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5.2.6 Source-specific planned improvements<br />

Pasture quality nationwide sampling measurements<br />

A review by Bown et al (<strong>2013</strong>) of values of the pasture metabolisable energy<br />

concentration and nitrogen content provided updated national estimates of pasture quality.<br />

An independent peer review of this report concluded that New Zealand should consider<br />

collecting more measurements before changing the values used in its national Agriculture<br />

Inventory (Stevens, 2014).<br />

Bown et al, (<strong>2013</strong>) had identified further improvements that could be made to sampling<br />

pasture quality, particularly of hill country pasture grazed by non-dairy cattle, sheep and<br />

deer, and further work to support regional disaggregation of pasture quality data.<br />

New Zealand organised a workshop in November 2014 to bring together industry<br />

associations and researchers. A smaller working group was formed and is due to meet in<br />

2015 to discuss and commission a multiyear study to improve the sampling, especially<br />

where gaps were identified by Bown et al (<strong>2013</strong>).<br />

Emission factor lactating cattle<br />

A three-year project to update the current estimate of the relationship between DMI and<br />

CH 4 emissions in lactating cattle started in early <strong>2013</strong>. The research is using the<br />

New Zealand Agriculture Greenhouse Gas Centre ruminant methane measurement<br />

facility purpose-built calorimeter chambers to measure the relationship between enteric<br />

fermentation emissions and DMI. As part of the study, milk yields and nitrogen content<br />

and partitioning of the feed will be conducted. The results will be used to improve the<br />

estimates of CH 4 and nitrous emissions from dairy cattle.<br />

Emission factor sheep<br />

Enteric emissions factors for sheep are being reviewed. This will include the results of<br />

recent trials using the respiration chambers based at New Zealand’s Agriculture<br />

Greenhouse Gas Research Centre. Results from these trials are undergoing detailed<br />

statistical analysis for future publishing and inclusion in the national Inventory.<br />

5.3 Manure management (CRF 3.B)<br />

5.3.1 Description<br />

In <strong>2013</strong>, emissions from the Manure management category contributed 1,219.0 kt CO 2 -e<br />

(3.1 per cent of emissions from the Agriculture sector). Emissions from Manure<br />

management have increased by 480.0 kt CO 2 -e (64.9 per cent) from the <strong>1990</strong> level of<br />

739.0 kt CO 2 -e. Methane from Manure management from dairy cattle was identified as a<br />

key category for New Zealand in the 2015 level and trend assessment and methane from<br />

Manure management from sheep was identified as a key category in a trend assessment.<br />

Livestock manure is composed principally of organic material. When the manure<br />

decomposes in the absence of oxygen, methanogenic bacteria produce CH 4 . The amount<br />

of CH 4 emissions is related to the amount of manure produced and the amount that<br />

decomposes anaerobically (ie relates to how the manure is stored) (table 5.3.1). In <strong>2013</strong>,<br />

CH 4 emissions contributed 1129.6 kt CO 2 -e (92.7 per cent of the Manure management<br />

category) (table 5.3.1).<br />

The Manure management category also includes N 2 O emissions related to manure<br />

handling before it is added to agricultural soil. The amount of N 2 O emissions depends on<br />

the system of waste management and the duration of storage. With New Zealand’s<br />

extensive use of all-year-round grazing systems, this sub-category contributed a relatively<br />

small amount of N 2 O in <strong>2013</strong> (89.4 kt CO 2 -e, 0.2 per cent of the Agriculture sector) (table<br />

148 New Zealand’s Greenhouse Gas Inventory <strong>1990</strong>–<strong>2013</strong>

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