5 Conclusions
This study concluded that Mg-rich, alkaline dust causes long-lasting soil degradation, which is manifested mainly near both magnesite processing factories, and the excess of available Mg along the direction of the prevailing spreading of alkaline emissions.
Dominant influence of excessive content of total and available magnesium compounds on soil chemical properties was confirmed by a significant increase of soil pH, carbonate content, and conductivity, while total and available Ca did not affect the mentioned characteristics. On the contrary, Ca was positively related to available Cu and Ni.
Negative relationship between the labile fraction of soil organic matter and available Mg suggests that in more affected localities weaker formation and stock of newly formed organic matter prevails, and consequently lower enzymatic activity. Thus, in addition to effective, alkaline emissions capturing filters, an important measure supporting the microbial activity of affected soil is enrichment by organic matter.
Research of soil enzymatic activities are essential, as these processes reflect the degree and size of contamination of the natural environment or any revisions by humans. It is important that the high enzymatic activity in soil was observed during a period of two to three consecutive years. This may indicate that the soil condition has become more stable.
At present, when the entry of Mg-rich, alkaline dust into the soil has been significantly reduced (by 99.75% compared to 1970), the application of measures can bring more lasting positive results than in the past, when the high deposition of Mg dust did not allow successful land reclamation.
Nevertheless, classical methods are still the most effective for reclaiming the most affected areas. It is suggested that the impermeable Mg-rich crust is mechanically removed, milled, and use as a magnesium fertilizer. Subsequently, the soil where the available Mg exceeded 2,000 mg kg-1 has to be treated chemically, by incorporating gypsum, phosphogypsum, citric-gypsum, sulphite leaches, anionic polyacrylamide and calcium dihydrogen phosphate as well as high doses of farmyard manure.
Recent methods are applicable to less affected areas. These involve the growing of Mg hyper-accumulating plants that, after composting, can be used as an organic fertilizer enriched with Mg, or growing plants that can be used for energy purposes. In the studied area, among naturally occurring vegetation, only Phragmites australis is characterised by high biomass production.
Sampling sites, where the available Mg decreased under the critical level of 1,000 mg kg-1, can be reused for agricultural production. Over the whole affected area, care must be taken to maintain a favourable state of natural vegetation. Consistent application of measures will enable a gradual return of the soil and landscape to a more productive state.