BVT-Merkblatt zu Abwasser- und Abgasbehandlung
BVT-Merkblatt zu Abwasser- und Abgasbehandlung BVT-Merkblatt zu Abwasser- und Abgasbehandlung
Annexes Art. 5.7.2.5 § 1. The quantities of SO 2, SO 3 and acid droplets - expressed in SO 2-equivalent - emitted by certain plants, must be calculated taking account of the volume of gases emitted during the specific activities concerned and the average SO 2/SO 3-content measured during the same period. The determination of the flow rate and of the SO 2/SO 3-content must be performed under the same conditions of temperature and humidity. § 2. Without prejudice to the provisions of article 5.7.1.4 and of chapters 2.5 and 4.4, at one or several measurement stations located near the establishment in a location which is representative for the pollution originating from the plant, the following must be monitored: 1. sulphur dioxide immissions, if use is made of the sulphate process for the production of titanium dioxide; 2. chlorine immissions, if use is made of the chlorination process for the production of titanium dioxide. If no immission measuring station as referred to in the first paragraph is provided, measurements must be made at least 12 times per year of the total quantity of gaseous emissions of sulphur dioxide and chlorine, respectively, from the production site. § 3. From 1 January 1995, unless specified otherwise in the environmental licence and as a derogation from the provisions of chapter 4.4, the SOx-emissions originating from the dissolution and roasting phases of the titanium dioxide production must be restricted to a value of no more than 10 kg of SO2-equivalent per tonne of titanium dioxide produced. Section 5.7.3. The production of sulphur dioxide, sulphur trioxide, sulphuric acid or oleum (fuming sulphuric acid) Art. 5.7.3.1 § 1. The provisions of this section are applicable to the sulphur dioxide, sulphur trioxide, sulphuric acid or oleum producing plants referred to in subsection 7.1 of the classification list. § 2. For the implementation of these provisions, the "conversion efficiency of SO 2 to SO 3" is defined as follows: conversion efficiency = Art. 5.7.3.2 SO 2(in) – SO 2(out) ________________________ SO2(in) x 100 (%) § 1. If - in view of the gases used as raw material - it is technically possible from the viewpoint of the best available techniques, the double-contact process must be used for the conversion of SO2 to SO3. If it proves indispensable, in order to achieve the emission limitations corresponding to the conversion efficiency values prescribed in § 4 of this article, the emissions of SO2 and SO3 can be further reduced by making use of a fifth contact bed, or by means of equivalent measures. The use of any alternative process is allowed, providing that such process is at least equivalent from the perspective of pollution control and in particular providing that it guarantees the same or higher conversion rates. § 2. The single-contact process (without intermediary absorption) is permitted only if gases with SO2-contents lower than 10 % are processed, or gases of which the SO2-contents are widely varying. If it proves indispensable, in order to achieve the emission limitations corre- 366 Waste Water and Waste Gas Treatment
Annexes sponding to the conversion efficiency values prescribed in § 4 of this article, the emissions of SO2 and SO3 must be further reduced by alkaline scrubbing, or by means of equivalent measures. § 3. The wet catalytic process is allowed only with molybdenum sulphide roasting and for flue gas desulphurisation. § 4. The daily average conversion rate must be at least: 1. when use is made of the single-contact process: a) with a feed gas containing less than 6 % SO 2, a conversion rate of at least 97.5 % must be achieved b) with a feed gas containing 6 % SO 2 or more, a conversion rate of at least 98.5 % must be achieved; 2. when use is made of the double-contact process: a) with a feed gas containing less than 8 % SO 2, a conversion rate of at least 99 % must be achieved b) with a feed gas containing 8 % SO2 or more, a conversion rate must be achieved of at least: � 99.5 % with varying gas conditions � 99.6 % with constant gas conditions; 3. when use is made of the wet catalytic process, a conversion rate of at least 97.5 % must be achieved; 4. when any other process is used, a conversion rate must be achieved of at least 99 %. § 5. As a derogation from the provisions of chapter 4.4, the following emission limit values apply for: 1. sulphur dioxide: 1700 mg/Nm 3 , without prejudice to the conversion rate prescribed in article 5.7.5.1; 2. sulphur trioxide: � with constant gas conditions: 60 mg/Nm 3 ; � in the other cases: 120 mg/Nm 3 . § 6. In addition, in the environmental