Welcome to “Exploring Ecological Data with R and Jamovi: A Beginner’s Guide to Statistical Data Analysis.” This manual is designed to be your comprehensive companion on the journey to becoming proficient in ecological data analysis using two powerful tools: R and Jamovi.
In the realm of ecology, data analysis is at the heart of understanding the intricate relationships within ecosystems, quantifying environmental impacts, and making informed decisions for conservation and research. The dynamic duo of R and Jamovi empowers ecologists and researchers to unlock the potential hidden within ecological datasets.
This manual is born out of the belief that mastering these tools should be an accessible and engaging experience for all, whether you are a seasoned ecologist looking to expand your analytical toolkit or a newcomer eager to embark on your ecological research journey.
What You Will Discover
Installation and Setup: In Chapter 1, we provide step-by-step guidance on installing R, RStudio, and Jamovi on your preferred operating system. Get ready to embark on a data analysis adventure!
Data Import and Cleaning: Chapter 2 introduces you to the critical process of importing ecological datasets into R and Jamovi. Learn techniques for cleaning and preprocessing data, ensuring your analyses are based on high-quality, error-free data.
Exploratory Data Analysis (EDA): Dive into Chapter 3, where you’ll discover the fascinating world of Exploratory Data Analysis (EDA). Visualize and summarize ecological data, uncover patterns, relationships, and outliers that hide within your datasets.
Statistical Tests: Chapter 4 demystifies statistical hypothesis testing, a fundamental aspect of ecological research. Explore common tests used in ecology, from t-tests to ANOVA and non-parametric tests, and learn how to perform them in R and Jamovi.
Regression Analysis: In Chapter 5, you’ll delve into regression analysis, a powerful tool for modeling ecological relationships. Understand linear and logistic regression and gain the skills to interpret regression outputs.
Data Visualization: Chapter 6 unveils the art of data visualization. Learn to create informative graphs and plots that effectively communicate your ecological findings.
Advanced Topics: As you progress, Chapter 7 opens doors to more advanced topics like multivariate analysis, spatial analysis, and time series analysis, expanding your ecological research possibilities.
Case Studies: Throughout this guide, you’ll encounter real-world ecological case studies in Chapter 8. These practical examples demonstrate how R and Jamovi are applied to solve ecological problems, offering valuable insights into the application of these tools in ecological research.
Your Ecological Journey Begins
With this manual as your guide, you’re embarking on a journey of discovery, analysis, and ecological understanding. We encourage you to embrace every chapter, practice with real datasets, and apply what you learn to your own ecological questions.
We extend our gratitude to all those who have contributed to this manual, and we’re excited to accompany you on your ecological data analysis adventure. Your passion for ecology and your drive to make data-driven decisions are the driving forces behind this endeavor.
Now, let’s dive into the fascinating world of ecological data analysis with R and Jamovi. Your ecological journey begins here.
Happy analyzing!
……………………
Dr. Jimmy Moses (Ph.D.)
The Papua New Guinea University of Technology
Ecology, the study of the interactions between organisms and their environment, generates vast amounts of data. Analyzing this data is crucial for understanding ecosystems, making informed conservation decisions, and addressing environmental challenges. Statistical data analysis is the cornerstone of ecological research, enabling scientists to derive meaningful insights from complex ecological datasets.
This guide, “Exploring Ecological Data with R and Jamovi,” is tailored for beginners in the field of ecology who are eager to harness the power of statistical analysis to unravel ecological mysteries. Whether you’re a budding ecologist, a conservation enthusiast, or a student embarking on ecological research, this guide will serve as your compass through the intricate world of data analysis.
Why R and Jamovi?
R (R Core Team, 2023) is a popular open-source statistical programming language renowned for its versatility and power in data analysis. It has become the lingua franca of data science and is extensively used in ecological research. R provides a vast ecosystem of packages tailored to various ecological analyses, making it an invaluable tool for ecologists.
Jamovi (Şahi̇n & Aybek, 2020), on the other hand, is a user-friendly statistical software designed with accessibility in mind. Its intuitive graphical interface and point-and-click functionality make it an excellent choice for beginners. Jamovi seamlessly integrates with R, allowing users to transition from a simple point-and-click environment to more complex analyses in R as they gain proficiency.
Who Is This Guide For?
This guide is tailored for:
Students and researchers entering the field of ecology or related fields.
Conservationists and environmentalists interested in data-driven decision-making.
Anyone curious about using R and Jamovi for data analysis, whether in ecology or any other field.
Embark on your ecological data analysis journey with confidence. This guide aims to demystify statistical analysis using R and Jamovi, providing you with the skills and knowledge to explore ecological data, ask critical questions, and contribute to the understanding and conservation of our natural world. Let’s begin our exploration of ecological data with R and Jamovi.
This comprehensive manual is intended to serve as a detailed and user-friendly guide to the installation and competent use of core data analysis tools: R (R Core Team, 2023), RStudio (RStudio Team, 2020), and Jamovi (Şahi̇n & Aybek, 2020). These software programmes play critical roles in a variety of sectors, including forestry and ecology, where they are essential for conducting demanding statistical analysis, creating intelligent data visualizations, and driving significant research initiatives.
Notably, this training manual played an important role as an integral component of a workshop held at the Department of Forestry, Papua New Guinea University of Technology. The primary goal of the workshop was to empower its participants, the majority of whom were novices, by providing them with the required tools and competences for competent data analysis within the specialized environment.
This manual, which will be converted to a handbook in the near future, will be regularly expanded to cover complex data analysis techniques such as geospatial mapping and modelling. These planned upgrades will serve as the foundation for a complete manual that will take your data analysis skills to the next level. These changes are intended to address the growing expectations of forestry and ecological researchers, professionals, and students.
Furthermore, this manual will serve as a foundation for future workshops. These workshops aim to dive further into complicated data analysis, sophisticated modelling methodologies, and the use of geospatial data for improved ecological insights. We are devoted to equipping participants with cutting-edge information and practical skills that will enable them to flourish in the dynamic fields of agriculture, environmental science, forestry and ecology.
Through these future developments and workshops, we aim to foster a community of proficient data analysts and researchers who can make significant contributions to the sustainable management of our natural ecosystems.
Key Outcomes:
Tool Proficiency: Participants are equipped with the proficiency to harness the capabilities of R, RStudio, and Jamovi as powerful aids in their data analysis workflows.
Statistical Analysis: Participants will obtain the knowledge and practical skills required for in-depth statistical analysis, allowing them to test hypotheses, investigate relationships, and develop data-driven conclusions.
Data Visualization: The handbook instructs users on how to use these tools to generate useful and aesthetically appealing data visualizations, which are an important feature of data communication.
Research Empowerment: With these essential tools and the know-how to properly use them, participants are better positioned to contribute meaningfully to research efforts, particularly in forestry and ecology.
Readers will not only obtain the skills to set up and utilize the aforementioned programs by immersing themselves in the contents of this handbook, but they will also receive vital insights into their practical applications. This newly acquired skill will not only improve their capacity to perform reliable data analysis but will also enable them to make significant contributions to the domains of forestry and ecology or any other related fields.
Before you begin the installation process, it is essential to ensure that you meet the following prerequisites:
Internet Connection: You must have a stable and active internet connection to download the required software packages and updates.
Administrator Privileges (Windows): If you are using a Windows operating system, you may need administrator privileges to install software. Ensure that you have the necessary permissions.
Operating System Compatibility: Verify that your operating system is compatible with the software you intend to install. Each software package has specific system requirements, which will be outlined in the installation sections.
Basic Computer Skills: This manual assumes that you have basic computer skills, including the ability to navigate your operating system and use a web browser.
Storage Space: Ensure that you have sufficient disk space available to accommodate the software installations. The installation sections will specify the approximate storage requirements.
Hardware Requirements: Check if your computer meets the hardware requirements specified by the software developers. This information is usually available on the respective software websites.
Computers operate on three of the most common operating systems: Windows, Mac OS, and Linux. Depending on your operating system, follow the installation instructions relevant to your specific platform. The process will differ slightly for Windows, macOS, and Linux users, so ensure you select the appropriate set of instructions based on your system.
Open your web browser and navigate to the R download page (download here).
Click on the “Download R for Windows” link.
Choose a CRAN mirror (usually the one geographically closest to you) and click on its link.
Download the base version of R for Windows by clicking on the “install R for the first time” link.
Locate the downloaded R installer (an .exe file) and double-click it.
Follow the installation wizard’s instructions:
Choose the language.
Accept the terms of the license.
Select the components you want to install (usually, you can leave the default settings).
Choose the installation location (you can leave the default).
Click “Next” to start the installation.
Once the installation is complete, you can now run R by searching for “R” in the Windows Start menu.
RTools is a collection of tools required for building and installing R packages from source on Windows. It is essential for users who want to compile and install R packages from CRAN or other sources. Here are the steps to download and install RTools on a Windows system:
Download RTools:
Open your web browser and navigate to the RTools download page (download here).
On the RTools download page, scroll down to find the “Download Rtools” section.
Click on the link that corresponds to the version of RTools recommended for your version of R. It is essential to match the RTools version with the R version you have installed. For example, if you have R version 4.1.x, download the RTools version recommended for R 4.1.x.
You will be directed to a new page with a list of download links. Click on the link that says “install.exe” to download the RTools installer.
Installing RTools:
Locate the downloaded RTools installer (an .exe file) and double-click it to start the installation.
Follow the installation wizard’s instructions:
Choose the language.
Accept the terms of the license.
Select the components you want to install. It is recommended to install all components, so leave the default settings selected.
Choose the installation location. By default, RTools will install in the “C:\Rtools” directory. You can change this location if necessary.
Click “Next” to start the installation.
During the installation, you may see a message about modifying the system PATH. Make sure to select the option that adds RTools to the system PATH. This is essential for R to find and use RTools when building packages.
Once the installation is complete, you can click “Finish” to exit the installer.
Verifying the Installation:
In the R console, you can run the following command to check if RTools is found:
Sys.which("make")
make.exe
executable associated with
RTools.That’s it! You have successfully downloaded and installed RTools on your Windows system. You are now ready to build and install R packages from source when needed.
Open your web browser and navigate to the R download page (download here). Note: the use of X11 (including tcltk) requires XQuartz (version 2.8.5 or later). Always re-install XQuartz when upgrading your macOS to a new major version.
Click on the “Download R for (Mac) OS X” link.
Download the latest R framework (pkg file) by clicking on the link.
Locate the downloaded R framework (a .pkg file) and double-click it.
Follow the installation instructions in the installer:
Agree to the license terms.
Choose the installation location (you can leave the default).
Click “Install” to start the installation.
Once the installation is complete, you can run R by searching for “R” in the Applications folder.
Open a terminal window.
Enter the following commands one by one to add the CRAN repository and the key:
sudo apt update
sudo apt install r-base
R
.Open your web browser and navigate to the RStudio download page (download here).
Scroll down to the “RStudio Desktop” section.
Click on the “Download” button under the “RStudio Desktop (Free)” option.
Download the RStudio installer for Windows.
Locate the downloaded RStudio installer (an .exe file) and double-click it.
Follow the installation wizard’s instructions:
Choose the language.
Accept the license agreement.
Choose the installation location (you can leave the default).
Select additional tasks (optional).
Click “Install” to begin the installation.
Once the installation is complete, you can run RStudio by searching for “RStudio” in the Windows Start menu.
Open your web browser and navigate to the RStudio download page (download here).
Scroll down to the “RStudio Desktop” section.
Click on the “Download” button under the “RStudio Desktop (Free)” option.
Download the RStudio installer for macOS.
Locate the downloaded RStudio installer (a .dmg file) and double-click it.
A new window will open. Drag the RStudio icon into the Applications folder.
Once the copy is complete, you can run RStudio from your Applications folder.
Open a terminal window.
Enter the following command to download the RStudio package (download here):
sudo apt-get install gdebi-core
wget https://download1.rstudio.org/desktop/bionic/amd64/rstudio-1.4.1717-amd64.deb
sudo gdebi rstudio-1.4.1717-amd64.deb
Open your web browser and navigate to the Jamovi download page (download here).
Click on the “Download for Windows” button.
Download the Jamovi installer for Windows.
Locate the downloaded Jamovi installer (an .exe file) and double-click it.
Follow the installation wizard’s instructions:
Choose the installation location (you can leave the default).
Select additional tasks (optional).
Click “Install” to begin the installation.
Once the installation is complete, you can run Jamovi by searching for “Jamovi” in the Windows Start menu.
Open your web browser and navigate to the Jamovi download page (download here).
Click on the “Download for macOS” button.
Download the Jamovi installer for macOS.
Locate the downloaded Jamovi installer (a .dmg file) and double-click it.
A new window will open. Drag the Jamovi icon into the Applications folder.
Once the copy is complete, you can run Jamovi from your Applications folder.
Open a terminal window.
Enter the following commands to download and install Jamovi (install via this page):
sudo add-apt-repository ppa:jamovi/jamovi
sudo apt-get update
sudo apt-get install jamovi
# or install via flatpak
flatpak install flathub org.jamovi.jamovi
flatpak run org.jamovi.jamovi
Windows
Open R by searching for “R” in the Start menu.
The R console should appear. You can start using R by entering commands.
macOS
Open the Applications folder and run R.
The R console should open, allowing you to use R.
Linux (Ubuntu)
Open a terminal and type
R
.
The R console should open.
Windows
Open RStudio by searching for “RStudio” in the Start menu.
The RStudio IDE should open, ready for use.
macOS
Open the Applications folder and run RStudio.
The RStudio IDE should open.
Linux (Ubuntu)
Open the applications menu and search for “RStudio.”
Launch RStudio from the menu.
Windows
Open Jamovi by searching for “Jamovi” in the Start menu.
The Jamovi interface should open.
macOS
Open the Applications folder and run Jamovi.
The Jamovi interface should open.
Linux (Ubuntu)
Open the applications menu and search for “Jamovi.”
Launch Jamovi from the menu.
Regularly update R to ensure you have the latest features and bug fixes.
Windows and macOS users can download the latest R installer and reinstall R. Your packages and scripts will remain intact.
Linux users can use package managers like
apt
to update R:
sudo apt-get update
sudo apt-get upgrade r-base
If you encounter difficulties downloading R, RStudio, or Jamovi, ensure you have a stable internet connection.
Try using an alternative download mirror if the default one is slow or unresponsive.
Disable any firewall or security software temporarily, as they may block downloads.
Ensure that you are downloading the correct version of the software that matches your operating system (Windows, macOS, Linux) and architecture (32-bit or 64-bit).
Verify that your operating system meets the minimum requirements for the software.
apt
for
Ubuntu).If you encounter issues when installing R packages using the
install.packages()
function, ensure you
have an internet connection.
Some packages may require additional system libraries. Check the package documentation for any specific requirements.
If you receive errors related to permissions, consider running R or RStudio with administrative privileges (e.g., “Run as administrator” on Windows).
When installing Jamovi modules (extensions), ensure that you are using a compatible version of Jamovi.
If a module installation fails, check if there are any error messages provided. These messages often indicate the cause of the issue.
If you encounter installation or package-related issues that are not covered here, consider seeking help from the following resources:
Online Forums: Visit community forums or discussion boards related to R, RStudio, and Jamovi. Experienced users often provide solutions to common problems.
Official Documentation: Consult the official documentation for each software. They often include troubleshooting sections.
User Communities: Join user communities or mailing lists where you can ask questions and seek assistance from experienced users.
RStudio Cloud is a powerful cloud-based platform that allows you to access the RStudio Integrated Development Environment (IDE) from anywhere with an internet connection and a web browser. This means you can work on your data analysis projects without being tied to a specific computer or location.
Accessibility: With RStudio Cloud, you can access your projects and data from virtually anywhere, whether you’re at home, in the office, or on the go. All you need is an internet connection and a web browser.
Collaboration: RStudio Cloud makes collaboration easy. You can share your projects with colleagues or collaborators, allowing them to work on the same analysis, view your code, and provide input in real-time, regardless of their physical location.
Version Control: RStudio Cloud often integrates with version control systems like Git and GitHub. This enables you to track changes in your projects, collaborate with others, and maintain a history of your work.
Resource Scalability: Cloud computing provides the flexibility to scale your computing resources as needed. If you require more processing power or memory for a specific analysis, you can often adjust your cloud resources accordingly.
Cost Efficiency: Many cloud platforms offer a pay-as-you-go pricing model, which can be cost-effective, especially for users who don’t require constant high-performance computing. You only pay for the resources you use.
Security: Reputable cloud providers invest heavily in security measures to protect your data. They often offer encryption, secure access controls, and data redundancy to safeguard your work.
Automatic Backups: Cloud platforms typically provide automated backup solutions, reducing the risk of data loss due to hardware failures or other issues.
Device Independence: Since RStudio Cloud runs in a web browser, it’s compatible with various devices, including laptops, desktops, tablets, and even smartphones, making it highly versatile.
Reduced Setup Time: Setting up and configuring R, RStudio, and packages can be time-consuming on a local machine. RStudio Cloud simplifies this process, allowing you to focus on your analysis rather than software installation and maintenance.
Learning Opportunities: For educators and trainers, RStudio Cloud offers a convenient way to teach R and data analysis. Students can access a consistent, pre-configured environment, eliminating the need for individual software installations.
In summary, RStudio Cloud and cloud computing provide numerous advantages, including enhanced accessibility, collaboration, cost efficiency, security, and scalability. These benefits make cloud-based platforms like RStudio Cloud valuable tools for data analysts, researchers, educators, and anyone who wants the flexibility of working with data and code from anywhere with ease.
Open your web browser and go to the RStudio Cloud website (https://posit.cloud/).
Click the “Sign Up” button to create a new account.
Fill out the required information, including your name, email address, and a password for your RStudio Cloud account.
Read and accept the Terms of Service and Privacy Policy.
Click the “Sign Up” button to complete the registration process.
Check your email inbox for a message from RStudio Cloud.
Open the email and click the confirmation link provided. This step verifies your email address and activates your account.
After confirming your email, log in to your RStudio Cloud account.
Click the “New Project” button on the dashboard.
Give your project a name and, optionally, a description.
Choose a project privacy setting (private or public) based on your preferences.
Click the “Create Project” button.
Once your project is created, you’ll be taken to your RStudio workspace within your web browser.
Here, you have access to the RStudio IDE, which includes a script editor, console, and other tools for data analysis.
You can now start working with R and RStudio within your RStudio Cloud environment. Here are some key points to remember:
You can write R scripts, execute code, and work with datasets just like you would in a local RStudio installation.
Your work is saved automatically within your RStudio Cloud project.
You can upload and download files, including R scripts and datasets, to and from your project.
Collaborate with others by sharing your project or working on shared projects.
RStudio Cloud provides a flexible environment that allows you to install additional R packages and extensions as needed.
To end your session, simply close your web browser. Your work will be saved, and you can resume from where you left off the next time you log in.
You can access your account settings, change your password, and manage your projects by clicking on your profile picture or username in the top right corner of the RStudio Cloud interface.
That’s it! You’ve successfully set up and started using RStudio Cloud, which provides a convenient way to work with R and RStudio from any device with an internet connection and a web browser.
To ensure that your R environment is fully functional and equipped with essential packages for data analysis, we will test the installation of key R packages. These packages include devtools, remotes, tidyverse, and rstatix. This process will help verify that the packages can be installed and loaded successfully within RStudio.
Follow these steps to install and load the required R packages using RStudio:
Open RStudio
Installing devtools and remotes
In the RStudio console, enter the following commands to install the devtools (Wickham et al., 2022) and remotes (Csárdi et al., 2023) packages:
install.packages("devtools")
install.packages("remotes")
Wait for the installations to complete. You may be prompted to select a CRAN mirror; choose a location geographically close to you for faster downloads.
Loading devtools and remotes
After installation, load the devtools and remotes packages by entering these commands in the console:
library(devtools)
library(remotes)
Installing tidyverse and rstatix
With devtools and remotes loaded, you can now install the tidyverse (Wickham et al., 2019) and rstatix (Kassambara, 2023) packages, which are essential for data manipulation and statistical analysis:
install.packages("tidyverse")
::install_github("kassambara/rstatix") remotes
Allow the installations to proceed. The remotes package is used to install rstatix directly from its GitHub repository.
Loading tidyverse and rstatix
Once installed, load the tidyverse and rstatix packages with the following commands:
library(tidyverse)
library(rstatix)
Verifying Package Loading
To confirm that the packages have been successfully loaded, you can execute a simple test. For instance, you can try running the following command, which uses a function from the tidyverse package:
::qplot(1:10, rnorm(10)) ggplot2
If the packages have been loaded correctly, you should see a basic scatterplot generated by ggplot2.
Testing the installation and loading of these packages ensures that your R environment is ready for data analysis tasks. By successfully installing and loading devtools, remotes, tidyverse, and rstatix, you have access to a powerful set of tools for data manipulation, visualization, and statistical analysis within RStudio.
You are now well-equipped to embark on data analysis projects with R, and you can confidently explore additional packages tailored to your specific needs.
In this manual, we have provided comprehensive guidance on the installation of essential data analysis tools: R, RStudio, and Jamovi. These tools are invaluable for conducting statistical analysis, data visualization, and research in various fields.
To recap the key steps covered in this manual:
Installing R
Choose the appropriate version for your operating system (Windows, macOS, or Linux).
Follow the step-by-step instructions provided to download and install R.
Verify the successful installation of R by launching the R console.
Installing RStudio
Select the correct version of RStudio for your operating system.
Follow the installation instructions to download and install RStudio.
Confirm the successful installation of RStudio and its integration with
Installing Jamovi
Download Jamovi for your operating system.
Execute the installation process as guided in the manual.
Validate the installation by launching Jamovi.
Verifying Installations
Ensure that R, RStudio, and Jamovi open without errors.
Confirm that you can access the R console and RStudio IDE smoothly.
Updating and Maintaining Software
Regularly check for updates to R, RStudio, and Jamovi to benefit from the latest features and bug fixes.
Follow the guidelines provided to update each software component.
Troubleshooting
Consult the troubleshooting section if you encounter common installation or package-related issues.
Utilize online forums, official documentation, and user communities to seek assistance for more complex problems.
Now that you have successfully installed R, RStudio, and Jamovi, you are equipped with powerful tools for data analysis, statistical modeling, and research. Your next steps might include:
Learning and Practicing: Explore online tutorials and resources to enhance your skills in using R, RStudio, and Jamovi for data analysis.
Working on Projects: Apply your newly acquired knowledge to real-world projects, research, or coursework.
Exploring Packages: Explore and install additional R packages that cater to your specific analytical needs.
Collaborating: Share your work with colleagues or collaborate on data analysis projects using these tools.
Staying Informed: Stay updated with the latest developments and updates for R, RStudio, and Jamovi by subscribing to relevant newsletters or communities.
Supporting Others: Share your knowledge and help others who are beginning their journey with these tools.
I hope that this installation manual has been a valuable resource in getting you started with R, RStudio, and Jamovi. These tools offer limitless possibilities for data analysis and research. Remember that practice, exploration, and continuous learning will enhance your proficiency in using these tools effectively. Thank you for choosing this manual as your guide to installing and working with these essential data analysis tools. We wish you success in your data analysis endeavors!
We will continue our exploration of data analysis tools by introducing you to two powerful platforms: R and Jamovi. As a brief recap of our previous session, you’ve learned about the significance of inferential statistics and its applications in forestry and ecological research (see supplementary section for more detail information). Furthermore, this section provides an introduction to R and Jamovi, covering packages and modules, installation of R and RStudio, basic R commands, data structures, and importing data. It also introduces Jamovi’s interface, data import, and basic data manipulation. Now, we will dive into the practical aspects of using R and Jamovi for data analysis.
R Packages and Jamovi Modules are both essential components of statistical analysis and data manipulation, but they differ in several key ways:
Language Foundation: R packages are part of the R programming language. R is a versatile, open-source scripting language and environment explicitly designed for statistical computing and data analysis.
