首页> 外国专利> METHOD FOR DETERMINING FACTOR SENSITIVITY biosensors, biologically active solid materials and gases, direct environmental and direct economic damage to the environmental objects at pollution, projected changes in the spatial and temporal scale of contaminated environmental objects, ecological and economic damage

METHOD FOR DETERMINING FACTOR SENSITIVITY biosensors, biologically active solid materials and gases, direct environmental and direct economic damage to the environmental objects at pollution, projected changes in the spatial and temporal scale of contaminated environmental objects, ecological and economic damage

机译:确定因子敏感性的方法生物传感器,具有生物活性的固体材料和气体,环境受到污染时对环境物体的直接环境损害和直接经济损害,受污染环境物体的时空尺度的预计变化,生态和经济损害

摘要

1.method u043eu043fu0440u0435u0434u0435u043bu0435u043du0438u00a0 coefficient sensitivity biosensors, biological activity of solid material and gas environments, u043fu0440u00a0u043cu043eu0433u043e environmental and u043fu0440u00a0u043cu043eu0433u043e eco u043du043eu043cu0438u0447u0435u0441u043au043eu0433u043e damage of objects to the natural environment in the u0437u0430u0433u0440u00a0u0437u043du0435u043du0438u0438, forecast the u0438u0437u043cu0435u043du0435u043du0438u00a0 u0441u043eu0441u0442u043eu00a0u043du0438u00a0 u0437u0430u0433u0440u00a0u0437u043du0435u043du0438u00a0 objects of the natural sr food, u043fu0440u00a0u043cu043eu0433u043e u043fu0440u00a0u043cu043eu0433u043e environmental and economic damage.including the choice of u0431u0438u043eu0441u0435u043du0441u043eu0440u0430 from one party to u0443u0441u043bu043eu0432u0438u00a0u043c adaptation u0431u0438u043eu0441u0435u043du0441u043eu0440u0430 experiment, the introduction of u0431u0438u043eu0441u0435u043du0441u043eu0440u0430 in u0442u0435u0441u0442u0438u0440u0443u0435u043cu044bu0435 and control objects, conditioning u0431u0438u043eu0441u0435u043du0441u043eu0440u0430 simultaneously at the u0442u043eu0436u0434u0435u0441u0442u0432u0435u043du043du044bu0445 u0443u0441u043bu043eu0432u0438u00a0u0445 in the tested and control objects for a given time, the measurement of the most sensitive u043fu0430u0440u0430u043cu0435 tra (response) biosensor on the effects of components in the tested objectthe dependence of the relative response u0431u0438u043eu0441u0435u043du0441u043eu0440u0430 from concentration of the component or mixture of components u043fu043eu0441u0442u043eu00a0u043du043du043eu0433u043e, definition of the u0431u0438u043eu043bu043e statement of activity ingredient (s), then the definition of biological activity components of testing environment as the product of the coefficient (s) of biological ak the concentration of the component (s) in the tested object u043eu0442u043bu0438u0447u0430u044eu0449u0438u0439u0441u00a0 orderwhat u0434u043bu00a0 u043eu043fu0440u0435u0434u0435u043bu0435u043du0438u00a0 coefficient sensitivity biosensors using solutions of one u0441u043eu0435u0434u0438u043du0435u043du0438u00a0 or mixtures of compounds u043fu043eu0441u0442u043eu00a0u043du043du043eu0433u043e composition and functional the dependence of the relative response of different