bahir dar university college of agriculture

93
BAHIR DAR UNIVERSITY COLLEGE OF AGRICULTURE AND ENVIRONMENTAL SCIENCES POSTGRADUATE PROGRAM ASSESSMENT AND MANAGEMENT OF WHITE MANGO SCALE (Aulacaspise tubercularis Newstead) ON MANGO (Mangifera indica L.) IN BAHIRDAR ZURIA DISTRICT, NORTH WESTERN ETHIOPIA MSc Thesis By ALEBEL ESKEZIA ADAM April, 2022 Bahir Dar, Ethiopia

Upload: khangminh22

Post on 23-Nov-2023

0 views

Category:

Documents


0 download

TRANSCRIPT

BAHIR DAR UNIVERSITY

COLLEGE OF AGRICULTURE AND ENVIRONMENTAL SCIENCES

POSTGRADUATE PROGRAM

ASSESSMENT AND MANAGEMENT OF WHITE MANGO SCALE (Aulacaspise tubercularis Newstead) ON MANGO (Mangifera indica L.) IN

BAHIRDAR ZURIA DISTRICT, NORTH WESTERN ETHIOPIA

MSc Thesis

By

ALEBEL ESKEZIA ADAM

April, 2022

Bahir Dar, Ethiopia

i

BAHIR DAR UNIVERSITY

COLLEGE OF AGRICULTURE AND ENVIRONMENTAL SCIENCES

POSTGRADUATE PROGRAM

ASSESSMENT AND MANAGEMENT OF WHITE MANGO SCALE

(Aulacaspise tubercularis Newstead) ON MANGO (Mangifera indica L.) IN

BAHIRDAR ZURIA DISTRICT, NORTH WESTERN ETHIOPIA MSc Thesis

By

ALEBEL ESKEZIA ADAM

A THESIS SUBMITTED TO THE COLLEGE OF AGRICULTURE AND ENVIRONMENTAL SCIENCES

GRADUATE PROGRAM OF BAHIR DAR UNIVERSITY IN PARTIAL FULFILMENT OF THE

REQUIREMENTS FOR THE DEGREE OF MASTER OF SCIENCE (M.Sc.) IN PLANT PROTECTION

Department: Plant science

Program: M.Sc. plant protection

My adviser: Abaynew Jemal (PhD)

April, 2022

Bahir Dar, Ethiopia

ii

iii

iv

ACKNOWLEDGEMENTS

First of all, I would like to say thank you for sincere gratitude and appreciation to my major

advisor Dr. Abaynew Jemal for supporting me from the beginning up to the final work of

the thesis manuscript. Secondly, I would like to say thank you Amhara Region Agricultural

Research Institute (ARARI) and Ethiopia Agricultural Research Institute (EIAR) for giving

scholarship and financial support as well as Bahirdar University College of Agriculture and

Environmental Science.

I also extend my thanks to all staff members of Adet, Sirinka and Fogera Rice Research

and Training Centres for helping directly or indirectly during the implementation of this

research work.

Finally, I would like to express my love and passion to my wife, children, brothers, sisters

and friends who gave courage and hospitality during the study period.

v

DEDICATION

This thesis is dedicated to my beloved family for their unwavering support, and for their

encouragement for everything follow up in my whole academic career, and for my life for

all success.

vi

TABLE OF CONTENT

Contents Page

THESIS APPROVAL SHEET Error! Bookmark not defined.

DECLARATION iii

ACKNOWLEDGEMENTS iv

DEDICATION v

LIST OF TABLES ix

LIST OF APPENDIX TABLES xii

LIST OF ABBREVIATIONS/ACRONYMS xiv

CHAPTER 1. INTRODUCTION 1

1.1. Background and Justification 1

1.2. Statement of the Problems 3

1.3. Objectives of the Study 4

1.3.1. General objective 4

1.3.2 Specific objectives 4

2.1. Mango, Origin, Taxonomy, Ecology 5

2.1.1. Mango origin and taxonomy 5

2.1.2. Ecology of mango 6

2.1.3. Management of mango tree 7

2.1.4. Mango production constraints 8

2.2. White mango scale origin, Taxonomy, Biology and Ecology 9

2.2.1. White Mango Scale origin and taxonomy 9

2.2.2. Biological characteristics of white mango scale 10

2.2.3. Ecology of white mango scale 12

2.2.4. Distribution of white mango scale 14

2.2.5. Host ranges of white mango scale 16

2.2.6. Sign and symptom of white mango scale 16

2.2.7. Damaging and economic impact of white mango scale 17

2.3. Management of white mango scale 19

2.3.1. Cultural and agronomical method 19

2.3.2. Biological control method 21

2.3.3. Use of tolerant mango variety 22

vii

TABLE OF CONTENT (continued)

2.3.4. Chemical control method 23

2.3.5. Integrated white mango scale practice 25

3.1. Assessment of White Mango Scale 26

3.1.1. Description of the survey area 26

3.1.2. Study design and sampling size 28

3.1.3. Procedures of survey work 29

3.2.1. Description of the experimental site 30

3.2.2. Insecticides and experimental design 30

3.2.3. Procedure of the study 31

3.3. Data collection 34

Response of the growers (%): About white mango scale infestation level, and the status of

mango tree plantation measured in each kebele in percent form. 34

3.3. Statistical data analysis 34

3.3.1. Analysis of survey 34

3.3.4. Experimental data analysis 36

CHAPTER 4. RESULTS AND DISCUSSIONS 37

4.1. Survey of White Mango Scale 37

4.1.1. Demographic characteristics of the respondents 37

4.1.2. Mango tree plantation status 38

4.1.3. White mango scale infestation and their perception 38

4.1.4. Growers response about pruning of mango tree 39

4.1.5. Agronomic practice of mango tree 40

4.1.6. Growers mango seedling source 41

4.1.7. Controlling practice of white mango scale 42

4.2. Assessment of White Mango Scale in mango orchards 43

4.2.1. Incidence, prevalence and severity 43

4.2.2. Mango variety and white mango scale infestation 43

4.2.3. Alternative host identification 45

4.3. Field Experiment 46

4.3.1. Severity of white mango scale on each phenology of mango tree 46

viii

TABLE OF CONTENT (Continued)

4.3.2. Severity of white mango scale in each growth of mango 46

4.3.3. Seasonal fluctuation of white mango scale 47

4.3.4. Screening of tolerance mango variety 48

4.3.5. Mango tree spacing and the severity of white mango scale 49

4.3.6. Effects of insecticides on white mango scale 51

4.3.7. Effects of insecticides on white mango scales mortality 52

5.1. Conclusions 54

5.2. Recommendations 54

REFERENCES 55

APPENDICES 70

ix

LIST OF TABLES

Tables Page

Table 4.1. Demographic characteristics of the respondents in Bahir Dar Zuria District from

2020/2021 cropping season 37

Table 4.2. Mango growing experience and the status of mango plantation in Bahir Dar

Zuria District from 2020/2021 cropping season 38

Table 4.3. White mango scale infestation and Perception of the respondent about the

infestation in Bahir Dar Zuria District during 2020/2021 cropping calendar 39

Table 4.4. Response of producers about pruning practice of mango tree in Bahir Dar Zuria

District during 2020/2021 cropping season 40

Table 4.5. Cultural practice of mango tree in Bahir Dar Zuria District from 2020/201

Cropping season 41

Table 4.6.Growers mango seedling source in Bahir Dar Zuria District during

2020/2021Cropping season 42

Table 4.7. Growers controlling practice of white mango scale infestation in Bahir Dar Zuria

District during 2020/2021 cropping season 42

Table 4.8. Infestation status of white mango scale in Bahir Dar Zuria District during

2020/2021 Cropping calander 43

Table 4.9. Cropping system of mango tree in Bahir Dar Zuria District from

2020/2021cropping season 44

Table 4.10. Alternative hosts of white mango scale in Bahir Dar Zuria District from

2020/2021cropping season 45

Table 4.11. Phenology of mango tree and the severity of white mango scale in Bahir Dar

Zuria District from 2020/2021 Cropping season 46

Table 4.12. Growth phase of mango tree and the severity of white mango scale in Bahir

Dar Zuria District from 2020/2021 cropping calander 47

Table 4.13. Mean fluctuation of White Mango Scale from August1/ 2020/September

1/2021 in Bahir Dar Zuria District cropping calander 48

Table 4.14. The severity of white mango scale in each mango variety in Bahir Dar Zuria

District from 2020/2021 cropping season 49

Table 4.15. The severity of white mango scale in each spacing of mango tree in Bahir Dar

Zuria District from 2020/2022 cropping season 50

x

LIST OF TABLE (continued)

Table 4.16. The number of white mango scale colonies pre and post application of

insecticides in Bahir Dar Zuria District during 2020/2021 cropping season 52

Table 4.17. Mean mortality of white mango scale colonies in Bahir Dar Zuria District from

2020/2021 cropping season 53

xi

LIST OF FIGURES

Figure Page

Figure 2.1. Mango white scale biology 12

Figure 3.1. Location map of the survey site 28

Figure 3.2. Location of the experimental site 30

Figure 3.3. The avoiding mechanism of producers after pruning the infected branch 40

Figure 3.4. Host plants of white mango scale

Error! Bookmark not defined.

xii

LIST OF APPENDIX TABLES Appendix Table Page

Appendix Table 1.Base line survey questionnaire 70

Appendix Table 2.Anova tables of severity in each phenology eggs 71

Appendix Table 3.Anova table of crawlers in phenology of mango tree 71

Appendix Table 4.Anova table of adult white mango scale 71

Appendix Table 4.Anova of mango growth phase and severity 72

Appendix Table 5.Anova table of Seasonal fluctuation of white mango scale 72

Appendix Table 6.Anova table of tolerant mango variety leaf parameters 72

Appendix Table 7.Anova tables of on stem parameters 72

Appendix Table 8.Anova table of fruit of mango tree 72

Appendix Table 9.Anova tables of inflorcence of mango tree 72

Appendix Table 10.Anova tables of petiole of mango tree 72

Appendix Table 11.Anova table intra and inter row spacing of mango tree 72

Appendix Table 12.Anova table before spraying of the insecticides 73

Appendix Table 13.Anova table after 1st spraying of the insecticides 73

Appendix Table 14.Anova after 2nd spraying application of the insecticides 73

Appendix Table 15.Anova table of mortality of white mango scale after 1st 73

Appendix Table 16.Anova table after second application 73

xiii

LIST OF APPENDIX FIGURES

Appendix Figures Page

Appendix Figure 1. Process of host plant of white mango scale identification 73

Appendix Figure 2. Host plants of white mango scale identified 74

Appendix Figure 3. Mango varieties adopted in the farm of mango 74

Appendix Figure 4. Experimental site and tested chemicals 75

xiv

LIST OF ABBREVIATIONS/ACRONYMS

AD Anno Domini

ARARI Amhara Regional Agricultural Research Institute

BBCH Biologische Bundesanstalt, Bundessortenamt

and Chemische Industrie

BoA Bureau of Agriculture

CABI Centre for Agriculture and Bioscience International

CSA Central Statistical Agency

EC Emulsifiable Concentrate

FYM Farm Yard Manure

GLM General Line Model

IPM Integrated Pest Management

MCDM Multi-Criteria Decision Making

MoA Minister of Agriculture

MORD Minister of Agriculture and Rural Development

NMA National Meteorological Agency

WMS White Mango Scale

xv

Assessment and Management of white mango scale (Aulacaspise tubercularis) on mango

(Mangifera indica L.) In Bahirdar Zuria District, North Western Ethiopia

ABSTRACT

Mango (Mangifera indica L.) is the second perennial fruit crops in Ethiopia in its coverage

and economic importance. However, this fruit crop is constrained by white mango scale.

Therefore, this study was conducted to assess the status the infestation, and to evaluate

synthetic insecticides as management option in Bahir Dar Zuria District, Ethiopia during

2020/2021 cropping season. The method of the study was through structured questionnaire

and assessment of the orchards. The sampling techniques were purposive for the selecting

study sites, households as well as mango orchards. For this study, about 3 study sites, and

33 mango growers or orchards from each site were selected. The data collected includes

white mango scale status and host plants. The collected data was analyzed using SPSS and

STATA software. The prevalence as well as the incidence of white mango scale was 100%

while the severity was about 80.76%. Other than mango, white mango scale was occurred

on guava, lime, and orange and eucalyptus forest tree. The maximum severity of white

mango scale was 71.7 on 1m*1m inter - and intera row spacing while the minimum severity

(41.43) was recorded on 6m*6m spacing. The screening of insecticides as well as tolerant

mango variety was carried out at Zenzelima. From the screened tolerant mango variety,

Tommy Atkins was the tolerant mango variety with the lowest severity recorded as 31.7,

34.2, 23.7, 13.6 11 and 24.4 respectively on the leaf, stem, inflorcence, fruit and petiole of

mango tree. For the evaluation of insecticides, there were four treatments namely

Nimbecidence 3% EC, Karate EC 5%, Folmit 40% EC and untreated. The design of the

experiment was Randomized Complete Block Design with three replications. Insect’s data

were collected, and counted from 20cm twigs from 12 mango tree. The data was analyzed

using SASv23 software. Nimbecidence 3% EC insecticide control better than others. The

mortality rate of white mango scale using Nimbecidence 3% EC in the 1stand 2nd spraying

was 70.71 and 44.2 respectively, which is the highest compared to others. Therefore, it is

recommended to apply Tommy atikine mango variety, 6m*6m intra and inter row plant

spacing, and Nimbecidence 3% EC insecticide for the controlling of white mango scale in

the study area.

Keywords: Host, Mango, Nimbecidine, Prevalence, Spacing, white mango scale

1

CHAPTER 1. INTRODUCTION

1.1. Background and Justification

Mango (Mangifera Indica L.) belongs to the Anacardiaceae family, which includes the genus

indica. The only species farmed commercially on a considerable scale is indica (Griesbach,

2003). Mango is a fruit that originated in tropical Asia and is now found in tropical and

subtropical lowland areas all over the world (Mukherjee and Litz, 1997; Dirou, 2004 and Crane

et al., 2008). In the tropics and subtropics, mango is a very important fruit crop (Singh, 1986).

Mango trees are erect and fast-growing trees with a canopy that can be broad and rounded or

more upright (Schnell et al., 2006).The tree is a deep-rooted, evergreen crop with the potential

to grow into massive trees. Mango is taproot descends to a depth of 20 feet, producing several

wide-spreading feeder roots as well as many anchor roots that penetrate for several feet

(Matsuoka, 2000). Mango tree is young, short-pointed, oblong and lanceolate. This crop has

the shape and measuring more than 30 cm in length and up to 13 cm in breadth, mango tree

leaves are simple, whole, leathery, dark green and glossy, pale green or red. The mango tree is

inflorescence is a branching terminal panicle that measures 4–24 inches in length and bears

500 to 10,000 flowers (Salim et al., 2002).

Mango is a very important fruit crop in the world. The crop is grown in over 85 countries with

a total production area of roughly 3.69 million hectares. The production was estimated to be

over 35 million tons per year worldwide (FAO, 2019). Mango output increased by 100 %

globally between the years 1971 and 2002 with production estimated at roughly 25.75 million

tons in 2002 (FAO, 2020).In Ethiopia, Mango fruit yield is large, and having the potential for

internal, and export markets as well as industrial processing (Takele Honja, 2014). According

to the Central Statistical Agency 2020 (CSA) estimate, the total production coverage was

around 1.08 million km2 .The total fruit production area coverage was about 107,890 hectares

(FAO, 2020).

Even though, Mango is the second most important fruit crop with the 1,857,387 households

contribute to mango production, which produces roughly 185,739 tons of mangos per year from

15,413.76 hectares. Despite the fact mango fruit cultivation has historically been important in

Ethiopia and the Amhara region, biotic and abiotic factors are presently limiting production

central statical agency (CSA, 2017).

Lack of inappropriate cultural practices which including planting pattern, planting system,

supplementary irrigation, lack of optimum rate of fertilizer application, lack of improved

2

tolerant mango variety, varietal mixture, absence of proper mango pruning practice and

unavailability of high quality planting materials were some of the abiotic factors (Gashawbeza

Ayalew et al., 2015; Tewodros Bezu et al., 2015).

Insect pests are some of the most critical biotic limiting factors for mango production. White

mango scale is one of the most common insect pests of mango trees. This insect pest is also

one of the most critical insect pests of mango fruit crops (Griesbach, 2003). The first report of

white mango scale insect pest infestation in Ethiopia was in 2010 in a mango orchard owned

by Green Fосus Ethiopia (Abo-Shanab, 2012). That was utilized to import mаngо seedlings

from India, and it has been deduced that insect pests may have reached Ethiopia by chance on

those seedlings (Abo-Shanab, 2012).

White mango scale is economic importance, and has been claimed to have a negative impact

on mangoes in various places of the world, including Ethiopia (Germain et al., 2010; Ofgaa

Digitra and Emana Getu, 2015).This insect pest is imperfect metaphoresis that means the insect

lacks pupal stage in its life cycle. White mango scale has polyphagous feeding habit which is

used two family vascular plants as its host (Germain et al., 2010).

The female armour is circular, flat, thin, and often wrinkled, and exuviae is near the margin,

and yellowish-brown, with a median black ridge, forming a dark distinct median line while

male armour is circular, flat, thin, and often wrinkled, and exuviae is near the margin, and

yellowish-brown, with a median black ridge, forming a dark distinct median line. Male armours

are small, white, and tricarinate, with sides that are nearly parallel. Crawlers are a rich vivid

brick red (Hodges and Hamon, 2006).

Currently, there was no quantifying the status of this insect and plantation status of mango tree.

Also there was no single insecticide, variety and spacing of mango has been authorized in the

early 1980s. Insecticides similar to those used to control white mango scale infested mango

were recommended for the control of Hemiptera insect scales like that of the red scale

(Aonidiella auranti) on citrus (Tsedeke Abate, 1994).

Several trials on white mango scale and insecticides demonstrated that Imidacloprid%SC,

Thiamethoxam 25%WG, Dimethoate%, and Lambda cyhalothrin17.5% SC were developed

and registered for the control of white mango scale (Andrew Manners, 2016; Parakash and

Patil, 2018). Meanwhile, insecticides such as Movento 150 OD, Methidathion 400 EC, and

Folmit 500 SL were developed in Ethiopia to suppress white mango scale (Gashawbeza

Ayalew et al., 2015; Ofgaa Djirata et al., 2016).

3

According to Ferdu Azerefegne et al., (2009) and Ofgaa Djirata, (2017), there have been few

reports of insecticide screening against the white mango scale insect pest in Ethiopia since the

white mango scale was introduced in the country less than 10 years ago. Imidacloprid % SC,

Thiamethoxam 25% WG, Dimethoate 40%, and Lambda cyhalothrin 17.5% SC are some of

the insecticides (Andrew Manners, 2016; Parakash and Patil SB, 2018). In particular,

insecticides such as Movento 150 OD, Methidathion 400 EC, and Folmit 500 SL were

developed in Ethiopia to control white mango scale (Gashawbeza Ayalew et al., 2015; Ofgaa

Djirata et al., 2016).

As a consequence, there was very little available information on effective management options

for eliminating white mango scale in the Amhara region of the Bahirdar Zuria District mango

potential area. Apart from that, regular pest assessments will tell us the status of white mango

scale occurrence, distribution and its impact of on mango tree. Also the study indicates farmer’s

knowledge and pest control practices.

1.2. Statement of the Problems

Mango trees in Bahirdar Zuria District, Amhara Region, North Western Ethiopia, were just

being negatively affected by white mango scale. According to Temesgen Fita (2014) studies,

the yield obtained before white mango scale emergence was significantly higher than the yield

obtained after white mango scale emergence, regardless of the infested Districts. Mohammed

Dawd (2012) also mentioned that before the emergence of white mango scale, fruit harvest was

up to one ton, but then after the occurrence of white mango scale, fruit harvest was decreased

to 0.2 to 0.3 ton or nothing at all.

The appearance of white mango scale in the District as well as its increasing prevalence to

other nearby mango fields in the study region had a massive effect on mango tree plantation

and yield. Due to the infestation pressure of this insect pest in the area, the insect caused mango

panicle destruction and loss of quality and market.

Also, newly planted mango trees were uprooted due to an infestation of white mango scale and

the plantation status of mango trees in the study area declines from time to time. Hence, this

study was carried out with the aim of to understand the status of mango and develop

management option for the white mango scale.

4

1.3. Objectives of the Study

1.3.1. General objective

To assess and develop management option for white mango scale in Bahirdar Zuria

District, North Western, Ethiopia

1.3.2 Specific objectives

To assess the plantation status of mango, and white mango scale infestation.

To assess alternative host ranges and tolerant mango variety for white mango scale.

To evaluate synthetic insecticides for the management of white mango scale.

