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Diversity and management of homestead resources: The case of Sandwip Upazila, Chittagong, Bangladesh


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Introduction

Homestead is an area adjoining a household, where a diversified combination of perennial and annual plant species are cultivated, often in association with livestock farming, and mostly maintained by household members for the sustenance of food supply and livelihood (Mekonen et al., 2015). Homesteads comprise several layers of vegetation, ranging from herbs and vegetables to shrubs and large trees, and typically include domestic and wild animal components (Castañeda-Navarrete, 2021). In addition, homesteads involve a traditional method of land use and are considered one of the socially accepted and sustainable local solutions that have been extensively implemented by communities with limited resources (Jegora et al., 2019). Also, the homestead forest is one of the significant components of rural economies in the tropical regions of the world (Foysal et al., 2013), and understanding species composition and diversity is one of the prerequisites to ensuring sustainable management of forest resources.

The homestead resources management and utilization approach are widespread in Asia, particularly in India, Sri Lanka, Nepal, and Bangladesh (Kumar et al., 2012; Rahman et al., 2017) through the carefully managed combination of annual and perennial farm crops and livestock within the courtyard of the households. The homesteads meet several social, cultural, and ecological demands, while plant species composition of homesteads varies depending on the meteorological and edaphic conditions of the location and the household’s income (Vibhuti et al., 2018). Homestead forests are significant sources of timber, fruits, fodder, fuelwood, and medicinal tree species in South-Asian countries such as Bangladesh (Baul et al., 2021), they help household members to maintain a balanced diet with additional food, fuel, and fodder (Mekonen et al., 2015).

Furthermore, over two-thirds of the total land of Bangladesh is suitable for agricultural activities and homestead areas account for more than three-quarters of all agroforestry activities (Zaman et al., 2010). Around 20 million homestead forests cover 0.27 million hectares amounting to 2% of the total land area and 10% of the natural forest area of the country (Baul et al., 2021; Kabir & Webb, 2008; Rahman et al., 2017). The diverse species of homesteads in Bangladesh fulfill approximately 70% of timber, 70% of fruit, 40% of vegetables, 90% of fuel, 48% of sawn and veneer logs, and over 90% of bamboo requirements of the country (Rahman et al., 2017; Roy et al., 2013). However, as a result of population pressure and the conversion of land for other uses, these homesteads are being overexploited and degraded, resulting in fragmentation (Baul et al., 2021). Additionally, Kabir et al. (2016) mentioned that the species composition and diversity of homestead plants in Bangladesh depend on household land area and economic conditions, the household head’s expertise, and time spent in management. Studying homestead plant species composition and diversity is necessary to align homestead management with these factors. Besides, improved systematic management of homesteads is needed to prevent exploitation and fragmentation (Baul et al., 2021), thus the homestead resources can be maintained for the betterment of health and economic benefits of the rural communities in Bangladesh.

Sandwip is Chittagong’s sole offshore island, which is frequently hit by tropical cyclones and storm surges of varied strengths, as well as abnormally high tides, and saltwater intrusion (Paul & Rahman, 2006). Households are shrinking in size and shape as a result of land erosion caused by rivers, population expansion, and industrialization. Thus, it is vital to understand the present status of homestead resource diversity and management practices of Sandwip. Here, each household’s primary livestock component was poultry, followed by goats, cattle, buffalo, and sheep (Alam & Masum, 2005). In addition, because of transportation difficulties with the mainland, people of the offshore island heavily depend on their homestead products. Although several studies were conducted in Bangladesh on homestead forests (Alam & Sarker, 2011; Alam et al., 1996; Das, 1990; Zaman et al., 2010), traditional uses of homestead agroforest (Alam et al., 1990; Millat-e-Mustafa, 1997b; Momin et al., 1990), and natural forest biodiversity (Chowdhury et al., 2018; Chowdhury et al., 2019; Alam et al., 2019; Rahman et al., 2020; Rahman et al., 2019), no study has been done on homestead forest resource management yet on Sandwip Upazila (sub-district) of Chittagong district, while there is a considerable possibility for developing homestead resources management approaches for conserving biodiversity and ensuring food and livelihood security. Following the background, this study was conducted to understand the diversity of homestead trees or vegetation species. This study also tried to assess the various aspects of the raising and management of different kinds of species in the rural homestead forest or area of the offshore island of Bangladesh. Here, the general objective is to understand the status and diversity of homestead resources along with practice and associated problems in homestead forest management in Sandwip Upazila, Chittagong. In addition, specific objectives are to understand the diversity and distribution of the tree species of the homestead area, including species composition, homestead agroforestry pattern, and problems associated with homestead resources management.

