| Literature DB >> 29308222 |
Christopher Finn McQuaid1, Christopher Aidan Gilligan2, Frank van den Bosch1.
Abstract
The success or failure of a disease control strategy can be significantly affected by the behaviour of individual agents involved, influencing the effectiveness of disease control, its cost and sustainability. This behaviour has rarely been considered in agricultural systems, where there is significant opportunity for impact. Efforts to increase the adoption of control while decreasing oscillations in adoption and yield, particularly through the administration of subsidies, could increase the effectiveness of interventions. We study individual behaviour for the deployment of clean seed systems to control cassava brown streak disease in East Africa, noting that high disease pressure is important to stimulate grower demand of the control strategy. We show that it is not necessary to invest heavily in formal promotional or educational campaigns, as word-of-mouth is often sufficient to endorse the system. At the same time, for improved planting material to have an impact on increasing yields, it needs to be of a sufficient standard to restrict epidemic spread significantly. Finally, even a simple subsidy of clean planting material may be effective in disease control, as well as reducing oscillations in adoption, as long as it reaches a range of different users every season.Entities:
Keywords: behavioural model; cassava brown streak; clean seed system
Year: 2017 PMID: 29308222 PMCID: PMC5749990 DOI: 10.1098/rsos.170721
Source DB: PubMed Journal: R Soc Open Sci ISSN: 2054-5703 Impact factor: 2.963
Model parameters and default values. For simplicity, we assume that there is one growing season of 300 days per year, ignoring the initial two months of the season when there is no foliage and whitefly cannot transmit the pathogen, although we note that in reality there may be some transmission between 1 and 2 months. We assume that the majority of growers are subsistence farmers, as is often the case. This implies that fields are harvested continuously at a constant rate over a period of months during the season, commencing after the first two months, with one replanting event at the start of each season (μ = 0, h > 0). The size of a cassava field is taken to be 1.5 hectares (e.g. [22]), and we presume an increase in affinity for whitefly of cassava fields over other areas. We presume that whitefly are a third again as likely to land on a cassava field as on a bare patch of land. We base the cassava field density of our model on the area of cassava harvested in Nakasongola district, Uganda (10 000 hectares, http://kids.fao.org/agromaps/), and hence consider 6000 cassava fields. Whitefly migration is calculated from Riis & Nachman [23], using the total population to find the immigration rate at equilibrium, which we presume to be identical to emigration. To simulate the dispersal of the vector we use data from Isaacs & Byrne [24] and Byrne et al. [25] for the dispersal of the sweet potato whitefly (on average, 50–700 m). We do not include the long-distance dispersal of whitefly that Byrne et al. [25] observe in a second peak of migration, as this is not consistent with the exponential dispersal kernel that we have assumed. More importantly, however, whitefly may not remain infectious, or even survive, for the duration of these journeys [15,26,27]. See McQuaid et al. [16] for further details. For harvesting and replanting, one example of the maximum potential yield in Uganda is UGX 1 200 000, while the cost to growers using certified clean planting material is UGX 300 000 compared to UGX 0 for those that obtain planting material through the recycling of cuttings. It is the ratio of the maximum potential yield to the cost of technology that is important, which from the above is taken to be 1 : 0.25 : 0, although we vary this to consider other systems. We estimate the responsiveness of growers to loss from the known adoption of certified seed and seed systems for other crops by growers in East Africa (roughly 5–15%, see [28–31]) and the maximum potential benefit of using certified clean planting material (0.01–0.28). The latter is calculated from equation (2.3) and the equilibrium yield (approx. 100% for users of the clean seed system, 47–74% for nonusers) from equation (2.1) when 5–15% of growers dispersed across the landscape use the clean seed system, where the users vary each season. Solving equation (2.2) using these values gives the range 0.18 ≤ θ ≤ 16.25, where we pick θ from this range. We choose stubbornness κ to be of a similar order of magnitude, with a default value of zero. Contrariness ψ was chosen to be two orders of magnitude less than σ, to represent its rarity, although we investigated values around this range. The unit ‘plants’ refers to the number of plants in a field.
| parameter | description | valuea | source |
|---|---|---|---|
| crop agronomy | |||
| | harvesting rate | 0.003 day−1 | Jeger |
| | replanting rate | 0 plants day−1 | see also van den Bosch |
| | roguing rate | 0 day−1 | — |
| | number of fields | 1000 | — |
| disease dynamics | |||
| | infection rate of plant | 0.007 vector−1 day−1 | Mware |
| | disease progression rate in plant | 0.035 day−1 | Mware |
| | reversion ratio | 0 | — |
| | cutting selection | 0% | — |
| | virus acquisition rate for vector | 0.007 plants day−1 | Mware |
| | rate of loss of disease by vector | 1 day−1 | Legg |
| | reservoir host density | 0 | — |
| vector dynamics | |||
| 1/ | mean vector dispersal distance | 150 m | Byrne [ |
| | vector population | 200 individuals | Jeger |
| | vector natural death rate | 0.12 day−1 | Jeger |
| | vector migration rate | 0.04 day−1 | Riis & Nachman [ |
| | attractive area of field | 20 000 m2 | — |
| trading behaviour | |||
| | chance of a grower trading for planting material | 50% | Njenga |
| | maximum trading partners | 3 | Rohrbach & Kiala [ |
| | growers loyal to trading partners | 0% | — |
| grower behaviour | |||
| — | farmer group size | 15–30 growers | A. Pariyo, 28 April 2014, personal communication |
| | probability of receiving information from farmer group, trade partners, extension worker (district scale) | 40%, 40%, 20% | see Apok [ |
| | responsiveness of growers | 1.6 | see table caption |
| | conformity/stubbornness of growers | 0 | see table caption |
| | contrariness of growers | 0.001 | see table caption |
| cost | |||
| | relative selling price of yield of uninfected field | 1 | T. Omara 2014, personal communication |
| | relative cost of using clean planting material, planting material recycled through reuse or trade | 0.25, 0 | T. Omara 2014, personal communication |
| | usable percentage of infectious plant | 30% | e.g. Gondwe |
aCertain parameters included for generality in the model are set to zero to simplify testing of hypotheses.
