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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Plant Sci.</journal-id>
<journal-title>Frontiers in Plant Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Plant Sci.</abbrev-journal-title>
<issn pub-type="epub">1664-462X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fpls.2022.871859</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Plant Science</subject>
<subj-group>
<subject>Review</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>A review of remote sensing for potato traits characterization in precision agriculture</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Sun</surname> <given-names>Chen</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="fn002"><sup>&#x2020;</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Zhou</surname> <given-names>Jing</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="author-notes" rid="fn002"><sup>&#x2020;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1393292/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Ma</surname> <given-names>Yuchi</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1513328/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Xu</surname> <given-names>Yijia</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Pan</surname> <given-names>Bin</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Zhang</surname> <given-names>Zhou</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/659781/overview"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Biological Systems Engineering, University of Wisconsin-Madison</institution>, <addr-line>Madison, WI</addr-line>, <country>United States</country></aff>
<aff id="aff2"><sup>2</sup><institution>Key Laboratory of Spectral Imaging Technology, Xi&#x2019;an Institute of Optics and Precision Mechanics</institution>, <addr-line>Xi&#x2019;an</addr-line>, <country>China</country></aff>
<aff id="aff3"><sup>3</sup><institution>School of Statistics and Data Science, Nankai University</institution>, <addr-line>Tianjin</addr-line>, <country>China</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Zhihan Lv, Uppsala University, Sweden</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Ankush Prashar, Newcastle University, United Kingdom; Penghao Wang, Murdoch University, Australia</p></fn>
<corresp id="c001">&#x002A;Correspondence: Zhou Zhang, <email>zzhang347@wisc.edu</email></corresp>
<fn fn-type="equal" id="fn002"><p><sup>&#x2020;</sup>These authors have contributed equally to this work</p></fn>
<fn fn-type="other" id="fn004"><p>This article was submitted to Sustainable and Intelligent Phytoprotection, a section of the journal Frontiers in Plant Science</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>18</day>
<month>07</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>13</volume>
<elocation-id>871859</elocation-id>
<history>
<date date-type="received">
<day>08</day>
<month>02</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>29</day>
<month>06</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2022 Sun, Zhou, Ma, Xu, Pan and Zhang.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Sun, Zhou, Ma, Xu, Pan and Zhang</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract>
<p>Potato is one of the most significant food crops globally due to its essential role in the human diet. The growing demand for potato, coupled with severe environmental losses caused by extensive farming activities, implies the need for better crop protection and management practices. Precision agriculture is being well recognized as the solution as it deals with the management of spatial and temporal variability to improve agricultural returns and reduce environmental impact. As the initial step in precision agriculture, the traditional methods of crop and field characterization require a large input in labor, time, and cost. Recent developments in remote sensing technologies have facilitated the process of monitoring crops and quantifying field variations. Successful applications have been witnessed in the area of precision potato farming. Thus, this review reports the current knowledge on the applications of remote sensing technologies in precision potato trait characterization. We reviewed the commonly used imaging sensors and remote sensing platforms with the comparisons of their strengths and limitations and summarized the main applications of the remote sensing technologies in potato. As a result, this review could update potato agronomists and farmers with the latest approaches and research outcomes, as well as provide a selective list for those who have the intentions to apply remote sensing technologies to characterize potato traits for precision agriculture.</p>
</abstract>
<kwd-group>
<kwd>precision agriculture</kwd>
<kwd>remote sensing</kwd>
<kwd>satellite imagery</kwd>
<kwd>potato</kwd>
<kwd>unmanned aerial system</kwd>
<kwd>sensors</kwd>
</kwd-group>
<contract-sponsor id="cn001">U.S. Department of Agriculture<named-content content-type="fundref-id">10.13039/100000199</named-content></contract-sponsor>
<contract-sponsor id="cn002">Wisconsin Alumni Research Foundation<named-content content-type="fundref-id">10.13039/100001395</named-content></contract-sponsor>
<counts>
<fig-count count="0"/>
<table-count count="4"/>
<equation-count count="0"/>
<ref-count count="171"/>
<page-count count="20"/>
<word-count count="16484"/>
</counts>
</article-meta>
</front>
<body>
<sec id="S1" sec-type="intro">
<title>Introduction</title>
<p>Potato (<italic>Solanum tuberosum</italic> L.) is one of the most essential and commonly consumed non-grain food in the world. Due to its importance in the food industry supply chain, potato has become a dominant crop in many countries (<xref ref-type="bibr" rid="B109">Ortiz and Mares, 2017</xref>). For example, more than 23 million tons of potato tubers were harvested from about 940 thousand acres in the United States in 2019 (<xref ref-type="bibr" rid="B145">U. S. Department of Agriculture, 2020</xref>). Also, recently, the planting area and the total yield of potatoes have increased more than those of any other food crop in Africa. However, the continuously enhanced use of agricultural inputs (e.g., fertilizer and pesticide) could lead an environmental degradation, including the depletion of natural resources, polluted surface water and underground flows, and eutrophication (<xref ref-type="bibr" rid="B78">Kleinman et al., 2011</xref>; <xref ref-type="bibr" rid="B80">Konikow, 2015</xref>; <xref ref-type="bibr" rid="B135">Sishodia et al., 2017</xref>). Moreover, the over and/or inefficient use of water, fertilizers, pesticides, and herbicides for potato crops over the growing season causes economic losses and negative impacts on the environment (<xref ref-type="bibr" rid="B61">Hendricks et al., 2019</xref>). To constantly and sustainably meet the increasing needs for potato production, reducing environmental losses with improved potato productivity is the key topic in precision agricultural activities for potatoes (<xref ref-type="bibr" rid="B31">Delgado et al., 2019</xref>).</p>
<p>Traditionally, the effects of precision field activities, such as irrigation timing and frequency, fertilizer applications, planting dates, and population density, were determined through field surveying and/or biophysical modeling on crop growth and yield under different environmental conditions (<xref ref-type="bibr" rid="B99">Molahlehi et al., 2013</xref>; <xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>). Such methods commonly require visual examinations and destructive sampling and thus can be time-consuming with poor scalability. In the past few decades, the development of technologies, such as remote sensing, global positioning system, geographic information systems, artificial intelligence, has significantly promoted the applications in precision agriculture for enhancing crop production and quality while reducing the negative impacts on the environment in a more efficient way (<xref ref-type="bibr" rid="B102">Mulla, 2013</xref>). Precision agriculture has been gradually applied to monitor the crop growth status, generate auto-irrigation systems and disease detection systems in both developed and developing countries. Based on the interaction of electromagnetic radiation with soil and canopy reflectance, the remote sensing technique is considered as an effective tool in precision management for optimizing the decision-making process, which helps to improve profitable tuber yield and quality and minimize the negative impacts on the natural resources (<xref ref-type="bibr" rid="B13">Banerjee et al., 2020</xref>; <xref ref-type="bibr" rid="B129">Sanchez et al., 2020</xref>; <xref ref-type="bibr" rid="B139">Sun et al., 2020</xref>). Also, the data processing approaches, such as machine learning and image processing, have been widely used for extracting useful information from remotely sensed data (<xref ref-type="bibr" rid="B36">Dutta Gupta and Pattanayak, 2017</xref>; <xref ref-type="bibr" rid="B108">Oppenheim and Shani, 2017</xref>; <xref ref-type="bibr" rid="B138">Suh et al., 2018</xref>). Besides, cloud computing systems have been successfully used in data storing and processing for precision agriculture (<xref ref-type="bibr" rid="B167">Zhou et al., 2016b</xref>). Remote sensing systems, integrating advances in imaging, data processing, and computing technologies, thus have the potential to monitor the crop growth status and help make the decisions for crop management (<xref ref-type="bibr" rid="B112">Pav&#x00F3;n-Pulido et al., 2017</xref>; <xref ref-type="bibr" rid="B132">Say et al., 2017</xref>).</p>
<p>In recent years, information-based precision agriculture has been successfully applied to explore potato crop traits and field phenotyping (<xref ref-type="bibr" rid="B43">Fortin et al., 2011</xref>; <xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref>; <xref ref-type="bibr" rid="B44">Franceschini et al., 2017a</xref>; <xref ref-type="bibr" rid="B113">Pei et al., 2019</xref>). Potatoes are stem tubers that are concealed in soils over the growing season. After being seeded in the soil, the top sides of the tuber produce shoot that grow into typical stems and leaves, and the undersides produce roots (<xref ref-type="bibr" rid="B77">Khayatnezhad et al., 2011</xref>). By establishing the relationship between traits of the aboveground parts and the underground tubers, remote sensing techniques have great potential in estimating the tuber growth conditions and predicting tuber yield prior to harvest (<xref ref-type="bibr" rid="B133">Shayanowako et al., 2014</xref>). Compared with traditional sampling methods, remote sensing is capable of providing a non-destructive and efficient way to collect the multi-temporal reflectance data of the aboveground plants for monitoring the biomarkers of potato crops (<xref ref-type="bibr" rid="B107">Nikolakopoulos et al., 2017</xref>; <xref ref-type="bibr" rid="B42">Feng et al., 2020</xref>). Past studies have focused on the specific applications of potatoes in precision agriculture using remote sensing approaches, such as tuber yield prediction (<xref ref-type="bibr" rid="B3">Akhand et al., 2016</xref>; <xref ref-type="bibr" rid="B159">Zaeen et al., 2020</xref>), above-ground biomass (AGB) estimation (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>; <xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref>), water stress detection (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>), nitrogen stress assessment (<xref ref-type="bibr" rid="B16">Bohman et al., 2019</xref>), and disease detection (<xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref>; <xref ref-type="bibr" rid="B45">Franceschini et al., 2017b</xref>,<xref ref-type="bibr" rid="B46">2019</xref>; <xref ref-type="bibr" rid="B115">Polder et al., 2019</xref>). Most of these studies demonstrated the strengths of remote sensing techniques along with their limitations and future challenges for the applications in potato production.</p>
<p>The primary purpose of this review is to provide a comprehensive background and knowledge on applications of remote sensing technologies in potato trait characterization in the context of precision agriculture. Both Web of Science and Google Scholar databases were used for literature review with keywords or topics of potato remote sensing from 2010 to the present. This paper is organized in the following main aspects: (1) compare the strengths and limitations of a variety of imaging sensors and remote sensing platforms and (2) summarize the remote sensing techniques adopted for the specific applications of potatoes in precision agriculture.</p>
</sec>
<sec id="S2">
<title>Imaging sensors</title>
<p>Remote sensing for crop trait characterization broadly involves a series of techniques in sensing, recording, analyzing, and/or modeling. When incident radiation (light source or natural light) hits plant surface, the radiation will either be absorbed, transmitted, or reflected. The reflected radiation is expressed as the electromagnetic spectrum with a range of wavelengths. The sensing technologies include developing devices to capture the reflected spectrum and convert them into readable signals for further analysis (<xref ref-type="bibr" rid="B156">Xie and Yang, 2020</xref>).</p>
<p>When choosing sensors for a specific purpose, image temporal, spatial, and spectral resolutions are the three main factors to consider. Temporal resolution refers to the time window between two images over the same place. Spatial resolution refers to the size of the smallest objects that can be captured and displayed in the imagery. Spectral resolution refers to the ability of a sensor to measure specific wavelengths of the electromagnetic spectrum and it is mainly decided by the sensor types.</p>