Methodology
Study area

The study was conducted at Sandwip Upazila of Chittagong district in Bangladesh (Figure 1). Sandwip Upazila is an island with an area of 762.42 square kilometers and a total population of 292,773 (BBS, 2012).

Figure 1.

Location of Sandwip Upazila, Chittagong, Bangladesh (study area).

The soil is composed of newly formed Meghna estuary floodplain alluvial soil. The maximum and minimum mean temperature is 31.6°C and 25.4°C, respectively, and the average annual rainfall of 3600 mm (Alam & Masum, 2005). Also, the main crops of this area are paddy, potato betel leaf, sugarcane, coconut, nut, palm, and different forms of vegetables.

Sampling procedure

Out of 15 unions in Sandwip Upazilla, two unions named Maitbhanga and Sarikait were selected using stratified sampling. From each union, one village was chosen following the same sampling procedure, resulting in a total of two villages: Sarikait and Maitbhanga. Here, due to restrictions on movement during COVID-19, collection of the data was limited within two unions and this study design was prepared accordingly. Also, from the reconnaissance survey, it was understood that the species pattern of the Upazila is somehow the same for the homestead area. Here, one union Sarikait is comparatively close to the sea compared to another union Maitbhanga. The size of a household’s homestead was utilized as the basis for stratification. The homestead sizes of the study area were classified into three groups: small, medium, and large. The sizes of small, medium and large homesteads were 0.05–0.14 ha, 0.15–0.20 ha, and >0.20 ha, respectively.

Data collection

A reconnaissance survey was conducted to understand the overall situation of different homestead resources of the study area before the collection of final data. The survey was carried out through a well-defined semi-structured questionnaire. Data or information about the demography of the respondent, income from the household, the status of present homestead resources, and their management of the selected sites were recorded. The data collection was done from December 2020 to February 2021.

A total of 90 households were surveyed, and 45 from each group (i.e. 20 small, 15 medium, and 10 large household groups from each village) were selected to represent the existing scenario. Here, random sampling was followed to conduct the household surveys. All field data were gathered through in-person interviews with household heads specifically from each family. After interviewing the respondents, a physical observation was done by visiting the plots and counting tree species at each homestead, attempting to relate and corroborate with the responses of respondents about the names and number of species.

Data analysis

The collected data were organized by using Microsoft Excel 2013. Before analyzing data, a double check was done to ensure the accuracy of the data. After that, both Microsoft Excel and SPSS (Statistical Package for Social Sciences) software were used to analyze the data following the objectives of this study. Here, species composition, relative density, occurrence frequency, diversity index, and distribution evenness are important attributes for determining the diversity status. The structural characteristics of a tree stand in a homestead were analyzed using various formulae in terms of relative density, the occurrence of tree species, and tree density (Alam & Sarker, 2011). Tree species diversity in the selected homesteads was calculated through the Shannon-Wiener Index of Diversity (Michael, 1990) and Index of Evenness, (E) (Magurran, 1988). Equations of indices are given below,

Occurrence of a tree species (Frequency) = Total number of farms in which the species occurTotal number of farms studies×100$${\rm{Occurrence of a tree species (Frequency) = }}{{Total{\rm{ }}number of farms in which the species occur} \over {Total{\rm{ }}number of farms studies}} \times 100$$

Relative density of a species = Total number of individuals of a species in all farmsTotal number of individuals of all species×100$${\rm{Relative density of a species = }}{{Total{\rm{ }}number of individuals of a species in all farms} \over {Total{\rm{ }}number of individuals of all species}} \times 100$$

The Shannon-Wiener Index of Diversity, H = -∑ Pi* lnPi

Where, H = Index of species diversity, Pi = No. of individuals of one species / Total no. of individuals in the samples.

Species Diversity Index, D = S/N

Where, D = Diversity index, S = Total number of species, N = Total number of individuals.

Species Richness Index, R = (S-1)/ log N

Where, R = Species richness index, S = Total no. of species, N = Total no. of individuals of all the species.

Species Evenness Index, E=H/LogS

Where, E = Species evenness index, H= Shannon-Wiener index for diversity, S = Total no. of species.

Results
Diversity and Dominance Index of fruit and timber species in homesteads

In the case of the diversity and dominance index of tree species in homesteads, it is observed that the data obtained from the Shannon-Wiener Diversity Index (3.32) showed a higher value which represents more diversity (Table 1). But the index of dominance value for the fruit and timber species of the study area was 0.06 which represents less dominancy of the tree species. The calculated value of the Species Richness Index was 14.12 which represents more richness of tree species and the total number of individuals distributed among all possible tree species.