licence limit values may be imposed for the mass flow of the SO 3 and H 2SO 4 emissions (expressed in SO 3) in the emitted waste gases. § 7. The conversion efficiency values indicated in § 4 of this article do not apply for SO3generators of category 3 which are used to stimulate the emission of fly ash by the injection of SO3 in the flue gases of heating installations. For the flue gases treated in this way, the SO3 emission standards of the corresponding heating installation apply. Section 5.7.4 The production of nitric acid Art. 5.7.4.1 § 1. The provisions of this section are applicable to the nitric acid producing plants referred to in subsection 7.1 of the classification list. § 2. As a derogation from the provisions of chapter 4.4, for nitrogen oxides in emitted gaseous effluents - expressed in NO 2 - an emission limit value applies of: 450 mg/Nm 3 . In addition, the gaseous effluents may only be emitted colourless into the ambient air. In order to achieve this, and without prejudice to the limit value prescribed in the first paragraph, the NO 2 emission may not exceed the value resulting from the calculation of the formula below: NO 2 concentration = 1200 _________________________________ open width of the chimney mouth in dm Waste Water and Waste Gas Treatment 367
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Annexes<br />
Art. 5.7.2.5<br />
§ 1. The quantities of SO 2, SO 3 and acid droplets - expressed in SO 2-equivalent - emitted by<br />
certain plants, must be calculated taking account of the volume of gases emitted during the specific<br />
activities concerned and the average SO 2/SO 3-content measured during the same period.<br />
The determination of the flow rate and of the SO 2/SO 3-content must be performed <strong>und</strong>er the<br />
same conditions of temperature and humidity.<br />
§ 2. Without prejudice to the provisions of article 5.7.1.4 and of chapters 2.5 and 4.4, at one or<br />
several measurement stations located near the establishment in a location which is representative<br />
for the pollution originating from the plant, the following must be monitored:<br />
1. sulphur dioxide immissions, if use is made of the sulphate process for the production of titanium<br />
dioxide;<br />
2. chlorine immissions, if use is made of the chlorination process for the production of titanium<br />
dioxide.<br />
If no immission measuring station as referred to in the first paragraph is provided, measurements<br />
must be made at least 12 times per year of the total quantity of gaseous emissions of sulphur<br />
dioxide and chlorine, respectively, from the production site.<br />
§ 3. From 1 January 1995, unless specified otherwise in the environmental licence and as a<br />
derogation from the provisions of chapter 4.4, the SOx-emissions originating from the dissolution<br />
and roasting phases of the titanium dioxide production must be restricted to a value of no<br />
more than 10 kg of SO2-equivalent per tonne of titanium dioxide produced.<br />
Section 5.7.3. The production of sulphur dioxide, sulphur trioxide, sulphuric acid or<br />
oleum (fuming sulphuric acid)<br />
Art. 5.7.3.1<br />
§ 1. The provisions of this section are applicable to the sulphur dioxide, sulphur trioxide, sulphuric<br />
acid or oleum producing plants referred to in subsection 7.1 of the classification list.<br />
§ 2. For the implementation of these provisions, the "conversion efficiency of SO 2 to SO 3" is<br />
defined as follows:<br />
conversion efficiency =<br />
Art. 5.7.3.2<br />
SO 2(in) – SO 2(out)<br />
________________________<br />
SO2(in)<br />
x 100 (%)<br />
§ 1. If - in view of the gases used as raw material - it is technically possible from the viewpoint<br />
of the best available techniques, the double-contact process must be used for the conversion of<br />
SO2 to SO3. If it proves indispensable, in order to achieve the emission limitations corresponding<br />
to the conversion efficiency values prescribed in § 4 of this article, the emissions of SO2<br />
and SO3 can be further reduced by making use of a fifth contact bed, or by means of equivalent<br />
measures. The use of any alternative process is allowed, providing that such process is at least<br />
equivalent from the perspective of pollution control and in particular providing that it guarantees<br />
the same or higher conversion rates.<br />
§ 2. The single-contact process (without intermediary absorption) is permitted only if gases<br />
with SO2-contents lower than 10 % are processed, or gases of which the SO2-contents are<br />
widely varying. If it proves indispensable, in order to achieve the emission limitations corre-<br />
366 Waste Water and Waste Gas Treatment