 |
|
ENVIS
Forestry Bulletin |
Vol.8,No.2; YEAR-2008 |
ESTIMATION OF GROWING STOCK IN TREES OUTSIDE FOREST OF THE COUNTRY
Rajesh Kumar and Prakash Lakhchaura
Forest Survey of India, Dehradun - 248 195
Introduction
T
he trees outside forests (TOF) play a significant role in livelihood
of rural and urban people of the country both economically and
ecologically. TOF act as important source for timber and fuel wood, contributes in carbon sequestration and conservation of biodiversity, provides habitat for wildlife, microclimate stabilization, etc. TOF exist in the form of small woodlots and block plantations, trees along linear features such as roads, canals, bunds, etc. and scattered trees on farmlands, homesteads, community lands and urban areas.
TOF have been defined differently by different countries and international agencies. In India, TOF is defined as all those trees, which have attained 10 cm or more diameter at breast height, available on lands, which is not notified as forests. However, FAO defines TOF as trees available on lands which is not defined as ‘forests’ or ‘other wooded land’.
Since there exists a large amount of wood resources outside the conventional forests, accurate information about tree resources is a pre-requisite for their proper management. FSI is assessing TOF of the country since 1991. Initially, the assessment was confined at districts and state level. However, since 2001, the methodology of TOF assessment was modified to generate national level estimates of growing stock in every two years.
The present paper, discusses the modified methodologies which FSI is currently using and results of TOF inventory conducted during second and third cycle i.e. 2002-06.
Methodology
For the assessment of growing stock of TOF, the country has been divided into 14 physiographic zones. All the districts of the country fall in 14 physiographic zone either completely or partially. The fourteen physiographic zones are Western Himalaya, Eastern Himalaya, North East, Northern Plains, Eastern Plains, Western Plains, Central Highlands, North Deccan, South Deccan, Western Ghats, Eastern Ghats, West Coast and East Coast.
A sample of 10 per cent districts (or 60 districts in the country) distributed over all the physiographic zones are randomly selected for detailed inventory of TOF to estimate the growing stock at zonal and national level during a cycle of two years. These estimates are further improved continuously in the subsequent cycles as the number of districts inventoried keeps on increasing with completion of each cycle. The random selection is without replacement; hence each time new districts are selected.
Separate methodology is followed for assessment of rural and urban TOF. For rural TOF, a methodology based on high resolution satellite is used for identification and stratification of TOF resources in districts. The urban TOF is assessed using Urban Frame Survey (UFS) blocks as sampling unit prepared by National Sample Survey Organization (NSSO). The methodology of assessment for rural and urban is described as follows:
Trees Outside Forests (Rural) LISS-IV Mx multi-spectral data of IRS P6 are acquired from National Remote Sensing Agency, Hyderabad for the selected districts. Thereafter, the LISS-IV image is geometrically rectified with the help of Survey of India toposheets on 1:50,000 scale. Since mapping of TOF areas is the objective, the boundary of forest area is digitized and masked out. The image is then classified into settlement, water bodies, tree cover, agriculture and other land covers. This classification enables the interpreter to distinguish between tree cover and other classes. The classified image is visually analysed for editing and refinement. Since the minimum mappable area is 0.1 ha, pixels are clumped and cluster of pixels having area less than 0.1 ha were eliminated. After editing of the classified image, the final classified map is generated having three classes in TOF areas, namely, block, linear and scattered. From the classified TOF map, area under each category (stratum) is calculated. In addition, areas which do not support tree vegetation, like rivers and water bodies, riverbeds, snow covered mountains, etc. which is termed as un-culturable non forest area were also calculated. The schematic chart of methodology of TOF using remote sensing is depicted in Fig. 1.
Fig. 1. Schematic chart of methodology of TOF
The optimum size of the plot and number of samples required for each stratum have been determined by FSI by conducting a pilot study in the past. The optimum plot size for block and linear strata are 0.1 ha and 10m ´125m strip, respectively. In case of scattered stratum, the optimum size of sample plot has been fixed as 3.0 ha for non-hilly district and 0.5 ha for hilly district. The sample sizes for block, linear and scattered strata have been determined as 35, 50 and 50, respectively for non-hilly districts and 35, 50 and 95, respectively for hilly district.
