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- Source title: Illuminating duckweed: hyperspectral reflectance highlights a predictive ceiling for accurate determination of biomass
- Author(s): Smith, K. E., Robles-Zazueta, C. A., Cowan, L., Yahya, M. H., McAusland, L., Murchie, E.
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## **Illuminating duckweed: hyperspectral reflectance highlights a predictive** **ceiling for accurate determination of biomass**


Kellie E. Smith &#91;1,2,‡,*&#93;, Carlos A. Robles-Zazueta &#91;1,§&#93;, Laura Cowan &#91;2&#93;, Muhamad Hazwan Yahya &#91;1,#&#93;, Lorna
McAusland &#91;1&#93;, Erik H. Murchie &#91;1&#93;


**Affiliations**


1 Division of Plant and Crop Sciences, School of Biosciences, University of Nottingham, Sutton
Bonington Campus, Loughborough, Leicestershire, LE12 5RD, UK


2 School of Life Sciences, University of Nottingham, Nottingham, NG7 2RD, UK


  - Present Address: Lincoln Institute for Agri-Food Technology, University of Lincoln, Riseholme Park,
Lincoln, LN2 2L, UK


§ Present Address: Department of Plant Breeding, Hochschule Geisenheim University, Von-Lade-Straße
1, 65366, Geisenheim, Germany


# Present Address: Faculty of Science, Universiti Malaya, 50603 Kuala Lumpur, Malaysia


&#91;*Author for correspondence: kellsmith@lincoln.ac.uk&#93;(mailto:kellsmith@lincoln.ac.uk)


Received: 06/11/2026


Number of tables and figures: 8


Word count: 7982


**Running title:** Hyperspectral reflectance for duckweed biomass prediction.


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# **Abstract**


Duckweed is a fast-growing aquatic plant with strong potential as a sustainable, high protein crop that
can be produced without expanding agricultural land. However, substantial trait variation necessitates
rapid selection proxies to identify genotypes with high growth, biomass and pigment content while
simultaneously suited to low input, controlled environments. Although hyperspectral reflectance
phenotyping is widely applied in conventional crops, its utility for duckweed remains unexplored. We
assessed 133 UK accessions from six species grown under ambient light, quantifying growth, pigment
composition, photosynthetic performance and spectral reflectance. A second panel with contrasting
light tolerance strategies, including growth and photosynthetic acclimation, was used to test whether
hyperspectral reflectance could detect photoprotective mechanisms associated with high light
resilience. Duckweed accessions displayed extensive variation across all traits. However, vegetation
indices (VIs) commonly used in arable crops demonstrated only limited predictive accuracy for total
chlorophyll (R &#91;2&#93; =0.34, p&lt;0.005) and maximum photosystem II (PSII) quantum yield ( _F_ v / _F_ m ) (R &#91;2&#93; =0.25,
p&lt;0.0001), with poor performance for other traits. Under high light, VIs moderately differentiated
tolerant accessions, including those maintaining higher _F_ v / _F_ m, 𝛷PSII operating efficiency and
carotenoid:chlorophyll ratios. Partial least squares regression (PLSR) modelling improved predictive
performance, providing reliable estimates of chlorophyll content (R &#91;2&#93; =0.5, RMSE =2.05 mg/g freeze
dry weight) maximum non-photochemical quenching (NPQ) (R &#91;2&#93; =0.5, RMSE =0.57) and NPQ
efficiency of PSII (R &#91;2&#93; =0.53, RMSE =0.04). Although predictions of biomass and growth rate remained
weak, green and red edge spectral regions were strongly associated with pigment contents and
photosynthesis and indirectly linked to biomass. This study provides the first comprehensive evaluation
of spectral phenotyping for duckweed crop development. Our findings indicate that broad spectrum
modelling approaches, integrated with other high throughput phenotyping tools, may support selection
of high vigour varieties and monitoring of commercial duckweed production systems.


**Keywords**


Duckweed; hyperspectral reflectance; novel food crops; photosynthesis; plant phenotyping; PLSR
modelling

# **1. Introduction**


The human population is predicted to increase to between 8.9 and 12.4 billion by 2100 (United Nations;
2022). However, current food systems are insufficient to support this population growth, mainly due to
limited availability of land, soil depletion and water scarcity (FAO; 2021). Alternative sources of food
which can be produced with lower environmental footprints could contribute to improved food security.
To this end, duckweed are miniature freshwater plants consisting of more than thirty six species with
worldwide distributions. Under the name of ‘water lentils’ they have been earmarked as a new
sustainable crop due to fast asexual reproductive rates (Sree _et al_ .; 2015b, Michael _et al_ .; 2021), high
protein compositions (Leng _et al_ .; 1995, Ziec _et al_ .; 2025), high macronutrients and carotenoids content
(Appenroth _et al_ .; 2017, 2018, Xu _et al_ .; 2023) and ability to grow in controlled hydroponic systems,
including for space agriculture (Coughlan _et al_ .; 2022, Petersen _et al_ .; 2022b, Polutchko _et al_ .; 2022).


Duckweed species and varieties thereof have displayed different growth rates in these systems (Ziegler
_et al_ .; 2015) with contrasting adaptation strategies to high light environments (Smith _et al_ .; 2024a, Xuan
_et al_ .; 2025), and unsurprisingly different nutrient, protein, amino acids, carotenoids and secondary
metabolite profiles between species and controlled environments (Landolt, 1986; McCann, 2016,
Stewart _et al_ .; 2020, 2021, Smith _et al_ .; 2024a, 2024b, 2024c, 2025). Growing duckweed for maximal
production of fresh biomass and freeze-dried biomass in low input systems are optimal target traits for


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food production. For example, production of fresh biomass could be used as a vegetable source and
freeze-dried biomass could be used to produce plant-based protein supplement powders. Concordantly,
duckweeds also produce numerous protection compounds known to be beneficial when included in
human diets. For instance, while zeaxanthin is a predominant plant carotenoid formed as a protective
mechanism from de-epoxidation in high light, its consumption supports eye health, the immune system
and it has shown to enhance anti-tumour immune responses (Zhang _et al_ .; 2025). Consumption of plant
chlorophylls and other secondary metabolites can provide high sources of amino acids, macro- and
micronutrients. Therefore, maximization of duckweed growth to produce high biomass containing these
key food quality traits using respective light and nutrient environments are of interest to growers
(Petersen _et al_ .; 2022a). To meet their economic potential as a protein source or vegetable, strategies to
select optimal duckweed candidates offering these traits should be developed by phenotyping in suitable
growth environments.


To develop duckweed with perspectives towards alternative food sources, it is vital to select for
performance in response to environment and differentiate the varieties based on their vigour in low
input systems. Pigment production directly relates to light capture and influences growth and stress
responses in plants. . Estimates of ‘greenness’ or leaf chlorophyll content from spectroradiometers are
commonly used as health indicators and nitrogen (N) status of staple field crops, e.g. maize
(Shivashankar _et al_ .; 2025), wheat (Islam _et al_ .; 2014) and rice (Kim _et al_ .; 2024). This trait is especially
important for the selection of leafy edible crops like spinach, lettuce or indeed duckweed (Gray _et al_ .;
2026). Unfortunately, it is challenging to use leaf clamp-on methods in duckweed due to small sizes of
fronds (instead of leaves) together with their aquatic growth habits. Other existing quantitative
measurement of duckweed health or ‘greenness’ require laboratory-based analysis using timeconsuming destructive methods including chlorophyll extraction (Calzadilla _et al_ .; 2022). Due to their
small sizes, total chlorophyll content is more easily achieved in duckweeds as a per unit biomass rather
than per area basis as applied in broader leaved crop plants. Chlorophyll content in duckweed depends
on the different species adaptation to their light environment and growth strategies (Strzalek &amp; Kufel.;
2021). While chlorophyll content has been reliable to study acclimation in small number of accessions,
it remains a slow approach for phenotyping large populations (Smith _et al_ .; 2024a). Therefore remote
approaches must be sought for phenotyping of green pigments to select for high vigour varieties and to
monitor health of duckweed populations.


Plant vigour is closely linked to photosynthetic capacity and light use efficiency, making these traits
particularly important in duckweed, the world's fastest-growing flowering plant. Understanding the
physiological basis of variation in light capture and growth is essential for optimizing biomass
accumulation, productivity and micronutrient production e.g. carotenoids for food production. Gas
analysers and chlorophyll fluorescence have the utility to screen plants for enhanced photosynthetic
performance and can predict yield in challenging environments (Pavlovic _et al_ .; 2014, Carmo-Silva _et_
_al_ .; 2017). However, these techniques require expensive specialized equipment and have typically
lagged behind research in traditional arable crops. Chlorophyll fluorescence provides a rapid, nondestructive measure of photosynthetic performance and has proven useful for assessing plant health in
duckweed (Stewart _et al_ .; 2020, 2021). Key traits include maximum quantum yield ( _F_ v / _F_ m ), which
reflects the maximum efficiency of photosystem II (PSII); PSII operating efficiency (ΦPSII) and
electron transport rate (ETR), which measure the efficiency of photochemistry and electron flow under
a given light environment; and photoprotective processes including non-photochemical quenching
(NPQ) and regulated thermal dissipation (Y(NPQ)), which dissipate excess absorbed light energy as
heat, largely through the xanthophyll cycle. Together, these traits provide insight into the balance
between photosynthesis and photoprotection that underpins growth and adaptation to contrasting light
environments. Complementary measurements of carbon assimilation have also recently become
possible in duckweed through adaptations of closed-system gas exchange analysers (Rintoul _et al_ .;
2026). Although still in its infancy, the adaptation of high throughput techniques such as hyperspectral
reflectance offers a promising non-invasive phenotyping approach for large duckweed germplasm


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collections. The application to duckweed could enable the identification of trait proxies associated with
photosynthetic capacity, pigment composition, photoprotection and growth-related traits or ‘vigour’ in
the context of controlled high and low growth environments designed for food production (Sanaeifar _et_
_al_ .; 2022).


Hyperspectral reflectance signatures, which can be obtained across simultaneous wavelengths in a
single scan or image, has proved useful in optimizing crop nutrition (Pandey _et al_ .; 2017, Mahajan _et_
_al_ .; 2017), predicting photosynthetic capacity (Robles-Zazueta _et al_ .; 2021; 2022, Zhi _et al_ .; 2022),
disease detection (Shi _et al_ .; 2018), for cultivar classification (Lyu _et al_ .; 2024) and maximizing crop
yield (Montesinos-López _et al_ .; 2017). These approaches have contributed to the improvement of
conventional crops using breeding panels. However, these approaches have not been explored in the
novel underutilised crop duckweed to select natural varieties which already feature enhanced nutrition,
photosynthesis or growth performance in high or low controlled environments. Whilst, breeding is
challenging to achieve in broadly asexually reproducing duckweed, selecting varieties by phenotyping
proxy traits could aid their selection for upscaled production. Furthermore, hyperspectral sensing could
become a tool for monitoring health and productivity of scaled-up operations in duckweed systems or
bioreactors.


Although hyperspectral phenotyping is extensively used in plant breeding, ecophysiology and
taxonomy studies, its use in duckweed remains currently limited. For example, leaf spectra from the
duckweed species _Lemna gibba_ was used to detect stress responses to a chemical contaminant through
changes in pigment absorption features (Dong _et al_ .; 2002). More recently, multispectral imaging was
combined with chlorophyll fluorescence to assess duckweed tolerance to high elemental loads through
changes in _F_ v / _F_ m, supporting the selection of varieties for water remediation (Audenaert _et al_ .; 2026).
In a food security context, higher duckweed tissue glucose and amino acid contents was linked with
higher green reflectance vegetation indices derived from hyperspectral reflectance of growing
duckweed populations (Smith _et al_ .; 2024c). However, there currently remains unexplored opportunities
to use hyperspectral information for selection of food production traits such as biomass production,
nuanced light harvesting components of photosynthesis and protective pigment production in the
prospective vegetable crop duckweed.


