-ammonia
menjadi N-nitrat dalam
kondisi oksigen yang cukup.

 Indirect N2O

 Dihasilkan dari N-volatile
seperti NH3 atau NOx

N2O

N2 O

Faktor Emisi pada ternak
tergantung dari berbagai hal:
Jenis dan Bangsa Ternak
 Berat Badan, Umur
 Produksi Susu/Kerja
 Status reproduksi
 Kualitas Pakan
 Sistem Pemberian Pakan
 Sistem Pemeliharaan
 Sistem Pengelolaan Kotoran

IPCC Guideline
 2006 IPCC Guideline for
National Greenhouse
Gas Inventory
 Vol 4 – Agriculture
 Chapter 10 – Emission
from Lovestock and
Manure Management
 Dilengkapi Worksheet
untuk inventory

IPCC Worksheet
 3A1 Enteric Fermentation
 3A2 Manure Management
 3C4 Direct N2O Soils
 3C5 Indirect N2O Soils
 3C6 Indirect N2O Manure

ALU Tool Software
 Digunakan untuk
inventory GRK pada
sektor peternakan dan
Land Use.
 Dikembangkan oleh
Colorado State
University


http://www.nrel.colostate.edu/
projects/ghgtool/index.php

2006 IPCC Software
 Digunakan untuk
inventory GRK untuk
berbagai sektor.
 Dikembangkan oleh
WMO-UNEP

Choise of Method
 TIER 1: BASIC CHARACTERISATION FOR
LIVESTOCK POPULATION
 TIER 2: ENHANCED CHARACTERISATION FOR
LIVESTOCK POPULATIONS
 Definitions for livestock subcategories;
 Livestock population by subcategory, with
consideration for estimation of annual population
as per Tier 1;
 Feed intake estimates for the typical animal in
each subcategory.
 TIER 3: FOR COUNTRY-SPECIFIC

Emisi Methan dari Fermentasi Enterik

Perhitungan Emisi Methan


Step 1: Populasi Ternak



Step 2: Faktor Emisi (FE)
Faktor Emisi harus sesuai dengan jenis
ternak. FE yang sesuai dengan negara
bersangkutan. Indonesia belum memiliki
EF untuk peternakan.
 Menggunakan Default (IPCC 2006)




Step 3: Menghitung Total Emisi

STEP 1: Animal Population






Misalnya: Ayam broiler umumnya dipelihara selama 60 hari.
Jika produksi broiler di suatu provinsi 1.000.000 ekor/tahun,
maka rataan populasi per tahun:
AAP = 60 x (1.000.000/365) = 164.383 ekor/tahun
Populasi ternak disesuaikan dengan Struktur Populasi (Dewasa
1 ST, Muda 0.5 ST, Anak 0.25 ST)

STEP 2: Faktor Emisi

Faktor Emisi Fermentasi Enterik
No

Species Type

Enteric Fermentation
(kg/head/year)

1

Beef Cattle

47

2

Dairy Cattle

68

3

Bufallo

55

4

Sheep

5

5

Goat

5

6

Pig

1

7

Horse

18

8

Local Chicken

-

9

Broiler

-

10

Layer

-

11

Duck

-

IPCC (2006) Table 10.10 & Table 10.11

STEP 3: Total Emisi



Misalnya: Pada tahun 2011 populasi sapi potong di Indonesia
adalah 14,8 juta, maka total emisi methan adalah:



Emisi CH4 dari fermentasi enterik =
47 x (14.800.000/1.000.000) = 698.6 Gg CH4/tahun

Emisi Methan dari Manajemen Manur

Perhitungan Emisi Methan


Step 1: Populasi Ternak



Step 2: Faktor Emisi (FE)
Faktor Emisi harus sesuai dengan jenis
ternak. FE yang sesuai dengan negara
bersangkutan. Indonesia belum memiliki
EF untuk peternakan.
 Menggunakan Default (IPCC 2006)




Step 3: Menghitung Total Emisi

STEP 2: Total Emisi

IPCC (2006) Table 10.14

STEP 2: Total Emisi

IPCC (2006) Table 10.15

Faktor Emisi Manajemen Manure
No

Species Type

Manure Management
(kg/head/year)

1

Beef Cattle

1

2

Dairy Cattle

31

3

Bufallo

2

4

Sheep

0.20

5

Goat

0.22

6

Pig

7

Horse

2.19

8

Local Chicken

0.02

9

Broiler

0.02

10

Layer

0.02

11

Duck

0.02

7

IPCC (2006) Table 10.14 & Table 10.15

STEP 3: Total Emisi



Misalnya: Pada tahun 2011 populasi sapi potong di Indonesia
adalah 4,8 juta, maka total emisi methan dari manajemen
manur adalah:



Emisi CH4 dari manajemen manur =
(1 x 14.800.000)/1.000.000 = 14.8 Gg CH4/tahun

Total Emisi
Emisi Methan dari Sapi Potong

14.8; 2.07%
698.6; 97.93%

Fermentasi Enterik
Manajemen Manur

Emisi N2O dari Manajemen Manur

Definition of Manure Management System
System

Definition

Pasture/Range/Paddock

The manure from pasture and range grazing
animals is allowed to lie as deposited, and is not
managed.

Daily spread

Manure is routinely removed from a confinement
facility and is applied to cropland or pasture
within 24 hours of excretion.

Solid storage

The storage of manure, typically for a period of
several months, in unconfined piles or stacks.
Manure is able to be stacked due to the presence
of a sufficient amount of bedding material or loss
of moisture by evaporation.

Dry lot

A paved or unpaved open confinement area
without any significant vegetative cover where
accumulating manure may be removed
periodically

Definition of Manure Management System
System

Definition

Liquid/Slurry

Manure is stored as excreted or with some minimal
addition of water in either tanks or earthen ponds
outside the animal housing, usually for periods less
than one year.

