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Appraisal for organic amendments and plant growth-promoting rhizobacteria to enhance crop productivity under drought stress: A review

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Abstract

Plants are sessile organisms, frequently face unfavourable growth conditions such as drought, salinity, chilling, freezing and high-temperature stresses, inhibiting growth and development, and ultimately reducing crop productivity. Among these stresses, drought stress has been a major challenge for sustainable crop production and a hot area of research under the current climate change scenario. Organic amendments such as biochar (BC) and compost along with plant growth-promoting rhizobacte-ria (PGPR) could be a sustainable strategy to improve crop growth and productivity under drought stress environment. There are several reports about compost, BC, and PGPR application as a single or combined treatment to enhance crop productivity under drought stress. Compost and BC act as conditioners to improve soil physico-chemical and biological properties thereby enhancing water holding capacity (WHC) and nutrient retention and availability to the plants. Both BC and compost also serve as carbon sources and suitable environment for PGPR and endogenous microbes to enhance their growth promotion activities under drought stress. PGPR alleviate drought stress via ACC-deaminase and P-solubilizing activities, production of phyto-hormones, secretion of organic acids, acting as biocontrol agents,etc. In the present review, the individual and combined effect of compost, BC, and PGPR to alleviate drought stress in plants has been critically summarized. Moreover, research gaps and future research directions have been identified and discussed in depth. K E Y W O R D S biochar, compost, drought stress, plant growth-promoting rhizobacteria, rhizobacteria, water deficit
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Appraisal for organic amendments and plant growth-promoting rhizobacteria
to enhance crop productivity under drought stress: A review
ArticleinJournal of Agronomy and Crop Science · May 2021
DOI: 10.1111/jac.12502
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J Agro Crop Sci. 2021;00:1–20. wileyonlinelibrary.com/journal/jac
|
  1© 2021 Wiley-VCH GmbH
Received: 18 September 2020 
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  Revised: 9 April 2021 
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  Accepted: 12 April 2021
DOI : 10.1111/jac.125 02
REVIEW ARTICLE
Appraisal for organic amendments and plant growth- promoting
rhizobacteria to enhance crop productivity under drought
stress: A review
Naseer Ullah1| Allah Ditta2,3 | Muhammad Imtiaz4| Xiaomin Li5| Amin Ullah Jan6|
Sajid Mehmood7,8 | Muhammad Shahid Rizwan9| Muhammad Rizwan10
1Environmental Chemistry Laboratory,
Department of Environmental Science
and Engineering, School of Space and
Environment, Beihang University, Beijing,
China
2Department of Environmental Sciences,
Shaheed Benazir Bhutto University
Sheringal, Dir (Upper), Pakistan
3School of Biological Sciences, The
University of Western Australia, Perth, WA,
Australia
4Soil and Environmental Biotechnology
Division, National Institute for
Biotechnology and Genetic Engineering,
Faisalabad, Pakistan
5School of Space and Environment, Beihang
University, Beijing, China
6Department of Biotechnology, Shaheed
Benazir Bhutto University Sheringal, Dir
(Upper), Pakistan
7Guangdong Provincial Key Laboratory
for Radionuclides Pollution Control and
Resources, School of Environmental Science
and Engineering, Guangzhou University,
Guangzhou, China
8School of Civil Engineering, Guangzhou
University, Guangzhou, China
9Cholistan Institute of Deser t Studies,
The Islamia University of Bahawalpur,
Bahawalpur, Pakistan
10Institute of Soil Science, PMAS- Arid
Agriculture University, Rawalpindi, Pakistan
Correspondence
Allah Ditta, Department of Environmental
Sciences, Shaheed Benazir Bhutto University
Sheringal, Dir (Upper) Khyber Pakhtunkhwa,
18000, Pakistan.
Emails: ad_abs@yahoo.com; allah.ditta@
sbbu.edu.pk
Abstract
Plants are sessile organisms, frequently face unfavourable growth conditions such as
drought, salinity, chilling, freezing and high- temperature stresses, inhibiting growth
and development, and ultimately reducing crop productivity. Among these stresses,
drought stress has been a major challenge for sustainable crop production and a hot
area of research under the current climate change scenario. Organic amendments
such as biochar (BC) and compost along with plant growth- promoting rhizobacte-
ria (PGPR) could be a sustainable strategy to improve crop growth and productivity
under drought stress environment. There are several reports about compost, BC, and
PGPR application as a single or combined treatment to enhance crop productivity
under drought stress. Compost and BC act as conditioners to improve soil physico-
chemical and biological properties thereby enhancing water holding capacity (WHC)
and nutrient retention and availability to the plants. Both BC and compost also serve
as carbon sources and suitable environment for PGPR and endogenous microbes
to enhance their growth promotion activities under drought stress. PGPR alleviate
drought stress via ACC- deaminase and P- solubilizing activities, production of phyto-
hormones, secretion of organic acids, acting as biocontrol agents,etc. In the present
review, the individual and combined effect of compost, BC, and PGPR to alleviate
drought stress in plants has been critically summarized. Moreover, research gaps and
future research directions have been identified and discussed in depth.
KEY WORDS
biochar, compost, drought stress, plant growth- promoting rhizobacteria, rhizobacteria, water
deficit
2 
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   ULLAH et AL.
1 | INTRODUCTION
As the world population is continuously increasing, there is a pros-
pect of global warming due to climate change (Borjas- Ventura
et al., 2020). Besides, the present agricultural activities such as exces-
sive usage of phosphatic fertilizers containing heavy metals, pesti-
cides, herbicides, untreated sewage sludge, industrial effluents, etc.,
are expected to cause pollution and soil degradation (Barrow, 2012).
Thus, food production should be based on environmental sustain-
ability while managing the environmental resources in a way that
evades their further degradation (Godfray et al., 2010). Under field
conditions, plants frequently face unfavourable growth conditions,
for example drought, salinity, chilling, freezing, and high tempera-
tures, which can obstruct plant growth, and in some cases, it could
lead to cause plant death (Chiappero et al., 2019; Zhang et al., 2020).
Under the current climate change scenario, drought stress has been
a significant environmental issue for sustainable crop production
(Delshadi et al., 2017).
Drought is a prolonged dryness period when a region or area
gets a shortage in water supply whether from atmospheric, surface
or groundwater (Mishra & Singh, 2010). It has been a widespread
problem that is 2/3rd of the cultivated area worldwide is facing
drought stress, which is expected to increase in the coming years
due to global warming. Drought stress has deleterious effects on
crop growth and productivity through physiological (stomatal clo-
sure, root architecture, and so on) and biochemical changes (oxi-
dative stress) and ultimately poses a threat to food security (Aslam
et al., 2013; Carvalho et al., 2021). It is highly likely to investigate
certain amendments with the potential to enhance crop productivity
under drought stress and ultimately leading to food security.
