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University of Massachusetts Amherst University of Massachusetts Amherst ScholarWorks@UMass Amherst ScholarWorks@UMass Amherst Doctoral Dissertations 1896 - February 2014 1-1-2007 Soilless culture of Moringa (Moringa oleifera Lam.) for the Soilless culture of Moringa (Moringa oleifera Lam.) for the production of fresh biomass. production of fresh biomass. George W. Crosby University of Massachusetts Amherst Follow this and additional works at: https://scholarworks.umass.edu/dissertations_1 Recommended Citation Recommended Citation Crosby, George W., "Soilless culture of Moringa (Moringa oleifera Lam.) for the production of fresh biomass." (2007). Doctoral Dissertations 1896 - February 2014. 6180. https://scholarworks.umass.edu/dissertations_1/6180 This Open Access Dissertation is brought to you for free and open access by ScholarWorks@UMass Amherst. It has been accepted for inclusion in Doctoral Dissertations 1896 - February 2014 by an authorized administrator of ScholarWorks@UMass Amherst. For more information, please contact [email protected].

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Page 1: Soilless culture of Moringa (Moringa oleifera Lam.) for

University of Massachusetts Amherst University of Massachusetts Amherst

ScholarWorks@UMass Amherst ScholarWorks@UMass Amherst

Doctoral Dissertations 1896 - February 2014

1-1-2007

Soilless culture of Moringa (Moringa oleifera Lam.) for the Soilless culture of Moringa (Moringa oleifera Lam.) for the

production of fresh biomass. production of fresh biomass.

George W. Crosby University of Massachusetts Amherst

Follow this and additional works at: https://scholarworks.umass.edu/dissertations_1

Recommended Citation Recommended Citation Crosby, George W., "Soilless culture of Moringa (Moringa oleifera Lam.) for the production of fresh biomass." (2007). Doctoral Dissertations 1896 - February 2014. 6180. https://scholarworks.umass.edu/dissertations_1/6180

This Open Access Dissertation is brought to you for free and open access by ScholarWorks@UMass Amherst. It has been accepted for inclusion in Doctoral Dissertations 1896 - February 2014 by an authorized administrator of ScholarWorks@UMass Amherst. For more information, please contact [email protected].

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This is an authorized facsimile, made from the microfilm

master copy of the original dissertation or master thesis

published by UMI.

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in UMI’s Dissertation Abstracts database, the only

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dissertation accepted in North America since 1861.

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Soilless Culture of Moringa (Moringa oleifera Lam.) for the Production of

Fresh Biomass

A Dissertation Presented

by

George W. Crosby

Submitted to the Graduate School of the University of Massachusetts Amherst in partial fulfillment

of the requirements for the degree of

DOCTOR OF PHILOSOPHY

February 2007

Department of Plant, Soil, and Insect Sciences

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UMI Number: 3254941

Copyright 2007 by

Crosby, George William

All rights reserved.

INFORMATION TO USERS

The quality of this reproduction is dependent upon the quality of the copy

submitted. Broken or indistinct print, colored or poor quality illustrations and

photographs, print bleed-through, substandard margins, and improper

alignment can adversely affect reproduction.

In the unlikely event that the author did not send a complete manuscript

and there are missing pages, these will be noted. Also, if unauthorized

copyright material had to be removed, a note will indicate the deletion.

UMI UMI Microform 3254941

Copyright 2007 by ProQuest Information and Learning Company.

All rights reserved. This microform edition is protected against

unauthorized copying under Title 17, United States Code.

ProQuest Information and Learning Company 300 North Zeeb Road

P.O. Box 1346 Ann Arbor, Ml 48106-1346

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© Copyright by George W. Crosby 2007

All Rights Reserved

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Soilless Culture of Moringa (Moringa oleifera Lam.) for the Production of

Fresh Biomass

A Dissertation Presented

by

George W. Crosby

Approved as to style and content by:

Lyle E. Craker, Chair

Allen V. Barker, Member

Stephen J. Herbert, Member

Fred P. Hulme, Outside member

Peter L. M. Veneman, Department Head Department of Plant, Soil and Insect Sciences

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Soilless Culture of Moringa (Moringa oleifera Lam.) for the Production of

Fresh Biomass

A Dissertation Presented

by

George W. Crosby

Approved as to style and content by:

Lyle E. Craker, Chair

Fred P. Hulme, Outside member

Peter L. M. Veneman, Department Head Department of Plant, Soil and Insect Sciences

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-

*

. ■ *

- -■ . > . • v

/

* ■

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DEDICATION

To my wife, Deborah:

Thank you for your patience, love, encouragement, and willingness to

provide the time that was necessary to make this possible.

To my daughters, Erin, Emily, Hannah, Abby, and Meghan:

A father could not be more blessed.

Remember always to finish what you begin.

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EPIGRAPH

So neither he who plants nor he who waters is anything, but only God,

who makes things grow. 1 Corinthians 3:7

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ACKNOWLEDGMENTS

I thank my advisor, Dr. Lyle E. Craker, for the guidance and

encouragement he has provided. I also thank the members of my committee, Dr.

Alan V. Barker, Dr. Stephen J. Herbert, and Dr. Fred P. Hulme for their helpful

comments and suggestions. Special thanks to Dr. Barker for his detailed review

of each chapter.

Heartfelt thanks to Abby Crosby for her assistance and great company as

greenhouse technician and to Bob Sutherland for his oversight of the

greenhouses and helpful suggestions regarding pest control. I also thank

Professor Kurt Verderber and Dr. Jiang Tan and for their statistical and software

expertise. Thanks to Nikolaus Foidl, Dr. Grace Ju, and Rev. Andrea Lubono for

providing seeds for the experiments.

I thank the administration at the State University of New York at Cobleskill

for release time, United University Professions for financial support, and my

colleagues for their encouragement.

v

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ABSTRACT

SOILLESS CULTURE OF MORINGA (Moringa oleifera Lam.) FOR THE PRODUCTION

OF FRESH BIOMASS

FEBRUARY 2007

GEORGE W. CROSBY, B.S.A., UNIVERSITY OF GEORGIA

M.A., STATE UNIVERSITY COLLEGE AT BUFFALO

Ph.D., UNIVERSITY OF MASSACHUSETTS AMHERST

Directed by: Dr. Lyle Craker

The many medicinal, nutritional, industrial, and agricultural uses of

moringa are well documented, although studies remain focused on moringa as a

wild, uncultivated plant and little horticultural research has been devoted to its

culture. Greenhouse experiments were conducted at the State University of New

York at Cobleskill, New York, USA during the summer of 2006. Soilless culture

has been investigated as an alternative production system for medicinal and

aromatic plants, and moringa seedlings were grown using hydroponic and

aeroponic culture at a pH of 5.5-6.0 and electrical conductivity levels of 2.0-2.3

dSm'1 in order to maximize leaf biomass production and gain access to root

biomass. Moringa leaves are valued for their human nutritional benefits and as a

livestock feed, however the monopodial growth habit of moringa requires removal

of the terminal growing point in order to encourage branching and maximize leaf

production. Seedlings are often subjected to extreme levels of vegetative harvest

when grown in high-density agroforestry production systems, often resulting in

high levels of mortality. Seedling decapitation induced outgrowth of lateral buds,

VI

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and no lateral buds were released by intact plants that were not decapitated. The

release from apical dominance was repressible by the application of exogenous

auxin (0.5% IAA) to the stumps of decapitated seedlings. Seedlings decapitated

to node 6 (15 cm, counted acropetally) released buds more quickly and produced

three times the dry weight per plant than seedlings decapitated to node 1 (5 cm).

Seedlings decapitated to 30 cm (approximately 12 nodes) released 2 more buds

per plant and twice the dry weight compared to those decapitated to 40 cm

(approximately 16 nodes). Pinching seedlings to remove 5 or 10 cm of apical

stem resulted in little regrowth with few buds released and low dry weights. The

percentage of stem removed was more important than the actual height to which

a seedling was decapitated in order to maximize regrowth. Twice-decapitated

plants released more buds (6.7/plant) than once-decapitated plants (2.7/plant),

demonstrating enhanced lateral bud response of previously decapitated

seedlings. The effect of four different pruning strategies on leaf biomass

production of young, pollarded moringa trees was also examined.

Vll

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TABLE OF CONTENTS

Page

ACKNOWLEDGEMENTS.v

ABSTRACT.vi

LIST OF TABLES.xi

LIST OF FIGURES.xiii

CHAPTER

1. INTRODUCTION AND LITERATURE REVIEW.1

1.1 Introduction.1

1.2 Literature Review.4

1.2.1 Moringa oleifera Lam.4

1.2.2 Moringa Cultivation.8

1.2.3 Moringa Shoot System Development and Architecture.10

1.3 Literature Cited.16

2. DEVELOPMENT OF SOILLESS CULTURE METHODS OF MORINGA FOR THE PRODUCTION OF FRESH ROOT AND LEAF BIOMASS.24

2.1 Abstract.24

2.2 Introduction.25

2.3 Materials and Methods.30

2.3.1 Seedling Production Experiment.31

2.3.2 Rockwool Slab Culture Experiment.31

2.3.3 pH Determination Experiment. 33

2.3.4 Aeroponic Culture Experiment.35

2.4 Results.36

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36 2.4.1 Seedling Production Experiment Results....

2.4.2 Rockwool Slab Culture Experiment Results.38

2.4.3 pH Determination Experiment Results.40

2.4.4 Aeroponic Culture Experiment Results.40

2.5 Discussion.41

2.6 Literature Cited.43

3. THE EFFECT OF POINT OF DECAPITATION ON LATERAL BUD OUTGROWTH OF MORINGA SEEDLINGS GROWN IN HYDROPONIC CULTURE.46

3.1 Abstract.46

3.2 Introduction.47

3.3 Materials and Methods.51

3.3.1 Nodal Point of Decapitation Experiment.53

3.3.2 Decapitation to 30 and 40 cm Experiment.54

3.3.3 Pinching Experiment.55

3.3.4 Auxin Replacement Experiment.55

3.4 Results.56

3.4.1 Nodal Point of Decapitation Experiment Results.56

3.4.2 Decapitation to 30 and 40 cm Experiment Results.59

3.4.3 Pinching Experiment Results.61

3.4.4 Auxin Replacement Experiment Results.62

3.5 Discussion.64

3.6 Literature Cited.68

IX

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4. REGROWTH OF COPPICED MORINGA SEEDLINGS IN RESPONSE TO

TWO DECAPITATIONS.71

4.1 Abstract.71

4.2 Introduction.73

4.3 Materials and Methods.75

4.3.1 Once and Twice-Decapitated Experiment.76

4.3.2 Second Decapitation Experiment.79

4.3.3 Shoot Removal Experiment.79

4.4 Results.80

4.4.1 Once and Twice-Decapitated Experiment Results.80

4.4.2 Second Decapitation Experiment Results.82

4.4.3 Shoot Removal Experiment Results.82

4.5 Discussion.83

4.6 Literature Cited.92

5. PRUNING STRATEGIES TO MAXIMIZE LEAF PRODUCTION OF POLLARDED MORINGA TREES.94

5.1 Abstract.94

5.2 Introduction.96

5.3 Materials and Methods.103

5.4 Results. 105

5.5 Discussion.108

5.6 Literature Cited.Ill

BIBLIOGRAPHY.114

x

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LIST OF TABLES

Table Page

2.1 Number (x/84) of germinated seeds, percent germination, and days to germination for four moringa seed (Uganda) treatments.37

2.2 Number (x/84) of germinated seeds, percent germination, and days to germination for four moringa seed (Haiti) treatments.38

2.3 Initial and final stem caliper, initial and final height, buds released, and dry weights for 60 moringa seedlings grown 48 days in hydroponic rockwool slab culture.39

2.4 Effect of pH on height and dry weight of moringa seedlings grown in hydroponic culture for 25 days.40

3.1 Effect of nodal point of decapitation on MTB, bud release, number of stems >40mm, total stem length, and dry weight/plant of moringa seedlings.57

3.2 Effect of percent stem removed on number of buds released and dry weight yield of moringa seedlings decapitated to 30 and 40 cm.60

3.3 Effect of 5 cm and 10 cm apical decapitation on the number of buds released and dry weight yield of moringa seedlings.62

3.4 Effect of decapitation, 0.5% IAA, and 0.5% IAA applied 7 days following decapitation on the number of buds released, number of stems, stem length, and dry weight of moringa seedlings.63

4.1 Stem diameter and height of moringa seedlings before half (Decapitated, n=30) received the first decapitation treatment and stem diameter at 1 month following the first decapitation.80

4.2 Bud release comparison of once-decapitated and twice-decapitated moringa seedlings.81

4.3 Dry weights of leaves and stems and total dry weight following decapitation of once-decapitated and twice-decapitated moringa seedlings.81

4.4 Effect of nodal point of decapitation on MTB, bud release, number of stems >40 mm, total stem length, and dry weights of moringa seedlings following a second decapitation.82

xi

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4.5 Total stem length, number of stems >40mm, and dry weight of once-decapitated, twice-decapitated, and once and twice-decapitated moringa seedlings pruned to three stems.83

4.6 Caliper range, caliper size groups (mm, mean), frequency, and number (n) of moringa seedlings in each group that were once or twice-decapitated sorted to 7 class intervals.85

4.7 Stem diameter, number of buds released, and dry weights following decapitation of once-decapitated and twice-decapitated moringa seedlings having stem diameters of similar size.90

5.1 Nodes per tree with lateral branches, laterals per node, and lateral branches per tree for four pruning strategies of moringa trees pollarded at 150 cm.106

5.2 Comparison of four pruning strategies of pollarded moringa seedlings after a single harvest.106

5.3 Dry weights of leaves and stems and total dry weight after two harvests of moringa trees pollarded at 150 cm and managed by three pruning strategies.107

5.4 Dry weight production per day for moringa trees pollarded at 150 cm with three pruning strategies after two harvests.108

Xll

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LIST OF FIGURES

Figure Page

2.1 Number of germinated moringa seeds (n=84; source=Uganda) in response to a 16-hour photoperiod and fluence level of 250 pmolm'^s'1 as a function of seed treatment and time.37

2.2 Number of germinated moringa seeds (n=84; source=Flaiti) in response to a 16-hour photoperiod and fluence level of 250 pmolm^s'1 as a function of seed treatment and time .38

3.1 Number of buds released per plant following decapitation of moringa seedlings at nodes 1-6 (n=12).58

3.2 Relationship between dry weight and buds released per plant (mean, n=12) following decapitation.58

3.3 Relationship between dry weights (g/plant) and total stem length per plant following decapitation (mean, n=12).59

3.4 Polynomial regression of dry weight of moringa seedlings decapitated to 30 and 40 cm as a function of percent of stem height removed.61

4.1 Scatter diagram of stem diameter and number of buds released per plant for once-decapitated and twice-decapitated moringa seedlings on 21 July 2006.86

4.2 Scatter diagrams of stem diameter and stem length and stem diameter and dry weights after bud release for once-decapitated (n=30) and twice-decapitated (n=30) moringa seedlings.87

4.3 Regression analysis of dry weight as a function of stem length for once-decapitated (n=30) and twice-decapitated (n=30) moringa seedlings.87

4.4 Relationship between seedling caliper and bud release and seedling caliper and dry weights after bud release for once-decapitated and twice-decapitated moringa seedlings sorted to 7 caliper class intervals ...88

4.5 Relationship between number of buds released and dry weight yield after bud release for once-decapitated (n=30) and twice-decapitated (n=30) moringa seedlings sorted to 7 caliper class intervals.89

Xlll

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4.6 Relationship between seedling caliper and crown diameter for once- decapitated (n=30) and twice-decapitated (n=30) moringa seedlings sorted to 7 caliper size groups. 89

XIV

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CHAPTER 1

INTRODUCTION AND LITERATURE REVIEW

1.1 Introduction

Moringa “is a tree of quite ordinary appearance, its branches are easily

broken, and it has little to recommend it (Standley, 1937).” Few people will argue

about the nondescript character of moringa, but nearly 70 years later, the current

medicinal evidence for the nutritional, therapeutic, and prophylactic properties of

moringa stands in stark contrast to Standley’s observations. Fahey (2005)

concludes that “the nutritional properties of moringa are now so well known that

there seems to be little doubt of the substantial health benefit to be realized by

consumption of moringa leaf powder in situations where starvation is imminent.”

Worldwide, approximately 840 million people lack adequate amounts of

food each day, and over 2 billion suffer from malnutrition, including protein-

calorie and micronutrient deficiencies. Vitamin A deficiency alone affects 7 million

pregnant women and 100 million children in more than 100 countries. More than

250,000 children lose their sight each year, half of who die within a year.

Vegetables are the primary source of micronutrients for human consumption and

provide the most practical and sustainable method for alleviating micronutrient

deficiencies (Chadha and Oluoch, 2002). Families in developing countries

depend on access to vegetables containing carotenoids, and implementing home

garden strategies may have the potential to provide low-cost, sustainable plant

food sources of provitamin A.

1

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Success in developing and maintaining food security and adequate %

nutritional levels will require a multifaceted approach with a continued focus on

developing best practice production strategies for indigenous or naturalized

drought-tolerant species. These species should have a wide range of adaptation,

multiple uses, rapid growth, propagate readily, and social acceptance for use

(Nautiyal and Venkataraman, 1987). Once identified, simple and specific cultural

practices appropriate for local growing conditions need to be identified to ensure

sustainable levels of production.

The many medicinal, nutritional, industrial, and agricultural uses of

moringa are well documented. However, little horticultural research has been

devoted to its culture and commercial production is limited. Studies remain

primarily focused on moringa as a wild, uncultivated plant. Recent interest in

exploiting less-familiar plant resources of the wild in developing countries

(Anhwange et al., 2004) suggests that increased medicinal and aromatic plant

(MAP) research is needed to investigate propagation and production techniques

of underexploited plants having promising potential as crops (Rao et al., 2004).

Intensive planting density studies indicate the potential for high biomass

production, although no research is available regarding the response of moringa

to extreme levels of vegetative harvest. Moringa exhibits a strong apical

dominance phenotype, and spacing will depend primarily on shoot system

architecture in response to apical pruning following vegetative harvest.

Soilless culture has been investigated as an alternative production system

for medicinal and aromatic plants in an attempt to improve the quality of plant

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Page 31: Soilless culture of Moringa (Moringa oleifera Lam.) for

1.2 Literature Review

1.2.1 Morinaa oleifera Lam.

Moringa is the sole genus of the Moringaceae, and with just thirteen

species is one of the most phenotypically varied groups of angiosperms (Olson et

al., 2001). Moringa is native to the sub-Himilayan tracts of northwestern India

and is cultivated in many regions of Africa, Arabia, Southeast Asia, the Pacific

and Caribbean Islands, and South America (Fuglie, 1999; Palada, 1996). It

stands out among the vegetables of the world as one of the most ecologically

friendly and highly nutritious crops (Seshadri and Nambiar, 2003). Moringa

roots, leaves, and seeds are used for industrial, food, and medicinal purposes

(Palada. 1996).

Reaching a height of 7 to 12 meters (Foidl et al., 1999), moringa is

considered a multipurpose tree and is known commonly as drumstick tree (for

the seed pods), ben oil tree (for the seed oil) and horseradish tree (for the flavor

of the roots) (Bosch, 2004). Moringa also is considered as a vegetable tree with

almost every part of the plant having food value. Roots are used as a substitute

for horseradish and the leaves are eaten as greens and used as an ingredient in

vegetable curries and as a seasoning in other dishes (Duke, 1983). Moringa is

often included in kitchen and courtyard gardens to provide easy access to

succulent leaves (Dalla Rosa, 1993). Leaves, flowers and green pods are used

in many regions of sub-Saharan Africa in subsistence cooking. Ounce for ounce,

moringa leaves contain more beta-carotene than carrots, more iron than spinach,

more potassium than bananas, more Vitamin C than oranges, and more protein

4

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than peas (Palada et al., 2003). Moringa leaf powder has been identified as a

dietary supplement in developing regions of the world, where leaves are dried

and crushed to make a powder that can be added to other foods (Fuglie, 1999).

Moringa has been promoted by non-governmental agencies such as the Church

World Service (CWS) and Educational Concerns for Hunger Organization

(ECHO) to combat malnutrition among nursing mothers and infants (Fuglie,

1999; Price, 2000).

Moringa may be particularly valuable in combating micronutrient

malnutrition worldwide. A wide variety of plant species and plant parts have been

identified as rich sources of natural antioxidants (Ramarathnam et al., 1995),

including moringa leaves (Siddhuraju and Becker, 2003). Seasonal temperature

differences and agroclimatic location have been demonstrated to have a

significant effect on productivity (Verma, 1982) and antioxidant activity of moringa

leaves (Iqbal and Bhanger, 2005). The carotenoid content of leafy vegetables

also varies with variety, degree of maturity at harvest, plant part, cultivation, and

postharvest practices (Lakshminarayana et al., 2005). Tender, young moringa

leaves are preferred for cooking (Morton, 1991) and have been reported to

contain higher levels of protein, lipid, and vitamins A, B1f B6, and C compared to

mature leaves (D’Souza and Kulkarni, 1993). Methods are under development

for isotopically labeling vegetables, including moringa leaves, to directly measure

beta-carotene absorption and the extent to which it is converted to Vitamin A in

the human body to better address vitamin A deficiency in the developing world

5

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(Grusak, 2005). This method requires that plant material be grown

hydroponically in nutrient solution enriched with deuterium oxide (heavy water).