biosensors in testing and in the control of the concentration of the sample.u0434u043bu00a0 u043eu043fu0440u0435u0434u0435u043bu0435u043du0438u00a0 biological activity of solid materials and gaseous environments u0442u0435u0441u0442u0438u0440u0443u0435u043cu044bu0435 objects u0433u043eu0442u043eu0432u00a0u0442 to measure in the form of equilibrium solutions in the u043au043eu043du0442u0430u043a the known mass of solid material or of known amounts of gas environment at fixed temperature, pressure and other parameters with known quantities of r u0430u0441u0442u0432u043eu0440u0438u0442u0435u043bu00a0, for example, waterthe control model can be a solvent, based on the functional dependence of relative response biosensors in testing and in u043au043eu043du0442u0440u043eu043bu044cu043d oh the sample concentration at first u043du0430u0445u043eu0434u00a0u0442 factor biological activity components in u0440u0430u0432u043du043eu0432u0435u0441u043du043eu043c solution.then the product of the rate of biological activity on the concentration of the component (s) are biological activity components in u0440u0430u0432u043du043eu0432u0435u0441u043du043eu043c r u0430u0441u0442u0432u043eu0440u0435, biological activity components in u0440u0430u0432u043du043eu0432u0435u0441u043du043eu043c solution u043eu043fu0440u0435u0434u0435u043bu00a0u044eu0442 biological activity components of solid material or gas environmenton the biological activity of components of solid material or the gas environment u043eu043fu0440u0435u0434u0435u043bu00a0u044eu0442 number of survivors and dead specimens of each species of living organisms, for the u043eu043fu0440u0435u0434u0435u043bu00a0u044eu0442 u043fu0440u00a0u043cu043eu0439 environmental damage by number of individuals of each species of living organismsthen u043eu043fu0440u0435u0434u0435u043bu00a0u044eu0442 u043fu0440u00a0u043cu043eu0439 economic damage on the number of deaths of all species of living organisms with a (fixed) value of each species is one species u0438u0432u044bu0445 organisms or based on the dependence of the relative size of the deceased individuals of each species of living organisms from biological activity testing the object in the predetermined u043fu043eu0441u0442u043eu00a0u043du043du044bu0445 or variables u043du043eu0440u043cu0438u0440u043eu0432u0430u043du043du044bu0445 u043au043eu044du0444u0444u0438u0446u0438u0435u043du0442u0430u0445 in the scale of biological activity, for example, the toxicity of u0434u043bu00a0 each kind of living organisms, and then u043fu0440u043eu0432u043eu0434u00a0u0442 forecasting u0438u0437u043cu0435u043du0435u043du0438u00a0 u0441u043eu0441u0442u043eu00a0u043du0438u00a0 u0437u0430u0433u0440u00a0u0437u043du0435u043d u0438u00a0 objects of the natural environment, biological activity components, u0437u0430u0433u0440u00a0u0437u043du00a0u044eu0449u0438u0445 objects of the environment, u043fu0440u00a0u043cu043eu0433u043e environmental and u043fu0440u00a0u043cu043eu0433u043e economic damages in spatial and temporal scale.;2. method for u043eu0442u043bu0438u0447u0430u044eu0449u0438u0439u0441u00a0 