Rhizobacteria are found in the rhizosphere of plants and those
having beneficial effects directly or indirectly on plant growth
and productivity through various mechanisms are termed as plant
growth- promoting rhizobacteria (PGPR) (Danish et al., 2020; Kasim
et al., 2013; Saharan & Nehra, 2011). The utilization of PGPR has
been an attractive and sustainable strategy for increasing crop
production under drought stress by replacing chemical fertiliz-
ers and pesticides (Kaushal & Wani, 2016). Various genera of rhi-
zobacteria like Pseudomonas, Azospirillum, Azotobacter, Klebsiella,
Enterobacter, Alcaligenes, Arthrobacter, Burkholderia, Bacillus and
Serratia have been investigated to improve the growth and produc-
tivity of various plants under drought stress (Danish & Zafar- Ul-
Hye, 2019; Kanwal et al., 2017; Kazeminasab et al., 2016; Mishra
& Singh, 2010; Zafar- ul- Hye et al., 2019). These drought- tolerant
PGPR induce systemic resistance in plants against drought (Hussain
et al., 2014; Kasim et al., 2013; Naveed et al., 2014). Under abiotic
stresses such as drought, there is an increased ethylene production,
which has a deleterious effect on the plants’ root growth (Arshad &
Frankenberger, 2002). Ethylene at low concentration (<25 µg/L) has
a stimulatory effect on crop growth while its higher concentration
inhibits seed germination and root development (Abeles et al., 1992;
Shaharoona et al., 2006). There are certain drought- tolerant PGPR
(Pseudomonas fluorescens, Pseudomonas fluorescens biotype G,
Pseudomonas putida biotype A, Burkholderia caryophylli, and so on)
that have ACC- deaminase activity which helps reducing ethylene
stress on roots (Shaharoona et al., 2006, 2007). The enzyme ACC-
deaminase converts 1- aminocyclopropane- 1- carboxylic acid (ACC), a
precursor of ethylene into ammonia and α- ketobutyrate through de-
amination (Shaharoona et al., 2006). In this way, PGPR improve root
architecture, which ultimately enhances plant water uptake under
drought stress (Nadeem et al., 2017). Other mechanisms through
which PGPR enhance crop growth and productivity under drought
stress include biological nitrogen fixation (BNF) through a symbi-
otic association between Rhizobia and plants, production of various
phytohormones (gibberellic acid, auxins, cytokinins, and so on), etc.,
(Ahmad et al., 2021; Kasim et al., 2013; Saharan & Nehra, 2011).
Biochar (BC) is carbon- rich organic materials derived through
the pyrolysis of agricultural wastes under minimal/no oxygen supply
(Bitarafan et al., 2020; Rizwan et al., 2018). BC can retain carbon
in soil and lessens the negative impacts of drought stress on crop
growth (Akhtar et al., 2014). Presently, BC is grabbing considerable
attention around the globe as a mean for carbon sequestration
and to decrease surface and groundwater contamination (Abbas
et al., 2018; Abideen, Koyro, Huchzermeyer, Ansari, et al., 2020;
Abideen, et al., 2020; Adejumo et al., 2020; Barrow, 2012; Bashan
et al., 2012). The characteristic of BC may moderate the effects
of drought on crop yield in areas, prone to drought stress. BC is a
beneficial soil amendment in retaining soil moisture, especially
under drought stress. It is an easily available input for sustain-
able agriculture and reduces global warming and land degradation
(Barrow, 2012). Poultry manure- derived BC serves as a natural or-
ganic fertilizer due to the large amount of NPK, and other micronu-
trients. Under drought stress, it improves the WHC of the soil due to
its positive effect on soil physicochemical and biological properties
(Bashan et al., 2012; Murtaza et al., 2021). Similarly, BC application
to sandy soil is beneficial to both crop growth and dramatically im-
proves the P availability of the coarse soil (Bashir et al., 2020; Foster
et al., 2016).
The use of BC is suggested for crops as it improves the mois-
ture contents of the soil (Abideen, Koyro, Huchzermeyer, Bilquees,
et al., 2020; Bitarafan et al., 2020; Rittl et al., 2018). When BC is
applied, it improves WHC and soil fertility by increasing soil organic
matter by a factor of 10– 100 and minimizes greenhouse gases emis-
sion from soils due to its stable nature against microbial decomposi-
tion (Cheng et al., 2008; Hale et al., 2011; Rittl et al., 2018; Roberts
et al., 2010). BC can make renewable energy in a climate- friendly
way and acts as an essential amendment for the soil to increase crop
productivity (Barrow, 2012). Due to its slow degradation in the soil,
it acts as a carbon source for soil microorganisms. As clear from
Figure 1, the high surface area and porous structure of BC provide a
safe environment for the soil microorganisms against various biotic
and abiotic stresses (Chen et al., 2014; Hale et al., 2014).
Compost is organic matter that has been decomposed through
compos ting. The application of compost improves the physicochem-
ical and biological properties of the soil (Ahmad et al., 2017; Salehi
et al., 2016), increases its WHC, which ultimately improves plant
  
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 3
ULLA H et AL.
growth and productivity under drought stress (Shahzad et al., 2014).
The addition of compost to the soil not only improves the soil or-
ganic matter but also increases the amount of available macro- and
micro- nutrients for crop growth (Ditta, Imtiaz, et al., 2018; Ditta,
Muhammad, et al., 2018; Singh, Singh, et al., 2019; Somerville
et al., 2019). Regarding the biological properties of soil, organic
amendments improve the microbial activities and their diversity in
soil, thereby improving nutrient release for crop growth and produc-
tivity (Singh, Prabha, et al., 2019).
Residues of agricultural wastes such as straws, nutshells, fruit
peels, fruit seeds, stoves and green leaves are among the pri-
mary raw materials for the production of BC and compost (Ditta,
Muhammad, et al., 2018; Singh, Prabha, et al., 2019). The disposal
methods currently being used to manage these residues are a source
of extensive environmental pollution. For example, disposal of rice
an d wheat st raw by open- f iel d burn ing cau s es air pollu tion. In th is re-
gard, organic amendments and PGPR could be a sustainable strategy
to improve crop growth and productivity under normal and drought
stress conditions. There are many reports about the combined syn-
ergistic effect of compost and BC (Adejumo et al., 2020; Bashir
et al., 2020; Obadi et al., 2020; Ramzani et al., 2017; Somerville
et al., 2019), compost, and PGPR (Armada et al., 2014; Duo
et al., 2018; Kanwal et al., 2017; Kazeminasab et al., 2016; Shahzad
et al., 2014; Yaseen et al., 2019), BC and PGPR (Ullah et al., 2020;
Zafar- ul- Hye et al., 2019) and compost, BC and PGPR (Nadeem
et al., 2017) under drought stress. The unique mechanisms respon-
sible for plant growth promotion have been discussed in earlier sec-
tions (Figures 2– 4). More specifically, organic amendments such as
BC and compost act as a conditioner to enhance soil physicochem-
ical properties, a nutrient source for plants, and a carbon source,
and a suitable environment for PGPR and indigenous microbes to
enhance their growth promotion activities under drought stress. In
the present review, first we have described the impacts of drought
stress from growth, physiological, and biochemical point of view.
We have then critically summarized the role of the individual and
combined application of organic amendments and PGPR to alleviate
drought stress through various mechanisms in plants. Moreover, the
research gaps found and future research directions for further stud-
ies have been proposed.
