Abstract: Of the approximately 50,000 nonnative species that have been introduced into the United States, nearly 4,600 of them are classified as harmful invasive species (Pimentel et al., 2000; Corn et al., 2002). These organisms have caused major economic and environmental damages to the tune of $120 billion per year (Pimentel, Zuniga, and Robinson, 2005). Invasive species have also been found to negatively impact human well-being (Jones, 2017) and to induce trophic cascades (Walsh, Carpenter, and Vander Zanden, 2016). The annual toll inflicted by invasive species to U.S. agriculture is significant: Pest insects cause an estimated $13 billion in crop losses on top of the $1.2 billion farmers spend in insecticides, while weeds cause an estimated reduction of 12% in crop yields ($33 billion in production losses) despite $3 billion spent on herbicides each year (Pimentel et al., 2000). Similarly, invasive forest pests cause nearly $5 billion in damages and losses throughout the United States, including $2.25 billion in costs to governments, $2.55 billion in costs to homeowners, and $152 million in losses to timber producers (Aukema et al., 2011). In the past 40 years, biological invaders and the risk associated with them have increased mainly due to rapid human population growth and mobility coupled with radical alteration of ecosystems across the globe. In addition, more goods and materials are being traded between nations than ever before, creating opportunities for unintentional introductions (Perrings et al., 2002; Evans, 2003; Alvarez, 2016). Recent analyses on invasion threats indicate that the level of damages to agriculture worldwide is likely to increase, with major food-producing nations such as the United States, Canada, China, Argentina, Australia, and South Africa among the most threatened nations (Paini et al., 2016). While government agencies have developed guidance documents with specific recommendations for early detection and rapid response (National Invasive Species Council, 2016; U.S. Department of the Interior, 2016) and some international agreements mention invasive species (Lodge et al., 2016), there are no clear science-based national policies to deal with invasive species in the United States (Mhina et al., 2016). Instead, response efforts have been established on a case-by-case basis, and policy makers and stakeholders play a big role in deciding which invasions are targeted for control or eradication and when those efforts are to take place. Here we offer evidence that the economic costs associated with invasive species is in large part determined by the response time between arrival of a pest and the beginning of eradication or control efforts. To make our case, we first discuss the three phases of a biological invasion and the main strategies—in terms of response time—that policy makers have followed to deal with the threat. We also present a review of representative biological invasions that have affected Florida’s agriculture industry, categorized by the invasion phase in which eradication efforts were implemented. Finally, we discuss policy implications and recommendations.

Abstract: Resource scarcity (labor, water, and energy) and high production costs are challenging the sustainability of conventional methods for rice and wheat establishment in Central Asia. Water saving irrigation and conservation agriculture (CA) practices (e.g., dry seeded rice, zero tillage wheat, residue retention) are potential alternative, resource-saving establishment methods. The Decision Support System for Agrotechnology Transfer (DSSAT) Cropping System Model (CSM) can both be a valuable ex-ante and ex-post tool to evaluate the effects of water saving irrigation and resource saving CA-practices. The CSM-CERES-Rice and CSM-CERES-Wheat models of DSSAT were evaluated using experimental data from the 2008 to 2010 rice and wheat seasons as monitored in Urgench, the Khorezm region of Uzbekistan for growth, development of these crops, as well as soil mineral nitrogen (N) and volumetric soil moisture content in these cropping systems. Thereafter, the models were used to explore the long-term impact of water saving irrigation and CA-practices on grain yield, soil organic carbon (SOC) dynamics, N dynamics, and water balance in a rice-wheat rotation for 39 years starting from 1971. The simulation results showed that the simulated yield of water-seeded rice without residue retention and flood irrigation (WSRF-R0-FI) is likely to remain the highest and constant over 39 years. The simulated yield of dry seeded rice (DSR) with alternate wet and dry (AWD) irrigation and varying levels of residue retention was penalized for the initial years. However, the simulated rice yield increased after 13 years of CA-practices and continued to increase for the remaining years. Wheat did not experience a yield penalty for any of the treatments and simulated yield increased over time across all CA-practices based treatments. In the long-term, the effect of tillage methods and different residue levels for both rice and wheat were apparent in terms of grain yield and SOC build up. The results of the sensitivity analysis showed that WSR using AWD irrigation with puddling (WSRF-R0-AWD-Puddled) could give equivalent yield with that of WSRF-R0-FI and that irrigation water for rice could be reduced from 5435 mm to 2161 mm (or by 60%). Deep placement of urea in DSR (CT-DSR-AWD-DPUS) has the potential to increase yields of DSR by about 0.5 t ha(-1). Despite the huge water saving potential through the adoption of water saving AWD irrigation in DSR, a major challenge will be to prevent N losses. Substantial amounts of N losses through leaching, immobilization by residue mulch, combined with gaseous losses through volatilization and denitrification are the major causes for the lower simulated yield of rice for the AWD treatments. During the rice season, the implementation of water saving irrigation can improve water use efficiency by reducing percolation and seepage losses, which is an option in particular for WSRF-R0-FI. For both crops, the water use efficiency can be improved by lowering evaporation losses e.g. through residue retention on the soil surface. The creation of a sub-surface hard pan (puddling) and deep placement of urea super granules/pellet (DPUS) fertilizer could be the key for water saving and better yields of rice. Because CA-practices require almost three times less irrigation water than conventional method, and provide a long-term positive impact on grain yields of both crops, the CA-practices should be considered for double, no-till, rice wheat cropping systems in the irrigated semi-arid drylands of Central Asia.

