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Received: 18 August 2022
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Revised: 20 December 2022
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Accepted: 28 December 2022
DOI: 10.1111/pce.14530
REVIEW
The overlooked functions of trichomes: Water absorption
and metal detoxication
Cui Li
1
|Yingying Mo
1
|Nina Wang
1
|Longyi Xing
1
|Yang Qu
2
|
Yanlong Chen
1
|Zuoqiang Yuan
1
|Arshad Ali
3
|Jiyan Qi
1
|
Victoria Fernández
4
|Yuheng Wang
1
|Peter M. Kopittke
5
1
School of Ecology and Environment,
Northwestern Polytechnical University,
Xi'an, China
2
Baoji Academy of Agriculture Sciences,
Baoji, China
3
College of Life Sciences, Hebei University,
Hebei, China
4
School of Forest Engineering, Technical
University of Madrid, Madrid, Spain
5
School of Agriculture and Food Sciences,
The University of Queensland, St Lucia,
Queensland, Australia
Correspondence
Cui Li and Yanlong Chen, School of Ecology
and Environment, Northwestern Polytechnical
University, Xi'an 710072, China.
Email: cui.li@nwpu.edu.cn and
ylchen8895@nwpu.edu.cn
Funding information
National Natural Science Foundation of China,
Grant/Award Numbers: NSFC, 32101838;
Fundamental Research Funds for the Central
Universities, Grant/Award Number:
D5000210898; Science Foundation for
Youths of Shaanxi Province,
Grant/Award Number: 2021JQ‐097
Abstract
Trichomes are epidermal outgrowths on plant shoots. Their roles in protecting plants
against herbivores and in the biosynthesis of specialized metabolites have long been
recognized. Recently, studies are increasingly showing that trichomes also play
important roles in water absorption and metal detoxication, with these roles having
important implications for ecology, the environment, and agriculture. However,
these two functions of trichomes have been largely overlooked and much remains
unknown. In this review, we show that the trichomes of 37 plant species belonging
to 14 plant families are involved in water absorption, while the trichomes of 33
species from 13 families are capable of sequestering metals within their trichomes.
The ability of trichomes to absorb water results from their decreased hydrophobicity
compared to the remainder of the leaf surface as well as the presence of special
structures for collecting and absorbing water. In contrast, the metal detoxication
function of trichomes results not only from the good connection of their basal cells
to the underlying vascular tissues, but also from the presence of metal‐chelating
ligands and transporters within the trichomes themselves. Knowledge gaps and
critical future research questions regarding these two trichome functions are
highlighted. This review improves our understanding on trichomes.
KEYWORDS
foliar water uptake, function, metal accumulation, metal detoxication, trichome,
water absorption
1|INTRODUCTION
Trichomes are epidermal structures that are found widely on plant
shoots (Hülskamp, 2004). Trichomes are extremely diverse in shape,
structure and size—they can be unicellular or multicellular, straight or
branched and capitate or stellate in shape. Depending upon whether
they have the ability to biosynthesize and secrete substances,
trichomes can be divided into non‐glandular and glandular trichomes
whereby glandular trichomes can biosynthesize, store and secrete
specialized metabolites (Werker, 2000). Often, non‐glandular tri-
chomes are unicellular and are common within the plant kingdom, in
contrast, glandular trichomes are typically multicellular, have a peltate
or capitate head, and are present in 20%–30% of vascular plant
species (Liu et al., 2020; Muravnik, 2021).
Trichomes have been investigated since the early 20th century,
with a rapid increase during the 1990s. Studies in the 20th century
were generally focused on the anatomy of trichomes (Carlquist,
1958; Ramaley, 1902), and the physiological interactions between
Plant Cell Environ. 2023;46:669–687. wileyonlinelibrary.com/journal/pce © 2022 John Wiley & Sons Ltd.
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trichomes and the surrounding environment (Johnson, 1975; Levin,
1973; Nielsen et al., 1984). Since the 21st century, most studies have
tended to focus on trichome morphogenesis (e.g., the non‐glandular
trichomes of Arabidopsis thaliana and glandular trichomes of Solanum
lycopersicum [Berhin et al., 2022; Guan et al., 2014; Pichersky et al.,
2006]) and on the metabolic network of glandular trichomes (e.g., the
regulation network for the production of artemisinin by the glandular
secretory trichomes of Artemisia annua [Maes et al., 2011; Xie et al.,
2021]). From these studies, many functions of trichomes have been
identified, with these functions generally falling into four broad
categories (Figure 1): (i) Protection of plants against abiotic stresses,
including against UV damage (Manetas, 2003), water repellence
(Fernández et al., 2011; Gutschick, 1999; Konrad et al., 2021) and
ozone resistance (S. Li et al., 2018; Oksanen, 2018); water absorption
(Eller et al., 2016; Raux et al., 2020) and metal detoxication (Blamey
et al., 2015; C. Li et al., 2021). (ii) Protection of plants against biotic
stress, including against herbivores and pathogens via physical
interference and the excretion of toxic or repellent chemical
compounds by glandular trichomes (Karabourniotis et al., 2020;
Peiffer et al., 2009; Pillemer & Tingey, 1976). (iii) Biosynthesis of
specialized metabolites, including the production of various func-
tional phytochemicals which could be used as fragrances, food
additives or pharmaceuticals (Celedon et al., 2020; Chen et al., 2017;
Schuurink & Tissier, 2020); and the production and emission of
volatile organic compounds for plant‐plant communications (Ninkovic
et al., 2021). (iv) Developmental roles, including the regulation of the
structure of the flower during flower development (Glover et al.,
2004; El Ottra et al., 2013; Tan et al., 2016); assisting with pollination
(Oelschlägel et al., 2009) and helping with the capture of prey in
carnivorous plants (Lin et al., 2021) (Figure 1).
For any given trichome, its functions depend upon not only the
plant species and the organ in which it is located, but also the
environment where they grow, the timing of activity and its structure
and chemical composition (Muravnik, 2021). Generally, trichomes of
plants from the same genus tend to have similarities in both
morphology and function (Glover et al., 2004). However, while
trichomes are governed by the genotype of the plant, the structure,
chemical constituents and functions of trichomes are greatly affected
by the environment given that they are ‘active sensors’and can
respond to various stimulations (Karabourniotis et al., 2020; Machado
FIGURE 1 The function of the trichomes. The trichome functions marked with ‘*’are the topic of the present review.
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et al., 2022; Zhou et al., 2017). For example, Zhou et al. (2017) found
that mechanical stimulation of the non‐glandular trichomes of A.
thaliana can cause Ca
2+
oscillations and apoplastic alkalisation in the
trichome base and the surrounding cells.
Of these various functions, some are well‐known and have been
well‐characterized. For example, the herbivory resistance function of
trichomes has been systematically studied, with this protection being
associated with the occurrence of the thick, hairy trichomes which
provide a physical barrier, the release of chemical repellents, the
production of calcium oxalate (present as raphides) and the presence
of phenolics within the trichomes which make it difficult for insects
to chew, and by inducing the expression of defense transcripts
when in contact with herbivores (Franceschi & Nakata, 2005;
Karabourniotis et al., 2020; Peiffer et al., 2009). By contrast, some
trichome functions have often been overlooked and are less studied.