2 | IMPACT OF DROUGHT STRESS ON
PLANTS
Drought is a meteorological term and it takes place when there is a
subs tantial loss of moisture from the surfa ce of the soi l to the at mos-
phere. It may also arise due to less water supply through rainfall or
any other source of precipitation to soil (Aslam et al., 2013). Drought
is a severe threat to food security having deleterious effects on the
growth, physiological, and biochemical processes of plants (Farooq
et al., 2020; Van der Weijde et al., 2017). It affects plant- water re-
lations on both the cellular and whole plant levels, which leads to
various specific and non- specific phenotypic and physiological re-
sponses (Beck et al., 2007). During drought stress, water availability
and turgidity of crops are decreased which disrupts the normal func-
tioning of the plant body (Sinha et al., 2016, 2019). Drought stress
has detrimental effects on the establishments of crop seedlings,
leaves and root growth, photosynthesis, pollination, grain develop-
ment, and ultimately on crop productivity (Farooq et al., 2017; Jaleel
et al., 20 09). The effect of drought stress is apparent at every step
of plant development and varies from morphological to molecular
stages. Drought stress significantly reduces seed germination and
FIGURE 1 The high surface area (a) and pore structure (b) of
biochar provide a safe environment for the soil microorganisms,
which enhance soil microbial activities and ultimately nutrient
availability to the crop plants under drought stress (Chen
et al., 2014; Hale et al., 2014)
(a)
(b)
4 
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   ULLAH et AL.
seedling development (Chiappero et al., 2019). Drought inhibits
leaf expansion and stomatal development resulting in lower photo-
synthesis, which finally reduces plant biomass (Endres et al., 2019;
Keipp et al., 2020) via oxidative stress (Aslam et al., 2013; Bistgani
et al., 2017; Elsayed et al., 2019). Several processes such as hydrau-
lic status, osmotic adjustment, phytohormones, and reactive oxy-
gen species (ROS) signals reduce plant growth under drought stress
(Guangyu et al., 2020; Moreno- Galván et al., 2020). ROS are the
by- products of aerobic metabolism, which are produced in various
cellular organelles such as chloroplasts, mitochondria, and peroxi-
somes under abiotic stress conditions. As reactive molecules, ROS
oxidize and modify cellular components, thereby causing irreversible
DNA damage and even cell death (Huang et al., 2019). Physiological
characteristics of plants such as gaseous exchange and water use
efficiency are mainly disturbed under drought (Carvalho et al., 2021;
Cotrim et al., 2020; Goodarzian- Ghahfarokhi et al., 2016). Moreover,
the integrity of cellular membranes, photosynthetic pigments, os-
motic adjustment of osmolytes, and photosynthesis are severely
affected by drought stress (Jafari et al., 2019). Both stomatal con-
ductance and leaf expansion are key mechanisms in plants to sur-
vive under drought stress conditions (Romdhane et al., 2019; Talbi
et al., 2020; Zlobin et al., 2018).
When plants are exposed to drought stress, there is a significant
reduction in leaf water potential, relative water contents, and tran-
spiration rate with an abrupt increase in leaf temperature (Bistgani
et al., 2017). The soil- plant- atmosphere greatly determines the
transpiration rate of crops. According to Salehi et al. (2016), water
deficiency alters the osmotic potential of tissue, defences against ox-
idative stress and growth rate. However, the growth of plant species
is differently affected by drought stress. Reduction in leaf size allows
plants to respond against water shortage (Jin et al., 2015). Stomatal
closure in plants is the first line of defines against drought stress,
which reduces the exchange of water, carbon dioxide, and oxygen
and ultimately reduces photosynthetic rate (Hlaváčová et al., 2018;
Kanwal et al., 2017; Kasim et al., 2013). Photosynthesis is the main
feature limited in plants exposed to drought stress, mostly under
arid and semi- arid climatic conditions (Talbi et al., 2020).
3 | IMPACT OF ORGANIC AMENDMENTS
AND PGPR ON CROP PRODUCTIVITY
UNDER DROUGHT STRESS
3.1 | Biochar
The use of biochar (BC) is gathering attention as a carbon- rich or-
ganic amendment for agriculture and environmental sustainability
(Bitarafan et al., 2020; Yang et al., 2020). The potential benefits of
the BC have readily been observed under limited water conditions
(Table 1). Adejumo et al. (2020) stated that BC has prospective ef-
fects on the production of agricultural products and remediation of
soil and water under stress due to its role in improving plant growth
and diminishing heavy metals’ pollution (Ijaz et al., 2020; Rizwan
et al., 2021). Various researchers have reported enhanced crop yield
FIGURE 2 Effects of biochar on
different characteristics of soil under
drought stress (Chen et al., 2014; Hale
et al., 2014)
  
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 5
ULLA H et AL.
following BC application to fertilizer amended soil that was infertile
and under drought stress (Abideen, Koyro, Huchzermeyer, Ansari,
et al., 2020; Abideen, Koyro, Huchzermeyer, Bilquees, et al., 2020;
Ahmed et al., 2018; Deluca et al., 2015). The increase in crop growth
and yield is commonly observed with the application of BC to soils
yet experimental outcomes are dynamic and depend on the experi-
mental set- up and soil properties.
The high surface area and porous structure of BC provide a safe
environment for microorganisms in the soil, which increases the
availability of micro- and macro- nutrients for plants under drought
stress (Figure 1). Moreover, BC improves soil porosity, moisture re-
tention capacity, and water use efficiency to reduce drought effects
on crop yield (Abideen, Koyro, Huchzermeyer, Ansari, et al., 2020;
Hafeez et al., 2017; Hansen et al., 2016). Since BC has high organic
carbon contents, it can act as a soil conditioner to improve the phys-
icochemical and biological properties of soil (Murtaza et al., 2021).
Increased plant growth such as in tomato (Akhtar et al., 2014;
Mulcahy et al., 2013) and barley (Hansen et al., 2016) has been
observed under drought stress via BC application. BC enhanced
drought stress tolerance under reduced irrigations in tomatoes
(Akhtar et al., 2014).
Although many studies have reported the efficacy of biochar ap-
plication in the soil for optimum growth and productivity of plants,
there are also some limitations. For example, the adsorption poten-
tial of biochar for plants nutrients especially N and Fe may result in
their deficiency (Kim et al., 2015). The positive effects of biochar
are dependent on pyrolysis temperature, biochar aging, soil type,
plant species, etc. (Kavitha et al., 2018). Biochar produced at high
temperatures tends to have more pH and it may not be suitable for
alkaline soils due to the formation of P precipitates with Ca and Mg,
thereby causing phosphorus deficiency (Xu et al., 2016). There are
also reports about the magnification of contaminants through bio-
mass used for biochar preparation (Jones & Quilliam, 2014). The
aged biochars may also have a detrimental effect on the growth of
earthworms and/or fungi (Anyanwu et al., 2018), thereby affect-
ing soil health and nutrient availability. Despite the above, a recent
meta- analysis study reported that application of biochar @ >50 t/ha
would be required for improvement of hydraulic properties of sandy
soils under laboratory conditions (Rabbi et al., 2021). The authors
suggested that the application of such a huge amount would involve
high costs during biochar production and would require further re-
search I producing effective biochar with optimum porosity, surface
area, and hydrophilic properties.