Community-Driven: R packages are developed by a diverse community of statisticians, data scientists, and programmers from around the world. Anyone can contribute to or create R packages, leading to a vast ecosystem with thousands of packages.
Functionality: R packages provide a wide range of functions and tools for statistical analysis, data visualization, machine learning, and more. These packages can be highly specialized, focusing on specific tasks or domains.
Flexibility: R packages offer a high level of customization and flexibility. Users can write their R code, combining functions from various packages to create tailored solutions.
Syntax: R uses its syntax, which is based on function calls and assignments. Users need to learn R’s specific syntax to work with R packages effectively.
Integration: R packages can be integrated with other programming languages like Python and C++, enabling users to harness the capabilities of these languages within R.
Code-Based: Using R packages often requires writing code or scripts to perform data analysis and visualization tasks. It’s suitable for those comfortable with programming.
Graphical User Interface (GUI): Jamovi is a statistical software that provides a point-and-click graphical user interface (GUI). Jamovi modules are components within this GUI that allow users to perform specific analyses without writing code.
Built-In Functionality: Jamovi modules come pre-installed with the software and cover a wide range of statistical analyses. Users can access these modules through a user-friendly interface, eliminating the need for coding.
Ease of Use: Jamovi is designed for users who may not have programming experience. It simplifies statistical analysis by providing intuitive menus, buttons, and options.
Accessibility: Jamovi is an excellent choice for beginners and users who prefer not to write code. It offers a low learning curve and helps users quickly perform common statistical tasks.
Interactivity: Jamovi allows users to interact with their data visually. Users can load datasets, click through options, and see immediate results in the interface.
Modular Design: Jamovi follows a modular design, meaning users can combine different modules to create analysis pipelines. This modular approach promotes reusability and versatility.
Scripting and R Integration: While Jamovi emphasizes point-and-click functionality, it also includes an R Syntax mode. This mode enables users to write and execute R code within Jamovi, combining the strengths of both approaches.
R Packages are code libraries for the R programming language, offering extensive functionality and flexibility but requiring coding skills. Jamovi Modules, on the other hand, are part of a user-friendly statistical software with a GUI, designed for ease of use and accessibility, making statistical analysis more accessible to a broader audience, including those without coding experience.
You can install R by following these steps:
Visit the CRAN (Comprehensive R Archive Network) website for your operating system (Windows, macOS, or Linux): https://cran.r-project.org/mirrors.html
Download the R installer for your OS and follow the installation instructions.
Once R is installed, you can proceed to install RStudio:
Visit the RStudio download page: https://www.rstudio.com/products/rstudio/download/
Download the appropriate RStudio installer for your OS (RStudio Desktop is recommended for most users).
Install RStudio by following the installation instructions.
Open RStudio by searching for “RStudio” in your computer’s application menu.
The RStudio interface consists of several panels, including the script editor, console, environment, and plots.
The script editor is where you write and execute R code.
The console displays R’s output and can be used for direct command entry.
Let’s explore some basic commands and data structures:
# Basic Arithmetic
2 + 3 # Addition: Calculates and returns 2 plus 3, which is 5.
5 - 2 # Subtraction: Calculates and returns 5 minus 2, which is 3.
4 * 6 # Multiplication: Calculates and returns 4 times 6, which is 24.
8 / 4 # Division: Calculates and returns 8 divided by 4, which is 2.
# Assigning Values to Variables
<-
x 10 # Assign 10 to the variable x: Creates a variable 'x' and assigns the value 10 to it.
<-
y 5 # Assign 5 to the variable y: Creates a variable 'y' and assigns the value 5 to it.
# Vectors
<-
my_vector c(3, 6, 9, 12) # Create a numeric vector: Constructs a vector 'my_vector' with the values 3, 6, 9, and 12.
length(my_vector) # Check the length of the vector: Returns the number of elements in 'my_vector' (4).
mean(my_vector) # Calculate the mean of the vector: Computes the average of the values in 'my_vector' (7.5).
# Data Frames (a common data structure in R)
# Create a sample forestry dataset: Generates a data frame 'forest_data' with columns 'TreeSpecies', 'Height', and 'Diameter'.
<- data.frame(
forest_data TreeSpecies = c("Oak", "Pine", "Maple", "Birch"),
Height = c(25, 20, 18, 22),
Diameter = c(10, 8, 7, 9)
)
print(forest_data) # Print the data frame 'forest_data': Displays the content of the data frame.
R Code Explanation
R allows you to import data from various file formats, such as CSV, Excel, or databases. Here’s an example of importing a CSV file:
# Check if the "pacman" package is available; if not, install it and load it
if (!require("pacman")) {
install.packages("pacman")
require(pacman)
}
# Use the "pacman" package to load multiple packages at once
::p_load(
pacman
rstatix,# rstatix: Provides functions for statistical analysis
tidyverse,# tidyverse: A collection of packages for data manipulation and visualization
easystats,# easystats: Provides easy-to-use functions for statistical analysis
readr,# readr: Used for reading data from various file formats
magrittr,# magrittr: Provides a pipe operator (%>%) for easier data manipulation
knitr,# knitr: Used for dynamic report generation
report,# report: A package for creating and formatting reports
scatr,# scatr: Tools for exploratory data analysis and visualization
jmv,# jmv: Tools for statistical analysis and hypothesis testing
haven,# haven: A package for reading and writing data in SAS format
foreign,# foreign: A package for reading and writing data in various formats
performance,# performance: Provides functions for assessing model performance
ggthemes,
here,install = TRUE,
# Install packages if not already installed
update = TRUE # Update packages if newer versions are available
)
# Load the iris dataset
data("iris") # Load the built-in iris dataset into the R environment
# Uncomment the following line to view the dataset in a separate window
# View(iris)
# Display a concise summary of the iris dataset
::glimpse(iris)
tibble
# Create a scatter plot using ggplot2 to visualize the relationship
# between Sepal.Length and Sepal.Width
ggplot(data = iris, aes(x = Sepal.Length, y = Sepal.Width)) +
geom_point() + # Add points to the plot
geom_smooth(method = "lm") # Add a linear regression line
# Read the iris dataset from a CSV file into a variable called iris_import
<-
iris_import read_csv(file = here::here("docs", "data", "Filtered.csv"))
# Uncomment the following line to view the imported dataset
# View(iris_import)
# Export the original iris dataset to a CSV file at the specified file path
::write.csv(
utilsx = iris,
# Dataset to export (iris)
file = "./data/iris.csv",
# File path to save the CSV
fileEncoding = "UTF-8",
# Encoding of the CSV file
row.names = FALSE # Exclude row names in the CSV
)
# Use getwd() to show your current working directory path
R Code Explanation
The code first checks if the “pacman” package [] is available
using the require
function. If it’s not
available, it installs the “pacman” package and then loads it using
require
.
The pacman::p_load
function is used
to load multiple packages at once. Each package listed is loaded, and if
any of them are not installed, they will be installed
(install = TRUE
). Additionally, if newer
versions of packages are available, they will be updated
(update = TRUE
).
Here’s a brief explanation of each package:
rstatix
(Kassambara,
2023): Provides functions for statistical analysis,
particularly for tidyverse users.
tidyverse
(Wickham et al.,
2019): A collection of packages (e.g., dplyr,
ggplot2) for data manipulation and visualization.
easystats
(Lüdecke et al.,
2022): Provides easy-to-use functions for various
statistical analyses.
readr
(Wickham et al., 2023):
Used for reading data from various file formats (e.g., CSV,
Excel).
magrittr
(Bache & Wickham,
2022): Provides the pipe operator
(%>%
**) for easier data manipulation.
knitr
(Xie,
2023): Used for dynamic report generation, often in
combination with R Markdown.
report
(Makowski et al.,
2023): A package for creating and formatting
reports.
scatr
(Selker,
2017): Provides tools for exploratory data analysis
and visualization.
jmv
(Selker et al.,
2022): Contains tools for statistical analysis and
hypothesis testing.
performance
(Lüdecke et al., 2021): Provides
functions for assessing model performance.
This code is an efficient way to ensure that all the necessary packages are available and up-to-date for your data analysis and reporting needs.
The next set of R codes above performs the following actions:
Loads the built-in iris dataset and optionally allows you to view
its summary using
tibble::glimpse(iris)
.
You can uncomment the line
# View(iris)
to view the dataset in a
separate window.
Creates a scatter plot using
ggplot2
to visualize the relationship
between Sepal.Length and Sepal.Width.
Imports the iris dataset from a CSV file located at
“data/iris.csv” into a variable called
iris_import
using the
read_csv
function from the
readr
package.
Exports the original iris dataset to a CSV file at the specified file path.
The last comment mentions that you can use
getwd()
to show your current working
directory path.
Please note that some lines of code are commented out and can be uncommented when needed.
Jamovi is a user-friendly statistical software with an intuitive interface. You can launch it by searching for “Jamovi” in your application menu.
Open your web browser.
In the address bar, type “https://www.jamovi.org/” and press Enter.
On the Jamovi website, click on the “Download” or “Try Online” button to access Jamovi.
If you choose to “Try Online,” it will open the Jamovi online interface in your browser.
Familiarize yourself with the Jamovi interface.
The top menu contains options for File, Edit, View, Analysis, Data, and more.
The left panel displays the data set (if loaded) and variables.
The right panel shows the analysis output.
In the left panel, under the “Data” tab, click “Import Dataset.”
Choose the data file you want to import (e.g., CSV, Excel).
Follow the on-screen instructions to configure data import settings and load your dataset.
After loading the data, explore the “Data” tab on the left panel.
To perform basic data manipulation tasks:
Select variables by clicking on their names.
Use the right-click menu or the “Transform” option to apply changes.
To save your project:
Click on “File” in the top menu.
Select “Save Project As” and choose a location to save your .omv project file.
Under the “Analysis” tab in the top menu, you’ll find a wide range of statistical analyses.
Select an analysis based on your research question (e.g., t-tests, ANOVA, regression).
Configure the analysis by specifying variables, settings, and options.
Click the “Run” button to execute the analysis.
After running an analysis, the results will appear in the right panel.
Interpret the output, including statistical measures, p-values, and visualizations.
Jamovi often provides descriptive statistics, charts, and inferential test results.
Jamovi provides a wide range of statistical analyses, including t-tests, ANOVA, regression, and more. In the following sessions, we will explore these analyses in greater detail.
Jamovi, a user-friendly and open-source statistical analysis software, offers an interface that seamlessly integrates with R, a powerful programming language and environment for statistical computing. This integration combines the user-friendly features of Jamovi with the robust statistical capabilities of R, providing a flexible platform for data analysis and visualization.
Key points to consider in integrating R in Jamovi:
Enhanced Statistical Power: Jamovi’s integration with R allows users to access a wide range of advanced statistical techniques and methods available in the R ecosystem. This includes specialized packages for complex data analysis and modeling.
Interactive Analysis: Users can perform analyses in Jamovi using its point-and-click interface while observing the R syntax generated in real-time. This helps users learn and understand the R code associated with their analyses.
Customization and Automation: For users familiar with R, the integration enables seamless customization and automation of analyses. R users can extend analyses conducted in Jamovi with additional scripting and package integration.
Data Visualization: R’s data visualization capabilities are available within Jamovi, allowing users to create custom plots and charts for data exploration and presentation.
Statistical Reporting: Users can generate reports in Jamovi, including statistical summaries, tables, and visualizations, which can be customized and exported for publication or sharing.
Collaboration: Teams with varying levels of statistical expertise can collaborate effectively. Users can share Jamovi projects with colleagues, even if they are not R proficient, ensuring consistent analyses and results.
Learning Opportunity: For those new to R, Jamovi serves as a valuable learning tool. Users can explore the R code generated by Jamovi, helping them transition to more extensive R-based analyses.
In essence, integrating R in Jamovi offers a powerful combination of user-friendly statistical analysis and the versatility of R scripting. It caters to both beginners and experienced statisticians, making it an ideal choice for data analysis, research, and collaboration across diverse domains.
R as a Backend: Jamovi, a user-friendly statistical analysis software, uses R as its computational backend. This means that when you perform statistical analyses or create plots in Jamovi, the software generates and executes corresponding R code in the background. This allows users who may not be familiar with R to take advantage of its powerful statistical capabilities.
Point-and-Click Interface: Jamovi provides a point-and-click interface for performing statistical analyses. Users can easily import datasets, perform various statistical tests, create visualizations, and generate reports without writing any R code.
Real-Time Syntax Generation: One of the key features of Jamovi is its ability to generate R syntax in real-time. As you perform actions in the Jamovi interface, such as running a t-test or creating a scatterplot, the corresponding R code is displayed. This provides users with a learning opportunity to understand the R commands associated with the analysis.
Easy Transition to R: For users who want to transition to R or have specific customization needs, Jamovi simplifies the process. Users can copy the generated R syntax from Jamovi and use it directly in their R environment for further customization or scripting.
R Packages for Jamovi: R users can take advantage of the “jmv” package, which allows them to interact with Jamovi directly from their R environment. This package provides functions to load Jamovi analyses, extract results, and incorporate Jamovi analyses into R scripts.
Seamless Collaboration: Researchers or data analysts who prefer R can still collaborate effectively with colleagues or team members using Jamovi. They can create their analyses in Jamovi, export the results as datasets, and then use R for advanced statistical modeling or further data manipulation.
Customization: R users can customize and extend the functionality of Jamovi analyses using R packages and scripts. This allows for greater flexibility and advanced data analysis when needed.
Leveraging the Best of Both Worlds: The integration of Jamovi in R and R in Jamovi offers the best of both worlds. Users can enjoy the simplicity and user-friendly interface of Jamovi for routine analyses while harnessing the extensive statistical and data manipulation capabilities of R when required.
The integration of R in Jamovi and Jamovi in R provides users with a flexible and powerful ecosystem for conducting statistical analyses. It accommodates users of varying skill levels, from those who prefer a graphical interface to those who are experienced R users, facilitating effective collaboration and streamlined workflows in data analysis and research.
Setting up R Syntax mode in Jamovi allows users to harness the full power of R programming within Jamovi’s user-friendly interface. This mode enables users to write, execute, and customize R code seamlessly while taking advantage of Jamovi’s data visualization and analysis features. Here’s how to set up R Syntax mode in Jamovi:
Install Jamovi: If you haven’t already, download and install Jamovi on your computer from the official Jamovi website (https://www.jamovi.org/download.html).
Launch Jamovi: Open Jamovi and create or open a dataset for analysis. You’ll typically start in the default point-and-click mode.
Enable R Syntax Mode
Navigate to the far end right corner of Jamovi window and click on the three vertical dots.
From the drop-down menu, select “R Syntax Mode.” This action switches your analysis interface to R Syntax mode.
R Syntax Mode: Once you enable R Syntax Mode, you’ll notice that for any analysis or plotting, R codes will appear next to the results.
Writing R Code in Jamovi
You can write and execute R codes directly from within Jamovi’s R editor. This is a module which is called “Rj” and can be accessed from the modules library. It must be installed and pinned to the main menu.
Click on the “Rj” icon and select “Rj editor”.
You can start writing R code directly in the console. For example, you can create variables, perform data manipulations, run statistical analyses, and create visualizations using R syntax. Examples are shown below.
Running R Code: To execute the R code you’ve written, simply press the “Run” button in the R Syntax Console or use the shortcut (typically Ctrl+Shift+Enter or Cmd+Shift+Enter).
Output and Visualizations: As you execute R code, any output, plots, or results will be displayed within the console. You can also create custom visualizations using R packages like ggplot2.
Combining Point-and-Click and R: Jamovi’s unique feature allows you to switch between Point-and-Click mode and R Syntax mode seamlessly. You can start with a point-and-click analysis and switch to R Syntax mode to access advanced options and customization.
Saving and Sharing: You can save your Jamovi project, which includes your dataset, analyses, and R code. This makes it easy to share your work or collaborate with others.
Learning Resources: If you’re new to R, there are plenty of online resources and tutorials available to help you learn R programming within Jamovi. Additionally, the generated R code can serve as a valuable learning tool.
Setting up R Syntax mode and Rj editor module in Jamovi empowers users to perform complex analyses and customizations, making it a versatile tool for both beginners and experienced data analysts and researchers. It combines the accessibility of Jamovi with the flexibility of R, offering the best of both worlds for data analysis and visualization.
jmv
(Selker et al., 2022) and
scatr
(Selker, 2017).
Furthermore, import the data set into R, paste the syntax copied over
from Jamovi and run the syntax as shown below.# Use pacman::p_load to load packages (jmv, scatr, jmvcore)
# with optional installation and no package updates
::p_load(jmv, scatr, jmvcore, install = TRUE, update = FALSE)
pacman
# Import above-ground carbon data from a CSV or the SAV file
<-
carbon ::read_csv(file = here::here("docs", "data", "Filtered.csv"))
readr
<-
carbon_spss_data ::read_sav(file = here::here("docs", "data", "Filtered.sav"))
haven
# Syntax from the scatr package to create a scatterplot with linear regression lines
# This code visualizes the relationship between Tree Density, Aboveground Carbon, and Management Regime
::scat(
scatrdata = carbon,
# Specify the dataset (carbon)
y = "Aboveground_Tree_Carbon_ton_per_ha_per_year",
# Choose the dependent variable (Y-axis)
x = "Tree_Density_per_ha",
# Choose the independent variable (X-axis)
group = "Management_regime",
# Group the data by Management Regime
line = "linear",
# Add linear regression lines
se = TRUE
# Display standard error bars )
R Code Explanation
pacman::p_load(jmv, scatr, jmvcore, install = TRUE, update = FALSE)
is used to load three packages: jmv
,
scatr
, and
jmvcore
. The
install = TRUE
parameter ensures that
these packages are installed if they are not already installed, and
update = FALSE
prevents the packages from
being updated.
carbon <- readr::read_csv("./data/Filtered.csv")
reads data from a CSV file named “Filtered.csv” located in the “./data”
directory and stores it in a variable called “carbon.” This line imports
the dataset needed for further analysis.
scatr::scat(...)
is a function from
the scatr
package used to create a
scatterplot with linear regression lines. The code specifies the dataset
as “carbon,” sets the Y-axis variable to
“Aboveground_Tree_Carbon_ton_per_ha_per_year,” sets the X-axis variable
to “Tree_Density_per_ha,” groups the data by “Management_regime,” adds
linear regression lines, and displays standard error bars. This code is
used to visualize the relationship between Tree Density, Aboveground
Carbon, and Management Regime in the dataset.
Note that plots created using the scatr
package has
limited functions to further tweak plots. A work around for this issue
is to use the ggplot2
package which has more customizable
functions. An example is shown below.
# Use pacman::p_load to load packages (ggthemes, ggplot2, patchwork)
# with optional installation and no package updates
::p_load(ggthemes,
pacman
ggplot2,
patchwork,install = TRUE,
update = FALSE)
# Import dataset from a CSV file
<- readr::read_csv("./data/Filtered.csv")
carbon
# Create a customizable plot using ggplot2
<- ggplot2::ggplot(
plot1 data = carbon,
# Specify the dataset (carbon)
aes(
# Define aesthetic mappings
x = carbon$Tree_Density_per_ha,
# X-axis variable
y = carbon$Aboveground_Tree_Carbon_ton_per_ha_per_year,
# Y-axis variable
col = carbon$Management_regime # Color by Management Regime
)+
) ::geom_point(size = 3, pch = 21) + # Add points with custom size and shape
ggplot2::geom_smooth(method = "lm") + # Add a linear regression line
ggplot2::labs(x = "Tree density (ha)", # Set X-axis label
ggplot2y = "Above-ground tree carbon (tonne/ha/year)", # Set Y-axis label
col = "Management Regime") + # Set legend title
::scale_x_continuous(limits = c(0, 1500)) + # Set X-axis limits
ggplot2::scale_y_continuous(limits = c(0, 6)) + # Set Y-axis limits
ggplot2::theme_base(base_size = 15, base_family = "times") + # Apply custom theme settings
ggthemes::theme(
ggplot2panel.grid.minor = element_line(size = 0.5, color = "grey"),
# Customize minor grid lines
axis.title = element_text(size = 20) # Customize axis title text
)
# Print the customized plot
print(plot1)
R Code Explanation
pacman::p_load(...)
is used to load
three packages: ggthemes
,
ggplot2
, and
patchwork
. The
install = TRUE
parameter ensures that
these packages are installed if they are not already installed, and
update = FALSE
prevents the packages from
being updated.
carbon <- readr::read_csv("./data/Filtered.csv")
reads data from a CSV file named “Filtered.csv” located in the “./data”
directory and stores it in a variable called “carbon.” This line imports
the dataset needed for plotting.
The ggplot2::ggplot(...)
function
is used to create a customizable plot. It specifies the dataset as
“carbon” and defines aesthetic mappings, including X-axis, Y-axis, and
color mapping based on the “Management_regime” column.
Various ggplot2::geom_
functions
are used to add geometrical elements to the plot, such as points and a
linear regression line.
ggplot2::labs(...)
,
ggplot2::scale_...
, and
ggthemes::theme_...
functions are used to
customize plot labels, axis limits, and theme settings.
Finally, print(plot1)
prints the
customized plot to the output.
# Modify the first plot (plot1)
<- plot1 +
p1 ::labs(x = "Tree density (ha)", # Change the X-axis label
ggplot2y = "Above-ground tree carbon (tonne/ha/year)", # Change the Y-axis label
col = "") # Remove the color legend title
# Create another customizable plot using ggplot2
<- ggplot2::ggplot(
plot2 data = carbon,
# Specify the dataset (carbon)
aes(
x = carbon$Management_regime,
# X-axis variable
y = carbon$Aboveground_Tree_Carbon_ton_per_ha_per_year # Y-axis variable
)+
) ::geom_boxplot(fill = "grey") + # Add a boxplot with grey fill
ggplot2::labs(x = "Management Regime", # Set X-axis label
ggplot2y = "Above-ground tree carbon (tonne/ha/year)") + # Set Y-axis label
::scale_y_continuous(limits = c(0, 6)) + # Set Y-axis limits
ggplot2::theme_base(base_size = 15, base_family = "times") + # Apply custom theme settings
ggthemes::theme(axis.title = element_text(size = 20)) # Customize axis title text
ggplot2
# Print the second plot (plot2)
print(plot2)
# Modify the second plot (plot2)
<-
p2 + ggplot2::labs(x = "Management Regime", # Change the X-axis label
plot2 y = "") # Remove the Y-axis label
# Combine both modified plots (p1 and p2) using the "&" operator
# Also, customize the legend position and add plot annotations
+ p2 & theme(legend.position = "bottom") &
p1 ::plot_annotation(tag_levels = "a",
patchworktag_prefix = "(",
tag_suffix = ")")
R Code Explanation
p1
is created by modifying
plot1
. The X-axis label is changed, and
the color legend title is removed.
plot2
is created as a new
customizable plot using ggplot2
. It
specifies the dataset and aesthetic mappings, creates a box-plot, and
customizes the plot labels, axis limits, and theme settings.
p2
is created by modifying
plot2
. The X-axis label is changed, and
the Y-axis label is removed.
p1 + p2 & ...
combines both
modified plots p1
and
p2
using the
&
operator. Additional customizations
are applied to the combined plot, including changing the legend position
and adding plot annotations with tags.
The following syntax and results (image) below were generated in Jamovi. Syntax is further modified in R.
