Wednesday, 12 February 2020

Effect of Interaction Between Ag Nanoparticles and Salinity on Germination Stages of Lathyrus Sativus L.

Lupine publishers|Effect of Interaction Between Ag Nanoparticles and Salinity on Germination Stages of Lathyrus Sativus L.

 Lupine publishers|Earth and environment journals

Abstract


The aim of the study was to effect of interaction between Ag nanoparticles and salinity on Germination Stages of Lathyrus Sativus L. Treatments included in the study were viz. To 3 levels of salinity (0 as control, 8 and 16 dS/m NaCl), 8 and 16 dS/m and four levels of silver nanoparticles (0, 5, 10 and 15 ppm) on grass pea seed were tested. An experiment was conducted to evaluate the effects of silver nanoparticles (AgNPs), on the seed germination factors, root and shoot length (RL and SL) and proline content of grass pea Survival under Salinity Levels. Results showed a significant reduction in growth and development indices due to the salinity stress. The salt stress impaired the germination factors of grass pea seedlings. The application of Ag in combination improved the germination percentage, shoot and root length, seedling fresh weight and seedling dry weight and seedling dry contents of grass pea seedlings under stressed conditions. The results suggest that Ag nanoparticles enhancement may be important for osmotic adjustment in grass pea under salinity stress and application of Ag mitigated the adverse effect of salinity and toxic effects of salinity stress on grass pea seedlings.
Keywords: Ag nanoparticles; Salinity; Germination Stages; Grass Pea; Lathyrus Sativus L.

Introduction

High salinity is a common abiotic stress factor that causes a significant reduction in growth. Germination and seedling growth are reduced in saline soils with varying responses for species and cultivars [1]. Soil saltiness may impact the germination of seeds either by causing an osmotic potential outside to the seed averting water uptake, or the poisonous effects of Na+ and Cl− ions on germinating seed [2]. Salt and osmotic stresses are responsible for both inhibition or delayed seed germination and seedling establishment [3]. The majority of our present-day crops are adversely affected by salinity stress [4]. NaCl causes extensive oxidative damage in different legumes, resulting in significant reduction of different growth parameters, seed nutritional quality, and nodulation [5,6]. To mitigate and repair damages triggered by oxidative stress, plants evolved a series of both enzymatic as well as a non-enzymatic antioxidant defense mechanism. Ascorbate and carotenoids are two important non-enzymatic defenses against salinity, whereas proline is the most debated osmoregulatory substances under stress [7].
Lathyrus Sativus L. (Grass pea) is an annual pulse crop belonging to the Fabaceae family and Vicieae tribe [8]. Grass pea has a long history in agriculture. The crop is an excellent fodder with its reliable yield and high protein content. This plant is also commonly grown for animal feed and as forage. The grass pea is endowed with many properties that combine to make it an attractive food crop in drought-stricken, rain-fed areas where soil quality is poor and extreme environmental conditions prevail [9]. Despite its tolerance to drought it is not affected by excessive rainfall and can be grown on land subject to flooding [10,11]. Compared to other legumes, it is also resistant to many insect pests [12-15]. Nanoparticles (NPs) are wide class of materials that include particulate substances, which have one dimension less than 100 nm at least [16]. The importance of these materials realized when researchers found that size can influence the physiochemical properties of a substance e.g. the optical properties [17]. NPs with different composition, size, and concentration, physical/ chemical properties have been reported to influence growth and development of various plant species with both positive and negative effects [18]. Silver nanoparticles have been implicated in agriculture for improving crops. There are many reports indicating that appropriate concentrations of AgNPs play an important role in plant growth [19,20]. The application of Nano silver during germination process may enhance germination traits, plant growth and resistance to salinity conditions in basil seedlings [21]. The use of Silver Nanoparticle on Fenugreek Seed Germination under Salinity Levels is a recent practice studied [22]. Nanomaterials have also been used for various fundamental and practical applications [23]. Although the potential of AgNPs in improving salinity resistance has been reported in several plant species [24,25], its role in the alleviation of salinity effect and related mechanisms is still unknown. Therefore, the main objective of this work was to study the effect of Silver Nanoparticles on salt tolerance in Lathyrus Sativus L.

Material and Methods

In order to investigate salinity stress on Lathyrus Sativus L. germination indices, an experiment was carried out in Iran from April to Juan 2017 at Ferdowsi University of Mashhad, to creation salinity, sodium chloride at the levels of 8 dS/m, 15 dS/m and 0 (as control), four levels of silver nanoparticles (0, 5, 10 and 15 ppm) on Grass pea were tested. The Ag NPs were obtained from US Research Nanomaterial’s, Inc. Transmission electron microscopy (ТЕМ) images of silver nanoparticles with diameters of 20 nm, shown in Figure 1. Seeds of Lathyrus Sativus L. where from seed bank of Research Center for Plant Sciences, Ferdowsi University of Mashhad. These all were washed with deionized water. Seeds were sterilized in a 5% sodium hypochlorite solution for 10 minutes [26], rinsed through with deionized water several times. Their germination was conducted on water porous paper support in Petri dishes (25 seed per dish) at the controlled temperature of 25 ± 1°C. After labeling the Petri dishes, seed were established between two Whatman No. 2 in Petri dishes. Silver nanoparticles in different concentration silver nanoparticles (0, 5, 10 and 15ppm) were prepared directly in deionized water and dispersed by ultrasonic vibration for one hour. Each concentration was prepared in three replicates. Every other day supply with 0.5 ml silver nanoparticles per every test plantlet was carried out for 21 days along with control. Germination counts were recorded at 2 days’ intervals for 21 days after sowing and the seedlings were allowed to grow. The germination percentages of the seeds were finally determined for each of the treatments. After 21 days of growth, the shoot and root lengths were long enough to measure using a ruler. The controlled sets for germinations were also carried out at the same time along with treated seeds (Figure 2).
Figure 1: Silver Nanopowder, Coated with ~0.2wt% PVP (Poly Viny Pyrrolidone) surfactant for low oxygen content and easy dispersing. True density: 10.5 g/cm3 Purity: 99.99% APS: 20 nm SSA: ~18-22 m2/g Color: black, Morphology: spherical.
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Figure 2: Effect of Ag Nanoparticles on Germination Stages of Lathyrus Sativus L. in Salinity level( 8 dS/m NaCl).
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Parameters Measured in this Study were:

A. Germination Stages
Total germination percentage (GT) was calculated as Gt = (n/N ×100), where n = total number of germinated seeds (normal and abnormal) at the end of the experiment and N = total number of seeds used for the germination test.
B. Germination Speed Index (GSI)
Conducted concomitantly with the germination test, with a daily calculation of the number of seeds that presented protrusion of primary root with length ≥2 millimeter, continuously at the same time amid the trial. The germination speed index was calculated by Maguire formula [27]: aguire formula (1962):

Where:
GSI = seedlings’ germination speed index;
G = number of seeds germinated each day;
N = number of days elapsed from the seeding until the last count.

Root and Shoot Length

Root length was taken from the point below the hypocotyls to the end of the tip of the root. Shoot length was measured from the base of the root- hypocotyl transition zone up to the base of the cotyledons. The root and shoot length were measured with the help of a thread and scale.

Seedling Vigour Index

The seedling vigor index was determined by using the formula given by Abdul baki and Anderson [28].

Fresh and Dry mass

The fresh mass was quantified through weighing on precision scale, and the dry mass was determined through weighing on a precision scale after permanence of the material in a kiln with air forced circulation, at a temperature of 70°C, until indelible weight. At the ending of the experiment, At the end of the experiment, radical and plumule length and fresh weight measured. Plants were placed in the oven at 70°C for 48 h and weighted with sensitive scale.