The Moringa genus has been divided into four habit classes based on

their gross appearance in the field: bottle trees, sarcorhizal trees, slender trees,

and tuberous shrubs, with moringa classified as a slender tree (Olson et al.,

2001). The members of the Moringa genus are considered xerophytes (Bennett

et al., 2003) of semi-arid regions, although, interestingly, they grow also in hot,

humid, wet conditions in areas of annual rainfall greater than 3000 mm (Francis

et al., 2005). A relationship between growth in ecologically different regions and

correlation of anatomical variation with resulting differences in morphology has

revealed a trend toward wider and longer vessel elements and higher conductive

area in moringa plants grown in moist locations (Olson et al., 2001).

Moringa leaf extracts have potential application as prophylactic or

therapeutic treatment for anti-herpes simplex virus type 1 activity (Lipipun et al.,

2003). Niaziminin, a thiocarbamate, has been isolated from moringa leaves and

may have potential as a natural source of cancer chemopreventers (Murakami et

al., 1997). Seed extracts have demonstrated antitumor promoting qualities

(Guevara et al., 1999). A compound, pterygospermin, in the roots is reported to

have antibiotic and fungicidal effects (Price, 2000). Numerous pharmacological

investigations have been reported on moringa root extract, although root bark

must be removed and discarded due to its toxic action (Ray et al., 2003).

Moringa oil, known as Ben Oil, may have importance as a high

temperature, high-stress, non-toxic lubricant, and sales of moringa oil for the

6

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cosmetics industry are expected to increase (Pratt et al., 2002). Seeds contain

natural polyelectrolytes which can be used to clarify turbid water (Babu, 2005;

Foidl et al., 2001). Shelled moringa seeds have demonstrated biosorbent

properties for the removal of cadmium from aqueous media under laboratory

conditions (Sharma et al., 2005).

Moringa is used commonly as a living fence for hedgerows, as a

windbreak, as a green manure crop, and as a plant in alley cropping and

agroforestry systems (Palada, 1996). Moringa shows promise as a livestock feed

(Foidl et al., 2001; Manh et al., 2005; Murro et al., 2003; Price, 2000; Reyes,

2006; Soliva et al., 2005) and has been fed to cattle, pigs, sheep, and goats.

Moringa leaves show promise as a fish feed component in developing regions for

use in aquaculture systems (Mebane, B., personal communication, 2006; Francis

et al., 2005). Leaf extract has been reported to contain zeatin, a plant growth

hormone from the cytokinins group and has been reported to increase yields

between 20 to 35% (Foidl et al., 2001; Price, 2000).

Moringa is among a select group of crops identified for potential

commercialization in developing regions of the world. Moringa was identified as

a Savannah ecosystem species with food and beverage (edible leaves) and

cosmetic (seed oil) potential for generating income from natural ecosystems in

Uganda (Baldascini, 2002). Ugandan moringa was identified as an herbal tea

constituent for natural products development strategy and also was included in a

medicinal, pigment, and nutraceutical plant group that should be given strong

commercial consideration. Moringa has been identified as a priority tree species

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selected for domestication in the Lake Victoria region of Uganda (Katumba et al.,

2004). The multiple applications of moringa, potential economic impact,

appropriateness of agronomic conditions, and ultimate benefit to farmers have

made moringa an important crop to be considered for development (Abele et al.,

2003). The International Plant Genetic Resources Institute has identified

moringa as a priority species of underutilized crops for food security in sub-

Saharan Africa (Padulosi et al., 2002). Tremendous opportunities exist with

moringa for sustainable agriculture and cash crop development in semi-arid

regions (Stephenson and Fahey, 2004).

1.2.2 Moringa Cultivation

Few attempts have been made to commercialize the production of

moringa, due at least in part to the lack of practical horticultural research

(Sutherland et al., 2001). Approximately 12.5% of the 422,000 plant species

documented worldwide are reported to have medicinal values, although only

several hundred of these are cultivated (Rao et al., 2004). Differences in the

quality of medicinal and aromatic plant (MAP) raw materials due to natural

variation, cultivation practices, and post-harvest handling continue to pose

challenges for the natural products and phytopharmaceutical industries (Craker

and Gardner, 2005). Cultivation will decrease the pressure on natural plant

populations and ensure sustainable production, although traditional agricultural

systems may not prove suitable for the domestication of all collected plant

materials (Craker and Gardner, 2005). Herbal roots may be difficult to harvest,

incorrectly identified, and subject to contamination from roots of other species.

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The recent use of an aeroponic system for herbal and phytopharmaceutical root

crops provided access to roots throughout the life of the crop, ensured purity, and

facilitated harvest (Hayden et al., 2004). Increased MAP production and

consumption will continue to provide new opportunities for farmers worldwide

(Craker, 1999), as new crops are placed into cultivation.

Moringa is propagated by seed or hardwood stem cuttings, has been

shield budded successfully (Asiedu et al., 1996; Palada and Chang, 2003; Peter,

1987; Sharma and Raina, 1982), and recently has been propagated by tissue

culture (Stephenson and Fahey, 2004). Seed germination rate is 60 to 70% and

no seed pretreatment is necessary (Katende et al., 1995). Moringa seeds

average 4200 seeds kg'1 and under ideal conditions will germinate within 60 to

75 days (Albrecht, 1993). Dehulled seed may germinate as quickly as 4 to 6

days while seeds with hulls may take 8 to 12 days (Foidl, N., personal

communication, 2006). Seedlings average 25 to 30 cm in two months and will

reach 40 cm in three months (Schabel, 2004). Moringa will tolerate a wide range

of soil pH (5.0-9.0) and grows best between 25 to 35°C (Palada and Chang,

2003); Schabel (2004) reports a pH range of 4.5 to 8.0 for favorable growth of

moringa. Moringa grows in well-drained soils in Puerto Rico with a pH of 5.5 to

7.5 (Parrotta, 1993) and in acid sulfate soils (pH 4.5-5.0) of the tropical monsoon

climate of the Mekong Delta in Vietnam (Manh et al., 2005).

Moringa responds well to pollarding, coppicing, and lopping and is fast

growing (Katende et al., 1995). Research suggesting the potential use of

moringa for fodder production in Jamaica used spacing distances of 60 cm

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between rows and 15 cm within rows. The response of moringa to fertilizer (8-18- \

32) was excellent and dry biomass shoot yield was 145.2 grrf2 at 24 weeks

post-emergence with plants measuring approximately 60 cm in height (Asiedu et

al., 1996). Moringa has been planted in high-density stands in The Gambia at

spacings of 15 cm x 15 cm (Akinbamijo, 2006). Moringa production averages

24.5 metric tons ha'1 of fresh leaves in Niger annually (Bosch, 2004).

Soilless culture may increase yields by as much as 4 tolO times that of

conventional soil conditions (Resh, 2001), and the potential for moringa biomass

production of up to 1,000 metric tons ha^-year'1 exists using high density seeding

and hydroponic technology (Foidl et al., 2001). Recent attempts to develop

tissue culture protocols for clonal multiplication and germplasm maintenance of

Moringa species have produced plantlets of normal shape and size with

substantial root systems, although only two of thirty plantlets survived

transplanting to soil (Stephenson and Fahey, 2004). The use of liquid culture

medium and membrane rafts suggests that plantlet transfer to hydroponic culture

rather than to soil culture would be desirable. There are no documented reports

in the literature suggesting that attempts have been made to grow moringa using

hydroponic culture. Examining the response of moringa to soilless culture may

provide further opportunities for maximizing production of this valuable crop

(Foidl, N., personal communication, 2003).

1.2.3 Moringa Shoot System Development and Architecture

Moringa can be grown as a pollarded, perennial vegetable tree or

coppiced under high-density culture and can withstand severe drought in areas

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where at times little else will grow. Moringa should be, in some way, trimmed to

promote branching, to increase yields, and to facilitate harvesting, as failure to

cut the main trunk will result in straight, fast growing trees with leaves and pods

on only the primary stem (Palada et al., 2003). “Pollarding, coppicing and

lopping or pruning are recommended to promote branching, increase production,

and facilitate harvesting” (Bosch, 2004). Pollarding is reported to be preferable

for fodder and vegetable production since shoots tend to be thinner and more

numerous in comparison to coppice shoots, which may be better suited for paper

pulp (Nautiyal and Venkataraman, 1987).

Little horticultural research has been devoted to moringa pruning

strategies, and the anecdotal reports that are available vary greatly in their

recommendations. One strategy identified is to remove the apical growing shoot

when the tree is 1 to 2 meters high and to cut 60-cm branches back by 30 cm.

(Palada et al., 2003); essentially a pollarding and lopping approach. Elsewhere,

farmers are reported to prune trees once the trees reach 1.5 m tall “at 50 cm

from the ground or to ground level for older ones once or twice a year” (Bosch,

2004). It also has been suggested to trim the terminal growing tips 10 cm from

the top, as the tree will become bushy (Mbora and Mundia, 2004).

Moringa has been planted for forage production in Nicaragua, where

individual plants are pruned at a height of 15 to 20 cm to remove the apical

growing shoot when the tree is 1 to 2 m tall. This vegetative harvest essentially

results in total plant defoliation. Regrowth time is typically 35 days, and mortality

is significant among plant populations (Foidl, N., personal communication, 2003,

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2005). Density trials ranged from 10,000 to 16,000,000 plants/ha 1 with an \

optimum density of 1,000,000 seeds/ha'1 (10 x 10 cm spacing) in sandy, well-

drained, fertile soil. A four-year study at the optimum density of 1,000,000

plants ha'1 under irrigation and fertilization and 9 cuttings per year provided yields

of 580 metric tons of fresh material-ha’1-yr'1 equivalent to approximately 99 tons

of dry matter (Foidl et al., 1999; Francis, 2005).

Moringa has been used as a multipurpose tree component in agroforestry

alley cropping and hedgerow cropping systems. In St. Croix, US Virgin Islands,

four-month-old seedlings averaged 275 cm in height and were lopped at 1.5

meters. At the time of the second pruning three months later seedlings averaged

337 cm. (Becker, 2004). Lopping, as described by the World Agroforestry

Center, refers to random upper branch removal, although in this study “lopped”

actually refers to pollarding, or complete removal of the top portions of the tree

inclusive of the growing point (Becker, B., personal communication, 2006). No

specific procedure for plant management following lopping was provided.

Spacing patterns of moringa will depend primarily on shoot system

architecture and response to vegetative harvest. Moringa exhibits a typical

strong apical dominance phenotype, resulting in the monopodial habit of this

slender tree. The repeated vegetative harvest of moringa seedlings by

decapitation and the resulting proliferation of vegetative shoots will cause these

plants in many ways to resemble herbaceous plants more than woody plants.

The extent to which lateral bud outgrowth occurs and the resulting plant

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geometry and stem architecture will dictate appropriate spacing patterns for

woody species used in short rotation intensive culture (Wu, 1994).

Woody plants generally have characteristic branching patterns that are the

result of apical control as lateral branch growth is inhibited by distal shoots

(Wilson, 2000). Branching patterns are determined genetically, although spatial

relationships among branches are plastic in their response to environmental

events and endogenous phytohormone-like signals (Beveridge et al., 2003).

Lateral buds of many woody species are proleptic and do not grow out during the

same season that they are formed, whereas others are sylleptic, growing out the

same season. Sylleptic branching in poplar (Populus spp.) may increase branch

number, leaf area, and overall growth and biomass of trees at a young age (Cline

and Dong-IL, 2002).

The overall architecture of the shoot system is a result of the activity of the

shoot apical meristem, with shoot branching typically involving two distinct

developmental stages: axillary meristem formation in the leaf axils and growth of

axillary buds. In herbaceous plants, the term apical dominance is used to

describe the “control exerted by the shoot apex over the outgrowth of lateral

buds” (Cline, 1997). Axillary meristems develop quickly into axillary shoots in

some plants like tomato, whereas in other plants, axillary bud development may

be delayed or buds may exhibit little growth or remain dormant due to apical

dominance and the inhibitory effects of the terminal bud. “Developmental

potential” describes if a bud has a tendency to remain suppressed or grows out

(Napolli et al., 1999). The inhibitory effect of basipetal polar transport of apically

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derived auxin on axillary bud outgrowth has been observed in many plant

species. Auxin replacement experiments have been carried out on many

herbaceous plants and a number of woody plants and provide evidence for this

repressive role of apically produced auxin (Cline, 2000). Axillary bud outgrowth

depends on the ratio of auxin to cytokinin, with bud growth inhibited by auxin and

promoted by cytokinin.

The release of apical dominance may occur due to decapitation of the

shoot apex, damage of the shoot apex by disease, and herbivory (Napolli et al.,

1999). Athough little horticultural research has been devoted to plant growth

following severe coppicing or pollarding, plant responses following herbivory

have been studied extensively by ecologists and may provide useful, transferable

information. For example, shoot regrowth in severely browsed acacia (Acacia

spp. Willd.) was so rapid that the plant compensated for continued removal and

achieved net annual growth equal to lightly browsed trees. The nutritional quality

of foliage was also found to be higher with heavily browsed than with lightly

browsed trees. Feeding habits of browsing ruminants have been compared to

pruning; the apical meristem of trees are removed, resulting in a release of apical

dominance, stimulation of shoot regrowth, increased foliar nutrient content,

reduced tannins, and increased palatability that encourages repeat browsing, or

a “feeding loop” (DuToit et al, 1990; Bergstrom et al., 2000). Simulated moderate

browsing as a one-time event induced a compensatory response in acacia with

greater length and numbers of shoots following browsing. Plants that did not

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compensate were suggested to be in a more vulnerable size class and at greater

risk for unsuccessful reproduction (Dangerfield and Modukanele, 1996).

Decapitation may trigger initial bud growth via an auxin-independent

mechanism whereas auxin operates after this initial stage (Morris et al, 2005).

Whether or not specific axillary buds exhibit sustained growth or revert back to

the dormant state is influenced by the development of other axillary buds

(Shimizu-Sato and Mori, 2001). Enhanced bud release due to multiple

decapitation events in woody plants has not yet been reported (Beveridge, C.,

personal communication, 2006). Detailed response of woody plants to frequent

coppicing or long-term management of tree canopies following pollarding is

lacking in the literature.

Light is the most limiting factor for plant growth when other environmental

factors such as nutrition, irrigation, and air temperature are controlled or

enhanced. Under these conditions, plant growth rate is ultimately proportional to

the amount of light received (Kania and Giaconelli, 2001). Radiation capture is

an important determinant of growth rate and biomass yield, with leaf expansion

rate and emergence rate being influenced greatly by temperature (Frantz et al.,

2004). Minimizing shading between coppiced plants or within individual pollarded

canopies will help to increase growth rates of moringa. Stems will compete for

light resources with close spacing in high-density culture; stem growth will likely

increase at the expense of leaf biomass. Photoperiod has been demonstrated to

affect shoot architecture as noninductive photoperiods encourage a vegetative

growth habit (Beveridge et al., 2003). Tropical plants do not exhibit uniform

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cambial activity throughout the year, and long days, high temperature, and V

rainfall have been demonstrated to be important in enhancing cambial activity.

Maximum cambial activity of moringa occurred at 13.4 hours of light and minimal

activity occurred during photoperiods of 10.2 hours (Anand and Paliwal, 1981).

Ten years remain before the 2015 deadline by which world leaders have

pledged to reduce hunger, established at the World Food Summit and by the

Millennium Development Goals (WHO, 2005). According to the United Nations

Millennium Project, the global epicenter of extreme poverty is the smallholder

farmer. Examining nontraditional crops and establishing cultural practices to

improve production will assist families in meeting their nutritional needs in

developing regions of the world. Maximizing the potential of moringa with

appropriate cultivation strategies and incorporating it further as a component of

small-scale agriculture can assist in this process.

1.3 Literature Cited

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Albrecht, J. (ed.). 1993. Tree seed handbook of Kenya. Kenya Forestry Seed Centre, Kenya Forestry Research Institute. Nairobi, Kenya.

Anand, S.K., G.S. Paliwal, 1982. Periodicity of cambial activity and differentiation of its derivatives in some tropical trees: Moringa oleifera Lamk. In: Contemporary trends in plant sciences. 245-253. S.C. Verma, ed. New Delhi Kalyani Publishers.

Anhwange, B. A., V.O. Ajibola, and S.J. Oniye. 2004. Chemical studies of the seeds of Moringa oleifera (Lam) and Detarium microcarpum (Guill and Sperr). Int. J. Biol. Sci.(6):711-715.

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Asiedu, F.H., G.A. Proverbs, and A.L. Fearon. 1996. Comparative study of Leucaena and Moringa: germination, root and shoot production. Proceedings of the Caribbean Food Crops Society:244-251.

Babu, S.C. 2000. Rural nutrition interventions with indigenous plant foods - a case study of vitamin A deficiency in Malawi. Biotechnol. Agron. Soc. Environ. 4(3):169-179.

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Becker, B. 2004. Integration of medicinal and culinary herbs in an agroforestry combination on St. Croix, United States Virgin Islands. MS Thesis, University of Florida, Gainesville, FL 32611 USA.

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Bergstrom, R., C. Skarpe, and K. Danell. 2000. Plant responses and herbivory following simulated browsing and stem cutting of Combretum apiculatum._J. Veg. Sci.11(3)409-414.

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Cline, M.G. and K. Dong-IL. 2002. A preliminary investigation of the role of auxin and cytokinin in sylleptic branching of three hybrid poplar clones exhibiting contrasting degrees of sylleptic branching. Ann. Bot. 90:417-421.

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Pratt, J. H., E.M.T. Henry, H.F. Mbeza, and E. Mlaka. 2002. “On-farm and wild trees: prospecting for commercial products” a paper for the regional agroforestry conference 2002, Marketing & Enterprise Program for Natural Resource-based Products (MEP) -Malawi Agroforestry Extension Project Pretoria, South Africa, May 20-24, 2002.

Price, M. The Moringa Tree. 1985. Revised 2000 by K. Davis. Educational Concerns for Hunger Organization (ECHO) Technical Note. www.echotech.org/technical/technotes/moringabiomasa.pdf.

Ramarathnam, N., T. Osawa, H. Ochi and S. Kawakishi. 1995. The contribution of plant food antioxidants to human health. Trends Food Sci. Technol. 6(3):75- 82.

Rao, M.R., M.C. Palada, and B.N. Becker. 2004. Medicinal and aromatic plants in agroforestry systems. Agrof. Systems 61-62(1-3): 107-122.

Ray, K., R. Hazra, and D. Guhar. Central inhibitory effect of Moringa oleifera root extract: possible role of neurotransmitters. Indian J. Exp. Biol. 41:1279-1284.

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Resh, H. 2001. Hydroponic Food Production. 6th ed. Woodbridge Press, Santa

Barbara, California.

Reyes S. N. 2006. Moringa oleifera and Cratylia argentea: potential fodder species for ruminants in Nicaragua. Doctoral diss. Dept, of Animal Nutrition and Management, SLU. Acta Universitatis agriculturae Sueciae vol. 2006:1.

Sail, J,A. Lehman, and L. Creighton. 2001. JMP Start Statistics - a guide to statistics and data analysis using JMP£ and JMP IN® software. 2nd ed. Duxbury Thompson Learning, California.

Sena, L.P., D.J. Vanderjagt, C. Rivera, A.T.C. Tsin, I. Muhamadu, O. Mahamadou, M. Millson, A. Pastuszyn, and R.H. Glew. 1998. Analysis of nutritional components of eight famine foods in the Republic of Niger. Plant Foods Hum. Nutr. 52:17-30.

Seshadri, S., and V.S. Nambiar. 2003. Kanjero (Digera arvensis) and drumstick leaves (Moringa oleifera): nutrient profile and potential for human consumption. In: Plants in human health and nutrition policy, Simopoulos, A.P. and C. Gopalan, eds. World Rev. Nutr. Diet 91:41-59.

Sharma, P., P. Kumari, M.M. Srivastava and S. Srivastava. 2005. Removal of cadmium from aqueous system by shelled Moringa oleifera Lam. seed powder. Bioresour. Technol. 97(2):299-305.

Shimizu-Sato, S. and H. Mori. 2001. Control of outgrowth and dormancy in axillary buds. Plant Phys. 127:1405-1413.

Siddhuraju, P. and K. Becker. 2003. Antioxidant properties of various solvent extracts of total phenolic constituents from three different agroclimatic origins of drumstick tree (Moringa oleifera Lam.) leaves. J. Agric. Food Chem. 51(8):2144- 2155.

Soliva, C.R, M. Kreuzer, N. Foidl, G. Foidl, A. Machmuller, and H.D. Hess. 2005. Feeding value of whole and extracted Moringa oleifera leaves for ruminants and their effects on ruminal fermentation in vitro. Anim. Feed Sci. Technol. 118:47-62.

Standley, P.C. 1937. Flora of Costa Rica. Pt. II, Pub. 392. Bot. Ser. Vol. XVIII. Field Museum of Natural History, Chicago, IL.

Stephenson, K., and J. Fahey. 2004. Development of tissue culture methods for the rescue and propagation of endangered Moringa spp. germplasm. Econ. Bot. 58:S116-S124.

Verma, S.C. 1982. Productivity in relation to phenology in Moringa spp. Moringa oleifera and Moringa concanensis trees. New Botanist 7:151-156.

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Wilson, B.F. 2000. Apical control of branch growth and angle in woody plants. Am. J. Bot. 87:601-607.

World Health Organization Report. 2005. The state of food insecurity in the world - eradicating world hunger - key to achieving the millennium development goals. ISBN:9251053847.

Wu, R-L. 1994. Qualitative genetics of yield breeding for Populus short rotation culture. II. Genetic determination and expected selection response of tree geometry. Can. J. For. Res. 24:155-165.

