Aquatic Macrophytes Ecology Functions And Services 1st Edition Sanjeev Kumar

Aquatic Macrophytes Ecology Functions And
Services 1st Edition Sanjeev Kumar download
https://ebookbell.com/product/aquatic-macrophytes-ecology-
functions-and-services-1st-edition-sanjeev-kumar-53773866
Explore and download more ebooks at ebookbell.com

Here are some recommended products that we believe you will be
interested in. You can click the link to download.
Algae And Aquatic Macrophytes In Cities Bioremediation Biomass
Biofuels And Bioproducts Vimal Chandra Pandey
https://ebookbell.com/product/algae-and-aquatic-macrophytes-in-cities-
bioremediation-biomass-biofuels-and-bioproducts-vimal-chandra-
pandey-46086274
The Ecotoxicology Of Aquatic Macrophytes Mirta L Menone Chris Metcalfe
https://ebookbell.com/product/the-ecotoxicology-of-aquatic-
macrophytes-mirta-l-menone-chris-metcalfe-50421912
Macrophytes In Aquatic Ecosystems From Biology To Management
Proceedings Of The 11th International Symposium On Aquatic Weeds
European Weed Research Society 1st Edition I Bernez
https://ebookbell.com/product/macrophytes-in-aquatic-ecosystems-from-
biology-to-management-proceedings-of-the-11th-international-symposium-
on-aquatic-weeds-european-weed-research-society-1st-edition-i-
bernez-4287004
Aquatic Macrophyte Risk Assessment For Pesticides 1st Edition Lorraine
Maltby
https://ebookbell.com/product/aquatic-macrophyte-risk-assessment-for-
pesticides-1st-edition-lorraine-maltby-2496722

Aquatic Lectins Immune Defense Biological Recognition And Molecular
Advancements Preetham Elumalai
https://ebookbell.com/product/aquatic-lectins-immune-defense-
biological-recognition-and-molecular-advancements-preetham-
elumalai-47285810
Aquatic Adaptations In Mesoamerica Subsistence Activities In
Ethnoarchaeological Perspective Eduardo Williams
https://ebookbell.com/product/aquatic-adaptations-in-mesoamerica-
subsistence-activities-in-ethnoarchaeological-perspective-eduardo-
williams-50202300
Aquatic Medicinal Plants Archana Bachheti Rakesh Kumar Bachheti
https://ebookbell.com/product/aquatic-medicinal-plants-archana-
bachheti-rakesh-kumar-bachheti-50501694
Aquatic Ecosystems 1st Edition Sheila A Browne
https://ebookbell.com/product/aquatic-ecosystems-1st-edition-sheila-a-
browne-51742454
Aquatic Insects Of California With Keys To North American Genera And
California Species 4th Printing Reprint 2020 Robert L Usinger Editor
https://ebookbell.com/product/aquatic-insects-of-california-with-keys-
to-north-american-genera-and-california-species-4th-printing-
reprint-2020-robert-l-usinger-editor-51819692

Sanjeev Kumar · Kuldeep Bauddh ·
Ritu Singh · Narendra Kumar ·
Rajesh Kumar Editors
Aquatic
Macrophytes:
Ecology,
Functions and
Services

Aquatic Macrophytes: Ecology, Functions
and Services

Sanjeev KumarKuldeep Bauddh
Ritu SinghNarendra Kumar
Rajesh Kumar
Editors
Aquatic Macrophytes:
Ecology, Functions
and Services

Editors
Sanjeev Kumar
Department of Geology, School of Earth
and Environmental Sciences
Babasaheb Bhimrao Ambedkar University
Lucknow, Uttar Pradesh, India
Kuldeep Bauddh
Department of Environmental Sciences
Central University of Jharkhand
Ranchi, India
Ritu Singh
Department of Environmental Science
Central University of Rajasthan
Ajmer, India
Narendra Kumar
Department of Environmental Sciences
Babasaheb Bhimrao Ambedkar University
Lucknow, Uttar Pradesh, India
Rajesh Kumar
Department of Environmental Science
Central University of Rajasthan
Ajmer, India
ISBN 978-981-99-3821-6 ISBN 978-981-99-3822-3 (eBook)
https://doi.org/10.1007/978-981-99-3822-3
# The Editor(s) (if applicable) and The Author(s), under exclusive license to Springer Nature Singapore
Pte Ltd. 2023
This work is subject to copyright. All rights are solely and exclusively licensed by the Publisher, whether
the whole or part of the material is concerned, speci
illustrations, recitation, broadcasting, reproduction on micro
transmission or information storage and retrieval, electronic adaptation, computer software, or by
similar or dissimilar methodology now known or hereafter developed.
The use of general descriptive names, registered names, trademarks, service marks, etc. in this publication
does not imply, even in the absence of a speciﬁc statement, that such names are exempt from the relevant
protective laws and regulations and therefore free for general use.
The publisher, the authors, and the editors are safe to assume that the advice and information in this
book are believed to be true and accurate at the date of publication. Neither the publisher nor the authors or
the editors give a warranty, expressed or implied, with respect to the material contained herein or for any
errors or omissions that may have been made. The publisher remains neutral with regard to jurisdictional
claims in published maps and institutional afﬁliations.
This Springer imprint is published by the registered company Springer Nature Singapore Pte Ltd.
The registered company address is: 152 Beach Road, #21-01/04 Gateway East, Singapore 189721,
Singapore

Preface
Aquatic macrophyte basically refers to those plants that grow in or around water and
are visible to the naked eye. It comprises vascular (emergent, submerged, or
plants, bryophytes, and macro-algae ourishing in waterbodies. Aquatic
macrophytes play a crucial role in assessing the ecological status of waterbodies.
As primary producers, they form the basis of food webs, share a major part of highly
productive aquatic ecosystems, and have a signicant impression on ecosystem
functions and services. They play a signicant role in maintaining water quality,
enhancing biodiversity, supporting aquatic food webs, etc. These plants constitute
the elementary biotic component of the ecosystem and have an important role in
structuring communities of the aquatic environment and nutrient cycling.
Macrophytes are also known to strongly inuence the micro-climate and biogeo-
chemical processes occurring in littoral zones of marine ecosystems and sediment
dynamics of freshwater systems. Aquatic macrophytes are also important for
mitigating the impacts of climate change. They serve as the most effective carbon
sinks and play an important role in carbon sequestration, which helps in reducing
greenhouse gas emissions and mitigating the effects of climate change. In addition,
they provide important ecosystem services, such as water purication and ood
control, which can help to reduce the negative impacts of climate change on human
societies. Apart from these, aquatic macrophytes play an important role in the area of
environmental clean-up. Remediation through these plants is considered as an easy,
cost-effective, eco-friendly, and energy-efcient method of decontamination. These
macrophytes help to remove organic and inorganic impurities as well as engineered
nanoparticles from contaminated water. Their self-purication utilities con
maintenance of water quality. Aquatic macrophytes is a key component of wetland
systems also, contributing much of the total ecosystem biomass. Besides their
presence in urban areas improves the aesthetic value of landscapes, contributing to
human well-being and quality of life. An understanding of the functions of aquatic
macrophytes in wetlands systems is critical for understanding the elementary pro-
cesses of the ecosystem and associated issues, such as restoration of ecological
integrity in the wetland ecosystem, wastewater treatment, and management of hostile
invasive/alien species.
Despite their critical importance, aquatic macrophytes face numerous threats,
including habitat loss, pollution, and invasive species. In the past three decades,
v

due to climate-induced changes and altered land use patterns, signi
the status, growth prole, general distribution, and abundance of these communities
have been recorded, which are likely to have a huge ecological impact on the
structural and functional part of the aquatic ecosystems on a global scale. Since
aquatic macrophytes are considered as the keystone species of aquatic ecosystems,
they are much prone to climate-induced changes; therefore, the knowledge of the
impacts of changing climate on the growth patterns, distribution, abundance, and
productivity of these plants with its probable implications are very much required in
present time. The study of their ecological functions and services is crucial for
understanding the impacts of these threats on aquatic ecosystems and developing
effective management strategies to protect them. For instance, understanding how
aquatic macrophytes respond to pollution can help to identify pollution hotspots and
develop strategies to reduce pollution levels. Similarly, understanding how invasive
species impact aquatic macrophytes can help to develop strategies to control inva-
sive species and prevent their spread.
vi Preface
This book is an attempt to document the information available on aquatic
macrophytes
able management of aquatic ecosystems and the benets of human society. The book
highlights several aspects of aquatic macrophytes, such as their role in nutrient
recycling, biogeochemical processes in the water column and sediments, biomass
production, wetland ecosystems, water resource management, carbon sequestration,
environmental clean-up, and bioenergy production. The book presents the current
status of aquatic macrophytes and highlights the major challenges towards
exploiting the benets served by aquatic macrophytes as ecosystem services. This
book will be benecial as a source of educational material for graduates and post-
graduate students, faculties, researchers, policymakers, and industrial personnel who
are engaged in assessing the functions of aquatic macrophytes in the natural envi-
ronment. It could also serve as a reference book for research scholars, scientists,
academicians, and readers from diverse backgrounds across various elds such as
ecology, environmental science, biology, biogeochemistry, wetland conservation,
phytoremediation, biomonitoring, wastewater management, and bioenergy produc-
tion. We hope that the chapters of this book will provide readers with valuable
insights into the varied aspects of the ecological functions and services offered by
aquatic macrophytes.
Lucknow, India Sanjeev Kumar
Ranchi, India Kuldeep Bauddh
Ajmer, India Ritu Singh
Lucknow, India Narendra Kumar
Ajmer, India Rajesh Kumar

Contents
1 An Introduction to the Functions and Ecosystem Services Associated
with Aquatic Macrophytes 1
Sanjeev Kumar, Ritu Singh, Dhananjay Kumar, Kuldeep Bauddh,
Narendra Kumar, and Rajesh Kumar
2 Factors Structuring Aquatic Macrophytes 21
Takudzwa C. Madzivanzira, Julie A. Coetzee, and Tatenda Dalu
3 Aquatic Macrophytes: Ecology, Function, and Services in Niger
Delta, Nigeria 53
H. E. Dienye
4 Environmental and Ecological Importance of Indian Aquatic
Macrophytes 71
Vimlesh Rawat and Amit Kumar Singh
5 Macrophytes Used as Complementary Medicines for Curing Human
Ailments to Facilitate Livelihood Opportunities 85
R. Bar and R. N. Mandal
6 Macrophytes and Their Role in Wetland Ecosystems 119
Arif J. Siddiqui, Sadaf Jahan, Mohd Adnan, Syed Amir Ashraf,
and Ritu Singh
7 Ecotoxicology of REEs in Aquatic Macrophytes and Prospect for
Bioremediation of REEs 139
Rajni Choudhary, Sana Parveen, and Shailesh Kumar Patidar
8 Ef 159
Dhananjay Kumar, Urvashi Sharma, Vishal Singh,
Aneet Kumar Yadav, Anita, Sanjeev Kumar, and Narendra Kumar
9 Phytoremediation of Organic Contaminants: An Eco-friendly
Approach-Based Application of Aquatic Macrophytes . 175
Ritu Singh, Avimanu Sharma, Prakriti Goswami, Dhiraj Pradhananga,
Deepak Aryal, Soni M. Pradhanang, and Rajesh Kumar
viivii

viii Contents
10 Remediation of Heavy Metals by Different Aquatic Macrophytes 207
Monalisa Mohanty
11 Translocations of Heavy Metals in Aquatic Macrophytes Naturally
Grown in the Riverine Ecosystem 221
Sushil Kumar Bharti, Narendra Kumar, and Nandkishor S. More
12 Enhanced Efuent Treatment and Bioelectricity Generation Using
Coupled Constructed Wetland-Microbial Fuel Cell (CW-MFC)
Technology: Challenges and Opportunities 237
Himani Chandel, Kashika Keshari, Sibiraj Murugesan, Rahul Yadav,
Kirti Shyam, Navneet Kumar, Geetansh Sharma, and Gaurav Saxena
13 Role of Microbial Communities and Aquatic Macrophytes in
Constructed Wetlands for Tannery Wastewater Treatment:
Challenges and Opportunities 261
Navneet Kumar, Prachi Bhatnagar, Rahul Yadav, Himani Chandel,
Sibiraj Murugesan, Geetansh Sharma, and Gaurav Saxena
14 Role of Plant-Bacteria Association in Constructed Wetlands for the
Removal of Iron (Fe) from Contaminated Water 297
Nopi Stiyati Prihatini and Soemarno

About the Authors
Sanjeev Kumar
Babasaheb Bhimrao Ambedkar University, Lucknow, India. Currently, he is work-
ing as an Assistant Professor in the Department of Geology at the same university.
Dr. Kumar has made signicant contributions in the eld of sustainable agriculture,
focusing on various aspects such as soil quality management, agriculture gaseous
emissions, slow-release fertilizers, and phytoremediation. His research endeavors
aim to develop innovative approaches for enhancing agricultural practices while
minimizing environmental impacts.
Kuldeep Bauddh
ronmental Sciences at the Central University of Jharkhand, Ranchi, India. He
received his M.Sc. and Ph.D. in Environmental Science from Babasaheb Bhimrao
Ambedkar University, Lucknow, India. Dr. Bauddh is currently teaching thrust areas
of environmental sciences like environmental pollution and management, environ-
mental impact assessment, environmental toxicology, etc. His major research areas
include environmental pollution and management, phytoremediation, and restora-
tion of abandoned mining sites.
Ritu Singh an Assistant Professor in the Department of Environmental Science,
School of Earth Sciences at the Central University of Rajasthan, Ajmer, India. She
received her Ph.D. in Environmental Science from the Indian Institute of Toxicology
Research (CSIR-IITR), Lucknow, and Babasaheb Bhimrao Ambedkar University,
Lucknow, Uttar Pradesh, India. She is actively involved in teaching and research in
the eld of environmental chemistry, environmental toxicology, and wastewater
treatment. Her research primarily focuses on the potential of metal nanoparticles
and nanocomposites for various environmental applications, including remediation
of emerging contaminants and wastewater treatment. She has a keen interest in the
study of nano-agro particles, exploring their applications in agriculture and environ-
mental remediation.
ixix

x About the Authors
Narendra Kumar
is currently the Head of the Department of Geology, Babasaheb Bhimrao Ambedkar
University, Lucknow, India. Dr. Kumar has made signicant contributions to vari-
ous areas of environmental science, including phytoremediation, air and water
pollutants, and wastewater treatment. His work involves exploring the capabilities
of different plant species in removing or degrading pollutants from contaminated
soil, water, and air. In addition to his expertise in phytoremediation, he has also
contributed to the eld of river ecology. He studies the ecological health and
dynamics of rivers, including their biodiversity, water quality, and the impact of
anthropogenic activities on river ecosystems.
Rajesh Kumar
presently serves as the Dean of the School of Earth Sciences at the Central University
of Rajasthan, Ajmer, India. He earned his M.Sc. (Tech.) and Ph.D. in Geophysics
specialization in Meteorology, from Banaras Hindu University (BHU), Varanasi,
India. With 23 years of experience in teaching and research, Dr. Kumar has made
signi
tise lies in the study of air pollution and its impact on human health, climate change,
arid and desert environments, as well as the application of remote sensing and
Geographic Information System (GIS). His current research focuses on the elds
of air pollution, climate change, and the Himalayan cryosphere.