Despite the development of methods for interpretation of hyperspectral data, limited prediction testing
has been used for diverse traits in duckweed. Vegetation indices (VIs) are computationally efficient and
readily interpretable mathematical operations developed for arable crops. Vegetation indicies target key
spectral signatures associated with specific traits but potentially overlook subtle genotypic biochemical
and biophysical variation captured elsewhere in the spectrum. By contrast, analysis of contiguous
narrowband hyperspectral spectra preserves detailed spectral information, enabling the detection of
absorption features linked to pigment composition, nutrient and water status, and stress-induced
biochemical, biophysical and physiological responses (Gamon _et al_ .; 2019). Careful consideration of
analytical approaches may be particularly important for aquatic plants, such as duckweed, which exhibit
rapid metabolic and morphological adaptations to their environment. In addition, the use of
hyperspectral reflectance data to predict biomass accumulation, light harvesting traits and growth in
aquatic macrophytes has already been shown to improve trait accuracy using whole spectra compared
to VIs (Villa _et al_ .; 2017, Stratoulias _et al_ .; 2015). Therefore, proxies for accurate trait prediction could
be employed as part of variety selection and monitoring performance in controlled environments used
for duckweed food production.


Hyperspectral linkage between biomass productivity and light resilience traits within and between
duckweed species has not been assessed. The objective of this study was to investigate variation in
vigour of a cohort of 133 UK duckweed varieties from six major species in common controlled
environments. We evaluated the predictive ability of vegetation indices (VIs) and hyperspectral
signatures spanning the visible and near-infrared (NIR) spectrum (400-1100 nm) using multivariate


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preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
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modelling approaches. To achieve this, different proxies of plant productivity were measured in the
laboratory including chlorophyll fluorescence dynamics, pigment composition and plant growth rates
primarily in ambient low growth light (GL), with a smaller cohort in a high growth light (GL)
environment. Our hypothesis is that reflectance wavelengths in the green and red regions of the
electromagnetic spectrum should positively associate with chlorophyll content, while NIR regions will
be linked with photosynthetic performance and higher growth rates.

# **2. Materials and methods**


**2.1. Duckweed collection**


One-hundred and thirty-three accessions of six species described in (Smith _et al_ .; 2025) were used as a
duckweed study panel to test the utility of hyperspectral reflectance to predict growth rate,
photosynthetic traits and pigment content as relevant traits for selection of novel food crops. The
selected species include: _Spirodela polyrhiza_, _Lemna minor_, _Lemna japonica_, _Lemna gibba_, _Lemna_
_minuta_ and putative hybrid species _Lmu/Lmo_ ( _L. minor_ x _L. minuta_ ). The UK duckweed cohort was
chosen for their species-level classifications, associated characterisation of their historical native pond
light environments and recent domestication to controlled environments (summarized in Table S1). The
data collection pipeline to assess relevant food crop traits in this study is presented in Fig. 1.


**Figure 1.** Workflow for characterisation of duckweed accessions towards novel food development. **A.**
Duckweed accessions were grown in individual flasks in controlled environments supplying low growth
light (GL) conditions (50 µmol m &#91;-2&#93; s &#91;-1&#93; ). **B-C** . Growth rate of biomass in flasks was assessed weekly for
four weeks. **D.** Duckweed biomass was split into three replicates in well plates after each growth
experiment. **E.** Duckweed biomass was imaged for chlorophyll fluorescence after dark adaptation to
produce false color image. Measurements were conducted for each replicate population using an
imaging system (800C Fluorcam, Photon System Instruments, Brno, Czech Republic). **F.** Hyperspectral
reflectance was measured from duckweed biomass with a spectroradiometer (ASD FieldSpec 4,
Malvern Panalytical, UK). **G.** Total fresh biomass for each accession was weighed and freeze-dried. **H.**
Freeze-dried biomass was aliquoted into known mass for destructive pigment extractions using acetone
to obtain total chlorophyll and carotenoid contents per mass. Each accession from low GL experiments
( _n_ = 133) was evaluated across three independent growth rate experiments. Per accession, this resulted
in nine chlorophyll fluorescence and nine hyperspectral datasets (three per growth rate experiment each)
and twelve chlorophyll extraction measurements (four per growth rate experiment). For the high GL
experiment, 24 accessions were each subjected to five growth rate experiments, resulting in fifteen
chlorophyll fluorescence datasets and fifteen hyperspectral datasets (three per experiment), and twenty
chlorophyll extraction measurements (four per experiment) per accession.


**2.2. Duckweed growth experiments**


Duckweed accessions were grown in low (50 µmol m &#91;-2&#93; s &#91;-1&#93; ) GL experimental conditions for four to six
weeks (Fig. 1A-C). GEN-1000 controlled environment cabinets (Conviron, Winnipeg, Canada)
provided broad-spectrum LED lights giving a light photoperiod of 16:8 hr days and temperature cycle
of 22 °C in the day and 18 °C during nights. Duckweed varieties were grown separately in Erlenmeyer


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preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


flasks for each growth rate experiment as batches according to the UK regions they were collected. At
the start of each experiment, a single colony was used to initiate the population and growth was then
measured weekly for each accession using (i). changes in green area normalized to initial frond area
(T0) using RGB from photos and (ii). colony counts. N-medium was made (as described in Appenroth
_et al_ .; 1996) and refreshed weekly to provide plentiful nutrient conditions for growth. Relative growth
rate (RGR) was obtained from total green area &#91;Eq1&#93; and from colony number &#91;Eq2&#93; during the log
phase of growth. After four weeks, the fastest growing accessions were harvested as they had exhausted
the surface growing space. Slower growing accessions were grown for a further two weeks with
continued N-medium replenishment to expand biomass yield to ~95% surface coverage. Each
duckweed growth experiment was repeated as batches for the 133 accessions three times over a threeyear period to obtain three biological replicates per accession.



𝑅𝐺𝑅𝑙𝑜𝑔 (𝑎𝑟𝑒𝑎) = log



𝑇21 𝑎𝑟𝑒𝑎 − 𝑇14 𝑎𝑟𝑒𝑎

&#91;Eq1&#93;
7



𝑅𝐺𝑅𝑙𝑜𝑔 (𝑐𝑜𝑙𝑜𝑛𝑖𝑒𝑠) = log



𝑇21 𝑐𝑜𝑙𝑜𝑛𝑦 𝑛𝑢𝑚𝑏𝑒𝑟−𝑇14 𝑐𝑜𝑙𝑜𝑛𝑦 𝑛𝑢𝑚𝑏𝑒𝑟

&#91;Eq2&#93;
7



Adaptation to controlled high GL was measured in a small subset of 24 accessions described in (Smith
_et al_ .; 2024a, highlighted in Table S1). _Lemna gibba_ and the putative hybrid species _Lmu/Lmo_ was not
included in this regional cohort. Instead, the parent species _Lemna turionifera_ which forms the hybrid
_L. japonica_ ( _L. minor_ x _L. turionifera_ ) featured exclusively in this specific region (Smith _et al_ .; 2025)
These duckweed accessions were selected for comprising species diversity and representing a local
cohort with spatial and seasonal light variability in their water habitats. In addition to their growth in
low GL environments, these accessions were grown concurrently under high GL conditions (350 µmol
m &#91;–2&#93; s &#91;–1&#93; ) with all other environmental parameters kept consistent and growth rates measured as per the
low GL experiments. High GL experiments on this subset were repeated five times over the three-year
period to give _n_ =5 replicates. During each GL experiment, the light environment (photosynthetically
active radiation; PAR, light intensity and quality) for each duckweed population was measured in the
controlled environments using a light meter (Li-250A, Licor Biosciences, NE, USA) and handheld
spectrometer (LI-180, Licor Biosciences, NE, USA) in each growing position to account for spatial
variation.


**2.3. Chlorophyll fluorescence as an indicator of duckweed photosynthetic health**


At the end of growth experiments, each accession represented by a duckweed population in each flask
was subset three times into separate six well plates to obtain a total of nine and fifteen biological
replicates for the low and high GL conditions respectively for chlorophyll fluorescence measurements.
Each well contained 3 ml N-medium and the surface of each well was filled (where possible) with dense
populations of each accession to maximize biomass signal and minimize duckweed colony repellence
and water visibility in each well (Fig. 1D-E). A closed chlorophyll fluorescence imager (800C
Fluorcam, Photon System Instruments, Brno, Czech Republic) was used to measure photosystem II
(PSII) chlorophyll fluorescence light reactions for each accession after 1 hr dark adaptation. A light
response curve protocol featuring eleven incremental light levels was setup as described in (Smith _et_
_al_ .; 2024a). Stepwise light levels were calculated to corresponding photosynthetic photon flux density
(PPFD) levels to select three contrasting light levels to capture specific light adaptive responses after
each GL condition. This included the light level corresponding closest to the low GL environment (LL)
(130 µmol m &#91;-2 &#93; s &#91;-1&#93; ), high GL environment (HL) (365 µmol m &#91;-2 &#93; s &#91;-1&#93; ) and very high light (VHL) (&gt;1000
µmol m &#91;-2 &#93; s &#91;-1&#93; ), which was the maximum light level experienced during the light curve but not
experienced in either GL environment. Photosynthetic traits from chlorophyll fluorescence were
calculated as outlined in (Murchie &amp; Lawson, 2013). Maximum quantum yield of PSII (𝐹 𝑣 /𝐹 𝑚 ) in the
dark was calculated using &#91;Eq3&#93;, operating PSII operating efficiency (ΦPSII) was calculated as in &#91;Eq4&#93;
and non-photochemical quenching (NPQ) as in &#91;Eq5&#93; for each light level.


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preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
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𝐹 𝑚 −𝐹 𝑜 &#91;Eq3&#93;

𝐹 𝑚



𝐹 𝑣 /𝐹 𝑚 =


𝛷𝑃𝑆𝐼𝐼=



𝐹𝐹 𝑚 𝑞 ′ &#91; ′&#93; &#91;Eq4&#93;



𝐹 𝑚 𝐹− 𝐹 𝑚 ′ 𝑚 ′ &#91;Eq5&#93;



𝐹 𝑚 − 𝐹 𝑚 ′



𝑁𝑃𝑄=



In addition to these, the following traits were derived from (Maxwell &amp; Johnson; 2000, Kramer _et al_ .;
2024): Electron transport rate (ETR) at LL (130 µmol m &#91;-2 &#93; s &#91;-1&#93; ) was calculated using incident PAR and
ΦPSII &#91;Eq4&#93; as in &#91;Eq6&#93;. Constants for this equation included 0.84 as the default fraction of incident
light absorbed by a leaf and 0.5 corresponding to average ratio of PSII:PSI reaction centres. Then
maximum NPQ at VHL (1050 µmol m &#91;-2 &#93; s &#91;-1&#93; VHL) was used to derive the yield of PSII regulated nonphotochemical energy dissipation as heat (Y(NPQ)) using &#91;Eq7&#93;.


