In Poland, soil acidification is, in addition to water deficiency, low humus content and low soil nutrient content, the main factor limiting plant production. The reasons for this state of affairs are both natural conditions, i.e. soil and climatic conditions, and anthropogenic conditions – human activity.
Over 90% of the land in the country was established on acidic soils, postglacial sedimentary rocks, in such soils the phenomenon of leaching of alkaline cations occurs very easily, especially in the autumn period. The lowering of soil pH occurs naturally – as a result of weathering of silicate and aluminosilicate minerals. The mineralization of organic matter in the soil is a source of CO2 – carbonic acid anhydride. Moreover, nitric and sulfuric acids are formed in soils as products of microbiological transformations of nitrogen and sulfur compounds. Natural acidification is expressed as a calcium equivalent, which indicates the number of kilograms of CaO per unit area or mass of soil that must be applied to balance a particular acidifying agent.
The anthropogenic causes of acidification became apparent only in the second half of the twentieth century. Since then, the problem of soil acidification, and especially the problem of toxic substances appearing as a result of strong soil acidification, has been the most serious factor of low productivity of arable soils and low efficiency of mineral fertilization in Poland (Lipiński 2005, Tkaczyk and Bednarek 2011). Human activities related to air pollution, the functioning of industry to a greater extent, the use of mineral fertilization, mainly nitrogen, ammonium, amide and potassium, acid rains and the intensification of agriculture are the main factors causing soil acidification. The reason for acidification to a large extent is the elevation of CaO together with the yield from 50 to 300 kg ha-1. The soil becomes acidified also after fertilization with manure and slurry as a result of the ongoing process of ammonium nitrogen nitrification. Table 1 shows the effect of mineral and natural fertilizers on soil pH. The use of mineral fertilization significantly affects the pH of the soil. The effect of mineral fertilizers on the pH of the soil depends on their properties. Nitrogen fertilizers and slurry strongly acidify the soil, when calculating the acidification strength with a calcium equivalent, it can be assumed that in order to balance one kilogram of nitrogen you need: 2 kg CaO for urea, ammonium nitrate 4 kg CaO for ammonium sulphate
Soil acidification processes take place constantly and are related to physicochemical, chemical and biological changes in the soil. Spiak (2015) states that they include, among others:

airing minerals

microbial production of organic acids

leaching into the soil profile of alkaline cations

respiration and CO₂ release processes

decomposition of organic matter

Wpływ nawozów na odczyn

Nawóz

Wpływ na glebę

Siarczan amonu

Silnie zakwaszający

Saletra amonowa

Zakwaszający

Mocznik

Zakwaszający

RSM

Zakwaszający

Gnojowica

Zakwaszający

Obornik

Słąbo zakwaszający

Sól potasowa

Neutralny

Siarczan potasu

Neutralny

Siarczan magnezu

Neutralny

Saletra potasowa

Alkalizujący

Wapno węglanowe

Alkalizujący

Dolomit

Alkalizujący