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CHAPTER 2

DEVELOPMENT OF SOILLESS CULTURE METHODS OF MORINGA

FOR THE PRODUCTION OF FRESH ROOT AND LEAF BIOMASS

Keywords: aeroponics, hydroponics, medicinal plants, Moringa oleifera,

rockwool, sustainable agroforestry

2.1 Abstract

The soilless culture of a xerophytic, multipurpose tree used in agroforestry

production systems was demonstrated. Medical evidence for the nutritional,

therapeutic, and prophylactic properties of moringa (Moringa oleifera Lam) and

many agricultural and industrial uses have encouraged scientists from a wide

variety of disciplines to continue to examine potential uses of moringa. Most

studies remain focused on moringa as a wild, uncultivated plant, and traditional

agricultural systems may not necessarily prove suitable for the domestication of

collected plant materials. Soilless culture has been investigated as an alternative

production system for medicinal and aromatic (MAP) plants in an attempt to

improve the quality of plant materials and to gain access to root biomass. In this

study, protocols were established for the soilless culture of moringa with a goal of

producing leaf and root biomass. Seed from Uganda and Haiti were germinated

at 25°C in rockwool using a 16-hour photoperiod and a photon fluence rate of

250 pmolm'^s'1. Germination rates of 65% for dehulled seeds were consistent

with those reported by others whereas hulled seeds germinated poorly. Seeds

began to germinate in 5 days. Moringa seedlings grew well in rockwool slab

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culture using a nutrient solution consisting of 1.0 g L'1 5-11-26 Hydro-Sol£ and

0.75 g L’1 15.5-0-0 Calcium Nitrate Plus™ (Scotts Sierra Horticultural Prod. Co.,

14111 Scottslawn Rd., Marysville, Ohio 43041 USA), and 0.25 g L'1

MgS047H20 Epsogrow® epsom salts (Hydro Agri North America 100 North

Tampa Street, Suite 3200, Tampa, Florida 33602 USA), with electrical

conductivity (EC) levels maintained between 2.0 and 2.3 dS m'1. Seedlings were

grown at pH 5.5, 6.0, 6.5, 7.0, or 7.5 with optimum growth occurring between pH

5.5 to 6.0. Moringa seedlings also were grown in a commercially available

recirculating aeroponics system (Aeroflo®, General Hydroponics, P.O. Box 1576,

Sebastopol, CA 95473 USA) and produced healthy, robust plants with well-

developed, fibrous root biomass. Maintaining a dry region around the base of the

stem is critical to successfully growing moringa in soilless culture.

2.2 Introduction

Approximately 12.5% of the 422,000 plant species documented worldwide

are reported to have medicinal values, although only several hundred of these

are known to be cultivated (Rao et al., 2004). Increased medicinal and aromatic

plant (MAP) production and consumption will continue to provide new

opportunities for farmers worldwide as new crops are placed into cultivation

(Craker, 1999). Differences in the quality of MAP raw materials due to natural

variation, cultivation practices, and post-harvest handling continue to pose

challenges for the natural products and phytopharmaceutical industries.

Cultivation will decrease the pressure on natural plant populations and ensure

sustainable production, although traditional agricultural systems may not

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necessarily prove suitable for the domestication of all collected plant materials \

(Craker and Gardner, 2005).

Moringa is a small tree reaching a height of 7 to 12 meters (Foidl et al.,

2001) and is native to the sub-Himalayan regions of northwest India. Moringa is

now cultivated in many regions of Africa, Arabia, Southeast Asia, the Pacific and

Caribbean Islands, and South America (Fuglie, 1999; Palada, 1996). The many

medicinal, nutritional, industrial, and agricultural uses of moringa are well

documented and continue to be investigated by scientists from a wide variety of

disciplines. A comprehensive review of the current medicinal evidence for the

nutritional, therapeutic, and prophylactic properties of moringa has recently been

published (Fahey, 2005).

Moringa is one of the most phenotypically varied groups of angiosperms

(Olson and Carlquist, 2001) and stands out among the vegetables of the world as

one of the most ecologically friendly and highly nutritious crops (Seshadri and

Nambiar, 2003). A wide variety of plant species and plant parts have been

identified as rich sources of natural antioxidants (Ramarathnam et al.,1995)

including moringa leaves (Siddhuraju and Becker, 2003). Seasonal temperature

differences and agroclimatic location have recently been demonstrated to have a

significant effect on the antioxidant activity of moringa leaves (Iqbal and Bhanger,

2005). A compound in the roots, pterygospermin, is reported to have antibiotic

and fungicidal effects (Price, 2000). Numerous pharmacological investigations

have been reported on moringa root extract, although root bark must be removed

and discarded due to its toxic action (Ray et al., 2003).

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Few attempts have been made to commercialize the production of

moringa, little practical horticultural research is available (Sutherland et al.,

2001), and most studies remain primarily focused on moringa as a wild,

uncultivated plant. Recent attention has been given to agroforestry production

systems using intensive planting densities and suggest the potential for high

moringa biomass production, with dry yields approaching 100 metric tons/ha'Vyr'1

(Foidl et al., 1999; Francis, 2005). The potential for moringa biomass production

of up to 1,000 metric tons/ha'Vyr'1 exists with use of high-density seeding and

hydroponic technology (Foidl et al., 2001).

Soilless culture may increase yields by as much as 4 to 10 times that of

conventional soil-grown conditions (Resh, 2001), and current soilless culture

technology permits closed, recirculating production in areas approaching 100

hectares. Nearly 90 hectares of hydroponic tomatoes are produced in a closed

system at Eurofresh Farms in Willcox, Arizona, USA (Kubota, C., personal

communication, 2006). Soilless culture has been investigated as an alternative

production system for medicinal and aromatic plants in an attempt to improve the

quality of plant materials and to gain access to valuable root biomass. Herbal

roots may be difficult to harvest, incorrectly identified, and subject to

contamination from roots of other species. Aeroponics is a method of soilless

culture where roots are suspended within a closed chamber and receive an

intermittent or constant application of sprayed nutrient solution. The recent use of

an aeroponic system for herbal and phytopharmaceutical root crops provided

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access to roots throughout the life of the crop, ensured purity, and facilitated

harvest (Hayden et al., 2004).

Tissue culture techniques have been developed for the Moringa genus in

order to ensure the maintenance of germplasm. Micropropagated plantlets of

normal shape and size with substantial root systems were cultured successfully,

though only two of thirty plantlets survived transplanting to soil (Stephenson and

Fahey, 2004). The use of liquid culture medium and membrane rafts suggests

that transfer to hydroponic culture rather than soil culture may increase survival

of plantlets. Moringa seedlings are reported to be highly susceptible to water

logging, however, and hydroponic culture may prove difficult.

The members of the Moringa genus are drought tolerant and occur in

regions having as little as 300 mm (Schabel, 2004) to 500 mm (Bosch, 2004) of

annual precipitation and are considered xerophytes (Bennet et al., 2003) of semi-

arid regions. Interestingly, they also grow in hot, humid, wet conditions in areas

of annual rainfall greater than 3000 mm (Francis et al., 2005). A relationship

between growth in ecologically different regions and correlation of anatomical

variation with resulting differences in morphology has revealed a trend toward

wider and longer vessel elements and higher conductive area in moringa plants

grown in moist locations (Olson and Carlquist, 2001). Moringa seedlings develop

a thick, tuberous taproot with few lateral roots (Parrotta, 1993).

Moringa is reported to tolerate a wide range of soil pH (5.0-9.0) and grows

best between 25 to 35°C (Palada and Chang, 2003). Schabel (2004) reports a

pH range of 4.5 to 8.0. Moringa grows in well drained soils in Puerto Rico with a

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pH between 5.5 and 7.5 (Parrotta, 1993) and in acid sulfate soils (pH 4.5-5.0) of

the tropical monsoon climate of the Mekong Delta in Vietnam (Manh et al., 2005).

Seed germination rate is 60 to 70%, no seed pretreatment is necessary

(Katende et al., 1995), and germination is reported to be epigeal (Nautiyal and

Venkataraman, 1987; Parrotta, 1993). Sharma and Raina (1982) reported

germination rates of 64% with no benefit of pre-soaking seeds in water for up to

48 hours. On average, there are 4200 seeds-kg'1 and under ideal conditions

seeds germinate between 30 (Sharma and Raina, 1982) and 75 days (Albrecht,

1993). Dehulled seed may germinate as quickly as 4 to 6 days while seeds with

hulls may take 8 to12 days (Foidl, N., personal communication, 2006). Seedlings

average 25 to 30 cm in two months and will reach 40 cm in three months

(Schabel, 2004). Stephenson and Fahey (2004) successfully germinated moringa

seeds in sterile vermiculite under fluorescent lighting using a 16-hour light, 8-hour

dark photoperiod at 25°C. Moringa seeds may be stored for several years if they

are dried to 5 to 8% moisture content and stored in airtight containers at 3°C

(Albrecht, 1993), and are therefore probably orthodox (Flynn et al., 2004).

The growing awareness of the ethnobotanical, dietary, and

pharmacological potential of moringa, challenges of tissue culture plantlet

survival, as well as the general interest worldwide in expanded MAP production

suggest a need for examining moringa culture more closely. Moringa may

tolerate a wide range of growing conditions, although it is important to continue to

investigate cultural practices that optimize growth. Examining the response of a

xerophytic, multipurpose tree used in agroforestry production systems to soilless

29

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culture will likely provide information that is also valuable for traditional field \

production of moringa. The objective of this study was to establish protocols for

the soilless culture of moringa with a goal of leaf and root biomass production.

2.3 Materials and Methods

Experiments were conducted in the greenhouses and laboratories of the

Department of Plant Science at the State University of New York at Cobleskill,

New York, USA. Where applicable, ANOVA followed by the Tukey-Kramer HSD

paired mean comparisons test (JMP®, v.4.0.3, SAS Institute, Inc., Cary, NC

27513 USA) were used to test for significant differences between treatments

(Hoshmand, 1998, Sail et al., 2001).

Yellow and blue sticky cards (IPM Laboratories, Inc., Locke, NY 13092-

0300 USA) were used to monitor insect pests throughout the experiments, and

biological pest controls were used during May and June of 2006. To monitor

fungus gnat (Orfelia spp.) larvae, potato discs were placed on rockwool

transplant blocks and in pots at the rate of 10 discs/90 m'2 and beneficial

nematodes (Steinernema feltiae ) (ScanMask™IPM Laboratories, Inc., Locke,

NY 13092-0300 USA) were applied in a media drench as a control measure.

Predatory mites (Amblyseius cucumeris, Hypoaspis miles) were used to control

thrips (Frankliniella spp.) and a parasitic wasp (Aphidius colemanii) was used as

a control for aphids (Myzsus spp.) (IPM Laboratories, Inc., Locke, NY 13092-

0300 USA). Biological controls were discontinued during July and August of

2006 at which time Duraplex®TR and Pyrethrum® TR micro total release

insecticides (Whitmire Micro-Gen Research Laboratories, Inc. 3568 Tree Court

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Industrial Blvd. St. Louis MO 63122-6682 USA) were used on alternate weeks for

control of the previously mentioned pests and two-spotted spider mites

(Tetranychus urticae).

2.3.1 Seedling Production Experiment

Moringa seeds were collected from the low plain, savannah region of

Kasese District in western Uganda during December 2006 and also were

obtained from Haiti (G. Ju, ECHO, 17391 Durrance Road, N. Ft. Myers, FL

33917 USA). Seeds were left intact or dehulled and sown dry or pre-soaked for

24 hours in tap water (EC = 0.2 dS-rrf1, pH = 7.0) placed in 2.5-cm rockwool

cubes (Grodan Company, Agro Dynamics, Coppell, TX 75019 USA) and placed

in 56 x 28 x 7-cm Perma-Nest plant trays (Park Seed Company, 1 Parkton Ave,

Greenwood, SC 29647 USA). Seeds remained uncovered without germination

media. Plant trays were placed in a Percival E 36L growth chamber (Percival

Scientific, Perry, IA 50220 USA) at a temperature of 25°C. Seeds were irrigated

by hand with tap water and were provided with a 16-hour photoperiod at a photon

fluence rate of 250 pmol m^ s'1. Each treatment consisted of 84 seeds and

germination percentage and time to germination were calculated for each

treatment.

2.3.2 Rockwool Slab Culture Experiment

Six individual recirculating hydroponic systems were constructed for the

rockwool slab culture experiment. Seedlings were transplanted to 10 x 10 x 8-cm

rockwool transplant blocks (Grodan Company, Agro Dynamics, Coppell, TX

75019 USA) and grown for an additional two weeks before being placed on 90 x

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15 x 7.5-cm rockwool slabs (Grodan Company, Agro Dynamics, Coppell, TX

75019 USA). Five seedlings were spaced approximately 15 cm apart on each

rockwool slab. The top of the plastic wrapping of rockwool slabs was cut with a

razor into the shape of an “X”. Slabs were wetted thoroughly with tap water

before the four resulting triangular pieces of plastic were lifted so that each

transplant block could be placed directly on the rockwool slab and secured using

a 0.635 x 15-cm tubing stake. Three 8-cm diagonal slits were made on each

side of the rockwool slab to permit drainage from the slabs.

Rockwool slabs were placed on sections of 122 x 122 cm x 4-cm plastic

ebb and flow trays (Midwest Gromaster, 48W 801 II Rt. 64, Maple Park, IL.

60151 USA). Ebb and flow trays were inserted into wooden frames constructed

of 2-cm, 5-ply sections of plywood measuring 123 x 123-cm to which 2.5 x 7.5-

cm lengths of pine furring strip had been attached as sides using 6-cm

galvanized screws. Individual frames were elevated on the supply (high) side by

using a standard plastic bulb crate and were supported at the discharge side by

a low density polyethylene tub (Kormex Plastics, La Mirada, CA. 90638 USA)

measuring 91 x 61 x 20-cm and having a volume of approximately 80 liters to

which nutrient solution was added.

The nutrient solution consisted of I.Og L'1 5-11-26 Hydro-Sol®and 0.75 g

L'1 15.5-0-0 Calcium Nitrate Plus™ (Scotts Sierra Horticultural Prod. Co., 14111

Scotts Lawn Rd., Marysville, Ohio 43041 USA), and 0.25 g L'1 MgS04-7H20

Epsogrow® Epsom Salts (Hydro Agri North America 100 North Tampa Street,

Suite 3200, Tampa, Florida 33602 USA) and was suitable following earlier

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soilless culture trials with moringa. Electrical conductivity (EC) was maintained

between 2.0 and 2.3 dS-m'1. Acidity was monitored and was corrected to and

maintained between pH 5.5 and 6.0 using phosphoric acid. EC and pH were

measured with a Hanna HI 9813 portable Gro Chek meter (Hanna Instruments,

584 Park East Drive, Woonsocket, Rl 02895 USA).

Individual plants were supplied with nutrient solution with 6-mm vinyl

distribution tubing secured by tubing stakes attached to 37.8-liter per hour

pressure compensating point source emitters (DT025, TS025, PC-10, Rain Bird

International, Inc., Glendora, CA 91741 USA). Nutrient discharge from the

distribution tubing was directed to the base of individual transplant blocks (the top

of the slab) rather than to the top of transplant blocks to ensure that the area

immediately around each plant stem remained only slightly moist to somewhat

dry. Emitters were attached to 12.7-mm low density polyethylene tubing (Cresline

HD-125, Cresline Plastic Pipe Company, Evansville, IN 47715 USA) and were

fed by a 946-liter per hour magnetically driven centrifugal utility pump (Model

MD2, Danner Mfg., Inc., Central Islip, NY 11749 USA). A digital timer (Radio

Shack No. 61-1060, Tandy Corp., Ft. Worth, TX 76102) was used to operate

each system automatically.

2.3.3 pH Determination Experiment

Seeds were dehulled, sown 17 April 2006 in 2.5-cm rockwool cubes

(Grodan Company, Agro Dynamics, Coppell, TX 75019 USA) and placed in 56 x

28 x 7-cm Perma-Nest plant trays (Park Seed Company, 1 Parkton Ave,

Greenwood, SC 29647 USA). Trays were placed in a Percival E 36L growth

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chamber (Percival Scientific, Perry, IA 50220 USA) at a temperature of 25°C and \

provided with a 16-hour photoperiod at a photon fluence rate of 250 pmolm'^s'1.

Seedlings were transplanted on 3 May 2006 to 7.5 x 7.5 x 6.5-cm rockwool

transplant blocks (Grodan Company, Agro Dynamics, Coppell, TX 75019 USA)

and grown for an additional 2 weeks before being placed on 90 x 15 x 7.5-cm

rockwool slabs (Grodan Company, Agro Dynamics, Coppell, TX 75019 USA) in a

recirculating hydroponic system on 17 May 2006.

Five pH set-points were employed: 5.5, 6.0, 6.5, 7.0, and 7.5. Each

treatment consisted of three rockwool slabs each having 8 seedlings spaced at

approximately 10-cm for a total of 24 plants. Seedlings were 6 to 10 cm in height

and 3 to 4 mm in diameter. pH set points were monitored daily and corrected as

needed with phosphoric acid or potassium hydroxide. Electrical conductivity

(EC) levels were maintained between 2.0 and 2.3 dSm'1. EC and pH were

measured using a Hanna HI 9813 portable Gro Chek meter (Hanna Instruments,

584 Park East Drive, Woonsocket, Rl 02895 USA). Plants were harvested after

25 days and dry weights were determined for each treatment following drying in a

70° C oven for 48 hours.

Five individual recirculating hydroponic systems were constructed for the

pH treatments, similar to those constructed for Experiment 2.3.2. Rockwool

slabs were placed on sections of 61 x 123 cm x 4-cm plastic ebb and flow trays

(Midwest Gromaster, 48W 801 II Rt. 64, Maple Park, IL. 60151 USA). Ebb and

flow trays were inserted into wooden frames constructed of 2-cm, 5-ply sections

of plywood measuring 61 x 123-cm to which 2.5 x 7.5-cm lengths of pine furring

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strip had been attached as sides using 6-cm galvanized screws. The remaining

equipment and procedure used for this experiment was the same as that used in

Experiment 2.3.2.

2.3.4 Aeroponic Culture Experiment

A commercially available recirculating aeroponics system (Aeroflo®,

General Hydroponics, P.O. Box 1576, Sebastopol, CA 95473 USA) was

determined to be suitable for initial attempts to grow moringa aeroponically. The

system consisted of a pump, nutrient solution reservoir, distribution manifold, and

tubular grow chambers. Standpipes within each tubular grow chamber permitted

the height of nutrient solution retained in each grow chamber to be adjusted.

Twenty seedlings were germinated in rockwool cubes as in Experiment 2.3.1,

placed in 7.6-cm diameter plastic net pots filled with 8 to 16-mm diameter kiln-

fired clay pebbles having a neutral pH (CropKing, Inc., 5050 Greenwich Road,

Seville, OH 44273-9413 USA) and placed in the aeroponics system on 12 July

2006.

Previous trials using a 50:50 mixture of coir and coarse perlite as a

growing medium in net pots suggested that this medium retained too much

moisture, contributing to rotting at the base of the stem. Seedlings were spaced

approximately 10-cm on center. Dissolved oxygen in the nutrient solution was

monitored using an Oakton DO 300 Series dissolved oxygen data meter

(OAKTON Instruments P.O. Box 5136, Vernon Hills, IL 60061 USA). Electrical

conductivity (EC) levels were maintained between 2.0 and 2.3 dSm'1. Acidity

was monitored, corrected, and maintained between pH 5.5 to 6.0 with phosphoric

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acid. EC and pH were measured using a Hanna HI 9813 portable Gro Chek

meter (Hanna Instruments, 584 Park East Drive, Woonsocket, Rl 02895 USA).

Standpipes were raised upon initial seedling establishment to ensure adequate

nutrient solution to roots and were lowered with increased root growth. Plants

were harvested after 28 days and dry weights were determined following drying

in a 70°C oven for 48 hours. Twenty seedlings were grown concurrently in

rockwool slab culture to compare moringa growth between the two systems.

2.4 Results

2.4.1 Seedling Production Experiment Results

Germination rates of approximately 65% were obtained for soaked and dry

dehulled seeds and were nearly identical for the Uganda and Haiti seed sources

(Table 2.1, Table 2.2). Dehulled seeds began germinating at 5 days after

sowing, averaging about 8 days after sowing. Seeds with hulls germinated

poorly, especially those from Uganda (Figure 2.1, Figure 2.2). Soaked seeds

with hulls from Haiti had a 10% higher germination rate and germinated 1.5 days

faster than dry seeds with hulls. Seedlings were robust and of high quality.

Seeds were observed also to germinate in the dark and at low light levels

of approximately 15 pmol-m'^s'1, although this light intensity was inadequate for

seedling growth. Supplemental incandescent lighting in addition to fluorescent

light did not have an effect on germination rates or time. Soaking hulled seeds

for 48 hours rather than 24 hours did not affect germination rate. An attempt to

scarify hulled seeds using heated water also was unsuccessful, resulting in no

germination. Water was heated to 100°C and removed from the heat source.

36

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Num

ber

of g

erm

inat

ed s

eeds

Seeds (n=50) were placed in the hot water once it had stopped boiling and left for

24 hours as the water cooled.

Table 2.1. Number (x/84) of germinated seeds, percent germination, and days to germination for four moringa seed (Uganda) treatments.

Seed Treatment Number

germinated Percent

germinated Days to

germination Soaked/Dehulled 55 65.5 8.7 Dry/Dehulled 54 64.3 8.8 Soaked/Hulls 6 7.1 8.5 Dry/Hulls 8 9.5 8.3

■ Dry/Dehulled .Soaked/Dehulled a- Dry/Hulls Soaked/Hulls

Fig. 2.1. Number of germinated moringa seeds (n=84; source=Uganda) in response to a 16-hour photoperiod and fluence level of 250 pmolm'^s'1 as a function of seed treatment and time.

