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<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Remote Sens.</journal-id>
<journal-title>Frontiers in Remote Sensing</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Remote Sens.</abbrev-journal-title>
<issn pub-type="epub">2673-6187</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
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<article-meta>
<article-id pub-id-type="publisher-id">1484582</article-id>
<article-id pub-id-type="doi">10.3389/frsen.2025.1484582</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Remote Sensing</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>What can we learn from a multi-season-stage-variety potato (<italic>Solanum tuberosum</italic> L.) study using aerial hyperspectral imagery?</article-title>
<alt-title alt-title-type="left-running-head">Crosby et al.</alt-title>
<alt-title alt-title-type="right-running-head">
<ext-link ext-link-type="uri" xlink:href="https://doi.org/10.3389/frsen.2025.1484582">10.3389/frsen.2025.1484582</ext-link>
</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Crosby</surname>
<given-names>Trevor</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2889063/overview"/>
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<contrib contrib-type="author">
<name>
<surname>Townsend</surname>
<given-names>Philip A.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<contrib contrib-type="author">
<name>
<surname>Ravindran</surname>
<given-names>Prabu</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<contrib contrib-type="author">
<name>
<surname>Heberlein</surname>
<given-names>Brendan C.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
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<contrib contrib-type="author">
<name>
<surname>Hills</surname>
<given-names>W. Beckett</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<contrib contrib-type="author" corresp="yes">
<name>
<surname>Wang</surname>
<given-names>Yi</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
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<aff id="aff1">
<sup>1</sup>
<institution>Department of Plant and Agroecosystem Sciences</institution>, <institution>University of Wisconsin-Madison</institution>, <addr-line>Madison</addr-line>, <addr-line>WI</addr-line>, <country>United States</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Department of Forest and Wildlife Ecology</institution>, <institution>University of Wisconsin-Madison</institution>, <addr-line>Madison</addr-line>, <addr-line>WI</addr-line>, <country>United States</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/450153/overview">Liangxiu Han</ext-link>, Manchester Metropolitan University, United Kingdom</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2194701/overview">Bee Khim Chim</ext-link>, University of Maine, United States</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2879326/overview">Ayush Sharma</ext-link>, University of Florida, United States</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Yi Wang, <email>Wang52@wisc.edu</email>
</corresp>
</author-notes>
<pub-date pub-type="epub">
<day>19</day>
<month>02</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>6</volume>
<elocation-id>1484582</elocation-id>
<history>
<date date-type="received">
<day>22</day>
<month>08</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>28</day>
<month>01</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Crosby, Townsend, Ravindran, Heberlein, Hills and Wang.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Crosby, Townsend, Ravindran, Heberlein, Hills and Wang</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>Proper monitoring of plant nitrogen (N) status and yield forecasting is essential to achieving a healthy crop and to maximizing profitability, especially in N-demanding crops such as potato. The most common method of monitoring potato N status (nitrate-N analysis of petioles) by the potato farmers in Wisconsin is time-consuming, destructive, and is impractical to sufficiently characterize spatial-temporal variability. This study utilized narrow-band hyperspectral imagery (including the visible and near-infrared (VNIR) and shortwave infrared (SWIR) spectral regions) collected over two growing seasons from two potato varieties (Russet Burbank and Soraya) grown under varied N treatments to develop robust partial least squares regression (PLSR) models for predicting potato in-season and at-harvest traits related to N. The results indicate that some traits such as leaf total N content, within-season tuber yield, and the marketable yield and quality at harvest could be well predicted for both varieties (<italic>R</italic>
<sup>2</sup> up to 0.78). The best spectral regions for those predictions varied depending on the growth stages of the plants, with VNIR predominating during early and mid-tuber, and SWIR during late tuber bulking. Our research suggests that the narrow-band hyperspectral imaging technique could be utilized to develop robust models to assist and potentially improve crop N fertilization decision-making, which will eventually result in higher input use efficiency of the cropping systems and better environmental stewardship for the farmers.</p>
</abstract>
<kwd-group>
<kwd>hyperspectral image</kwd>
<kwd>modeling</kwd>
<kwd>nitrogen</kwd>
<kwd>partial least squares regression</kwd>
<kwd>potato</kwd>
<kwd>quality</kwd>
<kwd>yield</kwd>
</kwd-group>
<contract-sponsor id="cn001">National Institute of Food and Agriculture<named-content content-type="fundref-id">10.13039/100005825</named-content>
</contract-sponsor>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Multi- and Hyper-Spectral Imaging</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1">
<title>1 Introduction</title>
<p>Potato (<italic>Solanum tuberosum</italic> L.) is a food crop that is grown globally in a wide variety of locations (<xref ref-type="bibr" rid="B30">Hijmans, 2001</xref>; <xref ref-type="bibr" rid="B20">FAO, 2021</xref>). Over 375 million tonnes of potatoes were produced around the world in 2022 (<xref ref-type="bibr" rid="B20">FAO, 2021</xref>). In the United States, potato cultivation covers approximately 400,000 ha, and produces a total raw product value of approximately $4 billion per year (<xref ref-type="bibr" rid="B49">National Potato Council, 2018</xref>). Despite the economic importance of potatoes, farmers lack sophisticated tools that allow them to accurately and efficiently monitor and predict growing status of their crop during the field season, and to aid them to achieve maximum productivity and profitability while minimizing impact of potato production on the environment.</p>
<p>Nitrogen (N) is one of the key inputs that farmers must manage to achieve high crop yield and premium quality (<xref ref-type="bibr" rid="B47">Muleta and Aga, 2019</xref>; <xref ref-type="bibr" rid="B65">Stark and Love, 2003</xref>; <xref ref-type="bibr" rid="B67">Vos, 1999</xref>; <xref ref-type="bibr" rid="B68">2009</xref>). Proper management of N fertilizer ensures the crop&#x2019;s ability to produce marketable tubers, to achieve optimal canopy size, as well as to resist pest and disease pressure and environmental stresses such as drought and heat (<xref ref-type="bibr" rid="B65">Stark and Love, 2003</xref>). In spite of the essential role of N, the potato plant itself is generally inefficient at taking up N. Potatoes have shallow roots, with the majority of them confined to the top 30&#xa0;cm of the soil (<xref ref-type="bibr" rid="B18">Epstein and Grant, 1973</xref>; <xref ref-type="bibr" rid="B65">Stark and Love, 2003</xref>). Potatoes in the U.S. are commonly grown on coarse-textured soils (<xref ref-type="bibr" rid="B90">King et al., 2020</xref>) in the northern part of the country that have low soil organic matter content (&#x3c;10&#xa0;g&#xa0;kg<sup>-1</sup>) and relatively shallow ground water tables. This soil feature together with rain events that produce soil saturation during the growing season are significant contributors to nitrate leaching and groundwater contamination in many regions of the country (<xref ref-type="bibr" rid="B35">Kraft et al., 1999</xref>; <xref ref-type="bibr" rid="B34">Kraft and Stites, 2003</xref>; <xref ref-type="bibr" rid="B37">Leghari et al., 2016</xref>; <xref ref-type="bibr" rid="B65">Stark and Love, 2003</xref>). Due to these factors, precision application of N fertilizer by potato farmers is highly necessary.</p>
<p>The most widely used method of monitoring N status and planning for fertilization is by collecting petiole tissues from the plants and analyzing them in a laboratory to determine the nitrate-N concentration (<xref ref-type="bibr" rid="B58">Rosen and Bierman, 2008</xref>; <xref ref-type="bibr" rid="B65">Stark and Love, 2003</xref>). If the petiole nitrate-N is lower than the published sufficiency range, a supplemental N fertilizer application is recommended, typically by 11&#x2013;34&#xa0;kg&#xa0;N&#xa0;ha<sup>-1</sup> (<xref ref-type="bibr" rid="B14">Colquhoun et al., 2020</xref>). Aside from petiole sampling, similar analysis of total N in other plant parts, most often the entire leaf or a portion of the canopy, are also utilized to assess N status of the plants (<xref ref-type="bibr" rid="B32">Jones et al., 2021</xref>; <xref ref-type="bibr" rid="B56">Reis Jr and Monnerat, 2000</xref>; <xref ref-type="bibr" rid="B36">Lauer, 1985</xref>). Petiole nitrate-N reflects the immediate N status of the plants at the time of testing, and total N in leaves or vines indicates the accumulated N uptake of the plants from planting up until the point of test (<xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>). However, these field sampling methods can only collect site-specific information from the sampled location in the field, with no ability to cover any spatial-temporal variability that might lead to under- or over-application of N fertilizer. Under-application could result in tuber yield and quality reduction, and over-application is often associated with underdevelopment of tuber skin at harvest and high chance of pathogen infection during storage, as well as nitrate leaching and groundwater quality issues.</p>
