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Understanding CDM Methodologies - SuSanA

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Debate on<br />

required Level of<br />

Detail of adipic<br />

Acid Production<br />

Calculation<br />

Box 26: Request for review of CER issuance due to unclear amount of<br />

adipic acid produced<br />

The EB launched a request for review of issuance for one of the two registered<br />

AM0021 projects as it felt that the calculation of the adipic acid production was<br />

not transparent and should be reproducable for the reader of the monitoring<br />

report. As a response the verifying DOE sent a 2 page-description of the method<br />

for calculation with the remark that the process of calculation is very complex<br />

and that the underlying data is stored and processed on SAP systems and other<br />

databases of the adipic acid plant. The DOE continued saying that a secondary<br />

check of the calculations by the RIT or EB would require sending a 10 MB file<br />

of which checking would require a few man-days of someone who is familiar<br />

with the subject. This argumentation was accepted and the CERs were issued<br />

subsequently.<br />

5.3.3 AM0034<br />

Project description<br />

Emission<br />

Reduction Options<br />

in Nitric Acid<br />

Production<br />

Applicability<br />

limited to<br />

secondary<br />

catalytic<br />

Reduction<br />

Plants built from<br />

1st January 2006<br />

onwards not<br />

eligible<br />

N 2<br />

O in nitric acid production is a by-product of the high temperature<br />

catalytic oxidation of ammonia (NH 3<br />

). The N 2<br />

O is normally vented into the<br />

atmosphere. The N 2<br />

O concentration in the tail gas depends on the pressure<br />

under which the nitric acid is produced. The emission factor can vary from 5<br />

kg N 2<br />

O/t nitric acid (+/- 10%) for atmospheric pressure plants to 9 kg N 2<br />

O/t<br />

nitric acid (+/- 40%) at high pressure plants (>8 bar). N 2<br />

O emission reduction<br />

in nitric acid plants happens through the installation of a dedicated N 2<br />

O<br />

abatement catalyst inside of the ammonia burner of the nitric acid plant.<br />

Currently, two technically proven N 2<br />

O abatement technologies exist. The first<br />

one is know as secondary catalytic reduction where N 2<br />

O is removed in the<br />

burner after the ammonia oxidation gauzes. These are the abatement project<br />

types AM0034 has been designed for. The second option is known as tertiary<br />

abatement where N 2<br />

O is removed from the tail gas. Tertiary abatement itself<br />

can be classified in non-selective catalytic reduction (NSCR) and selective<br />

catalytic reduction (SCR). The former option is used for reducing the local<br />

pollutant NO x<br />

from nitric acid manufacturing but also partly reduces N 2<br />

O<br />

emissions. Generally speaking secondary abatement achieves higher N 2<br />

O<br />

reduction at lower costs.<br />

Secondary catalytic reduction requires the installation of a dedicated N 2<br />

O<br />

catalyst in the ammonia burner and a complete N 2<br />

O monitoring system<br />

including both a gas volume flow meter and an infrared analyzer.<br />

Applicability conditions<br />

The methodology is applicable to nitric acid plants that have been built<br />

before 1 st January 2006 and where the host country does not mandate<br />

any reduction in N 2<br />

O emissions. For plants where any N 2<br />

O abatement<br />

technology (including a non-selective catalytic reduction unit) is operating the<br />

methodology is not applicable.<br />

Project boundary<br />

The project boundary encompasses all units and facilities required for the<br />

nitric acid production process from the inlet to the stack.<br />

70

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