CN112308398A - Risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species - Google Patents
Risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species Download PDFInfo
- Publication number
- CN112308398A CN112308398A CN202011171687.7A CN202011171687A CN112308398A CN 112308398 A CN112308398 A CN 112308398A CN 202011171687 A CN202011171687 A CN 202011171687A CN 112308398 A CN112308398 A CN 112308398A
- Authority
- CN
- China
- Prior art keywords
- plant
- invasive
- plants
- iai
- influence
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 241000196324 Embryophyta Species 0.000 title claims abstract description 351
- 238000000034 method Methods 0.000 title claims abstract description 23
- 238000012502 risk assessment Methods 0.000 title claims abstract description 14
- 238000011002 quantification Methods 0.000 title claims abstract description 11
- 238000011156 evaluation Methods 0.000 claims abstract description 7
- 241000894007 species Species 0.000 claims description 17
- 230000003211 malignant effect Effects 0.000 claims 6
- 238000011835 investigation Methods 0.000 claims 4
- 230000007613 environmental effect Effects 0.000 abstract description 4
- 230000009545 invasion Effects 0.000 description 21
- 208000015181 infectious disease Diseases 0.000 description 13
- 230000000694 effects Effects 0.000 description 5
- 230000003115 biocidal effect Effects 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 230000002265 prevention Effects 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 229910006119 NiIn Inorganic materials 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000012512 characterization method Methods 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000005183 environmental health Effects 0.000 description 1
- 230000004941 influx Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000031068 symbiosis, encompassing mutualism through parasitism Effects 0.000 description 1
Classifications
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q10/00—Administration; Management
- G06Q10/06—Resources, workflows, human or project management; Enterprise or organisation planning; Enterprise or organisation modelling
- G06Q10/063—Operations research, analysis or management
- G06Q10/0635—Risk analysis of enterprise or organisation activities
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q50/00—Information and communication technology [ICT] specially adapted for implementation of business processes of specific business sectors, e.g. utilities or tourism
- G06Q50/10—Services
- G06Q50/26—Government or public services
Landscapes
- Business, Economics & Management (AREA)
- Human Resources & Organizations (AREA)
- Engineering & Computer Science (AREA)
- Strategic Management (AREA)
- Economics (AREA)
- Tourism & Hospitality (AREA)
- General Physics & Mathematics (AREA)
- Theoretical Computer Science (AREA)
- Entrepreneurship & Innovation (AREA)
- Marketing (AREA)
- Development Economics (AREA)
- General Business, Economics & Management (AREA)
- Educational Administration (AREA)
- Physics & Mathematics (AREA)
- Quality & Reliability (AREA)
- Operations Research (AREA)
- Game Theory and Decision Science (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Primary Health Care (AREA)
- Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
Abstract
The invention relates to the relevant fields of invasive ecology, plant ecology, population ecology, community ecology, global change ecology, environmental ecology and the like, and discloses a risk assessment quantification method for the ecological influence of invasive plants on the diversity of plant species, which comprises five index systems: (I) the influence amplitude index IAI of invasive plants on the diversity of plant speciesS(ii) a (II) extent of influence of invasive plants on the diversity of plants Shannon index IAIH'(ii) a (III) the invasive plant influences the plant Simpson dominance degree by an amplitude index IAID(ii) a (IV) the extent of influence of the invasive plant on the Pielou evenness index IAI of the plantEH(ii) a (V) the influence amplitude index IAI of the invasive plant on the Margalef abundance of the plantF. The IAI is evaluated or averaged individually by the 5 indicesPTDThe method for evaluating the risk of the invasive plant on the ecological influence of the diversity of the plant species can be used for evaluating the risk of the invasive plant on the ecological influence of the diversity of the plant speciesAnd the evaluation quantification is simpler and more accurate. The method has the characteristics of convenience, rapidness, strong operability and high feasibility.
Description
Technical Field
The invention relates to the relevant fields of invasive ecology, plant ecology, population ecology, community ecology, global change ecology, environmental ecology and the like, and discloses a method for evaluating and quantifying risks of invasive plants on ecological influences of plant species diversity.
