44 research outputs found
ΠΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠ°Ρ Π΄ΠΈΠ°Π³Π½ΠΎΡΡΠΈΠΊΠ° ΠΏΡΠΎΠ±Π»Π΅ΠΌΠ½ΡΡ ΡΠΊΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΡ ΡΠΈΡΡΠ°ΡΠΈΠΉ Π½Π° ΠΎΠ±ΡΠ΅ΠΊΡΠ°Ρ ΡΠ΅ΠΊΡΠ΅Π°ΡΠΈΠΎΠ½Π½ΠΎΠ³ΠΎ ΠΏΡΠΈΡΠΎΠ΄ΠΎΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ
Completed long-term studies have shown dynamic changes in the composition and structure of the microbial soil population under the influence of soil compaction, which allows the use of microbial soil population as diagnostic indicators for environmental monitoring of recreational natural facilities.ΠΡΠΏΠΎΠ»Π½Π΅Π½Π½ΡΠ΅ ΠΌΠ½ΠΎΠ³ΠΎΠ»Π΅ΡΠ½ΠΈΠ΅ Π΄ΠΈΠ½Π°ΠΌΠΈΡΠ΅ΡΠΊΠΈΠ΅ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ ΠΏΠΎΠΊΠ°Π·Π°Π»ΠΈ ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΠ΅ ΡΠΎΡΡΠ°Π²Π° ΠΈ ΡΡΡΡΠΊΡΡΡΡ ΠΏΠΎΡΠ²Π΅Π½Π½ΠΎΠ³ΠΎ ΠΌΠΈΠΊΡΠΎΠ±Π½ΠΎΠ³ΠΎ Π½Π°ΡΠ΅Π»Π΅Π½ΠΈΡ ΠΏΠΎΠ΄ Π²Π»ΠΈΡΠ½ΠΈΠ΅ΠΌ ΡΠΏΠ»ΠΎΡΠ½Π΅Π½ΠΈΡ ΠΏΠΎΡΠ²Ρ, ΡΡΠΎ ΠΏΠΎΠ·Π²ΠΎΠ»ΡΠ΅Ρ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎ-Π²Π°ΡΡ ΠΈΡ
Π² ΠΊΠ°ΡΠ΅ΡΡΠ²Π΅ Π΄ΠΈΠ°Π³Π½ΠΎΡΡΠΈΡΠ΅ΡΠΊΠΈΡ
ΠΏΠΎΠΊΠ°Π·Π°ΡΠ΅Π»Π΅ΠΉ ΠΏΡΠΈ ΠΏΡΠΎΠ²Π΅Π΄Π΅Π½ΠΈΠΈ ΡΠΊΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ ΠΌΠΎΠ½ΠΈΡΠΎΡΠΈΠ½Π³Π° ΠΎΠ±ΡΠ΅ΠΊΡΠΎΠ² ΡΠ΅ΠΊΡΠ΅Π°ΡΠΈΠΎΠ½Π½ΠΎΠ³ΠΎ ΠΏΡΠΈΡΠΎΠ΄ΠΎΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ
ΠΠΈΠΊΡΠΎΠ±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠ°Ρ ΠΎΡΠ΅Π½ΠΊΠ° ΡΠΎΡΡΠΎΡΠ½ΠΈΡ Π»Π΅ΡΠ½ΡΡ ΠΈ Π»Π΅ΡΠΎΠΏΠ°ΡΠΊΠΎΠ²ΡΡ ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌ
The results of research of laws between the nitrogen-fixing ability of the soil and the surface con-dition of photosynthetic plants. It is established that the quantity of microbial biomass is an indicator of the state of the stand and can be used in the evaluation of the productivity and resilience of ecosystems under the influence of various factors anthropogenesis.Π ΡΡΠ°ΡΡΠ΅ ΠΏΡΠΈΠ²Π΅Π΄Π΅Π½Ρ ΡΠ΅Π·ΡΠ»ΡΡΠ°ΡΡ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ Π·Π°ΠΊΠΎΠ½ΠΎΠΌΠ΅ΡΠ½ΠΎΡΡΠ΅ΠΉ ΠΌΠ΅ΠΆΠ΄Ρ Π°Π·ΠΎΡΠΎΡΠΈΠΊΡΠΈΡΡΡΡΠ΅ΠΉ ΡΠΏΠΎΡΠΎΠ±Π½ΠΎΡΡΡΡ ΠΏΠΎΡΠ²Ρ ΠΈ ΡΠΎΡΡΠΎΡΠ½ΠΈΠ΅ΠΌ ΡΠΎΡΠΎΡΠΈΠ½ΡΠ΅ΡΠΈΡΠ΅ΡΠΊΠΎΠΉ ΠΏΠΎΠ²Π΅ΡΡ
Π½ΠΎΡΡΠΈ ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ. Π£ΡΡΠ°Π½ΠΎΠ²Π»Π΅Π½ΠΎ, ΡΡΠΎ Π²Π΅Π»ΠΈΡΠΈΠ½Π° ΠΌΠΈΠΊΡΠΎΠ±Π½ΠΎΠΉ Π±ΠΈΠΎΠΌΠ°ΡΡΡ ΡΠ²Π»ΡΠ΅ΡΡΡ ΠΈΠ½Π΄ΠΈΠΊΠ°ΡΠΎΡΠΎΠΌ ΡΠΎΡΡΠΎΡΠ½ΠΈΡ Π΄ΡΠ΅Π²ΠΎΡΡΠΎΡ ΠΈ ΠΌΠΎΠΆΠ΅Ρ Π±ΡΡΡ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½Π° ΠΏΡΠΈ ΠΎΡΠ΅Π½ΠΊΠ΅ ΠΏΡΠΎΠ΄ΡΠΊΡΠΈΠ²Π½ΠΎΡΡΠΈ ΠΈ ΡΡΡΠΎΠΉΡΠΈΠ²ΠΎΡΡΠΈ ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌ ΠΏΠΎΠ΄ Π²Π»ΠΈΡΠ½ΠΈΠ΅ΠΌ ΡΠ°Π·Π»ΠΈΡΠ½ΡΡ
ΡΠ°ΠΊΡΠΎΡΠΎΠ² Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π΅Π·Π°
ΠΠ»ΠΈΡΠ½ΠΈΠ΅ Π³ΠΎΡΠΎΠ΄ΡΠΊΠΎΠΉ ΡΡΠ΅Π΄Ρ Π½Π° Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΠ΅ ΠΏΠΎΡΠ² ΡΡΠΆΠ΅Π»ΡΠΌΠΈ ΠΌΠ΅ΡΠ°Π»Π»Π°ΠΌΠΈ Π² Π·Π°Π²ΠΈΡΠΈΠΌΠΎΡΡΠΈ ΠΎΡ ΡΠΎΡΡΠ°Π²Π° ΠΈ Π²ΠΎΠ·ΡΠ°ΡΡΠ° Π»Π΅ΡΠ½ΡΡ Π΄ΡΠ΅Π²ΠΎΡΡΠΎΠ΅Π² (Π½Π° ΠΏΡΠΈΠΌΠ΅ΡΠ΅ Π»Π΅ΡΠ½ΠΎΠΉ ΠΎΠΏΡΡΠ½ΠΎΠΉ Π΄Π°ΡΠΈ Π ΠΠΠ£-ΠΠ‘Π₯Π ΠΈΠΌ. Π.Π. Π’ΠΈΠΌΠΈΡΡΠ·Π΅Π²Π°)