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Table 2.2. Number (x/84) of germinated seeds, percent germination, and days to germination for four moringa seed (Haiti) treatments.

Seed Treatment Number

germinated Percent

germinated Days to

germination

Soaked/Dehulled 56 66.7 7.4

Dry/Dehulled 54 64.3 7.8

Soaked/Hulls 41 48.8 7.7

Dry/Hulls 32 38.1 9.3

•♦—Dry/De hulled —■— Soaked/Dehulled —Dry/Hulls —•—Soaked/Hulls

Fig. 2.2. Number of germinated moringa seeds (n=84; source=Haiti) in response to a 16-hour photoperiod and fluence level of 250 pmolm'^s'1 as a function of seed treatment and time.

2.4.2 Rockwool Slab Culture Experiment Results

Three replicates of 20 plants each were placed in recirculating hydroponic

rockwool slab systems on 24 May 2006 and harvested 48 days later on 11 July

2006. Growth was excellent as stem caliper increased 74% and height

increased more than 2.5 times relative to the original size (Table 2.3).

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Table 2.3. Initial and final stem caliper, initial and final height, buds released, and dry weights for 60 moringa seedlings grown 48 days in hydroponic rockwool slab culture.

Initial measurements

Final measurements

Replicate Stem

caliper 5/24/06

(mm)

Height 6/1/06 (cm)

Stem caliper 7/11/06

(mm)

Height 7/11/06

(cm)

Dry weight 7/14/06 (g/plant)

Buds released

1(n=20) 9 40.5 16 110.1 36.3 0

2(n=20) 9 43.7 15 108.3 26.6 0

3(n=20) 9 42.4 16 123.2 41.8 0

Mean (n=60) 9 42.2 16 113.9 34.9 0

Rockwool slabs were managed at higher moisture levels than might be

used traditionally in a commercial growing operation where slabs would be

managed to yield 10 to 20% drain water daily in an open system. The closed

systems used for this experiment permitted this action and provided an

opportunity to protect against excessive salt buildup in slabs, with slab drain

levels estimated to approach 50% on some hot and sunny days. Slab EC levels

were monitored periodically by drawing samples with a syringe to ensure that

they stayed close to the nutrient feed EC levels. No signs of stress were

observed due to these high root-system water levels. An irrigation system

distribution uniformity (DU) analysis was performed on system emitters to

compare output volume and ensure that seedlings were being fed equal amounts

of nutrient solution. Distribution tubing was removed from tubing stakes and

emitter discharge captured in 250 ml beakers. The mean of the lowest 25% of

catchments was divided by the overall mean and expressed as a percentage.

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DU values of 77 to 82% were calculated and considered acceptable due to the

high nutrient solution feed rates, close plant spacing, and rockwool slabs shared

by multiple plants.

2.4.3 pH Determination Experiment Results

Plants were harvested by decapitating them at the base of their stem,

flush with the top of the rockwool transplant block. After 25 days, plant height

and dry weight yields were calculated. Results suggest that a pH range of 5.5 to

6.0 is most desirable for soilless culture of moringa (Table 2.4).

Table 2.4. Effect of pH on height and dry weight of moringa seedlings grown in hydroponic culture for 25 days.

Measurement^ pH

treatment Height (mm)

Dry weight (g)

5.5 214a 1.85ab 6.0 243a 2.20a 6.5 188a 1,55bc 7.0 151b 0.82cd 7.5

2 n h 131b 0.75d

yValues with different letters within columns are significantly different at P< 0.05 (Tukey-Kramer HSD).

2.4,4 Aeroponic Culture Experiment Results

Nutrient solution was added as needed, and dissolved oxygen levels

remained > 5 mg-L'1 throughout the experimental period. Root systems were

white, fibrous, and highly branched with little to no thickening. Top growth was

excellent and no damage to the base of stems due to excessive moisture was

evident on any of the plants. Plants were harvested after 30 days of growth on 12

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August 2006. No significant difference was observed between aeroponic plants

(n=20, 10.1 g dry weight/plant) and plants grown in rockwool (n=20, 13.4 g dry

weight/plant).

2.5 Discussion

Trials during the summer of 2005 using standard greenhouse media

demonstrated that disturbing seedling root systems by transplanting was

damaging to young, developing plants. Young seedlings frequently developed

thick, tuberous taproots making transplanting difficult. Seedling production for

soilless culture necessitates selecting a medium that minimizes transplanting

shock. Rockwool cubes were selected since they could be used in transplanting

of seedlings to rockwool blocks and slabs and were of adequate size to

accommodate the relatively large-sized moringa seeds. Moringa seed

germination has mistakenly been reported by others to be epigeal (Nautiyal and

Venkataraman, 1987; Parrotta, 1993). Cotyledons remain belowground and

germination is, therefore, hypogeal.

Germination rates of dehulled seeds were similar to those reported by

others (Katende et al., 1995). Hulled seeds, especially those from Uganda, had

low germination rates. Seeds were dehulled by hand, and it was apparent that

Uganda seeds had thicker hulls that were more difficult to remove compared to

Haiti seeds. It is possible that germination of hulled seeds may be aided in soil

systems and that seeding in rockwool eliminated the opportunity of microbial

breakdown of hulls. Germination occurred in the dark as well as with minimal

light levels (15 pmol m^ s'1), although this light intensity was insufficient for

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subsequent growth. The photon fluence rate of 250 pmol-m'^s'1 and 16-hour \

lighting period (14.4 mol-day) yielded high quality seedlings for use in

subsequent experiments. Lateral root development was evident in rockwool

germinated seedlings, unlike the thickened roots previously observed.

Seedlings grown in rockwool slab culture grew approximately 1.5 cm in

height per day. The 34.9 g per plant dry weight yield obtained at 15 x 15-cm

spacing would result in slightly fewer than 450,000 plants per hectare and

approximately 15.5 metric tons of dry matter per hectare (118 metric tons per

hectare per year). Seedlings exhibited strong monopodial growth and no lateral

buds were released during this experiment. The wide range of acid tolerance

reported for moringa was evident as seedlings did not exhibit visible deficiency

symptoms or abnormal growth patterns at the pH treatments utilized. Height

and dry weights were greatest when growing moringa seedlings between pH 5.5

to 6.5. Maintaining a dry region around seedlings stems was critical to aeroponic

production and was accomplished by using clay pebbles to stabilize seedlings in

net pots. Root systems were fibrous and formed an extensive mat within the

growing tube, linking root systems of adjacent plants together.

Moringa is known as “Never Die” in parts of West Africa (Morton, 1991).

During the course of these experiments, 24 seedlings growing in 1-liter pots were

without irrigation for 3 months and left in a greenhouse that at times reached

temperatures of 48 C. Two days after watering plants resumed active growth

and all survived. A dry-tropic, xerophytic, multipurpose tree that can withstand

extended periods of drought was grown successfully using soilless culture with

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two recirculating hydroponic systems. Aeroponic culture can be used to produce

uncontaminated moringa root biomass, whereas hydroponic production within the

controlled environment of a greenhouse can be used to ensure high quality and

consistent leaf biomass production.

2.6 Literature Cited

Albrecht, J. (ed.). 1993. Tree seed handbook of Kenya. GTZ/Kenya Forestry Seed Centre, Kenya Forestry Research Institute, Nairobi.

Bennett, R.N., F.A. Mellon, N. Foidl, J.H. Pratt, M.S. Dupont, L. Perkins, and P. A. Kroon. 2003. Profiling glucosinolates and phenolics in vegetative and reproductive tissues of the multi-purpose trees Moringa oleifera L. (Horseradish Tree) and Moringa stenopetala L. J. Agric. Food Chem. 51(12):3546-3553.

Bosch, C.H., 2004. Moringa oleifera Lam. [Internet] Record from Protabase. Grubben, G.J.H. & Denton, O.A. (Editors). PROTA (Plant Resources of Tropical Africa / Resources vegetales de I’Afrique tropicale), Wageningen, Netherlands. http://database.prota.org/search.htm._Accessed 14 October 2005.

Craker, L.E. 1999. Trends in medicinal and aromatic plant production in the United States. Acta Hort. (ISHS) 502:71-76. http://www.actahort.org/books/502/502_8.htm.

Craker, L.E. and Z.Gardner. 2005. Sustaining the harvest: challenges in MAP production and markets. Acta Hort. (ISHS) 676:25-30. http://www.actahort.org/books/676/676_2.htm.

Fahey, J. W. 2005. Moringa oleifera: a review of the medical evidence for its nutritional, therapeutic, and prophylactic properties. Part 1. Trees for Life Journal 1:5. http://www.TFLJournal.org/article.php/20051201124931586.

Flynn, S., R.M. Turner, and J.B. Dickie. 2004. Seed information database (release 6.0, October 2004) http://www.rbgkew.org.uk/data/sid.

Foidl, N., H.P.S.Makkar, and K. Becker. 2001. The potential of Moringa oleifera for agricultural and industrial uses. In: The miracle tree - the multiple attributes of Moringa. Church World Service, Dakar, Senegal. 45-76.

Fuglie, L. 2001. The miracle tree - the multiple attributes of Moringa. Church World Service, Dakar, Senegal.

43

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Hayden, A.L., T.N. Yokelsen, G.A. Giacomelli, and J.J. Hoffmann. 2004. Aeroponics: an alternative production system for high-value root crops. Acta Hort. (ISHS) 629:207-213. http://www.actahort.org/books/629/629_27.htm.

Hoshmand, A.R. 1998. Statistical Methods for Environmental and Agricultural Sciences. 2nd ed. CRC Press, Florida.

Iqbal, S. and M.l. Bhanger. 2006. Effect of season and production location on antioxidant activity of Moringa oleifera leaves grown in Pakistan. J. Food Compos. Anal. 19:(6-7):544-551.

Katende A.B., A. Birnie and B.Tengnas. 1995. Useful trees and shrubs for Uganda: identification, propagation and management for agricultural and pastoral communities. Regional Soil Conservation Unit, RSCU/SIDA, Technical Handbook Series No. 10. ISBN 9966-896-22-8. 710 + 24 pp.

Manh, L.H., N.N.X. Dung, and T.P. Ngoi. 2005. Introduction and evaluation of Moringa oleifera for biomass production and as feed for goats in the Mekong Delta. Livest. Res. Rural Dev.17(9):Article #104. Retrieved, January 4, 2007 from http://www.cipav.org.co/lrrd/lrrd 17/9/manhl 7104.htm.

McBurney, R.P.H., C. Griffin, A.A. Paul, and D.C. Greenberg. 2004. The nutritional composition of African wild food plants: from compilation to utilization. J. Food Compos. Anal. 17:277-289.

Morton, J.F. 1991. The horseradish tree, Moringa pterygosperma (Moringaceae)- a boon to arid lands? Econ. Bot. 45(3): 318-333.

Nautiyal, B.P. and K.G. Venkataraman. 1987. Moringa (Drumstick) - an ideal tree for social forestry: growing conditions and uses - part 1. Myforest 23:53-58.

Olson, M.E., and S. Carlquist. 2001. Stem and root anatomical correlations with life form diversity, ecology, and systematics in Moringa (Moringaceae). Bot. J. Linn. Soc.135:315-348.

Palada, M.C. 1996. Moringa (Moringa oleifera Lam.): a versatile tree crop with horticultural potential in the subtropical United States. HortScience 3:794-797.

Palada, M.C. and L.C. Chang. 2003. Suggested cultural practices for Moringa. Asian Vegetable Research and Development Center pub. #03-545. PO Box 42, Shanhua, Tainan 74199; Taiwan ROC.

Parrotta, J.A. 1993. Moringa oleifera Lam. Reseda, horseradish tree. SO-ITF- SM-61. New Orleans, LA:U.S. Department of Agriculture, Forest Service, Southern Forest Experiment Station. 6 p.

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Price, M. The Moringa Tree. 1985. Revised 2000 by K. Davis. Educational Concerns for Hunger Organization (ECHO) Technical Note. www.echotech.org/technical/technotes/moringabiomasa.pdf.

Ramarathnam, N., T. Osawa, H. Ochi and S. Kawakishi. 1995. The contribution of plant food antioxidants to human health. Trends Food Sci. Technol. 6:75-82.

Rao, M.R., M.C. Palada, and B.N. Becker. 2004. Medicinal and aromatic plants in agroforestry systems. Agrof. Systems 61-62(1-3): 107 - 122.

Ray, K., R. Hazra, and D. Guhar. Central inhibitory effect of Moringa oleifera root extract: possible role of neurotransmitters. Indian J. Exp. Biol. 41:1279-1284.

Resh, H. 2001. Hydroponic Food Production. 6th ed. Woodbridge Press, Santa Barbara, California.

Sail, J., A. Lehman, and L. Creighton. 2001. JMP Start Statistics - a guide to statisticsand data analysis using JMP® and JMP IN® software. 2nd ed. Duxbury Thompson Learning, California.

Seshadri, S., and V.S. Nambiar, 2003. Kanjero (Digera an/ensis) and drumstick leaves (Moringa oleifera): nutrient profile and potential for human consumption. In: Plants in human health and nutrition policy, Simopoulos, A.P. and C. Gopalan, eds. World Rev. Nutr. Diet 91:41-59.

Schabel, H.G., 2004. Moringa oleifera Lam. In: Vosso, J.A. (Editor). Tropical tree seed manual. [Internet] http://www.rngr.net/Reforestation/Publications/TTSM. Accessed October 2005.

Sharma, G.K. and V. Raina. 1982. Propagation techniques of Moringa oleifera Lam. In: Improvement of forest biomass:symposium proceedings:. 175-181. Edited by P.K. Khosla. Indian Society of Tree Scientists.

Siddhuraju, P. and K. Becker. 2003. Antioxidant properties of various solvent extracts of total phenolic constituents from three different agroclimatic origins of drumstick tree (Moringa oleifera Lam.) leaves. J. Agric. Food Chem. 51(8):2144- 2155.

Stephenson, K., and J. Fahey. 2004. Development of tissue culture methods for the rescue and propagation of endangered Moringa spp. germplasm. Econ. Bot. 58:S116-S124.

Sutherland, J., 1999. The Moringa oleifera pages. [Internet] Department of Engineering, University of Leicester, Leicester, United Kingdom. Accessed January 2004. http://www.le.ac. uk./engineering/staff/Sutherland/moringa/moringa.htm.

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CHAPTER 3

THE EFFECT OF POINT OF DECAPITATION ON LATERAL BUD

OUTGROWTH OF MORINGA SEEDLINGS GROWN IN

HYDROPONIC CULTURE

Keywords: agroforestry, apical dominance, auxin, Moringa oleifera

3.1 Abstract

Moringa (Moringa oleifera Lam.) is a small multipurpose tree cultivated in

the dry tropics. The leaves of moringa are valued for their human nutritional

benefits as well as for their use as a livestock feed. The terminal growing point of

moringa must be trimmed in order to promote branching, increase yields, and

facilitate harvesting, as failure to cut the main trunk will result in straight, fast¬

growing trees with minimal leaf production on only the primary stem. Moringa

seedlings are subjected to frequent and extreme levels of vegetative harvest

when grown in intensive agroforestry production systems, and little research has

been devoted to the response of multipurpose trees to this type of management.

In this study, decapitation induced outgrowth of lateral buds of vigorous,

hydroponically grown moringa seedlings, and no lateral buds were released by

intact plants that were not decapitated. This release from apical dominance was

repressible by the application of exogenous auxin (0.5% IAA) to the stumps of

decapitated seedlings. Stem nodes (counted acropetally) were selected as

reference points to establish the heights to which seedlings would be

decapitated. Seedlings decapitated to node 1 (height=4.6 cm) were two days

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slower in releasing the number of buds that matched the number of elongated

shoots they would eventually produce than seedlings decapitated to node 6

(height= 15.6 cm). Node 6 seedlings released buds more quickly and produced

three times the dry weight per plant than node 1 seedlings, even though the

number of buds that grew out was approximately the same for each treatment

(node 1=2.2, node 6=2.3). Decapitation at the base of seedlings resulted in high

levels of mortality (82%).

Mean time to budbreak (MTB) decreased, and total dry weights increased

with increasing acropetal nodal point of decapitation (increasing stump height).

The smallest MTB values and largest total dry weights were observed for node 6

(15.6 cm) seedlings, suggesting that increasing stump heights further may result

in even greater dry weights. Seedlings decapitated to 30 cm (approximately 12

nodes) produced nearly 2 more buds per plant and more than twice the dry

weight yield compared to those decapitated to 40 cm (approximately 16 nodes).

Seedlings pinched to remove just 5 or 10 cm of apical stem released less than 2

buds per plant and had low dry weight yields. The site of decapitation with

respect to the percentage of stem removed appears to be more important than

the actual height to which a seedling is decapitated to maximize regrowth

potential of moringa in high-density stands.

3.2 Introduction

Moringa is the sole genus of the Moringaceae, and with just thirteen

species is one of the most phenotypically varied groups of angiosperms (Olson

and Carlquist, 2001). The Moringa genus has been divided into four habit

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classes based on their gross appearance in the field: bottle trees, sarcorhizal

trees, slender trees, and tuberous shrubs. Moringa is classified as a slender tree

(Olson and Carlquist, 2001) typically reaching a height of 7 to 12 meters (Foidl et

al., 1999) and is native to the sub-Himalayan regions of northwest India. Moringa

is cultivated as a multipurpose tree in many regions of Africa, Arabia, Southeast

Asia, the Pacific and Caribbean Islands, and South America (Fuglie, 2001;

Palada, 1996) and stands out among the vegetables of the world as one of the

most ecologically friendly and highly nutritious crops (Seshadri and Nambiar,

2003).

Roots, leaves, and seeds are used for industrial, food, and medicinal

purposes (Palada, 1996). Almost every part of the plant has value for food, with

roots used as a substitute for horseradish and the leaves eaten as greens, in

vegetable curries, and used for seasoning (Duke, 1983). Leaves are eaten fresh

or cooked, and moringa leaf powder can be stored for months without loss of

nutritional value. Ounce for ounce, moringa leaves contain more beta-carotene

than carrots, more iron than spinach, more potassium than bananas, more

Vitamin C than oranges, and more protein than peas (Palada et al., 2003).

Tender, young leaves are preferred for cooking (Morton, 1991) and have been

reported to contain higher levels of protein, lipid, and vitamins A, Bi, B6, and C

than mature leaves (D’Souza and Kulkarni, 1993).

The use of indigenous, wild plants is reported to be increasing in sub-

Saharan regions where social and political instability, disruption in farming or

food commerce, or adverse climatic conditions occur. Moringa can persist

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through dry seasons in the dry-tropics of Africa and has been identified as a high

protein famine food (Sena et al., 1998). A recent review of the reported

nutritional, therapeutic, and prophylactic qualities of moringa indicates that “the

nutritional properties of moringa are now so well known that there seems to be

little doubt of the substantial health benefit to be realized by consumption of

moringa leaf powder in situations where starvation is imminent” (Fahey, 2006).

Moringa has been promoted by non-governmental agencies such as the Church

World Service (CWS), Trees For Life (TFL) and Educational Concerns for

Hunger Organization (ECHO) to combat malnutrition (Fuglie, 1999; Price, 2000;

Fahey, 2006).

Moringa shows promise as a green manure crop and as a livestock feed

and has been used as a multipurpose tree component in alley and hedgerow

cropping systems (Foidl et al., 2001; Murro et al., 2003; Price, 2000; Soliva et al.,

2005). Moringa exhibits a typical strong apical dominance phenotype, resulting

in the monopodial habit of this slender tree. Seedlings usually grow straight and

tall and develop sparse canopies with little to no branching. Pollarding, coppicing,

lopping, and pruning are recommended to promote moringa branching (Bosche,

2004), and to encourage lateral bud release and new vegetative growth.

Individual plants are pruned in agroforestry forage production systems to a

height of 15 to 20 cm when the tree is 1 to 2 m tall to remove the apical growing

shoot. This extreme vegetative harvest essentially results in total plant

defoliation. Regrowth time is typically 35 days, with significant mortality occurring

among plant populations (Foidl, N., personal communication, 2003, 2005).

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Intensive planting density studies of moringa in agroforestry production systems

suggest the potential for extremely high biomass production. Trials in Nicaragua

ranged from 10,000 to 16,000,000 plants/ha'1 and suggested an optimum density

of 1,000,000 seeds/ha'1 (10 x 10 cm spacing) in sandy, well-drained, fertile soil. A

four year study at the optimum density of 1,000,000 plants/ha'1 under irrigation

and fertilization and that 9 cuttings per year provided yields of 580 metric tons of

fresh material/ha’Vyr*1 equivalent to approximately 99 tons of dry matter (Foidl et

al., 1999; Francis, 2005).

The repeated vegetative harvest of moringa seedlings by decapitation and

the resulting proliferation of vegetative shoots will cause these plants in many

ways to resemble herbaceous plants more than woody plants. High-density

spacing patterns of moringa depend primarily on shoot system architecture and

response to vegetative harvest. Understanding the extent to which lateral bud

outgrowth occurs and the resulting plant geometry and stem architecture will

dictate appropriate spacing patterns for woody species in short rotation intensive

culture (Wu, 1994).

Moringa should be, in some way trimmed to promote branching, increase

yields, and facilitate harvesting, as failure to cut the main trunk will result in

straight, fast growing trees with leaves and pods on only the primary stem

(Palada et al., 2003). Little horticultural research is available regarding the

response of multipurpose trees to extreme levels of vegetative harvest, and

anecdotal reports that are available vary greatly in their recommendations.