An Introduction to the Functions
and Ecosystem Services Associated
with Aquatic Macrophytes
1
Sanjeev Kumar, Ritu Singh, Dhananjay Kumar, Kuldeep Bauddh,
Narendra Kumar, and Rajesh Kumar
Abstract
In recent decades, aquatic macrophytes have been recognized as a signiﬁcant com-
ponent of aquatic ecosystems, which play an important role in providing environ-
ment and ecosystem services. Aquatic macrophytes also play a key role in the
production of bioenergy, biochar formation, climate change, photosynthesis, etc.
The presence and activity of macrophytes enhance sediment formation, carbon
sequestration, natural water puriﬁcation, remediation of organic and inorganic
pollutants, etc. in the aquatic ecosystem. They also provide natural medicines,
ﬁbers, biochemicals, and other resources to the human society. There are several
evidences that macrophyte diversity enhances the functioning, services, and stabil-
ity of the ecosystem and provides multiple beneﬁts to human well-being. This
chapter delves into the functions and ecosystem services associated with aquatic
macrophytes, which play a crucial role in maintaining the health and sustainability
of aquatic ecosystems and signiﬁcantly impact the well-being of human societies.
S. Kumar (✉) · D. Kumar
Department of Geology, School of Earth and Environmental Sciences, Babasaheb Bhimrao
Ambedkar University, Lucknow, Uttar Pradesh, India
R. Singh · R. Kumar
Department of Environmental Science, School of Earth Sciences, Central University of Rajasthan,
Ajmer, Rajasthan, India
e-mail: [email protected]; [email protected]
K. Bauddh
Department of Environmental Science, School of Earth Sciences, Central University of Jharkhand,
Ranchi, Jharkhand, India
e-mail: [email protected]
N. Kumar
Department of Environmental Science, Babasaheb Bhimrao Ambedkar University, Lucknow, Uttar
Pradesh, India
# The Author(s), under exclusive license to Springer Nature Singapore Pte
Ltd. 2023
S. Kumar et al. (eds.),
https://doi.org/10.1007/978-981-99-3822-3_1
1

2 S. Kumar et al.
Keywords
Ecosystem services · Environment · Macrophyte · Remediation · Pollutant
1.1 Introduction
Aquatic macrophytes constitute the elementary biotic component of the ecosystem
and have an important role in structuring communities of the aquatic environment
and nutrient cycling (Thomaz 2021; Lind et al. 2022). Basically, aquatic
macrophytes are large aquatic plants that grow in water bodies such as lakes,
ponds, rivers, and wetlands. There are many types of aquatic macrophytes, including
submerged plants, oating-leaved plants, and emergent plants (Chambers et al.
2008), as shown in Fig. 1.1. Submerged plants grow entirely underwater and can
be found at various depths in the water column, while
leaves that
(Chambers et al. 2008). Emergent plants grow partially or fully above the water
surface, with their roots anchored in the substrate and their leaves and stems rising
above the water (Chambers et al. 2008).
Aquatic macrophytes play an important role in the food chain and food web of
aquatic ecosystems (Bornette and Puijalon 2011). They provide food, shelter, and
habitat for a wide range of organisms, from tiny microorganisms to large
other aquatic animals (Bornette and Puijalon 2011; Engelhardt and Ritchie 2001). In
the food chain, aquatic macrophytes are the primary producers or the rst organisms
to convert sunlight into organic matter through the process of photosynthesis
(Bornette and Puijalon 2011). They produce a range of organic compounds, such
as carbohydrates, proteins, and lipids, that are used as food by herbivorous aquatic
animals, such as snails, insects, and some
habitat for a variety of organisms, including sh, amphibians, and aquatic
invertebrates. These animals use the plants as shelter and breeding grounds and
also as a source of food. For example, many sh species feed on insects that live on
or near the plants or on smaller sh that use the plants as cover. The presence of
aquatic macrophytes can also affect the structure and function of the food web in an
aquatic ecosystem. For example, in systems with dense macrophyte growth,
predators may be able to hunt and capture prey more easily, while herbivores may
consume a greater proportion of the available primary production. This signies that
aquatic macrophytes have a signicant role in supporting the diversity and produc-
tivity of aquatic ecosystems, and their presence is an important indicator of the
overall health of these systems (Ferna 1999; Ppalov2002;
Akasaka et al. 2010; Mikulyuk et al. 2011; Fernandez-Alaez et al. 2018).
Aquatic macrophytes are a major component of aquatic ecosystems and provide
many services to the environment, ecosystem, and humans (Thomaz 2021). Aquatic
macrophytes play a crucial role in assessing the ecological status of water bodies.
They are known to strongly in
cesses occurring in littoral zones of marine ecosystems and sediment dynamics of

freshwater systems. They serve as the most effective carbon sinks and play an
important role in carbon sequestration (Ankit et al. 2020; Lolu et al. 2019). Apart
from these, aquatic macrophytes play an important role in the area of environmental
clean-up (Ankit et al. 2020; Kumar et al. 2019). Remediation through these plants is
considered as an easy, cost-effective, eco-friendly, and energy-efcient method of
decontamination (Ankit et al. 2020; Kumar et al. 2019). These macrophytes help to
remove organic and inorganic impurities as well as engineered nanoparticles from
contaminated water (Ankit et al. 2020; Kumar et al. 2019; Anand et al. 2018; Mishra
et al. 2013). Their self-purication utilities conrm the maintenance of water quality
(Fawzy et al. 2012; Dhote and Dixit 2009). Aquatic macrophytes are the key
component of wetland systems, contributing much of the total ecosystem biomass
1 An Introduction to the Functions and Ecosystem Services Associated
Fig. 1.1

(Adhikari et al. 2009; Ankit et al. 2020). Despite their important ecological roles,
aquatic macrophytes can also cause problems in some situations. For example,
excessive growth of macrophytes can lead to oxygen depletion in the water column
and cause the death of sh and other aquatic animals. They can also impede water
ﬂow and navigation in rivers and canals and interfere with recreational activities
such as swimming and boating. Overall, aquatic macrophytes are important and
complex components of aquatic ecosystems, and their management requires careful
consideration of both their ecological benets and potential drawbacks. The present
chapter highlights the various functions and services of aquatic macrophytes to
better understand the elementary processes of the ecosystem and associated areas
such as restoration of ecological integrity in wetland ecosystem, wastewater treat-
ment, management of hostile invasive/alien species, etc.
4 S. Kumar et al.
1.2 Ecosystem Functions and Services Associated with Aquatic
Macrophytes
Ecosystem services are the ecological characteristics, functions, or processes that
directly or indirectly contribute to human well-being, the benets people derive from
functioning ecosystems. The Millennium Ecosystem Assessment (2005) categorized
ecosystem services into four different types, i.e., provisioning services, regulating
services, cultural services, and supporting services (Fig. 1.2). Provisioning services
are the benets that humans derive from ecosystems that involve the production of
natural resources. These services include food, water, timber,
other products that are directly extracted from ecosystems. For example, forests
provide timber for construction, fuel, and paper production. Agriculture provides
food crops, livestock, and sh. These services are critical for human survival and
form the basis of many economies worldwide. Regulating services refer to the
benets that ecosystems provide by regulating the physical and chemical conditions
of the environment. These services include climate regulation, ood control, water
purication, and pollination. For example, wetlands and forests absorb and store
carbon dioxide, which helps in regulating the Earth lter
and purify water, reducing the risk of oods and erosion. Pollination services
Fig. 1.2

provided by bees and other insects are critical for crop production and food security.
Cultural services are the non-material benets that humans derive from ecosystems.
These services include recreation, tourism, aesthetic enjoyment, and cultural and
spiritual values. For example, natural parks, beaches, and other scenic landscapes
provide opportunities for outdoor recreation and tourism. Ecosystems also have
cultural and spiritual signicance for many societies and communities, as they
provide a sense of connection to the natural world and a source of inspiration and
identity. Supporting services are the underlying services that are necessary for the
production of other ecosystem services. These services include soil formation,
nutrient cycling, and primary productivity. For example, soil formation is essential
for the growth of crops, while nutrient cycling and primary productivity are neces-
sary for the production of food, ber, and other ecosystem services. These services
are critical for maintaining the structure and function of ecosystems and for sustain-
ing human well-being (Daily et al. 2009; de Groot et al. 2010; Mace et al. 2012).
Each of these categories provides a range of benets that are critical for maintaining
healthy and functioning ecosystems and for sustaining human societies and
economies. Aquatic macrophytes are the key component of freshwater and marine
ecosystems, and they offer various ecological services, which are critical for the
health and sustainability of the ecosystems and for the well-being of human
societies, as represented in Fig. 1.3. All the ecosystem services are interrelated
with each other and cannot be considered in isolation. The following sections
presents an overview of the function and services of the aquatic macrophytes.
1 An Introduction to the Functions and Ecosystem Services Associated
Fig. 1.3

6 S. Kumar et al.
1.2.1 Primary Production
Primary production refers to the conversion of light energy into organic matter by
photosynthetic organisms. Aquatic macrophytes have a signicant inuence on
primary production in aquatic ecosystems (Kazanjian et al. 2018; Nõges et al.
2010). They contribute to primary production directly through photosynthesis and
indirectly by altering nutrient availability and water chemistry (Thomaz 2021;
Reitsema et al. 2020; Amir et al. 2019). Aquatic macrophytes have high photosyn-
thetic rates and contribute a signicant amount of organic matter to the ecosystem.
They provide a substrate for the attachment of algae and other small organisms,
which can grow and multiply on their surfaces. This can increase the overall
photosynthetic activity in the ecosystem, leading to higher primary production.
Further, aquatic macrophytes provide shelter and protection for small organisms
from predation, which can lead to higher growth rates and higher biomass of these
organisms. This, in turn, could lead to increased nutrient recycling, thus stimulating
primary production (Thomaz 2021). Besides, aquatic macrophytes could alter the
physical and chemical characteristics of the water column, creating microhabitats
that are more conducive to the growth and survival of photosynthetic organisms. For
example, they can reduce water ow and increase sediment deposition, which can
provide a nutrient-rich environment for plant growth. Aquatic macrophytes can also
inuence primary production by altering the light regime in the water column. They
can absorb and scatter light, which can reduce the amount of light available to other
photosynthetic organisms, and can also create shaded areas that are more suitable for
the growth of certain types of algae. Overall, the inuence of aquatic macrophytes on
primary production is signicant, and their presence or absence could have impor-
tant implications for the structure and function of aquatic ecosystems (Reitsema et al.
2020; Amir et al. 2019).
1.2.2 Food Source
Aquatic macrophytes provide food for a variety of aquatic animals and humans
(He et al. 2021; Yasuno et al. 2021). Many herbivorous
crustaceans, and other aquatic organisms feed on aquatic plants as a signicant
part of their diet. Additionally, some aquatic plants, such as water chestnuts and
lotus roots, are consumed by humans as food. They are commonly used in Asian
cuisine. Some other common examples of aquatic macrophytes that provide food
include water lilies, duckweed, and water hyacinth. These plants contain essential
nutrients like carbohydrates, proteins, vitamins, minerals, fats, and bers that can be
used by aquatic organisms as a source of energy and building blocks for growth
(He et al. 2021; Yasuno et al. 2021). For example, watercress is a popular leafy green
that is often used in salads and sandwiches. It is high in vitamin C, iron, and calcium.
Other aquatic plants that are commonly used as food include seaweed, which is a
popular ingredient in sushi and other Japanese dishes, and kelp, which is used in
many different types of food products. In addition to providing direct food for

aquatic organisms, aquatic macrophytes also play an important role in the food chain
by supporting the growth of phytoplankton and other small organisms that are the
foundation of the aquatic food web (He et al. 2021; Yasuno et al. 2021). Therefore,
the presence of aquatic macrophytes can have cascading effects on the overall health
and productivity of aquatic ecosystems.
1 An Introduction to the Functions and Ecosystem Services Associated
1.2.3 Habitat and Shelter
Aquatic macrophytes provide important habitat and shelter for a wide variety of
aquatic organisms (Haroon 2022; Dorn et al. 2001). These plants create a complex
three-dimensional structure in the water column, providing hiding places, resting
areas, and breeding grounds for many aquatic species. The leaves, stems, and roots
of aquatic macrophytes provide shelter for small aquatic invertebrates, such as snails,
insects, and crustaceans. These invertebrates, in turn, provide food for larger aquatic
animals, such as sh and amphibians, which also use the macrophytes as habitat
(Haroon 2022; Dorn et al. 2001). In addition to providing shelter, aquatic
macrophytes also help to create diverse microhabitats within aquatic ecosystems.
Different species of macrophytes have different structures and chemical
compositions, creating a variety of niches for different species of aquatic organisms
(Haroon 2022; Quirino et al. 2021; Dorn et al. 2001). The roots and rhizomes of
aquatic macrophytes also provide a substrate for periphyton, which are communities
of algae, bacteria, and other microorganisms that grow on surfaces in aquatic
environments. These periphyton communities provide additional food and habitat
for aquatic organisms (Quirino et al. 2021; Dorn et al. 2001). The presence of aquatic
macrophytes is critical for maintaining the diversity and abundance of aquatic
organisms in freshwater and saltwater ecosystems, making their conservation and
management important for the health and sustainability of these systems.
1.2.4 Nutrient Recycling
Aquatic macrophytes play a signi
2018; O 2014). These plants absorb nutrients such as nitrogen and
phosphorus from the water column and sediments, which are further used for growth
and reproduction. Their roots and rhizomes provide a substrate for the growth of
microorganisms, which break down the organic matter and release nutrients
(Kazanjian et al. 2018; O 2014; Lawniczak et al. 2010). They can take
up nutrients from the sediment also and prevent their release into the water column,
reducing the potential for nutrient pollution. Additionally, they release oxygen
during photosynthesis, which can enhance microbial activity and promote nutrient
cycling. Furthermore, when macrophytes die or shed their leaves, the organic matter
they release serves as a source of nutrients for other organisms (Kazanjian et al.
2018). Microbes in the sediment break down this organic matter, releasing nutrients
back into the water column, where they can be taken up by other plants or used by

other organisms. Macrophytes also inuence the water ow and turbulence, thereby
affecting sediment deposition and nutrient availability. Altogether, aquatic
macrophytes help to maintain nutrient cycling and improve water quality in aquatic
ecosystems (O 2014; Lawniczak et al. 2010). However, their excessive
growth could lead to eutrophication and other ecological problems, so it is important
to manage these systems carefully to maintain a healthy and balanced ecosystem.
8 S. Kumar et al.
1.2.5 Soil/Sediment Stabilization
Aquatic macrophytes play a crucial role in inuencing soil/sediment in aquatic
environments (Ali et al. 2021; Roelofs et al. 2002). They can affect sediment
composition, structure, and stability, as well as the biogeochemical processes that
occur within sediments. Aquatic macrophytes can help to stabilize sediment by
reducing water velocity, which prevents erosion and sediment transport (Ali et al.
2021; Roelofs et al. 2002). The plant roots also provide physical binding of the
sediment, preventing it from being resuspended. Macrophytes also trap sediment and
organic matter within their root systems, leading to the accumulation of sediment
and creation of new habitats. This accumulation of sediment can also help to increase
water clarity by removing suspended particles. Besides, macrophytes alter sediment
biogeochemistry (Thomaz 2021). They take up nutrients such as nitrogen and
phosphorus from the sediment, thereby reducing nutrient concentrations in the
water column. This can reduce the likelihood of harmful algal blooms and promote
the growth of desirable macrophyte species. Additionally, the macrophytes increase
the oxygen concentration in sediment via photosynthesis, creating a more hospitable
environment for the microbial communities that carry out the decomposition of
organic matter and recycle nutrients (Amir et al. 2019; Roelofs et al. 2002). Overall,
aquatic macrophytes can play an important role in shaping sediment dynamics in
aquatic ecosystems, with implications for water quality, habitat creation, and nutrient
cycling (Thomaz 2021; Reitsema et al. 2020; Amir et al. 2019).
1.2.6 Hydrologic Cycle and Regulation
Aquatic macrophytes play an important role in the water cycle and regulation (Keitel
et al. 2016; Sharip et al. 2012). Aquatic macrophytes absorb and store large amounts
of water from the surrounding environment, which helps in regulating the water level
in water bodies and reduces the volume of water available for runoff or evapotrans-
piration (Keitel et al. 2016; Sharip et al. 2012). This could further help in preventing
ﬂooding during periods of heavy rainfall and maintain water availability during dry
spells. Aquatic macrophytes release water vapor into the atmosphere through tran-
spiration, which contributes to the formation of clouds and precipitation (Madsen
et al. 2001; Kurilenko and Osmolovskaya 2006). This process also helps to regulate
the temperature and humidity of the surrounding environment. In addition, they help
in ltering and purifying water by absorbing nutrients and pollutants, which in turn

improves the water quality and reduces the risk of harmful algal blooms. Aquatic
macrophytes also help in stabilizing the sediment in water bodies, reducing erosion
and sedimentation, which further assist in maintaining the water ow and preventing
the sediments from accumulating in the water body (Keitel et al. 2016; Sharip et al.
2012; Kurilenko and Osmolovskaya 2006). Thus, the presence of aquatic
macrophytes has important effects on the hydrologic cycle of aquatic ecosystems,
contributing to water storage, nutrient cycling, and sedimentation processes.
1 An Introduction to the Functions and Ecosystem Services Associated
1.2.7 Aesthetic and Recreational Value
Aquatic macrophytes provide aesthetic and recreational value in aquatic
environments (Hunt et al. 2019; Tallar and Suen 2017). Their presence can enhance
the beauty of water bodies and provide opportunities for recreational activities such
as shing, boating, and bird-watching. The diverse forms and colors of aquatic
macrophytes can add visual interest to water bodies, creating a natural landscape
that attracts people to visit and enjoy them (Smith et al. 2015; Hunt et al. 2019).
Floating-leaved plants such as water lilies and lotus can be particularly visually
striking, with their large, showy owers and broad leaves. They also provide habitat
for sh and other aquatic animals, making them popular shing spots. Fishermen
often target areas with dense macrophyte growth because these areas are likely to be
home to a variety of sh species. In addition to shing, aquatic macrophytes provide
opportunities for other recreational activities such as kayaking, canoeing, and paddle
boarding. These activities are often enjoyed in areas with calm, shallow water where
aquatic macrophytes are abundant. The aesthetic and recreational value provided by
aquatic macrophytes can contribute to the economic and social well-being of local
communities, making their conservation and management important for the
sustainability of these systems (Püger et al. 2010; Smith et al. 2015; Hunt et al.
2019; Tallar and Suen 2017).
1.2.8 Water Purification
Aquatic macrophytes help in removing various nutrients, pollutants, and organic
matter from water bodies through various mechanisms (Ankit et al. 2020; Kumar
et al. 2019; Anand et al. 2018; Mishra et al. 2013). One of the primary ways that
aquatic macrophytes help to purify water is through their ability to take up and use
nutrients such as nitrogen and phosphorus (Anand et al. 2018). These nutrients are
often present in excessive amounts in water bodies due to agricultural runoff, sewage
discharge, and other human activities. By absorbing these nutrients, the macrophytes
help in reducing the excess concentration of nutrients in the water, which would
prevent algal blooms and other forms of water pollution (Töre and Özkoç 2022;
Ankit et al. 2020). Moreover, aquatic macrophytes provide habitat for
microorganisms that break down the contaminants present in the water bodies.
The roots of the plants provide a surface for these microorganisms to attach to,