Diversity and density analysis of the fruit and timber species in Sandwip Upazila.

Parameters Total Based on union
Maitbhanga Sarikait
No. of species (S) 57 57 57
No. of individuals (N) 9255 4833 4422
Shannon-Wiener Index of Diversity (H) 3.32 3.30 3.32
Diversity Index (D) 0.006 0.011 0.012
Index of Dominance (ID) 0.06 0.06 0.06
Species Richness Index (R) 14.12 15.20 15.36
Species Evenness Index (E) 1.89 1.88 1.89

In addition, a similar number of species (57) was found in both the Maithbhanga and Sarikait unions, while a higher number of total individuals was found in the Maitbhanga union than in Sarikait. In the case of the Shannon-Wiener Diversity Index, Diversity Index, Species Richness, and Evenness Index the associated value was higher for the Sarikait union, representing more diversity than in the Maitbhanga union.

A total of 17 vegetable species were found to be grown on a homestead several times around the year of which 3 species (Carica papaya L., Colocasia indica (Lour.) Kunth, Dioscorea alata L.) were grown around the year (Table 2). Also, three species e.g. Capsicum annuum L., Curcuma longa L., and Zingiber officinalis Roscoe were identified as spices in the homesteads of Sandwip Upazila. In addition, there were seven and four vegetables identified as summer and winter vegetable spices, respectively in the homesteads of Sandwip Upazila.

Vegetable species found in the homesteads of Sandwip Upazila.

All year Summer vegetable Winter vegetable Spices Spices
Carica papaya Trichosanthes anguina Dolichos lablab Capsicum annum
Colocasia indica Abelmoschuses culentus Vigna sinensis Curcuma longa
Dioscorea alata Basella rubra Legenaria siceraria Zingiber officinalis
- Luffa acutangula Cucurbita maxima -
- Cucumis sativus - -
- Momordica charantea - -
- M. cochinchinensis - -

Besides, three exotic timber species i.e. akashmoni (Acacia auriculiformis A. Cunn. ex Benth.), mahogany (Swietenia mahagoni (L.) Jacq), and gamar (Gmelina arborea Roxb.) were found in the study area. Akashmoni was the most abundant species (Relative Density 3.77, Table 4), while gamar was the least abundant species.

Homestead resources and diversity
Types of fruit and timber species

In terms of tree species in the homesteads, 57 tree species under 28 different families consisting of timber, fruits, fuel wood, and multi-purpose tree species were identified, while multi-purpose tree species provide different kinds of resources like timber, fruits, fuel wood, etc. (Table 3). Among all of the families, the majority (n=9) of the tree species were from the Leguminosae family, and the identified second largest (n=5) family was Rutaceae.

Families with number of Species observed in the study area.

SI. Family name No. of species (n)
1 Anacardiaceae 3
2 Annonaceae 4
3 Arecaceae 2
4 Averrhoaceae 1
5 Caricaceae 1
6 Casuarinaceae 1
7 Combretaceae 2
8 Dilleniaceae 1
9 Ebenaceae 1
10 Elaeocarpaceae 1
11 Euphorbiaceae 2
12 Leguminosae 9
13 Guttiferae 1
14 Lamiaceae 1
15 Lythraceae 1
16 Malvaceae 1
17 Meliaceae 2
18 Mimosaceae 1
19 Moraceae 3
20 Moringaceae 1
21 Musaceae 1
22 Myrtaceae 4
23 Oxalidaceae 1
24 Rhamnaceae 1
25 Rosaceae 1
26 Rubiaceae 1
27 Rutaceae 5
28 Sapindaceae 1

On the other hand, among 57 tree species, 49% were fruit species (Figure 2). Most of the homestead respondents concentrate on fruit species because of their subsistence and cash need. Next to fruit species people focus on fuel wood (18%) for their daily basis cooking purposes. The least percentage of species were observed as medicinal species (3%).

Figure 2.

Percentage distribution of fruit and timber species based on their types.

The category of large farms contained the greatest number of fruit and timber species (n=49), while the category of small farms contained the lowest number of species (n=36).

