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Bio-economic modeling of wine grape protection strategies for environmental policy assessment

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Abstract

This research had two objectives. The first was to model the behaviour of wine producers, and the second was to assess the effectiveness of policies designed to reduce pesticide use in viticulture. We modeled the decisions of producers aiming to maximize their expected income while subject to a number of constraints and phytosanitary risks. We also examined the impacts of different protection strategies targeting downy mildew, the main grape disease in European Atlantic vineyards. The Vineyard model for Environmental Policy Analysis (VINEPA) model is a multi-periodic stochastic programming model based on panel data of about one hundred representative winegrowing farms from the Farm Accountancy Data Network in the Bordeaux region. The response of vines to fungicide treatments against downy mildew was simulated through the downy mildew potential system, an epidemiologic model initially developed for decision support, using data from multiple weather stations along with special plots of untreated vines, monitored weekly over a 10-year period. The VINEPA model accurately reproduced the current chemical protection strategies in the region. Simulations were then carried out for different types of taxes (ad valorem and volume based) at different rates. In addition, we analysed the effects of policies on spraying practices, along with their potential impact on investment in precision technology equipment.

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Notes

  1. Protected Designation of Origin (PDO): quality wine and spirits with a protected origin, in accordance with Council Regulation 1234/2007.

  2. Contact fungicides remaining on the outside of the plant can protect it from new infections for only a short period (7 days) because of new leaf growth and exposure to the environment (rain, ultraviolet light). Such fungicides are usually used for the first and late treatments, often copper (Fig. 2). Systemic fungicides form a protective barrier on the plant, permeating into it and moving to both the top and bottom. They therefore play a protective role for both existing leaves and new shoots, guaranteeing efficient protection for a maximum of 14 days.

  3. The number of active substances has been limited to the most used ingredients within the Bordeaux vineyard.

  4. Herbicides were distinguished from other pesticides, as they are not applied with the same equipment as that used for spraying the canopy. Herbicides therefore are not concerned with reduction of the application rate.

  5. The base price is computed from theoretical wine yield (hectolitres) and the gross value of production (euros) of different products (wine in bulk and bottle, fresh grapes, musts, and by-products, e.g. pomace and lee).

  6. In assessing sustainable farming technology, capital budgeting studies concentrate on farm size and profitability thresholds, whereas economics highlights the importance of farmers’ individual characteristics, level of expertise, risk and uncertainty (Adrian et al. 2005; Greiner et al. 2009; Marra et al. 2003). Risk may be linked to new technology, as new equipment may not have the expected maximum effectiveness. Its expected performance is considered to be distributed around an average value (see technical references) although real performance is actually unknown by the farmer. The performance of PT equipment is assumed to follow a distribution formalised in three classes, marked out by the first and third quartiles. Low and high levels of performance therefore have a probability of 25 % and the average level a probability of 50 %. This level of performance is considered to remain unchanged from 1 year to another during the simulation period. Although training plays a significant role in the adoption of new technology (Sunding and Zilberman 2001), we consider that skills are immediate without any additional costs.

  7. We set the outgoings at 18,000 EUR per family worker, based on the average wage of a qualified farm worker wage in 2006.

  8. Multiple ANOVA on three factors was not possible because of the limited number of observations by crossing the modalities of the three factors (1 yield measurement per crossing).

  9. Application of different products: 1 run with 2 different products = 2 applications.

  10. There are four categories according to the Law: category I (toxic, very toxic, carcinogenic, mutagenic or toxic for reproduction), category II (Harmful for the environment), category III (Mineral substances harmful for the environment) and category IV (other active substances).

  11. In the case of substitution, a higher tax on one active ingredient will make other active ingredients relatively cheaper and more attractive. This will have a positive impact on the effects of a differentiated tax.

  12. There is complementarity when the use of one pesticide has a clear connection with the use of another pesticide (particularly pesticides including two or more active ingredients like contact + systemic fungicides usually applied against downy mildew). In this case, tax on active ingredients may have little impact.