Understanding the response of moringa to severe cutback is a requisite to

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determining optimum spacing strategies and managing production for vegetative

biomass. The objective of this study was to examine lateral bud release as a

function of point of apical meristem decapitation of moringa seedlings to

elucidate pruning management strategies that will maximize production.

3.3 Materials and Methods

Experiments were conducted in the greenhouses and laboratories of the

Department of Plant Science at the State University of New York at Cobleskill,

New York, USA. Where applicable, ANOVA followed by the Tukey-Kramer HSD

paired mean comparisons test (JMP®, v.4.0.3, SAS Institute, Inc., Cary, NC

27513 USA) were used to test for significant differences between treatments

(Hoshmand, 1998, Sail et al., 2001).

Seeds of moringa were collected from the low plain, savannah region of

Kasese District in western Uganda during December 2006 and were sown 21

March 2006 in 2.5-cm rockwool cubes. Seeds were germinated under fluorescent

lighting in a Percival E 36L growth chamber (Percival Scientific, Perry, IA, 50220

USA) at a photon fluence rate of 250 pmol m^ s'1 and 16-hour photoperiod.

Seedlings were transplanted to 7.5 x 7.5 x 6.5-cm rockwool transplant blocks on

1 May 2006, and placed on 90 x 15 x 7.5-cm rockwool slabs (Grodan Company,

Agro Dynamics, Coppell, TX 75019 USA).

The nutrient solution consisted of 1.0 g-L'1 5-11-26 Hydro-Sol£ and 0.75

g-L'1 15.5-0-0 Calcium Nitrate Plus™ (Scotts Sierra Horticultural Prod. Co.,

14111 Scotts Lawn Rd., Marysville, Ohio 43041 USA), and 0.25 g-L'1

MgS04-7H20 Epsogrow" epsom salts (Hydro Agri North America 100 North

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Tampa Street, Suite 3200, Tampa, Florida 33602 USA). Electrical conductivity \

levels were maintained between 2.0 and 2.3 dSm'1 and acidity was monitored,

corrected to, and maintained at pH 6.0 with phosphoric acid. Both electrical

conductivity and pH were measured using a Hanna HI 9813 portable Gro Chek

meter (Hanna Instruments USA HQ, 584 Park East Drive, Woonsocket, Rl 02895

USA).

Yellow and blue sticky cards (IPM Laboratories, Inc., Locke, NY 13092-

0300 USA) were used to monitor insect pests throughout the experiments, and

biological pest controls were used during May and June of 2006. To monitor

fungus gnat (Orfelia spp.) larvae, potato discs were placed on rockwool

transplant blocks and in pots at the rate of 10 discs/90 m'2 and beneficial

nematodes (Steinernema feltiae ) (ScanMask™IPM Laboratories, Inc., Locke,

NY 13092-0300 USA) were applied in a media drench as a control measure.

Predatory mites (Amblyseius cucumeris, Hypoaspis miles) were used to control

thrips (Frankliniella spp.) and a parasitic wasp (Aphidius colemanii) was used as

a control for aphids (Myzsus spp.) (IPM Laboratories, Inc., Locke, NY 13092-

0300 USA). Biological controls were discontinued during July and August of

2006 at which time Duraplex®TR and Pyrethrum® TR micro total release

insecticides (Whitmire Micro-Gen Research Laboratories, Inc. 3568 Tree Court

Industrial Blvd. St. Louis MO 63122-6682 USA) were used on alternate weeks for

control of the previously mentioned pests and two-spotted spider mites

(Tetranychus urticae).

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Rockwool slabs were watered and fertilized by hand, and moisture levels

managed by maintaining a target of 10 to 20 percent drainage from individual

slabs for Experiment 3.3.1. Experiments 3.3.2 to 3.3.4 utilized a closed,

recirculating, hydroponic system. Nutrient solution was contained in low-density

polyethylene tubs (Kormex Plastics, La Mirada, CA. 90638 USA) measuring 91 x

61 x 20-cm and having a volume of approximately 80 liters. Individual plants

were supplied with nutrient solution by 6-mm vinyl distribution tubing secured by

tubing stakes attached to 10 gallon per hour pressure compensating point source

emitters (DT025, TS025, PC-10, Rain Bird International, Inc., Glendora, CA

91741 USA). Emitters were attached to 12.7-mm low density polyethylene

tubing (Cresline HD-125, Cresline Plastic Pipe Company, Evansville, IN 47715

USA) and fed by a 946-liter per hour magnetically driven centrifugal utility pump

(Model MD2, Danner Mfg., Inc., Central Islip, NY 11749 USA). A digital timer

(Radio Shack No. 61-1060, Tandy Corp., Ft. Worth, TX 76102) was used to

automatically operate each system.

3.3.1 Nodal Point of Decapitation Experiment

Treatments consisted of 12 plants each, and seedlings averaged 7 mm in

diameter at the base. Seedlings were decapitated to remove their apical

meristems on 17 May 2006 above nodes 1 to 6 (nodes were counted acropetally)

to determine the optimum point of removal to enhance regrowth of axillary and

adventitious buds. Stem nodes were selected as reference points to establish the

heights to which seedlings would be decapitated. Node 1 was selected as the

lowest point of decapitation as previous observations during trials suggested that

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seedlings would not respond favorably to total cutback to ground level. Total

cutback of 104 seedlings resulted in only 19 plants (18%) releasing buds and

resuming growth. Node 6 was selected as the highest point of decapitation as it

corresponded with the height following decapitation of seedlings managed in

agroforestry forage production systems.

The number of buds released from inhibition was counted daily and the

date of release (when buds = 1 cm. in length) recorded. The mean time to

budbreak (MTB) was calculated for each treatment by multiplying each bud

released by the number of days since the date of decapitation. The total number

of accrued days for each plant (I buds x days) was then divided by the number

of buds released to determine the MTB. Fresh weights of stems and leaves were

determined for each treatment and dry weights were determined following drying

for 48 hours in a 70° C oven. Bud outgrowth was determined by tracking buds

that grew out to at least 40 mm of length, and the number of stems per plant > 40

mm was calculated for each treatment. Total stem length per plant also was

determined.

3.3.2 Decapitation to 30 and 40 cm Experiment

The effect of decapitation to 30 and 40 cm on bud release and dry weight

was examined to determine if increasing stump heights would result in greater

yields than those obtained with decapitation at 15.6 cm. Forty seedlings

averaging 56.5 cm in height were grown as in Experiment 3.3.1 and divided into

two groups and decapitated to either 30 cm (approximately 12 nodes) or 40 cm

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(approximately 16 nodes). The number of buds released, stem number, stem

length, and dry weights were determined for each treatment.

3.3.3 Pinching Experiment

The effect of pinching seedlings to remove 5 or 10 cm of terminal growth

was examined to determine the effect of decapitating only a small portion of

growing tip. Twenty seedlings each were pinched to 5 or 10 cm and forty

seedlings remained intact. The number of buds released, stem number, stem

length, and dry weights were determined for each treatment.

3.3.4 Auxin Replacement Experiment

An auxin replacement apical dominance test of exogenous auxin

repression of lateral bud release was performed to better determine the role that

auxin plays in bud release and outgrowth of moringa seedlings. Seedlings were

decapitated to 15 cm on 20 July 2006. Twelve of the decapitated seedlings had

0.5% IAA (indole-3-acetic acid) mixed in lanolin paste (Carolina Biological Supply

Company, Burlington, NC 27215-3398 USA) applied to each cut surface

immediately following decapitation. Twelve decapitated seedlings were

permitted to grow for one week at which point IAA was applied to the cut surface,

and the remaining twelve decapitated seedlings were untreated. The number of

buds released, stem number, stem length, and dry weights were determined for

each treatment.

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3.4 Results

3.4.1 Nodal Point of Decapitation Experiment Results

Plants were harvested on 7 June 2006, 21 days after decapitation, and dry

weight was measured for each treatment. Nodal point of decapitation affected

the rate of bud release following decapitation (Fig. 3.1). The number of buds

released and speed at which they were released increased with increasing

acropetal nodal point of decapitation. A significant difference among bud release

values was observed among treatments. Seedlings decapitated at node 6 (15.6

cm) released more than twice as many buds compared to those decapitated at

node 1 (4.9 cm) (Table 3.1). The number of buds that grew out (measured as the

number of stems longer than 40 mm) was approximately the same for each

treatment (node 1=2.2, node 6=2.3) and was not significantly different.

When the MTB is calculated for all buds for all days, there is a modest 0.8-

day difference between node 1 and node 6 seedlings (Table 3.1). However, day

7 following cutback was the day by which node 6 seedlings had released the

number of buds equal to the number of stems (2.3) > 40 mm that they would

ultimately produce. Node 1 seedlings had released only 0.7 buds by day 7, and

did not release the number of buds equal to the number of stems (2.2) greater

than or equal to 40 mm that they would ultimately produce until day 9. Node 1

seedlings were two days slower in releasing the number of buds equal to the

number of stems that would elongate compared to node 6 seedlings (Fig. 3.1).

Node 6 seedlings released buds more quickly and ultimately produced three

times the dry weight per plant compared to node 1 seedlings (Table 3.1).

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Seedlings having longer stem lengths remaining after decapitation had

increased numbers of buds for release. Increasing speed of bud release (lower

Table 3.1. Effect of nodal point of decapitation on MTBZ, bud release, number of stems >40mm, total stem length, and dry weight/plant of moringa seedlings.

Node

Height after

decap. (cm)

Measurement7*

MTBZ

(d)

Buds released per plant

Number of

stems >40 mm

Total stem length (mm)

Dry weight (g/plant)

1 4.9 8.5ab 2.9a 2.2a 171a 0.96a

2 6.6 8.8a 4 2ac 2.6a 206a 1.04a

3 8.9 8 2ab 4 3ac 2.5a 229a 1.51a

4 10.7 8.0ab 5.7bc 2.7a 246a 1,97ab

5 13.3 7.6b 5.8bc 3.1a 296a 2.23ab

6 15.6 7.7b 7.3b 2.3a 296a 2.99b ZMTB = mean time to budbreak yMean xWithin columns, means followed by different letters are significantly different (P< 0.05, Tukey-Kramer HSD)

MTB) appears to be a strong indicator of increased stem length and biomass

production (Fig. 3.1). Dry weights increased as the total number of buds

released per plant increased (Fig. 3.2). The advantage of having more buds

released does not appear to be in the total number of stems that grow out, but in

having buds released more quickly, resulting in increased early stem length

which provides greater access to light among competing growing shoots (Fig.

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V

X3 0 (/) CO 0 0 L_ cn -o Z3 Q

0 -Q

E

7 8 9 10

Days after decapitation

11 12

Fig. 3.1. Number of buds released per plant following decapitation of moringa seedlings at nodes 1-6 (n=12).

Node 1

Node 2

-a— Node 3

Node 4

■*— Node 5

Node 6

Buds released per plant (mean, n=12)

Fig. 3.2. Relationship between dry weight and buds released per plant (mean, n=12) following decapitation.

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Increased MTB values (slower bud release) tended to result in fewer buds

released, slower early growth, and lower dry weight. Increasing the speed of bud

release (decreasing MTB), should increase yield. The initial experiment

demonstrated increased rates of bud release and higher dry weights with

increasing heights of decapitation, suggesting that decapitation of stems that are

taller than the maximum of 15.6 cm previously used may result in even greater

growth.

_ 3.5 c\J

3

2.5 -

2 -

1.5 -

1

0.5 -

0 —

150

r^O.86, P=.0073

200 250 300

Total stem length per plant (mm) (mean, n=12)

Fig. 3.3. Relationship between dry weights (g/plant) and total stem length per plant following decapitation (mean, n=12).

3.4.2 Decapitation to 30 and 40 cm Experiment Results

The effect of decapitating seedlings to 30 or 40 cm on bud release and dry

weight was examined to determine if these treatments would result in greater

growth than those obtained with decapitation at 15.6 cm. Moringa seedlings

averaging 56.5 cm in height were decapitated to either 30 or 40 cm on 3 August

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2006 and were harvested on 24 August 2006. Decapitation to 30 cm released

4.7 buds per plant and produced 3.5 g/plant of dry weight compared to 2.8 buds

and 1.7 g/plant of dry weight for plants decapitated to 40 cm (Table 3.2).

Table 3.2. Effect of percent stem removed on number of buds released and dry weight yield of moringa seedlings decapitated to 30 and 40 cm.

Measurement2*

Treatment Original heighty

(cm) Percent stem

removed Buds

released Dry weight (g/plant)

30 cm 56a±13 43a 4.7a 3.5a 40 cm 57a±11 28b 2.8b 1.7b zMean yMean ± SD xWithin columns, means followed by different letters are significantly different (P< 0.05, Tukey-Kramer HSD)

Seedlings decapitated to 30 cm produced more than twice the dry weight

than seedlings decapitated to 40 cm, giving the opposite effect of what was

anticipated based on the results of the initial decapitation experiment. This result

suggests that the proportion of stem removed may be more important than the

height to which a plant is decapitated. Decapitation to 30 cm resulted in 43%

percent of the apical stem removed and 28% removed from seedlings

decapitated to 40 cm. Seedlings decapitated to 30 cm produced nearly 2 more

buds per plant and more than twice the dry weight as plants cut back to 40 cm

(Table 3.2, P< 0.05), even though 15% more fresh biomass was removed at the

time of decapitation than 40 cm seedlings.

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Regression analysis of the forty seedlings suggests that low dry weights

result from a small percentage of stem removal and that dry weights increase as

the percentage of stem removed increases (Fig. 3.4).

0 10 20 30 40 50 60 70

Percent height removed

Fig. 3.4. Polynomial regression of dry weight of moringa seedlings decapitated to 30 and 40 cm as a function of percent of stem height removed (n=40).

3.4.3 Pinching Experiment Results

To better understand the response of moringa to decapitation at a wide

range of seedling heights, 40 moringa seedlings had their apical growing points

pinched to either a targeted 5 or 10 cm of length on 22 July 2006 to test the

effect of removing a small portion of apical growing point (Table 3.3). Forty plants

were left intact without pinching. Pinching occurred at a node so that no

internodal stubs remained, resulting in average actual pinching lengths of 3.4 and

9.6 cm instead of 5 and 10 cm. Plants were grown for one month and harvested

on 23 August 2006.

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Table 3.3. Effect of 5 cm and 10 cm apical decapitation on the number of buds released and dry weight yield of moringa seedlings. Values are per plant.

Treatment Shoot

removed (cm) Buds

released Dry weight (g/plant)

5 cm (n=20) 3.4a 1,89a 17.3a

10 cm (n=20) 9.6b 1.94a 12.5a No decapitation (n=40) 0 0 22.0b 2Mean yWithin columns, means followed by different letters are significantly different (P<0.05, Tukey-Kramer HSD)

No buds were released on plants that were not decapitated, consistent

with results throughout all experiments where intact plants did not release buds.

There was no significant difference between the number of buds released by

treatment (1.89 for 5 cm, 1.94 for TO cm). The dry weights of plants that were not

decapitated were significantly higher than either of the treatments. The dry

weight (g/plant) of pinched stems removed was negligible, relative to the total

mass of the plants at harvest, at just 0.01 g/plant for 5 cm and 0.05 g/plant for 10

cm treatments. The high level of bud release and subsequent flush of growth

previously observed in seedlings which had a greater percentage of growing

point removed was not evident.

3.4.4 Auxin Replacement Experiment Results

Thirty-six seedlings were decapitated to 15 cm on 20 July 2006. Twelve

of the decapitated seedlings had 0.5% IAA (indole-3-acetic acid) mixed in lanolin

paste applied to each cut surface immediately following decapitation; 12

decapitated seedlings were permitted to grow for one week after which IAA was

applied to the cut surface of each seedling, and the remaining 12 decapitated

seedlings were not treated with IAA.

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The application of IAA to the cut surface of the stem immediately following

decapitation resulted in 100% inhibition of lateral bud release. The rate of bud

release of all remaining seedlings and subsequent outgrowth of stems was at

approximately the same rates previously observed with 15 cm decapitated

seedlings (Table 3.4). The application of exogenous auxin (IAA) to decapitated

stumps 7 days after decapitation repressed further outgrowth of buds that were

initially released from apical dominance. There was a significant difference in

stem lengths and dry weights between decapitated seedlings that received no

IAA and decapitated seedlings that had auxin applied 7 days after decapitation.

Control plants had approximately three times the stem length and four times the

dry weight yield compared to auxin treated plants.

Table 3.4. Effect of decapitation, 0.5% IAA, and 0.5% IAA applied 7 days following decapitation on the number of buds released, number of stems, stem length, and dry weight of moringa seedlings. Values are per plant.

Treatment Buds

released Number of

stems Stem length

(mm) Dry weight

yield (g/plant)

Decapitated and no IAA (n=12) 7.3a 2.3a 545a 5.5a

Decapitated and 0.5% IAA (n=12) 0 0 0 0

Decapitated and 0.5% IAA after 7 d 7.8a 2.0a 181b 1.4b

(n=12) Mean

yWithin columns, means followed by different letters are significantly different (P<0.05, Tukey-Kramer HSD)

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3.5 Discussion

The overall architecture of the shoot system is a result of the activity of the

shoot apical meristem, with shoot branching typically involving two distinct

developmental stages: axillary meristem formation in the leaf axils and growth of

axillary buds. “Developmental potential” describes whether or not a bud has a

tendency to remain suppressed or grows out (Napolli et al., 1999). Axillary

meristems develop quickly into axillary shoots in some plants like tomato,

whereas in other plants, axillary bud development may be delayed or buds may

exhibit little growth or remain dormant due to apical dominance and the inhibitory

effects of the terminal bud. Apical, dominance describes the “control exerted by

the shoot apex over the outgrowth of lateral buds” (Cline, 1997), and apical

control is the “inhibition of a lateral branch growth by shoots above it (dista5

shoots)” (Wilson, 2000). Apical dominance is generally considered most

applicable for herbaceous plants or current year woody plant growth whereas

apical control is a better descriptor of the complex branching patterns of woody

plants.

Lateral buds of many tropical tree species and a number of temperate

woody species are sylleptic and grow out the same season they are formed,

resulting in an increase in branch number, leaf area, and general growth.

Sylleptic branching in poplar (Populus spp.) may increase branch number, leaf

area, and overall growth and biomass of trees at a young age (Cline and Dong-

IL, 2002).

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Lateral buds of most temperate woody species are proleptic and do not

grow out during the same season that they are formed, although lateral buds

may release in response to environmental cues. This release from apical

dominance may occur due to a number of factors, including damage of the shoot

apex by disease, herbivory, (Napolli et al., 1999), or by application of cytokinin to

lateral buds or decapitation of the shoot apex by pruning (Cline,1997). Moringa

has a proleptic growth habit but tends to release buds freely once the terminal

growing point has been removed. No lateral buds were released from intact

seedlings that were not decapitated in this study.

High auxin levels may contribute to strong apical dominance and reduced

sylleptic growth and pruning may stimulate growth and branching (Tworkoski et

al., 2005). The inhibitory effect of basipetal polar transport of apically derived

auxin on axillary bud outgrowth has been observed in many plant species. Auxin

replacement experiments that have been carried out on many herbaceous plants

and a number of woody plants provide evidence for this repressive role of

apically produced auxin, and require the release of lateral buds by decapitation in

control (non auxin-treated) plants (Cline, 2000). Axillary bud outgrowth depends

on the ratio of auxin to cytokinin, with bud growth inhibited by auxin and

promoted by cytokinin. Decapitation may trigger initial bud growth via an auxin-

independent mechanism whereas auxin operates after this initial stage (Morris et

al., 2005). Whether or not specific axillary buds exhibit sustained growth or

revert back to the dormant state is influenced by the development of other buds

(Shimizu-Sato and Mori, 2001).

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Decapitation induced outgrowth of lateral buds of vigorously growing

moringa seedlings except for those decapitated at their base, an action which

resulted in high levels of mortality (82%). The release from apical dominance was

100% repressible by the application of exogenous auxin to the stumps of

decapitated seedlings. Auxin application at 7 days following decapitation

repressed further lateral bud outgrowth and significantly surpressed stem lengths

and dry weights even though the number of buds initially released and the

number that grew out were essentially the same. The number of buds released

and speed at which they were released increased with increasing acropetal nodal

point of decapitation.

Dry weight increased linearly with an increase in numbers of buds

released and total stem length per plant, although the number of stems that

ultimately grew out following decapitation remained relatively constant regardless

of the number of buds that are initially released. The speed with which buds were

initially released was critical as early bud release resulted in early stem growth

and a competitive advantage for light.

Since bud release and dry weight were increased with increasing point of

nodal decapitation, it was hypothesized that decapitation further up the stem

would result in increased growth. Even though the rate and numbers of buds

released increased acropetally, pinching a small portion of stem and the apical

growing point of seedlings and leaving a longer length of stem did not increase

bud release further. Plants lacked both an apical growing point and the requisite

length of stem removed to reduce the inhibitory effect of auxin on lateral bud

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release and outgrowth. Consequently, plants were without the concomitant

benefit of high levels of bud release and corresponding compensatory growth

following more severe decapitation and were observed to basically “idle” while

intact plants continued normal growth.

The results of this study suggest that adequate stem length must remain

following decapitation to ensure sufficient bud sites for regrowth, but enough

stem length must also be removed to ensure sufficient elimination of auxin as a

repressor of bud outgrowth. The percentage of stem length removed therefore

appears to be more important than the height to which a seedling is decapitated,

as long as ample stem length remains from which buds are released. Shorter,

30-cm seedlings (43% of the apical stem removed) produced more than twice the

dry weights than taller, 40-cm seedlings (28% of the apical stem removed), the

opposite of what was anticipated based on the results of the initial decapitation

experiment. This result suggests that the amount of stem removed may be more

important than the height to which a plant is decapitated.