and the plants themselves can take up some of the pollutants and convert them into
non-toxic forms (Fawzy et al. 2012; Anand et al. 2018). Additionally, the physical
presence of aquatic macrophytes improves the water quality by reducing sedimenta-
tion and erosion. The plants help to stabilize sediments on the bottom of the water
body, which prevents the further release of nutrients and other pollutants into the
water column (Srivastava et al. 2008; Fawzy et al. 2012; Anand et al. 2018). In
summary, aquatic macrophytes play a vital role in maintaining the health of aquatic
ecosystems and in ensuring the availability of clean water for societal use (Ankit
et al. 2020; Kumar et al. 2019; Anand et al. 2018).
10 S. Kumar et al.
1.2.9 Remediation
Aquatic macrophytes act as remediation agents by removing or reducing pollutants
from aquatic ecosystems (Anand et al. 2018; Bhaskaran et al. 2013; Yadav et al.
2023). This process is known as phytoremediation, and it involves the use of plants
to clean up contaminated soil or water. Aquatic macrophytes can remediate
pollutants through a variety of mechanisms. For example, they can absorb nutrients
such as nitrogen and phosphorus from the water column, which can reduce the
growth of harmful algae and improve water quality. Additionally, some macrophytes
can take up heavy metals such as lead, cadmium, and mercury from the water and
store them in their tissues, effectively removing these pollutants from the ecosystem.
This process is known as phytoextraction. In addition to nutrient and metal removal,
aquatic macrophytes can also help to break down organic pollutants such as
pesticides and herbicides through a process called phytodegradation (Mishra et al.
2013; Anand et al. 2018). In this process, the plant roots release enzymes and other
chemicals that break down the pollutants, making them less toxic or even non-toxic.
Overall, the use of aquatic macrophytes as remediation agents has several potential
benets. First, it can provide a natural, low-cost method for removing pollutants
from aquatic ecosystems. Second, it can promote the restoration and conservation of
aquatic habitats by reducing the impact of pollution on aquatic animals and plants.
Finally, it can help to improve water quality and reduce the risk of harmful algal
blooms and other negative impacts of pollution on human health and the environ-
ment (Anand et al. 2018; Bhaskaran et al. 2013; Yadav et al. 2023).
However, it is important to note that the effectiveness of phytoremediation using
aquatic macrophytes can vary depending on a variety of factors, including the type
and concentration of pollutants present in the ecosystem, the type of macrophyte
species used, and the environmental conditions of the ecosystem. As such, careful
monitoring and management are necessary to ensure the effectiveness and safety of
using aquatic macrophytes for remediation purposes.

1 An Introduction to the Functions and Ecosystem Services Associated
1.2.10 Carbon Sequestration
Carbon sequestration is the process of removing carbon dioxide from the atmosphere
and storing it in carbon sinks, such as plants, soils, and oceans (Nag et al. 2023;
Ankit et al. 2020; Lolu et al. 2019; Pal et al. 2017). Aquatic macrophytes are able to
sequester carbon from the atmosphere through the process of photosynthesis. During
photosynthesis, carbon dioxide is taken up from the surrounding water and used to
build organic molecules, such as carbohydrates, which are stored in the plant tissues
(Bloom et al. 2010; Kayranli et al. 2010). The carbon in these organic molecules can
then be stored for long periods of time, potentially for centuries or even millennia, in
the sediment at the bottom of the water body. The amount of carbon sequestered by
aquatic macrophytes can vary depending on a variety of factors, such as the species
of macrophyte, the environmental conditions in the water body, and the level of
disturbance or management of the ecosystem (Lolu et al. 2019; Pal et al. 2017).
However, studies have shown that aquatic macrophytes can be an important carbon
sink in aquatic ecosystems, especially in wetland habitats such as marshes and
swamps (Nag et al. 2023; Ankit et al. 2020). Carbon sequestration by aquatic
macrophytes can have important implications for mitigating climate change. By
removing carbon dioxide from the atmosphere and storing it in aquatic ecosystems,
macrophytes can help to reduce the concentration of greenhouse gases in the
atmosphere, thereby reducing the rate of global warming (Bloom et al. 2010;
Kayranli et al. 2010; Lolu et al. 2019; Pal et al. 2017).
1.2.11 Climate Change
Aquatic macrophytes play several roles in climate change, both as a result of their
ability to sequester carbon and their responses to changing environmental conditions
(Zhou et al. 2021; Pereira et al. 2021; Hossain et al. 2017). As mentioned in
the above section, aquatic macrophytes sequester signicant amounts of carbon
from the atmosphere through the process of photosynthesis. This carbon is then
stored in the plant tissue and in the sediment at the bottom of the water body, making
it unavailable for release into the atmosphere as carbon dioxide (Zhou et al. 2021;
Pereira et al. 2021). This carbon sequestration by aquatic macrophytes helps to
reduce the concentration of greenhouse gases in the atmosphere, thereby mitigating
climate change. The conversion rate of atmospheric carbon varies along the longitu-
dinal gradient as the plant
insolation, and cold temperature (Adhikari et al. 2009). Aquatic macrophytes also
affect the emission of methane (CH
4), a potent greenhouse gas, from aquatic
ecosystems. Some studies have shown that dense macrophyte growth can reduce
CH4 emission by creating anoxic zones in the sediment, which limit the activity of
methane-producing microorganisms. In contrast, other studies have suggested that
macrophytes can also enhance CH4 emission by promoting the growth of methane-
producing microorganisms. The quantity of generation and absorption of atmo-
spheric CH
4 depends on the water table of wetlands (Moore and Dalva 1993). It

has been reported that 20 4 emissions are emitted by
wetlands, which is around 15 4 per year, and in this, the contribution of
rice paddies alone is around 60 2010).
12 S. Kumar et al.
Aquatic macrophytes also play a role in regulating the temperature of aquatic
ecosystems. The dense growth of macrophytes can provide shade and cooling effects
in the water column, which can help to mitigate the effects of rising water
temperatures due to climate change. Additionally, macrophytes help to regulate
the oxygen content of aquatic ecosystems, which could also be impacted by changes
in temperature and other environmental factors. Coastal wetlands, which are often
dominated by aquatic macrophytes, could provide a buffer against storm surges and
sea level rise. These wetlands could help to protect coastal communities and
infrastructure from the impacts of climate change-induced extreme weather events
(Zhou et al. 2021; Pereira et al. 2021; Hossain et al. 2017).
However, the responses of aquatic macrophytes to climate change are complex
and not always predictable. Changes in water temperature, precipitation patterns,
and other environmental factors could impact the growth and distribution of
macrophytes, potentially altering the balance of aquatic ecosystems. For instance,
in some cases, warming temperatures and altered precipitation patterns may lead to
increased growth of invasive macrophyte species, which could outcompete native
species and reduce the biodiversity of aquatic ecosystems. The roles of aquatic
macrophytes in climate change are complex and multifaceted, highlighting the
importance of understanding the interactions between these plants and their
environments in order to develop effective strategies for mitigating and adapting
to the impacts of climate change (Xia et al. 2022; Zhou et al. 2021).
1.2.12 Biochar
Biochar is a type of charcoal obtained from the thermochemical conversion of
biomass in an oxygen-limited environment. Aquatic macrophytes are one such
organic material that can be used to synthesize biochar (Kumari et al. 2021). Aquatic
macrophytes are often harvested from lakes, rivers, and other bodies of water to
manage their growth and prevent them from becoming invasive. These harvested
plants can then be dried and converted into biochar through pyrolysis. Besides
pyrolysis, gasication and carbonization method has also been used to convert
aquatic plants into biochar (Yaashikaa et al. 2020; Cui et al. 2022).
Biochar synthesized from aquatic macrophytes has several potential benets. It
can be used as a soil amendment, helping to improve soil fertility, crop productivity,
and water retention (Bird et al. 2012). It can also be used to sequester carbon, helping
to mitigate climate change (Cui et al. 2016, 2022). In addition, biochar has been
shown to improve water quality when applied to lakes and other bodies of water, as it
can help to remove excess nutrients and pollutants (Gong et al. 2017; Li et al.
2018; Michalak et al. 2019; Mokrzycki et al. 2021). However, the quality of biochar
synthesized from aquatic macrophytes can vary depending on the species of plant
used and the conditions under which it was harvested and pyrolyzed. It is, therefore,

important to carefully control these factors in order to produce high-quality biochar
that can be effectively used for various purposes. Parallelly, harvesting large
amounts of macrophytes could disrupt aquatic habitats and impact biodiversity;
thus, it is important to judiciously assess the environmental impacts and ensure
sustainable practices are followed in the production of biochar from aquatic
macrophytes.
1 An Introduction to the Functions and Ecosystem Services Associated
1.2.13 Bioenergy and Biofuels
Aquatic macrophytes have the potential to produce biofuels, which are renewable
fuels made from organic matter, such as plants or algae (Ankit et al. 2020; Stabenau
et al. 2018; Anand et al. 2017). Aquatic macrophytes can be used as a feedstock for
biofuel production, either alone or in combination with other biomass sources (Röhl
et al. 2019; Anyanwu et al. 2022; Pinho and Mateus 2023). One of the most
promising types of biofuel that can be produced from aquatic macrophytes is
bioethanol. Bioethanol is an alcohol that is produced by fermenting sugars and
other carbohydrates found in the plant material (Ankit et al. 2020; Stabenau et al.
2018; Anand et al. 2017). Aquatic macrophytes such as water hyacinth and duck-
weed are particularly rich in sugars and starches, making them potential sources of
bioethanol. In addition to bioethanol, aquatic macrophytes can also be used to
produce other types of biofuels, such as biodiesel and biogas. Biodiesel is a fuel
made from vegetable oils or animal fats, which can be produced by extracting the oil
from the plant material and then processing it into a fuel. Biogas, on the other hand,
is a mixture of gases such as methane and carbon dioxide, which are produced by the
anaerobic digestion of organic matter (Anyanwu et al. 2022; Pinho and Mateus
2023). Aquatic macrophytes can be used as a feedstock for biogas production, either
alone or in combination with other organic materials (Anyanwu et al. 2022; Sricoth
et al. 2018).
In comparison to the biofuel produced from agro-waste material such as rice husk
and biochar, freshwater macrophytes ( ) have been
reported to produce more bioenergy (Anyanwu et al. 2022).
Eichhornia crassipes
generation owing to their faster growth rate, high dry mass production, and high
content of cellulose, hemicellulose, etc. (Sricoth et al. 2018). The production of
biofuels from aquatic macrophytes has several potential benets. For instance, it
provides a renewable source of energy that is less carbon-intensive than fossil fuels,
helping to mitigate climate change. It could provide economic opportunities for local
communities, particularly in areas where aquatic macrophytes are considered to be a
nuisance or an invasive species. Furthermore, it could help to reduce the reliance on
imported fossil fuels, promoting energy independence and security.
However, there are also challenges associated with the production of biofuels
from aquatic macrophytes. These challenges include the high costs associated with
harvesting and processing the plant material, as well as the potential environmental
impacts of large-scale cultivation and harvesting. Additionally, the use of aquatic

macrophytes for biofuel production may compete with other important ecosystem
services provided by these plants, such as their role in providing habitat and food for
aquatic animals. As such, the development of sustainable and environmentally
responsible methods for the production of biofuels from aquatic macrophytes will
be an important area of research in the coming years.
14 S. Kumar et al.
1.2.14 Environmental Monitoring
Aquatic macrophytes are commonly used as bioindicators of the health of aquatic
ecosystems because they are sensitive to changes in water quality and habitat
conditions (Töre and Özkoç 2022; Galal and Farahat 2015; Kolada 2010). They
can indicate changes in water quality by displaying characteristic symptoms of
nutrient deciencies or toxicity. For instance, if a water body has high nutrient
levels, macrophytes can become overgrown, leading to an imbalance in the ecosys-
tem. Similarly, if the water is contaminated with pollutants, macrophytes can display
signs of stress, such as leaf discoloration or stunted growth. The changes in macro-
phyte communities could indicate the introduction of invasive species that may
outcompete native plants, alter habitat availability, and disrupt ecosystem processes.
Besides, aquatic macrophytes provide important habitats for aquatic organisms, and
changes in their distribution could indicate changes in habitat quality (Töre and
Özkoç 2022; Jaramillo et al. 2019; Kolada 2010). For example, the disappearance of
certain macrophyte species can indicate changes in water depth, sediment composi-
tion, or water
aquatic organisms, and their presence or absence can indicate signicant changes in
biodiversity. The monitoring of the macrophyte communities could yield useful
insights into the health of the entire aquatic ecosystem. Additionally, aquatic
macrophytes are sensitive to changes in climate, including changes in temperature,
precipitation, and water availability. Monitoring the changes in macrophyte distri-
bution and abundance could provide insights into the impacts of climate change on
aquatic ecosystems. This indicates that aquatic macrophytes are valuable tools for
environmental monitoring and can provide valuable information on the health and
functioning of aquatic ecosystems (Töre and Özkoç 2022; Galal and Farahat 2015;
Kolada 2010).
1.3 Impact of Climate Change on Aquatic Macrophytes
Climate change refers to the long-term changes in temperature, precipitation, and
other climatic variables that have been observed over the past century and are
projected to continue in the future. Over the past century, the Earth
temperature has increased by about 1.1
occurring in the past few decades (Xia et al. 2022; Zhou et al. 2021; Pereira et al.
2021; Hossain et al. 2017). This warming trend is largely driven by the increase in
atmospheric concentrations of greenhouse gases, such as carbon dioxide, methane,

nitrous oxide, etc. While some natural factors, such as volcanic eruptions and solar
activity, can in
explained by these factors alone (Xia et al. 2022; Zhou et al. 2021). The evidence
suggests that human activities, such as burning fossil fuels, deforestation, and land-
use changes, are the primary drivers of climate change in recent times. In addition to
rising temperatures, other observed changes include changes in precipitation
patterns, melting of glaciers and sea ice, and rising sea levels. These changes have
signi
versity, changes in agricultural productivity, and increases in extreme weather events
such as droughts, 2022; Zhou et al. 2021; Pereira
et al. 2021).
1 An Introduction to the Functions and Ecosystem Services Associated
Climate change is a threat to aquatic macrophytes also. It could have substantial
impacts on the growth, distribution, and composition of aquatic macrophyte
communities, with potential consequences on the functioning of aquatic ecosystems
(Xia et al. 2022; Zhou et al. 2021). One of the most signicant impacts of climate
change on aquatic macrophytes is the alteration of water temperature regimes. As
temperatures rise, many macrophyte species may experience reduced growth rates,
altered phenology (timing of life cycle events), and changes in reproductive success.
Additionally, warmer water temperatures could promote the growth of invasive plant
species, which may outcompete native macrophytes for resource utilization (Pereira
et al. 2021; Hossain et al. 2017).
Changes in precipitation patterns and water availability could also have a signi-
cant impact on macrophyte communities. Drought conditions could lead to reduced
water levels and increased water temperatures, which in turn could put stress on
macrophyte populations and lead to declines in growth and reproductive success.
Conversely, increased precipitation could lead to ooding, resulting in damage or
uprooting of macrophyte populations (Xia et al. 2022; Zhou et al. 2021). Changes in
nutrient availability could also impact aquatic macrophyte communities. Increased
temperatures may accelerate nutrient cycling and increase nutrient availability,
which would promote the growth of certain macrophyte species. However, excessive
nutrient inputs from agricultural and urban runoff could lead to eutrophication,
leading to harmful algal blooms and promoting the growth of invasive macrophytes
(Hossain et al. 2017; Reitsema et al. 2020).
The interactions between macrophytes and other organisms in the ecosystem
could also get inuenced by climate change. For instance, the changes in macrophyte
growth rates and distribution alter the availability of food and habitat for
invertebrates, which could have cascading effects on the entire ecosystem (Xia et al.
2022; Pereira et al. 2021; Hossain et al. 2017; Reitsema et al. 2020). Overall, the
impacts of climate change on aquatic macrophytes are complex and varied and
depend on a range of factors such as species composition, ecosystem context, and
the speci
important implications for the functioning and resilience of aquatic ecosystems
and highlight the need for effective management strategies that can help mitigate
or adapt to the effects of climate change.