Proline Contents

Proline was determined spectrophotometrically following the ninhydrin method described, using L-proline as a standard [29]. Approximately 300 mg of dry tissue was homogenized in 10ml of 3% (w/v) aqueous sulphosalicylic acid and filtered. To 2ml of the filtrate, 2ml of acid ninhydrin was added, followed by the addition of 2ml of glacial acetic acid and boiling for 60 min. The mixture was extracted with toluene, and the free proline was quantified spectrophotometrically at 520nm from the organic phase using a spectrophotometer. Statistical analysis each treatment was conducted, and the results were presented as mean ± SD (standard deviation). The results were analyzed by one-way ANOVA with used Minitab Version 16.

Results and Discussion

The present study showed clearly that salinity had a negative effect on the yield and its components of grass pea. It is well known that seed germination provides a suitable foundation for plant growth, development, and yield [30]. Increased salt concentration caused a decrease in germination percent (Table 1). Seed germination decreased as the doses increased. The Strong reduction in germination (-47%) was observed mainly at the highest level of salt concentration as compared to control treatment. Delayed germination causes increased irrigation cost and irregular and weak seedling growth in the establishment of legume crops. Relevant results were reported by Gunjaca and Sarcevic [31] and Almansouri et al. [32]. They reported that increasing osmotic potential decreased water uptake and slow down germination time. The average time of germination increases with increasing levels of salinity. In view of mean germination time, there was a considerable increase in this character at 0 (as control), 8 and 16 DS/m salinity levels as compared to the others. Emergence was significantly affected by salinity levels. Moreover, many researchers have reported developmental delay of seed germination at high salinity [33]. The germination rate decreased as salt concentration increased to a 16 dS/m and delayed for the high salt dosage (Table 1). Since higher salinity limited water absorption, it has prevented nutrient assimilation, as a result, germination rate declined with increasing salinity. The findings from this study were like to the findings of Kaydan and Yagmur [34] and Akhtar and Hussain [35].
Table 1: The interaction effect of NaCl and AgNPs on Germination Speed Index.
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Table 2: Analysis of variance of the measured traits.
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Shoot fresh weight was significantly influenced (P<0.05) by salinity levels. The highest shoot fresh weight was obtained from 0dSm salinity level while the lowest weight was at 16dSm. Shoot fresh weight significantly decreased as salinity level increased above 8dSm (Table 2). Salinity stress significantly (P<0.05) affected shoot dry weight as the salt concentration dosage increased. Shoot dry weight significantly decreased in salt levels over 8dSm. When the salinity level was raised above, the proline content increased in grass pea. Culturing excised roots has demonstrated to be a really great test show for the early detection of tolerance to abiotic stresses such as saltiness [36-38].
Proline was studied in numerous works dealing with plant selection against abiotic stresses such as dry and salinity [39,40], and it may play a defensive part against the osmotic potential produced by salt [41,42]. The proline substance of the expanded with the NaCl concentration of the culture medium. At 16 dS/m NaCl, the proline concentration appeared a huge increment in reaction to salt stress, although the activity of the roots at this concentration was negligible, with no grateful longitudinal development. Proline, which happens broadly in higher plants and collects in bigger sums than other amino acids [43], regulates the aggregation of useable N. Proline collection normally occurs within the cytosol where it contributes significantly to the cytoplasmic osmotic alteration [44]. It is osmotically very active and contributes to membrane stability and mitigates the impact of on NaCl cell membrane disturbance [45]. In the present experiment application of Ag NPs enhanced seed potential by increasing the characteristics of seed germination (Tables 1 & 2). The results showed that the impact of Ag NPs was significant on germination percentage in P≤0. 05. The results about of this test appeared that utilization of Ag NPs nanoparticles can increment the germination in grass pea. Seed germination results indicate that Ag Nanoparticles at their lower concentrations advanced seed germination and early seedling growth in grass pea, anyway at higher concentration showed slight antagonistic impacts. Parameters of seed germination were expanded with increasing levels of Ag NPs up to 10 ppm. Among the treatments, application of 10 ppm of Ag NPs proved best by giving the highest values for percent seed germination, germination rate and germination mean time. It is well watched that the exogenous application of Ag NPs decreased the reduction of germination resulted from salt treatments. In the interim, the control treatments of salt and Ag nanoparticles gave the tallest plants contrasted with the other studied treatments. Darvishzadeh et al. [21] found that the utilization of Ag Nano particles at the concentration of 40 mg.kg-1 prompted the increases in germination percentage and improved the resistance to salinity conditions in basil. The proline content increased with increasing severity of salinity stress. Additionally, proline content significantly (P.0.01) increased when silver nanoparticles were applied in connected in serious saline stress in comparison without silver nanoparticles (Figure 3).
Figure 3: Effect of interaction between ag nanoparticles and salinity on germination stages of Lathyrus Sativus L. a - Main effects plot for Root length (mm); b - Main effects plot for dry weight of shoot and root (gr); c - Interaction Plot for fresh weight of shoot and root (gr); d - Interaction Plot for dry weight of shoot and root (gr); e - Interaction Plot for Proline (mg/gr).
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Conclusion

Salt stress through enhancement of osmotic pressure leads to the decrease of germination percentage, germination rate, germination index and an increment in mean germination time of Lathyrus sativus seeds. For overcoming the negative impacts of salinity on the plant growth and yield can be to attempt to new strategies. The dry and fresh weight of seedlings diminished as seedling length declined with increasing salinity levels since root number, shoot number, root length and shoot length decreased essentially. Results demonstrate that Ag NPs at lower concentration enhances seed germination, promptness index, and seedling growth. The positive effect of Ag on physiological properties was in conditions that the plant grew under salt stress was more increasingly exceptional in examination with the conditions that plant grown under normal conditions. The results of this study showed that Ag can be involved in the metabolic or physiological activity in higher plants exposed to abiotic stresses.

Acknowledgment

I would like to thank the Research Center for Plant Sciences, and Dr. Jafar Nabati for providing the necessary facilities.

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Friday, 7 February 2020

Green Revolution as Technological Fix to Agricultural Development

Lupine publishers|Green Revolution as Technological Fix to Agricultural Development
 Lupine publishers|Environmental science

Abstract

The beginning of Human being’s effort to meet the need for food production in parallel with the increasing number of population and environmental deterioration is lost in time. One of such known effort was green revolution which started in 1968 in order to revolutionize agricultural sectors through the utilization of modern technologies. Since agriculture is the fundamental source of livelihood for the majority of human population especially in developing countries, it will always be helpful to study any agricultural aspects to take lessons from it. Accordingly, this review article tries to study the historical, implementation and shortcoming of green revolution. The study only used secondary data materials.
Keywords:Saline agrolandscape; Catena; Macro and microelements; Sanitary and hygienic conditions

Introduction

Over centuries, Owing to some natural factors or unnatural (human-made) factors different societies across the world were encountered significant decrease in food production eventually leading into chronic food shortage that affected the life of millions of peoples and also resulted in death of large number of human individuals. In one way or another there have been responses from the people to deal with the problem of hunger at different time. As such, the so called “Green Revolution” is a technological response into the world-wide hunger that took place after Second World War. It was a great movement characterized by introduction of agricultural technology from developed nation in to developing countries with the intension of replacing traditional agricultural techniques with improved modern techniques so as to increase food production output and subsequently to put to an end the problem of food shortage. This review paper tries to analyze Green Revolution and then to discuss its historical development, implementation and failure. It will be dealt as follows.

Definition

The term green revolution was first used in 1968 by William Gaud the former director of United States Agency for International Development (USAID) to describe agricultural policy that has been adopted to deal with the world-wide hunger after Second World War. This policy was termed as green revolution because, it was characterized by great movement toward increasing agricultural output so as to meet the argent need for food production, that were exacerbated by population growth, whilst making intensive use of agricultural technologies that has been devised over centuries by developed nations mainly in United State and western European countries [1]. Green revolution is the extension of earlier agricultural revolution that was under taken in different nation such as France and England (David B. Grigg). But, the unique manifestation of green revolution in relation to the earlier phase of agricultural revolution was its intensive use of improved agricultural technology specially that of high yielding varieties (HYVs) that is adoptive to different changing condition. So, Green Revolution is a term used for rapid increases in wheat and rice yields in developing countries brought about by improved varieties combined with the expanded use of fertilizers and other chemical inputs that has had a dramatic impact on incomes and food supplies in many developing countries [2].