𝐸𝑇𝑅= 𝛷𝑃𝑆𝐼𝐼 × 𝑃𝐴𝑅 × 0.84 × 0.5 &#91;Eq6&#93;



′



𝑌(𝑁𝑃𝑄) =



𝐹 𝑡 ′

𝐹 𝑚 ′ &#91;− &#93;



𝐹 𝑡




&#91;Eq7&#93;
𝐹 𝑚



**2.4. Hyperspectral signatures from duckweed biomass**


Immediately after growth in low or high GL, followed by chlorophyll fluorescence experiments, a
spectroradiometer (ASD FieldSpec 4, Malvern Panalytical, UK) was used to measure the reflectance
signatures of duckweed biomass setup in six well plates (Fig. 1F). Reflectance was measured from
adaxial frond surfaces at 1 nm increments between 350 – 2500 nm in a laboratory providing consistent
low light at 5 µmol m &#91;-2&#93; s &#91;-1&#93; . A contact probe attachment with a halogen bulb light was suspended in a
tripod placed at a constant distance of 20 cm directly above each duckweed accession population. A
black background was placed behind well plates to reduce stray reflectance e.g. from N-medium and
metallic lab bench. A white reference panel was scanned every five minutes to re-calibrate the
instrument between measurements. Three pseudo-replicate measurements were taken per well to
capture hyperspectral variation within well populations, and biomass was placed in three individual
plates, giving a total of nine biological replicates for each accession ( _n_ = 9) after each growth rate
experiment.


**2.5. Harvesting duckweed biomass and destructive chlorophyll extraction**


After hyperspectral measurements, the three replicates per accession were removed from the well plates,
air dried for 20 mins and weighed to obtain the total fresh biomass weight from each growth rate
experiment. These replicate populations were then frozen in liquid nitrogen, freeze-dried for 2 days and
then re-weighed to obtain freeze-dried biomass for each accession replicate (Fig. 1G). Each of these
replicates were portioned into 5 mg whole tissue samples for pigment extraction (Fig. 1H). Chlorophyll
and carotenoids were extracted by acetone to quantify pigments on a per mass basis and detected by
absorption using spectrophotometry as described in (Smith _et al_ .; 2024a).


**2.6. Spectral data analysis**


Raw reflectance signatures from lab‑grown duckweed were pre‑processed using the signal package in
R (Ligges _et al_ ; 2015) with a Savitzky–Golay filter to smooth and reduce noise. Two analytical
approaches were then applied. First, reflectance measured at specific regions of the electromagnetic
spectrum was used to calculate vegetation indices (VI), which are derived from ratios and differences
of peaks in the visible, near-infrared (NIR) and shortwave infrared regions (Xue &amp; Su.; 2017).
Commonly used VIs were derived from blue, green, red, red edge and NIR spectral regions. Five VIs
(NDVI, GM, PRI, OVI, EVI) commonly used for prediction of vigour traits in plants and crops were
selected from the literature (Table 1) and calculated for each accession replicate under low GL


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conditions and with the subset panel in high GL conditions. Relationships between VIs and
physiological traits were assessed using Pearson’s pairwise correlations using the _cor_ function from the
stats package and visualized using a matrix from the corr package (Wei &amp; Simko.; 2024). Then key
associations were modelled for linear mixed‑effects models fitted with _lme4_ (Bates et al.; 2015). Prior
to modelling, alternative functional forms (linear, logarithmic, square‑root, polynomial, nonlinear) were
evaluated using Akaike Information Criterion and residual diagnostics and traits exhibiting
non‑normality or heteroscedasticity were transformed. Models included light intensity PAR measured
in each growth position as a fixed effect and accession as a random intercept, with species identity
incorporated either as a random effect or as a fixed interaction. Model performance was quantified using
marginal R² (fixed effects) and conditional R² (fixed + random effects).


**Table 1.** Common hyperspectral vegetation indices (VI) derived from (Index Database, 2026) and their
main uses to predict plant traits including crop yield and chlorophyll content. _R_ = Reflectance at
wavelength.



**VI** **Full name** **Formulae** **Estimates** **Plants** **References**
NDVI Normalized 𝑅800 −𝑅680 Green biomass, 13 spp. Gamon _et_

difference 𝑅800 + 𝑅680 leaf area index, _al_ .; 1995
vegetation chlorophyll
index content &lt;50 spp. Sims &amp;

Gamon;


Rice 2002

Sorghum Shi _et al_ .;


2018

Zhang _et_
_al_ .; 2022
EVI Enhanced 2.5 Crop yield Soybean Shammi &amp;
vegetation 𝑅800 −𝑅670 Meng;

∗

index ~~(~~ 𝑅800 + 6 ∗670 −7.5 ∗𝑅470 + 1 ~~&#91;)&#93;~~ 2021



Green biomass,
leaf area index,
chlorophyll

content



Normalized

difference

vegetation
index



𝑅800 −𝑅680

𝑅800 + 𝑅680



13 spp.

&lt;50 spp.

Rice

Sorghum



EVI Enhanced 2.5 Crop yield Soybean Shammi &amp;
vegetation 𝑅800 −𝑅670 Meng;

∗

index ~~(~~ 𝑅800 + 6 ∗670 −7.5 ∗𝑅470 + 1 ~~&#91;)&#93;~~ 2021


Rice Son _et al_ .;


2014
GM Green model 𝑅750 Chlorophyll 6 spp. Gitelson &amp;
𝑅550 &#91;−1&#93; content Merzlyak;


1997


Citrus Xiao _et al_ .;


2024


Glucose, amino Duckweed Smith _et_
acid content _S._ _al_ .; 2024c



Soybean

Rice



2.5



Crop yield



𝑅800 −𝑅670

∗
~~(~~ 𝑅800 + 6 ∗670 −7.5 ∗𝑅470 + 1 ~~&#91;)&#93;~~



6 spp.

Citrus

Duckweed

( _S._
_polyrhiza,_

_Lemna_

spp)



Gitelson &amp;

Merzlyak;

1997

Xiao _et al_ .;

2024

Smith _et_

_al_ .; 2024c



Photosynthesis,
carotenoids,
xanthophyll
cycle



20 spp.

&gt;100 spp.



PRI Photochemical

reflectance

index



𝑅531 −𝑅570

𝑅531 + 𝑅570



PRI Photochemical 𝑅531 −𝑅570 Photosynthesis, 20 spp. Gamon _et_
reflectance 𝑅531 + 𝑅570 carotenoids, _al_ .; 1997;
index xanthophyll &gt;100 spp. Garbulksy

cycle _et al_ .; 2011

OVI Optimal 𝑅760 −𝑅730 Nitrogen Wheat Erdle _et al_ .;
vegetation 2011
index Fresh biomass Duckweed Smith _et_



𝑅760 −𝑅730 Nitrogen

Fresh biomass



Wheat

Duckweed

( _S._
_polyrhiza,_

_Lemna_

spp.)



Erdle _et al_ .;

2011

Smith _et_

_al_ .; 2024c


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For the second approach, partial least squares regression (PLSR) was used to model the association
between pigments, photosynthetic and biomass traits with hyperspectral reflectance signatures. The
spectral range used for PLSR was 400-1100 nm to reduce the water absorption bands in the shortwave
infrared range (&gt;1200 nm). PLSR is a supervised regression approach that maximizes the covariance
between highly dimensional and collinear predictors (i.e. spectral reflectance at thousands of
wavelengths) and the response variable. Trait predictions were done using the orthogonal scores PLS
algorithm from the R _pls_ package (Mevik &amp; Wehrens.; 2007). The hyperspectral datasets were split in
80% for model training and 20% for model validation by species. The optimum number of components
was determined through cross-validation at the training stage to select the model with lower root mean
square error (RMSE). Finally, model performance metrics such as the determination coefficient (R &#91;2&#93; ),
RMSE and model bias were used to select the best model at the validation stage (Robles-Zazueta _et al_ .;
2022).

# **3. Results** 3.1. Varied performance of duckweed cohort for crop- associated traits


The duckweed cohort showed marked phenotypic variation in pigment contents, photosynthesis,
photoprotection, growth and biomass trait groups in a common low GL controlled environment (Fig.
2). The clear phenotypic separation among accessions highlights their value as a diverse panel for
evaluating hyperspectral signatures as a selection tool. Briefly, _Lemna japonica_ accessions
demonstrated consistently higher chlorophyll and carotenoid contents and higher fresh and freeze-dried
biomass, linking pigment content to productivity (Fig. 2A, C). Northern _Lemna minor_ accessions
displayed high photoprotective capacity under ambient light, achieving the highest maximum NPQ and
greatest regulatory dissipation as heat as Y(NPQ) (Fig. 2B). NPQ at very high light (VHL) significantly
varied between species and geographic origins, with accessions from the highest latitudes showing the
strongest NPQ responses (p &lt;0.0001) but yielding less biomass. This significant variability in vigour
and trade-offs due to geographic origin demonstrates that not all accessions have idealized crop traits
in low input environments.


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**Fig. 2.** Varied performance of 133 duckweed accessions in low GL environments for crop-associated
traits. **A.** Pigment contents measured by pigment extraction and spectrophotometry in mg g &#91;-1 &#93; freezedried weight: i. Chlorophyll a, ii. Chlorophyll b, iii. Carotenoids and iv. Total chlorophyll (a+b). **B.**
Photosynthesis and photoprotection measured by chlorophyll fluorescence: i. Maximum quantum yield
of PSII measured after dark adaption ( _F_ v / _F_ m ), ii. Electron transport rate (ETR) measured at LL (130
µmol m &#91;-2&#93; s &#91;-1&#93; ), iii. Non-photochemical quenching (NPQ) at VHL (1050 µmol m &#91;–2&#93; s &#91;–1&#93; ) and iv. Regulated
thermal dissipation (Y(NPQ)) measured at VHL. **C.** Growth and biomass traits: i. Fresh weight (FW)
biomass (g) at the end of growth period, ii. RGRlog area measured by green area increase during log
phase, iii. RGRlog colonies based on colony count gain during log phase and iv. freeze-dried weight
(FDW) at the end of the growth period. Unitless traits are indicated with (-).Trait averages were used
from all replicates for each accession, the top and bottom five accessions (based on accession averages)
are labelled and points for each accession are coloured by species.

# 3.2. Evaluating vegetation indices as predictors of pigment composition, photosynthetic performance and growth


Several positive correlations were observed between measured pigment contents (chlorophyll a, b and
total chlorophyll), electron transport rate and VIs derived from the green and red spectral regions,
particularly the GM index and OVI which incorporates the NIR region (Fig. 3A, 3B). Pigment


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concentrations, photosynthetic traits and VIs including GM, NDVI and OVI showed strong collinearity,
indicating overlaps in trait and spectral regions attributed to vigour. Vegetation indices which produced
the highest R &#91;2&#93; for key selected traits are summarized in Fig. 3. The strongest relationship was between
total chlorophyll and GM: accessions with higher chlorophyll content consistently showed higher GM
values (Fig. 3A). While maximum quantum yield ( _F_ v / _F_ m ) was most strongly related to OVI this was a
weaker correlation, with satisfactory separation of high and low performing accession clusters on the
axes (Fig. 3B). Model fits improved substantially when accession-level effects were included
(chlorophyll: R² = 0.337 to 0.501; _F_ v / _F_ m : R² = 0.250 to 0.432), indicating important accession and
species-specific variation in these traits. Species-specific responses influenced GM predictions for total
chlorophyll and OVI predictions for quantum yields, indicating species-specific differences in these
traits under low GL conditions.