In particular, the role of trichomes in the absorption of water and in
the detoxication of metals have received comparatively little
attention historically, although an increasing number of studies are
now demonstrating that trichomes are involved in foliar water uptake
(FWU) and plant metal detoxication (Eller et al., 2016; Raux
et al., 2020).
To shed light on these two lesser‐studied functions of trichomes
is of substantial interest, not only to better understand the
physiology, metabolism and biochemistry of the trichome itself, but
also because this information could potentially lead to new
possibilities in the use and management of plants. For example, the
absorption of water by the trichomes could potentially benefit plants
through multiple mechanisms, including by improving the leaf water
status (Eller et al., 2016; Fuenzalida et al., 2019), enhancing
photosynthesis (Simonin et al., 2009) and by increasing carbon
assimilation rates (Binks et al., 2019). In addition, given that the
frequency of drought events will likely increase in the future, such
leaf‐level effects could change plant hydraulics, improve plant growth
and adaptability and could ultimately influence the ecology
(Figure 2a). In a similar manner, understanding the detoxication of
metals by trichomes has important implications for both the
environment (e.g., phytoremediation) and agriculture (e.g., foliar
fertilisation) (Blamey et al., 2015; C. Li et al., 2021; F. Zhao et al.,
2000). Regarding the former (i.e., the importance of metal detoxica-
tion by trichomes in phytoremediation), metal compartmentalisation
and detoxification in the shoot has been shown to be a key process
for phytoremediation given that it determines the concentration of
the metals that can be accumulated without exerting a toxic effect,
with the trichomes being an important site for metal sequestration
and detoxification in some plant species (Rascio & Navari‐Izzo, 2011;
F.‐J. Zhao et al., 2022). For example, the concentration of Se in the
trichomes of the Se hyperaccumulator Astragalus bisulcatus has been
reported to be 7–11 times greater than that in the surrounding leaf
FIGURE 2 Implications of water
absorption and metal detoxication by
trichomes. (a) Water absorption by trichomes
affects plants and potentially influences
ecology. (b) The role of metal detoxication by
trichomes in plants in phytoremediation and
foliar fertilisation. [Color figure can be viewed
at wileyonlinelibrary.com]
THE OVERLOOKED FUNCTIONS OF TRICHOMES
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tissue (Freeman et al., 2006), and the Ni in the trichomes of the Ni
hyperaccumulators Alyssum murale and Alyssum pterocarpum has
been reported to account for 15%–20% of the dry weight of their
entire leaves (Broadhurst, Chaney, Angle, Maugel, et al., 2004).
Further on, the trichomes of the As hyperaccumulator Pteris vittata
can accumulate 20% of As in weight (W. Li et al., 2005), and it was
found in a field trial experiment that growing P. vittata reduced the
soil As concentration from 41 to 25 mg kg
−1
within 3 years (Wan
et al., 2020). Similarly, metal accumulation in the trichomes is also
important in foliar fertilisation—it was found in sunflower (Helianthus
annuus) that the non‐glandular trichomes play an important role in
not only the absorption but also the subsequent translocation of the
foliar Zn fertilizer (C. Li et al., 2019,2021) (Figure 2b).
Critically, these two lesser‐studied functions of trichomes (i.e.,
the absorption of water and the detoxication of metals) are
potentially related to each other. For example, it has been shown
that foliar application of fertilizers (such as Zn) to improve plant
growth in agricultural production systems can result in the
accumulation of these elements within the trichomes (C. Li et al.,
2019,2021), and it is possible that the absorption of these soluble
nutrients and their subsequent accumulation in the trichomes occurs
because the trichomes are efficient at absorbing water. Therefore, in
this review, we focus on two of the lesser‐known functions of
trichomes: (i) water absorption and (ii) metal detoxification. In this
regard, many issues remain unclear, such as what kind of trichomes
can absorb water or play roles in metal accumulation and detoxifica-
tion? Are these functions associated with special structures of
trichomes or occur in some specific plant genera? What are the
mechanisms that underpin these two functions? We first summarize
the current knowledge of trichome water absorption and metal
detoxification, then discuss the underlying physiological and molecu-
lar mechanisms that provide these functions. Finally, the implications
of these functions are considered, and future outstanding questions
are proposed. By examining the role of trichomes in water absorption
and metal detoxification, this review contributes to a better under-
standing of trichomes, allows for clearer recognition on these two
overlooked functions and provides the possibility of better using
trichomes.
2|THEROLEOFTRICHOMESINWATER
ABSORPTION
2.1 |Trichome and FWU
The first report of water uptake through leaves is from 1767,
reported by Mariott. However, this received comparatively little
attention until 1857, when Duchartr questioned this finding and
initiated a debate among plant physiologists as to whether water
could actually be absorbed by leaves. By the 20th century,
experimental evidence had demonstrated that water can indeed be
absorbed and utilized by leaves (Duchartre, 1857; Schreel & Steppe,
2020; Stone, 1963; Yang et al., 2010). In recent years, there has been
a considerable increase in interest in FWU (Berry et al., 2019;
Dawson & Goldsmith, 2018; Fernández et al., 2021; Guzmán‐
Delgado et al., 2021; Holanda et al., 2019; Limm et al., 2009;
Schreel & Steppe, 2019; Wang et al., 2016). For example, it has been
reported that at least 233 plant species from more than 70 plant
families can absorb water directly through their leaf surface (Berry
et al., 2019; Schreel et al., 2022).
Given the importance of FWU to both the plants and the ecology
as mentioned above, the pathway of FWU has been examined in
relation to the leaf epidermal structures—the cuticle, stomata and
trichomes (Eller et al., 2013; Guzmán‐Delgado et al., 2021; Ray et al.,
2022). It was found that FWU can occur through both the cuticle and
the stomata, with the structure and chemical composition of the
cuticle affecting the water diffusion efficiency (Eller et al., 2013; Ray
et al., 2022). For the stomata, FWU likely occurs by the diffusion of
water vapour rather than as liquid flow (Guzmán‐Delgado et al.,
2021). In addition, it has been reported that water absorption can
also occur through the trichomes—it has been reported previously
that at least 11 plant species from six different families can absorb
water through their leaf trichomes (Guzmán‐Delgado et al., 2021),
with this suggesting that trichomes can potentially play a role in
FWU. Here, we consider existing studies that focused on the capacity
of trichomes to absorb water, with the mechanisms by which FWU
occurs through trichomes discussed.