Historical Back Ground

Green revolution was a giant movement that took place the period after Second World War mainly between 1940s and 1960s. This movement was initially coming at the request of Mexican government to establish agricultural research station to develop more varieties of wheat. As it was also true for many other nations of the world, in 1940 Mexico needed high food production that could be used to feed the rapidly growing population of the country [3-5]. To this account, the Rock Feller Organization in cooperation with Mexican government created Office of Special Studies within the Mexican Department of Agriculture. One of the pioneers in this effort was the plant pathologist Norman Borlaug who won the Nobel Peace Prize for his green revolution work in 1970. He was often regarded as the Father of Green Revolution. The overall agricultural endeavor by Rock Feller Organization in Mexico were succeeded in engineering better seeds that was resulted in increased agricultural output to greater amount. News of this cooperative undertaking and agricultural improvement in Mexico Spread rapidly to other countries in Latin America and Asian countries. Eventually, inquiries to invite rock feller for collaboration began to come from other Latin American and Asian countries like India, Pakistan, Bangladesh, Indonesia and China and parts of Africa [7-9].
In 1957, the Rock Feller Foundation started its agricultural program in India and three years later the Rock Feller Foundation and Ford Foundation jointly created the International Rice Research Institute (IRRI) at Los Banos in the Pmhiliphins to find a rice as miraculous as the Pitic 62 and Penjamo 62 wheats, rice being at that time the main item of diet for six out of every ten people in the world. They were succeede in developing HYVs specially IR8-rice that was termed miracle seed [10].

Implementation of Green-Revolution

The initial aim of green revolution was to eradicate famine that has had deteriorated the well-being of many developing nation across the world. The plan was to maximize agricultural output because, as per the assumption of green revolution, once agricultural output has increased it will put to an end the hunger problem. So as to increase agricultural output, traditional agriculture must be replaced by modernized agriculture that makes intensive use of technology. This encompasses the use of hybrid seed, fertilizers, herbicides and pesticide, irrigation system etc. with such transformation in the agricultural sector, green revolution promised to eradicate famine. In account of this, the first practical implementation of green revolution had taken place in Mexico in 1940, funded by Rock Feller Organization. After intensive research, the team has succeeded in developing hybrid seed of wheat, maize etc. that could give high yields. The developed hybrid seed was cultivated and resulted in the increased output. Accordingly, Mexico become the first country to testify the result of green revolution. In 1943 Mexico imported half of its wheat; in 1956, the green revolution made Mexico self-sufficient; by 1964, Mexico started to export wheat. The improvement of agricultural output in Mexico attracted attention from many developing nations mainly from Asia [11].
In 1960 Philippines in collaboration with Ford Foundation and Rock Feller Foundation established International Rice Research Institute (IRRI). A rice crossing between Dee-geo-woo-gen and Peta was done at IRRI in 1962. In 1966, one of the breeding lines became a new cultivar, IR8. IR8 required the use of fertilizers and pesticides but produced substantially higher yields than the traditional cultivars. Annual rice production in the Philippines increased from 3.7 to 7.7 million tons in two decades. The switch to IR8 rice made the Philippines a rice exporter for the first time in the 20th century. At the same time, heavy pesticide use reduced the number of fish and frog species found in rice paddies [12].
In 1961, India was on the brink of mass famine. Being impressed by the agricultural transformation that Mexico had under gone, India invited the green revolution to assure food security for its rapidly growing population. To this effort, green revolution was first introduced into parts of India with the collaboration of Rock Feller Organization. Later on, India began its own green revolution program of plant breeding, irrigation development and financing of agro-chemical. India also adopted IR8, a rice semi-dwarf variety developed by the IRRI that could give more grains of rice per plant when grown properly with fertilizer and irrigation. This IR8 rice variety was success through Asia and termed as miracle rice. India become one of the world’s most successful rice producers and is now a major rice exporter [13].
There have been numerous attempts to introduce the successful concepts from the Mexican and Indian projects into Africa. These programs have generally been less successful, for a number of reasons. Reasons cited include widespread corruption, insecurity, a lack of infrastructure, and a general lack of will on the part of the governments. Yet environmental factors, such as the availability of water for irrigation, the high diversity in slope and soil types in one given area are also reasons why the Green Revolution is not so successful in Africa.

The Short Coming of Green-Revolution

Besides maximizing food production, Green revolution was not as such successful as it was expected to be. This could be ascribed to many reasons. First and for most, green revolution was one directional- it only considers the increase in food production as the sole solution to eradicate hunger. For many farmers the cost of machinery was too much, and they couldn’t afford it. Many very poor farmers were tenant farmers, with little money to buy even the new seeds or fertilizer. Dam construction in some areas resulted in the flooding of some good farming land. The large amounts of fertilizers and pesticides required by HYVs also led to serious environmental problems as they inter water supplies. Areas where there was an increase in mechanization, there was an increase in unemployment fewer people needed to do the job this led in rural-urban migration with more people moving to the city causing urban problem. Many farmers who had tried to take on the new technologies became heavily in debt. These and other long-term problems made green revolution ineffective [14].

Conclusion

Generally, Green Revolution was a movement that started after Second World War as response to world-wide hunger. The main aim of this revolution was to increase agricultural output by intensive use of modernized agricultural technology specially by using hybrid seed supplemented by mechanical and bio-chemical technologies. This revolution was succeeded in increasing food production by innovating HYVs of different cereals but, at its first stage it was mainly contributed to wheat, maize, rice and later on its contribution extended into other cereals. With its first move in Mexico, green revolution introduced into other parts of Latin America, Asia and also some parts of Africa. However, green revolution was mainly implemented in Asia than any other countries. And this revolution was not that much succeeded in eradicating poverty as it was first promised to do so. It also brought about many problems that accounts to its failure.


Friday, 1 November 2019

Lupine Publishers | The Role of Photoperiodic and Climatic Conditions in the Formation of Bird Biodiversity in Northern Eurasia


Lupine Publishers- Environmental and Soil Science Journal



Abstract

The southern limits of the distribution of the Snow Bunting Plectrophenax nivalis in Eurasia are determined by the light regime of the region - outside the zone of the polar day the birds will not come to a state of sexual activity. Northern limits of the range of Snow Bunting in the modern climate of the Arctic is not. The limits of Penetration to the North of the Horned Lark Eremophila alpestris glasses are determined by a set of biotopic, fodder and temperature minima, allowing to penetrate into the Arctic, but not to master most of it. The southern limits of distribution of the Red-throated Pipit Anthus cervinus are limited by the zone of the polar day defining maturation of gonads, mountain tundras of the polar Urals and bogs of the West Siberian plain. The Meadow Pipit Anthus pratensis has no ecological adaptations to the subarctic conditions, but develops its southern half, moving along the forest-tundra and shrubby tundra to the East, which is facilitated by the warming of the climate in Western Siberia. The prospects of changing species habitats in a changing climate are discussed.

