;where B' is the estimated biomass, X is water mineralisation, and k1 and k2 are empirical coefficients. ; <mrow><mi>В</mi><mi>р</mi><mo>=</mo><mi>В</mi><mo>'</mo><mo>'</mo><mo>−</mo><mi>В</mi><mo>'</mo><mo>,</mo><mtext>                           (2)</mtext></mrow> ;where Bp is potentially lost biomass with increasing mineralisation, B'' is estimated biomass with mineralisation of 3 g/dm3. From equations (1) and (2) the potential biomass is determined that would be in the absence of inhibitory effect of mineralisation as follows: ; <mrow><mi>В</mi><mi>m</mi><mo>=</mo><mi>В</mi><mi>a</mi><mi>v</mi><mo>+</mo><mi>В</mi><mi>р</mi><mo>,</mo><mtext>                          (3)</mtext></mrow> ;where Bm is potential biomass in the absence of inhibitory effect of mineralisation, Bav is average biomass in the foreshore of the water reservoir.;EFFECT: invention enables to estimate the real trophic status of lake ecosystems under the influence of natural and anthropogenic factors and to predict the biomass of aquatic communities when change in the water mineralisation of lakes.;1 dwg, 1 ex"/> METHOD OF EVALUATING TROPHIC STATUS OF ECOSYSTEMS OF MINERALISED LAKES ON LEVEL OF DEVELOPMENT OF AQUATIC COMMUNITIES
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METHOD OF EVALUATING TROPHIC STATUS OF ECOSYSTEMS OF MINERALISED LAKES ON LEVEL OF DEVELOPMENT OF AQUATIC COMMUNITIES

机译:评价水生社区发展程度矿化湖生态系统营养状况的方法

摘要

FIELD: agriculture.;SUBSTANCE: invention relates to the field of ecology and hydrobiology and is designed to assess the trophic status of ecosystems of mineralised lakes. In assessing the trophic status of the lake ecosystem with water mineralisation over 3 g/dm3 according to the level of development of aquatic communities the negative effect of mineralisation level is taken into account by calculating the amount of lost biomass using the obtained empirical dependence and its approximation in the form of a power function of the form:; <mrow><mi>В</mi><mo>'</mo><mo>=</mo><msub><mi>k</mi><mn>1</mn></msub><mo>⋅</mo><msup><mi>X</mi><mrow><mi>k</mi><mn>2</mn></mrow></msup><mo>,</mo><mtext>                       (1)</mtext></mrow> ;where B' is the estimated biomass, X is water mineralisation, and k1 and k2 are empirical coefficients. ; <mrow><mi>В</mi><mi>р</mi><mo>=</mo><mi>В</mi><mo>'</mo><mo>'</mo><mo>−</mo><mi>В</mi><mo>'</mo><mo>,</mo><mtext>                           (2)</mtext></mrow> ;where Bp is potentially lost biomass with increasing mineralisation, B'' is estimated biomass with mineralisation of 3 g/dm3. From equations (1) and (2) the potential biomass is determined that would be in the absence of inhibitory effect of mineralisation as follows: ; <mrow><mi>В</mi><mi>m</mi><mo>=</mo><mi>В</mi><mi>a</mi><mi>v</mi><mo>+</mo><mi>В</mi><mi>р</mi><mo>,</mo><mtext>                          (3)</mtext></mrow> ;where Bm is potential biomass in the absence of inhibitory effect of mineralisation, Bav is average biomass in the foreshore of the water reservoir.;EFFECT: invention enables to estimate the real trophic status of lake ecosystems under the influence of natural and anthropogenic factors and to predict the biomass of aquatic communities when change in the water mineralisation of lakes.;1 dwg, 1 ex
机译:技术领域本发明涉及生态学和水生生物学领域,并且被设计用于评估矿化湖泊的生态系统的营养状况。在根据水生生物的发展水平评估矿化度高于3 g / dm 3 的湖泊生态系统的营养状态时,通过计算损失量来考虑矿化度的负面影响使用获得的经验依赖性及其近似形式的生物量,其形式为幂函数: <数学> <![CDATA [ В ' = k 1 X k 2 (1)( ]]> ;其中B'是估计的生物量,X是水的矿化作用,k 1 和k 2 是经验系数。 ; <数学> <![CDATA [ В р = В ' ' В ' (2) ]]> ;其中Bp可能随着矿化程度的增加而损失生物量,而B''是矿化度为3 g / dm 3 的生物量。由等式(1)和(2)确定潜在的生物量,该生物量在没有矿化抑制作用的情况下如下: <数学> <![CDATA [ В m = В a v + В р (3) ]]> ; Bm是没有矿化抑制作用的潜在生物量,Bav是水库前滨的平均生物量。;效果:本发明能够估算自然和人为因素影响下湖泊生态系统的实际营养状况。预测湖泊水矿化变化时水生生物量。1dwg,1 ex

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