CN106990216A - A kind of shallow lake wawter bloom risk analysis early warning system and its analysis and early warning method - Google Patents
A kind of shallow lake wawter bloom risk analysis early warning system and its analysis and early warning method Download PDFInfo
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Abstract
本发明公开一种浅水湖泊水华风险分析预警系统及其分析预警方法,系统包括数据汇集模块和数据挖掘模块,数据汇集模块由常规监测装置、声学遥测装置和辅助装置组成,数据挖掘模块由驱动因子识别单元、驱动因子适宜区间确定单元、驱动因子独立效应量化单元、环境驱动模式分析比较单元和水华风险评估单元组成。本发明实现环境因子高空间分辨率监测的同时避免了传统环境监测方法面临的硬件设施大规模布设问题,水华预警误报、漏报率低,可服务于浅水湖泊水华灾害防治与水资源管理。
The invention discloses a risk analysis and early warning system for algal blooms in shallow lakes and an analysis and early warning method thereof. The system includes a data collection module and a data mining module. The data collection module is composed of a conventional monitoring device, an acoustic telemetry device and an auxiliary device. The data mining module is driven by It is composed of factor identification unit, driving factor suitable interval determination unit, driving factor independent effect quantification unit, environmental driving mode analysis and comparison unit and algal bloom risk assessment unit. The invention realizes the high spatial resolution monitoring of environmental factors while avoiding the large-scale deployment of hardware facilities faced by traditional environmental monitoring methods, and has a low rate of misreporting and false alarms for early warning of algae blooms, and can serve the prevention and control of algal bloom disasters in shallow lakes and water resources. manage.
Description
技术领域technical field
本发明属于水环境保护技术领域,具体涉及一种浅水湖泊水华风险分析预警系统及其分析预警方法。The invention belongs to the technical field of water environment protection, and in particular relates to a risk analysis and early warning system for algal blooms in shallow water lakes and an analysis and early warning method thereof.
背景技术Background technique
在全球范围内,越来越多的浅水湖泊出现不同程度的富营养化特征,水华暴发频次和规模都在增加,该问题已经成为社会关注的一个焦点。水体富营养化是指水体所包含的营养物质浓度过高的状态,易于导致水生植物快速生长、水质恶化和水生态系统平衡破坏。富营养化湖泊中的浮游植物在适宜条件下快速生长并积聚,即产生水华现象。水华暴发的负面影响已为学术界与大众熟知,包括供水危机、水体变色、水体缺氧和鱼类死亡等。Globally, more and more shallow lakes are characterized by varying degrees of eutrophication, and the frequency and scale of algal blooms are increasing. This problem has become a focus of social attention. Eutrophication of water body refers to the state where the concentration of nutrients contained in water body is too high, which is easy to lead to rapid growth of aquatic plants, deterioration of water quality and destruction of water ecosystem balance. Phytoplankton in eutrophic lakes grow rapidly and accumulate under suitable conditions, which is called algal bloom. The negative impacts of algal blooms are well known to academics and the general public, including water supply crisis, discoloration of water bodies, lack of oxygen in water bodies, and fish kills.
浮游植物生长涉及物理及化学因子对其生理需求的满足程度,也受浮游动物捕获影响,因而水华暴发可视为藻类对水体环境的响应。然而湖泊所处环境的不断改变对其生态系统的影响愈发强烈。一方面,人类活动显著增加了进入湖泊水体限制性营养盐(如氮、磷等)的通量,从而为消除藻类快速生长限制埋下伏笔。另一方面,高温条件下蓝藻生长速率得到加大、水体垂向紊动受到抑制且水体粘滞性有所减弱,为蓝藻生长创造了有利条件,因此全球气候变暖很可能加重富营养化湖泊的蓝藻水华危害。The growth of phytoplankton involves the satisfaction of physical and chemical factors to their physiological needs, and is also affected by the capture of zooplankton. Therefore, algae blooms can be regarded as the response of algae to the water environment. However, the continuous change of the lake's environment has an increasingly strong impact on its ecosystem. On the one hand, human activities have significantly increased the flux of limiting nutrients (such as nitrogen, phosphorus, etc.) into lake water, thus paving the way for the elimination of the rapid growth of algae. On the other hand, under high temperature conditions, the growth rate of cyanobacteria is increased, the vertical turbulence of the water body is suppressed, and the viscosity of the water body is weakened, which creates favorable conditions for the growth of cyanobacteria. Therefore, global warming is likely to aggravate the eutrophication of lakes. cyanobacteria bloom hazard.