Desired number of sample points are randomly generated for each stratum and the data on pre-decided variables like dbh, crown diameter, species name and category of plantation, etc. are collected on designed formats. Data processing is carried out using data processing module developed for this purpose by FSI.
Trees Outside Forests (Urban) In urban areas, it is not feasible to lay out plots of desired size, therefore, a separate methodology is adopted for inventory of urban areas. National Sample Survey Organisation (NSSO) has prepared sampling frames for each urban area of this country. This organization conducts surveys by dividing all the urban centres of a district in blocks called Urban Frame Survey (UFS) blocks (Fig.2). These blocks have well defined natural boundaries and are formed on the basis of population or households and cover the whole area within the geographical boundary of towns including vacant lands. The description of urban areas is obtained from District Census Book for conducting the TOF inventory.
Fig. 2. UFS block map
For the purpose of survey the towns have been classified on the basis of population as given below:
Class I: Population of 100,000 and above
Class II: Population between 50,000 and 99,999
Class III: Population between 20,000 and 49,999
Class IV: Population between 10,000 and 19,999
Class V: Population between 5,000 and 9,999
UFS blocks are used as sampling units. The sample blocks ( 25 to 60 in a district) in each class of town were randomly selected based on its size. Complete enumeration of all the trees of dbh of 10 cm and above was carried out in the prescribed formats having similar parameters as for rural inventory.
Data Processing
The data pertaining to 120 districts (two cycles) have been analysed for estimation of growing stock in outside forest areas.
The data collected in the field was checked manually to detect any inconsistency or recording error before entering into the computer. The data is entered in the computer using data entry module, designed and developed by FSI separately for TOF (Rural) and TOF (Urban) inventories.
The data processing was carried out separately for rural and urban areas. In rural areas, the estimation of growing stock was carried out separately for block, linear and scattered strata. The area figure for block and linear stratum was obtained by digital interpretation of remote sensing data, whereas the area of scattered stratum was obtained by subtracting the area of block and linear patches from rural CNF (culturable non-forest) area. In case of urban stratum, the area was taken from census data. Species and diameter class wise number of stems enumerated in sample plots were used for calculating stems per hectare under each stratum. The corresponding volume per hectare was also calculated using volume equations available with FSI. To obtain the growing stock in TOF of the district per ha figures of stems and volume and area factor of each stratum was used and then growing stock of the physiographic zone was estimated. The country wide growing stock estimates of TOF were generated by adding the estimates of physiographic zones.
Results
The growing stock estimates of trees outside forests at physiographic zone and national level have been generated. The present estimate is based on 120 districts and is therefore more robust and accurate compared to the estimates given in ‘SFR 2003’ where results were estimated on the basis of 60 districts only.
The physiographic zone wise growing stock (stems and volume) in TOF is presented in Table 1.
Table 1. Physiographic zone wise growing stock (stems and volume)
|
Physiographic zone |
Areas of physiographic zone (km2) |
Recorded forest area(km2) |
Growing stock Stems Volume
(million) (million cum) |
|
Western Himalayas |
329,255 |
91,073 |
539
194.23 |
|
Eastern Himalayas |
74,618 |
47,965 |
162
67.470 |
|
North East Ranges |
133,990 |
79,431 |
521
99.390 |
|
Northern Plains |
295,780 |
14,230 |
520
113.803 |
|
Eastern Plains |
223,339 |
31,709 |
341
91.437 |
|
Western Plains |
319,098 |
13,666 |
340
82.215 |
|
Central Highlands |
373,675 |
80,665 |
317
106.806 |
|
North Deccan |
355,988 |
87,260 |
291
71.157 |
|
East Deccan |
336,289 |
128,757 |
355
175.255 |
|
South Deccan |
292,416 |
49,459 |
423
147.608 |
|
Western Ghats |
72,381 |
32,399 |
267
109.273 |
|
Eastern Ghats |
191,698 |
74,418 |
213
89.839 |
|
West Coast |
121,242 |
20,765 |
513
158.329 |
|
East Coast |
167,494 |
17,826 |
359
109.439 |
|
Total |
3,287,263 |
769,621 |
5,160
1,616.244 |
The total growing stock of wood in the TOF of the country is estimated to be 1,616 million cubic metres. Maximum growing stock in TOF area is found in Western Himalayas followed by East Deccan and West Coast. The percentage distribution in growing stock of top 10 species of TOF are given in Table 2.