Background
At present, biological safety represented by biological invasion dominated by invasive plants has posed a serious threat to environmental health and ecological safety as well as to social sustainable development. Therefore, biosafety, represented by biological invasion dominated by invasive plants, has become one of the major environmental and ecological problems worldwide. Meanwhile, the national level also places high importance on biological safety, and brings the biological safety into the national safety system for supervision. Therefore, the risk assessment of ecological influence of invasive plants on the ecosystem has become one of the most concerned core scientific problems in the field of global environmental ecology research.
The core of the normal execution of the structure and the function of the ecosystem is the species diversity of the ecosystem. Therefore, under the background of a new era, in order to construct 'modern beautiful China with harmonious symbiosis between human and nature', the ecological impact risk assessment caused by the biosafety represented by the biological invasion dominated by the invasive plant is urgently needed, on one hand, a solid theoretical basis is laid for measuring the ecological harm degree of the invasive plant to the structure and the function of an ecological system, particularly the diversity of species and the like, and on the other hand, a solid scientific basis, a theoretical support, an effective execution basis and an effective practical guide are provided for carrying out precise administrative decision management and effective early warning prevention and control deployment aiming at the biosafety problem represented by the biological invasion. Although the existing quantification method aims at evaluating the risk of the invasive plants on the ecological influence of the diversity of plant species, the quantification method is not uniform and is relatively complicated. Therefore, a set of simpler, more accurate and feasible scientific quantitative index system is needed to be provided to evaluate and determine the risk of the invasive plant on the ecological influence of the diversity of the plant species, so as to lay a strong theoretical support and practical foundation for deeply clarifying the driving mechanism of the invasive plant successful invasion and further constructing an invasive plant ecological management and early warning prevention and control system.
Disclosure of Invention
The invention provides a risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species, which comprises the following five index systems:
(I) indexes for representing risk assessment of plant species diversity ecological influence of invasive plants: the extent of Influence of the invasive plant on the diversity of plant species is an index [ infection index of important plants on specific varieties (S), IAIS];
(II) indexes for characterizing risk assessment of invasive plants on plant Shannon diversity ecological impact: the magnitude of the effect of invasive plants on plant Shannon diversity index [ infection amplitude index of origin innovative plants on Shannon's diversity (H'), IAIH'];
(III) indexes for representing risk assessment of ecological influence of invasive plants on Simpson dominance degree: the magnitude of Influence of invasive plants on the dominance of Simpson plants [ infection amplitude index of infinite invasive plants on Simpson's dominance (D), IAID];
(IV) characterization of invasive plants on the Pielou plants for uniformityIndexes of state impact risk assessment: the magnitude of Influence of the invasive plant on the uniformity of the plant Pielou [ fluorescence amplitude index of infinite innovative plants on Pielou's evaluation (E)H),IAIEH];
(V) representing indexes of risk evaluation of the invasive plants on ecological influence of Margalef abundance on plants: the magnitude of Influence of the invasive plant on the abundance of Margalef plants [ infection amplitude index of infinite innovative plants on Margalef's richness (F), IAIF]。
The invention independently evaluates or calculates the average value of the 5 indexes to obtain the influence amplitude IAI of invasive plants on the diversity of plant speciesPTDA method for assessing the risk of an invasive plant ecologically affecting the diversity of plant species.
In the technical scheme of the invention, the parameters are as follows:
(I) the extent of Influence of the invasive plant on the diversity of plant species is an index [ infection index of important plants on specific varieties (S), IAIS]Calculated according to the following formula:
IAIS=1-(Si/Sck)
in the formula, SiThe diversity of the plant species into which the invasive plant has invaded (i.e. the number of all plant species),
Sckthe variety of the plants which are not invaded by the invaded plants.
IAISA larger value indicates a greater risk of the invasive plant having an ecological impact on the diversity of the plant species.
(II) the breadth index of the effect of an invasive plant on the diversity of plants [ infection amplitude index of antibiotic innovative plants on Shannon's diversity (H'), IAIH']Calculated according to the following formula:
IAIH'=1-(H'i/H'ck)
in the formula (II), H'iThe plant Shannon diversity, H 'to which the invasive plant has invaded'ckThe Shannon diversity of the plant which is not invaded by the invader.
IAIH'The larger the value is, the moreThe greater the risk of ecological impact of the invasive plant on the Shannon diversity of the plant.
