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Development of a cost efficient model for nature conservati Development of a cost efficient model for nature conservati

Development of a cost efficient model for nature conservati - PowerPoint Presentation

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Development of a cost efficient model for nature conservati - PPT Presentation

David Lehrer Advisors Prof Pua Bar Kutiel and Prof Nir Becker The aim of this study is to estimate the marginal cost function and marginal benefit function for nature conservation in Israel and to use these functions to build a supply curve for nature conservation in Israel ID: 533589

nature conservation area cost conservation nature cost area species israel size data budgets initial areas development reserves 106 000

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Slide1

Development of a cost efficient model for nature conservation in Israel

David Lehrer

Advisors

Prof Pua Bar Kutiel and Prof Nir BeckerSlide2

The aim of this study is to estimate the marginal cost function and marginal benefit function for nature conservation in Israel and to use these functions to build a supply curve for nature conservation in Israel.

Development of a cost efficient model for nature conservation in IsraelSlide3

[1]

Where;

Cost

is the cost of operating the PA, x1,2,3… are the coefficients found in the multiple regression step analysis for a value of each predictor such as the area of nature reserves, the species richness in the area, the number of Redbook species in the area, a measure of ecosystem heterogeneity and other factors.

Development of a cost efficient model for nature conservation in IsraelSlide4

[2]

Where;

Benefit

is the benefit that the PA provides to nature conservation, AA, BB, CC … are the factors for establishing conservation priorities such as, species richness, the number of Redbook species, ecosystem heterogeneity and other factors, W1, W2, W3…are the relative weights of conservation importance for each factor. These weights will be derived from the opinions of conservation experts.

Development of a cost efficient model for nature conservation in IsraelSlide5

Development of a cost efficient model for nature conservation in Israel

The model will be used to estimate the cost efficient distribution of limited conservation funding as well as to estimate the gap between current expenditure on conservation in Israel and the expenditure necessary to effectively achieve conservation goals.Slide6

Literature Review the Cost of Protecting NatureSlide7

Literature Review the Cost of Protecting Nature

Conclusions from Literature Review:

PA Size is a positive predictor of conservation costs

No consensus on other predictors Slide8

Hypothesis

We

expect to find that

PA size

is a significant predictor of the variation in costs in Israel.

We expect to find that in addition to PA size, at least

one or more additional PA attributes contributes

significantly to predicting variation in conservation costs.

By studying the nature conservation marginal cost function, significant

cost efficiencies

can be achieved which will enable a

higher level of nature conservation (more conservation goals achieved) for a given budget or enable reaching a given level of nature conservation (specific conservation goals) for a lower budget.Slide9

Methodology

Data Mining:

INPA budgets

GIS - species richness

GIS - abundance

GIS - red

b

ook species

GIS – habitat

h

eterogeneity

Expert Surveys:

Invasive species

Tourism

Forest Fire Threat

Adequate

resources

Linear RegressionSlide10

Data Normalization

Financial Data – Range Area Budgets

Spatial Data – Reserve Areas

Species Data – Species Presence in Range AreasRed Book Species Data – Red Book Species Presence in Range AreasFire Threat – GIS LayerTourism – List of tourist sites

Habitat Heterogeneity Data - UnfinishedSlide11

Financial Data

Organizational Structure of INPA

National Office in Jerusalem

5 Districts15 Regions43 Ranger AreasOver 600 Nature ReservesSlide12

Financial Data

Decided not to study Yehuda and

Shomron

4 Districts13 Regions37 Ranger AreasOver 600 Nature ReservesSlide13

Financial Data

Original intended study unit: nature

r

eservesINPA budgets are set by DistrictsNo way to determine a budget for a nature reserveMany conservation activities which protect the reserves takes place outside of the reserves – control of invasive species, supervision of infrastructure work

Unit of study: Ranger Areas

Needed to transform District Budgets to Ranger Area BudgetsSlide14

Slide15

INPA Northern DistrictSlide16

In order to create Range Area Budgets

District Operation Budgets

Ranger Areas

Manager Surveys

Ranger Area Budgets

District Development BudgetsSlide17

District Operation BudgetsSlide18

District Development BudgetsSlide19

Data Sets for Cost Function

N = 37 Ranger Areas

Regression

Dependent Variable: Range Area BudgetCandidate Independent Variables:Range areas size