The condition of wood plantings in forest-park ecosystems of megalopolises and performance of private sanitary and ecological functions by them substantially depends on intensity of influence of anthropogenic factors of the city. Intensity of these changes is corrected also by structure of tree species: it is established that for the centenary period (1909β2000) pollution of soils of LOD by heavy metals considerably increased: on lead β at 40β50 time, on copper at 17β24 time and to zinc β 4β9 times. Accumulation of heavy metals in the soil is closely connected with removal from a pollution source (city highways, the industrial enterprises), and also with a complex of properties of the soils caused by its consolidation at intensive recreational loading, and also from structure wood and shrubby plantings.Π‘ΠΎΡΡΠΎΡΠ½ΠΈΠ΅ Π»Π΅ΡΠ½ΡΡ
Π½Π°ΡΠ°ΠΆΠ΄Π΅Π½ΠΈΠΉ Π² Π»Π΅ΡΠΎΠΏΠ°ΡΠΊΠΎΠ²ΡΡ
ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΠ°Ρ
ΠΌΠ΅Π³Π°ΠΏΠΎΠ»ΠΈΡΠΎΠ² ΠΈ Π²ΡΠΏΠΎΠ»Π½Π΅Π½ΠΈΠ΅ ΠΈΠΌΠΈ ΡΠ°ΡΡΠ½ΡΡ
ΡΠ°Π½ΠΈΡΠ°ΡΠ½ΠΎ-ΡΠΊΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΡΠ½ΠΊΡΠΈΠΉ Π² Π·Π½Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎΠΉ ΡΡΠ΅ΠΏΠ΅Π½ΠΈ Π·Π°Π²ΠΈΡΠΈΡ ΠΎΡ ΠΈΠ½ΡΠ΅Π½ΡΠΈΠ²Π½ΠΎΡΡΠΈ Π²ΠΎΠ·Π΄Π΅ΠΉΡΡΠ²ΠΈΡ Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π½ΡΡ
ΡΠ°ΠΊΡΠΎΡΠΎΠ² Π³ΠΎΡΠΎΠ΄Π° ΠΈ ΠΊΠΎΡΡΠ΅ΠΊΡΠΈΡΡΠ΅ΡΡΡ ΡΠ°ΠΊΠΆΠ΅ ΡΠΎΡΡΠ°Π²ΠΎΠΌ Π΄ΡΠ΅Π²Π΅ΡΠ½ΡΡ
ΠΏΠΎΡΠΎΠ΄: ΡΡΡΠ°Π½ΠΎΠ²Π»Π΅Π½ΠΎ, ΡΡΠΎ Π·Π° ΡΡΠΎΠ»Π΅ΡΠ½ΠΈΠΉ ΠΏΠ΅ΡΠΈΠΎΠ΄ (1909β2000 Π³Π³.) Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΠ΅ ΠΏΠΎΡΠ² ΠΠ΅ΡΠ½ΠΎΠΉ ΠΎΠΏΡΡΠ½ΠΎΠΉ Π΄Π°ΡΠΈ (ΠΠΠ) Π ΠΠΠ£-ΠΠ‘Π₯Π ΠΈΠΌΠ΅Π½ΠΈ Π.Π. Π’ΠΈΠΌΠΈΡΡΠ·Π΅Π²Π° ΡΡΠΆΠ΅Π»ΡΠΌΠΈ ΠΌΠ΅ΡΠ°Π»Π»Π°ΠΌΠΈ Π·Π½Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎ Π²ΠΎΠ·ΡΠΎΡΠ»ΠΎ: ΠΏΠΎ ΡΠ²ΠΈΠ½ΡΡ β Π² 40β50 ΡΠ°Π·, ΠΏΠΎ ΠΌΠ΅Π΄ΠΈ β Π² 17β24 ΡΠ°Π·Π° ΠΈ ΡΠΈΠ½ΠΊΡ β Π² 4β9 ΡΠ°Π·. ΠΠ°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΠ΅ ΡΡΠΆΠ΅Π»ΡΡ