目前浅水湖泊水华预警所需的基础环境信息往往通过两种主要途径获取,一是卫星影像反演,二是水体定点监测。前者从数据获取角度来说比较方便,但现有反演方法有着极大的不确定性,得出的环境因子数据伴随较大误差;同时,卫星影像反演还受到不良天气(阴、雨、雪等)的极大制约。水体定点监测一般而言精度较高,数据获取相对来说也更为可靠、稳定,但该方法在满足环境因子高空间分辨率监测的需求下必然导致基础设施的密集布设问题,带来高昂的环境监测成本。在预警方法选择上,基于过程的水质模型具有较好的理论基础,但在实际应用时面临计算耗时长、参数难以估计等诸多问题;数据驱动方法可以实现水华风险高效预警,但在极端情况下得出的结果往往并不理想。鉴于此,针对浅水湖泊日益突出的富营养化和水华问题,提供一种新的浅水湖泊水华风险分析预警系统和方法显得尤为迫切。At present, the basic environmental information required for early warning of algae blooms in shallow lakes is often obtained through two main methods, one is satellite image inversion, and the other is fixed-point monitoring of water bodies. The former is more convenient from the perspective of data acquisition, but the existing inversion methods have great uncertainty, and the obtained environmental factor data is accompanied by large errors; at the same time, satellite image inversion is also affected by bad weather (cloudy, rainy, Great constraints from snow, etc.). Generally speaking, fixed-point monitoring of water bodies has high precision, and data acquisition is relatively more reliable and stable. However, this method will inevitably lead to the problem of intensive infrastructure deployment under the condition of meeting the needs of high spatial resolution monitoring of environmental factors, which will bring high costs. environmental monitoring costs. In the selection of early warning methods, the process-based water quality model has a good theoretical basis, but it faces many problems such as long calculation time and difficult parameter estimation in practical application; data-driven methods can realize efficient early warning of algae bloom risk, but in extreme cases The results obtained below are often not ideal. In view of this, it is particularly urgent to provide a new shallow lake algal bloom risk analysis and early warning system and method for the increasingly prominent problems of eutrophication and algal bloom in shallow lakes.
发明内容Contents of the invention
发明目的:本发明的目的在于解决现有技术中存在的不足,提供一种浅水湖泊水华风险分析预警系统及其分析预警方法。Purpose of the invention: The purpose of the present invention is to solve the deficiencies in the prior art and provide a risk analysis and early warning system for algal blooms in shallow lakes and an analysis and early warning method thereof.
