TWI401214B - Early Warning Mode and Detection Method of Water Quality Excellent Oxidation - Google Patents

Early Warning Mode and Detection Method of Water Quality Excellent Oxidation Download PDF

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TWI401214B
TWI401214B TW97139446A TW97139446A TWI401214B TW I401214 B TWI401214 B TW I401214B TW 97139446 A TW97139446 A TW 97139446A TW 97139446 A TW97139446 A TW 97139446A TW I401214 B TWI401214 B TW I401214B
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water
nitrogen
chlorophyll
phosphorus
concentration
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TW97139446A
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TW201014798A (en
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Pei Jie Meng
Wen Hung Twan
Ming Yih Leu
Jih Terng Wang
Jim Huang Chen
Pei Ting Chiang
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Pei Jie Meng
Wen Hung Twan
Ming Yih Leu
Jih Terng Wang
Jim Huang Chen
Pei Ting Chiang
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Description

水質優氧化之預警模式及其偵測方法Early warning mode of water quality oxidation and its detection method

本發明係有關於檢測水質之方法,特別係指一種利用一水體中之氮磷比即可預測水質是否優氧化之方法。The invention relates to a method for detecting water quality, in particular to a method for predicting whether water quality is preferentially oxidized by using a ratio of nitrogen to phosphorus in a water body.

按,水體優養化係指湖泊、水庫或養殖池由於承受過多營養鹽,使得藻類有足夠的養分大量繁殖,其中營養鹽的主要來源是水區的農業、社區居民的活動或其他人為因素所造成之各種污染,本來污染物係累積在集水區,當大雨發生時會將污染物帶入水區中,使大量營養鹽帶入該水體中,導致該水體中浮游植物大量繁殖,因此造成水體生態系急遽變化,使得水質嚴重惡化。換言之,水體優養化將造成藻類大量繁殖。According to the water body eutrophication, the lake, the reservoir or the breeding pond is exposed to excessive nutrients, so that the algae have sufficient nutrients to multiply. The main source of nutrients is the agriculture of the water area, the activities of the community residents or other human factors. The various pollutants caused by the accumulation of pollutants are accumulated in the catchment area. When heavy rain occurs, the pollutants will be brought into the water area, and a large amount of nutrient salts will be brought into the water body, resulting in the massive reproduction of phytoplankton in the water body, thus causing The rapid changes in the water ecosystem have caused serious deterioration of water quality. In other words, the eutrophication of water will cause algae to multiply.

一般而言,影響藻類生長之主要因素有營養鹽、日照、溫度、風場、氣候、滯留時間等,其中最重要者為營養鹽。近年來,隨著人類增加農藥、肥料、餌料與洗衣粉等使用量及製造排放大量污水,造成水體加速優養化現象。當藻類大量繁殖後,常會產生藻華,藻華常伴隨藻毒而形成毒害,更會引發惡臭;又因為藻類之光合作用及呼吸作用造成水體溶氧量晝夜變化差異大,當藻類於夜間行呼吸作用或藻類大量死亡時,就會快速消耗水中溶氧量,常致使水中溶氧量太低,而呈缺氧狀態,造成魚類等水中生物無法生存,屍體亦使水體產生惡臭,這就是水體優養化所引發之現象。In general, the main factors affecting algae growth are nutrient salts, sunshine, temperature, wind field, climate, and residence time. The most important one is nutrient salt. In recent years, as humans increase the use of pesticides, fertilizers, bait and washing powder, and the production of large amounts of sewage, the phenomenon of accelerated water quality is caused. When algae are multiplied, algal blooms are often produced. Algal blooms often form poison with algae poisoning, which may cause malodors. Because of the photosynthesis and respiration of algae, the difference in dissolved oxygen content between water and water is large, when algae are at night. When respiration or a large number of algae die, it will quickly consume the dissolved oxygen in the water, often causing the dissolved oxygen in the water to be too low, and in an oxygen-deficient state, causing the fish and other aquatic organisms to survive, and the body also causes the water body to produce a foul smell. This is the water body. The phenomenon caused by eutrophication.