1, however, that in determining the biological activity test object u043fu0440u043eu0432u043eu0434u00a0u0442 standardization conditions u043fu043eu043bu0443u0447u0435u043du0438u00a0 equilibrium solution s directly in the experiment or by converting the known methods of fixed parameters (temperature, u0434u0430u0432u043bu0435u043du0438u00a0 air, u0441u043eu043eu0442u043du043eu0448u0435u043du0438 u00a0 volume gas environment or the mass of solid material and so on.with the level of u0440u0430u0441u0442u0432u043eu0440u0438u0442u0435u043bu00a0 to obtain equilibrium solutions) to the standard (normal) values, for example the temperature 25u0441, u0434u0430u0432u043bu0435u043du0438u00a0 1 h and etc, and then convert to u0442u0430u043du0434u0430u0440u0442u043du044bu043c u0443u0441u043bu043eu0432u0438u00a0u043c factor biological activity and biological activity testing environment.;3. method for u043fu043f.1 and 2, u043eu0442u043bu0438u0447u0430u044eu0449u0438u0439u0441u00a0, u043fu0440u00a0u043cu043eu0439 environmental damage u043eu043fu0440u0435u0434u0435u043bu00a0u044eu0442 on the basis of information on the u0432u043bu0438u00a0u043du0438u0438 u0437u0430u0433u0440u00a0u0437u043du0435u043du0438u00a0 individual and / or all objects u043eu043au0440u0443u0436u0430u044eu0449u0435 in the natural environment.;4. method for u043fu043f.1 - 3, u043eu0442u043bu0438u0447u0430u044eu0449u0438u0439u0441u00a0, u043fu0440u00a0u043cu043eu0439 economic damage u043eu043fu0440u0435u0434u0435u043bu00a0u044eu0442 under experimental or calculated value of the environmental information found technical damage, taking into account the u0432u043bu0438u00a0u043du0438u00a0 u0437u0430u0433u0440u00a0u0437u043du0435u043du0438u00a0 individual and / or all objects in the environment or on the basis of the biological u0430u043au0442u0438u0432u043du043eu0441 u0438u0437u043cu0435u043du0435u043du0438u00a0 you u0437u0430u0433u0440u00a0u0437u043du00a0u044eu0449u0438u0445 substances u0434u043bu00a0 individuals of all the species.;5. method for ap.1 - 4, u043eu0442u043bu0438u0447u0430u044eu0449u0438u0439u0441u00a0, forecasting u0438u0437u043cu0435u043du0435u043du0438u00a0 u0441u043eu0441u0442u043eu00a0u043du0438u00a0 u0437u0430u0433u0440u00a0u0437u043du0435u043du0438u00a0 objects of the environment and / or u043fu0440u00a0u043cu043eu0433u043e environmental damage and / or u043fu0440u00a0u043cu043eu0433u043e the economic damage on the basis of kinetic parameters u043fu0440u043eu0432u043eu0434u00a0u0442 specifically u0434u043bu00a0 each u0441u043bu0443u0447u0430u00a0 environmental change in the u043fu0440u0430u0432u043eu043du0430u0440u0443u0448u0435u043du0438u00a0 menny and space u0437u0430u0433u0440u00a0u0437u043du00a0u044eu0449u0438u0445 biological activity substances in one.two or all three objects of the environment and the subsequent calculation of projection u0438u0437u043cu0435u043du0435u043du0438u00a0 situation in spatial and temporal scale.