16 S. Kumar et al.
1.4 Conclusion
Aquatic macrophytes are an essential component of aquatic ecosystems. This chap-
ter discusses the various functions and ecological services offered by the aquatic
macrophytes, which are critical for the health and sustainability of freshwater and
marine ecosystems and for the well-being of human societies. Understanding and
managing these services is essential for the effective conservation and management
of aquatic environments; however, this has become a challenge in recent decades.
Climate change and anthropogenic activities, directly or indirectly, have disturbed
the growth, distribution, and composition of the aquatic macrophyte communities,
which will have potential consequences on the functioning of aquatic ecosystems.
The complex and interactive nature of these threats underscores the need for
effective management strategies that can help mitigate or adapt to the effects of
climate change on aquatic macrophytes and the ecosystems they support.
References
Adhikari S, Bajracharaya RM, Sitaula BK (2009) A review of carbon dynamics and sequestration in
wetlands. J Wetl Ecol 2:42
Akasaka M, Takamura N, Mitsuhashi H, Kadono Y (2010) Effects of land use on aquatic
macrophyte diversity and water quality of ponds. Freshw Biol 55:902
Ali F, Jilani G, Bai L, Wang C, Tian L, Jiang H (2021) Effects of previous drying of sediment on
root functional traits and rhizoperformance of emerged macrophytes. Front Environ Sci Eng
15(6):1
Amir M, Paul D, Samal RN (2019) Sources of organic matter in Chilika lagoon, India inferred from
stable C and N isotopic compositions of particulates and sediments. J Mar Syst 194:81
Anand S, Bharti SK, Dviwedi N, Barman SC, Kumar N (2017) Macrophytes for the reclamation of
degraded waterbodies with potential for bioenergy production. In: Bauddh K, Singh B, Korstad
J (eds) Phytoremediation potential of bioenergy plants. Springer, Singapore
Anand S, Kumar S, Kumar N (2018) Remediation of inorganic substances and heavy metals
through aquatic macrophytes from
47(2):29–
Ankit BN, Tiwari J, Kumar S, Korstad J, Bauddh N (2020) Removal of organic pollutants from
contaminated water bodies by using aquatic Macrophytes coupled with bioenergy production
and carbon sequestration. In: Bharagava R (ed) Emerging eco-friendly green Technologies for
Wastewater Treatment. Microorganisms for sustainability, vol 18. Springer, Singapore
Anyanwu IN, Okeke CS, Nwankwo SC, Nwachukwu MO, Michael MO, Opara VC, Chamba EB
(2022) Aquatic macrophytes (Spirogyra porticalis
production: potentials and challenges. Scienti
Bhaskaran K, Vijaya Nadaraja A, Tumbath S, Babu Shah L, Veetil PGP (2013) Phytoremediation
of perchlorate by free
Bird MI, Wurster CM, de Paula Silva PH, Paul NA, De Nys R (2012) Algal biochar: effects and
applications. GCB Bioenergy 4(1):61
Bloom AA, Palmer PI, Fraser A, Reay DS, Frankenberg C (2010) Large-scale controls of
methanogenesis inferred from methane and gravity space borne data. Science 327:322
Bornette G, Puijalon S (2011) Response of aquatic plants to abiotic factors: a review. Aquat Sci
73(1):1
Chambers PA, Lacoul P, Murphy KJ, Thomaz SM (2008) Global diversity of aquatic macrophytes
in freshwater. Hydrobiologia 595:9

1 An Introduction to the Functions and Ecosystem Services Associated
Cui X, Hao H, He Z, Stoffella PJ, Yang X (2016) Pyrolysis of wetland biomass waste: potential for
carbon sequestration and water remediation. J Environ Manag 15(173):95
Cui X, Wang J, Wang X, Khan MB, Lu M, Khan KY, Song Y, He Z, Yang X, Yan B, Chen G
(2022) Biochar from constructed wetland biomass waste: a review of its potential and
challenges. Chemosphere 287:132259
Daily GC, Polasky S, Goldstein J, Kareiva PM, Mooney HA, Pejchar L, Ricketts TH, Salzman J,
Shallenberger R (2009) Ecosystem Services in Decision Making: time to deliver. Front Ecol
Environ 7(1):21
De Groot R, Alkemade R, Braat L, Hein L, Willemen L (2010) Challenges in integrating the
concept of ecosystem services and values in landscape planning, management and decision
making. Ecol Complex 7(3):260
Dhote S, Dixit S (2009) Water quality improvement through macrophytes
Monit Assess 152:149
Dorn NJ, Cronin G, Lodge DM (2001) Feeding preferences and performance of an aquatic
lepidopteran on macrophytes: plant hosts as food and habitat. Oecologia 128:406
Engelhardt KAM, Ritchie ME (2001) Effects of macrophyte species richness on wetland ecosystem
functioning and services. Nature 441:687
Fawzy MA, Badr NES, El-Khatib A, Abo-El-Kassem A (2012) Heavy metal biomonitoring and
phytoremediation potentialities of aquatic macrophytes in River Nile. Environ Monit Assess
184(3):1753–
Ferna
on the structure and composition of the macrophyte vegetation in two small temporary lakes in
the northwest of Spain. Hydrobiologia 415:155
Fernandez-Alaez C, Fernandez-Alaez M, Garcia-Criado F, Garcio-Giron J (2018) Environmental
drivers of aquatic macrophyte assemblages in ponds along an altitudinal gradient.
Hydrobiologia 812:79
Galal TM, Farahat EA (2015) The invasive macrophyte
water pollution in Lake Mariut, Egypt. Environ Monit Assess 187:701
Gong YP, Ni ZY, Xiong ZZ, Cheng LH, Xu XH (2017) Phosphate and ammonium adsorption of
the modi
Res 24(9):8326
Haroon AM (2022) Review on aquatic macrophytes in Lake Manzala, Egypt. The Egypt J Aquat
Res 48:1
He Y, Zhao K, Zhang H, He L, Niu Y, Zhang M, Xu J (2021) Linking macrophyte community
structure with food chain length: a case study in the largest freshwater lake in China and
ecological restoration implications. Ecol Indic 123:107363
Hossain K, Yadav S, Quaik S, Pant G, Maruthi AY, Ismail N (2017) Vulnerabilities of macrophytes
distribution due to climate change. Theor Appl Climatol 129(3):1123
Hunt LM, Morris DM, Drake DAR, Buckley JD, Johnson TB (2019) Predicting spatial patterns of
recreational boating to understand potential impacts to
Res 211:111
Jaramillo E, Duarte C, Labra FA, Lagos NA, Peruzzo B, Silva R et al (2019) Resilience of an
aquatic macrophyte to an anthropogenically induced environmental stressor in a Ramsar
wetland of southern Chile. Ambio 48:304
Kayranli B, Scholz M, Mustafa A, Hedmark A (2010) Carbon storage and
wetlands: a critical review. Wetlands 30:111
Kazanjian G, Flury S, Attermeyer K et al (2018) Primary production in nutrient-rich kettle holes and
consequences for nutrient and carbon cycling. Hydrobiologia 806:77
Keitel J, Zak D, Hupfer M (2016) Water level
sediment drying, aquatic macrophyte dieback, and oxygen availability on phosphorus mobili-
zation. Environ Sci Pollut Res 23:6883
Kolada A (2010) The use of aquatic vegetation in lake assessment: testing the sensitivity of
macrophyte metrics to anthropogenic pressures and water quality. Hydrobiologia 656:133

18 S. Kumar et al.
Kumar D, Anand S, Poonam, Tiwari J, Kisku GC, Kumar N (2019) Removal of inorganic and
organic contaminants from terrestrial and aquatic ecosystems through phytoremediation and
biosorption. In: Sobti R, Arora N, Kothari R (eds) Environmental biotechnology: for sustainable
future. Springer, Singapore
Kumari K, Swain AA, Kumar M et al (2021) Utilization of
production of biochar and its feasibility in agroecosystems: a review. Environ Sustain 4:285–
297
Kurilenko VV, Osmolovskaya NG (2006) Ecological-biogeochemical role of macrophytes in
aquatic ecosystems of urbanized territories (an example of small water bodies of
St. Petersburg). Russ J Ecol 37:147
Lawniczak AE, Zbierska J, Choi
to hydrological changes in a shallow lake, with special reference to nutrient cycling.
Hydrobiologia 656:243
Li J, Fan J, Zhang J (2018) Preparation and evaluation of wetland plant-based biochar for nitrogen
removal enhancement in surface
13937
Lind L, Eckstein RL, Relyea RA (2022) Direct and indirect effects of climate change on distribution
and community composition of macrophytes in lentic systems. Biol Rev 97:1677
Lolu AJ, Ahluwalia AS, Sidhu MC, Reshi ZA (2019) Carbon sequestration potential of
Macrophytes and seasonal carbon input assessment into the Hokersar wetland, Kashmir.
Wetlands 39:453
Mace GM, Norris K, Fitter AH (2012) Biodiversity and ecosystem services: a multilayered
relationship. Trends Ecol Evol 27(1):19
Madsen JD, Chambers PA, James WF, Koch EW, Westlake DF (2001) The interaction between
water movement, sediment dynamics and submersed macrophytes. Hydrobiologia 444:71
Michalak I, Ba
as a potential biosorbent for wastewater treatment. Water 11(7):1390
Mikulyuk A, Sharma S, Van Egeren S, Erdmann E, Nault ME, Hauxwell J (2011) The relative role
of environmental spatial and land-use patterns in explaining aquatic macrophyte community
composition. Can J Fish Aquat Sci 68:1778
Millennium Ecosystem Assessment (2005) Ecosystems and human well-being: synthesis. Island
Press, Washington DC
Mishra S, Mohanty M, Pradhan C (2013) Physico-chemical assessment of paper mill ef
heavy metal remediation using aquatic macrophytes
India. Environ Monit Assess 185:4347
Mokrzycki J, Michalak I, Rutkowski P (2021) Biochars obtained from freshwater biomass—
macroalga and hornwort as Cr (III) ions sorbents. Biomass Conversion and Biore
313
Moore TR, Dalva M (1993) The inﬂ
dioxide and methane emissions from laboratory columns of peatland soil. J Sci 44:651
Nag SK, Das Ghosh B, Nandy S, Aftabuddin M, Sarkar UK, Das BK (2023) Comparative
assessment of carbon sequestration potential of different types of wetlands in lower Gangetic
basin of West Bengal, India. Environ Monit Assess 195(1):154
Nõges T, Luup H, Feldmann T (2010) Primary production of aquatic macrophytes and their
epiphytes in two shallow lakes (Peipsi and Võrtsjärv) in Estonia. Aquat Ecol 44:83
O
cycling in lowland streams. Ecosystems 17:405
Pal S, Chattopadhyay B, Datta S, Mukhopadhyay SK (2017) Potential of wetland macrophytes to
sequester carbon and assessment of seasonal carbon input into the East Kolkata wetland
ecosystem. Wetlands 37(3):497
Pereira KM, He
aquatic macrophyte richness and composition in ponds. Flora 279:151811

1 An Introduction to the Functions and Ecosystem Services Associated
P
preferences for large and small rivers. Landsc Urban Plan 95:68
Pinho HJ, Mateus DM (2023) Bioenergy routes for valorizing constructed wetland vegetation: an
overview. Ecol Eng 187:106867
Ppalov
Bot 73:9
Quirino BA, Lansac-Tôha FM, Thomaz SM, Heino J, Fugi R (2021) Macrophyte stand complexity
explains the functional
Reitsema RE, Preiner S, Meire P, Hein T, Dai Y, Schoelynck J (2020) Environmental control of
macrophyte traits and interactions with metabolism and hydromorphology in a groundwater-fed
river. River Res Appl 37:294. https://doi.org/10.1002/rra.3708
Roelofs J, Brouwer E, Bobbink R (2002) Restoration of aquatic macrophyte vegetation in acidi
and eutrophicated shallow soft water wetlands in The Netherlands. Hydrobiologia 478:171
Röhl M, Roth S, Schütz W, Zehnsdorf A, Herbes C (2019) Biogas production from submerged
macrophytes
9(1):1
Sharip Z, Schooler SS, Hipsey MR et al (2012) Eutrophication, agriculture and water level control
shift aquatic plant communities from
Malaysia. Biol Invasions 14:1029
Smith AJ, Duffy BT, Novak MA (2015) Observer rating of recreational use in wadeable streams of
New York state, USA: implications for nutrient criteria development. Water Res 69:195
Sricoth T, Meeinkuirt W, Pichtel J, Taeprayoon P, Saengwilai P (2018) Synergistic
phytoremediation of wastewater by two aquatic plants (Typha angustifolia and Eichhornia
crassipes) and potential as biomass fuel. Environ Sci Pollut Res 25:5344
Srivastava J, Gupta A, Chandra H (2008) Managing water quality with aquatic macrophytes. Rev
Environ Sci Biotechnol 7:255
Stabenau N, Zehnsdorf A, Rönicke H, Wedwitschka H, Moeller L, Ibrahim B, Stinner W (2018) A
potential phosphorous fertilizer for organic farming: recovery of phosphorous resources in the
course of bioenergy production through anaerobic digestion of aquatic macrophytes. Energy
Sustain Soc 8(1):1
Tallar RY, Suen JP (2017) Measuring the aesthetic value of multifunctional lakes using an
enhanced visual quality method. Water 9(4):233
Thomaz SM (2021) Ecosystem services provided by freshwater macrophytes. Hydrobiologia 850:
1
Töre GY, Özkoç ÖB (2022) Recent developments in aquatic macrophytes for environmental
pollution control: a case study on heavy metal removal from lake water and agricultural return
wastewater with the use of duckweed (Lemnaceae). In: Phytoremediation Technology for the
Removal of heavy metals and other contaminants from soil and water. Elsevier, Amsterdam, pp
75
Xia W, Zhu B, Zhang S, Liu H, Qu X, Liu Y, Rudstam L, Anderson JT, Ni L, Chen Y (2022)
Climate, hydrology, and human disturbance drive long-term (1988
in water diversion lakes. J Environ Manag 319:115726
Yaashikaa PR, Kumar PS, Varjani S, Saravanan A (2020) A critical review on the biochar
production techniques, characterization, stability and applications for circular bioeconomy.
Biotechnology Reports 1(28):e00570
Yadav N, Ahn HJ, Rane NR, Kurade MB, Li X, Park YK, Khan MA, Chung WJ, Chang SW, Jeon
BH (2023) Comprehensive study on removal of bisphenol-S and its metabolic fate using aquatic
macrophytes. Chem Eng J 455:140967

20 S. Kumar et al.
Yasuno N, Shimada T, Fujimoto Y (2021) Semiaquatic spiders
prey derived from macrophyte-based food web: evidence from Lake Izunuma, Japan. Wetl Ecol
Manag 29:507
Zhou L, Yan W, Sun X, Shao J, Zhang P, Zhou G, Zhou X (2021) Regulation of climate, soil and
hydrological factors on macrophyte biomass allocation for coastal and inland wetlands in China.
Sci Total Environ 774:145317