Introduction

The biosphere approaches critical for the animal and vegetable world of the period of rapid increase renesemee temperature. The likely consequence of” global warming “ for the North of the Ural region will be the promotion of taiga in the forest-tundra, foresttundra- in the tundra zone, the displacement to the North of the tundra subzones, the disappearance or reduction of the Arctic deserts. All this has already been observed in the period of thermal maximum 9-5 thousand years ago [1]. Changing landscapes will be accompanied by changes for the animals inhabiting them. As forest-tundra-tundra strip is the world of birds (177 species of terrestrial vertebrates 215 of the Polar Urals and Peninsula Yamal), changes in the greatest measure will affect this group the possible advancement to the North common species, kinds, mastering the sub-Arctic, the retreat to the North of the species-subarctic and Arctic species. At the same time, there may be no direct connection between habitat changes and changes in distribution and shift of habitat boundaries. For example, the fauna of the waterfowl forest-tundra lakes of the Lower Ob differs from the fauna of the tundra lakes Of the middle Yamal [2] in the absence of differences or insignificance of differences between the lakes. The aim of this work is to generalize the data of observations and experiments on a number of Passeriformes species in the Polar Urals, Lower Ob and Yamal Peninsula to predict changes in the range boundaries within the region.

Study Area

The study of birds started at the forest-tundra the hospital, “Harp”, located 13 km from the town of Labytnangi (66°30N 66°25E.), continued in the polar Urals (the Sob ‘ hospital, 66°40N 60°50E.), then research was moved to the valley of the Ob river, on the left a native beach in the vicinity of Oktyabrsky 5 km below the city of Labytnangi (Figure1). The boundaries of the ranges of the species discussed on the Yamal Peninsula were determined during expeditions in 1974-1982 to the southern, Middle and Northern Yamal.
Figure 1: Location of the research area.
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Method of Research

On the inpatient Sob and October, we carried out the trapping of passerines lines spider nets and large traps. On the test sites, nests were found, ingots were banded with aluminum and colored rings (more than 1,300 Chicks of 8 species were ringed), and the movement of broods was observed, and later - for individual birds marked with colored rings. All captured birds underwent a single complex of in vivo testing: weight, fatness, wing length, sex, age was determined; the state of plumage was described according to the known technique [3]. Analysis of the replacement sequence of the entire plumage requires the division of the molting process into a number of stages- stages. When you complete the molt over the stage taking the period from the loss of a single primary feather up to the moment of loss following [4]. In this case usually stands 11 stages, with a partial molt stage are to participate in various pteryla [5]. Depending on the number of pteryla, which is replaced by feathers in the partial moult allocate from 2 to 8 stages.
Experimental work was carried out in 1985-1989 and 1999- 2012 on birds taken from nests found in the Lower Ob and middle Yamal. From 10-14-day-old Chicks or adult birds to Supplement with formula or fed artificially. The aim was to form three groups of birds of 5-20 individuals: short-day photoperiod (16C:8T), photoperiod, natural for the latitude of the Polar circle and longday photoperiod (24C:0T). The purpose of these studies is to study the features of photoperiodic and temperature control of the summer part of the annual cycle of birds with different types of development of high latitudes - penetrating the Subarctic, mastered the Subarctic, mastered the Subarctic and the Arctic. In the processing of quantitative materials used conventional statistical methods to assess the reliability of differences used student criterion. Differences were considered significant At p < 0.05. All calculations are performed in Microsoft Excel 2003 and Statistica V. 6.0 (StatSoft, Ink., 1984-2001).

Results and Discussion

Environmental Determinants of Latitudinal Boundaries of the Habitats of the Horned Lark Eremophila alpestris and Snow Buntings Plectrophenax nivalis

The southern boundary of the habitat of the Horned Lark Eremophila alpestris and Snow Buntings Plectrophenax nivalis on the maps of the Yamal Peninsula conducted at the same points parallel to the southern border of shrub tundra. On the Ural ridge, the area of the Northern subspecies of the Horned Lark Eremophila alpestris (Figure 2) does not extend beyond the latitude of the Polar Circle (66°30´N). Most South registration litter of Snow Buntings Plectrophenax nivalis in the Subpolar Urals in the hillside Sable (64°30´N) [6]. To the North, the occurrence of these birds in the mountains increases, at the end of the Polar Urals, at the outcrops of rocks, the Snow Buntings Plectrophenax nivalis are ubiquitous [6]. On the plain of the Yamal Peninsula, the Horned Lark Eremophila alpestris are found from the southern subarctic tundra to the Arctic tundra of the Northern tip of Yamal and The white island. Snow Bunting Plectrophenax nivalis in the wild, on the plains of Yamal, is found in the Northern half of the subzone of the Arctic tundra and on the island of White in accordance with Figure 3, mainly, along the coasts [7].

