Search citation statements
Paper Sections
Citation Types
Year Published
Publication Types
Relationship
Authors
Journals
Aim Decision-making for conservation management often involves evaluating risks in the face of environmental uncertainty. Models support decision-making by (1) synthesizing available knowledge in a systematic, rational and transparent way and (2) providing a platform for exploring and resolving uncertainty about the consequences of management decisions. Despite their benefits, models are still not used in many conservation decision-making contexts. In this article, we provide evidence of common objections to the use of models in environmental decision-making. In response, we present a series of practical solutions for modellers to help improve the effectiveness and relevance of their work in conservation decision-making.Location Global review.Methods We reviewed scientific and grey literature for evidence of common objections to the use of models in conservation decision-making. We present a set of practical solutions based on theory, empirical evidence and best-practice examples to help modellers substantively address these objections.Results We recommend using a structured decision-making framework to guide good modelling practice in decision-making and highlight a variety of modelling techniques that can be used to support the process. We emphasize the importance of participatory decision-making to improve the knowledgebase and social acceptance of decisions and to facilitate better conservation outcomes. Improving communication and building trust are key to successfully engaging participants, and we suggest some practical solutions to help modellers develop these skills.Main conclusions If implemented, we believe these practical solutions could help broaden the use of models, forging deeper and more appropriate linkages between science and management for the improvement of conservation decision-making.
Aim Decision-making for conservation management often involves evaluating risks in the face of environmental uncertainty. Models support decision-making by (1) synthesizing available knowledge in a systematic, rational and transparent way and (2) providing a platform for exploring and resolving uncertainty about the consequences of management decisions. Despite their benefits, models are still not used in many conservation decision-making contexts. In this article, we provide evidence of common objections to the use of models in environmental decision-making. In response, we present a series of practical solutions for modellers to help improve the effectiveness and relevance of their work in conservation decision-making.Location Global review.Methods We reviewed scientific and grey literature for evidence of common objections to the use of models in conservation decision-making. We present a set of practical solutions based on theory, empirical evidence and best-practice examples to help modellers substantively address these objections.Results We recommend using a structured decision-making framework to guide good modelling practice in decision-making and highlight a variety of modelling techniques that can be used to support the process. We emphasize the importance of participatory decision-making to improve the knowledgebase and social acceptance of decisions and to facilitate better conservation outcomes. Improving communication and building trust are key to successfully engaging participants, and we suggest some practical solutions to help modellers develop these skills.Main conclusions If implemented, we believe these practical solutions could help broaden the use of models, forging deeper and more appropriate linkages between science and management for the improvement of conservation decision-making.
Rangeland managers often must decide whether to suppress dicotyledonous weed populations with expensive and time-consuming management strategies. Often, the underlying goal of weed suppression efforts is to increase production of native forage plants. Many managers suppress weeds only when they feel the unwanted plants are substantially impacting their forage base. Currently, intuition and guesswork are used to determine whether weed impacts are severe enough to warrant action. We believe scientific impact assessments could be more effective than these casual approaches to decision making. Scientific approaches will necessitate data on weed abundances because the severity of a weed's impact is highly correlated with its abundance. The need for weed abundance data poses major obstacles because gathering these data with readily available techniques is time consuming. Most managers cannot or will not spend a lot of time gathering vegetation data. In this paper, we explore a rapidly measured index (,2 minutes per sample location) that is highly correlated with weed (i.e., leafy spurge Euphorbia esula L.) abundance per unit area. This index is based on the light attenuation leafy spurge causes. After measuring light attenuation in plots planted to leafy spurge and grasses, we developed a probabilistic model that predicts leafy spurge impacts on forage production. Data from experiments where herbicides suppressed leafy spurge provided an opportunity to evaluate prediction accuracy of the model. In each case herbicide experiment data fell within the range of values (i.e., credibility intervals) the model predicted, even though the model development experiments were separated from the herbicide experiments by several hundred kilometers in space and 4 years in time. Therefore, we conclude that the model successfully accounts for spatial and temporal variation. We believe light attenuation could help natural resource managers quickly quantify some kinds of weed impacts. ResumenLos manejadores de pastizales a menudo deben decidir si suprimen o no las poblaciones de malezas dicotiledó neas con estrategias de manejo caras y que consumen mucho tiempo. Frecuentemente, la meta de suprimir las malezas es incrementar la producció n de las plantas forrajeras nativas. Muchos manejadores solo suprimen las malezas cuando sienten que las plantas indeseables está n impactando substancialmente su producció n de forraje. Actualmente, la intuició n y suposiciones son usadas para determinar si los impactos de la maleza son los suficientemente severos o no para justificar la acció n de supresió n. Nosotros creemos que las evaluaciones científicas del impacto de la maleza pueden ser má s efectivas que las estos métodos casuales de toma de decisiones. Los métodos científicos necesitará n datos de la abundancia de la maleza, porque la severidad del impacto de la maleza esta altamente correlacionado con su abundancia. La necesidad de datos de abundancia de la maleza presenta grandes obstá culos porque la recopilació n de estos datos con...