<p>With growers&#x2019; interest in adopting new technologies to maximize their fertilizer use efficiency and increase precision in their crop management, agricultural remote sensing has expanded rapidly into new areas of application in recent years (<xref ref-type="bibr" rid="B52">Pinter Jr et al., 2003</xref>). Remote sensing techniques are of particular interest and value to the agricultural industry due to the unique challenges that it faces, such as the seasonality in biological life cycles and the weather and climate variables that can impact crop production (<xref ref-type="bibr" rid="B7">Atzberger, 2013</xref>). By avoiding contact with the crop, remote sensing allows for data collection that is not invasive and destructive compared to the traditional field sampling methods. As well, remote sensing has the potential to be more time-efficient and less labor-intensive than field sampling (<xref ref-type="bibr" rid="B4">Alkhaled et al., 2023</xref>). Remote sensing in agriculture generally uses the relationship that leaf or canopy spectral signature has with biological traits of the plants to estimate or predict information on features of the crop (<xref ref-type="bibr" rid="B16">Curran, 1989</xref>; <xref ref-type="bibr" rid="B48">Mu&#xf1;oz-Huerta et al., 2013</xref>). The optical properties used to obtain this information may stem from characteristics such as spectral reflectance or transmittance of plant tissues as well as fluorescence of chlorophyll or polyphenol (<xref ref-type="bibr" rid="B48">Mu&#xf1;oz-Huerta et al., 2013</xref>). Because N is a critical element in chlorophyll synthesis, photosynthetic capacity and plant productivity, spectral regions associated with chlorophyll content are oftentimes the key basis for evaluations of crop N status and vigor (<xref ref-type="bibr" rid="B2">Ali, 2020</xref>; <xref ref-type="bibr" rid="B17">Delloye et al., 2018</xref>; <xref ref-type="bibr" rid="B51">Patane and Vibhute, 2014</xref>; <xref ref-type="bibr" rid="B61">Schlemmer et al., 2013</xref>). As a pigment, chlorophyll content is directly associated with reflectance from the visible and near-infrared (VNIR) spectral regions (<xref ref-type="bibr" rid="B16">Curran, 1989</xref>; <xref ref-type="bibr" rid="B19">Evans, 1989</xref>; <xref ref-type="bibr" rid="B25">Gitelson and Merzlyak, 1996</xref>; <xref ref-type="bibr" rid="B26">1998</xref>). In addition, many spectral ranges in the shortwave infrared (SWIR) region (1,400&#xa0;nm&#x2013;2,500&#xa0;nm) are correlated with plant traits such as content of starch, lignin, protein, cellulose, and nonstructural carbohydrates (<xref ref-type="bibr" rid="B16">Curran, 1989</xref>; <xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>). Together, spectra from the visible through shortwave infrared (VSWIR, 400&#x2013;2,500&#xa0;nm) offer great potential for concurrent mapping of many plant traits (<xref ref-type="bibr" rid="B70">Wang et al., 2020</xref>). In agriculture, these traits can directly influence plant total N content, plant vigor, yield and quality.</p>
<p>Handheld sensors have been deployed in N content prediction (<xref ref-type="bibr" rid="B1">Abdelbaki et al., 2021</xref>; <xref ref-type="bibr" rid="B2">Ali, 2020</xref>; <xref ref-type="bibr" rid="B3">Ali et al., 2020</xref>; <xref ref-type="bibr" rid="B53">Prikaziuk et al., 2022</xref>; <xref ref-type="bibr" rid="B64">Singh et al., 2018</xref>; <xref ref-type="bibr" rid="B74">Zheng et al., 2018</xref>), and remote cameras mounted on unmanned aerial vehicles have also been used to predict crop N status (<xref ref-type="bibr" rid="B1">Abdelbaki et al., 2021</xref>; <xref ref-type="bibr" rid="B11">Cai et al., 2019</xref>; <xref ref-type="bibr" rid="B38">Li et al., 2020</xref>; <xref ref-type="bibr" rid="B39">Li et al., 2018</xref>; <xref ref-type="bibr" rid="B74">Zheng et al., 2018</xref>). These smaller-scale methods often have high resolution but are less adept at effectively capturing information from large agricultural areas, compared to larger-scale methods such as imagery collected from airplanes and satellites. In addition, the use of a small number of broadband spectral data captured in multispectral imagery may fail to capture the nuance of a crop canopy&#x2019;s spectral signatures. By comparison, hyperspectral imagery collects continuous measurements of spectral data from a wide range of narrow bands across the electromagnetic spectrum, and it is these narrow features that enable detection of foliar nutrition (<xref ref-type="bibr" rid="B16">Curran, 1989</xref>; <xref ref-type="bibr" rid="B44">Martin and Aber, 1997</xref>). Hyperspectral images are generally described as a data cube, with the X and Y planes containing spatial information and the Z plane containing a large range of spectral information, i.e., each &#x201c;pixel&#x201d; in the image is a continuous spectrum covering the VSWIR wavelengths (<xref ref-type="bibr" rid="B62">Shukla and Kot, 2016</xref>).</p>
<p>Partial least squares regression (PLSR) is a statistical model which utilizes weighted predictor components to model the relationship between predictor variables and a response variable (<xref ref-type="bibr" rid="B24">Garthwaite, 1994</xref>). A key feature of PLSR is that it uses latent variables to explain the effects of correlated independent variables, causing it to perform well in situations where multicollinearity is high (<xref ref-type="bibr" rid="B29">Haenlein and Kaplan, 2004</xref>; <xref ref-type="bibr" rid="B71">Wold et al., 1984</xref>). Multicollinearity is an issue that occurs when two or more independent variables in a multiple regression model are highly correlated, resulting in a raised or lowered standard error within the coefficients of the model, and ultimately leading to models that are overfitted and difficult to accurately interpret (<xref ref-type="bibr" rid="B66">Tsagris and Pandis, 2021</xref>). Multicollinearity is a critical concern when developing predictive models using hyperspectral data, as the number of ground-truthed field measurements can be considerably fewer than the number of initial wavelengths, resulting in high correlation between the independent variables of the model (<xref ref-type="bibr" rid="B28">Grossman et al., 1996</xref>; <xref ref-type="bibr" rid="B43">Martens and Naes, 1992</xref>). For this reason, PLSR has been used to avoid overfitting while accurately predicting foliar chemistry from hyperspectral imagery, including traits associated with plant N status and productivity (<xref ref-type="bibr" rid="B6">Asner et al., 2015</xref>; <xref ref-type="bibr" rid="B38">Li et al., 2020</xref>; <xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>; <xref ref-type="bibr" rid="B50">Nguyen and Lee, 2006</xref>; <xref ref-type="bibr" rid="B63">Singh et al., 2015</xref>; <xref ref-type="bibr" rid="B70">Wang et al., 2020</xref>; <xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>).</p>
<p>While the use of hyperspectral remote sensing to capture a wide range of narrowband reflectance values from the full VSWIR has been shown to aid in the prediction of biophysical traits of plants, this technology has not been widely investigated in most crops, including potatoes. Much of the existing scientific literature on predictions of potato N status from hyperspectral data only focuses on the visible-near infrared (VNIR) region, which in remote sensing covers the range of 400&#xa0;nm&#x2013;1,000&#xa0;nm (<xref ref-type="bibr" rid="B1">Abdelbaki et al., 2021</xref>; <xref ref-type="bibr" rid="B13">Cohen et al., 2010</xref>; <xref ref-type="bibr" rid="B38">Li et al., 2020</xref>; <xref ref-type="bibr" rid="B31">Jain et al., 2007</xref>; <xref ref-type="bibr" rid="B46">Morier et al., 2015</xref>).</p>
<p>The objective of the research presented in this paper is to develop data-driven models to predict in-season and at-harvest aboveground and belowground traits of potato plants grown under different N treatments using hyperspectral data from a 2-year field study. By using image data from multiple years and across the growing season, this research addresses issues of generalizability that arise from analyses using data from a single plant growth stage or year, since the relevant spectral characteristics may differ seasonally or between years if climatic conditions differ. The models developed in this study will likely allow potato growers to make more informed management decisions, resulting in more efficient use of N fertilizer while still optimizing crop yield and quality, and minimizing the impact of fertilizer use on the invaluable ground water resource.</p>
</sec>
<sec id="s2">
<title>2 Data and methods</title>
<sec id="s2-1">
<title>2.1 Field data</title>
<sec id="s2-1-1">
<title>2.1.1 Study location, experimental design, and weather conditions</title>