机译:1.方法 u043e u043f u0440 u0435 u0434 u0435 u043b u0435 u043d u0438 u00a0系数敏感性生物传感器,固体材料和气体环境的生物活性, u043f u0440 u00a0 u043c u043e u0433 u043e环境和 u043f u0440 u00a0 u043c u043e u0433 u043e eco u043d u043e u043c u0438 u0447 u0435 u0441 u043a u043e u043e u0433 u043e物体对自然环境的损害 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u0435 u043d u043d u0438 u0438,预测 u0438 u0437 u043c u0435 u043d u0435 u043d u043d u0438 u00a0 u0441 u043e u044 u0442 u043e u00a0 u043d u0438 u00a0 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u0435 u043d u043d u0438 u00a0天然sr食物的对象, uc043f u0440 u00a0 u043 u0433 u043e u043f u0440 u00a0 u043c u043e u0433 u043e对环境和经济的损害,包括选择 u0431 u0438 u043e u0441 u0435 u043d u0441 u0431 u043e u0440 u0430到 u0443 u0441 u043b u043e u0432 u0438 u00a0 u043c改编 u0431 u0438 u043e u0441 u04 35 u043d u0441 u043e u0440 u0430实验中,在 u0442 u0435 u043e u0440 u0430中引入了 u0431 u0438 u043e u044e u0441 u0435 u043d u043d u0441 u043e u0440 u0430 u0443 u0435 u043c u044b u0435和控制对象,同时在 u0442 u043e u043e u0440 u0430 u0431 u0438 u043e u043e u0441 u0435 u043d u0441 u043e u043e u0440 u0430在给定时间内被测对象和对照对象中的u0442 u0432 u0435 u043d u043d u044b u0445 u0443 u0441 u043b u043e u0432 u0438 u00a0 u0445 u0440 u0430 u043c u0435 tra(响应)生物传感器对被测对象中成分的影响相对响应的依赖性 u0431 u0438 u043e u0441 u0435 u043d u0441 u043e u0440 u0430 u043f u043e u0441 u0442 u043e u00a0 u043d u043d u043e u0433 u043e的定义, u0431 u0438 u043e u043b u043e活动成分说明的定义,然后是生物活性的定义测试环境中的y成分是生物系数ak乘以被测对象中的成分浓度 u043e u0442 u043b u0438 u0447 u0430 u044e u0449 u0438 u0439 u0441 u00a0顺序 u0434 u043b u00a0 u043e u043f u0440 u0435 u0434 u0434 u0435 u043b u0435 u043d u043d u0438 u00a0使用一个 u0441 u043e u0435 u0434 u0434的溶液的系数灵敏度生物传感器u043d u0435 u043d u0438 u00a0或化合物的混合物 u043f u043e u0431 u0441 u0442 u043e u00a0 u043d u043d u043d u043e u0433 u043e在测试和测试中不同生物传感器相对响应的组成和功能依赖性 u0434 u043b u00a0 u043e u043f u0440 u0435 u0434 u0435 u043b u0435 u0435 u043d u0438 u00a0固体材料和气体环境的生物活性 u0442 u0435 u0441 u0442 u0438 u0440 u0443 u0435 u043c u044b u0435对象 u0433 u043e u0442 u043e u0432 u00a0 u0442以平衡溶液的形式进行测量 u043a u043e u043d u0442 u0430 u043a中的ns,具有已知数量的r u0430 u0441 u0442 u0432 u043e u0440 u0438 u0442 u0435 u043b u00a0例如,水在控制模型可以作为溶剂的基础上,基于测试和 u043a u043e u043d u0442 u0440 u043e中相对响应生物传感器的功能依赖性 u043b u044c u043d哦,最初的样品浓度 u043d u0430 u0445 u043e u0434 u00a0 u0442 u0440 u0430 u0432 u043d u043e u0432 u0432 u0435 u0441 u043d u043d u043e u043c溶液。然后,生物活性比率对成分浓度的乘积就是 u0440 u0430 u0432 u043d u043e u0432 u0435 u0431 u043d u043e u043c中的生物活性成分r u0430 u0441 u0442 u0432 u043e u0440 u0435, u0440 u0430 u0432 u043d u043e u0432 u0432 u0435 u0441 u043d u043e u04中的生物活性成分3c溶液 u043e u043f u0440 u0435 u0434 u0435 u043b u00a0 u044e u0442固体物质或气体环境中的生物活性成分对固体物质或气体环境中的生物活性的影响 u043e u043f u0440 u0435 u0434 u0435 u043b u00a0 u044e u0442每个生物物种的幸存者和死亡标本数量,对于 u043e u043e u043f u0440 u0435 u0434 u0435 u043b u00a0 u044e u0442 u043f u0440 u00a0 u043c u043e u0439对环境造成的损害u043f u0440 u0435 u0434 u0435 u043b u00a0 u044e u0442 u043f u0440 u00a0 u043c u043e u0439经济损失对所有生物物种死亡数的影响(每个数字具有固定值)种是一种生物,或者是根据每个活生物体的已故个体相对大小的依赖关系从生物活性测试对象中预定的对象中确定的。 