Population Status of Hagenia abyssinica and Myrica salicifolia : A Reflection from Rungwe District, Mbeya Region, Tanzania

This study aimed at prioritizing medicinal plants used to manage HIV/AIDS opportunistic infections and assessing their wild population status. Data were collected using focus group discussions and inventories. Preference ranking and Microsoft Excel and QGIS software were used for data analysis. Up to seven species were prioritized as the most important in the disease management. It was also found that the species dominated the landscape with elevation between 1950 to 2050 masl. Moreover, the species displayed linear pattern distribution adjacent rivers. With regards to population structure, the species revealed J-shaped curves. The species density was 200/ha for Hagenia abyssinica and 28/ha for Myrica salicifolia. The dominance of species in higher altitudes as cited above indicates that they flourish well in highlands. The tendency of them to grow adjacent water sources reveals their water or moisture loving. Moreover, the J-shaped curves observed imply poor recruitment and hence unsustainable. The study recommends for urgent conservation plans especially on the sampled species. There is a need to ensure strict measures are put in place to safeguard the medicinal plant species to ensure their sustainability.

By 2010's the HIV patients were reported to constitute one billion people who partly relied on medicinal plants [11], adding more pressure on the wild population of medicinal plants [7] [8].
In Tanzania, more than 60% of population depend on traditional medicine for primary health care [12]. For HIV patients, medicinal plants are mostly used as a solution to multiple related opportunistic infections. The trend of using plant medicine is associated with their availability all year long and affordability, both of which are not the case with modern drugs [13]. This has increased the extractive activities of most medicinal plants which contribute to alteration of their population status in the wild [8].
According to [14] report, 21% of the world plants are under threat of extinction. While Africa loses about 3.4 million hectares of forests [15] [16], Tanzania is estimated to lose 0.3% hectares of her forests annually due to conversion and over-exploitation of plant resources [17]. Though data on the loss are not specific to medicinal plants, it is likely that there is a large percentage of medicinal plants which are depleted [7], something which calls for urgent suitable conservation plans to guarantee their sustainable utilization [7] [11] [18] [19].
Numerous ethnobotanical studies have been conducted across the country including [9] [13] [20] [21]. However, these studies focused on the identification of species and their use in managing various diseases. In Rungwe particularly Poroto forest reserve, most of the studies conducted focused on gathering information mostly on general plant use and the presence of medicinal plant species in the area. A good example of these studies is a study by [22] who confirmed Poroto forest to be rich in diverse plant species and a study by [23] who related Poroto reserve's thick vegetation with the plenty of rainfall in the area and the adjacent communities that rely on the forest for livelihood including medicine. A study by [24] reported on the vegetation of Poroto forest reserve and the associated powerful ancestral spirits of Lake Ngozi with a special potency of most medicinal plants collected in the reserve.
Besides the confirmed use of medicinal plants among the HIV patients in Rungwe district [25], priority medicinal plant species are not documented. Also, limited studies have assessed the population status of the medicinal plants for managing HIV/AIDS opportunistic infections. This study was carried out to assess the population status of selected priority medicinal plant species used in the managing HIV/AIDS opportunistic infections in the Poroto forest reserve. Specifically, the study documented the priority medicinal plant species used to manage HIV/AIDS opportunistic infections and determined population structure, spatial distribution pattern, and population density to reveal its sustainability. These findings may benefit conservationists in their activities, the policy makers at all levels and the community at grassroots.
where N is the number of trees per ha; n is the number of trees in plot i and a is the plot area I.

Priority medicinal plants
Results from preference ranking showed seven medicinal plant species to be of priority in managing HIV/AIDS opportunistic infections in the study area (Table 1)    were poorly represented to indicate poor recruitment of the species. The worst scenario was observed on Myrica salicifolia as the species was not represented by trees in the lowest diameters (<10 cm) (Figure 4 and Figure 5).

Population density of Hagenia abyssinica and Myrica salicifolia
The density of the two priority medicinal plant species encountered in the Poroto forest reserve was 228 stems per ha. Hagenia Abyssinica contributed the largest share as compared to Myrica salicifolia. From the overall density, the individual species densities the stem per ha, of the two medicinal plants, Hagenia abyssinica and Myrica salicifolia are presented in Table 2.

Discussions
The communities interviewed in the study area seemed to be knowledgeable on the priority medicinal plant species as they mentioned up to seven of them in dealing with HIV/AIDS opportunistic infections. The prioritized species implies that they may contain bioactive ingredients as stated in literature by [32] [33].
The literature reveals that if plants are repeatedly used for the same purpose they are likely containing active ingredients. The medicinal plant species that were prioritized in this study have also been reported as priority species in other areas, for example, Berberis holstii by [34] in Malawi. Hagenia abyssinica and Myrica salicifolia by [35] [36] in Ethiopia.
The two priority medicinal plant species revealing their distribution in higher altitudes indicate they are afro-montane habitat. The findings from this study are supported by studies conducted by [35] [37] which showed similar species growing in higher altitudes. However, the species tended to decrease as the altitudes were getting to the peak, which is probably due to poor edaphic factors and prevailing high soil erosions. Therefore, in order to implement conservation strategies of Hagenia abyssinica and Myrica salicifolia in the study area or other places, efforts should focus on among others physiological factors and identifying favourable altitude thresholds. The altitudinal range reported in this study was considered favourable due to its thicker soils and low soil erosion as compared to steeper slopes. Moreover, the tendency of species displaying linear pattern adjacent rivers may indicate that these plants require high soil moisture content and that in drier areas these species survival could be uncertain. These findings relate to those reported by [38] who associated the growth of Hagenia abyssinica with fertile and moist soils. Also, similar findings are reported in studies conducted in Ethiopia which confirm that Myrica salicifolia was found to be highly threatened by prolonged drought although other factors including anthropogenic activities contributed as well [6] [36].
The implication of J-shaped curves revealed by both species is that, the future of medicinal plants is uncertain. This is because both plants missed or had few younger plants (seedlings) to succeed the mature plants which signal for unsustainability medicinal plant species. According to [39], the proportion of plant population in the seedling (young) stage determines a predictable plant population at mature stage. A study conducted by [40] indicated that similar species (Hagenia abyssinica and Myrica salicifolia) missing representation in the lowest DBH class sizes (seedlings). Other studies have reported on Hagenia abyssinica and Myrica salicifolia being utilized for various purposes other than medicine such as house construction, furniture making and fuel wood, hence, threatening the species [6]. This implies the species have multiple uses and thus highly demanded to probably require conservation measures to ensure sustainability in future.
Generally, the density of the two species especially for the lowest DBH size class indicated that these species could be threatened. The threats might have been caused by factors such as fuel wood extraction, farming activities and animal grazing as they were observed during the survey in the forest reserve. The findings relate to what [41] stated that activities such as farm size expansion, extraction of wood for furniture and construction materials posed threats to the survival of Myrica salicifolia in Ethiopia.

Conclusions and Recommendations
The respondents in the study area were revealed to attach values to some species than others. These species are the most species people living with HIV/AIDS use or once used to manage the HIV/AIDS related infections. The population assessment performed on the two priority species (Hagenia abyssinica and Myrica salicifolia) growing in the Poroto forest reserve revealed that the species were unsustainable as the young plants were poorly represented. The study findings inform the policy makers and other stakeholders interested in medicinal plants of what is taking place in the forest reserve. Likewise, the study urges for joint efforts among policy makers, conservationists, local authorities, people at grassroots and other stake holders interested in medicinal plants to safeguard the medicinal plant species.