<p>A 2-year field trial was conducted at the University of Wisconsin-Madison Hancock Agricultural Research Station (Hancock, WI, latitude: 44.12&#xb0;N; longitude 89.53&#xb0;W; elevation 328&#xa0;m) using a randomized complete block design for each variety. In 2020, only Russet Burbank (a fry processing variety) was grown, and in 2021 both Russet Burbank and Soraya (a yellow fresh market variety) were grown. Russet Burbank is the No.1 potato variety grown in the U.S., and it is highly N-demanding (<xref ref-type="bibr" rid="B9">Bethke, et al., 2014</xref>). Soraya is a recently released variety from the Netherlands, and was bred to develop small canopies with minimum use of N fertilizer but high yield potential (D. Maum, personal communication, 10 January 2020). The soil type in this location is categorized as a loamy fine sand (organic matter &#x3c;1%) from a depth of 0&#x2013;45&#xa0;cm and as a fine sand (organic matter &#x3c;0.5%) from a depth of 45&#x2013;75&#xa0;cm. Each plot consisted of eight 6-m by 0.9-m rows. Within a plot, the outermost rows (rows one and 8) were used as guard rows, rows 2 and 3 were used for in-season tuber digging and whole vine collection, rows 4 and 5 were used for in-season petiole and leaf collection, and rows 6 and 7 were harvested for final yield and quality evaluation. The study included four replications of 4&#xa0;N fertilizer treatments, each treatment with varied fertilizer amounts and application timings (<xref ref-type="table" rid="T1">Table 1</xref>). Stater fertilizer was banded with a planter attachment. Fertilizer at hilling was banded and incorporated. All the in-season fertilizer was side dressed and irrigated immediately. Aside from N application, other production practices including irrigation and pest management were performed following University of Wisconsin&#x2013;Madison Extension recommendations (<xref ref-type="bibr" rid="B14">Colquhoun et al., 2020</xref>).</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Nitrogen application treatments applied in this study.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Application</th>
<th colspan="2" align="center">Date</th>
<th rowspan="2" align="center">Treatments receiving N</th>
<th align="center">Applied N</th>
<th align="center">Seasonal total N</th>
<th rowspan="2" align="center">Final treatments</th>
</tr>
<tr>
<th align="center">2020</th>
<th align="center">2021</th>
<th colspan="2" align="center">(kg ha<sup>-1</sup>)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Starter</td>
<td align="center">5/1</td>
<td align="center">4/26</td>
<td align="left">All</td>
<td align="center">45</td>
<td align="center">45</td>
<td align="center">Control</td>
</tr>
<tr>
<td align="left">Hilling</td>
<td align="center">5/21</td>
<td align="center">5/17</td>
<td align="left">Rate 1, 2, and 3</td>
<td align="center">78</td>
<td align="center">123</td>
<td align="left"/>
</tr>
<tr>
<td align="left">Tuber Initiation</td>
<td align="center">6/12</td>
<td align="center">6/9</td>
<td align="left">Rate 1, 2, and 3</td>
<td align="center">45</td>
<td align="center">168</td>
<td align="left"/>
</tr>
<tr>
<td align="left">Early Bulking</td>
<td align="center">7/8</td>
<td align="center">7/2</td>
<td align="left">Rate 1 and 3</td>
<td align="center">56</td>
<td align="center">224</td>
<td align="center">Rate 1</td>
</tr>
<tr>
<td align="left">Mid-Bulking</td>
<td align="center">7/20</td>
<td align="center">7/16</td>
<td align="left">Rate 2</td>
<td align="center">56</td>
<td align="center">224</td>
<td align="center">Rate 2</td>
</tr>
<tr>
<td align="left">Mid-Bulking</td>
<td align="center">7/20</td>
<td align="center">7/16</td>
<td align="left">Rate 3</td>
<td align="center">56</td>
<td align="center">280</td>
<td align="center">Rate 3</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Planting occurred on 1 May 2020 and 22 April 2021. Emergence was observed on 25 May 2020 and 20 May 2021 respectively. Monthly average air temperature and average precipitation between May and August in 2020 and 2021 is shown in <xref ref-type="sec" rid="s11">Supplemental Figure 1</xref>. In both years, daily minimum temperatures dropped below freezing (0&#xb0;C) within 2&#xa0;weeks of planting. While precipitation events were generally evenly distributed across 2020, there was one large (approximately 5&#xa0;cm) precipitation 2&#xa0;weeks after planting. In 2021, a long dry spell coincided with daily average temperatures above 30&#xb0;C in early-to-mid June. Overall higher variation in precipitation amounts were observed with frequent small or large events in 2021 than 2020.</p>
</sec>
<sec id="s2-1-2">
<title>2.1.2 Ground truthing data collection</title>
<p>All in-season sampling occurred between 8:00 a.m. and 12:00 p.m. 1&#xa0;day at early, mid-, and late tuber bulking stages respectively in each year. Petioles and whole leaves (petioles &#x2b; leaflets) were collected from 20 randomly selected healthy plants per plot for nitrate-N and total N analysis separately. On the same day, three healthy plants per plot were randomly removed and separated for whole canopy samples (including leaves, stems and flowers) and tuber samples. Whole canopy samples were measured for biomass at sampling and were chopped into pieces to measure total N content and total N uptake later. Tuber samples were measured for tuber biomass at sampling. Petiole, whole leaf, and whole canopy samples were placed into paper bags separately and transported to a dryer at 70&#xb0;C for a minimum duration of 48&#xa0;h until no more weight was lost. Post drying, the tissues were ground using a Wiley mini mill (Thomas Scientific, Swedesboro, New Jersey) to facilitate passage through a 2-mm sieve.</p>
<p>For petiole nitrate-N analysis, extraction of nitrate was conducted with 2% acetic acid (<xref ref-type="bibr" rid="B42">MacKown and Weik, 2004</xref>). Firstly 0.10&#xa0;g of ground dry tissue samples was weighed into a 50&#xa0;mL centrifuge tube before the addition of 25&#xa0;mL of 2% acetic acid. Capped tubes were then shaken for 15&#xa0;minutes before filtration of samples through Whatman No. 2 filter papers. The filtered samples were analyzed by flow injection analysis on a Fialyzer 1,000 Series instrument (FIALab, Seattle, WA) using a nitrate/nitrite analysis by the Griess method with cadmium reduction of nitrate to nitrite (<xref ref-type="bibr" rid="B23">Gal et al., 2004</xref>). Unit of petiole nitrate-N was mg (kg of dry weight)<sup>&#x2212;1</sup>.</p>
<p>For total N content analysis of whole leaves and whole canopies, ground dry tissue samples were weighed (2 &#x2013; 5&#xa0;mg) into tin foil capsules and analyzed using an elemental combustion analyzer (Costech Analytical Technologies, INC., Valencia, CA). Whole canopy total N uptake per plot was calculated by the equation: whole canopy dry weight &#xd7; total N %.</p>
<p>All plots were harvested to measure marketable yield, tuber specific gravity, and fertilizer N recovery % in late September of both years. Tubers were washed and graded by weight (for Russet Burbank) or diameter (for Soraya) using an AgRay Vision x-ray grading machine (AgRay Vision, Acampo, California). Marketable yield was calculated as the yield of non-culled tubers that had a weight larger than 170&#xa0;g (for Russet Burbank) or a diameter larger than 3.8&#xa0;cm (for Soraya). These values were used to reflect regional industry standards. Culled tubers that were misshaped, diseased or defected were disposed. Tuber quality was assessed by measuring specific gravity (an indicator for tuber starch content) with a Weltech PW-2050 Dry Matter Assessment System. After taking the weight of a 2000 g&#x2013;3,000&#xa0;g of tuber samples from each plot in the air and in water, the system used the following formula to calculate the specific gravity for the sample (<xref ref-type="bibr" rid="B33">Kleinkopf, et al., 1987</xref>):<disp-formula id="equ1">
<mml:math id="m1">
<mml:mrow>
<mml:mtext>Specific&#x2009;Gravity</mml:mtext>
<mml:mo>&#x3d;</mml:mo>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mtext>Weight&#x2009;in&#x2009;air</mml:mtext>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mo>/</mml:mo>
<mml:mtext>&#x2009;</mml:mtext>
<mml:mrow>
<mml:mfenced open="(" close=")" separators="|">
<mml:mrow>
<mml:mtext>Weight&#x2009;in&#x2009;air&#x2009;</mml:mtext>
<mml:mo>&#x2013;</mml:mo>
<mml:mtext>&#x2009;Weight&#x2009;in&#x2009;water</mml:mtext>
</mml:mrow>
</mml:mfenced>
</mml:mrow>
</mml:mrow>
</mml:math>
</disp-formula>
</p>
<p>Subsequently, a subsample of tubers ranging from 200 to 350&#xa0;g were randomly selected from the same batch, chopped and placed in paper bags for drying at 70&#xb0;C until no weight was lost. Post drying, these samples were ground using a Thomas-Wiley laboratory mill (Model 4) to pass through a 2-mm sieve, ground dry tuber tissue samples were then weighed (2 &#x2013; 5&#xa0;mg) into tin foil capsules and analyzed for total N content (% dry weight basis) of the plants in each plot. Total N uptake per plot was calculated by the equation: tuber dry weight &#xd7; total N %. Fertilizer N recovery % was defined as the ratio of N that was taken up by the tubers and removed from the field during harvest to the seasonal total N applied.</p>
</sec>
</sec>
<sec id="s2-2">
<title>2.2 Imaging data collection and processing</title>