3.2 | Biochar and compost
Recently, the integration of organic amendments is gaining interest
to improve soil fertility and crop productivity under drought stress
(Akhtar et al., 2014). The combined use of biochar (BC) and compost
has a synergistic effect on crop growth and productivity, especially
under drought stress (Table 2). An increase in soil WHC, plant water
status and plant ions, net photosynthesis, and photosystem II effi-
ciency in Phragmite s karka after BC ap plication was observed (Abideen,
FIGURE 3 Effects of compost on
different characteristics of soil under
drought stress (Bashir et al., 2020;
Ramzani et al., 2017)
6 
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   ULLAH et AL.
Koyro, Huchzermeyer, Bilquees, et al., 2020). Moreover, plants treated
with BC had lower oxidative stress, enhanced water- use proficiency,
and diminished soil respiration. The BC- compost blend considerably
improved the plant growth, leaf turgor potential, and gaseous ex-
change parameters such as photosynthesis, transpiration, etc.
Obadi et al. (2020) conducted a study on sweet pepper (Capsicum
annum L.) to evaluate the effect of BC and compost under partial root-
zone dr ying ir rigat ion (droug ht st ress). In resul t s, a su bstantia l decl ine in
morphological traits like flowering, fruit set, and vigorous fruit- bearing
stages due to a reduction in the water supply was observed. A strong
beneficial outcome on plant development such as plant height, num-
ber of leaves, and yield was observed with the combined application
of BC and compost at the rate of 2% (w/w). It was suggested that the
combined utilization of BC and compost with partial root- zone drying
irrigation strategy (80% ETc) could be a practical manage me nt strategy
to improve the production of sweet pepper by saving about 22% of
applied water. Adejumo et al. (2020) studied the growth of maize in
lead- contaminated soil under drought stress and found that compared
to un- amended soil, the combination of BC with compost enhanced
biomass production in stressed maize crop by 50%– 75%. Similarly,
Bashir et al. (20 20) demonst rated that Cd and drought alone decreased
the wheat growth, elevated the oxidative stress and Cd contents in
wheat tissues while application of co- composted farm manure and BC
increased the growth, yield, chlorophyll contents and minimized the
oxidative stress in the leaves along with the reduction in Cd concentra-
tions in wheat tissues mainly in grains.
Ramzani et al. (2017) studied the application of acidified BC and
compost in three soils having different stresses to examine the qui-
noa growth, physiological response, and seed nutritional quality. It
was found that drought, salt- affected and nickel- contaminated soils
produced ROS in quinoa plants, which were reduced by the addition
of acidified BC and compost. Moreover, plant growth, yield, physio-
logical, chemical, and biochemical parameters were significantly im-
proved under all stressed soils by applying acidified BC and compost.
Nevertheless, when combined with compost, the results of BC ap-
plications have not been completely grasped and need further eluci-
dation, especially under long- term field trials. Also, BC and compost
combined response has not been studied extensively in vegetables,
especially under sandy soil conditions, and require further research
in the future with a special focus on the response mechanisms of soil
properties (carbon sequestration) to biochar application under long
term field conditions.
3.3 | Biochar and PGPR under drought stress
The function of PGPR in the establishment , grow th, and drought tol-
erance in plants is the product of the sum of nutritional, physiological,
FIGURE 4 Effects of PGPR on
different characteristics of soil under
drought stress (Barnawal et al., 2017;
Govindasamy et al., 2020; Saharan &
Nehra, 2011)
  
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 7
ULLA H et AL.
TABLE 1 Impact of biochar on plant growth under drought stress
Feedstock
Pyrolysis
Temp.
Application
rate Drought condition Crop plant Impact Reference
Corn straw 500°C 5% Full irrigation (30% of soil volumetric
water content), deficit irrigation (soil
moisture decreased to 10%) and
alternate root- zone drying irrigation
Quinoa
(Chenopodium
quinoa)
Biochar improved both photosynthesis
and stomatal conductance in all irrigation
regimes, enhanced plant height, shoot
biomass, and grain yield by 11.7%, 18.8%
and 10.2%, respectively
Yang
et al. (2020)
Rice husk, standard rice husk,
wheat straw or oilseed rape
straw
500°C 2% Irrigation was reduced from 80% of FC
to 40% in half of the pots to create
water stress when 50% of the plants
flowered
Fenugreek
(Trigonella foenum-
graecum L.)
All standard biochars increased plant dry
weight (18% − 25%) and number of seeds
pod−1 (9.0% − 14.5%) compared with the
control
Bitarafan
et al. (2020)
wheat straw 55 C 0, 5, and 10 g/
kg
Drought stress (main factor): soil
moisture was kept at 75%– 80% WHC
as control (D- C), 40%– 45% WHC as
low drought stress (D- L), 20%– 25%
WHC as high drought stress (D
Soybean(Glycine
max)
Biochar addition significantly enhanced
soybean grain yield by 3.1%– 14.8%,
Zhang
et al. (2020)
Coniferous wood and hardwood
chips (1:4 ratio by weight)
750° C 0%, 0.75% and
2.5%
The WHC was kept at 40% of maximum
WHC of the respective treatment.
Tall Reed
(Phragmites karka)
Biochar application enhanced plant fresh
and dry biomass, root to shoot ratio and
root mass fraction, was paralleled by
an increase of chlorophyll content, net
photosynthesis rate and WUE of plants
and reduced oxidative stress
Abideen, Koyro,
Huchzermeyer,
Ansari,
et al. (2020)
Poplar (Popolus alba L.) woodchip 800°C 0% and 1%
(w/w), 2.6 kg
BC m−2
Natural rainfall without irrigation Maize (Zea mays)Biochar improved physicochemical
characteristics and the water content
of treated soils with increased root
elongation and transpiration
Romdhane
et al. (2019)
Rice straw 450 and
550° C
0%, 3.0% and
5.0%
Three levels of drought stress (well-
watered, mild drought and severe
drought containing 70%, 50%, and
35% of soil WHC respectively) were
applied to 45- d- old wheat plants
Wheat (Tr iticu m
aestivum)
Biochar improved morphological and
physiological parameters of wheat
under combined drought and Cd stress
and reduced the oxidative stress and
Cd contents and increased antioxidant
enzymes activities
Abbas
et al. (2018)
Rice straw 450 and
550° C
0%, 3%, and
5%, (w/w)
Three moisture levels including zero
drought as a control (1– 2 cm water
layer on soil), mild drought (MD, 50%
of soil WHC), and severe drought (SD,
35% of soil WHC)
Rice (Oryza sativa) The biochar supply reduced the
bioavailable Cd in the soil whereas
increased the soil EC and pH than the
control treatment.
Rizwan
et al. (2018)
Wheat straw 350– 550°C 0, 25 and 50 t/
ha
Three irrigation regimes (W1 = 50%,
W2 = 75% and W3 = 100% of the
reference evapotranspiration)
Tom ato (Solanum
lycopersicum)
The integration of BA along with DI can
be considered as a viable approach that
improves crop productivity and promotes
irrigation water use efficiency
Agbna
et al. (2017)
(Continues)
8 
|
   ULLAH et AL.
Feedstock
Pyrolysis
Temp.
Application
rate Drought condition Crop plant Impact Reference
Corn cob 450°C 10, 20 t/ha For water level treatments pots were
watered after two days and pots with
non stress conditions were watered
daily
Soybean (Glycine
max L.)