5

CHAPTER 2. LITERATURE REVIEW

2.1. Mango, Origin, Taxonomy, Ecology

2.1.1. Mango origin and taxonomy

Mango (Mangifera indica L.) is an important perennial tropical fruit crop. This perennial fruit

crop is a prized dietary component (Rocha Ribeiro et al., 2007). Mango tree is thought to have

originated in the region between north-east India and Myanmar (Samson, 1986; Yadav and

Singh, 2017). This tropical fruit crop is found under the categories of Kingdom plantae, class,

Mangoliopsida, phylum, magnoliophyte, order, Sapindales, family Anacardiaceae, genus

mangifera, and the species indica are the taxonomic classifications for mango tree (Wauthoz

et al., 2007).

This fruit crop is consumed as a fresh fruit crop. The fruit of mango has many forms of

preparations (Nabil et al., 2012). It is also utilized in animal feeds, poultry diets,

Ethnopharmacology, and a variety of chemical businesses around the world (Wauthoz et al.,

2007; Kayode and Sani, 2008). Mango fruit has a rich, fragrant aroma and a flavor that is

pleasantly balanced between sweetness and acidity (Hobson and Grierson, 1993).

Mango fruit is mature, the skin is usually a mix of green, red, and yellow colors, depending on

the variety (Matsuoka, 2000). The flesh of mango is bright orange and tender with a wide flat

pit in the middle (Ben-Dov, 2012). It has attractive color, sweetness, excellent flavor, delicious

taste, high nutritional value and health promoting qualities (Fowomola, 2010). Mango fruit has

high amount of sugar, protein, fats, and all known vitamins. Moreover, it is an excellent source

of dietary antioxidants such as ascorbic acid, carotenoids, and especially phenolic compounds

(Nabil et al., 2012).

The mature leaves of mango tree are simple, entire, leathery, dark green and glossy, pale green

or red while the young, short-pointed, oblong and lanceolate in shape and relatively long and

narrow and measuring more than 30 cm in length and up to 13 cm in width (Salim et al., 2002).

The inflorescence of mango tree is a branched terminal panicle 4–24 in length. The inflorcence

has the capability of bearing what has been variously estimated to range from 500 to 10,000

(McGregor, 1976, 200 to 6000 Free, 1993), and 1000 to 6000 (Mukherjee, 1953). The flowers

of mango tree are borne collectively on panicles. Individual mango flowers are small ranging

in size from five to ten mm in diameter (Scholefield, 1982; Mukherjee and Litz., 1997).

6

The number of panicles of mango range from 200 to 3000 per tree depending on tree size and

extent of branching. Mango trees are often irregular in their cropping habit with no clear pattern

across different years and place. Plantings system of mango can also suffer from alternate or

biennial bearing of fruit where a tree or an orchard produces a large fruit crop in an on-year

followed by a small crop in the following off-year (Souza et al., 2004). There can be periods

of irregular bearing of mango and periods of alternate bearing in the same orchard (Fitchett et

al., 2016).

Mango trees are monogenic, and polygenic which bears both perfect and hermaphroditic

genetic nature. Flowers having both pistil and staminate structures are purely male or staminate

flowers. Both types of flowers are born on same inflorescence, and it is monoicous fruit crop

(Mukherjee and Litz, 1997). Knight (1997) reported that as mango fruit matures in 100 to 150

days after flowering and the fruit will have the best flavor if allowed to ripen on the tree.

Griesbach, (1992) reported that commercial marketability requires 13 % dissolved sugars and

the fruit ripens best on the condition placed stem end down in trays to prevent the sap from

spreading to other parts of the fruit and also to encourage even ripening at room temperature

20-25°C and covered with a dampened cloth to avoid shriveling, and that loss of fruit increases

dramatically after harvest as the fruit maturity increased (Bautista-Rosales, 2005).

Mango trees which grown in most parts of Ethiopia developed from seedlings, and they are

inferior in productivity in terms of fruit quality. Considering this, the inferior quality trait of

mango, improved mango varieties named Kent, Keitt, Tommy Atkins and apple were

introduced from Israel in 1983 and are being commercially produced by the Upper Awash Agro

industry enterprise and distributed in to different parts of the country (Mohammed Dawd et al.,

2012; Temesgen Fita, 2014).

2.1.2. Ecology of mango

The mango species can grow successfully from sea level up to 1200 meters above sea level.

The production and productivity of mango tree varied according to elevation, altitude, and

temperature. Mango has indeed been successfully developed in a wide range of climates from

hot and humid to cool and dry or arid, with mean annual rainfall of 400mm to 3600mm. The

crop grown in the temperatures of at least 21°C with an optimum of 25°C (Bally, 2006). This

tree is drought tolerant and may survive with very little as 300 mm of yearly precipitation

(Johnson et al., 1997; Al-Kazafy, 2015).

7

2.1.3. Management of mango tree

Proper spacing of mango trees is crucial for all the tree physiological functions (Dirou, 2014).

The production of mango is hindered whenever adequate spacing, also which is not maintained,

and the pest outbreaks are more likely to happen (Seid Hussen and Zeru Yimer, 2013). Mango

tree spacing appears to be an essential consideration in production, and the pest management

according Olaniyan (2004). Mango trees can grow to be massive examples, orchards are

typically planted with a field condition and a lower population density (Khan et al., 2015).

Overpopulation of mango trees in cultivation of mango tree resulted in fewer fruits. When the

tree become more populated, the insect become more prone to be damaged and pest-infested

the tree. Tall trees can pose a harvesting challenge and make spraying and pruning exceedingly

difficult (Griesbach, 2003). Study showed that mango fruits grown in high-density planting

had a progressive decline in crop yield after 14–15 years (Sharma et al., 2006).

Since commercial fruit cultivation on a small scale in Ethiopia is indeed a floral crop,

agronomic procedures in nurseries and orchards of different fruit crops rely heavily on human

labor. Having the right tools, knowing how to use them, and making management decisions

about horticultural tools and equipment, practice selection, market availability, and storage

facility availability, among other things, are all important factors that can affect horticultural

operations and profits in a number of different ways (Andrew Manners, 2019).

Regular annual pruning is important for very well mango orchard. Pruning of mango tree is

maintaining of mango tree canopy size. Maintaining of mango canopy allows the entrance of

air and sunlight to penetrate mango tree (Bally, 2006). In Ethiopia, a significant portion of

mango growers utilize river water, even if only a significant fraction of smallholders uses

pound water. Mango yields are higher in river water irrigation than in pond water irrigation.

One of the parameters that determines mango yield is the quantity and quality of accessible

water. The amount and frequency of irrigation required is determined by a variety of variables

including soil type, property, climate, and others (Seid Hussen and Zeru Yimer, 2013).

The use of organic and inorganic fertilizers for the mango production purpose is rare except

some innovative farmers that use organic fertilizer. Similar study conducted by Ayelech

Tadesse, (2011) indicated that farm yard manure principally transported from homestead to the

field mostly during the dry season and spread in the bottom of each tree in circular form.

Fertilizer treatment, irrigation, pest and disease control, wind break, and trimming are among

8

the mango production strategies used by smallholder farmers in the area, according to the same

study (Rosals et al., 2005).

Chemical inputs were entirely exploited neither for fertilization nor for pest treatment,

according to the assessment research report. According to different studies, smallholder

farmers in the area intercrop mango with maize, taro, ginger, chat, cabbage, and banana at

various phases of development, along with annual and perennial crops (Tesfaye Hailu et al.,

2014).

Collecting of mango tree by hand picking, scissor cutting, and stick harvesting are the methods

used mostly by smallholder farmers in Ethiopia. Hand picking is indeed a way of gathering

produce that preserves the quality of the fruit while also protecting it from mechanical damage.

It produces fruit with a stem, which reduces bruising and damage, whereas stick structures

enable fruit to drop and leave the fruit without a stem, which increases bruising and mechanical

damage to the fruit. Ayelech Tadesse (2011) demonstrated that harvesting typically begins after

fruit dropping, which is the primary maturity indicator, indicating that cuts, punctures, and

bruising boosted ethylene production and expedited fruit softening, resulting in mechanical

injuries and decay (Seid Hussen and Zeru Yimer, 2013).

2.1.4. Mango production constraints

Mango fruit production constrained by several factors. That means lacks of pest tolerant

improved mango variety, lack of proper agronomic practices, prevalence of wind and bird’s

postharvest loss and poor marketing and outbreak of pest with relation to the climate change

(Seid Hussen and Zeru Yimer, 2013; Tewodros Bezu, 2015).

The other constraints of the production of mango according to different research findings were

insect and disease pest. From diseases such as Anthracnose, Bacterial Black spot, stone and

from insect pests’ weevil (Sternochetus spp), fruit fly, mango gall flies, Mango leaf coating,

Mites, Mango seed weevil, Mealy bug, Powdery mildew, Scale, Spider mites, mango tip borer,

Stem-end rot, Termite, Thrips and White flies (Balock and Kozuma, 1963; Halteren, 1970;

Griesbach, 2003 and FAO, 2010).

In Ethiopia, the production and productivity of mango was constrained by insect pests such as

fruit flies, mango seed weevil, mites, thrips, mealy bugs and scale insects and reported to have

caused damages ranging from significant vegetative damage to total mango yield losses (Seid

Hussen and Zeru Yimer, 2013 and Alemayehu Chala et al., 2014). Moreover, Tewodros Bezu

et al., (2015) reported thrips, fruit flies, termites, and various fungal diseases constrain mango

9

production in Ethiopia, from the insect pests of mango, white mango scale was the most

important insects which was reported to have damaged mango in various parts of the world

(Cunningham, 1989; SRA, 2006; Germain et al., 2010 and Abo-Shanab, 2012).

White mango scale was among insect pests inflicting damage to mango trees in Amhara region

Bahirdar zuria District in Amhara Region, Western Ethiopia. The study finding of Temesgen

Fita, (2014) indicated that, infested Districts by white mango scale, the yield obtained before

white mango scale emergence was significantly higher than after white mango scale

emergence. Mohammed Dawd, (2012) also reported that fruit harvest up to one tons before the

occurrence of white mango scale decreased after the occurrence of mango white scale.

Literatures reported regarding the impact of white mango scale, and losses caused by fruit

rejection from Nayarit due to white mango scale infestation were ranged from 50 to 100%

(Hodges and Harmon, 2006).

2.2. White mango scale origin, Taxonomy, Biology and Ecology

2.2.1. White Mango Scale origin and taxonomy

White mango scale is an insect whose common names are cinnamon scale, mango scale, white

mango scale, escama Del mango, escama Blanca del mango. This insect was known by its

accepted name Aulacaspis tubercularis New stead in 1906 (Varshney et al., 2002). This insect

pest commonly known as armored scale insects, as one of the most species in the families and

it is composed of 2650 species in 400 genera (Osuna-García et al., 2016; Ben-Dov, 2012).

The feeding nature of White mango scale is polyphagous armored scale. The insect is

considered as one of the key pests of mango crops around the world (Llewellyn, 2000). It

produces conspicuous pink blemishes on the mango fruits, which depreciate their commercial

value, and it makes them unacceptable for export markets. In the absence of control measures,

the pest could cause up to 90% yield losses in mango groves, and which may pose a threat to

sustainability mango production (Hodges and Harmon, 2006).

The pest reproduces during both dry and wet seasons (Halteren, 1970). White Mango Scale

was a sucking insect that poses severe threat to mango plantations in various mango growing

countries (Labuschagne et al., 1996; Pena et al., 1998 and Juárez-Hernández et al., 2014).

The feeding nature of white mango scale is sap-feeding insects which injure plants directly by

depriving the plants of its food and water supply (Pellizzari and Germ, 2010). Indirect damage

of white mango scale is by gall formation, foliage disturbances such as bleaching or yellowing,

10

and deformation such as leaf curling. Generally, however, the effect of sucking insects upon

trees is much less conspicuous than the effect of defoliators (Juárez-Hernández et al., 2014).

The damage caused by White Mango Scale included yellowing of leaves, appearance of

conspicuous pink blemishes on mature and ripe fruits, and dieback of the plant (El-Metwally

et al., 2011 and Abo-Shanab, 2012). Infestation in young trees might lead to excessive fall off

leaves, retarded growth and death of the whole plant (Nabil et al., 2012).

This insect pest caused economic problem on mangoes in most mango potential continents and

their countries. The ultimate economic impact of this insect pest could range from low to high

depending on the targeted market (local versus international) and part of mango infested

seedling, leaves and fruits (Daneel, and Joubert, 2009; Urias-López et al., 2010).

The insect pest was reported in most of the mango producing zones in African countries.

However, Majority of the farmers still do not know it nor consider it as a pest Likewise, the

incidence and impact of white mango scale in Ethiopia in Amhara region of white mango scale

has spread in all mango producing area has become problem of mango and to alleviate this

insect effect, there were several management options those were available for this insect pest

(Ofgaa Djirata et al., 2016).

2.2.2. Biological characteristics of white mango scale

White mango scale is a sessile armored, tiny shelled insect which belonging to the Hemiptera

order as well as the Diaspididae family (CABI, 2019). It is swollen angular, quadrate, prosoma

body, wide at conspicuous lateral tubercles in approximately level with anterior spiracle and

posterior spiracles usually associated with spiracle pores; gland spines and macro ducts absent

from thorax and head; circular, flat, thin, and wrinkled with opaque white shells (Moharum,

2012; Harmon, 2016).

Male white mango scales were tiny, white, and tricarinate, with nearly parallel sides. The body

of the white mango scale is broadest at prominent lateral tubercles, almost level with anterior

spiracles, and posterior spiracles are part of the growing with spiracle pores and gland spines,

and macro-ducts are absent from the thorax and head whenever mounted on a plate with an

angular prosoma (Soysouvanh and Hong, 2016). The white mango scale is a circular, flat, thin,

wrinkled adult male insect. Exuviae are yellowish-brown and have a median black ridge which

produces a dark prominent median line near the margin (Meyer and Whitlow, 1992). Male

covers acquire a reddish brown color and take on a more elliptical shape as they mature into

11

pre-pupal, pupal, and adult generations. For males, the second instar lasts 5–8 days (Williams,

and Watson, 1988).

The female scale cover is just about spherical, white, and transparent, with black, oval exuviae,

whereas the male scale cover is smaller, rectangular, white, and also has three prominent

longitudinal ridges exuviae (New Zealand, 2018). Food availability impacts white mango scale

sexual reproduction, but the sex ratio is typically 1:1 (male: female), though both male and

female colonies have been observed (Ahmad and Ghani, 1972).

Adult females of the white mango scale deposit 28–65 eggs in concentric circles underneath

the scale cover over the duration of 11–13 days, and might even produce 3 or 4 batches in

their lifetime (Gilbert, 1985). The white mango scale has a general look, and mature female

white mango scales can lay 80-200 eggs (Sayed, 2012). Females stay pale yellow, round and

somewhat visible in the second instar, which lasts for 8–10 days. Females nymphs are 0.6–1.1

mm long (Williams, and Watson, 1988).

Smooth, elongate, and whitish when it was first laid, eggs start turning pale yellow as they

mature. The eggs are placed behind the scale layer that surrounds the female's body. The

average egg length and breadth are 0.22 mm and 0.09 mm, respectively (Salahuddin et al.,

2015). The eggs hatch in eight days generating red-orange nymphs or crawlers that move to

branches, leaves, and flowers and attach themselves to feed on plant tissue where they grow

and reproduce (Bautista-Martinez, 2006). White mango scale crawlers are light green to

yellowish brown in color, translucent, and rectangular in shape, measuring 0.23 mm in length

and 0.11 mm in width (Salahud din et al., 2015).

Nymphs of white mango scale may emerge after that the female has begun depositing the next

batch of eggs (personal observation). About 80% of the crawlers of newly hatched nymphs'

white mango scale (also known as crawlers) become males The newly hatched nymph of WMS

is very small, elongate, oval, and completely devoid of any wax secretion, and the crawler

moves there until it finds a suitable place to settle on. Legs, antennae, and a pair of bristles at

the tip of the abdomen move over the leaf surface for 2–48 hours to find a feeding site, and the

crawler is free moving and recognized by the presence of legs, antennae and wings (Halteren,

1970).

The crawlers were deep bright red. The life cycle of white mango scale took between 35– 40

days for females and 23 – 28 days for males (Halteren, 1970). Depending on temperature

females lay 80 to 200 eggs and crawlers moved to feeding sites settling within 24 hours after

12

hatching. Male crawlers settled in groups close to females and female crawlers settled

randomly Up to 80% of crawlers become males in nurseries, infestation at early stage retards

growth of seedlings (Halteren, 1970).

After settling, females remain sessile throughout their development and Females released

pheromones through their anus to attract males (Moreno,1972) and adult males undergo a

pseudo-pupation, develop a pair of wings and can disperse by flying to find mates (Ghauri,

1962). The male pre-pupal and pupal stages are spent under the scale produced by the second

instar. The insect pest could produce five to six generations per year at a maximum day time

temperature of 26°C and night time minimum of 13°C (Miller and Davidson, 2005).

White mango scale was a pest that is present all year round-with overlapping generations.

Overlapping generation is growing the population within the same year. Increasing of the

generation of white mango scale damages organs of mango tree by feeding the parenchyma.

(Miller et al, 2005).

(A. tubercularis): A=A group of male covers with one female cover (lower right); B=High resolution

female white cover=High resolution male and female white scale

Figure 2.1. Mango white scale biology

2.2.3. Ecology of white mango scale

Weather is an important parameter that affects white mango scale distribution, abundance and

their management. According to Dharmendra et al. (2014) favorable weather condition for

13

high pest infestation ranges between 24-35°C and relative humidity 70-95% in both mango

orchards. Abo-Shanab (2012) reported a significant positive relationship between daily mean

temperature and relative humidity, and recorded population density of white mango scale. On

the other hand, the author reported a significant negative relationship between wind speed and

dew point, and population density of white mango scale which may be due to transference of

insect crawlers and early nymphal instars by the wind to another plants and/or places

(Dharmendra et al.,2014)).

White mango scale can produce five to six generations per year at a maximum day time

temperature of 26°C and night time minimum temperature of 13°C (Miller and Davidson,

2005). Weather is an important factor determines white mango scale distribution, abundance

and their dominance. According to Dharmendra et al., (2014) favorable weather condition for

high pest infestation ranges between 24-35°C and relative humidity 70-95% in both mango

orchards (Salem et al.,2015).

Studies reported as that has significant positive relationship between daily mean temperature

and relative humidity and recorded population density of white mango scale. On the other hand,

Literatures reported a significant negative relationship between wind speed and dew point and

population density of white mango scale which may be due to transference of insect crawlers

and early nymphal instars by the wind to another plants and/or places (Abo-Shanab, 2012).

The study on effective temperature requirement of scale (Hemiptera: Diaspididae) by

González-Zamora et al., (2012) reported that the first and second stage nymphs and young

female individuals require 24.4,11, and 13.2 days to complete their developments at 25°C

while showed no development at 30°C (Wong et al., 2008). Thus, it is possible to say that

Aulacaspise tuber cularise is more susceptible against seasonal and global temperature. Studies

conducted a two-sex life table study of white mango scale (Hemiptera: Diaspididae) at

20,23,25,28, and 31°C the intrinsic rate of increase under these temperatures was 0.06,

0.07,0.09, 0.10, and 0.08 d-1 (Ravuiwasa et al., 2012).

The same types of studies reported in the same ways as global warming modified

environmental conditions of different regions because of an increase in greenhouse gas

emissions, particularly temperature, rainfall, and relative humidity (Netherer and Schop

2010).The phenomenon generated changes in population development, and the ecology of

diverse plant, and animal species, thus favoring displacement of diverse pests and diseases to

14

other locations, an important problem in terms of pathogens such as fungi, bacteria, and viruses,

as well as the vectors involved (Netherer and Schop, 2010).

White mango scale does well at warmer temperatures 25-28°C; however, lower temperatures

adversely affect its performance. In a study of the life cycle of white mango scale (Hemiptera:

Diaspididae), the preoviposition period first and second nymph stage periods, and ovipositional

period were recorded as 6-13,7-18,9-26, and 28-59 days, respectively at 22.5–25.5°C under

laboratory conditions (Abd El-Razzik, 2000).

White mango scale could produce five to six generations per year in a maximum day time

temperature of 26°C and night time minimum of 13°C (Miller and Davidson, 2005). According

to Sayed, 2012, the total population of white mango scale had maximum value 1006.89

individuals/leaf on June 15th at 15.2-28.40 C and 56.8% relative humidity. The lowest level was

in mid-December 39.80 individuals /leaf at 15.0-22.20 C and 55.6% relative humidity

(Deloatch, 1974). The mean numbers of nymphal adult female per sample unit were the highest

in mid-March as 343.75 and 147.66 individuals (Davidson, 2005).

The gravid female and prepupae and pupae stages reached their maximum as 129.94 and

694.31 on July 15th and April 15th (Kogan and Ortman, 1978). The lowest densities of nymphs,

and gravid female were 12.33 and 5.33 individuals on Mid-December whereas the least values

of adult female and pre-male 3.94 and 15.49 were observed in early September and mid-

November respectively. The total population had maximum value of 1095.65 individuals on

April 15th at 12.3-23.80C and 57.20% R.H. The lowest total population 58.30 individuals were

observed during Dec. 15th 38.72 individuals/leaf at 15.2-21.80 C and 56.3% RH (Owens,

2016).

