Abstract

ABSTRACTEcosystem monitoring is fundamental to our understanding of how ecosystem change is impacting our natural resources and is vital for developing evidence‐based policy and management. However, the different types of ecosystem monitoring, along with their recommended applications, are often poorly understood and contentious. Varying definitions and strict adherence to a specific monitoring type can inhibit effective ecosystem monitoring, leading to poor program development, implementation and outcomes. In an effort to develop a more consistent and clear understanding of ecosystem monitoring programs, we here review the main types of monitoring and recommend the widespread adoption of three classifications of monitoring, namely, targeted, surveillance and landscape monitoring. Landscape monitoring is conducted over large areas, provides spatial data, and enables questions relating to where and when ecosystem change is occurring to be addressed. Surveillance monitoring uses standardised field methods to inform on what is changing in our environments and the direction and magnitude of that change, whilst targeted monitoring is designed around testable hypotheses over defined areas and is the best approach for determining the causes of ecosystem change. The classification system is flexible and can incorporate different interests, objectives, targets and characteristics as well as different spatial scales and temporal frequencies, while also providing valuable structure and consistency across distinct ecosystem monitoring programs. To support our argument, we examine the ability of each monitoring type to inform on six key types of questions that are routinely posed for ecosystem monitoring programs, such as where and when change is occurring, what is the magnitude of change, and how can the change be managed? As we demonstrate, each type of ecosystem monitoring has its own strengths and weaknesses, which should be carefully considered relative to the desired results. Using this scheme, scientists and land managers can design programs best suited to their needs. Finally, we assert that for our most serious environmental challenges, it is essential that we include information from each of these monitoring scales to inform on all facets of ecosystem change, and this is best achieved through close collaboration between the scales. With a renewed understanding of the importance of each monitoring type, along with greater commitment to monitor cooperatively, we will be well placed to address some of our greatest environmental challenges.

Highlights

  • Ecosystem monitoring is fundamental to our understanding of how ecosystem change is impacting our natural resources and is vital for developing evidence-based policy and management

  • These are: (i) what elements within the environment are changing? (ii) What is the direction and magnitude of that change? (iii) Where is environmental change occurring in the landscape? (iv) When is environmental change occurring and is the rate of change increasing or decreasing? (v) What is the cause of the environmental change we are observing? (vi) What action can be taken to ameliorate deleterious change and/or encourage positive change?

  • To help understand how different types of monitoring can provide essential information to deal with the significant challenges we have identified, we advocate for the classification of ecosystem monitoring into the framework of targeted monitoring, surveillance monitoring and landscape monitoring first described in Eyre et al (2011)

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Summary

MONITORING QUESTIONS AND CLASSIFICATIONS

Each year we expect ecosystem monitoring programs to answer a great number of questions and/or test and evaluate a range of hypotheses. Surveillance monitoring collects information to enable change detection on a wide variety of variables more so than identifying the cause, and as such, it is not essential to have a complete understanding of the ecosystem to conduct effective monitoring (Wallace, Caccetta, & Kiiveri, 2004) These broadly focused programs can be effective even under circumstances where the environmental drivers for the system are not fully known (Hutto & Belote, 2013). Remote-sensing techniques used in landscape monitoring can be applied consistently across vast areas, with some authors (Pettorelli et al, 2014a; Luque et al, 2018) claiming that remotely sensed data is the only way to obtain standardised biodiversity information over large areas in reasonable time periods This spatial focus means that this type of monitoring is often conducted by national research infrastructures (Cleverly et al, 2019), or groups of international cooperation such as the Group on Earth Observation (earthobservations.org), NASA and other similar groups. With the move to larger-scale continental and global analyses, requiring the integration of targeted, surveillance and landscape monitoring (Couvet et al, 2011; Ferreira, Rios-Saldana, & Delibes-Mateos, 2016) there will be an increased requirement for the scaling up of field information to validate imagery techniques with fieldbased monitoring data

WHY OUR SYSTEM NEEDS TO CONSIDER ALL MONITORING TYPES?
CONCLUSIONS
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