Biochar significantly improved sugar and
proline content under drought stress as
compared to control
Hafeez
et al. (2017)
Wood chip sieving of Picea abies
L. (70%) and Fagus sylvatica L.
(30%)
550– 6 00 °C 0, 15 and
30 Mg/ha
Watering regime (rainfed or irrigated) Maize(Zea mays),
wheat (Tr iticu m
aestivum), peas
(Pisum sativum)
and barley
(Hordeum vulgare)
Biochar amendments significantly reduced
NO3 leaching, improved soil moisture and
higher NO3 amount
Haider et al.
(2017 )
Rice husk and shell of cotton
seed
400°C 0% and 5%
(w/w)
Three irrigation regimes, i.e. full
irrigation (FI), deficit Irrigation (DI),
and partial root- zone drying irrigation
(PRD). In case of FI, plants were
irrigated daily to FC while in DI and
PRD, 70% water used for FI was
irrigated on either the whole or one
side of the pots, respectively
Tomato (Solanum
lycopersicum)
Biochar increased the soil moisture
contents in DI and PRD, which
consequently improved physiology, yield,
and quality of tomato as compared with
the non- biochar control. Also, water use
efficiency, leaf relative water content,
membrane stability index and fruit yield
were improved
Akhtar
et al. (2014)
Pseudotsuga menziesii - 0%, 15% and
30% (v/v)
Plants were watered daily, and
abundantly, for the first 24 days after
transplanting, but not thereafter
Tomato (Solanum
lycopersicum)
Biochar application (30% v/v), significantly
increased seedling resistance to wilting
Mulcahy
et al. (2013)
TABLE 1 (Continued)
  
|
 9
ULLA H et AL.
TABLE 2 Impact of biochar and compost on plant growth under drought
Plant spe cie Biochar Compost Drought Stress Impact References
Wheat ( Tritic um
aestivum)
Garden peat Farm yard manure Seeds were sown in the soil at normal soil moisture (70%
of soil WHC level. Both normal and drought stress (35%
WHC) levels, after 50- day of sowing, were applied and
plants were harvested at 122 days after seed sowing
Shoot dry weight increased by 80% and 95%
while dry root weight increased by 68%
and 82% and spike length and grain weight
increased by 69% and 87% under normal and
drought stress
Bashir
et al. (2020)
Sweet pepper (Capsicum
annuum L.)
Date palm Commercial Compost Partial root zone drying irrigation (PRD) i- e IR1 (80%
ETc) and IR2 (100% ETc).
Moderate improvement (39.9%) in yield with a
higher WUE (103.8%) than the control
Obadi
et al. (2020)
Maize (Zea mays) Rice husk Mexican sunflower and
poultry manure
Drought stress was imposed by reducing the soil FC to
25% and 50%.
Biochar in combination with compost
enhanced biomass production in stressed
maize crop by 50%– 75% compared to
unamended soil
Adejumo
et al. (2020)
Mesic (Corymbia
maculate) and Xeric
(Eucalyptus torquata)
tree
Eucalypt hardwood Municipal green waste All WD pots received 50% of the estimated daily mean
evapotranspiration (ET) measured for the WW pots of
the same species
The ET of the xeric tree species was greater
for all the OM amended soils for both well-
watered (WW) and water deficit ( WD) plants.
The compost/biochar amended clay soil had
PAW that was 69% of the control PAW
Somerville
et al. (2019)
Wheat ( Tritic um
aestivum)
Rice husk ash Farm yard manure The control and traditional packages received full
irrigation water whereas emergent agronomic package
received ~10% less irrigation water for observing the
crop performance under reduced water application
Irrigation (WPi) and total water productivity
(WPt) were respectively found maximum
under reduced (0.67 ± 0.01 and
0.57 ± 0.01 kg/ha mm) and full irrigation
with organic amendments (0.66 ± 0.03 and
0.57 ± 0.02 kg/ha mm) whereas minimum
under RB (0.53 ± 0.01 and 0.46 ± 0.01 kg/
ha mm) and control with full irrigation
(0.54 ± 0.01 and 0.46 ± 0.01 kg/ha mm)
Singh, Singh,
et al. (2019)
Quinoa
(Chenopodium quinoa
Willd.)
Maize cob Maize plants Drought- stressed soil was artificially created by the
reduction of 80%– 85% crop water requirement
Acidified biochar increased root, shoot, seed
yield pot−1, A, E, gs and chlorophyll content
by 61%, 60%, 55%, 33%, 81%, 51% and 70%
in salt- affected; 31%, 50%, 38%, 31%, 41%,
42% and 61% in Ni contaminated and 58%,
62%, 62%, 43%, 100%, 79% and 88% in
drought soil, respectively, compared to their
corresponding controls
Ramzani
et al. (2017)
Maize (Zea mays) Virgin pine wood Steer
manure
Irrigation occurred once per week for the well- watered
“full” irrigation and all irrigation inputs were withheld
from the appearance of the seventh collared leaf (V7)
to maize tasseling for limited irrigation treatment.
In comparison to the control, manure
application increased gravimetric soil
moisture by approximately 15%, total
nitrogen by 10%, usable phosphorus by
45% and microbial biomass carbon by 15%
(p <.05). Relative to power, biochar raised
overall soil carbon by 80 percent and
changed EEAs (p <.05).
Foster
et al. (2016)
10 
|
   ULLAH et AL.
and cellular effects of PGPR on plants (Czarnes et al., 2020). PGPR
control the physiology of plants to a superior degree due to their
large number in the rhizosphere (Kasim et al., 2013). The combined
application of PGPR with BC has various additional benefits for ex-
ample, the BC not only improves the physicochemical properties
of the soil but also serves as carrier material for PGPR inoculation
(Danish et al., 2020; Ullah et al., 2020). BC as carrier material for
PGPR not only serves as a carbon source for bacterial multiplica-
tion but also provides a safer environment against various biological
competitors in soil due to porous structure (Chen et al., 2014; Hale
et al., 2014). Moreover, the combined application reduces the costs
involved during the separate application of PGPR and BC.
The combined effect of BC with PGPR or inoculated BC has been
summarized in Table 3. Various researchers have confirmed the role
of BC and PGPR in improving crop growth and productivity under
drought stress via an increase in organic carbon and WHC of the soil,
carbon source for PGPR, provision of protection sites for microbes,
and subsequent microbial action against ethylene stress and various
other mechanisms (Danish & Zafar- ul- Hye, 2019; Danish et al., 2020;
Ullah et al., 2020; Zafar- ul- Hye et al., 2019). Although biochar with
PGPR has a positive effect on crop productivity; further research
is needed to confirm its efficacy under long- term field conditions
under various climatic conditions.
3.4 | Compost and PGPR under drought stress
The combined application of compost and PGPR has a synergis-
tic effect on crop growth and productivity under drought stress.