The pest was abundance throughout the period extended from mid-February up to mid-

September while it was lower in abundance from early October up to early February (Sayed,

2012).White mango scale females and males were randomly distributed on leaves, stems and

fruit in mango orchards under organic and conventional management although males were

grouped in colonies of a few individuals to more than 100, which eventually allows them to

occupy the entire leaf in depending on the season (Urias-López et al., 2010).

2.2.4. Distribution of white mango scale

White mango scale distributed more than 43 countries in tropical and subtropical countries,

Oceania, South America, the Caribbean, and Asia, where it feeds on more than 40 plant species

(Malumphy, 2014; Stocks and Pena, 2013). According to Hodges and Harmon, (2006), the

15

distribution of white mango scale in the world classified in different agro ecological zones with

the variability of ecology (Dinka et al., 2005).

After the occurrence of the insect pest, it was distributed to the other adjacent peasant mango

farm within a short period of time and infestation source once infested takes less time. At the

time of the infestation of white mango scale, most farmers were uprooted mango trees from

their farm due to lack of affordable management options since the pest was new for them. And

then, the infestation of pest has been speeded at an alarming rate into different districts (Ofgaa

Digrata et al., 2017), and the author shown the distribution of white mango scale from its first

observed into four directions. Once presence of white mango scale in the region, the pest

spreads more and more in the quickly manner because of its small body size and which makes

it easy to spread with fruits, seedlings, and even by the wind (Kondo Muñoz-Velasco, 2009).

This characteristic has made this pest to colonize most of the mango producing zones. Being

an invasive pest, the information about the pest and its management practices was less available

for researchers, policymakers, and farmers in the most region of mango potential area. In fact,

most research work in the region focused around assessing the distribution and population

dynamics (Tsegaye Babege et al., 2017; Teshale et al., 2019) with a few trying to answer

questions around management practices (Abo-Shanab, 2012; Gashawbeza Ayalew et al.,

2015).

The pest distributed over the air distances of 97, 98, 92 and 43 km to the east, south, west and

north directions respectively (Teshale et al., 2102). Study showed that white mango scale

distribution was expanded to the southwestern part of Ethiopia and considerably affecting

mango production and productivity and they recorded very low population density and the pest

free areas. The pest spreaded too many other neighboring districts including the mango

production belt in the area (Mohammed Dawd et al., 2012; Gashawbeza Ayalew et al., 2015).

The distribution of white mango scale in Western Oromia, East Wollega, spreaded quickly

from one mango growing area to another and now distributed to all Districts (2014).

Severity status of white mango scale in mango orchards was studied by Temesgen Fita (2014).

In central rift valley, more than seventeen Districts, over 200 hectares of mango orchard

infested by white mango scale recorded (Gashawbeza Ayalew et al., 2015). During 2020/2021

severity of White Mango Scale in South Western part of Ethiopia was very high except some

Districts were recorded from mid to very high infestation of white mango scale.

16

2.2.5. Host ranges of white mango scale

White mango scale had many alternative host plants with relation to the feeding nature of the

insect pest. This insect pest was mostly polyphagous species (Panda and Khush, 1995). And

they were more prone to become major pests when introduced to new areas because their wide

host range facilitates their establishment (Kosztarab, 1996; Stocks, 2013). White mango scale

was reported to have been 93 infesting plants other than mango in different countries

(Malumphy, 2014).

Plant species found under families Sapindaceae and Rutaceae served as host plants for white

mango scale (Sarwar, 2013). It was recorded mainly from hosts belonging to four plant

families: Palmae, Lauraceae, Rutaceae, Anacardiaceae, particularly on mangoes and cinnamon

(Miller and Davidson, 2005; Borchsenius, 1966). White mango scale species were polyphagous

(Kosztarab, 1996, Miller and Miller, 2003). Additional studies supported the idea as the insect

family Diaspididae (Hemiptera: Coccoidea) includes a number of important pests of wild and

cultivated plants (Beck, 1965).

The pest attacked common perennial crops and that included tropical fruits and ornamental

plants including banana, coconut, camellia, guava, mango, palm, papaya, breadfruit, ginger,

bird of paradise, sugarcane, ficus, apple, plumeria, avocado, citrus, grape, and palms, citrus,

papaya, avocado, ginger, cinnamon, and pumpkin (Dinca, 2017).Similar reports from several

countries indicated that white mango scale is a polyphagous pest that inflicts damage to many

host plants (Erichsen and Schoeman, 1992;Malumphy, 2014).

The first report of white mango scale infestation of mango in Ethiopia has now been near to a

decade (Mohammed Dawd et al., 2012). The insect pest spreaded and has caused damages to

mango production in western Ethiopia (Tesfaye Hailu et al., 2014; Temesgen Fita, 2014; Ofgaa

Djirata and Emana Getu, 2015; Urias-López et al., 2010).

2.2.6. Sign and symptom of white mango scale

The signs and symptoms of White Mango Scale in white mango scale fertilization taken place,

and the crawlers hatched out. The hatched white mango scale stage moved until they glue

themselves to the part of the plant. The insect stage developed, and remained sucking the juice

of the plant under their armors on the leaf of mango tree (Louw, et al., 2008). The insect sucking

by penetrating pattern of leaf. That pattern revealed as it could penetrate not only cell wall but

also the lignified xylem. The infested xylem materials leaving behind a reddish mass have been

17

phenolic acid. From infested mango leaves the slices followed the stylet bundle penetration

path through the leaf from the piercing site on the leaf epidermis (Goble et al., 2012).

Including oblique, and parallel orientations in relation to the leaf surface, the stylet bundle

changed directions several times depend upon entering the spongy mesophyll (Juarez, et al.,

2014). Histological evidence indicates that after penetrating the coriaceous cuticle and

epidermis, the white mango scale stylet bundle explores the interior of mango leaf tissue

including vascular bundles by changing its path yet maintaining most of its pathway in the

mesophyll (Rice-Evans et al., 1998).

The female feeds mainly on the mesophyll cells as it pierces them from the path of stylet bundle

without causing their collapse. The exploration pathway of the stylet bundle through the leaf

tissues is mostly intracellular, and the stylet bundle is capable of piercing the lignified cell

walls of vascular bundles (Selman and Dawd, 2012). The feeding nature of scale insects

depends on young mango growing tips and, which can cause distorted foliage. Feeding of the

leaf of mango leaves may cause them to turn yellow and plants may appear water stressed. The

heavily infestations of white mango scale can cause stems and branches to dieback and

unhealthy plants may die (Juarez-Hernández et al., 2014).

The presence of scales on mango fruit caused them to be blemished or distorted, particularly

on the condition of the infestations of white mango scale occurred when fruit were developing.

The small number of white mango scale species induces ornate galls in their host plants. As

mentioned above, the honeydew which released by white mango scale causes the development

of black sooty mold, which can be extremely unattractive and may cause plants to be unsalable.

Black sooty mold which is released by white mango scale can sometimes be removed with

some fungicide applications while it is only recommended after scale insects have been

eradicated (Andrew Manners, 2016).

2.2.7. Damaging and economic impact of white mango scale

Mango trees are subjected to infestation by different pests. Among these pests, White mango

scale insect is considered as the one and the major destructive sap feeding insect pests of mango

trees (El-Zoghby, 2019). White mango scale insects are known to survive on plants completely

submerged at high tide (Harrison, 1916). Many of them are important pests of agriculture

(Miller and Davidson, 2005; Peronti et al., 2001) and may injure or kill plants by depleting

them of their sap, injecting toxins, transmitting viruses or excreting honeydew, which serves

as a medium for sooty moulds (Williams, 1992; Gullan and Martin, 2003).

18

The adaptation of feeding nature of mouth of white mango scale had the form a beak which

was used to pierce the tissues and suck the fluid from the leaf. These types of nature of feeding

of white mango scale mouth was piercing and sucking mouthparts that may damage mango

plants which cause loss of plant vigor due to removal of excessive quantities of sap. When the

infestation level become extreme cases, the leaf of mango become wilting and foliage distortion

(Schoeman, 1992; Miller and Davidson, 2005).

White mango scale infestation cause stunting of vigor of mango tree, damage floral organs and

reduce seed production cause premature leaf-fall by injecting toxins into the plant body using

saliva and then mango tree finally become distortion, proliferation (galls) or necrosis (Duressa,

2018). Some of examples capsid damage on bean leaves and shoots and the stem necrosis on

plants by Helopeltis and other Heteroptera provide entry points for pathogenic fungi and

bacteria (Great head and Pope, 1977).

White mango scale injured mangoes by different mechanism by feeding on the plant sap

through leaves, branches and fruits causing defoliation, drying up of young twigs, poor

blossoming and so affecting the commercial value of fruits and their export potential especially

to late cultivars where it caused conspicuous pink blemishes around the feeding sites of the

scales (Erichsen, 2005).

The insect sucks sap from the plant and secretes honeydew, which deposits on the leaves or

other parts of the plant (Duressa et al., 2018). The honeydew provides conducive substrate

for growth of black sooty mould (Erichsen, 2005). At the beginning of the infestation, only the

leaf base was affected. However, the entire leaf becomes covered with mealy bugs over time

disrupting normal photosynthetic activities and thereby decreasing fruit production (Fitchett

et al., 2016).

White mango scale infestation significantly reduces fruit production and causes substantial

reduction in income to mango and fruit farmers throughout West Africa. Moreover, the

infestation of mango trees by this insect pest significantly reduces the esthetic and shade value

of mango trees in communities (Baker et al., 2009).

The infested areas on leaves turned pale green or yellow and ultimately died. Heavy infestation

of white mango scale could kill leaves, branches and attack of the pest on mango fruit causes

development of conspicuous pink blemishes around its feeding sites and as a result export

potential of the fruits and their commercial value are greatly affected (Joubert et al., 1999;

Hodges and Hamon, 2006; Abo-Shanab, 2012).

19

In the nurseries of mango orchard, the severe infestation white mango scale on the early stage

of mango retards the growth rate of it. Early stage of mango is particularly vulnerable to

excessive leaf loss and death of twigs, during hot dry weather. The heavily infested premature

fruits dropping and the mature fruits became small in size with lacking of juice ((Fitchett et

al, 2016).).

This pest injures the shoots, twigs, leaves, branches and fruits and sucks the plant sap. The

mouth parts of white mango scale were causing, thereafter deformations, and defoliation,

drying up of young twigs, dieback, poor blossoming and death of twigs. The action of the toxic

saliva of this insect pest affecting the commercial value of fruits, and their validity for

exportation potential especially too late cultivars where it causes conspicuous pink blemishes

around the feeding sites of the scales ((Fitchett et al., 2016).).

Attacked fruit is particularly susceptible to this loss in quality as seen by skin blemishes and

hard scales on mango fruit. Contamination by insect faeces, exuviae, and corpses all reduce the

marketability of a crop as do black and sooty moulds growing on the honeydew excreted by

various homopterous bugs. A major problem in the tropics is ‘stickiness’ of cotton lint caused

by honeydew from cotton whitefly, the sticky cotton is difficult to gin and its value is

diminished (Nabil et al., 2012).

2.3. Management of white mango scale

There were management options developed for insect pest controlling in general and for white

mango scale in particular. Managements of white mango scale is genetically by developing

tolerant mango variety from varietal improvement point of view (Dharmendra, et al., 2014)).

Agronomically by practicing appropriate agronomic management and in the field of plant

protection from pest management point of view such as using artificial insecticides; cultural

approach; biological, botanical methods and integrated pest management and the widespread

and rapid establishments of white mango scale in mango orchards or gardens required

immediate changes in integrated pest management program as promising prospect (Sarwar et

al., 2014).

2.3.1. Cultural and agronomical method

Cultural control is one of the management principle in plant protection in order to make the

environment less favorable to pest establishment, growth and development which means

application of optimum amount of fertilizer, pruning, mulching and supplementary irrigation

20

promote plant vigor, tolerance to pest damage, and reduce sap-sucking insect population

growth (Dreistadt, 2014; Dreistadt, 2007).

There were trials with organic and inorganic fertilizer that applied in conventional plantations

of mango management and the infestation increase more in organic farming. White scale

females were more abundant in organic than conventional mango orchards possibly because of

the six monthly applications of fertilizer as indicated by Altieri and who claimed that pests

increased with excessive use of fertilizer especially nitrogen and phosphorus (Bautista-Rosales

et al., 2013).

Plantations of mango under organic farming means, there is no application of input that favored

the presence of natural enemies of white scale like the trash-carrying lacewing Cereaochrysa

sp. (Neuropteran: Chrysopidae), Chilocorussp., Cybocephalus sp (Coleoptera: Coccinelidae)

(Urias-Lopez and Flores, 2005, Isiordia-Aquino et al, 201). The author suggested that organic

farming system increased nutritional quality of plants, and favors reproduction and dispersal

of this insect pest (Nicholls, 2003; Chau et al., 2003).

Pruning is removal of unwanted infested branches from a tree. It is one of the effective in

removing infested plant tissues and reducing populations of scale insect (Kabashima and

Dreistadt, 2014). This types of cultural practice are one of the most important for fruit tree

insect pest management by the improvement of air circulation and reaching of sun light

radiation evenly distribution in order to modify the microclimate of the insect so as to suppress

them. This is one of the most important mechanism to prevent the incidence of insect pest

(Fivaz, 1997).

There are different ways of pruning such as formative pruning which is done in the first years

of the young tree to guide the tree into the desired shape. In the first year, when the trees are

about one meter from the ground, that cap the seedling in order to encourage side branches 3

to 4 well branches. Structural pruning should be done for proper maintenance of the trees. The

height of the trees should be controlled about 3.5 m in height and at this stage, all branches at

knee level should be pruned. Any dead branches and sucker branches should be removed to

allow more sunlight through the canopy to the ground under the tree. There should be done

every year in order to maintain the tree at and develop a suitable canopy density. Post-harvest

pruning was an effective control measure and also helped the penetration of chemical sprays

through the tree canopy (Fitchett et al, 2016).).

21

Different authors suggested that the other possible cultural control measures such as quarantine

new plants and treat before placing them with established plants spot treat with insecticidal

soap if needed taking care to cover all crack cervices and other possible hiding places water

and oil treatments. The application of a garden hose with water in a hard spray and washing off

white scales can be removed following the application of oil wash plants with soapy water

(Tsegaye Babege et al., 2017).

2.3.2. Biological control method

Biological control of insect pest was the utilization of natural enemies. The mechanism reduce

the damage of the crop caused by organisms to tolerable level (Ofgaa Djirata et al., 2016). The

study of white mango scale parasitoids on infested mango in the presence parasitoids was the

common parasitoids represented 40% followed by Encarsia sp., 34% and A. citrinus 26%. Over

40 species of parasitoids and predators, and several fungal pathogens are known to attack the

insect pest of mango (Ben-Dov et al., 2012).

There were commercially available natural occurring parasitoids and predator’s insects. The

parasitoids helped to maintain populations below levels that cause significant damage to the

plants (Hodgson and Martin, 2001). The most known natural enemies used as bio-control

agents in frequency of their application include parasitoids (parasitic wasps and flies) predators

(some insects, spiders and predatory mites) and pathogens (fungi, protozoa, bacteria and virus

(Mills and Daane, 2005).

In the absence of these natural enemies, population explosions of the pest can occur. Aphytis

melinus DeBach and Aphytis lingnanensis Compere (Hymenoptera: Aphelinidae) are the most

common parasitoid species controlling white mango scale populations (DeBach 1974; Watson

et al., 2015).

It was recommended to seek advice from the biological control agent producer prior to

releasing a predator for the first time so that their release was optimized (Mani and

Krishnamoorthy, 2001). If pesticides applied, ensure that a sufficient time period elapses

before releasing beneficial insect’s (Sarwar, 2015). White mango scale was under good

biological control in most other mango producing countries and therefore it was decided to

introduce an exotic biological control agent and try to establish it in different mango producing

areas (Eagling, 2009).

Both the parasite and predators were successfully augmented and released in to mango orchards

and became well established (Daneel, and Dreyer, 1997 and 1998), the predatory thrips

22

Auleurodothrips fasciapennis franklin and the parasitoid (Setegn et al., 2015). White mango

scale was reported as the manageable by predators (Labuschagne, 1996). According to Sayed,

(2012) Cybocephalus sp., Chrysoperla carnea (Stephens), Chilocorus bipustulatus L.). And

predacious mites are predators of white mango scale and Aphytis spp., Aspidiotiphagus citrinus

(Craw) and Encarsia sp. are parasitoids of white mango scale with regard to the collected

numbers of predators (Setegn et al., 2015).

The larvae of the ladybird beetle Chilocorus sp. (Coleoptera: Coccinelidae) infested with white

mango scale and they were found feeding on both male and female white mango scales. When

feeding, the larvae easily destructed coat of the male mango scale and reached it where as they

forcefully pushed their heads inward and partly opened up cover of the female captured and

chewed it (Ikewuchi and Ikewuchi, 2008). In all instances of observations, the presence of the

larvae was associated with colony of white mango scales (Ofgaa Djirata et al., 2016).

In Ethiopia, there were white mango scale (Homoptera: Diaspididae), and its associated natural

enemies and according to the suggestion of him, there were identified and confirmed pecimens

of A. tubercularis, its predators, and its parasitoids were identified via di nucleic acid (DNA)

sequencing. Di nucleic acid sequences of the (COI) gene of all Ethiopian scales sampled were

identical and confirmed as a single haplotype of white mango scale and the author generalized

the predators of white mango scale were recovered. These included two Coccinelidae

(Coleoptera), Rhizobius lopanthe (Blaisdell) and species of Platynaspis and the third

unidentified beetle species from the family Nitidulidae. Di nucleic acid (DNA) sequences of

the parasitoid specimens identified two species of Encarsia, E. lounsburyi Berlese and Paoli

and E. citrina Craw (Hymenoptera: Aphelinidae). These natural enemies were identified for

the first time as resident natural enemies of white mango scale in Ethiopia (Temesgen Fita et

al., 2014; Daneel and Joubert, 2006).

2.3.3. Use of tolerant mango variety

Tolerance plants can be described as the extent to which a plant can support an insect infestation

without loss of vigor, and the reduction of crop yield (Beck, 1965). This does not consider that

tolerance falls within the definition of resistance (Vasugi et al., 2012). The mechanisms of

resistance are divided into three categories namely no preference, antibiosis and tolerance

(Inayatullah and Fargo, 1990). Resistant cultivars are economically feasible and

environmentally safe, and socially acceptable method for controlling various pests and diseases

including insects like white mango scale (Painter, 1951).

23

Host plant resistance to scale insects is likely conferred by an interaction between plant genetic,

physiology, and biochemistry (McClure, 1985; Iyer and Schnell, 2009). The term non-

preference has subsequently been replaced by antixenosis because non-preference refers to the

insect and this is incongruous with the notion of resistance being a property of the plant (Kogan

and Ortman, 1978).

White mango scale infestation on mango was varied among different mango cultivars.

Different literature have different suggestion, Apple mango variety was among the least

infested cultivars (Ofgaa Djirata et al., 2016) on the contrary, Tommy Atkin mango variety has

the capability of tolerance for white mango scale (Camacho and Chong, 2015).The variety of

Alfa and Espada Stahl mango were susceptible compared to Tommy Atkins mango variety to

white mango scale (Rossetto et al., 2006).

2.3.4. Chemical control method

Controlling of insects using chemical method refers to the use of synthetic or organic

compounds capable of killing white mango scale. Various insecticides are registered for control

of white mango scale for mango fruit crop (Stark and Banks, 2003). Crawler are the most

susceptible stage of white mango scale to insecticides. Contact action insecticides including

horticultural oils, become progressively less effective once the scale insects develop their waxy

cover. Insect growth regulators may be effective, provided they are applied when the immature

stages are present (Souaya et al., 2012).

Location of the insect on the plant, growth stage of the plant, and solubility of the insecticide

influence the effectiveness of systemic insecticides applied for control of white mango scales.

Several spray applications at 15–20 day intervals might be necessary for complete management

of a heavy infestation. The toxicity of insecticides to parasitoids and other beneficial insects

should be considered before starting a spray program for scale insects. Since scale is a

quarantine pest in many areas, phytosanitary treatment with gamma irradiation has been

developed as a potential control measure for this scale (Al-Kazafy, 2015).

Synthetic insecticides registered for soft scale management can be broadly categorized into

contact and systemic insecticide. Systemic insecticides include members of organophosphates,

neonicotinoids, tetramic acid derivatives and diamides and which function as contact

insecticides when applied as topical sprays directly on the scale insects. When applied as soil

drench, soil injection, basal trunk spray, trunk injection, granular broadcast and pellet broadcast

24

systemic insecticides were absorbed by plant tissues and translocate to the canopy (Frank,

2012).

Scale insects were difficult to manage using pesticides in the egg and adult phase of life. If

pesticides were to be used to manage scale insects, it is recommended to apply contact products

only when there is a high proportion of crawlers present because crawlers are very susceptible

to many pesticides including oil based products. On the condition of high populations are

present, a systemic product was probably of being required (Andrew Manners, 2016).