<p>Within the context of potato trait characterization, a variety of sensors has been developed and applied for different purposes. The sensors, varying in their spatial and temporal resolutions, mainly include visible Red-Green-Blue (RGB) cameras, multi- and hyper-spectral cameras, thermal infrared (TIR) cameras, and light detection and ranging (LiDAR) sensors. In this section, we summarized the sensors that have been applied in characterizing potato traits with comparisons of their strengths and limitations.</p>
<sec id="S2.SS1">
<title>Visible red-green-blue cameras</title>
<p>Visible RGB cameras receive lights in red (564&#x2013;580 nm), green (534&#x2013;545 nm), and blue (420&#x2013;440 nm) board spectral bands in the visible spectrum regions to emulate human vision. Due to the broad applicability of RGB cameras in all the fields, they are well-developed products by private sectors with a large selective range in price, sensor sizes, lens availability, data storage, and transmission. For characterizing crop traits, the RGB cameras generally have the best performance in providing high spatial-resolution images with the ability to be associated with various sensing environments, which makes them the most commonly adopted sensors in the areas of remote sensing.</p>
<p>Applications in potato trait characterization have been leveraging the advantages of RGB images in different ways. In potato, studies have been conducted on quantifying disease severity using the RGB images by detecting pixels of diseased leaves with that of healthy leaves and soil. It was shown that the diseased leaves could be clearly distinguished from the transformed color spaces (<xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref>) or spectral indices (<xref ref-type="bibr" rid="B53">Gibson-Poole et al., 2017</xref>; <xref ref-type="bibr" rid="B134">Siebring et al., 2019</xref>) from the RGB color space. Also due to the contrast between plant and soil background captured by the RGB image, promising applications have been seen in detecting potato emergence (<xref ref-type="bibr" rid="B52">Gibson-Poole et al., 2018</xref>; <xref ref-type="bibr" rid="B84">Li et al., 2019</xref>) and calculating ground vegetation coverage (<xref ref-type="bibr" rid="B52">Gibson-Poole et al., 2018</xref>). Other than the color-based features, high resolution images from the RGB cameras can be used to reconstruct three-dimensional (3D) dense point models using photogrammetry methods. Plant height is then obtained by subtracting the digital elevation model (DEM) which represents the absolute elevation of the bare ground from the digital surface model (DSM) which represents the absolute height of the plant canopies. <xref ref-type="bibr" rid="B85">Li B. et al. (2020)</xref> compared the performance in estimating potato plant height from the RGB 3D models with the plant height regressed from the hyperspectral reflectance and the results showed that the RGB 3D models lead to a higher correlation with the ground truth data [Coefficient of determination <italic>R</italic><sup>2</sup> = 0.93, root mean square error (RMSE) = 6.39 cm] than the full spectra regression (<italic>R</italic><sup>2</sup> = 0.85, RMSE = 7.24 cm).</p>
<p>Compared with other sensors, the RGB cameras provide an intuitive way to visualize and quantify crop traits. RGB cameras are typically low-cost, lightweight, and can be easily mounted on various platforms for data collection. However, three spectral bands and the broad bandwidth of the RGB cameras limit their ability to receive crop traits other than human perceptions and consequently their applications in sensing more complicated crop traits, such as yield and nutrient deficit. Besides, it requires extra efforts to remove background noises from the RGB images under certain situations when the plants have similar visual colors to the background or when plants are covered with shadows and other plants (<xref ref-type="bibr" rid="B89">Li et al., 2014</xref>).</p>
</sec>
<sec id="S2.SS2">
<title>Multi- and hyper-spectral cameras</title>
<p>Multi- and hyper-spectral cameras provide information with higher spectral resolutions than the RGB cameras and spectral bands additional to the visible range. The multispectral cameras usually consist of a small number (less than 10) of discrete wavebands in the visible-near infrared range from 400 to 1,000 nm. The spectral wavebands usually are narrower RGB bands and those with prior knowledge of their sensitivity in receiving important crop information (<xref ref-type="bibr" rid="B64">Hunt et al., 2013</xref>), such as red edge (700&#x2013;730 nm) and NIR (760&#x2013;900 nm). There are two types of multispectral cameras currently used in precision agriculture, that is, customized and commercial off-the-shelf cameras. As suggested by the name, the customized camera has the internal NIR filter removed from a visible RGB camera and is then replaced with an external filter to alter the camera spectral sensitivity (<xref ref-type="bibr" rid="B168">Zhou et al., 2016a</xref>), for example, from R-G-B to R-G-NIR. The commercial multispectral cameras are explicitly made with an interference filter to block or transmit specific lights (<xref ref-type="bibr" rid="B156">Xie and Yang, 2020</xref>). Compared with the customized camera, the commercial ones can provide more than three wavebands with other selectable spectral regions, but with lower spatial resolutions (<xref ref-type="table" rid="T1">Table 1</xref>).</p>
<table-wrap position="float" id="T1">
<label>TABLE 1</label>
<caption><p>Sensors and their applications in potato trait characterization.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Sensors</td>
<td valign="top" align="left">Manufacturers</td>
<td valign="top" align="left">Models</td>
<td valign="top" align="center">Image resolution</td>
<td valign="top" align="center">Spectral range (nm)</td>
<td valign="top" align="center">No. of bands</td>
<td valign="top" align="center">Applications</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Visible red&#x2013;green&#x2013;blue (RGB)</td>
<td valign="top" align="left">DJI</td>
<td valign="top" align="left">Phantom 4 Pro</td>
<td valign="top" align="center">5,472 &#x00D7; 3,648</td>
<td valign="top" align="center">400&#x2013;700</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Plant height estimation (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>); Disease detection (<xref ref-type="bibr" rid="B137">Sugiura et al., 2018</xref>); Emergence estimation (<xref ref-type="bibr" rid="B84">Li et al., 2019</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Sony</td>
<td valign="top" align="left">NEX-5N</td>
<td valign="top" align="center">1,920 &#x00D7; 1,080</td>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Canon</td>
<td valign="top" align="left">A2200</td>
<td valign="top" align="center">4,320 &#x00D7; 3,240</td>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B53">Gibson-Poole et al., 2017</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">ELPH 115 IS</td>
<td valign="top" align="center">4,608 &#x00D7; 3,456</td>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Growth status prediction (<xref ref-type="bibr" rid="B52">Gibson-Poole et al., 2018</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Panasonic</td>
<td valign="top" align="left">GX1</td>
<td valign="top" align="center">4,592 &#x00D7; 3,448</td>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B134">Siebring et al., 2019</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Multispectral</td>
<td valign="top" align="left">Tetracam</td>
<td valign="top" align="left">Micro-MCA RGB + 3</td>
<td valign="top" align="center">1,280 &#x00D7; 1,024</td>
<td valign="top" align="center">350&#x2013;950</td>
<td valign="top" align="center">6</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B141">Tanabe et al., 2019</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">ADC Lite</td>
<td valign="top" align="center">2,048 &#x00D7; 1,536</td>
<td valign="top" align="center">520&#x2013;920</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Crop scouting (<xref ref-type="bibr" rid="B144">Th&#x00E9;au et al., 2020</xref>); Insect detection (<xref ref-type="bibr" rid="B67">Hunt et al., 2016</xref>); nitrogen stress estimation (<xref ref-type="bibr" rid="B67">Hunt et al., 2016</xref>, <xref ref-type="bibr" rid="B65">2018</xref>; <xref ref-type="bibr" rid="B66">Hunt and Rondon, 2017</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Mini-MCA</td>
<td valign="top" align="center">1,280 &#x00D7; 1,024</td>
<td valign="top" align="center">450&#x2013;1,000</td>
<td valign="top" align="center">6</td>
<td valign="top" align="left">Beetle damage assessment (<xref ref-type="bibr" rid="B66">Hunt and Rondon, 2017</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Kodak</td>
<td valign="top" align="left">Megaplus 4.2i cameras (customized)</td>
<td valign="top" align="center">2,024 &#x00D7; 2,044</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B130">Sankaran et al., 2015</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Canon</td>
<td valign="top" align="left">S95 (customized)</td>
<td valign="top" align="center">3,648 &#x00D7; 2,736</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">4</td>
<td valign="top" align="left">Chlorophyll content estimation (<xref ref-type="bibr" rid="B38">Elarab et al., 2015</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">S110 (customized)</td>
<td valign="top" align="center">4,000 &#x00D7; 3,000</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref>; <xref ref-type="bibr" rid="B33">Duarte-Carvajalino et al., 2018</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Powershot ELPH 340 HS (customized)</td>
<td valign="top" align="center">4,608 &#x00D7; 3,456</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Growth status estimation (<xref ref-type="bibr" rid="B144">Th&#x00E9;au et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">ELPH 110 (customized)</td>
<td valign="top" align="center">4,608 &#x00D7; 3,456</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Hail damage assessment (<xref ref-type="bibr" rid="B168">Zhou et al., 2016a</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Redlake</td>
<td valign="top" align="left">MS4100</td>
<td valign="top" align="center">1,920 &#x00D7; 1,080</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Nitrogen stress prediction (<xref ref-type="bibr" rid="B106">Nigon et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">MicaSense</td>
<td valign="top" align="left">RedEdge</td>
<td valign="top" align="center">1,280 &#x00D7; 960</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">5</td>
<td valign="top" align="left">Structural change (<xref ref-type="bibr" rid="B7">Angulo-Morales et al., 2020</xref>); Radiation use efficiency assessment (<xref ref-type="bibr" rid="B114">Peng et al., 2021</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Hyperspectral</td>
<td valign="top" align="left">Headwall</td>
<td valign="top" align="left">Nano-Hyperspec</td>
<td valign="top" align="center">640 &#x00D7; 1</td>
<td valign="top" align="center">400&#x2013;1,000</td>
<td valign="top" align="center">270</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>; <xref ref-type="bibr" rid="B139">Sun et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Specim</td>
<td valign="top" align="left">ImSpector V10 2/3&#x201D;</td>
<td valign="top" align="center">Depending on the combined imager</td>
<td valign="top" align="center">400&#x2013;950</td>
<td valign="top" align="center">61</td>
<td valign="top" align="left">Chlorophyll content assessment, leaf area index (LAI) estimation and ground cover assessment (<xref ref-type="bibr" rid="B44">Franceschini et al., 2017a</xref>); nitrogen stress detection (<xref ref-type="bibr" rid="B105">Nigon et al., 2015</xref>); canopy changes assessment (<xref ref-type="bibr" rid="B45">Franceschini et al., 2017b</xref>); crop growth assessment (<xref ref-type="bibr" rid="B50">Gevaert et al., 2014</xref>); Reflectance anisotropy measurements (<xref ref-type="bibr" rid="B125">Roosjen et al., 2016</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Cubert</td>
<td valign="top" align="left">UHD 185</td>
<td valign="top" align="center">1,000 &#x00D7; 1,000</td>
<td valign="top" align="center">450&#x2013;950</td>
<td valign="top" align="center">125</td>
<td valign="top" align="left">Chlorophyll content assessment (<xref ref-type="bibr" rid="B86">Li C. et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Rikola</td>
<td valign="top" align="left">Fabry-Perot interferometer</td>
<td valign="top" align="center">1,010 &#x00D7; 1,010</td>
<td valign="top" align="center">500&#x2013;900</td>
<td valign="top" align="center">16</td>
<td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B46">Franceschini et al., 2019</xref>); Chlorophyll content assessment and LAI estimation (<xref ref-type="bibr" rid="B124">Roosjen et al., 2018</xref>); Reflectance anisotropy assessment (<xref ref-type="bibr" rid="B126">Roosjen et al., 2017</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Thermal infrared</td>
<td valign="top" align="left">Infrared cameras</td>
<td valign="top" align="left">Microbolometer</td>
<td valign="top" align="center">640 &#x00D7; 480</td>
<td valign="top" align="center">7,000&#x2013;14,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Chlorophyll content assessment (<xref ref-type="bibr" rid="B38">Elarab et al., 2015</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Wilsonville</td>
<td valign="top" align="left">TAU 640</td>
<td valign="top" align="center">640 &#x00D7; 512</td>
<td valign="top" align="center">7,500&#x2013;13,500</td>
<td valign="top" align="left"/><td valign="top" align="left">Crop scouting (<xref ref-type="bibr" rid="B144">Th&#x00E9;au et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">FLIR</td>
<td valign="top" align="left">E60</td>
<td valign="top" align="center">320 &#x00D7; 240</td>
<td valign="top" align="center">7,500&#x2013;13,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B26">Cucho-Padin et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">FLIR</td>