In TOF, Magnifera indica contributes maximum volume of 11.18 per cent of total volume followed by Cocos nucifera, Syzygium cumini, Azadirachta indica and Madhuca latifolia having a contribution of 4.94, 4.2, 3.91 and 3.72 per cent,respectively.
Table 2. Growing stock in TOF for top ten species
|
S. no. |
Species |
Total stems (%) |
Total volume (%) |
|
1. |
Mangifera indica |
8.91 |
11.18 |
|
2. |
Cocos nucifera |
4.29 |
4.94 |
|
3. |
Syzygium cumini |
1.23 |
4.20 |
|
4. |
Azadirachta indica |
4.36 |
3.91 |
|
5. |
Madhuca latifolia |
1.09 |
3.72 |
|
6. |
Borassus flabelliformis |
1.79 |
3.64 |
|
7. |
Ficus species |
0.66 |
2.72 |
|
8. |
Prosopis cineraria |
3.26 |
2.65 |
|
9. |
Tamarindus indica |
0.62 |
2.57 |
|
10. |
Acacia arabica |
3.87 |
2.31 |
Conclusion
The methodology using digital image processing and geographical information system, as explained above is very useful and time effective to generate the national level estimates of growing stock in TOF every two years. In addition, spatial distribution of TOF resources on maps along with other features will provide information for planning and implementation and utilization of these resources in a sustainable manner. After the completion of few more cycles, FSI will be in position to generate state level estimates of growing stock of TOF which will be of immense use of state governments for planning purposes.
References
Forest Survey of India. 2003. Manual on assessment of trees outside forests. Dehradun, Forest Survey of India.
Forest Survey of India. 2005. State of forest report 2003. Dehradun, Forest Survey of India.
Hidalgo, D.M. and Kleinn, C. 2002. Trees outside forests. Costa Rica, FAO.
International Training Workshop on Assessment of Trees Outside Forests, Dehradun, April 2002. Proceedings. Dehradun, Forest Survey of India.
Kleinn, C. 2000. On large area inventory and assessment of trees outside forests. Unasylva, 200(51): 3-1
FORESTRY STATISTICS: ITS SIGNIFICANCE, PRESENT STATUS AND SUGGESTIVE MEASURES FOR IMPROVEMENT
V.P. Tewari
Arid Forest Research Institute, Jodhpur - 342 005
Introduction
F
orests are essential for the well being of humanity and the role
that the forests play in maintaining ecological balance,
environmental stability and sustainable development is well known. The practice of scientific forestry in the country has undergone a paradigm shift over the past few decades as the focus has shifted from sustained timber yield to sustainable eco-system management.
Forests and forest produce play a major role in the society and life of a human being, apart from significantly contributing to the economy of our country. They provide timber, fuel, fodder and a host of other goods and services for immediate consumption or consumption after processing, notwithstanding the intangible benefits that accrue from the protection of environment, tourism and other related activities. However, the contribution of forests to the gross domestic product GDP of our country remains clouded with skepticism for want of data and precise estimation of the value of inputs and the outputs associated with it.
The varied nature of the products provided by the forests for our consumption, the location of forests in our country and the nature of terrain make it difficult to collect data that can present true picture of this contribution of forests to the Indian economy. The contribution may be best measured by expressing it per unit of forest area, generally measured in hectares. It is to estimate this ratio that such studies are essential to be taken-up at regular intervals and also to take into account the forever-changing role of forests and forest management.
Forestry has, thus, emerged not only as a major scientific discipline but also as a provider of goods and services to the masses. The contribution of forestry sector in Indian economy is immense but this contribution has been grossly underestimated for want of proper statistics. The haphazard way of data collection in forestry sector (and most of the time their unavailability) has been the focal point for discussions at various forums. This became more pronounced when the contribution of forestry sector to the GDP of our country could not be calculated directly and had to depend on indirect methods of estimation.
Forestry in developing countries, including India, is increasingly being seen as a means for eradicating rural poverty and achieving sustainable development. A proper system for maintenance of forestry statistics is required to assist planners and policy makers. Moreover, India is also a signatory to International Tropical Timber Agreement (ITTA) wherein various demand and supply, production and consumption data regarding timber and fuel wood etc. is required on an annual basis (Behari and Nautiyal, 2007). Thus in this context, maintenance of proper statistics and records are inevitable for the management of forests on a sustainable basis. It is not only the long rotation involved but also the nature of forests as a renewable resource which requires comprehensive information for proper management.
It is a fact that the forestry statistics is a useful tool in decision-making process for optimum utilization of scarce resources and allocation of resources to the sector. It also helps in estimating the contribution of the sector to the economy of the country. However, the present level of statistical reporting in the forestry sector is far from satisfactory.
Timber and Non-Timber Forests Products - Two Important Components
The products for which we depend upon the forests can broadly be classified into two categories – timber and non-timber forest products (NTFPs). The latter category includes a wide spectrum of products that vary with the geographical regions of our country.
Though the timber still forms an important component of use in our country, NTFP or minor forests produce (MFP) is a major component of the direct contribution of forests in income generation of our country. They constitute a vast resource being tapped and waiting to be tapped for internal use as well as for exports. Considering the huge variation in forest types of our country, there are different MFPs pertaining to the particular forest type.
The collection of data pertaining to NTFPs becomes difficult, as the collection of NTFPs is unorganized to some extent. The collection agencies vary from the well organized state forest departments (SFDs) to the unorganized villagers and tribal people who do not keep any record of the value of the forest product they are collecting. The timber market, on the other hand, is quite organized and sale is through the SFD depots or well established timber markets.
The data regarding production of timber and non-timber forest products (as provided by the state forests departments) in Rajasthan and Gujarat from 2000-01 to 2005-06 are shown in Table 1 A and B and Fig. 1 and 2 which shows large variations in production of fuel wood and NTFPs during different years.
Table 1A. Production of timber and non-timber forest products in Rajasthan during 2000-01 to 2005-06
|
Year |
Round wood (non coniferous, m3) |
Wood fuel (m3) |
Tendu/bidi leaves (standard bags)* |
Bamboo** (lakh) |
|
2000-01 |
25675.08 |
62295.11 |
595381 |
19.26 |
|
2001-02 |
22541.36 |
487421.40 |
453187 |
17.98 |
|
2002-03 |
31429.20 |
50314.90 |
464238 |
16.47 |
|
2003-04 |
29011.88 |
35516.95 |
193276 |
17.73 |
|
2004-05 |
27715.26 |
36752.71 |
303260 |
19.06 |
|
2005-06 |
27125.47 |
38435.05 |
157273 |
10.62 |
*1 standard bag = 0.5 quintal, **250 bamboos = 1 MT, 1 standard bamboo = 4.5 metres
Table 1B. Production of timber and non-timber forest products in Gujarat during 2000-01 to 2005-06
|
Year |
Round wood (non coniferous, m3) |
Sawn timber (m3) |
Pole (m3) |
Wood fuel (m3) |
Bamboo (MT) |
Tendu/bidi leaves (standard bags)* |
Grass and Grazing(MT) |
Gum and Resin(MT) |
|
2000-01 |
10129.38 |
1095.02 |
18470.77 |
30963.73 |
128281.00 |
2237.55** |
8754.60 |
0.30 |
|
2001-02 |
9671.11 |
- |
- |
44203.51 |
64917.00 |
2030.35** |
10236.70 |
0.93 |
|
2002-03 |
12769.05 |
11135.79 |
8943.58 |
33386.93 |
9994.93 |
32934.00 |
- |
67.94 |
|
2003-04 |
21206.73 |
27686.67 |
6212.41 |
87678.85 |
2392.17 |
154344.00 |
- |
65.10 |
|
2004-05 |
18293.85 |
957.16 |
18013.16 |
146553.34 |
73346.47 |
423504.00 |
12043.01 |
66.54 |
|
2005-06 |
16661.52 |
1630.97 |
10160.83 |
62636.24 |
75607.67 |
266944.00 |
14120.00 |
78.63 |
Fig. 1. Production of timber and non-timber forest products in Rajasthan during 2000-01 to 2005-06
Fig. 2. Production of timber and non-timber forest products in Gujarat during 2000-01 to 2005-06
Present Status of Data Reporting
Annual Administrative Reports prepared at the division level are the basic unit of the reporting system in forest administration. The basic data originates at the range level in a set of forms standardized for the whole state. These data are eventually used for Administrative Reports/Annual reports and performance budgets.
