CN112836441A - Ecological scheduling simulation analysis method of river channel model - Google Patents

Ecological scheduling simulation analysis method of river channel model Download PDF

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CN112836441A
CN112836441A CN202011630554.1A CN202011630554A CN112836441A CN 112836441 A CN112836441 A CN 112836441A CN 202011630554 A CN202011630554 A CN 202011630554A CN 112836441 A CN112836441 A CN 112836441A
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黄膺翰
傅利
肖武
颜剑波
李翔
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Abstract

The invention discloses an ecological scheduling simulation analysis method of a river channel model, which enables designers to simulate hydrodynamics work such as water level, flow velocity and the like in a river channel when each cascade scheduling scheme changes in an ecological scheduling process and provides data support for fine analysis and optimal design of the scheduling scheme.

Description

Ecological scheduling simulation analysis method of river channel model
Technical Field
The invention relates to the field of model analysis, in particular to an ecological scheduling simulation analysis method of a river channel model.
Background
With the development of the hydropower construction industry in China, a plurality of gate dams are built on the domestic main rivers. The hydraulic association of the gate dams is tight, so that a step joint scheduling research needs to be developed, the scheduling mode of each power station on the river is optimized, and the power generation, shipping and ecological benefits of each step are brought into play to the maximum extent.
Simulation analysis is one of the important means of the cascade joint scheduling research. Through simulation analysis, simulation analysis can be carried out on various cascade scheduling schemes, the implementation effect of the schemes is evaluated, and the method has important significance on comparison and selection and optimization of the cascade scheduling schemes.
However, the step joint scheduling research has a difficulty that the scheduling procedure of each step is changed along with time in the joint ecological scheduling process. Generally, when the ecological dispatching is started, each step starts to increase the drainage flow rate to form an artificial flood peak. Even part of the steps can fully empty the reservoir, and the open state is achieved. And in the later stage of ecological scheduling, each step is gradually closed to store water, and the power generation state is recovered.
At present, the existing river simulation analysis software in the industry, such as SWMM, MIKE, HEC-RAS and the like, cannot perform simulation analysis on the model with the complex scheduling scheme changing along with time. This severely restricts the development of fine analysis and optimization design work of the scheduling scheme. Therefore, it is urgently needed to develop a simulation analysis method, so that designers can simulate hydrodynamic work such as water level, flow velocity and the like in a river channel when each step scheduling scheme changes in the ecological scheduling process, and provide data support for fine analysis and optimization design of the scheduling scheme.
Disclosure of Invention
In order to solve the problem that the existing river simulation analysis software in the background technology cannot perform simulation analysis on the model which is complex and the scheduling scheme of which changes along with time, the invention provides an ecological scheduling simulation analysis method of a river model, and the specific technical scheme is as follows.
An ecological scheduling simulation analysis method of a river channel model is characterized by comprising the following steps:
s1, respectively increasing an upstream section and a downstream section of the gate dam at the upstream and downstream of the river channel model gate dam, and sequentially connecting the upstream section, the downstream section and the downstream section;
s2, connecting a water inlet end of a pump in the river channel model with the upstream section of the gate dam, and connecting a water outlet end with the downstream section of the gate dam;
s3, initializing and setting the section bottom elevation of each gate dam in the river channel model and the capacity curve of the pump according to each cascade scheduling regulation;
s4, calculating the flow, water level and flow velocity of each section in the river channel model at the current time step;
if the cascade scheduling rules of the next time step of the current time step change, reloading the model according to the water level data of each section of the current time step and the flow data of each river reach, resetting the section bottom elevation and the pump capacity curve of each gate dam in the river channel model according to the cascade scheduling rules of the next time step, and calculating the flow, the water level and the flow speed of each section in the river channel model of the next time step;
if the scheduling rules of each step of the next time step of the current time step are not changed, directly calculating the flow, water level and flow rate of each section in the river channel model of the next time step;
and S5, repeating the step S4 until the flow, the water level and the flow speed of each section in the river channel model at the last time step are calculated, finishing the calculation and outputting the flow, the water level and the flow speed of each section in the river channel model at all time steps.
By the method, designers can simulate hydrodynamic work such as water level, flow velocity and the like in the river channel when each cascade scheduling scheme changes in the ecological scheduling process, and data support is provided for fine analysis and optimal design of the scheduling scheme
Specifically, in S3 and S4, the setting method of the section bottom elevation of each gate dam and the capacity curve of the pump is specifically as follows:
when the gate dam begins to empty the reservoir capacity, setting the bottom elevation of the gate dam section as an operating water level, and setting the pump as the maximum downward discharge flow;
when the gate dam enters an open-drain state, setting the bottom elevation of the cross section of the gate dam as the river bed elevation, and closing the pump;
when the gate dam is restored to the normal water storage level, the section bottom elevation of the gate dam is set as the running water level, and the running water level h of the gate dam is used as the running water level0The water level amplitude dh and the lower discharge Q set the capacity curve of the pump:
when the water level is h0-dh/n1When the flow rate is set to Qn2
When the water level is h0When, the flow rate is set to Q;
when the water level is h0+dh/n3When the flow rate is set to Qn4
Wherein, 1 is more than n1<100、0<n2<1、1<n3<100、1<n4<10。
Preferably, the depth body point of the downstream section of each gate dam is set to a normal water level or a blocking elevation of the gate dam after the bottom elevation of the section of each gate dam and the capacity curve of the pump are reset.
Preferably, the step of setting the distance between the upstream section of the gate dam and the downstream section of the gate dam to the width of the gate dam is further included in S1.
Based on the same inventive concept, the present invention also provides a computer storage medium storing a program for executing the steps of the above-described method.
Due to the adoption of the technical scheme, compared with the prior art, the method and the system enable designers to simulate the hydrodynamics work of water level, flow velocity and the like in the river channel when each step scheduling scheme changes in the ecological scheduling process, and provide data support for fine analysis and optimal design of the scheduling scheme.
Drawings
Fig. 1 is a schematic flow chart of an ecological scheduling simulation analysis method of a river model according to the present invention;
fig. 2 is an overall schematic view of a river model according to an embodiment of the present invention;
fig. 3 is a schematic diagram of a treegarden home terminal in a river model according to an embodiment of the present invention.
Detailed Description
The present invention is described in further detail below with reference to the attached drawing figures.
The embodiment of the method is carried out by depending on the combination of the dry flow cascade ecological power stations in the middle and lower reaches of Hanjiang. The research range of the dry flow cascade combined ecological dispatching in the middle and lower reaches of the Han river is mainly characterized in that the middle and lower reaches of the Han river section below the Danjiang river mouth comprises 2 cascade hydraulic cascade hubs of a Rui Jiaying and Xinglong, and the research river section is about 652km in length. During ecological scheduling, each step scheduling procedure is as follows:
(1) the Xinglong and the standing-up hub start to open the gate and drain water at the same time, and the drainage flow does not exceed 4700m3(s) until entering an open-drain state;
(2) after the flood process is performed by the bloom, the standing and camping, the two hubs start to store water from top to bottom, and the ecological flow discharged downwards during the water storage period is 4700m3/s;
(3) The Xinglong and the Runjiao are reclaimed and stored to the normal water storage level (62.73 m and 36.20m respectively), and the ecological flow is kept at 2000m during the water storage period3And/s, finishing the dispatching when the normal water storage level is reached.
The method comprises the following specific implementation steps:
firstly, a river channel model of a 2-step water conservancy step junction needs to be established, wherein the river channel model is as shown in a figure 2; as shown in fig. 3, the treegarden camping station is located between the upstream section HJ59 and the downstream section HJ 60.
The method for establishing the model of the Hanjiang river channel in the research area can refer to the following documents:
the Application of SWMM model in urban rainwater drainage system analysis is characterized by Application of SWMM in urban storm roof network model [ J ]. water supply and drainage, 2009,035(005): 198-.
②Temprano J,Arango,
Figure BDA0002874588230000051
Cagiao J,et al.Stormwater quality calibration by SWMM:A case study in Northern Spain[J].Water Sa,2007,32(1)。
Then, according to the ecological scheduling simulation analysis method of the river channel model disclosed by the invention, simulation analysis is carried out on the river channel model, and the method specifically comprises the following steps:
s1, deleting a connecting line (link of a river section where the gate dam is located) between an upstream section and a downstream section of the river section where the gate dam is located in the river channel model, respectively adding a gate dam upstream section (node) CuiJianying-U and a gate dam downstream section (node) CuiJianying-D at the upstream and downstream of the gate dam, and sequentially connecting the upstream section HJ59, the gate dam upstream section CuiJianying-U, the gate dam downstream section CuiJianying-D and the downstream section HJ 60; the distance between the upstream section CuiJianying-U of the gate dam and the downstream section CuiJianying-D of the gate dam is the width of the gate dam.
S2, arranging a pump (pum), wherein the water inlet end of the pump is connected with the upstream section CuiJianying-U of the gate dam, and the water outlet end of the pump is connected with the downstream section CuiJianying-D of the gate dam.
And S3, initializing and setting the section bottom elevation of each gate dam and the capacity curve of the pump according to each cascade scheduling regulation. The method for setting the section bottom elevation of each gate dam and the capacity curve of the pump comprises the following specific steps:
when the gate dam begins to empty the reservoir capacity, setting the bottom elevation of the gate dam section as an operating water level, and setting the pump as the maximum downward discharge flow;
when the gate dam enters an open-drain state, setting the bottom elevation of the cross section of the gate dam as the river bed elevation, and closing the pump;
when the gate dam is restored to the normal water storage level, the section bottom elevation of the gate dam is set as the running water level, and the running water level h of the gate dam is used as the running water level0The water level amplitude dh and the lower discharge Q set the capacity curve of the pump:
when the water level is h0-dh/n1When the flow rate is set to Qn2
When the water level is h0When, the flow rate is set to Q;
when the water level is h0+dh/n3When the flow rate is set to Qn4
Wherein, 1 is more than n1<100、0<n2<1、1<n3<100、1<n4<10。