Factors Structuring Aquatic Macrophytes
2
Takudzwa C. Madzivanzira , Julie A. Coetzee ,
and Tatenda Dalu
Abstract
Aquatic macrophytes are a key component of freshwater ecosystems, providing
habitats for aquatic organisms, and play an integral role in food webs and nutrient
cycles. Understanding the factors that inuence macrophyte growth, distribution,
structure and community composition is indispensable for their integrated man-
agement, which are explored in this chapter. Among these are biotic (herbivory,
macrophyte properties and competition and pathogens and diseases) and abiotic
(water chemistry including temperature, substrate composition/embeddedness
and hydrological conditions) factors. Anthropogenic stressors further drive
these biotic and abiotic factors individually or in combination, causing either
the extinction of important native macrophytes or the uncontrolled proliferation
of macrophytes, usually invasive alien species, which has been recognised as an
important issue of aquatic ecosystem management in freshwater systems glob-
ally. Among the notorious aquatic macrophytes of global concern are the invasive
water hyacinth (
which have detrimental impacts in invaded freshwater systems. The global
problem of nuisance macrophytes needs to be holistically handled at all levels
to prevent ecological and socioeconomic impacts associated with their prolifera-
tion. Solutions to curb the nuisance growth of aquatic macrophytes include
mechanical removal, biological control and chemical treatment although
T. C. Madzivanzira (✉) · T. Dalu (✉)
Aquatic Systems Research Group, School of Biology and Environmental Sciences, University of
Mpumalanga, Nelspruit, South Africa
South African Institute for Aquatic Biodiversity, Makhanda, South Africa
J. A. Coetzee
South African Institute for Aquatic Biodiversity, Makhanda, South Africa
Centre for Biological Control, Department of Botany, Rhodes University, Makhanda, South Africa
# The Author(s), under exclusive license to Springer Nature Singapore Pte
Ltd. 2023
S. Kumar et al. (eds.),
https://doi.org/10.1007/978-981-99-3822-3_2
21

integrated control is the most cost-effective control option. The control efforts
need to be integrated at catchment and regional scales, facilitating the integration
and partnerships of institutions to ensure functional aquatic systems and conser-
vation of global biodiversity.
22 T. C. Madzivanzira et al.
Keywords
Eutrophication · Freshwater · Climate change · Nutrients · Invasive · Plant · Water
hyacinth
2.1 Introduction
Aquatic macrophytes are macroscopic forms of aquatic plants (including mosses,
macroalgae, ferns and angiosperms), with vegetative parts that grow actively either
intermittently or permanently oating on, submerged below and growing up through
the water surface (Pieterse 1990; Piedade et al. 2022). This includes macrophytes
that live in temporary and permanent freshwater systems (Chambers et al. 2008;
Murphy et al. 2019). Macrophytes include (1) free-
typically oating on or under the water surface; (2) emergent macrophytes rooted in
soil or soils periodically or intermittently inundated, with vegetation extending
above the water surface; (3) oating-leaved macrophytes that are rooted to the
sediment with leaves oating on the surface of the water; and (4) submerged
macrophytes growing completely submersed under water, with roots attached to or
closely associated with the substrate (Chambers et al. 2008). The global diversity of
macrophytes is well reported in Chambers et al. (2008), and there are 3457 macro-
phyte species within 456 genera and 93 families. Out of these, 49.8% are
monocotyledons, 44.0% dicotyledons, 6.1% ferns and fern allies and 0.2%
clubmosses and horsetails (Murphy et al. 2019).
Macrophytes play crucial roles in the structure and functioning of freshwater
systems (Fig. 2.1) (Chambers et al. 2008; Swe et al. 2021; Haroon 2022; Piedade
et al. 2022). For example, they are important in nutrient cycling and stabilising and
maintaining clear waters in turbid and hypertrophic systems (Scheffer et al. 1993).
This helps in suppressing algal growth through several mechanisms that include
nutrient competition (Mjelde and Faafeng 1997) and/or allelopathic chemical
release, which are toxic and harmful to algae (Gross et al. 2007). Macrophytes
also remove heavy metals in freshwater systems that potentially affect the health
of various faunal groups and humans (Ladislas et al. 2011; Prajapati et al. 2017;
Netshiongolwe et al. 2020). Healthy macrophytes provide crucial habitat structure
for macroinvertebrates and 2008; Choi and Kim 2020; Piedade
et al. 2022) and provide a food source for primary consumers and detritivores (when
they decompose), thereby providing an important base of aquatic food webs
(Newman 1991).
Macrophytes are, however, recognised as a major issue in aquatic ecosystem
management across many ecosystem types of the world if they are allowed to grow

and proliferate uncontrollably (Coetzee et al. 2014; Kagami et al. 2019; Haroon
2022). Recently, aquatic macrophytes have been receiving great attention because of
the devastating effects they cause when they grow and proliferate uncontrollably
(Hussner et al. 2021; Haroon 2022). Thus, the diversity and abundance of
macrophytes are extensively affected by the water physicochemical environment,
sediment texture or embeddedness and biotic interactions among different organisms
2 Factors Structuring Aquatic Macrophytes 23
Fig. 2.1
an aquatic ecosystem. (b
supporting services
photosynthesis resulting in oxygen production;
(i.e. through movement across sediment, water and plant compartments); ,
habitat provisioning]; , erosion regulation through wave disturbance
reduction; , water puri
H, disease regulation via pathogen reduction;
ﬁ 2021)

(Haroon and Abd Ellah 2021). The challenge faced by environmental managers and
various authorities is to determine and properly manage the degree and magnitude to
which disturbance, climatic, hydrogeomorphic and physicochemical factors in com-
bination, individually or in tandem affect macrophyte communities (Lougheed et al.
2001; Coetzee et al. 2021; Datta et al. 2021). In view of the signicant roles played
by macrophytes, understanding the factors that in
indispensable for their integrated management (Dar et al. 2014), and this forms the
main objective of this chapter.
24 T. C. Madzivanzira et al.
2.2 Factors that Affect Macrophyte Structuring
Several biotic and abiotic factors have been shown to interact, thereby affecting the
productivity, distribution, abundance and species composition of macrophytes
(Fig. 2.2) (Germ et al. 2021). The most notable biotic factors include herbivory,
macrophyte functional traits, competition among the macrophyte species and
pathogens and diseases (Germ et al. 2021). Abiotic factors include light, water
chemistry including temperature, substrate composition/embeddedness and hydro-
logical conditions (Harvey et al. 1987; Piedade et al. 2022). These are discussed in
detail in the sections below.
2.3 Biotic Factors
2.3.1 Herbivory
All oating-leaved, emergent and submersed macrophytes are subject to extensive
herbivory losses, which directly alters their biomass, relative abundance and pro-
ductivity (Lodge and Lorman 1987; Liu et al. 2021; Ghirardi et al. 2022). Several
studies (e.g. Liu et al. 2021; Filho et al. 2021; Ghirardi et al. 2022; Masese et al.
2022) suggest that many small (i.e. invertebrates) and large grazers (i.e. sh,
waterfowls, hippos) may affect macrophytes through consumption and
non-consumptive destruction. Reductions in macrophyte root biomass or shoots by
grazers can result in 100% macrophytes loss, with reductions that exceed 50%
reported for invasive cray
2021; Filho et al. 2021; Ghirardi et al. 2022; Masese et al. 2022). For example,
redbreast tilapia
through consumption and tends to prefer certain species over others. In Lake Kariba,
C. rendalli
(Chifamba 1990). In Spain, extensive removal of macrophytes by craysh is posited
to have led to the local extinction of three macrophytes,
alterni 1993). Non-consumptive
destruction can also affect macrophytes, for example, shoots of submersed macro-
phyte species may be clipped near the sediment by rusty craysh,
(Lodge et al. 1994). An undetermined macrophyte percentage destruction by coypu,

2 Factors Structuring Aquatic Macrophytes 25
Fig. 2.2

Jones et al.
(

muskrats and waterfowl goes into building nests and waste (Anderson and Low
1976; Howell and Richardson 2019). All macrophytes sustain substantial damage,
except for emergent macrophytes, which appear to be less susceptible to invertebrate
damage or consumption than submersed and oating-leaved forms due to their
physical structure and lack of leaves (Lodge et al. 1989; Piedade et al. 2022).
Waterfowls in
scales, with snow geese reducing macrophytes substantially on their summer breed-
ing grounds at migration stopover sites and wintering grounds (Lodge et al. 1989).
The importance of herbivory in structuring macrophyte communities is perhaps most
evident in biological control programmes implemented against invasive
macrophytes where host-speci cantly
reduce macrophyte biomass, allowing recovery of native macrophyte communities
(Coetzee et al. 2021).
26 T. C. Madzivanzira et al.
2.3.2 Macrophyte Properties
Since herbivore and macrophyte growths are highly dependent on the nutrients,
nitrogen (N) and phosphorus (P) (Rao et al. 2020), macrophytes that grow rapidly
may be good food and energy source for herbivores, since N-P contents of those
macrophytes are relatively high (Grutters et al. 2016). For example, grass carp and
rudd prefer macrophytes characterised by low C:N ratios (Dorenbosch and Bakker
2011). Apart from the elemental stoichiometry, macrophytes differ in their chemical
feeding deterrent properties and in their respective ratios of feeding deterrents to
attractants (Cronin et al. 2002; Choi et al. 2002). The caterpillar
ephemerella
better on
(Choi et al. 2002). In a similar situation, sh eat more of the well-defended
M. spicatum 2011). Foliar traits
interestingly differ between the native and introduced macrophytes, with herbivores
restricting the introduced macrophyte growth, thereby allowing the growth of native
macrophytes by selective consumption, i.e. if the exotic species are the favoured
macrophytes and vice versa (Penuelas et al. 2010; Grutters et al. 2016).
2.3.3 Macrophyte Interactions
The community structure of macrophytes is merely not an assemblage of species in
each area; however, its dynamics, structure and functioning are governed by posi-
tive, negative or indifferent interactions between and/or among macrophyte species,
besides environmental interactions. Species can interact through exploitative, inter-
ference and allelopathy competition (Gopal and Goel 1993). Exploitative competi-
tion is the most common where two macrophytes of the same or different species
compete whenever a speci
the species share is limited (Harper 1977). In contrast to this, interference

competition involves actively denying resource access by an individual competitor
to the other (Begon et al. 1986). Allelopathy is where a competing organism
produces chemicals, which when released into the environment retard or impair
the growth of the other species, providing the organism with a competitive advan-
tage against the latter (Gopal and Goel 1993). The ability of macrophytes to produce
allelochemicals may have evolved to suppress or even kill their neighbours, thus
eliminating the competition for limited resources. While most studies have looked at
allelopathy of macrophytes on other biotic components, few studies have shown
how macrophytes affect other macrophytes, but nevertheless, some interactions
between macrophytes could involve the release of allelochemicals (Thiébaut et al.
2018; Puche et al. 2020). This was demonstrated in the laboratory whereby invasive
water primrose
ing and quercitrin), which affected two exotic species, the emergent growth form of
Myriophyllum aquaticum
et al. 2018). Several macrophytes such as
been shown to affect phytoplankton (Gross 2003; Maredov 2021;
Wijewardene et al. 2022) and inhibit the germination seeds and/or the growth of
seedlings (Gopal and Goel 1993) via the release of allelochemicals. Many
macrophytes, however, release allelopathic chemicals into the freshwater system
with very little impacts on performance of the other macrophytes due to long
co-evolutionary history (Thorpe et al. 2009).
2 Factors Structuring Aquatic Macrophytes 27
2.3.4 Pathogens and Diseases
Literature on the role of pathogens and diseases in determining the distribution and
abundance of macrophytes is scant (Shearer 1994). However, there are examples
where fungal pathogens are used in biological control of invasive macrophytes. Of
the 60 fungal taxa reported around the world to be pathogenic to the oating
P. crassipes
highly virulent (Charudattan 1996; Shabana 2005), and some of these have been
developed into mycoherbicides for 2001). In
the USA, the feasibility of using some native pathogens in the control of invasive
Hydrilla verticillata cation of
Mycoleptodiscus terrestris
late 1980s (Joye 1990). Both eld and lab experimental studies have demonstrated
that
after inoculation compared with plants that are untreated (Shearer 2010). Pathogens
have also been highlighted as a cause of
USA (Shearer 1994).

28 T. C. Madzivanzira et al.
2.3.5 Abiotic Factors
2.3.5.1 Light
As macrophytes photosynthesise, the availability of light is considered as a major
limiting factor for primary production and growth (Harvey et al. 1987; Chambers
et al. 2008). The quality, intensity and duration of the light matters the most as this
affects macrophytes, with the availability of light being affected by water depth,
turbidity and shading (Harvey et al. 1987). Riparian vegetation shades aquatic
ecosystems, thereby reducing the duration of light availability to macrophytes.
Turbidity is increased by algal blooms in nutrient-rich freshwater systems and clay
and silt (mostly from run-off), which can result in decreases in water transparency
and light availability, thus inhibiting submerged macrophyte growth (Harvey et al.
1987).
Aquatic ecosystems with low light penetration and intensity are dominated by
free-oating and rooted oating-leaved macrophytes adapted to grow their leaves
above the water surface, where there is plenty of light (Lacoul and Freedman 2006).
Submerged macrophytes are conversely abundant in ecosystems where water col-
umn light is abundantly available (Lacoul and Freedman 2006). The light regime is
the main primary driver for macrophyte niche within lakes and reservoirs
zones (Harvey et al. 1987), which typically consists of angiosperms at shallow
depths, with bryophytes and charophytes occupying the deeper depths of the littoral
zone (Chambers et al. 2008). This characteristic zonation is driven primarily by a
combination of light availability and macrophytes
conditions.
2.3.5.2 Water Temperature
Water temperature within the thermal tolerance range of macrophytes promotes their
growth and reproduction. The distribution of certain macrophytes is mainly
temperature-driven, indicating that temperature is equally as important as light in
structuring macrophytes (Kõrs et al. 2012). Macrophytes exhibit different tempera-
ture tolerances, and many of them have an optimal photosynthetic rate of between
20 and 35
Puijalon 2011).
2.3.5.3 Nutrients
The distribution and growth of macrophytes also require nutrients, particularly N
and P, which are assimilated in the form of nitrate (NO
3
-
), ammonium (NH
4
+
) and
phosphate (PO
4
3
), respectively (Dalu et al. 2012; Rao et al. 2020). These two
macronutrients are important components of all the biotic components and are
closely linked to the aquatic carbon, N and P cycles, determining both primary
production and microbial mineralisation of the organic matter in aquatic ecosystems.
Nitrogen contributes to structural component and metabolic and generic compounds
in macrophyte cells. Nitrogen is an essential part of chlorophyll and also the building
block of most proteins and amino acids and qualitative defence compounds. Phos-
phorus contributes mainly to the complexity of the nucleic acid structure (Rao et al.

2020). The nucleic acid is a requirement for protein synthesis regulation, and
therefore, P is important in cell division as well as the development of new tissues
within macrophytes (Rao et al. 2020).
2 Factors Structuring Aquatic Macrophytes 29
Fig. 2.3
common carp (
relation to conditions where the species is still able to grow (i.e. trophy), whereas the area shaded
represents the species
to the trophy were the only ones that were selected, and species with broad trophic ranges were not
included. Adopted from Francov 2019)
An example of nutrient effects on macrophytes is highlighted by Francov
(2019) who observed that the nutrient loading level resulted in oligotrophic or
mesotrophic status of carp ponds, which caused a substantial spectrum of species
reected in an increased diversity of macrophytes but low overall biomass (Fig. 2.1).
This allowed growth in oligo-mesotrophic (e.g.
to hypertrophic (e.g.
observed that in ponds with low trophic status, macrophyte species (e.g.
maxima 2.3).
Both N and P are generated within aquatic ecosystems from the decomposition of
organic matter and nutrient cycles, as well as from external sources such as water
ﬂowing into the aquatic ecosystem containing fertilisers washed away from agricul-
tural elds, and municipal (i.e. sewage, industrial) deposition from towns, which are
discussed in the later sections of the chapter. Submerged and
are able to lter nutrients directly from water columns, while rooted-emergent
macrophytes take up nutrients from sediment (Preiner et al. 2020). Not much

literature is available on the secondary and micronutrient requirements of
macrophytes despite their importance. Secondary nutrients are required in moderate
amounts (e.g. potassium, calcium, magnesium, sulphur), and trace or micro-nutrients
are required in tiny amounts (boron, chlorine, copper, iron, manganese,
molybdenum, zinc).
30 T. C. Madzivanzira et al.
2.3.5.4 Hydrological Variations
Water-level uctuation triggers shoreline erosion and, depending on
range, also affects macrophyte species composition and/or disappearance of sensi-
tive macrophytes (Dalu et al. 2012). The degree to which macrophytes tolerate
hydrological uctuations (i.e. ooding events and drawdown) determines macro-
phyte community structure (poljar et al. 2021; Zhao et al. 2021). Rapid water-level
rises induced by summer oods after exceptionally aberrant strong rains generally
cause large reductions in the shoot spatial extent and biomass and disappearance of
submerged macrophytes in aquatic systems due to low-light availability (Zhu et al.
2012). Flooding increases the water depth, compromising light penetration, and the
most affected are emergent macrophytes as they fail to reach the water surface
(Casanova and Brock 2000). Deep waters can also inhibit macrophytes
and decrease their mechanical resistance (Zhu et al. 2012).
Drawdown also has catastrophic effects on macrophytes, primarily through
exposure of both above-ground vegetation parts and beneath-ground rhizome and
root systems to desiccation under either hot or freezing conditions (Wagner and
Falter 2002). Freshwater systems repeatedly disturbed by drawdown events are then
likely to be dominated by desiccation-tolerant species (Maltchik et al. 2007).
Drawdown can also indirectly affect macrophytes through its effect on the habitat
by forming frost heaves on dewatered sediments and subsequent mechanical damage
to rhizomes and roots of macrophytes (Wagner and Falter 2002). For example, a
study by Kang et al. (2022) assessed how
logically and reproductively) to the water depth gradients of 0.6
drawdown of up to 0.3 m. It was observed that
of 1 m and manifested high biomass (Kang et al. 2022). At the low water depth,
V. spinulosa
biomass, while drawdown produced
Vallisneria spinulosa
depth decline as expressed by increased stolon weight, ramet number and below-
ground biomass. The uctuations of water levels can also affect substrate particle
size distribution and sediment particle size, which is an important factor structuring
macrophytes as it controls root attachment surfaces, nutrient dynamics and intra-
sediment chemistry (Wagner and Falter 2002).
Mechanical resistance of macrophytes is signicantly affected by hydraulic
forces from water wave action and wind, which results in mechanical damage
(uprooting, leaf damage, stem breakage), which has adverse effects on the growth
of a plant (Zhu et al. 2012). Root anchorage strength and the stem mechanical
properties are essential macrophyte traits for mechanical resistance to reduce this
type of damage in aquatic habitats, and hence, macrophytes that possess these traits