Wherein the plant Shannon diversity is calculated according to the following formula (Shannon CE, Weaver W.1949.the chemical Theory of communication. university of Illinois Press, Urbana, Illinois, pp.1-117.):
wherein S is the diversity of plant species (i.e., the number of all plant species) of the survey sample.
PiTo investigate the relative abundance of plant i, P, within a samplei=niN, wherein NiIn order to investigate the number of plants of plant i in the sample side, N is the total number of plants of all plants in the investigated sample side.
(III) the magnitude of the Effect of invasive plants on Simpson dominance index [ infection amplitude index of iterative innovative plants on Simpson's dominance (D), IAID]Calculated according to the following formula:
IAID=1-(Di/Dck)
in the formula, DiPlant Simpson dominance for invaded plantckThe plant Simpson dominance of the non-invasive species of the invasive plant.
IAIDA larger value indicates a greater risk of the invasive plant having an ecological impact on the dominance of the plant Simpson.
Wherein the plant Simpson dominance is calculated according to the following formula (Simpson EH.1949.measurement of diversity. Nature 163: 688.):
wherein S is the diversity of plant species (i.e., the number of all plant species) of the survey sample. n isiIn order to investigate the number of plants of plant i in the sample side, N is the total number of plants of all plants in the investigated sample side.
(IV) the magnitude of the Influence of the invasive plant on the uniformity of the plant Pielou [ infection index of antibiotic innovative plants on Pielou's evaluation (E)H),IAIEH]Calculated according to the following formula:
IAIEH=1-(EHi/EHck)
in the formula, EHiPielou homogeneity of plants from which the plants have invaded the species, EHckPlant Pielou uniformity for non-invasive species of invasive plants.
IAIEHA larger value indicates a greater risk of the invasive plant having an ecological impact on the Pielou homogeneity of the plant.
Wherein the plant Pielou homogeneity is calculated according to the following formula (Pielou EC.1966.the measurement of diversity in diversity types of biological classifications. journal of biological Biology 13: 131-:
wherein H' is the Shannon diversity of the plant of the survey sample, and S is the plant species diversity of the survey sample (i.e., the number of all plant species).
(V) the magnitude of Influence of the invasive plant on the abundance of Margalef plants [ infection amplitude index of infinite innovative plants on Margalef's richness (F), IAIF]Calculated according to the following formula:
IAIF=1-(Fi/Fck)
in the formula, FiMargalef's plant abundance, F, for an invaded species of plantckMargalef, a plant not invaded by invasive plants.
IAIFA higher value indicates a higher risk of the invasive plant having an ecological impact on the richness of the plant Margalef.
Wherein the plant Margalef abundance index is calculated according to the following formula (Margalef R.1951. diversified de especies en las populations naturales (Vol.6, pp.59-72). Barcelona: public cities institute to de biologica Aplica.):
wherein S is the variety of the plant species (i.e., the number of all plant species) of the survey sample, and N is the total number of plants of all plants in the survey sample.
The invention has the beneficial effects that:
(1) the invention independently evaluates or calculates the average value of the 5 indexes to obtain the influence amplitude IAI of invasive plants on the diversity of plant speciesPTDThe method for evaluating the risk of the invasive plant on the ecological influence of the diversity of the plant species can carry out simpler and more accurate evaluation and quantification on the risk of the invasive plant on the ecological influence of the diversity of the plant species.
(2) The method has the characteristics of convenience, rapidness, strong operability and high feasibility.