At the Bottom Ob the first Snow Buntings Plectrophenax nivalis flew between 24.03 and 2. 05, average 7.04 (n = 39). Night temperatures these days fell to -23°C, the day was somewhat warmer. The average temperature in the first decade of April was -15.9° ± 1.2°C. (n = 10) the Flight lasted until the end of May - beginning of June. The first flocks included only males, the last - females with a small share of males. No changes in the start of the flight over the past 40 years have been detected, in contrast to the terms of the flight of Horned Larks Eremophila alpestris. In the 70’s-the first half of the 80’s. the Larks of Eremophila alpestris are met between 1.05-29.05, the average date of the first meeting is 13.05 (n=11), the mass flight was observed before the ice drift and intensive snow melting on plakor. By the mid-1980s, the migration of this species had shifted from the first half of May to the second half. In the 90-ies [8] arrival of these larks Eremophila alpestris began between 11.05-30.05, the average date - 22.05 (n = 13). Currently, Eremophila alpestris‘ horned larks often fly over an icefree river and snow-free tundra. The average daily temperature on the day of the first registration of Horned Larks in the period 1978- 1983 was 9°C ... -3.1°C, an average of 1°C (n = 5).
Figure 2: Distribution of Eremophila alpestris in the Lower Ob-region and Yamal.
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Figure 3: The distribution of Plectrophenax nivalis in the Lower Ob- region and in Yamal.
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Nesting sites at the polar stations of the Middle and Northern Yamal males Snow Buntings Plectrophenax nivalis held in April. Females arrived much later, in May. Migrating flocks Of Eremophila alpestris larks included birds of both sexes; some pairs may be formed on migration. Snow Buntings Plectrophenax nivalis from pairing to the laying of the first egg as the weeks pass, larks-days. Despite the early occupation of the nesting areas, the bunches of Plectrophenax nivalis laid eggs in time, common with other passerines, including larks Eremophila alpestris, in some years somewhat earlier. In Northern Yamal oviposition was found in the nests of Plectrophenax nivalis and Lapland Longspur Calcarius lapponica in 1974 he started and 17.06 22.06 (calculated according to the age of the Chicks). In the polar Urals, south of the Arctic circle, the Plectrophenax nivalis fledglings occurred after 10.07. 2000, and fledglings of other birds, the estimated start date of oviposition of Plectrophenax nivalis June 2-3, [6]. On the middle Yamal in 1990, the author observed simultaneously fledglings plantain Calcarius lapponica, Motacilla alba, Plectrophenax nivalis and Eremophila alpestris between 5-9.07. From the Passeriformes of Yamal, the Horned Larks of Eremophila alpestris had a minimum laying size of 2-5 eggs, with an average of 4.12 ± 0.06 eggs (n = 98). 4-7 eggs were found In the nest of Plectrophenax nivalis, with an average of 5.42 ± 0.18 eggs (n = 19). Differences between species are significant at p ≤ 0.05. Larks Eremophila alpestris begin to hatch from the 2nd egg when laying 3-4 eggs. Duration of incubation from the first egg to the first nestling is 11-14 days, average 12.8 ± 0.42 days (n=7); duration of nestling - 9-12 days, average 10.4 ± 0.6 days (n = 9). The total duration of the period from the first egg to the last nestling is 21-24, on average 22.3 ± 0.48 days (n=6). For North Рasseriformes this is the shortest period. The Horned Lark Eremophila alpestris is the only one of the Passeriformes subarctic species, part of the pairs of which after feeding the Chicks of the first brood build a new nest and feed the second brood. Nenets name of the species “Sidnigy” translates as “nesting twice.” On the middle Yamal Peninsula of 8 ringed with coloured rings couples twice on his site bred 2 pairs [2]. In case of loss of the first nest birds also nest again on the site. After leaving the nest, the broods were fed for a decade, so the breeding season of Eremophila alpestris, considering the second clutch in the subarctic tundra of Yamal, lasts more than two months (65-75 days) and ends in mid-August. The breeding season of the Snow Buntings Plectrophenax nivalis lasts less than two months (35-45 days). Females began incubation with the last egg, some earlier; incubation lasts 12-13 days, nestlings sit 9-15 days, more often 12-13 days. The total duration of the period from the first egg to the departure of the last chick is 27-33 days.
In the annual cycle of larks Eremophila alpestris one molt, postjuvenile the first years, postnuptial adults in the breeding range. In the annual cycle of Snow Buntings Plectrophenax nivalis two molting: postjuvenile young, postnuptial adults in the breeding range, prenuptial moult from immature and adult individuals in the field of hibernation. Postjuvenil molt at larks Eremophila alpestris full. Examination of the two extracted on the middle Yamal young birds, and inspection of the tail of the carcasses of young North lark (n = 5) of the ornithological collection of the Zoological Museum of Moscow state University shows that the flight feathers in birds, Northern populations are replaced completely, probably completely replaced by contouring and feathering, at least in birds, moulting in normal terms. The age of the beginning of molting is not established, but the first-year Eremophila alpestris caught in the area of Seyaha settlement (70°10N 72°30E) 1.08 was at the 4th stage of molting (from 11 stages). Based on the terms of hatching in this area, the age of the bird was 30-35 days, ie molting he started at the age of not older than 30 days. Replacement of plumage in Horned Larks Eremophila alpestris, due to the large volume, cannot last less than 45-55 days. At birds of the second brood, (hatching 20.07-30.07) at duration of a molt of 40-45 days, for timely departure the beginning of a molt has to be shifted on age 25-30 days. Probably, the timing and pace of this shedding is controlled by the photoperiod, i.e. the shorter the day, the sooner it starts and ends faster, which is especially important for the second brood. Molting individual’s Balkan subspecies of the horned lark Eremophila alpestris began in 38 days (26.07), lasted 80 days, to 14.10. [9].
Viewing the carcasses of adult northern larks Eremophila alpestris from the ornithological collection of the Zoological Museum of Moscow University (n = 13) and a small number of birds shot on the middle Yamal (n = 5) indicate the beginning of post-marital molting from 10.07 to 10.08. The average calculated duration of molting - 68 days, beginning -2.07, end - 7.09. In birds with a second clutch, shedding should be combined with feeding the Chicks. In a cage of four birds contained in the spring. Two males of Eremophila alpestris began moulting in the second decade of July, two - in the third, and finished it in the third decade of September, after 65-75 days. The female began molting 12.07, finished after 68 days, 18.09. The post-marital molt of the Balkan subspecies began on 22.06 and ended on 92 days, on 22.09 [9]. Postjuvenile molt of Plectrophenax nivalis partial. As a result of its individual wears a mixed first winter outfit consisting of a youthful flight feathers of the wing, the wing, tail feathers and succeeding in a result of shedding of part of the wing coverts, contour feathers of the head and torso. In a cage under short-day birds have not replaced the large upper coverts of the secondaries, i.e. the completeness of molt is determined by photoperiodic conditions. In the natural photoperiod of middle Yamal, molting of young birds began at the age of 33-44 days on average 37.4 ± 2.1 days (n =5), between 24.07- 30.07. When the photoperiod 16C:8T Snow Buntings have started moulting to 29, 31, 32 days, an average of 30.7 days. Despite a small sample, there is reason to believe that the timing of the molt is controlled by the photoperiod, because with a short day molt began earlier. The molting rate is also controlled by the photoperiod. Under lighting conditions close to the natural Middle Yamal birds replaced plumage for 48-51 days, an average of 49.4 ± 0.6 days. and finished it between 10.09-15.09. With a short day of molting lasted 37, 39, 40 days, an average of 38.7 days, ie. the shrinking day stimulates not only a shift in the timing of the beginning of molting on earlier dates, but also earlier its end (24.08-30.08) by reducing the number of replaced feathers. Very early on 5th or 6th molt stages (7 stages), poultry has gained the “average” fat reserves. In early October, 3 young birds were examined in the forest-tundra. Two of them have finished shedding, one was in the last stage; in the middle of October all 6 examined birds were in the new feather. The period of post-juvenile molting in the population of Yamal punches of Plectrophenax nivalis continues 2-2.5 months.
Postnuptial moult of Plectrophenax nivalis full. In enclosures hospital October Snow Buntings (n=7) started moult between 12.07-25.07 average date 18.07. In Yamal male moult apparently begins in the third decade of July, but some birds can start it in the second decade. Perhaps some males, like other Northern Bunting [10], started the replacement of feathers prior to fledging from the nest; with supplemental foods juvenile moult must combine all males and some females because of the summer time, it remains small. In Greenland [11] some moulting males fed female and nestlings always combined with supplemental foods moult juveniles; females always started moult after leaving the nests hatchlings. Molting of Plectrophenax nivalis aviary punches lasted 51-65 days, on average-57.8 ± 2.0 days (n=7), which is twice the duration of molting of Plectrophenax nivalis in Greenland (720 N) - 28 days [11]. Usually in the aviary molt is somewhat delayed, but two-fold differences in the rate of molting Plectrophenax nivalis indicate that the Yamal birds shed really slower than the Greenland. Starting molting in late July - early August, they finished it in mid- September, at the same time with young birds. However, they did not lose the ability to fly, unlike the birds of Greenland [11]. Through the Bottom Ob the adult birds are flying without a trace of molt.
Departure of larks Eremophila alpestris from the forest-tundra falls on the period from 18.09-15.10. Snow Buntings Plectrophenax nivalis appear in the forest after the first snowfall, in the third decade of September - early October. The main period of migration Plectrophenax nivalis mid-late October, ends in November. Near the city of Labytnangi the average duration of the migration period of Plectrophenax nivalis 23 days. The unifying features of the ecology of the studied species include, first of all, high resistance to low air temperatures. It is supported by wintering in the lowsnow continental zone, where night temperatures -20°... -30°C are very common. Arriving in spring to the North of the subarctic and Arctic, Snow Buntings Plectrophenax nivalis and larks Eremophila alpestris do not go beyond the lower limits. Resistance to low temperatures and, probably, dense hatching, allows early risers to keep the eggs and Chicks in a relatively shallow socket with low thermal insulation qualities. By the Ural mountains Snow Buntings penetrate to the South to the highlands without going down to the foothills, where there are mountain tundras, but apparently too warm. Horned Larks need to better endure summer temperatures than Snow Buntings because other species inhabit the lower latitudes, but in the subarctic region South of the July isotherms 12°C they do not nest. High density nesting of Eremophila alpestris within July isotherms of 5-10°C, Plectrophenax nivalis - 2-5°C . No. Beetles [12] revealed similarities to the southern boundary of the area of the Eremophila alpestris with the isotherm of July 10°C. Perhaps in the Arctic lark Eremophila alpestris and Plectrophenax nivalis for stimulation of oogenesis enough temperatures close 0°C. or required additional signals (ready biotope, abundance of feed).
A significant role in the formation of the fauna of the subarctic is played by the duration of the frost-free period. When feeding two broods in part of the larks Eremophila alpestris breeding period should last up to 2 months. On the white island and on Novaya Zemlya (73°N) the second brood is probably not present, because the frost-free period is short there. In Western Siberia, the area of larks Eremophila alpestris is in the limits of frost - free period 70 days (68°N) - 35 days (75°N.), that in the subarctic tundra allows you to feed two broods in the Arctic-one.
A characteristic feature of high latitudes - summer polar day. Northern migratory birds with increasing length of the day faced on the wintering grounds and during spring migration. But already on approach to a Polar circle they get to conditions of constant 24- hour day. The reduction of the day length in the subarctic begins much later than in the temperate latitudes, in the middlelate summer, and in the Arctic - in late autumn. In the spring-autumn part of the annual cycle of Northern birds there are two critical points depending on the length of the day: the period of gonad formation and the period of molts. For full maturation of gonads, based on the photoperiod of the extreme southern nesting point in the circumpolar Urals, Plectrophenax nivalis need a short stay (exposure) at the photoperiod 24C: 0T (occurs only during the summer solstice), so nesting should begin at the end of June. Indeed, G. Boyko [13] in XP. The saber (the southernmost nesting point, 64°30N60°E), met several adult punches of Plectrophenax nivalis with ingots 3.08, i.e. the oviposition of these birds began after the summer solstice. North of the Arctic circle, where the polar day begins in the first decade of May, the registration of broods falls on the first - second decade of July, birds were exposed long before the summer solstice. On the Arctic Islands, where the polar day lasts almost six months, the photoperiod does not prevent the early start of egg laying, but there are no external nesting conditions: weather, fodder, biotopic. Horned Lark for the maturation of the gonads is necessary more long stay under continuous light. In spring the birds fly over the forest-tundra at the photoperiod of 24C: 0T to the southern border of the area in the tundra zone, where the gonads reach full maturity. The period from the appearance of an individual in the polar day zone to arrival at the nest site in the shrub tundra, due to the very slow migration through the forest tundra, lasts a few days; to the Arctic tundra larks Eremophila alpestris fly 5-10 days (based on the dates of arrival in North Yamal). The likely duration of exposure 24-hour day for sexual activity-3-5 days.
Molt of Snow Bunting in the polar Urals and flows starts with shrinking the bottom, in the Northern sub-Arctic and Arctic-at a constant 24-hour day. Photoperiodic control of the time and rate of post-juvenile molt is adaptive to the light conditions of the polar Urals, where in August the day is rapidly decreasing, but in the Northern and main parts of the area photoperiodic control does not work, i.e. there is no need for such a reaction. Age and rate of molting in the bottom of the Arctic controlled by the endogenous, but the young from the second egg laying and their parents with the onset of dark nights enabled the photoperiodic reaction. In the Arctic, due to the need for departure in late September - the first half of October, but before the beginning of the dark nights in mid-October, shedding should occur accelerated endogenously controlled pace. In this regard, an interesting 28-day duration post-nuptial moult, Plectrophenax nivalis in Greenland. G. Green, R. Summers [11] in discussing such moult rates suggested that they increase to the North, because Greenland, unlike Iceland, punches Plectrophenax nivalis lose the ability to fly due to the rapid moult of the flight feathers, which “indicates further adaptation to a shorter season at higher latitudes.” The moult of Eremophila alpestris in different photoperiodic conditions has not been studied, but probably in the southern tundra the terms and rates of molts are controlled by the decreasing day, and in the conditions of the long polar day (in the Northern subarctic and Arctic tundra) the terms and rates are controlled endogenously, by the internal rhythm. Only in this case the larks Eremophila alpestris at 75°N (range limit on the island of Novaya Zemlya) are able to finish a complete molt and fly away for the winter in the middle-end of September.
Ecological differences between species belong to the nesting period. Acquiring resistance to low summer temperatures and adaptation to the light regime, larks Eremophila alpestris did not change the requirements for breeding habitat, have not started to build a warm and sheltered from the winds of the nest, but for food for the Chicks learned to fly in the floodplain, to find earthworms, larvae and imago Tipulidae, larvae of sawflies, i.e. the preference for large invertebrates. The expansion of their range at the expense of the Arctic Islands prevents the whole range of Arctic conditionsthe lack of suitable for nesting biotopes, the lack of the required number and mass of large invertebrates, a short period of positive temperatures. Plectrophenax nivalis are distinguished by nesting in shelters and a large nest, which protects the clutch and brood from low temperatures, a wide range of feed biotopes, from garbage dumps to sea shores and the composition and size of invertebrates - from the tailings to beetles and sea crustaceans. The nesting of Plectrophenax nivalis on all Arctic Islands indicates that there are currently no limiting factors for the species.