Frequency and relative density of fruit and timber species

Among the different kinds of fruit tree species, the frequency of fruit species supari (Areca catechu L.), narikel (Cocos nucifera L.), and am (Mangifera indica L.) is higher in both unions. In the Matibhanga union, the frequency of supari, narikel, and raintree (Albizia saman (Jacq.) F. Muell.) was 100%, 95.56%, and 97.78%, respectively (Table 4), while in the case of the Sarikait union, the frequency of both narikel and supari was found to be 97.78%. Besides the Maitbhanga union, the least amount of fruit species were apples (6.67%) and golabjams (8.89%), while in Sarikait, the same species were identified as the least frequency species concentrating 8.89% and 4.44% for apples and golabjam, respectively. In the case of the relative density, the highest value was observed for supari in Maitbhanga (15.64%) and Sarikait (12.5%) followed by narikel (9.21%) in Maitbhanga and 10.20% in Sarikait.

Fruit and timber species of homesteads and their uses, occurrence, and density.

Local name Scientific name Family Major uses Total Based on union
Maitbhanga (%) Sarikait (%)
F (%) RD (%) F RD F RD
Supari Areca catechu Annonaceae Fruit 98.89 14.18 100 15.64 97.78 12.57
Narikel Cocos nucifera Arecaceae Fruit, fuel wood 96.67 9.68 95.56 9.21 97.78 10.20
Raintree/ fulkoroi Albizia saman Leguminosae Timber, fuel wood 93.33 9.11 97.78 9.00 86.67 9.23
Am Mangifera indica Anacardiaceae Fruit, timber 93.33 6.85 93.33 6.52 93.33 7.21
Silkoroi/ sadakoroi Albizia procera Leguminosae Timber, fuel wood 72.22 6.14 73.33 5.94 71.11 6.35
Kala koroi/ sherish Albizia lebbeck Leguminosae Timber 62.22 4.04 51.11 3.91 73.33 4.18
Akashmoni Acacia auriculiformis Leguminosae Timber 74.44 3.77 71.11 3.41 77.78 4.16
Mahagoni Swietenia mahagoni Meliaceae Timber 84.44 3.37 84.44 3.50 84.44 3.23
Kathal Artocarpus heterophyllus Moraceae Fruit, fodder, Timber 78.89 3.12 77.78 2.67 80.00 3.62
Papaya Carica papaya Caricaceae Fruit 84.44 3.10 84.44 2.79 84.44 3.44
Kola Musa sapientum Musaceae Fruit 48.89 2.27 48.89 2.23 48.89 2.31
Peyara Psidium guajava Myrtaceae Fruit 82.22 2.19 84. .00 1.97 82.80 2.44
Tentul Tamarindus indica Leguminosae Fruit, fuel wood 84.44 2.00 82.22 1.97 86.67 2.04
Kafla - - Fuel wood, fence 74.44 1.84 77.78 1.90 71.11 1.76
Mandar Erythrina indica Leguminosae Fuel wood, fence 75.55 1.78 75.56 1.68 75.56 1.90
Gojom - - Fuel wood 66.67 1.73 62.22 1.76 71.11 1.70
Boroi Ziziphus jujuba Mill. Rhamnaceae Fruit, fuel wood, fence 75.56 1.69 77.78 2.69 73.33 0.59
Pundal - - Fuel wood 66.66 1.62 66.67 1.63 66.67 1.61
Gab Diospyros peregrina Ebenaceae Fruit, pole 62.22 1.55 53.33 1.78 71.11 1.29
Amra Spondias pinnata Anacardiaceae Fruit 52.22 1.38 53.33 1.34 51.11 1.42
Gamar Gmelina arborea Lamiaceae Timber 28.89 1.33 31.11 1.37 26.67 1.29
Jam Syzygium cumini Myrtaceae Fruit, timber 66.67 1.24 75.56 1.20 57.78 1.29
Lebu Citrus limon Rutaceae Fruit 74.44 1.21 75.56 1.43 73.33 0.97
Dumur Ficus hispida Moraceae Fruit, fuel wood 74.44 1.21 73.33 1.34 75.56 1.06
Badam Terminalia catappa Combretaceae Fruit, fuel wood 74.44 1.06 75.56 1.03 73.33 1.09
Tal Borassus flabellifer Annonaceae Fruit, pole 51.11 0.95 53.33 0.97 48.89 0.93
Simul Bombax ceiba Malvaceae Cotton, fuel wood, timber 53.33 0.95 53.33 0.95 53.33 0.95
Bhadi Lannea coromandelica Anacardiaceae Fuelwood 36.67 0.93 37.78 0.93 35.56 0.93
Khejur Phoenix dactylifera Arecaceae Fruit, fence 35.56 0.80 35.56 0.72 35.56 0.88
Kamranga Averrhoa carambola L. Oxalidaceae Fruit 42.22 0.76 46.67 0.79 37.78 0.72
Jambura Citrus maxima Rutaceae Fruit 35.56 0.68 37.78 0.62 33.33 0.75
Dewa Artocarpus lacucha Moraceae Fruit 26.67 0.61 28.89 0.46 24.44 0.77
Litchi Litchi chinensis Sapindaceae Fruit 38.89 0.57 40.00 0.54 37.78 0.61
Neem Azadirachta Indica Meliaceae Medicinal 51.11 0.53 51.11 0.56 51.11 0.50
Bandarlathi Cassia fistula Leguminosae Timber, fuel wood 15.56 0.43 17.78 0.41 13.33 0.45
Amloki Phyllanthus emblica L. Euphorbiaceae Fruit 31.11 0.42 31.11 0.43 31.11 0.41
Jamrul Syzygium samarangense Myrtaceae Fruit 33.33 0.41 35.56 0.39 31.11 0.43
Jhau Casuarina equisetifolia Casuarinaceae Fuel wood 13.33 0.38 11.11 0.29 15.56 0.47
Kodom Neolamarckia cadamba Rubiaceae Fuel wood 26.67 0.37 24.44 0.35 28.89 0.38
Belumbo Averrhoa bilimbi Averrhoaceae Fruit 32.22 0.35 33.33 0.33 31.11 0.36
Jalpai Elaeocarpus fioribundus Elaeocarpaceae Fruit 28.89 0.30 31.11 0.31 26.67 0.30
Bel Aegle marmelos Rutaceae Fruit 26.67 0.30 26.67 0.29 26.67 0.32
Arboroi Cicca acida Euphorbiaceae Fruit, fuel wood 28.89 0.30 26.67 0.29 31.11 0.32
Babla Acacia niotica. Mimosaceae Fuel wood, fence 18.89 0.30 20.00 0.31 17.78 0.29
Krishnochura Delonix regia Leguminosae Fuelwood 24.44 0.27 24.44 0.27 24.44 0.27
Dalim Punica granatum Lythraceae Fruit 21.11 0.26 22.22 0.25 20.00 0.27
Sofeda Annona squamosa L. Annonaceae Fruit 17.78 0.22 17.78 0.27 17.78 0.23
Ata Annona reticulata Annonaceae Fruit 18.89 0.22 17.78 0.21 20.00 0.23
Sajna Moringao leifera Moringaceae Fruit, fuel wood 11.11 0.18 11.11 0.21 11.11 0.16
Arjun Terminalia arjuna Combretaceae Medicinal 13.33 0.17 13.33 0.17 13.33 0.18
Kau Garcinia cowa Roxb. Guttiferae Fruit 16.67 0.16 17.78 0.17 15.56 0.16
Sissoo Dalbergia sissoo Leguminosae Timber, fodder 14.44 0.16 15.56 0.17 13.33 0.16
Chalta Dillenia indica Dilleniaceae Fruit 15.56 0.15 13.33 0.12 17.78 0.18
Kodbel Feronia limonia Rutaceae Fruit 13.33 0.13 8.89 0.10 17.78 0.16
Malta Citrus limetta Rutaceae Fruit 11.11 0.13 11.11 0.12 11.11 0.14
Apple Malus domestica Rosaceae Fruit 7.78 0.08 6.67 0.06 8.89 0.09
Golabjam Eugenia jambos L. Myrtaceae Fruit 6.67 0.08 8.89 0.08 4.44 0.07