The present system of data reporting need to be further improved, updated and reinforced as integral parts of the forest statistical system. Apart from the information on administrative part, sectoral information is helpful in plan/policy related deliberations. Paucity of such information has proved crucial in forestry sector planning. For example, production, consumption, trade and movement of wood and non-wood forest produce outside the government owned forest estate contribute substantially to the national economy. The role of wood is amongst the most prominent natural resources in infrastructure, governance, trade and rural as well as urban economy. Statistics on paper production are required to compare the position of raw material derived from forests vis-à-vis from other sources. Statistics on pulp are also required with segregation into chemical, mechanical, bleached and unbleached, type of chemical used, etc. Compilation of such information for forest administration is vital along with forest estate management (Behari and Nautiyal, 2007).
Presently, there are many constraints in the data collection and the agencies involved in this task are not consistent in sending data for compilation and dissemination. It not only affects the continuity in data collection important for future statistical work, creating a huge gap in the data bank, but also affects our ability to provide timely information to other national and international agencies. In the absence of a mechanism to facilitate, monitor and control the important work of data collection, market information on various parameters of importance of forestry is greatly hampered.
The national picture of many parameters of forestry still remains unclear as the requisite data from many state forest departments are not available in appropriate form. Moreover, the contribution of forestry products viz. timber, poles, fuel-wood and non-timber forest products including the medicinal plants to GDP remains unaddressed.
Suggestions for Improvement
The state forest departments must come forward to develop, strengthen and streamline the forestry statistics collection, compilation and dissemination mechanism through capacity building/development of human resources.
The gaps in collection of data need to be identified and plugged in so that the rates and ratios can be updated with latest data. Such studies are also expected to provide a momentum to funding in forestry research once the importance has been quantified in monetary terms as a ratio to the GDP, notwithstanding the fact that intangible benefits are immense and expression of all these benefits in monetary terms is not always possible.
The value of input and output of timber and non-timber forest products in the country must be estimated at regular intervals to arrive at the rates and ratios of these two components. Annual surveys should be a feature for data on agroforestry and social forestry.
Electronic submission of information/returns should be promoted. In particular, consideration should be given to the use of web-based returns. It will reduce time for information flow at all levels.
Statistical cells in the state forest departments are necessary for data collection and validation works. The technical needs of SFDs should be assessed and governments should take necessary steps to fill in long standing vacancies. Computing facilities should be provided at the range level with skilled manpower.
A data warehouse is required which would help in development of decision support system, improve the quality of information, provide effective linkages with other organizations, improve efficiency of organization by optimal management of its resources, utilize scarce resources of various organizations effectively and act as a tool for planning (Rai, 2007).
Establishing linkages with other all India data such as National Census, National Sample Surveys (NSS) and National Export and Import databases, etc. are also essential to strengthen the socio-economic dimensions of forest statistics.
It is highly essential that the entire forest statistical system be carefully reviewed, restructured and reporting capacity reinforced in an appropriate manner. By adopting this measure, the contribution of forests to social, economic and ecological well-being of the nation can be recognized with the development support to the sector thereby maintaining the health of the forests in an optimum condition (Behari and Nautiyal, 2007).