Environmental Factors that Determine the Latitudinal Boundaries of the Areas of Red-throated Pipit and Meadow Pipit

Red-throated Pipit Anthus cervinus is associated with the origin of the Subarctic, its nesting area is mostly limited to the forest-tundra strip, sometimes penetrates into the Northern taiga. In our area nests (Figure 4) in the band from the Northern tip of Yamal (73°N) to the Western Saleda ridge (65°N) in the polar Urals. Tundra Red-throated Pipits everywhere, with the exception of riparian forests, and avoided deciduous woodland of placore. In the southern subarctic tundra, Anthus cervinus skates were found in all biotopes, in the Northern subarctic tundras they were found regularly in floodplains, and in open tundras on plains and on the southern slopes of hills and ravines. In the South of the Arctic tundra of Red-throated Pipits Anthus cervinus was recorded in dry lichen tundra, cut by ravines of small streams and in areas of bumpy rather dry tundra.
Figure 4: Distribution the Anthus cervinus in the Lower Ob- region and in Yamal.
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Meadow pipit Anthus pratensis at the beginning of the twentieth century. nesting to Salekhard (66°31N 66°53E), but not North; in the middle of the century skates nesting in the middle reaches of the river Pike (67°N) [14]. In 1974-1976 nesting Pipits greeted us at the village of Mys Kamennyy (68°40N 73°10E.) and to the North, the middle reaches of the R. Mardiah (69°50N.). But they were not on the 70th latitude on the West coast near the polar station of Marre-Sale, on the East coast near the village of Seyaha (70°10N 72°30E) and 30 km from the coast, in the middle reaches of the Yasaveyaha river [2]. In 1988-1990 Meadow Pipits Anthus pratensis continued to meet in the middle reaches of the river Mardiah, and in 2006 they are found nesting in the vicinity of the settlement of Seyakha [15]. Thus, over the last 100 years, the species has moved to the North by more than 300 km, to the 70th parallel (Figure 5). At the same time, the area to the East is expanding. The Eastern border of the Anthus pratensis nesting in the middle of the last century was carried out along the Ob valley (63°50N).; somewhat later, the species was found in the upper reaches of the Kazym and Nadym rivers [16]. Currently, as a rare breeding species Meadow Pipit Anthus pratensis found on the right tributary of the lower Pelvis-p. Russian (67°20 n 82°E) [17].
Figure 5: The distribution of Anthus pratensis in the Lower Ob-region and in Yamal.
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The arrival of the first Red-throated Pipits Anthus cervinus in a neighborhood of the city of Labytnangi in the period 1971-2014 was observed between 10.5-7.06. The earlier spring began, the earlier the first birds appeared. The air temperature on the day of registration of the first bird in the forest tundra was 0.1-5.8°C, on average 2.3°C (n=6); in Yamal, the arrival also began at positive temperatures. For the forest-tundra period 1970-2004. the average date of the meeting of the first Anthus pratensis-25.05, the earliest date-3.05.1982, late-4.06.1978. the air Temperature on the day of the meeting of the first bird was 0.2°C...-11.4°C, an average of 3.0°C (n = 8), in the late spring birds flew with the first wave of warm air. Meadow Pipit Anthus pratensis always arrived before the Anthus cervinus for 1-10 days. Easter S. [18] showed that in the Lower Ob area of Meadow Pipits and Red-throated Pipits in 1986-2001. began to arrive significantly earlier (P ≤ 0.05) than in the previous 15 years.
In Red-throated Pipit from the first in the season of birds encountered before oviposition, forest tundra passed 13-20, an average of 16.0 days (n = 8), in the middle Yamal this period lasted 7-13 days, an average of 10 days (n = 4). In the Meadow Pipit the duration of the pre-breeding period in the forest-tundra, from the first in the season encountered birds to the beginning of laying in the forest-tundra reached 12-27 days, an average of 7 years-18.7 ± 2.1 days. Oviposition in Anthus cervinus began after 8-13 days, an average of 9.8 days (n = 5) after the transition of the average daily temperature through 0°C the average Daily temperature on the day of the beginning of egg laying in the forest tundra in different years was 6.0-11.5°C (n = 5). In the Lower Ob the earliest date of the beginning of the period of egg laying by the Red-throated Pipit Anthus cervinus 9.06. 1973, the latest-21.06.1972g, average 16.06. (n = 5). On the Middle Yamal these dates are as follows: 5.06.1990 - 29.06.1987 and 1992, the average date is 14.06 (n = 9), on the North Yamal 9.06.1988 - 1.07.1992 and 1994, the average date is 21.06 (n = 6). In some years, with the advance to the North, the timing of the beginning of egg laying is also shifted to later dates. In 1990 at the 69th parallel oviposition began 5.06, 70 10.06, in the 71st - 13.06. In other years, the delay in the beginning of the egglaying season on the 71st parallel compared with the 69th was 4 (1988) - 15 (1991) days.
In the Lower Ob in 1971-1990 the first eggs in the nests of Meadow Pipit Anthus pratensis appeared between 7.06.1989 and 18.06.1971, the average for 9 years of observations the date of the beginning of oviposition-14.06. On the Middle Yamal Peninsula in 1974-1992 years and the earliest date of oviposition - 13.06.1989, the beginning of masonry in Ob - 8.06.1989. The latest date the beginning of masonry on the Middle Yamal - 19.06.1974, with the beginning of oviposition in the Lower Ob - 16.06.1974. Masonry of the bulk of females begins in the first 6 days: in the forest tundra 98 masonry of 112 (87.5%); in the middle Yamal 126 of 160 (78.7%), in the North Yamal - 12 of 26 (46%). The total duration of the laying season in the forest tundra is 14-21 days, average 16.8 ± 1.3 days (n = 5), average 9.8 ± 1.0 days in the tundra of the middle Yamal (n = 9), 13-28 days in the Arctic tundra of the Northern Yamal, average 18.8 ± 2.9 days (n = 5). The stretch of the season connected with the finding of subsequent clutches.
In the masonry of the Red-throated Pipit Anthus cervinus 2-7 eggs. In The lower Ob in the clutch was 5.34 ± 0.06 eggs (n = 209): in the Northern Yamal the average size of the clutch was 5.46 ± 0.14. The increase in masonry from the forest-tundra to the tundra Of the Middle Yamal is highly significant (t ≤ 11.1) and is associated with an increase in the proportion of masonry with 7 eggs, but in the Northern Yamal masonry value decreases again due to the reduction in the proportion of nests with 7 eggs. In the nests of Meadow Pipit in the Lower Ob ‘ region and in the Southern Yamal Peninsula was 5.41 ± 0.09 eggs (n = 101). On the Middle Yamal there were 5.88 ± 0.06 eggs (n = 58). The differences are significant (t = 4.7, P ≤ 0.01) due to the absence of clutches with 2-4 eggs in the sample. Thus, both types of skates with promotion to the North, the number of eggs in a clutch increase.
According to the results of instrumental measurements, the female of the Red-throated seahorse Anthus cervinus starts to incubate regularly after laying the 2nd-3rd egg with 5-6 eggs. The duration of incubation from the last egg to the first nestling on 28 nests is from 10 to 13 days, on average 11.5 ± 0.15 days. Hatching is stretched for 1-3 days, more often for 2 days, on average 1.8 ± 0.15 (n = 13). The Chicks sat in the nest 9-13, on average, 11.6 ± 0.29 days. (n = 26), ingots from large broods left the nest earlier. The duration of the breeding season Anthus cervinus tundra 36-43, on average, 38.8 ± 1.0 days. (n= 6). At the meadow ridge incubation begins with the penultimate or last egg. From the last eggs before the first Chicks in the control nests of meadow Pipits Anthus pratensis took place 12-15 days, an average of 13.9 ± 0.19 (n=16). In the nest the Chicks were sitting 9 to 14 days, on average 10.9±0.4 days (n = 16). The total duration of the breeding season at the Polar circle latitude from the first egg to the departure from the control nests of the last nestling in different years: 38-44 days, on average - 41.5 ± 1.6 (n = 8). On the Middle Yamal the breeding season of Anthus pratensis lasted 43-50 days, on average 46.7 (n = 3).
Up to 20-22 days of age, Anthus cervinus Red-throated Pipit fledglings were in the area of the breeding area and were fed by adult birds. The disintegration broods Red-throated Pipits occurs at 23-25 days and the birds leave the nesting area in the process of dispersion of the dispersion. Older this age re-caught 2 seahorses at the age of 35 and 39 days. In the forest tundra adult Meadow Pipits was worried at nesting sites until the beginning of August. Of the 20 ringed Chicks in the nests in the area of the nesting area, 2 birds were caught at the age of 33 and 54 days, i.e. after the disintegration of the broods, most of the young birds are included in the dispersion spread, but some remain in the birth area for a long time. Postjuvenile moult Red-throated Pipit partial, minimal among the Northern Motacillidae completeness: replaced a part of the contour feathers of the head and trunk down on apteryx and some wing coverts. Postjuvenile molt Meadow Pipit partial, but more complete than the Red-throated Pipit. Coverts moult of the head and torso, grew up in the nest, and part of wing coverts, where everyone is viewed on the secondary stages of molting birds were replaced by a small upper-coverts of secondaries, upper and lower opacity brush, wing-coverts, tertials coverts lower, secondary lower coverts of secondaries.