2.2 |Studies examining water absorption by
trichomes
A total of 37 plant species belonging to 14 families and 12 orders
have been found to have trichomes that are involved in FWU
(Table 1). A variety of methods have been used to examine water
entering the leaf through trichomes, including the use of dye tracers
(Eller et al., 2016; Holanda et al., 2019; Losada et al., 2021; Pina et al.,
2016; Schreel et al., 2020; Vitarelli et al., 2016), radiolabeled water
tracers (Ohrui et al., 2007) and by comparing FWU in species
differing in trichome density (Z.‐L. Pan et al., 2021; Schwerbrock &
Leuschner, 2017). Of these 37 plant species, 15 belong to the
Bromeliaceae family and 6 belong to the Orchidaceae family. All
these 21 species are epiphytes, and hence their water and nutrient
uptake largely relies upon foliar absorption. Furthermore, the
trichomes involved in water absorption in the Bromeliaceae family
are similar in structure and morphology—they are all large peltate
wing‐shaped, multicellular non‐glandular trichomes (Figure 5). In
addition, for tank‐type atmospheric epiphytes, the peltate trichomes
on the leaf sheath (where water collects) have also been reported to
absorb water (Table 1). Apart from these 21 epiphytes, 9 of the
remaining 37 plant species (Opuntia microdasys,Tortula caninervis,
Capparis odoratissima, Croton erythroxyloides, Croton pygmaeus,
Croton splendidus, Combretum leprosum, Eremanthus erythropappus,
and Myrsine umbellata) from a range of other plant families that can
be categorized as either xerophytes or as plants that live in dry
habitats. In addition, trichome water absorption has also been
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TABLE 1 Trichomes involved in plant water absorption (the morphology of the trichomes listed in this table are shown in Figure 5)
Oder Family Species Trichome features Habitats References
Poales Bromeliaceae Tillandsia ionantha Peltate wing‐shaped trichome Epiphytes Ohrui et al. (2007)
Tillandsia usneoides Martin et al. (2013)
Tillandsia aeranthos
Tillandsia landbeckii
Raux et al. (2020)
Tillandsia streptophylla Peltate wing‐shaped trichome Epiphytes Benzing et al. (1976)
Tillandsia rigida Peltate wing‐shaped trichome Epiphytes Benzing et al. (1976)
Vriesea splenriet Peltate wing‐shaped trichome Tank‐type epiphytes Vanhoutte et al. (2017)
Vriesea galaxia
Neoregelia spectabilis Peltate wing‐shaped trichome on the leaf sheath Tank‐type epiphytes Benzing et al. (1976)
Billbergia pyramidalis Peltate wing‐shaped trichome on the leaf sheath Tank‐type epiphytes Benzing et al. (1976)
Aechmea bracteata Peltate wing‐shaped trichome on the leaf sheath Tank‐type epiphytes Benzing et al. (1976)
Guzmania monostachya Peltate wing‐shaped trichome on both the leaf
sheath and leaf blade
Tank‐type epiphytes Benzing et al. (1976)
Catopsis floribunda Peltate wing‐shaped trichome on both the leaf
sheath and leaf blade
Tank‐type epiphytes Benzing et al. (1976)
Vriesea glutinosa Peltate wing‐shaped trichome on both the leaf
sheath and leaf blade
Tank‐type epiphytes Benzing et al. (1976)
Brocchinia reducta Peltate wing‐shaped trichome on both the leaf
sheath and leaf blade
Tank‐type epiphytes Benzing et al. (1985)
Asparagales Orchidaceae Dendrobium bellatulum
Dendrobium cariniferum
Dendrobium draconis
Dendrobium longicornu
Dendrobium trigonopus
Dendrobium williamsonii
Hair‐like non‐glandular trichomes Epiphytic orchids Z.‐L. Pan et al. (2021)
Caryophyllales Cactaceae Opuntia microdasys Needle‐like and belt‐structured trichomes Xerophilous plant, fog collection Ju et al. (2012)
Pottiales Pottiaceae Tortula caninervis Hair‐like non‐glandular trichome Xerophilous plant, desert moss Z. Pan et al. (2016)
Brassicales Capparaceae Capparis odoratissima Peltate wing‐shaped trichomes Semiarid environments, fog collection Losada et al. (2021)
Euphorbiales Euphorbiaceae Croton erythroxyloides Peltate wing‐shaped trichomes Xeric environment, soil drought Vitarelli et al. (2016)
Croton pygmaeus Peltate wing‐shaped trichomes and stellate non‐
glandular trichomes
Croton splendidus Peltate wing‐shaped trichomes and fasciculate
trichomes
(Continues)
THE OVERLOOKED FUNCTIONS OF TRICHOMES
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reported in a halophytic plant (Avicennia marina) that grows in salty
soils with low water availability. These trichomes have been found to
assist in capturing water from fog or dew to cope with water scarcity.
The structure and morphology of these trichomes vary greatly,
including belt‐structured, peltate, fasciculate, stellate, tector and hair‐
like trichomes (Table 1).
The observation that trichomes are involved in water absorption in
the above‐mentioned plants that are epiphytes or those which are
adapted to water‐limiting environments is perhaps not unexpected.
However, it has also been reported that plants grown in temperate
regions can absorb water via foliar trichomes (Fagus sylvatica)(Schreel
et al., 2020) and Mediterranean regions (Quercus ilex) (Fernández et al.,
2014), with this assisting the plants to gain water especially during
drought and when the leaves are wet (such as when dew is formed). In
addition, trichome water absorption has also been found in ferns
growing in highly humid environments (Polystichum braunii, Athyrium
filixfemina, Polystichum aculeatum,andDryopteris filix‐mas), but it must
be noted that this conclusion was derived by comparing the
relationship between trichome density in the pinnate fronds and foliar
water absorption rather than by direct evidence (Schwerbrock &
Leuschner, 2017). Finally, of the trichomes that have been identified as
being involved in water absorption, only those of M. umbellata and A.
marina are glandular trichomes (Table 1).
2.3 |Mechanisms of water absorption through
trichomes
The 15 Bromeliaceae species identified above all have large
multicellular peltate wing‐shaped non‐glandular trichomes (Ohrui
et al., 2007; Raux et al., 2020). For this type of trichome, it has been
found that the highly hygroscopic wing helps water accumulate at the
leaf surface by capillarity during wetting events, with the water then
flowing to the central foot cells before being driven inward by an
osmotic gradient (Raux et al., 2020). Furthermore, this water uptake
pathway is unidirectional—when the wetting event is finished and the
effective water potential of the environment falls below the water
potential of the foot cells, the thick cell wall of the trichome cells then
acts as a capillary wick and prevents outward flow and evaporation
(Raux et al., 2020). Interestingly, foliar water absorption through the
peltate trichomes of C. odoratissima (Losada et al., 2021) and C.
splendidus (Vitarelli et al., 2016) occurs in a manner similar to that
described for the peltate trichomes of the Bromeliaceae species. In
this regard, it has also been reported that the peltate wings of these
trichomes are rich in compounds with a high affinity for water, such
as pectic substances (pectin is a component of the primary cell wall
and comprises a wide variety of polysaccharides rich in galacturonic
acid, which can help maintain plant water status), while the basal cells
are rich in lipophilic substances (such as cutin) (Fernández et al.,
2021). Furthermore, trichomes are sometimes connected with
vascular tissues via idioblasts (Losada et al., 2021; Z. Pan et al.,
2016; Vitarelli et al., 2016), with this facilitating the translocation of
the absorbed water and improving further water absorption.