技术方案:本发明公开了一种浅水湖泊水华风险分析预警系统,包括数据汇集模块(1)和数据挖掘模块(2);所述数据汇集模块(1)包括常规监测装置(11)、声学遥测装置(12)和辅助装置(13);所述常规监测装置(11)包括浮式站点和桩式站点,共同实时监测浅水湖泊与藻类生长和水华暴发有关的物理和生化信息,该浮式站点为布置在浅水湖泊内等间距方形阵列顶点的浮标,浮标底部装配有多参数水质传感器,桩式站点是指布置在浅水湖泊内2倍浮式站点间距的方形阵列顶点并固定于湖床上的桩体,桩体水下部分装配有多参数水质传感器和叶绿素a传感器,且桩体水上部分装配有多参数气象传感器、光合有效辐射传感器;所述声学遥测装置(12)包括声学标签载体、声学标签和水听器,实时监测声学标签所处位置与藻类生长和水华暴发有关的多重水体物理参数,声学标签载体为浅水湖泊鱼类,声学标签配置水质传感器并使用尼龙扎带固定于声学标签载体的背鳍上,声学标签使用超声波周期性地将其身份识别信息和物理参数监测结果发送至周围水体,水听器布置于各个浮式站点和桩式站点处,水听器方向朝下并没入水中,实时接收周围声学标签所发送的信息;所述辅助装置(13)包括存储设备和通讯设备,均布置于各个浮式站点和桩式站点处,存储设备保存常规监测装置(11)和声学遥测装置(12)的监测数据,通讯设备实现存储设备和数据挖掘模块(2)之间的数据传输;所述数据挖掘模块(2)由驱动因子识别单元(21)、驱动因子适宜区间确定单元(22)、驱动因子独立效应量化单元(23)、环境驱动模式分析比较单元(24)和水华风险评估单元(25)组成;所述驱动因子识别单元(21)根据浅水湖泊环境因子历史监测数据,筛选出与叶绿素a浓度显著关联且驱动水华发生的部分环境因子作为驱动因子;所述驱动因子适宜区间确定单元(22)确定促使叶绿素a浓度处于高位的各个驱动因子的变化范围作为各自的适宜区间;所述驱动因子独立效应量化单元(23)在其他驱动因子限定于各自适宜区间的情况下,量化叶绿素a浓度对每个驱动因子变化的独立响应;所述环境驱动模式分析比较单元(24)分别率定考虑驱动因子对水华发生累加影响、累乘影响或综合影响的三种水华风险模型及各自的临界风险值,比较后给出最优的水华风险模型及其临界风险值;所述水华风险评估单元(25)结合驱动因子实时监测信息和最优水华风险模型得出浅水湖泊当前环境下水华发生风险分布,在水华发生风险大于临界风险值的情况下向湖泊管理部门进行水华预警。Technical solution: The present invention discloses a risk analysis and early warning system for algal blooms in shallow lakes, including a data collection module (1) and a data mining module (2); the data collection module (1) includes a conventional monitoring device (11), an acoustic Telemetry device (12) and auxiliary device (13); Described conventional monitoring device (11) comprises floating station and pile station, monitors the physical and biochemical information relevant to algae growth and algae bloom outbreak in shallow water lake jointly in real time, and this floating The floating station is a buoy arranged at the vertices of a square array at equal intervals in a shallow lake, and the bottom of the buoy is equipped with a multi-parameter water quality sensor. The pile body, the underwater part of the pile body is equipped with a multi-parameter water quality sensor and a chlorophyll a sensor, and the above-water part of the pile body is equipped with a multi-parameter meteorological sensor and a photosynthetically active radiation sensor; the acoustic telemetry device (12) includes an acoustic label carrier, Acoustic tags and hydrophones, real-time monitoring of multiple water body physical parameters related to algae growth and algae blooms at the location of the acoustic tag, the carrier of the acoustic tag is fish in shallow water lakes, the acoustic tag is equipped with a water quality sensor and fixed to the acoustic tag with a nylon cable tie On the dorsal fin of the tag carrier, the acoustic tag uses ultrasonic waves to periodically send its identification information and physical parameter monitoring results to the surrounding water body. The hydrophones are arranged at each floating station and pile station. When submerged in water, the information sent by the surrounding acoustic tags is received in real time; the auxiliary device (13) includes storage equipment and communication equipment, which are all arranged at each floating site and pile site, and the storage equipment preserves the conventional monitoring device (11) and The monitoring data of the acoustic telemetry device (12), the communication equipment realizes the data transmission between the storage device and the data mining module (2); the data mining module (2) is determined by the driving factor identification unit (21) and the suitable interval of the driving factor unit (22), driving factor independent effect quantification unit (23), environmental driving model analysis and comparison unit (24) and algal bloom risk assessment unit (25); Monitor the data, screen out some environmental factors that are significantly associated with the concentration of chlorophyll a and drive the occurrence of water blooms as the driving factor; the suitable range determination unit for the driving factor (22) determines the range of variation of each driving factor that promotes the concentration of chlorophyll a to be at a high level as respective suitable intervals; the driving factor independent effect quantification unit (23) quantifies the independent response of chlorophyll a concentration to the change of each driving factor when other driving factors are limited to their respective suitable intervals; the environmental driving mode analysis and comparison Unit (24) respectively determines the three types of water bloom risk models and their respective critical risk values considering the cumulative impact, multiplicative impact or comprehensive impact of driving factors on the occurrence of water blooms. After comparison, the optimal water bloom risk model and its Critical risk value; described water bloom risk assessment unit (25) draws water bloom occurrence risk distribution under the current environment of shallow lakes in combination with driving factor real-time monitoring information and optimal water bloom risk model, When the risk of algae bloom is greater than the critical risk value, an early warning of algae bloom will be issued to the lake management department.