Specifically, a water level-flow rate correspondence is selected. According to the dispatching principle of the parent house and the hydropower stationThen, the corresponding relation setting of the water level-flow is shown in table 1. Specifically, considering that the dead water level of the Ruan home is 62.23m, 470m of drainage is needed at least for ensuring navigation3S, therefore, the reservoir area downstream bleed down flow rate 470m is set at a water level of 62.23m3And s. When the normal water storage level is reached, the generator is in a power generation state, and the maximum power generation flow of the generator set is 2200m3And s. When the warehousing flow is more than 2200m3When the water level is over the set/s, the water level is continuously raised only by the unit discharge water level, so that the power station enters a flood discharge state, a water level interval of 62.73-63.23 m is set, and the discharge flow rate is 2200m3The number of/s increases to 10000m3/s。
Water level (m) Flow rate (m)3/s)
62.23 500
62.73 2200
63.23 10000
TABLE 1A measuring family camp curve data sheet
The normal water level of the treegarden camping power station hub is 62.73m, so the deep body point (Invert E) I of CuiJianying-D is set to 62.73 m. When the upstream water level is higher than 62.73m, the water can overflow to the downstream river channel. The boom setting steps are similar to those of a family camp and are not repeated. The main difference is that the elevation of the section bottom is different from the capacity curve (pum curve).
Water level-to-flow pairs according to the Xinglong power station dispatching principleThe corresponding relationship settings are shown in table 2. Specifically, considering that the rising dead water level is 34.70m, 420m need to be discharged at least for ensuring navigation3S, therefore, the reservoir area downstream bleed down flow rate 420m is set when the water level is 34.70m3And s. When the normal water storage level is reached, the generator is in a power generation state, and the maximum power generation flow of the generator set is 2800m3And s. When the warehousing flow is more than 2800m3When the water level is changed to be 36.20-37.70 m, the water level interval is set, and the downward discharge flow is 2800m3The number of/s increases to 10000m3/s。
Water level (m) Flow rate (m)3/s)
34.70 420
36.20 2800
37.70 10000
Table 2 xing Long pu curve data table
And each step scheduling regulation is set as a fixed lower discharge rate of 4700m3/s。
S4, calculating the flow, water level and flow rate of each section in the river channel model at the current time step in the SWMM;
if the cascade scheduling rules of the next time step of the current time step change, reloading the model according to the water level data of each section of the current time step and the flow data of each river reach, resetting the section bottom elevation and the pump capacity curve of each gate dam in the river channel model according to the cascade scheduling rules of the next time step, and calculating the flow, the water level and the flow speed of each section in the river channel model of the next time step;
if the scheduling rules of each step of the next time step of the current time step are not changed, directly calculating the flow, water level and flow rate of each section in the river channel model of the next time step;
specifically, when the third hour is calculated, the scheduling procedure changes: at this time, the user is left empty. Therefore, the calculation is finished, the SWMM is closed, and the water level of each section and the flow data of each river reach at the last time step in the calculation result are extracted to obtain the data in tables 3 and 4 (only part of the data is shown because the data amount is large).
Figure BDA0002874588230000081
TABLE 3 Link flow data sheet
Figure BDA0002874588230000082
TABLE 4 Water level data table for each node (section)
And covering the extracted node (section) water level data into an Elevation column of a model file (JUNCTIONS) tab, and covering link (river reach) flow data into a CONDUITS tab and storing the link (river reach) flow data. And starting SWMM software and loading a new model file. And resetting the elevation of the bottom of the section of each gate dam and the capacity curve of the pump according to the setting method of the elevation of the bottom of the section of each gate dam and the capacity curve of the pump. Specifically, the bottom elevation of the node (cross section) of the treegarden house is set as the river bed elevation, pum (pump) is closed, and then the flow, water level and flow speed of each cross section in the river channel model at the next time step are calculated.
Calculating the prosperous warehouse to the 18 th hour, and needing to enter an open relief state, then setting the bottom elevation of the prosperous hub node (section) as the river bed elevation, closing pum (pump), and then calculating the flow, water level and flow rate of each section in the river channel model at the next time step.
Calculating the flood peak border of 0 hour till the 10 th day, starting water storage, setting the bottom elevations of the nodes (sections) of the treegarden home and the Xinglong hub as respective normal water storage levels, starting pum (pumps), setting pum (pumps) curves as shown in table 2, and then calculating the flow, water level and flow speed of each section in the river channel model at the next time step.
And S5, repeating the step S4 until the flow, the water level and the flow speed of each section in the river channel model at the last time step are calculated, finishing the calculation and outputting the flow, the water level and the flow speed of each section in the river channel model at all time steps.
Specifically, 30 minutes after 12 days 12, the calculation is judged to be the last time step, the calculation is finished, and the flow, the water level and the flow speed of each section in the river channel model at all the time steps are output, so that the ecological scheduling simulation analysis result of the river channel model is obtained.
Finally, it should be noted that: the above examples are only intended to illustrate the technical solution of the present invention, but not to limit it; although the present invention has been described in detail with reference to the foregoing embodiments, it will be understood by those of ordinary skill in the art that: the technical solutions described in the foregoing embodiments may still be modified, or some technical features may be equivalently replaced; and such modifications or substitutions do not depart from the spirit and scope of the corresponding technical solutions of the embodiments of the present invention.