The application of the insecticides had to be made just before crawler emergence to ensure the

highest concentration of active ingredients in the plant tissues. Although systemic insecticides

had the benefits of greater flexibility and residual longevity, recent studies suggested that

neonicotinoids should be used carefully because of their potential impact on pollinator health

(Cowles, 2014; Pisa et al., 2015; Johnson and Corn, (2015) and their implication in spider mite

outbreaks (Szczepaniec et al., 2011; Raupp, 2013).

According to Smith et al., (1997) suggestion, petroleum sprays were important for the control

of hard scales in Australia. Application of systemic or growth regulators helped to prevent

population increase. Pre-harvest applications to prevent the scale insects built up during

harvest. High volume (1200L/ha) cover sprays after pruning with mineral oils and methidathion

depending on scale activity. Chloropyrifos, methidathion, Dimethoate 40%EC, (Howard,

1989), Diver and CAPL oils have been found successful in reducing the population of white

mango scale (Abo-Shanab, 2012; Abhilash, and Singh, 2009).

According to Andrew Manners,2016 suggestion in his recommendation, active ingredients

registered against scale insects relevant to Australian mango nurseries included Carbaryl,

Chloropyrifos, Diazinon, Dimethoate, Methylation, Imidaclopride, Pyriproxyfen, Buprofezin,

Paraffinic oil and Sulfer. The studies of Gashawbeza Ayalew et al., (2015) reported to the

Move to be effective pesticides against integrated white mango scale.

According to Ofgaa Djirata et al., (2016) Folimat 500SL was found to be the most effective

of the three insecticides and the best period for application of insecticide for the control of

white mango scale is from April to June when white mango scale crawlers are more abundant

in western Ethiopia. White mango scale introduced to Ethiopia recently from its origin and

related natural enemies should be conducted for the designing and implementation of classical

biological control. The population density of white mango scale was above the economic injury

25

level so that there should be the implementation of insecticides and Folmit 500SL was found

to be the most effective insecticides against white mango scale.

2.3.5. Integrated white mango scale practice

Proper and constant scouting and monitoring of pest populations is another important (IPM)

strategy towards management of white mango scale pests. Monitoring is the process of

searching, and watching regularly for the appearance of white scale pests to help in early

detection and control before causing injuries. White scale should be monitored fortnightly from

flushing stage after mango harvesting (here, check on leaves) and when fruits are 1.5-2 cm

across (here, check for both fruits and leaves) (Duressa, 2018).

It minimizes pest damage with minimal disturbance to the natural balance of the agro-

ecosystem and minimal risk to human health. It does this by decreasing the net chemical

pesticide inputs to agriculture. This eventually minimizes dependence on chemical pest control

(Goodwin, 2000).

Integrated pest management falls between conventional and organic agriculture. The

introduction of integrated pest management presents ecologically feasible, socially acceptable

and economically effective alternative to conventional agriculture by significantly lowering the

costs of chemical pesticide application as well as an alternative to organic agriculture

(Vayssières et al., 2010).Controlling white mango scale using individual management

strategies of pest management principle is impossible so that white mango scale has to be

applied that would consist of a combination of pesticides, tolerant mango variety, biological

control agents, botanical, cultural practices and chemical together is the best option (Meyerdirk,

2002).

White mango scale management strategies were often the exception rather than the norm

because of their higher labor demands and this was generally the reason why they practiced on

a small scale. In many cases, it demonstrated not to substantially affect productivity (Kumari,

et al., 2014). According to Ofgaa Djirata, et al., (2016) integrated approaches to managing

white mango scale management was effective in Ethiopia. The study was revealed that cultural

practices such as cyclic pruning and consistent scouting for white mango scale infestation and

removal of infested parts are essential management practices (Wageningen, et al., 1999).

It can be enhanced by proper canopy management practices, especially for commercial fruit

cultivation, the natural form and shape of fruit trees are to be modified through the practice of

pruning to achieve the targeted yield by scientific approach. The allowance of a plant to

26

develop naturally since unwanted portions may develop at the expense of those which are

essential. Appropriate pruning practices keep the plant in such shape and condition as to yield

fruits of desired quality.

CHAPTER 3.MATERIALS AND METHODS

3.1. Assessment of White Mango Scale

3.1.1. Description of the survey area

The survey was conducted at Wogelsa, Sebatamit and Gombat rural kebele in 2020 cropping

season located in Bahir Dar Zuria District in Amhara region, North Western Ethiopia from

September 2020 to September 2021 (Figure 3.1). The District was situated at 576 km

Northwest of Addis Ababa, the capital city of Ethiopia.

Bahir Dar Zuria District is geographically located at 11° 14' 60.00" N North latitudes and 37°

09' 60.00 East longitudes. The maximum rainfall of the study area was 430mm per year while

the minimum rainfall was 380mm per year. The maximum temperature of the study area was

27C0 while the minimum temperature was 10.7C0.

The average elevation is about 1801meters above sea level. The land scape is flat with some

small hills to the east and west (BoARD, 2020). The area consist three ecology types. The

farming practices of the study area is cultivated major crops like Finger millet, maize and tef;

and from fruit crops mango, orange, Guava and banana were the major once.

27

Figure. 3. Meteorological data Source: Bahir Dar meteorology service agency, 2021

0

5

10

15

20

25

30

35

0

50

100

150

200

250

300

350

400

450

500

Jan

Feb

Mar

Ap

ril

May

Jun

e

July

Au

g

Sep

Oct

No

v

Dec

Tem

pra

ture

(o

C)

Rai

nfa

ll (

mm

)

Months

Rainfall (mm) Maximum temprature (oC) Minimum teprature (oC)

28

Figure 3.1. Location map of the study site

3.1.2. Study design and sampling size

The perception of the growers about the insect, status of mango tree, white mango scale,

alternative host range, seedling source, grower’s management practice was carried out from

September 1, 2020 to August 15, 2021.For the survey research work, about thirty-three mango

orchards or growers in Wogelsa, Sebatamit and Gombat were selected for the survey work with

the help of (Yemane taro, 1967). The sample areas of the survey sites were selected with the

help of the District administration based on mango growing potentiality.

The focus of survey was the infestation of white mango scale as a hot spot area. The selected

mango growers had minimum of ten mango tree in their mango orchards. The total area

coverage of mango tree in hectares nine, eleven and fifteen respectively for Wogelsa, Sebatamit

and Gombat rural Kebele. Farmers participated in the growing of mango were about 256 in

Wogelsa,244 in Sebatamit and about 229 in Gombat.

29

3.1.3. Procedures of survey work

3.1.3.1. Procedures of survey of grower’s perception

The survey was started from Wogelsa rural Kebele in Bahirdar Zuria District, West Gojjam

administrative Zone. In the first step growers in Wogelsa rural kebele was interviewed with the

help of close, and open ended standard structural quatinaire. That means in the close ended

questions only from us for them whereas in the open ended respondent can give from them for

us. The growers were asked in Amharic. The interviewing of growers was carried out in the

face to face approach. The selected mango Growers for interview lived at series of spots within

intervals of 5 to 10 kilometers land distance considered their village in each household. The

survey continued to Sebatamit, and finally to Gombat. Growers gave response based on their

observation and experience for the prepared questions (Appendix Table. 1).

3.1.3.1. Procedures host plant identification

In the identification of host of white mango scale, the activity was carried out in mango

orchards. In the mango orchard that means Mango, Guava, Orange, Papaya, Banana, and

Avocado and, forest plants like eucalyptus, and Wanza farms potential areas, there was

diagnosed activity. In this work, four sample leaves per selected vascular plant cut from four

cardinal compass directions with 10Km distance interval in each farm. The collected sample

leaves in each vascular plants were collected, pressed and mounted, and taken to Bahir Dar

University College of Agriculture and Environmental sciences, Department of Plant sciences

plant protection laboratory (Appendix Figure. 2).

3.1.3.2. Procedures of infestation survey

In the assessment of prevalence, incidence, and severity, the survey was carried out with the

similar procedure of the above, ten mango leaves (3 from upper, 3 from center and 4 from

lower canopies) were plucked from every mango tree selected from about 50 central position

within each farm. Collecting of sampling continued as far as there were mango farms and

infestation of the insect pest along with mango farm. Sampling was terminated when it was

confirmed that there was achieving the number, over land distance of about 5 Km from the spot

of the last sampling. However, considering a report on quick spread of the pest to the west

(Temesgen Fita, 2014).

3.1.3.3 Procedure of mango variety selection

30

For the surveying of mango variety, varieties were characterized with the help of phenotypic

features of mango tree. That means Morphological characters were the first step that should be

done before more profound biochemical or molecular studies were carried out (Hoogendijk

and Williams, 2001). In this regard, in mango cultivars character, mango leafs were used in the

identification of the variety with the help of morphological features like precocious, dwarfness,

regular and prolific in bearing, early flowering and fruit setting, canopy architecture, growing

habit, attractive fruit color and size of leaf (Litz, 2009; Davis et al, 2012).

3.2. Field Experiment

3.2.1. Description of the experimental site

Experiment study was conducted at Zenzelima located in Bahir Dar District, Amhara Region

North Western, and Ethiopia during 2020/2021 cropping calendar in private mango orchards.

Zenzelima lied between the 11°37'8.86"N latitude and 37°27'38.04"E longitude, and the mean

altitude 1820 meters above sea level. Zenzelima situated at the out skirt of Bahir Dar city about

10km.The minimum temperature of the area is 10.7C0 while the maximum temperature was 25

C0.The maximum rainfall of the area was 380 mm while the minimum rainfall was 300mm.The

Agro-ecological zone classified as being too cool to sub-moist mid-highlands. The kebele has

this kebele consists of the three villages Sesaberet, Gedro and Michael (Figure 3.2).

Figure 3.2. Location of the experimental site

3.2.2. Insecticides and experimental design

There were four tested insecticides. These were Nimbecidence (3%) EC, Folmit (40%) EC,

Karate (5%) EC, and untreated check. These insecticides had their own features namely

31

Nimbecidence (3%) EC is a neem-oil-based botanical insecticide, and occurs naturally in neem.

This insecticides is foliarly applicable with multipurpose namely antifeedant, repellent,

ovipositional deterrent, antifeedant, insect growth regulator and sterility (Patil, 2009). The

insecticide was important for pests of Hemiptera diaspidea family. The manufacturer

recommendation of this insecticide per hectare ratio was 3 liters of Nimbecidence (3%) EC

with the volume of 300-liter water (Maha, 2009).

Folmit (40%) EC is the systematic insecticides chemical group organ phosphorus. It is suitable

for the controlling of sucking types of insects. The insecticide penetrates the tissue of the plant,

and that becomes toxic for sucking types of insect. The insecticide was recommended 2 liters

folmit (40%) EC per hectare with the volume of water 500-liter ratio (Walthall and Stark,

1997).

Karate (5%) EC was a group three emulsifiable concentrate contact. This is stomach insecticide

for the control of various insects. This insecticide is broad spectrum synthetic parathyroid

insecticide for the control of insect pests (Smiley and Yan, 2011). It was effective product, and

had the capability of controlling several crop pests in one spray with knockout properties.

Karate EC 5% was formulated with the active ingredient lambda cyhalothrin its novel granular

formulation-pours like a liquid. Karate (5%) EC was recommended with quantity of volume of

2 litters per insecticides per hectare ratio of this insecticide with the amount of water 300L

(MoA, 2016).

The variety used for chemical evaluation was Tommy mango. The variety was selected with

the help of morphological and physiological features. That means Tommy mango variety has

scatred canopy, less melting of the organic compounds. That features of mango tree make it

less susiptable. The selected mango trees were uniform in size, similar in age about four years

old (Table, 3.1). The experimental study of chemical screening was single factor experiment

so that Simple Randomized Complete Block Design (RCBD) with three replications was used

for the evaluation.

3.2.3. Procedure of the study

3.2.3.1. Procedure of the experimental study

Tommy mango tree was blocked into three blocks considering as a plot. Each of mango tree

was marked as plot. Before the spraying of the insecticides: The insect occurrence was checked

with the help of hand lense in economical threshold level, the flowering of mango takes into

consider relation to abortion so that the selected mango trees were treated before the flower

32

induction, and spray was taken place during active stage of mango flowering stage by

considering abortion effect (Williams et al., 2002).

The collection of recording data of white mango scale was carried out randomly from four

sample 20 cm twing of mango tree. The 20 cm length twing were collected from four directions

with the totality of 16 sample twing per replication and 48 sample twing from the three

replication in 12 treatments. While recording the insect data, the death and live insects was

identified using hand lenses (Gashawbeza Ayalew et al., 2014 and Ofgaa Djirata et al.,

2017).

Before the application of the insecticides, mean number of white mango scale population per

plot 4 twing which had the length of 20 cm prior to treatment application four 20 cm sample

twing plunked by measuring using pocket meters from one mango tree with the totality of 48

mango twing was plucked from each mango tree, and collected in bags as a base line data. The

collected base insect data from each mango tree was counted, and recorded in the data recording

sheet of mango tree. Then the calibration of the insecticides as well as volume of water per

hectare was calculated per hectare ratio. The amount of insecticides was measured siring and

needle. The amount of insecticide as well as water volume rated according to the leveling of

the manufacturer. The amount of insecticides was measured based on four hundred mango tree

per hectare ratio.

The amount of insecticides, and volume of water was calculated per mango as treatment. About

0.0075L of Nimbecidine EC 40% with 1.5 L,0.0075L Karate EC 3% with 0.75L water, and

0.005L Folmit EC 5% with 1.25L water. The rated insecticides of each plot was mix in the

knap sack for each of mango tree turn by turn finally spraying of the insecticides implemented

from starting from the top section of mango tree with the help of ladders.

Spraying of the first round insecticides application was implemented in December 15/2021

before 3:00 Ethiopian local time for each mango tree, while spraying the direction of the wind

was considered using personal techniques by wearing gloves. One week after the first round

spraying application, mean number of insects from post treatment was used to assess efficacy

of the suggested management option four 20cm sample mango twigs 48 twigs from each mango

tree was cut, and which was inserted into the bags paralally in their plots according to their

level. Then the second round spraying application was applied one week later from the first

round spraying application then the application of the second phase considered interval of

33

application two weeks during December 22/2020 before 3:00 Ethiopian local time using

motorized knapsack sprayer.

Spraying of the second round application of the insecticides, mean number of white mango

scale population per plot 4 twing which had the length of 20 cm prior to treatment application

the plucked 20cm mango twigs with the totality of 48 mango twigs inserted in posta and dead

and live insects collected, identified recorded and counted with the help of hand lenses.

Other mango variety in the middle of the experimental site was considered as protector of drift

problem as well as insect transportation. The untreated checks were maintained

for comparison purposes. The untreated control mango tree was wetted two times with water

to avoid moisture difference between mango trees. All the non-experimental variables were

kept in the same way for all mango tree during the experimental period.

3.2.3.2. Procedures of phenology study mango tree

Mango trees were selected in the private mango orchards. The selected mango variety were

marked.The sample scoring data were collected one time from representative farmer’s mango

orchards. In the first round, 20cm length sample mango twigs were plucked from four compass

directions in the first of the activity. These cuttings were put into posta and finally counting of

the numbers of white mango scale was with the help of handlense. The recording of the number

of white mango scale number was carried out randomly from four sample 4 mango leaves. The

counting of the insect continued in similar way in each phase of mango tree (Gashawbeza

Ayalew et al., 2014 and Ofgaa Djirata et al., 2017).

3.2.3.3. Procedures of study of variety selection

In the selection of mango variety, The selected mango trees were designed and marked.

Then in each mango tree, the scoring of insect’s severity has been determined using the scoring

techniques (Williams et al., 2009). According to the nature of the study. The scoring of white

mango scale on the leaf of mango tree in the phenological nature of mango tree, growth phase,

spacing and variety selection were determined with the help of scoring techniques from 0 to

5 scale using different ranges as follow: Free= <5% (0) of the panicle destroyed, minimal

damage = 5 to 24% (1-2%) of the panicle destroyed, Moderate = 25 to 50% (2-4%) damage,

Severe =51 to 70% (4-5%) damage and Very severe = 71 to 100% (5) damage (Williams et al.,

2009 ) rating and categorizing white mango scale in different life cycle of white mango scale

namely eggs, nymph and adult.

34

3.3. Data collection

Response of the growers (%): About white mango scale infestation level, and the status of

mango tree plantation measured in each kebele in percent form.

Awarmess level of white mango scale (%): The response of growers about their knowledge of

white mango scale counted and determined in the percent form.

Distribution (%): It was determined by calculation the number of study unit kebele that

occurred or not white mango scale, and measured in the percent form.

Incidence (%): It was determined by the number of plant infested from the total observed

plants in the percent form.

Severity (%): It was collected by scoring using scoring ranges from (1-5) in the infested plant

parts.

Insect colonies (N): This was counted and recorded of white mango scale by counting out

from the sample 20 cm length twing of mango tree.

Eggs of white mango scale (N): It was determined by counting the scale of white mango on

the leaf surface of mango tree.

Nymphs of white mango scale (N): It was counted on the leaf of mango tree with the help of

hand lense.

Adults of white mango scale (N): Adult insect of white mango scale was measured by

counting from the surface of tree.

Severity level of white mango scale (%): It was recorded by scoring with the scoring gade (1-

5) the damaging leaf surface of mango tree with the help of hand lense.

3.3. Statistical data analysis

3.3.1. Analysis of survey

3.1.1.1. Analysis of infestation of white mango scale

The percent of prevalence, incidence and severity of white mango scale were determined as

suggested by earlier researchers. The frequency of white mango scale occurrence at each

locality (mango farm) was calculated by the use of equation adopted from Kataria and Kumar

(2012). This value was used to define severity index from which severity status at each farm

was determined. Abundance at each the distribution of white mango scale refers to the total

number of district assessed farms divided by the total number of samples kebele and it is

expressed by the following formula:

Frequencies of WMS prevalence (%) =Number of WMS recorded per study site x100

35

Total number of WMS recorded from surveyed

The frequency of white mango scale incidence expresses as the percentage of the number of

total samples relation to total sample occurrence. It is obtained from the relationship between

the number of samples containing the farms and the total number of samples in the case of the

total white mango scale sampled.

Percentage of WMS incidence (%) = Number of infested mango tree plants X100

Total number of observed mango plants

The frequency of white mango scale severity was expressed as the percentage of the number

of total samples relation to total sample plant leaf scored. It is obtained from the relationship

between the number of samples containing the farms and the total number of samples in the

case of the total white mango scale sampled.

Severity (%) =Sum of total grade point (1-5infestation grade) of the infested plantx100

Total number of infested plants observed

3.3.1.2. Analysis of grower’s perception

Demography characteristics, plantation status of mango, white mango scale status and all farm

assessment agronomic data namely pruning, irrigation, mulching and others that were collected

from the sample farms survey was managed, and analyzed using Microsoft excels software

version 2010, and the Statistical Program for Social Sciences (SPSS) software version 2016,

and (STATA) considering the aforementioned suggestion. Descriptive statistics (percentage)

were used for computing data on distribution and Constance of white mango scale was carried

out.

Appropriate statistical method, T test and chi square(X2) was used for computing the

distribution, and frequency of white mango scale occurrence in sex determination and avoiding

of the pruning of mango tree recorded from sampled mango orchards of the study area

Significant differences between means were separated by Turkey’s honestly significant

difference (THSD) test at 95% confidence interval level.

3.3.1.3. Analysis of host plant

For confirmation of the white mango scale, about 10 leaves, 5 twigs and 5 fruits which present

at different heights were cut from every vascular plant found within the proximity of infested

mango trees by measuring using pocket meters. These Cutting plant leaf and twing was checked

by hand lens for the presence/absence of white mango scale. They are host or not for white

mango scale with the help of hand lenses. Mango, Guava, Orange, Papaya, Banana, Avocado

and, forest plants like eucalyptus, and Wanza farms potential areas (Appendix Figure.1).The

36

procedures, and keys of the books related to white mango scale insect pests, and other

arthropods by different authors (Hag strum, et al., 2013;Hagstrum and Subramanian, 2006;

Rees, 2004, 2007) were used for identification this insect.

Identification of white mango scale hosts plants was done using sign and symptom of white

mango scale such as white scale or nest on different vascular plants among others, using keys,

and morphological characters of the aforementioned books. Then after, sample leaves were

sorted according to the crop family and counted for each sub sample leave different.

3.3.4. Experimental data analysis

The mean number of white mango scale, and the mean severity of each white mango scale

colonies were subjected to one-way analysis of variance to compute mean severity, and mean

number of white mango scale in each factors. Moreover, the status of each pest was determined

using distribution, and frequency of occurrence of the pests as suggested by the aforementioned

scholars. Significant differences between means were separated by least significant difference

(LSD) test at 95% confidence interval level (Gomez and Gomez, 1984 and SAS Institute,

2009). Percent reduction in white mango scale population over control was worked out after

each treatment using Henderson and Tilton (1955) formula of mortality correction.

