Ecological aspects of meadow phytocenoses

T. Nahirniak
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Abstract

The article states that meadow phytocenoses are distinguished from others (forest, steppe, desert, water and others) by the dependence of the composition and structure (structure) of meadow communities on environmental conditions. At the same time, onions differ from agrophytocenoses on arable lands. On arable land, in the process of crop rotation every year (or with a break of one year in the chain of peren-nial grasses), the existence of phytocenosis is disturbed by the agricultural machinery used to cultivate the soil. Therefore, crops of grain or row crops are always available for the spread of weeds. In order to control their number, it is necessary to use an integrated system of plant protection, which includes agrotechnical measures, and biological and chemical methods of control. The meadow, unlike such agrophytocenosis, is closed to the spread of weeds, since there are competitive relationships between the plant populations that are part of it. It is substantiated that as a result of competition and differentiation of niches, the structure of the meadow phytocenosis is formed – the height difference of the aerial parts and the depth of the root systems. There are no clear layers of it above ground or below ground in meadow grass stands, but sometimes stable combinations of species are formed on the meadow, which are repeated like spots. Such spots are called micro groups, and the phenomenon itself is called mosaicism. However, mosaicism is not very common and is usually associated with the distribution of leguminous components, which have a stronger impact on the environment than other species. Leguminous grasses are known to enrich the soil with nitrogen as a result of the activity of nitrogen fixers symbiotically associated with them, and in favorable years they form many leaves, which can limit the growth of light-loving species. It was noted that the peculiarity of meadow phytocenoses is the correspondence of their composition and structure to the smallest changes in environmental conditions, which in forest phytocenoses will be leveled as a result of the strong influence of trees, and in arable land they are somewhat leveled by the system of soil cultivation, application of fertilizers and sowing. However, rapid spatial variability is only one of the many qualities of these plastic communities. Meadow phytocenoses can change over time quite quickly. At the same time, it is worth distinguishing 2 types of changes – reversible and irreversible. In the first case, changes in the composition of meadow phytocenosis are associated with seasonal changes, with fluctuations in weather conditions in different years, with the intensity of pasture use, outbreaks of the number of certain types of meadow grasses, or the spread of nematodes or pest insects on meadow grasses. In the second case, meadow communities change under the influence of anthropogenic factors (hay mowing or fertilization) or, on the contrary, self-restore after the cessation of the influence of a certain factor. It should be noted that usually 2 main variants of successions can be observed on meadow phytocenoses: caused by internal causes (autogenic) and external (allogenic). However, it should be noted that the main successions in meadows are allogenous, which are related to changes in environmental conditions or the mode of use. Most often, the root cause of these changes is the human factor. Autogenous changes are most often restorative in nature.
草甸植物群落的生态学特征
草甸植物群落的组成和结构(结构)对环境条件的依赖性是草甸植物群落与其他植物群落(森林、草原、沙漠、水等)的区别。同时,洋葱不同于耕地上的农业植物。在可耕地上,在每年轮作(或多年生草链中中断一年)的过程中,用于耕作土壤的农业机械干扰了植物病的存在。因此,粮食作物或行栽作物总是为杂草的蔓延提供了条件。为了控制其数量,有必要采用综合的植物保护系统,包括农业技术措施和生物和化学控制方法。草甸,不像这样的农业植物共生,是封闭的杂草蔓延,因为有竞争关系的植物种群之间的一部分。结果表明,由于生态位的竞争和分化,形成了草甸植物群落的结构——地上部分的高度差和根系的深度差。在草甸草地中,地上或地下没有明确的层次,但有时在草甸上形成稳定的物种组合,这些组合像斑点一样重复。这样的斑点被称为微群,这种现象本身被称为马赛克。然而,镶嵌现象并不常见,通常与豆科成分的分布有关,豆科成分对环境的影响比其他物种更大。众所周知,豆科草可以通过与之共生的固氮菌的活性来丰富土壤中的氮,在有利的年份,它们会形成许多叶子,这可能会限制喜光物种的生长。有人指出,草甸植物群落的特点是其组成和结构与环境条件的最小变化相对应,在森林植物群落中,由于树木的强烈影响,环境条件会被夷平,而在耕地中,由于土壤耕作、施肥和播种制度,它们会在一定程度上被夷平。然而,快速的空间变异性只是这些塑料群落的众多特性之一。草甸植物群落可以很快地随时间变化。同时,有必要区分两种类型的变化——可逆的和不可逆的。在第一种情况下,草甸植物病组成的变化与季节变化、不同年份天气条件的波动、牧场使用的强度、某些类型草甸草数量的爆发或线虫或害虫在草甸草上的传播有关。在第二种情况下,草甸群落在人为因素(割草或施肥)的影响下发生变化,或者相反,在某种因素的影响停止后自我恢复。需要注意的是,草甸植物群落的演替通常有两种主要的变异:内因(自生)和外因(异体)。但是,应该指出的是,草甸的主要演替是异质的,这与环境条件或利用方式的变化有关。大多数情况下,这些变化的根本原因是人为因素。自生变化在本质上通常是恢复性的。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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