进一步的,所述声学遥测装置(12)中的声学标签采用长基线测位法进行定位。Further, the acoustic tag in the acoustic telemetry device (12) adopts a long baseline positioning method for positioning.
本发明还公开了一种浅水湖泊水华风险分析预警系统的分析预警方法,具体包括以下步骤:The present invention also discloses an analysis and early warning method of a risk analysis and early warning system for algal blooms in shallow lakes, which specifically includes the following steps:
(一)数据汇集模块(1)的常规监测装置(11)实时监测浅水湖泊与藻类生长和水华暴发有关的物理和生化信息;声学遥测装置(12)对分散在浅水湖泊内的各个声学标签进行实时定位并接收声学标签监测的多重水体物理参数;辅助装置(13)将常规监测装置(11)和声学遥测装置(12)所获取的监测信息保存至存储设备;(1) The conventional monitoring device (11) of the data collection module (1) monitors the physical and biochemical information related to algae growth and algae blooms in shallow lakes in real time; the acoustic telemetry device (12) detects the acoustic tags scattered in shallow lakes Perform real-time positioning and receive multiple physical parameters of water bodies monitored by acoustic tags; the auxiliary device (13) saves the monitoring information acquired by the conventional monitoring device (11) and the acoustic telemetry device (12) to a storage device;
(二)数据挖掘模块(2)调用浅水湖泊环境因子历史监测数据,构建浅水湖泊水华风险模型,按如下步骤执行:(2) Data Mining Module (2) Call the historical monitoring data of environmental factors of shallow lakes to build a risk model of algal blooms in shallow lakes, and perform the following steps:
(a)驱动因子识别单元(21)从数据汇集模块(1)的存储设备调取桩式站点处所有环境因子历史监测数据;(a) The driving factor identification unit (21) retrieves the historical monitoring data of all environmental factors at the pile site from the storage device of the data collection module (1);
(b)驱动因子识别单元(21)基于历史监测数据,采用偏互信息方法筛选出与叶绿素a浓度显著关联且驱动发生的部分环境因子作为驱动因子;(b) The driving factor identification unit (21) uses the partial mutual information method to screen out some environmental factors that are significantly associated with the concentration of chlorophyll a and drive the occurrence of the driving factor based on historical monitoring data;
(c)驱动因子适宜区间确定单元(22)使用正交表设计从历史监测数据中挑选出满足正交性的驱动因子水平组合,利用极差分析得出叶绿素a浓度随单个驱动因子水平变化规律,进而确定促使叶绿素a浓度处于高位的各个驱动因子的变化范围作为各自的适宜区间;(c) The determination unit for the appropriate interval of driving factors (22) uses the orthogonal table design to select the driving factor level combination that meets the orthogonality from the historical monitoring data, and uses the range analysis to obtain the change law of the concentration of chlorophyll a with the level of a single driving factor , and then determine the variation range of each driving factor that promotes the chlorophyll a concentration to be at a high level as their respective appropriate intervals;
(d)驱动因子独立效应量化单元(23)在其他驱动因子限定于各自适宜区间的情况下,量化叶绿素a浓度对各个驱动因子变化的独立响应;(d) the driving factor independent effect quantification unit (23) quantifies the independent response of the chlorophyll a concentration to the change of each driving factor when other driving factors are limited to their respective appropriate intervals;