<p>A co-aligned HySpex (Norsk Elektro Optikk, Norway) system was utilized to capture hyperspectral imagery during each field season. This system was made up of a VNIR-1800 camera with 186 spectral bands between 400&#xa0;nm and 1,000&#xa0;nm and a spectral resolution of 3.26&#xa0;nm, as well as a SWIR-384 camera with 288 spectral bands between 953&#xa0;nm and 2,518&#xa0;nm and a resolution of 5.45&#xa0;nm. The flight was at an altitude of approximately 365&#xa0;m above the ground, giving a spatial resolution of 0.25&#xa0;m in the VNIR-1800 system and 0.5&#xa0;m in the SWIR-348 system. Imagery collection dates (as indicated by crops&#x2019; days after emergence (DAE)) in 2020 and 2021 were chosen to ensure they covered the critical potato growth stages in each field season. They included: early tuber bulking (53 DAE in 2020 and 51 DAE in 2021), mid tuber bulking (61 DAE in 2020 and 59 DAE in 2021), and late tuber bulking (81 DAE in 2020 and 85 DAE in 2021). Imagery collection dates were coordinated with field sampling dates as closely as possible, although weather factors (primarily precipitation and cloud coverage) limited the ability to align flight dates perfectly. For predictions of in-season traits, ground truthing data was paired with imaging data only when their collection dates were no more than 3&#xa0;days apart. Pairs of collection dates for aerial imaging and in-season field measurement in this study are shown in <xref ref-type="table" rid="T2">Table 2</xref>. Data from Russet Burbank and Soraya individually and combined were used for in-season predictions. End-of-season traits were predicted using at-harvest measurements paired with spectral data collected at early, mid- and late tuber bulking separately in each of the 2&#xa0;years. In addition, models for end-of-season traits were developed using spectral data collected from all three growth stages combined across the 2&#xa0;years. This paper reported at-harvest predictions for Russet Burbank because only this variety was grown in both years.</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Timeline of data collection (as indicated by days after emergence) for paired imaging and in-season field measurements.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Growth stage</th>
<th colspan="2" align="center">2020</th>
<th colspan="2" align="center">2021</th>
</tr>
<tr>
<th align="left">Imagery</th>
<th align="left">Ground truthing</th>
<th align="left">Imagery</th>
<th align="left">Ground truthing</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Early tuber bulking</td>
<td align="left">53</td>
<td align="left">54</td>
<td align="left">51</td>
<td align="left">51</td>
</tr>
<tr>
<td align="left">Mid tuber bulking</td>
<td align="left">61</td>
<td align="left">61</td>
<td align="left">59</td>
<td align="left">60</td>
</tr>
<tr>
<td align="left">Late tuber bulking</td>
<td align="left">81</td>
<td align="left">78</td>
<td align="left">85</td>
<td align="left">88</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>HySpex images were processed using a consistent and open-source workflow following <xref ref-type="bibr" rid="B40">Liu et al. (2021)</xref>, <ext-link ext-link-type="uri" xlink:href="https://github.com/EnSpec/hypro">https://github.com/EnSpec/hypro</ext-link>). Processing steps included radiometric calibration using manufacturer-provided coefficients, correction for smile effects (shifts in wavelength position across spectrometer focal array (<xref ref-type="bibr" rid="B60">Schl&#xe4;pfer and Richter, 2010</xref>), orthorectification to &#x3c;1&#xa0;m precision using GPS-IMU data, atmospheric correction (<xref ref-type="bibr" rid="B57">Richter and Schl&#xe4;pfer, 2010</xref>), and correction of bi-directional reflectance distribution effects due to variations in sun-sensor-target geometry across flightlines (<xref ref-type="bibr" rid="B54">Queally et al., 2022</xref>).</p>
<p>Spectral smoothing and data extraction for statistical analyses Savitzky&#x2013;Golay filter (window size: 7) was used to reduce noise in surface reflectance (<xref ref-type="bibr" rid="B59">Schafer, 2011</xref>). Then, the average reflectance of all vegetation pixels within each subplot was extracted. Non-vegetation pixels (e.g., shadows and soil) were excluded using NDVI<italic>&#x3c;</italic>0.5. Vector normalization was performed to reduce the effects of illumination conditions on reflectance (<xref ref-type="bibr" rid="B6">Asner et al., 2015</xref>; <xref ref-type="bibr" rid="B22">Feilhauer et al., 2010</xref>). Reflectance values extracted from the hyperspectral imagery were averaged over each plot for modeling. Spectral data from atmospheric water absorption features at 1,320&#x2013;1,470&#xa0;nm and 1780&#x2013;2000&#xa0;nm were removed from analysis, as were noisy data from 2,350&#x2013;2,500&#xa0;nm. Plot mean reflectance values were paired with the target predicted trait measured from each plot and were then used to build partial least squares regression (PLSR) models. All steps were performed using the open-source Geospatial Data Abstraction Library (GDAL, version 3.0.4), as well as Python packages Pillow (6.2.0), Numpy (1.17.2) and Scipy (1.3.1).</p>
</sec>
<sec id="s2-3">
<title>2.3 Modeling</title>
<p>All PLSR modeling was done using the HyTraits package in Python. PLSR analyses (<xref ref-type="fig" rid="F1">Figure 1</xref>) consisted of an outer loop, where the original dataset was split into a calibration (70%) and testing (30%) dataset, and an inner loop, where the calibration dataset was further split into a training (70%) and validation (30%) dataset, which was used for hyperparameter testing. Models were built using different values for the maximum number of components in the PLS process, with the model that performed the best on the validation data being saved. The outer loop was nested within the inner loop, with each inner loop process repeated 100 times, and a total of 200 outer loop processes. This pipeline yielded 200 final models that were saved from each model&#x2019;s respective inner loop process. Final predictions were created by averaging the output of these 200 final models. Models were evaluated according to the testing <italic>R</italic>
<sup>2</sup> and Normalized Root Mean Square Error (NRMSE). The standardized regression coefficients were used to evaluate the contribution of each wavelength to the estimation of potato traits (<xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>A flowchart illustrating the HyTraits PLSR modeling process.</p>
</caption>
<graphic xlink:href="frsen-06-1484582-g001.tif"/>
</fig>
<p>Cross-year validation was conducted where the models were calibrated using data from 1&#xa0;year and tested on data from the other year. Only data from Russet Burbank that was cultivated in both years was used for the cross-year validation. Cross-variety validation was performed using data from one variety for calibration and those from the other variety for testing. In addition to models using the entire spectrum (400&#xa0;nm&#x2013;2,500&#xa0;nm), models were built using only the visible-near infrared (VNIR) spectrum (400&#xa0;nm&#x2013;1,300&#xa0;nm) or the shortwave infrared (SWIR) spectrum (1,400&#xa0;nm&#x2013;2,500&#xa0;nm) (<xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>).</p>
<p>All data management was performed using the Python (version 3.8.8) packages NumPy (version 1.20.1), pandas (version 1.2.4), and SciKit Learn (version 0.24.1) and the R (<xref ref-type="bibr" rid="B55">R Core Team, 2019</xref>) package ggplot2 (version 3.4.2).</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>3 Results</title>
<sec id="s3-1">
<title>3.1 Evaluation of PLSR models created to predict in-season and at-harvest traits using the whole spectrum</title>
<p>For analyses using both years, model performance across all five in-season traits of interest and by variety exhibited <italic>R</italic>
<sup>2</sup> &#x3e; 0.5 and NRMSE ranging 0.15&#x2013;0.27 (<xref ref-type="fig" rid="F2">Figure 2</xref>). Compared to the control treatment, the three higher N rates (Rate one&#x2013;3) were consistently associated with higher N status indicators, and higher total N uptake in both aboveground whole canopies and belowground tubers. However, no general trends could be summarized about N effects on the in-season immediate tuber yield. In most cases, the models created using the Russet Burbank data alone slightly outperformed those created using the Soraya data alone or models created from both varieties.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>PLSR modelling testing results (testing <italic>R</italic>
<sup>2</sup> and Normalized Root Mean Square Error (NRMSE)) of in-season aboveground traits including petiole nitrate-N, leaf total nitrogen (N) content, and whole canopy N uptake, and belowground traits that included tuber N uptake and immediate tuber yield of each variety as well as of both varieties combined. In each figure, different colors were used to indicate the 2&#xa0;years, and different marks were used to indicate the 4&#xa0;N treatments. Horizontal bars indicate the uncertainty (&#xb1;1 standard deviation) in predictions.</p>
</caption>
<graphic xlink:href="frsen-06-1484582-g002.tif"/>
</fig>
<p>Models built from the leaf data had better performance (total leaf N, <italic>R</italic>
<sup>2</sup> &#x3d; 0.66&#x2013;0.70) than those built from the petiole data (petiole nitrate-N, <italic>R</italic>
<sup>2</sup> &#x3d; 0.54&#x2013;0.58). Models predicting whole canopy N uptake showed moderate accuracy, whereas those predicting tuber N uptake and in-season immediate yield were strong with <italic>R</italic>
<sup>2</sup> values ranging from 0.52 to 0.71.</p>