TABLE 1 (Continued)
Oder Family Species Trichome features Habitats References
Myrtales Combretaceae Combretum leprosum Peltate wing‐shaped trichomes Semiarid environments, dew collection Holanda et al. (2019); Pina
et al. (2016)
Asterales Asteraceae Eremanthus erythropappus Tector trichomes Soil drought, fog collection Eller et al. (2016)
Ericales Primulaceae Myrsine umbellata Peltate glandular trichomes Soil drought, fog collection Eller et al. (2016)
Fagales Fagaceae Fagus sylvatica Hair‐like non‐glandular trichomes Temperate regions Schreel et al. (2020)
Quercus ilex Mostly stellate non‐glandular trichomes Mediterranean regions Fernández et al. (2014)
Lamiales Acanthaceae Avicennia marina Pilate glandular trichomes Halophyte mangrove species Nguyen, Meir, P., Sack, et al.
(2017); Meir, P., Wolfe,
et al. (2017); Schaepdryver
et al. (2022)
Polypodiales Dryopteridaceae Polystichum braunii Morphology was not examined Woodland ferns, high air humidity Schwerbrock and Leuschner (2017)
Athyriaceae Athyrium filixfemina
Dryopteridaceae Polystichum aculeatum
Dryopteris filix‐mas
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Together with the water absorption mechanism of trichomes of the
Bromeliaceae species (Raux et al., 2020), it can be concluded that
water absorption by these peltate trichomes occurs by the following
pathway: (i) the highly hydrophilic peltate wings are responsible for
holding water on the leaf surface during wetting events, (ii) the water
is driven inward by an osmotic gradient through the foot cells via the
apoplastic pathway, (iii) the lipid base of the trichomes prevents
water counterflow, and (iv) the sclereids or vascular cells connecting
the trichome base with the leaf vascular tissues provide translocation
of the absorbed water (Figure 3).
In a similar manner, the tector trichomes involved in water absorption
in E. erythropappus have also been found to have relatively high
hydrophilicity (Eller et al., 2016). In addition, a hair‐like trichome in F.
sylvatica (belonging to the Fagaceae family) growing in temperate regions
has also been reported to absorb water, likely due to the pectin‐rich
composition of the trichome and the non‐lignified cell wall which makes it
easier for water to penetrate (Schreel et al., 2020). This high water
sorption capacity of trichomes potentially results not only from their
special cuticle composition that makes them more hydrophilic, but also
because the phyllosphere microbes associated with the trichomes may
potentially produce biosurfactants and increase their water sorption
capacity (Remus‐Emsermann et al., 2011; Schlechter et al., 2019). Indeed,
the trichome surface is covered by a cuticle and its chemical composition
may differ significantly from the cuticle of the other leaf areas (Fernández
et al., 2021; C. Li et al., 2021).
Although peltate trichomes have been shown to play a role in water
absorption as discussed above, other kinds of trichomes can also be
important. For two desiccation‐tolerant xerophilous plants (O. microdasys
and T. caninervis), their trichome water absorption functions result from a
multiscale water harvesting system formed by the trichomes, with these
structures generating a strong capillary force that allows efficient water
collection and absorption from various wetting events, such as from
humid atmospheres, from fog or dew, and during precipitation (Ju et al.,
2012; Z. Pan et al., 2016). Another Fagaceae species, Q. ilex (holm oak), a
typical Mediterranean species, has stellate trichomes that also contribute
to FWU (Fernández et al., 2014). It has been suggested that these stellate
trichomes on the adaxial surface of the holm oak leaves increase the
adhesion of water to the leaf surface and that these trichomes are
connected with bundle sheath extensions in the leaf, with this facilitating
water absorption and translocation (Fernández et al., 2014).
Overall, it is apparent that the ability of trichomes to absorb water
depends upon: (i) a special water collection structure formed by the
trichomes to enable water collection during wetting events, (ii) a special
surface chemical composition (e.g., the cuticle of the trichomes possessing
high content of polysaccharides made it has a high affinity for water) that
enables wetting and adhesion of atmospheric water as a prerequisite for
water absorption, (iii) the osmotic pressure that allows water to enter the
leaf, especially to plants growing in xeric environments, (iv) the base of the
trichomes connecting with leaf vascular tissues favours the translocation
of the absorbed water, and (v) the lipid trichome base prevents outflow of
water (Figure 3).
Regardless, the relationship between trichomes and water is not
straightforward, and trichomes play contrasting roles in FWU (Berry
et al., 2019; Brewer et al., 1991). For example, it was found in some
studies that trichomes could promote water condensation on the leaf
surface and increase FWU (Konrad et al., 2015), whereas other
studies found that trichomes are water‐repellent which is often
recognized as one of the trichomes' protection functions (Brewer &
Smith, 1997; Konrad et al., 2021). This is because the interactions of
trichomes with water are influenced by a variety of factors, including
not only the special chemical and structural properties described
above, but also other factors such as trichome density, leaf
properties, water form (e.g., minute or macro droplets), the
pattern in which the water interacts with the trichomes (e.g., contact
angle), environmental conditions and physiological situations
(Roth‐Nebelsick et al., 2022).
3|THEROLEOFTRICHOMESINPLANT
METAL DETOXIFICATION
The detoxification of metals by plants is a critical process for growth
in environments containing elevated concentrations of metals, but
much remains unknown regarding the mechanisms by which plants
FIGURE 3 Water absorption by the
peltate wing‐shaped trichome based upon the
Bromeliaceae species (Raux et al., 2020),
Capparis odoratissima (Losada et al., 2021) and
Corton splendidus (Vitarelli et al., 2016). The
special structure and chemical composition
allow the trichomes to absorb water
efficiently. (a) Top view showing a peltate
wing‐shaped trichome which consists of a
wing and central foot cells. (b) Leaf cross
section showing the peltate trichome. [Color
figure can be viewed at
wileyonlinelibrary.com]
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are able to accumulate and detoxify these metals within their tissues.
This accumulation and detoxification of metals are important in a
range of conditions, including for hyperaccumulators in ultramafic
soils, which contain high concentrations of metals such as Ni, acid
soils, which contain high concentrations of bioavailable metals such
as Al and Mn, and contaminated soils which contain high concentra-
tions of metals due to human activities. In such instances,
phytoremediation has been proposed as an approach for decreasing
the concentration of contaminants in soil due to their extraction,
accumulation and removal in the plant shoots (Beans, 2017;
Chaney & Baklanov, 2017; Oh et al., 2014). Here, we summarize
the plant species that have been reported to accumulate metals in
their trichomes, with the characteristics of the trichomes and the
mechanisms of metal accumulation and detoxification by the
trichomes also discussed.