ΠΌΠ΅ΡΠ°Π»Π»ΠΎΠ² Π² ΠΏΠΎΡΠ²Π΅ ΡΠ΅ΡΠ½ΠΎ ΡΠ²ΡΠ·Π°Π½ΠΎ Ρ ΡΠ΄Π°Π»Π΅Π½ΠΈΠ΅ΠΌ ΠΎΡ ΠΈΡΡΠΎΡΠ½ΠΈΠΊΠ° Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΡ (Π³ΠΎΡΠΎΠ΄ΡΠΊΠΈΡ
Π°Π²ΡΠΎΠΌΠ°Π³ΠΈΡΡΡΠ°Π»Π΅ΠΉ, ΠΏΡΠΎΠΌΡΡΠ»Π΅Π½Π½ΡΡ
ΠΏΡΠ΅Π΄ΠΏΡΠΈΡΡΠΈΠΉ), Ρ ΠΊΠΎΠΌΠΏΠ»Π΅ΠΊΡΠΎΠΌ ΡΠ²ΠΎΠΉΡΡΠ² ΠΏΠΎΡΠ²Ρ, ΠΎΠ±ΡΡΠ»ΠΎΠ²Π»Π΅Π½Π½ΡΡ
Π΅Π΅ ΡΠΏΠ»ΠΎΡΠ½Π΅Π½ΠΈΠ΅ΠΌ ΠΏΡΠΈ ΠΈΠ½ΡΠ΅Π½ΡΠΈΠ²Π½ΠΎΠΉ ΡΠ΅ΠΊΡΠ΅Π°ΡΠΈΠΎΠ½Π½ΠΎΠΉ Π½Π°Π³ΡΡΠ·ΠΊΠ΅, Π° ΡΠ°ΠΊΠΆΠ΅ Ρ ΡΠΎΡΡΠ°Π²ΠΎΠΌ Π΄ΡΠ΅Π²Π΅ΡΠ½ΠΎ-ΠΊΡΡΡΠ°ΡΠ½ΠΈΠΊΠΎΠ²ΡΠΉ Π½Π°ΡΠ°ΠΆΠ΄Π΅Π½ΠΈΠΉ
ΠΠΎΡΠ²Π΅Π½Π½ΠΎ-ΡΠΊΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠ°Ρ Ρ Π°ΡΠ°ΠΊΡΠ΅ΡΠΈΡΡΠΈΠΊΠ° ΠΠ΅ΡΠ½ΠΎΠΉ ΠΎΠΏΡΡΠ½ΠΎΠΉ Π΄Π°ΡΠΈ Π ΠΠΠ£ - ΠΠ‘Π₯Π ΠΈΠΌ. Π.Π. Π’ΠΈΠΌΠΈΡΡΠ·Π΅Π²Π° ΠΏΠΎΠ΄ Π½Π°ΡΠ°ΠΆΠ΄Π΅Π½ΠΈΡΠΌΠΈ Π² ΡΡΠ»ΠΎΠ²ΠΈΡΡ ΡΠ°Π·Π»ΠΈΡΠ½ΠΎΠΉ Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π½ΠΎΠΉ Π½Π°Π³ΡΡΠ·ΠΊΠΈ
The heavy metals circulating in the biosphere have a huge negative impact on ecosystem components. At the same time however, the real danger from the environmental pollution by the heavy metals (HM) is constituted not by gross volume of metals, but by their mobile forms as the last practically define the accumulation of elements in biomass and influence the biological activity of soils. Meanwhile, the level study of this question is very weak. The influence of soil consolidation on HM mobility is almost not unknown. In this regard at wood sites with unequal anthropogenic loading we have conducted