The compost adds organic carbon to the soil, thereby improving
soil physicochemical and biological properties of the soil (Bashan
et al., 2012). The compost is also well renowned for the provision
of micro and macronutrients to the plants (Ditta et al., 2015; Ditta,
Imtiaz, et al., 2018; Ditta, Muhammad, et al., 2018). Combined with
PGPR, compost serves as carrier material for microbial inoculation
of crop seeds, thereby improving their survival and subsequent mi-
crobial activities for example, enhanced ACC- deaminase activity to
scavenge ethylene stress, P- solubilizing activity to enhance phos-
phorus availability, production of phytohormones, exopolysaccha-
rid es, organic acids, etc. (A hmad et al., 2017; Duo et al., 2018; Moridi
et al., 2019; Yaseen et al., 2019, 2020). As summarized in Table 4,
various researchers have confirmed a synergistic effect of compost
with PGPR on crop growth and productivity under drought stress.
For example, seed inoculation with PGPR (Alcaligenes faecalis,
Bacillus amyloliquefaciens, and Pseudomonas moraviensis) along with
the application of biogas slurry (BGS) under drought stress condi-
tions showed significantly improved grain and biological yield of
wheat (Yaseen et al., 2019). Further, the combined application of
PGPR with BGS was suggested as a sustainable strategy for im-
proved crop growth and productivity under drought stress. Earlier,
the combined application of compost with rhizobacteria enhanced
crop growth, quality, and productivity under desertified soil con-
ditions (Ahmad et al., 2017; Duo et al., 2018; Kanwal et al., 2017;
Moridi et al., 2019; Yaseen et al., 2019, 2020). Under semiarid con-
ditions, the application of indigenous microbes with Aspergillus niger
treated agro- wastes alleviated drought stress and subsequently en-
hanced crop growth (Armada et al., 2014). In vermiculture, vermi-
compost is produced through the artificial cultivation of worms and
is used for crop production as it provides nutrients to the plants.
Inoculation of vermicompost with PGPR had an additive effect on
crop productivity, especially under drought stress due to its effect
on physicochemical and biological properties of soil (Kazeminasab
et al., 2016).
Similarly, nodulation and growth of chickpea were significantly
enhanced with the combined application of phosphorus enriched
compost with Mesorhizobium ciceri and PGPR under normal and
rainfed irrigation systems (Shahzad et al., 2014). Moreover, nutri-
ent contents, enzyme activities such as dehydrogenase, and phos-
phomonoesterase activities significantly enhanced chickpea growth
and productivity under a rainfed irrigation system. In another study,
the combined application of PGPR with compost and mineral fertil-
izer improved growth, physiological and biochemical parameters of
wheat under drought stress (Kanwal et al., 2017).
Recently, nanotechnology has played a significant role in crop
growth and productivity under normal and abiotic stress conditions.
Nanomaterials with smaller sizes have a large surface area, making
them robust for various agricultural applications (Ditta, 2012, 2019;
Ditta & Arshad, 2016; Ditta et al., 2020). In this regard, nano- compost
was prepared via ball mill technology after enriching municipal solid
waste compost with nutrients. The nano- compost was applied with
drought- tolerant PGPR to enhance the growth and productivity
of turfgrass under drought stress (Duo et al., 2018). In results, the
combined application of PGPR with nano- compost significantly al-
leviated oxidative stress under drought, thereby increasing drought
tolerance and ultimately growth and productivity in turfgrass. In the
future, more studies are needed to confirm its effectiveness under
natural field conditions using different crops.
3.5 | Biochar, PGPR, and compost under
drought stress
Since there is positive feedback on the individual role of PGPR,
BC, and compost in enhancing plant growth under normal as well
as drought stress, there is meager information on the interactive
impact of PGPR with BC and compost, particularly under drought
stress (Table 5). Recently, Uzinger et al. (2020) found that combined
application of PGPR with BC and compost significantly enhanced
the microbial activity with the lowest arbuscular mycorrhizal fungi
(AMF) colonization. However, there was a non- significant effect on
the soil fertility level with the combined application of PGPR with
BC and compost. The interactive effect of BC, compost, and PGPR
in improving drought stress tolerance in cucumber was evaluated
by Nadeem et al. (2017). In results, improved cucumber growth
was recorded with the combined application of BC, compost, and
PGPR under drought stress. With the combined application of
  
|
 11
ULLA H et AL.
TABLE 3 Impact of biochar and PGPR under Drought Stress
Crop Biochar Inoculum Drought Stress Impact Reference
Maize (Zea
mays)
T i m b e r- w a s t e Pseudomonas aeruginosa,
Enterobacter cloacae,
Achromobacter xylosoxidans
and Leclercia adecarboxylata
Normal moisture (NM) was
maintained at the level of
70% of FC. Mild (MD) and
severe drought stress (SD)
were maintained at 50% and
30% of FC
Grain yield plant−1, photosynthetic rate, stomatal conductance,
chlorophyll a, total chlorophyll and carotenoids contents
were increased up to 60%, 73%, 43%, 69%, 76% and 42%
respectively and grain yield plant−1, photosynthetic rate,
stomatal conductance, chlorophyll a, total chlorophyll and
carotenoids contents up to 200%, 213%, 113%, 152%, 148%
and 284%
Danish
et al. (2020)
Wheat
(Tr it icu m
aestivum)
Timber waste Leclercia adecarboxylata,
Agrobacterium fabrum,
Bacillus Amyloliquefaciens,
Pseudomonas aeruginosa
Polyethylene glycol 6,000
(PEG- 6000) used (0%,
10% and 20%) to maintain
osmotic potential (0.05,
−0.23 and −0.78 MPa) to
introduce drought stress
Combined application improved chlorophyll a, chlorophyll b,
photosynthetic rate, transpiration rate, 100- grain weight, and
grain N, P and K by 114%, 123%, 118%, 73%, 59%, 58%, 18%
and 23%, respectively
Danish and Zafar-
ul- Hye (2019)
Wheat
(Tr it icu m
aestivum)
Timber- waster Agrobacterium fabrum or
Bacillus amyloliquefaciens
Mild drought (three
irrigations were applied (one
irrigation was skipped at
the tillering stage). Severe
drought stress was induced
by using two irrigations (two
irrigations were skipped;
one at the tillering stage and
other at the milky stage)
Combined application of B. amyloliquefaciens and 30 Mg/ha
BC under 3I, significantly increased growth and yield traits
of wheat: grain yield (36%), straw yield (50%), biological yield
(40%). The same soil application under 2I resulted in greater
increases in several of the growth and yield traits: grain yield
(77%), straw yield (75%), above and below- ground biomasses
(77%), as compared to control
Z a f a r - u l - H y e
et al. (2019)
Maize (Zea
mays)
Algal biomass Serratia odorifera One group of plants was
given a water level 75% FC;
another group was given
50% FC while the remaining
group was watered at
normal (100% FC)
Combined application of algal BC and PGPR significantly
increased fresh and dry weights of shoot and root and root
length by 2.76, 5.94, 3.24, 13.82, and 4.06 percent.
Ullah et al. (2020)
Lupin (Lupinus
angustifolius
L.)
Hydrochar from maize silage,
pyrolysis biochar from
maize (MBC) and pyrolysis
biochar from wood (WBC)
Bradyrhizobium sp.Two conditions, namely
irrigated conditions
(watered at 75% FC) and
drought stress (irrigation at
45% FC)
The HTC- based formulation of Bradyrhizobium sp. provides
an effective carrier for inocula, thereby improving growth,
nutrient uptake and symbiotic performance of lupins
under drought. lupins that were treated with HTC- BR had
significantly greater shoot (18%) and root (39%) weights.