3.1 |Studies examining metal accumulation in
trichomes
We have identified 37 studies examining metal accumulation in
trichomes (Table 2). These studies have been conducted for a wide
range of purposes, including for examining plant metal tolerance and
detoxication mechanisms (Choi et al., 2001;Čiamporová et al., 2021;
Iwasaki & Matsumura, 1999), observing metal distribution in plant
leaves (Ager et al., 2003; Lei et al., 2008) and for examining the
specific roles of trichomes in plant metal hyperaccumulation (W. Li
et al., 2005; Mcnear & Kupper, 2014; Ricachenevsky et al., 2021). In
addition, a variety of analytical approaches have been used to
investigate the accumulation of metals in the trichomes, including
scanning electron microscopy coupled with energy dispersive
spectroscopy (SEM‐EDS), synchrotron‐based X‐ray fluorescence
microspectroscopy (XFM), nuclear microprobe analysis and confocal
microscopy with specific fluorescence dyes (Ager et al., 2003;
Broadhurst, Chaney, Angle, Erbe, et al., 2004; Kozhevnikova
et al., 2014).
A total of 33 plant species from 13 families have been reported
to accumulate high concentrations of metals in their trichomes
(Table 2), with 61% of these 33 plant species belonging to the family
Brassicaceae. This is likely because, at least in part, the Brassicaceae
family is the second largest plant family of hyperaccumulators (the
first being Phyllanthaceae), especially for Ni hyperaccumulators
(Global Hyperaccumulator Database, 2022; Manara et al., 2020). As
a result, it is likely that more attention has been given to the
distribution of metal elements in this plant family, and correspond-
ingly, more species of this family have been observed to accumulate
metals in their trichomes. Apart from the Brassicaceae family, the
other plant families in which trichomes have been found to
accumulate metals are Acanthaceae, Asteraceae, Cannabaceae,
Cucurbitaceae, Fabaceae, Lythraceae, Moraceae, Polygonaceae,
Polypodiaceae, Pteridiaceae, Solanaceae and Violaceae, with two
plant species having been identified in Asteraceae whereas only one
plant species has been identified for the remaining families (Table 2).
For the trichomes of these 33 plant species, over 90% are non‐
glandular trichomes and more than 50% accumulate metals in the
base of the trichomes. In addition, it has been observed in some
species that the metals accumulate in the apoplast or cell wall of the
trichome basal cells. For example, in sunflower, Zn (C. Li et al., 2019)
and Mn (Blamey et al., 2018) are localized in the apoplast of the basal
cell of the non‐glandular trichomes, and in A. thaliana Cd is chelated
in the cell wall of the non‐glandular trichome basal cells (Gao et al.,
2021). A. marina,Rumex acetosella and Nicotiana tabacum are the only
three species where glandular trichomes have been found to
accumulate metals. Interestingly, the glandular trichomes of A. marina
and N. tabacum have also been found to excrete metals from
glandular trichomes, with enhanced Ca concentrations promoting this
excretion in N. tabacum (Choi et al., 2001;Čiamporová et al., 2021;
Macfarlane & Burchett, 2000). Across the 33 plant species, the
morphology and structure of the trichomes involved in metal
accumulation vary greatly, including trichomes that are ‘Y’shaped,
stellate, dendritic, simple branch shaped and ‘T’shaped (Table 2and
Figure 5). As discussed previously for water absorption, for plants
within the same genus, we find similarities in both trichome
morphology and their metal accumulation properties. For example,
within the Brassicaceae family, the Arabidopsis genus accumulates Cd
and Zn at the base of dendritic non‐glandular trichomes (Fukuda
et al., 2020; Guo et al., 2022; Isaure et al., 2015; F. Zhao et al., 2000),
while the Alyssum genus accumulates Ni and Mn in the base of the
stellate non‐glandular trichomes (Broadhurst, Chaney, Angle, Erbe,
et al., 2004; Ghasemi et al., 2009; Tappero et al., 2007).
The metals that accumulate in trichomes include Zn, Cu, Mn, Cd,
Ni, Co, Tl, Se, Sr, As and Pb, with Zn, Mn, Ni and Cd being the most
frequently identified metals. Regarding the sources of the metals,
most studies have examined the accumulation of metals in trichomes
following uptake by the roots, but for sunflower, the accumulation of
metals in the trichomes have been examined for both root uptake and
for foliar absorption (i.e., foliar fertilisation). Interestingly, the
accumulation of metals in trichomes has been reported not only in
hyperaccumulators and metal tolerant plants, but also in non‐
hyperaccumulator and non‐metal tolerant species, with 16 of the
33 species being hyperaccumulators and four being metal tolerant
species (Table 2).
3.2 |Mechanisms of metal accumulation
and detoxication in trichomes
It is of considerable interest to understand the mechanisms whereby
metals accumulate in trichomes. Firstly, it has been found that the
basal cells of the trichomes in which metals accumulate are generally
connected with the surrounding mesophyll or epidermal cells by
plasmodesmata, and that the trichome basal cells are generally
further connected with vascular tissues such as bundle sheath
extensions—these enable the translocation of metals in or out of the
trichomes (Čiamporová et al., 2021; C. Li et al., 2021). Secondly, once
the metals have been translocated into the trichome, they must then
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TABLE 2 Trichomes involving in plant metal accumulation and detoxication (the morphology of the trichomes listed in this table are shown in Figure 5)
Family Species
Heavy
metals
Metal distribution
in the trichomes Metal sources
Whether hyperaccumulator
or metal tolerant plants References
Acanthaceae Avicennia marina Zn, Cu Zn and Cu were excreted out
from the pilate glandular
trichomes
Macfarlane and Burchett (1999,2000)
Asteraceae Helianthus annuus Mn, Zn Uniseriate non‐glandular
trichome base
Root uptake or
foliar
absorption
Mn tolerant plant Blamey et al. (1986,2018)
C. Li et al. (2021)
Picris divaricata Cd, Zn In the ‘Y’shaped non‐
glandular trichome
Root uptake Zn and Cd hyperaccumulator Hu et al. (2012)
Bauchan et al. (2014)
Brassicaceae Alyssum murale/
Odontarrhena
muralis
Ni, Mn, Co Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator Broadhurst, Chaney, Angle, Maugel, et al. (2004); Mcnear and
Kupper (2014); McNear DH et al. (2005); Tappero et al.