Where n=white mango scale population

T= treated, and Co=control

37

CHAPTER 4. RESULTS AND DISCUSSIONS

4.1. Survey of White Mango Scale

4.1.1. Demographic characteristics of the respondents

From the total number of participants considered for the study, the response rate obtained was

100 % .From the total respondent,72.8 % was male while 27.2 % of the growers were female.

About 17.17 % of the respondents were below 30 years while 19.9 % of them were ranging

from 30-40 years, and 12.23 % of them were from 41-50 years while 13.5 % of them were

from 51-60 years and 35.6 % of them were over 60 years old. About 34.73 % of them had

less than 5 families while 37.1% of them had from 5-10 family, and about 28.26 % of them had

greater than 10 family members. About 32.5 % of them were illiterate while 32.0 % were

in primary school, and about 19.05 % of them were secondary school, and about 16.45 % of

them were University and College level (Table 4.1).The study indicated the variability of

educational sex, education, family size as well as age of the respondent.

Table 4.1. Demographic characteristics of the respondents in Bahir Dar Zuria District from

2020/2021 cropping season

Proportions of the respondent (%)

Variable Wogelsa Sebatamit Gombat Total

Sex

Female 29.3 25.5 26.8 27.2

Male 70.7 74.5 73.2 72.8

Age categories

Below 30 31.1 11.2 9.2 17.17

31-40 29.2 19.3 11.2 19.9

41-50 13.2 13.2 10.3 12.23

51-60 10.3 10.1 20.1 13.5

Above 60 16.2 46.2 49.2 37.2

Sum

Family size

<5 44.5 30.5 29.2 34.73

5-10 35.4 34.4 41.4 37.1

>10 20.1 35.1 29.4 28.26

Education status

Illiterate 34.4 33.3 30.4 32.5

Primary school 35.1 30.3 30.4 32.0

Secondary school 13.2 16.2 27.0 19.05

University/college 17.3 20.2 12.2 16.45

38

4.1.2. Mango tree plantation status

About 13.06 % growers were increase while 62.08 % of them were decreasing, and 24.76 %

of them were no change of mango tree number from the previous. About 28.8 % of them were

two years while 45.03 % of the growers from 3-5 years, and 28.17 % they were before 6 years.

About 22.23 % of the producers had < than 15 mango tree while 34.36 % of them had ranging

from 16-20 numbers of mango tree, and 16.86 % of them possessed from 21-40 numbers of

mango tree and 15.83 % of the producers had > 41 numbers of mango trees in their orchards.

(Table, 4.2).

The study perceived that as this insect infestation pressure on mango tree. The infestation

pressure of the insect is directly connected with the introduction of white mango scale. Studies

supported that white Mango Scale was a sucking insect that poses severe threat to mango

plantations mango growing countries (Labuschagne et al., 1996; Pena et al., 1998 and Juárez-

Hernández et al., 2014).

Table 4.2. Mango growing experience and the status of mango plantation in Bahir Dar Zuria

District from 2020/2021 cropping season

4.1.3. White mango scale infestation and their perception

22.8 % growers were unfamiliar of this insect pest problem while 77.2% of the producers were

informed about white mango scale. About 63.63 % of them were increase while 15.85 % of the

respondents decrease, and 16.99 % of them were had no clue (Table, 4.3).

Proportion of the respondent (%) Variables Wogelsa Sebatamit Gombat Total

Number of mango

tree

<15 20.2 29.4 17.1 22.23

16-20 43.4 40.4 19.3 34.36

21-40 22.0 13.1 22.4 16.86

>41 14.2 12.0 21.3 15.83

Status of plantation

Increasing 9.1 9.7 20.4 13.06

Decreasing 63.5 72.7 52.3 62.83

No change 27.4 16.7 30.2 24.76

Time of decrease

<2 years 35.4 29.7 21.3 28.80

3-5 years 38.4 48.3 48.4 45.03

> 6 years 26.2 22.0 30.3 26.17

39

About the awareness of white mango scale in terms of gender, they had not significant different

(F 0.226, P> 0.05%). This might due to less attention giving for the occurrence and impacts of

white mango scale.

Table 4.3. White mango scale infestation and Perception of the respondent about the

infestation in Bahir Dar Zuria District during 2020/2021 cropping calendar

Proportion of the respondent (%)

Variable Wogelsa Sebatamit Gombat Total

Awareness

Yes

21.3

22.9

24.3

22.8

No 78.7 77.1 75.7 77.2

Infestation status

Increasing 67.2 56.3 67.4 63.63

Decreasing 15.6 18.2 13.8 15.86

No change 17.2 25.5 18.8 20.5

Gender Yes % X2 (P-value)

Female 22 43.13

Male 29 56.86 0.226(0.635)ns

4.1.4. Growers response about pruning of mango tree

From the interviewed growers, 84.7 % of mango growers did not prune their mango trees while

15.7 % of them pruned their mango trees. About 15 % the respondents was used as mulched

materials while 9% of them were used for fencing. About 4 % of them were avoided by buried

while 2 ሰ% of them avoided by burned (Table, 4.4).

Concerning to the avoiding mechanisms of pruned mango tree, there were no significant

difference among the avoiding mechanisms of pruned branches (F14.08, ns, P>.05) when

compared each other (Figure 3.3). The study indicated that canopy management depends on

the nature and growth pattern of plant number of plants per hectare and pruning techniques

(Temesgen Fita, 2014).

The results of the study revealed as mango growers lack of comprehension of the usefulness of

pruning as a cultural practice in the management of white mango scale. According to the

literature, pruning allowed air, sunlight, reducing pests, and improving fruit color (Bally,

2006). Also pruning of the tree increases output, minimizes costs of production, improves fruit

quality both size and color, eliminates insect pest and disease incidence, sustains productivity,

and extends the productive age of a fruit tree. The fruit size of Tommy Atkins and Sensation

mango cultivars for example was enhanced by pruning after fruit set (Fivaz et al., 1997).

40

Most growers were unfamiliar only with dumping technique even if they had sought to manage

white mango scale culturally. Similar studies have indicated that distributing vegetative

elements, and other plant parts as well as any material beneficial in destroying white mango

scale habitat (Williams et al., 2009).

Table 4.4. Response of producers about pruning practice of mango tree in Bahir Dar Zuria

District during 2020/2021 cropping season

Proportion of the respondent (%)

Pruning Wogelsa Sebatamit Gombat Total

No 69.9 40.2 13.3 84.7

Yes 30.7 39.5 19.9 15.3

Disposing

Response

Percent

X2 (p-value)

Burning 2 7.0

Buried 4 23.0

14.708ns

Mulching 15 50.0

Fencing 9 30.0

Ns=Non-significant difference.

Figure 3.3. The avoiding mechanism of producers after pruning the infected branch

4.1.5. Agronomic practice of mango tree

From the assessed mango farms, 37.73% was mulched while 62.27 % of the tree was not

mulched. About 47.97 % of the farm had not irrigated while 52.03 % of the farm did non-

irrigated. About 40.2 % of the farm did not use input for mango, and 59.08 % of them were

used input. About 31.93 % of them were used conventional farming practice while about 68.06

% of them were used organic farm (Table, 4.5).

The study perceived that white mango scale insect incidence had relationship with the cultural

practice of mango tree. When mango tree was practiced in conventional and cultural, the

pressure of white mango scale varied accordingly. Literatures supported that study as excessive

41

use of chemical, insecticides, and traditional farms influenced mango production and

productivity. Improper agricultural practices encourage the incidence of insect pests

(Salahuddin et al., 2015; El Llano et al., 2010).

Table 4.5. Cultural practice of mango tree in Bahir Dar Zuria District from 2020/201

Cropping season

Proportion of the respondent (%)

Variable Wogelsa Sebatamit Gombat Total

Mulching

Yes 50.1 42.6 20.5 37.73

No 49.9 57.4 79.5 62.27

Irrigation

Yes 42.8 55.6 45.5 47.97

No 57.2 44.4 54.5 52.03

Fertilization

Yes 55.7 39.5 25.4 40.2

No 44.3 60.5 74.6 59.8

Farming system

Organic 9.6 70.4 15.8 31.93

Inorganic 90.4 29.6 84.2 68.06

4.1.6. Growers mango seedling source

About 46.43 % of the growers got their mango seedling from government grafting nurseries

while 24.96 % of the respondent were used their own mango seedlings, and 28.61 % they got

their seedling from a private multiplication site. About 30.9 % of mango tree were improved

mango variety while 34.3 % the trees were indigenous mango trees, and 34.08 % of mango

trees were consolidated both local and improved (Table, 4.6). This indicated government

multiplication site is the main source of mango seedlings. White mango scale spreaded by the

transfer of infested plant material and the importation of fruit, as according various research

findings (Suit, 2006).

This study indicated that the fruit crops grown was less in terms of quality. Literatures

supported that Mango trees which grown in most parts of Ethiopia developed from seedlings,

and are inferior in terms of in productivity in terms of fruit quality. Considering this, the inferior

quality trait of mango, improved mango varieties named Kent, Keitt, Tommy Atkins and apple

were introduced from Israel in 1983 and are being commercially produced by the Upper Awash

Agro industry enterprise and distributed in to different parts of the country (Mohammed Dawd,

et al., 2012; Temesgen Fita, 2014).

42

Table 4.6. Growers mango seedling source in Bahir Dar Zuria District during

2020/2021Cropping season

4.1.7. Controlling practice of white mango scale

About 91.5% was implemented integrated white mango scale controlling practice while 93.7%

of the growers were applied cultural practice, and 34.2% of them were applied botanical insect

pest management, and 24.2% of them were used chemical insect pest management practice.

About 41.5% of the respondent were uncertain about the effectiveness of the effectiveness of

practice while 30.3% of them were not successful in their controlling practice, and 12.2% of

the growers were succeed to some extent in their controlling practice, and the rest 9.1% of the

growers were successful in their controlling techniques (Table, 4.7).

This implied as growers were not satisfied for what they have practiced for their management

option of white mango scale. The management of white mango scale was influenced by the

nature of the insect itself.

Table 4.7. Growers controlling practice of white mango scale infestation in Bahir Dar Zuria

District during 2020/2021 cropping season

Proportions of the respondent (%)

Variables Wogelsa Sebatamit Gombat Total

Management

Cultural 33.0 33.0 33.0 33.0

Botanical 16.9 17.8 20.3 18.33

Chemical 17.8 16.9 14.8 16.5

IPM 32.3 32.3 31.9 32.17

Effectiveness

Yes 19.0 19.0 19.0 19.0

Proportion of the respondent (%)

Variables Wogelsa Sebatamit Gombat Total

Seedling sources

Government nursery 48.6 49.4 41.3 46.43

Own seed/seedlings 21.5 22.8 30.6 24.96

Privet multiplication 29.9 27.8 28.1 28.61

Variety

Local 34.2 29.9 28.6 30.9

Improved 32.8 31.0 39.1 34.3

Both mango variety 33.0 39.1 32.3 34.8

43

To some

extent

12.8 23.9 19.9 18.86

Not at all 27.2 24.1 29.0 26.77

Not aware 41.0 33.0 32.1 35.37

4.2. Assessment of White Mango Scale in mango orchards

4.2.1. Incidence, prevalence and severity

The distribution of white mango scale was 100% while the occurrence of white mango scale

were 100%, and the severity of white mango scale were 80.76% (Table, 4.8).

The findings of this study indicated that white mango scale had been influenced by several

factors. Study reports indicated as White mango scale pest spread so fast, and is expected to be

present throughout the year with high incidences at flowering and fruit maturation stages. In

Ethiopia. The incidence of white mango scale was reported to vary between 40 and 100%

(Duressa, 2018). Weather is an important factor determines white mango scale distribution,

abundance and their dominance. According to Dharmendra et al., (2014) favorable weather

condition for high pest infestation ranges between 24-35°C and relative humidity 70-95% in

both mango orchards (Salem et al.,2015).

Table 4.8. Infestation status of white mango scale in Bahir Dar Zuria District during

2020/2021 Cropping calander

Proportions of the respondent (%)

Infestation Wogelsa Sebatamit Gombat Total

Prevalence 100.0 100.0 100.0 100.0

Incidence 100.0 100.0 100.0 100.0

Severity 74.5 88.1 79.7.0 80.78

4.2.2. Mango variety and white mango scale infestation

About 20.26 % of mango tree were planted with other crops while 79.73 % of mango tree were

planted without other crops. About 37.5 % of mango were planted in triangular planting

technique, while 39.9 % of mango farm were planted in rectangular planting ways, and 22.8%

of mango farm planted in square planting method (Table. 4.9). About 33% of the tree were

local while 30.5% of the variety were Tommy, and 29.7% of the variety adopted were Kent,

and 28.4 % of the variety were Apple, and 30.2%% of the mango variety were Keitt mango

variety (Appendix Table, 3).

44

The result of the study indicated that white mango scale incidence had direct relation with the

planting system, and pattern of mango tree. According to studies, the most significant element

in attaining a reasonable return by controlling the incidence of insect was the regular planting

pattern of mango trees (Verheij, 2006). This types of practice become the cause for competition

and stress for mango tree. Such kinds of agronomic practice make the crop succulent for insect

pests. According to studies, the most significant element in attaining a reasonable return by

controlling the incidence of insect was the regular planting pattern of mango trees (Verheij,

2006).

The results of the study indicated that grower is adopted all mango varieties considering their

yield quantity and quality and adaptability, but not, gave focused for tolerant level of the insect

pests.Literatures supported that improved mango cultivars named Kent, Keitt, Tommy Atkins,

and apple mango varieties were brought from Israel in 1983 and were commercially cultivated

by the Upper Awash Agro Industry Enterprise and distributed throughout the country because

of their high yield and ecological adaptability (Mohammed Dawd, et al.,2012; Temesgen Fita,

2014).Mango trees are often irregular in their cropping habit with no clear pattern across

different years and place due to the variability of mango ecological adaptation and genotypes

of mango tree.

Table 4.9. Cropping system of mango tree in Bahir Dar Zuria District from

2020/2021cropping season

Proportions of the respondents (%)

Variables Wogelsa Sebatamit Gombat Total

Cropping system

Sole crop 34.7 14.3 11.8 20.26

Intercrop 65.3 85.7 88.2 79.73

Cropping pattern

Rectangulate 52.5 39.2 20.7 37.5

Triangulate 18.4 40.4 60.8 39.9

Square 29.1 20.4 18.5 22.8

Variety

Local 33.0 33.0 33.0 33.0

Apple 28.3 32.6 30.6 30.5

Kent 30.9 28.6 29.6 29.7

Keitt 28.5 30.6 26.2 28.4

Tommy 30.1 30.4 30.1 30.2

45

4.2.3. Alternative host identification

From the assessed vascular plants farm about the occurrence of White mango scale in the

survey mango orchards, there were fruit and forest tree plants infested (Appendix Figure. 2).

From the selected vascular plants in the survey, Mangifera indica and Guava from tropical fruit

crops while lime and orange from citrus family and Eucalyptus from field forest tree plants

were infested by white mango scale (Figure, 3.4). Each of the vascular plants in the field of

crops had been identified as host plant of white mango scale (Table 4.10).

The result of the study indicated that white mango scale infested other vascular plants other

than mango tree with relation to its polyphagous feeding nature. Studies other than Ethiopia

reports supported as polyphagous species were the most prevalent insect, and they were more

become major pests when introduced to new areas because of their wide host range facilitates

their establishment (Kosztarab, 1996) leading to a shortage of natural enemies to control their

populations (Stocks, 2013).

However, Studies reported as mango was the only host of white mango scale in Ethiopia (Ofgaa

Digitera et al, 2017). According to the explanation of him abundance of mango plantation may

be one possible reason to have been the only colonized plant by white mango scale in western

Ethiopia.

The author stated described that host plant abundance is known to positively influence host

plant use, in both specialist and generalist herbivorous insects. The rate at which a dispersing

or foraging insect finds a host plant can be limited by abundance of the plant. It is obvious that

western Ethiopia is one of the most known mango producing regions in the country (Ethiopian

Ministry of Agriculture and Rural Development, 2009; Takele Honja, 2014).

Table 4.10. Alternative hosts of white mango scale in Bahir Dar Zuria District from

2020/2021cropping season

Botanical Name Common Name White Mango Scale

Psidium guajava Guava R

Key lime Lemon R

Eucalyptus globulus Blugum R

Mangifera indica Mango R

Citrus sinensis Orange R

Carica papaya Papaya Nr

Musa spp. Banana Nr

Persea Americana Mill Avocado Nr

Cordia Africana Wanza Nr

Nr = non recorded, R= recorded

46

4.3. Field Experiment

4.3.1. Severity of white mango scale on each phenology of mango tree

The presence of white mango scales populations ranging from 61 (15.1%) to 14 (4.4%) per

four leaves per tree was significant different (F 35.09=992.07, P<.05%) when compared to the

other parameters (Appendix Table. 3).

The number of eggs, nymphs and adult colonies respectively on phenological cycles of mango

was about 76.0,61.4 and 55.4 for fruit set while 67.5,40.3 and 37.4 for young shoot, and

54.3,29.2 and 37.4 for inflorcence,46.3,20.7 and 19.4 for fruit development while 44.7,15.8

and 14.5 sensenced;21.2,13.4 and 13.2 for maturity, and 16.8,9.9 and 12.2 for bud

development, and 15.0,8.4 and 5.33 for old shoot of mango tree respectively (Table. 4.11).

This explains that white mango scale infests throughout entire phenological cycle of mango

tree (Rajan, et al., 2011). This insect exploits this crop as a nutrient availability as well as a

source of protection. White mango scale infestation on various parts of mango organs such as

leaves, twigs, branches, and roots, with some currently residing inside plant domatia (Peronti,

2001; Miller and Davidson, 2005; Culik et al., 2007). This may injure or kill plants by

depleting sap, injecting toxins, transmitting viruses, or excreting honeydew, which serves as a

medium for sooty moulds (Mitra, 2016).

Table 4.11. Phenology of mango tree and the severity of white mango scale in Bahir Dar

Zuria District from 2020/2021 Cropping season

Phenology Egg Crawlers Adults

Fruit set 76.0a 61.4a 55.4a

Young shoot 67.5b 40.3b 37.4ab

Inflorescence 54.3c 29.2c 23.2ab

Fruit development 46.3d 20.7cd 19.4ab

Sensenced 44.7d 15.8cd 14.5ab

Maturity 21.2e 13.4de 13.2ab

Bud development 16.8f 9.9de 12.2ab

Old shoot 15.0f 8.4 de 5.33ab

Mean 42.7 24.8 22.56

LSD (0.05%) 3.2 9.2 47.05

Mean values in the column of the same letter have not significantly different. Mean values have

the different letter have significant different (P<0.05).

4.3.2. Severity of white mango scale in each growth of mango

White mango scales were recorded in numbers ranging from 42 (7.1) to 9 (1.5) per four leaves

per tree was significant different among the growth stage of mango tree. The infestation of

47

white mango scale was varied in each of them (F 52.83=669.137, P<0.05%) comparing to each

other (Appendix Table.4). The mean severity values of white mango scale for different growth

phase of mango tree was about 56.7, 34.82, 29.7, 21.3 and 18.5 for flowering, yield formation,

late vegetative, early vegetative and establishment stage of the fruit crop respectively (Table,

4.12).

This indicated that the infestation of white mango scale was influenced by the growth phase of

mango tree. The active physiological stage of the mango tree is directly related to the severity

of mango growth. The photo assimilation nature of the mano tree is affected insect pest.

Therefore, leads flower, and fruit set to failure. Study supported that the severity was become

less due to the mango stage being non-physiologically activity. Flowering stage of mango tree

allows for less absorption. The results of the study were supported by Abo Shanaba (2012) in

which the author stated that mature fruits are extensively infested due to immature fruits drop,

and become tiny in size. Moreover, the fruit contained insufficient juice. Finally, the entire

plant might be die (Abo Shanaba, 2012).

Table 4.12. Growth phase of mango tree and the severity of white mango scale in Bahir Dar

Zuria District from 2020/2021 cropping calander

Mango growth Mean + SEm Flowering 56.7(3.09)a Yield formation 34.9(2.74)b Late vegetative 29.7(1.54)b Early vegetative 21.3(0.14)c Establishment 18.5 (0.21)c Mean 31.95 LSD(0.05) 6.5

Mean values in the column of the same letter have not significantly different.

Mean values have the different letter have significant different (P<0.05%).

4.3.3. Seasonal fluctuation of white mango scale

The mean white mango scale infestation was different in the study months (F 17.5=313,

P<.05%) comparing to others (Appendix Table. 5). The maximum number of white mango

scale was recorded in April whereas the minimum insect numbers was recorded in August. The

mean numbers of white mango in the recorded months was described. In June 72.2, May 69.16,

February 50.1, March 48.6, December 39.9, January 38.6, April 34.7, October 26.0, September

22.9, November 22.8, July 20.1 and August 20.5 respectively (Table, 4.13).

