5 research outputs found
ΠΠ°ΡΠ°Π·ΠΈΡΡ Π΄Π°Π»ΡΠ½Π΅Π²ΠΎΡΡΠΎΡΠ½ΠΎΠ³ΠΎ Π»Π΅ΠΎΠΏΠ°ΡΠ΄Π° (Panthera pardus orientalis) Π½Π° ΡΠ³ΠΎ-Π·Π°ΠΏΠ°Π΄Π΅ ΠΡΠΈΠΌΠΎΡΡΠΊΠΎΠ³ΠΎ ΠΊΡΠ°Ρ Π ΠΎΡΡΠΈΠΈ
The results of long-term studies of invasions of the Panthera pardus orientalis, Schlegel 1857. The study of parasitic invasions of the Far Eastern leopard was carried out by two methods. The first method included the study of excrement of the Far Eastern leopard collected in different seasons of the year from January 2009 to December 2014 by the Kotelnikov-Khrenov method. The second method is a complete parasitologic autopsy on Scriabin, the dead animals on the basis of PGHS. The autopsy was conducted by the chief veterinarian of the Primorsky Krai, and the autopsy report was compiled. To analyze the data obtained, the indicator was used - the index of occurrence, expressed as a percentage. As a result, the species composition of helminths parasitizing the Far Eastern leopard is supplemented by species of nematodes - Ancylostoma sp., Gnathostoma spinigerum Capillaria sp., Dirofilaria sp; cestodes - Taenia sp., Dipylidium caninum, Spirometra erinaceieuropei, Mesocestoides lineatus; trematodes - Nanophyetus salmicola schikhobalowi, Clonorchis sinensis, Metagonimus yokogawa. Dominiruet monoinvasion (66,6%). Di-invasion and triinvasia are much less common - 17,7% and 4,4%. Of the protozoans, oocysts were found isospora rivolta. On the body of the dead animals were found ixodid mites - Haemaphysalis flava, Haemaphysalis longicornis, Haemaphysalis japonica douglasi, Haemaphysalis punctate. It indicates the presence in the excrement of fleas of genus Ctenocephala ΠΈ ΠΊΠ»Π΅ΡΠ΅ΠΉ ΡΠΎΠ΄Π° and mites of the genus Otodectes.Π¦Π΅Π»Ρ ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΡ - Π²ΡΡΠ²ΠΈΡΡ ΡΠΊΡΠΎ- ΠΈ ΡΠ½Π΄ΠΎΠΏΠ°ΡΠ°Π·ΠΈΡΠΎΠ² Π΄Π°Π»ΡΠ½Π΅Π²ΠΎΡΡΠΎΡΠ½ΠΎΠ³ΠΎ Π»Π΅ΠΎΠΏΠ°ΡΠ΄Π° (Panthera pardus orientalis, Schlegel 1857). ΠΠ°ΡΠ΅ΡΠΈΠ°Π»Ρ ΠΈ ΠΌΠ΅ΡΠΎΠ΄Ρ. ΠΠ·ΡΡΠ΅Π½ΠΈΠ΅ ΠΏΠ°ΡΠ°Π·ΠΈΡΠ°ΡΠ½ΡΡ
ΠΈΠ½Π²Π°Π·ΠΈΠΉ Π΄Π°Π»ΡΠ½Π΅Π²ΠΎΡΡΠΎΡΠ½ΠΎΠ³ΠΎ Π»Π΅ΠΎΠΏΠ°ΡΠ΄Π° ΠΏΡΠΎΠ²ΠΎΠ΄ΠΈΠ»ΠΈ Π΄Π²ΡΠΌΡ ΠΌΠ΅ΡΠΎΠ΄Π°ΠΌΠΈ. ΠΠ΅ΡΠ²ΡΠΉ ΠΌΠ΅ΡΠΎΠ΄ Π²ΠΊΠ»ΡΡΠ°Π» ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΠ΅ ΡΠ΅ΠΊΠ°Π»ΠΈΠΉ Π΄Π°Π»ΡΠ½Π΅Π²ΠΎΡΡΠΎΡΠ½ΠΎΠ³ΠΎ Π»Π΅ΠΎΠΏΠ°ΡΠ΄Π°, ΡΠΎΠ±ΡΠ°Π½Π½ΡΡ
Π² ΡΠ°Π·Π½ΡΠ΅ ΡΠ΅Π·ΠΎΠ½Ρ Π³ΠΎΠ΄Π° Ρ ΡΠ½Π²Π°ΡΡ 2009 Π³. ΠΏΠΎ Π΄Π΅ΠΊΠ°Π±ΡΡ 2014 Π³. ΠΌΠ΅ΡΠΎΠ΄ΠΎΠΌ ΠΠΎΡΠ΅Π»ΡΠ½ΠΈΠΊΠΎΠ²Π°-Π₯ΡΠ΅Π½ΠΎΠ²Π°. ΠΡΠΎΡΠΎΠΉ ΠΌΠ΅ΡΠΎΠ΄ Π²ΠΊΠ»ΡΡΠ°Π» ΠΏΠΎΠ»Π½ΠΎΠ΅ Π³Π΅Π»ΡΠΌΠΈΠ½ΡΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΎΠ΅ Π²ΡΠΊΡΡΡΠΈΠ΅ ΠΏΠΎ Π‘ΠΊΡΡΠ±ΠΈΠ½Ρ ΠΏΠΎΠ³ΠΈΠ±ΡΠΈΡ