Figure 1.Low adoption of clean planting material over time in a system where there is no external disease pressure, reasonably high whitefly numbers and clean planting material is expensive (200 whitefly per plant, planting material cost = 1/4 maximum potential yield, solid grey line). External disease pressure (simulated through the immigration of infected whitefly from external sources at rate or the introduction of a reservoir infected host at density 0.1, dotted line), higher whitefly numbers (500 whitefly per plant, dot-dashed line) or a low cost to clean planting material (planting material cost = 1/10 maximum potential yield, dashed line) alone are insufficient to promote high adoption. However, when combined, adoption approaches 100% (black line).
Figure 2.Change in average adoption (solid line) and yield (dashed line) with (a) density of a reservoir host, (b) likelihood of information being obtained at a regional scale, and (c) stubbornness of growers to change over 25 seasons.
Change in dynamics for increasing parameter values. Parameter values are grouped into those describing the agronomic system, the disease pressure, the clean planting material, the actions of growers and their behaviour. Varying these parameters affects the adoption of clean planting material and the percentage yield obtained, averaged over a period of 25 seasons, as well as the amplitude and frequency of oscillations and their dampening in adoption and yield. Increasing parameter values may increase or decrease these results monotonically (↗ or ↘ respectively), have no effect at all (→) or have a non-monotonic effect (↗↘, ↘↗ or ↘↗↘). Note that in all cases oscillations in adoption and yield are similarly affected by changes in parameter values.
| parameter | adoption | yield | dampening | amplitude | frequency |
|---|---|---|---|---|---|
| casual | → | → | → | → | → |
| commercial | ↗ | → | ↘ | ↗ | ↗ |
| likelihood of trading | → | ↘ | ↘ | ↗ | ↗ |
| number of suppliers | ↗ | → | ↘ | ↗ | ↗ |
| disloyalty to suppliers | ↗ | ↘ | ↘ | ↗ | ↗ |
| initial disease pressure | → | → | → | ↗ | ↘ |
| number of whitefly | ↗ | → | ↗ | ↘ | ↗ |
| reservoir host | ↗↘ | ↘ | ↗ | ↘ | ↘ |
| cost of material | ↘ | ↘ | ↗ | ↘ | ↗ |
| tolerance of material | ↘ | ↗ | ↗ | ↘ | ↘ |
| resistance of material | ↘ | ↗ | ↗ | ↘ | ↘ |
| cleanliness of material | ↘ | ↗ | ↘ | ↗ | ↘ |
| roguing | ↘ | ↗ | ↗ | ↘ | ↘ |
| cutting selection | ↘ | ↗ | ↗ | ↘ | ↘ |
| information sources | ↗ | ↗ | ↘↗ | ↗ | ↗ |
| responsiveness | ↘ | ↗ | ↘↗ | ↘ | ↗ |
| stubbornness | ↘↗↘ | ↘↗↘ | ↘↗ | ↗↘ | ↘ |
| contrariness | ↗ | ↗ | ↗ | ↘ | ↘ |
Figure 3.Effect of parameter changes on oscillations in adoption compared to the default parameter set (dotted line). Results show adoption for (a) a casual or (b) a commercial system, and for an increasing (solid line) or decreasing (dashed line) parameter values for (c) the likelihood of trade occurring, (d) the number of suppliers, (e) the number of growers disloyal to suppliers, (f) the initial incidence of disease, (g) the number of whitefly per plant, (h) the density of a reservoir host, (i) the cost of planting material, (j) the tolerance to disease of the planting material, (k) the resistance to disease of the planting material, (l) the incidence of disease in the planting material, (m) the rate of roguing, (n) the likelihood of successfully selecting out infectious cuttings, (o) the likelihood of growers obtaining regional-scale information, (p) the responsiveness of growers, (q) the stubbornness of growers or (r) the contrariness of growers.
Figure 4.(a–r) Effect of parameter changes on oscillations in yield compared to the default parameter set (dotted line) as in figure 3.
Figure 5.Different approaches to distributing subsidized clean planting material to 10% of growers for free, and the effect on adoption in the population as a whole. Distribution occurs at random throughout the district, either to different growers each season (black solid line) or to the same growers each season (black dashed line), compared to a case with no subsidy (grey dotted line). Results are similar if distribution focuses on communities of growers, as opposed to dispersed individuals.