Furthermore, among the identified 10 medicinal species in homestead, leaf, oil, and seed of neem (Azadirachta Indica A. Juss.) are used to get cures for liver and blood diseases (Table 5). Local people also use arjun (Terminalia arjuna (Roxb.) Wight & Arn.), thankuni (Centella asiatica (L.) Urban), basok (Justicia adhatoda L.), tulsi (Ocimum tenuiflorum L.), pudina (Mentha spicata L.), etc. for their daily purposes as medicinal plants.

Medicinal species found in the homesteads of Sandwip Upazila.

Name Scientific name Use
Neem Azadirachta Indica Leaf, oil, seeds relieve skin problems; liver tonic, blood purifier
Arjun Terminalia arjuna Bark as heart tonic
Thankuni Centella asiatica Whole plant as memory booster, blood purifier
Basok Justicia adhatoda Leaf as cough remover
Tulsi Ocimum tenuiflorum Leaf, flower good for heart, blood, lungs, and cough
Pudina Mentha spicata Leaf for increasing digestion, preventing cold
Sajna Moringa oleifera Fruit, leaf for controlling blood pressure, preventing stroke
Papaya Carica papaya Fruit for curing ulcers, preventing cancer
Lemon Citrus limon Fruit, leaf for reducing cholesterol, as blood purifier, and for reducing vomiting
Ginger Zingiber officinale Rhizome, leaf for reducing nausea, sickness and vomiting

Moreover, am (Mangifera indica), kathal (Artocarpus heterophyllus Lam.), koroi (Albizia saman), narikel (Cocos nucifera), mahogany (Swietenia mahagoni), and supari (Areca catechu) were found in addition to a variety of tree-vegetable associations in the study area (Table 6). In addition, eleven vegetables that can grow in direct shadow or as a creeper beside trees were found.