Detailed Description
In order to quantitatively evaluate the risk of ecological influence of invasive plants on the diversity of plant species, 30 invasive samples (2m × 2m) and 30 non-invasive sample samples (2m × 2m) of a herbaceous invasive plant were randomly investigated in the field. The number of all plant species, the number of plants per plant and the total number of plants per plant were recorded for each sample. Then calculating the species diversity of each sample, namely: plant species diversity (i.e.number of all plant species) (S), plant Shannon diversity (H'), plant Simpson dominance (D), plant Pielou uniformity (E)H) Margalef plant abundance (F). The data are tabulated below:
TABLE 1 species diversity of unintrusive squares
TABLE 2 species diversity of low intrusion swatches
TABLE 3 species diversity of highly invasive species
Then, the average value of the species diversity of the non-invasive sample and the invasive sample is calculated in sequence. The data are tabulated below:
TABLE 4 comparison of species diversity of different invasion degree varieties of invasive plants
Then, according to a set of ecological impact risk assessment and quantification methods for the diversity of plant species by the invasive plant, respectively calculating an impact amplitude index (S) of the invasive plant on the diversity of plant species, IAIS]And the magnitude index of the effect of the invasive plant on the Shannon diversity of the plant [ infection amplitude index of origin innovative plants on Shannon's diversity (H'), IAIH']And the dominance of the invasive plant to the plant SimpsonInfluence amplitude index [ influx index of Influence innovative places on Simpson's domino (D), IAID]And the Influence amplitude index of the invasive plant on the plant Pielou uniformity [ infection amplitude index of ideal invasive plants on Pielou's evaluation (E)H),IAIEH]And the magnitude index of Influence of the invasive plant on the Margalef abundance of the plant [ infection amplitude index of ideal invasive plants on Margalef's richness (F), IAIF]And the magnitude of the effect of the invasive plant on the diversity of the plant species [ infection amplitude index of infinite plants on Plant Taxon Diversity (PTD), IAIPTD]. The data are tabulated below:
TABLE 5 quantitative comparison of risk assessment of ecological impact on plant species diversity by invasive plants of different invasive degrees
IAIS | IAIH' | IAID | IAIEH | IAIF | IAIPTD | |
Low-degree invasion sample | 0.155689 | 0.114627 | 0.074621 | 0.011881 | 0.189563 | 0.109276 |
High intrusion proof cube | 0.479042 | 0.626751 | 0.616617 | 0.378587 | 0.602361 | 0.540672 |
According to the result, the influence range of the low-degree invasion of the invasive plant on the diversity of the plant species reaches the level i (the ecological influence risk is general, and the identification color can adopt yellow), and the influence range of the high-degree invasion of the invasive plant on the diversity of the plant species reaches the level ii (the ecological influence risk is serious, and the identification color can adopt orange); the low degree of invasion of the invasive plant has the influence on the diversity of the plant Shannon reaching the level i (the ecological influence risk is general, the identification color can adopt yellow), and the high degree of invasion of the invasive plant has the influence on the diversity of the plant Shannon reaching the level ii (the ecological influence risk is serious, and the identification color can adopt orange); the influence range of the low-degree invasion of the invasive plant on the Simpson dominance of the plant reaches the level i (the ecological influence risk is general, and the identification color can adopt yellow), and the influence range of the high-degree invasion of the invasive plant on the Simpson dominance of the plant reaches the level ii (the ecological influence risk is serious, and the identification color can adopt orange); the influence range of the low-degree invasion of the invasive plant on the Pielou uniformity of the plant reaches the level i (the ecological influence risk is general, and the identification color can adopt yellow), and the influence range of the high-degree invasion of the invasive plant on the Pielou uniformity of the plant reaches the level ii (the ecological influence risk is serious, and the identification color can adopt orange); the influence range of the low-degree invasion of the invasive plant on the Margalef richness of the plant reaches a level i (the ecological influence risk is general, and the identification color can adopt yellow), and the influence range of the high-degree invasion of the invasive plant on the Margalef richness of the plant reaches a level ii (the ecological influence risk is serious, and the identification color can adopt orange); the low degree invasion of the invasive plant has the influence on the diversity of the plant species reaching the level i (the ecological influence risk is general, and the identification color can adopt yellow), and the high degree invasion of the invasive plant has the influence on the diversity of the plant species reaching the level ii (the ecological influence risk is serious, and the identification color can adopt orange). Therefore, the invasive plant has a general ecological influence risk when the invasive plant is slightly invasive, can be classified as a general invasive plant, and the identification color can adopt yellow. However, when the invasion degree is increased to high invasion, the ecological influence risk is serious, the plants can be classified as serious invasive plants, and the identification color can be orange.
Claims (8)
1. The risk assessment and quantification method for the ecological influence of the invasive plants on the diversity of plant species is characterized in that the risk assessment and quantification method is implemented by the aid of an impact amplitude index IAI of the invasive plants on the diversity of plant speciesSInvasive plant has an amplitude index IAI on the Shannon diversity of plantsH'The magnitude index IAI of the influence of the invasive plant on the dominance of the Simpson plantDThe influence amplitude index IAI of the invasive plants on the Pielou evenness of the plantsEHThe influence amplitude index IAI of invasive plants on the Margalef abundance of plantsF5 indexes are used for evaluating or calculating the average value of the influence amplitude IAI of invasive plants on the diversity of plant species independentlyPTDA method of evaluation.