will dominate in such systems (Zhu et al. 2012). Macrophytes may also respond to
high wave action and winds over time by changing and altering their morphology
(Bornette and Puijalon 2011). Wave action also disturbs the
thereby increasing turbidity, which decreases light available for submersed
macrophytes (Madsen and Cedergreen 2002). Silt presence due to wave action
was negatively correlated with species richness and diversity in Lake Schilling,
USA, which was previously dominated by curly leaf pondweed,
crispus 2021). The fragrant water lily,
dominated Lake Silver as it produces thicker rhizomes, which are able to support
large oating leaves (Schmid et al. 2021). Once oating leaves reach the water
surface,
reason why water lilies and other macrophyte species (morphologically similar to
water lilies) are often dominant in shallow, turbid freshwater systems (Lacoul and
Freedman 2006). Therefore, as observed in Lake Silver,
inhibited by suspended silt due to high wave action but benets from high sediment
nutrient availability as a result of the high cation exchange capacity of silt
(Gerbersdorf et al. 2007).
2 Factors Structuring Aquatic Macrophytes 31
2.3.5.5 Substrate Composition
Free-oating macrophyte dominance in an aquatic ecosystem creates an anoxic and
dark condition that affects aquatic life beneath (Abdel-Tawwab et al. 2006; Coetzee
et al. 2014). Free-oating macrophytes create environmental alternate stable states
when compared to submerged plant growth, and the two can co-exist. Since
macrophytes directly acquire water column nutrients, the submerged rooted
macrophytes take their required nutrients from both the water column (Madsen
and Cedergreen 2002) and substrate (Chambers et al. 1989). A decit in nutrients
in the water column can result in the dominance of the submerged rooted
macrophytes (Lu et al. 2013). In contrast, substrates that are nutrient-poor will result
in submerged macrophytes strongly competing with oating macrophytes for
nutrients from the water column, but considering the cover and shading effect of
ﬂoating macrophytes, the latter are likely to dominate (Lu et al. 2013). Thus,
depending on water quality, submerged and oating-leaved macrophytes can be
excellent competitors for particular resources mainly due to an asymmetry in their
competitive abilities. As submerged macrophytes access nutrients from the sediment
and water column, they can limit the oating macrophyte growth, whereas the
ﬂoating-leaved macrophytes have more light access and can cause reductions in
light for the submerged macrophytes (Kosten et al. 2009).
Rooted submerged macrophytes are often inuenced by the characteristics of the
substrate that surrounds them through organic content and redox potentials, as well
as through impacts on their rates of nutrient uptake (Madsen and Adams 1989;
Engloner et al. 2013; Shields and Moore 2016). Sandy substrates are least preferred
by macrophytes as sand is too unstable for proper rooting, and areas without sand
provide macrophytes with a better grip (Madsen and Adams 1989). Macrophytes can
become depressed in sections that contain purely sand sediments, and furthermore,
in lakes and reservoirs, wave action washes away silt leaving behind rough and less

fertile substrates like gravel and sand. Once the ne substrates are gone, continued
wave action threatens macrophytes growing in the sand with abrasion or uprooting
(Madsen and Adams 1989). Silt/muck-dominated habitats appear to be the most
preferred environments by a diverse range of macrophytes as recorded in south-
eastern South Dakota lakes (Kading and Xu 2021).
32 T. C. Madzivanzira et al.
2.3.6 Anthropogenic Activities
2.3.6.1 Climate Change
While global biodiversity is alarmingly declining, the decline is more pronounced in
aquatic ecosystems than other ecosystems (Dudgeon et al. 2006; Reid et al. 2019).
Macrophytes
et al. 2017). Human-induced stressors such as climate change, eutrophication,
habitat loss, pollution and invasive species are causing macrophytes to be vulnerable
(Kundzewicz et al. 2008). Climate change is a major stressor driven by the release of
greenhouse gases (GHG) (e.g. carbon dioxide (CO2), uorinated gases, methane,
nitrous oxide (NO2)) with drastic implications for freshwater ecosystems (Sala et al.
2000; Hartmann et al. 2013; Biesbroek et al. 2022). Changes in climate affect water
quality and quantity, either directly by the observed and projected rising
concentrations of CO
2 that affects the water salinity levels and associated tempera-
ture changes, which can impact on growth and reproduction, or indirectly through
changes in precipitation levels and regimes, water-level variations and melting ice
cover and glaciers (Rosenzweig et al. 2007; Meehl et al. 2007; Biesbroek et al.
2022). The global atmospheric GHG concentration is presently at the highest levels,
and average temperatures have increased by over 1
predicted to rise by 1.5
temperatures continue to rise at the current rate, aquatic ecosystems will get warmer
too (IPCC 2018; Saintilan et al. 2018).
Rising atmospheric CO
2 concentrations may increase dissolved inorganic carbon
(DIC) levels and stimulate photosynthetic rates and, hence, macrophytes
ity (Mormul et al. 2020). Macrophyte growth is also impaired under high dissolved
organic carbon (DOC) concentrations, particularly by the humic substances, which
turn the water brown (i.e. brownication) and attenuate light. Increased CO2
concentrations benet free-
macrophytes, which leads to lower macrophyte abundances and diversities. Surpris-
ingly, information on the potential increased atmospheric carbon dioxide level
effects on submerged aquatic biotic components is scant, even though species
composition and diversity are highly correlated with 2 (Mormul et al. 2020).
As a result of species-speciﬁ 3
-
and carbon dioxide
availability, effects of increasing the atmospheric carbon dioxide would likely to
vary with water body and the macrophyte species. Soft water lakes are characterised
by poor DIC concentrations and often occur in temperate and boreal regions and at
high altitudes (Lind et al. 2022). Soft water lakes are limited in bicarbonate and
characterised by low acidity neutralisation capacity (Arts 2002; Lind et al. 2022).

Native isoëtid macrophyte species do well in these low bicarbonate conditions
(Smolders et al. 2002), where macrophytes that utilise CO2 from the sediment of
the aquatic system (e.g. 2 concen-
tration and acidication in these soft water lakes results in the large-scale invasion of
the water column with fast-growing rooted submerged macrophytes
users (e.g. elodeids), thereby replacing the native rooted submerged slow-growing
isoëtids (Arts 2002). Dissolved inorganic carbon-rich waters, which have strong
alkaline pH (greater than 8.2), where carbon dioxide availability is the limiting factor
for the growth of carbon dioxide users (e.g. ), are often
dominated by hydrogen carbonate users, while CO2 increases would support the
growth as well as the competitive strength of carbon dioxide users in soft water lakes
(Hussner et al. 2015).
2 Factors Structuring Aquatic Macrophytes 33
Several studies (e.g. Rosenzweig et al. 2007; Hintz et al. 2020; Magadza et al.
2020) exemplify the warming trend for aquatic ecosystems. The effects of climate
change on macrophyte communities are well summarised in Lind et al. (2022) and
include drastic changes in their physiology, phenology, morphology, biomass,
productivity, distribution, species composition and population dynamics, although
such effects are species specic. A temperature rise enhances macrophyte growth of
certain species to a greater extent.
exposed to different temperature treatments, which represents the natural seasons,
showed a difference in growth responses (Silveira and Thiébaut 2017). Macrophytes
also exhibit variations in their warming response, depending on geographic location
and biological properties, with oating macrophytes together with those inhabiting
shallow zones being exposed to higher temperatures than other macrophyte types
(Santamaría 2002; McKee et al. 2002). In a laboratory experiment on climate
change, McKee et al. (2002) found that the total abundance of three macrophyte
species (i.e. cantly
affected by warming; however, the macrophyte community structure and composi-
tion changed, i.e. the relative
increases in growth rate under a continuous warming treatment, while
increased its oating leaf surface (Lind et al. 2022). In most high-altitude aquatic
systems, reduced ice cover because of warming has allowed prolonged growing
seasons, which ultimately results in increased algal abundance and productivity
(Karst-Riddoch et al. 2005; Dalu et al. 2022). Algal abundance increases reduced
the amount of light available and ultimately decreased macrophyte cover (Karst-
Riddoch et al. 2005). The rate of photosynthesis increases with warming up to an
optimum point, beyond which it decreases; therefore, high temperatures of aquatic
systems cause a resultant negative effects/impacts on the net primary production
(Tait and Schiel 2013; Lind et al. 2022). Since this response will depend on
individual macrophyte species to some extent and the growth conditions, an increase
in the water temperature may cause major changes in the macrophyte species
community and distribution, although precisely the response is dependent on species
and region (Kirschbaum 2004; Lind et al. 2022).
Climate change is causing increased weather conditions
precipitation periods and increased drought frequencies (Meehl et al. 2007;

Rosenzweig et al. 2007; Kundzewicz et al. 2008; IPCC 2018). Changes in water
levels associated with drought will impact macrophytes particularly those that are
dependent on speci
Florida lake following a natural drought,
the littoral habitats for 1 year, and thereafter,
vascular taxa, became dominant (Havens et al. 2005). Severe drought in Argentina
ﬂoodplain lake region resulted in a decreased free-
(O 2011).
34 T. C. Madzivanzira et al.
Increases in water levels due to increased precipitation in Turkish shallow lakes
negatively affected submerged macrophytes (Tan and Beklioglu 2005). Heavy
rainfall washes away nutrients from the terrestrial environment, resulting in aquatic
ecosystem nutrient enrichment, thereby causing signicant shift in species composi-
tion (Vaithiyanathan and Richardson 1999). This was described in a study from the
Everglades, USA, where the macrophytes
(Vaithiyanathan and Richardson 1999). Evidence from these studies implies that
both heavy rainfall and droughts can cause either increases or decreases in macro-
phyte species diversity, biomass and cover (O 2011; Lind et al. 2022).
2.3.6.2 Invasive Species
The spread of invasive alien species (IAS) is facilitated increasingly by anthropo-
genic activities, which break geographical barriers for species distribution, often
through intentional movements of species by humans for food, trade, recreation and
other economic interests across the world, although unintentional introductions also
occur through stowaway species of contamination (Nuñez et al. 2012; Blackburn
et al. 2014). Most invasive macrophyte species have been introduced by humans for
ornamental purposes (e.g. water hyacinth 2020). Once IAS
are released into the aquatic systems, they spread via ow and oods that enable the
connectivity of water bodies. Propagules of invasive macrophytes can also be
dispersed by birds and boats. Among the notorious macrophytes are water primroses
(
montevidensis
crassipes
aquaticum
have been introduced to almost all the continents where they have established and
extending their invasive ranges (Thouvenot et al. 2013). These taxa are highly
invasive because of their documented impacts on freshwater systems where they
form dense masses, which cover aquatic system surfaces, thereby obstructing
waterways making it difﬁcult for navigation, decrease dissolved oxygen, reduce
native macrophyte diversity and even threaten human health by providing refugia for
vectors such as mosquitoes (Hill et al. 2020; Piedade et al. 2022). With their
allelopathy effects, they can affect other native macrophytes (Gopal and Goel 1993).
Several factors contribute to invasive macrophytes
macrophytes (Lind et al. 2022). These include the absence of natural enemies or
competitors and disturbances, e.g. eutrophication, climate change and altered
hydrology, which selectively affects the native macrophytes over the invasive ones

(Lind et al. 2022). Climate change may cause invasive macrophytes to potentially
establish in previously unsuitable habitats through thermal acclimation, thereby
increasing their invasion range. Several studies (e.g. Lacoul and Freedman 2006;
Tattersdill 2017) reported a shift in the geographical range of invasive macrophytes,
e.g. the establishment of the threadleaf crowfoot
elevation Himalayan lakes, which previously were non-vegetated (e.g. Lacoul and
Freedman 2006), and the spread of the pondweed
Europe (e.g. Tattersdill 2017). Increased temperatures because of climate change
have been shown to promote
Thiébaut 2017). The invasive free-oating t from
warming, whereas 2011). Further
projections have predicted that the Iceland climate will be suitable for
and 2017), while
invade beyond 35
°
S and N (Kriticos and Brunel 2016).
2 Factors Structuring Aquatic Macrophytes 35
Invasive macrophytes also facilitate the establishment and spread of other IAS
generally termed as an invasional meltdown (Simberloff 2006). In Lake Kariba,
Zimbabwe, sh
Cherax quadricarinatus oating macrophytes (Marufu
et al. 2018), with impacts cascading to sheries (Madzivanzira et al. 2022). Invasive
craysh species have been shown to affect macrophyte species through direct
herbivory (Madzivanzira et al. 2020, 2022). In Lake Kariba (Zambia and
Zimbabwe), aquatic macrophytes dominated craysh diet across different size
classes as revealed by gut content analysis and stable isotopes (Marufu et al.
2018), whereas, in Lake Naivasha (Kenya), the red swamp craysh
clarkii
Nymphaea nouchali sh (Low-
ery and Mendes 1977).
Australia resulted in 100% macrophyte cover loss and subsequent reorganisation of
the community (Pinder et al. 2019).
2.3.6.3 Eutrophication
Anthropogenic nutrient enrichment above natural acceptable levels of aquatic
systems is one of the pervasive forms of aquatic ecosystem change, which strongly
inuences both abiotic and biotic factors (Alexander et al. 2017). Eutrophication has
affected most aquatic ecosystems globally from freshwater to saline waters and is
mostly caused by industrial and urban sewage, erosion run-off and leached nutrients
from farming lands (Smith et al. 2009). The amount of nutrients (mainly N and P)
entering the aquatic systems has been increasing gradually since human beings
began clearing land for settlements and agriculture, with nutrients
cally increasing in many aquatic ecosystems mid-1900s (Smith et al. 2009). This
increase in nutrient release was driven by human population growth increases and
the improvements of households
water bodies with minimal treatment (Alexander et al. 2017).
Several studies (e.g. Toivonen and Huttunen 1995; Portielje and Roijackers 1995;
Houlahan and Findlay 2004; Thiébaut and Muller 1998; Lougheed et al. 2001; Wu

et al. 2021) have established that nutrient enrichment in aquatic ecosystems causes
changes in macrophyte species composition, richness and density. Nutrient enrich-
ment drives competition for light between macrophyte taxa and between
macrophytes and their benthic, attached and water column phytoplankton (Hilton
et al. 2006), which is a well-described process for aquatic systems whereby nutrients
promote phytoplankton proliferation, which outcompetes littoral macrophytes for
light (Moss 1998). Macrophytes are initially lost from pelagic waters where light
penetration is less, and as the process becomes worse, the submerged macrophytes
will eventually disappear from algae-dominated aquatic systems (Moss 1998). When
established, the algae-dominated state of the aquatic ecosystem is stable, and it is
challenging to change an aquatic ecosystem between two stable states that are either
algae-dominated or macrophyte-dominated (Scheffer and van Nes 2007). O
et al. (2018) concluded that an individual macrophyte morphotype replacement can
proceed only where physical conditions are suitable (Fig. 2.4). Thus, the reality is
36 T. C. Madzivanzira et al.
Fig. 2.4
conditions of different bed slopes. Adapted from O 2018)

different with the physical habitat characteristics of an aquatic system, which
determine the potential for different macrophyte morphotypes in the rst instance.
2 Factors Structuring Aquatic Macrophytes 37
Eutrophication has caused declines in submerged macrophytes due to the exces-
sive growth of lamentous and periphytic algae (Phillips et al. 1978). In Northern
Vosges Mountain streams in France, disturbed sites with high nutrient loading had
low macrophytes lamentous algae biomass (Thiébaut
and Muller 1998). Highly sensitive macrophytes, for example, stoneworts, are
mostly affected by eutrophication, and the presence of stoneworts is generally
indicative of a pristine or slightly disturbed habitat (Van den Berg et al. 1999).
Eutrophication seriously threatens stoneworts, which is reected by their establish-
ment in the shallow regions of the littoral zones migrating from the deeper regions,
followed by rapid declines and extinction (Van den Berg et al. 1999; Kolada 2021)
and hence the widespread use of stoneworts as a bioindicator in ecological
assessments in many countries (Poikane et al. 2018; Kolada 2021). A survey of
lakes and reservoirs in Poland revealed that stoneworts were present in systems that
had signicantly low N, P and chlorophyll- 2021). Under
eutrophic conditions, other macrophytes proliferate, for example, the enormous mats
of
and Lake Victoria (Uganda), which further strains the native macrophyte
community.
2.4 Management
This section mainly focuses on the management of notorious invaders, which have
established and perform well in disturbed aquatic ecosystems. The most effective
strategy in IAS management is preventing their initial arrival. It is, however, very
difcult to prevent the introduction and spread of invasive macrophytes mainly due
to the connectivity of aquatic ecosystems. In the event of failures to prevent the
invasive macrophytes from arriving, early detection programmes and rapid response
should be implemented to contain the invasion (Robertson et al. 2020). For the issue
of invasive macrophytes, their complete eradication is virtually impossible because
of their ecology. Macrophytes are negatively perceived as aquatic weeds especially
during the periods of nuisance growth when they form dense masses, which interfere
with various human activities (Thiemer et al. 2021). Macrophytes removal is desired
to prevent ooding of adjacent land, prevent clogging of hydropower electric plants,
facilitation of irrigation, trade and commerce, disease control, recreational activities
such as swimming, angling, boating and water skiing. Management options to
control nuisance macrophytes include mechanical (cutting, dredging), biological
(biocontrol agents such as herbivorous insects and sh or shading) and chemical
(herbicide, salt) control (Madsen 1997; Thiemer et al. 2021). When evaluating the
available management techniques, an assumption is erroneously made that not doing
anything is environmentally neutral (Madsen 1997). The environmental
repercussions of not taking action against invasive macrophyte species such as
Eurasian watermilfoil, giant