ΠΆΠΈΠ²ΠΎΡΠ½ΡΡ
Π½Π° Π±Π°Π·Π΅ ΠΡΠΈΠΌΠΎΡΡΠΊΠΎΠΉ Π³ΠΎΡΡΠ΄Π°ΡΡΡΠ²Π΅Π½Π½ΠΎΠΉ ΡΠ΅Π»ΡΡΠΊΠΎΡ
ΠΎΠ·ΡΠΉΡΡΠ²Π΅Π½Π½ΠΎΠΉ Π°ΠΊΠ°Π΄Π΅ΠΌΠΈΠΈ. ΠΡΠΊΡΡΡΠΈΠ΅ ΠΏΡΠΎΠ²ΠΎΠ΄ΠΈΠ»ΠΈ Π³Π»Π°Π²Π½ΡΠΌ Π²Π΅ΡΠ΅ΡΠΈΠ½Π°ΡΠ½ΡΠΌ Π²ΡΠ°ΡΠΎΠΌ ΠΡΠΈΠΌΠΎΡΡΠΊΠΎΠ³ΠΎ ΠΊΡΠ°Ρ; ΡΠΎΡΡΠ°Π²Π»Π΅Π½ ΠΏΡΠΎΡΠΎΠΊΠΎΠ» Π²ΡΠΊΡΡΡΠΈΡ. Π‘ΠΎΠ±ΡΠ°Π½Π½ΡΡ
ΠΏΠ°ΡΠ°Π·ΠΈΡΠΎΠ² ΡΠΈΠΊΡΠΈΡΠΎΠ²Π°Π»ΠΈ ΠΈ ΠΎΠ±ΡΠ°Π±Π°ΡΡΠ²Π°Π»ΠΈ ΡΡΠ°Π½Π΄Π°ΡΡΠ½ΡΠΌΠΈ ΠΌΠ΅ΡΠΎΠ΄ΠΈΠΊΠ°ΠΌΠΈ. ΠΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΠ΅ Π²ΠΈΠ΄Π° ΠΊΠ»Π΅ΡΠ΅ΠΉ ΠΏΡΠΎΠ²ΠΎΠ΄ΠΈΠ»ΠΈ ΠΏΠΎ ΠΎΠΏΡΠ΅Π΄Π΅Π»ΠΈΡΠ΅Π»Ρ Π. A. Π€ΠΈΠ»ΠΈΠΏΠΏΠΎΠ²ΠΎΠΉ (1997). ΠΠ»Ρ Π°Π½Π°Π»ΠΈΠ·Π° ΠΏΠΎΠ»ΡΡΠ΅Π½Π½ΡΡ
Π΄Π°Π½Π½ΡΡ
ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π»ΠΈ ΠΏΠΎΠΊΠ°Π·Π°ΡΠ΅Π»Ρ - ΠΈΠ½Π΄Π΅ΠΊΡ Π²ΡΡΡΠ΅ΡΠ°Π΅ΠΌΠΎΡΡΠΈ, Π²ΡΡΠ°ΠΆΠ΅Π½Π½ΡΠΉ Π² ΠΏΡΠΎΡΠ΅Π½ΡΠ°Ρ
. Π Π΅Π·ΡΠ»ΡΡΠ°ΡΡ ΠΈ ΠΎΠ±ΡΡΠΆΠ΄Π΅Π½ΠΈΠ΅. ΠΠΈΠ΄ΠΎΠ²ΠΎΠΉ ΡΠΎΡΡΠ°Π² Π³Π΅Π»ΡΠΌΠΈΠ½ΡΠΎΠ², ΠΏΠ°ΡΠ°Π·ΠΈΡΠΈΡΡΡΡΠΈΡ
Ρ Π΄Π°Π»ΡΠ½Π΅Π²ΠΎΡΡΠΎΡΠ½ΠΎΠ³ΠΎ Π»Π΅ΠΎΠΏΠ°ΡΠ΄Π°, Π΄ΠΎΠΏΠΎΠ»Π½Π΅Π½ Π²ΠΈΠ΄Π°ΠΌΠΈ Π½Π΅ΠΌΠ°ΡΠΎΠ΄ - Ancylostoma sp., Gnathostoma spinigerum, Capillaria sp., Dirofilaria sp; ΡΠ΅ΡΡΠΎΠ΄ - Taenia sp., Dipylidium caninum, Spirometra erinaceieuropei, Mesocestoides lineatus; ΡΡΠ΅ΠΌΠ°ΡΠΎΠ΄ - Nanophyetus salmicola schikhobalowi, Clonorchis sinensis, Metagonimus yokogawa. ΠΠΎΠΌΠΈΠ½ΠΈΡΡΠ΅Ρ ΠΌΠΎΠ½ΠΎΠΈΠ½Π²Π°Π·ΠΈΡ (66,6 %). ΠΠΈΠΈΠΈΠ½Π²Π°Π·ΠΈΡ ΠΈ ΡΡΠΈΠΈΠ½Π²Π°Π·ΠΈΡ Π½Π°Π±Π»ΡΠ΄Π°ΡΡΡΡ Π³ΠΎΡΠ°Π·Π΄ΠΎ ΡΠ΅ΠΆΠ΅ - 17,7 ΠΈ 4,4 % ΡΠΎΠΎΡΠ²Π΅ΡΡΡΠ²Π΅Π½Π½ΠΎ. ΠΠ· ΠΏΡΠΎΡΡΠ΅ΠΉΡΠΈΡ
Π±ΡΠ»ΠΈ ΠΎΠ±Π½Π°ΡΡΠΆΠ΅Π½Ρ ΠΎΠΎΡΠΈΡΡΡ Isospora rivolta. ΠΠ° ΡΠ΅Π»Π΅ ΠΏΠΎΠ³ΠΈΠ±ΡΠΈΡ
ΠΆΠΈΠ²ΠΎΡΠ½ΡΡ
Π±ΡΠ»ΠΈ Π½Π°ΠΉΠ΄Π΅Π½Ρ ΠΈΠΊΡΠΎΠ΄ΠΎΠ²ΡΠ΅ ΠΊΠ»Π΅ΡΠΈ Haemaphysalis flava, H. longicornis, H. japonica douglasi, H. punctate. Π£ΠΊΠ°Π·ΡΠ²Π°Π΅ΡΡΡ Π½Π° Π½Π°Ρ
ΠΎΠΆΠ΄Π΅Π½ΠΈΠ΅ Π² ΡΠ΅ΠΊΠ°Π»ΠΈΡΡ
Π±Π»ΠΎΡ
ΡΠΎΠ΄Π° Ctenocephala ΠΈ ΠΊΠ»Π΅ΡΠ΅ΠΉ ΡΠΎΠ΄Π° Πtodectes
Invasion diseases of the far eastern leopard (Panthera pardus orientalis) in the south-west of the Primorsk territory of Russia
The results of long-term studies of invasions of the Panthera pardus orientalis, Schlegel 1857. The study of parasitic invasions of the Far Eastern leopard was carried out by two methods. The first method included the study of excrement of the Far Eastern leopard collected in different seasons of the year from January 2009 to December 2014 by the Kotelnikov-Khrenov method. The second method is a complete parasitologic autopsy on Scriabin, the dead animals on the basis of PGHS. The autopsy was conducted by the chief veterinarian