Uncovered anaerobic
lagoon

A type of liquid storage system designed and operated
to combine waste stabilization and storage. Lagoon
supernatant is usually used to remove manure from the
associated confinement facilities to the lagoon.
Anaerobic lagoons are designed with varying lengths of
storage (up to a year or greater), depending on the
climate region, the volatile solids loading rate, and
other operational factors. The water from the lagoon
may be recycled as flush water or used to irrigate
and fertilise fields.

Pit storage below
animal confinements

Collection and storage of manure usually with little or
no added water typically below a slatted floor in an
enclosed animal confinement facility, usually for
periods less than one year.

Definition of Manure Management System
System

Definition

Anaerobic digester

Animal excreta with or without straw are collected and
anaerobically digested in a large containment vessel or
covered lagoon. Digesters are designed and operated
for waste stabilization by the microbial reduction of
complex organic compounds to CO2 and CH4, which
is captured and flared or used as a fuel

Burned for fuel

The dung and urine are excreted on fields. The sun
dried dung cakes are burned for fuel.

Cattle and Swine deep
bedding

As manure accumulates, bedding is continually added
to absorb moisture over a production cycle and possibly
for as long as 6 to 12 months. This manure
management system also is known as a
bedded pack manure management system and may be
combined with a dry lot or pasture.

Composting - invessel

Composting, typically in an enclosed channel, with
forced aeration and continuous mixing.

Composting - Static
pile

Composting in piles with forced aeration but no mixing.

Definition of Manure Management System
System

Definition

Composting - Intensive
windrow

Composting in windrows with regular (at least daily) turning
for mixing and aeration.

Composting - Passive
windrow

Composting in windrows with infrequent turning for mixing
and aeration.

Poultry manure with litter

Similar to cattle and swine deep bedding except usually not
combined with a dry lot or pasture. Typically used for all
poultry breeder flocks and for the production of meat type
chickens (broilers) and other fowl.

Poultry manure without litter

May be similar to open pits in enclosed animal confinement
facilities or may be designed and operated to dry the
manure as it accumulates. The latter is known as a high-rise
manure management system and is a form of passive
windrow composting when designed and operated Properly

Aerobic treatment

The biological oxidation of manure collected as a liquid with
either forced or natural aeration. Natural aeration is limited
to aerobic and facultative ponds and wetland systems and is
due primarily to photosynthesis. Hence, these systems
typically become anoxic during periods
without sunlight.

Emisi N2O dari Manur
 Direct N2O

 Dihasilkan dari proses
kombinasi nitrifikasi dan
detrifikasi N dari manur
selama dalam penyimpanan.
 Proses nitrifikasi adalah
perubahan N-NH3 menjadi Nnitrat dalam kondisi oksigen
yang cukup.

 Indirect N2O

 Dihasilkan dari N-volatile
menjadi NH3 atau NOx. N
organic yang mudah menjadi
volatil adalah urea dan ureic
acid

N2O

N2 O

DIRECT N2O EMISSION

Nitrogen Exretion Rate (Nrate)

IPCC (2006) Table 10.19

Nitrogen Exretion Rate (Nrate)
No

Species Type

N Exreation Rate
(kg N/1000 kg mass/day)

1

Beef Cattle

0.34

2

Dairy Cattle

0.47

3

Bufallo

0.32

4

Sheep

1.17

5

Goat

1.37

6

Swine

0.50

7

Horse

0.46

8

Local Chicken

0.82

9

Broiler

1.10

10

Layer

0.82

11

Duck

0.83

IPCC (2006) Table 10.19

Typical Animal Mass of
Livestock Category (TAM)
No

Species Type

Typical Animal Mass of
Livestock Category

1

Beef Cattle

350

2

Dairy Cattle

319

3

Bufallo

330

4

Sheep

28

5

Goat

30

6

Swine

28

7

Horse

238

8

Local Chicken

0.9

9

Broiler

1.2

10

Layer

1.8

11

Duck

1.5

IPCC (2006) Table 10.A4 – 10.A.9

Annual Nitrogen Exretion per
Species Nex (N kg/animal/year)
 Banyaknya N yang diekresikan
seekor ternak per tahun.
 Tergantung pada exretion N dan animal
body mass

 Nex = Nrate x TAM x 365 / 1000
(N kg/animal/year)

Total Nitrogen Excretion for the
MMS (NEMMS)
 Banyaknya N yang diekresikan oleh
seluruh populasi ternak per tahun.
 NEMMS = T x Nex x MS
(N kg/jenis ternak/year)

Total Nitrogen Excretion for the MMS
(NEMMS)
 NEMMS = ex = Nrate x TAM x 365 /
1000
 N kg/animal/year

Faktor Emisi untuk Direct N2O
No

Species Type

Emission Factor for Direct
N2O

1

Beef Cattle

0.02

2

Dairy Cattle

0.02

3

Bufallo

0.02

4

Sheep

0.02

5

Goat

0.02

6

Swine

0.02

7

Horse

0.02

8

Local Chicken

0.001

9

Broiler

0.001

10

Layer

0.001

11

Duck

0.001

IPCC (2006) Table 10.21

Annual Direct N2O Emission from
Manure Management
 N2O emission = NEMMS x EF x 44/28
 (kg N2O per year)
 44/28 is conversion (N2O-N) to (N2O)

INDIRECT N2O EMISSION

Fraction of managed livestock manure
nitrogen that volatilises
 Fraksi N
yang volatil
untuk setiap
jenis ternak
dan
manajemen
manur

IPCC (2006) Table 10.22

Terima Kasih