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**Fig. 3.** Associations between pigment concentrations, photosynthesis and fresh biomass with selected
vegetation indices (VIs) using 133 duckweed accessions from a low GL environment. **A.** Total
chlorophyll concentration vs GM. **B.** Maximum quantum yield ( _F_ v / _F_ m ) vs OVI. **C.**
Carotenoid:chlorophyll ratio vs NDVI. **D.** Fresh weight (FW) biomass vs EVI. Mixed-effects regression
models were fitted for each trait–VI relationship.Log transformation was used for pigment content and
fresh weight; square‑root transformation was used for _F_ v / _F_ m . Fitted slope lines show model predictions
for each species. Marginal R² values and model p values are reported for each panel. Points represent
averages for each accession from experimental replicates and are coloured by species type.. The top
and bottom five accessions for each vigour trait are labelled.


Although several VIs showed statistically significant associations with physiological traits, marginal R²
values &lt; 0.5 indicated limited prediction power of VIs in low GL conditions.NDVI showed a weak,
negative relationship with carotenoid:chlorophyll ratio, with substantial overlap among accessions
preventing clear separation of high and low trait values (Fig. 3C). The model explained just 13.7% of
trait variation, increasing when accession effects were included (conditional R² = 0.416), indicating
substantial accession- and species-level variation not captured by NDVI.


Total fresh weight (FW) biomass was a key trait of interest, given the substantial variation found
between accessions (Fig. 2Ci) and requirement for food production. NDVI showed little association
with FW despite its ability to predict yield in arable crops, so EVI was evaluated as an alternative index
to account for canopy density and reduce saturation in the red edge region between red and NIR.
Although EVI showed a weak, positive association between with FW, high and low biomass-producing
accessions overlapped extensively. The mixed effects model using EVI explained only 12% of variance


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and EVI was not a significant predictor overall (p = 0.47), indicating that VIs using NIR tested here
have limited potential to predict biomass production in dense duckweed conditions (Fig. 3D).


Despite clear variation in photoprotective traits among accessions (Fig. 2B), including carotenoid
content, xanthophyll cycle activity via NPQ and regulated heat dissipation as Y(NPQ), no VI showed a
strong association with these traits under low GL conditions. This contrasts with the established use of
PRI to predict photoprotective responses in arable crops. To test whether spectral sensitivity improves
when photoprotection is more strongly induced, a subset of accessions with contrasting light adaptation
strategies was exposed to high GL.

# 3.3. Association between VIs and high light stress responses


A subset of twenty-four accessions selected from (Smith _et al_ .; 2024a, 2025) was grown under high GL
conditions and VIs derived from hyperspectral reflectance were evaluated for their ability to predict
light adaptive traits. As in the low GL experiment, several positive correlations emerged, most notably
between maximum quantum yield _F_ v / _F_ m, operating efficiency (𝛷PSII) measured at three key light levels
(LL, HL, VHL) and predictor indices from the green, red and NIR spectral regions, particularly PRI
and NDVI (Fig. 4A). However, even under high GL when photoprotection is induced, no VI showed a
significant association with NPQ measured at any light level (LL, HL, VHL). This indicates that the
VIs still lacked sensitivity to capture photoprotective responses in duckweed grown under high GL
environments.


Multiple VIs (GM, NDVI, OVI, PRI) showed negative associations with carotenoid:chlorophyll ratios
(Fig. 4A, D), mimicking the trends found in the low GL experiment with the larger cohort (e.g. Fig.
3C). In the high GL condition, NDVI was positively associated with 𝛷PSII operating efficiency across
all three key light levels (Fig. 4A), with the strongest relationship under HL, when the light intensity
matched the growth environment (R &#91;2&#93; = 0.38, p &lt; 0.001; Fig. 4B). PRI showed the strongest overall
association with maximum quantum yield ( _F_ v / _F_ m ) (R &#91;2&#93; = 0.3, p &lt;0.01; Fig. 4C), outperforming OVI
which was the best predictor in the low GL experiment (Fig. 3B). PRI also displayed weak, positive
associations with chlorophyll a, b and carotenoid contents under high GL (p &lt; 0.05, Fig. 4A). Overall,
these results indicate that PRI and NDVI capture variation in pigment composition and photosynthetic
efficiency which are traits known to differ between light susceptible and light resilient duckweed
varieties. Light stress susceptible _L. minuta_ accessions could be separated from the better adapted _L._
_minor_ and _L. japonica_ accessions using PRI and NDVI for predicting _F_ v / _F_ m and 𝛷PSII (Fig. 4B-C).
However, notably the highest R &#91;2&#93; for any VI remained below 0.5 which is consistent with the low GL
experiment, highlighting the limitations of VIs to be used as a solo proxy for vigour traits.


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**Fig. 4.** Significant associations between VIs with pigment and photosynthetic traits in a subset of 24
duckweed accessions from high GL experiment. **A.** Pearson correlation matrix showing relationships
among pigment traits, photosynthetic traits and reflectance-derived VIs. Vegetation indices (GM,
NDVI, PRI, OVI) are outlined by a box. Color and scale indicate direction of association, circle size
indicates strength of association and asterisks denote statistical significance (*** p &lt;0.001, ** p &lt;0.01,

  - p &lt;0.05). **B-D.** Pairwise relationships between measured traits and predictive VIs. **B.** 𝛷PSII operating
efficiency at HL (365 µmol m &#91;-2&#93; s &#91;-1 &#93; ) association vs NDVI, **C.** Maximum quantum yield ( _F_ v / _F_ m ) vs PRI,
**D.** Carotenoid:chlorophyll ratio vs PRI. Points represent averages for each accession from replicates
and are colored by species. The top and bottom five accessions for each measured trait are labelled.

# 3.4. PLSR improves spectral prediction of pigments and photoprotection but not growth or biomass


To address the limitations of VIs for predicting duckweed traits, PLSR modelling was applied using
spectral signatures ranging from 400-1100 nm, with the aim of improving prediction accuracy for novel
crop traits. PLSR was used in the large duckweed cohort grown in low GL only where power was high
enough to use training and validation. Whole-spectrum PLSR modelling substantially improved
prediction of chlorophyll contents (Table 2, Fig. 5A) and significantly enhanced the prediction of
baseline photoprotective traits compared with models using selected VIs (Fig. 5B). However, biomass
and growth rate remained challenging to predict using whole spectral signatures.


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**Table 2.** PLSR models of pigment, photosynthesis, photoprotection and growth traits using
hyperspectral reflectance (400–1100 nm). Training (80%) and validation (20%) datasets were split by
species. Model outputs include R &#91;2&#93;, RMSE = root mean square error, model bias error and _n_ = sample
sizes.



**Training** **Validation**
**Trait (units)** **R** **&#91;2&#93;** **RMSE** **Model** _**n**_ **R** **&#91;2&#93;** **RMSE** **Model**

**bias** **bias**



_**n**_



Chl a (mg/g FDW) 0.52 1.26 -0.01 523 0.5 1.45 0.06 123
Chl b (mg/g FDW) 0.47 0.41 -0.002 520 0.44 0.46 0.02 133
Total chl (mg/g FDW) 0.53 1.53 -0.02 514 0.49 2.05 -0.14 132
_F_ v / _F_ m (-) 0.51 0.04 -0.0001 527 0.36 0.06 0.005 134
NPQ VHL (-) 0.45 0.44 0.001 527 0.49 0.57 -0.04 134
Y(NPQ) VHL (-) 0.39 0.04 0.0003 527 0.53 0.04 0.0018 134
Car (mg/g FDW) 0.21 0.42 -0.001 477 0.15 0.52 -0.03 122
Chl a:b (-) 0.06 0.64 0.0002 509 -0.04 0.54 0.03 131
Car:Chl (-) 0.19 0.05 0.0001 482 0.28 0.06 0.0006 123
FW (g) 0.31 337.9 -2.11 171 -0.09 457.9 -26.04 45
RGRlog area (day &#91;-1&#93; ) 0.06 0.62 0.01 167 0.15 0.63 -0.13 44


PLSR modelling performed well for all chlorophyll content estimates: chlorophyll a, b and total
chlorophyll, each achieving R &#91;2&#93; ~ 0.5, with a good alignment between the validation and training models
(Fig. 5A). Modelling with PLSR improved chlorophyll prediction compared to using the GM index
alone, and accessions with low and high chlorophyll contents showed good separation and proximity to
validation fitting slopes (Fig. 5A). The spectral region with the highest predictive contribution was 550
nm as indicated by higher peaks in variable importance in projection (VIP) scores (Fig. 6A). A
secondary peak for chlorophyll at the red edge between red and NIR around 700 nm was also
consistently important (Fig. 6). In contrast, the early NIR region 750 – 900 nm which is used in key VI
calculations such as NDVI and EVI, did not contribute to trait projections.


For NPQ and regulated photoprotective dissipation (Y(NPQ)) at VHL, validation models outperformed
the training models, yielding moderate R² values of 0.49 and 0.53, respectively (Table 2, Fig. 5B). The
strongest VIP signal for photoprotection traits occurred at 550 nm, with Y(NPQ)photoprotection
dissipation at VHL showing the highest VIP score of all modelled traits (Fig. 6). Notably, this region
overlapped with chlorophyll and carotenoid contents. Although NPQ VHL did not correlate with any
VI derived from NIR or visible spectra in either GL conditions, PLSR substantially improved prediction
of photoprotective traits even in low GL conditions.. In contrast, validation performance for maximum
quantum yield, _F_ v / _F_ m, was lower (R &#91;2&#93; = 0.36) than the training results (R &#91;2&#93; = 0.51, Table 2) indicating a
poorer fit using PLSR. Divergence of slopes at the lower end of _F_ v / _F_ m values suggests that PLSR had
limited predictive power for accessions with reduced photosynthetic efficiency (Fig. 5B).


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**Fig. 5.** Physiological trait prediction using PLSR modelling for hyperspectral signatures of 133
duckweed accessions from low GL experiments. Observed measurements plotted against prediction
derived from PLSR of hyperspectral data. **A.** Chlorophyll content. **B.** Photosynthetic and
photoprotection traits. **C.** Carotenoid content and pigment ratios. Model training results are marked with
grey sloped lines while validation results are indicated with black sloped lines. Top and bottom five
performing accessions from the validation models are labelled in each panel.


PLSR modelling produced weak predictions for growth rate, biomass and pigment ratios (chlorophyll
a:b and carotenoid:chlorophyll) (Table 2, Fig. 5). Notably, growth traits showed a high VIP score in the
650-700 nm region which overlapped with key wavelengths for predicting chlorophyll content and
photoprotection traits NPQ and Y(NPQ) VHL. A distinctive peak between 1000-1050 nm was also
identified for growth rate and biomass, corresponding to the NIR region characteristic of water
absorption and commonly associated with vegetation moisture content, biomass and yield (Fig. 6).
However, no trait (including growth rate and biomass) showed an association with water band indices
such as NDWI (Fig. S1). For carotenoid content and pigment ratios, PLSR did not improve upon the
low predictive power of VIs (Fig. 5C). Accessions were not well separated along model axes, especially
for chlorophyll a:b where low and high performing accessions overlapped and predictions were
especially poor at higher chl a:b ratios. Overall, these results suggest that hyperspectral signatures of
duckweed biomass are effective for estimating total chlorophyll content but lack the sensitivity needed


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to reliably resolve variation in pigment ratios or to differentiate important growth and biomass trait
capability of accessions.


**Fig. 6.** VIP scores from PLSR models reveal shared spectral regions contributing to the prediction of
physiological traits in 133 duckweed accessions grown under low GL.. **A.** Chlorophyll content. **B.**


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Photosynthesis and photoprotection. **C.** Carotenoid content and pigment ratios. **D.** Growth and biomass.
The dashed horizontal line indicates the VIP threshold for important predictors (VIP = 1). Dotted
vertical lines highlight spectral regions near 550 and 700 nm, where multiple vigour-related traits
showed strong predictive peaks.