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Acknowledgments

The authors acknowledge the financial support provided by the Aquitaine Regional Council (Environment and Vine and Wine Quality, collaborative Project no. 20101202001, Institute of Vine and Wines Sciences—ISVV). We would like to thank Geneviève Souville and Maria Aránzazu Simó Ramiro for their excellent research assistance. We also thank the French Ministry of Agriculture for allowing us to access data from FADN and wine grape cultural practice survey, and INRA UMR SYSTEM for providing us the database on pesticide costs and recommended application rates. The authors are responsible for any remaining errors. The article in no way reflects the opinions of the Aquitaine Regional Council or those of the French Ministry of Agriculture.

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Appendices

Appendix 1

The VINEPA model (expected value model)

$$ \begin{aligned} {\text{Max E}}\left( \pi \right) &= \mathop \sum \limits_{n = 0}^{N} w^{n} \hfill \\ &\quad \times \left( \begin{array}{l} \mathop \sum \limits_{a} \left( {{ \Pr }\left( a \right) \times \left( {rdtT0_{a} + \mathop \sum \limits_{t = 1}^{20} \left( {ita_{a,t} \times y_{{n,t,p_{0} }} + \left( {ita_{a,t} + ita_{a,t + 1} } \right) \times y_{{n,t,p_{1} }} } \right)} \right)} \right) \times \left( {v \times Y \times area - varCost} \right) \hfill \\ - area \times \left( {\left( {1 - \mathop \sum \limits_{e} x_{n,e} Eco_{e} } \right) \times \left( {\mathop \sum \limits_{p} productPrice_{p} \times z_{n,p} + fongiPrice} \right) + \mathop \sum \limits_{p} fuelPrice_{p} \times z_{n,p} } \right) \hfill \\ - area \times \left( {\hbox{max} \left( {0, 6 - \mathop \sum \limits_{p} z_{n,p} } \right) \times COidiumFuel + CBotrytisFuel} \right) \hfill \\ - area \times \left( {\left( {1 - r_{n} } \right) \times cdc + r_{n} \times cdm + \left( {1 - t_{n} } \right) \times chc + t_{n} \times ccs} \right) \hfill \\ + s_{n - 1} \times i + \mathop \sum \limits_{e} x_{n,e} \times maintenanceCost_{e} \hfill \\ - \mathop \sum \limits_{e} \left( {\left( {x1_{n,e} - x1_{n - 1,e} } \right) \times Cmat_{e} + x2_{n,e} \times R_{e } } \right) \hfill \\ \end{array} \right) \hfill \\ \end{aligned} $$
$$ \mathop \sum \limits_{p} y_{n,t,p} \le 1 \quad \forall n,t $$
(1)
$$ y_{n,t,p1} + \mathop \sum \limits_{p} y_{n,t + 1,p} \le 1\quad \forall n,t $$
(2)
$$ y_{n,t,p1} = 0 \quad \forall n,\forall t \in \left[ {t16,t20} \right] $$
(3)
$$ x1_{n,e} \ge x1_{n - 1,e} \quad \forall n,e $$
(4)
$$ x2_{n,e} \ge x2_{n - 1,e} \quad \forall n,e $$
(5)
$$ \mathop \sum \limits_{e} \left( {x1_{n,e} + x2_{n,e} } \right) \le 1 \quad \forall n $$
(6)
$$ x 1_{n,e} + x 2_{n,e} = x_{n,e} \quad \forall n,e $$
(7)
$$ z_{n,p} = \sum _{t} y_{n,p,t} \quad \forall n,p $$
(8)
$$ s_{n} \le { \hbox{max} }(0, s_{n - 1} \times \left( {1 + i} \right) + \pi_{n - 1} - minCons - \mathop \sum \limits_{e} \left( {x1_{n,e} - x1_{n - 1,e} } \right) \times Cmat_{e} )\quad \forall n $$
(9)
$$ x1_{n,e} \le x1_{n - 1,e} + { \hbox{max} }(0, 1 + s_{n - 1} \times \left( {1 + i} \right) + \pi_{n - 1} - minCons - Cmat_{e} )\quad \forall n $$
(10)
$$ x_{n,e } , x1_{n,e } , x2_{n,e} , y_{n,t,p} , r_{n} ,t_{n} \in \left\{ {0,1} \right\}\quad \forall n,t,p,e $$
(11)
$$ z_{n,p} \in \left[ {0,20} \right] \quad \forall n, t $$
(12)
$$ s_{n} \ge 0\quad \forall t $$
(13)