Types of crops with major tree species in Sandwip Upazila.

Tree species Vegetables grown under trees Creeper Vegetables Grown Using Trees as Trails
Am Aroids, amaranthus, spinach, turmeric, ginger Bitter guard, sponge gourd
Kathal Pineapple, chili, turmeric, aroids Country bean, ribbed gourd
Koroi Aroids -
Narikel Aroids, spinach, turmeric -
Mahogany Spinach, ginger Country bean, yam
Supari Turmeric, pineapple Yam, country bean
Income from homestead resources

The total annual average income of the small households was 13,457 Bangladeshi taka (BDT) and the large households’ total annual average income was 24,700 BDT (Table 7). The maximum income of the households came from selling timber, while the second highest income of different farm categories was generated from selling the fishes.

Distribution of income of homestead (BDT/ year) according to farm category.

Category of household Timber species (BDT) Fuel (BDT) Fruit (BDT) Bamboo (BDT) Fish (BDT) Total (BDT)
Small 4287 1183.66 2533.34 1149 4304 13457
Medium 5313 2179 3750 1940 4375 17557
Large 7750 3489 4500 2465 6500 24700
Average (Tk) 5783.33 2283.88 3594.45 1851.33 5059.66 55714

Here, BDT = Bangladeshi Taka

Purpose of tree plantation, choice, and value of home garden species

Among the entire respondents, the majority of the households (45.56%) addressed getting timber, fuel, and fruit as their purpose, while 42.23% of the households planted trees to get timber and fruit (Figure 3).

Figure 3.

Perception of respondents on the purpose of the plantation, choice of species, and value of species.

In the case of interest of respondents to plant new trees in their homestead, it was observed that the majority of the people prioritized fruit species (82.22%) as a top priority, while timber (77.78%), fuel (52.22%) vegetables (47.77%), medicinal plant (29.55%), spice (13.5%) were considered based on their choice.

Management practice of homestead

The majority of the site selection decisions are taken by females (34%) for planting purposes. Moreover, 27% and 39% of site selection decisions were taken by male and female participants, respectively. Also, plantation (31.11%) and fertilization (50%) were done by the male (Table 8).

List of activities for management of homesteads by people.

Activities Gender involvement (%)
Male Female Both (male & female) Both (male & children) Both (female & children) Children Others
Seedling collection 30 13.33 40 16.66 - - -
Planting 31.11 22.22 20 17.77 8.88 - -
Watering 22.22 38.88 33.33 5.55 - - -
Weeding 20 33.33 16.66 8.88 13.33 7.77 -
Fertilizing 50 11.11 13.33 15.55 10 - -
Thinning 13.33 11.11 16.66 17.77 13.33 15.55 12.23
Pruning 12.23 10 13.33 20 14.44 8.88 22.22
Harvesting 23.23 13.33 15.55 38.8 5.55 3.33 -

Most of the respondents (52%) purchased their planting materials from the market (Table 9). The common planting materials were seeds, seedlings, and vegetative propagules, while the farmers prefer seedlings mostly because of their availability and better survivability.

Source of planting materials/ seedlings.

Aspects Response (%)
Sources Market/private nursery 52%
Govt. nursery 14%
Homestead forest 22%
Neighbours, relatives, and others 12%
Types of planting materials/ Knowledge on reasons for use and non-use
Item Reason for use Reason for non-use
Seed Easy to grow, easily available Lower survival rate, more damage, prone to insect attack
Seedlings Better survival rate, less damage, costly Not readily available
Vegetative propagules Better survivability, easily available, Growth is fast Costly
Protection measures of trees in homestead
Protection measures are taken for protecting planting seedlings Yes 71.11%
No 28,89%

Moreover, 71.11% of the household took various measures such as fencing, binding with a hard stick, regular observation, etc. to protect seedlings planted in the homestead, while 28.89% of the household were reported to take no measures for protecting the planted seedling.

In the case of the fertilizer used in homesteads, 32% of the respondents said that they have used a chemical fertilizer in their homestead to improve soil fertility followed by cow dung (27%), household residue (27%), and a small amount used (14%) all the fertilizer.