Abstract: As awareness of the potential threats posed by climate change increases, researchers and agricultural advisors are being called upon to determine the risks that different stakeholder groups will likely confront and to develop adaptive strategies. Yet, engaging with stakeholders takes time. It also requires a clear and detailed plan to ensure that research and outreach activities yield useful outputs. In this article, we focus on the role of anthropologists as researchers and conveners in stakeholder engagement and provide a generalised overview of a long-term engagement process proceeding in three stages: (1) fact-finding and relationship-building; (2) incubation and collaborative learning; and (3) informed engagement and broad dissemination. We conclude with a discussion of perspectives and challenges that were encountered during two engagement experiences in the south-eastern United States.

Abstract: In this chapter, we describe Florida�s agriculture, the vulnerability of its crops and livestock to climate change and possible adaptation strategies. Much of Florida�s agricultural success is linked to its moderate climate, which allows vegetable and fruit crop production during the winter/spring season as well as the production of perennial crops such as citrus and sugarcane. In addition, there is a substantial livestock industry that uses the extensive perennial grasslands. While rising CO2 is generally beneficial to crop production but detrimental to nutritional quality, increase in temperature will cause mostly negative effects on yield. Florida�s agriculture faces additional challenges from climate change characterized by sea level rise and intensified extreme climate events, affecting land and irrigation water availability, livestock productivity and pest and disease pressure. New technologies and adaptation strategies are needed for sustainable agricultural production in Florida, including increased water and nutrient use efficiency in crops, crop and livestock breeding for heat stress, pest and disease resistance and reduced exposure of livestock to high temperature. Irrigation is a favored adaptation, but places an even greater burden or potential conflict between agriculture and community use of water resources.

Abstract: This study compares responses to seasonal climate forecasts conducted by farmers of three agro-ecological zones of Burkina Faso, including some who had attended local level workshops and others who had not attended the workshops. While local inequalities and social tensions contributed to excluding some groups, about two-thirds of non-participants interviewed received the forecast from the participants or through various means deployed by the project. Interviews revealed that almost all those who received the forecasts by some mechanism (workshop or other) shared them with others. The data show that participants were more likely to understand the probabilistic aspect of the forecasts and their limitations, to use the information in making management decisions and by a wider range of responses. These differences are shown to be statistically significant. Farmers evaluated the forecasts as accurate and useful in terms of both material and non-material considerations. These findings support the hypothesis that participatory workshops can play a positive role in the provision of effective climate services to African rural producers. However, this role must be assessed in the context of local dynamics of power, which shape information flows and response options. Participation must also be understood beyond single events (such as workshops) and be grounded in sustained interaction and commitments among stakeholders. The conclusion of this study point to lessons learned and critical insights on the role of participation in climate-based decision support systems for rural African communities.