1.1 Indices

\( n = 0, \ldots ,N \) :

Years included in the planning period, where t = 0 is the present and t = N is the terminal period,

\( t = 1, \ldots ,20 \) :

Weeks included in a crop year,

\( a \in \left\{ {gp1,gp2,gp3} \right\} \) :

Levels of disease pressure

\( p \in \left\{ {p0, p1} \right\} \) :

Type of treatment which can be chosen by the winegrower, where p0 is a contact treatment and p1 a systemic treatment,

\( e \in \left\{ {B, C^{ - } , C, C^{ + } , D} \right\} \) :

Different PT equipments

1.2 Parameters

\( w \) :

Discount rate,

\( \text{Pr}(a) \) :

Probability for level of disease pressure a,

\( rdtT0_{a} \) :

Percentage of the objective yield obtained if any treatment are realized for the level of disease pressure a,

\( ita_{a,t} \) :

Percentage of the objective yield earned if a contact treatment is realized in the week t for the level of disease pressure \( a \),

\( v \) :

Production value,

\( Y \) :

Objective yield of the winegrower,

\( area \) :

Size in hectare of the winegrowing farm,

\( varCost \) :

Variable costs which depend on income,

\( opc \) :

Sum of other products, subsidies and expenses,

\( Eco_{e} \) :

Percentage of plant protection products savings (or losses avoided),

\( productPrice_{p} \) :

Cost per hectare of the p treatment products (copper at the end of the period),

\( fuelPrice_{p} \) :

Cost per hectare of the fuel used for the p treatment,

\( fongiPrice \) :

Cost per hectare of the other fungicide products (powdery mildew, grey rot),

\( COidiumFuel \) :

Cost per hectare of the fuel used for the powdery mildew treatments,

\( CBotrytisFuel \) :

Cost per hectare of the fuel used for the Grey rot treatment,

\( cdc \) :

Cost per hectare of a chemical weeding program,

\( cdm \) :

Cost per hectare of a mechanical weeding program,

\( chc \) :

Cost per hectare of an insecticide program,

\( ccs \) :

Cost per hectare of a sexual confusion program,

\( i \) :

Saving rate,

\( maintenanceCost_{e} \) :

Repair and maintenance costs for equipment e,

\( minCons \) :

Household consumption of the year,

\( {Cmat}_{{e}} \) :

Initial purchase cost for equipment \( e \),

\( R_{e} = \frac{{{\text{Cmat}}_{\text{e}} \times {\text{tx}} \times (1 + {\text{tx}})^{\text{N}} }}{{(1 + {\text{tx}})^{\text{N}} - 1}} \) :

Reimbursement cost of the loan made for purchasing equipment e

1.3 Decision variables

x n,e , x1 n,e , x2 n,e :

Binary investment variables: x n,e  = 1 if the winegrower invests in the equipment e the year n or if he has already invested in this equipment a previous year and 0 otherwise, x1 n,e  = 1 if the winegrower purchase the equipment e without borrowing the year n (or a previous year), 0 otherwise and x2 n,e  = 1 if the equipment e is bought with a loan

y n,t,p :

Binary treatment decision variables: y n,t,p  = 1 if the winegrower realizes a p treatment in the t week of the year n

z n,p :

Number of p treatments realized the year n

r n :

Binary variables: r n  = 1 if the winegrower doesn’t use any herbicide (mechanical weeding) the year n and 0 otherwise

t n :

Binary variables: t n  = 1 if the protection against moths is carried out by sexual confusion the year n and 0 if it is by insecticides

s n :

Savings realized the year n

Appendix 2

See Tables 7, 8 and 9.

Table 7 FADN data (averages by sub-region with standard deviation in italic characters)
Table 8 Pesticide average practices and related pesticides costs within the Bordeaux region
Table 9 Characteristics of the main active ingredients used in Bordeaux

Appendix 3

See Figs. 9 and 10.

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Lescot, JM., Rouire, M., Raynal, M. et al. Bio-economic modeling of wine grape protection strategies for environmental policy assessment. Oper Res Int J 14, 283–318 (2014). https://doi.org/10.1007/s12351-014-0152-y

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