Egamberdieva
et al. (2017)
12 
|
   ULLAH et AL.
TABLE 4 Impact of Compost and PGPR under Drought Stress
Crop Compost Inoculum Drought Stress Impact Reference
Wheat ( Tritic um
aestivum)
Biogas slurry
(BGS)
Pseudomonas moraviensis The irrigation was skipped at the
tillering (SIT) and flowering (SIF)
stages of the crop while there
were four irrigations applied
during normal irrigation (NI).
After 15 days of seed sowing
three levels of irrigation were
maintained i.e., 100%, 70% and
50% WHC
The Pseudomonas moraviensis with BGS application improved
the grain yield and plant height up to 30.3% and 24.3%,
respectively, where irrigation was skipped at the tillering
stage, as compared to the uninoculated controls. The same
treatment significantly increased RWC, catalase activity,
ascorbate peroxidase activity, as well as grain and shoot
phosphorus contents, up to 37%, 40%, 75%, 19%, and 84%,
respectively, at SIF
Yaseen
et al. (2020)
Maize (Zea mays) Vermicompost
tea (VT) and
vermiwash (V)
Micrococcus yunnanensis Three levels of water deficit stress
(WDS) (FC, 80% FC and 60% FC)
PGPR enriched liquid organic fer tilizers (LOFs) were more
effec tive and practical approach for amplifying drought
tolerance and reducing the risk of water scarcity in maize
cultivation. At all WDS levels, application of LOFs increased
shoot dry weight and nutrients uptake
Moridi
et al. (2019)
Wheat ( Tritic um
aestivum)
Biogas slurry
(BGS)
Alcaligenes faecalis,
Bacillus amyloliquefaciens
and Pseudomonas
moraviensis
After 15 days of seed sowing
three levels of irrigation were
maintained i.e. 100%, 70% and
50% WHC
ACCD possessing rhizobacterial inoculations with BGS
improved stomatal and sub- stomatal conductance,
transpiration and photosynthetic rates up to 98%, 46%,
38%, and 73%, respectively, compared to the respective
uninoculated controls. The Pseudomonas moraviensis with BGS
application improved the grain yield and plant height up to
30.3% and 24.3%, respectively, where irrigation was skipped
at the tillering stage, as compared to the uninoculated controls
Yaseen
et al. (2019)
Turfgrass (Festuca
arundinacea
Schreb.)
Municipal solid
waste
Bacilluscereus,
Lysinibacillus sp. and
Rhodotorula glutinis
Water was supplied daily to
maintain 75% FC of soil. 20 days
after planting, plants were
exposed to two levels of drought
stress, namely moderate drought
stress (watered and maintained
at 55% FC) and severe drought
stress (watered and maintained at
40% FC) for 40 days
The enhancement in plant biomass was pronounced in plants
treated with both nano- compost and microbial inoculants,
i.e. 210% and 226% increases in shoot and root biomass,
respectively, than control plants under moderate drought
stress. Under severe drought stress, same treatment increased
shoot and root biomass by 209% and 215%, respectively,
compared to the control.
Duo et al. (2018)
Chickpea (Cicer
arietinum)
Farm yard
manure
Mesorhizobium
cicri, Pseudomonas sp. and
Bacillus sp.
Natural desert conditions With the application of biofertilizer, the maximum increase
in number of nodules plant−1 as compared to control was
observed at site 16BC that was 126% higher than control. The
combined application of P- enriched compost and biofertilizer
resulted in maximum increase (230%) in number of nodules as
compared to un- inoculated control at the same site
Ahmad
et al. (2017)
(Continues)
  
|
 13
ULLA H et AL.
Crop Compost Inoculum Drought Stress Impact Reference
Wheat ( Tritic um
aestivum)
Food waste Azospirillum
lipoferum
Soil moisture was maintained at
15 ± 1% i.e. 65 ± 5% by weight of
FC, by water holding in drought
exposed plants; and at 19 ± 1%
(i.e. 85 ± 5% by weight of FC) in
well- watered plants. To induce
drought, water was withheld for
ten days at vegetative stages
Inoculated seed with compost and mineral fertilizer grown
in drought condition showed 43% increase in relative water
content (RWC) of 9.39% in membrane stability index and
82.20% in chlorophyll as compared to control. Drought
affected the accumulation of osmolytes, but PGPR in
combination with compost and mineral fertilizer under
drought stress triggered higher accumulation of soluble sugar
and proline content, i.e. 28.96% and 73.91%, respectively
Kanwal
et al. (2017)
Lemon Balm (Melissa
officinalis L.)
Vermicompost Pseudomonas fluorescent,
Azotobacter chrococum,
Azospirillm brasilense
Plants in the drought- stressed
treatment were watered to 60%
of FC same times
Only RWC and total chlorophyll were positively affected
by biofertilizer application while vermicompost enhanced
essential oil content, essential oil yield, total chlorophyll, cell
membrane stability, proline and RWC
Kazeminasab
et al. (2016)
Maize (Zea mays) and
clover
(Trifolium repens)
Sugar beet waste Bacillus megaterium and/or
consortium of arbuscular
mycorrhizal fungi (AMF)
Natural drought conditions with
polyethylene glycol (PEG) (0%, 5%
and 10%) in the culture medium to
induce osmotic stress.
Inoculated residue amended soil promoted plant growth and
hydric content and decreased most antioxidant activities to
a greater extent than AMF inoculation. Comparing the total
shoot plant biomass yielded in control plants with those
amended and inoculated, the highest differences in shoot
biomass were of 157% (BC) and 135% (MC)
Armada
et al. (2014)
Chickpea (Cicer
arietinum)
Fruit and
vegetable waste
and enriched
with single
super phosphate
Mesorhizobium ciceri Irrigated and rainfed farming
systems
Compared to irrigated farming system, inoculation with
phosphorus- enriched compost under rainfed conditions
was more beneficial in improving grow th and nodulation of
chickpea
Shahzad
et al. (2014)
Sesame (Sesamum
indicum)
Organic fertilizer Serratia sp., B. polymyxa
and P. fluorescens
Irrigation water intervals (6, 9 and
12 days
The interaction effect among irrigation water intervals,
compost rates and bacterial inoculation were significant on all
estimated traits
Ismail
et al. (2013)
Cumin (Cuminum
cyminum)
Animal manure Pseudomonas putida and
P. fluorescence
Two irrigation treatments
(rainfall + 3 irrigations as water
stress and rainfall + 6 irrigations
as control)
Enhanced cumin seed and essential oil yields via improving soil
WHC
Seghatoleslami
(2013)
Giant cardon cactus
(Pachycereus pringlei)
Dairy cow
manure
Azospirillum brasilense Cd Natural barren desert soil Addition of small amounts of common compost; 6%– 25% of
the growth substrate gave the best growth response and, to a
lesser extent, so did inoculation with A. brasilense Cd
Bacilio
et al. (2006)
TABLE 4 (Continued)
14 
|
   ULLAH et AL.
BC, compost and PGPR, shoot length, shoot biomass, root length
and root biomass was significantly increased by 88%, 77%, 89%
and 74%, respectively as compared to uninoculated control under
drought stress. Moreover, an increase in chlorophyll and relative
water contents and reduction in electrolyte leakage was also ob-
served with the combined application of BC, compost, and PGPR.