<p>Prediction of traits measured at harvest are shown in <xref ref-type="fig" rid="F3">Figure 3</xref>. The control treatment consistently produced the lowest yield, smallest tuber size, and lowest fertilizer N recovery % at harvest. No trend of N effects on specific gravity were observed. Marketable yields in 2021 were higher than those in 2020 across all treatments, likely due to different weather conditions during the two growing seasons. In general, models built from imaging data collected from the three different growth stages had comparable results, with the best results from early- and mid-tuber bulking stages. In all cases, models predicting marketable yield and specific gravity all performed well (<italic>R</italic>
<sup>2</sup> &#x3e; 0.6), whereas models predicting fertilizer N recovery % exhibited lower evaluation statistics (<italic>R</italic>
<sup>2</sup> &#x3c; 0.4).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>PLSR modeling testing results (testing <italic>R</italic>
<sup>2</sup> and Normalized Root Mean Square Error (NRMSE)) of at-harvest traits that included marketable yield, specific gravity and fertilizer nitrogen recovery using images collected at early, mid-, and late tuber bulking stages across the 2&#xa0;years for Russet Burbank. In each figure, different colors were used to indicate the 2&#xa0;years, and different marks were used to indicate the 4&#xa0;N treatments. Horizontal bars indicate the uncertainty (&#xb1;1 standard deviation) in predictions.</p>
</caption>
<graphic xlink:href="frsen-06-1484582-g003.tif"/>
</fig>
<p>Models to predict at-harvest traits using spectral data combined from all three growth stages (named multi-stage models) for Russet Burbank typically did not improve in comparison to those built using only one date of imagery (named single-date models), except for marketable yield (data not shown). No general trends emerged when comparing multi-stage models with the single-date models developed using imagery from the mid- or late tuber bulking stages.</p>
</sec>
<sec id="s3-2">
<title>3.2 Cross-year and cross-variety validation results</title>
<p>In general, models calibrated with Soraya and tested with Russet Burbank generated similar or better prediction results (similar or higher <italic>R</italic>
<sup>2</sup>) for both aboveground and belowground traits than those calibrated with Russet Burbank and tested with Soraya (<xref ref-type="table" rid="T3">Table 3</xref>). The belowground tuber N uptake could be well validated both ways with <italic>R</italic>
<sup>2</sup> close to or higher than 0.6. Comparatively, predictions of the immediate tuber yield could not be well validated across the two varieties.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Evaluation statistics of cross-variety validation models to predict in-season aboveground and belowground potato traits.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="2" align="center">Trait</th>
<th colspan="2" align="center">Calibration with soraya and tested with RB</th>
<th colspan="2" align="center">Calibration with RB and tested with soraya</th>
</tr>
<tr>
<th align="center">
<italic>R</italic>
<sup>2</sup>
</th>
<th align="center">NRMSE</th>
<th align="center">
<italic>R</italic>
<sup>2</sup>
</th>
<th align="center">NRMSE</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Petiole Nitrate-N</td>
<td align="center">0.48</td>
<td align="center">0.20</td>
<td align="center">0.52</td>
<td align="center">0.19</td>
</tr>
<tr>
<td align="left">Leaf Total N</td>
<td align="center">0.39</td>
<td align="center">0.36</td>
<td align="center">0.17</td>
<td align="center">0.49</td>
</tr>
<tr>
<td align="left">Whole canopy total N uptake</td>
<td align="center">0.42</td>
<td align="center">0.24</td>
<td align="center">0.17</td>
<td align="center">0.47</td>
</tr>
<tr>
<td align="left">Tuber total N uptake</td>
<td align="center">0.55</td>
<td align="center">0.16</td>
<td align="center">0.67</td>
<td align="center">0.13</td>
</tr>
<tr>
<td align="left">Immediate tuber yield</td>
<td align="center">0.31</td>
<td align="center">0.43</td>
<td align="center">0.05</td>
<td align="center">0.49</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>For the cross-year validation, the multi-stage model predicting marketable yield showed better performances with higher <italic>R</italic>
<sup>2</sup> and lower NRMSE than the single-date models for both ways of validation (<xref ref-type="table" rid="T4">Table 4</xref>). Specific gravity could not be well validated in either case. Fertilizer N recovery % showed moderate validation results across different growth stages or over the whole season.</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>Cross-year validation results that show evaluation statistics of single-date (at early, mid- and late tuber bulking) and multi-stage models predicting at-harvest traits for Russet Burbank.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th rowspan="3" align="left">Traits</th>
<th colspan="2" align="center">Early tuber bulking</th>
<th colspan="2" align="center">Mid-tuber bulking</th>
<th colspan="2" align="center">Late tuber bulking</th>
<th colspan="2" align="center">Multi-stage</th>
</tr>
<tr>
<th align="center">
<italic>R</italic>
<sup>2</sup>
</th>
<th align="center">NRMSE</th>
<th align="center">
<italic>R</italic>
<sup>2</sup>
</th>
<th align="center">NRMSE</th>
<th align="center">
<italic>R</italic>
<sup>2</sup>
</th>
<th align="center">NRMSE</th>
<th align="center">
<italic>R</italic>
<sup>2</sup>
</th>
<th align="center">NRMSE</th>
</tr>
<tr>
<th colspan="8" align="center">Calibration with 2021 and tested with 2020</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Marketable yield</td>
<td align="center">0.16</td>
<td align="center">0.37</td>
<td align="center">0.07</td>
<td align="center">0.41</td>
<td align="center">0.28</td>
<td align="center">0.32</td>
<td align="center">0.48</td>
<td align="center">0.22</td>
</tr>
<tr>
<td align="left">Specific gravity</td>
<td align="center">0.03</td>
<td align="center">0.44</td>
<td align="center">0.02</td>
<td align="center">0.54</td>
<td align="center">0.07</td>
<td align="center">0.49</td>
<td align="center">0.01</td>
<td align="center">0.55</td>
</tr>
<tr>
<td align="left">Fertilizer N recovery %</td>
<td align="center">0.36</td>
<td align="center">0.28</td>
<td align="center">0.3</td>
<td align="center">0.29</td>
<td align="center">0.24</td>
<td align="center">0.29</td>
<td align="center">0.25</td>
<td align="center">0.27</td>
</tr>
</tbody>
</table>
<table>
<thead valign="top">
<tr>
<th colspan="9" align="center">Calibration with 2020 and tested with 2021</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Marketable yield</td>
<td align="center">0.24</td>
<td align="center">0.32</td>
<td align="center">0.25</td>
<td align="center">0.3</td>
<td align="center">0.29</td>
<td align="center">0.28</td>
<td align="center">0.53</td>
<td align="center">0.19</td>
</tr>
<tr>
<td align="left">Specific gravity</td>
<td align="center">0.02</td>
<td align="center">0.56</td>
<td align="center">0.01</td>
<td align="center">0.59</td>
<td align="center">0.22</td>
<td align="center">0.32</td>
<td align="center">0.02</td>
<td align="center">0.55</td>
</tr>
<tr>
<td align="left">Fertilizer N recovery %</td>
<td align="center">0.25</td>
<td align="center">0.3</td>
<td align="center">0.29</td>
<td align="center">0.31</td>
<td align="center">0.22</td>
<td align="center">0.3</td>
<td align="center">0.23</td>
<td align="center">0.29</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s3-3">
<title>3.3 Standardized regression coefficients</title>
<p>Full spectrum standardized regression coefficient values (&#x201c;coefficients&#x201d; in short) illustrate the contribution of different wavelengths or wavelength regions to models predicting in-season aboveground and belowground traits (<xref ref-type="fig" rid="F4">Figure 4</xref>). For interpretation, these are used to identify the plant spectral characteristics that contribute to the prediction capacity, in particular since some traits (e.g., marketable yield, specific gravity) are not directly sensed in the imagery, but rather are inferred from foliar characteristics. In both the VNIR and SWIR regions, coefficient weights typically followed consistent trends among the different trait prediction models. The coefficients of features from the regions (530&#x2013;630&#xa0;nm and 700&#x2013;750&#xa0;nm) mostly associated with chlorophyll had relatively large weights. Coefficients from the red-edge position (680&#xa0;nm&#x2013;780&#xa0;nm) were weighted heavily as well. Although coefficients from the near-infrared region were not consistently weighted heavily, some portions of this region had high weights, particularly from 900 to 1,200&#xa0;nm (the region that is related to plant structure).</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>Standardized regression coefficients for models predicting in-season aboveground and belowground traits for each variety as well as the two varieties combined across different nitrogen treatments.</p>
</caption>
<graphic xlink:href="frsen-06-1484582-g004.tif"/>
</fig>
<p>Features had overall lower coefficients in the SWIR region than in the VNIR region. And features in the SWIR region showed more difference between the two varieties, which is likely related to their genetic differences. In general, features at the beginning (from 1,500&#xa0;nm to 1,600&#xa0;nm) and the end (from 2,300&#xa0;nm to 2,450&#xa0;nm) of the SWIR region had larger weights. Coefficients from the SWIR region were overall the highest in models built from the Soraya data alone and were the lowest in those built from the Russet Burbank data alone. Over the whole spectrum, although following the same trends, coefficients at specific wavelengths of Russet Burbank are different from those of Soraya, indicating that those two varieties have different spectral signatures under the same N treatments.</p>