u043e u00a0 u043d u043d u044b u0445或变量 u043d u043e u0440 u043c u0438 u0440 u043e u0432 u0430 u043d u043d u044b u0445 u0445 u043a u043e u044d u0444 u044d u0438 u0446 u0438 u0435 u043d u0442 u0430 u0445的生物活性范围,例如,每种生物的毒性,然后是 u043f u0440 u043e u0432 u043e u0434 u00a0 u0442预测 u0438 u0437 u043c u0435 u043d u0435 u043d u0438 u00a0 u0441 u043e u0441 u0441 u0442 u043e u00a0 u043d u0 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u0435 u043d u0438 u00a0对象,生物活性成分, u0437 u0430 u0433 u0440 u00a0 u0437 u043d u00a0 u044e u0449 u0438 u0445环境对象, u043f u0440 u00a0 u043c u043e u043e u0433 u043e环境和 u043f u0440 u00a0 u043c u043e u0433 u043e在时空尺度上造成经济损失。; 2 。 u043e u0442 u043b u0438 u0447 u0430 u044e u0449 u0438 u0439 u0441 u00a0 1的方法,然而,在确定生物活性测试对象 u043f u0440 u043e u043e u0432 u0432 u043e u0434 u00a0 u0442标准化条件 u043f u043e u043b u0443 u0447 u0435 u043d u0438 u00a0平衡溶液s直接在实验中或通过转换已知的固定参数方法(温度, u0434 u0430 u0432 u043b u0435 u043d u0438 u00a0空气, u0441 u043e u043e u0442 u043d u043d u043e u0448 u0435 u043d u0438 u00a0气体环境体积或固体物质的质量等 u0440 u0430 u0441 u0442 u0432 u043e u0440 u0438 u0442 u0435 u043b u00a0以获得标准(正常)值的平衡溶液,例如温度25 u0441, u0434 u0430 u0432 u043b u0435 u043d u0438 u00a0 1小时等,然后转换为 u0442 u0430 u043d u0434 u0430 u0440 u0442 u043d u044b u043c u0443 u0441 u043b u043e u0432 u0438 u00a0 u043c因子生物学活性和生物活性测试环境;; 3。 u043f u043f.1和2的方法, u043e u0442 u043b u0438 u0447 u0430 u044e u0449 u0438 u0439 u0441 u00a0, u043f u0440 u00a0 u043c u043c u043e u0439 u043e u043f u0440 u0435 u0434 u0435 u043b u00a0 u044e u0442基于 u0432 u043b u0438 u00a0 u043d u0438 u0438 u0437 u0430 u0433 u0440 中的信息u00a0 u0437 u043d u0435 u043d u0438 u00a0个人和 /或所有对象 u043e u043a u0440 u0443 u0436 u0430 u044e u0449 u0435。 u043f u043f.1-3的方法, u043e u0442 u043b u0438 u0447 u0430 u044e u0449 u0438 u0439 u0441 u00a0, u043f u0440 u00a0 u043c u043e u0439经济损失 u043e u043f u0440 u0435 u0434 u0435 u043b u00a0 u044e u0442在对环境信息进行实验或计算得出的值中发现了技术损害,同时考虑了 u0432 u043b u0438 u00a0 u043d u0438 u00a0 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u0435 u043d u0438 u00a0个人或 /或环境中的所有对象,或基于生物 u0430 u043a u0442 u0438 u0432 u043d u043e u0441 u0438 u0437 u043c u0435 u043d u0435 u043d u043d u0438 u00a0您 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u043d u00a0 u044e u0449 u0438所有物种的个体; 5。 ap.1-4的方法, u043e u0442 u043b u0438 u0447 u0430 u044e u0449 u0438 u0439 u0441 u00a0,预测 u0438 u0437 u043c u0435 u043d u043d u0435 u043d u0438 u00a0 u0441 u043e u0441 u0442 u043e u00a0 u043d u0438 u00a0 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u043d u0435 u043d u043d u0438 u00a0对象和环境对象 u043f u0440 u00a0 u043c u043e u0433 u043e基于动力学参数 u043f u0440 u043e 或 u043f u0440 u043e u043e u043e u0433 u043e经济损失u0432 u043e u0434 u00a0 u0442特别是 u0434 u043b u00a0每个 u0441 u043b u0443 u0447 u0430 u00a0环境更改在 u043f u0440 u0430 u0430 u0432 u043e u043d u0430 u0440一个或两个或全部三个对象的生物活性物质中的u0443 u0448 u0435 u043d u0438 u00a0和空间 u0437 u0430 u0433 u0440 u00a0 u0437 u043d u043a u04e环境和投影的后续计算 u0438 u0437 u043c u0435 u043d u0435 u043d u0438 u00a0时空尺度的情况。

著录项

  • 公开/公告号RU2003124356A

    专利类型

  • 公开/公告日2005-03-10

    原文格式PDF

  • 申请/专利号RU20030124356

  • 发明设计人

    申请日2003-08-07

  • 分类号G01N33/50;

  • 国家 RU

  • 入库时间 2022-08-21 22:02:38

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