The moult of the Anthus cervinus begins at an early age, in birds older than 20 days of age. Of the 11 skates ringed in nests and caught at the age of 20-38 days, molting was 4 individuals: the horse at the age of 25 days was at the 1st stage, at the age of 28 days at the 2nd stage, 2 birds at the age of 33 and 38 days were at the 3rd stage.The rest, at the age of 20-25 days did not shed. In experimental conditions molting began in 22-25 days at a short day (23.4 ± 0.4; n=8), in 24-25 days at natural (24.4 ± 0.2; n = 5) and 24-26 days (25.0 ± 0.2; n = 9) at a long day, i.e. the age of onset of moult in this species is controlled by endogenous. Meadow Pipit Anthus pratensis, ringed in nests and caught in nature at the age of 22-30 days, did not start molting. Skates, fed and overexposed at the natural day, began shedding at the age of 36-45, an average of 38.0 ± 1.4 days (n = 6). Under short-day molt started no earlier than 27 (27 to 36 days, averaging 31.8 ± 1.1; n = 8), the long - not later than 50 (45 to 50 days, averaging 46.7 ±.0; n = 5). The differences in the age of molt onset are significant between all groups: short-day and natural day (t-criterion = 4.04, P ≤ 0.01); natural day and long-day (t-criterion = 4.53, P ≤ 0.01); short-day and long-day (t-criterion = 10.1, P ≤ 0.01). Thus, the timing of post-juvenile molting in meadow skates Anthus pratensis controlled photoperiod, in contrast to the Anthus cervinus.
The rate of shedding is controlled by the photoperiodic response in both species. Molt Meadow Pipits Anthus pratensis under short-day regime molt lasted 30 to 36 days, averaging 34.0 ± 0.8 (n = 8); natural 37-40 days, averaging 38.5 ± 0.8 (n = 5); the long-day regime 40-55 days, averaging 45.0 ±1.6 (n = 9). The differences are significant between the groups of short and long days (t-criterion = 3.0, p ≤ 0.05). the period of post-juvenile molting in the population of Red-throated Pipit Anthus cervinus of The lower Ob should last 45-55 days. By the time of its completion, the young skates fly away from the Lower Ob. Molt Anthus pratensis under short-day molt lasted for 35-45 days, an average of 39.7 ± 1.2 (n = 8); natural 44-49 days, averaging 46.0±1.6 (n = 6); the long - 58- 62 days, averaging 59.5 ± 0.5 (n = 6). The differences are significant between the groups of short-day and natural day (t-criterion = 3.15, p ≤ 0.05); natural day and long-day (t-criterion = 8.08, P ≤ 0.01); short-day and long-day (t-criterion = 15.2, P ≤ 0.01).
Young Red-throated Pipit usually started shedding without leaving the nest surroundings and the last stages of shedding the skates combined with migration. Migration from Meadow probably starts after the completion of the moult, because in the third week of September in the vicinity of Labytnangi appeared regularly flocks are skates; in 1982, in the last five days of September caught 7 birds, 3 of them have finished molting, 4 were in new plumage. Season postjuvenile shedding Anthus pratensis in the tundra lasts 2 months, a third longer than the Anthus cervinus. Full post-nuptial molt in both species, Anthus cervinus partially simultaneously with the feeding of the Chicks. In the second half of the molting period, the skates partially lose their ability to fly [19]. According to the results of the regression analysis, the average date of the beginning of the post - marital molt of the Red - throated Pipit Anthus cervinus falls on July 22, the end of the growth of the flight feathers-on August 19, the duration of the molt of the flight feathers-29 days, contour plumage finishes molting not earlier than a week. The actual duration of the post-nuptial moult is 37-45 days. It is necessary to pay attention to high rates of replacement of flight feathers: in 25-30 days after its beginning birds are able to begin migration. The slow rate of formation of contour feathers does not prevent flights. The season of post-marital molting in the population of red-throated skates Anthus cervinus of The lower Ob region lasts 45-50 days. Post-marital molting in Meadow Pipit Anthus pratensis began in the second half of July - early August. The first shedding pipit caught 23.07, the average calculated date of the beginning of molting - 27.07; in the old plumage of birds caught up to 5.08. The duration of molting in the first beginners of her skates 45-50 days. Males, overexposed from spring (n = 4) in the aviary, shed 56-65 days, on average 59 days; female, taken with Chicks, completely replaced the plumage for 49 days. The average end date of molting in nature 3.09, the average duration of molting regression 39 days, the duration of the season of post-marital molting 60-70 days.
Red-throated Pipits Anthus cervinus fly away from the forest before the meadow. Maximum span in 1975 was observed 2.09. The last meeting of the young birds on the tour in 1975 have on 17.09, adults - 8.09, the departure period lasted about a month. In 1980 from the Enzor-Yakha and Baydarata rivers (68°15N 69°10°E) the departure of red-throated skates Anthus cervinus ended in the last days of August [20]. The departure of the Anthus pratensis begins at the end of August and ends at the end of September. The most recent meetings in the Lower Ob are 21.09.1980, 28.09.1982, 25.09.1984. One flock met on the first snow. N. N. Danilov [21] attributed the Meadow Pipit Anthus pratensis species have mastered the southern sub-Arctic. Currently, in Western Siberia, the species is developing the Northern subarctic And quite well mastered the “middle” Subarctic-sub-zone of the subarctic tundra of Yamal and Tazov Peninsula. V. S. Zhukov [12] the Northern boundary of the range of Anthus pratensis correlates with the isotherm in July is +6°C. V. A. Utkin [22] when building the model, the gradient of the range of Meadow Pipit Anthus pratensis southern border holds for the boundaries of the territory with a relatively short summer nights and the July isotherm of + 20°C. July isotherm of the southern border of the Red-throated ridge -15°C, the Northern border of the area-3°C. the Main part of the area lies in the polar day from mid-May to late July, i.e. photoperiod 24C:0T. The southern limits of the area pass through the territory of the polar day only during the summer solstice.
In the forest-tundra and southern tundra Anthus pratensis arrive with developed gonads in connection with the stimulation of” long “ day on the approach to the Arctic circle, they can engage in reproduction in the forest-tundra and southern tundra, especially in late spring or return of cold weather, which is not uncommon in the North. But in the early spring, which happens more often, birds continue to migrate and expand the area to the North. Red-throated Pipit Anthus cervinus have higher requirements for the length of the light phase, as arrive with underdeveloped gonads. The polar day probably stimulates an increase in the fertility of both types of skates, because on the middle Yamal the number of eggs in the clutches of both species is higher than in the Ob.
The timing of the post-juvenile molting of the Anthus cervinus is associated with age (22-25 days), the molting rate is high, which allows birds to start flying before the onset of cold weather even from the southern Arctic. Adult birds combine molting with reproduction, conduct it at a high rate, which also provides a fairly early flight. Photoperiodic control of moult in the meadow ridge Anthus pratensis shifts its origin in the forest-tundra to the first decade of August, in the Northern subarctic tundra to the second decade. Despite the low completeness postjuvenile molting, it lasts more than a month even in the tundra - to mid-September, and in the Northern tundra, in connection with the late start and the slow pace at longer bottom until the third decade of September, in some years until early winter. Adult skates are also in no hurry to start shedding, because they separate it from feeding. But since the rate of post-marital moult of Anthus pratensis is very high, the late departure is probably also associated with the late formation of the migration state, as in the first years. For this reason, the migration starts later than the departure of other insect-eating birds of the tundra.
The penetration of meadow Pipit Anthus pratensis in the taigatundra part of Asia is facilitated by the absence of interspecific territorial competition [23] and increased fertility in the zone of Sunny nights, creating a sufficiently high abundance for movement to the East. Currently, the North-Eastern tip of the area reaches the Ob-Yenisei watershed, and the entire part of the area in Western Siberia is in the zone of white nights. It is unlikely that there are factors that significantly impede the expansion of the species range to the East, at least on the plain to the Yenisei. But further, the movement in Central Siberia, with its mountainous terrain, also should not be an obstacle, because in the mountains of the Northern, polar and Polar Urals Meadow Pipit Anthus pratensis one of the background species.