researches which have demonstrated the dependence of toxic heavy metals forms, diverse by durability of commu-nication, on the consolidation of soil. In many respects the density of soil profile defines the formation of the soil modes β water-air, temperature, oxidation-reduction, biochemical, and often makes decisive im-pact on demonstration of the soil main ecological functions, conditions of growth, development and efficien-cy of plants, microorganisms activity and soil fauna.Π’ΡΠΆΠ΅Π»ΡΠ΅ ΠΌΠ΅ΡΠ°Π»Π»Ρ, ΡΠΈΡΠΊΡΠ»ΠΈΡΡΡΡΠΈΠ΅ Π² Π±ΠΈΠΎΡΡΠ΅ΡΠ΅, ΠΎΠΊΠ°Π·ΡΠ²Π°ΡΡ ΠΎΠ³ΡΠΎΠΌΠ½ΠΎΠ΅ ΠΎΡΡΠΈΡΠ°ΡΠ΅Π»ΡΠ½ΠΎΠ΅ Π²Π»ΠΈΡΠ½ΠΈΠ΅ Π½Π° ΠΊΠΎΠΌΠΏΠΎΠ½Π΅Π½ΡΡ ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΡ. ΠΠ΄Π½Π°ΠΊΠΎ ΠΏΡΠΈ ΡΡΠΎΠΌ ΡΠ΅Π°Π»ΡΠ½ΡΡ ΠΎΠΏΠ°ΡΠ½ΠΎΡΡΡ Π·Π°Π³ΡΡΠ·Π½Π΅Π½ΠΈΡ ΠΎΠΊΡΡΠΆΠ°ΡΡΠ΅ΠΉ ΡΡΠ΅Π΄Ρ ΡΡΠΆΠ΅Π»ΡΠΌΠΈ ΠΌΠ΅ΡΠ°Π»Π»Π°ΠΌΠΈ (Π’Π) ΠΏΡΠ΅Π΄ΡΡΠ°Π²Π»ΡΡΡ Π½Π΅ Π²Π°Π»ΠΎΠ²ΡΠ΅ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΡ ΠΌΠ΅ΡΠ°Π»Π»ΠΎΠ², Π° ΠΈΡ
ΠΏΠΎΠ΄Π²ΠΈΠΆΠ½ΡΠ΅ ΡΠΎΡΠΌΡ, ΡΠ°ΠΊ ΠΊΠ°ΠΊ ΠΏΠΎΡΠ»Π΅Π΄Π½ΠΈΠ΅ ΠΏΡΠ°ΠΊΡΠΈΡΠ΅ΡΠΊΠΈ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΡΡ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΠ΅ ΡΠ»Π΅ΠΌΠ΅Π½ΡΠΎΠ² Π² ΡΠΈΡΠΎΠΌΠ°ΡΡΠ΅ ΠΈ Π²Π»ΠΈΡΡΡ Π½Π° Π±ΠΈΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΡΡ Π°ΠΊΡΠΈΠ²Π½ΠΎΡΡΡ ΠΏΠΎΡΠ². ΠΠ΅ΠΆΠ΄Ρ ΡΠ΅ΠΌ ΠΈΠ·ΡΡΠ΅Π½Π½ΠΎΡΡΡ ΡΡΠΎΠ³ΠΎ Π²ΠΎΠΏΡΠΎΡΠ° ΠΎΡΠ΅Π½Ρ ΡΠ»Π°Π±Π°Ρ. ΠΡΠ°ΠΊΡΠΈΡΠ΅ΡΠΊΠΈ Π½Π΅ ΠΈΠ·ΡΡΠ΅Π½Π½ΡΠΌ ΡΠ²Π»ΡΠ΅ΡΡΡ Π²Π»ΠΈΡΠ½ΠΈΠ΅ ΡΠΏΠ»ΠΎΡΠ½Π΅Π½ΠΈΡ ΠΏΠΎΡΠ²Ρ Π½Π° ΠΏΠΎΠ΄Π²ΠΈΠΆΠ½ΠΎΡΡΡ Π’Π. Π ΡΡΠΎΠΉ ΡΠ²ΡΠ·ΠΈ Π½Π° ΡΡΠ°ΡΡΠΊΠ°Ρ