It was also obser ved that BC and comp ost app lied together showe d
the highest population of P. fluorescens which may also help im-
prove the biological properties of the soil. To confirm these results,
more and more extensive studies involving different crops and
under different environmental conditions are required to authen-
ticate these observations. Moreover, the elucidation of different
mechanisms involved using state- of- the- art analytical techniques
is also required.
4 | MECHANISMS OF PLANT GROWTH
PROMOTION OF ORGANIC AMENDMENTS
AND PGPR UNDER DROUGHT STRESS
The application of BC and compost serves as a conditioner to im-
prove the organic matter in the soil, which subsequently enhances
the physicochemical and biological properties of the soil (Figures 2
and 3). The improvement in soil properties develops soil structure,
enhances WHC of the soil, and ultimately improved water use effi-
ciency under drought stress (Hale et al., 2011; Roberts et al., 2010).
BC remains stable in the soil and leads to slow degradation, which
ultimately serves as a long- term carbon source in soil (Lehmann
et al., 2009). The porous structure of BC serves as protection sites
for indigenous and foreign (inoculated) microbes especially PGPR
which directly or indirectly improve soil nutrient availability under
drought stress (Chen et al., 2014; Hale et al., 2014). Moreover, BC
improves soil porosity while decreases bulk density which ultimately
enhances water and nutrient availability to the plants under drought
stress (Chen et al., 2014). In case of compost, similar mechanisms as
in BC improve physicochemical and biological properties of the soil,
and ultimately water and nutrient availability is increased. Both com-
post and BC serve as carbon sources and carrier material for PGPR
(Hale et al., 2014).
PGPR are well renowned for enhancing crop growth and pro-
ductivity under normal and drought stress through various di-
rect and indirect mechanisms (Figure 4). Under drought stress,
PGPR reduce the production of ethylene via ACC- deaminase ac-
tivity. Increased production of ethylene via its precursor 1- amin
ocyclopropane- 1- carboxylic acid (ACC) during drought stress re-
duces root growth and ultimately leads to plant death (Arshad &
Frankenberger, 2002). During ethylene production, S- Adenosyl-
Methionine (SAM) is converted into ACC via ACC- synthase, which
is activ ate d unde r hig her le vels of in dole acet ic aci d (IA A) pro duc ed
und e r ab i o tic st re s s (P a rr a y et a l ., 20 16). PG PR wi th ACC- de am ina s e
are capable of converting ACC into ammonia and α- ketobutyrate,
thereby reducing ethylene production and ultimately enhanced
root growth and better water and nutrient availability especially
TABLE 5 Impact of biochar, compost and PGPR under drought stress
Crop Biochar Compost Inoculum Drought Stress Impact Reference
Maize
(Zea mays L.)
Grain husks
and paper
fibre sludge
Green waste and sewage
sludge from municipalities
Consortium of Bacillus aryabhattai,
Azospirillum brasilense (NF7),
Azospirillum brasilense (242/9),
Paenibacillus peoriae and Arthrobacter
crystallopoietes
The pots were watered
up to 65% of maximum
FC
The combined application of BC,
compost and PGPR did not result in
higher fertility on the investigated
soil. The mixture of compost and
PGPR with 1.5% BC resulted in
35% higher availability of P and
K due to higher microbial activity
relative to BC alone. Only compost
used on its own at 0.5% raised
maize biomass by 2.7 times.
Uzinger et al. (2020)
Cucumber
(Cucumis
sativus)
Pine wood Kelp meal, worm castings,
dehydrated poultry manure
and mycorrhizae
Pseudomonas fluorescens Three water levels i.e.
FC (D0), 75% FC (D1)
and 50% FC (D2)
Combined application increased
shoot length, shoot biomass, root
length and root biomass by 88%,
77%, 89% and 74%, respectively.
Also increase in population of
P. Fluorescens, improved chlorophyll
and relative water contents while
leaf electrolyte leakage was
reduced
Nadeem et al. (2017)
  
|
 15
ULLA H et AL.
under dr o ught st ress (S h a h aroon a et al ., 20 06 , 20 07 ) . PG PR ar e al so
known to enhance nutrient availability especially nitrogen through
BNF and P through P- solubilizing activity (Ditta et al., 2015; Ditta,
Imtiaz, et al., 2018; Ditta, Muhammad, et al., 2018). Under drought
stress, another mechanism employed by PGPR is the upregulation
of stress- responsive genes. For example, sbP5CS2 and sbP5CS1 in
sorghum were upregulated with the inoculation of multi- trait PGPR
and ultimately resulted in enhanced growth via induced stress tol-
erance (Govindasamy et al., 2020). Similarly, PGPR inoculation up-
regulated the genes involved in the regulatory component (CTR1)
of the ethylene signaling pathway (Barnawal et al., 2017), lipoxy-
genase pathway, and jasmonic acid pathway (Ahmad et al., 2019),
dehydrin proteins (Borovskii et al., 2002), ROS scavenging (Tiwari
et al., 2016), etc. Other mechanisms include the secretion of or-
ganic acids, production of phytohormones, acting as biocontrol
agents, etc. (Kasim et al., 2013; Rocha et al., 2019; Saharan &
Nehra, 2011).
5 | SUMMARY AND FUTURE
PERSPECTIVES
Under drought stress, reduced growth and development of crops
have been observed in many crops. For the sustainable manage-
me nt of dr ought str ess , it is im por tant to dev elop cer tain strat egies
that are efficient and low- cost to increase crop productivity.
These resource management strategies include the integrated use
of PGPR and organic amendments (compost, and BC). Figure 5
gives an overview of the impacts of drought stress on plants and
its amelioration through economical, environment- friendly, and
sustainable ways. These strategies help reduce environmental pol-
lution due to the usage of various organic wastes for BC and com-
post preparation and are environment- friendly. Numerous studies
have confirmed their efficacy in improving the growth and yield of
crops under drought stress. Algal BC is comparatively low in car-
bon content, surface area and cation exchange capacity, but high
in pH, ash, nitrogen, and extractable inorganic nutrients including
P, K, Ca and Mg. Th ere for e, alg al BC ha s prop erti es that pro vid e di-
rect nutrient benefits to soils and crop productivity under drought
stress.
In the case of integrated use of PGPR, compost and BC, very
few studies have been conducted under normal as well as under
abiotic stress conditions such as drought stress. In the future,
more rigorous studies are required to evaluate their additive ef-
fect during drought stress under field conditions. Moreover, in-
sights into the mechanisms behind the interaction of PGPR and
plants under drought stress need further investigation. For this
elucidation, employing various state- of- the- art molecular ap-
proaches would help find out the mechanisms behind their syn-
ergistic effect.
FIGURE 5 Overview of the impacts of drought stress on plants and its amelioration through economical, environment- friendly and
sustainable way
16 
|
   ULLAH et AL.
DATA AVA ILAB ILITY STATE MEN T
Data sharing not applicable to this article as no datasets were gener-
ated or analyzed during the current study
ORCID
Allah Ditta https://orcid.org/0000-0003-1745-4757
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Appraisal for organic amendments and plant growth-
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https://doi.org/10.1111/jac.12502
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