<p>The standardized regression coefficient values for models using the images collected at one of the three growth stages across the 2&#xa0;years for Russet Burbank to predict at-harvest traits follow the same trends as those found in the in-season belowground traits, with the highest weights found in the 900&#xa0;nm&#x2013;1,200&#xa0;nm range (<xref ref-type="fig" rid="F5">Figure 5</xref>). No consistent trends were noted across different traits for models built from imagery taken at different growth stages (i.e., early vs. mid-vs. late tuber bulking). For models predicting marketable yield and fertilizer N recovery % by tubers, the coefficients of features from the chlorophyll-associated wavelengths were weighted lower at the late tuber bulking stage of the season than in the early season, whereas the opposite was true for models predicting specific gravity. Models built using imagery from the mid-tuber bulking stage had larger weights on features in the 2,250&#xa0;nm&#x2013;2,450&#xa0;nm range than those built using imagery from the early or late tuber bulking phases.</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>Standardized regression coefficients for models predicting at-harvest traits using images collected at each of the three growth stages during the field season (i.e., early, mid-, and late) across the 2&#xa0;years and different nitrogen treatments for Russet Burbank.</p>
</caption>
<graphic xlink:href="frsen-06-1484582-g005.tif"/>
</fig>
</sec>
<sec id="s3-4">
<title>3.4 PLSR model performance with different spectral regions</title>
<p>Predictions of each in-season trait were performed using three different spectral datasets: 1) the entire set of spectral data; 2) the visible-near infrared (VNIR) region ranging from 420&#xa0;nm&#x2013;1,300&#xa0;nm; and 3) the shortwave infrared (SWIR) region ranging from 1,400&#xa0;nm&#x2013;2,350&#xa0;nm. The best spectral region (with the highest <italic>R</italic>
<sup>2</sup> and lowest NRMSE) for each trait of the two varieties individually and combined is reported in <xref ref-type="table" rid="T5">Table 5</xref>. The use of different spectral regions generally resulted in comparable <italic>R</italic>
<sup>2</sup> and NRMSE values for each trait, but predictive models built from the two varieties individually or combined had noticeably different performances under different spectral regions. For Russet Burbank, the models using the SWIR spectral data consistently underperformed those using the VNIR spectral data or the full spectrum. In comparison, when creating predictive models with only the Soraya data or with data of both varieties, no single spectral region consistently performed the best. Predictions of plant N status using petioles and leaves, and the whole canopy N uptake generally favored the VNIR region.</p>
<table-wrap id="T5" position="float">
<label>TABLE 5</label>
<caption>
<p>The best performing spectral region for predicting in-season traits of each variety and the two varieties combined across the 2&#xa0;years. Performance was evaluated by the highest coefficient of determination (<italic>R</italic>
<sup>2</sup>) and the lowest Normalized Root Mean Square Error (NRMSE). For those cells with two results (e.g., visible and near-infrared (VNIR)/Full or shortwave infrared (SWIR)/Full), it meant that the two regions generated similar <italic>R</italic>
<sup>2</sup> and NRMSE.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Trait</th>
<th align="center">Russet burbank</th>
<th align="center">Soraya</th>
<th align="center">Both varieties</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Petiole Nitrate-N</td>
<td align="center">VNIR</td>
<td align="center">VNIR</td>
<td align="center">VNIR</td>
</tr>
<tr>
<td align="left">Leaf total N</td>
<td align="center">VNIR/Full</td>
<td align="center">Full</td>
<td align="center">VNIR/Full</td>
</tr>
<tr>
<td align="left">Whole canopy total N uptake</td>
<td align="center">VNIR</td>
<td align="center">VNIR</td>
<td align="center">VNIR</td>
</tr>
<tr>
<td align="left">Tuber total N uptake</td>
<td align="center">VNIR</td>
<td align="center">SWIR</td>
<td align="center">SWIR/Full</td>
</tr>
<tr>
<td align="left">Immediate tuber yield</td>
<td align="center">VNIR</td>
<td align="center">SWIR</td>
<td align="center">SWIR</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Similar to in-season predictions, evaluation statistics were often similar between models predicting the at-harvest traits using different spectral regions (<xref ref-type="table" rid="T6">Table 6</xref>). Models predicting fertilizer N recovery mostly showed better performances using only the VNIR region, while those predicting tuber marketable yield were less consistently impacted by spectral regions, for both single-date and multi-stage models. Notably, the SWIR region at the late tuber bulking stage produced the best prediction results for all the three at-harvest traits. For multi-stage models, using the full spectrum always produced the best prediction results.</p>
<table-wrap id="T6" position="float">
<label>TABLE 6</label>
<caption>
<p>The best performing spectral region for predicting at-harvest traits of Russet Burbank using the single-date imagery or all images across growth stages in the 2&#xa0;years. Performance was evaluated by the highest coefficient of determination (<italic>R</italic>
<sup>2</sup>) and the lowest Normalized Root Mean Square Error (NRMSE). For those cells with two results (e.g., visible and near-infrared (VNIR)/Full or shortwave infrared (SWIR)/Full), it meant that the two regions generated similar <italic>R</italic>
<sup>2</sup> and NRMSE.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="center">Trait</th>
<th align="center">Early tuber bulking</th>
<th align="center">Mid-tuber bulking</th>
<th align="center">Late tuber bulking</th>
<th align="center">Multi-stage</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Marketable yield</td>
<td align="center">VNIR/Full</td>
<td align="center">VNIR/SWIR</td>
<td align="center">SWIR</td>
<td align="center">Full</td>
</tr>
<tr>
<td align="left">Specific gravity</td>
<td align="center">Full</td>
<td align="center">VNIR/Full</td>
<td align="center">SWIR</td>
<td align="center">Full</td>
</tr>
<tr>
<td align="left">Fertilizer N recovery</td>
<td align="center">Full</td>
<td align="center">VNIR</td>
<td align="center">SWIR</td>
<td align="center">Full</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>4 Discussion</title>
<sec id="s4-1">
<title>4.1 PLSR models provided accurate predictions for in-season traits about potato plant growth</title>
<p>For the predicted indicators to assess crop N status (petiole nitrate-N and leaf total N), higher N rates consistently resulted in higher crop N status indicators. Predictive models built from petiole nitrate-N showed moderate <italic>R</italic>
<sup>2</sup> and NRMSE (<xref ref-type="fig" rid="F2">Figure 2</xref>). Although petioles are the primary plant parts that transport inorganic N in the form of nitrate within the plants, and nitrate-N levels are the most common indicators to guide potato farmers&#x2019; in-season N fertilization decisions (<xref ref-type="bibr" rid="B14">Colquhoun, et al., 2020</xref>; <xref ref-type="bibr" rid="B73">Zebarth and Rosen, 2007</xref>), agronomic studies often see high levels of variability in petiole nitrate-N levels under varied N treatments, as they can be influenced by many factors such as time of tissue collection during the day, cloud cover, and temperature (<xref ref-type="bibr" rid="B40">Liu, et al., 2021</xref>; <xref ref-type="bibr" rid="B69">Wang, et al., 2022</xref>). In contrast, total N content in the leaves does not exhibit this high variability, and, as well, foliage (in contrast to petioles) is directly observed by the sensor. With a higher number of field measurements, the variability in petiole nitrate-N might be reduced, possibly resulting in stronger predictions. While additional research is needed to further refine the understanding of the relationship between plant tissue types and the spectral data collected from them, the results of this study suggest that whole leaf total N (directly observed) are better than petiole nitrate-N for monitoring and predicting potato N status, and should be used instead of petiole nitrate-N to inform in-season N fertilization if remote sensing technologies are applied (<xref ref-type="bibr" rid="B40">Liu, et al., 2021</xref>).</p>
<p>Predictive models of in-season N uptake by both aboveground canopies and belowground tubers of each and both varieties had moderately good performance with <italic>R</italic>
<sup>2</sup> values between 0.43 and 0.64 (<xref ref-type="fig" rid="F2">Figure 2</xref>). Tuber initiation leads to a sharp increase of N absorbed and utilized by the plants, and tuber bulking signals a transition for potato plants to rapidly partition N and energy from the aboveground canopy to the belowground tubers (<xref ref-type="bibr" rid="B5">Alva et al., 2002</xref>; <xref ref-type="bibr" rid="B36">Lauer, 1985</xref>; <xref ref-type="bibr" rid="B45">Millard et al., 1989</xref>; <xref ref-type="bibr" rid="B73">Zebarth and Rosen, 2007</xref>). Typically, 70%&#x2013;85% of the N in the plants is present in the tubers, although as much as 40% of plant N can be present in potato vines (<xref ref-type="bibr" rid="B72">Zebarth, et al., 2004</xref>). Our results suggest that hyperspectral remote sensing of the foliage could be moderately effective in estimating potato N uptake both aboveground and belowground. Notably, predictions of tuber N uptake were slightly better (with higher <italic>R</italic>