<td valign="top" align="left">SC2000</td>
<td valign="top" align="center">320 &#x00D7; 240</td>
<td valign="top" align="center">7,500&#x2013;13,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">FLIR</td>
<td valign="top" align="left">SC655</td>
<td valign="top" align="center">640 &#x00D7; 480</td>
<td valign="top" align="center">7,500&#x2013;13,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">JeanOptics</td>
<td valign="top" align="left">IDM200</td>
<td valign="top" align="center">640 &#x00D7; 480</td>
<td valign="top" align="center">7,500&#x2013;13,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Fluke</td>
<td valign="top" align="left">Ti-32</td>
<td valign="top" align="center">320 &#x00D7; 240</td>
<td valign="top" align="center">7,500&#x2013;14,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Fluke</td>
<td valign="top" align="left">TiR1</td>
<td valign="top" align="center">160 &#x00D7; 120</td>
<td valign="top" align="center">7,500&#x2013;14,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B48">Gerhards et al., 2016</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Telops</td>
<td valign="top" align="left">HyperCamLW</td>
<td valign="top" align="center">320 &#x00D7; 256</td>
<td valign="top" align="center">7,700&#x2013;11,500</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B48">Gerhards et al., 2016</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Palmer Wahl Instruments</td>
<td valign="top" align="left">HSI3000</td>
<td valign="top" align="center">160 &#x00D7; 120</td>
<td valign="top" align="center">8,000&#x2013;14,000</td>
<td valign="top" align="left"/><td valign="top" align="left">Water status (<xref ref-type="bibr" rid="B51">Ghazouani et al., 2017</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Light detection and ranging (LiDAR)</td>
<td valign="top" align="left">RIEGL</td>
<td valign="top" align="left">VUX-1</td>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">Crop height and biomass estimation (<xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref>)</td>
</tr>
</tbody>
</table></table-wrap>
<p>By integrating both spectroscopic and imaging techniques into one system, hyperspectral cameras provide 3D hyperspectral cubes that contain both contiguous spectral information and two-dimensional spatial information. There are four types of hyperspectral cameras based on their image acquisition methods, namely point scanning, line scanning, area scanning, and snapshot cameras (<xref ref-type="bibr" rid="B155">Wu and Sun, 2013</xref>). The line scanning, also known as the pushbroom cameras, records a line of an image at each time and then forms the whole image by scanning along the other direction. The line scanning cameras are particularly suitable for being carried on imaging platforms that follow certain moving patterns (e.g., zigzag paths) to cover a large field and thus are the most popular ones in precision agricultural applications (<xref ref-type="bibr" rid="B156">Xie and Yang, 2020</xref>). Compared with the multispectral camera, hyperspectral cameras provide a real spectrum in every image pixel, allowing to calculate advanced vegetation indices (VIs) and estimate unperceived crop phenotypes. However, hyperspectral cameras have more restrictions on reflectance calibration procedures and moving patterns and they are more costly both in the devices and data storage (<xref ref-type="bibr" rid="B89">Li et al., 2014</xref>).</p>
<p>The spectral cameras have been widely used to predict potato leave biomass (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>; <xref ref-type="bibr" rid="B114">Peng et al., 2021</xref>)/tube yield (<xref ref-type="bibr" rid="B130">Sankaran et al., 2015</xref>; <xref ref-type="bibr" rid="B141">Tanabe et al., 2019</xref>; <xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>; <xref ref-type="bibr" rid="B139">Sun et al., 2020</xref>), detect canopy damage/disease (<xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref>; <xref ref-type="bibr" rid="B66">Hunt and Rondon, 2017</xref>; <xref ref-type="bibr" rid="B33">Duarte-Carvajalino et al., 2018</xref>; <xref ref-type="bibr" rid="B46">Franceschini et al., 2019</xref>), and estimate potato biophysical properties, such as chlorophyll content (<xref ref-type="bibr" rid="B38">Elarab et al., 2015</xref>; <xref ref-type="bibr" rid="B44">Franceschini et al., 2017a</xref>; <xref ref-type="bibr" rid="B86">Li C. et al., 2020</xref>), nitrogen concentrations (<xref ref-type="bibr" rid="B106">Nigon et al., 2014</xref>, <xref ref-type="bibr" rid="B105">2015</xref>; <xref ref-type="bibr" rid="B66">Hunt and Rondon, 2017</xref>; <xref ref-type="bibr" rid="B65">Hunt et al., 2018</xref>), and leaf area index (LAI, <xref ref-type="bibr" rid="B44">Franceschini et al., 2017a</xref>). Among them, disease detection is the common application of visible RGB and spectral cameras. Unlike separating the healthy and unhealthy leaf areas in RGB images, spectral cameras are used to investigate the relationship between spectral measurements and disease severity at plot/field level. For example, the normalized difference vegetation index (NDVI) combined with spectral reflectance values in NIR and R was able to highlight sites infested by blight disease in a large potato field (<xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref>). <xref ref-type="bibr" rid="B9">Atherton et al. (2015)</xref> also reported that heavily diseased plants had significantly different spectral profiles from healthy plants.</p>
</sec>
<sec id="S2.SS3">
<title>Thermal infrared cameras</title>
<p>Radiation emitted by objects in the longwave infrared range (8&#x2013;1.3 &#x03BC;m) is proportional to their surface temperature, which can be exploited for remote measurements of plant canopy temperature using TIR cameras (<xref ref-type="bibr" rid="B82">Kuenzer and Dech, 2013</xref>; <xref ref-type="bibr" rid="B153">Williams et al., 2018</xref>). Plant canopy temperature has been used as an indicator of plant stomatal traits (e.g., stomatal conductance, stomatal aperture, or leaf porosity) because leaves surfaces are cooled by evaporation, and stomatal opening or higher transpiration rates lead to high evaporation rates (i.e., decreased temperatures; <xref ref-type="bibr" rid="B28">Deery et al., 2019</xref>). In plant science and agronomy, measuring plant leaf temperature using thermal imaging has long been used to study the mechanisms behind plant water relations (<xref ref-type="bibr" rid="B19">Chaerle and Van Der Straeten, 2000</xref>), plant physiology processes (<xref ref-type="bibr" rid="B73">Jones et al., 2002</xref>; <xref ref-type="bibr" rid="B4">Aldea et al., 2006a</xref>; <xref ref-type="bibr" rid="B57">Grant et al., 2010</xref>), plant responses to pathogens (<xref ref-type="bibr" rid="B18">Chaerle et al., 1999</xref>) or environmental stressors (<xref ref-type="bibr" rid="B72">Jones et al., 2009</xref>), and plant photosynthetic rate (<xref ref-type="bibr" rid="B5">Aldea et al., 2006b</xref>; <xref ref-type="bibr" rid="B150">V&#x00ED;tek et al., 2020</xref>). In the area of precision agriculture, substantial interests have been witnessed in irrigation scheduling (<xref ref-type="bibr" rid="B90">Li et al., 2022</xref>), yield prediction (<xref ref-type="bibr" rid="B15">Bellis et al., 2022</xref>), evapotranspiration estimation (<xref ref-type="bibr" rid="B94">Lu et al., 2022</xref>; <xref ref-type="bibr" rid="B154">Wolff et al., 2022</xref>), pre-symptomatic diagnosis (<xref ref-type="bibr" rid="B24">Cohen et al., 2022</xref>), and stress tolerance (<xref ref-type="bibr" rid="B166">Zhou et al., 2020</xref>; <xref ref-type="bibr" rid="B29">Degani et al., 2022</xref>; <xref ref-type="bibr" rid="B123">Rippa et al., 2022</xref>).</p>
<p>In potato applications, TIR cameras are primarily used to evaluate potato water status. Plant water stress indicators, for example the Crop water stress index (CWSI), were calculated using TIR image-derived temperature and validated by comparing with biophysical measurements of plant water status. Related studies showed that the TIR image-based indices highly agreed with the ground measurements and were able to reflect the effects of different irrigation treatments (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>; <xref ref-type="bibr" rid="B48">Gerhards et al., 2016</xref>; <xref ref-type="bibr" rid="B26">Cucho-Padin et al., 2020</xref>; <xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref>). In some other applications, the TIR cameras were used as an aid tool for spectral cameras for detecting pest stress (<xref ref-type="bibr" rid="B144">Th&#x00E9;au et al., 2020</xref>) or assessing chlorophyll content (<xref ref-type="bibr" rid="B38">Elarab et al., 2015</xref>).</p>
<p>The TIR cameras are the most effective tool in remotely sensing plant leaf/canopy temperature and water-related status. In practical, pre-calibration and post-correction procedures are required for receiving reliable temperature readings from the TIR cameras especially under changing ambient environmental factors such as air temperature, humidity, and wind speed (<xref ref-type="bibr" rid="B72">Jones et al., 2009</xref>; <xref ref-type="bibr" rid="B71">Jin et al., 2021</xref>). Additionally, the low spatial resolutions of the TIR cameras (<xref ref-type="table" rid="T1">Table 1</xref>) make them easily affected by image background temperature. It is also reported by <xref ref-type="bibr" rid="B144">Th&#x00E9;au et al. (2020)</xref> that spectral indices (including visible ones) would be preferred over the TIR indices when both performed similarly in detecting various plant characteristics.</p>
</sec>
<sec id="S2.SS4">
<title>Light detection and ranging system</title>
<p>Light detection and ranging (or laser scanner) sensors are used to obtain depth information of targeted objects. A LiDAR device has a single-beam laser (narrowband in 600&#x2013;1,000 nm) that emits a light pulse and a receiver measures the propagation time of the light pulse from emission to reflection. The time is then converted into a distance given the known speed of light (<xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref>). LiDAR devices are lightweight with compact sizes and thus can be easily integrated on different platforms. Unmanned aerial vehicle (UAV)-based LiDAR systems have been applied to map the 3D structure of the plant canopy and topography of the landscape (<xref ref-type="bibr" rid="B92">Lin et al., 2019</xref>; <xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref>). UAV-based LiDAR devices were reported to deliver accurate estimations of plant height with the RMSE of 0.02, 0.07, and 0.12 m compared with the manual measurements on snap bean crops (<xref ref-type="bibr" rid="B162">Zhang et al., 2021</xref>), sugar beet, and potato (<xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref>), respectively. However, LiDAR devices can be expensive and require longer imaging times, compared to other stereo vision methods from images for 3D mapping.</p>
</sec>
</sec>
<sec id="S3">
<title>Remote sensing platforms for data collection</title>
<p>In precision agriculture, a variety of remote sensing platforms have been developed and applied for different purposes, mainly including ground and aerial platforms. The ground platforms provide higher spatial and temporal resolution imagery than the aerial platforms and generally do not require a specific certificate to operate. Depending on the structural differences, four types of ground platforms are often seen, namely pole-based, cable-suspended, tractor, and gantry platforms (<xref ref-type="bibr" rid="B87">Li et al., 2021b</xref>). However, due to the limited spatial coverage, vibrations, and causes of soil compaction, ground platforms are challenged to be used in large-scale applications (<xref ref-type="bibr" rid="B130">Sankaran et al., 2015</xref>), such as potato precision management. Thus in this section, we focused on the aerial platforms that have been largely applied in precision potato management, that is, satellite-based and UAV-based platforms, with comparisons of their strengths and limitations.</p>
<sec id="S3.SS1">
<title>Satellite-based remote sensing platforms</title>
<p>Satellite imagery, as one of the remote sensing means, began more than half a century ago and has been used efficiently in multiple agricultural applications (<xref ref-type="bibr" rid="B97">Ma et al., 2021</xref>; <xref ref-type="bibr" rid="B152">Wang Y. et al., 2021</xref>). Its major benefits include non-destructive capture of the earth surface at wide geographical regions (hundreds of square kilometers in a single image), selectable revisit time (1 day&#x2013;2 weeks), and sensors with high spatial and spectral resolutions (<xref ref-type="bibr" rid="B161">Zhang et al., 2020</xref>). In recent years, a number of studies have investigated the potential of using satellite-based remote sensing platforms for precision potato management activities. The specifications for eleven representative platforms and their corresponding applications in precision potato management have been summarized in <xref ref-type="table" rid="T2">Table 2</xref>.</p>
<table-wrap position="float" id="T2">
<label>TABLE 2</label>
<caption><p>Satellite-based remote sensing platforms and their applications in potato trait characterization.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Satellite</td>
<td valign="top" align="left">Instrument</td>
<td valign="top" align="center">Spatial resolution (m/pixel)</td>
<td valign="top" align="center">Temporal resolution (days)</td>
<td valign="top" align="center">Spectral range (nm)</td>
<td valign="top" align="center">No. of bands</td>
<td valign="top" align="left">Applications</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Terra</td>
<td valign="top" align="left">Moderate Resolution Imaging Spectroradiometer (MODIS)</td>
<td valign="top" align="center">250&#x2013;1,000</td>