2. The method for assessing and quantifying the risk of the invasive plant on ecologically affecting the diversity of plant species as recited in claim 1, wherein each index specifically comprises:
(I) the influence amplitude index IAI of invasive plants on the diversity of plant speciesSCalculated according to the following formula:
IAIS=1-(Si/Sck)
in the formula, SiThe diversity of plant species into which the invasive plant has invaded, namely: number of all plant species;
Sckthe variety of plant species of the non-invasive sample of the invasive plant;
IAISa larger value indicates a greater risk of the invasive plant ecologically affecting the diversity of the plant species;
(II) extent of influence of invasive plants on the diversity of plants Shannon index IAIH'Calculated according to the following formula:
IAIH'=1-(H'i/H'ck)
in the formula (II), H'iThe plant Shannon diversity, H 'to which the invasive plant has invaded'ckThe Shannon diversity of the plant which is not invaded by the invaded plant;
IAIH'a larger value indicates a greater risk of the invasive plant having an ecological impact on the Shannon diversity of the plant;
wherein the plant Shannon diversity is calculated according to the following formula:
wherein S is the plant species diversity of the survey sample, namely: number of all plant species;
Pito investigate the relative abundance of plant i, P, within a samplei=niN, wherein NiThe number of plants of the plant i in the investigation sample prescription is obtained, and N is the total number of plants of all plants in the investigation sample prescription;
(III) the invasive plant influences the plant Simpson dominance degree by an amplitude index IAIDCalculated according to the following formula:
IAID=1-(Di/Dck)
in the formula, DiPlant Simpson dominance for invaded plantckThe plant Simpson dominance of the non-invasive species of the invasive plant;
IAIDa larger value indicates a larger risk of the invasive plant having an ecological impact on the dominance of the plant Simpson;
wherein the plant Simpson dominance is calculated according to the following formula:
wherein S is the plant species diversity of the survey sample, namely: number of all plant species;
nithe number of plants of the plant i in the investigation sample prescription is obtained, and N is the total number of plants of all plants in the investigation sample prescription;
(IV) the extent of influence of the invasive plant on the Pielou evenness index IAI of the plantEHCalculated according to the following formula:
IAIEH=1-(EHi/EHck)
in the formula, EHiPielou homogeneity of plants from which the plants have invaded the species, EHckPlant Pielou uniformity for non-invasive species of invasive plants;
IAIEHa larger value indicates a greater risk of the invasive plant having an ecological impact on the Pielou evenness of the plant;
wherein the plant Pielou uniformity is calculated according to the following formula:
wherein H' is the plant Shannon diversity of the survey sample, S is the plant species diversity of the survey sample, namely: number of all plant species;
(V) the influence amplitude index IAI of the invasive plant on the Margalef abundance of the plantFCalculated according to the following formula:
IAIF=1-(Fi/Fck)
in the formula, FiMargalef's plant abundance, F, for an invaded species of plantckThe Margalef abundance of the plant which is a non-invasive sample of the invasive plant;
IAIFa larger value indicates a greater risk of the invasive plant having an ecological impact on the richness of the plant Margalef;
wherein the Margalef abundance index of the plant is calculated according to the following formula:
wherein S is the plant species diversity of the survey sample, namely: number of all plant species; n is the total number of plants of all plants in the survey sample.
3. The method for assessing and quantifying the risk of ecologically affecting the diversity of plant species by invasive plants according to claim 2, wherein the selected survey sample in index (I) is divided into two categories, namely: the invasive plant invades the sample side and the invasive plant does not invade the sample side;
the selection quantity of the invaded sample parties and the non-invaded sample parties of the invaded plant is at least 3, and the more the selection quantity of the sample parties is, the better the selection quantity is;
the survey sample size recommendation is set as: (1) and (3) arbor: 20m by 20 m; (2) and (3) shrub: 10m by 10 m; (3) herbaceous: 2m by 2 m; (4) moss: 0.5m by 0.5 m;
the magnitude of the impact of invasive plants on plant species diversity can be divided into three levels, namely: (i)0.00<IAIS≤0.35;(ii)0.35<IAIS≤0.75;(iii)0.75<IAISThe plant identification color is less than or equal to 1.00, and the plant species diversity influence range reaches the i level, the plant can be classified as a general invasive plant, the ecological influence risk is general, and the identification color can adopt yellow;
the plants with the variety influence range reaching the level ii can be classified as serious invasive plants, the ecological influence risk is serious, and the identification color can be orange; the plants with the diversity influence range reaching the iii level can be classified as malignant invasive plants, the ecological influence risk is very serious, and the identification color can adopt red.