of the Primorsky Krai, and the autopsy report was compiled. To analyze the data obtained, the indicator was used - the index of occurrence, expressed as a percentage. As a result, the species composition of helminths parasitizing the Far Eastern leopard is supplemented by species of nematodes - Ancylostoma sp., Gnathostoma spinigerum Capillaria sp., Dirofilaria sp; cestodes - Taenia sp., Dipylidium caninum, Spirometra erinaceieuropei, Mesocestoides lineatus; trematodes - Nanophyetus salmicola schikhobalowi, Clonorchis sinensis, Metagonimus yokogawa. Dominiruet monoinvasion (66,6%). Di-invasion and triinvasia are much less common - 17,7% and 4,4%. Of the protozoans, oocysts were found isospora rivolta. On the body of the dead animals were found ixodid mites - Haemaphysalis flava, Haemaphysalis longicornis, Haemaphysalis japonica douglasi, Haemaphysalis punctate. It indicates the presence in the excrement of fleas of genus Ctenocephala ΠΈ ΠΊΠ»Π΅ΡΠ΅ΠΉ ΡΠΎΠ΄Π° and mites of the genus Otodectes
High Doses of Pesticides Induce mtDNA Damage in Intact Mitochondria of Potato In Vitro and Do Not Impact on mtDNA Integrity of Mitochondria of Shoots and Tubers under In Vivo Exposure
It is well known that pesticides are toxic for mitochondria of animals. The effect of pesticides on plant mitochondria has not been widely studied. The goal of this research is to study the impact of metribuzin and imidacloprid on the amount of damage in the mtDNA of potato (Solanum tuberosum L.) in various conditions. We developed a set of primers to estimate mtDNA damage for the fragments in three chromosomes of potato mitogenome. We showed that both metribuzin and imidacloprid considerably damage mtDNA in vitro. Imidacloprid reduces the rate of seed germination, but does not impact the rate of the growth and number of mtDNA damage in the potato shoots. Field experiments show that pesticide exposure does not induce change in aconitate hydratase activity, and can cause a decrease in the rate of H2O2 production. We can assume that the mechanism of pesticide-induced mtDNA damage in vitro is not associated with H2O2 production, and pesticides as electrophilic substances directly interact with mtDNA. The effect of pesticides on the integrity of mtDNA in green parts of plants and in crop tubers is insignificant. In general, plant mtDNA is resistant to pesticide exposure in vivo, probably due to the presence of non-coupled respiratory systems in plant mitochondria