these invasive macrophyte species can have deleterious effects on native
macrophytes, water quality and the abundance and diversity of
(Madsen 1997).
38 T. C. Madzivanzira et al.
2.4.1 Mechanical Control
Mechanical control methods involve manually removing macrophytes by hand
pulling, raking with weed rakes or motor-driven harvesters with underwater cutting
blades; deep sediment dredging; nutrient removal; and water-level drawdown.
Mechanical control methods have been implemented in many countries in the
world. In Collins Lake, USA, biomass of cantly lower
10 years after dredging than pre-dredging levels (Tobiessen et al. 1992). Manual
control successfully controlled approximately 1500 ha of
invaded an Indian hydroelectric reservoir (Cook 1976). On Lake Chivero,
Zimbabwe, ~500 t of
slowed the regeneration of 1999). This man-
agement strategy was, however, discontinued due to lack of resources, and the lake is
presently infested by the invasive macrophyte.
Despite the cost as well as the limited applicability of mechanically harvesting
P. crassipes
European freshwater systems. For example, approximately 8 km (560,000 m
2
)of
the Mare
of
~6700 t of plant biomass had been removed, costing
2
stretch
of the Mare
remained, and an additional
to 2013 (Brundu et al. 2012).
To successfully manage macrophytes and keep their densities manageable, weed
harvesters must be operated a number of times during the season of nuisance growth
to effectively cut the vegetation. When mechanically controlling macrophytes, the
cut vegetation should be dumped where it cannot re-enter the water as fragments left
to oat can produce new macrophytes. Since most macrophytes are perennial, they
have underground rhizomes and portions that can re-sprout new shoots; therefore, it
is essential to harvest the below-ground growth (rhizomes and roots) for an effective
mechanical control. With larger plants such as cult.
Mechanical control methods are labour intensive and costly and have short-term
effects due to the regrowth of macrophytes. A manual removal effort to control
S. molesta
macrophyte, which could not be entirely removed in combination with its extremely
rapid regrowth. Some macrophytes, for example,
and macrophyte survival is guaranteed in the long term (Baattrup-Pedersen et al.
2002). Cutting
for regeneration, and its residual fragments tend to form several lateral branches and
sprouts after being cut (Mielecki and Pieczynska 2005). In the cut regions, light

penetration into the water column promotes fast regrowth (Baattrup-Pedersen et al.
2002). Mechanical harvesting is also non-selective and affects desirable native
macrophytes in the treatment area, as well as other organisms such as amphibians,
insects, macroinvertebrates and reptiles that can also become trapped by harvesters
(Haller et al. 1980; Engel 1990; Booms 1999). Mechanical removal requires periodic
repetitions to control macrophytes to maintain them at acceptable levels
(Murphy 1988).
2 Factors Structuring Aquatic Macrophytes 39
2.4.2 Chemical Control
Herbicidal chemicals are used to manage both terrestrial and aquatic plants, except in
Europe where chemical control in aquatic ecosystems is banned. Herbicide applica-
tion is relatively an easy method and, in some situations, may be the only practical
control method. Common herbicides include glyphosate (Rodeo, Pondmaster),
ﬂuridone (Sonar), endothall (Aquathol, Hydrothol), 2,4-D, chelated copper
compounds and diquat, which are registered with the US Environmental Protection
Agency (EPA) and, when used as recommended and directed, pose no signicant
threat to both public health and the environment. Herbicides vary in their effective-
ness, toxicity and aquatic use restrictions (Ortiz et al. 2020). Herbicide selection
depends largely on the macrophyte to be treated, for example, submersed and
ﬂoating macrophytes are often treated with uridone and diquat; emergent
macrophytes are effectively treated with glyphosate. Controlling nuisance
macrophytes using herbicides can range in scale from backpack sprayers to large-
scale treatments, which target the entire aquatic ecosystems using aircraft and boats.
To successfully control submersed macrophytes and some emergent and oating
macrophytes not normally treated via the foliar application, herbicides are applied
directly to the water around target plants (Ortiz et al. 2020). The chemical must also
remain at prescribed concentrations in the water column, and macrophytes must be
exposed to the chemical for a certain period of time (ranging from hours to months)
(Gettys et al. 2014).
Herbicides have been used to control
world. The Zambezi River Authority (ZRA) aerial sprayed 2,4-D at the rate of 6 L/ha
in Lake Kariba in 1998 and successfully controlled and reduced
(ZRA 1999). Water and sh samples were taken before, during and after spraying to
determine any detrimental effects, and none were detected (ZRA 1999). In the
Burdekin oodplain complex, Australia, four aerial spray applications of glyphosate
(mixture ratio of 10 mg/L) were completed to target
water surface) between 2013 and 2015 (Waltham and Fixler 2017). In Canada,
diquat is the only herbicide registered for aquatic use under a permit to directly
control macrophytes although other herbicides are occasionally permitted under an
emergency registration from the Pest Management Regulatory Agency (PMRA) of
Canada (Breckels and Kilgour 2018). In 2016, 500 ha of
was treated with Aquasurf and glyphosate. Imazapyr and the surfactant Ag-Surf II
have been used in 2013 to control ats in the British

Columbia coast and were approved in 2016 in Lake Isle, Canada, to control
umbellatus 2018). Spraying of diquat herbicide on weed
mechanical harvesters before operation was done to reduce the risk of transferring
macrophyte fragments from one aquatic ecosystem to the other as reported in
macrophyte control protocols in New Zealand (Howard-Williams et al. 1996).
40 T. C. Madzivanzira et al.
Fish kills may occur after herbicides have been applied, even when the chemical
used is not prescribed to be directly harmful and toxic to sh. Suffocation can cause
ﬁsh to die, rather than from direct chemical poisoning as masses of decomposing
macrophytes killed by the chemical create anoxic conditions. When chemicals are
used to control macrophytes, one half (or even less) of the aquatic system should be
treated at a time to give allowance for the sh to freely move to oxygen-rich areas
without chemical treatment. Herbicides should also be applied during the season
when the water temperatures are cooler.
Herbicide control of invasive macrophytes is often a limitation in developing
countries, as it is costly and requires highly skilled personnel, and often the
herbicides are perceived as poisons. For example, spraying
2,4-D in Lake Chivero, Zimbabwe, in the early 1970s generated an outcry and
claims of increased abortions in women and deliveries of deformed babies (Phiri
et al. 2000). This shows the extreme social problems associated with
Furthermore, in developing countries, the water in most invaded sites is used for
drinking, washing and shing, and therefore, the use of herbicides to control
nuisance macrophytes contaminates these sites, thereby threatening human health
(Phiri et al. 2000).
2.4.3 Biological Control
Introducing organisms that compete with or eat nuisance macrophytes represents
another control method. Herbivorous animals (examples discussed in the herbivory
chapter) can be stocked into an aquatic ecosystem to consume the nuisance
macrophytes. Among shes, grass carp
researched and used organism in biological control of macrophytes (Silva et al.
2014). This sh was introduced in Europe, America and Africa to control
macrophytes and for sh production through polyculture (Silva et al. 2014). High
numbers of
nuttallii
Otte 1996). The weevils
hyacinth borer
on 2004).
These insects feed on
seed production (Akers et al. 2017). In Lake Guiers, Senegal, green mats of the water
lettuce , which persisted prior to the release of the control agent,
Neohydronomus af 2006).
Salvinia molesta
salviniae

Random documents with unrelated
content Scribd suggests to you:

S’engageant ensuite, au milieu du
passé détruit, dans les allées, les
carrefours et les rues de ces villes des
vieux âges, il gagnait, malgré les
parfums, l’entrée des sépulcres non
pareils où gisent les restes de ces rois
hindous.
Les portes n’en étant défendues que
par des colosses de jaspe, sortes de
monstres ou d’idoles aux vagues
prunelles de perles et d’émeraudes,—aux
formes créées par l’imaginaire de
théogonies oubliées,—il y pénétrait
aisément, bien que chaque degré
descendu fît remuer les longues ailes de
ces dieux.
Là, faisant main basse autour de lui,
dans l’obscurité, domptant le vertige
étouffant des siècles noirs dont les
esprits voletaient, heurtant son front de
leurs membranes, il recueillait, en
silence, mille merveilles. Tels, Cortez au
Mexique et Pizarre au Pérou s’arrogèrent
les trésors des caciques et des rois, avec
moins d’intrépidité.
Les sacoches de pierreries au fond de
sa barque, il remontait, sans bruit, les
fleuves, en se garant des dangereuses
clartés de la lune. Il nageait, crispé sur
ses rames, au milieu des ajoncs, sans
s’attendrir aux appels d’enfants plaintifs
que larmoyaient les caïmans à ses côtés.
En peu d’heures, il atteignait ainsi
une caverne éloignée, de lui seul connue,

et dans les retraits de laquelle il vidait
son butin.
Ses exploits s’ébruitèrent.—De là, des
légendes, psalmodiées encore
aujourd’hui dans les festins des nababs,
à grand renfort de théorbes, par les
fakirs. Ces vermineux trouvères,—non
sans un vieux frisson de haineuse
jalousie ou d’effroi respectueux,—y
décernent à cet aïeul le titre de
Spoliateur de tombeaux.
Une fois, cependant, l’intrépide
nocher se laissa séduire par les insidieux
et mielleux discours du seul ami qu’il
s’adjoignit jamais, dans une circonstance
tout spécialement périlleuse. Celui-ci, par
un singulier prodige, en réchappa, lui!—
Je parle du bien-nommé, du trop fameux
colonel Sombre.
Grâce à cet oblique Irlandais, le bon
Aventurier donna dans une embuscade.
—Aveuglé par le sang, frappé de balles,
cerné par vingt cimeterres, il fut pris, à
l’improviste, et périt au milieu d’affreux
supplices.
Les hordes hymalayennes, ivres de sa
mort, et dans les bonds furieux d’une
danse de triomphe, coururent à la
caverne. Les trésors une fois recouvrés,
ils s’en revinrent dans la contrée
maudite. Les chefs rejetèrent pieusement
ces richesses au fond des antres
funèbres où gisent les mânes précités de
ces rois de la nuit du monde. Et les

vieilles pierreries y brillent encore,
pareilles à des regards toujours allumés
sur les races.
J’ai hérité,—moi, le Gaël,—des seuls
éblouissements, hélas! du soldat
sublime, et de ses espoirs.—J’habite, ici,
dans l’Occident, cette vieille ville fortifiée,
où m’enchaîne la mélancolie. Indifférent
aux soucis politiques de ce siècle et de
cette patrie, aux forfaits passagers de
ceux qui les représentent, je m’attarde
quand les soirs du solennel automne
enflamment la cime rouillée des
environnantes forêts.—Parmi les
resplendissements de la rosée, je
marche, seul, sous les voûtes des noires
allées, comme l’Aïeul marchait sous les
cryptes de l’étincelant obituaire!
D’instinct, aussi, j’évite, je ne sais
pourquoi, les néfastes lueurs de la lune
et les malfaisantes approches humaines.
Oui, je les évite, quand je marche ainsi,
avec mes rêves!... Car je sens, alors, que
je porte dans mon âme le reflet des
richesses stériles d’un grand nombre de
rois oubliés.
(Des Contes Cruels, édition Calmann Lévy).

Akëdysséril
A Monsieur le Marquis de
Salisbury.
Toute chose ne se
constitue que de son
vide.
Livres Hindous.

a ville sainte apparaissait,
violette, au fond des brumes
d’or: c’était un soir des vieux âges; la
mort de l’astre Souryâ, phénix du

monde, arrachait des myriades de
pierreries aux dômes de Bénarès.
Sur les hauteurs, à l’est occidental, de
longues forêts de palmiers-palmyres
mouvaient les bleuissements dorés de
leurs ombrages sur les vallées du Habad;
—à leurs versants opposés s’alternaient,
dans les flammes du crépuscule, de
mystiques palais séparés par des
étendues de roses, aux corolles par
milliers ondulantes sous l’étouffante
brise. Là, dans ces jardins, s’élançaient
des fontaines dont les jets retombaient
en gouttes d’une neige couleur de feu.
Au centre du faubourg de Sécrole, le
temple de Wishnou-l’éternel, de ses
colonnades colossales, dominait la cité;
ses portails, largement lamés d’or,
réfractaient les clartés aériennes et,
s’espaçant à ses alentours, les cent
quatre-vingt-seize sanctuaires des Dêvas
plongeaient les blancheurs de leurs
bases de marbre, lavaient les degrés de
leurs parvis dans les étincelantes eaux
du Gange: les ciselures à jour de leurs
créneaux s’enfonçaient jusque dans la
pourpre des lents nuages passants.
L’eau radieuse dormait sous les quais
sacrés; des voiles, à des distances,
pendaient, avec des frissons de lumière,
sur la magnificence du fleuve, et
l’immense ville riveraine se déroulait en
un désordre oriental, étageant ses
avenues, multipliant ses maisons sans

nombre aux coupoles blanches, ses
monuments, jusqu’aux quartiers des
Parsis où le pyramidion du lingham de
Sivà, l’ardent Wissikhor, semblait brûler
dans l’incendie de l’azur.
Aux plus profonds lointains, l’allée
circulaire des Puits, les interminables
habitations militaires, les bazars de la
zone des Échanges, enfin les tours des
citadelles bâties sous le règne de
Wisvamîthra se fondaient en des teintes
d’opale, si pures qu’y scintillaient déjà
des lueurs d’étoiles. Et, surplombant
dans les cieux mêmes ces confins de
l’horizon, de démesurées figures d’êtres
divins, sculptées sur les crêtes rocheuses
des monts du Habad, siégeaient, évasant
leurs genoux dans l’immensité: c’étaient
des cimes taillées en forme de dieux; la
plupart de ces silhouettes élevaient, dans
l’abîme, à l’extrémité d’un bras
vertigineux, un lotus de pierre:—et
l’immobilité de ces présences inquiétait
l’espace, effrayait la vie.
Cependant, au déclin de cette
journée, dans Bénarès, une rumeur de
gloire et de fête étonnait le silence
accoutumé des tombées du soir.—La
multitude emplissait d’une allégresse
grave les rues, les places publiques, les
avenues, les carrefours et les pentes
sablonneuses des deux rivages, car les
veilleurs des Tours-saintes venaient de
heurter, de leurs maillets de bronze, leurs
gongs où tout à coup avait semblé

chanter le tonnerre. Ce signal, qui ne
retentissait qu’aux heures sublimes,
annonçait le retour d’Akëdysséril, de la
jeune triomphatrice des deux rois d’Agra,
—de la svelte veuve au teint de perle,
aux yeux éclatants,—de la souveraine,
enfin, qui, portant le deuil en sa robe de
trame d’or, s’était illustrée à l’assaut
d’Eléphanta par des faits d’héroïsme qui
avaient enflammé autour d’elle mille
courages.
*
* *
Akëdysséril était la fille d’un pâtre,
Gwalior.
Un jour, au profond d’un val des
environs de Bénarès, par un automnal
midi, les Dêvas propices avaient conduit,
à travers des hasards, aux bords d’une
source où la jeune vierge baignait ses
pieds, un chasseur d’aurochs, Sinjab,
l’héritier royal, fils de Séür le Clément qui
régnait alors sur l’immense contrée du
Habad. Et, sur l’instant même, le charme
de l’enfant prédestinée avait suscité,
dans tout l’être du jeune prince, un
amour divin! La revoir encore embrasa
bientôt si violemment les sens de Sinjab
qu’il l’élut, d’un cœur ébloui, pour sa
seule épouse,—et c’était ainsi que

l’enfant du conducteur de troupeaux était
devenue conductrice de peuples.
Or, voici: peu de temps après la
merveilleuse union, le prince,—qu’elle
aussi avait aimé à jamais,—était mort.
Et, sur le vieux monarque, un désespoir
avait à ce point projeté l’ombre dont on
succombe, que tous entendirent, par
deux fois, dans Bénarès, l’aboiement des
chiens funèbres d’Yama, le dieu qui
appelle,—et les peuples avaient dû
élever, à la hâte, un double tombeau.
Désormais, n’était-ce pas au jeune
frère de Sinjab,—à Sedjnour, le prince
presque enfant,—que la succession
dynastique du trône de Séür, sous la
tutelle auguste d’Akëdysséril, devait être
transmise?
Peut-être: nul ne délimitera la justice
d’aucun droit chez les mortels.
Durant les rapides jours de son
ascendante fortune,—du vivant de
Sinjab, enfin,—la fille de Gwalior, émue,
déjà, de secrètes prévisions et d’un cœur
tourmenté par l’avenir, s’était conduite
en brillante rieuse de tous droits
étrangers à ceux-là seuls que consacrent
la force, le courage et l’amour.—Ah!
comme elle avait su, par de politiques
largesses de dignités et d’or, se créer, à
la cour de Séür, dans l’armée, dans la
capitale, au conseil des vizirs, dans l’État,
dans les provinces, parmi les chefs des
brahmes, un parti d’une puissance que,

d’heure en heure, le temps avait
consolidée!... Anxieuse, aujourd’hui, des
lendemains d’un avènement nouveau,
dont la nature, même, lui était inconnue
—car Séür avait désiré que la jeunesse
de Sedjnour s’instruisit au loin, chez les
sages du Népâl—Akëdysséril, dès que le
rappel du jeune prince eut été ordonné
par le conseil, résolut de s’affranchir,
d’avance, des adversités que le caprice
du nouveau maître pourrait lui réserver.
Elle conçut le dessein de se saisir, au
dédain de tous discutables devoirs, de la
puissance royale.
Pendant la nuit du souverain deuil,
celle qui ne dormait pas avait donc
envoyé, au-devant de Sedjnour, des
détachements de sowaris bien éprouvés
d’intérêts et de foi pour sa cause, pour
elle et pour les outrances de sa fortune.
Le prince fut fait captif, brusquement,
avec son escorte,—ainsi que la fille du roi
de Sogdiane, la princesse Yelka, sa
fiancée d’amour, accourue à sa
rencontre, faiblement entourée.
Et ce fut au moment où tous deux
s’apparaissaient pour la première fois,
sur la route, aux clartés de la nuit.
Depuis cette heure, prisonniers
d’Akëdysséril, les deux adolescents
vivaient précipités du trône, isolés l’un de
l’autre en deux palais que séparait le
vaste Gange, et surveillés, sans cesse,
par une garde sévère.