<td valign="top" align="center">1&#x2013;2</td>
<td valign="top" align="center">400&#x2013;1,440</td>
<td valign="top" align="center">36</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B128">Salvador et al., 2020</xref>); disease assessment (<xref ref-type="bibr" rid="B34">Dutta et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">Advanced Spaceborne Thermal Emission and Reflection Radiometer (ASTER)</td>
<td valign="top" align="center">15&#x2013;90</td>
<td valign="top" align="center">4&#x2013;16</td>
<td valign="top" align="center">500&#x2013;12,000</td>
<td valign="top" align="center">14</td>
<td valign="top" align="left">Herbicide rate assessment (<xref ref-type="bibr" rid="B147">Van Evert et al., 2012</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Planet scope</td>
<td valign="top" align="left">PS2</td>
<td valign="top" align="center">3</td>
<td valign="top" align="center">1</td>
<td valign="top" align="center">455&#x2013;860</td>
<td valign="top" align="center">4</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B1">Abou Ali et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Resourcesat-1</td>
<td valign="top" align="left">Advanced Wide Field Sensor (AWiFS)</td>
<td valign="top" align="center">56</td>
<td valign="top" align="center">5</td>
<td valign="top" align="center">520&#x2013;1,700</td>
<td valign="top" align="center">3</td>
<td valign="top" align="left">Disease assessment (<xref ref-type="bibr" rid="B34">Dutta et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Sentinel-2</td>
<td valign="top" align="left">Multispectral Instrument (MSI)</td>
<td valign="top" align="center">10&#x2013;60</td>
<td valign="top" align="center">5</td>
<td valign="top" align="center">400&#x2013;2,190</td>
<td valign="top" align="center">13</td>
<td valign="top" align="left">Leaf area index (LAI) and chlorophyll content estimation (<xref ref-type="bibr" rid="B63">Herrmann et al., 2011</xref>; <xref ref-type="bibr" rid="B22">Clevers and Kooistra, 2012</xref>; <xref ref-type="bibr" rid="B21">Clevers and Gitelson, 2013</xref>; <xref ref-type="bibr" rid="B23">Clevers et al., 2017</xref>); Radiation utilization assessment (<xref ref-type="bibr" rid="B114">Peng et al., 2021</xref>); Yield prediction (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>; <xref ref-type="bibr" rid="B56">G&#x00F3;mez et al., 2019</xref>; <xref ref-type="bibr" rid="B1">Abou Ali et al., 2020</xref>); crop mapping (<xref ref-type="bibr" rid="B8">Ashourloo et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Sentinel-3</td>
<td valign="top" align="left">The Ocean and Land Color Instrument (OLCI)</td>
<td valign="top" align="center">300</td>
<td valign="top" align="center">27</td>
<td valign="top" align="center">400&#x2013;1,020</td>
<td valign="top" align="center">21</td>
<td valign="top" align="left">Nitrogen stress prediction (<xref ref-type="bibr" rid="B21">Clevers and Gitelson, 2013</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Landsat-5</td>
<td valign="top" align="left">Thematic Mapper (TM)</td>
<td valign="top" align="center">30&#x2013;120</td>
<td valign="top" align="center">16</td>
<td valign="top" align="center">450&#x2013;12,500</td>
<td valign="top" align="center">7</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B104">Newton et al., 2018</xref>); LAI and Crop height estimation (<xref ref-type="bibr" rid="B110">Papadavid et al., 2011</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Landsat-7</td>
<td valign="top" align="left">Enhanced Thematic Mapper Plus (ETM+)</td>
<td valign="top" align="center">15&#x2013;60</td>
<td valign="top" align="center">16</td>
<td valign="top" align="center">450&#x2013;12,500</td>
<td valign="top" align="center">8</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B104">Newton et al., 2018</xref>; <xref ref-type="bibr" rid="B11">Awad, 2019</xref>); LAI and Crop height estimation (<xref ref-type="bibr" rid="B110">Papadavid et al., 2011</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Landsat-8</td>
<td valign="top" align="left">Operational Land Imager (OLI)</td>
<td valign="top" align="center">30</td>
<td valign="top" align="center">16</td>
<td valign="top" align="center">433&#x2013;1,390</td>
<td valign="top" align="center">9</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>; <xref ref-type="bibr" rid="B104">Newton et al., 2018</xref>; <xref ref-type="bibr" rid="B11">Awad, 2019</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Formosat-2</td>
<td valign="top" align="left">Remote Sensing Instrument</td>
<td valign="top" align="center">8</td>
<td valign="top" align="center">1</td>
<td valign="top" align="center">450&#x2013;900</td>
<td valign="top" align="center">4</td>
<td valign="top" align="left">Spectral-Temporal Response Surfaces (STRS) estimation (<xref ref-type="bibr" rid="B49">Gevaert et al., 2015</xref>); Crop growth assessment (<xref ref-type="bibr" rid="B50">Gevaert et al., 2014</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Proba-1</td>
<td valign="top" align="left">Compact High Resolution Imaging Spectrometer (CHRIS)</td>
<td valign="top" align="center">18</td>
<td valign="top" align="center">2</td>
<td valign="top" align="center">400&#x2013;1,050</td>
<td valign="top" align="center">19</td>
<td valign="top" align="left">LAI estimation (<xref ref-type="bibr" rid="B10">Atzberger and Richter, 2012</xref>; <xref ref-type="bibr" rid="B30">Delegido et al., 2013</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Polar Orbiting Environmental Satellites (POES)</td>
<td valign="top" align="left">The Advanced Very High-Resolution Radiometer (AVHRR)</td>
<td valign="top" align="center">1,100</td>
<td valign="top" align="center">7/14</td>
<td valign="top" align="center">580&#x2013;12,500</td>
<td valign="top" align="center">5</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B76">Khan et al., 2012</xref>; <xref ref-type="bibr" rid="B3">Akhand et al., 2016</xref>)</td>
</tr>
</tbody>
</table></table-wrap>
<p>Among all the selected satellite missions, the Landsat program involves a series of satellites that have been successfully used in agricultural monitoring because of the availability of historical data of the Earth&#x2019;s surface for over 40 years. The most recent Landsat-8 was launched in 2013 with two imagers (Operational Land Imager and Thermal Infrared Sensor) that provide spectral observations in nine spectral bands at a 30-m spatial resolution. Several studies thus adapted the high-resolution observations from Landsat-8 for potato yield prediction (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>; <xref ref-type="bibr" rid="B104">Newton et al., 2018</xref>; <xref ref-type="bibr" rid="B11">Awad, 2019</xref>).</p>
<p>Besides the Landsat missions, Sentinel-2 is another popular platform for agriculture monitoring. For the potato management, Sentinel-2 imagery has been used for LAI and chlorophyll content estimation (<xref ref-type="bibr" rid="B63">Herrmann et al., 2011</xref>; <xref ref-type="bibr" rid="B22">Clevers and Kooistra, 2012</xref>; <xref ref-type="bibr" rid="B21">Clevers and Gitelson, 2013</xref>; <xref ref-type="bibr" rid="B23">Clevers et al., 2017</xref>), radiation utilization assessment (<xref ref-type="bibr" rid="B114">Peng et al., 2021</xref>), yield prediction (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>; <xref ref-type="bibr" rid="B56">G&#x00F3;mez et al., 2019</xref>; <xref ref-type="bibr" rid="B1">Abou Ali et al., 2020</xref>), and crop mapping (<xref ref-type="bibr" rid="B8">Ashourloo et al., 2020</xref>). Launched in 2015 by Copernicus Programme, Sentinel-2 systematically acquires optical imagery with global coverage. It is equipped with a push-broom multi-spectral instrument (MSI) which provides optical observations at 13 spectral bands ranging from visible (VIS) to short-wave infrared (SWIR) at high spatial resolutions (10&#x2013;60 m/pixel). Like Landsat-8, Sentinel-2 also provides a global coverage but with a much higher temporal resolution (<xref ref-type="table" rid="T1">Table 1</xref>), which makes Sentinel-2 the most widely used satellite platform in potato precision management.</p>
<p>Other satellite platforms with unique specifications in one of the resolutions have been used to address specific purposes in potato management. For example, Terra Moderate Resolution Imaging Spectroradiometer has the highest spectral resolution of 36 bands in the range between 400 and 1,440 nm and thus the benefits for detecting the abnormal reflectance from leaves in the narrow bands for potato disease assessment (<xref ref-type="bibr" rid="B34">Dutta et al., 2014</xref>). Planet Scope provides images with the highest spatial resolution (3 m/pixel) every day through a constellation of about 130 low-orbit satellites. Though costly (&#x223C;&#x0024; 218 per 100 km<sup>2</sup>) compared to the publicly launched satellites, its imagery has been used as a good source for the decision-making at field-level and plot-level potato management on a daily basis (<xref ref-type="bibr" rid="B1">Abou Ali et al., 2020</xref>).</p>
</sec>
<sec id="S3.SS2">
<title>Unmanned aerial vehicle-based remote sensing platforms</title>
<p>Over the decades, UAV-based platforms have been a popular approach in precision agriculture. UAVs refer to devices with flying capacity without humans onboard (<xref ref-type="bibr" rid="B37">Eisenbeiss, 2004</xref>; <xref ref-type="bibr" rid="B130">Sankaran et al., 2015</xref>). Other than the UAV and its accessories (e.g., batteries and remote controller), UAV-based remote sensing platforms for agricultural purposes generally include onboard sensors for collecting data, a gimbal for motion correction and stabilization, and a flight planning App installed in a smart mobile device for automated flight control. To deliver precisely geo-referenced data, UAV platforms are typically coupled with ground control points (GCPs) with known global navigation satellite system positions.</p>
<p>The UAV platforms are available in several types with distinguishing features. The most widely used UAVs in precision agriculture are multi-rotor copters or fixed-wings (<xref ref-type="bibr" rid="B87">Li et al., 2021b</xref>). Multi-rotor copters can be quadcopters, hexacopters, or octocopters depending on the number of propellers they have. Multi-rotor copters are driven by the pairs of propellers to create thrust downward and directed by changing the thrust of one or more propellers. Thus, they are able to hover, take off and land vertically and have no lower limits on flight altitude. Fixed-wing UAVs, like airplanes, have a pair of rigid wings and a thruster at back. The lift of fixed-wing UAVs comes from the air pressure differences between the upper and lower sides that are generated passively as its wings cut through the air at a specific angle when being pushed forward. Fixed-wing UAVs are fast and energy-efficient, and thus allow much larger ground coverage than the multi-rotor copters. On the other hand, they do not have the capability to hover and fly close to the ground. A list of popular UAV models and their applications in potato applications are summarized in <xref ref-type="table" rid="T3">Table 3</xref>.</p>
<table-wrap position="float" id="T3">
<label>TABLE 3</label>
<caption><p>UAV-based remote sensing platforms and their applications in potato traits characterization.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">UAV type</td>
<td valign="top" align="left">Manufacturer</td>
<td valign="top" align="center">Model</td>
<td valign="top" align="center">On board sensors</td>
<td valign="top" align="center">Max. speed (km/h)</td>
<td valign="top" align="center">Duration (min)</td>
<td valign="top" align="center">Applications</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Quadcopters</td>
<td valign="top" align="left">DJI</td>
<td valign="top" align="center">Phantom 4 Pro</td>
<td valign="top" align="center">Visible RGB</td>
<td valign="top" align="center">50&#x2013;72</td>
<td valign="top" align="center">30</td>
<td valign="top" align="left">Plant height estimation (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>); Disease detection (<xref ref-type="bibr" rid="B137">Sugiura et al., 2018</xref>); Emergence estimation (<xref ref-type="bibr" rid="B84">Li et al., 2019</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Quadcopters</td>
<td valign="top" align="left">DJI</td>
<td valign="top" align="center">Inspire 2</td>
<td valign="top" align="center">RGB; Multispectral</td>
<td valign="top" align="center">94</td>
<td valign="top" align="center">25</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B88">Li et al., 2021a</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Quadcopters</td>
<td valign="top" align="left">3D Robotics</td>
<td valign="top" align="center">Solo</td>
<td valign="top" align="center">Visible RGB</td>
<td valign="top" align="center">80</td>
<td valign="top" align="center">25</td>
<td valign="top" align="left">Growth status prediction (<xref ref-type="bibr" rid="B52">Gibson-Poole et al., 2018</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Quadcopters</td>
<td valign="top" align="left">DJI</td>
<td valign="top" align="center">Matrice 100 <xref ref-type="table-fn" rid="t3fns1">&#x002A;</xref></td>
<td valign="top" align="center">Multispectral</td>
<td valign="top" align="center">61&#x2013;79</td>
<td valign="top" align="center">20&#x2013;40</td>
<td valign="top" align="left">Radiation use efficiency assessment (<xref ref-type="bibr" rid="B114">Peng et al., 2021</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Hexacopter</td>
<td valign="top" align="left">DJI</td>
<td valign="top" align="center">Matrice 600 Pro</td>
<td valign="top" align="center">Customizable</td>
<td valign="top" align="center">65</td>
<td valign="top" align="center">25</td>
<td valign="top" align="left">Yield prediction (<xref ref-type="bibr" rid="B139">Sun et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Hexacopter</td>