(2007); Do Nascimento et al. (2020)
Alyssum fallcinium Ni, Mn Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator Broadhurst, Chaney, Angle, Maugel, et al. (2004)
Alyssum pterocarpum Ni, Mn Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator Broadhurst, Chaney, Angle, Maugel, et al. (2004)
Alyssum inflatum Ni Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator Ghasemi et al. (2009)
Alyssum corsicum Ni, Mn Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator Babaoğlu Aydaşet al. (2013); Broadhurst, Chaney, Angle,
Maugel, et al. (2004); Leigh Broadhurst et al. (2009)
Alyssum serpyllifolium Ni Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator De La Fuente et al. (2007)
Alyssum lesbiacum Ni Peripheral regions of the
stellate non‐glandular
trichomes
Root uptake Ni hyperaccumulator Baklanov (2011); Krämer et al. (1997); Smart et al. (2007)
Alyssum bertolonii Ni Base of the stellate non‐
glandular trichomes
Root uptake Ni hyperaccumulator Marmiroli et al. (2004)
Arabidopsis thaliana Cd, Zn Base of the dendritic non‐
glandular trichome
Root uptake Ager et al. (2003); Gao et al. (2021); Guo et al. (2022);
Ricachenevsky et al. (2021)
Arabidopsis halleri Cd, Zn Base of the dendritic non‐
glandular trichome
Root uptake Zn and Cd hyperaccumulator Fukuda et al. (2020); Sarret et al. (2009); F. Zhao et al. (2000)
Arabidopsis lyrata Cd, Zn Base of the dendritic non‐
glandular trichome
Root uptake Isaure et al. (2015); Sarret et al. (2009)
Biscutella laevigata Tl Middle of the uniseriate
non‐glandular trichomes
Root uptake Tl hyperaccumulator Wierzbicka et al. (2016)
(Continues)
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TABLE 2 (Continued)
Family Species
Heavy
metals
Metal distribution
in the trichomes Metal sources
Whether hyperaccumulator
or metal tolerant plants References
Biscutella auriculata Cd Non‐glandular trichome base
(morphology was not
examined)
Root uptake Cd tolerant plant Peco et al. (2020)
Bornmuellera
emarginata
Mn Stalkless T‐shaped non‐
glandular trichome
Root uptake Hopewell et al. (2021)
Bornmuellera tymphaea Mn Stalkless T‐shaped non‐
glandular trichome
Root uptake Ni hyperaccumulator Hopewell et al. (2021)
Brassica juncea Cd Uniseriate non‐glandular
trichomes
Root uptake Salt et al. (1995)
Capsella bursa‐pastoris Ni, Zn Base of the stellate non‐
glandular trichomes
Root uptake Kozhevnikova et al. (2014)
Chinese cabbage Cd Base of the hair‐like non‐
glandular trichomes
Root uptake Guo et al. (2022)
Lepidium ruderale Zn Base of the unicellular non‐
glandular trichomes
Root uptake Kozhevnikova et al. (2014)
Odontarrhena
chalcidica
Ni Stellate non‐glandular
trichomes
Root uptake Ni‐hyperaccumulator Hopewell et al. (2021)
Cannabaceae Cannabis sativa Cu Hair‐like non‐glandular
trichome
Root uptake Arru et al. (2004)
Cucurbitaceae Cucurbita moschata Mn Uniseriate non‐glandular
trichome base
Root uptake Iwasaki and Matsumura (1999)
Fabaceae Astragalus bisulcatus Se Hair‐like non‐glandular
trichomes
Root uptake Se hyperaccumulator Freeman et al. (2006)
Lythraceae Trapa natans Mn Rod‐shaped pluricellular non‐
glandular trichome base
Root uptake Mn tolerant hydrophyte Baldisserotto et al. (2007)
Moraceae Morus alba Zn, Sr Uniseriate non‐glandular
trichome
Root uptake Katayama et al. (2013); Kesavacharyulu et al. (2004)
Polygonaceae Rumex acetosella Zn, Cu Capitate glandular trichomes Root uptake Čiamporová et al. (2021)
Polypodiaceae Microsorum pteropus Cd Unicellular non‐glandular
trichomes
Root uptake Cd tolerant plant Lan et al. (2019)
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be detoxified. In this regard, organic ligands (to chelate with the metal
ions) and metal transporters (such as for the transport of the metals
into the vacuoles) play important roles. For example, using in situ
hybridisation, Foley and Singh (1994) demonstrated a pronounced
expression of metallothionein in the leaf trichomes of Vicia faba.
Later, transcriptome analysis in N. tabacum found that its trichomes
are the primary sites for the expression of genes encoding stress‐
related proteins such as antipathogenic T‐phylloplanin‐like proteins
and glutathione peroxidase. It was also observed that the concentra-
tion of glutathione (related to metal complexation and sequestration)
was higher in the trichome cells than in other types of leaf cells
(Harada et al., 2010). In a similar manner, in sunflower, it was found
that its non‐glandular trichomes have nine groups of metal‐chelating
ligands and nine groups of heavy metal transporters that are involved
in the Zn accumulation in the trichomes (C. Li et al., 2021). In addition,
the metal found in the apoplast or in the cell wall of the trichomes
could be in the secondary cell wall as it can provide chelating sites for
the metal ions (Gao et al., 2021). Together, these special physiological
structures and molecular properties enabled metals to accumulate
within trichomes (Figure 4). Regardless, these mechanisms have only
been explored in a few plant species. A broader understanding of
trichome's physiology, molecular characteristics and cellular metabo-
lism are necessary.
4|FUTURE RESEARCH PERSPECTIVES
We have identified plant species (and their trichomes) that are
involved in water absorption and metal accumulation and detoxifica-
tion (Tables 1and 2), but these lists will certainly increase over time.
TABLE 2 (Continued)
Family Species
Heavy
metals
Metal distribution
in the trichomes Metal sources
Whether hyperaccumulator
or metal tolerant plants References
Pteridiaceae Pteris vittata As Base and stalk of the pilate
trichome
Root uptake As hyperaccumulator W. Li et al. (2005)
Solanaceae Nicotiana tabacum Cd, Zn Cd or Zn can be excreted out
of the pilate glandular
trichomes
Root uptake Choi et al. (2001); Harada and Choi (2008);
Sarret et al. (2006)
Violaceae Viola principis H. de
Boiss.
Pb, As Prickle like non‐glandular
trichome
Root uptake Pb, As and Cd hyperaccumulator Lei et al. (2008)
FIGURE 4 Metal detoxification by the uniseriate non‐glandular
trichome of Helianthus annuus (C. Li et al., 2019,2021). The metal
detoxication function of this trichome results not only from the good
connection of their basal cells to their surrounding cells and the
underlying vascular tissues, but also from the presence of metal‐
chelating ligands and transporters within the trichomes themselves.
[Color figure can be viewed at wileyonlinelibrary.com]
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Comparatively few studies have focused on these two functions of
trichomes and our current understanding of these two functions of
trichomes is still fragmented and further information still needs to be
acquired.
4.1 |Water absorption by trichomes
Of the 37 plant species found to absorb water through trichomes,
57% are epiphytes and 24% are plants that grow in water‐stressed
environments (Table 1). This suggests that the ability to absorb water
through trichomes is likely associated with exposure to abiotic stress.
Indeed, not all plant trichomes can absorb water. For example, the
egg‐beater‐like trichomes of the floating fern (Salvinia molesta) are
highly water‐repellent and can keep its leaves largely free from water
even when the leaf is immersed in water or during rainfall events
(Konrad et al., 2021; Roth‐Nebelsick et al., 2022). This again indicates
that the structure and function of trichomes can be highly variable
and likely evolved to assist plants to cope with a range of biotic and
abiotic stress factors. However, it is still unclear why plants growing
in high‐humidity environments also have trichomes that can absorb
water. In this regard, few studies have examined the water
absorption capacity of trichomes, and the mechanisms by which
trichomes absorb water have been investigated in only a limited
number of species. Hence, further studies are needed in plants
growing in different environmental scenarios and from different plant
taxa to get a better picture of their diversity.