4. The method for assessing and quantifying the risk of ecologically affecting the diversity of plant species by invasive plants according to claim 2, wherein the selected survey sample In Index (II) is divided into two categories, namely: the invasive plant invades the sample side and the invasive plant does not invade the sample side;
the selection quantity of the invaded sample parties and the non-invaded sample parties of the invaded plant is at least 3, and the more the selection quantity of the sample parties is, the better the selection quantity is;
the survey sample size recommendation is set as: (1) and (3) arbor: 20m by 20 m; (2) and (3) shrub: 10m by 10 m; (3) herbaceous: 2m by 2 m; (4) moss: 0.5m by 0.5 m;
the magnitude of the impact of invasive plants on the Shannon diversity of plants can be divided into three levels, namely: (i)0.00<IAIH'≤0.35;(ii)0.35<IAIH'≤0.75;(iii)0.75<IAIH'The identification color can be yellow, and the identification color can be classified into a general invasive plant with the influence range of the Shannon diversity of the plant reaching the i level, the ecological influence risk is general; the plant which has the influence range of Shannon diversity reaching the level ii can be classified as a serious invasive plant, the ecological influence risk is serious, and the identification color can be orange; the plants with the Shannon diversity influence amplitude reaching the iii level can be classified as malignant invasive plants, the ecological influence risk is very serious, and the identification color can adopt red.
5. The method for assessing and quantifying the risk of ecologically affecting the diversity of plant species by invasive plants according to claim 2, wherein the selected survey sample in index (III) is divided into two categories, namely: the invasive plant invades the sample side and the invasive plant does not invade the sample side;
the selection quantity of the invaded sample parties and the non-invaded sample parties of the invaded plant is at least 3, and the more the selection quantity of the sample parties is, the better the selection quantity is;
the survey sample size recommendation is set as: (1) and (3) arbor: 20m by 20 m; (2) and (3) shrub: 10m by 10 m; (3) herbaceous: 2m by 2 m; (4) moss: 0.5m by 0.5 m;
the influence of the invasive plant on the Simpson dominance of the plant can be divided into three levels, namely: (i)0.00<IAID≤0.35;(ii)0.35<IAID≤0.75;(iii)0.75<IAIDThe influence range on the dominance of the plant Simpson is less than or equal to 1.00, the plant Simpson can be classified as a general invasive plant, the ecological influence risk is general, and the identification color can be yellow; to pairThe plants with the influence range of Simpson dominance reaching the level ii can be classified as serious invasive plants, the ecological influence risk is serious, and the identification color can be orange; the plants with the influence range of Simpson dominance reaching the iii level can be classified as malignant invasive plants, the ecological influence risk is very serious, and the identification color can be red.
6.The method for assessing and quantifying the risk of ecologically affecting the diversity of plant species by invasive plants according to claim 2, wherein the selected survey sample in Index (IV) is divided into two categories, namely: the invasive plant invades the sample side and the invasive plant does not invade the sample side;
the selection quantity of the invaded sample parties and the non-invaded sample parties of the invaded plant is at least 3, and the more the selection quantity of the sample parties is, the better the selection quantity is;
the survey sample size recommendation is set as: (1) and (3) arbor: 20m by 20 m; (2) and (3) shrub: 10m by 10 m; (3) herbaceous: 2m by 2 m; (4) moss: 0.5m by 0.5 m;
the influence of the invasive plants on the Pielou uniformity of the plants can be divided into three levels, namely: (i)0.00<IAIEH≤0.35;(ii)0.35<IAIEH≤0.75;(iii)0.75<IAIEHThe plant Pielou uniformity is less than or equal to 1.00, and the plant Pielou uniformity reaches the level i, the plant can be classified as a general invasive plant, the ecological influence risk is general, and the identification color can be yellow; the plants with the Pielou uniformity influence amplitude reaching the level ii can be classified as serious invasive plants, the ecological influence risk is serious, and the identification color can be orange; plants with Pielou uniformity affecting the magnitude of iii level can be classified as malignant invasive plants, the ecological impact risk is very serious, and the identification color can be red.