# Load necessary R packages using pacman
::p_load(jmv, # Load the jmv package for statistical analysis
pacman# Load the magrittr package for data manipulation
magrittr, install = TRUE, # Install packages if not already installed
update = FALSE # Do not update packages if newer versions are available
)
# Perform Kruskal-Wallis test with pairwise comparisons
<- jmv::anovaNP(
kruskal_pairwise formula = Aboveground_Tree_Carbon_ton_per_ha_per_year ~ Plantation_age, # Specify the formula
data = carbon, # Specify the dataset (carbon)
pairs = TRUE # Perform pairwise comparisons
)
# Display the Kruskal-Wallis significance test results
%>% print() kruskal_pairwise
##
## ONE-WAY ANOVA (NON-PARAMETRIC)
##
## Kruskal-Wallis
## ───────────────────────────────────────────────────────────────────────────────
## χ² df p
## ───────────────────────────────────────────────────────────────────────────────
## Aboveground_Tree_Carbon_ton_per_ha_per_year 50.05889 7 < .0000001
## ───────────────────────────────────────────────────────────────────────────────
##
##
## DWASS-STEEL-CRITCHLOW-FLIGNER PAIRWISE COMPARISONS
##
## Pairwise comparisons - Aboveground_Tree_Carbon_ton_per_ha_per_year
## ──────────────────────────────────────────────────────────────────
## W p
## ──────────────────────────────────────────────────────────────────
## 7 8 -5.0245113 0.0091010
## 7 10 -0.4276180 0.9999889
## 7 11 1.7104719 0.9296347
## 7 12 -2.7795169 0.5055258
## 7 17 1.2828540 0.9855155
## 7 18 4.8107024 0.0154435
## 7 21 4.2761799 0.0511307
## 8 10 4.5968934 0.0254800
## 8 11 4.7037979 0.0199077
## 8 12 4.0623709 0.0783341
## 8 17 5.3452248 0.0039229
## 8 18 5.3452248 0.0039229
## 8 21 5.3452248 0.0039229
## 10 11 1.3897585 0.9769915
## 10 12 -0.8552360 0.9988368
## 10 17 2.1380899 0.8016074
## 10 18 4.2761799 0.0511307
## 10 21 4.4899889 0.0323768
## 11 12 -2.8864214 0.4543784
## 11 17 0.5345225 0.9999489
## 11 18 4.3830844 0.0408393
## 11 21 4.1692754 0.0635316
## 12 17 3.3140394 0.2701716
## 12 18 5.3452248 0.0039229
## 12 21 4.7037979 0.0199077
## 17 18 4.8107024 0.0154435
## 17 21 4.0623709 0.0783341
## 18 21 1.6035675 0.9494883
## ──────────────────────────────────────────────────────────────────
R Code Explanation
pacman::p_load(...)
is used to load
the required R packages, including jmv
for
statistical analysis and magrittr
for data
manipulation. The install
parameter is set
to TRUE
to install the packages if they
are not already installed, and update
is
set to FALSE
to prevent updating
packages.
kruskal_pairwise
stores the result
of the Kruskal-Wallis test with pairwise comparisons. It calculates the
Kruskal-Wallis test for the specified formula and dataset, and the
pairs = TRUE
argument indicates that
pairwise comparisons should be performed.
kruskal_pairwise %>% print()
is
used to display the Kruskal-Wallis significance test results directly
without the need to extract them into a data frame.
Chapter 2 focuses on the critical aspects of data preparation for ecological data analysis. Here, you will learn how to efficiently import ecological datasets into R and Jamovi. Additionally, you’ll explore techniques for cleaning and preprocessing data, ensuring that your analyses are based on high-quality, error-free data. By the end of this chapter, you will have:
Acquired the skills to import data from various file formats.
Understood the importance of data cleaning and preprocessing.
Applied techniques to handle missing data, outliers, and data transformations.
Data import is a critical initial step in ecological research, as it involves bringing external data into your analysis environment (typically R or a similar software) for examination, manipulation, and analysis. The significance of data import in ecological research is multifaceted:
Data Collection and Compilation: Ecological research often requires gathering data from various sources, such as field surveys, remote sensing, weather stations, or pre-existing databases. Data import is the process of bringing these diverse datasets together for a comprehensive analysis.
Data Integration: Ecologists work with heterogeneous datasets, including numeric measurements, spatial coordinates, categorical variables, and textual descriptions. Data import allows you to integrate these diverse data types into a unified dataset, making it ready for analysis.
Quality Assurance: Imported data may contain errors, missing values, outliers, or inconsistencies. During the import process, researchers can identify and address data quality issues, ensuring the integrity and reliability of subsequent analyses.
Data Exploration: Once imported, data can be visualized and explored to gain insights into patterns, trends, and relationships. Effective data import facilitates initial exploratory data analysis (EDA), helping researchers decide on suitable statistical methods.
Statistical Analysis: Ecological research often involves a wide range of statistical techniques, from simple descriptive statistics to advanced modeling. To apply these methods, data must be in a format that allows for statistical analysis, which data import achieves.
Communication and Reporting: Accurate and well-organized data is crucial for communicating research findings to peers, policymakers, or the public. Data import ensures that data is in a format conducive to creating meaningful charts, graphs, and reports.
Field Surveys: Researchers collect primary data through field surveys, which can include measurements of species abundance, biodiversity, habitat characteristics, and environmental variables like temperature and precipitation.
Remote Sensing: Satellite and aerial imagery, LiDAR (Light Detection and Ranging), and drones provide remote sensing data that can be used to monitor land cover, vegetation health, and changes in the environment over time.
Climate and Weather Data: Climate and weather data, obtained from weather stations, are essential for studying the effects of climate change on ecosystems and wildlife behavior.
Geospatial Data: Geographic Information Systems (GIS) data, including spatial coordinates, topography, and land use, are often used to study spatial patterns and relationships within ecosystems.
Government Databases: Government agencies and organizations maintain extensive ecological datasets, including data on wildlife populations, conservation areas, and environmental regulations.
Scientific Literature: Ecologists may extract data from published research papers or online databases, such as GenBank for genetic data or Global Biodiversity Information Facility (GBIF) for species occurrence records.
Social Surveys: Ecological research may incorporate social surveys to assess human interactions with ecosystems, such as visitor behavior in national parks or community perceptions of environmental issues.
Laboratory Experiments: Experimental data from controlled laboratory studies are used to investigate specific ecological hypotheses.
In summary, data import in ecological research serves as the gateway to the analysis and interpretation of complex ecological systems. It allows researchers to leverage diverse data sources, address data quality concerns, and ultimately gain a deeper understanding of the natural world.
# Load the readr package (if not already loaded)
library(readr)
# Set the file path to your CSV file
<- "path/to/your/data.csv"
file_path
# Import the CSV file into a data frame
<- readr::read_csv(file_path)
csv_data
# View the imported data
head(csv_data)
# Load the readxl package (if not already loaded)
library(readxl)
# Set the file path to your Excel file
<- "path/to/your/data.xlsx"
file_path
# Import the Excel file into a data frame (assuming the data is in the first sheet)
<- readxl::read_excel(file_path, sheet = 1)
xlsx_data
# View the imported data
head(xlsx_data)
R Code Explanation
For Importing a CSV File:
Load the readr
Package: This line
(line 2) loads the readr
package, which is
used for reading CSV files.
Set the File Path: In line 5, you need to set
the file path to your CSV data file. Replace
"path/to/your/data.csv"
with your actual
file path.
Import the CSV File: Line 8 uses the
read_csv
function from the
readr
package to read the CSV file
specified by file_path
and stores it in
the csv_data
data frame.
View the Imported Data: Line 11 displays the
first few rows of the imported CSV data using the
head
function, allowing you to inspect the
data.
For Importing an Excel File:
Load the readxl
Package: This line
(line 14) loads the readxl
package, which
is used for reading Excel files.
Set the File Path: In line 17, you should set
the file path to your Excel data file. Replace
"path/to/your/data.xlsx"
with your actual
file path.
Import the Excel File: Line 20 uses the
read_excel
function from the
readxl
package to read the Excel file
specified by file_path
. The imported data
is stored in the xlsx_data
data
frame.
View the Imported Data: Line 23 displays the
first few rows of the imported Excel data using the
head
function for initial data
exploration.
These steps guide you through the process of importing data from CSV and Excel files into R, allowing you to work with your ecological datasets. Remember to replace the file paths with your actual file paths when applying these steps in your R script or environment.
# Load the DBI and odbc packages (if not already loaded)
library(DBI)
library(odbc)
# Define the database connection details
<- dbConnect(
db_connection ::odbc(),
odbcDriver = "Your_Database_Driver",
# e.g., "SQL Server" or "PostgreSQL"
Server = "Your_Server_Address",
Database = "Your_Database_Name",
UID = "Your_Username",
PWD = "Your_Password"
)
# Check the database connection
dbIsValid(db_connection)
# Specify the SQL query to retrieve data from a table
<- "SELECT * FROM Your_Table_Name"
sql_query
# Execute the SQL query and import the data into a data frame
<- dbGetQuery(db_connection, sql_query)
db_data
# View the imported data
head(db_data)
R Code Explanation
Load DBI and odbc Packages
DBI
is a database interface,
and odbc
is a package for database
connectivity.Define the Database Connection Details
db_connection <- dbConnect(odbc::odbc(), ...)
sets up a connection to a database. You need to specify details such as
the database driver, server address, database name, username, and
password.
Replace "Your_Database_Driver"
,
"Your_Server_Address"
,
"Your_Database_Name"
,
"Your_Username"
, and
"Your_Password"
with your actual database
information.
Check the Database Connection
dbIsValid(db_connection)
verifies if
the database connection is valid. It will return
TRUE
if the connection is successful.Specify the SQL Query:
sql_query <- "SELECT * FROM Your_Table_Name"
sets up an SQL query to retrieve data from a specific table in your
database.
Replace "Your_Table_Name"
with the
actual name of the table you want to query.
Execute the SQL Query and Import Data
db_data <- dbGetQuery(db_connection, sql_query)
executes the SQL query on the database server and imports the result
into an R data frame called db_data
.View the Imported Data
head(db_data)
displays the first few
rows of the imported data frame, allowing you to inspect the data.These codes are used to establish a connection to a database, retrieve data from it using an SQL query, and bring that data into R for further analysis. Remember to replace the placeholders with your actual database information.
Note that structured data management is of paramount importance in ecological research, and here’s why it deserves special attention:
Data Quality Assurance: Structured data management ensures that the data you work with is accurate, reliable, and consistent. This includes addressing issues like missing values, outliers, duplicates, and data entry errors. High-quality data is essential for making sound ecological inferences and drawing reliable conclusions.
Data Integrity: Managing data in a structured manner preserves its integrity throughout the research process. It reduces the risk of inadvertent changes, deletions, or overwrites that can compromise the reliability of your findings.
Reproducibility: Structured data management facilitates research reproducibility. When others attempt to replicate your research or when you revisit your own work after some time, well-structured data ensures that you can easily understand, replicate, and build upon your previous analyses.
Data Traceability: Structured data management often involves proper documentation of data sources, collection methods, and transformations. This traceability is critical for establishing the credibility and transparency of your research.
Efficient Analysis: Structured data is easier to work with, reducing the time and effort required for data cleaning, preprocessing, and analysis. Researchers can focus on the ecological questions and insights rather than wrestling with messy data.
Collaboration: If your research involves collaboration with other researchers or teams, structured data management becomes indispensable. It ensures that everyone is on the same page regarding data formats, variable definitions, and data handling protocols.
Long-Term Data Preservation: Ecological research often spans long periods. Properly structured data ensures that data can be preserved and reused over time, even as technology and personnel change.
Data Sharing and Accessibility: In many cases, ecological research data is of broader interest and value to the scientific community, policymakers, and conservationists. Well-structured data can be more easily shared, reused, and made accessible to a wider audience.
Statistical Analysis: Structured data is a prerequisite for conducting meaningful statistical analyses. Many statistical tools and software packages require data to be organized in a particular format. Structured data management ensures that your data is analysis-ready.
Ethical Considerations: Ethical research practices often include data protection and privacy considerations. Structured data management helps in anonymizing and securing sensitive data as needed, ensuring compliance with ethical guidelines.
In summary, structured data management is the foundation upon which ecological research is built. It ensures data quality, facilitates analysis, promotes transparency, and enhances the overall credibility and impact of your research. Researchers who invest in structured data management are better equipped to make significant contributions to the understanding and conservation of ecosystems.
Jamovi simplifies data import with its user-friendly interface, making it accessible to users who may not be familiar with coding or complex data manipulation.
Data cleaning is of paramount significance in ecological analysis due to its substantial impact on research outcomes. Here’s why data cleaning is essential in ecological research:
Data Quality Assurance: Raw ecological data often contain errors, inaccuracies, or inconsistencies due to various factors, such as measurement errors, sensor malfunctions, or human errors during data collection. Data cleaning is the process of identifying and rectifying these issues, ensuring that the data accurately represent the ecological phenomena under study.
Accurate Analyses: Cleaned data provide a reliable foundation for statistical analyses and modeling. Without data cleaning, the results of analyses may be misleading or erroneous, potentially leading to incorrect conclusions about ecological relationships or trends.
Reducing Bias: Incomplete or erroneous data can introduce bias into research outcomes. Data cleaning helps reduce this bias, ensuring that the results are more representative of the true ecological conditions.
Enhanced Interpretability: Cleaned data are easier to interpret and visualize. Researchers can trust that patterns and relationships observed in the data are genuine and not artifacts of data errors or anomalies.
Effective Data Visualization: Data cleaning improves the quality of data visualization. Visualizations, such as graphs and charts, are crucial for conveying ecological findings. Cleaned data enable researchers to create informative and accurate visual representations.
Comparability: Cleaned data allow for meaningful comparisons within and between ecological studies. Researchers can confidently compare data from different sources or time periods, knowing that data quality issues have been addressed.
Scientific Credibility: Ecological research relies on the credibility of findings. Cleaned data enhance the scientific rigor of a study, increasing confidence in its results and conclusions.
Effective Decision-Making: Ecological research often informs conservation efforts, policy decisions, and resource management. Cleaned data ensure that decisions made based on research outcomes are well-founded and have a positive impact on ecosystems and biodiversity.
Data Archiving: High-quality, cleaned data are more suitable for long-term archiving and sharing with the scientific community. Properly cleaned and documented data sets can contribute to broader ecological knowledge and support future research.
Time and Resource Efficiency: Although data cleaning requires effort, it ultimately saves time and resources during analysis. Cleaned data lead to more efficient and accurate statistical procedures.
In ecological analysis, where data are collected in diverse and often challenging environments, data cleaning is a critical step in the research process. It transforms raw, potentially problematic data into a reliable foundation for meaningful analysis, interpretation, and the generation of ecological insights that contribute to our understanding of the natural world.
Handling missing data in ecological research is crucial to ensure the integrity and validity of your analyses. Here are techniques for identifying and handling missing data:
Identifying Missing Data
Summary Statistics: Calculate summary statistics such as mean, median, and standard deviation for each variable. Missing data will be indicated by “NA” or “NaN” values in R or blank cells in spreadsheets.
Visualization: Create visualizations like histograms or bar plots to visualize the distribution of missing data for each variable. This can reveal patterns of missingness.
Missing Data Packages: R packages like naniar
,
skimr
or VIM
provide functions and plots specifically designed for visualizing and
understanding missing data patterns.
Handling Missing Data
Removal: Sometimes, the simplest approach is to remove observations (rows) or variables (columns) with missing data. However, this should be done judiciously, as it can lead to loss of valuable information.
Imputation: Imputation involves estimating
missing values based on observed data. Common imputation methods include
mean imputation (replacing missing values with the mean of the
variable), median imputation, or regression imputation (predicting
missing values based on other variables). R packages like mice
and missForest
provide powerful imputation tools.
Data Augmentation: In Bayesian statistics, data augmentation techniques can be used to account for missing data by treating them as additional parameters to be estimated.
Interpolation/Extrapolation: In time series or spatial data, missing values can often be estimated through interpolation (estimating values within the range of observed data) or extrapolation (estimating values beyond the range of observed data).
Multiple Imputation: This advanced technique
involves creating multiple datasets with different imputed values for
missing data and analyzing each dataset separately. Results are then
combined to account for uncertainty due to missing data. The mice
package in R is commonly used for multiple imputation.
Exploring Patterns of Missing Data
Missing Data Heatmaps: Use heat-maps to visualize the patterns of missing data in your dataset. This helps identify if missingness is random or if there are systematic patterns related to specific variables or time periods.
Missing Data by Subgroup: Explore if missingness varies by subgroups within your data (e.g., by location, species, or time). Understanding these patterns can inform imputation strategies.
Missing Data Mechanisms: Consider the mechanism behind missing data. Is it missing completely at random (MCAR), missing at random (MAR), or not missing at random (NMAR)? This information can guide imputation methods.
Sensitivity Analysis: Perform sensitivity analyses to assess how different imputation methods or missing data assumptions impact your results. This helps quantify the uncertainty associated with missing data.
Collect More Data: In some cases, the best solution is to collect more data to reduce missingness in critical variables.
Remember that there is no one-size-fits-all approach to handling missing data in ecological research. The choice of method should depend on the nature of the data, the extent of missingness, and the goals of your analysis. Transparently report your methods for handling missing data in research publications to ensure the reproducibility of your findings.
Outliers are data points that significantly deviate from the rest of the data in a dataset. Detecting and addressing outliers is essential in ecological research for several reasons:
Importance of Addressing Outliers
Influence on Statistics: Outliers can strongly influence summary statistics like the mean and standard deviation, leading to biased estimates. This can affect the interpretation of ecological patterns and relationships.
Model Assumptions: Many statistical models assume that the data follow a certain distribution or have homogeneous variances. Outliers violate these assumptions, potentially leading to incorrect model inferences.
Ecological Significance: Outliers may represent rare or unusual ecological events that are of particular interest or concern. Identifying and understanding these outliers can be critical for ecological research.
Methods for Detecting Outliers
Visual Inspection: The simplest method is to create visualizations like scatter plots, box plots, or histograms. Outliers often appear as data points far from the main cluster or as individual points outside the whiskers of a box plot.
Z-Scores: Calculate the Z-score for each data point, which measures how many standard deviations a data point is from the mean. Data points with Z-scores beyond a certain threshold (e.g., |Z| > 2 or 3) are considered outliers.
Tukey’s Method: Tukey’s method uses the Interquartile Range (IQR) to detect outliers. Data points outside the range defined by Q1 - 1.5 * IQR and Q3 + 1.5 * IQR are considered outliers, where Q1 and Q3 are the first and third quartiles, respectively.
Modified Z-Scores: In cases where data are not normally distributed, modified Z-scores like the Median Absolute Deviation (MAD) can be more robust for outlier detection.
Techniques for Outlier Treatment
Removal: The simplest approach is to remove outliers from the dataset. However, this should be done cautiously and with justification, as removing data points can lead to information loss.
Transformation: Transforming the data using mathematical functions (e.g., logarithm) can reduce the impact of outliers and make the data more amenable to analysis.
Winsorization: Winsorization replaces extreme values with values closer to the rest of the data (e.g., setting all values above a certain threshold to that threshold). This approach preserves the data distribution while mitigating the influence of outliers.
Robust Statistical Methods: Robust statistical methods, such as robust regression or robust estimation of central tendency and variance, are less influenced by outliers and provide more reliable estimates.
Modeling Approaches: In some cases, it may be appropriate to model outliers explicitly as a separate group or to use models that are robust to outliers.
Reporting: Regardless of the approach chosen, it is essential to transparently report how outliers were handled in research publications to ensure the reproducibility and credibility of the analysis.
The choice of outlier detection and treatment methods should depend on the nature of the data and the research objectives. It is advisable to perform sensitivity analyses to assess how different outlier strategies impact research findings.
Data preprocessing refers to a set of procedures and techniques used to clean, transform, and prepare raw data for analysis. It plays a pivotal role in the data analysis process, as the quality and structure of the data significantly influence the outcomes of statistical analyses and machine learning models.
The key steps in data preprocessing include data cleaning (dealing with missing values and outliers), data transformation (changing the format or distribution of data), and data reduction (reducing the volume but preserving the key information). Data preprocessing aims to ensure that the data is in a suitable form for analysis, making it more interpretable and increasing the accuracy and reliability of analytical results.
Data transformation involves altering the data values to meet the assumptions of statistical analysis. Various data transformation techniques can be applied in ecological research:
Log Transformation: Logarithmic transformation is commonly used to stabilize variance, make the data more symmetric, and approximate a normal distribution. It is particularly useful when dealing with data that exhibit exponential growth or decay, such as species abundance data or tree growth rates.
Square Root Transformation: Similar to log transformation, square root transformation can be used to stabilize variance and approximate normality. It is effective when dealing with count data or data with non-constant variance.
Box-Cox Transformation: The Box-Cox transformation is a family of power transformations that can be applied to make data conform to normality assumptions. It includes both logarithmic and square root transformations as special cases. The optimal transformation is selected based on maximum likelihood estimation.
Arcsine Transformation: Arcsine square root transformation is used for proportional data or data with bounded values (e.g., percentage data). It can make the data more symmetric and suitable for parametric tests.
Exponential Transformation: When dealing with data that follows a decay process, an exponential transformation can be applied to linearize the relationship.
Data transformations should be applied when:
Data violate assumptions of normality or homoscedasticity required for parametric tests.
Data exhibit heteroscedasticity (variance changes with the level of a variable).
The research question or theoretical considerations suggest that a particular transformation is appropriate (e.g., log-transforming biomass data).
Data transformations can improve normality by reducing skewness and kurtosis in the data distribution. Normality is essential for parametric tests like t-tests and ANOVA, which assume that data follow a normal distribution.
Transformations can also help in achieving homoscedasticity, where the variance of the residuals is constant across levels of an independent variable. This is crucial for linear regression and ANOVA, as violations of homoscedasticity can lead to incorrect inferences.
Scaling: Scaling variables involves transforming them to have a common scale or range, typically between 0 and 1 or with a mean of 0 and a standard deviation of 1. Scaling is essential when variables have different units or scales because it ensures that all variables contribute equally to analyses like clustering or principal component analysis.
Centering: Centering involves subtracting the mean of a variable from each data point. Centering is useful when interpreting regression coefficients because it makes the intercept more interpretable. In the context of multiple regression, centering can reduce multicollinearity between predictor variables.
When variables have different units or scales, their magnitudes can dominate the results of certain analyses. Scaling ensures that all variables are treated equally, preventing larger variables from unduly influencing the outcomes. It also facilitates the interpretation of coefficients in regression models because the coefficients represent the effect of a one-unit change in the predictor variable while holding other variables constant. Scaling ensures that this one-unit change is consistent across all predictors, regardless of their units or scales.
Chapter 2 of “Exploring Ecological Data with R and Jamovi” emphasizes the critical importance of successful data import, cleaning, and preprocessing in ecological data analysis. Here are the key takeaways:
Data Import Significance: Data import is the initial step in any data analysis project. Ecological researchers often deal with diverse data sources, including flat files (e.g., CSV, Excel) and databases. Accurate data import ensures that you have access to the necessary information for analysis.
Common Data Sources: Ecological research commonly involves data from various sources, including field observations, experiments, and remote sensing. Understanding how to import data from these sources is essential for ecologists.
R and Jamovi Integration: Both R and Jamovi
offer user-friendly approaches to data import. Jamovi provides a
point-and-click interface, while R offers versatile functions like
readr
and
readxl
for importing data from flat
files.
Database Connection: For larger datasets stored in relational databases, knowing how to connect to and import data from databases is crucial. R provides packages like DBI and odbc for this purpose.
Structured Data Management: Structured data management ensures that your data is organized, consistent, and error-free. This process involves tasks such as handling missing data, identifying and treating outliers, and transforming data when necessary.
Missing Data Handling: Missing data can impact the validity of your analyses. Techniques like data imputation, removal of missing values, and exploring patterns of missingness are essential for handling missing data effectively.
Outlier Detection and Treatment: Outliers can distort statistical analyses and lead to inaccurate conclusions. Visual inspection, Z-scores, and Tukey’s method are valuable tools for identifying and addressing outliers.