# **4. Discussion**


**4.1. Limitations of hyperspectral reflectance information for biomass and growth prediction**


Attainable biomass and growth rate are key traits to monitor for duckweed food production. Although
accessions differed in their growth potential, hyperspectral VIs showed weak predictive power for
biomass and growth rate. Red edge spectral regions around 680–710 nm associated with growth rates
and biomass accumulation, yet PLSR models performed poorly. This contrasts with earlier duckweed
studies, where VIs GM and OVI correlated with green area and fresh biomass during early growth in
glasshouse conditions (Smith _et al_ .; 2024c), and NDVI tracked _Lemna minor_ biomass expansion in
aquatic habitats (Gerardo &amp; de Lima.; 2022). These studies measured biomass expansion coupled with
water background reflectance compared to high density canopy endpoint measurements in this study.
In fact, NDVI and EVI did not capture biomass variation sufficiently, and similarly low predictive
power of NDVI was reported in other high density leafy systems such as mixed grasslands (R² = 0.4)
(Ningthoujam _et al_ .; 2025). In line with our results, red edge VIs including SR and EVI did not enhance
biomass prediction accuracy for dense grassland (Fig. 3D, Fig. S1).


Under dense biomass conditions, leaf area and pigment content are maximized, maximizing high red
absorbance for photosynthesis (low reflectance) and high NIR reflectance, resulting in saturation in
calculated NDVI. Duckweed shows high NIR reflectance from dense mats (Ningthoujam _et al_ .; 2025)
particularly due to its floating adaptations including their waterproofing adaxial cuticle, intracellular air
spaces for buoyancy and air-water interfaces (Cho _et al_ .; 2008, Ziegler _et al._ ; 2023). Reduced NIR
reflectance occurs with lower vegetation coverage when water is visible between fronds in river habitats
(Tian _et al_ .; 2010). Therefore, in high density laboratory-standardised contexts, rather than NDVI
capturing expanding leaf area and simultaneously reducing water reflectance as vegetation expands,
signal sensitivity to growth dynamics is reduced and biomass prediction has an upper limit. NDVI
readings above 0.6 are reported for healthy vegetation (Khdery _et al_ .; 2026) but these values can be
obtained even at low coverage (Murakami _et al._ ; 2025), demonstrating that NDVI is sensitive to
vegetation presence, but it does not increase linearly with biomass. Here, NDVI for accessions ranged
between 0.3-0.75, showing variation in plant density and greenness under low GL growing conditions
but a limit is reached to predict growth and biomass. Consequently, indices using R, red edge and NIR
spectral regions such as NDVI, EVI, OVI and GM may be more informative to monitor greenness via
pigments during active growth rather than under highly saturated conditions.


Treating duckweed like a standard arable crop also has limitations for yield prediction. Unlike
conventional arable crops, duckweed remains vegetative and lacks the canopy transitions that can
strengthen performance of VIs like NDVI and PRI for yield prediction. In crops, canopy organisation
complexity and pigment composition have distinct vegetative and reproductive phases. For example,
NDVI correlates moderately with chlorophyll content in the underutilised legume crop Bambara
groundnut ( _Vigna subterranea_ ) during vegetative growth (R² = 0.57) which improved during
reproductive stages (R &#91;2&#93; = 0.78) (Suhairi _et al_ .; 2020), and VIs produced better yield predictions at pod
filling (Jewan _et al_ .; 2020). Similar patterns were found in cereals, where NDVI could strongly predict
yield, biomass and light interception in vegetative stages and at peak canopy closure (R² = 0.75–0.87)
(Lopresti _et al_ .; 2015; Robles-Zazueta _et al_ .; 2021; Kumar _et al_ .; 2022; Pratiwi _et al_ .; 2025). In contrast,
duckweed forms a dense, flat and structurally uniform canopy with no definitive switch to reproductive
and pod filling stages, meaning that hyperspectral VIs could not simply be applied to duckweed biomass
in the same way as arable crops with growth stage shifts.


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Taken together, this suggests that canopy saturation, aquatic floatation characteristics and limited
phenological complexity could restrict the sensitivity of VIs to biomass detection or yield in duckweed.
Despite these limitations, hyperspectral reflectance was suitable for monitoring or predicting pigment
traits related to growth, such as chlorophyll content.


**4.2. Spectral regions for prediction of pigment contents in duckweed**


Chlorophyll content prediction was achievable using the GM index, with further improvement achieved
through PLSR modelling. GM uses reflectance from green 550 nm and red edge 750 nm, whereas the
PLSR model consistently highlighted 550 nm but the red edge region around 700 nm as key chlorophyll
predictors, aligning with chlorophyll spectral regions in forest (Gitelson _et al_ .; 2003) and wheat
canopies (Wu _et al_ .; 2008). As hypothesised, hyperspectral reflectance could identify duckweed
varieties which maintained greener fronds in low input (light) environments and offers a robust nondestructive alternative to chlorophyll assays. To support the development of duckweed as a commercial
crop, hyperspectral sensors could be integrated alongside existing RGB imaging systems in controlledenvironment agriculture and vertical farming platforms, as has been demonstrated for salad crop
production (Qin _et al._ ; 2023). Spectral markers within the green and red edge regions could be used to
monitor crop vigour, detect light stress and optimise nutrient management throughout production.


A remaining challenge is the separation of overlapping chlorophyll and carotenoid signals and to
overcome limitations of VIs and PLSR for carotenoid prediction. Integration of hyperspectral
reflectance and transmittance measurements, similar to approaches developed for broadleaf species like
tobacco (Falcioni _et al.;_ 2023b), may improve carotenoid quantification and isolate chlorophyll-specific
spectral responses. Although implementing transmittance measurements is more challenging in small
aquatic plants such as duckweed, combining reflectance, transmittance and chlorophyll fluorescence
data could improve discrimination of pigment pools. Improved carotenoid detection would be
particularly valuable for assessing both nutritional quality under low light cultivation and
photoprotective responses under high irradiance. For example, high light finishing treatments have been
used to enhance zeaxanthin accumulation in _Lemna_ (López‑Pozo _et al_ .; 2024) and there remains
opportunities for hyperspectral approaches to optimize pigments for nutritional applications.


**4.3. Spectral regions for photosynthetic and photoprotection predictions in duckweed**


Photoprotective traits such as NPQ and Y(NPQ) at VHL showed the strongest PLSR prediction overall.
Although this modelling was performed for low GL duckweeds, there may be promise for PLSR to
predict photoprotection capacity and efficiency in HL-grown duckweeds. In comparison, greenness VIs
in both low and high GL lacked sensitivity to predict maximum NPQ VHL (Fig. S1–S2), indicating that
PLSR models captured more relevant wavelengths associated to photoprotection which simple VIs
missed. The spectral regions driving NPQ and Y(NPQ) VHL prediction, particularly the green peak
around 550 nm and the red edge between 700–750 nm, were the same regions that drove chlorophyll
and carotenoid models. This spectral overlap reflects the fundamental role of chlorophyll and carotenoid
maintenance and xanthophyll cycle conversion underpinning dissipation as NPQ. The red edge spectral
region also associated with growth and biomass prediction, support the linking of pigment composition
and photoprotection to overall vigour in light environments. Consistent with this association, strong
collinearity was observed among pigment contents, photosynthetic traits (ETR, _F_ v / _F_ m, ΦPSII) and
greenness‑based VIs (PRI, GM, GI, NDVI, OVI) (Fig. S1). Therefore, suggesting that reductions in
pigment content and photosynthetic performance are accompanied by reduced vigour in low GL.
Together, these findings highlight the potential of hyperspectral monitoring of pigments and
photosynthetic traits to optimise duckweed production. By integrating hyperspectral cameras and
tracking spectral markers of pigments and photoprotection in real time, light intensity and spectral
recipes could be tailored to maximise biomass accumulation or enhance photoprotective pigments for
food applications. This would mirror techniques used to enhance biomass of microgreens under high
intensity blue light (Dmitriev _et al_ ;. 2026) or could be used to increase xanthophylls in _Lemna_ .


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Vegetation indices moderately associated with photosynthetic traits in high GL duckweed; NDVI
showed a positive relationship with ΦPSII HL and VHL, while PRI was associated with both _F_ v / _F_ m and
carotenoid:chlorophyll ratios. Carotenoid and specifically zeaxanthin levels are low in low GL but
accumulation is strongly influenced by light intensity. Therefore, high GL promotes xanthophyll cycle
de-epoxidation, increasing zeaxanthin production to dissipate excess absorbed energy through NPQ
(Stewart _et al_ .; 2021; Smith _et al_ .; 2024a). As zeaxanthin absorbs light strongly at 531 nm, this
contributes to the importance of the green peak and is used in calculating the PRI index in traditional
crops. In duckweed, PRI was negative and narrow in range (0 to -0.03), which likely reflects variation
in light stress, including both short-term xanthophyll cycle activity and longer-term changes in
chlorophyll–carotenoid balance (Gamon _et al_ .; 2015; Ogawa _et al_ .; 2024).


Although NDVI and PRI captured some variation in photosynthesis and pigment dynamics in duckweed
from high GL conditions, chlorophyll fluorescence remains essential for detecting immediate
photosynthetic adjustment to light. For example, PRI responded slower to thermal stress than _F_ v / _F_ m in
wheat (Cao _et al_ .; 2019), but such a temporal delay is unknown in duckweed. Together with relatively
low predictive performance of VIs for trait association in duckweed below R &#91;2&#93; = 0.5, potential lack of
sensitivity and possible temporal delay, this may limit independent use of hyperspectral reflectance to
characterise duckweed productivity under fluctuating light environments. Therefore, hyperspectral
reflectance cameras should be developed alongside fluorometers to compliment photosynthetic data and
together with RGB cameras to track growth. This connected and automated approach could be used to
maximize duckweed productivity in high irradiance or under niche light recipes (Wong _et al_ .; 2020,
Lanoue _et al_ .; 2026). Furthermore, there remains opportunities for integrating hyperspectral information
with photosynthetic efficiency through both light‑dependent electron transport and CO₂ assimilation
measurements to elucidate the mechanisms underpinning growth rate variation in duckweed (Rintoul
_et al_ .; 2026). To this end, more nuanced components of chlorophyll fluorescence kinetic parameters
(e.g. Falcioni _et al.;_ 2023a) could be described for duckweed to improve proxies relevant to food
production under different light environments.

# **5. Conclusions**


This study demonstrates that hyperspectral reflectance can capture meaningful physiological variation
in duckweed, particularly for chlorophyll content and photoprotection traits, however, the predictive
power for biomass and growth rate was limited. Furthermore, uncoupling specific chlorophyll and
carotenoid content responses presented challenges using hyperspectral reflectance alone. The use of
multivariate statistical approaches, such as PLSR, provides a strong framework for predicting
chlorophyll and key photosynthetic traits, demonstrating the value of full spectrum modelling rather
than simple VIs applied from other crops. Future work should compare additional machine learning
approaches and integrate hyperspectral data with other measurements to elucidate physiological
mechanisms driving duckweed growth variation.