Aggregate reserve area

Number of reserves

Species richness

Species diversityThreatened species

Invasive species

Fire threat

TourismSlide20

Analysis of Data

אושר מינים

אזור פיקוח

תקציב שוטף

תקציב פיתוח

סה"כ תקציבים 2013 בש"ח

שטח פיקוח

שטח שמורות

יחס שמורה לפיקוח

מספר שמורות

נתוני נוכחות

מינים אדומים נומינלי

מינים אדומים משוקלל

חרמון

1,089,525

145,633

1,235,158

312.54

7.45

0.02

12

1,704

231

14,699

מרכז הגולן

1,089,525

145,633

1,235,158

459.89

28.89

0.06

19

1,147

2

75

יהודיה

1,089,525

145,633

1,235,158

132.53

36.73

0.28

3

919

0

0

דרום הגולן

1,089,525

145,633

1,235,158

329.76

60.72

0.18

13

1,254

19

903

גליל עליון מזרחי

1,198,478

144,106

1,342,583

467.88

46.21

0.10

37

1,679

70

4,133

הר מירון

1,198,478

144,106

1,342,583

231.30

101.77

0.44

14

1,370

33

1,520

גליל מערבי

1,198,478

144,106

1,342,583

274.84

24.99

0.09

12

883

0

0

חוף ים גליל מערבי

1,198,478

144,106

1,342,583

240.57

13.74

0.06

10

1,281

38

2,225

כנרת וגליל תחתון

980,573

157,106

1,137,678

428.96

19.53

0.05

13

1,324

0

0

גליל תחתון מערבי

980,573

151,106

1,131,678

456.42

16.21

0.04

13

1,315

3

111

גליל תחתון מזרחי

980,573

151,106

1,131,678

293.37

50.83

0.17

8

1,076

0

0

גלבוע

980,573

351,106

1,331,678

500.19

32.50

0.06

16

1,345

0

0

אלונים - שפרעם

1,162,160

155,467

1,317,627

418.81

4.27

0.01

7

1,232

14

565

כרמל

1,162,160

155,467

1,317,627

432.48

63.77

0.15

21

1,631

34

1,527

מנשה - אלונה

1,162,160

197,689

1,359,849

460.35

14.67

0.03

22

1,554

76

4,213

שרון

2,035,639

61,500

2,097,139

613.07

2.68

0.00

16

1,494

116

5,798

פלשת

678,546

65,500

744,046

946.08

14.18

0.01

7

1,768

8

313

ירושלים

1,357,093

0

1,357,093

119.90

0.31

0.00

2

1,257

15

620

הרי יהודה

2,035,639

33,000

2,068,639

417.05

25.16

0.06

16

1,370

0

0

שפלה דרומית

2,035,639

42,500

2,078,139

633.29

19.73

0.03

3

1,119

0

0

מישור חוף דרומי

1,357,093

102,500

1,459,593

861.79

33.05

0.04

11

1,247

0

0

מדבר יהודה

2,134,974

11,000

2,145,974

1,251.68

282.34

0.23

4

1,354

15

656

נגב צפוני

533,743

54,833

588,577

625.63

7.23

0.01

3

976

0

0

נגב מערבי

1,601,230

11,000

1,612,230

700.73

7.53

0.01

3

793

0

0

ערבה צפונית

533,743

53,750

587,493

891.79

383.41

0.43

5

788

0

0

בקעת צין והמכתש הגדול

1,067,487

11,000

1,078,487

1,133.90

315.12

0.28

9

945

0

0

עין עבדת ובקעת צין

1,601,230

11,000

1,612,230

58.45

19.98

0.34

1

590

0

0

ערבה מרכזית ועשוש

533,743

53,750

587,493

1,148.97

432.78

0.38

5

720

0

0

חולות עגור

1,067,487

11,000

1,078,487

1,511.45

240.24

0.16

4

849

0

0

הר הנגב הגבוה

533,743

30,833

564,577

1,048.53

125.78

0.12

4

788

0

0

מכתש רמון

533,743

11,000

544,743

889.63

558.67

0.63

2

886

15

606

מזרח הרמון

1,067,487

11,000

1,078,487

100.01

89.29

0.89

2

320

0

0

הר הנגב הדרומי

533,743

30,833

564,577

1,218.50

970.78

0.80

4

608

0

0

נחלים גדולים

878,296

137,417

1,015,713

1,410.63

431.95

0.31

6

572

0

0

ערבה דרומית

878,296

189,083

1,067,380

430.07

209.10

0.49

5

771

0

0

הרי אילת

878,296

162,417

1,040,713

383.46

310.99

0.81

4

970

0

0

מפרץ אילת

1,129,238

54,083

1,183,321

28.91

1.72

0.06

3

97

0

0Slide21

Initial Results

Range Area SizeSlide22

Initial Results

Range Area SizeSlide23

Initial Results

Range Area SizeSlide24

Initial Results

Reserve AreaSlide25

Initial Results

Reserve AreaSlide26

Initial Results

Reserve AreaSlide27

Slide28

Slide29

Initial Results

Reserve Area LnSlide30

Initial Results

Reserve Area LnSlide31

Initial Results

Reserve Area LnSlide32

Initial Results

Reserve Area LnSlide33

Literature Review the Cost of Protecting Nature

Conclusions from Literature Review:

PA Size is a positive predictor of conservation costs

No consensus on other predictors Slide34

So Far

Research Hypothesis

This study will test the following hypotheses:

From a review of previous studies on the cost of nature conservation we expect to find that PA size is a significant predictor of the variation in costs in Israel. PA size appears to be a significant predictor of operation and development costs. The relationship, however, between PA size and costs is negative. We expect to find that in addition to PA size, at least one or more additional PA attributes contributes significantly to predicting variation in conservation costs.

I have not yet tested the model of multiple predictors but so far on an individual basis I have not found another significant predictor of operation and development cost variation. Slide35

Next Stage

Research Hypothesis

This study will test the following hypotheses:

By studying the nature conservation marginal cost function, significant cost efficiencies can be achieved which will enable a higher level of nature conservation (more conservation goals achieved) for a given budget or enable reaching a given level of nature conservation (specific conservation goals) for a lower budget.In order to create the marginal cost function (supply curve) for nature conservation, we must build a marginal benefit function which shows the incremental increase in conservation benefit as we add more and more PA’s (reserves) to our study area (IsraelSlide36

Methodology

Weighted Index

Weight

Weight of Ecological Attributes

of Range Areas

? %

A Species richness

and abundance of individuals

? %

B Presence of

endangered and endemic species

? %

C Diversity

and uniqueness of habitats and ecosystems

? %

D Connectivity between reserves and proximate

natural areas

? %

E Representativeness

of nature reserves in Israel

? %

F Geological

phenomenon/geomorphological uniqueness

? %

G Landscape

and historical value for tourism

100%

TotalSlide37

Weighted IndexSlide38

Marginal Cost Curve (Supply Curve)