Data Transformation: Data transformation techniques like log transformation, square root transformation, and Box-Cox transformation can help meet assumptions of normality and homoscedasticity, improving the reliability of statistical analyses.
Scaling and Centering: Scaling variables to a common range and centering variables around their mean are important for ensuring that variables with different units or scales are treated equally in analyses.
Key Emphasis: Successful data import, cleaning, and preprocessing are essential steps to ensure that ecological analyses are based on accurate and reliable data. These steps lay the foundation for meaningful and trustworthy research outcomes.
By mastering these data management techniques, you are now well-prepared to explore and analyze ecological datasets with confidence, setting the stage for robust ecological research.
In Chapter 3, you will embark on a journey into the world of Exploratory Data Analysis (EDA) for ecological data. EDA is a crucial step that allows you to understand and gain insights from your datasets before diving into formal statistical analyses. By the end of this chapter, you will have:
Mastered various visualization techniques for ecological data.
Learned how to summarize and describe your data effectively.
Discovered patterns, relationships, and outliers within your datasets.
Exploratory Data Analysis (EDA) is a critical phase in the data analysis process that involves the initial examination, visualization, and summary of data. It serves as a fundamental tool in ecological research and data analysis. Here’s an explanation of the concept and its significance in ecological research:
EDA is an approach used to understand the main characteristics of a dataset before applying more complex statistical methods.
It aims to uncover patterns, relationships, anomalies, and other insights within the data.
EDA employs a combination of graphical and numerical techniques to achieve these objectives.
It is a crucial step in the data analysis pipeline, allowing researchers to formulate hypotheses and make informed decisions about subsequent analyses.
Ecological datasets are often complex and multidimensional, containing numerous variables and data points.
EDA helps researchers gain an initial understanding of the dataset’s structure and content.
It aids in identifying potential data quality issues such as outliers, missing values, or data inconsistencies.
EDA enables the discovery of trends and patterns within ecological data, which can guide further analysis.
Through visualization, EDA helps in the communication of results to both scientific and non-scientific audiences.
EDA can highlight relationships between ecological variables, supporting the formulation of research questions and hypotheses.
In ecological research, where the influence of environmental factors on ecosystems is studied, EDA is crucial for uncovering insights that can drive conservation efforts and environmental management decisions.
The typical workflow of an EDA process in ecological research involves the following steps:
Data Collection: Gather ecological data from various sources, such as field surveys, experiments, or remote sensing.
Data Cleaning and Preprocessing: As discussed in Chapter 2, prepare the data by handling missing values, identifying and treating outliers, and performing necessary data transformations.
Univariate Analysis: Begin with a univariate analysis, which involves exploring each variable individually. Compute summary statistics, generate histograms, density plots, and box plots to understand the distribution and central tendency of each variable.
Bivariate Analysis: Move on to bivariate analysis to examine relationships between pairs of variables. Scatter plots, correlation matrices, and cross-tabulations can reveal associations between ecological factors.
Multivariate Analysis: Explore relationships involving multiple variables simultaneously. Techniques like principal component analysis (PCA) or multidimensional scaling (MDS) can provide insights into complex data structures.
Visualization: Utilize data visualization tools, such as scatter plots, bar charts, heat-maps, and spatial maps, to create visual representations of ecological patterns and trends.
Hypothesis Generation: Based on insights gained from EDA, generate hypotheses about ecological processes, interactions, or correlations that warrant further investigation.
Summary and Reporting: Summarize key findings and insights from the EDA process. Create reports, presentations, or visuals to communicate the results to stakeholders, colleagues, or the broader scientific community.
Iterative Process: EDA is often iterative, as insights from initial analysis may lead to further questions or refinements in subsequent analyses.
In ecological research, EDA serves as a powerful tool for uncovering hidden insights within complex datasets, guiding subsequent analyses, and informing ecological decision-making processes. It enables researchers to make data-driven conclusions and contributes to a deeper understanding of ecological systems and environmental dynamics.
Data visualization is a cornerstone of Exploratory Data Analysis (EDA) in ecological research. It is a powerful technique that allows researchers to represent complex data visually, making it easier to understand and interpret. Here’s an overview of the significance of data visualization in EDA:
Understanding Complex Data: Ecological datasets often contain numerous variables and data points. Visualization provides a means to simplify complex data structures and reveal patterns, trends, and relationships that might be hidden in raw numbers.
Quality Assessment: Visualization aids in identifying data quality issues, such as outliers, missing values, and anomalies. Visual cues can highlight problematic data points for further investigation.
Hypothesis Generation: Visual exploration of data can spark hypotheses and research questions. Researchers can form initial insights into ecological processes and phenomena, guiding subsequent analyses.
Effective Communication: Visual representations of data are powerful tools for communicating research findings to both scientific and non-scientific audiences. Clear and compelling visuals enhance the impact of ecological research.
Now, let’s delve into various aspects of data visualization, including univariate, bivariate, and multivariate visualization techniques, using the CO2 dataset in R.
Univariate visualization focuses on visualizing single variables to understand their distributions and characteristics. Here are some common techniques and interpretations:
# Load the CO2 dataset
data("CO2")
# Create a histogram of CO2 uptake
hist(CO2$uptake, main = "Histogram of CO2 Uptake", xlab = "CO2 Uptake")
R Code Explanation
data("CO2")
loads the built-in CO2
dataset into your R environment. This dataset contains measurements
related to the uptake of carbon dioxide (CO2) by different plants under
varying conditions.
hist(CO2$uptake, ...)
creates a
histogram of the “uptake” variable within the CO2 dataset.
Specifically:
CO2$uptake
extracts the “uptake”
column (variable) from the CO2 dataset, which represents the CO2 uptake
measurements.
hist(...)
is the function used to
create histograms in R.
main = "Histogram of CO2 Uptake"
specifies the main title of the histogram, which is displayed at the top
of the plot. In this case, it’s titled “Histogram of CO2
Uptake.”
xlab = "CO2 Uptake"
labels the
x-axis of the histogram, providing a description of what the x-axis
represents. Here, it indicates that the x-axis represents CO2
uptake.
This code, when executed, will load the CO2 dataset and then generate a histogram showing the distribution of CO2 uptake measurements. The histogram’s title will be “Histogram of CO2 Uptake,” and the x-axis will be labeled “CO2 Uptake,” making the plot informative and easy to understand.
# Create a density plot of CO2 uptake
plot(density(CO2$uptake), main = "Density Plot of CO2 Uptake", xlab = "CO2 Uptake")
R Code Explanation
plot(density(CO2$uptake), ...)
creates a density plot (also known as a kernel density plot) of the
“uptake” variable within the CO2 dataset. Specifically:
density(CO2$uptake)
calculates the
density estimate for the “uptake” variable, representing the
distribution of CO2 uptake measurements. This estimate is what the
density plot will be based on.
plot(...)
is used to create plots
in R.
main = "Density Plot of CO2 Uptake"
specifies the main title of the density plot, which is displayed at the
top of the plot. In this case, it’s titled “Density Plot of CO2
Uptake.”
xlab = "CO2 Uptake"
labels the
x-axis of the density plot, providing a description of what the x-axis
represents. Here, it indicates that the x-axis represents CO2
uptake.
When this code is executed, it will calculate the density estimate of CO2 uptake measurements and create a density plot to visualize the distribution. The main title will be “Density Plot of CO2 Uptake,” and the x-axis will be labeled “CO2 Uptake,” making the plot informative and easy to interpret.
# Create a box plot of CO2 uptake
boxplot(CO2$uptake, main = "Box Plot of CO2 Uptake", xlab = "CO2 Uptake")
R Code Explanation
boxplot(CO2$uptake, ...)
creates a
box plot of the “uptake” variable within the CO2 dataset.
Specifically:
CO2$uptake
specifies the variable to
be plotted, which is CO2 uptake in this case.main = "Box Plot of CO2 Uptake"
specifies the main title of the box plot, which is displayed at the top
of the plot. In this case, it’s titled “Box Plot of CO2
Uptake.”
xlab = "CO2 Uptake"
labels the
x-axis of the box plot, providing a description of what the x-axis
represents. Here, it indicates that the x-axis represents CO2
uptake.
When this code is executed, it will create a box plot of the CO2 uptake variable, allowing you to visualize the distribution of CO2 uptake measurements. The main title will be “Box Plot of CO2 Uptake,” and the x-axis will be labeled “CO2 Uptake,” making the plot informative and easy to interpret. Box plots are useful for visualizing the spread and central tendency of a dataset, as well as identifying potential outliers.
Bivariate visualization involves exploring relationships between two variables. Here are some techniques and their interpretations:
# Create a scatter plot of CO2 uptake vs. CO2 concentration
plot(CO2$conc,
$uptake,
CO2main = "Scatter Plot of CO2 Uptake vs. CO2 Concentration",
xlab = "CO2 Concentration",
ylab = "CO2 Uptake")
R Code Explanation
plot(CO2$conc, CO2$uptake, ...)
creates a scatter plot with CO2 concentration (x-axis) on one axis and
CO2 uptake (y-axis) on the other. Specifically:
CO2$conc
specifies the variable to
be plotted on the x-axis, which is CO2 concentration.
CO2$uptake
specifies the variable
to be plotted on the y-axis, which is CO2 uptake.
main = "Scatter Plot of CO2 Uptake vs. CO2 Concentration"
specifies the main title of the scatter plot. In this case, it’s titled
“Scatter Plot of CO2 Uptake vs. CO2 Concentration.”
xlab = "CO2 Concentration"
labels
the x-axis of the scatter plot, providing a description of what the
x-axis represents. Here, it indicates that the x-axis represents CO2
concentration.
ylab = "CO2 Uptake"
labels the
y-axis of the scatter plot, providing a description of what the y-axis
represents. Here, it indicates that the y-axis represents CO2
uptake.
When this code is executed, it will create a scatter plot that allows you to visualize the relationship between CO2 concentration and CO2 uptake. The main title will be “Scatter Plot of CO2 Uptake vs. CO2 Concentration,” and both the x-axis and y-axis will be appropriately labeled, making the plot informative and easy to interpret. Scatter plots are useful for identifying patterns and relationships between two continuous variables.
# Create a bar chart of Plant types
barplot(table(CO2$Type),
main = "Bar Chart of Plant Types",
xlab = "Type",
ylab = "Frequency")
R Code Explanation
barplot(table(CO2$Type), ...)
creates a bar chart of plant types based on the
CO2$Type
variable. Specifically:
table(CO2$Type)
computes a
frequency table of the plant types in the CO2 dataset. It counts how
many times each unique plant type appears.
barplot(...)
takes the frequency
table as input and generates a bar chart from it.
main = "Bar Chart of Plant Types"
specifies the main title of the bar chart. In this case, it’s titled
“Bar Chart of Plant Types.”
xlab = "Type"
labels the x-axis of
the bar chart, providing a description of what the x-axis represents.
Here, it indicates that the x-axis represents different plant
types.
ylab = "Frequency"
labels the
y-axis of the bar chart, providing a description of what the y-axis
represents. Here, it indicates that the y-axis represents the frequency
(count) of each plant type.
When this code is executed, it will create a bar chart that visually displays the frequency of each plant type in the CO2 dataset. The main title will be “Bar Chart of Plant Types,” and both the x-axis and y-axis will be appropriately labeled, making the chart informative and easy to interpret. Bar charts are useful for comparing categories or groups by showing the frequency or count of each category.
# Compute the correlation matrix
<- cor(CO2[, c("uptake", "conc")])
cor_matrix
# Create a correlation heatmap
heatmap(cor_matrix, main = "Correlation Heatmap")
R Code Explanation
heatmap(...)
generates a heatmap (a
graphical representation of data in which values are depicted as colors)
based on the correlation matrix provided as input. Here’s how it’s used
in this code:
cor_matrix
is the correlation
matrix we computed earlier, containing the correlation coefficients
between “uptake” and “conc.”
main = "Correlation Heatmap"
specifies the main title of the heatmap. In this case, it’s titled
“Correlation Heatmap.”
When this code is executed, it will create a heatmap that visually represents the correlations between the “uptake” and “conc” variables from the CO2 dataset. The heatmap’s colors and intensity will indicate the strength and direction of the correlations between these variables. It provides a quick and informative way to assess the relationships between variables in a dataset.
Multivariate visualization techniques allow researchers to analyze interactions among multiple variables. Here’s an example:
# Load the corrplot package for enhanced heatmap visualization
library(corrplot)
## corrplot 0.92 loaded
# Load data
data("iris")
# Compute the correlation matrix
<-
cor_matrix2 cor(iris[, c("Petal.Length", "Petal.Width", "Sepal.Length", "Sepal.Width")])
# Create a correlation heatmap for multiple variables
corrplot(cor_matrix2, method = "color", title = "Correlation Heatmap")
R Code Explanation
library(corrplot)
loads the
corrplot
package, which provides enhanced
capabilities for visualizing correlation matrices.
data("iris")
loads the famous
“iris” dataset, which contains measurements of sepal and petal length
and width for different species of iris flowers. This dataset is used
for the correlation analysis.
cor(...)
calculates the correlation
coefficients between variables. In this case, it calculates the
correlation coefficients between four variables: “Petal.Length,”
“Petal.Width,” “Sepal.Length,” and “Sepal.Width.” The resulting
cor_matrix2
is a 4x4 correlation matrix,
where each entry represents the correlation between two
variables.
corrplot(...)
from the
corrplot
package generates a correlation
heatmap based on the correlation matrix provided as input
(cor_matrix2
). Here’s how it’s used in
this code:
method = "color"
specifies the
method for displaying the correlations using colors. This method colors
the cells of the heatmap based on the correlation values.
title = "Correlation Heatmap"
sets
the title of the heatmap to “Correlation Heatmap.”
When this code is executed, it will create an enhanced correlation heatmap that visually represents the correlations between the specified variables (Petal.Length, Petal.Width, Sepal.Length, Sepal.Width) in the iris dataset. The colors and intensity in the heatmap indicate the strength and direction of the correlations between these variables. This visualization is helpful for understanding the relationships between multiple variables in a dataset.
In ecological research, these visualization techniques aid in understanding the data, generating hypotheses, and communicating findings effectively. They are essential tools for any ecologist seeking to explore and analyze ecological datasets.
Summary statistics are essential in ecological research for several reasons:
Data Summarization: They provide a concise summary of large datasets, making it easier to grasp the dataset’s characteristics.
Data Exploration: Summary statistics help ecologists understand the distribution, central tendency, and variability of ecological measurements.
Comparison: They enable researchers to compare different datasets or subsets within a dataset.
These measures describe the center or average of a dataset:
Mean: The mean, also known as the average, is calculated by summing all values in a dataset and dividing by the number of values. It’s appropriate for normally distributed data.
Median: The median is the middle value when data is sorted in ascending order. It’s robust to outliers and appropriate for skewed data.
Mode: The mode is the most frequent value(s) in a dataset. It’s suitable for categorical or discrete data.
Measures of variability quantify the spread or dispersion of data:
Variance: Variance measures how much each data point deviates from the mean. It’s calculated as the average of the squared differences between each data point and the mean.
Standard Deviation: The standard deviation is the square root of the variance. It provides a more interpretable measure of dispersion in the same units as the data.
Quantiles: Quantiles divide a dataset into equal portions. For instance, the median is the 50th percentile, dividing data into two equal halves. Quantiles can reveal data distribution and detect outliers.
Percentiles: Percentiles are specific quantiles that indicate the relative standing of a value within a dataset. For example, the 25th percentile is the value below which 25% of the data falls.
The following code chunk below provides summary of all important descriptive stats outlined above.
# Load necessary packages
library(skimr) # For data summary statistics
library(dplyr) # For data manipulation
library(flextable) # For creating formatted tables
library(elucidate) # For quick data visualization
# Define formatting properties of tables using flextable
::set_flextable_defaults(
flextablefont.size = 12,
# Set font size
theme_fun = "theme_apa",
# Apply APA-style theme
font.family = "times",
# Set font family
digits = 3,
# Number of decimal places
font.color = "#FFFFFF" # Font color (white)
)
# Display data properties for the CO2 dataset using skimr and create a flextable
%>% skimr::skim_without_charts() %>% flextable::flextable() CO2
skim_type | skim_variable | n_missing | complete_rate | factor.ordered | factor.n_unique | factor.top_counts | numeric.mean | numeric.sd | numeric.p0 | numeric.p25 | numeric.p50 | numeric.p75 | numeric.p100 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
factor | Plant | 0 | 1.00 | TRUE | 12 | Qn1: 7, Qn2: 7, Qn3: 7, Qc1: 7 | |||||||
factor | Type | 0 | 1.00 | FALSE | 2 | Que: 42, Mis: 42 | |||||||
factor | Treatment | 0 | 1.00 | FALSE | 2 | non: 42, chi: 42 | |||||||
numeric | conc | 0 | 1.00 | 435.00 | 295.92 | 95.00 | 175.00 | 350.00 | 675.00 | 1,000.00 | |||
numeric | uptake | 0 | 1.00 | 27.21 | 10.81 | 7.70 | 17.90 | 28.30 | 37.12 | 45.50 |
# For only one variable (e.g., 'conc' column) in the CO2 dataset
$conc %>% skimr::skim_without_charts() %>% flextable::flextable() CO2
skim_type | skim_variable | n_missing | complete_rate | numeric.mean | numeric.sd | numeric.p0 | numeric.p25 | numeric.p50 | numeric.p75 | numeric.p100 |
---|---|---|---|---|---|---|---|---|---|---|
numeric | data | 0 | 1.00 | 435.00 | 295.92 | 95.00 | 175.00 | 350.00 | 675.00 | 1,000.00 |
# Group data by a factor variable ('Type' column) and create flextables for selected columns
c(2, 4:5)] %>%
CO2[, ::group_by(Type) %>% # Group data by 'Type' column
dplyr::skim_without_charts() %>% # Calculate summary statistics
skimr::qflextable() # Create a flextable with APA-style formatting flextable
skim_type | skim_variable | Type | n_missing | complete_rate | numeric.mean | numeric.sd | numeric.p0 | numeric.p25 | numeric.p50 | numeric.p75 | numeric.p100 |
---|---|---|---|---|---|---|---|---|---|---|---|
numeric | conc | Quebec | 0 | 1.00 | 435.00 | 297.72 | 95.00 | 175.00 | 350.00 | 675.00 | 1,000.00 |
numeric | conc | Mississippi | 0 | 1.00 | 435.00 | 297.72 | 95.00 | 175.00 | 350.00 | 675.00 | 1,000.00 |
numeric | uptake | Quebec | 0 | 1.00 | 33.54 | 9.67 | 9.30 | 30.33 | 37.15 | 40.15 | 45.50 |
numeric | uptake | Mississippi | 0 | 1.00 | 20.88 | 7.82 | 7.70 | 13.87 | 19.30 | 28.05 | 35.50 |
# Quick plot/visual display of data for variables 'conc' and 'uptake'
%>% elucidate::plot_var_all(cols = c("conc", "uptake")) CO2
R Code Explanation
The code loads the necessary packages (skimr
,
dplyr
),
including elucidate
for quick data visualization.
Formatting properties for tables using flextable
are defined. These properties include font size, theme, font family,
number of decimal places, and font color, ensuring that all subsequent
flextables adhere to these formatting settings.
The CO2
dataset is summarized using
skimr::skim_without_charts()
, which
provides summary statistics without charts. The result is then formatted
into a table using
flextable::flextable()
.
To summarize a single variable (in this case, ‘conc’), the same process is repeated, but only the ‘conc’ column is selected for summary statistics.
The script groups the data by the ‘Type’ column (renamed from
‘Plant’) and calculates summary statistics for the selected columns
(columns 1, 4, and 5) within each group. The result is formatted into a
table using flextable::qflextable()
. This
demonstrates how to perform group-wise summaries and format the results
into an APA-style table.
Finally, a quick visual display of the data for the ‘conc’ and
‘uptake’ variables is generated using
elucidate::plot_var_all()
, providing a
convenient way to visualize these variables. Note that dashed lines on
the density plots are theoretical normal distribution curves.
These codes enhance the data summarization and visualization capabilities for the CO2 dataset, making it easier to analyze and present the data.
In ecology, summarizing data helps researchers understand ecological patterns, such as species abundance or plant growth, and assess biodiversity in an ecosystem.
Measures of central tendency are used to describe typical values within ecological datasets. For instance, the mean body size of a species or the median population density.
Measures of variability are crucial for assessing the heterogeneity of ecological data, like the spread of species across habitats.
Quantiles and percentiles can help ecologists identify critical thresholds, such as the 90th percentile of pollution levels in a river, which can indicate environmental stress.
Overall, these summary statistics provide ecologists with a toolbox for effectively summarizing, analyzing, and interpreting ecological data. They are fundamental for gaining insights into ecological phenomena and supporting evidence-based decisions in conservation and environmental management.
Outliers are data points that significantly differ from the majority of the data in a dataset. They are observations that are unusually high or low in value compared to the central tendency of the data. In ecological data analysis:
Outliers may represent rare events, such as extreme weather conditions or ecological disturbances.
They can indicate errors in data collection, data entry, or measurement.
Outliers can have a substantial impact on statistical analyses, potentially leading to biased results and incorrect conclusions.
Ecological processes are often complex, and outliers can be indicative of interesting and significant phenomena, such as invasive species or environmental stressors.
IQR (Interquartile Range) Method: The IQR is the range between the first quartile (Q1, 25th percentile) and the third quartile (Q3, 75th percentile) of the data. Outliers are defined as data points that fall below Q1 - 1.5 * IQR or above Q3 + 1.5 * IQR. This method is robust to extreme values and suitable for skewed distributions.
# Detect outliers using the IQR method
<- quantile(iris$Sepal.Width, 0.25)
Q1 <- quantile(iris$Sepal.Width, 0.75)
Q3 <- Q3 - Q1
IQR <- Q1 - 1.5 * IQR
lower_bound <- Q3 + 1.5 * IQR
upper_bound <-
iqr_outliers $Sepal.Width[iris$Sepal.Width < lower_bound |
iris$Sepal.Width > upper_bound]
irisprint(iqr_outliers)
## [1] 4.4 4.1 4.2 2.0
R Code Explanation
Q1 <- quantile(data, 0.25)
: This
line calculates the first quartile (Q1), which represents the 25th
percentile of the dataset data
. The
quantile()
function is used to compute
quartiles.
Q3 <- quantile(data, 0.75)
: This
line calculates the third quartile (Q3), which represents the 75th
percentile of the dataset.
IQR <- Q3 - Q1
: The
interquartile range (IQR) is calculated by subtracting Q1 from Q3. The
IQR measures the spread of the middle 50% of the data.
lower_bound <- Q1 - 1.5 * IQR
:
The lower bound for potential outliers is computed by subtracting 1.5
times the IQR from Q1. Any data point below this lower bound is
considered a potential outlier.
upper_bound <- Q3 + 1.5 * IQR
:
The upper bound for potential outliers is computed by adding 1.5 times
the IQR to Q3. Any data point above this upper bound is considered a
potential outlier.
outliers <- data[data < lower_bound | data > upper_bound]
:
In this line, potential outliers are identified. It selects data points
where the data values are less than the lower bound or greater than the
upper bound, as determined by the IQR method. These data points are
stored in the variable outliers
.
The IQR method is a robust technique for detecting outliers because it is less sensitive to extreme values compared to the Z-score method. It identifies potential outliers based on the spread of the central 50% of the data. In ecological data analysis, identifying and handling outliers is crucial for accurate statistical analyses and ecological interpretations.