Overall, this work establishes a framework for integrating hyperspectral information with vigour traits
to accelerate the selection of high-performing duckweed varieties for sustainable food production,
which could be expanded to include other duckweed species. Species-level differences identified here,
most notably the consistently high biomass, chlorophyll and carotenoid content of _Lemna japonica_,
highlight promising accessions for low-input food production systems (Smith _et al_ .; 2024a). _Lemna_
_japonica_ is also supported for upscaling in high GL due to its enhanced carotenoid yields. In contrast,
the putative hybrid _Lmu/Lmo_ could not be distinguished from _L. minuta_ by pigments, growth or
photosynthetic traits, suggesting these accessions could be unified taxonomically as _Lemna minuta_
(Smith _et al_ .; 2025).


Finally, extending hyperspectral approaches to the remote prediction of nutrient composition represents
an important next step for duckweed production systems. Chlorophyll content, for example, is closely


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preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
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tied not only to photosynthetic performance but also to nutritional components such as leaf N status
(Yoder &amp; Pettigrew‑Crosby.; 1995). Hyperspectral monitoring has shown the potential to predict
chlorophyll and nutrient status in other emerging crops (Wijewardane _et al_ .; 2023), but this capability
has yet to be established in duckweed despite substantial variation in nutrient composition in varieties
grown under common conditions (Smith _et al_ .; 2024b; 2025). Consequently, integrating hyperspectral
monitoring of pigments, photoprotection and nutrient status could provide a foundation for precision
duckweed cultivation, enabling biomass, nutritional quality and resource-use efficiency to be optimised
simultaneously in future food production systems.

# **6. Supplementary data**


The following supplementary data are available online.


**Table S1.** One hundred and thirty three accessions included in this study including species types,
collection site coordinates, regions and native water light environment measurements from different

seasons.


**Fig. S1.** Correlation matrix showing relationships between vegetation indices and pigment,
photosynthetic and growth traits across 133 duckweed accessions grown under a common low light
environment.


**Fig. S2.** Correlation matrix showing relationships between vegetation indices and pigment,
photosynthetic, biomass and macronutrient traits across 24 duckweed accessions grown under a
common high light environment.

# **Acknowledgements**


Thanks to Emma Jougla for assistance with chlorophyll extractions, Kade Marshall and Bethany Severn
for assistance with fresh biomass. Thanks to Laura Briers for support with chlorophyll fluorescence and
thanks to Hayley Newman for freeze-drying duckweed samples.

# **Author contributions**


KES: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Validation,
Visualization, Writing – Original draft. CARZ: Conceptualization, Formal analysis, Investigation,
Methodology, Software, Validation, Writing – Original draft. LC: Data curation, Methodology. MHY:
Data curation, Methodology. LM: Formal analysis, Methodology, Software. EHM: Conceptualization,
Funding acquisition, Project administration, Resources, Supervision. All authors contributed to writing
– Review and editing the final draft.

# **Conflict of interest**


The authors declare that there is no conflict of interest.

# **Funding**


The work was supported by a Biotechnological and Biological Sciences Research Council (BBSRC)
PhD scholarship (BB/M008770/1 to KES). The work was supported by the University of Nottingham
Future Food Beacon of Excellence. CARZ acknowledges support from the LOEWE Professorship for


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preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


Plant Breeding at Hochschule Geisenheim University funded by the Hessian Ministry of Higher
Education, Research and the Arts in Hesse, Germany while working on this manuscript.

# **Data availability**


The data from this study are available from the corresponding authors upon request.

# **References**


**Appenroth, K.J., Teller, S., Horn, M.** 1996. Photophysiology of turion formation and germination in
_Spirodela polyrhiza_ . Biologia Plantarum 38, 95–106. https://doi.org/10.1007/BF02879642


**Appenroth, K.J., Sree, K.S., Böhm, V., Hammann, S., Vetter, W., Leiterer, M., Jahreis, G.** 2017.
Nutritional value of duckweeds (Lemnaceae) as human food. Food Chemistry 217: 266–273.
https://doi.org/10.1016/j.foodchem.2016.08.116


**Appenroth, K.J., Sree, K.S, Bog, M.** _**et al**_ **.** 2018. Nutritional value of the duckweed species of the
genus _Wolffia_ (Lemnaceae) as human food. Frontiers in Chemistry 6: 483.
https://doi.org/10.3389/fchem.2018.00483


**Audenaert, L., Fernandes De Souza, M., De Zutter, N., Rousseau, D., Meers, E.** 2026. Evaluation
of the tolerance of duckweed (Lemnaceae) to abiotic stress factors associated with nutrient recycling
systems via multispectral imaging. Plant Stress, 19. 101198.
https://doi.org/10.1016/j.stress.2025.101198


**Bates, D., Mächler, M., Bolker, B., Walker, S.** 2015. Fitting Linear Mixed-Effects Models Using
lme4. Journal of Statistical Software, 67(1), 1–48. https://doi.org/10.18637/jss.v067.i01.


**Calzadilla, P.I., Carvalho, F.E.L., Gomez, R., Lima Neto, M.C., Signorelli, S** 2022. Assessing
photosynthesis in plant systems: A cornerstone to aid in the selection of resistant and productive crops.
Environmental and Experimental Botany. 201. 104950.
https://doi.org/10.1016/j.envexpbot.2022.104950


**Cao, Z., Yao, X., Liu, H., Liu, B., Cheng, T., Tian, Y., Cao, W., Zhu, Y.** 2019. Comparison of the
abilities of vegetation indices and photosynthetic parameters to detect heat stress in wheat. Agricultural
and Forest Meteorology, 265, 121-136. https://doi.org/10.1016/j.agrformet.2018.11.009


**Carmo-Silva, E., Andralojc, P.J., Scales, J.C., Driever, S.M., Mead, A., Lawson, T., Raines, C.A.,**
**Parry, M.A.J.** 2017. Phenotyping of field-grown wheat in the UK highlights contribution of light
response of photosynthesis and flag leaf longevity to grain yield. Journal of Experimental Botany, 68:
&#91;13, 3473–3486. https://doi.org/10.1093/jxb/erx169&#93;(https://doi.org/10.1093/jxb/erx169)


**Cho, H.J., Kirui, P., Natarajan, H.** 2008. Test of multi-spectral vegetation index for floating and
canopy-forming submerged vegetation. Int J Environ Res Public Health. Dec. 5, (5), 477-483.
https://doi.org/10.3390/ijerph5050477


**Coughlan, N.E., Walsh, É., Bolger, P., Burnell, G., O’Leary, N., O’Mahoney, M., Paolacci, S.,**
**Wall, D., Jansen, M.A.K.** 2022. Duckweed bioreactors: Challenges and opportunities for large-scale
indoor cultivation of Lemnaceae. Journal of Cleaner Production 336.

&#91;https://doi.org/10.1016/j.jclepro.2021.130285&#93;(https://doi.org/10.1016/j.jclepro.2021.130285)


**Dmitriev, P.A., Kozlovsky, B.L., Dmitrieva, A.A., Varduni, T.V., Lysenko, V.S.** 2026.
Hyperspectral Detection of Spectral Responses to Acute High-Irradiance Blue Light in Five Microgreen
Species. Stresses, 6(3), 61. https://doi.org/10.3390/stresses6030061


&#91;bioRxiv preprint doi: https://doi.org/10.64898/2026.11.06.764931; this version posted November 11, 2026. The copyright holder for this&#93;(https://doi.org/10.64898/2026.11.06.764931)

preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


**Dong, W., Carter, G.A., Barber, J.T.** 2002. Spectral reflectance of _Lemna gibba_ fronds exposed to
ethylene glycol. Aquatic Botany 73(3):275-281. https://doi.org/10.1016/S0304-3770(02)00026-8


**Erdle, K., Mistele, B., Schmidhalter, U.** 2011. Comparison of active and passive spectral sensors in
discriminating biomass parameters and nitrogen status in wheat cultivars. Field Crops Research. 124(1),
74-84. &#91;https://doi.org/10.1016/j.fcr.2011.06.007&#93;(https://doi.org/10.1016/j.fcr.2011.06.007)


**Falcioni, R., Antunes, W.C., Oliveira, R.B.d., Chicati, M.L., Demattê, J.A.M., &amp; Nanni, M.R.**
2023a. Assessment of Combined Reflectance, Transmittance, and Absorbance Hyperspectral Sensors
for Prediction of Chlorophyll a Fluorescence Parameters. Remote Sensing, 15(20), 5067.
https://doi.org/10.3390/rs15205067


**Falcioni, R., Antunes, W.C., Demattê, J.A.M., Nanni, M.R.** 2023b. A Novel Method for Estimating
Chlorophyll and Carotenoid Concentrations in Leaves: A Two Hyperspectral Sensor Approach. Sensors
(Basel). Apr 9;23(8):3843. https://doi.org/10.3390/s23083843


**Food and Agriculture Organisation of the United Nations (FAO)** 2021. The state of the world’s
land and water resources for food and agriculture – Systems at breaking point. Synthesis report 2021.
Rome. Accessed at: https://doi.org/10.4060/cb7654en Accessed on 25/01/206


**Gamon, J.A., Serrano, L., Surfus, J.S.** 1997. The photochemical reflectance index: an optical
indicator of photosynthetic radiation use efficiency across species, functional types, and nutrient levels.
Oecologia; 112(4):492-501. https://doi.org/10.1007/s004420050337


**Gamon, J.A., Field, C.B., Goulden, M.L., Griffin, K.L., Hartley, A.E., Joel, G., Penuelas, J.,**
**Valentini, R..** 1995. Relationships Between NDVI, Canopy Structure, and Photosynthesis in Three
Californian Vegetation Types. Ecological Applications, 5: 28-41. https://doi.org/10.2307/1942049


**Gamon, J. A., Kovalchuck, O., Wong, C. Y. S., Harris, A., Garrity, S.R.** 2015. Monitoring seasonal
and diurnal changes in photosynthetic pigments with automated PRI and NDVI sensors,
Biogeosciences, 12, 4149–4159. https://doi.org/10.5194/bg-12-4149-2015


**Garbulsky, M.F., Peñuelas, J., Gamon, J., Inoue, Y., Filella, I.** 2011. The photochemical reflectance
index (PRI) and the remote sensing of leaf, canopy and ecosystem radiation use efficiencies: A review
and meta-analysis. Remote Sensing of Environment. 115(2). 281-297.
https://doi.org/10.1016/j.rse.2010.08.023


**Gerardo, R., de Lima, I.P.** 2022. Monitoring Duckweeds ( _Lemna minor_ ) in Small Rivers Using
Sentinel-2 Satellite Imagery: Application of Vegetation and Water Indices to the Lis River (Portugal).
Water, 14, 2284. https://doi.org/10.3390/w14152284


**Gitelson, A.A., M. N. Merzlyak M.N** . 1997. Remote estimation of chlorophyll content in higher plant
leaves, International Journal of Remote Sensing, 18:12, 2691-2697.
https://doi.org/10.1080/014311697217558


**Gitelson, A.A., Gritz, Y., Merzlyak, M.N.** 2003. Relationships between leaf chlorophyll content and
spectral reflectance and algorithms for non-destructive chlorophyll assessment in higher plant leaves.
Journal of Plant Physiology, 160(3), 271-282 https://doi.org/10.1078/0176-1617-00887


**Gray, D.A, Sutcharit, P., Wattanakul, J.** _**et al**_ **.** 2026. Chloroplasts as ingredients for food: a review.
Food &amp; Function. 17. 12. https://doi.org/10.1039/D5FO03797B


**He, C., Sun, J., Chen, Y., Wang, L., Shi, S., Qiu, F., Wang, S., Tagesson, T.** 2023. A new vegetation
index combination for leaf carotenoid-to-chlorophyll ratio: minimizing the effect of their correlation.
International Journal of Digital Earth, 16(1), 272–288. https://doi.org/10.1080/17538947.2023.2168772