Π»Π΅ΡΠ° Ρ Π½Π΅ΠΎΠ΄ΠΈΠ½Π°ΠΊΠΎΠ²ΠΎΠΉ Π°Π½ΡΡΠΎΠΏΠΎΠ³Π΅Π½Π½ΠΎΠΉ Π½Π°Π³ΡΡΠ·ΠΊΠΎΠΉ Π½Π°ΠΌΠΈ Π±ΡΠ»ΠΈ ΠΏΡΠΎΠ²Π΅Π΄Π΅Π½Ρ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ, ΠΊΠΎΡΠΎΡΡΠ΅ ΠΏΠΎΠΊΠ°Π·Π°Π»ΠΈ Π·Π°Π²ΠΈΡΠΈΠΌΠΎΡΡΡ ΡΠ°Π·Π»ΠΈΡΠ½ΡΡ
ΠΏΠΎ ΠΏΡΠΎΡΠ½ΠΎΡΡΠΈ ΡΠ²ΡΠ·ΠΈ ΡΠΎΡΠΌ ΡΠΎΠΊΡΠΈΡΠ½ΡΡ
ΡΡΠΆΠ΅Π»ΡΡ
ΠΌΠ΅ΡΠ°Π»Π»ΠΎΠ² ΠΎΡ ΡΠΏΠ»ΠΎΡΠ½Π΅Π½ΠΈΡ ΠΏΠΎΡΠ²Ρ. ΠΠ»ΠΎΡΠ½ΠΎΡΡΡ ΡΠ»ΠΎΠΆΠ΅Π½ΠΈΡ ΠΏΠΎΡΠ²Π΅Π½Π½ΠΎΠ³ΠΎ ΠΏΡΠΎΡΠΈΠ»Ρ Π²ΠΎ ΠΌΠ½ΠΎΠ³ΠΎΠΌ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΡΠ΅Ρ ΡΠΎΡΠΌΠΈΡΠΎΠ²Π°Π½ΠΈΠ΅ ΠΏΠΎΡΠ²Π΅Π½Π½ΡΡ
ΡΠ΅ΠΆΠΈΠΌΠΎΠ² - Π²ΠΎΠ΄Π½ΠΎ-Π²ΠΎΠ·Π΄ΡΡΠ½ΠΎΠ³ΠΎ, ΡΠ΅ΠΌΠΏΠ΅ΡΠ°ΡΡΡΠ½ΠΎΠ³ΠΎ, ΠΎΠΊΠΈΡΠ»ΠΈΡΠ΅Π»ΡΠ½ΠΎ-Π²ΠΎΡΡΡΠ°Π½ΠΎΠ²ΠΈΡΠ΅Π»ΡΠ½ΠΎΠ³ΠΎ, Π±ΠΈΠΎΡ
ΠΈΠΌΠΈΡΠ΅ΡΠΊΠΎΠ³ΠΎ ΠΈ ΠΎΠΊΠ°Π·ΡΠ²Π°Π΅Ρ ΡΠ°ΡΡΠΎ ΡΠ΅ΡΠ°ΡΡΠ΅Π΅ Π²Π»ΠΈΡΠ½ΠΈΠ΅ Π½Π° ΠΏΡΠΎΡΠ²Π»Π΅Π½ΠΈΠ΅ ΠΏΠΎΡΠ²Π΅Π½Π½ΡΡ
ΠΎΡΠ½ΠΎΠ²Π½ΡΡ
ΡΠΊΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΡΠ½ΠΊΡΠΈΠΉ, ΡΡΠ»ΠΎΠ²ΠΈΡ ΡΠΎΡΡΠ°, ΡΠ°Π·Π²ΠΈΡΠΈΡ ΠΈ ΠΏΡΠΎΠ΄ΡΠΊΡΠΈΠ²Π½ΠΎΡΡΡ ΡΠ°ΡΡΠ΅Π½ΠΈΠΉ, ΠΆΠΈΠ·Π½Π΅Π΄Π΅ΡΡΠ΅Π»ΡΠ½ΠΎΡΡΡ ΠΌΠΈΠΊΡΠΎΠΎΡΠ³Π°Π½ΠΈΠ·ΠΌΠΎΠ² ΠΈ ΠΏΠΎΡΠ²Π΅Π½Π½ΠΎΠΉ ΡΠ°ΡΠ½Ρ
ΠΠ΅Π³Π°ΠΏΠΎΠ»ΠΈΡΡ 2050: ΠΎΡ ΡΠ³ΡΠΎΠ· ΡΡΠ±Π°Π½ΠΈΠ·Π°ΡΠΈΠΈ ΠΊ ΡΡΡΠΎΠΉΡΠΈΠ²ΠΎΠΌΡ ΡΠ°Π·Π²ΠΈΡΠΈΡ Π³ΠΎΡΠΎΠ΄ΠΎΠ²
Urbanization is a global land-use change tendency, responsible for substantial environmental changes. At the same time urban ecosystems are vulnerable to global changes, and their adaptation is necessary to maintain sustainable functionality and important ecosystem services. Sustainable urban development demands for integration of innovative green technologies and natural-based solutions in urban management, which is only possible through a collaboration of scientists, landscape designers, civil engineers and policy-makers.