7. The method for assessing and quantifying the risk of ecologically affecting the diversity of plant species by invasive plants according to claim 2, wherein the selected survey sample in the index (V) is divided into two categories, namely: the invasive plant invades the sample side and the invasive plant does not invade the sample side;
the selection quantity of the invaded sample parties and the non-invaded sample parties of the invaded plant is at least 3, and the more the selection quantity of the sample parties is, the better the selection quantity is;
the survey sample size recommendation is set as: (1) and (3) arbor: 20m by 20 m; (2) and (3) shrub: 10m by 10 m; (3) herbaceous: 2m by 2 m; (4) moss: 0.5m by 0.5 m;
the influence range of the invasive plants on the Margalef richness of the plants can be divided into three levels, namely: (i)0.00<IAIF≤0.35;(ii)0.35<IAIF≤0.75;(iii)0.75<IAIFThe mark color can be yellow, and the mark color can be general invasive plants with the influence range reaching the i level on the Margalef abundance of the plants, the ecological influence risk is general; the plant Margalef with the influence range reaching the level ii can be classified as a serious invasive plant, the ecological influence risk is serious, and the identification color can be orange; the plants with the Margalef richness influence reaching the iii level can be classified as malignant invasive plants, the ecological influence risk is very serious, and the identification color can be red.
8. The method for assessing and quantifying the risk of ecologically affecting the diversity of plant species by an invasive plant according to claim 1, wherein the magnitude of the impact IAI of the invasive plant on the diversity of plant speciesPTDCalculated according to the following formula:
the magnitude of the impact of invasive plants on the diversity of plant species can be divided into three levels, namely: (i)0.00<IAIPTD≤0.35;(ii)0.35<IAIPTD≤0.75;(iii)0.75<IAIPTDThe identification color can be yellow, and the identification color can be classified into general invasive plants with the influence range reaching the i level on the diversity of plant species, the ecological influence risk is general; the plants with the variety influence amplitude reaching the level ii can be classified as serious invasive plants, the ecological influence risk is serious, and the identification color can be orange; the plants with the variety influence amplitude reaching the iii level can be classified as malignant invasive plants, the ecological influence risk is very serious, and the identification color can adopt red.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202011171687.7A CN112308398A (en) | 2020-10-28 | 2020-10-28 | Risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202011171687.7A CN112308398A (en) | 2020-10-28 | 2020-10-28 | Risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species |
Publications (1)
Publication Number | Publication Date |
---|---|
CN112308398A true CN112308398A (en) | 2021-02-02 |
Family
ID=74331276
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202011171687.7A Pending CN112308398A (en) | 2020-10-28 | 2020-10-28 | Risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN112308398A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113222222A (en) * | 2021-04-23 | 2021-08-06 | 贵州民族大学 | Method for measuring invasion risk of foreign species in grass sea wetland |
CN113420977A (en) * | 2021-06-18 | 2021-09-21 | 中国水产科学研究院黄海水产研究所 | Risk quantitative evaluation method for ecological influence of sudden jellyfish on marine swimming animals |
CN116304600A (en) * | 2023-03-06 | 2023-06-23 | 四川省林业科学研究院 | Foreign invasive species early warning method and system based on big data analysis |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105493858A (en) * | 2015-12-24 | 2016-04-20 | 中国矿业大学(北京) | Method for performing long-term monitoring of dynamic change of sand vegetation diversity in western mining areas |
CN110928926A (en) * | 2019-12-03 | 2020-03-27 | 华中农业大学 | Method for measuring diversity of plants |
-
2020
- 2020-10-28 CN CN202011171687.7A patent/CN112308398A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105493858A (en) * | 2015-12-24 | 2016-04-20 | 中国矿业大学(北京) | Method for performing long-term monitoring of dynamic change of sand vegetation diversity in western mining areas |
CN110928926A (en) * | 2019-12-03 | 2020-03-27 | 华中农业大学 | Method for measuring diversity of plants |