<td valign="top" align="left">Tarot</td>
<td valign="top" align="center">680 Pro</td>
<td valign="top" align="center">Customizable</td>
<td valign="top" align="center">&#x2013;</td>
<td valign="top" align="center">&#x2013;</td>
<td valign="top" align="left">Structural change (<xref ref-type="bibr" rid="B7">Angulo-Morales et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Octocopter</td>
<td valign="top" align="left">Aerialtronics</td>
<td valign="top" align="center">Altura AT8 <xref ref-type="table-fn" rid="t3fns1">&#x002A;</xref></td>
<td valign="top" align="center">Customizable</td>
<td valign="top" align="center">&#x2013;</td>
<td valign="top" align="center">&#x2013;</td>
<td valign="top" align="left">Chlorophyll content assessment, leaf area index (LAI) estimation and ground cover assessment (<xref ref-type="bibr" rid="B44">Franceschini et al., 2017a</xref>); Crop growth assessment (<xref ref-type="bibr" rid="B50">Gevaert et al., 2014</xref>); Chlorophyll content assessment and LAI estimation (<xref ref-type="bibr" rid="B124">Roosjen et al., 2018</xref>); Reflectance anisotropy measurements (<xref ref-type="bibr" rid="B125">Roosjen et al., 2016</xref>, <xref ref-type="bibr" rid="B126">2017</xref>); Disease detection (<xref ref-type="bibr" rid="B134">Siebring et al., 2019</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Octocopter</td>
<td valign="top" align="left">Riegl</td>
<td valign="top" align="center">RiCOPTER</td>
<td valign="top" align="center">Visible RGB; LiDAR</td>
<td valign="top" align="center">30</td>
<td valign="top" align="center">30</td>
<td valign="top" align="left">Crop height and biomass estimation (<xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref>)</td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="left">GmbH HiSystems</td>
<td valign="top" align="center">Unspecified</td>
<td valign="top" align="center">Visible RGB</td>
<td valign="top" align="center">&#x2013;</td>
<td valign="top" align="center">&#x2013;</td>
<td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref>, <xref ref-type="bibr" rid="B137">2018</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Fixed-wing</td>
<td valign="top" align="left">Trimble</td>
<td valign="top" align="center">UX5 HP</td>
<td valign="top" align="center">Visible RGB</td>
<td valign="top" align="center">80</td>
<td valign="top" align="center">35</td>
<td valign="top" align="left">Plant height estimation (<xref ref-type="bibr" rid="B27">De Jesus Colwell et al., 2021</xref>)</td>
</tr>
<tr>
<td valign="top" align="left">Fixed-wing</td>
<td valign="top" align="left">senseFly</td>
<td valign="top" align="center">eBee micro <xref ref-type="table-fn" rid="t3fns1">&#x002A;</xref></td>
<td valign="top" align="center">Visible RGB; Multispectral</td>
<td valign="top" align="center">110</td>
<td valign="top" align="center">25&#x2013;50</td>
<td valign="top" align="left">Disease detection (<xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref>)</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="t3fns1"><p>&#x002A;Better versions are available now.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>Selection of UAVs is conditional on specific tasks, including field area, spatial resolution, flexibility for carrying various cameras, and costs. Among all UAV types, quadcopters are the most popular as they are light weight and easy to operate. The DJI Phantom series with high-resolution motion RGB cameras have been used in applications for obtaining plant structural traits (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>) and recently they have an updated multispectral version for those who favor spectral measurements. Hexacopters generally are not sold with onboard sensors but offer interfaces to power and control third-party cameras. Thus the hexacopters are often used to carry multi- or hyper-spectral cameras for perceiving complicated crop traits such as yield responses (<xref ref-type="bibr" rid="B42">Feng et al., 2020</xref>; <xref ref-type="bibr" rid="B164">Zhou et al., 2021b</xref>) or stress (<xref ref-type="bibr" rid="B166">Zhou et al., 2020</xref>, <xref ref-type="bibr" rid="B165">2021a</xref>). Similar to the hexacopter, octocopters are flexible in carrying multiple sensors and other devices for durable flight. The most widely accepted octocopter is the Altura AT8 (Aerialtronics, South Holland, Netherlands) which was used to carry a hyperspectral imaging system (2.0 kg in total) as the original version of the Hyperspectral Mapping System (HYMSY, <xref ref-type="bibr" rid="B140">Suomalainen et al., 2014</xref>). The HYMSY system costs around &#x0024;12,769 and is largely used in potato studies conducted in European. On the opposite to multi-rotor UAVs, the fixed-wings offer a solution to the need of covering large fields because of their nature of high flight speed and altitude. Cameras on fixed-wings should have high frame rates and short exposure time to avoid blurred images caused by the high flight speed (<xref ref-type="bibr" rid="B87">Li et al., 2021b</xref>). As products evolve, fixed-wings vendors now offer a variety of versions with dual or triple cameras for agricultural purposes.</p>
</sec>
</sec>
<sec id="S4">
<title>Applications</title>
<p>Precision agricultural management is the key to reducing environmental impact and enhancing agricultural sustainability (<xref ref-type="bibr" rid="B162">Zhang et al., 2021</xref>). Within the context of potato management, a variety of activities are employed to ensure its productivity and quality throughout the growing cycle. Some of these activities heavily rely on <italic>in situ</italic> field monitoring of potato growing conditions, field environmental conditions and diseases, followed by in-season decision-making on irrigation, fertilization, pesticides and off-season guidance on storage, sell, and post-harvest field management. Remote sensing techniques have been explored and applied to directly measure crop yield, disease damages, and some key indicators of potato growth. In this section, we reviewed the applications of these techniques in potato management, including tuber yield prediction, AGB estimation, water deficit stress assessment, nitrogen concentration estimation, and disease detection. Some key traits that are closely related to potato growth were also summarized, namely plant height, LAI, chlorophyll, and emergence detection and plant counting. The details of the applications can be found in <xref ref-type="table" rid="T4">Table 4</xref>.</p>
<table-wrap position="float" id="T4">
<label>TABLE 4</label>
<caption><p>Applications of remote sensing technologies in Potato traits characterization.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Application</td>
<td/>
<td valign="top" align="left">Platform</td>
<td valign="top" align="center">Sensor</td>
<td valign="top" align="center">Model</td>
<td valign="top" align="left">Sensor-derived feature</td>
<td valign="top" align="left">References</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left"><bold>Tuber yield prediction</bold></td>
<td/>
<td valign="top" align="left">UAV</td>
<td valign="top" align="left">Hyperspectral camera</td>
<td valign="top" align="left">OLS; Ridge; PLSR; SVR; RF; AdaBoost</td>
<td valign="top" align="left">Full spectra</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B139">Sun et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">RGB, multi- and hyper- spectral cameras</td>
<td valign="top" align="left">RF; PLSR</td>
<td valign="top" align="left">13 narrow-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">ANN</td>
<td valign="top" align="left">NDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B141">Tanabe et al., 2019</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">RF; SVR</td>
<td valign="top" align="left">15 wide-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B88">Li et al., 2021a</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Satellite</td>
<td valign="top" align="left">Terra MODIS</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B12">Bala and Islam, 2009</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">RF; SVM; LR</td>
<td valign="top" align="left">NDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B128">Salvador et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Sentinel-2</td>
<td valign="top" align="left">9 machine learning models</td>
<td valign="top" align="left">54 features including band reflectance and VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B56">G&#x00F3;mez et al., 2019</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Landsat-8; Sentinel-2</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">NDVI; SAVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Above-ground biomass (AGB) estimation</bold></td>
<td valign="top" align="left">UAV</td>
<td valign="top" align="left">RGB and Hyperspectral camera</td>
<td valign="top" align="left">RF; PLSR</td>
<td valign="top" align="left">13 narrow-band VIs; Image-based plant height</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">LiDAR</td>
<td valign="top" align="left">3D Profile Index (<xref ref-type="bibr" rid="B70">Jimenez-Berni et al., 2018</xref>)</td>
<td valign="top" align="left">LiDAR point cloud</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Handheld</td>
<td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">PLSR, MLR, RF</td>
<td valign="top" align="left">NDSI, RSI, DSI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B113">Pei et al., 2019</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">GA; ANFIS</td>
<td valign="top" align="left">20 narrow-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B40">Elsayed et al., 2021b</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">RF</td>
<td valign="top" align="left">12 narrow-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B158">Yang et al., 2021</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">TIR and RGB cameras</td>
<td valign="top" align="left">MLR; ANFIS</td>
<td valign="top" align="left">NRCT and 12 wide-based VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">UAV; Satellite; handheld</td>
<td valign="top" align="left">Multispectral camera; Sentinel-2; multispectral spectrometer</td>
<td valign="top" align="left">Carnegie&#x2013;Ames&#x2013;Stanford approach</td>
<td valign="top" align="left">RVI and raw bands</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B114">Peng et al., 2021</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Water deficit stress assessment</bold></td>
<td valign="top" align="left">UAV; handheld</td>
<td valign="top" align="left">TIR and RGB cameras</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">CWSI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B127">Rud et al., 2014</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Handheld</td>
<td valign="top" align="left">TIR camera</td>
<td valign="top" align="left">&#x2013;</td>
<td valign="top" align="left">CWSI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B26">Cucho-Padin et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">MLR; ANFIS</td>
<td valign="top" align="left">NRCT</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">LR</td>
<td valign="top" align="left">CWSI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B51">Ghazouani et al., 2017</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Nitrogen concentration estimation</bold></td>
<td valign="top" align="left">UAV</td>
<td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">NDVI; GNDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B66">Hunt and Rondon, 2017</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">MAV</td>
<td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">GNDVI; GRVI; NDVI; NG</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B106">Nigon et al., 2014</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">PLSR</td>
<td valign="top" align="left">NG and 6 narrow-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B105">Nigon et al., 2015</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Handheld</td>
<td valign="top" align="left">Multispectral radiometer</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">8 wide-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B21">Clevers and Gitelson, 2013</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">4 SWIR-based indices</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B63">Herrmann et al., 2011</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">NDVI; RVI; RRE; RRE/GC</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B170">Zhou et al., 2018</xref></td>
</tr>
<tr>
<td valign="top" align="left"><bold>Disease detection</bold></td>
<td valign="top" align="center">PVY</td>
<td valign="top" align="left">Ground vehicle</td>
<td valign="top" align="left">RGB-Depth camera; hyperspectral line scan camera</td>
<td valign="top" align="left">FCN</td>
<td valign="top" align="left">Full spectra</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B115">Polder et al., 2019</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left">Handheld</td>
<td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">SVM</td>
<td valign="top" align="left">5 EM wavelength segments</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B59">Griffel et al., 2018</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">PLS-DA</td>
<td valign="top" align="left">NDSI for all combinations of wavelengths</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B25">Couture et al., 2018</xref></td>
</tr>
<tr>
<td valign="top" align="left"></td>
<td valign="top" align="center">Late blight</td>
<td valign="top" align="left">UAV</td>
<td valign="top" align="left">RGB camera</td>
<td valign="top" align="left">Color threshold</td>
<td valign="top" align="left">HSV color space</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left"/><td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">&#x2013;</td>
<td valign="top" align="left">NDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">CNN; SVR; RF</td>
