Method for reducing heavy metals of flue gases
A flue gas, heavy metal technology, applied in separation methods, chemical instruments and methods, dispersed particle separation, etc., can solve problems such as danger
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Embodiment 1
[0024] Use of non-functionalized sepiolite in a household waste incinerator with a capacity of 8t / h waste, which produces about 50,000Nm 3 / h of flue gas to be treated. The sepiolite, 90% of which has a particle size of less than 600 μm, is metered by a screw and injected pneumatically at 150° C. at a rate of 12 kg / h into the air stream and then lodged in a fabric filter.
[0025] Measurement of heavy metal content: mercury and (cadmium + thallium) in gases downstream of injection operations and filters. These heavy metals are measured by inductively coupled plasma atomic absorption or emission spectrometry:
[0026] - measurement of solid particles transported by the gas, trapped by the filter and subsequently mineralized, and
[0027] - measurement of the volatile fraction trapped by bubbling in a specific absorption solution;
[0028] The content of heavy metals is the sum of the values measured for the particulate and volatile fractions.
[0029] Concentrations norma...
Embodiment 2
[0032] In a similar manner, the same sepiolite as in Example 1 was injected into the gas of another household waste incinerator at a high temperature of 190°C. The capacity of this incinerator is 5t / h, it produces 30,000Nm 3 / h air flow; as in Example 1, metered sepiolite was added at a speed of 5.5 kg / h.
[0033] The mercury concentration measured according to the method shown in Example 1 before and after adding sepiolite is 42 μg / Nm respectively 3 and 8μg / Nm 3 , that is, the reduction rate of mercury is 80%.
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