Non-Patent Citations (1)
Title |
---|
CONGYAN WANG等: "Moderate and heavy Solidago canadensis L. invasion are associated with decreased taxonomic diversity but increased functional diversity of plant communities in East China", ECOLOGICAL ENGINEERING, 31 March 2018 (2018-03-31), pages 56 - 57 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113222222A (en) * | 2021-04-23 | 2021-08-06 | 贵州民族大学 | Method for measuring invasion risk of foreign species in grass sea wetland |
CN113420977A (en) * | 2021-06-18 | 2021-09-21 | 中国水产科学研究院黄海水产研究所 | Risk quantitative evaluation method for ecological influence of sudden jellyfish on marine swimming animals |
CN116304600A (en) * | 2023-03-06 | 2023-06-23 | 四川省林业科学研究院 | Foreign invasive species early warning method and system based on big data analysis |
CN116304600B (en) * | 2023-03-06 | 2024-02-02 | 四川省林业科学研究院 | Foreign invasive species early warning method and system based on big data analysis |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN112308398A (en) | Risk assessment and quantification method for ecological influence of invasive plants on diversity of plant species | |
Katsiapi et al. | Watershed land use types as drivers of freshwater phytoplankton structure | |
Ninčević-Gladan et al. | The response of phytoplankton community to anthropogenic pressure gradient in the coastal waters of the eastern Adriatic Sea | |
Brito et al. | Defining phytoplankton class boundaries in Portuguese transitional waters: An evaluation of the ecological quality status according to the Water Framework Directive | |
Borics et al. | The role of phytoplankton diversity metrics in shallow lake and river quality assessment | |
Ban et al. | Application of composite water quality identification index on the water quality evaluation in spatial and temporal variations: a case study in Honghu Lake, China | |
Lücke et al. | Detection of ecological change in stream macroinvertebrate assemblages using single metric, multimetric or multivariate approaches | |
Feng et al. | Can tintinnids be used for discriminating water quality status in marine ecosystems? | |
Cupertino et al. | Phytoplankton assemblage composition as an environmental indicator in routine lentic monitoring: Taxonomic versus functional groups | |
Nõges et al. | Spatial and annual variability of environmental and phytoplankton indicators in Lake Võrtsjärv: implications for water quality monitoring | |
Chabrerie et al. | Biodiversity and ecosystem functions in wetlands: a case study in the estuary of the Seine river, France | |
Chun et al. | Diversity patterns and phylogenetic structure of vascular plants along elevational gradients in a mountain ecosystem, South Korea | |
Matsuda et al. | Colonization status and community structure of arbuscular mycorrhizal fungi in the coniferous tree, Cryptomeria japonica, with special reference to root orders | |
CN112581038A (en) | Mangrove wetland health condition evaluation method | |
Brabec et al. | Macrophytes and diatoms—major results and conclusions from the STAR project | |
Peng et al. | Annual changes in periphyton communities and their diatom indicator species, in the littoral zone of a subtropical urban lake restored by submerged plants | |
Zhang et al. | Distribution patterns and associations of dominant tree species in a mixed coniferous-broadleaf forest in the Changbai Mountains | |
Vieira et al. | The relevance of bryophytes in the macrophyte-based reference conditions in Portuguese rivers | |
Adloff et al. | Analysis of the phytoplankton community emphasizing cyanobacteria in four cascade reservoirs system of the Iguazu River, Paraná, Brazil | |
Kowal et al. | Atmospheric pollution, soil nutrients and climate effects on Mucoromycota arbuscular mycorrhizal fungi | |
CN107400723A (en) | The authentication method and purposes of seed plant species | |
Zhang et al. | Distinct community assembly and co‐existence of arbuscular mycorrhizal fungi and diazotrophs across large‐scale soil fertility to improve functions in alfalfa cultivation systems | |
CN111340671A (en) | Method for carrying out detection of connectivity between species by using mathematical mode | |
CN112801471B (en) | Method for quantifying competitive dominance of invasive plant | |
Tian et al. | Habitat ecological characteristics and soil fungal community structure of Paphiopedilum subgenus Brachypetalum Hallier (Orchidaceae) plants in Southwest China |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |