Non-Timber Forest Products (NTFPs) is part of a forest ecosystem that has an important role. One of NTFPs which have high economic value and is a source of livelihood of rural communities is often called wild honey or honey sialang. This study aims to: 1) Calculate the potential of the tree and the honey produced sialang 2) Knowing how to manage the honey sialang by society and the problems. Primary data was collected through interviews with respondents using the help of questioners. Data were analyzed descriptively. Potential production of honey from the beehive tree is quite large, each tree can sialang inhabited by about 30 colonies/nest, where the number has further decreased when compared to the time of the woods yet many are converted. In each tree each harvest can be produced approximately 150 kg of honey. Institutional managers honey sialang in the Sub-District of Middle Kampar Kiri is still very minimal. Honey gatherers farmers' organizations have not yet formed, there is only one indigenous group in the village of Penghidupan, whose members are people who are still there family relationship. There are 130 trees sialang and produced 19,500 kg of honey. Honey sialang management is still done traditionally.

Minas Jaya is one of the villages adjacent to Sultan Syarif Hasyim Forest Park (Tahura SSH). Tahura SSH is one of the conservation areas in Riau Province which is currently in critical condition due to forest encroachment, illegal logging, forest fires and illegal land conversion. In order to restore it requires an approach that combines conservation and community empowerment. One is the concept of Conservation Village. The initial stage in Conservation Village development needs to be a priority class map of conservation. The problems faced by partners to produce such maps require special expertise in spatial planning, mapping, and understanding of conservation village concepts. Based on the mapping identification showing that data of the conservation priority area 1, were identified it consisted of 243.92 hectares, then the conservation priority area 2 consisted of 257.87 hectares. Further, the conservation priority area 3 also identified and consisted of 504.28 hectares, moreover the conservation level 4 conservation area around 1,868.57 hectares, and conservation priorities 5 identified around 1,082.79 hectares. Conservation program directives were linked to each priority of conservation classes. It generally includes a good forest covers protection activities, enrich the land with tree crops. Furthermore, critical land rehabilitation with agroforestry patterns has the choice of species and proportion of annual crops and trees adapted to the degree of land criticality and gradient.

City forest with many stratum provides the surrounding environment is relatively more comfortable than the low stratum. In order to achieve success in achieving management objectives, the types planted in urban forest development and development programs should be selected based on the consideration that crops grow well and can cope with emerging environmental problems in the region. Identifying the suitability of existing tree species in urban forest is intended to obtain maximum plant growth and municipal forest benefits. The purpose of this study is to identify the suitability of forest conifer tree species in Pekanbaru City. Data collection is done by survey in the field by defecting the existing tree species in urban forest. The result of tree species identification is used to evaluate the suitability of tree species of forest forest. A literature study was conducted to find out the growing requirements and characteristics of tree species of urban forest in the study sites. Data analysis is conducted by considering silvicultural, management and aesthetic requirements. Based on this criteria are made that is appropriate, quite appropriate, and not appropriate. Based on the results of the study can be summarized as follows: The type of urban forest in Pekanbaru City is the protection and recreation with the form of clusters / gangs and paths; There are 15 species of trees that have appropriate criteria based on silvicultural, management and aesthetic requirements; There are 15 species of trees capable of controlling air pollution.

The existence and spread of birds are closely related to the availability of food and habitat for birds while showing the existence of an individual or group of individuals. Species of birds and how the spread of bird species is based on habitat in the buffer zone of Tahura Sultan Syarif Hasyim. The method used is to use the Point Count method while calculating existing vegetation using anveg (vegetation analysis). The composition of birds in various vegetation cover is divided into 2 namely secondary forest and agroforestry land, in secondary forests there are 292 individuals, 41 species, 25 families from 9 orders while on agroforestry land there are 213 individuals, 25 species, 16 families of 6 orders. Thus, in the buffer zone of Tahura Sultan Syarif Hasyim, there were 505 individuals, 48 ​​species, 28 families of 10 orders with diversity included in the category of "High Diversity" with a value of 3.54, in the distribution of 14 species of land species, 27 types of lower canopy, 37 types of middle canopy and 26 types of top canopy.

KHDTK has an area of ​​103 hectares, more than 70% of the KHDTK area contains palm oil. And less than 30% there is forest area in it. It is necessary to identify the potential in the area. The purpose of the study was to identify the potential and tourist attraction of KHDTK Buluh Cina, Kampar Regency, Riau Province. The measurement of potential uses the One Score-One Indicator System, namely giving a score of 1 (one), for 1 (one) indicator, with the scale used is 1-7 (which is a development of the Likert scale 1-5). The use of a scale of 1-7 is applied because it is in accordance with the character of the Indonesian people who articulate a value in great detail (Avenzora 2008). The results of the research on the Assessment of Tourism Potential and Attractiveness of the Chinese Reeds KHDTK for oil palm stretches have a value of (3.23) which is somewhat unattractive, due to difficult access to entry and the status of land conflicts. Forest area has potential and attractiveness value (3.39) which is somewhat unattractive because it is dominated by oil palm.