Understanding CDM Methodologies - SuSanA
Understanding CDM Methodologies - SuSanA
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 />
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