<td valign="top" align="left">Differences between G and B as well as between NIR and G</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B33">Duarte-Carvajalino et al., 2018</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left">Satellite</td>
<td valign="top" align="left">Terra MODIS; AWiFS</td>
<td valign="top" align="left">Clustering</td>
<td valign="top" align="left">NDVI and LSWI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B34">Dutta et al., 2014</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left">Handheld</td>
<td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">ANOVA; Stepwise Discriminant Analysis</td>
<td valign="top" align="left">NDVI; SR; SAVI; REI; and full spectra</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B120">Ray et al., 2011</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td valign="top" align="center">Early blight</td>
<td valign="top" align="left">Ground vehicle</td>
<td valign="top" align="left">Hyperspectral camera</td>
<td valign="top" align="left">PLS-DA; SVM</td>
<td valign="top" align="left">Full spectra; five wide-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B146">Van De Vijver et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" align="left"/><td/>
<td valign="top" align="left">Handheld</td>
<td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">PCA; spectral change analysis; and PLSR</td>
<td valign="top" align="left">Full spectra</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B9">Atherton et al., 2015</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Plant height</bold></td>
<td valign="top" align="left">UAV</td>
<td valign="top" align="left">RGB camera and hyperspectral sensor</td>
<td valign="top" align="left">SfM; RF and PLSR</td>
<td valign="top" align="left">RGB images and 13 narrow-band VIs</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">LiDAR scanner</td>
<td valign="top" align="left">3DPI</td>
<td valign="top" align="left">3D-point cloud</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B143">ten Harkel et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">RGB camera</td>
<td valign="top" align="left">SfM; &#x201C;trace all triangles&#x201D; method and &#x201C;do not track breaklines&#x201D; method</td>
<td valign="top" align="left">RGB images</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B27">De Jesus Colwell et al., 2021</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Leaf area index (LAI)</bold></td>
<td valign="top" align="left">Handheld</td>
<td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">PLSR</td>
<td valign="top" align="left">Full spectra NDVI; REIP</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B63">Herrmann et al., 2011</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Handheld; satellite</td>
<td valign="top" align="left">Hyperspectral spectrometer; Landsat TM/ETM+</td>
<td valign="top" align="left">Linear, exponential, and logarithmic regression</td>
<td valign="top" align="left">NDVI; SAVI; WDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B110">Papadavid et al., 2011</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">UAV</td>
<td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">PROSAIL model inversion</td>
<td valign="top" align="left">Multi-angular multispectral data</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B124">Roosjen et al., 2018</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Satellite</td>
<td valign="top" align="left">Sentinel-2 MSI</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">WDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B23">Clevers et al., 2017</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Landsat-8 OLI; Sentinel-2 MSI</td>
<td valign="top" align="left">LR; SNAP model</td>
<td valign="top" align="left">SAVI; NDVI; EVI2; SeLI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B101">Mourad et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Leaf chlorophyll content (LCC)</bold></td>
<td valign="top" align="left">Handheld</td>
<td valign="top" align="left">RGB camera</td>
<td valign="top" align="left">ANN; LR</td>
<td valign="top" align="left">Mean brightness parameters and mean brightness ratio</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B35">Dutta Gupta et al., 2013</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Hyperspectral spectrometer</td>
<td valign="top" align="left">PLSR</td>
<td valign="top" align="left">Full spectra; normalized spectra; MFs spectra</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B93">Liu et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">LR; MLR</td>
<td valign="top" align="left">mean and std of R and G</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B17">Borhan et al., 2017</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">Handheld; satellite</td>
<td valign="top" align="left">Hyperspectral spectrometer; REIS</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">TCARI/OSAVI, TCI/OSAVI and CVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B81">Kooistra and Clevers, 2016</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left">UAV; satellite</td>
<td valign="top" align="left">Hyperspectral spectrometer; FORMOSAT-2</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">Spectral&#x2013;temporal response surfaces</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B49">Gevaert et al., 2015</xref></td>
</tr>
<tr>
<td valign="top" align="left" colspan="2"><bold>Emergence detection and plant counting</bold></td>
<td valign="top" align="left">UAV</td>
<td valign="top" align="left">RGB camera</td>
<td valign="top" align="left">Mask R-CNN</td>
<td valign="top" align="left">RGB images</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B98">Machefer et al., 2020</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left"/><td valign="top" align="left">RF</td>
<td valign="top" align="left">Morphological features</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B84">Li et al., 2019</xref></td>
</tr>
<tr>
<td valign="top" colspan="2"/><td valign="top" align="left"/><td valign="top" align="left">Multispectral camera</td>
<td valign="top" align="left">LR</td>
<td valign="top" align="left">NDVI</td>
<td valign="top" align="left"><xref ref-type="bibr" rid="B131">Sankaran et al., 2017</xref></td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn><p>Abbreviations for <xref ref-type="table" rid="T3">Table 3</xref>: OLS, ordinary least squares; PLSR, partial least square regression; SVR, support vector regression; RF, random forest; VI, vegetation index; ANN, artificial neural network; NDVI, normalized difference vegetation index; LR, linear regression; SVM, support vector machine; SAVI, soil adjusted vegetation index; NDSI, normalized difference snow index; RSI, ratio spectral index; DSI, difference spectral index; MLR, multiple linear regression; GA, genetic algorithm; ANFIS, adaptive neuro-fuzzy inference system; NRCT, normalized relative canopy temperature; RVI, ratio vegetation index; CWSI, crop water status index; GNDVI, green normalized difference vegetation index; GRVI, green and red ratio vegetation index; NG, normalized green; RRE, ratio red edge vegetation index; GC, canopy cover; FCN, fully convolution neural network; EM, electromagnetic spectrum; PLS-DA, partial least-squares discriminate analysis; CNN, convolution neural network; G, green; B, blue; NIR, near infrared; LSWI, integration of leaf water content index; ANOVA, analysis of variance; SR, simple ratio; REI, red edge index; PCA, principal components analysis; SfM, structure from motion; 3DPI, 3D profile index; REIP, red-edge inflection point; WDVI, weighted difference vegetation index; PROSAIL, the coupling of the PROSPECT and SAIL models; SANP, sentinel application platform; EVI2, enhanced vegetation index 2; SeLI, sentinel-2 LAI index; REIS, RapidEye earth-imaging system; TCARI, transformed chlorophyll absorption in reflectance index; OSAVI, optimized soil-adjusted vegetation index the optimized soil-adjusted vegetation index; TCI, triangular chlorophyll index; and CVI, chlorophyll vegetation index.</p></fn>
</table-wrap-foot>
</table-wrap>
<sec id="S4.SS1">
<title>Tuber yield prediction</title>
<p>Achieving the maximum crop yield at the lowest investment is an ultimate goal for farmers (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>). Early detection of problems associated with crop yield can greatly help with the decision-making for field management and reduce profit loss. In addition, yield mapping pre- or post-harvest can be used as spatial references for implementing variable rate technologies to achieve precise applications of field-level inputs and thus optimize production across entire fields (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>).</p>
<p>Potato tuber yield is jointly affected by genetic variation, environmental conditions (soil and weather), seed quality, and crop management practices (<xref ref-type="bibr" rid="B88">Li et al., 2021a</xref>). Classical potato yield prediction models are often used to estimate yields within the growing season by considering nitrogen fertilizer, temperature, and daylight or the incidence of solar radiation (<xref ref-type="bibr" rid="B151">Wang X. et al., 2021</xref>). Recent studies showed higher prediction accuracies by using machine learning models with remote sensing data at various levels, providing target-specific insights and recommendations for precision agriculture practices.</p>
<p><xref ref-type="bibr" rid="B128">Salvador et al. (2020)</xref> predicted potato tuber yield at a municipal level in Mexica using machine learning models with satellite remote sensing imagery. The models were trained with NDVI values calculated from the TERRA satellite images combined with meteorological data on a monthly basis. The best testing performance was from the Random Forest model for the winter cycle (<italic>R</italic><sup>2</sup> = 0.76 and RMSE% = 18.9) and the polynomial Support Vector Machine for the summer cycle (<italic>R</italic><sup>2</sup> = 0.86 and RMSE% = 14.9). There are a few similar studies using satellite imagery and machine learning models for predicting potato yield at large scales in Spain (<xref ref-type="bibr" rid="B56">G&#x00F3;mez et al., 2019</xref>), Saudi Arabia (<xref ref-type="bibr" rid="B6">Al-Gaadi et al., 2016</xref>), and Bangladesh (<xref ref-type="bibr" rid="B12">Bala and Islam, 2009</xref>).</p>
<p>Unmanned aerial vehicle-based imagery is largely used for predicting potato yield in site-specific studies. Multi- (<xref ref-type="bibr" rid="B141">Tanabe et al., 2019</xref>; <xref ref-type="bibr" rid="B88">Li et al., 2021a</xref>) and hyper-spectral (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>; <xref ref-type="bibr" rid="B139">Sun et al., 2020</xref>) have been used to establish and validate a variety of machine learning models for predicting potato yield. The prediction performance of images collected at different growth stages was compared. It was found that images at earlier growth stages, i.e., the tuber initiation stage (<xref ref-type="bibr" rid="B88">Li et al., 2021a</xref>) and vegetative growth stage (<xref ref-type="bibr" rid="B141">Tanabe et al., 2019</xref>), tuber bulking stage (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>) had better prediction performances than those at the later stage when close to the end of seasons. Even though, <xref ref-type="bibr" rid="B139">Sun et al. (2020)</xref> reported a decent prediction accuracy with <italic>R</italic><sup>2</sup> = 0.63, RMSE = 3.03 ton/ha, and RMSE% = 5.8 when using hyperspectral image features at tuber maturation stage and machine learning models to predict potato tuber yield under four irrigation levels.</p>
</sec>
<sec id="S4.SS2">
<title>Potato above-ground biomass estimation</title>
<p>Above-ground biomass is a basic agronomic trait in field investigations and is often used to indicate crop growth status, the effectiveness of agricultural management measures, and the carbon sequestration ability of crops (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>). Particularly for potatoes, AGB is one of the most important indicators for calculating the nitrogen nutrition index and diagnosing the potato nitrogen status for precise nitrogen fertilizer management (<xref ref-type="bibr" rid="B71">Jin et al., 2021</xref>; <xref ref-type="bibr" rid="B158">Yang et al., 2021</xref>). Manual measurement of AGB requires cutting culms at the ground level for a defined portion of the experimental plot, and then weighing before (AGB fresh weight) and after drying (AGB dry weight) in an oven until constant weight (<xref ref-type="bibr" rid="B111">Pask et al., 2012</xref>), which is laborious and subject to experimental errors (<xref ref-type="bibr" rid="B70">Jimenez-Berni et al., 2018</xref>).</p>
<p>Estimations of potato AGB using remote sensing methods have been explored in a variety of ways, by integrating spectral-based VIs, plant height (manual- or sensor-based) with machine learning, classical and empirical models. Ground-based data acquired on potato canopies by spectroradiometers (<xref ref-type="bibr" rid="B113">Pei et al., 2019</xref>; <xref ref-type="bibr" rid="B40">Elsayed et al., 2021b</xref>; <xref ref-type="bibr" rid="B158">Yang et al., 2021</xref>), RGB, and thermal cameras (<xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref>) were used as predictors in machine learning models and the studies showed that the agreements between the estimated and measured biomass were up to <italic>R</italic><sup>2</sup> of 0.7&#x2013;0.8. <xref ref-type="bibr" rid="B113">Pei et al. (2019)</xref> also compared the estimation performance using the ground spectral data at different stages and the best result was given by the spectral features at the tube growth stage with <italic>R</italic><sup>2</sup> = 0.71 and RMSE% = 19.3.</p>