This study, therefore, underlines decline and buildup of mango scale population is affected by

rainfall in two ways, even though other contributing factors shall be investigated further. First,

48

minimum amount of average monthly rainfall of about 50mm is required to initiate buildup of

mango scale population, whereas the optimum rainfall for the insect to reach its peak may vary

spatially and temporally, as it was found to be 110mm in April at and 140mm in May at buildup

of mango scale population coincides with mango fruit physiological maturity; both happening

at the beginning of rainy season in the study area.

Studies reported that maturation and ripening of mango fruit begin to take place during the first

months of rainy season as of March-April and continues for few months, vis-à-vis significant

infestation of mango fruits by white mango scale, in western Ethiopia. The study's findings

revealed that white mango scale infestation might be connected directly to the variability of

seasons and precipitation (Ofgaa Djirata and Emana Getu (2015).

Table 4.13. Mean fluctuation of White Mango Scale from August1/ 2020/September 1/2021

in Bahir Dar Zuria District cropping calander

Months Mean severity

June 72.76a

May 69.16b

February 50.1c

March 48.6cd

December 39.9cd

January 38.6cd

April 34.7e

October 26.0ef

September 22.9ef

November 22.8ef

July 20.1ef

August 17.5ef

Mean 38.08

LSD (0.05) 4.9

Mean values in the column of the same letter have not significantly different. Mean values have

the different letter have significant different (P<0.05).

4.3.4. Screening of tolerance mango variety

The severity of white mango scale in different mango variety in Bahir Dar Zuria District

2020/2021 in the study orchards was significantly different in mango tree (F 35.4=2528.3, P<

0.05%) when comparing to the other treatments (Appendix Table.6). The maximum severity

of white mango scale was recorded on Apple mango variety, and the minimum severity of

white mango scale was recorded on Tommy mango variety. The severity of white mango scale

for leaf, stem, fruit, inflorcence and petiole for different mango variety was about 54.4, 63.63,

84.9, 81.7, 61.1 for Apple while 42.5, 51.08, 51.08, 53.9, 58.5 and 59.9 for kitte mango variety

49

while 35.9, 50.4, 42.35, 52.8 and 42.1 for Kent mango, and 31.9, 43.2, 42.3, 64.3 and 40.2 for

local, and 31.7, 34.2, 23.7, 13.6 and 24.4 for Tommy mango variety respectively (Table 4.14).

The result of the study indicated that as Tommy mango exhibited the highest tolerance level in

this investigation, owing to its morphological, physiological, growth habit, and genetical

characteristics. On the contrary, other studies, Apple mango was one of the least infected

cultivars (Ofgaa Djirata, et al., 2016). According to Camacho and Chong's (2015)

investigation, the Tommy Atkin mango variety has the capability to withstand white mango

scale, even though in similar studies, the types mango Alfa and Espada Stahl were highly

susceptible to white mango scale compared to Tommy Atkin mango variety (Rossetto et al.,

2006).

Tommy mango variety was ended up finding to be a more tolerant variety, according to that

studies. Unlike other mango varieties, this fruit crop has a reduced melting chemical

carbohydrate content. Secondly, the morphological characteristics of this type, which is

characterized by a long and dispersed canopy architecture that is exploited for light and air

circulation. Tommy mango has dwarf, compacted, denced, interlocked self-branches structure

and growth habit (Mukherjee and Litz, 1997).

Table 4.14. The severity of white mango scale in each mango variety in Bahir Dar Zuria

District from 2020/2021 cropping season

Variety leaf Stem Fruit Inflorcence Petiole

Apple 54.4a 63.63a 84.9a 81.7a 61.1a

Keitt 42.5b 51.08b 53.9b 58.5b 59.9a

Kent 35.9bc 50.4b 42.35c 52.8bc 42.1b

Local 31.9cd 43.2bc 42.3d 64.3cd 40.2b

Tommy 31.7cd 34.2bc 23.7e 13.6e 24.4c

Mean 39.3 48.5 49.5 52.49 45.6

LSD(0.05) 7.4 9.4 5.6 10.001 4.2

Mean values in the column of the same letter have not significantly different. Mean values

have the different letter have significant different (P<0.05).

4.3.5. Mango tree spacing and the severity of white mango scale

White mango scale severity had shown significantly different in different mango spacing

(F20.64=864.62, P<0.05%) when compared to the other treatments (Appendix Table.11). The

mean maximum severity of white mango scale was recorded on the spacing of 1mx1m while

the mean minimum severity of white mango scale was recorded on 6mx6m.The severity of

white mango scale recorded on different mango tree spacing was about 73.3 for 1mx1m while

50

53.0 for 2mx2m, and 43.4 for 3mx3m while 37.1 for 4mx4m, 29.1 for 5mx5m and 28.6 for

6mx6m mango tree spacing respectively (Table 4.15).

The study indicated that non consistent spacing of mango tree between rows and trees. Spacing

of mango tree is influenced by the ecology. Spacing of 10mx10m in the dry zones and

12mx12m in wet and rich soils is recommended for the production of grafted mango tree. In

the study area, the study area is potential for mango growth in terms of soil fertility and altitude,

but planted them in the marrow spacing (Ngethe et al, 2019).

Planting systems with a high density allow for a greater number of plants per unit area. Mango

trees are normally planted 10 meters apart, with only 100 plants per hectare. The result of the

study indicated that there is no consistency in the spacing used among farmers with others

planting as narrow as 2mx2m leading to the high densities (Dessalegn et al., 2014; Neguse et

al., 2019). Mango tree spacing is influenced by climate, soil fertility and variety. According to

Ngethe et al. (2019) spacing of 10mx10m in the dry zones and 12m x12m in wet and rich soils

is recommended for the production of grafted mango tree (Dessalegn et al., 2014).

Optimum spacing ensures that plants do not compete for growth factors leading to better pest

resistance. Again, avoiding crowded fields reduces the rate at which these pests spread.

Currently, according to this study, as the population density of mango trees grows. Similar

research found that mango fruits planted in high-density planting had a progressive drop in

crop output after 14-15 years due to canopy overcrowding, implying that constant canopy

management was required (Sharma et al., 2006).

Table 4.15. The severity of white mango scale in each spacing of mango tree in Bahir Dar

Zuria District from 2020/2022 cropping season

Intra and Inter row spacing

M/square Mango/hectare Mean severity

1m*1m 1m2 10,000 73.3a 2m*2m 4m2 2,500 53.0b 3m*3m 3m2 1,100 43.4bc 4m*4m 16m2 625 37.1cd 5m*5m 25m2 400 29.1cd 6m*6m 36m2 277 28.6cd Mean 44.2 LSD (0.05) 11.6

Mean values in the column of the same letter have not significantly different. Mean values

have the different letter have significant different (P<0.05).

51

4.3.6. Effects of insecticides on white mango scale

The pre-spraying of the number of white mango scales was from 254 (93.0) to 254 (98.1) per

tree per four leaves, had significant variation (F 1.476=63.0 ns, P >. 05) comparing from other

treatments 12). This had shown uniformly distribution of white mango scale (Appendix Table

.12).

The number of white mango scale in each insecticide seventh day after the first spraying

application was ranged from 99.1(1.7) to 239.3. The number of white mango scale per four

leaves per tree was significantly different in different treatments (F 0.04=72.32, P<.0.05)

comparing others (Appendix Table .13). The mean maximum number of white mango scale

was recorded on Control treatment, on the contrary, the minimum mean number of white

mango scale was recorded on Nimbecidine EC 3% insecticides. The mean number of insects

recorded after the first round application of the insecticides were about 213.0 for local, and

183.0 for Karate EC 5% while 172.7 for Folmit EC 5%, and 148.7 for Nimbecidine EC (40%)

treatments respectively (Table 4.16).

The results of the study indicated that Synthesized Nimbecidine was able to influence the

fecundity potential of white mango scale. Similar studies supported as this insecticide can

control Hemiptera insect orders such as aphid with multiple mode of action (Kora and

Teshome, 2021).

The mean number of white mango scale revealed after second spraying application of the

insecticides was ranged from 44 (3.91) to 92.67 (12.18) per four leaves per tree in different

treatment were significantly different among treatments (F0.0=60.11.08, P<0.05) comparing

to other treatments (Appendix Table. 14). The mean number of white mango scale recorded on

different insecticides was about 253.7 control while 144.4 for Karate EC 3%, and 123.0 for

Folmit EC 5%, and 99.4 for Nimbecidence EC 40% treatments respectively (Table, 4.16).

This indicated that Nimbecidine achieved in the reduction of the number of the nymphs

produced by adults. Kraiss and Cullen, (2008) found that azadirachtin significantly increased

nymphal mortality (80.0 and 77.0% respectively).

52

Table 4.16. The number of white mango scale colonies pre and post application of

insecticides in Bahir Dar Zuria District during 2020/2021 cropping season

Insecticides Before Spraying After 1st spraying After 2nd spraying

Nimbecidine 3%EC 257.7a 148.7d 99.4d

Folmit 40% EC 253.7a 172.7c 123.0c

Karate5% SL 247.4a 183.0b 144.4b

Control(check) 254.4a 213.0a 253.7a

LSD(0.05) 12.712 53.4 3.9

Mean values in the column of the same letter have not significantly different. Mean values

have the different letter have significant different (P<0.05).

4.3.7. Effects of insecticides on white mango scales mortality

The mortality of white mango scale was significantly different among treatments seven days

after the first application (F268.65=682.287, P<0.05) when compared from other treatments

(Appendix Table. 15). The maximum percent mortality of colonies was recorded on

Nimbecidine EC 40% synthetic insecticides, on the contrary, the minimum mortality percent

of colonies were recorded on control treatments. The mean percent of mortality colonies after

the application of different insecticides was about 41.43 for Nimbecidine EC 40% while 36.6

for Folmit EC 5%, and 29.3 for Karate 5%, and about 6.2 for un treated control treatments

respectively (Table, 4.17).

This indicated that the persistent nature of the insecticide influences the insect reproduction.

Nimbecidine has the capability of influencing egg hatchability, and finally the eggs not viability

and the nymphal production was reduced significantly. This ingredient increase development

time of those surviving to adult insects and fecundity of adult’s insects.

Seven days after the second application of different insecticides, the number of colonies was

significantly different (F 630.79=16260.71, P<. 05%) comparing to the other treatments

(Appendix Table.16).

The mean number of colonies mortality after second round application of insecticides were

about 71.1on Nimbecidine 40% while 58.9 for Folmit EC 40%, and 42.3 for Karate SL 5% and

9.7 for untreated control insecticides respectively (Table, 4.17).

This implied as Nimbecidine EC 40% had the capability of persistent nature and multiple

modes of action namely anti-feed ant, volatile repellent, ovipositional deterrent, growth

regulator and sterility. Similar literatures supported as Nimbecidine insecticides have the

enabling potential with the nature of controlling by influencing egg hatchability, and finally the

53

eggs not viability, and the nymphal production was reduced significantly. Nimbecidine

achieved reduction in the number of the nymphs produced by adults (Liu et al., 2001).

The mortality rate of white mango scale using Nimbecidence 3% EC in the 1st and

2nd spraying

was 70.71 and 44.2 respectively, which is the highest compared to others. Also, Bayhan et al.,

(2006) found that Nimbecidine clearly reduced adult longevity, survival rate (zero survival),

fecundity and life table parameter of the aphid. (Liu, et al., 2001). Kraiss and Cullen, (2008)

found that azadirachtin significantly increased nymphal mortality while significantly

increasing development time of those surviving to adult of the insect.

Table 4.17. Mean mortality of white mango scale colonies in Bahir Dar Zuria District from

2020/2021

Insecticides After 1st spraying After 2nd spraying

Nimbecidence 3% EC 41.43a 71.1a

Folmit 40%EC 36.6b 58.9b

Karate 5% SL 29.3c 42.3c

Un treated 6.2d 9.7d

Mean 87.6 87.6

LSD (0.05) 3.0 11.4

Mean values in the column of the same letter have not significantly different. Mean values have

the different letter have significant different (P<0.05).

54

CHAPTER 5. CONCLUTIONS AND RECOMMENDATIONS

5.1. Conclusions

White mango scale insect pest occurred, and distributed in all locations. On the one hand the

infestation of white mango scale increased and on the other hand the plantation status of mango

tree decreased from time to time. This insect pest had several host fruit crops including forest

tree.

There were improper application of mango management practices such as pruning, removal

mechanism of infested branches, planting pattern, plantation system, and irrigation, mulching

and farming system which were aggravating factors for the prevalence and severity of this

insect pest.

White mango scale infested young shoot of mango tree. Young shoot of mango tree was

mostly infested by nymphal stage from white mango scale colonies. The insect pest mainly

influenced fruit bearing stage of mango tree. Tommy atikine mango variety is one of the

tolerant varieties among others. High mortality rate of white mango scale was recorded in

Nimbecidence 3% EC insecticide.

5.2. Recommendations

From the assessment and management of white mango scale study, the following

recommendations are forwarded.

Most of mango producers did not aware regarding to this insect pest so that it should

be interested to give more focus for awareness creation training to mango producers.

Proper agronomic practices are imperative, but, mango orchards were not practiced in

the proper way so that producers have to be practiced with the proper planting system

and planting pattern.

The insect pest influenced other vascular plants beyond mango tree so that producers

and other concerned body should give more emphasis for these newly infested crops.

Combination of proper inter and intra row spacing of mango tree with 6mx6m with

Tommy atikine variety and Nimbecidence (3%) EC insecticide can be the best

management option for the white mango scale.

In addition to assessment and management, dissemination of this study result would be

imperative. Therefore, it is necessary to extend the result of the study as technology of

white mango scale management so that concerned bodies should move it forward to the

mango sector through demonstration and scale out it.

55

REFERENCES

Abhilash, P.C. and Singh, N. 2009. Pesticide use and application. an Indian scenario. Journal

of hazardous materials,165 (1-3):1-12.

Abo-Shanab, A.S.H. 2012. Suppression of white mango scale, Aulacaspis tubercularis

(Hemiptera: Diaspididae) on mango trees in El-Beheira Governorate. Egyptian

Academic Journal of Biological Sciences 5:43-50.

Alemayehu Chala, Muluken Getahun, Samuel Alemayehu and Mekuria Tadesse. 2014.

Survey of Mango Anthracnose in Southern Ethiopia and in-Vitro Screening of Some

Essential Oils against Colletotrichum Gloeosporioides. International Journal of Fruit

Science. 14:157-173.

Al-Kazafy, H., Abd-El Rahman, T.A. and Abolmaaty, S.M. 2015. Influence of some new

insecticides on sweet potato whitefly, Bemisia tabaci and American serpentine leaf

miner, Liriomyza trifolii and their residues in cucumber fruits. International Journal,

3(10):1874-1881.

Andrew Manners. 2016. Building the resilience and on-farm biosecurity capacity of the

Australian production nursery industry.

Andrew Manners. 2016. Scale insects: A difficult problem that can be managed. Agri-science

Queensland, Department of Agriculture and Fisheries, Eco sciences Precinct,

Brisbane Queensland, Australia, 1–12. 10 October 2019.

Ayantu Tucho, Fikre Lamessa and Gezahegn Berecha. 2014. Distribution and occurrence of

mango anthracnose, Colletotrichum gloiesporioides Penz and Sacc in humid agro-

ecology of southwest Ethiopia. Plant Pathology Journal 13(4): 268-277.

Ayelech Tadesse. 2011. Market chain analysis of fruits for Goma woreda, Jimma zone,

Oromia regional state. M.Sc. Thesis, Haramaya University, Haramaya, Ethiopia.

Bakr, R.F., Badawy, R.M., Mousa, S.F., Hamooda, L.S. and Atteia, S.A. 2009. Ecological

and taxonomic studies on the scale insects that infest mango trees at Qaliobiya

Governorate. Egyptian Academic Journal of Biological Sciences. A,

Entomology, 2:69-89.

Bally, I.S.E. 2006. Mangifera indica (mango), ver. 3.1. In: Elevitch, C.R. (Ed.). Species

Profiles for Pacific Island Agro-forestry. Permanent Agriculture Resources (PAR),

Hōlualoa, and Hawai‘ mango.pdf. Retrieved 5 on September 2018.

Banerjee, G.D. and Banerjee, G.D. 2011. Economics of mango cultivation. National Bank

for Agriculture and Rural Development.

56

Bautista-Rosales, P.U., Ragazzo-Sánchez, J. A., Calderón-Santoyo, M., Cortéz-Mondaca, E.

and Servín-Villegas, R. 2013. Aulacaspis tubercularis Newstead in mango orchards

of Nayarit, Mexico, and relationship with environmental and agronomic factors.

Southwestern Entomologist. 38(2):221-230.

Beck, S.D. 1965. Resistance of plants to insects. Annual review of entomology.10 (1) :207-

232.

Belaineh Legesse, Yared Ayele and Woldeamlak Bewket. 2013. Farmers perceptions and

adaptation to climate change in Ethiopia. IEEE Potentials,32 (5):30-33.

Ben-Dov, Y. 2012. The scale insects (Hemiptera: Coccoidea) of Israel-checklist, host plants,

zoogeographical considerations and annotations on species. Israel Journal of

Entomology 41:21-48.

Camacho, E.R.and Chong, J.H. 2015. General biology and current management approaches

of soft scale pests (Hemiptera: Coccidae). Journal of integrated pest

management.6:17.

Central statistical agency (CSA). 2017: Agricultural Sample Survey 2016 / 2017: Report on

Area and Production of Major Crops, Statistical Bulletin 584; Addis Ababa, Ethiopia.

Cowles, R.S.2014. Systemic insecticide impacts on the environment and bee pollinators.

Crane, J. H. 2008. Mangifera indica. In: Janick, J., Paull, R.E. (Eds.). The Encyclopedia of

Fruit & Nuts. CABI, Wallingford. UK. 15–20.

Daneel, M.S. and Dreyer, S. 1997. Further Studies on the Establishment of Aphytis sp. and

Cybocephalus Binotatus in Mango Orchards for the Control of Mango Scale. South

African Mango Growers’ Association Yearbook, 17:144-146.

Daneel, M.S. and Dreyer, S. 1998. Biological control of the mango scale, Aulacaspis

tubercularis, in South Africa. Yearbook-South African Mango Growers' Association,

18:52-55.

Daneel, M.S. and Joubert, P.H. 2006. Biological control of the mango scale Aulacaspis

tubercularis Newstead (Coccidae: Diaspididae) by a parasitoid Aphytis chionaspis

Ren (Hymenoptera: Aphelinidae). In VIII International Mango Symposium 820 (pp.

567-574).

Dirou JF. 2014. Mango growing. NSW Centre for Tropical Horticulture, Alstonville,6.

Davis, CA. Karar, H., Arif, M.J., Ali, A., Hameed, A., Abbas, G. and Abbas, Q. 2012.

Assessment of yield losses and impact of morphological markers of various mango

57

(Mangifera indica) genotypes on mango mealy bug (Rosita Mangifera Green)

(Homoptera: Margarodidae). Pakistan Journal of Zoology, 44(6).

Deloatch, C.J. 1974. Rate of increase of populations of cabbage, green peach, and turnip

aphids at constant temperatures. Annals of the Entomological Society of

America.67(3):332- 340.

Dharmendra, S., Rajendra, S., Jitendra, S., and Hariom, K. 2014. Influence of weather

parameters on population fluctuation of scale insect, Aulacaspis tubercularis

(Newstead) in mango. Annals of Horticulture, 6(2):267-271.

Dinka, T.D., Terefe, T.H., Wendafrash, B.H. and Edosa, T.T. 2005. Distribution and

Population Dynamics of the White Mango Scale, Aulacaspis tubercularis in

Southwest Ethiopia.

Dip lock, A.T., Charuleux, J.L., Crozier-Willi, G., Kok, F.J., Rice-Evans, C., Roberfroid, M.,

Stahl, W. and Vina-Ribes, J. 1998. Functional food science and defense against

reactive oxidative species. British journal of nutrition, 80:77-112.

Dreistadt, S.H. 2007. Integrated pest management for avocados.3503. UCANR Publications.

Duressa TF. 2018. Newly Emerging Insect Pests and Diseases as a Challenge for Growth and

Development of Ethiopia.

Duressa, D., Weerasoriya, D., Bean, S.R., Tilley, M. and Tesso, T. 2018. Genetic basis of

protein digestibility in grain sorghum. Crop Science, 58(6):2183-2199.

Eagling, D. 2009. Soil borne diseases in the context of plant biosecurity. Australasian Plant

Pathology,38:334-337.

EIAR. 2018. National tropical fruits research program. Designed by EIAR ICT directoret,

link http://www.eiar.gov.et/marc/index.php/anrl-research/crop-research Evans, P.D.,

Kerkut, G.A. and Entomologic Hellenica, 19(2):124-131.

Erichsen, C. and Schoeman, A. 1992. Economic Losses Due to Insect Pests on Avocado Fruit

in the Nelspruit/Hazy view Region of South Africa during 199. South African

Avocado Growers’ Association Yearbook, University of Pretoria, Pretoria.14.