<sup>2</sup>) than those of the whole canopy N uptake (<xref ref-type="fig" rid="F2">Figure 2</xref>). This capability likely results from a tight linkage between aboveground N (detected in imagery from leaves) and N availability belowground to tubers (which is not directly imaged). This correspondence can be seen in the standardized PLSR coefficients for whole canopy total N (<xref ref-type="fig" rid="F4">Figure 4</xref>, third row) and fertilizer N recovery % (<xref ref-type="fig" rid="F5">Figure 5</xref>, third row), which are comparable and show higher coefficients in similar wavelength ranges.</p>
<p>In addition, in-season immediate tuber yield predictions had favorable evaluation statistics. Photosynthetic activity is one of the major factors affecting tuber growth, and spectral reflectance data can reflect photosynthetic activity well (<xref ref-type="bibr" rid="B25">Gitelson and Merzlyak, 1996</xref>; <xref ref-type="bibr" rid="B26">Gitelson and Merzlyak, 1998</xref>; <xref ref-type="bibr" rid="B51">Patane and Vibhute, 2014</xref>). Besides, plant vigor is generally highly correlated with crop yield and is reflected well in hyperspectral images due to high reflectance of starch, cellulose, lignin, and nonstructural carbohydrates in the near-infrared and shortwave infrared regions (<xref ref-type="bibr" rid="B16">Curran, 1989</xref>; <xref ref-type="bibr" rid="B40">Liu et al., 2021</xref>). These factors may contribute to the good real-time prediction for the immediate tuber productivity using the hyperspectral signatures of the foliage. Note that standardized PLSR coefficients for intermediate yield and nitrogen-related traits track closely (<xref ref-type="fig" rid="F4">Figure 4</xref>), further supporting the interpretation that the ability to predict yield depends on the ability to characterize factors related to photosynthesis, such as plant N.</p>
</sec>
<sec id="s4-2">
<title>4.2 In-season spectral signatures and cross-year/cross-variety validation</title>
<p>Models predicting end-of-season marketable yield performed well (<italic>R</italic>
<sup>2</sup> &#x3d; 0.77&#x2013;0.78). Final marketable yield could be well predicted as early as the beginning stage of tuber bulking (<italic>R</italic>
<sup>2</sup> &#x3d; 0.77, NRMSE &#x3d; 0.2), and the good prediction results could be found throughout the mid- and late tuber bulking periods, showing that higher N rates could produce higher marketable yields (<xref ref-type="fig" rid="F3">Figure 3</xref>). Accurate prediction of marketable yield from in-season imagery over the course of the growing season is greatly valuable to potato farmers as it could inform economic and management decision-making for producing sellable agricultural products, support sustainable practices that underscore efficient N fertilizer use, and reduce impact of crop production on the environment and the groundwater quality (<xref ref-type="bibr" rid="B12">Chang, et al., 2023</xref>; <xref ref-type="bibr" rid="B41">Luczaj and Masarik, 2015</xref>).</p>
<p>Models predicting at-harvest specific gravity showed good evaluation statistics as well (<xref ref-type="fig" rid="F3">Figure 3</xref>). As a major indicator of potato crop quality, predictions of end-of-season specific gravity complement the good marketable yield predictions, allowing for farmers to further estimate the final value of their crops before the end of the season so they can adjust their harvest time and practices to ensure the optimal conditions for maximum crop profitability. The models derived from late-season imagery did not perform as well as those derived from early and mid-season imagery (<italic>R</italic>
<sup>2</sup> &#x3d; 0.61 compared to 0.74 and 0.68). Tuber starch accumulation, a quality parameter that tuber specific gravity indicates, tends to level off during the later part of the growing season than in the early or middle of the season, when tuber bulking occurs at an exponential rate (<xref ref-type="bibr" rid="B73">Zebarth and Rosen, 2007</xref>). This may result in a relatively weaker late-season prediction for specific gravity of the tubers.</p>
<p>Fertilizer N recovery is the ratio of total amount of N that leaves a cropping system through the harvested tubers to total seasonal applied fertilizer N. The N that was not recovered by tubers at harvest will be lost to the groundwater via nitrate leaching, to the atmosphere via denitrification, and to terrestrial and aquatic systems through wet or dry deposition, all of which could cause environmental concerns (<xref ref-type="bibr" rid="B73">Zebarth and Rosen, 2007</xref>). Compared to the better performance of models predicting the in-season tuber N uptake (<xref ref-type="fig" rid="F2">Figure 2</xref>), evaluation statistics for models predicting fertilizer N recovery at the end of the season were relatively weak (<italic>R</italic>
<sup>2</sup> &#x3c; 0.4, <xref ref-type="fig" rid="F3">Figure 3</xref>). This could suggest that unlike for other potato traits, hyperspectral remote sensing might not have the capacity to predict a trait that needed to be calculated compared to a trait that could be directly measured.</p>
<p>For cross-variety testing, our study showed that models calibrated with Soraya, a Dutch variety bred to be a highly efficient N user, could be moderately tested on Russet Burbank, the No.1 variety developed and grown in the U.S. for over 100 years that is values for its frozen fry processing quality but requires high nutrient and water inputs. Our findings suggest that the new elite potato varieties possess similar in-season traits as the traditional ones, but otherwise they harbor some unique characteristics such as the high N use efficiency and low need of fertilizer inputs, which could make them more sustainable to grow. There is ongoing research to replace Russet Burbank in the U.S., and varieties such as Soraya from other germplasms could provide good genetic resources to facilitate that effort. This indicates that the development of new varieties bred for different characteristics will be best predicted from hyperspectral imagery using models that explicitly include those varieties in the training data.</p>
<p>For cross-year testing using Russet Burbank, we did not achieve satisfying results to predict the at-harvest traits from the single-date models, but the multi-stage models to predict marketable tuber yield produced relatively strong results. This finding demonstrates that there are systematic differences in plant growth caused by different temperature and precipitation conditions in each season (<xref ref-type="sec" rid="s11">Supplemental Figure 1</xref>), or in the hyperspectral images collected at different growth stages of each year. These differences may not be accounted for in the single-stage or single-season models to predict specific gravity and fertilizer recovery %. However for marketable tuber yield, if we combined images over all three growth stages (early, mid-, and late tuber bulking) that covered the growing condition range throughout the season, it could generate moderate testing results between the 2&#xa0;years. In conjunction with the cross-variety results, this result points to the need to develop training data sets that cover the reasonable variation that would be expected across varieties, growth stages and years.</p>
</sec>
<sec id="s4-3">
<title>4.3 The optimal spectral region for making predictive models varied</title>
<p>The PLSR coefficients were similar to those observed in <xref ref-type="bibr" rid="B40">Liu et al. (2021)</xref> for petiole nitrate-N, whole leaf total N, and yield at harvest. Positions of the most important wavelengths in predicting the in-season traits were consistently found in the visible and red-edge region (530&#x2013;630&#xa0;nm and 680&#x2013;780&#xa0;nm) that is highly associated with chlorophyll absorption and canopy greenness, the near-infrared region (900&#x2013;1,200&#xa0;nm) that is directly related with the canopy structure and overall vegetation health (<xref ref-type="bibr" rid="B10">Brewer, et al., 2022</xref>; <xref ref-type="bibr" rid="B15">Croft, et al., 2020</xref>), and at the beginning (1,500&#x2013;1,600&#xa0;nm) and the end of the shortwave infrared region (2,300&#x2013;2,450&#xa0;nm) that are related to plant starch, cellulose and protein content (<xref ref-type="bibr" rid="B21">Fathi, 2022</xref>). Although the positions of the most importance wavelengths stayed within the same ranges over the spectrum between the two varieties (<xref ref-type="fig" rid="F4">Figure 4</xref>), specific wavelengths were typically differed between Russet Burbank and Soraya, noting that all the in-season traits measured in this study were related to plant N status and N uptake. This finding again suggests that although the foliar hyperspectral signatures generally showed similar relationships with plants&#x2019; biophysical and biochemical characteristics, some wavelengths were still variety-specific, caused by the unique N use efficiency and partitioning between aboveground and underground N of that variety.</p>
<p>When comparing models built from the VNIR region alone, the SWIR region alone, or the full spectrum, the best spectral regions that generated the highest <italic>R</italic>