The increased use of multipurpose trees in high-density agroforestry

production systems necessitates a better understanding of how these trees

respond to severe, repeated cutback at harvest in order to maximize production

and minimize seedling mortality. This response is complex, and the data

obtained in this study help to develop a framework for understanding the

response of moringa seedlings to decapitation. Anecdotal reports that include

“pinching” as a recommendation should be re-evaluated; the monopodial and

proleptic habit of a moringa seedling can be manipulated by a single decapitation

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event, though the location of the decapitation appears to be critical to maximize \

regrowth potential.

3.6 Literature Cited

Bosch, C.H. 2004. Moringa oleifera Lam. [Internet] Record from Protabase. Grubben, G.J.H. & Denton, O.A. (Editors). PROTA (Plant Resources of Tropical Africa / Resources vegetales de I’Afrique tropicale), Wageningen, Netherlands. http://database.prota.org/search.htm. Accessed 14 October 2005.

Cline, M.G. 1997. Concepts and terminology of apical dominance. Am. J. Bot. 84: 1064.

Cline, M.G. 2000. Execution of the auxin replacement apical dominance experiment in temperate woody species. Am. J. Bot. 87:182-190.

Cline, M.G. and K. Dong-IL. 2002.. A preliminary investigation of the role of auxin and cytokinin in sylleptic branching of three hybrid poplar clones exhibiting contrasting degrees of sylleptic branching. Ann. Bot. 90:417-421.

D’Souza, J., and A.R. Kulkarni. 1993. Comparative studies on nutritive values of tender foliage and mature plants of Moringa oleifera Lam. J. Econ. Tax. Bot. 17(2):479-485.

Duke, J.A. 1983. Handbook of Energy Crops. Electronic publication. http://www.hort.purdue.edu/newcrop/duke_energy/dukeindex.html.

Fahey, J.W. 2005. Moringa oleifera: a review of the medical evidence for its nutritional, therapeutic, and prophylactic properties. Part 1. Trees for Life Journal 1:5. http://www.TFLJournal.org/article.php/20051201124931586.

Foidl, N., L. Mayorga, and W. Vasquez. 1999. Utilization of Marango (Moringa oleifera) as fresh forage for cattle. FAO Anim. Prod. Health Paper (143):341-346.

Francis, G., H.P.S. Makkar, and K. Becker. 2005. Products from little researched plants as aquaculture feed ingredients, Agrippa - FAO online journal (www.fao.org/agrippa) .

Fuglie, L. 2001. The miracle tree - the multiple attributes of Moringa. Church World Service, Dakar, Senegal.

Hoshmand, A.R. 1998. Statistical Methods for Environmental and Agricultural Sciences. 2nd ed. CRC Press, Florida.

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Mauget, J.C., N. Rizot, and J. Guinard. 1993. Effect of time and position of summer pruning on the release from inhibition of the axillary buds of walnut stump sprouts. Acta Hort. (ISHS) 311:210-216.

Morris, S.E., M.C.H. Cox, J.J. Ross, S. Krisantini, and C.A. Beveridge. 2005. Auxin dynamics after decapitation are not correlated with the initial growth of axillary buds. Plant Phys.138:1665-1672.

Morton, J. 1991. The Horseradish Tree, Moringa pterygosperma (Moringaceae) - a boon to arid lands? Econ. Bot. 45(3):318-333.

Murro, J.K., V.R.M. Muhikambele, and S.V. Sarwatt. 2003. Moringa oleifera leaf meal can replace cottonseed cake in the concentrate mix fed with Rhodes grass (Chloris gayana) hay for growing sheep. Livest. Res. Rural Dev.15(11). Retrieved August 25, 2005, from http://www.cipav.org.co/lrrd/lrrd15/11/murr1511.htm.

Napoli, C.A., C.A. Beveridge, and K.C. Snowden. 1999. Reevaluating concepts of apical dominance and the control of axillary bud outgrowth. Curr. Top. Dev. Biol. 44:127-69. Review.

Olson, M.E., and S. Carlquist. 2001. Stem and root anatomical correlations with life form diversity, ecology, and systematics in Moringa (Moringaceae), Bot. J. Linn. Soc.135:315-348.

Palada, M.C. 1996. Moringa (Moringa oleifera Lam.): a versatile tree crop with horticultural potential in the subtropical United States. HortScience 3:794-797.

Palada, M.C. and L.C. Chang. 2003. Suggested cultural practices for Moringa. Asian Vegetable Research and Development Center pub. #03-545. PO Box 42, Shanhua, Tainan 74199; Taiwan ROC.

Price, M. The Moringa Tree. 1985. Revised 2000 by K. Davis. Educational Concerns for Hunger Organization (ECHO) Technical Note. www.echotech.org/technical/technotes/moringabiomasa.pdf.

Sail, J., A. Lehman, and L. Creighton. 2001. JMP Start Statistics - a guide to statisticsand data analysis using JMPfi and JMP IN" software. 2nd ed. Duxbury Thompson Learning, California.

Sena, L.P., D.J. Vanderjagt, C. Rivera, A.T.C. Tsin, I. Muhamadu, O. Mahamadou, M. Millson, A. Pastuszyn, and R.H. Glew. 1998. Analysis of nutritional components of eight famine foods in the Republic of Niger. Plant Foods Hum. Nutr. 52:17-30.

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Seshadri, S. and V.S. Nambiar. 2003. Kanjero (Digera arvensis) and drumstick leaves (Moringa oleifera): nutrient profile and potential for human consumption. In: Plants in human health and nutrition policy, Simopoulos, A.P. and C. Gopalan, eds. World Rev. Nutr. Diet 91:41-59.

Shimizu-Sato, S. and H. Mori. 2001. Control of outgrowth and dormancy in axillary buds. Plant Phys. 127:1405-1413.

Soliva, C.R, M. Kreuzer, N. Foidl, G. Foidl, A. Machmuller, and H.D. Hess. 2005. Feeding value of whole and extracted Moringa oleifera leaves for ruminants and their effects on ruminal fermentation in vitro. Anim. Feed Sci.Technol. 118:47-62.

Tworkoski, T., S.S. Miller, and R. Scorza. 2005. Effects of pruning on auxin and cytokinin levels and subsequent regrowth among different growth habits of peach. Proceedings of Plant Growth Regulation Society of America. V. 32. p 46.

Wilson, B.F. 2000. Apical control of branch growth and angle in woody plants. Am. J. Bot. 87:601-607.

Wu, R-L. 1994. Qualitative genetics of yield breeding for Populus short rotation culture. II. Genetic determination and expected selection response of tree geometry. Can. J. For. Res. 24:155-165.

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CHAPTER 4

REGROWTH OF COPPICED MORINGA SEEDLINGS

IN RESPONSE TO TWO DECAPITATIONS

Key words: lateral bud release, agroforestry, Moringa oleifera

4.1 Abstract

The regrowth of coppiced moringa (Moringa oleifera Lam.) seedlings

following a second decapitation was examined to determine if previously

decapitated seedlings show enhanced lateral bud outgrowth compared to

seedlings decapitated for the first time. The effect of increased stem diameter on

regrowth following decapitation also was investigated. Moringa is a multipurpose

vegetable tree commonly used in intensive, high-density agroforestry production

systems. Seedlings are subjected to frequent and extreme levels of vegetative

harvest when they are decapitated 15 to 20 cm above the ground, or “coppiced”.

Coppicing is a pruning management strategy used to encourage lateral bud

release and to promote branching and new vegetative growth. Little horticultural

research has been devoted to coppiced multipurpose trees, and the response of

seedlings to this type of management is complex. Greenhouse experiments

were completed using hydroponic culture during the summer of 2006. One

hundred twenty seedlings were grown from seed obtained from Haiti; 60 plants

were decapitated to 15 cm on 1 June 2006 and 60 remained intact. All seedlings

were decapitated on 12 July 2006. Previously decapitated seedlings (twice-

decapitated) released significantly greater numbers of buds following their

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second decapitation compared to intact plants decapitated for the first time (once \

decapitated). Twice-decapitated plants released ten times the number of buds

than once-decapitated plants (5.4 vs. 0.5/plant) at one week following

decapitation. No significant difference in total dry weights occurred between twice

and once-decapitated plants. The number of lateral buds that were released

decreased, and stem length and dry weights increased with increasing stem

diameter. Intact seedlings had significantly larger stem diameters (16 mm) than

once-decapitated seedlings (12 mm) prior to the second decapitation. Stem

diameter data were sorted to 7 class intervals, and the rate of bud release for 30

once-decapitated (n=13) and twice-decapitated (n=17) seedlings having no

significant difference in stem diameter was examined. A statistically significant

(P< 0.05) difference in the rate of bud release was detected. Bud release of

twice-decapitated plants (6.7/plant) was more than twice that of once-decapitated

plants (2.7/plant), demonstrating enhanced lateral bud response of previously

decapitated seedlings. Dry weights were not significantly different between these

two groups. Selective removal of non-elongating stems suppressed dry weights

of decapitated seedlings compared to intact seedlings given the same treatment.

Photosynthate produced by these stems may contribute to overall regrowth of

previously decapitated seedlings. Selective removal of non-elongating stems of

intact seedlings had little effect. The results of this study may be used to begin to

develop a framework for understanding the response of seedlings to severe,

repeated coppicing.

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4.2 Introduction

Moringa is a small multipurpose tree reaching a height of 7 to 12 meters

(Foidl et al., 1999) and is native to the sub-Himalayan regions of northwest India.

Moringa is cultivated in many regions of Africa, Arabia, Southeast Asia, the

Pacific and Caribbean Islands, and South America (Fuglie, 1999; Palada, 1996),

and is planted at densities as high as 1,000,000 plants ha'1 in agroforestry forage

production systems when spaced 10 x 10 cm apart (Foidl et al., 2001). Individual

seedlings are decapitated or “coppiced” when the tree is 1 to 2 m tall to a height

of 15 to 20 cm to remove the apical growing shoot. Individual plants are

defoliated; adventitious and axillary bud regrowth occurs from the remaining

stem, which is again harvested after approximately 30 days. Numerous studies

have compared cutting height and cutting interval of agroforestry tree species,

the majority of which have focused on forage tree legumes. Few studies have

investigated the fundamental response of trees to coppicing at regular intervals

(Stur et al., 1994).

Spacing patterns of coppiced moringa depends primarily on the response

to vegetative harvest and the type of biomass production desired. Close spacing

encourages stem growth at the expense of leaf growth as lower leaves are

shaded and individual plants compete for light. Highest total biomass yield is

obtained with long harvest intervals, but with decreasing leaf:stem ratios (Reyes

Sanchez, 2006). Total biomass yield increases with longer cutting intervals with

forage tree legumes, and yield increase is due primarily to stem growth (Stur et

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al., 1994). Moringa stem biomass can be as much as 50% of dry weight yield \

(Amaglo et al., 2006).

Recent auxin research suggests that initial bud outgrowth in decapitated

plants is not triggered by depleted IAA levels and that auxin is involved in

controlling a later stage of bud outgrowth - a process termed “autoregulation”

(Morris et al., 2005). Autoregulation of bud outgrowth may act to suppress buds

that are already in a transition stage toward bud outgrowth. Adventitious and

axillary buds of previously decapitated plants may be in a transition stage toward

bud outgrowth and may exhibit enhanced responses to subsequent decapitation

events (Beveridge, K., personal communication, 2006). Attempts to locate

reports in the literature documenting elevated levels of bud outgrowth in

response to multiple decapitation events were unsuccessful.

Understanding the extent to which lateral bud outgrowth occurs and

resulting stem architecture will dictate appropriate spacing patterns for woody

species used in short rotation intensive culture (Wu, 1994). Currently, there are

no regrowth studies of moringa following coppicing, and spacing decisions for

high-density production systems are made without the benefit of fully

understanding the growth response of moringa seedlings to multiple decapitation

events. The extent to which planting densities of 1,000,000 plants-ha'1 can be

sustained due to competition between plants is questionable, especially in areas

where supplemental water is unlikely to be available. Irrigated and fertilized high-

density production systems provide an opportunity for high biomass production,

although this method of intense production is not practical for many dry-tropic

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regions. Increased spacing patterns and more typical crop husbandry practices

may provide opportunities for sustainable moringa production once more is

understood about how this valuable multipurpose vegetable tree can be grown as

a row crop.

The purpose of this study was to examine regrowth of coppiced moringa

seedlings following a second decapitation and determine if previously

decapitated seedlings develop enhanced lateral bud outgrowth compared to

seedlings decapitated for the first time. The effect of increased stem diameter on

regrowth following decapitation also was investigated.

4.3 Materials and Methods

Experiments were conducted in the greenhouses and laboratories of the

Department of Plant Science at the State University of New York at Cobleskill,

New York, USA. Where applicable, ANOVA followed by the Tukey-Kramer HSD

paired mean comparisons test (JMP®, v.4.0.3, SAS Institute, Inc., Cary, NC

27513 USA) were used to test for significant differences between treatments

(Hoshmand, 1998, Sail et al., 2001).

Yellow and blue sticky cards (IPM Laboratories, Inc., Locke, NY 13092-

0300 USA) were used to monitor insect pests throughout the experiments, and

biological pest controls were used during May and June of 2006. To monitor

fungus gnat (Orfelia spp.) larvae, potato discs were placed on rockwool

transplant blocks and in pots at the rate of 10 discs/90 m'2 and beneficial

nematodes (Steinernema feltiae ) (ScanMask™IPM Laboratories, Inc., Locke,

NY 13092-0300 USA) were applied in a media drench as a control measure.

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Predatory mites (Amblyseius cucumeris, Hypoaspis miles) were used to control

thrips (Frankliniella spp.) and a parasitic wasp (Aphidius colemanii) was used as

a control for aphids (Myzsus spp.) (IPM Laboratories, Inc., Locke, NY 13092-

0300 USA). Biological controls were discontinued during July and August of

2006 at which time Duraplex®TR and Pyrethrum® TR micro total release

insecticides (Whitmire Micro-Gen Research Laboratories, Inc. 3568 Tree Court

Industrial Blvd. St. Louis MO 63122-6682 USA) were used on alternate weeks for

control of the previously mentioned pests and two-spotted spider mites

('Tetranychus urticae).

4.3.1 Once and Twice-Decapitated Experiment

Seeds of Moringa oleifera Lam. from Haiti (Grace Ju, ECHO, 17391

Durrance Road, N. Ft. Myers, FL 33917 USA) were sown 4 October 2005 in

greenhouse flats containing PRO-MIX “BX” (Premier Horticulture Inc.,

Quakertown, PA 18951 USA). Seedlings were transplanted after 3 weeks to 15-

cm diameter, 9-cm deep, open-bottom, plastic hydroponics pots (CropKing, Inc.,

Seville, OH 44273-9413 USA) and were grown through the fall of 2005.

Seedlings were permitted to go dormant in a cool greenhouse with minimal water

before resuming growth in the spring of 2006 at which point 60 plants were

decapitated to 15 cm on 1 June 2006 and 60 remained intact. All plants were

decapitated to 15 cm on 12 July 2006. Data reported in Chapter 3 identified 15

cm as an appropriate height for seedling decapitation.

Five seedlings were spaced approximately 15 cm apart on 90 x 15 x 7.5-

cm rockwool slabs (Grodan Company, Agro Dynamics, Coppell, TX 75019 USA).

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Five 15-cm-diameter circles were cut from the top of the plastic wrapping of

individual rockwool slabs with a razor at each location where plants were to be

placed. Slabs were thoroughly wetted with tap water before plants were placed

on rockwool slabs. Pots were secured to slabs using a 0.635 x 15-cm tubing

stake. Three 8-cm diagonal slits were made on each side of the rockwool slab to

permit drainage from the slabs.

Six individual recirculating hydroponics systems were constructed.

Rockwool slabs were placed on sections of 122 x 122 cm x 4-cm plastic ebb and

flow trays (Midwest Gromaster, 48W 801 II Rt. 64, Maple Park, IL. 60151 USA).

Ebb and flow trays were inserted into wooden frames constructed of 2-cm, 5-ply

sections of plywood measuring 123 x 123-cm to which 2.5 x 7.5-cm lengths of

pine furring strip had been attached as sides using 6-cm galvanized screws.

Individual frames were elevated on the supply (high) side using a standard

plastic bulb crate and supported at the discharge side by a low-density

polyethylene tub (Kormex Plastics, La Mirada, CA. 90638 USA) measuring 91 x

61 x 20-cm and having a volume of approximately 80 liters to which nutrient

solution was added.

The nutrient solution consisted of 1.0 g L'1 5-11-26 Hydro-SoF and 0.75 g

L'1 15.5-0-0 Calcium Nitrate Plus™ (Scotts Sierra Horticultural Prod. Co., 14111

Scotts Lawn Rd., Marysville, Ohio 43041 USA) and 0.25 g L'1 MgS04-7H20

Epsogrow® epsom salts (Hydro Agri North America 100 North Tampa Street,

Suite 3200, Tampa, Florida 33602 USA) and was suitable following earlier

soilless culture trials. Electrical conductivity (EC) levels were maintained between

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2.0 and 2.3 dSm'1. Acidity was monitored, corrected to, and maintained V

between pH 5.5 to 6.0 with phosphoric acid. EC and pH were measured using a

Hanna HI 9813 portable Gro Chek meter (Hanna Instruments, 584 Park East

Drive, Woonsocket, Rl 02895 USA).

Individual plants were supplied with nutrient solution using 6-mm vinyl

distribution tubing secured by tubing stakes attached to 37.8-liter-per-hour,

pressure-compensating, point source emitters (DT025, TS025, PC-10, Rain Bird

International, Inc., Glendora, CA 91741 USA). Nutrient discharge from the

distribution tubing was directed to the base of individual pots (the top of the slab)

rather than to the top of pots to ensure that the area immediately around each

plant stem remained slightly moist to somewhat dry as previous trials have

demonstrated rotting at the base of stems to be a potential problem. Emitters

were attached to 12.7-mm, low-density polyethylene tubing (Cresline HD-125,

Cresline Plastic Pipe Company, Evansville, IN 47715 USA) and fed by a 946-

liter- per-hour magnetically driven, centrifugal, utility pump (Model MD2, Danner

Mfg., Inc., Central Islip, NY 11749 USA). A digital timer (Radio Shack No. 61-

1060, Tandy Corp., Ft. Worth, TX 76102 USA) was used to operate each system

automatically. Rockwool slabs were irrigated with fertilizer solution automatically

following the first decapitation and were removed from systems and watered and

fertilized by hand after the second decapitation. Moisture levels were managed

by maintaining a target of 10 to 20% percent solution drainage from individual

rockwool slabs. Hand irrigation and fertilization permitted lower placement of

plants on greenhouse benches and facilitated data collection.

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4.3.2 Second Decapitation Experiment

Plants previously used in Experiment 3.3.1 were permitted to grow out

following the 7 June 2006 harvest to compare the rate of growth following a

second decapitation. Plants were decapitated to the same heights used initially

and were harvested on 17 July 2006. The number of buds released from

inhibition was counted daily, and the date of release (when buds=1 cm. in length)

was recorded. The mean time to budbreak (MTB) was calculated for each

treatment by multiplying each bud released by the number of days since the date

of decapitation. The total number of accrued days for each plant (I buds x days)

was then divided by the number of buds released to determine the MTB. Dry

weights were determined following drying of plants for 48 hours in a 70° C oven.

Bud outgrowth was determined by tracking buds that grew out to at least 40 mm

of length, and the number of stems per plant > 40 mm was counted for each

treatment. Total stem length per plant was determined.

4.3.3 Shoot Removal Experiment

Results in Chapter 3 indicated that seedlings that were decapitated to 15

cm released an average of 7.3 buds with 2.3 stems growing out. Five buds per

plant did not ultimately elongate. The effect of removing any buds beyond the

first 3 that grew out on each seedling was examined on both intact and

previously decapitated plants in an attempt to elucidate any role these buds may

play in seedling growth beside serving as a bud bank. Thirty previously

decapitated seedlings and 30 previously intact seedlings had all but 3 of their

longest new shoots removed following a second decapitation. Plants were

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harvested at 25 days following the second cutback and dry weights were

determined.

4.4 Results

4.4.1 Once and Twice-Decapitated Experiment Results

Seedlings were of similar size prior to the first decapitation with no

significant difference in stem diameter (10 mm, measurement taken at the base

of the seedling) or height (19 cm) on 24 May 2006 before the first decapitation on

1 June 2006 (Table 4.1). Six weeks later, decapitated plants had average stem

diameters of 12 mm whereas intact plants measured 16 mm in diameter

(measurements taken on 4 July 2006). Stem diameters were significantly

different between intact and once-decapitated seedlings prior to the second

decapitation on 12 July 2006.

Table 4.1. Stem diameter and height of moringa seedlings before half (Decapitated, n=30) received the first decapitation treatment and stem diameter at 1 month following the first decapitation

Measurement27

Stem diameter Height before Stem diameter 30 d

Treatment before 1st decap. 1st decap. after 1st decap. treatment treatment treatment

(mm) (cm) (mm) Intact (n=30) 10a+2.0 19.6a±5.4 16a±4.0 Decapitated (n=30) 10a±1.7 18.5a±5.6 12b±2.6 zMean±SD yWithin columns, means followed by different letters are significantly different (P< 0.05, Tukey-Kramer HSD)

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Previously decapitated plants (twice-decapitated) had significantly greater

numbers of buds released 7 and 9 days following decapitation than previously

intact plants (once-decapitated plants) (Table 4.2). One week following

decapitation (data collected 19 July 2006) twice-decapitated plants had released

ten times the number of buds as once-decapitated plants (5.4 vs. 0.5/plant).

After 9 days, twice-decapitated plants had three times the number of released

buds as once-decapitated plants (6.9 vs. 2.3/plant). No significant difference in

total dry weight occurred between twice-decapitated plants and once-decapitated

plants (Table 4.3). Once-decapitated plants had significantly higher stem dry

weights than twice-decapitated plants.

Table 4.2. Bud release comparison of once-decapitated and twice-decapitated moringa seedlings.

Measurement27 Bud release Bud release

Treatment after 7 d after 9 d Once-decapitated (n=30) 0.5a 2.3a Twice-decapitated (n=30) 5.4b 6.9b zMean yWithin columns, means followed by different letters are significantly different (P< 0.05, Tukey-Kramer HSD )

Table 4.3. Dry weights of leaves and stems and total dry weight following decapitation of once-decapitated and twice- decapitated moringa seedlings.

Measurement27 Dry Dry Dry

weight weight weight leaf yield stem yield total yield

Treatment (g) (g) (g) Once-decapitated (n=30) 5 6a 1.9a 7.4a Twice-decapitated (n=30) 4.8a 1.3b 6.1a

zMean yWithin columns, means followed by different letters

are significantly different (P< 0.05, Tukey-Kramer HSD)

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4.4.2 Second Decapitation Experiment Results

Data for the growth of seedlings decapitated in Experiment 3.3.1 that were

decapitated a second time on 17 July 2006 are presented in Table 4.4 and are

consistent with results from the first decapitation. The number of buds released

for seedlings decapitated at node 6 (7.6/plant) approximates the number

released following the first decapitation and reported in Chapter 3 (7.3/plant). The

MTB of 7.7 days following the first decapitation for node 6 seedlings is similar to

the 8.6 day MTB obtained after the second decapitation. Regardless of the

number of buds released at each nodal point of decapitation, the number of

stems that ultimately grew out remained consistent at approximately 3

stems/plant.

Table 4.4. Effect of nodal point of decapitation on MTBZ, bud release, number of stems >40 mm, total stem length, and dry weights of moringa seedlings following a second decapitation.

Node

Height after

decap. (cm)

Measurement

MTBZ

(d)

Buds released per plant

Number of stems >40

mm

Total stem length (mm)

Dry weight

(g/plant)

1 4.9 8.1 4.0 2.9 160 3.2

2 6.6 7.9 3.8 2.4 183 2.7

3 8.9 7.3 5.1 2.8 234 4.4

4 10.7 8.8 6.3 3.1 242 5.5

5 13.3 9.6 8.2 3.3 300 6.7

6

Zr /itn

15.6 8.6 7.6 2.8 292 8.0

ZMTB = mean time to budbreak

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4.4,3 Shoot Removal Experiment Results

Thirty previously decapitated seedlings and 30 previously intact seedlings

had all but 3 of their longest new shoots removed following a second

decapitation. Twenty-five days following the second cutback, twice-decapitated

seedlings produced an average of 726 mm of new stem growth on 4.1

stems/plant, whereas seedlings decapitated only once on 12 July 2006 produced

an average of 809 mm of new growth on 3.4 stems/plant. Three-stem, twice-

decapitated seedlings had an average of 497 mm of new stem growth on 2.8

stems/plant, whereas 3-stem, once-decapitated seedlings had an average of 704

mm of new stem growth on 2.9 stems/plant (Table 4.5).

Table 4.5. Total stem length, number of stems >40mm, and dry weight of once-decapitated, twice-decapitated, and once and twice-decapitated moringa seedlings pruned to three stems.

Measurement^

Treatment

Total stem length

(mm/plant)

Number of stems/plant

> 40mm

Dry weight

(g/plant) Once-decapitated 809a 3^ie 7.4a

Twice-decapitated 726a 4.1a 6.1a

Once-decap., 3 stems 704a 2.9b

OJ

CD

CD

Twice-decap., 3 stems 497b 2.8b 4.1b

zMean yWithin columns, means followed by different letters

are significantly different (P£ 0.05, Tukey-Kramer HSD)

4.5 Discussion

Previously decapitated plants released ten times the number of buds

compared to intact plants (5.4 vs. 0.5/plant) at 7 days following decapitation,

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supporting the hypothesis of enhanced lateral bud outgrowth of previously V

decapitated moringa seedlings compared to seedlings decapitated for the first

time. Although a significant difference was detected in bud release, the high rate

of 6.9 buds released after 9 days for twice-decapitated plants is similar to that

reported in Chapter 3 (7.3) after one decapitation and obtained in Experiment

4.4.2 (7.6) after a second decapitation. Therefore, the difference observed in

bud release rates between once and twice-decapitated seedlings is not due to

enhanced rates of release for twice-decapitated plants but rather because of

depressed rates of bud release among intact plants decapitated for the first time.

Intact plants had stem diameters that were 4 mm larger than those of previously

decapitated plants at the time of the second decapitation, resulting from lesser

stem diameter growth following decapitation.

Scatter diagrams of buds released as a function of stem diameter

suggests that fewer buds were released with increasing stem diameter according

to 21 July 2006 data (Figure 4.1). Previous observations reported in Chapter 3

identified increases in stem length as a strong predictor of increased dry weights.

Scatter diagrams of stem length per plant as a function of stem diameter

suggests increased stem length with increasing stem diameters (Figure 4.2). Dry

weights increased with increasing stem lengths (Figure 4.3), consistent with

results reported in Chapter 3. Data were analyzed by caliper, regardless of

whether or not they had been decapitated previously at the time of the second

decapitation, to see if the difference in stem diameter was contributing to

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depressed bud release rates. Stem diameters were sorted into 7 class intervals

using Sturge’s rule (Hoshmand, 1998) as follows:

k= 1 + 3.322 (logio n)

where k = class interval

n = number of observations

The number of class intervals was calculated for 60 observations:

k= 1 + 3.322 (log10 60)

= 1 + 3.322 (1.778)

~ 7

Table 4.6. Caliper range, caliper size groups (mm, mean), frequency, and number (n) of moringa seedlings in each group that were once or twice-decapitated sorted to 7 class intervals.

Class Caliper range (mm)

Caliper size

(mm) Frequency

Number (n) once-decapitated

Number (n) twice-decapitated

1 8-9 9 6 1 5 2 10-11 11 8 2 6 3 12 12 13 3 10 4 13-14 14 9 5 4 5 15-17 16 8 5 3 6 18 18 7 5 2 7 19-25 21 9 9 0

Natural data distribution points were used as a guide; for example, thirteen

12-mm stems were treated as a single-size range. Mean stem diameters were

calculated for each of the seven groups, resulting in the following stem diameter

size groups: 9, 11, 12, 14, 16, 18, and 21. The two smallest size groups (9, 11)

and the two largest size groups (18, 21) each accounted for approximately 25%

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Bu

ds

rele

ase

d b

y 21

Ju

ly 2

006

(16/60, 14/60) of the total. The remaining 50% of the seedlings (30/60) were

distributed among the three middle size groups (Table 4.6).

The number of buds released, stem length, and dry weights were

calculated for each of the seven caliper class intervals. The majority of large

seedlings (14/16) had been intact whereas most of the smaller seedlings (11/14)

had previously been decapitated before the second decapitation. Bud release

decreased and dry weights increased with increasing stem diameter (Figure 4.4)

and dry weights decreased with increased numbers of buds released (Figure

4.5).

O Twice-decapitated □ Once-decapitated

16

14

12

10

8

6

4

2

0

O

o o - O <0

O o oo

oo

o

□ □ □

o o o

o 8° on

-

o

o

□ o □ □ □□ on B □

n □ □ n

0 5 10 15 20

□ □

25

Stem diameter (mm) 4 July 2006

30

Fig. 4.1. Scatter diagram of stem diameter and number of buds released per plant for once-decapitated and twice-decapitated moringa seedlings on 21 July 2006.

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20-

c m a. 15-

D)

10 15 20 25

Stem diameter (mm) 4 July 2006

Fig. 4.2. Scatter diagrams of stem diameter and stem length and stem diameter and dry weights after bud release for once-decapitated (n=30) and twice- decapitated (n=30) moringa seedlings.

Fig. 4.3. Regression analysis of dry weight as a function of stem length for once-decapitated (n=30) and twice-decapitated (n=30) moringa seedlings.

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Fig. 4.4. Relationship between seedling caliper and bud release and seedling caliper and dry weights after bud release for once-decapitated and twice- decapitated moringa seedlings sorted to 7 caliper class intervals. Data points are means for each caliper class interval.

The 30 seedlings from the middle 3 (12-mm, n=13; 14-mm, n=9; 16-mm,

n=8) of the 7 caliper class intervals (Table 5) represented a mixed group of once

(n=13) and twice (n=17) decapitated plants. Statistical analysis was used to

determine if they were sufficiently similar in stem diameter size to be analyzed for

their rate of bud release as a mixed group of once and twice-decapitated plants.

No statistical difference in stem diameter size was observed, but the number of

buds released by twice-decapitated plants was more than twice that of once-

decapitated plants and statistically significant (Table 4.7). Dry weights were not

statistically different between these two groups.

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Buds released by 21 July 2006

Fig. 4.5. Relationship between number of buds released and dry weight yield after bud release for once-decapitated (n=30) and twice-decapitated (n=30) moringa seedlings sorted to 7 caliper class intervals. Data points are means for each caliper class interval.

Seedling caliper (mm)

Fig. 4.6. Relationship between seedling caliper and crown diameter for once- decapitated (n=30) and twice-decapitated (n=30) moringa seedlings sorted to 7 caliper size groups. Data points are means for each caliper class interval.

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Table 4.7. Stem diameter, number of buds released, and dry weights following decapitation of once-decapitated and twice- decapitated moringa seedlings having stem diameters of similar size.

Measurement Stem Number of Dry weight

diameter2 buds yield7 Treatment (mm) released7 (g)

Once-decapitated (n=13) 14a±1.8 2.7a 5.6a Twice-decapitated (n=17) 13a±1.6 6.7b 6.1a zMean ± SD yMean xWithin columns, means followed by different letters

are significantly different (P< 0.05, Tukey-Kramer HSD)

Regrowth following decapitation will determine appropriate spacing

patterns for moringa in high-density stands. Seedling crown diameters

(measurements taken from widest leaf tip to leaf tip point across the canopy)

increased with increasing stem diameter. Light measurements (n=20) taken at

the top of each of 20 seedlings on 9 August 2006 measured an average

photosynthetically active radiation of 840 pmol-m^ s'1. Measurements taken at

the midpoint of seedling canopies averaged 104 pmolm'^s'1 and were

approximately 12% of those at the top. The current practice of spacing

seedlings 10 to 15 cm on center in high-density stands provides little opportunity

for maximizing individual plant yields.

Results presented in Chapter 3 showed that dry weights increased linearly

with increased numbers of buds released and increasing total stem length per

plant, although the number of stems that ultimately grew out following

decapitation remained relatively constant regardless of the number of buds that

were released initially. The speed with which buds were released initially was

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critical as early bud release resulted in early stem growth. Stems that began to

grow earlier had a competitive advantage for light. In the current study, large-

diameter seedlings released fewer buds than small-diameter seedlings, and

once-decapitated seedlings released fewer buds than twice-decapitated

seedlings.

Twice-decapitated, 3 stem pruned seedlings had significantly lower dry

weights and stem lengths than plants in other treatments although the number of

stems was only significantly different (lower) compared to twice-decapitated

seedlings that had not been pruned to 3 stems. Twice-decapitated plants appear

to benefit from photosynthate produced by non-elongating buds and leaves so

that removal of these resulted in less growth. Once-decapitated seedlings have

more stored carbohydrate reserves and invest less in growth of multiple stems

than twice-decapitated seedlings. Pruning once-decapitated seedlings back to 3

stems did not significantly change the number of stems that grew out and

resulted in no significant differences in dry weights compared to once or twice-

decapitated plants.

When once and twice- decapitated seedlings of similar stem diameter

were compared, the rate of bud release of twice-decapitated plants was more

than twice that of once-decapitated plants, and supports the hypothesis of

enhanced lateral bud response of previously decapitated seedlings. Dry weights

were not significantly different between these two groups. Small-diameter

seedlings apparently achieve their growth following decapitation by releasing

more buds with non-elongating stems contributing to the growth of elongating

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stems. Removal of these non-elongating stems greatly suppressed growth in \

twice-decapitated seedlings but had little to no effect on growth of seedlings

cutback for the first time. Small seedlings have a lower capacity for survival if

decapitated due to fewer stored carbohydrate reserves and smaller root systems

than plants that have not been decapitated. Enhanced bud release provides

earlier photosynthetic ability and more bud sites for new stems if needed.

The results of this study suggest that large-diameter seedlings are at less

risk if decapitated than small seedlings and release fewer buds and utilize larger

root systems and stored reserves to invest in fewer elongating stems. Increasing

stem diameter does not appear to result in reduced capacity for regrowth

following coppicing, although the strategy for regrowth changes somewhat.

Spacing moringa seedlings farther apart than the 10 x 10-cm used in high density

agroforestry forage production systems to encourage large-diameter seedling

growth may contribute to sustainable moringa production.

4.6 Literature Cited

Amaglo, N.K., G.M. Timpo, W.O. Ellis, and R.N. Bennett. 2006. Effect of spacing and harvest frequency on the growth and leaf yield of Moringa (Moringa oleifera Lam.), a leafy vegetable crop. Paper presented to Conference on Moringa and other highly nutritious plant resources: strategies, standards, and markets for a better impact on nutrition in Africa. Accra, Ghana; November 16, 2006. Available from: PROPAGE, 211 rue du Faubourg Saint Antoine 75011 Paris, France.

Foidl, N., FI.P.S.Makkar, and K. Becker. 2001. The potential of Moringa oleifera for agricultural and industrial uses. In: The miracle tree - the multiple attributes of Moringa. Church World Service, Dakar, Senegal. 45-76.

Fuglie, L. 2001. The miracle tree - the multiple attributes of Moringa. Church World Service, Dakar, Senegal.

92

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Hoshmand, A.R. 1998. Satistical methods for environmental and agricultural sciences. 2nd edition. CRC Press.

Morris, S.E., M.C.H. Cox, J.J. Ross, S. Krisantini, and C.A. Beveridge. 2005. Auxin dynamics after decapitation are not correlated with the initial growth of axillary buds. Plant Phys. 138:1665-1672.

Palada, M.C. 1996. Moringa (Moringa oleifera Lam.): a versatile tree crop with horticultural potential in the subtropical United States. HortScience 3:794-797.

Reyes Sanchez, N. 2006. Moringa oleifera and Cratylia argentea: potential fodder species for ruminants in Nicaragua. Doctoral dissertation. Dept, of Animal Nutrition and Management, SLU. Acta Universitatis agriculturae Sueciae vol. 2006:1.

Sail, J., A. Lehman, and L. Creighton. 2001. JMP Start Statistics - a guide to statisticsand data analysis using JMP® and JMP INa software. 2nd ed. Duxbury Thompson Learning, California.

Stur, W.W., H.M. Shelton, and R.C. Gutteridge. 1994. Defoliation management in forage tree legumes. In: Gutteridge, R. C. and H. M. Shelton, ed. Forage tree legumes in tropical agriculture. United Kingdom, CABI. P. 158-167.

Wu, R-L. 1994. Qualitative genetics of yield breeding for Populus short rotation culture. II. Genetic determination and expected selection response of tree geometry. Can. J. For. Res. 24:155-165.

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CHAPTER 5

PRUNING STRATEGIES TO MAXIMIZE LEAF PRODUCTION OF POLLARDED

MORINGA TREES

Keywords: agroforestry, drought tolerance, medicinal and aromatic plants,

Moringa ole if era, vegetable tree

5.1 Abstract

Moringa (Moringa oleifera Lam.) is a small multipurpose tree that has

many medicinal and nutritional uses and that can withstand severe drought in

areas where at times little else will grow. Moringa is grown in the dry-tropics as a

pollarded, perennial vegetable tree, although little information is available

regarding how tree standards are managed after pollarding. The purpose of this

study was to determine the effect of four different pruning strategies on leaf

biomass production of young, pollarded moringa trees. A total of 24 single-stem

trees ranging in height from 163 to 264 cm (mean = 197.7 cm) and 1.9 to 3.0 cm

in caliper (mean = 2.39 cm) were pollarded to a height of 150 cm and subjected

to one of four pruning strategies:

Treatment 1 -Defoliation (DEF)

Following pollarding to 150 cm, the remaining leaves and petioles were also

harvested, resulting in totally defoliated, decapitated trees. Pairs of stems that

grew out were harvested when they had at least six fully expanded leaves.

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Treatment 2 - Laterals pruned to 10 cm (LP10)

Lateral stems that were released due to decapitation were cut back to a targeted

length of 10 cm to encourage additional branching. Pruning cuts were made at

locations acropetal to the nearest node located at least 10 cm. from where the

lateral branch attached to the main stem so that no internodal cuts would be

made. Pairs of stems were harvested when they had at least six fully expanded

leaves.

Treatment 3 - 2 stems harvested every 30 days (2S30)

The two largest stems were harvested from each of six trees at 30-day intervals

following cutback and each subsequent harvest.

Treatment 4 - 6 leaves per stem (6LPS)

Stems were harvested when any two stems had at least six fully expanded

leaves.

DEF plants released fewer lateral buds per node but did so at more nodal

points along the stem than other treatmernts. DEF plants provided dry weights

similar to other treatments after a single harvest but demonstrated inadequate

regrowth for a second harvest. Pruning of laterals that were released following

pollarding to 10 cm (LP10) encouraged the release of more laterals per node but

on fewer nodes compared to other treatments. When dry weights were calculated

on a daily basis there was no significant difference between harvesting two

lateral stems every 30 days (2S30) or when there were six fully expanded leaves

per stem (6LPS). However, each of these treatments were significantly greater

than daily dry weights of DEF and LP10 treatments. Overall, dry weight was

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approximately 18% of fresh weight. Dry leaf weight was 76% of total dry weight

whereas dry stem weight was 24% of total dry weight. Trees that were not

pollarded did not release lateral buds. Harvesting shoots whenever they had 6

fully expanded leaves provided a simple guideline and harvesting strategy that

utilized the iterative processes of regrowth and harvest for pollarded moringa.

Harvesting shoots at 30-day intervals worked well under the growing conditions

of this study, but may not be appropriate for other growing locations. Vegetables

are the primary source of micronutrients for human consumption and provide the

most practical and sustainable method for alleviating micronutrient deficiencies.

Moringa leaves are rich in micronutrients and implementing home garden

strategies that include the sustainable production of moringa may assist in

meeting the nutritional needs of families in developing regions of the world.

5.2 Introduction

Lack of food availability and inadequate nutrition continue to plague

regions of sub-Saharan Africa as well as other areas of the world and are often

exacerbated during periods of drought. Introduced food crops such as maize

and soybean have provided tremendous benefits to local populations.

Frequently, however, introduced crops have often been in place of rather than in

addition to local, drought resistant crops that may have traditionally been grown

(Babu, 2000). Attempts to capture high-value markets through the production of

introduced fruits and vegetables during rainy seasons often fail with the periods

of drought that inevitably follow. Seasonality of production associated with

introduced foods frequently leaves low-income, subsistence farmers and their

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families particularly vulnerable during the dry seasons and frequently results in

inadequate food availability. Displacement of indigenous or naturalized food

crops by newly introduced foods may result in a corresponding loss of indigenous

food crop knowledge (Babu, 2000).

Areas where people regularly experience hunger also frequently depend

on traditional medicines that many times are deeply embedded in local belief

systems and continue to grow in popularity (Katumba et al., 2004). For example,

more than 80% of the rural Ugandan population depend on traditional medicine

as their primary health care (Wright, 2002). Harvesting plants for traditional

remedies may require excavation of plant roots, bark stripping, or plant

defoliation and can threaten wild plants. Increased medicinal and aromatic plant

(MAP) production and consumption will continue to provide new opportunities for

farmers worldwide as new crops are placed into cultivation (Craker, 1999).

Cultivation of MAP will decrease the pressure on natural plant populations and

help ensure sustainable production (Craker and Gardner, 2005), but in many

regions of the world there is limited knowledge regarding the propagation and

domestication of wild food and medicinal plants. Additional MAP research is

needed to investigate propagation and production techniques of underexploited

plants having promising potential as crops (Rao et al., 2004). Crops that have

both nutritional and medicinal values and that can persist through periods of

drought will be particularly useful in underdeveloped regions.

Moringa is a small, multipurpose tree reaching a height of 7 to 12 meters

(Foidl et al., 1999) and is native to the sub-Himalayan regions of northwest India.

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Moringa now grows throughout the semi-arid tropics and is cultivated to some

extent in many regions of Africa, Arabia, Southeast Asia, the Pacific and

Caribbean Islands, and South America (Fuglie, 1999; Palada, 1996). Moringa is

often grown as a vegetable tree (Price, 2000; Ram, 1994), and stands out among

the vegetables of the world as one of the most ecologically friendly and highly

nutritious crops (Seshadri and Nambiar, 2003). Roots, leaves, and seeds are

used for industrial, food, and medicinal purposes (Palada, 1996). The many

medicinal, nutritional, industrial, and agricultural uses of moringa are well

documented and continue to be investigated by scientists from a wide variety of

disciplines. A recent review of the nutritional, therapeutic, and prophylactic

qualities of moringa indicates that “the nutritional properties of moringa are now

so well known that there seems to be little doubt of the substantial health benefit

to be realized by consumption of moringa leaf powder in situations where

starvation is imminent” (Fahey, 2005).