&#91;bioRxiv preprint doi: https://doi.org/10.64898/2026.11.06.764931; this version posted November 11, 2026. The copyright holder for this&#93;(https://doi.org/10.64898/2026.11.06.764931)

preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


**Index** **DataBase** 2026. A Database for Remote Sensing Indices. Accessed at:
https://www.indexdatabase.de Accessed on: 05/05/2026


**Islam, M.R., Haque, S., Akter, N., Karim, M.A.** 2014. Leaf chlorophyll dynamics in wheat based on
SPAD meter reading and its relationship with grain yield. Journal of Scientia Agriculture. 8; 1. 13-18.
https://doi.org/10.15192/PSCP.SA.2014.4.1.1318


**Jewan, S.Y.Y., Pagay, V., Billa, L., Tyerman, S.D., Gautam, D., Sparkes, D., Chai, H.H., Singh,**
**A.** 2022. The feasibility of using a low cost near-infrared, sensitive, consumer-grade digital camera
mounted on a commercial UAV to assess Bambara groundnut yield. International Journal of Remote
&#91;Sensing, 43:2, 393-423. https://doi.org/10.1080/01431161.2021.1974116&#93;(https://doi.org/10.1080/01431161.2021.1974116) **Khdery, G.A., Shokr, M.S,**
**Rebouh, N.Y., El-Amier, Y.A.** 2026. Field-based hyperspectral characterization of wetland plant
diversity and vitality in Burullus Lagoon (Nile Delta, Egypt). PLoS One. Mar 4;21(3):e0341891.
https://doi.org/10.1371/journal.pone.0341891


**Kim, T-H.,Kim, S-M.** 2024. Effects of SPAD value variations according to nitrogen application levels
on rice yield and its components. Frontiers Plant Science. 15:1437371.
https://doi.org/10.3389/fpls.2024.1437371


**Kramer, D.M., Johnson, G., Kiirats, O. Edwards, G.E.** 2004. New fluorescence parameters for the
determination of QA redox state and excitation energy fluxes. Photosynth Res 79: 209–218.
https://doi.org/10.1023/B:PRES.0000015391.99477.0d


**Kumar, D.A., Neelima, T.L., Srikanth, P., Uma Devi, M., Suresh, K., Murthy, C.S.** 2022. Maize
yield prediction using NDVI derived from Sentinal 2 data in Siddipet district of Telangana state. Journal
of Agrometeorology, 24(2), 165–168. https://doi.org/10.54386/jam.v24i2.1635


**Landolt, E.** 1986. Biosystematic investigations in the family of duckweeds (Lemnaceae). Vols 1 and
2. Zürich: Geobotanisches Institut der Eidgenössische Technische Hochschule.


**Lanoue, J., Little, C., Louis, S., Terlizzese, D., Hawley, D., Hao, X.** 2026. The Effect of Light
Spectrum on Growth, Yield, and Spectral Transmission in Greenhouse Eggplant: Red-blue versus
Broad Spectrum. September. 61(9):2040-2050


**Leng, R., Stambolie J.H., Bell R.** 1995. Duckweed - a potential high-protein feed resource for domestic
animals and fish. Livestock Research for Rural Development 7: 1–11. Accessed at:
http://www.lrrd.org/lrrd7/1/3.htm Accessed on 29/04/2026


**Ligges U., Short T., Kienzle P.** 2015. signal: Signal Processing. R package version 0.7-6, Accessed at:
https://CRAN.R-project.org/package=signal Accessed on 03/11/2025


**Liran, O., Shir, O.M., Levy, S., Grunfeld, A., Shelly, Y.** 2020. Novel Remote Sensing Index of
Electron Transport Rate Predicts Primary Production and Crop Health in _L. sativa_ and _Z. mays_ . Remote
Sens. 2020, 12, 1718. https://doi.org/10.3390/rs12111718


**Lopresti, M.F., Di Bella, C.M., Degioanni, A.J.** 2015. Relationship between MODIS-NDVI data and
wheat yield: A case study in Northern Buenos Aires province, Argentina. Information Processing in
Agriculture. 2(2). 73-84. https://doi.org/10.1016/j.inpa.2015.06.001


**Lyu, X., Du, W., Zhang, H., Ge, W., Chen, Z., &amp; Wang, S.** 2024. Classification of Different Winter
Wheat Cultivars on Hyperspectral UAV Imagery. Applied Sciences, 14(1), 250.
https://doi.org/10.3390/app14010250


**López-Pozo, M., Adams III, W.W., McNamara, M., Demmig-Adams, B** 2024. A preharvest
finishing procedure for _Lemna_ to produce high levels of zeaxanthin that is retained post-high-light
exposure. Future Foods, 10, 100517. https://doi.org/10.1016/j.fufo.2024.100517


&#91;bioRxiv preprint doi: https://doi.org/10.64898/2026.11.06.764931; this version posted November 11, 2026. The copyright holder for this&#93;(https://doi.org/10.64898/2026.11.06.764931)

preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


**Mahajan, G.R., Pandey, R.N., Sahoo, R.N., Gupta, V.K., Datta, S.C., Kumar, D.** 2017. Monitoring
nitrogen, phosphorus and sulphur in hybrid rice ( _Oryza sativa_ L.) using hyperspectral remote sensing.
Precision Agriculture. 18(5). 736-761. https://doi.org/10.1007/s11119-016-9485-2


**Maxwell, K., Johnson, G.N.** Chlorophyll fluorescence -a practical guide. J Exp Bot 2000
Apr;51(345):659-68. https://doi.org/10.1093/jxb/51.345.659


**McCann, M.** 2016. Response diversity of free-floating plants to nutrient stoichiometry and
temperature: growth and resting body formation. PeerJ 4: e1781. https://doi.org/10.7717/peerj.1781


**Mevik, B.-H., &amp; Wehrens, R.** 2007. The pls Package: Principal Component and Partial Least Squares
Regression in R. Journal of Statistical Software, 18(2), 1–23. https://doi.org/10.18637/jss.v018.i02


**Michael, T.P., Ernst** _**et al**_ **.** 2021. Genome and time-of-day transcriptome of _Wolffia australiana_ link
morphological minimization with gene loss and less growth control. Genome Research 31, 225–238.
https://doi.org/10.1101/gr.266429.120


**Montesinos-López, O.A., Montesinos-López, A., Crossa, J., de Los Campos, G., Alvarado, G.,**
**Suchismita, M., Rutkoski, J., González-Pérez, L., Burgueño, J** 2017. Predicting grain yield using
canopy hyperspectral reflectance in wheat breeding data. Plant Methods. 3;13:4.
&#91;https://doi.org/10.1186/s13007-016-0154-2&#93;(https://doi.org/10.1186/s13007-016-0154-2)


**Murakami, A., Komatsu, Y., Takizawa, K.** 2025. Remote Detection of Red Edge Spectral
Characteristics in Floating Aquatic Vegetation. Astrobiology. Mar;25(3):209-224.
https://doi.org/10.1089/ast.2024.0127


**Murchie, E.H., Lawson, T.** 2013. Chlorophyll fluorescence analysis: a guide to good practice and
understanding some new applications. J Exp Bot. 2013 Oct;64(13):3983-98.
https://doi.org/10.1093/jxb/ert208


**Ningthoujam, R.K., Bloomfield, K.J., Crawley, M.J., Estrada, C., Prentice, C.I.** 2025.
Hyperspectral Sensing of Aboveground Biomass and Species Diversity in a Long-Running Grassland
Experiment. Ecological Informatics. 86, 103028. https://doi.org/10.1016/j.ecoinf.2025.103028


**Ogawa, T., Tamaki, M., Usui, T., Hikosaka, K.** 2024. Hyperspectral image extraction to evaluate the
photosynthetic and stress status of plants, using a photochemical reflectance index (PRI). Scientia
Horticulturae 336, 113349. https://doi.org/10.1016/j.scienta.2024.113349


**Pandey, P., Ge, Y., Stoerger, V., Schnable, J.C.** 2017. High Throughput In vivo Analysis of Plant
Leaf Chemical Properties Using Hyperspectral Imaging. Front. Plant Sci. 8:1348.
https://doi.org/10.3389/fpls.2017.01348


**Pavlović, D., Bogdan, N., Sanja, D., Waisi, H. Anđelković A.A., Marisavljević, D.** 2014.
Chlorophyll as a measure of plant health: agroecological aspects. Pesticidi I Fitomedicina 29: 21-34.
https://doi.org/10.2298/PIF1401021P


**Petersen F., Demann, J., Restemeyer, D., Olfs, H., Westendarp, H., Appenroth, K., Ulbrich, A**
2022a. Influence of light intensity and spectrum on duckweed growth and proteins in a small-scale, recirculating indoor vertical farm. Plants Apr 7;11(8):1010. https://doi.org/10.3390/plants11081010


**Petersen, F., Demann, J., von Salzen, J., Olfs, H.W., Westendarp, H., Wolf, P., Appenroth, K.J.,**
**Ulbrich, A.** 2022b. Re-circulating indoor vertical farm: Technicalities of an automated duckweed
biomass production system and protein feed product quality evaluation. Journal of Cleaner Production
380:134894. https://doi.org/10.1016/j.jclepro.2022.134894


&#91;bioRxiv preprint doi: https://doi.org/10.64898/2026.11.06.764931; this version posted November 11, 2026. The copyright holder for this&#93;(https://doi.org/10.64898/2026.11.06.764931)

preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


**Polutchko, S.K., Adams, W.W., Escobar, C.M., Demmig-Adams, B** 2022. Conquering space with
crops that produce ample oxygen and antioxidants. Oxygen 2, 211–226.
https://doi.org/10.3390/oxygen2020016


**Pratiwi, G.R., Indarto, I., Hakim, F.L., Sulistiono, W., Roivansah, M.F., Ramadhan, R.P.,**
**Helmanto, H., Pustika, A.B.** 2025. Rice yield estimation using vegetation indexes derived from

                                                               Sentinel-2 imagery for sustainable agriculture. Discov Sustain 6, 1048. &#91;https://doi.org/10.1007/s43621&#93;(https://doi.org/10.1007/s43621-025-01743-3)

025-01743-3


**Qin, J., Monje, O., Nugent, M.R., Finn, J.R., O’Rourke, A.E., Wilson, K.D., Fritsche, R.F., Baek,**
**I., Chan, D.E. Kim, M.S.** 2023. A hyperspectral plant health monitoring system for space crop
production. Frontiers Plant Science. 14:1133505. https://doi.org/10.3389/fpls.2023.1133505


**Rintoul, R.C, Gill, A.R., McAusland, L., Murchie, E.H., Gilliham, M., Mortimer, J.C.** 2026.
Developing carbon assimilation methods in duckweed for insights into photosynthesis and growth
mechanisms. Plant Physiology. https://doi.org/10.1093/plphys/kiag311


**Robles-Zazueta, C.A., Molero, G., Pinto, F., Foulkes, M.J., Reynolds, M.P., Murchie E.H.** 2021.
Field-based remote sensing models predict radiation use efficiency in wheat. J. Exp. Bot. 723756–3773.
https://doi.org/10.1093/jxb/erab115


**Robles-Zazueta, C.A., Pinto, F., Molero, G., Foulkes, M.J., Reynolds, M.P. Murchie E.H.** 2022.
Prediction of Photosynthetic, Biophysical, and Biochemical Traits in Wheat Canopies to Reduce the
Phenotyping Bottleneck. Front. Plant Sci. 13:828451. https://doi.org/10.3389/fpls.2022.828451


**Sanaeifar, A., Yang C., de la Guardia M., Zhang W., Li X., He Y.** Proximal hyperspectral sensing
of abiotic stresses in plants. Sci Total Environ 2023 Feb 25;861:160652.
https://doi.org/10.1016/j.scitotenv.2022.160652.