The article contains sections titled: 1. Introduction 1.1. Definitions of Weeds 1.2. Losses from Weeds 2. Biology of Weeds 2.1. Plant Types 2.1.1. Land Plants 2.1.2. Aquatic Plants 2.1.3. Parasitic Seed Plants 2.2. Life Cycles 2.2.1. Annuals 2.2.2. Biennials 2.2.3. Perennials 2.3. Reproduction 2.4. Interference Between Crops and Weeds 2.4.1. Competition 2.4.2. Allelopathy 2.5. Biological Variability and Adaptability in Relation to Control Systems 2.5.1. Species Shifts 2.5.2. Resistance Development within a Species 3. General Concepts Underlying Weed Control 4. Physical Methods of Weed Control 4.1. Manual Methods 4.2. Tillage Methods 4.3. Mowing and Cutting 4.4. Flooding 4.5. Mulching 4.6. Use of Heat 5. Biological Control of Weeds 5.1. Herbivore Management 5.2. Classical Biological Control 5.3. Inundative Biological Control 6. Controlling Weeds by Habitat Management 7. Chemical Control of Weeds 7.1. History and Introduction 7.2. Adjuvants 7.2.1. Surfactants 7.2.2. Oils 7.2.3. Drift Retardants 7.2.4. Other Adjuvants 7.3. Herbicide Formulations 7.3.1. Spray Formulations 7.3.1.1. Soluble Concentrates (SC) 7.3.1.2. Emulsifiable Concentrates (EC) 7.3.1.3. Wettable Powders (WP) 7.3.1.4. Flowables (F) 7.3.1.5. Dispersible Granules or Dry Flowables (DF) 7.3.1.6. Invert Emulsions 7.3.1.7. Encapsulated Formulations 7.3.2. Formulations Applied Dry 7.3.3. Active Ingredient vs. Acid Equivalent 7.4. Factors Influencing Foliage‐Applied Herbicides 7.5. Factors Influencing Soil‐Applied Herbicides 7.5.1. Microbiological Effects 7.5.2. Adsorption on Soil Colloids 7.5.3. Chemical Decomposition 7.5.4. Leaching 7.5.5. Volatilization 7.5.6. Photodecomposition 7.5.7. Uptake and Translocation from the Soil 7.6. Selective Action of Herbicides 7.7. Classification of Herbicides 8. Economic Aspects 9. Regulatory Aspects of Pesticides 10. General Comments
scite is a Brooklyn-based organization that helps researchers better discover and understand research articles through Smart Citations–citations that display the context of the citation and describe whether the article provides supporting or contrasting evidence. scite is used by students and researchers from around the world and is funded in part by the National Science Foundation and the National Institute on Drug Abuse of the National Institutes of Health.
hi@scite.ai
10624 S. Eastern Ave., Ste. A-614
Henderson, NV 89052, USA
Copyright © 2024 scite LLC. All rights reserved.
Made with 💙 for researchers
Part of the Research Solutions Family.