(e)环境驱动模式分析比较单元(24)在驱动因子独立效应量化单元(23)所提供信息的基础上,采用进化算法分别率定考虑驱动因子对水华发生累加影响、累乘影响或综合影响的三种水华风险模型及各自的临界风险值以保证各个模型对水华发生/不发生的预测准确率最高,比较各自准确率后最终给出最优的水华风险模型及其对应的临界风险值;(e) On the basis of the information provided by the driving factor independent effect quantification unit (23), the environmental driving mode analysis and comparison unit (24) adopts an evolutionary algorithm to determine the accumulative, multiplicative, or comprehensive effects of the driving factors on algae blooms. The three affected algae bloom risk models and their respective critical risk values ensure that each model has the highest prediction accuracy for the occurrence/non-occurrence of algae blooms. After comparing the respective accuracy rates, the optimal algal bloom risk model and its corresponding critical risk value;
(三)数据挖掘模块(2)的水华风险评估单元(25)调用浅水湖泊驱动因子实时监测信息,进行浅水湖泊水华风险分析与预警,按如下步骤执行:(3) The algae bloom risk assessment unit (25) of the data mining module (2) invokes the real-time monitoring information of the driving factors of shallow water lakes to carry out risk analysis and early warning of algae blooms in shallow lakes, and executes according to the following steps:
(A)从数据汇集模块(1)的存储设备调取常规监测装置(11)和声学遥测装置(12)的驱动因子实时监测数据;(A) retrieve the driving factor real-time monitoring data of the conventional monitoring device (11) and the acoustic telemetry device (12) from the storage device of the data collection module (1);
(B)使用克里金插值算法将实时监测数据空间插值到整个湖泊范围;(B) Using Kriging interpolation algorithm to spatially interpolate real-time monitoring data to the entire lake range;
(C)基于环境驱动模式分析比较单元(24)给出的最优水华风险模型计算获得浅水湖泊当前环境下水华发生风险分布,将水华发生风险大于临界风险值的区域识别为预测发生水华区域;(C) Based on the optimal algal bloom risk model given by the environment-driven model analysis and comparison unit (24), the algal bloom risk distribution in the current environment of shallow lakes is obtained, and the areas where the algal algal bloom risk is greater than the critical risk value are identified as predicted algal blooms. Hua area;
(D)若当前预测发生水华区域存在,将浅水湖泊水华发生风险分布以及预测发生水华区域向湖泊管理部门发布。(D) If there are areas where water blooms are currently predicted to occur, release the risk distribution of water blooms in shallow lakes and the areas where water blooms are predicted to occur to the lake management department.
有益效果:本发明实现环境因子高空间分辨率监测的同时避免了传统环境监测方法面临的硬件设施大规模布设问题,水华预警误报、漏报率低,可服务于浅水湖泊水华灾害防治与水资源管理。Beneficial effects: the present invention realizes the monitoring of environmental factors with high spatial resolution while avoiding the large-scale deployment of hardware facilities faced by traditional environmental monitoring methods, and the rate of misreporting and false alarms of algae bloom early warning is low, and it can serve for the prevention and control of algae bloom disasters in shallow lakes and water resource management.
附图说明Description of drawings
图1为本发明的系统结构示意图;Fig. 1 is a schematic diagram of the system structure of the present invention;
图2为本发明的方法流程示意图;Fig. 2 is a schematic flow chart of the method of the present invention;
图3为实施例1中常规监测装置和声学遥测装置的布置方式;Fig. 3 is the arrangement mode of conventional monitoring device and acoustic telemetering device in embodiment 1;
图4为实施例2中水华发生风险分布以及预测发生水华区域。Fig. 4 is the risk distribution of water bloom occurrence in embodiment 2 and the area where water bloom is predicted to occur.
具体实施方式detailed description
下面对本发明技术方案进行详细说明,但是本发明的保护范围不局限于所述的实施例。The technical solution of the present invention will be described in detail below, but the protection scope of the present invention is not limited to the described embodiments.