Problems associated with home gardening

On the other hand, the study revealed some common problems faced by the house owners in home gardening. Damages caused by animals were the most significant obstacle for farmers while planting and growing trees (50%) (Figure 4).

Figure 4.

Problems faced by the households in homestead resources management.

Discussion

Homestead depicts the combination of different groups or species of trees, shrubs, including vegetables within the periphery of an individual house, which is fully managed by the family members (Fernandes & Nair, 1986). Homestead is one of the most important production areas of different resources in Bangladesh, which provides a significant contribution to the group of people with low economic status (Miah & Hussain, 2010). Following the aspects of the importance of homestead resources, this study covered the diversity and management of homestead resources in Sandwip Upazila, Chittagong, Bangladesh. The findings revealed that the number of plant species (excluding vegetable species) in this study area was 57 under 28 families, which indicates the homestead has a moderately high diversity and species richness, which is higher than the findings of Abedin & Quddus (1990). They were found in homesteads of Tangail district (52 spp.), Ishurdi (34 spp.), Jessore (28 spp.), Patuakhali (20 spp.), Rajshahi (28 spp.), and Rangpur (21 spp.), respectively. Besides, in a study conducted in different regions of the country, Millat-e-Mustafa (1997a) found 92 species of perennial plants.

Furthermore, in the case of diversity and density of fruit and timber species, the Shannon-Wiener Diversity Index is higher than the Index of Dominance, indicating less dominance of the tree species with greater diversity in the home garden. The computed value of the Species Richness Index also specifies a greater diversity of tree species and a more even distribution of the total number of individual trees across all tree species. This result is consistent with those of a few studies with similar objectives. This index was reported to be 3.33 by Millat-e-Mustafa (1997a) and 3.16 by Nath et al. (2015) for homesteads of varying sizes in Bangladesh. On the contrary, it was found that the tree species in this study (Evenness Index = 1.89) were more evenly distributed than the distribution. Nath et al. (2015) found homestead forests in ecologically critical areas in Bangladesh (Evenness Index = 0.84). Shannon-Wiener’s Diversity Index values range between 1.5 and 3.5 in the majority of ecological studies, and rarely exceed 4.0. The Shannon Index rises when both the diversity and uniformity of a plant community increase. Besides, a total of 17 vegetable species were found to grow on a homestead several times a year of which 3 grew round the year. The number was higher than in another study (14 spp.) conducted by Momen et al. (2006) in Sandwip Upazila.

Moreover, eleven vegetables were found under the direct shade of trees or as a creeper in association with trees. Under the trees, various shade-tolerant and/ or shade-requiring plants, such as ginger (Zingiber officinale), turmeric (Curcuma longa L.), aroids (Colocasia indica), etc. were identified growing in homesteads. Few large and medium-sized farms were growing vegetables using horticultural and forest species, which is an additional source of income for those farms. Typically, farmers did not cultivate crops beneath the canopy of trees, although some of the mentioned species required shade. Lack of adequate knowledge, provision of inputs, and technology were identified as the primary reasons for its non-practice. In addition, the insufficiency of labor to plant and care for the vegetables was also a factor for those who do not cultivate them. Similar to the findings of Zaman et al. (2010) the present study discovered that some shade-loving plants thrive beneath and close to tree canopies. Among them, Zingiber officinale, Curcuma longa, Ananas comosus (L.) Merr., Colocasia indica, Capsicum frutescens L., Amorphophallus Blume ex Decne, and Dioscorea L. were found in homestead forests.

Furthermore, among all species, fruit species comprised the highest percentage (42%). Here, supari (Areca catechu), narikel (Cocos nucifera), and am (Mangifera indica) were the most frequent fruit tree species as these trees provided economic return and fulfilled a portion of the nutritional requirement. In timber and fuel wood species, raintree (Albizia saman), mahogani (Swietenia mahagoni), and mandar (Erythrina indica L.) have the highest frequencies. On the other hand, the present study revealed that traditional fruits of low economic value, such as chalta (Dillenia indica L.), kodbel (Feronia limonia L. Swingle), and golabjam (Eugenia jambos L.) are gradually decreasing from the homestead. Exotic timber species, such as Swietenia mahagoni, and Acacia auriculiformis are increasing in terms of relative density and frequency in the homestead. On the other hand, Ahmed & Islam (1994) indicated that about 31 minor fruit species have reached a stage of near extinction from their home in Bangladesh. Malta (Citrus limetta Risso) and apple (Malus domestica Borkh.) species were found in small amounts in very few homesteads which were provided by the government under the “Ekti Bari Ekti Khamar (One House One Farm)” project.