Regarding the mechanisms by which water is absorbed by
trichomes, current research largely investigates at the organ‐and
chemical‐level (i.e., the physical structure of the trichomes as well as
the related structure to the leaves and the chemical composition of
the trichomes), whereas no studies have examined water absorption
at the protein‐and gene‐level. For example, aquaporins are channel
proteins that can facilitate the transport of water across the
membranes of plant cells (Maurel et al., 2015), yet it is unclear
whether the cell membrane of the water absorption trichomes has
any aquaporins. In addition, it has been reported that some genes
participate not only in trichome development, but also in stress
responses (Zhang, Liu, Wang, Yuan, 2021), yet it is unclear which
genes contribute to trichome water absorption. These research
aspects could be included in future studies to help elucidate the
mechanisms by which water is absorbed by trichomes, thus helping
improve our understanding of trichome water absorption and its
contribution to plant water economy.
It has previously been demonstrated that the water absorbed by
trichomes is translocated to other tissues within the plant where it is
then utilized (Ha et al., 2021; Waseem et al., 2021). Hence, it is clear
that the water that is acquired through the trichomes can be of
general benefit to plants. For individual plants, the absorption of
water through trichomes not only can improve the leaf water status
FIGURE 5 The morphology of the trichomes listed in Tables 1and 2
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and drought resistance, but it also contributes broadly to plant
survival when growing in environments where water is scarce
(Figure 2a). Furthermore, at the ecosystem level, this absorption of
water through the trichomes is potentially of substantial importance
to both forest and agricultural ecosystems as drought events are
likely to continue to increase in severity in the future (Schreel &
Steppe, 2020) (Figure 2a). For instance, species with this special
water acquisition function could potentially be selected or bred for
use in low‐rainfall regions. In this regard, current studies mostly focus
on forest species, with the absorption of water by trichomes in crop
species requiring evaluation. For example, it may be possible to breed
crop cultivars that have a high density of trichomes that are capable
of absorbing atmospheric water to improve their drought resistance.
4.2 |Metal detoxication by trichomes
Of the 33 plant species for which metal detoxification has been
found to be important in trichomes, 61% are either hyperaccumu-
lators or metal tolerant species, suggesting that sequestration of
metals in the trichomes is an important plant metal detoxication
mechanism (Table 2). It has been estimated that perhaps one‐third of
all plant species are able to accumulate metals in their trichomes
(Broadhurst, Chaney, Angle, Erbe, et al., 2004; Hopewell et al., 2021;
Kozhevnikova et al., 2014). Furthermore, the accumulation of metals
in trichomes is also a mechanism used by leaves to adjust plant metal
homoeostasis. For example, it was found in sunflower that the foliar‐
absorbed Zn was stored in the non‐glandular trichome base when the
leaf Zn concentration was high, while it was translocated out of the
non‐glandular trichomes and moved to other parts of the leaf tissues
when the leaf Zn concentration was decreased (C. Li et al., 2021). In a
similar manner, it was observed in A. thaliana that increasing the leaf
metal concentration further increased the metal concentration in the
trichomes (Ricachenevsky et al., 2021). However, due to the limited
number of studies, our knowledge of the interactions between
trichomes and metals is still in its infancy. Further studies are required
to identify additional plant species having different types of
trichomes and to provide a comprehensive understanding of the
mechanisms involved in metal detoxification by trichome.
In addition, it has been found that trichome density can increase
greatly when plants are under metal stress. For example, Azmat et al.
(2009) found that the trichome density of Phaseolus mungo and Lens
culinaris increased after exposure to high concentrations of Pb, Choi
et al. (2001) found that the trichome density of tobacco increased
upon Cd stress and Čiamporová et al. (2021) found that the density
of glandular trichomes of R. acetosella increased under Zn and Cu
stress. In this regard, it is likely that trichomes are part of plant's
stress‐response system, with an increase in trichome density under
various stresses, including metal stress (C. Li et al., 2017). Yet
whether increasing in trichome density is a strategy that used by
plants to cope with metal stress is still unclear. It is known that the
various stress‐coping functions of trichomes are interlinked. For
example, Guo et al. (2022) found that mechanical stimulation of
trichomes (an imitation of herbivores) of A. thaliana upregulated
genes involved in Cd
2+
ion detoxification and increased the Cd
concentration in the trichomes. In this regard, some authors have
proposed that the metals that accumulate in the trichomes are not
only for metal detoxification but also that plants could utilize these
metals as a herbivores defense mechanism (Boyd, 2007; Gao et al.,
2021; Stolpe et al., 2017). Continued research is needed to decipher
the interplay between metal detoxication by trichomes and the other
trichome functions, such as protecting against herbivores.
It has been proposed that glandular trichomes could be used as
breeding targets for improving crop resistance to herbivores (Glas et al.,
2012). Taking this approach into account, for those species (especially
hyperaccumulators) whose trichomes can accumulate metals, breeding a
new genotype that has a higher density of this type of trichome would
potentially improve the efficiency of phytoremediation. Indeed, Zhang,
Lu, Wang, Yan, & Cui (2021) found that knockout of NtCycB2
(a negative regulator for glandular trichome initiation) in N. tabacum
resulted in a higher density and larger heads of glandular trichomes and
enhanced plant Cd‐stress tolerance due to the excretion of calcium
oxalate crystals by this glandular trichomes. Therefore, a better
understanding of the morphogenesis of trichomes and the underlying
mechanisms of metal detoxication is essential for the optimal utilization
of these plants in phytoremediation. In this regard, there is a substantial
need for deciphering the development of the metal‐accumulating
trichomes. In addition, metal‐chelating ligands and transporters are two
important factors that affect metal accumulation in trichomes. To find
the key genes which regulate the biosynthesis of metal‐chelating ligands
and the expression of the related metal transporters is pivotal for using
genetic engineering approaches to improve the efficiency of phytoex-
traction (Kumar et al., 2022). For example, it was found in A. thaliana
that overexpressing the cytosolic O‐acetylserine(thiol)lyase gene
(Atcys‐3A) (i.e., enhancing cysteine biosynthesis) significantly improved
Cd accumulation in the leaf trichomes (Ager et al., 2003;Domínguez‐
Solís et al., 2004). However, information regarding specific genes of
metal‐chelating ligands and metal transporters remains largely unknown.
Future studies could use the newly developed EPIDERMALMORPH
method to examine the development of trichomes (Brown & Jordan,
2022)andthesingle‐cell spatial transcriptome technique to decipher
the key genes involved in trichome metal accumulation and detoxication
(Xia et al., 2022).
Finally, the non‐glandular trichomes of sunflower have been
found to accumulate both foliar and root absorbed Zn and Mn
(Blamey et al., 2015,2018; C. Li et al., 2021). This suggests that
trichomes can accumulate metals either taken up by the roots or by
the foliage either from the atmospheric or foliar application.