<p>In addition to the spectral features, plant height was considered as an important contributor to potato biomass. <xref ref-type="bibr" rid="B143">ten Harkel et al. (2020)</xref> derived the potato plant height from a UAV-LiDAR device and imported it to an empirical model originated from (<xref ref-type="bibr" rid="B70">Jimenez-Berni et al., 2018</xref>) for the estimation of biomass from LiDAR. The biomass solely based on plant height had an <italic>R</italic><sup>2</sup> of 0.24 with the RMSE of 22.1 g/m<sup>2</sup>. In another case, the UAV image-based plant height (from RGB images using the Structure from Motion method) was integrated with UAV hyperspectral VIs into a Random Forest model. The model accuracy for the biomass fresh weight was up to <italic>R</italic><sup>2</sup> = 0.90 with RMSE% = 20.6, and for the biomass dry weight up to <italic>R</italic><sup>2</sup> = 0.92 with RMSE% = 17.4 (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>).</p>
<p>An interesting comparison in the estimation performance of potato biomass using ground, UAV, and satellite data was conducted by <xref ref-type="bibr" rid="B114">Peng et al. (2021)</xref>. Data from each source were independently used as variables in a classical model (the Carnegie&#x2013;Ames&#x2013;Stanford approach). The results showed that the ground spectral data reached the highest accuracy with <italic>R</italic><sup>2</sup> = 0.76 and RMSE% = 22.2, while the UAV and the Satellite multispectral image features had the similar performance with <italic>R</italic><sup>2</sup> = 0.70 (RMSE% = 22.4) and <italic>R</italic><sup>2</sup> = 0.72 (RMSE% = 24.4), respectively.</p>
</sec>
<sec id="S4.SS3">
<title>Potato water deficit stress assessment</title>
<p>Potato plants are sensitive to water stress due to their shallow root systems. Approximately 70% of the total water needed for potato growth comes from the upper 30 cm of the soil (<xref ref-type="bibr" rid="B2">Ahmadi et al., 2011</xref>). Potato commonly grows in coarse-textured soil with low water holding capacity (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>) or in arid and semiarid countries (<xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref>). Therefore, inappropriate water management practices or water deficit stress in potato plants could cause significant reductions in tuber yield (<xref ref-type="bibr" rid="B75">Karam et al., 2014</xref>) and degraded tuber quality (<xref ref-type="bibr" rid="B32">Djaman et al., 2021</xref>).</p>
<p>The plant water deficit is conventionally detected by measuring plant water statuses, such as leaf water potential and stomatal conductance, or by measuring soil gravimetric water content. All of the measurements are direct, destructive, labor-intensive, and unable for large-scale cultivation or tracking intra-field variability (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>). CWSI, accounting for the differences between canopy and air temperatures at a fixed air vapor pressure deficit, has been extensively validated to represent plant water status, after it was designed by <xref ref-type="bibr" rid="B69">Idso et al. (1981)</xref>. The use of leaf or canopy temperature to detect the water-related stresses is based on the principle that a plant&#x2019;s stomatal closure takes place during water stress, which results in a decrease of energy dissipation and an increase in plant temperature (<xref ref-type="bibr" rid="B69">Idso et al., 1981</xref>; <xref ref-type="bibr" rid="B39">Elsayed et al., 2021a</xref>). The CWSI has been proposed as a good indicator of plant water stress (<xref ref-type="bibr" rid="B26">Cucho-Padin et al., 2020</xref>) and proved relating to stomatal conductance (<xref ref-type="bibr" rid="B127">Rud et al., 2014</xref>) and yield (<xref ref-type="bibr" rid="B51">Ghazouani et al., 2017</xref>).</p>
<p>The computation of CWSI requires the knowledge of plant canopy temperature which can be acquired through remote sensing technologies. Handheld infrared cameras have been used to obtain temperature values of plant canopy and soil to calculate the CSWI values for potato plants under irrigation treatments. <xref ref-type="bibr" rid="B26">Cucho-Padin et al. (2020)</xref> found that the CWSI values derived from a TIR camera had a high correlation (the Pearson&#x2019;s correlation coefficient <italic>r</italic> = 0.84) with those from ground proximal sensors. The results also showed that no significant reduction in tuber yield was observed by using CWSI &#x003C; 0.4 as a threshold for irrigation in potato crops, compared to the irrigation amount with CWSI &#x003E; 0.4, which agrees with other works (<xref ref-type="bibr" rid="B118">Ram&#x00ED;rez et al., 2016</xref>; <xref ref-type="bibr" rid="B122">Rinza et al., 2019</xref>) and provides a reference for saving irrigation water in arid and semiarid regions (<xref ref-type="bibr" rid="B26">Cucho-Padin et al., 2020</xref>).</p>
<p>The effectiveness of aerial TIR images in representing potato water status was evaluated in <xref ref-type="bibr" rid="B127">Rud et al. (2014)</xref> by comparing the image-derived CWSI with the biophysical measurements of leaf stomatal conductance values. In this study, RGB images were acquired simultaneously with the TIR images and used to create masks for the TIR images to distinguish between vegetation and soil. The CWSI was calculated based on the difference between leaf and air temperatures normalized to the variation in environmental meteorological conditions and showed high correlations (0.64 &#x2264; <italic>R</italic><sup>2</sup> &#x2264; 0.99) with the stomatal conductance measurements.</p>
<p>A few studies have tried to combine spectral indices with the CWSI and canopy temperature to indicate potato water stress. <xref ref-type="bibr" rid="B39">Elsayed et al. (2021a)</xref> reported a good alignment (<italic>R</italic><sup>2</sup> = 0.89) between the estimated and measured water content of the potato AGB by using the spectral indices derived from RGB and thermal images combined with machine learning models. Similarly, <xref ref-type="bibr" rid="B48">Gerhards et al. (2016)</xref> compared the performance of detecting water content in potato plants between spectral and thermal-based indices. The results showed that the CWSI was most suitable for water stress detection among all the thermal-based indices. Additionally, it was found that the NIR/SWIR reflectance-based indices and the spectral emissivity (non-imaging devices) were equally sensitive to plant water content and responded quicker than the indices from imaging devices (such as the NDVI from a hyperspectral TIR camera; <xref ref-type="bibr" rid="B48">Gerhards et al., 2016</xref>).</p>
</sec>
<sec id="S4.SS4">
<title>Potato nitrogen concentration estimation</title>
<p>Potato growth depends largely on the nitrogen availability in the soil (<xref ref-type="bibr" rid="B106">Nigon et al., 2014</xref>). However, the shallow-root system coupled with their common cultivation in coarse-textured soils leads to poor nitrogen use efficiency in potato plants (<xref ref-type="bibr" rid="B106">Nigon et al., 2014</xref>). Excessive applications of nitrogen fertilizers, on one hand, might have negative impacts on potato productivity by inducing a greater growth of aboveground biomass but reducing the root growth. On the other hand, it raises the health risks associated with nitrate-contaminated groundwater caused by the high rates of nitrate leaching in irrigated potato fields (<xref ref-type="bibr" rid="B160">Zebarth and Rosen, 2007</xref>; <xref ref-type="bibr" rid="B96">Lynch et al., 2012</xref>). Therefore, precise spatial and temporal nitrogen management is important to optimize production and minimize environmental nitrogen losses (<xref ref-type="bibr" rid="B106">Nigon et al., 2014</xref>).</p>
<p>One of the typical guidance on the timing and amount of nitrogen applications on potato is nitrogen nutrition index, defined as the ratio of the actual nitrogen concentration (N<sub>c</sub>) over the minimum crop nitrogen concentration allowing for maximum biomass production (N<sub>cri</sub>). While N<sub>cri</sub> is an estimated value depending on the potato AGB, N<sub>c</sub> needs to be determined along with the potato growth and traditionally by wet tests in laboratory. However, N<sub>c</sub> values from the sampled potato plants might not accurately represent nitrogen status for an entire field and potato nitrogen status might change considerably by the time of analysis (<xref ref-type="bibr" rid="B170">Zhou et al., 2018</xref>). Thus, fast and accurate estimation of potato N<sub>c</sub> values is urgently needed to assist the precision nitrogen management in potato productions.</p>
<p>Canopy spectral reflectance has been used extensively in agriculture to measure the actual nitrogen status of crop growth in order to guide nitrogen fertilization (<xref ref-type="bibr" rid="B119">Raun et al., 2002</xref>; <xref ref-type="bibr" rid="B147">Van Evert et al., 2012</xref>; <xref ref-type="bibr" rid="B169">Zhou et al., 2016c</xref>). The principle that the canopy spectral reflectance can indicate the canopy N<sub>c</sub> values is based on the fact that the light reflected in certain wavebands is sensitive to leaf chlorophyll concentration, which in turn closely depends on leaf nitrogen concentration (<xref ref-type="bibr" rid="B83">Lawlor et al., 1989</xref>; <xref ref-type="bibr" rid="B14">Baret and Fourty, 1997</xref>; <xref ref-type="bibr" rid="B60">Hansen and Schjoerring, 2003</xref>). Studies have been conducted to compare the performances in estimating the potato N<sub>c</sub> among canopy spectral reflectance obtained at different scales (handheld/UAV/Satellite) with narrow or wide spectral bandwidths and various ranges in spectral wavelength. The commonly used spectral features and their details have been summarized in <xref ref-type="table" rid="T3">Table 3</xref>.</p>
</sec>
<sec id="S4.SS5">
<title>Potato disease detection</title>
<p>Potato production is threatened by several diseases resulting in considerable yield losses, causing decreases in the quality and increases in the price of potatoes (<xref ref-type="bibr" rid="B142">Taylor et al., 2008</xref>). In-season early detection is particularly important for disease management decisions to control disease severity and prevent the spread of diseases (<xref ref-type="bibr" rid="B108">Oppenheim and Shani, 2017</xref>). Besides, detecting the overall disease grade of potato fields allows growers to make decisions regarding the best way to store, sell, and manage the fields for future generations (<xref ref-type="bibr" rid="B52">Gibson-Poole et al., 2018</xref>). Traditional potato disease inspection requires visual identification of the signs of disease. However, the disease plants can be difficult to identify, especially when symptoms are not yet developed or at the early stages. The remote sensing technique provides an opportunity to overcome the limitations, and they have already been widely used to detect diseases of potatoes for many years.</p>
<p>Among all the diseases that occurred during potato growth, Potato Virus Y (<italic>Potyviridae</italic>, PVY) is the most common reason for the rejection of seed lots from certification and one of the most common potato diseases (<xref ref-type="bibr" rid="B59">Griffel et al., 2018</xref>). The foliar symptoms of PVY include mosaic, leaf drop, and interveinal necrosis, and this virus can also cause necrotic rings on potato tubers (<xref ref-type="bibr" rid="B58">Gray et al., 2010</xref>). However, the recently prevalent PVY strains exhibit transient and milder foliar symptoms, making it less effective the visual inspection of seed lots with high PVY incidence (<xref ref-type="bibr" rid="B47">Frost et al., 2013</xref>). Spectral reflections in the NIR and SWIR regions have provided differentiable profiles in the underlying responses to the PVY stress. <xref ref-type="bibr" rid="B25">Couture et al. (2018)</xref> assessed the efficacy of hyperspectral information (a handheld device with narrow bands between 350 to 2,500 nm) in detecting the presence of PVY in potato leaves prior to the onset of the visual symptoms and observed a significant difference in the whole spectral profile between the PVY-negative and PVY-positive plants, especially in the NIR and SWIR spectral regions. A partial-least square discriminate analysis model trained with normalized spectral indices derived from the hyperspectral bands correctly identified the positive PVY infection status <italic>in vivo</italic> with a mean cross-validation accuracy of Kappa = 0.73. Similarly, high accuracy of 89.8% was reported by <xref ref-type="bibr" rid="B59">Griffel et al. (2018)</xref> in classifying the PVY-infected and non-infected potato plants using the UAV-based spectral information in the NIR and SWIR regions. Another example was given by <xref ref-type="bibr" rid="B115">Polder et al. (2019)</xref> that the healthy potato plants were distinguished from PVY infected ones (the classification Precision = 0.78) by a deep learning model directly using the hyperspectral images (400&#x2013;1,000 nm).</p>