# Detect outliers using Z-scores
<- mean(iris$Sepal.Width)
mean_val <- sd(iris$Sepal.Width)
std_dev <- (iris$Sepal.Width - mean_val) / std_dev
Z_scores <- iris$Sepal.Width[abs(Z_scores) > 2]
z_outliers print(z_outliers)
## [1] 4.0 4.4 4.1 4.2 2.0
R Code Explanation
mean_val <- mean(data)
: This
line calculates the mean (average) value of the dataset
data
. The
mean()
function computes the arithmetic
mean of a numeric vector.
std_dev <- sd(data)
: This line
calculates the standard deviation of the dataset
data
. The
sd()
function calculates the sample
standard deviation.
Z_scores <- (data - mean_val) / std_dev
:
Z-scores are calculated for each data point in the dataset. Z-scores
indicate how many standard deviations a data point is away from the
mean. A Z-score of 2 (or -2) is often used as a threshold to identify
potential outliers.
outliers <- data[abs(Z_scores) > 2]
:
In this line, potential outliers are identified. It selects data points
where the absolute value of the Z-score
(abs(Z_scores)
) is greater than 2. These
data points are considered potential outliers and are stored in the
variable outliers
.
The Z-score method is a common technique for detecting outliers. By calculating the Z-scores for each data point and comparing them to a threshold (in this case, 2), you can identify data points that deviate significantly from the mean. These identified data points are often flagged as potential outliers.
In ecological data analysis, identifying outliers is essential as they can skew statistical analyses and affect the accuracy of ecological interpretations.
Box plots provide a visual way to detect outliers by displaying the distribution of data and highlighting potential outliers. In a box plot:
Data points below Q1 - 1.5 * IQR or above Q3 + 1.5 * IQR are typically marked as individual points, allowing you to identify them easily.
Box plots provide a quick overview of the spread of data and help identify skewness or asymmetry in the distribution.
# Create a box plot to visualize potential outliers
boxplot(iris$Sepal.Width, main = "Box Plot with Outliers")
R Code Explanation
boxplot(data, main = "Box Plot with Outliers")
:
This line of code generates a box plot of the data stored in the
variable data
. The
boxplot()
function is used for creating
box plots in R.
data
: This should be replaced with
the actual name of the dataset you want to visualize for potential
outliers.
main = "Box Plot with Outliers"
:
This part of the code specifies the title or main title of the box plot.
In this case, the title is set to “Box Plot with Outliers” to provide
context for the plot.
The resulting box plot will display the distribution of the data and highlight any potential outliers. In a box plot:
The box represents the interquartile range (IQR), which contains the middle 50% of the data.
The line inside the box represents the median (the middle value when the data is sorted).
“Whiskers” extend from the box to the minimum and maximum values within a defined range (usually 1.5 times the IQR).
Data points beyond the whiskers are considered potential outliers and are typically displayed as individual points.
This visualization allows you to quickly identify any data points that fall outside the “whiskers,” indicating that they may be outliers. It provides a visual summary of the data’s spread and helps you assess the distribution’s symmetry and skewness.
Box plots are valuable for identifying and visualizing potential outliers, which can have a significant impact on the results of statistical analyses and ecological interpretations.
Visual inspection of box plots is an intuitive way to identify outliers, especially when dealing with smaller datasets. It provides a qualitative assessment of data distribution and potential anomalies.
In ecological data analysis, detecting outliers is critical to ensure the integrity and accuracy of analyses. Addressing outliers appropriately, whether by excluding them or using robust statistical methods, is essential to avoid bias and ensure the validity of ecological research findings.
Exploratory Data Analysis (EDA) is a fundamental step in ecological research, providing essential insights into your datasets:
Importance of EDA: EDA is the process of visually and statistically exploring your data to understand its characteristics. It helps uncover patterns, relationships, and potential outliers in your ecological datasets.
Data Visualization: EDA relies heavily on data visualization techniques. You learned how to create various types of plots, including histograms, density plots, box plots, scatter plots, bar charts, and correlation heatmaps.
Univariate Visualization: You can explore single variables using histograms, density plots, and box plots. These visualizations provide a sense of the data’s distribution, central tendency, and variability.
Bivariate Visualization: To understand relationships between two variables, scatter plots, bar charts, and correlation plots are used. These visualizations help identify patterns, associations, and potential dependencies.
Multivariate Visualization: Exploring interactions among multiple variables is crucial in ecological research. Techniques like heatmaps, stacked bar charts, and parallel coordinate plots reveal complex relationships and dependencies within ecological datasets.
Summary Statistics: Beyond visualization, summary statistics like mean, median, mode, variance, and standard deviation provide numerical insights into the central tendency and variability of your data.
Outlier Detection: Identifying and handling outliers is an integral part of EDA. Techniques like the IQR method, Z-scores, and visual inspection of box plots help detect and address potential outliers.
In conclusion, EDA is a foundational step in ecological research. By conducting thorough exploratory data analysis, you gain a deep understanding of your ecological datasets. This knowledge empowers you to make informed decisions about subsequent analyses, hypothesis testing, and research directions. EDA is a powerful tool for uncovering the hidden stories within your ecological data.
Chapter 4 delves into the core of statistical data analysis for ecological research. You will gain a comprehensive understanding of statistical hypothesis testing and learn to perform a variety of tests commonly used in ecology. By the end of this chapter, you will have:
Acquired knowledge of fundamental statistical concepts.
Explored various statistical tests relevant to ecological research.
Gained hands-on experience in conducting these tests using R and Jamovi.
In ecological research, hypothesis testing plays a crucial role in making data-driven decisions and drawing valid conclusions from data. It allows researchers to systematically evaluate whether there is enough evidence to support a particular claim or hypothesis about ecological phenomena. Hypothesis testing helps distinguish between random variation in data and meaningful patterns or effects.
Null Hypothesis (H0): The null hypothesis is a statement that suggests there is no significant effect, relationship, or difference between groups or variables in the population being studied. It serves as a default assumption or starting point for hypothesis testing.
Alternative Hypothesis (Ha): The alternative hypothesis is a statement that contradicts the null hypothesis. It suggests that there is a significant effect, relationship, or difference in the population. Researchers typically design experiments or analyses with the hope of finding evidence to support the alternative hypothesis.
The significance level, denoted as alpha (α), is a critical parameter in hypothesis testing. It represents the threshold for determining statistical significance. In other words, it sets the standard for how strong the evidence must be to reject the null hypothesis.
Commonly used alpha values include 0.05 (5%) and 0.01 (1%). A significance level of 0.05 means that the researcher is willing to accept a 5% chance of making a Type I error (rejecting the null hypothesis when it’s true). A lower alpha (e.g., 0.01) requires stronger evidence to reject the null hypothesis but increases the risk of Type II errors (failing to reject the null hypothesis when it’s false). The choice of alpha depends on the research question, the consequences of Type I and Type II errors, and prevailing scientific standards.
Understanding these fundamental concepts of hypothesis testing is essential for conducting meaningful ecological research and making valid inferences from data. Researchers design experiments, collect data, and perform statistical tests with the aim of either supporting the alternative hypothesis or failing to reject the null hypothesis, based on the evidence provided by the data. The significance level alpha serves as a critical tool for controlling the balance between making Type I and Type II errors, ensuring that research findings are robust and reliable.
Parametric Tests: Parametric tests are statistical tests that make specific assumptions about the population distribution, such as normality and homogeneity of variances. These tests rely on the estimation of population parameters (e.g., means and variances) and often provide more statistical power when the assumptions are met.
Non-Parametric Tests: Non-parametric tests are statistical tests that do not rely on assumptions about the population distribution. They are distribution-free tests that use ranking and order statistics to make inferences about the population. Non-parametric tests are robust to violations of distributional assumptions.
Parametric tests are appropriate when data meet the assumptions of normality and homogeneity of variances. They are more powerful than non-parametric tests when these assumptions are met.
Non-parametric tests are suitable when data do not meet the assumptions of normality and homogeneity of variances or when dealing with ordinal or categorical data. They are also preferred when researchers want to make minimal distributional assumptions.
T-Tests: T-tests are used to compare the means of two groups or conditions. For example, in ecology, a t-test can be used to compare the mean tree height between two different treatment groups.
ANOVA (Analysis of Variance): ANOVA is used to compare the means of three or more groups or conditions. In ecology, it can be applied to compare the mean biomass across multiple vegetation types.
Linear Regression: Linear regression is used to model the relationship between a dependent variable and one or more independent variables. Ecological examples include modeling the relationship between temperature and species diversity.
Mann-Whitney U Test: The Mann-Whitney U test compares the distributions of two independent groups when the assumptions for a t-test are not met. For example, it can be used to compare the abundance of a species in two different habitats.
Kruskal-Wallis Test: The Kruskal-Wallis test extends the Mann-Whitney U test to three or more independent groups. It is used when comparing medians across multiple groups, such as testing the effect of different soil types on plant growth.
Understanding when to use parametric and non-parametric tests is crucial for ecological research. Parametric tests are powerful when assumptions are met, while non-parametric tests provide robust alternatives when assumptions are violated or when dealing with non-normally distributed data. The choice between these two types of tests should be based on the nature of the data and the specific research question at hand.
R: R is a versatile and powerful statistical programming language. It offers a wide range of packages and libraries specifically tailored for ecological data analysis. R provides the flexibility to perform basic to advanced statistical tests, hypothesis testing, regression analysis, multivariate analysis, spatial analysis, and more. Its extensive graphical capabilities also enable the creation of informative data visualizations, which are crucial for ecological research.
Jamovi: Jamovi is a user-friendly statistical software that simplifies data analysis. It is particularly suitable for beginners in ecological research due to its intuitive graphical interface and point-and-click functionality. Jamovi seamlessly integrates with R, allowing users to transition from simple analyses in Jamovi to more complex statistical tests in R as they gain proficiency. Jamovi’s ecosystem includes a range of statistical tests commonly used in ecological research.
Versatility: Both R and Jamovi offer a wide array of statistical tests commonly used in ecological research. Researchers can perform t-tests, ANOVA, regression analysis, non-parametric tests, and advanced multivariate analyses using these tools.
Flexibility: R, in particular, provides unlimited flexibility. Users can customize analyses, create bespoke statistical models, and develop complex ecological workflows to suit their research needs.
Visualization: Both R and Jamovi excel in data visualization. Researchers can create publication-quality graphs, plots, and charts to present their ecological findings effectively.
Integration: Jamovi’s integration with R is a valuable feature. Users can start with simple analyses in Jamovi and gradually transition to more advanced analyses in R as their skills grow.
Community Support: R benefits from a large and active user community. Researchers can find extensive resources, tutorials, and forums to seek help and share knowledge. Jamovi also has a growing community and offers user support.
Open Source: Both R and Jamovi are open-source software, making them accessible and cost-effective tools for ecological research.
Reproducibility: Using R or Jamovi for data analysis enhances the reproducibility of ecological research. Researchers can document their analyses, share code, and ensure transparency in their work.
Teaching and Learning: Jamovi’s user-friendly interface makes it an excellent tool for teaching ecological data analysis to students and beginners. R, with its extensive capabilities, serves as a powerful teaching tool for advanced statistical concepts.
In summary, R and Jamovi offer a robust and accessible environment for ecological data analysis. They empower researchers, from beginners to experts, to conduct a wide range of statistical tests, explore data visually, and enhance the rigor and reproducibility of ecological research.
Set Up Your Environment and perform t-test
First do normality test to decide whether to use a parametric or non-parametric test.
# Load necessary libraries (if not already loaded)
library(tidyverse) # Loads the tidyverse package for data manipulation and visualization.
library(janitor) # Loads the janitor package for data cleaning.
library(report) # Load the report package, for generating summary reports.
# Load the InsectSprays dataset
data("InsectSprays")
# Perform the Shapiro-Wilk normality test on the 'count' variable
<- stats::shapiro.test(InsectSprays$count)
shapiro_test_result
# View the normality test result
print(shapiro_test_result)
##
## Shapiro-Wilk normality test
##
## data: InsectSprays$count
## W = 0.9216, p-value = 0.0002525
# create a function to interpret the result
if (shapiro_test_result$p.value < 0.05) {
cat(
"The data is not normally distributed (p < 0.05). Select a non-parametric counterpart test.\n"
)else {
} cat("The data is normally distributed (p >= 0.05). Proceed with parametric test.\n")
}
## The data is not normally distributed (p < 0.05). Select a non-parametric counterpart test.
R Code Explanation
This code loads necessary libraries, loads the
InsectSprays
dataset, performs the
Shapiro-Wilk normality test on the count
variable, and prints the test result. The interpretation is provided
using a function based on the p-value, indicating whether the data is
normally distributed or not, and suggesting whether to proceed with a
parametric or non-parametric test accordingly.
# Load necessary libraries (if not already loaded)
library(tidyverse) # Loads the tidyverse package for data manipulation and visualization.
library(janitor) # Loads the janitor package for data cleaning.
library(report) # Load the report package, for generating summary reports.
# Use the InsectSprays data to test for the effectiveness of Insect Sprays.The dataset contains counts of insects in agricultural experimental units treated with different insecticides.
data("InsectSprays")
# Subset the dataset to use only two types of insecticides (spray A and spray B). The dplyr::filter() function is used to filter rows where spray is either "A" or "B".
<- InsectSprays %>% dplyr::filter(spray %in% c("A", "B"))
insectides # Perform the Mann-Whitney U Test on the 'insectides' dataset
<-
mann_whitney_result ::wilcox.test(count ~ spray, data = insectides, alternative = "two.sided")
stats
# View the Mann-Whitney U Test result
print(mann_whitney_result)
##
## Wilcoxon rank sum test with continuity correction
##
## data: count by spray
## W = 62, p-value = 0.5812
## alternative hypothesis: true location shift is not equal to 0
# create a function to interpret the result
if (mann_whitney_result$p.value < 0.05) {
cat("There is a significant difference between spray 'A' and spray 'B' (p < 0.05).\n")
else {
} cat("There is no significant difference between spray 'A' and spray 'B' (p >= 0.05).\n")
}
## There is no significant difference between spray 'A' and spray 'B' (p >= 0.05).
R Code Explanation
Loading Necessary Libraries: The code begins by
loading several R packages using the
library()
function. Each package serves a
specific purpose in the analysis:
tidyverse
: This package is loaded
for data manipulation and visualization. The “tidyverse” collection
includes a set of packages that make data analysis and visualization
more efficient and consistent.
janitor
: The “janitor” package is
loaded for data cleaning tasks. It provides functions for cleaning and
tidying data, which is an essential step in data analysis.
report
: The “report” package is
loaded to facilitate the generation of summary reports based on
statistical analysis results. It automates the report creation
process.
Loading the InsectSprays Dataset: The code loads
the “InsectSprays” dataset using the
data()
function. This dataset contains
information about counts of insects in agricultural experimental units
treated with different insecticides. It’s a common dataset used for
statistical testing and analysis.
Subsetting the Dataset: The
insectides
variable is created by
subsetting the original dataset. It selects only the rows where the
“spray” column has values “A” or “B.” This subset of data will be used
for the Mann-Whitney U Test, focusing on comparing the effectiveness of
these two insecticide sprays.
Performing the Mann-Whitney U Test: The
Mann-Whitney U Test is conducted using the
wilcox.test()
function. It assesses
whether there is a significant difference in the distribution of insect
counts between spray “A” and spray “B.” The
count ~ spray
formula specifies that the
“count” variable is being compared across the different “spray”
groups.
Viewing the Test Result: The result of the
Mann-Whitney U Test is printed to the console using the
print()
function. This result includes
statistics such as the U statistic and the p-value, which are crucial
for interpreting the test outcome.
Interpreting the Result: A conditional statement is used to interpret the test result. If the p-value is less than 0.05 (typically chosen as the significance level), it suggests that there is a significant difference between spray “A” and spray “B” regarding their effectiveness in controlling insects. If the p-value is greater than or equal to 0.05, it suggests that there is no significant difference between the two sprays.
In summary, this code demonstrates how to perform and interpret a Mann-Whitney U Test using R. It focuses on comparing the effectiveness of two insecticide sprays (“A” and “B”) in controlling insect populations based on count data. The “report” package is used to facilitate report generation, which can be helpful for documenting and communicating the results of statistical tests.
p >= 0.05
)# Load necessary libraries (if not already loaded)
library(tidyverse) # Loads the tidyverse package for data manipulation and visualization.
library(janitor) # Loads the janitor package for data cleaning.
library(report) # Load the report package, for generating summary reports.
# Use the InsectSprays data to test for the effectiveness of Insect Sprays.The dataset contains counts of insects in agricultural experimental units treated with different insecticides.
data("InsectSprays")
# Subset the dataset to use only two types of insecticides (spray A and spray B). The dplyr::filter() function is used to filter rows where spray is either "A" or "B".
<- InsectSprays %>% dplyr::filter(spray %in% c("A", "B"))
insectides
# Assuming you want to compare two groups (spray A and spray B).
# Perform a t-Test for independent samples using the stats::t.test() function.
# The formula count ~ spray specifies that you want to compare the 'count' variable across different 'spray' groups.
# 'data = insectides' specifies the dataset to use.
<- stats::t.test(count ~ spray, data = insectides)
t_test_result
# View the t-test result using the print() function.
%>% print() t_test_result
##
## Welch Two Sample t-test
##
## data: count by spray
## t = -0.45352, df = 21.784, p-value = 0.6547
## alternative hypothesis: true difference in means between group A and group B is not equal to 0
## 95 percent confidence interval:
## -4.646182 2.979515
## sample estimates:
## mean in group A mean in group B
## 14.50000 15.33333
# autogenerate a report. Ingnore the warning.
%>% report::report() t_test_result
## Effect sizes were labelled following Cohen's (1988) recommendations.
##
## The Welch Two Sample t-test testing the difference of count by spray (mean in
## group A = 14.50, mean in group B = 15.33) suggests that the effect is negative,
## statistically not significant, and very small (difference = -0.83, 95% CI
## [-4.65, 2.98], t(21.78) = -0.45, p = 0.655; Cohen's d = -0.19, 95% CI [-1.03,
## 0.65])
R Code Explanation
Libraries are loaded to make the necessary functions available
for data manipulation (tidyverse
)
and cleaning (janitor
).
The InsectSprays
dataset is loaded,
which contains information about the effectiveness of various insect
sprays in controlling insect populations.
The dataset is subsetted to include only two types of
insecticides, “A” and “B,” using the
dplyr::filter()
function.
The t-test is performed using
stats::t.test()
. It compares the
‘count
’ of insects between the two groups
defined by ‘spray
’ (A and B).
The t-test result is stored in the variable
‘t_test_result
.’
The t-test result is printed to the console using the
print()
function.
Finally, the script generates an automatic report using the
report::report()
function, providing a
summary of the t-test results.
This script helps you assess whether there is a significant difference in the effectiveness of insect sprays A and B in controlling insect populations. The t-test compares the means of the ‘count’ variable between the two groups and provides information about the statistical significance of any observed differences.
Check the p-value in the t-test result. If p < 0.05 (assuming a significance level of 0.05), you can reject the null hypothesis (H0) and conclude that there is a significant difference between the groups.
Below are other tests conducted in R.
One-Way ANOVA (parametric)
# Load necessary libraries (if not already loaded)
library(tidyverse)
# Load the InsectSprays dataset
data("InsectSprays")
# Subset the dataset to use only two types of insecticides (spray A and spray B)
<-
insecticides %>% dplyr::filter(spray %in% c("A", "B"))
InsectSprays
# Perform a one-way ANOVA
<- stats::aov(count ~ spray, data = insecticides)
anova_result
# View the ANOVA result
summary(anova_result)
## Df Sum Sq Mean Sq F value Pr(>F)
## spray 1 4.2 4.167 0.206 0.655
## Residuals 22 445.7 20.258
Two-Way ANOVA (parametric)
# Perform a two-way ANOVA
<-
two_way_anova_result ::aov(count ~ spray, data = InsectSprays)
stats
# View the two-way ANOVA result
summary(two_way_anova_result)
## Df Sum Sq Mean Sq F value Pr(>F)
## spray 5 2669 533.8 34.7 <2e-16 ***
## Residuals 66 1015 15.4
## ---
## Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1
Kruskal-Wallis Test (non-parametric)
# Load necessary libraries (if not already loaded)
library(tidyverse)
# Perform a Kruskal-Wallis test
<-
kruskal_wallis_result ::kruskal.test(count ~ spray, data = InsectSprays)
stats
# View the Kruskal-Wallis test result
kruskal_wallis_result
##
## Kruskal-Wallis rank sum test
##
## data: count by spray
## Kruskal-Wallis chi-squared = 54.691, df = 5, p-value = 1.511e-10
Post-Hoc Pairwise Comparison Test
To perform a post hoc test with Bonferroni correction using the Agricolae R package on the InsectSprays dataset, you can follow these steps:
Install and load the Agricolae package (if not already installed).
Perform a Kruskal-Wallis test on the dataset.
Conduct a post hoc test with Bonferroni correction to compare groups.
Here’s the R code to achieve this:
# Install and load the required packages
# We use 'pacman' to install and load packages in a single step.
# If not already installed, 'pacman' will install the packages.
# 'agricolae' for conducting Kruskal-Wallis tests and post hoc analysis.
# 'install = TRUE' specifies to install the packages if not present.
# 'update = FALSE' prevents updating existing packages.
::p_load(agricolae, install = TRUE, update = FALSE)
pacman
# Load the InsectSprays dataset
# The 'data()' function loads the InsectSprays dataset, which contains insect count data.
data("InsectSprays")
# Perform Kruskal-Wallis test without grouping
# 'agricolae::kruskal()' conducts the Kruskal-Wallis test.
# We specify the 'count' variable as the dependent variable and 'spray' as the independent variable.
# 'group = FALSE' indicates that we don't want to group the results.
# 'p.adj = "bon"' specifies Bonferroni correction for post hoc tests.
<- with(InsectSprays,
comparison_stats ::kruskal(count, spray,
agricolaegroup = FALSE,
p.adj = "bon"))
# Display selected statistical results
# We extract specific results from the 'comparison_stats' object.
# In this case, we're interested in columns 1, 2, and 4.
c(1:2, 4)] comparison_stats[
## $statistics
## Chisq Df p.chisq t.value MSD
## 54.69134 5 1.510845e-10 3.045792 12.91015
##
## $parameters
## test p.ajusted name.t ntr alpha
## Kruskal-Wallis bonferroni spray 6 0.05
##
## $comparison
## Difference pvalue Signif. LCL UCL
## A - B -2.6666667 1.0000 -15.576816 10.243483
## A - C 40.7083333 0.0000 *** 27.798184 53.618483
## A - D 26.5833333 0.0000 *** 13.673184 39.493483
## A - E 32.8333333 0.0000 *** 19.923184 45.743483
## A - F -3.4583333 1.0000 -16.368483 9.451816
## B - C 43.3750000 0.0000 *** 30.464851 56.285149
## B - D 29.2500000 0.0000 *** 16.339851 42.160149
## B - E 35.5000000 0.0000 *** 22.589851 48.410149
## B - F -0.7916667 1.0000 -13.701816 12.118483
## C - D -14.1250000 0.0212 * -27.035149 -1.214851
## C - E -7.8750000 1.0000 -20.785149 5.035149
## C - F -44.1666667 0.0000 *** -57.076816 -31.256517
## D - E 6.2500000 1.0000 -6.660149 19.160149
## D - F -30.0416667 0.0000 *** -42.951816 -17.131517
## E - F -36.2916667 0.0000 *** -49.201816 -23.381517
# Perform Kruskal-Wallis test with grouping
# This time, we set 'group = TRUE' to group the results for plotting.
<- with(InsectSprays,
comparison_grp ::kruskal(count, spray,
agricolaegroup = TRUE,
p.adj = "bon"))
# Plot group comparison
# 'agricolae::plot.group()' is used to create a bar chart of group comparisons.
# 'variation = "SE"' specifies to display standard errors.
# 'decreasing = TRUE' orders the bars in descending order of means.
# 'main = "Insecticide Sprays"' sets the chart's title.
::plot.group(
agricolae
comparison_grp,variation = "SD",
decreasing = TRUE,
main = "Comparing Effect of \nInsecticide Sprays",
xlab = "Sprays",
ylab = "Insect Count"
)
R Code Explanation
The code begins by installing and loading the necessary R
packages using the ‘pacman
’ package
manager.
