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CN101995380A - Method for monitoring soil petroleum pollution based on hyperspectral vegetation index - Google Patents

Method for monitoring soil petroleum pollution based on hyperspectral vegetation index Download PDF

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CN101995380A
CN101995380A CN 201010502657 CN201010502657A CN101995380A CN 101995380 A CN101995380 A CN 101995380A CN 201010502657 CN201010502657 CN 201010502657 CN 201010502657 A CN201010502657 A CN 201010502657A CN 101995380 A CN101995380 A CN 101995380A
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soil
vegetation
hyperspectral
total petroleum
hydrocarbon content
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CN101995380B (en
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朱林海
丁金枝
王健健
刘南希
来利明
赵学春
王永吉
郑元润
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Institute of Botany of CAS
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Abstract

一种基于高光谱植被指数监测土壤石油污染的方法属于环境监测领域,本发明通过以下技术方案来实现:1)建立土壤总石油烃含量高光谱预测模型,包括以下步骤:选择采样点;高光谱测定;土壤取样和总石油烃含量测定;计算植被指数;确定最佳预测模型;2)土壤总石油烃含量高光谱预测模型的集成。本发明的有益效果为:相对于传统的土壤、植被监测方法,本发明简单易行,可节约大量的人力、财力和时间,对植被破坏小;结合航空、航天等遥感技术,可实现土壤石油污染的定时、定位、定量、大面积监测。

Figure 201010502657

A method for monitoring soil oil pollution based on hyperspectral vegetation index belongs to the field of environmental monitoring. The present invention is realized through the following technical solutions: 1) establishing a hyperspectral prediction model for total petroleum hydrocarbon content in soil, comprising the following steps: selecting sampling points; determination; soil sampling and determination of total petroleum hydrocarbon content; calculation of vegetation index; determination of the best prediction model; 2) integration of hyperspectral prediction models for soil total petroleum hydrocarbon content. The beneficial effects of the present invention are: compared with traditional soil and vegetation monitoring methods, the present invention is simple and easy to implement, can save a lot of manpower, financial resources and time, and has little damage to vegetation; combined with remote sensing technologies such as aviation and spaceflight, it can realize soil petroleum monitoring. Timing, positioning, quantification, and large-scale monitoring of pollution.