实施例1:Example 1:
本实施例的一种浅水湖泊水华风险分析预警系统,如图1所示,由数据汇集模块1和数据挖掘模块2组成。A risk analysis and early warning system for algal blooms in shallow lakes in this embodiment, as shown in FIG. 1 , consists of a data collection module 1 and a data mining module 2 .
第一部分:数据汇集模块1Part 1: Data Collection Module 1
数据汇集模块1由常规监测装置11、声学遥测装置12和辅助装置13组成;Data collection module 1 is made up of conventional monitoring device 11, acoustic telemetry device 12 and auxiliary device 13;
(一)如图3所示,常规监测装置11包括浮式站点和桩式站点,实时监测浅水湖泊与藻类生长和水华暴发有关的物理、生化信息;其中,浮式站点为布置在浅水湖泊内等间距方形阵列顶点的浮标,浮标底部装配有GDYS-201M多参数水质分析仪;桩式站点为布置在浅水湖泊内2倍浮式站点间距的方形阵列顶点并固定于湖床上的桩体,桩体水下部分装配有GDYS-201M多参数水质分析仪、AP-700-SDI叶绿素a传感器,水上部分装配有IIES-1128多参数气象传感器、HAD-WHY光合有效辐射传感器。(1) As shown in Figure 3, the conventional monitoring device 11 includes a floating station and a pile station to monitor in real time the physical and biochemical information related to the growth of algae and the outbreak of algal blooms in shallow water lakes; wherein, the floating station is arranged in a shallow lake The buoys at the vertices of the square array at equal intervals are equipped with GDYS-201M multi-parameter water quality analyzers at the bottom of the buoys; the pile stations are arranged at the vertices of the square array at twice the spacing of the floating stations in shallow lakes and fixed on the lake bed. The underwater part of the pile body is equipped with GDYS-201M multi-parameter water quality analyzer and AP-700-SDI chlorophyll a sensor, and the above-water part is equipped with IIES-1128 multi-parameter meteorological sensor and HAD-WHY photosynthetically active radiation sensor.
(二)声学遥测装置12包括声学标签载体、声学标签和水听器,实时监测声学标签所处位置与藻类生长和水华暴发有关的多重水体物理参数;其中的声学标签载体为浅水湖泊鱼类;声学标签(Vemco公司产品)配置水质传感器并使用尼龙扎带固定于声学标签载体的背鳍上;水听器(Vemco公司产品)安装在各浮式站点和桩式站点上,方向朝下并没入水中。(2) The acoustic telemetry device 12 includes an acoustic tag carrier, an acoustic tag and a hydrophone, and monitors in real time multiple water body physical parameters related to the growth of algae and the outbreak of algal blooms at the position of the acoustic tag; wherein the acoustic tag carrier is fish in shallow water lakes ; Acoustic tags (products of Vemco Company) are equipped with water quality sensors and fixed on the dorsal fin of the acoustic tag carrier with nylon cable ties; hydrophones (products of Vemco Company) are installed on each floating site and pile site, facing downward and submerged in the water.
(三)辅助装置13包括存储设备和通讯设备,布置于各个浮式站点和桩式站点处,存储设备保存常规监测装置11和声学遥测装置12的监测数据,通讯设备实现存储设备和数据挖掘模块2之间的数据传输。(3) The auxiliary device 13 includes storage equipment and communication equipment, which are arranged at each floating site and pile site. The storage equipment saves the monitoring data of the conventional monitoring device 11 and the acoustic telemetry device 12, and the communication equipment realizes the storage equipment and data mining module 2 data transmission between.
第二部分:数据挖掘模块2Part II: Data Mining Module 2
数据挖掘模块2由驱动因子识别单元21、驱动因子适宜区间确定单元22、驱动因子独立效应量化单元23、环境驱动模式分析比较单元24和水华风险评估单元25组成,用于构建浅水湖泊水华风险模型。The data mining module 2 is composed of a driving factor identification unit 21, a driving factor suitable interval determination unit 22, a driving factor independent effect quantification unit 23, an environmental driving mode analysis and comparison unit 24, and an algal bloom risk assessment unit 25, and is used to construct shallow water lake algal blooms risk model.
(一)驱动因子识别单元21根据浅水湖泊环境因子历史监测数据,筛选出与叶绿素a浓度显著关联且驱动水华发生的部分环境因子作为驱动因子;(1) The driving factor identification unit 21 screens out some environmental factors that are significantly related to the concentration of chlorophyll a and drive the occurrence of algae blooms as driving factors according to the historical monitoring data of environmental factors in shallow water lakes;
(二)驱动因子适宜区间确定单元22确定促使叶绿素a浓度处于高位的各个驱动因子的变化范围作为各自的适宜区间(2) The driving factor suitable interval determination unit 22 determines the variation range of each driving factor that promotes the chlorophyll a concentration to be at a high level as the respective suitable interval
(三)驱动因子独立效应量化单元33在其他驱动因子处于各自适宜区间的情况下量化叶绿素a浓度对各个驱动因子变化的响应;(3) The driving factor independent effect quantification unit 33 quantifies the response of the chlorophyll a concentration to the change of each driving factor when other driving factors are in their respective appropriate intervals;
(四)环境驱动模式分析比较单元24分别率定考虑驱动因子对水华发生累加影响、累乘影响或综合影响的三种水华风险模型及各自的临界风险值,比较后给出最优的水华风险模型及其临界风险值。(4) The analysis and comparison unit 24 of the environment driving mode determines three kinds of algal bloom risk models and their respective critical risk values considering the accumulative impact, multiplicative impact or comprehensive impact of the driving factors on algae blooms, and gives the optimal one after comparison Algal bloom risk model and its critical risk value.
(五)水华风险评估单元25结合驱动因子实时监测信息和最优水华风险模型得出浅水湖泊当前环境下水华发生风险分布,在水华发生风险大于临界风险值的情况下向湖泊管理部门进行水华预警。(5) The water bloom risk assessment unit 25 combines the real-time monitoring information of driving factors and the optimal water bloom risk model to obtain the risk distribution of water blooms in the current environment of shallow lakes, and report to the lake management department when the risk of water blooms is greater than the critical risk value Carry out water bloom warning.
实施例2:Example 2:
本实施例中的浅水湖泊水华风险分析预警方法包括以下步骤进如图2所示:The risk analysis and early warning method for algal blooms in shallow lakes in this embodiment includes the following steps as shown in Figure 2:
(一)数据汇集模块1的常规监测装置11包括浮式站点和桩式站点,实时监测浅水湖泊与藻类生长和水华暴发有关的物理、生化信息;浮式站点为布置在浅水湖泊内等间距方形阵列顶点的浮标,桩式站点为布置在浅水湖泊内2倍浮式站点间距的方形阵列顶点并固定于湖床上的桩体;声学遥测装置12对分散在浅水湖泊内的各个声学标签进行实时定位并接收声学标签监测的多重水体物理参数;辅助装置13将常规监测装置11和声学遥测装置12所获取的监测信息保存至存储设备;(1) The conventional monitoring device 11 of the data collection module 1 includes a floating station and a pile station, and real-time monitoring of physical and biochemical information related to algae growth and blooms in shallow lakes; the floating stations are arranged at equal intervals in shallow lakes The buoys at the vertices of the square array, the pile sites are arranged at the vertices of the square array at twice the spacing of the floating sites in the shallow lake and fixed on the piles on the lake bed; the acoustic telemetry device 12 performs real-time monitoring of each acoustic tag scattered in the shallow lake Locate and receive multiple water body physical parameters monitored by the acoustic tag; the auxiliary device 13 saves the monitoring information acquired by the conventional monitoring device 11 and the acoustic telemetry device 12 to a storage device;
(二)数据挖掘模块2调用浅水湖泊环境因子历史监测数据,构建浅水湖泊水华风险模型,按如下步骤执行:(2) The data mining module 2 calls the historical monitoring data of environmental factors of shallow lakes to construct a risk model of algal blooms in shallow lakes, and executes according to the following steps:
从数据汇集模块1的存储设备调取桩式站点处所有环境因子历史监测数据;From the storage device of the data collection module 1, the historical monitoring data of all environmental factors at the pile site are retrieved;