Π£ΡΠ±Π°Π½ΠΈΠ·Π°ΡΠΈΡ - Π³Π»ΠΎΠ±Π°Π»ΡΠ½Π°Ρ ΡΠ΅Π½Π΄Π΅Π½ΡΠΈΡ ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΡ ΡΠΎΠ²ΡΠ΅ΠΌΠ΅Π½Π½ΠΎΠ³ΠΎ Π·Π΅ΠΌΠ»Π΅ΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ, ΡΡΠ½Π΄Π°ΠΌΠ΅Π½ΡΠ°Π»ΡΠ½ΠΎ ΠΈΠ·ΠΌΠ΅Π½ΡΡΡΠ°Ρ ΠΎΠΊΡΡΠΆΠ°ΡΡΡΡ ΡΡΠ΅Π΄Ρ. Π ΡΠ²ΠΎΡ ΠΎΡΠ΅ΡΠ΅Π΄Ρ, ΡΡΠ±ΠΎΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΡ ΠΏΠΎΠ΄Π²Π΅ΡΠΆΠ΅Π½Ρ Π²ΠΎΠ·Π΄Π΅ΠΉΡΡΠ²ΠΈΡ Π³Π»ΠΎΠ±Π°Π»ΡΠ½ΡΡ
(Π² ΡΠΎΠΌ ΡΠΈΡΠ»Π΅ ΠΊΠ»ΠΈΠΌΠ°ΡΠΈΡΠ΅ΡΠΊΠΈΡ
) ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΠΉ. ΠΠ΄Π°ΠΏΡΠ°ΡΠΈΡ Π³ΠΎΡΠΎΠ΄ΡΠΊΠΈΡ
ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌ ΠΊ Π³Π»ΠΎΠ±Π°Π»ΡΠ½ΡΠΌ ΠΈΠ·ΠΌΠ΅Π½Π΅Π½ΠΈΡΠΌ - Π½Π΅ΠΎΠ±Ρ
ΠΎΠ΄ΠΈΠΌΠΎΠ΅ ΡΡΠ»ΠΎΠ²ΠΈΠ΅ ΡΠΎΡ
ΡΠ°Π½Π΅Π½ΠΈΡ ΠΈΡ
ΡΡΡΠΎΠΉΡΠΈΠ²ΠΎΠ³ΠΎ ΡΡΠ½ΠΊΡΠΈΠΎΠ½ΠΈΡΠΎΠ²Π°Π½ΠΈΡ ΠΈ ΠΏΡΠ΅Π΄ΠΎΡΡΠ°Π²Π»ΡΠ΅ΠΌΡΡ
ΠΈΠΌΠΈ ΡΠΊΠΎΡΠΈΡΡΠ΅ΠΌΠ½ΡΡ
ΡΠ΅ΡΠ²ΠΈΡΠΎΠ². Π£ΡΡΠΎΠΉΡΠΈΠ²ΠΎΠ΅ ΡΠ°Π·Π²ΠΈΡΠΈΠ΅ Π³ΠΎΡΠΎΠ΄ΠΎΠ² ΠΏΠΎΠ΄ΡΠ°Π·ΡΠΌΠ΅Π²Π°Π΅Ρ Π²Π½Π΅Π΄ΡΠ΅Π½ΠΈΠ΅ ΡΠΎΠ²ΡΠ΅ΠΌΠ΅Π½Π½ΡΡ
ΡΠ΅Ρ
Π½ΠΎΠ»ΠΎΠ³ΠΈΠΉ Π·Π΅Π»Π΅Π½ΠΎΠ³ΠΎ ΡΡΡΠΎΠΈΡΠ΅Π»ΡΡΡΠ²Π° ΠΈ ΡΠ°ΡΠΈΠΎΠ½Π°Π»ΡΠ½ΠΎΠ³ΠΎ ΠΏΡΠΈΡΠΎΠ΄ΠΎΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ Π² ΡΠΈΡΡΠ΅ΠΌΡ Π³ΠΎΡΠΎΠ΄ΡΠΊΠΎΠ³ΠΎ ΠΌΠ΅Π½Π΅Π΄ΠΆΠΌΠ΅Π½ΡΠ°, ΡΡΠΎ Π΄ΠΎΡΡΠΈΠΆΠΈΠΌΠΎ ΡΠΎΠ»ΡΠΊΠΎ ΠΏΡΠΈ Π²Π·Π°ΠΈΠΌΠΎΠ΄Π΅ΠΉΡΡΠ²ΠΈΠΈ Π²ΡΠ΅Ρ
Π·Π°ΠΈΠ½ΡΠ΅ΡΠ΅ΡΠΎΠ²Π°Π½Π½ΡΡ
ΡΡΠΎΡΠΎΠ½, Π²ΠΊΠ»ΡΡΠ°Ρ Π½Π°ΡΡΠ½ΠΎΠ΅ ΡΠΎΠΎΠ±ΡΠ΅ΡΡΠ²ΠΎ, Π»Π°Π½Π΄ΡΠ°ΡΡΠ½ΡΡ
Π°ΡΡ
ΠΈΡΠ΅ΠΊΡΠΎΡΠΎΠ², ΠΈΠ½ΠΆΠ΅Π½Π΅ΡΠΎΠ²-Π³ΡΠ°Π΄ΠΎΡΡΡΠΎΠΈΡΠ΅Π»Π΅ΠΉ, Π³ΠΎΡΠΎΠ΄ΡΠΊΡΡ ΠΈ ΠΌΡΠ½ΠΈΡΠΈΠΏΠ°Π»ΡΠ½ΡΡ Π°Π΄ΠΌΠΈΠ½ΠΈΡΡΡΠ°ΡΠΈΡ
Analyzing Soil Metal Toxicity: Spiked or Field-Contaminated Soils?
