Stirling March 24 ’09 A combinatorial optimisation approach to non-market environmental benefit...
-
date post
19-Dec-2015 -
Category
Documents
-
view
216 -
download
1
Transcript of Stirling March 24 ’09 A combinatorial optimisation approach to non-market environmental benefit...
StirlingMarch 24 ’09
A combinatorial optimisation approach to non-market
environmental benefit aggregation via simulated populations
Stephen Hynes, Nick Hanley, Cathal O’Donoghue
StirlingMarch 24 ’09
Background
This research considers the use of spatial microsimulation in the aggregation of regional environmental benefit values.
Use matched survey and Census information to produce regional aggregate WTP figures
An application to corncrake conservation on Irish farmland
StirlingMarch 24 ’09
The Corncrake
StirlingMarch 24 ’09
StirlingMarch 24 ’09
StirlingMarch 24 ’09
The Datasets The Irish National Farm Survey
Collected as part of the Farm Accountancy Data Network of the European Union (FADN) Farmers asked WTP info in conjunction with the usual farm activity info.
The Census of Agricultureidentifies every operational farm in the country and collect data on agricultural activities undertaken on them
The 2006 NFS contains 1,177 nationally representative farms and the Census contains info on 145,000 farms.
StirlingMarch 24 ’09
WTP Question in NFS A payment card showing the bid amounts of €10,
€20, €30, €40, €50 and €60 and farmers were asked: “of these bid amounts which would be the maximum you would be willing to pay (€) each year into a conservation fund to aid in the restoration of this bird and bring the singing male population back up to a sustainable population of 900 birds”
Given the nature of the CV elicitation format we use an interval regression to model WTP
StirlingMarch 24 ’09
The combinatorial optimisation problem Want to find an optimum configuration (i) of farms satisfying:
where denotes the minimum error between the actual census tables of size, system and soil type and the simulated tables constructed using the configuration of NFS farms
But there is a maximum possible number of farm configurations in the matching process and also a computation time constraint
In order to solve this combinatorial optimisation problem we employ what is defined as an approximation algorithm which yields an approximate solution in an acceptable amount of computation time.
),(min)( iEiEERi
oopt
optE
StirlingMarch 24 ’09
Process for a Single ED Choose a configuration (i) of NFS farms to represent the Census
SAP tables for a single ED. Another configuration j can be obtained by randomly selecting a
number of records in configuration i and replaced them with ones chosen at random from the universe of NFS records.
The number of records to be replaced is defined as T. Letting the probability that configuration j will
be the next configuration of farms in a predefined sequence of configurations (the java program sets the number of iterations) is given by 1, if <0 and by if >0.
The acceptance of a new configuration is decided by drawing random numbers from a uniform distribution on [0, 1] and comparing these with . This process continues, with T being lowered at each step until the maximum number of iterations has been hit or the error falls within the desired setting.
),()( iEjEEij
ijE TEij /exp ijE
TEij /exp
StirlingMarch 24 ’09
Simulating Annealing ProcessOn completion of the matching process we
have a list of farm ids from NFS for each ED in the country
We then simply merge all the information associated with the farms in the NFS (including WTP for corncrake conservation) to characterise our ED population of farms
Now have farm activity information and WTP for each farm in each ED
StirlingMarch 24 ’09
WTP Aggregation
We calculate the aggregate environmental value of the corncrake conservation program in 3 alternative ways.
1. 2.
3.
n
iSIMiTPW
1
ˆNFSPnWT ˆ
n
iSIMigionalTPW
1_Re
ˆ
StirlingMarch 24 ’09
Results-CV Interval Regression
Variable NFS Model
Size of Farm (acres) -0.043 (-0.02)** Family Farm Income (€/1000) 0.075 (0.03)*** Age of Farm Operator 0.027 (0.05) Organic Nitrogen Production (kg/hectare) -0.036 (-0.02)** REPS farma 2.072 (1.26)* Total crops and pasture as a fraction of Total Farm Size -4.97 (-4.85) Constant 14.73(5.31)*** Log likelihood -274263
Likelihood Ratio 2 (6) test 18.55
StirlingMarch 24 ’09
WTP estimates for the 4 alternative estimation methods
Average WTP Total environmental value of a
Method of Analysis Per Farm (€) corncrake conservation program (€) Payment Card Interval Regression for NFS sample 10.65 (10.49, 10.82) 1,544,857 NFS Payment Card Interval Regression applied to simulated farm population 10.40 (10.39, 10.42) 1,508,592 Payment Card Interval Regression estimated using simulated farm population 9.58 (9.56, 9.59) 1,388,195
StirlingMarch 24 ’09
Total WTP estimates per County for the 4 alternative aggregation methods
County NFSPnWT ˆ
n
iSIMiTPW
1
ˆ
n
iSIMiREGIONALTPW
1_
ˆ
Extensive Counties Galway 141,293 145,010 151,238 Donegal 89,939 91,996 98814
Intensive Counties Tipperary S 40,289 37,170 33,616 Cork 162,572 149,369 135,506
StirlingMarch 24 ’09
StirlingMarch 24 ’09
StirlingMarch 24 ’09
Conclusions
Using the combinatorial optimisation one can take into account the spatial heterogeneity of the target population in the aggregation process.
The synthetic spatial micro-data can be combined with other GIS datasets for follow on analysis.
Usage in other stated and revealed preference valuation techniques
StirlingMarch 24 ’09
Thank You!
Hynes, S., Hanley, N. and O’Donoghue, C. (forthcoming). A combinatorial optimisation approach to non-market environmental benefit aggregation via simulated populations, Land Economics
Hynes, S. and Hanley, N. (2009). The ‘‘Crex crex’’ lament: Estimating landowners willingness to Pay for Corncrake Conservation on Irish Farmland, Biological Conservation 142: 180-188.