Figure 201010502657

Description

A kind of method based on the oil pollution of high spectrum vegetation index monitoring soil
Technical field
The invention belongs to the environmental monitoring field, be specifically related to high-spectrum remote-sensing in soil oil pollution Application in Monitoring.
Background technology
Be accompanied by the suitability for industrialized production and the utilization of oil, oil pollution has become a serious environmental problem.After oil entered the ecosystem, not only structure, the function to the ecosystem produced considerable influence, and petroleum pollution can finally enter human body, harm humans health by food chain enrichment step by step in animal and plant body.
In the oil total production of the whole world, about 80% by the land field produces.The crude oil that China produces also major part comes from onshore oil field.Therefore, how to carry out environmental monitoring that terrestrial ecosystems PetroChina Company Limited. the pollutes diffusion for the prevention oil pollution effectively, efficiently carry out the degraded and the repair of oil pollution, to administer oil pollution significant comprehensively.
At present, conventional soil, vegetation monitoring are generally carried out in the environmental monitoring of land oil pollution.But the monitoring of soil and vegetation often needs a large amount of samplings, and the assay determination of sample needs a large amount of instruments, and the mensuration program is also comparatively complicated, therefore is a consumption power, consumption wealth, work consuming time.Studies show that of past, oil pollution meeting influence physiological and biochemical indexs such as the leaf area index, biomass, vegetation cover degree, photosynthetic pigments of plant.And the variation of these indexs can utilize vegetation index to monitor effectively.Simultaneously, with respect to traditional broadband remote sensing technology, the high light spectrum image-forming spectrometer can reach nanoscale in the spectral resolution of visible light-near infrared region, therefore, can obtain research object spectral information in detail and accurately.Thereby be the calculating of the vegetation index space that provides more choices, the susceptibility and the accuracy of vegetation index monitoring are further improved.For these reasons, the present invention is directed to the reed is the ecosystem of sociales, utilizes the open-air vegetation high-spectral data that obtains, and calculates high spectrum vegetation index, has finally set up the high spectral prediction model of reed ecosystem soil oil pollution.
Summary of the invention
The purpose of this invention is to provide a kind of method, to overcome traditional soil, vegetation monitoring method consumption power, consumption wealth, deficiency consuming time based on the oil pollution of high spectrum vegetation index monitoring soil.
Purpose of the present invention is achieved through the following technical solutions:
1) set up the high spectral prediction model of soil total petroleum hydrocarbons content, may further comprise the steps:
(a) select sampled point: select 30 sampled points on the reed vegetation around the oil well, between 30-130m, sampled point does not suffer artificial interference to each sampling point apart from the distance of oil well, and vegetation is trampleed on, and sampled point does not exist non-oil pollution to coerce;
(b) high spectroscopic assay: adopt portable ground-object spectrum instrument through measuring the high-spectral data of reed vegetation on step (a) the selected sampled point, carry out sky ceiling unlimited during mensuration between when being determined at the 10-12 of every morning; Replication is 10 times on each sampled point, obtains 10 high curves of spectrum, and there are the abnormal curve of notable difference in deletion and other curves, calculate the mean value that each sampled point remains the high curve of spectrum again, obtain the high curve of spectrum of each sampled point reed vegetation;
(c) soil sample and total petroleum hydrocarbons content are measured: get the soil that the degree of depth is 0-30cm in each sample point, the heavy 450-550g of soil sample amount, adopt each sampled point soil total petroleum hydrocarbons content of infrared spectrophotometric determination then, the unit of soil total petroleum hydrocarbons content is mg/kg;
(d) calculate vegetation index:, calculate 44 kinds of vegetation indexes of each sampled point according to the high curve of spectrum data of step (b) gained reed vegetation;
(e) determine the optimum prediction model: adopt linearity, logarithm, inverse, secondary, three times, power, S type curve, exponential Function Model that the relation of 44 kinds of vegetation indexes of each sampled point and this sampled point soil total petroleum hydrocarbons content is carried out match respectively; Determine that the optimum prediction model is TPH=0.131/RES, wherein TPH is the soil total petroleum hydrocarbons content, and the unit of soil total petroleum hydrocarbons content is mg/kg; RES is a red limit slope, i.e. the maximal value of wavelength spectral reflectivity single order differential in the 680-750nm scope;
2) the high spectral prediction model of soil total petroleum hydrocarbons content is integrated: will be integrated in the accompanying software of ground-object spectrum instrument through step 1) gained forecast model, and realize the real-time positioning and the Quantitative Monitoring of soil oil pollution; In conjunction with the Aeronautics and Astronautics remote sensing technology, further realize the large tracts of land fast monitored of soil oil pollution.
Beneficial effect of the present invention is: with respect to traditional soil, vegetation monitoring method, the present invention is simple, can save great amount of manpower, financial resources and time, and is little to vegetation deterioration; In conjunction with remote sensing technologies such as Aeronautics and Astronautics, can realize timing, location, quantitative, the large tracts of land monitoring of soil oil pollution.
Description of drawings
Fig. 1 is the described a kind of graph of relation based on vegetation index red limit slope and soil total petroleum hydrocarbons content in the method for high spectrum vegetation index monitoring soil oil pollution of the embodiment of the invention.
Embodiment
The described a kind of method based on the oil pollution of high spectrum vegetation index monitoring soil of the embodiment of the invention may further comprise the steps:
1) set up the high spectral prediction model of soil total petroleum hydrocarbons content, may further comprise the steps:
(a) select sampled point: select 30 sampled points on the reed vegetation around the oil well, between 30-130m, sampled point does not suffer artificial interference to each sampling point apart from the distance of oil well, and vegetation is trampleed on, and sampled point does not exist non-oil pollution to coerce;
(b) high spectroscopic assay: adopt portable ground-object spectrum instrument through measuring the high-spectral data of reed vegetation on step (a) the selected sampled point, carry out sky ceiling unlimited during mensuration between when being determined at the 10-12 of every morning; Replication is 10 times on each sampled point, obtains 10 high curves of spectrum, and there are the abnormal curve of notable difference in deletion and other curves, calculate the mean value that each sampled point remains the high curve of spectrum again, obtain the high curve of spectrum of each sampled point reed vegetation;
(c) soil sample and total petroleum hydrocarbons content are measured: get the soil that the degree of depth is 0-30cm in each sample point, the heavy 450-550g of soil sample amount, adopt each sampled point soil total petroleum hydrocarbons content of infrared spectrophotometric determination then, the unit of soil total petroleum hydrocarbons content is mg/kg;
(d) calculate vegetation index:, calculate 44 kinds of vegetation indexes of each sampled point according to the high curve of spectrum data of step (b) gained reed vegetation;
(e) determine the optimum prediction model: adopt linearity, logarithm, inverse, secondary, three times, power, S type curve, exponential Function Model that the relation of 44 kinds of vegetation indexes of each sampled point and this sampled point soil total petroleum hydrocarbons content is carried out match respectively; Determine that the optimum prediction model is TPH=0.131/RES, wherein TPH is the soil total petroleum hydrocarbons content, and the unit of soil total petroleum hydrocarbons content is mg/kg; RES is a red limit slope, i.e. the maximal value of wavelength spectral reflectivity single order differential in the 680-750nm scope;
2) the high spectral prediction model of soil total petroleum hydrocarbons content is integrated: will be integrated in the accompanying software of ground-object spectrum instrument through step 1) gained forecast model, and realize the real-time positioning and the Quantitative Monitoring of soil oil pollution; In conjunction with the Aeronautics and Astronautics remote sensing technology, further realize the large tracts of land fast monitored of soil oil pollution.
In above-mentioned method based on the oil pollution of high spectrum vegetation index monitoring soil, during spectroscopic assay, the portable ground-object spectrum instrument of FieldSpec3 that portable ground-object spectrum instrument adopts U.S. ASD company (U.S. spectrometric instrument company) to produce.The portable ground-object spectrum instrument of FieldSpec3 is applicable to remote sensing survey, the crops monitoring, and forest research, industrial lighting is measured, the each side of oceanographic research and mineral prospecting.This instruments weight is light, can measure and observe reflection, transmission, the radiancy curve of spectrum in real time; Can show absolute reflectance in real time; Have advantages such as high s/n ratio, high reliability, high duplication.This instrument can be measured the spectrum of 350-2500nm wavelength coverage, and spectral resolution is 3-10nm.
In above-mentioned method based on the oil pollution of high spectrum vegetation index monitoring soil, when calculating vegetation index, the present invention has selected existing 44 kinds of vegetation indexes, and each vegetation index and computing formula thereof see Table 1.Because a lot of vegetation indexs calculate with the wide-band spectrum reflectivity at first, the spectral reflectivity with sensitive wave length in the corresponding wave band among the present invention replaces.
The vegetation index that uses among table 1 the present invention
Figure BSA00000297248700041
The vegetation index that uses among continuous table 1 the present invention
Figure BSA00000297248700051
The vegetation index that uses among continuous table 1 the present invention
Figure BSA00000297248700061
The vegetation index that uses among continuous table 1 the present invention
Figure BSA00000297248700071
In above-mentioned method based on the oil pollution of high spectrum vegetation index monitoring soil, when determining the optimum prediction model, adopt function models such as linearity, logarithm, inverse, secondary, three times, power, S type curve, index that the relation of each vegetation index and soil total petroleum hydrocarbons content has been carried out match respectively.Fitting result sees Table 2.
Each function model of table 2 is to the fitting result (n=30) of vegetation index
Figure BSA00000297248700072
Continuous each function model of table 2 is to the fitting result (n=30) of vegetation index
There is negative value in the result of calculation of some vegetation index, therefore can't obtains the fitting result of this some function model of vegetation index, in table, represent with missing values symbol "-".
Index of correlation R in the table 2 2>0.85 forecast model sees Table 3.Relatively each forecast model can determine that TPH=0.131/RES is the optimum prediction model, and its model as shown in Figure 1.Wherein TPH is the soil total petroleum hydrocarbons content, and the unit of soil total petroleum hydrocarbons content is mg/kg; RES is a red limit slope, i.e. the maximal value of spectral reflectivity single order differential in the 680nm-750nm wavelength coverage.The R of this forecast model 2Up to 0.948, the p value shows that also much smaller than 0.01 the degree of reliability of this model prediction is higher.From now on, this forecast model can be integrated in the accompanying software of ground-object spectrum instrument, realize the location of soil oil pollution, real-time, Quantitative Monitoring.In conjunction with remote sensing technologies such as Aeronautics and Astronautics, can further realize the large tracts of land fast monitored of soil oil pollution.This method is with respect to traditional soil, vegetation monitoring, and is simple, can save great amount of manpower, financial resources and time, little to vegetation deterioration.
Table 3 index of correlation R 2>0.85 forecast model and check (n=30)
Figure BSA00000297248700091
When adopting the present invention to monitor the soil oil pollution, because the difference of the ecosystem, soil suffers the vegetation index possibility of oil pollution degree different in the reflection ecosystem; Therefore at other ecosystems, can utilize other vegetation index (comprising the vegetation index that utilizes other sensitive wave lengths to calculate) to propose new spectral prediction model in conjunction with other function models.

Claims (1)

1.一种基于高光谱植被指数监测土壤石油污染的方法,其特征在于,包括以下步骤:1. A method for monitoring soil oil pollution based on hyperspectral vegetation index, is characterized in that, comprises the following steps: 1)建立土壤总石油烃含量高光谱预测模型,包括以下步骤:1) Establish a hyperspectral prediction model for soil total petroleum hydrocarbon content, including the following steps: (a)选择采样点:在油井周围的芦苇植被上选择若干个采样点,各样点距油井的距离在30-130m之间,采样点未遭受人为干扰,植被未遭践踏,且采样点不存在非石油污染胁迫;(a) Selection of sampling points: Select several sampling points on the reed vegetation around the oil well. The distance between each sampling point and the oil well is between 30-130m. There is a non-oil pollution threat; (b)高光谱测定:采用便携式地物波谱仪在经过步骤(a)所选采样点上测定芦苇植被的高光谱数据,测定在每天上午的10-12时之间进行,测定时天空晴朗无云;每个采样点上重复测定10次,获取10条高光谱曲线,删除与其他曲线存在明显差异的异常曲线,再计算每个采样点剩余高光谱曲线的平均值,得到每个采样点芦苇植被的高光谱曲线;(b) hyperspectral measurement: adopt portable object spectrometer to measure the hyperspectral data of reed vegetation on the selected sampling point through step (a), measure and carry out between 10-12 o'clock in the morning every day, the sky is clear during measurement. Cloud; repeat the measurement 10 times at each sampling point, obtain 10 hyperspectral curves, delete the abnormal curves that are significantly different from other curves, and then calculate the average value of the remaining hyperspectral curves at each sampling point to obtain the reed Hyperspectral curves of vegetation; (c)土壤取样和总石油烃含量测定:在各采样点处取深度为0-30cm的土壤,土壤取样量重450-550g,然后采用红外分光光度法测定每个采样点土壤总石油烃含量,土壤总石油烃含量的单位为mg/kg;(c) Soil sampling and determination of total petroleum hydrocarbon content: take soil with a depth of 0-30cm at each sampling point, the soil sampling weight is 450-550g, and then use infrared spectrophotometry to measure the soil total petroleum hydrocarbon content of each sampling point , the unit of soil total petroleum hydrocarbon content is mg/kg; (d)计算植被指数:根据步骤(b)所得芦苇植被的高光谱曲线数据,计算出每个采样点的44种植被指数;(d) calculate the vegetation index: according to the hyperspectral curve data of step (b) gained reed vegetation, calculate 44 kinds of vegetation indexes of each sampling point; (e)确定最佳预测模型:分别采用线性、对数、倒数、二次、三次、幂、S型曲线、指数函数模型对每个采样点44种植被指数与该采样点土壤总石油烃含量的关系进行拟合;确定最佳预测模型为TPH=0.131/RES,其中TPH为土壤总石油烃含量,土壤总石油烃含量的单位为mg/kg;RES为红边斜率,即波长在680-750nm范围内光谱反射率一阶微分的最大值;(e) Determine the best forecasting model: use linear, logarithmic, reciprocal, quadratic, cubic, power, S-curve, and exponential function models to compare the 44 vegetation indices of each sampling point with the total petroleum hydrocarbon content of the soil at the sampling point Fitting the relationship; determine the best prediction model as TPH=0.131/RES, where TPH is the total petroleum hydrocarbon content of the soil, and the unit of the total petroleum hydrocarbon content of the soil is mg/kg; RES is the slope of the red edge, that is, the wavelength is between 680- The maximum value of the first order differential of spectral reflectance in the range of 750nm; 2)土壤总石油烃含量高光谱预测模型的集成:将经过步骤1)所得预测模型集成到地物波谱仪的随机软件中,实现土壤石油污染的实时定位和定量监测;结合航空、航天遥感技术,进一步实现土壤石油污染的大面积快速监测。2) Integration of hyperspectral prediction model for soil total petroleum hydrocarbon content: integrate the prediction model obtained through step 1) into the random software of ground object spectrometer to realize real-time positioning and quantitative monitoring of soil oil pollution; combined with aviation and aerospace remote sensing technology , to further realize large-area rapid monitoring of soil oil pollution.
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CN105527230A (en) * 2015-12-04 2016-04-27 成都理工大学 High vegetation coverage area remote sensing prospecting method based on near-infrared band 670-
CN109543654A (en) * 2018-12-14 2019-03-29 常州大学 A kind of construction method for the modified vegetation index reflecting crop growth situation

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