[No abstract available
Microfungal community composition and alternaria phytotoxic effect in the lead polluted Urban soil
The present study is devoted to investigate the effect of high lead contamination on the soil microfungal composition of the urban forest. The investigation was performed for the urban forest soil contaminated by following concentrations of lead: 80, 800, 8,000 and 80,000Β ppm. The experiments revealed high resistances of Alternaria and Fusarium fungi to Pb contamination of urban soil. Simultaneously was determined the relatively low tolerance of soil Penicillium microfungi along lead concentration gradient (up 80 to 80,000Β ppm). Moreover, the phytotoxic effect of Alternaria microfungi cultivated on high-lead contaminated soil (80β8,000Β ppm) was assessed. Obtained results showed the significant impact of lead concentrations (>80Β ppm) on the phytotoxicity of Alternaria. Decrease in germination of pea seeds and average root growth was more than 85% in the high lead contaminated soils in comparison to the control sample. Β© Springer International Publishing AG, part of Springer Nature 2019
The effects of soil-ecological factors on the Pb migration in the soil of urban forest ecosystem
Leadisone of the most dangerous heavy metals for human. The studies of lead migration in the soil as are significantly important to forecast the transfer factors of lead in ecosystems. The paper represents data of lead concentration in dependence of the soil depth and degrees of anthropogenic impact. The research revealed influence of anthropogenic impact and species of arboreal vegetation on Pb migration in the soil profile. The results of lead concentration positively varyin the soil due to anthropogenic impact from 62.2 mg/kg to 139 mg/kg. The effect of arboreal vegetation species results in the high Pb migration down the soil profile in pine and birch sites and preferable accumulation of Pb in the upper humus horizon in the oak sites. Β© Springer International Publishing AG 2018
Environmental monitoring of sod-podzolic soils under the forest stands over one hundred year period: The case study at the forest experimental station in Moscow, Russia
This study of forest soil ecology conducted in the forest experimental station of the Russian State Agrarian University of Moscow Agricultural Academy reveals the evolution of a soil profile over a 100-year period influenced by a change from pine and spruce stands to two-tier mixed plantations of birch, maple, linden and oak. The rates of formation of the humus horizon and the reduction of the thickness of the podzolic horizon was determined by this change. Native pine tree growth enhances the podzol development process resulting in the development of an admixture of deciduous tree populations. This growth of hardwoods succeeding into the pine forest turn reduces the rate of accumulation of the upper horizon by 3 times. Humus horizon under these mixed stands was found to be the thickest in the locations, hardwood dominated. Comparison of the taxonomic properties with the soil characteristics will help in developing criteria for the vegetation stability and productivity in urban and suburban areas. This study reveals that the composition of tree species and their successions influences the main soil forming processes in the profile of sod-podzolic soil. The results of the study can be used to predict the soil-forming processes and the states of the forests. The ability to assess and predict these conditions is extremely important for soil-ecological monitoring in recreational forests for ecological landscape mapping. Β© Springer International Publishing AG 2018
Evaluation of connected clonal growth of Solidago chilensis as an avoidance mechanism in copper-polluted soils
Plant resistance to metals can be achieved by two strategies, tolerance and avoidance. Although metal tolerance has been broadly studied in terrestrial plants, avoidance has been less considered as a strategy to cope with soil metal pollution. Avoidance may be an effective alternative in herbaceous plants with connected clonal growth in environments having high heterogeneity in soil micro-spatial distribution of available metals and other soil conditions (i.e. organic matter). In this study, we performed a laboratory experiment on clonal growth of Solidago chilensis when exposed to copper-spiked soils (800 mg kgβ1) at different depths (0, 2, 5 and 8 cm depth), with (20%) and without addition of organic matter to mimic contrasting microhabitats found at smelter hinterlands (i.e. open bare ground and microhabitats below shrubs). Results showed that plants grown in the 2 cm-depth Cu-spiked soils were able to growth and produce ramets and rhizomes. However, increased Cu uptake of plants determined phytotoxic effects and a reduction in clonal spread in the 5 cm- and 8 cm-depth Cu-spiked soils. Addition of organic matter to the Cu-spiked soil layers allowed clonal spread. Considering that ramet and rhizome production is decreased but not inhibited when copper pollution is restricted to the uppermost soil layer (2 cm depth) and that organic matter eliminated soil copper toxicity allowing normal clonal spread, connected clonal growth may be an effective avoidance mechanism of Solidago chilensis, particularly in environments with high heterogeneity in micro-spatial distribution of metals and organic matter in the soil profile and between microhabitats. Β© 2019 Elsevier Lt