Isolation and characterization of the hydrophilic BNI compound, 6-methoxy-2(3H)-benzoxazolone (MBOA), from maize roots
Plant Soil
https://doi.org/10.1007/s11104-023-06021-7
RESEARCH ARTICLE
Isolation and characterization of the hydrophilic BNI
compound, 6‑methoxy‑2(3H)‑benzoxazolone (MBOA),
from maize roots
Junnosuke Otaka ·
Guntur Venkata Subbarao · Jiang MingLi ·
Hiroshi Ono · Tadashi Yoshihashi
Received: 16 January 2023 / Accepted: 5 April 2023
© The Author(s) 2023
Abstract
Background and aims Biological nitrification inhibition (BNI) is a chemical ecological phenomenon
whereby plants specifically suppress nitrification by
releasing inhibiting compounds from roots, an effective strategy for improving nitrogen uptake by limiting nitrogen losses from agricultural fields. During
this study, we have aimed at characterizing hydrophilic BNI activity released from maize roots to
Responsible Editor: Devrim Coskun.
Supplementary Information The online version
contains supplementary material available at https://doi.
org/10.1007/s11104-023-06021-7.
J. Otaka (*) · T. Yoshihashi (*)
Biological Resources and Post‑harvest Division, Japan
International Research Center for Agricultural Sciences
(JIRCAS), 1‑1 Ohwashi, City of Tsukuba, Ibaraki, Japan
e-mail:
T. Yoshihashi
e-mail:
G. V. Subbarao · J. MingLi
Crop, Livestock and Environment Division, Japan
International Research Center for Agricultural Sciences
(JIRCAS), 1‑1 Ohwashi, City of Tsukuba, Ibaraki, Japan
H. Ono
National Agriculture and Food Research Organization
(NARO), 2‑1‑12 Kannondai, City of Tsukuba, Ibaraki,
Japan
understand the chemical basis for BNI function in
maize.
Methods Maize plants were grown hydroponically
and root exudates were collected using water-based
solutions and hydrophilic BNI activity was extracted.
We isolated the target BNI compounds by a combination of chromatographic techniques and bioassays
using a recombinant luminescent ammonia-oxidizing
bacterium Nitrosomonas europaea (pHLUX20).
Results We identified 6-methoxy-2(3H)-benzoxazolone (MBOA) as the responsible BNI compound
with a median effective dose (ED50) = 0.76 μM.
MBOA inhibited the conversion of N
H3 to NH2OH as
−
well as N
H2OH to N
O2 in N. europaea, suggesting
that MBOA blocks both ammonia monooxygenase
and hydroxylamine oxidoreductase enzymatic pathways. Treatment with MBOA significantly suppressed
O3− production during soil incubation,
NO2− and N
but this activity was reduced subsequently due to
biodegradation of MBOA by soil microbes. A quantification experiment revealed that MBOA accounted
for nearly 50% of the total BNI activity in hydrophilic
and hydrophobic exudates from maize roots. A soil
incubation test showed that two previously identified benzoxazinoids, HDMBOA and HDMBOA-βglucoside, can be eventually transformed into MBOA.
Conclusion We elucidated MBOA as the key component of BNI in maize. Collectively, the present
findings will serve as the groundwork for construction of an advanced environment-friendly agricultural
system.
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Plant Soil
Keywords Biological nitrification inhibition · BNI ·
Maize · MBOA · Nitrification inhibitors · Nitrogen
pollution
Introduction
In agriculture, large amounts of nitrogen fertilizers are used for crop production to feed the growing
world population. Nearly 50% of the nitrogen fertilizer
applied to Poaceae crops (e.g., maize, wheat, and rice)
is lost largely because of two soil microbial transformations, nitrification and denitrification, resulting in loss
of soil-nitrogen and low nitrogen use efficiency (NUE)
(Coskun et al. 2017; Subbarao et al. 2013b; Thakur and
Medhi 2019). Nitrification, a stepwise oxidation process from NH3 to nitrate ( NO3−) by soil microbes, plays
an important role in the nitrogen cycle. However, excessive production of N
O3− and its high mobility leads to
groundwater contamination and generation of harmful
greenhouse gas such as N
2O and NO (Kuypers et al.
2018; Rivett et al. 2008; Scheer et al. 2020; Stayner
et al. 2017; Tian et al. 2020). Thus, overapplication of
nitrogen fertilizer (as N
H3) together with generation of
excess soil-NO3− provoke serious economic and environmental damage (Subbarao and Searchinger 2021).
Therefore, a strategy is needed for suppression of nitrification to increase NUE to correct the imbalances in
nitrogen cycle. Biological nitrification inhibition (BNI)
provides an innovative way to reduce nitrogen loss from
agricultural system (Ghatak et al. 2022; Subbarao and
Searchinger 2021). BNI is a chemical ecological phenomenon by which specific natural products (secondary metabolites) secreted from the plant root system,
including terpenoids, alkaloids, fatty acids, and phenylpropanoids, that inhibit nitrification and growth of
nitrifiers (Subbarao et al. 2009; Subbarao et al. 2013b;
Wendeborn 2020). The BNI-possessing crops can
retain more NH4 in the rhizosphere through circumvention of N
O3− production. Therefore, utilization of BNI
has several major advantages. (a) It is eco-friendly: the
environmental pollution risk is reduced through using
the activity of phytochemicals released from crop root
systems. (b) The effect is sustainable: plant crops can
continuously biosynthesize and secrete BNI compounds from roots into rhizosphere to keep nitrifier
activity under check. (c) Costs are reduced: application
of additional agrochemicals is not needed. To date, BNI
has been observed in certain plants, including main
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staple food crops, namely maize, wheat, rice, and sorghum (Otaka et al. 2022; Subbarao et al. 2021; Subbarao et al. 2013a; Sun et al. 2016; Zakir et al. 2008).
Understanding BNI function in maize is important due
to: (a) Among staple crops, maize is the most productive crop providing food and feed, (b) It consumes a
major portion of nitrogen fertilizer produced globally,
and (c) Maize production systems contribute to nitrogen pollution in a major way globally.
To develop a BNI strengthened crop with a higher
yield of BNI compounds, understanding the chemical identity of BNI compounds released from roots is
essential. For isolation of BNI compounds, a crucial
property is whether the root exudates and compounds
are water-insoluble (hydrophobic) or water-soluble
(hydrophilic) (Subbarao et al. 2013a). Water-insoluble hydrophobic compounds with lower mobility are
predominant in the rhizosphere, whereas hydrophilic
compounds in water can move more farther from
the roots and have wide-reaching influence. Chemical identities of both hydrophobic and hydrophilic
BNI compounds in plant crops will lead to a deeper
understanding of BNI function in the soil. We have
recently reported two major hydrophobic BNI-contributing compounds from the root surface in maize,
namely 2,7-dimethoxy-1,4-naphthoquinone (zeanone;
ED50 = 2 μM) and 2-hydroxy-4,7-dimethoxy-2H-1,4benzoxazin-3(4H)-one (HDMBOA;
ED50 = 13 μM),
together with two analogs of HDMBOA from inside
the roots, namely 7-methoxy-2H-1,4-benzoxazin3(4H)-one (HMBOA; ED50 = 91 μM) and HDMBOAβ-glucoside (ED50 = 94 μM) (Fig. S1) (Otaka et al.
2022). This study is (...truncated)