<p>Potato late blight (<italic>Phytophthora infestans</italic>) is another serious disease affecting potato production worldwide (<xref ref-type="bibr" rid="B68">Hwang et al., 2014</xref>). The disease rapidly destroys leaves, and it consequently leads to yield losses and tuber quality deterioration. Symptoms of late blight on potato plants mostly appear on the leaves, developing from small, dark green, irregular-shaped water-soaked spots to large, dark brown or black lesions surrounded by a yellow chlorotic halo. Compared to the PVY, late blight affections are more easily detectable from potato canopies using remote sensing techniques. Various sensing combinations have been evaluated with promising potential to estimate the late blight severity, from ground-based spectrometer (<xref ref-type="bibr" rid="B120">Ray et al., 2011</xref>; <xref ref-type="bibr" rid="B44">Franceschini et al., 2017a</xref>; <xref ref-type="bibr" rid="B55">Gold et al., 2020</xref>) to UAV-based RGB (<xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref>), multi-/hyper-spectral (<xref ref-type="bibr" rid="B103">Nebiker et al., 2016</xref>; <xref ref-type="bibr" rid="B45">Franceschini et al., 2017b</xref>; <xref ref-type="bibr" rid="B33">Duarte-Carvajalino et al., 2018</xref>) cameras and to satellite-based MSI (<xref ref-type="bibr" rid="B34">Dutta et al., 2014</xref>). Despite using considerably different prediction models, the general idea of quantifying the late blight severity is first to differentiate the infected and the healthy leaves parts and then obtain as the estimations the percentage of the damaged part over the healthy part (<xref ref-type="bibr" rid="B34">Dutta et al., 2014</xref>; <xref ref-type="bibr" rid="B136">Sugiura et al., 2016</xref>; <xref ref-type="bibr" rid="B33">Duarte-Carvajalino et al., 2018</xref>).</p>
<p>Another potato disease that has been detected using remote sensing techniques is early blight (<italic>Alternaria solani</italic>). <xref ref-type="bibr" rid="B9">Atherton et al. (2015)</xref> analyzed the spectral profile of potato plants with the early blight and noticed a significant difference in the spectral reflectance between heavily diseased plants and healthy plants. <xref ref-type="bibr" rid="B146">Van De Vijver et al. (2020)</xref> developed a ground-based proximal sensing platform-Hypercart for acquiring hyperspectral images in the potato field. The machine learning models highly agreed (<italic>R</italic><sup>2</sup> = 0.92) with the visual assessments. Additionally, significant differences between healthy leaf and injected leaf tissues were observed in the green (550 nm), red (680 nm), and NIR (720&#x2013;750 nm) regions and the NIR was recognized as the most helpful region for detecting the early blight lesions.</p>
</sec>
<sec id="S4.SS6">
<title>Other traits</title>
<sec id="S4.SS6.SSS1">
<title>Potato plant height</title>
<p>Plant height is one of the most important traits for precision agricultural management. Plant height usually had a significantly positive correlation with yield in many types of crops, thus it is often used as an indicator of crop yield potential (<xref ref-type="bibr" rid="B91">Li et al., 2016</xref>; <xref ref-type="bibr" rid="B41">Feng et al., 2019</xref>). Besides, plant height can be used to estimate crop AGB and crop lodging. Remote sensing of plant height commonly adopts two different techniques, one directly obtaining the depth information from sensors, for example, the LiDAR devices. The other one is to estimate the 3D information from highly overlapped 2D images using photogrammetric methods such as stereo vision or structure from motion.</p>
<p>The effectiveness and accuracy of plant height measurement in remote sensing depend on the joint effects of the device type, measuring distances, algorithms, and plant variations. For estimating the potato plant height, <xref ref-type="bibr" rid="B143">ten Harkel et al. (2020)</xref> used a UAV-LiDAR system at 40 m above ground level and obtained the estimation accuracy of <italic>R</italic><sup>2</sup> = 0.50 and RMSE = 12 cm. By using photogrammetric methods, a less expensive way than the LiDAR devices is to take the difference between DSM (representing the absolute elevation of the object in image pixels) and DEMs (representing the absolute elevation of the bare ground under the canopy) derived from RGB imagery. Estimated potato heights often showed high correlations with the <italic>R</italic><sup>2</sup> = 0.93 and RMSE = 6.39 cm using a high-resolution RGB camera at a flight height of 30 m (<xref ref-type="bibr" rid="B85">Li B. et al., 2020</xref>) and <italic>R</italic><sup>2</sup> = 0.52 at a flight height of 75 m with more than 200 potato varieties (<xref ref-type="bibr" rid="B27">De Jesus Colwell et al., 2021</xref>).</p>
</sec>
<sec id="S4.SS6.SSS2">
<title>Leaf area index</title>
<p>Leaf area index is one of the most fundamental vegetation biophysical parameters, defined as a dimensionless measure of the one-sided leaf area (m<sup>2</sup>) per unit ground surface area (m<sup>2</sup>). LAI has long been reported as a good indicator of vegetation status (<xref ref-type="bibr" rid="B121">Reyes-Gonz&#x00E1;lez et al., 2019</xref>), photosynthesis rate (<xref ref-type="bibr" rid="B23">Clevers et al., 2017</xref>), biomass accumulation (<xref ref-type="bibr" rid="B149">Vi&#x00F1;a et al., 2011</xref>), evapotranspiration (<xref ref-type="bibr" rid="B74">Jung et al., 2010</xref>), yield estimation (<xref ref-type="bibr" rid="B95">Luo et al., 2020</xref>), etc. In potato growth, LAI is also crucial in estimating plant nitrogen concentration. <xref ref-type="bibr" rid="B171">Zhou et al. (2017)</xref> developed a ratio vegetation index/LAI-reference curve defining the optimal nitrogen-nutrition for potatoes throughout the season and it could be used as a diagnostic tool to detect nitrogen stress in potato plants during the season.</p>
<p>A variety of handheld instruments have been developed specifically for measuring plant LAI in field conditions, such as the LAI-2000/LAI-2200C instrument (Li-Cor, Inc, Lincoln, NE, United States) the SS1 Sun-Scan canopy analyzer (Delta-T Devices Ltd, Cambridge, United Kingdom), and AccuPAR LP-80 ceptometer (Decagon Devices, Inc). Multi-/hyper-spectral spectrometers are also commonly used to estimate LAI through empirical models that were derived from historical data between LAI measurements (by the LAI instruments) and spectral indices (<xref ref-type="bibr" rid="B63">Herrmann et al., 2011</xref>; <xref ref-type="bibr" rid="B110">Papadavid et al., 2011</xref>; <xref ref-type="bibr" rid="B23">Clevers et al., 2017</xref>). Satellite and UAV-based LAI estimates were validated for measuring at larger scales by observing significant linear relationships with the measurements of the handheld LAI instruments (<xref ref-type="bibr" rid="B63">Herrmann et al., 2011</xref>; <xref ref-type="bibr" rid="B23">Clevers et al., 2017</xref>; <xref ref-type="bibr" rid="B124">Roosjen et al., 2018</xref>).</p>
</sec>
<sec id="S4.SS6.SSS3">
<title>Leaf chlorophyll content</title>
<p>Leaf chlorophyll content (LCC) plays a significant role in plant growth, helping crops to absorb and store the energy to build their tissues. Combining carbon dioxide (absorbed from the air) and water, the stored energy can be converted into glucose through the photosynthesis process (<xref ref-type="bibr" rid="B163">Zheng et al., 2018</xref>). Then, the plants utilize the glucose and the nutrients (such as fertilizers and water) from the soil to generate new leaves and other parts, and release the produced oxygen back into the air (<xref ref-type="bibr" rid="B157">Yadav et al., 2010</xref>). The LCC is one essential indicator of plant health, and can be used to assess the photosynthetic rate, plant productivity, and nutrient level (<xref ref-type="bibr" rid="B22">Clevers and Kooistra, 2012</xref>; <xref ref-type="bibr" rid="B148">Vesali et al., 2017</xref>).</p>
<p>A portable non-imaging device, the Soil Plant Analysis Development chlorophyll meter, provides a rapid, accurate, and non-destructive approach to measure the LCC for different crops. Readings from this device have been successfully used as an indicator of plant health status and nitrogen concentrations in potato remote sensing (<xref ref-type="bibr" rid="B54">Giletto et al., 2010</xref>; <xref ref-type="bibr" rid="B117">Ram&#x00ED;rez et al., 2014</xref>, <xref ref-type="bibr" rid="B116">2015</xref>) and often used as ground truth for investigating the effectiveness of RGB and spectral images (in lab conditions) in estimating the LCC, providing the basis for monitoring the LCC <italic>in situ</italic> with the remote sensing platforms for potato management (<xref ref-type="bibr" rid="B35">Dutta Gupta et al., 2013</xref>; <xref ref-type="bibr" rid="B17">Borhan et al., 2017</xref>). Under field conditions, handheld hyperspectral spectrometer (<xref ref-type="bibr" rid="B93">Liu et al., 2020</xref>), satellite multispectral imagery (<xref ref-type="bibr" rid="B81">Kooistra and Clevers, 2016</xref>), and UAV hyperspectral imagery (<xref ref-type="bibr" rid="B49">Gevaert et al., 2015</xref>) have been explored with promising potential in estimating the potato LLC.</p>
</sec>
<sec id="S4.SS6.SSS4">
<title>Potato emergence detection and plant counting</title>
<p>Potato emergence rate and uniformity play important roles in potato field management (<xref ref-type="bibr" rid="B100">Moran et al., 1997</xref>) and yield prediction (<xref ref-type="bibr" rid="B20">Ciuberkis et al., 2007</xref>). Poor potato emergence and canopy uniformity lead to variations in the amount of canopy sunlight interception and hence varied photosynthetic efficiency (<xref ref-type="bibr" rid="B100">Moran et al., 1997</xref>). Thus, consistent potato emergence is always desirable at early growth stages and is a key trait being routinely assessed in potato agronomy and potato improvement research. Potato emergence can be affected by many factors, such as seed quality, dormancy period, soil temperature, water stress, and nutrient deficiency (<xref ref-type="bibr" rid="B131">Sankaran et al., 2017</xref>; <xref ref-type="bibr" rid="B84">Li et al., 2019</xref>). The standard method for assessing crop emergence is to visually count the number of plants that emerged at frequent intervals during the establishment phase of development, whereas the uniformity is estimated by subjective and inaccurate manual scoring (<xref ref-type="bibr" rid="B79">Knowles and Knowles, 2006</xref>; <xref ref-type="bibr" rid="B62">Herman et al., 2016</xref>). Remote sensing techniques can greatly enhance the efficiency in the emergence evaluation. There have been a number of studies leveraging UAV-based imagery and advanced machine learning methods for detecting potato emergence.</p>
<p><xref ref-type="bibr" rid="B131">Sankaran et al. (2017)</xref> observed a significant correlation (<italic>r</italic> = 0.82) between the image-based and manual plant count. Image pixels representing plant canopies were separated (by a color threshold) from the UAV-based multispectral images collected at 15 m in a potato field and then the number of image polygons were estimated as the plant count. Similarly, <xref ref-type="bibr" rid="B84">Li et al. (2019)</xref> obtained the image polygons from the UAV-based RGB images using the Otsu thresholding method. The potato emergence rate of a pixel polygon was then estimated from six morphological features of the polygon by a trained machine learning model. The estimations showed a high correlation (<italic>R</italic><sup>2</sup> = 0.96) with the manual count. Despite the excellent performance, the image plant counts in these two studies required the accurate separation of pixels between plant and background, which limits its applications for situations with non-uniform backgrounds and changing illuminations. A more adaptable way was proposed by <xref ref-type="bibr" rid="B98">Machefer et al. (2020)</xref> for potato plant counting by directly inputting UAV-based RGB images to a transferred deep learning architecture. The model was previously trained on low-density crops so a much smaller number of labeled images was needed to train the model for potato plants. Besides, no pre-processing step was required on the UAV images, which helps to keep the stable performance under varying UAV image collection conditions.</p>
</sec>
</sec>
</sec>
<sec id="S5" sec-type="conclusion">
<title>Conclusion</title>
<p>Remote sensing has great potential in characterizing potato traits for precision agricultural applications, as a promising alternative to conventional field scouting and visual examination for farmers. This review fills a critical gap in precision agriculture literature by providing a comprehensive review of the applications of remote sensing technologies specifically used in potato trait characterization. We reviewed the commonly used imaging sensors and remote sensing platforms with the comparisons of their strengths and limitations in characterizing potato traits. The main applications that are benefited from the development of advanced remote sensing technologies have been summarized with the scientific logic behind the scenes and the current research status. The applications include tuber yield prediction, AGB estimation, water stress detection, nitrogen stress assessment, and disease detection. Four other agronomic traits that were widely investigated relating to potato growth were listed as well, namely plant height, LAI, LCC, and emergence rate and plant counting. This review will update potato agronomists and farmers with the latest approaches and research outcomes, as well as provide a selective list for those who have the intentions to apply remote sensing technologies to characterize potato traits for precision agriculture.</p>
</sec>
<sec id="S6">
<title>Author contributions</title>
<p>CS: conceptualization and writing&#x2014;original draft preparation. JZ, YM, YX, and BP: writing&#x2014;reviewing and editing. ZZ: conceptualization, resources, and writing&#x2014;reviewing and editing. All authors contributed to the article and approved the submitted version.</p>
</sec>
<sec id="conf1" sec-type="COI-statement">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="pudiscl1" sec-type="disclaimer">
<title>Publisher&#x2019;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
</body>
<back>
<sec id="S7" sec-type="funding-information">
<title>Funding</title>
<p>This work was supported by the USDA National Institute of Food and Agriculture, Hatch project WIS03081, University of Wisconsin&#x2013;Madison, Office of the Vice Chancellor for Research, and Graduate Education with funding from the Wisconsin Alumni Research Foundation.</p>
</sec>
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