The ‘InsectSprays
’ dataset is
loaded using the ‘data()’ function. This dataset contains insect count
data.
Two Kruskal-Wallis tests are performed, one without grouping and
one with grouping. The
‘agricolae::kruskal()
’ function is used
for this purpose.
Bonferroni correction
(‘p.adj = "bon"
’) is applied to adjust
p-values in post hoc tests.
Selected statistical results are displayed for the first Kruskal-Wallis test.
A bar chart of group comparisons is created for the second
Kruskal-Wallis test using
‘agricolae::plot.group()
’. This chart
displays standard errors, orders bars by decreasing means, and sets the
title.
Overall, this code demonstrates the use of the ‘agricolae
’
package for Kruskal-Wallis tests and post hoc analysis, along with
visualizing group comparisons.
Step 1: Set Up Your Environment
Open Jamovi and load your ecological dataset. We’ll use the same
dataset “InsectSprays
”. First in R, save
this data as a flat csv file to your data directory. Here the dataset in
called “insecticide
”.
# Load the readr package
# Load the readr package
library(readr)
# Load the here package for managing file paths
library(here)
# Write the InsectSprays dataset to a CSV file
# Specify the dataset to be written (InsectSprays)
# Specify the file path where the CSV file will be saved (./docs/data/insecticide.csv)
# Specify that column names should be included in the CSV file (col_names = TRUE)
::write_csv(
readr
InsectSprays,# Dataset to be written
file = here::here("docs", "data", "insecticide.csv"),
# File path and name
col_names = TRUE,
# Include column names in the CSV file
append = FALSE # Don't append to an existing file, create a new one
)
R Code Explanation
This section of the code is responsible for writing the
InsectSprays
dataset to a CSV
file.
readr::write_csv()
is used to write
the CSV file. Here’s what each argument does:
InsectSprays
: The first argument is
the dataset you want to write to the CSV file, in this case, it’s the
InsectSprays
dataset.
file
: This argument specifies the
file path and name for the CSV file. The
here::here()
function is used to create a
file path that is relative to the project’s root directory. It specifies
that the file should be saved in the “docs/data” directory with the name
“insecticide.csv.”
col_names
: This argument specifies
whether column names should be included in the CSV file. Setting it to
TRUE
means that the first row of the CSV
file will contain the column names.
append = FALSE
ensures that if a
file with the same name already exists at the specified path, it won’t
be appended to. Instead, a new file will be created, potentially
overwriting the existing one.
In summary, this code loads the necessary packages, specifies the dataset to be written, defines the file path and name, specifies that column names should be included in the CSV file, and ensures that a new CSV file is created at the specified location.
Step 2: Perform the t-Test, Mann-Whitney, One-Way and Two-Way Anova; and Kruskal-Wallis tests.
Open the file in Jamovi.
Remove unnecessary columns/ variables
Append new columns to the original dataset. Note that we would need these variables for the t-test, mann-whitney and one-way anova tests. These tests require the data to have a grouping variable with 2 levels. Other variables with > 2 variables can used in a two-way anova etc.
Add two new columns and named as “count2
” and
“spray2
”. change their measure types for count2 as
“continuous
” and spray2 as “nominal
”. Measure/
data types should be the same as the original variables (i.e.,
“count
” and “spray
”).
Click on “Analyses” in the top menu.
Select “T-Tests”.
Choose “Independent Samples T-Test” if comparing two groups or “One Sample T-Test” if comparing against a fixed value.
Drag and drop your ecological variable of interest into the “Test Variables” box.
Drag and drop your grouping variable into the “Grouping Variable” box (for independent samples t-test).
Customize options and click “OK.”
Now perform the one-way anova test.
Selected appropriate statistics to appear in the results.
Do the same for the two-way anova. Use the original variables with > 2 spray levels. You can perform a post-hoc comparison if anova test is significant (p < 0.05). Note that our data as previously diagnosed does not conform to the normality assumption hence a non-parametric counterpart test in advisable.
Next, perform Kruskal-Wallis test. Notice normality test is p < 0.05 from the two-way anova test. Notice p < 0.05 so a further pairwise comparison is appropriate.
Step 3: Interpret the Results
Interpreting the results of statistical tests is a critical aspect of ecological research. Here’s a general guideline on how to interpret the results, with a focus on understanding p-values and effect sizes:
Understand the Null Hypothesis (H0) and Alternative Hypothesis (Ha): Before interpreting the results, it’s essential to recall the null hypothesis (H0) and alternative hypothesis (Ha) that you formulated for your test. The null hypothesis typically represents the absence of an effect or relationship, while the alternative hypothesis states the expected outcome.
Examine the Test Statistic: Most statistical tests generate a test statistic (e.g., t-statistic, F-statistic, chi-square statistic) that quantifies the difference or relationship observed in the data. Larger test statistics often indicate stronger evidence against the null hypothesis.
Check the p-value: The p-value measures the strength of evidence against the null hypothesis. It represents the probability of obtaining results as extreme as, or more extreme than, the observed results if the null hypothesis is true. A small p-value (typically less than the chosen significance level, alpha) suggests strong evidence against the null hypothesis. Conversely, a large p-value suggests weak evidence against it.
Interpretation of p-values:
p < alpha (e.g., p < 0.05): Strong evidence against H0; you may reject the null hypothesis.
p >= alpha: Weak evidence against H0; you fail to reject the null hypothesis.
Consider the Effect Size: While p-values tell you whether there is a significant difference or relationship, effect sizes provide information about the practical or clinical significance of the result. Effect sizes quantify the strength or magnitude of the observed effect. In ecological research, understanding the biological or ecological significance of an effect is often more important than its statistical significance.
Look at Confidence Intervals: Confidence intervals provide a range of values within which the true population parameter (e.g., mean, proportion) is likely to fall. They complement p-values and offer additional insights into the precision of your estimates.
Consider Ecological Relevance: In ecological research, it’s crucial to consider whether the results have practical significance. Statistical significance may not always translate to ecological significance. Evaluate the results in the context of your research question and the potential impact on the ecosystem or species you are studying.
Replication and Consistency: Consider whether the results are consistent with previous research or if they need to be replicated in other studies or under different conditions to strengthen their validity.
Beware of Multiple Comparisons: If you are conducting multiple tests on the same dataset, be cautious about the issue of multiple comparisons. Adjusting alpha (e.g., Bonferroni correction) can help control the family-wise error rate.
Consult Experts: If you are unsure about the interpretation of your results, consider seeking guidance from statistical or ecological experts. Collaborating with colleagues who have expertise in the field can enhance the quality of your interpretation.
This is a general overview of performing a t-test, Mann-Whitney u test, anova and Kruskall-Wallis tests in both R and Jamovi. The specific steps may vary depending on your dataset and research question. In ecological research, it’s not only important to detect statistically significant results but also to understand their ecological implications. A strong understanding of p-values, effect sizes, and their ecological relevance will contribute to more meaningful and robust ecological research outcomes.
Chapter 4 provides comprehensive insights into statistical hypothesis testing, which is a fundamental aspect of ecological research.
You have learned about the significance of hypothesis testing in ecological research, where it helps you make data-driven decisions and draw conclusions about ecological phenomena.
Key terms like null hypothesis (H0), alternative hypothesis (Ha), and significance level (alpha) have been defined and their roles in hypothesis testing explained.
You now understand the distinction between parametric and non-parametric tests, as well as when to use each type based on data characteristics.
Parametric tests such as t-tests, ANOVA, and linear regression have been introduced, along with practical ecological examples for each.
Non-parametric tests like Mann-Whitney U and Kruskal-Wallis have also been explained, along with ecological examples.
You’ve gained practical skills through step-by-step instructions for performing these tests in both R and Jamovi.
The importance of interpreting results, understanding p-values and effect sizes, and considering ecological relevance has been emphasized.
Overall, Chapter 4 equips you with a strong foundation in statistical hypothesis testing, empowering you to conduct a wide range of tests essential for ecological data analysis and make informed ecological conclusions.
Chapter 5 is a deep dive into regression analysis, a powerful tool for modeling ecological relationships. In this chapter, you will learn about two essential types of regression: linear and logistic. By the end of this chapter, you will have:
A solid understanding of regression analysis and its relevance in ecological research.
Proficiency in performing linear and logistic regression in both R and Jamovi.
The ability to interpret regression outputs and draw meaningful ecological insights.
Regression analysis is a powerful statistical method used to model relationships between variables. It helps us understand how one or more independent variables are related to a dependent variable and how changes in the independent variables impact the dependent variable. In ecological research, regression analysis plays a crucial role in modeling ecological relationships, making predictions, and understanding the impact of environmental factors on biological phenomena.
Key Concepts:
Dependent Variable (Response Variable): This is the variable we want to predict or explain. In ecological research, it could be the population of a species, the growth rate of a plant, or any other measurable ecological outcome.
Independent Variables (Predictors or Explanatory Variables): These are the variables that we believe influence or explain changes in the dependent variable. Independent variables can be continuous (e.g., temperature, rainfall) or categorical (e.g., habitat type, presence/absence of a predator).
Regression Equation: The mathematical formula that represents the relationship between the dependent and independent variables. It allows us to make predictions based on the values of the independent variables.
Types of Regression: There are different types of regression analysis, including linear regression (for continuous dependent variables), logistic regression (for binary outcomes), and more complex forms like polynomial regression and mixed-effects models.
Applications in Ecological Research
Species-Habitat Relationships: Ecologists often use regression analysis to model how the abundance or presence of a species is related to habitat variables such as vegetation type, temperature, or elevation.
Climate Change Impact: Regression models can help assess the impact of climate change variables (e.g., temperature, precipitation) on ecological systems, predicting how ecosystems may respond to future climate scenarios.
Population Dynamics: Ecological researchers use regression to model population growth, decline, or other changes over time. For example, how does temperature affect the growth rate of a plant species?
Community Ecology: Regression can be applied to understand the relationships between species richness, diversity, and various environmental factors, shedding light on the mechanisms driving community structure.
Ecosystem Functioning: Researchers explore how changes in ecological variables (e.g., nutrient availability) impact ecosystem functions (e.g., carbon cycling) using regression modeling.
Regression analysis is a fundamental tool in ecological research that allows researchers to quantify and understand the relationships between ecological variables. It helps in making predictions, testing hypotheses, and gaining insights into the complex dynamics of ecological systems.
Definition: Linear regression is a statistical method used to model the relationship between a dependent variable (DV) and one or more independent variables (IVs) by fitting a linear equation to observed data. It assumes a linear relationship between the IVs and the DV, where changes in the IVs lead to a proportional change in the DV.
Species Abundance: Linear regression can be used to understand how environmental factors like temperature, precipitation, or habitat type influence the abundance of a particular species.
Growth Rates: Ecologists often use linear regression to model the growth rates of plants or animal populations as a function of variables like temperature or nutrient availability.
Biodiversity: Researchers can examine how habitat diversity, fragmentation, or disturbance affect species richness using linear regression.
Carbon Sequestration: Linear regression can be applied to study the relationship between forest characteristics (e.g., tree density, age) and carbon sequestration rates in ecosystems.
Load Required Packages: Begin by loading
necessary packages like tidyverse
for data
manipulation and lm()
for linear
modeling.
Load Data: Import your ecological dataset into R.
Fit the Model: Use the
lm()
function to fit a linear regression
model. For example:
model <- lm(DV ~ IV1 + IV2, data = dataset)
,
where DV
is the dependent variable,
IV1
and IV2
are independent variables, and dataset
is
your data.
View Model Summary: Use
summary(model)
to view the regression
model’s summary, including coefficients, R-squared, and
p-values.
Example: The
ToothGrowth
dataset in R is a built-in
dataset that comes with the base R installation. It provides data on the
effect of vitamin C on tooth growth in guinea pigs. This dataset is
often used for teaching and learning purposes and is useful for
practicing various statistical analyses.
Here’s some information about the
ToothGrowth
dataset:
Description: The dataset contains observations on the length of guinea pig teeth (tooth growth) under different dosage levels of vitamin C and two delivery methods.
Variables:
len
: The length of tooth growth (in
millimeters).
supp
: The supplement type, either
“VC” (vitamin C) or “OJ” (orange juice).
dose
: The dosage of the supplement
in milligrams per day, which can be 0.5, 1.0, or 2.0.
Data Structure: The dataset consists of 60 observations.
You can load and access the ToothGrowth
dataset in R by simply typing:
# load tooth growth dataset
data("ToothGrowth")
Once loaded, you can explore the dataset using functions like
head(ToothGrowth)
,
summary(ToothGrowth)
, or by creating
visualizations and conducting statistical analyses.
This dataset is often used to demonstrate concepts like hypothesis testing, analysis of variance (ANOVA), and regression analysis in introductory statistics and data analysis courses.
# Load necessary R packages using the 'pacman' package
# 'pacman' is a package management tool that makes it easy to load and manage multiple packages at once.
# It installs the packages if they are not already installed and loads them into the R session.
# The 'tidyverse' package includes a collection of packages for data manipulation and visualization.
# The 'report' package is used for generating summary reports.
::p_load(
pacman# Load the tidyverse package for data manipulation and visualization.
tidyverse, # Load the report package for generating summary reports.
report, install = TRUE, # Install the packages if not already installed.
update = FALSE # Do not update already installed packages.
)
# Load the ToothGrowth dataset
# The 'ToothGrowth' dataset is included in R and contains data related to the effect of vitamin C on tooth growth in guinea pigs.
data("ToothGrowth")
# Define a linear regression model
# Create a linear regression model using the 'lm' function.
# The model predicts the 'len' (tooth length) variable based on 'supp' (supplement type) and 'dose' (dose level) predictors.
<- lm(
lm_mod1 ~ supp + dose, # Model formula specifying the response variable and predictor variables.
len data = ToothGrowth # Specify the dataset in which to find the variables.
)
# Show the summary of the linear regression model
# The 'summary' function provides detailed information about the linear regression model, including coefficients, standard errors, t-values, and p-values.
summary(lm_mod1)
##
## Call:
## lm(formula = len ~ supp + dose, data = ToothGrowth)
##
## Residuals:
## Min 1Q Median 3Q Max
## -6.600 -3.700 0.373 2.116 8.800
##
## Coefficients:
## Estimate Std. Error t value Pr(>|t|)
## (Intercept) 9.2725000 1.2823649 7.231 1.31e-09 ***
## suppVC -3.7000000 1.0936045 -3.383 0.0013 **
## dose 0.0097636 0.0008768 11.135 6.31e-16 ***
## ---
## Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1
##
## Residual standard error: 4.236 on 57 degrees of freedom
## Multiple R-squared: 0.7038, Adjusted R-squared: 0.6934
## F-statistic: 67.72 on 2 and 57 DF, p-value: 8.716e-16
# Extract and print a model output report
# The 'report' package is used here to generate a summary report
R Code Explanation
The codes above load necessary packages and the ToothGrowth dataset,
defines a linear regression model, displays a summary of the model using
the summary
function, and generates a
detailed model output report using the
report
package. The report includes
information about the model’s coefficients and statistics related to its
fit.
Result/ Report Interpretation
The provided report output contains detailed information about the linear regression model’s performance and parameter estimates. Let’s break down the key interpretations:
Model Explanation
len
) based
on two predictors: supp
(supplement type)
and dose
(dose level). The formula used
for the model is len ~ supp + dose
.Model Fit
The model is statistically significant and explains a substantial proportion of variance. The key statistics include:
R-squared (R²) value of 0.70: This indicates that approximately 70% of the variability in tooth length is explained by the model.
F-statistic (F(2, 57)) of 67.72: This tests the overall significance of the model, and the low p-value (< 0.001) suggests that the model is statistically significant.
Adjusted R-squared (adj. R²) of 0.69: This adjusts R² for the number of predictors in the model, providing a measure of model fit.
Model Intercept
The model’s intercept corresponds to
supp = OJ
and
dose = 0
.
The intercept value is 9.27 with a 95% confidence interval (CI) of [6.70, 11.84].
The t-statistic (t(57)) is 7.23, and the p-value is < 0.001.
This indicates that when supp
is
OJ, and dose
is 0, the estimated average
tooth length is 9.27.
Parameter Effects
The report provides information about the effects of individual predictors within the model.
The effect of supp
(supplement
type) with the level [VC]
is statistically
significant and negative.
The beta coefficient is -3.70 with a 95% CI of [-5.89, -1.51].
The t-statistic is -3.38, and the p-value is 0.001.
The standardized beta (Std. beta) is -0.48.
The effect of dose
is statistically
significant and positive.
The beta coefficient is 9.76 with a 95% CI of [8.01, 11.52].
The t-statistic is 11.14, and the p-value is < 0.001.
The standardized beta (Std. beta) is 0.80.
Standardized Parameters
Confidence Intervals and p-values
In summary, the report indicates that the linear regression model is
a good fit for explaining tooth length
(len
) based on the predictors
supp
and
dose
. The model’s parameters, including
intercept and effects of predictors, are statistically significant and
provide valuable insights into the relationship between these variables
and tooth length.
A better approach for linear modelling in R is shown as:
# a better stats output summary can be done
%>% anova(test = "F") %>% report::report() lm_mod1
## The ANOVA suggests that:
##
## - The main effect of supp is statistically significant and large (F(1, 57) =
## 11.45, p = 0.001; Eta2 (partial) = 0.17, 95% CI [0.05, 1.00])
## - The main effect of dose is statistically significant and large (F(1, 57) =
## 123.99, p < .001; Eta2 (partial) = 0.69, 95% CI [0.57, 1.00])
##
## Effect sizes were labelled following Field's (2013) recommendations.
In the context of linear regression modeling in R, using
anova(lm_mod1, test = "F-test")
is more
appropriate than using summary(lm_mod1)
when you want to compare the fit of nested models or assess the overall
significance of a group of predictors. Here’s why:
Comparison of Nested Models:
anova(lm_mod1, test = "F-test")
is
particularly useful when you want to compare two or more nested linear
regression models. Nested models are those where one model is a subset
of the other, typically achieved by adding or removing predictor
variables. The F-test provided by anova
helps you determine whether the inclusion of additional predictors
significantly improves the model fit. This is essential for model
selection and assessing the relevance of specific predictors.
Hypothesis Testing for Groups of Predictors: Sometimes, you may want to test the overall significance of a group of predictors rather than examining each predictor individually. The F-test allows you to test the null hypothesis that all the coefficients associated with a specific group of predictors are equal to zero simultaneously. This is useful in scenarios where you have multiple predictors with a similar theoretical basis (e.g., multiple related ecological variables) and want to determine if, collectively, they contribute significantly to explaining the response variable.
Model Comparison: The
anova
function provides a way to perform
statistical tests for model comparison. By comparing nested models or
models with different sets of predictors, you can make informed
decisions about which variables are essential for explaining the
variance in the response variable and which can be omitted. This helps
in simplifying models and avoiding overfitting.
In contrast, summary(lm_mod1)
typically
provides detailed information about the coefficients of the linear
regression model, including the estimated coefficients, standard errors,
t-values, and p-values for each predictor. While this is valuable for
understanding the individual effects of predictors, it doesn’t directly
address the questions related to model comparison or the overall
significance of groups of predictors.
In summary,
anova(lm_mod1, test = "F-test")
is a
valuable tool for model comparison, assessing the significance of groups
of predictors, and making informed decisions about model complexity. It
complements the summary
function, which is
more focused on providing detailed information about individual
predictor coefficients.
Let’s first export the tooth-growth dataset to a csv flat file for use in Jamovi.
Write tooth-growth data with name “toothgrowth.csv” to csv in R.
# load packages
::p_load(readr, here, install = TRUE, update = F)
pacman
# load dataset
data("ToothGrowth")
# save R dataset to csv file
::write_csv(
readr
ToothGrowth,file = here::here("docs", "data", "toothgrowth.csv"),
col_names = TRUE,
append = FALSE
)
Open/ import the file in Jamovi. In Jamovi, the variable
“len
” should be a continuous data type, “supp
”
as nominal and “dose
” as continuous.
Go to “Analyses” tab, click “Regression” button and select
“Linear Regression”. Perform linear regression by using
“len
” as the Dependent variable, “supp
” in
Factors and “dose
” as a Covariate. Now compare your results
to the previous results generated in R. Interpretations should be the
same as those above for R stats.
Coefficients: Interpret the coefficients of the IVs. A positive coefficient means that as the IV increases, the DV also tends to increase (and vice versa for negative coefficients).
R-squared (R²): R-squared measures the proportion of variance in the DV explained by the IVs. Higher R-squared values indicate a better fit.
P-values: P-values test the null hypothesis that there’s no relationship between IVs and DV. Low p-values (typically < 0.05) indicate statistically significant relationships.
Assumptions: Assess model assumptions, including linearity, independence of errors, homoscedasticity (equal variance of errors), and normality of residuals. Diagnostic plots help check these assumptions. Note that we did not perform any assumptions assessments prior to running the model. We’ll incorporate this workflow in later models.
In ecological research, linear regression provides valuable insights into the relationships between ecological variables. It helps answer questions about ecological processes and how they are influenced by environmental factors. Proper interpretation of model results and assessment of assumptions are crucial for robust ecological conclusions.
Definition: Logistic regression is a statistical method used to model the probability of a binary outcome variable (0/1, Yes/No, True/False) as a function of one or more independent variables. It’s particularly useful when the dependent variable represents a categorical response with two levels.
Species Presence/Absence: Logistic regression is widely used in ecology to model the probability of species presence or absence based on environmental factors such as temperature, habitat type, or elevation.
Habitat Suitability: Ecologists can employ logistic regression to determine the suitability of habitats for specific species. For example, modeling the presence of a particular bird species in relation to forest cover or proximity to water sources.
Biodiversity Conservation: Logistic regression can help predict the likelihood of the presence of endangered species in different regions based on factors like land use, climate, or protected areas.
Disease Spread: In disease ecology, logistic regression can be used to model the probability of disease occurrence in relation to environmental variables, aiding in the understanding and management of disease spread.
# Load necessary libraries (if not already loaded)
::p_load(
pacman
tidyverse,
flextable,install = T,
update = F
)
# Load the ToothGrowth dataset
data("ToothGrowth")
# Perform logistic regression using glm
<-
logistic_mod glm(supp ~ len + dose, data = ToothGrowth, family = "binomial")
# Output analysis of deviance table as a formatted flextable
%>%
logistic_mod anova(test = "LRT") %>% # Perform an analysis of deviance
::rownames_to_column(., var = "Predictors") %>% # Add a column for predictor names
tibble::qflextable() # Create a formatted flextable flextable
Predictors | Df | Deviance | Resid. Df | Resid. Dev | Pr(>Chi) |
---|---|---|---|---|---|
NULL | 59 | 83.18 | |||
len | 1 | 3.64 | 58 | 79.53 | 0.06 |
dose | 1 | 7.20 | 57 | 72.33 | 0.01 |
R Code Explanation
Library Loading: This section loads the
necessary R libraries, including the
tidyverse
package for data manipulation
and visualization.
Dataset Loading: The
data("ToothGrowth")
command loads the
ToothGrowth dataset into your R session. This dataset contains
information about the effect of vitamin C dose on tooth growth in Guinea
pigs.
Logistic Regression: Logistic regression is
performed using the glm
function. It
models the relationship between the binary variable
supp
(supplement type) and the predictor
variables len
(tooth length) and
dose
(dose of vitamin C). The
family
argument is set to “binomial” to
specify logistic regression.
Analysis of Deviance: The
anova
function is used to perform an
analysis of deviance on the logistic regression model, assessing the
significance of variables in the model. The
anova(test = "LRT")
code calls the
anova
function on the logistic regression
model (logistic_mod
) specifying the type
of test to be performed, which is the likelihood ratio test (LRT). The
LRT is used to compare the fit of two nested models: one with the
predictors and one without.