Conclusion

The southern limits of the distribution of Snow Bunting Plectrophenax nivalis are probably determined by the light regime of the region, outside the zone of the polar day birds will not come to a state of sexual activity. Additional requirements of Plectrophenax nivalis average July temperature below 10°C. the Northern limits of the range of Plectrophenax nivalis in the modern climate of the Arctic, actually, no. In conditions of further warming, the punches of Snow Bunting may fall from the list of breeding species of the polar and Polar Urals.
The limits of penetration to the North of the Horned Larks Eremophila alpestris are determined by a set of biotope and feed factors and temperature lows, allowing to penetrate into the Arctic, but not to master most of it. In the conditions of further warming the larks of Eremophila alpestris will master all Arctic Islands but will drop out of the list of birds of the southern subarctic tundra. The southern limits of distribution of the Red-throated Pipit Anthus cervinus are limited by the zone of the polar day defining maturation of gonads, mountain tundras of the polar Urals and tundra-like bogs of the West Siberian plain. The limits to the North, apparently, the readiness of biotopes to the beginning of arrival (the presence of invertebrates, thawed tundra). As heat moves to the North, replacing the tundra Arctic deserts, the species will expand its range.
The limits of penetration to the North of the Horned Larks Eremophila alpestris are determined by a set of biotope and feed factors and temperature lows, allowing to penetrate into the Arctic, but not to master most of it. In the conditions of further warming the larks of Eremophila alpestris will master all Arctic Islands but will drop out of the list of birds of the southern subarctic tundra. The southern limits of distribution of the Red-throated Pipit Anthus cervinus are limited by the zone of the polar day defining maturation of gonads, mountain tundras of the polar Urals and tundra-like bogs of the West Siberian plain. The limits to the North, apparently, the readiness of biotopes to the beginning of arrival (the presence of invertebrates, thawed tundra). As heat moves to the North, replacing the tundra Arctic deserts, the species will expand its range.

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