<sup>2</sup> and lowest NRMSE were trait- and variety-specific, again pointing to differences in plant spectral and nutrient usage characteristics resulting from genetic differences. Models predicting the aboveground traits (N status and whole canopy N uptake, <xref ref-type="table" rid="T5">Table 5</xref>) consistently performed better when the VNIR region was used. Specifically for whole leaf total N prediction, when using the full spectrum to build models, the contribution from SWIR wavelengths seemed to be suppressed so that using the full spectrum and only using the VNIR generated the same model evaluation statistics, possibly due to very small variations in the SWIR reflectance among different N treatments (<xref ref-type="bibr" rid="B40">Liu, et al., 2021</xref>). For belowground traits (tuber N uptake and immediate tuber yield, <xref ref-type="table" rid="T5">Table 5</xref>), the best regions are highly variable between different varieties/combination of varieties. The VNIR region contains wavelengths where plant spectral signatures are impacted by chlorophyll activity, likely leading to the observed effects of VNIR on the photosynthetic aboveground tissues than on the belowground traits. In comparison, the ubiquitous preference of the SWIR region by Soraya models to predict the belowground traits (<xref ref-type="table" rid="T5">Table 5</xref>) may be influenced by its high N-use efficiency and special characteristics to partition N between the canopy and the tubers (D. Maum, personal communication, 10 January 2020), as the SWIR wavelengths have important features related to plant nutrient uptake and overall plant physiology (<xref ref-type="bibr" rid="B27">Gold, et al., 2020</xref>).</p>
<p>
<xref ref-type="table" rid="T6">Table 6</xref> clearly shows that during the early and mid-tuber bulking phases, the best regions to predict traits at harvest mostly included the VNIR part of the spectrum, related to vegetation greenness and vigor, but they switched to the SWIR region during the late tuber bulking phase, more related to foliar nutrition and foliar chemical content. Results from our PLSR models using the late tuber bulking images indicated the importance of the SWIR region to predict potato traits at harvest. It has been reported that SWIR wavelengths are related to crop dry matter content. During the latter part of the growing season, potato dry matter content accumulation plateaus and is maximized, while the aboveground canopy is senescing and wilting (<xref ref-type="bibr" rid="B73">Zebarth and Rosen, 2007</xref>), and therefore the utility of VNIR data that&#x2019;s related to chlorophyll and canopy structure would be substantially reduced, and the SWIR-only model became the best option for predicting potato traits using late-growth-stage imagery. As well, information from the SWIR region may be more strongly related to nitrogen absorption features associated with proteins (<xref ref-type="bibr" rid="B8">Berger, et al., 2020</xref>), despite of confounding effects from chlorophyll and canopy vigor. When making predictions on data that include aerial images across different growth stages of the crop, using the whole spectrum including both the VNIR and SWIR regions may result in more robust predictive results (<xref ref-type="table" rid="T6">Table 6</xref>), as the relationships between plants&#x2019; spectral reflectance and their biophysical and biochemical properties changed over the course of the growing season.</p>
</sec>
<sec id="s4-4">
<title>4.4 What can we learn from this study?</title>
<p>Optimally managing nitrogen for potato production is extremely challenging. The amount of N the crop needs and the available amount in the soil change throughout the growing season. Ideally, N should be added as it is needed, matching nutrient supply with crop demand. Unfortunately, growers cannot currently make real-time nitrogen budgets and calculate the ideal amount of N to add at any certain time. Instead, they use guidelines developed through research and past experiences for fertilization scheduling. The most commonly adopted method in the U.S. is petiole nitrate-N testing, and the measurements are typically made every 5&#x2013;10 days. Petiole nitrate-N suffers from high variability, high labor costs and long turnaround testing time (typically 3 days). The present study shows that by using narrow-band hyperspectral imagery collected at different potato growth stages, it is possible to develop relatively robust PLSR models with higher <italic>R</italic>
<sup>2</sup> and low NRMSE values for the most popular potato variety (Russet Burbank) in the U.S. and a new variety (Soraya) from Europe. The prediction results could help farmers to gain a real-time picture of their crop N status and yield forecasting, so that better N fertilization decisions can be made, unnecessary N use can be reduced, and the associated groundwater contamination may eventually be mitigated. To further refine this approach, additional spectral and field measurement data gathered from different locations and years, potato varieties, and production practices should be used for training and testing. It will create more robust models, capture further nuance behind variations in the relationship between spectra and crop biophysical and biochemical traits, and generate more finely tuned precision resource management tools.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="s5">
<title>5 Conclusion</title>
<p>This study utilized the partial least squares regression (PLSR) analysis of full-spectrum hyperspectral data (including VNIR and SWIR) from aerial imagery to predict in-season potato growth and N status as well as at-harvest yield and quality of two potato varieties over two growing seasons. The results revealed that some traits such as leaf total N content and immediate tuber yield during the season, and marketable yield and specific gravity at harvest could be well predicted, suggesting that this method could be used to inform N fertilization decisions based on crop growth and productivity forecasting. The study also found that the best spectral regions to predict potato traits at harvest could change as the field season progresses, since the relationships between plant physiological characteristics and their spectral signatures were changing at different growth stages. This study illustrates the potential for this approach (PLSR &#x2b; hyperspectral imaging) to be used with future datasets to improve crop input efficiency and environmental stewardship in agricultural cropping systems.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="s6">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="sec" rid="s11">Supplementary Material</xref>, further inquiries can be directed to the corresponding author.</p>
</sec>
<sec sec-type="author-contributions" id="s7">
<title>Author contributions</title>
<p>TC: Data curation, Formal Analysis, Investigation, Validation, Writing&#x2013;original draft, Writing&#x2013;review and editing. PT: Conceptualization, Funding acquisition, Methodology, Project administration, Writing&#x2013;review and editing. PR: Methodology, Writing&#x2013;original draft. BH: Data curation, Investigation, Resources, Writing&#x2013;original draft. WH: Data curation, Investigation, Resources, Writing&#x2013;original draft. YW: Conceptualization, Funding acquisition, Methodology, Project administration, Supervision, Writing&#x2013;review and editing.</p>
</sec>
<sec sec-type="funding-information" id="s8">
<title>Funding</title>
<p>The author(s) declare that financial support was received for the research, authorship, and/or publication of this article. Have filled out in previous submissions. Support for this research was provided by funding from the Wisconsin Potato and Vegetable Growers Association, Wisconsin Potato Industry Board and USDA NIFA award 2020-6801-30866 to YW and PT. Additional support was provided by USDA Hatch awards WIS03089 and WIS01874 to PT. PR and WH were supported by NSF ASCEND Biology Integration Institute (BII) award DBI 2021898.</p>
</sec>
<ack>
<p>Thank you to Guolong Liang, Alfadhl Alkhaled, Ophelia Tsai, Taqdeer Gill, Paul Sytsma and the UW HARS field crew for assistance with field management, N application, and field data collection, to Kyle Kovach for assistance with model development, and to the UW Soil and Forage Lab for plant tissue processing and analysis.</p>
</ack>
<sec sec-type="COI-statement" id="s9">
<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 sec-type="disclaimer" id="s10">
<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>
<sec id="s11">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/frsen.2025.1484582/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/frsen.2025.1484582/full&#x23;supplementary-material</ext-link>
</p>
<supplementary-material>
<label>SUPPLEMENTARY FIGURE S1</label>
<caption>
<p>Daily max (red dotted line), average (green dotted line), and min (purple dotted line) temperature, as well as precipitation amount (blue bars) during the growing season of 2020 <bold>(A)</bold> and 2021 <bold>(B)</bold>.</p>
</caption>
</supplementary-material>
<supplementary-material>
<label>SUPPLEMENTARY FIGURE S2</label>
<caption>
<p>Mapped predictions of in-season whole leaf nitrogen (in % dry weight).</p>
</caption>
</supplementary-material>
<supplementary-material>
<label>SUPPLEMENTARY FIGURE S3</label>
<caption>
<p>Mapped predictions of end-of-season marketable yield (in Mg&#xa0;ha<sup>-1</sup>) from late tuber bulking stage imagery.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.docx" id="SM1" mimetype="application/docx" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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