驱动因子识别单元21基于历史监测数据,采用偏互信息方法筛选出与叶绿素a浓度显著关联且驱动发生的部分环境因子作为驱动因子;The driving factor identification unit 21 uses the partial mutual information method to screen out some environmental factors that are significantly correlated with the concentration of chlorophyll a and driven to occur as driving factors based on historical monitoring data;
驱动因子适宜区间确定单元22使用正交表设计从历史监测数据中挑选出满足正交性的驱动因子水平组合,利用极差分析得出叶绿素a浓度随单个驱动因子水平变化规律,进而确定促使叶绿素a浓度处于高位的各个驱动因子的变化范围作为各自的适宜区间;The determination unit 22 of the suitable interval of the driving factor uses the orthogonal table design to select the combination of driving factor levels satisfying the orthogonality from the historical monitoring data, and uses the range analysis to obtain the change rule of the concentration of chlorophyll a with the level of a single driving factor, and then determines the driving factor level that promotes chlorophyll a. a The variation range of each driving factor whose concentration is at a high level is taken as the appropriate interval;
驱动因子独立效应量化单元23在其他驱动因子限定于各自适宜区间的情况下,量化叶绿素a浓度对各个驱动因子变化的独立响应;The driving factor independent effect quantification unit 23 quantifies the independent response of the chlorophyll a concentration to the change of each driving factor when other driving factors are limited to their respective appropriate intervals;
环境驱动模式分析比较单元24在驱动因子独立效应量化单元23所提供信息的基础上,采用进化算法分别率定考虑驱动因子对水华发生累加影响、累乘影响或综合影响的三种水华风险模型及各自的临界风险值以保证各个模型对水华发生/不发生的预测准确率最高,比较各自准确率后最终给出最优的水华风险模型及其对应的临界风险值;The environmental driving mode analysis and comparison unit 24, on the basis of the information provided by the driving factor independent effect quantification unit 23, adopts an evolutionary algorithm to determine the three types of water bloom risks considering the cumulative impact, multiplicative impact or comprehensive impact of the driving factors on the water bloom. Models and their respective critical risk values to ensure that each model has the highest prediction accuracy for the occurrence/non-occurrence of water blooms. After comparing the respective accuracy rates, the optimal water bloom risk model and its corresponding critical risk values are finally given;
(三)数据挖掘模块2的水华风险评估单元25调用浅水湖泊驱动因子实时监测信息,进行浅水湖泊水华风险分析与预警,按如下步骤执行:(3) The algae bloom risk assessment unit 25 of the data mining module 2 calls the real-time monitoring information of the driving factors of shallow lakes to carry out risk analysis and early warning of algae blooms in shallow lakes, and executes according to the following steps:
从数据汇集模块1的存储设备调取常规监测装置11和声学遥测装置12的驱动因子实时监测数据;The real-time monitoring data of the driving factor of conventional monitoring device 11 and acoustic telemetry device 12 are transferred from the storage device of data collection module 1;
使用克里金插值算法将实时监测数据空间插值到整个湖泊范围;Use kriging interpolation algorithm to spatially interpolate real-time monitoring data to the entire lake range;
基于环境驱动模式分析比较单元24给出的最优水华风险模型计算获得浅水湖泊当前环境下水华发生风险分布,将水华发生风险大于临界风险值的区域识别为预测发生水华区域(如图4所示);Based on the optimal algal bloom risk model given by the environment-driven model analysis and comparison unit 24, the algal bloom risk distribution under the current environment of shallow lakes is obtained, and the areas where the algal bloom occurrence risk is greater than the critical risk value are identified as areas where algal blooms are predicted to occur (as shown in Fig. 4);
若当前预测发生水华区域存在,将浅水湖泊水华发生风险分布以及预测发生水华区域向湖泊管理部门发布。If there are areas where water blooms are currently predicted to occur, the risk distribution of water blooms in shallow lakes and the areas where water blooms are predicted to occur will be released to the lake management department.
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