Conclusion
Maintenance of proper statistics and records are essential for management of every sector. Forestry is one of such areas which contribute significantly to the economy of the country. Collection of forest related statistics is one of the major issues for management of forest resources on a sustainable basis. Besides fulfilling the international commitments, the collection, compilation, validation and dissemination of forestry statistics is urgently required for satisfying the national commitments for the policy and planning. The present structure of statistical reporting needs to be revamped in order to improve the statistics of the forestry sector in the country.
References
Behari, B. and Nautiyal, R. 2007. National forestry database management system (NFDMS): Theme, concepts and vision. In: India. Ministry of Environment and Forests. Survey and Utilization Divison. National forestry database management system – a vision. The author. pp. 1-11.
Rai, A. 2007. National forestry database management system (NFDMS): Theme, concepts and vision. In: India. Ministry of Environment and Forests. Survey and Utilization Divison. National forestry database management system – a vision. The author. pp. 21-28.
ENVIRONMENTAL
UPS
and DOWNS
Environmental Ups
In a bid to save endangered species of herbal plants and encourage their mass cultivation of marketing in the state, the Uttarakhand government has started a new “buy back” scheme. Under this scheme, the farmers with a “buy back” certificate will not only get suitable prices of their products but will also be given compensation for their losses by forest department and Kumaun Mandal Vikas Nigam.
India’s National Action Plan on Climate Change has been unveiled by the Prime Minister Dr. Manmohan Singh. According to this action plan India’s per capita GHG emission would at no point exceed that of the developed countries and that it has not committed to specific emission reduction targets or energy efficiency targets.
Efforts are afoot in Bangalore to make rainwater harvesting compulsory to address the problem of impending water shortage.
Haryana government has declared that under the new forest policy of the state, area under forest cover would be increased from 7.13 per cent to 10 per cent by 2010.
The only known habitat of one of the world’s rarest birds has been saved from destruction. Thanks to a compromise between environmentalists, villagers and Andhra Pradesh government, the 400-km Telugu Ganga Canal which will stretch from Srisailam in Central Andhra to Chennai, will be diverted around the only remaining habitat of the Jerdon’s courser, a nocturnal bird.
The humpback whale, nearly hunted into history four decades ago, is now on the “road to recovery” and is no longer considered at high risk of extinction.
The International Labour Organisation in its report “Green Jobs: Towards Decent Works in a Sustainable, Low-Carbon world,” says that changing patterns of employment and investment resulting from efforts to reduce climate change and its effects are already generating new jobs in many sectors and economies, and could create millions more in both developed and developing countries.
In a serious bid to emerge as the first “Carbon Neutral” state of Asia, Himachal Pradesh has prepared a multi-pronged strategy to minimise emission of greenhouse gases envisaging preventive and remedial measures for striking a realistic balance between “development and environment.”
A research by the scientists at Michigan Technological University’s School of Forest Resources and Environmental Science determined that moderate increase in temperature and nitrogen from atmospheric pollution actually improve forest productivity. They found that the trees grow faster at higher temperatures and store more carbon at greater concentration of nitrogen provided there is sufficient moisture.
The Forest Survey of India, alongwith Indian Council of Forestry Research and Education, FDAs and independent agencies under National Afforestation Programme has treated with over 1.41 million hectares of land at a cost of Rs. 1,570 crores till last financial year.
Uttar Pradesh government is planning to release gharials in Betwa, Son, Ken and Ghagra rivers as the gharial sanctuary along the Chambal river has been deemed unfit for the safety of the species.
The beautiful Demoiselle cranes are back in the Thar desert districts of Rajasthan. The smallest and second most abundant among the world’s crane species, Demoiselle cranes or Kurjas are part of the desert love lore about Marwari migrants of yore who were forced to live separately from their loved ones due to compulsions of trade.
Pilibhit Tiger Reserve has finally got an in principle approval from the Project Tiger authorities.