Claims (5)

1. An ecological scheduling simulation analysis method of a river channel model is characterized by comprising the following steps:
s1, respectively increasing an upstream section and a downstream section of the gate dam at the upstream and downstream of the river channel model gate dam, and sequentially connecting the upstream section, the downstream section and the downstream section;
s2, arranging a pump in the river channel model, connecting a water inlet end of the pump with the upstream section of the gate dam, and connecting a water outlet end of the pump with the downstream section of the gate dam;
s3, initializing and setting the section bottom elevation of each gate dam in the river channel model and the capacity curve of the pump according to each cascade scheduling regulation;
s4, calculating the flow, water level and flow velocity of each section in the river channel model at the current time step;
if the cascade scheduling rules of the next time step of the current time step change, reloading the model according to the water level data of each section of the current time step and the flow data of each river reach, resetting the section bottom elevation and the pump capacity curve of each gate dam in the river channel model according to the cascade scheduling rules of the next time step, and calculating the flow, the water level and the flow speed of each section in the river channel model of the next time step;
if the scheduling rules of each step of the next time step of the current time step are not changed, directly calculating the flow, water level and flow rate of each section in the river channel model of the next time step;
and S5, repeating the step S4 until the flow, the water level and the flow speed of each section in the river channel model at the last time step are calculated, finishing the calculation and outputting the flow, the water level and the flow speed of each section in the river channel model at all time steps.
2. The ecological scheduling simulation analysis method of the river channel model according to claim 1, wherein: in S3 and S4, the setting method of the section bottom elevation of each gate dam and the capacity curve of the pump is specifically as follows:
when the gate dam enters an open-drain state, setting the bottom elevation of the gate dam section as the river bed elevation;
when the gate dam is restored to the normal water storage level, the gate dam operates according to the operation water level h0The water level amplitude dh and the lower discharge Q set the capacity curve of the pump:
when the water level is h0-dh/n1When the flow rate is set to Qn2
When the water level is h0When, the flow rate is set to Q;
when the water level is h0+dh/n3When the flow rate is set to Qn4
Wherein, 1 is more than n1<100、0<n2<1、1<n3<100、1<n4<10。
3. The method of claim 2, wherein the deepbody site of the downstream section of the gate dam is set to a normal impoundment level or a barrage elevation of the gate dam after the bottom elevation of the section of each gate dam and the capability curve of the pump are reset.
4. The ecological scheduling simulation analysis method of the river channel model according to claim 1 or 2, wherein: the step of S1 further includes setting a distance between an upstream cross section of the gate dam and a downstream cross section of the gate dam to a gate dam width.
5. A computer storage medium, characterized in that it stores a program for executing the steps of the method according to any one of claims 1 to 4.
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