**Abbreviations**

sample mass. In contrast to conventional heating, in microwave systems, the heat is generated internally, and thus, the metalized product porous mass covered heat loss from the sample. There were porosity and density factor that controlled the flame inhibiting weight decrease by fire heating behavior. For samples with a relatively low mass, the high surface area to volume ratio restricted the flame power. The rate of temperature rises, and the maximum attainable temperature could be inhibited by slurry composts. As a result, the conductivity at soil peat values was relatively low, and the soil sample was effectively coupled with inhibition of the fire dish. On the other hand, for the same cross-sectional area of the clay pot, as the sample mass depth was increased, there was a reduction in the surface area to inhibition volume ratio, and this reduced the inhibition matter in fire loss from the bottom, leading to a higher flame and fire temperature. Additionally, as Pot dish depth mass decreased, there was more efficient inhibition on fuel material to reduce interaction with the

*Advances in Forest Management under Global Change*

The inhibitor granules and water granule slurries at lightweight matter resulted in successive heat absorption in the flame plasma, and the composite granules of gypsum in the bubble composite form were so effective. The shale hydrated was

The microwave radiation metallization of char showed heat absorption in the

Şırnak porous limestones containing 20% porosity and the high gypsum content discarded as sponge stone from aggregate stocks swept to waste products. Şırnak produces the porous gypsum stones by construction stone product about 50,000 tons per annum for swept to waste broken stone wall matter to dispose, Siirt and Şırnak porous limestone was not also evaluated. Those waste stone products both should mainly be evaluated as fire inhibitor material as sponge isolator stone. Those must be evaluated in terms of high valuable metal contents emitting heat conduction and radiation. In this study, samples were subjected to microwave melting of metalized anhydrite shale tailings, fly ash, and subsequently pelletized and subjected to microwave bubbling briquetting over stone surface blocking to clusters. Porous limestone sand, fine waste of porous limestone were wide advantageous in filer raw material sequence in the region containing disseminated distribution of low and high quality cementing limestones. The porous limestones over 50–70% were produced by filler construction or isolation stones processed at least 100,000 tons waste. Every year about a few million tons of limestones could be used as waste fire inhibitor or extinguishing material. The granule in a particle size of these wastes usually occurs below 10 mm in size, which may be advantageous for the evaluation of shock wave şolator composite stone production. The evaluation of those waste sources in sponge composite iron stone block production was prompted

flame increasing process time and sample mass in the flame. Due to the heat decrease response of the composite gypsum to carbon, low slurry densities of 1.2 and 1.3 kg/lt were found to be suitable for inhibition flaming as higher densities resulted in bubbling and foaming of the metalized char/anhydrite. The waste metalized char/shale/anhydrite weight rates after radiation route in microwave were over 25%, and the bubbling route was continued in the flaming fire period of wood to those obtained by conventional heating. The main advantages of microwave melting were that both the total flaming heat rates conducted to metalized char gypsum surface equally disseminated pores, and the cooled bubbling over cooling rates was higher, and the specific energy area of solid matters in flame was lower

also effective with metalized carbon content and hydrate content.

fire field.

**120**

**5. Conclusions**

than in fly ash composite granule.

