Hydrogen sulphide is a natural component of biogas. Its concentration depends on the sulphur content of the raw material being digested and lies in the range 1,500 ppm 5,000 ppm or 0,15-0.5 vol. % or 2.1-7 g H2S/m³. Hydrogen sulphide is responsible for corrosion of various parts of the plant equipment.
The use of biogas in an internal combustion engine causes uncontrollable corrosion problems. Engine components are very susceptible to corrosion by H2S and its reaction product SO2.
The experience of various manufacturers and users, as well as the (older) literature indicate that with the sulphur concentrations mentioned, the service life of the engines can be reduced by up to 15% of their normal value. Not only are the resulting repair and maintenance costs increased but also the costs for service materials such as spark plugs and lubricating oils. Even with special oils the oil change interval drops up to one-fifth of that under normal conditions. The oil becomes acidic from sulphur dioxide and thus loses its lubricating properties.
Acidic exhaust gases corrode the exhaust systems very severely.
Desulphurizing biogas with acceptable investment and operating costs is only possible employing the dry desulphurization method. Iron-containing materials of specified compositions are utilized as absorbing agents for H2S. Alongside the traditional, commercially available absorbents, certain substitutes can be used. Various tropical and subtropical soils contain sufficient iron in a suitable form. They must be prepared, in order to obtain the proper purifying characteristics. The material must be loose, porous, moist and granular.
The raw soil has to be ground and mixed with a filler and water to obtain a homogeneous texture. The finished absorbent is placed on gas-permeable trays in a purification chamber. The raw biogas is fed in at the bottom and the desulphurized or partially desulphurized gas is extracted from the upper part of the chamber.
Eventually the absorbing agent is saturated with sulphur and can be regenerated either inside the chamber or outside through natural ventilation with air (oxygen). The absorbent material can, therefore, be re-used several times.
Using two or more purification chambers connected in series ensures a continual production of purified gas and allows a good capacity utilization.
The spent absorbent can be disposed of safely by burying it. Various factors must be considered when dimensioning the purification chambers. A certain maximum flowspeed should not be exceeded The gas volume to be purified per unit time determines the cross section of the purification chamber. The chamber volume and, hence, the amount of absorbent determine the operating time for the purification process up to regeneration or exhange of the absorbent.
A calculation procedure simplifies the dimensioning of the desulphurization unit.