Here’s what the likelihood ratio test (LRT) does in the context of logistic regression:
It compares two models:
The null model (reduced model): This is a model that includes only an intercept (no predictors).
The full model: This is the logistic regression model you have
fitted (logistic_mod
) with one or more
predictor variables.
The LRT assesses whether the full model (with predictors) provides a significantly better fit to the data compared to the null model (with no predictors).
The test statistic for the LRT follows a chi-squared distribution, and its significance is assessed by comparing it to a chi-squared distribution with degrees of freedom equal to the difference in the number of parameters estimated between the two models.
The output typically includes the chi-squared test statistic, degrees of freedom, and the associated p-value. The p-value tells you whether the addition of the predictors significantly improves the model fit.
In summary, the line
logistic_mod %>% anova(test = "LRT")
is
used to perform a likelihood ratio test on the logistic regression model
to assess the overall significance of the predictors in improving the
model’s fit compared to a null model. If the p-value is below a chosen
significance level (e.g., 0.05), it suggests that the predictors
collectively have a significant impact on the response
variable.
Data Manipulation: The
%>%
operator is used to pipe the
results of the analysis into a series of data manipulation and
formatting functions.
tibble::rownames_to_column(., var = "Predictors")
adds a column named “Predictors” to the output, containing predictor
variable names.
flextable::qflextable()
creates a
formatted flextable, which can be used for generating tables with a
customized appearance.
Overall, this code performs logistic regression, analyzes the deviance, and presents the results in a formatted table for better readability and interpretation.
Interpretation
Interpretation for the logistic regression output generated by the following R code chunk is defined below.
%>%
logistic_mod anova(test = "LRT")
The “Analysis of Deviance” table provides information about the statistical significance of the predictor variables in a logistic regression model. Here’s how to interpret the table:
Model Information: The table begins with some general information about the logistic regression model:
Model type: “binomial
”
indicates that it’s a binary logistic regression.
Link function: “logit
”
refers to the log-odds link function used in logistic
regression.
Response variable: “supp
” is the variable being
predicted.
Sequential Analysis: The table then lists the
predictor variables (“len
” and “dose
”) added
sequentially from first to last. Each variable’s impact on the model is
assessed in turn.
Df (Degrees of Freedom): The
“Df
” column indicates the degrees
of freedom associated with each variable. For “len
” and
“dose
,” there is 1 degree of freedom each.
Deviance: The
“Deviance
” column shows the
deviance associated with each variable. Deviance is a measure of how
well the model fits the data. It’s similar to the residual sum of
squares in linear regression. Smaller values indicate a better
fit.
Resid. Df (Residual Degrees of Freedom): The
“Resid. Df
” column represents the
degrees of freedom associated with the residuals after including each
variable in the model. It’s calculated as the total degrees of freedom
minus the degrees of freedom associated with the variable.
Resid. Dev (Residual Deviance): The
“Resid. Dev
” column shows the
residual deviance after including each variable in the model. Like
deviance, smaller values indicate a better fit.
Pr(>Chi): The
“Pr(>Chi)
” column provides the
p-value associated with each variable’s contribution to the model. This
p-value represents the probability of observing a deviance statistic as
extreme as, or more extreme than, the one calculated if the variable had
no effect on the response. Smaller p-values suggest stronger evidence
against the null hypothesis that the variable has no effect.
Significance Codes: Significance codes are used
to indicate the level of statistical significance of each variable’s
contribution to the model. They are often represented as asterisks
(*
). In this table:
“0.001” corresponds to
‘***,
’ indicating extremely high
significance.
“0.01” corresponds to
‘**,
’ indicating high
significance.
“0.05” corresponds to ‘*,
’
indicating moderate significance.
“0.1” corresponds to a space (’ ’), indicating marginal significance.
“1” indicates that the variable is not statistically significant.
Interpretation
The initial model (NULL model) does not include any predictors and has a deviance of 83.178 with 59 degrees of freedom.
When the “len
” variable is added to the model, it
reduces the deviance by 3.6436 units with 1 degree of freedom. The
p-value associated with “len
” is 0.056286, which is greater
than the typical significance level of 0.05. Therefore,
“len
” is not statistically significant at the 0.05
level.
When the “dose
” variable is added to the model, it
further reduces the deviance by 7.2043 units with 1 degree of freedom.
The p-value associated with “dose
” is 0.007273, which is
less than 0.05. Therefore, “dose
” is statistically
significant at the 0.05 level.
In summary, the analysis of deviance indicates that the
“dose
” variable is statistically significant in predicting
the “supp” variable, while the “len
” variable is not
statistically significant at the 0.05 significance level.
From the “Analyses” tab, select 2 Outcomes (binomial under logistic regression). Compare results and interpretation to R outputs.
Coefficients: Interpret the coefficients of the IVs. Positive coefficients indicate an increase in the log-odds of the binary outcome, while negative coefficients indicate a decrease.
Odds Ratios: Exponentiate the coefficients to get odds ratios. An odds ratio greater than 1 indicates an increase in the odds of the outcome, and less than 1 indicates a decrease.
P-values: P-values test the null hypothesis that there’s no relationship between IVs and the binary outcome. Low p-values (typically < 0.05) indicate statistically significant relationships.
Logistic regression is a valuable tool in ecological research for modeling binary outcomes and understanding the factors influencing ecological phenomena like species presence, habitat suitability, and disease occurrence. Proper interpretation of model results is essential for making ecologically meaningful conclusions.
Residual Analysis: Residuals are the differences between the observed and predicted values. In regression analysis, it’s crucial to assess the distribution of residuals. A well-fitting model should have residuals that are normally distributed with mean zero. You can visualize residuals using residual plots, such as scatter-plots of residuals against predicted values or against independent variables. Deviations from normality or patterns in these plots can indicate issues with model fit.
R-squared (Coefficient of Determination): R-squared measures the proportion of variance in the dependent variable explained by the model. Higher R-squared values indicate better model fit, but it’s important to balance model complexity with model fit.
Adjusted R-squared: Adjusted R-squared accounts for the number of predictors in the model, penalizing models with too many predictors. It helps prevent overfitting by adjusting R-squared for the number of predictors.
Residual Sum of Squares (RSS) and Deviance: These measures represent the sum of squared differences between observed and predicted values. Smaller values indicate better fit.
p-values of Coefficients: Low p-values suggest that predictor variables are statistically significant in explaining the variation in the dependent variable. High p-values indicate that a variable may not be relevant.
Residual analysis involves examining plots of residuals to identify patterns or outliers. For instance, you might create:
# Load necessary libraries (if not already loaded)
::p_load(
pacman
tidyverse,
easystats,
car,install = T, update = F
)
# Load the ToothGrowth dataset
data("ToothGrowth")
# Fit a linear regression model
<- lm(len ~ supp + dose, data = ToothGrowth)
lm_mod1
# Create a Residual vs. Fitted Value Plot
plot(lm_mod1, which = 1, main = "Residual vs. Fitted Value Plot")
R Code Explanation
The provided R code is for creating a “Residual vs. Fitted Value Plot” to assess the relationship between the residuals (the differences between the observed and predicted values) and the fitted values (the values predicted by the regression model). This plot is used to check whether the linear regression assumptions, particularly the assumption of homoscedasticity (constant variance of residuals), are met.
Here’s what each part of the code does:
Loading Libraries: The code begins by loading several R libraries. These libraries include:
tidyverse
: A collection of packages
for data manipulation and visualization.
easystats
: A package for easy and
consistent statistical reporting.
car
: The “car” package, which
provides various diagnostic tools for regression analysis.
Loading Data: The
data("ToothGrowth")
command loads the
“ToothGrowth” dataset, which is a built-in dataset in R. This dataset
contains measurements of tooth length in guinea pigs.
Fitting a Linear Regression Model: The code fits
a linear regression model (lm_mod1
) to the
data. This model predicts tooth length
(len
) based on two predictor variables:
supp
(supplement type) and
dose
(dose of the supplement).
Creating the Residual vs. Fitted Value Plot: The
plot()
function is used to create the
Residual vs. Fitted Value Plot for the linear regression model. The
arguments provided to plot()
are as
follows:
lm_mod1
: The fitted linear
regression model.
which = 1
: Specifies that you want
to create the Residual vs. Fitted Value Plot.
main = "Residual vs. Fitted Value Plot"
:
Sets the main title of the plot.
The resulting plot will display the residuals on the vertical axis and the fitted (predicted) values on the horizontal axis. Each point on the plot represents an observation from the dataset. The plot helps you assess whether the residuals have a consistent spread across different fitted values, which is crucial for the validity of linear regression assumptions. A horizontal band or cloud of points with no discernible pattern indicates that the assumption of homoscedasticity is likely met. If there is a pattern or funnel shape in the plot, it suggests heteroscedasticity, which may violate the assumption.
In summary, this code segment allows you to create a diagnostic plot to assess the homoscedasticity assumption in a linear regression model using the “ToothGrowth” dataset.
# Load necessary libraries (if not already loaded)
::p_load(
pacman
tidyverse,
easystats,
car,install = T, update = F
)
# Load the ToothGrowth dataset
data("ToothGrowth")
# Fit a linear regression model
<- lm(len ~ supp + dose, data = ToothGrowth)
lm_mod1
# Create a Normal Probability Plot (Q-Q Plot) for residuals
qqnorm(residuals(lm_mod1), main = "Normal Probability Plot (Q-Q Plot) of Residuals")
qqline(residuals(lm_mod1), col = "red")
R Code Explanation
The provided R code is for creating a “Normal Probability Plot” (also known as a Q-Q Plot) to assess whether the residuals of a linear regression model follow a normal distribution. This plot is used to check the assumption of normality of residuals.
Here’s an explanation of each part of the code:
Loading Libraries: The code starts by loading
several R libraries using the
pacman::p_load()
function. These libraries
include:
tidyverse
: A collection of packages
for data manipulation and visualization.
easystats
: A package for easy and
consistent statistical reporting.
car
: The “car” package, which
provides various diagnostic tools for regression analysis.
Loading Data: The
data("ToothGrowth")
command loads the
“ToothGrowth” dataset, which contains measurements of tooth length in
guinea pigs. This dataset will be used for fitting a linear regression
model and assessing its residuals.
Fitting a Linear Regression Model: The code fits
a linear regression model (lm_mod1
) to the
data. This model predicts tooth length
(len
) based on two predictor variables:
supp
(supplement type) and
dose
(dose of the supplement).
Creating the Normal Probability Plot (Q-Q Plot) for Residuals:
qqnorm(residuals(lm_mod1), main = "Normal Probability Plot (Q-Q Plot) of Residuals")
:
This line of code generates the Q-Q Plot for the residuals of the linear
regression model. The qqnorm()
function is
used to create the Q-Q Plot, and
residuals(lm_mod1)
extracts the residuals
from the model. The main
argument sets the
main title of the plot.
qqline(residuals(lm_mod1), col = "red")
:
This line adds a reference line to the Q-Q Plot. The
qqline()
function is used to add a line to
the plot to help assess how closely the residuals follow a normal
distribution. In this case, the line is colored red for
visibility.
The resulting Q-Q Plot displays the quantiles of the observed residuals against the quantiles of a theoretical normal distribution. If the residuals closely follow a normal distribution, the points on the plot will closely align with the reference line (red line). Deviations from the line may indicate departures from normality.
In summary, this code segment allows you to create a Q-Q Plot to visually assess the normality assumption of the residuals of a linear regression model using the “ToothGrowth” dataset.
# Load necessary libraries (if not already loaded)
::p_load(
pacman
tidyverse,
easystats,
car,install = T, update = F
)
# Load the ToothGrowth dataset
data("ToothGrowth")
# Fit a linear regression model
<- lm(len ~ supp + dose, data = ToothGrowth)
lm_mod1
# Create a Residual vs. Predictor Variable Plot
::residualPlots(lm_mod1, col.quad = "red") car
## Test stat Pr(>|Test stat|)
## supp
## dose -3.7144 0.0004714 ***
## Tukey test -4.5770 4.717e-06 ***
## ---
## Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1
R Code Explanation
Loading Libraries: This code begins by loading
several R libraries using the
pacman::p_load()
function. These libraries
include:
tidyverse
: A collection of packages
for data manipulation and visualization.
easystats
: A package for easy and
consistent statistical reporting.
car
: The “car” package, which
provides various diagnostic tools for regression analysis.
Loading Data: The
data("ToothGrowth")
command loads the
“ToothGrowth” dataset, which contains measurements of tooth length in
guinea pigs. This dataset will be used for fitting a linear regression
model and assessing its residuals.
Fitting a Linear Regression Model: The code fits
a linear regression model (lm_mod1
) to the
data. This model predicts tooth length
(len
) based on two predictor variables:
supp
(supplement type) and
dose
(dose of the supplement).
Creating the Residual vs. Predictor Variable Plot:
car::residualPlots(lm_mod1, col.quad = "red")
:
This line of code generates the Residual vs. Predictor Variable Plot
using the residualPlots()
function from
the “car” package. The lm_mod1
model is
passed as an argument. The
col.quad = "red"
argument specifies that
points outside a certain range will be colored red. This plot helps
visualize the relationship between the residuals and the predictor
variables.The resulting plot displays the relationship between the residuals and the predictor variables in the linear regression model. It can be used to identify patterns or trends in the residuals, such as heteroscedasticity or nonlinearity.
In summary, this code segment allows you to create a Residual vs. Predictor Variable Plot for a linear regression model fitted to the “ToothGrowth” dataset, which can be useful for diagnosing potential issues with the model’s assumptions.
# Load necessary libraries (if not already loaded)
::p_load(
pacman
tidyverse,
easystats,
car,install = T, update = F
)
# Load the ToothGrowth dataset
data("ToothGrowth")
# Fit a linear regression model
<- lm(len ~ supp + dose, data = ToothGrowth)
lm_mod1
# Create a Leverage Plot
::leveragePlots(lm_mod1, col.lines = "red") car
R Code Explanation
Loading Libraries: This code begins by loading
several R libraries using the
pacman::p_load()
function, just like in
the previous example. These libraries include
tidyverse
,
easystats
, and
car
, which are used for data manipulation,
statistical reporting, and regression analysis.
Loading Data: The
data("ToothGrowth")
command loads the
“ToothGrowth” dataset, which contains measurements of tooth length in
guinea pigs. This dataset will be used for fitting a linear regression
model and assessing its leverage.
Fitting a Linear Regression Model: The code fits
a linear regression model (lm_mod1
) to the
data. This model predicts tooth length
(len
) based on two predictor variables:
supp
(supplement type) and
dose
(dose of the supplement).
Creating the Leverage Plot:
car::leveragePlots(lm_mod1, col.lines = "red")
:
This line of code generates the Leverage Plot using the
leveragePlots()
function from the “car”
package. The lm_mod1
model is passed as an
argument. The col.lines = "red"
argument
specifies that lines corresponding to specific observations with high
leverage will be colored red.The resulting plot displays the leverage values for each observation in the dataset. High-leverage observations are typically those that have a strong influence on the regression model’s coefficients. The red lines on the plot help identify observations with high leverage.
In summary, this code segment allows you to create a Leverage Plot for a linear regression model fitted to the “ToothGrowth” dataset, helping you identify influential observations in the model.
Start with a Simple Model: Begin with a simple model that includes only essential predictor variables.
Add Complexity: Gradually add complexity by including additional predictors or higher-order terms (e.g., quadratic terms) if necessary. Assess whether the added complexity improves model fit.
Compare Models: Use information criteria like AIC (Akaike Information Criterion) and BIC (Bayesian Information Criterion) to compare different models. Lower AIC and BIC values indicate better-fitting models, with a balance between goodness of fit and model complexity.
Cross-Validation: Perform cross-validation, like k-fold cross-validation, to assess how well the model generalizes to new data. This helps avoid overfitting.
Domain Knowledge: Consider ecological domain knowledge when selecting the most appropriate model. Sometimes, theoretical understanding of the system can guide model selection.
Akaike Information Criterion (AIC): AIC estimates the relative quality of statistical models. It penalizes models for their complexity. Smaller AIC values indicate better-fitting models, but AIC does not provide an absolute measure of model fit.
Bayesian Information Criterion (BIC): BIC, similar to AIC, penalizes models for complexity. However, it applies a stronger penalty for additional parameters. Like AIC, lower BIC values indicate better-fitting models.
In ecological research, assessing model fit and selecting the most appropriate model are critical steps to ensure that the regression analysis accurately captures the underlying relationships in the data. Residual analysis and information criteria like AIC and BIC provide valuable tools for model evaluation and selection.
In conclusion, Chapter 5 has been a comprehensive journey into the world of regression analysis, tailored for ecological research. Here are the key takeaways:
Fundamentals of Regression: You’ve grasped the fundamental concepts of regression analysis, understanding how it models relationships between variables. This knowledge forms the foundation for exploring ecological data.
Linear Regression: You’ve delved into linear regression, a powerful tool for modeling linear relationships between variables. Real-world examples have shown you how to apply this technique to ecological questions.
Logistic Regression: Logistic regression has been introduced as a means to model binary outcomes in ecological contexts. You’ve seen its applications and how to interpret results.
Model Assessment: You’ve learned the importance of assessing model fit, employing techniques like residual analysis, R-squared, and p-values to validate your models. These tools ensure your models accurately represent the data.
Model Selection: Model selection strategies, including starting simple, adding complexity, and using information criteria like AIC and BIC, have been highlighted. You’re now equipped to choose the most appropriate model for your ecological research.
Continuous Learning: Remember that regression analysis is a dynamic field. Stay curious, continue learning, and consider domain-specific knowledge to enhance the relevance and accuracy of your models.
This chapter empowers you with the skills to navigate and model ecological relationships effectively. Whether you’re exploring linear associations or tackling binary outcomes, you now have the tools to build, assess, and interpret regression models. These models are invaluable for gaining insights in ecological research, enabling you to make data-driven decisions and contribute to the understanding of complex ecological systems.
Chapter 6 delves into the art of data visualization, a crucial skill for communicating ecological findings effectively. In this chapter, you will:
Learn various data visualization techniques.
Gain expertise in creating informative graphs and plots.
Understand the role of visualization in conveying ecological insights clearly.
Why Data Visualization Matters
Data visualization plays a pivotal role in ecological research for several reasons:
Pattern Recognition: Visualizations make it easier to identify patterns, trends, and anomalies in data. In ecology, this can reveal phenomena like population fluctuations, seasonal changes, or the impact of environmental factors.
Communication: Effective visualizations simplify complex ecological concepts, enabling researchers to convey findings to both expert and non-expert audiences. This is particularly valuable when sharing results with policymakers, stakeholders, or the general public.
Hypothesis Testing: Visualizations assist in formulating and testing ecological hypotheses. Researchers can visually explore data distributions, relationships, and spatial patterns, which informs the design of hypothesis tests.
Decision-Making: Visualizations aid in making informed decisions about ecological conservation and management strategies. For example, they can illustrate the effects of different interventions on ecosystem health.
Types of Ecological Data
Ecological data come in various forms, including:
Categorical Data: These represent qualitative characteristics, such as species names, habitat types, or land-use categories. Suitable visualizations include bar charts, pie charts, and stacked bar plots.
Numerical Data: Numerical data involve measurements or counts, such as temperature, population size, or nutrient concentrations. Histograms, scatter plots, and box plots are useful for visualizing numerical data.
Spatial Data: Spatial data describe the geographical distribution of ecological features. Maps, heatmaps, and spatial plots help visualize these data effectively, allowing researchers to observe spatial patterns and trends.
Introduction to Basic Plots
Here’s an overview of common basic plots in ecological research and when to use them:
Bar Charts:
Use: Bar charts are suitable for visualizing categorical data, such as the frequency of different species in a habitat.
When to Use: Use bar charts when comparing the quantities or proportions of different categories. They’re great for showing discrete data.
Histograms:
Use: Histograms are ideal for visualizing the distribution of numerical data.
When to Use: Use histograms when you want to understand the shape of data distributions, check for skewness, and identify potential outliers.
Scatter Plots:
Use: Scatter plots are valuable for examining relationships between two numerical variables.
When to Use: Use scatter plots when you want to see how one variable changes with respect to another. They’re helpful for identifying correlations or trends.
These basic plots serve as building blocks for more advanced visualizations and are foundational tools for exploring and communicating ecological data.
Visualizations not only enhance the understanding of ecological phenomena but also foster data-driven decision-making in ecological research and conservation efforts. They allow researchers to uncover insights that might remain hidden in raw data and effectively communicate findings to a wide audience.
library(ggplot2) # Load the ggplot2 package for data visualization.
data("ToothGrowth") # Load the ToothGrowth dataset.
# Create a bar chart
<-
bar_chart ::ggplot(ToothGrowth, aes(x = supp, y = len, fill = supp)) +
ggplot2::geom_bar(stat = "summary",
ggplot2fun = "mean",
position = "dodge") +
::labs(title = "Average Tooth Length by Supplement Type",
ggplot2x = "Supplement Type",
y = "Average Tooth Length") +
::theme_minimal()
ggplot2
# Display the bar chart
print(bar_chart)
R Code Explanation
The provided R code is used to create a bar chart using the
ggplot2
package in R. This code visualizes
the average tooth length (len
) by
supplement type (supp
) using the
ToothGrowth
dataset. Let’s break down the
code step by step:
Step 1: Load Required Libraries.
ggplot2
package,
which is a popular data visualization package in R. It provides a
flexible and powerful way to create a wide range of visualizations,
including bar charts.Step 2: Load the Dataset
ToothGrowth
dataset, which
is included in R by default. This dataset contains information about the
length of tooth growth in guinea pigs exposed to different supplement
types (supp
) and different doses
(dose
).Step 3: Create a Bar Chart
Now, we create the bar chart step by step:
ggplot(ToothGrowth, aes(x = supp, y = len, fill = supp))
:
We specify that we’re using the
ToothGrowth
dataset and map the
supp
variable to the x-axis
(x
) and the
len
variable to the y-axis
(y
). We also fill the bars with colors
based on the supp
variable for better
differentiation.
geom_bar(stat = "summary", fun = "mean", position = "dodge")
:
This part specifies that we want to create a bar chart. We use
stat = "summary"
to summarize the data,
fun = "mean"
to calculate the mean of
len
for each
supp
category, and
position = "dodge"
to create grouped bars
for each supp
category.
labs(...)
: Here, we set the title
and axis labels for the chart.
theme_minimal()
: We apply a minimal
theme to the chart for a clean and simple appearance.
Step 4: Display the Bar Chart
The resulting bar chart visually represents the average tooth length
for each supplement type (OJ and VC) in the
ToothGrowth
dataset, making it easy to
compare the effects of different supplements on tooth growth in guinea
pigs.
Practical Example
In ecological research, you might use bar charts to visualize the following scenarios:
Plant Species Abundance: Create a bar chart to show the abundance of different plant species in a study area.
Bird Species Distribution: Visualize the distribution of bird species in different habitats or seasons.
Invasive Species Monitoring: Use bar charts to track the population changes of invasive species over time.
Land Use Composition: Show the composition of land use types (e.g., forests, agriculture, urban areas) in a region.
Habitat Preferences: Compare the preferences of a particular animal species for different types of habitats.
library(ggplot2) # Load the ggplot2 package for data visualization.
data("ToothGrowth") # Load the ToothGrowth dataset.