故由上可知,水體中營養鹽過多而發生優氧化現象,即會引發大量藻類生長,對於水質會造成十分嚴重的影響,例如水庫的水發生優氧化現象,不僅使水庫壽命減短,亦增加水的處理費用。故許多研究皆致力於監測水質變化,希望能事先對於水體優氧化之現象有所防範,但是過去對於水體優養化之預測,大多數都憑藉經驗法則,例如風向、氣候、氣溫等因子之改變等,然而此種預測方式缺乏科學根據,無法準確地預測優氧化之發生,因此成效不彰。Therefore, it can be seen that there is too much nutrient salt in the water body to cause excellent oxidation, which will cause a large amount of algae growth, which will have a very serious impact on water quality. For example, the excellent oxidation of water in the reservoir will not only shorten the life of the reservoir but also increase it. Water treatment costs. Therefore, many studies are devoted to monitoring water quality changes, hoping to prevent the phenomenon of water oxidation in advance, but in the past, most of the predictions of water body eutrophication rely on the rule of thumb, such as changes in wind direction, climate, temperature and other factors. Etc. However, this type of prediction lacks a scientific basis and cannot accurately predict the occurrence of superior oxidation, so the results are not effective.

本發明之主要目的係提供一種水質優氧化之預警模式及其偵測方法,藉由一水體中氮磷比與葉綠素甲動態變化,建立一建立水體生態環境的有效管理方法。The main object of the present invention is to provide an early warning mode for water quality oxidation and a detection method thereof, and establish an effective management method for establishing a water body ecological environment by dynamically changing the nitrogen-phosphorus ratio and chlorophyll A in a water body.

本發明之另一目的係提供一種水質優氧化之預警模式及其偵測方法,僅需要測量計算一水體中之氮磷比,即可簡單並有效地預測是否發生優氧化之現象。Another object of the present invention is to provide an early warning mode for water quality oxidation and a detection method thereof. It is only necessary to measure and calculate the ratio of nitrogen to phosphorus in a water body, and it is simple and effective to predict whether or not preferential oxidation occurs.

緣是,為了達成上述目的,本發明係提供一種水質優氧化之預警模式,其係利用一水體之氮磷比(N/P)與該水體葉綠素甲濃度(Chl.a)兩者間之關連性,達到預警該水體是否優氧化之功效。更進一步而言,水質優氧化之預警模式係包含有下列步驟:(1)選定採樣地點;(2)採集水樣並測量該水樣之氮磷比及葉綠素甲濃度;(3)建立數據關聯性;(4)定義且分析該數據關聯性。In order to achieve the above object, the present invention provides an early warning mode for water quality superior oxidation, which utilizes the relationship between the nitrogen/phosphorus ratio (N/P) of a water body and the chlorophyll A concentration (Chl.a) of the water body. Sexuality, to achieve the effect of warning whether the water body is excellent in oxidation. Furthermore, the early warning mode of water quality oxidation includes the following steps: (1) selecting the sampling site; (2) collecting the water sample and measuring the nitrogen to phosphorus ratio and the concentration of chlorophyll A of the water sample; (3) establishing data association (4) define and analyze the data relevance.

本發明亦提供一種水質優氧化之預警模式及其監測方法,其包含有下列步驟:(1)選定採樣地點;(2)採集水樣並測量該水樣之氮磷比及葉綠素甲濃度;(3)建立數據關聯性;(4)定義且分析該數據關聯性;(5)監測水質,以判定該水體是否優氧化。The invention also provides an early warning mode for water quality oxidation and a monitoring method thereof, which comprises the following steps: (1) selecting a sampling location; (2) collecting a water sample and measuring a ratio of nitrogen to phosphorus and a concentration of chlorophyll A of the water sample; 3) Establish data correlation; (4) Define and analyze the data relevance; (5) Monitor water quality to determine whether the water body is excellent for oxidation.

以下,茲就本發明一較佳實施例配合圖式做更進一步說明如后。Hereinafter, a preferred embodiment of the present invention will be further described with reference to the drawings.

第一圖係本發明中水質優氧化之預警模式之方法流程圖。The first figure is a flow chart of the method for the early warning mode of water quality oxidation in the present invention.

第二圖係本發明中水質優氧化之預警模式及其監測方法之流程圖。The second figure is a flow chart of the early warning mode of water quality oxidation and the monitoring method thereof in the present invention.

第三圖係本發明之實施例實測數據之示意圖。The third figure is a schematic diagram of measured data of an embodiment of the present invention.

本發明所揭一種水質優氧化之預警模式及其監測方法。首先,關於水質優氧化之預警模式,其係利用一水體之氮磷比(N/P)與該水體葉綠素甲濃度(Chl.a)兩者間呈現一乘冪關係,以氮磷比為X軸,葉綠素甲濃度為Y軸,兩者間之圖形關係式為Y=A X-B 而為一下凹曲線圖;水體優氧化之判斷值被定義為葉綠素甲濃度超過10μg/L,故當該水體之氮磷比小於10(log(A/10))/B 值時,該水體係發生優氧化現象;其中該A與B分別為第一係數及第二係數,該A及B值均會隨著水體的 不同而有所變化。The invention discloses an early warning mode for water quality oxidation and a monitoring method thereof. First, regarding the early warning mode of water quality oxidation, the nitrogen-phosphorus ratio (N/P) of a water body and the chlorophyll-methyl concentration (Chl.a) of the water body are presented in a power relationship, and the ratio of nitrogen to phosphorus is X. The axis, the concentration of chlorophyll A is the Y axis, and the relationship between the two is Y=AX -B and is a concave curve. The judgment value of water oxidation is defined as the concentration of chlorophyll A exceeds 10 μg / L, so when the water body When the ratio of nitrogen to phosphorus is less than 10 (log(A/10))/B , the water system is excellent in oxidation; wherein A and B are the first coefficient and the second coefficient, respectively, and the A and B values are The water changes from place to place.

更進一步而言,請參閱第一圖,水質優氧化之預警模式,其包含有下列步驟:Further, please refer to the first figure, the warning mode of water quality oxidation, which includes the following steps:

一、選定採樣地點(11)。First, select the sampling location (11).

二、採集水樣及測量(12):分別於不同時間分別採集不同區域之水體做為水樣,再以儀器分別測出各該水樣之氮磷比(N/P)及葉綠素甲濃度(Chl.a),至少取得兩組數值。其中,採取水樣之方式係依照行政院環保署檢字第02198號公告「湖河池泊水庫藻類採樣方法」,檢測方式係依環署檢字第094001591號公告「水質檢測方法總則」做為測量水樣中氮含量、磷含量及葉綠素甲濃度。2. Collecting water samples and measuring (12): separately collect water bodies of different areas as water samples at different times, and then measure the nitrogen-phosphorus ratio (N/P) and chlorophyll-methyl concentration of each water sample by instrument ( Chl.a), at least two sets of values are obtained. Among them, the method of taking water samples is in accordance with the "Environmental Sampling Method of Huhechibo Reservoir" published by the Environmental Protection Department of the Executive Yuan, No. 02198, and the detection method is based on the "General Principles of Water Quality Testing Methods" in the Announcement No. 094001591 of the Environmental Protection Department. Nitrogen content, phosphorus content and chlorophyll A concentration in water samples.

三、建立數據相關性(13):將Y軸設為葉綠素甲濃度(Chl.a),X軸設為氮磷比(N/P),得到一個下凹曲線圖,該葉綠素甲濃度與該氮磷比兩者間呈現一乘冪關係,其關係式為Y=A X-B ;其中,A及B分別為第一係數及第二係數,該第一係數A與該第二係數B值均會隨著不同性質之水體及環境而有所改變。Third, establish data correlation (13): set the Y axis to the chlorophyll A concentration (Chl.a), the X axis to the nitrogen to phosphorus ratio (N / P), get a concave curve, the chlorophyll A concentration and the Nitrogen and phosphorus have a power relationship between the two, and the relationship is Y=AX -B . Among them, A and B are the first coefficient and the second coefficient, respectively, and the first coefficient A and the second coefficient B are both It will change with different water bodies and environments.

四、運算分析(14):將該水體葉綠素甲濃度定義為超過10μg/L,則該水體發生優養化之現象,故由該關係式可得氮磷比小於10(log(A/10))/B 時,該水體即會產生優氧化之現象。Fourth, the operation analysis (14): the water body chlorophyll A concentration is defined as more than 10μg / L, then the water body is eutrophication phenomenon, so the relationship between the nitrogen and phosphorus ratio can be less than 10 (log (A/10) When /B , the water body will produce excellent oxidation.

其次,請參閱第二圖,關於本發明之水質優氧化之預警模式與其監測方法,其包含下列步驟:Secondly, please refer to the second figure, regarding the early warning mode of water quality oxidation of the present invention and its monitoring method, which comprises the following steps:

一、選定採樣地點(21),例如選定一養殖池。First, select the sampling location (21), for example, select a breeding pond.

二、採集水樣及測量(22):分別於不同時間採集該地點不同區域之水體做為水樣,再以儀器分別測出各該水樣之氮、磷之含量及葉綠素甲濃度(Chl.a),計算出水樣中氮磷比(N/P),其中至少取得兩組數值。2. Collecting water samples and measuring (22): Collect water bodies in different areas of the site at different times as water samples, and then measure the nitrogen and phosphorus contents and chlorophyll A concentration of each water sample by the instrument (Chl. a) Calculate the ratio of nitrogen to phosphorus (N/P) in the water sample, at least two sets of values are obtained.

三、建立數據相關性(23):將Y軸設為葉綠素甲濃度(Chl.a),X軸設為氮磷比(N/P),由步驟二(22)可得到一下凹曲線圖,該葉綠素甲濃度與該氮磷比兩者間呈現一乘冪關係,其 關係式為Y=A X-B ;其中,A及B分別為第一係數及第二係數。Third, establish data correlation (23): set the Y axis to the chlorophyll A concentration (Chl.a), the X axis to the nitrogen to phosphorus ratio (N / P), from step 2 (22) can get a concave curve, The chlorophyll-methyl concentration and the nitrogen-phosphorus ratio exhibit a power relationship, and the relationship is Y=AX- B ; wherein A and B are the first coefficient and the second coefficient, respectively.

四、運算分析(24):將該水體葉綠素甲濃度定義為超過10μg/L,則該水體發生優養化之現象,故由該關係式可得10(log(A/10))/B 為發生優氧化之臨界值。Fourth, the operation analysis (24): the water body chlorophyll A concentration is defined as more than 10μg / L, then the water body is eutrophic, so the relationship can be obtained 10 (log (A/10)) / B The critical value of excellent oxidation occurs.

五、監測水質:定期取該水體任一區域為一水樣,以儀器測量該水樣之氮含量及磷含量,並求出氮磷比,再比較該氮磷比是否小於優氧化之臨界值,即達到監測並預警該水體優氧化之功效。V. Monitoring water quality: Regularly take any water in the water body as a water sample, measure the nitrogen content and phosphorus content of the water sample by instrument, and find the nitrogen-phosphorus ratio, and then compare whether the nitrogen-phosphorus ratio is less than the critical value of excellent oxidation. That is, the monitoring and warning of the effect of the oxidation of the water body is achieved.

請參閱第三圖,其係本發明所揭水質優氧化之預警模式實施例實測數據之示意圖,選取一養殖池做為採樣地點,分別於不同季節採取不同區域之水樣約20組,分別檢測各該水樣之氮含量、磷含量及葉綠素甲濃度。在以Y軸代表葉綠素甲濃度,X軸代表水體氮磷比值,計算出該第一係數A係為3.468,該第二係數B係為0.4847,即該關係式為Y=3.468X-0.4847 。由於葉綠素甲濃度大於10μg/L時,該養殖池會發生優氧化之現象,換言之,當Y=3.468X-0.4847 ≧10時,該養殖池即會發生優氧化之現象。故經由運算,未來可以藉由定期測量該養殖池之氮磷比,只要該氮磷比趨近於10(log0.3468)/0.4847 ,可判斷出該養殖池將可能發生優氧化之現象。Please refer to the third figure, which is a schematic diagram of the measured data of the embodiment of the warning mode for water quality oxidation of the present invention. A breeding pond is selected as a sampling site, and about 20 groups of water samples in different regions are taken in different seasons, respectively. Nitrogen content, phosphorus content and chlorophyll A concentration of each of the water samples. The Y-axis represents the concentration of chlorophyll-methyl, and the X-axis represents the ratio of nitrogen to phosphorus in the water. The first coefficient A is calculated to be 3.468, and the second coefficient B is 0.4847, that is, the relationship is Y=3.468X- 0.4847 . Since the concentration of chlorophyll A is greater than 10 μg/L, the culture pond will undergo excellent oxidation. In other words, when Y=3.468X -0.4847 ≧10, the culture pond will undergo excellent oxidation. Therefore, through calculation, the ratio of nitrogen to phosphorus in the culture pond can be measured in the future. As long as the ratio of nitrogen to phosphorus approaches 10 (log 0.3468) / 0.4847 , it can be judged that the oxidation pond may be preferentially oxidized.

綜上所述,本發明之功效可歸納為:In summary, the effects of the present invention can be summarized as follows:

1.藉由監測一水體中氮磷比與葉綠素甲動態變化,建立一個水體生態環境的有效管理方法。1. Establish an effective management method for the aquatic ecosystem by monitoring the nitrogen-phosphorus ratio and the dynamic change of chlorophyll A in a water body.

2.提供簡單並有效的一種預測水體優氧化之方法,僅需利用儀器測量計算出一水體中氮磷比,即可推得該水體近期內是否有產生優氧化之可能性。2. To provide a simple and effective method for predicting the oxidation of water bodies. It is only necessary to use the instrument to calculate the ratio of nitrogen to phosphorus in a water body, so as to whether the water body has the possibility of producing excellent oxidation in the near future.

3.可建立客觀之歷史資料庫,藉由本發明需要紀錄各該水體不同區域之氮磷含量與葉綠素甲濃度,未來亦可提供於分析或是研究之用,或是做為更進一步統合整理之依據。3. An objective historical database can be established. According to the invention, the nitrogen and phosphorus contents and the chlorophyll A concentration in different regions of the water body need to be recorded, and the future can also be provided for analysis or research, or as a further integration. in accordance with.

(11)(21)...選定採樣地點(11) (21). . . Selected sampling location

(12)(22)...採集水樣及測量(12) (22). . . Collecting water samples and measuring

(13)(23)...建立數據關聯性(13)(23). . . Establish data relevance

(14)(24)...定義及分析(14)(24). . . Definition and analysis

(25)...監測水質(25). . . Monitoring water quality

第一圖係本發明中水質優氧化之預警模式之方法流程圖。The first figure is a flow chart of the method for the early warning mode of water quality oxidation in the present invention.

第二圖係本發明中水質優氧化之預警模式及其監測方法之流程圖。The second figure is a flow chart of the early warning mode of water quality oxidation and the monitoring method thereof in the present invention.

第三圖係本發明之實施例實測數據之示意圖。The third figure is a schematic diagram of measured data of an embodiment of the present invention.

(21)...選定採樣地點(twenty one). . . Selected sampling location

(22)...採集水樣及測量(twenty two). . . Collecting water samples and measuring

(23)...建立數據關聯性(twenty three). . . Establish data relevance

(24)...定義及分析(twenty four). . . Definition and analysis

(25)...監測水質(25). . . Monitoring water quality

Claims (3)

一種水質優氧化之預警模式,其係一水體之氮磷比(N/P)與該水體葉綠素甲濃度(Chl.a)兩者間呈現一乘冪關係,分別於不同時間分別採集不同區域之該水體做為水樣,再分別測出各該水樣之氮磷比(N/P)及葉綠素甲濃度(Chl.a),以各該水樣之氮磷比為X軸座標及葉綠素甲濃度為Y軸座標,兩者間存在一圖形關係式為Y=A X-B 而為一曲線圖;水體優氧化之判斷值被定義為葉綠素甲(Y)濃度超過10μg/L,故當該水體之氮磷比(X)小於10(log(A/10))/B 值時,該水體係發生優氧化現象;其中,A及B分別為第一係數及第二係數並隨著不同水體及環境而定義。An early warning mode for water quality oxidation, in which the ratio of nitrogen to phosphorus (N/P) of a water body and the concentration of chlorophyll A (Chl.a) of the water body are in a power relationship, respectively, and different regions are collected at different times. The water body is used as a water sample, and the nitrogen-phosphorus ratio (N/P) and the chlorophyll-methyl concentration (Chl.a) of each water sample are respectively measured, and the nitrogen-phosphorus ratio of each water sample is the X-axis coordinate and the chlorophyll A. The concentration is the Y-axis coordinate, and there is a graph relationship between the two is Y=AX- B and is a graph; the judgment value of water oxidation is defined as the concentration of chlorophyll A (Y) exceeds 10 μg/L, so when the water body When the ratio of nitrogen to phosphorus (X) is less than 10 (log(A/10))/B , the water system is excellent in oxidation; wherein A and B are the first coefficient and the second coefficient respectively, and with different water bodies and Defined by the environment. 一種水質優氧化之預警模式,其包含下列步驟:一、選定採樣地點;二、採集水樣及測量:分別於不同時間採集不同區域之水體做為水樣,再分別測出各該水樣之氮磷比(N/P)及葉綠素甲濃度(Chl.a);三、建立數據關聯性:以Y軸座標代表葉綠素甲濃度(Chl.a),X軸座標代表氮磷比(N/P),以各該水樣之氮磷比為X軸座標及葉綠素甲濃度為Y軸座標,存在一曲線圖,該葉綠素甲濃度與該氮磷比兩者間呈現一乘冪關係,其關係式為Y=A X-B ;其中,A及B分別為第一係數及第二係數並隨著不同水體及環境而定義;四、定義及分析:將該水體葉綠素甲濃度定義為超過10μg/L,則該水體發生優養化之現象,故由該關係式可得氮磷比小於10(log(A/10))/B 時,該水體即會產生優氧化之現象。An early warning mode for excellent oxidation of water quality, comprising the following steps: 1. selecting a sampling location; 2. collecting water samples and measuring: collecting water bodies of different regions at different times as water samples, and respectively measuring the water samples. Nitrogen-phosphorus ratio (N/P) and chlorophyll-methyl concentration (Chl.a); Third, establish data correlation: Y-axis coordinates represent chlorophyll-methyl concentration (Chl.a), and X-axis coordinates represent nitrogen-phosphorus ratio (N/P) ), the nitrogen-phosphorus ratio of each water sample is the X-axis coordinate and the chlorophyll-methyl concentration is the Y-axis coordinate, and there is a graph, and the relationship between the chlorophyll-methyl concentration and the nitrogen-phosphorus ratio is a power relationship. Y=AX -B ; where A and B are the first coefficient and the second coefficient, respectively, and are defined with different water bodies and environments; 4. Definition and analysis: The water chlorophyll A concentration is defined as more than 10 μg/L, Then, the water body is eutrophicated. Therefore, when the nitrogen-phosphorus ratio of the relationship is less than 10 (log(A/10))/B , the water body is excellent in oxidation. 一種水質優氧化之預警模式及其監測方法,其包含下列步驟:一、選定採樣地點;二、採集水樣及測量:分別於不同時間採集不同區域之水體做為水樣,再分別測出各該水樣之氮磷比(N/P)及葉綠素甲濃度(Chl.a); 三、建立數據關聯性:以Y軸座標代表葉綠素甲濃度(Chl.a),X軸座標代表氮磷比(N/P),以各該水樣之氮磷比為X軸座標及葉綠素甲濃度為Y軸座標,存在一曲線圖,該葉綠素甲濃度與該氮磷比兩者間呈現一乘冪關係,其關係式為Y=A X-B ;其中,A及B分別為第一係數及第二係數並隨著不同水體及環境而定義;四、定義及分析:將該葉綠素甲之濃度定義為超過10μg/L,會發生水體優養化之現象,故當氮磷比小於優氧化之臨界值時,該水體即會產生優氧化;其中該臨界值為10(log(A/10))/B ;五、監測水質:定期取該水體任一區域為水樣,以儀器測量該水樣之氮含量及磷含量,並求出氮磷比,再比較該氮磷比與該臨界值之大小,即達到監測並預警該水體優氧化之功效。An early warning mode for water quality oxidation and a monitoring method thereof, comprising the following steps: 1. selecting a sampling location; 2. collecting water samples and measuring: collecting water bodies of different regions at different times as water samples, and respectively measuring each The nitrogen-phosphorus ratio (N/P) and chlorophyll-methyl concentration (Chl.a) of the water sample; 3. Establish data correlation: the chlorophyll-methyl concentration (Chl.a) is represented by the Y-axis coordinate, and the nitrogen-phosphorus ratio is represented by the X-axis coordinate. (N/P), the nitrogen-phosphorus ratio of each water sample is the X-axis coordinate and the chlorophyll-methyl concentration is the Y-axis coordinate, and there is a graph, and the chlorophyll-methyl concentration and the nitrogen-phosphorus ratio exhibit a power relationship. , the relationship is Y=AX -B ; wherein A and B are the first coefficient and the second coefficient respectively and are defined with different water bodies and environments; 4. Definition and analysis: the concentration of the chlorophyll A is defined as exceeding 10μg/L, the phenomenon of water body eutrophication occurs, so when the nitrogen-phosphorus ratio is less than the critical value of excellent oxidation, the water body will produce excellent oxidation; wherein the critical value is 10 (log(A/10))/B 5. Monitoring water quality: regularly take any water in the water body as a water sample, and measure the nitrogen of the water sample by instrument And the amount of phosphorus content, and the nitrogen to phosphorus ratio is obtained, and then comparing the ratio of the size of nitrogen and phosphorus with the threshold value, i.e. to achieve excellent effect monitoring and warning of the oxidation of water.
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