Farmers derive benefits from homesteads in various ways as they use homestead resources as a “reserve bank” for food and income. It was discovered that the annual average income of the small households was 13457 BDT and the large households’ annual average income was 24700 BDT. The maximum income of the households comes from selling timber. The income from trees for the small farm categories was substantially lower than the income from trees for the other farm categories. Smaller farms had fewer trees and less land devoted to tree production, which contributed to a lower income from tree products. This observation conforms with Zaman et al. (2010) homesteads study. The second highest income of different farm categories came from selling fish.

Most households (82.2%) preferred largely food or fruit species for planting due to monetary incentives and family demands, and this conclusion is supported by the findings of Masum et al. (2008) and Siddiqui & Khan (1999) and in various parts of the country. Fruit trees were preferred by farmers due to their numerous applications and consumption. According to Bashar (1999), farmers prefer fruit trees in their homesteads. The study revealed that geographical location, better financial condition, availability of planting materials, commercial values, and more so the local tradition are identified as the factors affecting people’s species preference in a different region. These findings are corroborated by the research of Millat-e-Mustafa (1997a) on home gardens in four regions of Bangladesh.

The respondents were found to use cow dung, household residue, and chemical fertilizer on their land to maintain soil fertility. In tree planting and management work male participation was (52.08%) slightly higher than that of females, however, females actively took part in the development and care of home gardens. As the area of homesteads was near female working areas it was easy for them to look after it compared to men. The site selection decision for planting purposes was mostly taken by female (34%) members and less by male members (27%). Women play the most active role in maintaining homesteads. Although men performed heavier tasks at home gardens, such as planting, thinning, and fertilization in homestead management, women and children performed lighter work, such as weeding and watering.

The majority of the respondents (60%) had given an emphasized economic value. Here, 23.33% of the respondents mentioned combined economic and ecological value and only 16.67% of the respondents were aware of the economic, ecological, and medicinal value of what home garden should be conserved. As a strategy for maintaining ecological balance and a source of medicinal plants, the majority of the respondents assessed the home garden as “least significant“. Consequently, it appears that there is still a shortage of understanding in these two areas since Roy et al. (2013) obtained similar findings.

Due to the lack of better management techniques and high-quality varieties, the traditional maintenance system of homestead gardens in the study area was characterized by a low level of cultural practices. Typically, farmers rely on plants that grow naturally inside their homestead’s perimeter. In addition, a review of the present management regime revealed that cultivators lack scientific knowledge. The vast majority of household owners still adhere to traditional homestead management approaches, while just a few have adopted modern practices. Agriculturalists, ecologists, biologists, and economists must communicate and interact across disciplines to protect homestead resources, identify and implement appropriate evaluation methodologies for sustainable management, and increase profits from the homestead. A greater understanding of agro-biodiversity as natural capital for delivering ecosystem goods and services is required. This knowledge will assist in increasing agricultural output and encouraging forestry (Swift et al., 2004; Wood & Lenné, 2005) in the least forested regions by building human-managed farm forestry.

Conclusion

In terms of plant management and utilization, Bangladesh homestead forestry practices are following conventional methods and need improvement. Findings reveal that homesteads provide tangible benefits, such as fruit, fuel wood, and food materials with some income. There was enough unused land in the homesteads, which were relatively safe from flood and other threats. The land can be used for tree-growing purposes with desirable species. Producing various nutritious foods around the house may be a sensible way to provide adequate food to the household members. Thus, selective plantation of fruit species around the home garden can greatly influence the promotion of proper nutrition. It is evident from the study that farmers possess extensive indigenous knowledge related to several aspects of homestead forestry management. Farmers are mostly concerned about improving the growth of fruit trees in their home gardens. There is still immense scope to improve technologies for species selection, clonal propagation, species interaction, soil management, etc. To achieve a stable ecological balance and sustainable productivity of the homesteads, the proper initiative should be reintroduced along with the rare indigenous fruit trees and careful management of homesteads.

Recommendations

The following recommendations may be made to improve the status of homestead biodiversity:

Proper training and motivation of both male and female members of the family for better management of homestead forestry.

Distribute seedlings that have the potential to grow in homestead conditions.

Promoting awareness on the need for community forestry and planting of more indigenous tree species on homestead land.

Detail analysis of the tree crop interaction is needed for the selection of appropriate species.

Combined application of indigenous and scientific knowledge.

Identifying and introducing shade-tolerant crops and vegetables for growing under trees.

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