Eshetu Derso, Asfaw Zelleke, Lemma Desalegn, Zemedu Worku, Hailemichael K/ Mariam,

Getachew Tabore and Ynew Getachew (Eds.). 2012. Proceedings of the 3rd Biennale

Conference of Ethiopian Horticultural Science Society (EHSS). Volume III. 4-5

February 2011. Addis Ababa. Ethiopia. 257-267.

Ferdu Azerefegne., Mohammed Dawd., Difabachew Belay and Bezawork Mekonen. 2009.

58

Review of Entomological Research on fruit crops in Ethiopia. In: Abraham Tadesse (Ed.).

Increasing Crop Production through Improved Plant Protection- Volume II. Plant

Protection Society of Ethiopia (PPSE). PPSE and EIAR, Addis Ababa Ethiopia. 69-

92.

Food and agricultural organization (FAO). 2019. Utilization of tropical foods, fruit and

leaves. Food and nutrition paper, via delle terme dicaracalla,00100 Rome, Italy. FiBL,

Research Institute of Organic Agriculture, Switzerland,www.fbl.org. African Organic

Agriculture Training Manual a Resource Manual for Trainers Draft Version 1.0 June

2011.

Fitchett, J., Grab, S.W. and Thompson, D. I. 2016. Temperature and tree age interact to

increase mango yields in the Lowveld, South Africa. South Afr. Geogr. J. 98:105–

117.

Fivaz, J., Stassen, P.J.C. and Grove, H.G. 1997. Pruning and training strategies for Tommy

Atkins and sensation mango trees in higher density hedgerow systems. South African

Mango Growers' Association Yearbook.17:37-40.

Food and agricultural organization (FAO). 2019. Principles and methods for the risk

assessment of chemicals in food. Environmental Health Criteria, 240.

Food and Agriculture Organization of the United Nation (FAO). 2010. Technical guidelines

on tropical fruit tree management in Ethiopia, FAO.

Frank, S.D. 2012. Reduced risk insecticides to control scale insects and protect natural

enemies in the production and maintenance of urban landscape plants. Environmental

entomology, 41(2), pp.377-386.

Fowomola, M.A. 2010. Some nutrients and ant nutrients contents of mango (Mangifera

indica) seed. African Journal of Food Science, 4(8):472-476.

Free, J.B. 1993. Insect Pollination of Crops. Second edition. Academic Press. London. 684.

Gashawbeza Ayalew, Abiy Fekadu and Birhanu Sisay. 2015. Appearance and chemical

control of white mango scale (Aulacaspis tubercularis) in Central Rift Valley. Science,

Technology and Arts Research Journal. 4: 59–63.

Germain, J.F., Vayssières, J.F. and Matile-Ferrero, D.2010. Preliminary inventory of scale insects

on mango trees in Benin.

Gilbert, L. 1985. Comprehensive insect biochemistry, physiology and pharmacology.

Pergamon Press, Oxford, pp.499-503. FAO, Publishing & Multimedia service, FAO,

Rome, 2002.

59

Gomez, K.A. and Gomez, A.A. 1984. Statistical Procedures for Agricultural Research. 2nd

Edition, A Wiley Interscience Publications John Wiley and Sons, New York. 680.

Goodwin, S., M. Steiner, R. Parker, L. Tesoriero, G. Connellan, E. Keskula, B. Cowper, A.

Medhurst, and C. Rodriguez, C. 2000. Integrated Pest Management in Ornamentals:

Information Guide. Horticulture Series: Agrilink, your growing guide to better

farming.

Griesbach, J., 2003. Government of India Ministry of Agriculture. Major uses of pesticides

Registered under the Insecticides Act, 1968.

Great head, D.J. and Pope, R.D. 1977. Studies on the biology and taxonomy of some

Chilocorus spp. (Coleoptera: Coccinelidae) preying on Aulacaspis spp. (Hemiptera:

Diaspididae) in East Africa, with the description of a new species. Bulletin of

Entomological Research. 67: 259–270.

Griesbach, J. 1992. A guide to propagation and cultivation of fruit trees in Kenya.

Schriftenreihe der GTZ no. 230. Eschborn, Germany.180.

Griesbach, J. 2003. Mango growing in Kenya, World Agroforestry Centre (ICRAF), Nairobi.

Halteren, P.V. 1970. Notes on the biology of the scale insect Aulacaspis mangiferae

Newstead. (Diaspididae, Hemiptera) on mango. Ghana Jnl agric. Sci. 3: 83-85.

Hodges, A. Gyeltshen, J. 2006. Azalea lace bug, Stephanitis pyrioides (Scott) (Insect:

Hemiptera: Tingidae). EDIS, 2006 (20).

Hernández Delgado, E. 2010. El desplazamiento forzado y la oferta estatal parallel attention

de la población desplazada por la violence en Colombia.

Hobson, G. E. and Grierson, D. 1993. in Biochemistry of Fruit Ripening; Seymour, G. B.,

Ed.; Chapman and Hall: London. 405–442.

Hodges, G.and Hamon, A. 2006. Pest Alert. White mango scale Aulacaspis tubercularis

Newstead (Coccoidea: Diaspididae). Florida Department of Agriculture and

Costumer Services. Division of Plant Industry.

Hoegh-Guldberg, O., Hughes, L., McIntyre, S., Lindenmayer, D.B., Parmesan, C.,

Possingham, H.P. and Thomas, C.D. 2008. Assisted colonization and rapid climate

change.

Takele Honja, T. 2014. Review of mango value chain in Ethiopia. J Biol Agric Health.

4(25):230- 239.

60

Howard, F.W. 1989. Insecticidal control of magnolia white scale and long-tailed mealy bug

on sago-palms1. In Proc. Fla. Turf grass Mgt. 27:61-65.

Seid Hussen and Zeru Yimer .2013. Assessment of production potentials and constraints of

mango (Mangifera indica) at Bati, Oromia zone, Ethiopia. International Journal of

Sciences: Basic and Applied Research, 11(1), pp.1-9.

IARAS. 2017. Determining Sample Size; How to Calculate Survey Sample Size.

International Journal of Economics and Management System.

Ikewuchi, C.C. and Ikewuchi, J.C.2008. Chemical profile of Pleurotus tuberregium (Fr)

Sing’s sclerotic. The Pacific Journal of Science and Technology,10:28-30.

Inayatullah, C., Webster, J.A. and Fargo, W.S. 1990. Index for measuring plant resistance to

insects. Entomologist,109:146-152.

Iyer CPA and Schnell R.J. 2009. Breeding and Genetics. The Mango, 2nd Edition. Botany,

Production and Uses. CABI, Oxfordshire. UK. 67-96.

Johnson, G.I., Sharp, J.L., Mine, D.L and Oostluyse, S.A. 1997. Postharvest Technology and

Quarantine treatments. In: R.E.

Johnson, R., and M. L. Corn. 2015. Bee health: The role of pesticides. United States

Congress, Lybrary of Congress, Congressional Research Service Report 7-5700,

R43900 (http://fas.org/sgp/crs/misc/R43900.pdf). Last accessed 18 August 2015.

Joosten, F.J. 2007. Development strategy for the export-oriented horticulture in Ethiopia.

Juárez-Hernández z, P., Valde z-Carrasco, J., Valdo inos -Ponce, G., Mora-Aguilera, A.J.,

Otero- Colina, G., Téliz-Ortiz, D., Hernánde z-Castro, E., Ramírez-Ramírez, I. and

González- Hernánde z, V.A. 2014. Leaf penetration pattern of Aulacaspis tubercularis

(Hemiptera: Diaspididae) stylet in mango. Florida Entomologist. 97: 100–107.

Kabashima, J. N., and S. H. Dreistadt. 2014. Scales: integrated pest management for home

gardeners and landscape professionals. University of California, Agriculture and

Natural Resources, Statewide Integrated Management Program, Pest Notes.

Kayode, R.M.O. and Sani, A. 2008. Physicochemical and proximate composition of mango

(Mangifera indica) kernel cake fermented with mono-culture of fungal isolates

obtained from naturally decomposed mango kernel. Life Science Journal,5(4):55-63.

Khan, A.S., Ali, S., Khan, I.A. 2015. Morphological and molecular characterization and

evaluation of mango germplasm: an overview. Sci. Hortic. 194: 353–366.

61

Khatri-Chhetri, A., Aggarwal, P.K., Joshi, P.K. and Vyas, S. 2017. Farmers' prioritization of

climate-smart agriculture (CSA) technologies. Agricultural systems, 151:184-191.

Knight RJ (Jr.). 1997. Important mango cultivars and their descriptors. Homestead, Florida,

USA: Tropical Research and Education Center, University of Florida.

Kogan, M. and Ortman, E.F. 1978. Antixenosis–a new term proposed to define Painter's “no

preference” modality of resistance. Bulletin of the ESA, 24(2):175-176.

Kondo, T. and Muñoz-Velasco, J.A. 2009. Nuevos registros de Aulacaspis tubercularis

Newstead (Hemiptera: Diaspididae) in Colombia y experimentos de transferencia de

hospederos. Rev. Asiava. 84:18-20.

Kora D, Teshome. 2021. Determination of the application rate and Frequency of

Nimbecidine for the effective management of pea aphid Acrythosiphon pisum

(Homoptera: Aphididae) on field pea. J Agric Food Technol 7(3): 381-384. DOI:

https://dx.doi.org/10.17352/2455-815X.000136

Kumari, D.A., Anitha, V.and Lakshmi, B.K.M. 2014. Evaluation of insecticides for the

management of scale insect in mango (Mangifera indica). International Journal of

Plant Protection, 7(1):64-66.

Labuschagne, T.I. and Pasques, B.P. 1994. Imported parasites of the mango scale, Aulacaspis

tubercularis, and the effect of fenthion on the mango parasitoid, Aspidiotiphagus

citrinus. Yearbook-South African Mango Growers' Association. 14:75-77.

Labuschagne, T.I., Daneel, M.S. and De Beer, M. 1996. Establishment of Aphytis sp.

(Hymenoptera: Aphelinidae) and Cybocephalus binotatus Grouvelle (Coleoptera:

Nitidulidae) in mango orchards in South Africa for control of the mango scale,

Aulacaspis tubercularis Newstead (Homoptera: Diaspididae). South African Mango

Growers' Association Yearbook (South Africa).

Litz, R.E. 2003. Mango Botany, Production and uses. Tropical Research and Education

Center, University of Florida. USA. 587.

Llewellyn. 2000. The Good Bug Book, second edition. Integrated Pest.Management Pty Ltd.,

Richmond, NSW.

Louw, E.C., Labuschagne and Swart, SH. 2008. Developing a mango programme for

optimum mango yield and quality. SA Mango growers’ association Research Journal.

28:1-11.

M.O. and Nwiloh, B.I. 2008. Effects of aqueous extract of Mangifera indica L.(Mango) stem

bark on hematological parameters of normal albino rats. Pakistan Journal of

Nutrition.7(5):663-666.

62

Ma, X., Wu, H., Liu, L., Yao, Q., Wang, S., Zhan, R., Xing, S. and Zhou, Y. 2011.

Polyphenolic compounds and antioxidant properties in mango fruits. Scientia

Horticulture,129:102-107.

Maha A. Shoaib · Mahmoud F. Mahmoud. 2009 Nagla Loutfy Mohamed A. Taw WC Marek

Barta effect of botanical insecticide Nimbecidine® on food consumption and egg

hatchability of the terrestrial snail Monacha obstructa

Malumphy, C. 2014. An annotated checklist of scale insects (Hemiptera: Coccoidea) of Saint

Lucia, Lesser Antilles. Zootaxa. 3846 (1):69-86.

Mango growing in Kenya. World Agroforestry Centre. Halteren, P.V. 1970. Notes on the

biology of the scale insect Aulacaspis Mangifera Newst. (Diaspididae, Hemiptera) on

mango. Ghana Journal of Agricultural Science, 3(2):83-85.

Mani, M. and Krishnamoorthy, A. 2001. Suppression of Maconellicoccus hirsutus (Green)

on guava. Insect Environment, 6(4).

Matsuoka, T. 2000. Non-destructive techniques for quality evaluation of intact fruits and

vegetables. Food Science and Technology Research. 6:248–251.

McClure, M.S. 1985. Susceptibility of pure and hybrid stands of Pinus to attack by

Matsucoccus matsumurae in Japan (Homoptera: Coccoidea: Margarodidae).

Environmental entomology,14(4):535-538.

Meyer, G.A. and Whitlow, T.H. 1992. Effects of leaf and sap feeding insects on

photosynthetic rates of goldenrod. Oecologia, 92(4), pp.480-489.

Miller, D.R. and Davidson, J.A. 2005. Armored scale insect pests of trees and shrubs

(Hemiptera: Diaspididae). Cornell University Press.

Miller, D.R., Miller, G.L., Hodges, G.S. and Davidson, J.A. 2005. Introduced scale insects

(Hemiptera: Coccoidea) of the United States and their impact on US agriculture.

Proceedings of the entomological Society of Washington, 107(1):123-158.

Mills, N. and Daane, K.2005. Biological and cultural controls… No pesticide alternatives can

suppress crop pests. California agriculture,59(1):3-28.

Mitra, S.K. 2016. Mango production in the world – present situation and future prospect.

Acta Hortic. 1111:287–295.

Mohammed Dawd., Belay, H., Lemma, A., Konjit, F., Seyoum, H. and Teshome, B. 2012.

White mango scale: A new insect pest of mango in Western Ethiopia. In Proc.of 3rd

Biennial Conference of Ethiopian Horticulture Science Society (pp. 257-267).

63

Moharum, F.A. 2012. Description of the first and second female and male instars of white

mango scale, Aulacaspis tubercularis Newstead (Coccoidea: Diaspididae). The

Journal of Basic and Applied Zoology. 65:29-36.

Mukherjee, S.K. and Litz, R.E. 1997. The Mango: botany, production and uses. The Mango:

botany, production and uses.

Mukherjee, S.K. 1972.Origin of mango (Mangifera indica). Economic Botany, 26 (3), pp.260-

264.

Nabil, H.A., Shahein, A.A., Hammad, K.A.A. and Hassan, A.S. 2012. Ecological studies of

Aulacaspis tubercularis (Diaspididae: Hemiptera) and its natural enemies infesting

mango trees in Sharkia Governorate, Egypt. Acad. J. Biology. Sci, 5 (3):9-17.

Nabil, S. and Samman, N. 2012. Risk factors for osteoradionecrosis after head and neck

radiation: a systematic review. Oral surgery, oral medicine, oral pathology and oral

radiology, 113 (1):54-69.

Netherer, S. and Schopf, A. 2010. Potential effects of climate change on insect herbivores in

European forests—general aspects and the pine recessionary moth as specific

example. Forest Ecology and Management.259 (4):831-838.

Nwinuka, N.M., Monanu. 2088. PaDIL Species Nufarm Australia Limited ACN 004 377

780 103-105 Pipe Road Laverton North Victoria 3026, 2014. For the control of a wide

range of insect pests on fruit, vegetables, oilseeds, cotton, cereals, pasture, turf and

other situations

Northern Territory Government Department of Resources. 2010.’Field Guide to Pest,

Beneficials, Diseases and Disorders of mangoes’, viewed on the 20th of

September2016.http://dpif.nt.gov.au/_data/assets/pdf_file/0006/227832/mango_field

_guide.pdf , retrieved on 20 September 2018.

Ofgaa Djirata and Emana Getu. 2015. Infestation of Aulacaspis tubercularis (Homoptera:

Diaspididae) on Mango Fruits at Different Stages of Fruit Development, in Western

Ethiopia. Journal of Biology. Agriculture and Healthcare. 5(18): 34-38.

Ofgaa Djirata. 2017.Bionomics and Management of White Mango Scale, Aulacaspis

tubercularis Newstead (Homoptera: Diaspididae) on Mango in Western Ethiopia, and

Central and Eastern Kenya. PhD Thesis, University of Addis Abeba, Addis

Abeba.166.

Ofgaa Djirata, Emana Getu and Kahuthia-Gathu. 2017. Association of a native predator

Chilocorus sp. (Coleoptera: Coccinelidae) with a new exotic mango pest, Aulacaspis

tubercularis Newstead (Hemiptera: Diaspididae) in Ethiopia. Israel Journal of

Entomology. 47: 1–8.

64

Ofgaa Djirata, Emana Getu and Kahuthia-Gathu. 2018. Population dynamics of white mango

scale, Aulacaspis tubercularis Newstead (Hemiptera: Diaspididae) in Western

Ethiopia, African journal of agricultural research. 13 (31): 1598 – 1605.

Ofgaa Djirata, O., Getu, E. and Kahuthia-Gathu, R. 2016. Trend in mango production and

potential threat from emerging white mango scale, Aulacaspis tubercularis

(Homoptera: Diaspididae) in Central and Eastern Kenya. Journal of natural sciences

research,6:87-94.

Ofgaa Djirata, O., Getu, E. and Kahuthia-Gathu, R. 2019. A survey of geographical

distribution and host range of white mango scale, Aulacaspis tubercularis Newstead

(Hemiptera: Diaspididae) in Western Ethiopia. Journal of Entomology and

Nematology.11(5):59-65.

Olaniyan, A.O. 2004. General information about mango and citrus production in Nigeria.

Oc. 2004. 1-10.

Owens, G. 2016. Mango scale and Pink Wax scale IPM in the Burdekin.

blackearth.com.au/tag/white-mango-scale/on 20 October 2018.

Painter R. H. 1951. Insect resistance in crop plants. The Macmillan Company New York.

Panda, N. and Khush, G.A. 1995. Host plant resistance to insects. CAB international.

Parakash and Patil. 2018. Field evaluation of new insecticides against, scale insect,

Hemilecanium imbricans (Coccidae: Homoptera on mango).

Patil SB, Udikeri SS, Matti PV, Guru Prasad SG, Hirekurubar RB, Shaila HM, Vandal NB.

2009. Bio efficacy of new molecule fipronil 5% SC against sucking pest complex in

but cotton. Karnataka J. Agric. Sci. 22: 1029-1031.

Pellizzari, G. and Germain, J.F. 2010. Scales (Hemiptera, Superfamily Coccoidea).Alien

terrestrial arthropods of Europe. Bio Risk, 4 (1):475-510.

Pena, J.E., Mohyudd in, A.I. and Wysok I, M. 1998. A review of the pest management

situation in mango agro ecosystems. Phytoparasitica. 26: 129–148.

Pisa, L.W., Amaral-Rogers, V., Belzunces, L.P., Bonmatin, J.M., Downs, C.A., Goulson, D.,

Kreutzweiser, D.P., Krupke, C., Liess, M., McField, M. and Morrissey, C.A. 2015.

Effects of neonicotinoids and fipronil on non-target invertebrates. Environmental

Science and Pollution Research, 22 (1):68-102, Plant disease.95 (8):983-989.

Rajan, S., Tiwari, D., Singh, V.K., Saxena, P., Singh, S., Reddy, Y.T.N., Upreti, K.K.,

Burondkar, M.M., Bhagwan, A. and Kennedy, R. 2011. Application of extended

65

BBCH scale for phenological studies in mango (Mangifera indica L.). Journal of

Applied Horticulture,13 (2):108-114.

Raupp, M.J., Webb, R.E., Szczepaniec, A., Booth, D. and Ahern, R. 2004. Incidence,

abundance, and severity of mites on hemlocks following applications of Imidacloprid.

Journal of Arboriculture,30 (2):108-113.

Small Research Activity Report (SRA) report. 2006. Assessment of mango diseases, pest

and production problems in Pakistan, Department of primary industries and fisheries,

Queensland.

Rocha Ribeiro SM, Queiroz JH, Lopes Ribeiro Queiroz ME, de Campos FM, Pinheiro

Sant’ana HM . 2007. Antioxidant in mango (Mangifera indica L.) pulp. Plant Foods

Hum Nutr 6:13–17.

Rosals, C.A. 2005. Skin Color and pigment change during ripening and related post-harvest

management of fruit. National Inc. USA. 321-345.

Rossetto, C.J., Bortoletto, N., Walder, J.M.M., Mastrângelo, T.D.A., Carvalho, C.R.L., de

Castro, J.V., Pinto, A.D.Q. and Cortelazzo, A.L. 2006. Mango resistance to fruit flies,

resistance of the alfa cultivar.

Salahuddin, B., Ur Rahman, H., Khan, I. and Daud, M.K. 2015. Incidence and management

of coconut scale, Aspidiotus destructor Signoret (Hemiptera: Diaspididae), and its

parasitoids on mango (Mangifera sp.) Crop Protection.74:103-109.

Salem, H.A., Mahmoud and, Y.A. and Ebadah, I.M.A. 2015. Seasonal abundance, number

of generations and associated injuries of the white mango scale, Aulacaspis

tubercularis (Mangifera) (Newstead) (Homoptera: Diaspididae) attacking mango

orchards. research journal of pharmaceutical biological and chemical

sciences.6(4):1373-1379.