**Shammi, S.A, Meng, X.** 2021. Use time series NDVI and EVI to develop dynamic crop growth metrics
for yield modeling. Ecological Indicators. 121, 107124. https://doi.org/10.1016/j.ecolind.2020.107124


**Shi, Y., Huang, W., Ye, H., Ruan, C., Xing, N., Geng, Y., Dong, Y., Peng, D.** 2018. Partial Least
Square Discriminant Analysis Based on Normalized Two-Stage Vegetation Indices for Mapping
Damage from Rice Diseases Using PlanetScope Datasets. Sensors, 18(6), 1901.
https://doi.org/10.3390/s1806190


**Shivashankar, K., Potdar** _**et al**_ **.** 2025. SPAD dynamics in maize crop with precision nitrogen
management under rain-fed and irrigated conditions. Sci Rep 15, 22842.
https://doi.org/10.1038/s41598-025-05255-y


**Sims, D.A., Gamon, J.A.** 2002. Relationships between leaf pigment content and spectral reflectance
across a wide range of species, leaf structures and developmental stages. Remote Sensing of
Environment. 81(2-3), 337-354. https://doi.org/10.1016/S0034-4257(02)00010-X


**Smith, K.E., Cowan, L, Taylor, B, McAusland, L, Heatley, M, Yant, L, Murchie, E.H.** 2024a.
Physiological adaptation to irradiance in duckweeds is species and accession specific and depends on
light habitat niche. Journal of Experimental Botany. https://doi.org/10.1093/jxb/erad499


**Smith, K.E., Zhou M., Flis, P., Jones, D.H., Bishopp, A., Yant, L..** 2024b. The evolution of the
duckweed ionome mirrors losses in structural complexity. Annals of Botany.
https://doi.org/10.1093/aob/mcae012


**Smith, K.E., Schäfer, M., Lim, M., Robles-Zazueta, C.A., Cowan, L., Fisk, I.D., Xu, S., Murchie,**
**E.H.** 2024c. Aroma and metabolite profiling in duckweeds: Exploring species and ecotypic variation to


&#91;bioRxiv preprint doi: https://doi.org/10.64898/2026.11.06.764931; this version posted November 11, 2026. The copyright holder for this&#93;(https://doi.org/10.64898/2026.11.06.764931)

preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


enable wider adoption as a food crop. Journal of Agriculture and Food Research. 18. Dec. doi:
https://doi.org/10.1016/j.jafr.2024.101263


**Smith, K.E., Cowan L., Flis P., Moore C., Heatley M., Robles-Zazueta C.A., Lee A., Yant L** 2025.
An ecological, phenotypic, and genomic survey of duckweeds with their associated aquatic
environments in the United Kingdom. AoB Plants. Mar 31;17(3)
https://doi/org/10.1093/aobpla/plaf018


**Son, N.T., Chen, C.F., Chen, C.R., Minh, V.Q., Trung, N.H** 2014. A comparative analysis of
multitemporal MODIS EVI and NDVI data for large-scale rice yield estimation. Agricultural and Forest
Meteorology. 197, 52-64. https://doi.org/10.1016/j.agrformet.2014.06.007


**Sree, K.S., Sudakaran S., Appenroth K.J.** 2015b. How fast can angiosperms grow? Species and
clonal diversity of growth rates in the genus _Wolffia_ (Lemnaceae). Acta Physiologiae Plantarum. 37.
204. https://doi.org/10.1007/s11738-015-1951-3


**Stewart, J.J., Adams W.W., Escobar C.M., López-Pozo M., Demmig-Adams B** 2020. Growth and
essential carotenoid micronutrients in _Lemna gibba_ as a function of growth light intensity. Frontiers in
Plant Science 11: 1–14. https://doi.org/10.3389/fpls.2020.00480


**Stewart, J.J., Adams W.W., López-Pozo M., Doherty Garcia N., McNamara M., Escobar C.M.,**
**Demmig-Adams B** 2021. Features of the duckweed _Lemna_ that support rapid growth under extremes
of light intensity. Cells 10: 1–21. https://doi.org/10.3390/cells10061481


**Stratoulias, D., Balzter, H., Zlinszky, A., &amp; Tóth, V.R.** 2015. Assessment of ecophysiology of lake
shore reed vegetation based on chlorophyll fluorescence, field spectroscopy and hyperspectral airborne
imagery. Remote Sensing of Environment, 157, 72-84. &#91;https://doi.org/10.1016/j.rse.2014.05.021&#93;(https://doi.org/10.1016/j.rse.2014.05.021)


**Strzalek, M., Kufel, L..** 2021. Light intensity drives different growth strategies in two duckweed
species: _Lemna_ _minor_ L. and _Spirodela_ _polyrhiza_ (L.) Schleiden. PeerJ, 9:e12698
&#91;http://doi.org/10.7717/peerj.12698&#93;(http://doi.org/10.7717/peerj.12698)


**Suhairi, T.A.S.T.M., Sinin, S.S.M., Wimalasiri, E.M., Nizar, N.M.M., Tharmandran, A.S.,**
**Jahanshiri, E., Gregory, P.J., Azam-Ali, S.N.** 2020. Use of Unmanned Aerial Vehicles (UAVs)
Imagery in Phenotyping of _Bambara_ Groundnut. J. Agric. Sci. 2020, 12, 12–22.
&#91;https://doi.org/10.5539/jas.v12n6p12&#93;(https://doi.org/10.5539/jas.v12n6p12)


**Tian, Y.Q., Yu, Q., Zimmerman, M.J. Flint, S., Waldron, M.C.** 2010. Differentiating aquatic plant
communities in a eutrophic river using hyperspectral and multispectral remote sensing. Freshwater
Biology. 55, 8, 1658-1673. https://doi.org/10.1111/j.1365-2427.2010.02400.x


**United Nations** 2022, World Population Prospects 2022 - Summary of results. Department of economic
and social affairs. New York, 2022. Accessed at:
https://www.un.org/development/desa/pd/sites/www.un.org.development.desa.pd/files/wpp2022_sum
mary_of_results.pdf Accessed on: 25/01/2026


**Villa, P., Pinardi, M., Tóth, V. R., Hunter, P. D., &amp; Bolpagni, R** 2017. Remote sensing of macrophyte
morphological traits: implications for the management of shallow lakes. Journal of Limnology, 76(s1),
109-126. https://doi.org/10.4081/jlimnol.2017.1629


**Wang, R., Gamon, J.A** 2019. Remote sensing of terrestrial plant biodiversity. Remote Sensing of
&#91;Environment. 231. 111218. https://doi.org/10.1016/j.rse.2019.111218&#93;(https://doi.org/10.1016/j.rse.2019.111218)


**Wei,** **T.,** **Simko,** **V.** 2024. corrplot: Visualization of a Correlation Matrix.
10.32614/CRAN.package.corrplot


&#91;bioRxiv preprint doi: https://doi.org/10.64898/2026.11.06.764931; this version posted November 11, 2026. The copyright holder for this&#93;(https://doi.org/10.64898/2026.11.06.764931)

preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in
&#91;perpetuity. It is made available under a CC-BY 4.0 International license.&#93;(http://creativecommons.org/licenses/by/4.0/)


**Wijewardane, N.K., Zhang, H., Yang, J., Schnable, J.C., Schachtman, D.P., Ge, Y..** 2023. A leaflevel spectral library to support high-throughput plant phenotyping: predictive accuracy and model
&#91;transfer, Journal of Experimental Botany, 74 (14), 4050–4062. https://doi.org/10.1093/jxb/erad129&#93;(https://doi.org/10.1093/jxb/erad129)


**Wong, C. E., Teo, Z. W. N., Shen, L., Yu, H.** 2020. Seeing the lights for leafy greens in indoor vertical
farming, Trends in Food Science &amp; Technology, 106, 48-63, https://doi.org/10.1016/j.tifs.2020.09.031


**Wu, C., Niu, Z., Tang, Q., Huang, W.** 2008. Estimating chlorophyll content from hyperspectral
vegetation indices: Modeling and validation. Agricultural and Forest Meteorology. 148(8-9). 12301241 https://doi.org/10.1016/j.agrformet.2008.03.005


**Xiao, B., Li, S., Dou, S.** _**et al**_ **.** 2024. Comparison of leaf chlorophyll content retrieval performance of
citrus using FOD and CWT methods with field-based full-spectrum hyperspectral reflectance data.
Computers and Electronics in Agriculture. 217. 108559. https://doi.org/10.1016/j.compag.2023.108559


**Xu, J., Shen, Y., Zheng, Y., Smith, G., Sun, X.S., Wang, D., Zhao, Y., Zhang, W., Li, Y.** 2023.
Duckweed (Lemnaceae) for potentially nutritious human food: A review. Food Rev. Int. 39:3620–3634.
https://doi.org/10.1080/87559129.2021.2012800


**Xue, J., &amp; Su, B** 2017. Significant remote sensing vegetation indices: A review of developments and
applications. Journal of sensors, 2017(1), 1353691. https://doi.org/10.1155/2017/1353691


**Yoder, B.J, Pettigrew‑Crosby, R.E.** 1995. Predicting nitrogen and chlorophyll content and
concentrations from reflectance spectra (400–2500 nm) at leaf and canopy scales. Remote Sensing of
Environment, 53(3), 199-211. https://doi.org/10.1016/0034-4257(95)00135-N


**Zhang H., Ge Y., Xie X., Atefi A., Wijewardane N.K., Thapa S** 2022. High throughput analysis of
leaf chlorophyll content in sorghum using RGB, hyperspectral, and fluorescence imaging and sensor
fusion. Plant Methods. May 3;18(1):60. https://doi.org/10.1186/s13007-022-00892-0.


**Zhang, F.Q., Li, J., Zhang, R.** _**et al**_ **.** 2025. Zeaxanthin augments CD8+ effector T cell function and
immunotherapy efficacy. Cell Rep Med. Sep 16;6(9):102324.
https://doi.org/10.1016/j.xcrm.2025.102324


**Zhi, X., Massey-Reed, S.R., Wu, A.** _**et al**_ **.** 2022. Estimating Photosynthetic Attributes from HighThroughput Canopy Hyperspectral Sensing in Sorghum. Plant Phenomics. Apr 8;2022:9768502.
https://doi.org/10.34133/2022/9768502


**Ziegler, P., Adelmann, K., Zimmer, S., Schmidt, C., Appenroth, K.J** 2015. Relative _in vitro_ growth
rates of duckweeds (Lemnaceae)—the most rapidly growing higher plants. Plant Biology 17, 33–41.
&#91;https://doi.org/10.1111/plb.12184&#93;(https://doi.org/10.1111/plb.12184)


**Ziegler, P., Appenroth, K.J., Sree, K.S.** 2023. Survival Strategies of Duckweeds, the World's Smallest
Angiosperms. Plants (Basel). Jun 3;12(11):2215. https://doi.org/10.3390/plants12112215 **Zięć, G.,**
**Michalski, O., Konieczna-Molenda, A., Dera, T., &amp; Tkaczewska, J.** 2025. Nutritional Value, Health
Properties, Safety Considerations, and Consumer Acceptance of Lemnoideae as Human Food. Nutrients
17(18), 3026. https://doi.org/10.3390/nu17183026