# Create a histogram
<- ggplot(ToothGrowth, aes(x = len, fill = supp)) +
histogram geom_histogram(binwidth = 5, position = "dodge") +
labs(
title = "Histogram of Tooth Length",
x = "Tooth Length",
y = "Frequency"
+
) facet_grid(. ~ supp) +
theme_minimal()
# Display the histogram
print(histogram)
R Code Explanation
Now, let’s break down the code for creating the histogram:
ggplot(ToothGrowth, aes(x = len, fill = supp))
:
We specify that we’re using the
ToothGrowth
dataset and map the
len
variable to the x-axis. We also fill
the bars with colors based on the supp
variable for better differentiation.
geom_histogram(binwidth = 5, position = "dodge")
:
This part specifies that we want to create a histogram. We set the bin
width to 5 (you can adjust this to visualize the data differently) and
use position = "dodge"
to create separate
histograms for each supp
category.
labs(...)
: Here, we set the title
and axis labels for the chart.
facet_grid(. ~ supp)
: This line
adds subplots for each supp
category,
allowing us to compare the histograms of tooth length for “VC” and “OJ”
supplements side by side.
theme_minimal()
: We apply a minimal
theme to the chart for a clean appearance.
Interpretation
The resulting histogram visualizes the distribution of tooth lengths for the “VC” and “OJ” supplement categories. Here are some interpretations:
Shape of Histograms: You can observe the shape of each histogram. For example, if the “VC” histogram is skewed to the right (positively skewed), it suggests that most observations have shorter tooth lengths with a long tail of longer lengths. If it’s skewed to the left (negatively skewed), it suggests the opposite. A roughly symmetric histogram suggests a more normal distribution.
Center and Spread: You can also see where the bulk of the data lies (center) and how spread out it is (spread). In ecological research, this could be important for understanding the variability in tooth growth under different conditions.
Faceting: Faceting by
supp
allows you to compare the
distributions of tooth lengths for “VC” and “OJ” supplements. This can
be valuable in ecological contexts to see how different treatments
affect the distribution of a variable.
Histograms are useful for visually exploring the distribution of continuous data, helping researchers identify patterns and deviations that may inform further analysis and research questions.
library(ggplot2) # Load the ggplot2 package for data visualization.
data("ToothGrowth") # Load the ToothGrowth dataset.
# Create a scatter plot
<- ggplot(ToothGrowth, aes(x = dose, y = len, color = supp)) +
scatter_plot geom_point(size = 3) +
labs(
title = "Scatter Plot of Tooth Length vs. Dose",
x = "Dose",
y = "Tooth Length"
+
) theme_minimal()
# Display the scatter plot
print(scatter_plot)
R Code Explanation
Now, let’s break down the code for creating the scatter plot:
ggplot(ToothGrowth, aes(x = dose, y = len, color = supp))
:
We specify that we’re using the
ToothGrowth
dataset and map the
dose
variable to the x-axis and the
len
variable to the y-axis. We also use
the color
aesthetic to differentiate
points by the supp
variable.
geom_point(size = 3)
: This part
specifies that we want to create a scatter plot with points. We set the
size of the points to 3 (you can adjust this for better
visibility).
labs(...)
: Here, we set the title
and axis labels for the chart.
theme_minimal()
: We apply a minimal
theme to the chart for a clean appearance.
Interpretation
The resulting scatter plot visualizes the relationship between tooth
length (len
) and dose
(dose
) for the “VC” and “OJ” supplement
categories. Here are some interpretations:
Trend: You can assess whether there is a discernible trend or pattern in the data points. In this case, you can see that for both “VC” (in green) and “OJ” (in red) supplements, tooth length tends to increase with increasing dose.
Variability: Scatter plots also allow you to observe the spread or variability in the data. Wider spreads suggest higher variability.
Outliers: Look for any data points that deviate significantly from the overall pattern. Outliers may represent unusual or interesting observations that warrant further investigation in ecological research.
Scatter plots are valuable for exploring relationships between two continuous variables, helping researchers identify trends, clusters, or potential outliers. They provide a visual basis for formulating research questions and hypotheses.
Here’s an example of how to create box plot and violin plot in R
using the ggplot2
package with
explanations and interpretations using the
ToothGrowth
dataset.
library(ggplot2) # Load the ggplot2 package for data visualization.
data("ToothGrowth") # Load the ToothGrowth dataset.
# Box Plot
<- ggplot(ToothGrowth, aes(x = factor(dose), y = len, fill = supp)) +
boxplot_plot geom_boxplot() +
labs(
title = "Box Plot of Tooth Length by Dose and Supplement",
x = "Dose",
y = "Tooth Length"
+
) theme_minimal() +
scale_fill_manual(values = c("#F8766D", "#00BFC4"))
# Violin Plot
<- ggplot(ToothGrowth, aes(x = factor(dose), y = len, fill = supp)) +
violin_plot geom_violin(trim = FALSE) +
labs(
title = "Violin Plot of Tooth Length by Dose and Supplement",
x = "Dose",
y = "Tooth Length"
+
) theme_minimal() +
scale_fill_manual(values = c("#F8766D", "#00BFC4"))
# Display box plot and violin plot
print(boxplot_plot)
print(violin_plot)
R Code Explanation
In this code, we create both a box plot and a violin plot of tooth
length (len
) by dose
(dose
) and supplement type
(supp
). Here’s the breakdown:
ggplot(ToothGrowth, aes(x = factor(dose), y = len, fill = supp))
:
We specify the dataset and map the dose
variable to the x-axis, the len
variable
to the y-axis, and use the fill
aesthetic
to differentiate data by supp
.
geom_boxplot()
: This adds the box
plot layer. Box plots show the median, quartiles, and potential outliers
in the data.
geom_violin(trim = FALSE)
: This
adds the violin plot layer. Violin plots are similar to box plots but
also provide a density estimation of the data distribution.
labs(...)
: We set titles and axis
labels.
theme_minimal()
: We apply a minimal
theme.
scale_fill_manual(...)
: We manually
set fill colors for the two supplement types.
Interpretation
Box Plot: The box plot provides a summary of the distribution of tooth lengths for each dose level and supplement type. The box represents the interquartile range (IQR), the line inside the box is the median, and the whiskers extend to the minimum and maximum values within 1.5 times the IQR. Outliers, shown as individual points, are values beyond the whiskers.
Violin Plot: The violin plot combines a box plot with a rotated kernel density estimation. It displays the same quartile information as the box plot but also provides a more detailed view of the data distribution. The width of the violin at any given y-value represents the density of data points. Wider sections indicate higher data density, while narrower sections suggest lower density.
In ecological research using this dataset, these plots can help visualize how tooth length varies across different doses and supplement types. Researchers can assess whether the distribution of tooth lengths differs between supplement types for each dose level. These plots can also identify potential outliers or skewness in the data.
The choice between a box plot and a violin plot depends on the level of detail required. Box plots provide a concise summary of central tendency and spread, making them suitable for a quick overview. Violin plots offer a more comprehensive view of data distribution, making them useful when exploring the shape of the distribution.
These plots aid in making informed decisions, such as whether differences between groups are significant, whether the data distribution is skewed, and whether transformations or further analyses are necessary. They are valuable tools in ecological research for exploring and communicating data patterns.
Let’s use the lynx
dataset from the
datasets
package in R, which contains data
on the number of lynx trapped in the Mackenzie River area of Canada over
multiple years. We’ll create line plots to visualize trends over
time.
# Load necessary libraries (if not already loaded)
::p_load(
pacman
tidyverse,install = T, update = F
datasets,
)
# Load the 'lynx' dataset
data("lynx")
# Create a sequence of years
<- seq(from = as.Date("1821-01-01"), by = "years", length.out = length(lynx))
years
# Create a data frame with the 'Year' and 'Lynx' columns
<- data.frame(
lynx_df Year = years,
Lynx = lynx
)
# Create a line plot to show the trend in lynx population over time
::ggplot(data = lynx_df, aes(x = Year, y = Lynx)) +
ggplot2::geom_line() +
ggplot2::labs(title = "Lynx Population Over Time",
ggplot2x = "Year",
y = "Number of Lynx") +
::theme_minimal() ggplot2
R Code Explanation
Loading Necessary Libraries: The code begins by
loading required R packages using the
pacman::p_load()
function. These packages
include tidyverse
for data manipulation
and visualization, datasets
for accessing
built-in datasets, and ggplot2
for
creating plots. The install = T
and
update = F
arguments ensure that the
packages are installed if they are not already and that they are not
updated.
Loading the ‘lynx’ Dataset: The
data()
function is used to load the ‘lynx’
dataset, which is a built-in dataset in R. This dataset contains time
series data representing the Canadian lynx population from 1821 to
Converting Time Series to Data Frame: The next
step involves converting the time series data from the ‘lynx’ dataset
into a data frame. This is done to make it easier to work with the data
in a tabular format. The data.frame()
function is used for this purpose.
Converting ‘Year’ to a Date Format: The ‘lynx’
dataset includes a ‘Year’ variable representing the years from 1821 to
1934. However, by default, it is treated as numeric. To make it suitable
for time series plotting, the code uses the
as.Date()
function to convert ‘Year’ to a
date format. The origin = "1800-01-01"
argument specifies the origin date from which to calculate the dates.
This allows ‘Year’ to be interpreted as dates with proper
intervals.
Creating a Line Plot: We use the
ggplot()
function from the
ggplot2
package to create a line plot of
the lynx population over time. Within the
ggplot()
function:
data = lynx_df
specifies the
dataset to use.
aes(x = Year, y = Lynx)
sets up the
aesthetics for the plot, with ‘Year’ on the x-axis and ‘Lynx’ on the
y-axis.
geom_line()
adds the actual line to
the plot.
labs()
sets the plot title and axis
labels.
theme_minimal()
applies a
minimalistic theme to the plot.
This line plot provides a visual representation of the trend in lynx population over time, which is a common scenario in ecological time series data analysis. You can adapt this code to explore other ecological time series datasets and visualize trends in various ecological variables over time.
Spatial data plays a fundamental role in ecological research as it provides critical information about the location, distribution, and interactions of organisms and ecosystems in their natural environment. Understanding spatial patterns and relationships is essential for addressing ecological questions and making informed conservation and management decisions. Here are some key aspects of spatial data in ecology:
Habitat Mapping: Ecologists use spatial data to map habitats, such as forests, wetlands, and grasslands. This information helps identify areas with unique ecological characteristics and supports biodiversity conservation efforts.
Species Distribution: Spatial data is crucial for studying the distribution of species. Ecologists use techniques like species distribution modeling (SDM) to predict where organisms are likely to occur based on environmental variables.
Migration and Movement: Tracking the movement and migration of animals is possible through spatial data. GPS data and satellite tracking provide valuable insights into animal behavior and migration patterns.
Land Use and Land Cover Change: Spatial data allows researchers to monitor changes in land use and land cover over time. This is essential for assessing the impact of urbanization, deforestation, and other human activities on ecosystems.
Spatial Interactions: Ecological processes often depend on spatial interactions among organisms. For example, the spread of diseases, competition for resources, and predator-prey interactions can be better understood by considering the spatial context.
Spatial data visualization techniques are essential for effectively conveying information contained within spatial datasets. They help ecologists and researchers explore patterns, trends, and relationships within ecological systems. Here are some common spatial data visualization techniques:
Maps: Maps are a fundamental tool for visualizing spatial data. They can show the distribution of species, land cover types, and environmental variables. Geographic Information Systems (GIS) software is commonly used for creating and analyzing maps.
Heatmaps: Heatmaps use color gradients to represent the intensity or density of data at different locations. In ecology, heatmaps can visualize species abundance, biodiversity hot-spots, and environmental gradients.
Spatial Plots: Scatter plots and bubble plots can be adapted to include spatial information. These plots are useful for visualizing relationships between two or more variables across spatial locations.
Interpolation Maps: Interpolation methods like kriging and inverse distance weighting are used to create continuous surfaces from point data. These maps provide insights into how environmental variables change spatially.
Choropleth Maps: Choropleth maps use color-coding to represent data for regions or polygons. They are effective for visualizing regional variations in ecological parameters or environmental conditions.
Flow Maps: Flow maps illustrate the movement of organisms or materials between locations. For example, they can show the migration routes of birds or the dispersal of seeds.
Spatial Analysis Outputs: Visualizations of spatial statistical analyses, such as cluster maps (showing areas of high or low values) or spatial autocorrelation plots (indicating spatial patterns of similarity), provide insights into ecological processes.
3D Visualization: In some cases, 3D visualization techniques are used to represent ecological landscapes and terrain. This can aid in understanding topographical features and their influence on ecosystems.
Spatial data visualization techniques help ecologists and researchers communicate their findings effectively to both scientific and non-scientific audiences. They are particularly important in addressing complex spatial questions and informing conservation and resource management strategies.
Creating Maps
To create ecological maps using geospatial data in R, you can follow
these step-by-step instructions. In this example, we’ll use the rinat
package to acquire data from iNaturalist, but you can also
use other sources of geospatial data.
Step 1: Install and Load the Required Packages
Before creating ecological maps, make sure you have the necessary R
packages installed. You can install them using the
install.packages()
function if you haven’t
already:
# Load packages
::p_load(rinat,
pacman
tidyverse,
sf,install = T,
update = F)
# Search iNaturalist and download data for species observations
# uncomment line below to search and download data
# colibri <- rinat::get_inat_obs(taxon_name = "Colibri",
# quality = "research",
# maxresults = 500) %>%
# dplyr::as_tibble()
# save the data to csv file (for later use if internet drops)
# readr::write_csv(
# colibri,
# file = here::here("docs", "data", "colibri.csv"),
# col_names = TRUE,
# append = FALSE
# )
# Load data if above internet connection drops
<- readr::read_csv(file = here::here("docs", "data", "colibri.csv"),
colibri col_names = TRUE)
# Create a map of Colibri sp.
::ggplot(data = colibri, aes(x = longitude,
ggplot2y = latitude,
colour = scientific_name)) +
::geom_polygon(
ggplot2data = ggplot2::map_data("world"),
aes(x = long, y = lat, group = group),
fill = "grey90",
color = "gray20",
size = 0.1
+
) ::geom_point(cex = 3.5, alpha = 0.5) +
ggplot2::coord_fixed(
ggplot2xlim = range(colibri$longitude, na.rm = TRUE),
ylim = range(colibri$latitude, na.rm = TRUE)
+
) ::labs(
ggplot2x = "Longitude",
y = "Latitude",
colour = "Scientific Name"
+
) ::theme_bw() ggplot2
R Code Explanation
The necessary R packages are loaded.
Step 1: Load Packages
rinat
is used for accessing
iNaturalist data.
tidyverse
includes a collection of
packages for data manipulation and visualization.
sf
is used for working with spatial
data.
Step 2: Search iNaturalist Data
This step uses the rinat
package to
search iNaturalist data.
It looks for species observations of “Colibri” (hummingbirds) with the quality of “research” and a maximum of 500 results.
The data is then converted into a tibble for easier manipulation.
Step 3: Create a Map
This step creates a map of Colibri species observations.
ggplot2
is used to create the
map.
aes(x = longitude, y = latitude, colour = scientific_name)
specifies the aesthetics for the plot, where longitude and latitude are
on the x and y axes, and the color represents the scientific name of the
species.
geom_polygon
is used to add a world
map as the background with grey fill and grey border.
geom_point
adds points for the
Colibri species observations.
coord_fixed
fixes the aspect ratio
of the plot to ensure it’s geographically accurate.
labs
labels the axes and the color
scale.
theme_bw
applies a basic
black-and-white theme to the plot.
The code combines data from iNaturalist with geographic data to create a map showing the distribution of Colibri species. The points on the map represent individual observations, and their colors indicate different species of hummingbirds. The map is interactive, allowing users to zoom in and out and explore the distribution of these species.
Effective data visualization practices are essential for communicating findings in a clear and impactful way, especially in ecological research. Here are some key principles and guidelines for creating effective visualizations:
1. Simplicity
Less is More: Avoid cluttering your plots with unnecessary elements. Focus on the core message you want to convey.
Clear Labels: Ensure that labels for axes, data points, and legends are concise and easy to read.
Minimize Distractions: Remove distracting grid-lines, background colors, and decorations that don’t add value to the visualization.
2. Clarity
Data-Driven Storytelling: Your visualization should tell a story about your data. Choose visuals that help convey your intended message.
Consistency: Use consistent color schemes, fonts, and styles throughout your plots for a cohesive look.
Annotation: Add informative text or labels to highlight key findings, trends, or outliers in your data.
3. Right Visualization for the Message
Match Data to Visualization: Choose the type of plot that best represents your data. For example, use scatter plots for relationships, bar charts for comparisons, and maps for spatial data.
Consider the Audience: Tailor your visualizations to your target audience’s level of expertise. Avoid jargon and explain complex visuals when necessary.
4. Labeling and Legends
Axis Labels: Clearly label the x and y-axes, including units of measurement. Use meaningful, informative axis labels.
Legends: If your plot includes multiple series or categories, use a legend to explain what each color or symbol represents.
5. Color Usage
Color Palette: Choose a color palette that is both visually appealing and accessible to color-blind viewers. Tools like ColorBrewer can help.
Contrast: Ensure there’s enough contrast between data points and background to make the plot readable.
6. Data Integrity
Data Accuracy: Double-check your data for accuracy before creating visualizations. Errors in data will lead to misleading visuals.
Avoid Distortion: Be cautious when using 3D plots or perspective distortion, as they can distort the true relationships in the data.
7. Interactivity (when appropriate)
8. Testing and Feedback
User Testing: If possible, gather feedback from potential viewers to ensure your visualizations are easy to understand and interpret.
Iterate: Don’t hesitate to revise and refine your visuals based on feedback and changing data.
9. Ethical Considerations
Avoid Misrepresentation: Ensure your visualizations accurately represent the data and avoid manipulating visuals to mislead viewers.
Privacy: Respect data privacy and confidentiality when creating visualizations, especially with sensitive ecological data.
10. Accessibility
Effective data visualization in ecological research not only simplifies complex data but also enhances understanding and supports data-driven decisions. By adhering to these principles and guidelines, you can create visualizations that are not only informative but also visually engaging and impactful.
Interactive Ecological Visualization without Shiny
JavaScript Libraries: You can create interactive ecological visualizations using JavaScript libraries like D3.js, Plotly.js, or Leaflet.js. These libraries offer a wide range of interactive features that can be embedded in web pages or applications.
D3.js: D3.js (Data-Driven Documents) is a powerful JavaScript library for creating data visualizations that are highly customizable and interactive.
Plotly.js: Plotly.js provides interactive charting capabilities, including scatter plots, bar charts, and maps, which can be embedded in web pages.
Leaflet.js: Leaflet.js is excellent for creating interactive maps. It allows you to add markers, popups, and custom layers to display ecological data spatially.
R Packages: In R, you can create interactive
visualizations using packages that support interactivity. For instance,
the plotly
package can be used to create
interactive plots from R data frames.
HTML Widgets: R packages like
htmlwidgets
allow you to create
interactive visualizations and embed them in HTML documents. These
widgets can be easily shared online.
Python Libraries: If you’re working with Python, libraries like Bokeh and Plotly provide interactive plotting capabilities for ecological data.
Bokeh: Bokeh is a Python library that creates interactive, web-ready plots.
Plotly: Plotly for Python can generate interactive plots for data exploration.
Online Data Visualization Tools: Platforms like Tableau Public and Flourish offer user-friendly interfaces to create interactive visualizations without coding.
Storytelling: Regardless of the tool or library you choose, you can incorporate storytelling elements into your visualization by providing context, explanations, and annotations within the visualization or in accompanying text.
Interactive ecological visualizations help engage users, facilitate exploration, and convey insights effectively. Depending on your preferred programming language and tools, you can choose the best approach to create interactive and informative visualizations for your ecological research.
In this comprehensive journey through ecological data visualization, we’ve covered essential principles, techniques, and tools that equip you to create impactful visualizations for your ecological research. Here are the key takeaways from Chapter 6:
1. Principles of Effective Visualization:
Simplicity and clarity are paramount. Choose the right visualization type that conveys your message succinctly.
Thoughtful color choices and annotation can enhance understanding.
Label axes, provide legends, and include captions to make your visualizations self-explanatory.
Visualize data honestly, without distorting or exaggerating.
2. Interactivity and Storytelling:
Interactivity engages your audience, allowing them to explore data at their pace.
Storytelling adds context to your visualizations, turning them into compelling narratives.
JavaScript libraries like D3.js, Plotly.js, and Leaflet.js provide powerful tools for interactivity.
R and Python offer packages like
plotly
,
htmlwidgets
, and Bokeh for creating
interactive visualizations.
3. Tools for Spatial Data Visualization:
Spatial data plays a crucial role in ecological research.
Use libraries like Leaflet.js for creating interactive maps and visualizing geographic data.
R packages such as sf
(Simple
Features) enable spatial data manipulation and visualization.
4. Data Sharing and Reproducibility:
Share your visualizations through various means, including web hosting and sharing platforms.
Aim for reproducibility by documenting your data sources, code, and design choices.
5. Effective Data Communication:
Visualizations are powerful tools for communicating ecological findings.
Tailor your visualizations to your audience, whether they are scientists, policymakers, or the general public.
Use visualizations to support your research publications, presentations, and outreach efforts.
In conclusion, Chapter 6 empowers you with the skills to create compelling and informative visualizations that effectively communicate your ecological research findings. Whether you are presenting data distributions, exploring spatial patterns, or telling ecological stories, the tools and principles covered in this chapter will help you enhance the impact of your ecological research and foster a deeper understanding of the natural world.
In this exercise we will perform a simple hypothesis test using real-world data set. Data used in this exercise was extracted from the mendeley database (Win, Kyaw (2023), “Aboveground Tree Carbon of Teak Plantations in West Bago Mountains, Myanmar”, Mendeley Data, V1, doi: 10.17632/3xvcfskhwz.1): Aboveground Tree Carbon of Teak Plantations in West Bago Mountains, Myanmar.
Steps
Open “Filtered.sav” file in Jamovi. The data should already be placed in the “data” sub-directory.
Go to the “Variables” tab and remove the last four columns/ variables as we won’t use them.
Go to the “Data” tab and change the “Plantation_age” data/ measure type to “ordinal” via the “Setup” button.
Navigate to the “Analyses” tab and from the “Exploration” button select “Descriptives”. Use the functions from this window to explore the data set.
You can further perform data exploration visually. Select the “scatterplot” from the “Exploration” button and insert the appropriate variables to generate a scatterplot with linear fits along with density plots.
You can also perform correlation test including other statistical tests.
Formulating the Hypothesis: To assess the impact of plantation age on above-ground tree carbon content, we formulate our hypotheses:
Null Hypothesis (Ho): There are no significant differences in above-ground tree carbon content among different plantation ages.
Alternative Hypothesis (Ha): There are significant differences in above-ground tree carbon content among different plantation ages.
Selecting the Appropriate Test: To scrutinize these hypotheses, we opt for a two-way ANOVA. This choice aligns with our research objectives as we intend to explore variations in above-ground carbon content across multiple plantation ages.
Addressing Data Normality: As a prerequisite for conducting an ANOVA, we assess the normality of our response variable, ‘Aboveground_Tree_Carbon_ton_per_ha_per_year,’ using the Shapiro-Wilk test. The outcome reveals a significant effect (p < 0.001), implying that this variable doesn’t adhere to a normal distribution. Consequently, we pivot to the non-parametric equivalent, the “Kruskal-Wallis” test, as a robust alternative.
Executing the Kruskal-Wallis Test: Navigating to
the Analysis tab, we select the ANOVA button and then opt for the
“Kruskal-Wallis” test from the non-parametric section. The results
uncover a significant effect of plantation age on carbon content
(p < .001
). This substantiates the presence of
meaningful disparities in carbon content across plantation
ages.
Unearthing Specific Differences: To pinpoint where these differences manifest, we proceed with a pairwise comparison. This step elucidates the precise distinctions in carbon content among different plantation ages.
Visualizing Results: To provide a more intuitive understanding, we employ box plots as a visual aid. These plots vividly display the variations in above-ground tree carbon content across different plantation ages, enhancing our ability to interpret and communicate the findings.