However, the majority of the existing studies have solely investigated
the distribution of metals in trichomes following uptake by roots
(either in soil or hydroponic system). Future investigations should
therefore include other plant species and further explore whether
their trichomes can accumulate metals absorbed by the foliage. If so,
plants having this ability could also be used, for example, for the
absorption of atmospheric metal pollutants in an environmental
context or for improving the efficacy of foliar fertilizers in agriculture.
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4.3 |Interconnection of water absorption
and metal detoxification by trichomes
Although much remains unclear regarding these two functions, we
note that >90% of the trichomes having these two functions are non‐
glandular (Tables 1and 2). In addition, unsurprisingly, both of these
functions appear to largely result from the interaction of the plant with
its surrounding environment—over half of the plants that have water‐
absorbing trichomes are epiphytes, while over half of the plants with
trichomes involved in metal detoxication are hyperaccumulators or
metal tolerant plants (Tables 1and 2). Nevertheless, the range of plant
species found to have these two functions is highly variable. Indeed, A.
marina is the only plant species that has glandular trichomes involved
in both plant water absorption and metal detoxication (Tables 1and 2).
However, this could be due to the fact that most of the previous
studies focused on either water absorption via the trichomes or metal
detoxication by the trichomes, rather than examining both functions
simultaneously. In fact, these two functions could co‐exist, as they
both involve translocation processes—from the trichomes to the inner
leaf tissues for water absorption and vice versa for metal detoxication.
Further studies are required to determine the relationship between
these two important functions of trichomes.
BOX 1 Current knowledge
Water absorption by trichomes
•A total of 37 plant species from 14 families have been
found to have trichomes that can absorb water, with
57% of these 37 species being epiphytes and 24% being
either xerophytes or growing in a dry habitat.
•For trichomes involved in water absorption, although
95% are non‐glandular, their structure and morphology
vary greatly, with similarities observed for species within
the same family.
•The ability of trichomes to absorb water is determined
by their structure (e.g., a water collection structure while
having the base of the trichome connected to the leaf
vascular tissues), surface chemical composition (e.g., the
surface of water absorbing structures being more
hydrophilic), and osmotic pressure.
Metal detoxication by trichomes
•A total of 33 plant species from 13 families have been
reported to have trichomes that can accumulate metals
in their trichomes, with 61% of these 33 species
belonging to the family Brassicaceae and 48% being
hyperaccumulators. The most frequently identified
metals in the trichomes are Zn, Mn, Ni and Cd.
•For the trichomes of the 33 plant species that are
accumulating metals: >90% are non‐glandular trichomes,
and >50% have metals that accumulate in the base of
the trichomes.
•The ability of trichomes to accumulate and detoxify
metals is related to the special structure (i.e., the
trichome basal cells are well connected with the leaf
vascular tissues) and to the presence of metal‐binding
ligands and transporters within the trichomes.
BOX 2 Outstanding research questions
Water absorption by trichomes
•Water absorption by trichomes appears to be related to
the nutrient and water acquisition regime of the plant
(e.g., 57% of the species are epiphytes) or to abiotic
stress experienced by the plant (e.g., drought). However,
water absorption by trichomes has only been examined
in a limited number of plant species. To provide a better
understanding on the relationship between the ability of
trichomes to absorb water and the growth environment
of the plant, additional research is required to evaluate
further plant species from different taxa under a variety
of environmental conditions.
•A better understanding on the mechanisms controlling
the absorption of water by trichomes will enable better
use of trichomes having this function (e.g., to improve
plant drought resistance and benefit the broader
ecosystem during drought) and inspire novel biomimetic
materials or devices to collect atmospheric water. Yet,
most studies examining the mechanisms by which
trichomes absorb water have focused primarily on the
physical structure and the surface chemical constitution
of the trichomes. Systematic research is required to
explore the mechanisms by which trichomes absorb
water, especially giving consideration to the protein‐and
gene‐level.
Metal detoxication by trichomes
•Our current understanding regarding the role of
trichomes in plant metal accumulation and detoxication
remains in its infancy—it is necessary to examine a
broader range of trichomes in various plant species.
•Studies are required to determine whether trichomes
that accumulate metals via root uptake can also
accumulate metals following foliar absorption. If so, this
could be used to remove atmospheric metal pollutants
and improve the absorption of foliar fertilizers.
•Key genes related to the metal detoxicating ligands and
key metal transporters need to be identified, with
genetic engineering approaches potentially used to
improve the efficiency of phytoremediation.
682
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LI ET AL.
13653040, 2023, 3, Downloaded from https://onlinelibrary.wiley.com/doi/10.1111/pce.14530 by CochraneChina, Wiley Online Library on [02/02/2023]. See the Terms and Conditions (https://onlinelibrary.wiley.com/terms-and-conditions) on Wiley Online Library for rules of use; OA articles are governed by the applicable Creative Commons License
5|CONCLUSIONS
We show that the trichomes of 37 plant species from 14 families are
involved in water absorption, with 21 of these species belonging to
atmospheric epiphytes. These plants are found to various environments,
including water‐stressed and saline areas, but also in temperate,
Mediterranean and highly humid regions. Our current understanding of
the role of trichomes in water absorption is primarily based upon
observations of the physical structure and chemical composition of
trichomes. In regard to metal detoxification by trichomes, we show that a
total of 33 plant species from 13 families have been reported to
sequester metals in their trichomes, with 90% of these trichomes being
non‐glandular and over 50% accumulating metals in their trichome base.
The elements most frequently reported to accumulate in trichomes are
Zn, Mn, Ni and Cd. Of these 33 plant species, 16 are hyperaccumulators
and four are metal‐tolerant species. The ability to sequester and detoxify
metals in trichomes is attributed to not only the special structure of the
trichomes but also the elevated levels of metal ligands and transporters
within the trichomes (Box 1). Furthermore, trichomes seem also to play a
role in maintaining the leaf metal homoeostasis. However, our current
understanding on these two trichome functions remains limited. Studies
should focus on identifying more plant species and types of trichomes
that contribute to water absorption and metal detoxification, focusing on
examining the properties of trichomes at the chemical, genetic and
protein level to better understand the mechanisms associated with these
two trichome functions (Box 2).
ACKNOWLEDGEMENTS
This work was supported by National Natural Science Foundation of
China (NSFC, 32101838), and Science Foundation for Youths of
Shaanxi Province (2021JQ‐097). Support was also provided to Cui Li
through the Fundamental Research Funds for the Central Universities
(D5000210898).
CONFLICT OF INTEREST
The authors declare no conflict of interest.
DATA AVAILABILITY STATEMENT
Data sharing is not applicable to this article as no new data were
created or analysed in this study.
ORCID
Cui Li https://orcid.org/0000-0001-9885-3674
Arshad Ali http://orcid.org/0000-0001-9966-2917
Jiyan Qi http://orcid.org/0000-0003-3541-5751
Peter M. Kopittke http://orcid.org/0000-0003-4948-1880
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How to cite this article: Li, C., Mo, Y., Wang, N., Xing, L.,
Qu,Y.,Chen,Y.etal.(2023)The overlooked functions of
trichomes: water absorption and metal detoxication. Plant, Cell &
Environment,46,669–687. https://doi.org/10.1111/pce.14530
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