Vitamin A deficiency is a serious nutritional problem in many

underdeveloped parts of the world, and the beta-carotene content of moringa

leaves recently has received substantial attention. Plants do not contain Vitamin

A, but many plants contain carotenoids such as beta-carotene that can be

converted to Vitamin A once in the human body (Grusak, 2005). Moringa was

reported to have the highest pro-Vitamin A content and was the least expensive

source of Vitamin A when compared to all other commonly used foods in Malawi

(Babu, 2000). Similar results were reported for calcium and Vitamin C. Tender,

young moringa leaves have been reported to contain higher levels of protein,

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lipid, and vitamins A, Bi, B6, and C than mature leaves (D’Souza and Kulkarni,

1993). Carotenoid content in leafy vegetables varies with variety, plant part,

maturity at harvest, climatic conditions, cultivation, and postharvest handling

(Lakshminarayana et al., 2005). Moringa leaves had 7 times the beta-carotene

content of spinach (Seshadr and Nambiar, 2003) and are to be included among a

wide variety of vegetables analyzed using a new, stable isotope method to

measure vegetable specific beta-carotene absorption in humans (Grusak, 2005).

Horticultural practices that encourage sustainable production of moringa leaves

will assist in meeting the nutritional need of families in developing regions of the

world.

Moringa has been used as a multipurpose tree component in agroforestry

alley cropping and hedgerow cropping systems. Failure to cut the main trunk

results in straight, fast-growing trees that have leaves and pods on only the

primary stem (Palada et al., 2003). Pollarding and coppicing are two pruning

strategies that have been recommended to promote branching, increase

production, and facilitate harvesting (Bosch, 2004). Pollarding is a method of

severely pruning the crown of a tree down to a primary stem, or standard.

Moringa generally is pollarded to a height of 1 to 2 meters to encourage the

regrowth of multiple shoots. Coppicing involves cutting the main stem or trunk at

or near ground level and encourages new shoots to grow from adventitious buds

near the base of the plant. Pollarding is reported to be preferable for fodder and

vegetable production since shoots tend to be thinner and more numerous in

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comparison to coppice shoots, which may be better suited for paper pulp

(Nautiyal and Venkataraman, 1987).

Much attention recently has been given to the use of multipurpose trees in

high-density agroforestry forage production systems, and many of these species

have been used in dry-tropic farming systems. Moringa has been planted at

densities of up to 1,000,000 plants-ha'1 and biomass production of up to 580

metric tons of fresh material-ha'1-yr"1, equivalent to approximately 99 tons of dry

matter is possible (Foidl et al., 1999; Francis, 2005). Individual plants are

pruned, or “coppiced” when the tree is 1 to 2 m tall to a height of 15 to 20 cm to

remove the apical growing shoot. This extreme vegetative harvest results in total

plant defoliation, regrowth time is typically 35 days, and there is significant

mortality among plant populations (Foidl, N., personal communication, 2003,

2005).

Total biomass production increases in high density plantings with

increased population density, although per plant yield decreases. Close spacing

encourages stem growth at the expense of leaf growth as lower leaves are

shaded and individual plants compete for light. Highest total biomass yield is

obtained with long harvest intervals, but with decreasing leaf:stem ratios (Reyes

Sanchez, 2006). Total biomass yield increases with longer cutting intervals with

forage tree legumes, with yield increase due primarily to stem growth (Stur et al.,

1994). Moringa stem growth can be as much as 50% of dry weights (Amaglo et

al., 2006).

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High-density moringa plantations have the potential for high biomass

production, but are particularly subject to drought and perform best under

irrigation. Moringa planted at high-densities produced higher yields than at low-

densities if plants were irrigated and fertilized (Foidl et al., 2001). High-density

production may be impractical in many regions of the world when the ultimate

goal is sustainable leaf biomass production and irrigation capacity is limited.

Management practices that minimize mortality, improve leaf:stem ratios, and

encourage drought tolerance will be beneficial in drought-prone areas.

Moringa can be grown as a pollarded, perennial vegetable tree that can

withstand severe drought in areas where at times little else will grow. Trees also

can be managed to produce seed crops so that local farmers are not dependent

on external seed sources. Little horticultural research has been devoted to

moringa pruning strategies, and the anecdotal reports that are available vary

greatly in their recommendations. Four-month old moringa seedlings in St. Croix,

US Virgin Islands, averaged 275 cm in height and were lopped at 1.5 meters.

Lopping, as described by the World Agroforestry Center, refers to random upper

branch removal, though in this study “lopped” actually refers to pollarding, or

complete removal of the top portions of the tree inclusive of the growing point

(Becker, B., personal communication, 2006). At the time of the second pruning

three months later seedlings averaged 337 cm.

An additional pruning strategy is to remove the apical growing shoot when

the tree is 1 to 2 meters high and cut back 60 cm branches by 30 cm. (Palada et

al., 2003) - essentially a pollarding and lopping approach. Elsewhere, farmers

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are reported to prune trees once the trees reach 1.5 m tall at 50 cm from the

ground or to ground level for older ones once or twice a year (Bosch, 2004).

Defoliation has been observed to encourage lateral bud release in woody plants

(Mauget et al., 1993). In the dry-tropics, moringa will often defoliate during the

dry season and refoliate during the rainy season. It is possible that decapitation

concurrent with defoliation may encourage additional lateral bud release.

Success in developing and maintaining food abundance and adequate

nutritional levels will require a multifaceted approach. The introduction of exotic

food crops must coincide with continued focus on developing best practice

production strategies for indigenous, drought-tolerant species. These species

should have a wide range of adaptation, multiple uses, rapid growth, propagate

easily, and be socially accepted for use (Nautiyal and Venkataraman, 1987).

Once identified, simple and specific cultural practices appropriate for local

growing conditions need to be identified to ensure sustainable levels of

production.

The literature is replete with references to pollarding moringa, but provides

few specifics as to how the remaining tree standards are managed following

pollarding. According to Pasternak (2004), “it is difficult to kill a Moringa tree, and

it recovers well from mismanagement.” Understanding the fundamental

response of moringa to selective pruning strategies following pollarding may help

to increase leaf:stem biomass production and minimize the effect of extreme

defoliation characteristic of coppiced plants. The purpose of this study was to

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determine the effect of four different pruning strategies on moringa trees

following pollarding at 150 cm.

5.3 Materials and Methods

Experiments were conducted in the greenhouses and laboratories of the

Department of Plant Science at the State University of New York at Cobleskill,

New York, USA. Where applicable, ANOVA followed by the Tukey-Kramer HSD

paired mean comparisons test (JMP®, v.4.0.3, SAS Institute, Inc., Cary, NC

27513 USA) were used to test for significant differences between treatments

(Hoshmand, 1998, Sail et al., 2001).

Seeds were sown 18 June 2005 with seed obtained from Nicaragua

(Nikolaus Foidl, Biomasa). Seedlings were transplanted after 3 weeks to 4-L

plastic greenhouse pots and grown through the fall of 2005. Seedlings were

permitted to go dormant before resuming growth in the spring of 2006, at which

point they were cut back on 19 March 2006 to 15-cm and a single shoot

permitted to grow. Thirty trees were repotted on 27 June 2006 to 26.5-L plastic

nursery containers with a sterilized potting mix consisting of 1-part peat moss: 1-

part coarse perlite: 1-part composted cow manure and placed in an outdoor

growing area. Plants were watered and fertilized daily using a nutrient solution

consisting of I.Og L'1 5-11-26 Hydro-Sol®and 0.75 g L'1 15.5-0-0 Calcium

Nitrate Plus™ (Scotts Sierra Horticultural Prod. Co., 14111 Scotts Lawn Rd.,

Marysville, Ohio 43041 USA), and 0.25 g L'1 MgS04-7H20 Epsogrow5 Epsom

Salts (Hydro Agri North America 100 North Tampa Street, Suite 3200, Tampa,

Florida 33602 USA). Trees were single-stemmed, unbranched, and ranged in

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height from 163 to 264 cm (mean=197.7 cm) and 1.9 to 3.0 cm in caliper

(mean=2.39 cm). All plants were pollarded to a height of 150 cm on 18 July 2006.

Six plants were not pollarded and observed for lateral bud release. There were

four treatments:

Treatment 1 -Defoliation (DEF)

Following pollarding to 150 cm, the remaining leaves also were harvested,

resulting in totally defoliated, decapitated trees. Pairs of stems were harvested

when they had at least six fully expanded leaves.

Treatment 2 - Laterals pruned to 10 cm (LP10)

Lateral stems that were released due to decapitation were cut back to a targeted

length of 10 cm to encourage additional branching on six trees. Pruning cuts

were made at locations acropetal to the nearest node located at least 10 cm.

from where the lateral branch attached to the main stem so that no internodal

cuts would be made. Pairs of stems were harvested when they had at least six

fully expanded leaves.

Treatment 3 - 2 stems harvested every 30 days (2S30)

The two largest stems were harvested from each of six trees at 30-day intervals

following cutback and each subsequent harvest.

Treatment 4 - 6 leaves per stem (6LPS)

Stems were harvested when any two stems had at least six fully expanded

leaves.

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5.4 Results

Seedlings that were not pollarded did not release lateral buds, consistent

with previous experience with moringa. DEF plants released fewer lateral buds

per node than other treatments but did so at more nodal points along the stem

(Table 5.1). LP10 plants had significantly more laterals per node (2.0) than other

treatments that were released on the fewest number of nodes per tree (4.7)

(Table 5.1). An average of 2.8 stems and 43 cm of total stem length were

removed from LP10 trees when the laterals released following pollarding were

pruned back to 10 cm on 4 August 2006.

DEF trees released the fewest number of laterals per node (1.2) on the

greatest number of nodes per tree (8.3). After two weeks, DEF trees had

released buds at approximately the same rate as any of the foliated trees (3.8

nodes/tree compared to 3.7 nodes/tree) but had produced just 21 mm of stem

growth/tree compared to 158 mm/tree for foliated trees. Three weeks following

pollarding, DEF trees had released buds on two more nodes/tree (8.8 nodes/tree

compared to 6.7 nodes/tree) and had produced 405 mm of stem growth/tree

compared to 739 mm/tree for all foliated trees. DEF trees demonstrated an

increase in stem length from 13 to 55% of foliated tree stem length in one

additional week of growth.

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Table 5.1. Nodes per tree with lateral branches, laterals per node, and lateral branches per tree for four pruning strategies of moringa trees pollarded at 150 cm.

Measurement27

Treatment following pollarding to 150 cm

Nodes/tree with lateral branches

Laterals/ node

Laterals/ tree

LP10 4.7a 2.0a 9.2a

2S30 6.1b 1.5b 9.1a

6LPS 7.0b 1.5b 10.2a

DEF 8.3b 1,2b 10.2a

zMean yWithin columns, means followed by different letters are significantly different at P< 0.05 (Tukey-Kramer HSD).

Table 5.2. Comparison of four pruning strategies of pollarded moringa seedlings after a single harvest. Values are per plant.

T reatment (n=6)

following pollarding to

150 cm

Days since

decap. to first harvest

No.(n) stems

removed

Total stem length (mm)

Fresh weight total

(g)

Dry weight

total

(g)

Dry weight

stem: leaf percent

LP10 42 2.2 159 26 4.4 27:73

DEF 42 2.5 157 29 5.4 21:79

2S30 30 2.0 143 33 6.2 21:79

6LPS 26 2.3 162 34 6.3 21:79

The number of days to the first harvest increased for DEF and for LP10

treatments (Table 5.2) due to the severity of the treatments. LP10 plants

produced the lowest dry weights at the first harvest (Table 5.2). However, when

the dry weight of 4.7 g from the 4 August lateral cutback to 10 cm is added to the

weight of the first harvest the actual dry weight for the 42-day period is 9.1 g.

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LP10 plants also had the highest dry weights at the second harvest. DEF plants

produced higher dry weights than LP10 plants but grew minimally following the

first harvest and were not abie to be harvested a second time.

Dry weights were not significantly different among treatments (Table 5.3).

When the dry weights from the 4 August lateral cutback to 10 cm is added the

actual total dry weight for the two LP10 harvests is 32.7 g. Leaf dry weight was

slightly lower and stem dry weight was slightly higher for LP10 seedlings than

other treatments. Pruning laterals back to 10 cm encouraged bud release at the

base of the pruned laterals, resulting in more laterals per node on fewer nodes.

Dry weights were approximately 18% of fresh weights and leaf biomass

accounted for 76% of dry weight whereas 24% was stem biomass. Diameters of

harvested stems averaged 10 mm. Daily dry weight production from the 6LPS

and 2S30 pruning treatments was significantly greater than that of the LP10 and

DEF treatments (Table 5.4).

Table 5.3. Dry weights of leaves and stems and total dry weight after two harvests of moringa trees pollarded at 150 cm and managed by three pruning strategies.

Treatment following

pollarding to 150 cm

Days to

harvest

Leaf dry weight

(g)

Measurement^

Stem dry weight

(g)

Total dry weight

(g)

LP10 (n= 12) 42 20.9 7.1 32.7X

2S30 (n= 12) 30 25.1 7.4 32.5

6LPS (n=11) 26 25.2 7.9 33.0

zMean/plant Measurements are not significantly different (Tukey-Kramer HSD). xlncluding 4.7 g cutback dry weight/plant.

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Table 5.4. Dry weight production per day for moringa trees pollarded at 15'0 cm with three pruning strategies after two harvests. Treatment

following pollarding to 150 cm

Dry weight growth per dayzy (g/plant)

DEF (n=6) 0.8a

LP10 (n=12) 0.9a

2S30 (n=12) nb

6LPS (n=11) 1,4b

zMean yWithin columns, means followed by different letters are significantly different at P< 0.05 (Tukey-Kramer HSD).

5.5 Discussion

Form is the sum of features of the crown, major branches, and stem that

characterize a whole tree (Wilson, 1990). The related mechanisms of apical

dominance and apical control as well as shading within the canopy determine the

development of pollarded moringa tree form. Apical dominance represses lateral

bud outgrowth; buds are released following pollarding, and apical dominance is

reinstated with the re-established of the replacement terminal meristem. Apical

control represses elongation of lateral shoots, is temporarily removed as the

most distal growing shoots are harvested, and is reinstated with re-established of

the replacement terminal meristem.

Distal lateral shoots elongated and bent upward following each

subsequent harvest, maintaining an inventory of sequentially elongating stems

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for future harvests. Coupled with lateral bud release due to pollarding, the

strongly monopodial nature of moringa can be harnessed to generate rapid

terminal growth that eventually exerts apical control over more proximal shoots.

The resulting entity is less a result of the specific act of pollarding and more the

product of a concerted effort of renewal pruning and canopy management.

Defoliated (DEF) trees were observed to release the fewest number of

laterals per node on the greatest number of nodes per tree. Defoliation of

decapitated black walnut (Juglans regia L.) stump sprouts always increased the

number of buds released from inhibition and reduced the average length of

axillary shoots (Mauget et al., 1993). Initial regrowth of DEF plants was similar to

other pruning treatments and suggests that a single defoliation may be used at

the time of pollarding to encourage lateral bud release. Regrowth after the first

harvest was poor, suggesting that DEF trees require more time to recover from

being defoliated and to re-establish shoot systems. Defoliation may be a cultural

practice that can be used strategically with pollarded trees managed for leaf

biomass production if it appears necessary to encourage lateral bud release to

establish additional lateral shoots to replace those previously harvested.

Similarly, cutting back laterals will encourage additional bud release at the

junction of the lateral stem to the main trunk and also serves as a method for

producing additional lateral shoots. Generating lateral bud release by either of

these strategies slows the elongation and growth of existing laterals and in the

short-term reduces leaf biomass yield. LP10, 2S30, and 6LPS pruning produced

similar dry weights (32.7, 32.5, 33.0 g/plant) and the results suggest that the

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guidelines used for determining harvests were uniform throughout the

experimental period and consistent with the plant based approach to this study.

Dry weights were obtained over different time periods (68, 60, and 48 days),

indicative of the wide range of plant response to the pruning strategies employed.

Pollarding combined with selective pruning and management of the tree

canopy can be used to build a vertical column of multiple, renewable growing

sites. The mass defoliation associated with cyclic coppiced production is

eliminated when selective pruning is used and less plant resources must be

committed to rebuild overall stem architecture. Lower leaves and branches that

persist help to ensure consistent levels of light interception and interior plant

canopies can be effectively managed for light penetration through the selective

removal and harvest of stems. Although the response of root systems was not

examined, it is anticipated that root system biomass would be disrupted less by

pollarding than under coppiced management.

Managing pollarded plants in this way should still permit relatively high-

density production. Spacing plants at 50 cm on center would provide 40,000

plants-ha'1. Harvesting 1.4 g dry weight-plant'1-day'1 would yield approximately

20 metric tons of dry weight-ha'1 -yr'1, 75% of which would be leaf biomass.

Harvesting shoots whenever there are 6 fully-expanded leaves/stem

provides a simple guideline and harvesting strategy that utilizes the iterative

processes of regrowth and harvest for pollarded moringa. Harvesting stems at

30-day intervals worked well under the growing conditions of this study but may

not be appropriate for other geographic regions. Horticultural practices that

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encourage sustainable production of moringa leaves will assist in meeting the

nutritional need of families in developing regions of the world.

5.6 Literature Cited

Babu, S.C. 2000. Rural nutrition interventions with indigenous plant foods-a case study of vitamin A deficiency in Malawi. Biotechnol. Agron. Soc. Environ. 4(3):169-179.

Bosch, C.H. 2004. Moringa oleifera Lam. [Internet] Record from Protabase. Grubben, G.J.H. & Denton, O.A. (Editors). PROTA (Plant Resources of Tropical Africa / Resources vegetales de I’Afrique tropicale), Wageningen, Netherlands. http://database.prota.org/search.htm. Accessed 14 October 2005.

Craker, L.E. 1999. Trends in medicinal and aromatic plant production in the United States. Acta Hort. (ISHS) 502:71-76. http://www.actahort.org/books/502/502_8.htm.

Craker, L.E. and Z. Gardner. 2005. Sustaining the harvest: challenges in MAP production and markets. Acta Hort. (ISHS) 676:25-30. http://www.actahort.org/books/676/676_2.htm.

Dalla Rosa, K.R. 1993. Moringa oleifera: A perfect tree for home gardens. Agroforestry Species Highlights, The Agroforestry Information Service, USDA Forest Service, 1010 Holomua Road, Paia, Hawaii 96779-6744 USA.

D’Souza, J., and A.R. Kulkarni. 1993. Comparative studies on nutritive values of tender foliage and mature plants of Moringa oleifera Lam. J. Econ. Tax. Bot. 17(2):479-485.

Fahey, J.W. 2005. Moringa oleifera: a review of the medical evidence for its nutritional, therapeutic, and prophylactic properties. Part 1. Trees for Life Journal 1:5. http://www.TFLJournal.org/article.php/20051201124931586.

Foidl, N., L. Mayorga, and W. Vasquez. 1999. Utilization of Marango (Moringa oleifera) as fresh forage for cattle. FAO Anim. Prod. Health Paper (143):341 -346.

Foidl, N., H.P.S.Makkar, and K. Becker. 2001. The miracle tree: the multiple attributes of Moringa: the potential of Moringa oleifera for agricultural and industrial uses. Church World Service, Dakar.45-76.

Francis, G., H.P.S. Makkar, and K Becker. 2005. Products from little researched plants as aquaculture feed ingredients. Agrippa - FAO online journal (www.fao.org/agrippa) .

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Fuglie, L. 2001. The miracle tree - the multiple attributes of Moringa. Church World Service, Dakar, Senegal.

Grusak, M. 2005. Plant foods as sources of pro-vitamin A: application of a stable isotope approach to determine vitamin A activity. Trees for Life Journal 1:4. http://www.TFLJournal.org/article.php/20051201123813474.

Hoshmand, A.R. 1998. Statistical Methods for Environmental and Agricultural Sciences. 2nd ed. CRC Press, Florida.

Katumba, B.M., J.M. Buffa, G. Abigaba, and J. Okorio. 2004. Domestication of medicinal tree species in the Victoria Lakeshore Region. Uganda J. Agric. Sci. 9:84-88.

Lakshminarayana, R., M. Raju, T.P. Krishnakantha, and V. Baskaran. 2005. Determination of major carotenoids in a few Indian leafy vegetables by high- performance liquid chromatography. J. Agric. Food Chem. 53:2838:2842.

Mauget, J.C., N. Rizot, and J. Guinard. 1993. Effect of time and position of summer pruning on the release from inhibition of the axillary buds of walnut stump sprouts. Acta Hort. (ISHS) 311:210-216.

Nautiyal, B.P. and K.G. Venkataraman. 1987. Moringa (Drumstick) - an ideal tree for social forestry: growing conditions and uses - part 1. Myforest 23:53-58.

Palada, M.C. 1996. Moringa (Moringa oleifera Lam.): a versatile tree crop with horticultural potential in the subtropical United States. HortScience 3:794-797.

Palada, M.C. and L.C. Chang. 2003. Suggested cultural practices for Moringa. Asian Vegetable Research and Development Center pub. #03-545. PO Box 42, Shanhua, Tainan 74199; Taiwan ROC.

Pasternak, D. and J. Ram. 1994. Moringa: a highly nutritious vegetable tree. Tropical Rural and Island/Atoll Development Experimental Station (TRIADES), Technical Bulletin No.2.

Price, M. The Moringa Tree. 1985. Revised 2000 by K. Davis. Educational Concerns for Hunger Organization (ECHO) Technical Note. www.echotech.org/technical/technotes/moringabiomasa.pdf.

Reyes Sanchez, N. 2006. Moringa oleifera and Cratylia argentea: potential fodder species for ruminants in Nicaragua. Doctoral diss. Dept, of Animal Nutrition and Management, SLU. Acta Universitatis agriculturae Sueciae vol. 2006:1.

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