Salim, AS., Simons, AJ. Orwa, C., Chege, J., Owuor, B. and Mutua, A. 2002. Agroforestry

database: a tree species reference and selection guide. Version 2.0 CD-ROM

International Centre for Research in Agroforestry. Nairobi, Kenya. 123.

Samson, J.A. 1986. Tropical fruits. Second edition. Longman scientific and Technical. New

York. 216-255.

Sarwar, M., Ahmad, N., Rashid, A. and Shah, S.M.M. 2015. Valuation of gamma irradiation

for proficient production of parasitoids (Hymenoptera: Chalcidoidea and Eucoilidae)

in the management of the peach fruit-fly, Bactrocera zonata (Saunders). International

journal of pest management. 61(2):126-134.

66

Sarwar, M., Hamed, M., Rasool, B., Youssef, M. and Hussain, M. 2013. Host preference and

performance of fruit flies Bactrocera zonata (Saunders) and Bactrocera cucurbitae

(Coquillett) (Diptera: Tephritidae) for various fruits and vegetables. International

Journal of Scientific Research in Environmental Sciences, 1(8):188.

Sarwar, M., Hamed, M., Youssef, M. and Hussain, M. 2014. Surveillance on population

dynamics and fruits infestation of Tephritid fruit flies (Diptera: Tephritidae) in mango

(Mangifera indica L.) orchards of Faisalabad, Pakistan. International Journal of

Scientific Research in Environmental Sciences,2 (4):113.

Sayed, A.M.M. 2012. Influence of certain bio-agents and climatic changes on the population

density of the white mango scale insect, Aulacaspis tubercularis Newstead. Egypt. J.

Agric. Res.90 (2):607-624.

Schnell, J.S. Brown, C.T. 2006. Olano, A.W. Meerow, R.J. Campbell and D.N. Kuhn.

“Mango genetic diversity analysis and pedigree inferences for Florida cultivars using

microsatellite markers. Journal of the American Society for Horticultural Sciences,

Vol. 131, pp. 214-224,

Scholefield, P.B. 1982. Scanning electron microscope study of flowers of avocado, litchi,

macadamia and mango. Sci. Hortic. 16:263–272.

Seid Hussen and ZeruYimer. 2013. Assessment of production potentials and constraints of

mango (Mangifera indica) at Bati, Oromia Zone, Ethiopia. International Journal of

Sciences: Basic and Applied Research. 11 (1):1-9.

Selman, S. and Dawd, L.A. 2012. Using Multiple Linear Regression Models to Determine

the Effect of Some Factors on Consumption of Electricitrical Power in

Basra. Engineering and Technology Journal.30 (7).

Setegn, T., Takele, A., Gizaw, T., Nigatu, D. and Haile, D. 2015. Predictors of mortality

among adult antiretroviral therapy users in southeastern Ethiopia: retrospective cohort

study. AIDS research and treatment, 2015.

Shah, S.M.M., Ahmad, N., Sarwar, M. and Tofique, M. 2014. Rearing of Bactrocera zonata

(Diptera: Tephritidae) for parasitoids production and managing techniques for fruit

flies in mango orchards. International Journal of Tropical Insect Science,34(1):108-

113.

Sharma R.R. and Singh R. 2006. Effect of pruning intensity on light penetration and leaf

physiology in Amrapali mango trees under high-density planting, Trop. Sci. 46:16–

19.

67

Singh, D.P. 1986. Breeding for Diseases Resistance and Insect Pest. Small Research Activity.

Singh, S.P. 2017.Mango: History origin and distribution. Journal of Pharmacognosy and

Phytochemistry, 6 (6), pp.1257-1262.

Smiley, R.W., Marshall, J.M. and Yan, G.P. 2011. Effect of foliarly applied spirotetramat on

reproduction of Heterodera avenae on wheat roots.

Smith, D., Beattie, G. and Broadly, R. 1997. Citrus pests and their natural enemies: integrated

pest management in Australia. Plant resistance to arthropods: molecular and

conventional approaches. PLoS One, 6(5), p. 20018.

Souaya, E.R., El-kholy, S.A., Abd El-Rahman, A.M., Elshafie, M. and Abo-Shanab, Z.L.

2012. Evaluation and application of surfactants synthesized from asphalt

components. Egyptian Journal of Petroleum, 21(1):45-54.

Souza, M.P. de, Queiroz, M.A. de, Possídio, E.L. de, Pereira, F.A. and Melo Nunes, R.F. de.

2004. Study of flowering and alternate bearing of mango varieties in the SãoFrancisco

Valley. Acta Hortic. 645:353–358.

Soysouvanh, P. and Hong, K.J. 2016. Scale insects (Hemiptera: Coccoidea) on mango in

Laos.

Stark, J.D. and Banks, J.E. 2003. Population-level effects of pesticides and other toxicants on

arthropods. Annual review of entomology,48 (1):505-519.

Stocks, I. and Peña, J.E. 2013. Recent adventive scale insects (Hemiptera: Coccoidea) and

whiteflies (Hemiptera: Aleyrodidae) in Florida and the Caribbean Region. Potential

Invasive Pests of Agricultural Crops. CAB International, Wallingford, United

Kingdom, pp.342-362.

Stocks, I. 2014. An annotated checklist of scale insects (Hemiptera: Coccoidea) of Saint

Lucia, Lesser Antilles Zootaxa,3846 (1):069-086.

Stout, M.J. 2013. Reevaluating the conceptual framework for applied research on host‐plant

resistance. Insect Science.20 (3):263-272.

Szczepaniec, A. and Raupp, M.J. 2013. Direct and indirect effects of imidacloprid on

fecundity and abundance of Eurytetranychus buxi (Acari: Tetranychidae) on

boxwoods. Experimental and applied acarology,59 (3):307-318.

Szczepaniec, A., Creary, S.F., Laskowski, K.L., Nyrop, J.P. and Raupp, M.J. 2011.

Neonicotinoid insecticide imidacloprid causes outbreaks of spider mites on elm trees

in urban landscapes.

68

Szczepaniec, A., Raupp, M.J., Parker, R.D., Kerns, D. and Eubanks, M.D.

2013.Neonicotinoid insecticides alter induced defenses and increase susceptibility to

spider mites in distantly related crop plants. Plops on,8(5):62620.

Temesgen Fita. 2014. White mango scale, Aulacaspis tubercularis, distribution and severity

status in East and West Wollega Zones, western Ethiopia. Science, Technology and

Arts Research Journal, 3 (3):1-10. Florida Entomologist, 97:100-107.

Terefe, T.H., Tsegaye, S. and Wakuma, T. 2014. White Mango Scale Insect’s Infestations

and Its Implications in Guto Gida and Diga Districts’ of East Wellega Zone. ABC

Research Alert, 2 (2).

Tesfaye Hailu, Solomon Tsegaye, and Tadele Wakuma. 2014. White Mango Scale Insect’s

Infestations and Its Implications in Guto Gida and Diga Distrcts of East Wellega Zone,

ABC Research Alert. 2(2):1-32.

Teshome Burka. 2012. White mango Scale: A new Insect Pest of Mango in Western Ethiopia,

pp.257-267.

Tewodros Bezu, Kebede Woldetsadik and Tamado Tana. 2015. Production scenarios of

mango (Mangifera indica L.) in Harari regional state, Eastern Ethiopia. Science,

Technology and Arts Research Journal, 3(4), pp.59-63.

Tsedeke Abate. 1994. Entomological studies on fruit crops. In Herath and Lemma (eds.),

Horticultural research and Development in Ethiopia. Addis Ababa Ethiopia. 1-3 Dec

1992: 177-186.

Tsegaye Babege, Bewuketu Haile and Awalom Hailu. 2017. Survey on distribution and

significance of White Mango scale (Aulacaspis tubercularis) in Bench-Maji Zone,

Southwest Ethiopia. Journal of Horticulture and Forestry. 9(4): 26 – 32.

Urias-López, M.A., Osuna-García, J.A., Vázquez-Valdivia, V. and Pérez-Barraza, M.H.

2010. Fluctuation poblacional y distribution de la escama blanca del mango

(Aulacaspis tubercularis Newstead) en Nayarit, México.

Varshney, R.K., Jadhav, M.J. and Sharma, R.M. 2002. Scale Insects and Mealy Bugs

(Insecta: Homoptera: Coccoidea). Zoological Survey of India, Pune.49.

Vasugi, C., Dinesh, M.R., Sekar, K., Shivashankara, K.S., Padmakar, B. and Ravishankar,

K.V. 2012.Genetic diversity in unique indigenous mango accessions (Appemidi) of

the Western Ghats for certain fruit characteristics. Current Science, pp.199-207.

Verheij. J., van Lingen, A., Beishuizen, A., Christians, H.M., deJong, J.R., Girbes, A.R.,

Wisselink, W., Rauwerda, J.A., Huybregts, M.A. and Groeneveld, A.J. 2006. Cardiac

69

response is greater for colloid than saline fluid loading after cardiac or vascular

surgery. Intensive care medicine, 32(7), pp.1030-1038.

Wageningen Ur. Joubert, P.H., Daneel, M.S. and Grove, T. 1999, April. Progress towards

integrated pest management (IPM) on mangoes in South Africa. In VI International

Symposium on Mango. 509:811-818.

Walthall, W.K. and Stark, J.D. 1997. A comparison of acute mortality and population growth

rate as endpoints of toxicological effect. Ecotoxicology and Environmental

Safety,37(1):45-52.

Wauthoz, N., Balde, A., Balde, E.S., Van Damme, M. and Duez, P. 2007.

Ethnopharmacology of Mangifera indica L. bark and pharmacological studies of its

main C-glucosylxanthone, mangifera indica. International Journal of Biomedical and

Pharmaceutical Sciences, 1(2), pp.112-119.

Williams B, Jocelyn E, Hernani G, Oscar S, Ernesto O, Elda B, Terry C, Les B. 2009.

Integrated pest management and supply chain improvement for mangoes in the

Philippines and Australia. 1-139.

Wong, P.M., Lees, A.N., Louw, J., Lee, F.Y., French, N., Gain, K., Murray, C.P., Wilson, A.

and Chambers, D.C. 2008. Emphysema in young adult survivors of moderate.

70

APPENDICES

Appendix Table.1 Base line survey questionnaire

The survey study was carried out in the survey area with structural quationaire. The quatinaire included

quation in each variable. The variables included in the quation were perception, demographic

characteristics, infestation status, adopted mango variety, geographical distribution, occurrence and

severity management practice, host range and status of mango plantation, source of mango seedlings

and mango variety adopted.

Social demographical characterization format

A. Environment (locality)

1.Region------------------zone---------woreda------kebele--------village-----------

2.Location----East----------------North---------------------------Altitude-------------

Name of the farmer---Age----Sex------Martial status-----Education status------

B. Status of mango tree plantation

D. Name of Farmers___________________ State or private farm____________

1. What is your Educational level? 0=no education 1=primary 2=secondary 3=institution

4=university

2. How many mango tree in your mango orchards do you have? Age

3. What was the plantation status of mango tree? A/increase/b/decrease/c/no change

4. If the answer for Q3 is insect, what type of insect?

5. Is there any local name given to this pest?

6. If the answer is ‘Yes’ for Q5 what is the name?

7. Have you pruned mango tree? “Yes’ or No”

8. When the period of time since white mango scale has been known in the survey area? (1)

Below 5 years (2) 5 - 10 years (3) not aware

9. How did you manage white mango scale?

(1) High (2) Medium (3) Low

10. What was the extent of severity in your respective?

(1) High (2) Medium (3) low

11. Which parts of the plants attacked by the pest?

12. By which ways you identify the pest? 1. Color/sign 2. Symptom

13. What is the color/sign you used for identification?

14. What type of mango variety have you planted?

15. How the pests distribute / spread?

16. How long take to spread to your neighborhood farms (week/months)?

17. In which season the white mango scale insect pest become serious?

18. On which farm site you observed the pest infestation were serious?

71

(1) Field farm (2) Backyard (3) No difference (4) Not aware

19. Did you have observation whether the pest was affected the local varieties and exogenous ones

equally or not? (1) Yes (2) No

20. If they answer, no, please ask them the reason why?

21. Did you observe other than mango tree which is attacked by MWS? (1) Yes (2) No

22. If ‘Yes’ for Q21, ask what type of plant?

23. What was the pest prevalence level variation over time?

(1) Increasing (2) Decreasing (3) No change

24. What type of management practice you attempt to control white mango scale?

(1) Cultural (2) Pesticide (3) IPM (4) No measure

25. What are the types of mango tree did you have?

26. If Q24 cultural practices were used as one type of control measure, what type of cultural

practices used?

27. Did the management option you used was successful?

(1) Yes (2) To some extent (3) No (4) Not aware

28. What were the agronomic practice that influence white mango scale?

29. What were the management practice of white mango scale?

30. Did you get extension service for the management of white mango scale? (1) Yes (2) No

31. If the Q30 ‘No’ do you have interest to take

Appendix Table 2: Anova tables of severity in each phenology eggs

Source DF Sum of Squares Mean Square F Value Pr > F

Model 7 11341.29333 1620.18476 472.82 <.0001

Error 16 54.82667 3.42667

Corrected Total 23 11396.12000

Appendix Table 3: Anova table of crawlers in phenology of mango tree

Source DF Sum of Squares Mean Square F Value Pr > F

Model 7 6944.509583 992.072798 35.09 <.0001

Error 16 452.340000 28.271250

Corrected Total 23 7396.849583

Appendix Table 4: Anova table of adult white mango scale

Source DF Sum of Squares Mean Square F Value Pr >F

Model 16 5593.65958 799.09423 1.08 0.4189

Error 23 738.89875 17416.03958

Corrected Total 11822.38000

72

Appendix Table 4: Anova of mango growth phase and severity

Source DF Sum of Squares Mean Square F Value Pr > F

Model 4 2676.550667 669.137667 52.83 <.0001

Error 10 126.666667 12.666667

Corrected Total 14 2803.217333

Appendix Table 5: Anova table of Seasonal fluctuation of white mango scale

Source DF Sum of Squares Mean Square F Value Pr > F

Model 11 12014.20306 1092.20028 129.54 <.0001

Error 24 202.36000 8.43167

Corrected Total 35 12216.56306

Appendix Table 6: Anova table of tolerant mango variety leaf of mango tree

Source DF Sum of Squares Mean Square F Value Pr > F

Model 4 2157.415333 539.353833 14.05 <.0001

Error 25 959.418333 38.376733

Corrected Total 29 3116.833667

Appendix Table 7: Anova tables of on stem parameters

Source DF Sum of Squares Mean Square F Value Pr > F

Model 4 2836.624667 709.156167 11.48 <.0001

Error 25 1544.150000 61.766000

Corrected Total 29 4380.774667

Appendix Tables 8: Anova table of fruit of mango tree

Source DF Sum of Squares Mean Square F Value Pr > F

Model 4 12256.32533 3064.08133 121.42 <.0001

Error 25 630.88833 25.23553

Corrected Total 29 12887.21367

Appendix Table 9: Anova tables of inflorcence of mango tree

Source DF Sum of Squares Mean Square F Value Pr > F

Model 4 10113.20867 2528.30217 35.74 <.0001

Error 25 1768.53833 70.74153

Corrected Total 29 11881.74700

Appendix Table 10: Anova tables of petiole of mango tree

Source DF Sum of Squares Mean Square F Value Pr > F

Model 4 5597.520000 1399.380000 111.98 <.0001

Error 25 312.406667 12.496267

Corrected Total 29 5909.926667

Appendix Table 11: Anova table intra and inter row spacing of mango tree

Source DF Sum of Squares Mean Square F Value Pr > F

Model 5 4323.111111 864.622222 20.64 <.0001

Error 12 502.666667 41.888889

73

Corrected Total 17 4825.777778

Appendix Table 12: Anova table before spraying of the insecticides

Source DF Sum of Squares Mean Square F Value Pr > F

Model 2 126.0000000 63.0000000 1.40 0.2965

Error 9 406.2500000 45.1388889

Corrected Total 11 532.2500000

Appendix Table 13: Anova Table after 1st spraying of the insecticides

Source DF Sum of Squares Mean Square F Value Pr > F

Model 2 144.66667 72.33333 0.04 0.9597

Error 9 15772.00000 1752.44444

Corrected Total 11 15916.66667

Appendix Table 14: Anova after 2nd spraying application of the insecticides

Source DF Sum of Squares Mean Square F Value Pr > F

Model 2 22.16667 11.08333 0.00 0.9976

Error 9 41928.75000 4658.75000

Corrected Total 11 41950.91667

Appendix Table 15: Anova Table of mortality of white mango scale after 1st

Source DF Sum of Squares Mean Square F Value Pr > F

Model 3 2061.862500 687.287500 268.65 <.0001

Error 8 20.466667 2.558333

Corrected Total 11 2082.329167

Appendix Table 16: Anova Table after second application

Source DF Sum of Squares Mean Square F Value Pr > F

Model 3 6382.443333 2127.481111 58.26 <.0001

Error 8 292.113333 36.514167

Corrected Total 11 6674.556667

Appendix Figure 1. Process of host plant of white mango scale identification

74

Appendix Figure 2. Host plants of white mango scale identified

Appendix Figure 3. Mango varieties adopted in the farm of mango

A. Local mango

B. Tommy mango

C.Keitt mango

D.Apple mango E. Kent mango

75

Appendix Figure 4. Experimental site and tested chemicals

76

Appendix Figure 4: Meteorological data of the study area

Element: Monthly Rain fall

Station: Zenzelima

Year Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

2011 1.5 0.0 16.4 13.3 137.1 162.9 384.8 377.5 311.6 72.3 33.7 0.8

2012 2.1 0.0 3.5 1.0 21.3 209.4 442.2 408.1 361.6 29.8 23.2 33.9

2013 0.0 0.0 0.0 0.0 110.7 178.3 683.5 421.2 170.0 203.8 34.1 0.0

2014 2.8 2.1 38.2 49.6 177.3 112.2 339.6 387.4 223.7 104.1 3.2 0.0

2015 na na na na na na na na na na na na

2016 0.0 0.0 6.0 18.9 186.0 333.3 351.0 na 138.9 80.5 0.0 0.0

2017 0.0 17.3 1.7 39.6 94.3 53.3 837.4 334.2 193.7 101.8 0.0 na

2018 1.4 na 37.7 na na 30.1 370.4 210.7 26.6 na na na

2019 1.6 9.5 na 4.0 96.8 na 422.5 na na na 99.6 na

2020 2.3 9.9 4.3 71.3 285.3 359.8 455.2 229.1 na na na 8.6

mean 1.2 3.9 10.8 19.8 110.9 143.9 428.7 236.8 142.6 59.2 19.4 4.3

total 11.7 38.8 107.8 197.7 1108.8 1439.3 4286.6 2368.2 1426.1 592.3 193.8 43.3

1.3 4.85 13.475 24.7125 138.6 179.9125 476.2889 338.3143 203.7286 98.71667 27.68571 7.216667 1514.801

Months Rainfall (mm) Maximum temprature (oC) Minimum teprature (oC)

Jan 1.2 25.7 12.6

Feb 3.9 29.8 12.1

Mar 10.8 30.5 14.2

April 19.8 25.7 12.6

May 110.9 25.6 11.5

June 143.9 24.4 11.1

July 428.7 24.9 9.2

Aug 236.8 24.8 9.1

Sep 142.6 24.1 9

Oct 59.2 22.3 9.02

Nov 19.4 21.8 9.01

Dec 4.3 20.5 9.05

Mean 25 10.7

Total 1181.5

Appendex table 1. Mean monthly rainfall (Zenzelma station), monthly minimum and maximum tempratures (Bahir Dar station) for the years from 2011 to 2020

source : Bahir Dar meteorology service agency, 2021

0

5

10

15

20

25

30

35

0

50

100

150

200

250

300

350

400

450

500

Ja

n

Fe

b

Ma

r

Ap

ril

Ma

y

Ju

ne

Ju

ly

Au

g

Se

p

Oct

No

v

De

c

Tem

pratu

re (o

C)

Rain

fall (m

m)

Months

Rainfall (mm) Maximum temprature (oC) Minimum teprature (oC)

77

BIOGRAPHICAL SKETCH

The author of this paper was Alebel Eskezia Adam. He was born from his Mother Fenta Asaye and his

Father Eskezia Adam in Yilmana Densa District in Adet Town in Amhara Region Ethiopia in

1980.When his age reached for education, he had started to learn in Adet Town. He had learnt from

grade 1-6 in Adet Gafat Primary school, from 7-8 in Adet junior school and from 9-12 in Adet secondary

and preparatory school.

The author had got his first degree in plant science in 2005 E.C in Debre Markos University. He worked

in different Agricultural Research Centers in different plant protection disciplines in weed and insect

management research case team. From 2006 up to 2009 in Amhara Region Agricultural Research

Institute in Sirinka Agricultural Research Center in North Wollo from 2009 up to 2012 in Amhara

Region Agricultural Research Institute (ARARI) in Adet Agricultural Research Center. Currently He

has worked in Fogra Rice Research and Training Center in Ethiopian Agricultural Research Institute

(EIAR) in insect pest management research directorate.