Ce double isolement, une raison
d’État le motivait: si l’un d’eux parvenait
à s’enfuir, l’autre demeurerait en otage
et, réalisant la loi de prédestination
promise aux fiancés dans l’Inde
ancienne, ne s’étant apparus, cependant,
qu’une fois, ils étaient devenus la pensée
l’un de l’autre et s’aimaient d’une ardeur
éternelle.
*
* *
Près d’une année de règne affermit le
pouvoir entre les mains de la dominatrice
qui, fidèle aux mélancolies de son
veuvage et seulement ambitieuse, peut-
être, de mourir illustre, belle et toute-
puissante, traitait, en conquérante
aventureuse, avec les rois hindous, les
menaçant!—Son lucide esprit n’avait-il
pas su augmenter la prospérité de ses
États? Les Dêvas favorisaient le sort de
ses armes. Toute la région l’admirait,
subissant avec amour la magie du regard
de cette guerrière—si délicieuse qu’en
recevoir la mort était une faveur qu’elle
ne prodiguait pas.
Et puis, une légende de gloire s’était
répandue touchant son étrange valeur
dans les batailles: souvent, les légions
hindoues l’avaient vue, au fort des plus

ardentes mêlées, se dresser, toute
radieuse et intrépide, fleurie de gouttes
de sang, sur l’haodah lourd de pierreries
de son éléphant de guerre, et,
insoucieuse, sous les pluies de javelots et
de flèches, indiquer, d’un altier
flamboiement de cimeterre, la victoire.
C’est pourquoi le retour d’Akëdysséril
dans sa capitale, après un guerroyant
exil de plusieurs lunes, était accueilli par
les transports de son peuple.
Des courriers avaient prévenu la ville
lorsque la reine n’en fut plus distante
que de très peu d’heures. Maintenant, on
distinguait, au loin déjà, les éclaireurs
aux turbans rouges, et des troupes aux
sandales de fer descendaient les collines:
la reine viendrait, sans doute, par la
route de Surate; elle entrerait par la
porte principale des citadelles, laissant
camper ses armées dans les villages
environnants.
Déjà, dans Bénarès, au profond de
l’allée de Pryamvêda, des torches
couraient sous les térébinthes; les
esclaves royaux illuminaient de lampes,
en hâte, l’immense palais de Séür.
La population cueillait des branches
triomphales et les femmes jonchaient de
larges fleurs l’avenue du palais,
transversale à l’allée des Richis, s’ouvrant
sur la place de Kama; l’on se courbait,
par foules, à de fréquents intervalles, en
écoutant frémir la terre sous l’irruption

des chars de guerre, des fantassins en
marche et des flots de cavaleries.
Soudain, l’on entendit les sourds
bruissements des tymbrils mêlés à des
cliquetis d’armes et de chaînes—et,
brisées par les chocs sonores de ces
cymbales, les mélopées des flûtes de
cuivre. Et voici que, de toute part, des
cohortes d’avant-garde entraient dans la
ville, enseignes hautes, exécutant, en
désordre, les commandements vociférés
par leurs sowaris.
Sur la place de Kama, l’esplanade de
la porte de Surate était couverte de ces
fauves tapis d’Irmensul—et des lointaines
manufactures d’Ypsamboul—tissus aux
bariolures éteintes, importés par les
caravanes annuelles des marchands
touraniens qui les échangeaient contre
des eunuques.
Entre les branches des aréquiers, des
palmiers-palmyres, des mangliers et des
sycomores, le long de l’avenue du
Gange, flottaient de riches étoffes de
Bagdad, en signe de bonheur. Sous les
dais de la porte d’Occident, aux deux
angles du porche énorme de la
forteresse, un éblouissant cortège de
courtisans aux longues robes brodées,
de brahmes, d’officiers du palais,
attendaient, entourant le vizir-
gouverneur auprès duquel étaient assis
les trois vizirs-guikowars du Habad.—On
donnerait des réjouissances, on

distribuerait au peuple le butin
d’Eléphanta—de la poudre d’or, aussi—
et, surtout, on livrerait, aux lueurs d’une
torche solitaire, dans la vaste enceinte
du cirque, de ces nocturnes combats de
rhinocéros qu’idolâtraient les Hindous.
Les habitants redoutaient seulement que
des blessures eussent atteint la beauté
de la reine; ils questionnaient les
haletants éclaireurs; à grand’peine, ils
étaient rassurés.
Dans un espace laissé libre, entre
d’élevés et lourds trépieds de bronze
d’où s’échappaient de bleuâtres vapeurs
d’encens, se tordaient, en des
guirlandes, des théories de bayadères
vêtues de gazes brillantes; elles jouaient
avec des chaînes de perles, faisaient
miroiter des courbures de poignards,
simulaient des mouvements de volupté,
—des disputes, aussi, pour donner à
leurs traits une animation;—c’était à
l’entrée de l’avenue des Richis, sur le
chemin du palais.
*
* *
A l’autre extrémité de la place de
Kama s’ouvrait, silencieusement, la plus
longue avenue. Celle-là, depuis des
siècles, on en détournait le regard. Elle

s’étendait, déserte, assombrissant, sur
son profond parcours à l’abandon, les
voûtes de ses noirs feuillages. Devant
l’entrée, une longue ligne de psylles,
ceinturés de pagnes grisâtres, faisaient
danser des serpents droits sur la pointe
de la queue, aux sons d’une musique
aiguë.
C’était l’avenue qui conduisait au
temple de Sivà. Nul Hindou ne se fût
aventuré sous l’épaisseur de son horrible
feuillée. Les enfants étaient accoutumés
à n’en parler jamais—fût-ce à voix basse.
Et, comme la joie oppressait,
aujourd’hui, les cœurs, on ne prenait
aucune attention à cette avenue. On eût
dit qu’elle n’arrondissait pas là, béante,
ses ténèbres, avec son aspect de songe.
D’après une très vieille tradition, à de
certaines nuits, une goutte de sang
suintait de chacune des feuilles, et cette
ondée de pleurs rouges tombait,
tristement, sur la terre, détrempant le sol
de la lugubre allée dont l’étendue était
toute pénétrée de l’ombre même de
Sivà.
*
* *
Tous les yeux interrogeaient l’horizon.
—Viendrait-elle avant que montât la nuit?

Et c’était une impatience à la fois
recueillie et joyeuse.
Cependant le crépuscule s’azurait, les
flammes dorées s’éteignaient et, dans la
pâleur du ciel, déjà,—des étoiles...
Au moment où le globe divin oscillait
au bord de l’espace, prêt à s’abîmer, de
longs ruisseaux de feu coururent, en
ondulant, sur les vapeurs occidentales—
et voici qu’en cet instant même, au sortir
des défilés de ces lointaines collines
entre lesquelles s’aplanissait la route de
Surate, apparurent, en des
étincellements d’épaisses poussières, des
nuages de cavaliers, puis des milliers de
lances, des chars—et, de tous côtés,
couronnant les hauteurs, surgirent des
fronts de phalanges aux caftans brunis,
aux semelles fauves, aux genouillères
d’airain d’où sortaient de centrales
pointes mortelles: un hérissement de
piques dont presque toutes les
extrémités, enfoncées en des têtes
coupées, entre-heurtaient celles-ci en de
farouches baisers, au hasard de chaque
pas. Puis, escortant l’attirail roulant des
machines de siège, et les claies sans
nombre, attelées de robustes onagres,
où, sur des litières de feuilles, gisaient
les blessés, d’autres troupes de pied, les
javelots ou la grande fronde à la
ceinture;—enfin, les chariots des vivres.
C’était là presque toute l’avant-garde; ils
descendaient, en hâte, les pentes des
sentiers, vers la ville, y pénétrant

circulairement par toutes les portes. Peu
après, les éclats des trompettes royales,
encore invisibles, répondirent, là-bas,
aux gongs sacrés qui grondaient sur
Bénarès.
Bientôt des officiers émissaires
arrivèrent au galop, éclaircissant la route,
criant différents ordres, et suivis d’un
roulis de pesants traîneaux d’où
débordaient des trophées, des dépouilles
opulentes, des richesses, le butin, entre
deux légions de captifs cheminant tête
basse, secouant des chaînes et que
précédaient, sur leurs massifs chevaux
tigrés, les deux rois d’Agra. Ceux-ci, la
reine les ramenait en triomphe dans sa
capitale, bien qu’avec de grands
honneurs.
Derrière eux venaient des chars de
guerre, aux frontons rayonnants, montés
par des adolescentes en armures
vermeilles, saignant, quelques-unes, de
blessures mal serrées de langes, un
grand arc, transversal, aux épaules,
croisé de faisceaux de flèches: c’étaient
les belliqueuses suivantes de la maîtresse
terrible.
Enfin, dominant ce désordre
étincelant, au centre d’un demi-orbe
formé de soixante-trois éléphants de
bataille tout chargés de sowaris et de
guerriers d’élite—que suivait de tous
côtés, là-bas, l’immense vision d’un
enveloppement d’armées—apparut

l’éléphant noir, aux défenses dorées,
d’Akëdysséril.
A cet aspect, la ville entière, jusque-là
muette et saisie à la fois d’orgueil et
d’épouvante, exhala son convulsif
transport en une tonnante acclamation;
des milliers de palmes, agitées,
s’élevèrent; ce fut une enthousiaste furie
de joie.
Déjà, dans la haute lueur de l’air, on
distinguait la forme de la reine du Habad
qui, debout entre les quatre lances de
son dais, se détachait, mystiquement,
blanche en sa robe d’or, sur le disque du
soleil. On apercevait, à sa taille élancée,
le ceinturon constellé où s’agrafait son
cimeterre. Elle mouvait, elle-même, entre
les doigts de sa main gauche, la
chaînette de sa monture formidable. A
l’exemple des Dêvas sculptés au loin sur
le faîte des monts du Habad, elle élevait,
en sa main droite, la fleur sceptrale de
l’Inde, un lotus d’or mouillé d’une rosée
de rubis.
Le soir, qui l’illuminait, empourprait le
grandiose entourage. Entre les jambes
des éléphants pendaient, distinctes, sur
le rouge-clair de l’espace, les diverses
extrémités des trompes,—et, plus haut,
latérales, les vastes oreilles sursautantes,
pareilles à des feuilles de palmiers. Le
ciel jetait, par éclairs, des rougeoiements
sur les pointes des ivoires, sur les pierres

précieuses des turbans, les fers des
haches.
Et le terrain résonnait sourdement
sous ces approches.
Et, toujours entre les pas de ces
colosses, dont le demi-cercle effroyable
masquait l’espace, une monstrueuse
nuée noire, mouvante, sembla s’élever,
de tous côtés à la fois, orbiculaire—et
graduellement—du ras de l’horizon:
c’était l’armée qui surgissait derrière eux,
là-bas, étageant, entrecoupées de mille
dromadaires, ses puissantes lignes. La
ville se rassurait en songeant que les
campements étaient préparés dans les
bourgs prochains.
Lorsque la reine du Habad ne fut plus
éloignée de l’Entrée-du-Septentrion que
d’une portée de flèche, les cortèges
s’avancèrent sur la route pour l’accueillir.
Et tous reconnurent, bientôt, le
visage sublime d’Akëdysséril.
*
* *
Cette neigeuse fille de la race solaire
était de taille élevée. La pourpre mauve,
intreillée de longs diamants, d’un
bandeau fané dans les batailles, cerclait,

espacée de hautes pointes d’or, la pâleur
de son front. Le flottement de ses
cheveux, au long de son dos svelte et
musclé, emmêlait ses bleuâtres ombres,
sur le tissu d’or de sa robe, aux
bandelettes de son diadème. Ses traits
étaient d’un charme oppressif qui,
d’abord, inspirait plutôt le trouble que
l’amour. Pourtant des enfants sans
nombre, dans le Habad, languissaient, en
silence, de l’avoir vue.
Une lueur d’ambre pâle, épandue en
sa chair, avivait les contours de son
corps: telles ces transparences dont
l’aube, voilée par les cimes
hymalayennes, en pénètre les blancheurs
comme intérieurement.
Sous l’horizontale immobilité des
longs sourcils, deux clartés bleu sombre,
en de languides paupières de Hindoue,
deux magnifiques yeux, surchargés de
rêves, dispensaient autour d’elle une
magie transfiguratrice sur toutes les
choses de la terre et du ciel. Ils
saturaient d’inconnus enchantements
l’étrangeté fatale de ce visage, dont la
beauté ne s’oubliait plus.
Et le saillant des tempes altières,
l’ovale subtil des joues, les cruelles
narines déliées qui frémissaient au vent
du péril, la bouche touchée d’une lueur
de sang, le menton de spoliatrice
taciturne, ce sourire toujours grave où
brillaient des dents de panthère, tout cet

Welcome to our website – the perfect destination for book lovers and
knowledge seekers. We believe that every book holds a new world,
offering opportunities for learning, discovery, and personal growth.
That’s why we are dedicated to bringing you a diverse collection of
books, ranging from classic literature and specialized publications to
self-development guides and children's books.
More than just a book-buying platform, we strive to be a bridge
connecting you with timeless cultural and intellectual values. With an
elegant, user-friendly interface and a smart search system, you can
quickly find the books that best suit your interests. Additionally,
our special promotions and home delivery services help you save time
and fully enjoy the joy of reading.
Join us on a journey of knowledge exploration, passion nurturing, and
personal growth every day!
ebookbell.com

Aquatic Macrophytes Ecology Functions And Services 1st Edition Sanjeev Kumar

About This Presentation

Slide Content

Tags

Categories

Download

Quick Actions

Statistics

Related Slideshows

Aquatic Macrophytes Ecology Functions And Services 1st Edition Sanjeev Kumar

About This Presentation

Slide Content

Slide 1

Slide 2

Slide 3

Slide 5

Slide 6

Slide 7

Slide 8

Slide 9

Slide 10

Slide 11

Slide 12

Slide 13

Slide 14

Slide 15

Slide 16

Slide 17

Slide 18

Slide 19

Slide 20

Slide 21

Slide 22

Slide 23

Slide 24

Slide 25

Slide 26

Slide 27

Slide 28

Slide 29

Slide 30

Slide 31

Slide 32

Slide 33

Slide 34

Slide 35

Slide 36

Slide 37

Slide 38

Slide 39

Slide 40

Slide 41

Slide 42

Slide 43

Slide 44

Slide 45

Slide 46

Slide 47

Slide 48

Slide 49

Slide 50

Slide 51

Slide 52

Slide 53

Slide 54

Slide 55

Slide 56

Slide 57

Slide 58

Slide 59

Slide 60

Slide 61

Slide 62

Slide 63

Slide 64

Slide 65

Slide 66

Slide 67

Slide 68

Slide 69

Slide 70

Slide 71

Slide 72

Slide 73

Slide 74

Slide 75

Slide 76

Tags

Categories