The Ministry of Environment and Forests (MOEF) has turned down Ministry of Mines’ proposal to ease environmental regulations for mineral exploration in forests. MOEF’s tough stand may adversely impact investments in locating new mineral reserves in the country.
Wind power could produce 12 per cent of the world’s energy needs and prevent 10 billion tonnes of carbon dioxide emissions within 12 years, according to a report of Global Wind Energy Council and Greenpeace International.
Scientists at Centre for Aromatic Plants in Uttarakhand have successfully managed to grow Artemesia, which in near future is expected to provide a fillip to production of malaria related drugs in the state.
The old pugmark is transforming into a digital footprint. With real time information on tigers available through observation of tigers fitted with satellite collars, GPS collars and radio VHF collars, the National Tiger Conservation Authority (NTCA) is for the first time creating a system for a central database on tiger movement and analysis, especially real time information with a view to track tigers, monitor source population, movement patterns and also empower forest guards to make inputs into the centralised software.
Environmental Downs
Deforestation is leading to close to 20 per cent of global greenhouse gas emissions, which in turn are leading to climate change and possible extinction of 20-30 per cent of all species on Earth.
Climate related disasters will result in 9-13 per cent of loss of GDP in India by 2010. This will be a key factor in preventing the economic growth in India.
The F.A.O. has issued a caution on the repercussions of climate change in fisheries and aquaculture. The changes in seas and oceans will have direct implications for food security as the marine organisms are responding faster to global warming than previously thought.
Striking new research in southern California mountains suggests recent warming is behind a massive die-off and rapid migration to higher ground by nine different plants - from desert shrubs to white firs. Within 30 years, most had moved to elevations 200 feet above their previous growth range. The findings provide a glimpse of what could happen to the world’s vegetation and the Earth faces inevitable global warming.
United Nations Industrial Development Organisation said that climate change was likely to have a greater impact on India compared to other countries similarly positioned, on account of the unique combination of its geography, diverse population characteristics and extremely high carbon related energy dependence.
A team at the Wildlife Conservation Society has identified cholera, plague and sleeping sickness among the dozen diseases which it claims are increasing their geographical range because of the global warming.
International Union for Conservation of Nature (IUCN) has said in a study that more than 7,000 species in the world – 35 per cent of birds, 52 per cent of amphibians and 71 per cent of warm-water reef-building corals are likely to be particularly susceptible to climate change.
Climatic change will amplify the risk of flooding in northwestern Europe, water scarcity and forest fires on the northern Mediterranean rim and bring milder winters to Scandinavia, the Copenhagen-based European Environment Agency said.
While the administration is spending a lot of money on the cleaning of the Ganga and maintenance of ghats and Hindu organisations launching a campaign to clean the holy river, yet waste water and filth through sewer pipes continue to pour into the Ganga, making it one of the dirtiest rivers in the world.
‘Nicobar Megapod’ an endemic endangered bird species can be extinct in the next 10 years. The population of this bird has reduced to 70 per cent in just 12 years and can be gone soon.
The highly endangered Great Indian Bustard face squeeze in area from 8,500 sq. km. to 350 sq. km. in Maharashtra as the state government has made a plea before Supreme Court seeking to reduce their habitat.
The Indian vulture is facing near extinction, recording a 99.9 per cent decline in population since 1992, says a global survey conducted by the Cambridge-based Birdlife International.
Air pollution has shot up the cases of asthama in Chandigarh. It has become the most common lung disease among the residents, says S.K. Jindal, professor and head, Department of Pulmonary Medicine, Post-Graduate Institute of Medical Education and Research, Chandigarh.
FORESTRY STATISTICAL DATABASE AND DATA MINING: A CASE STUDY OF KERALA STATE
M. Sivaram
Kerala Forest Research Institute, Peechi, Kerala - 680653
Introduction
I
n recent years, forests and forestry have attracted greater attention
all over the world in view of their complex role in the environment
amelioration besides the social and economic benefits they provide to the population. It is this fact that led to the development of sustainable forest management based on scientific principles and reliable data. There has been a wider use of forest statistics in resource accounting, making crucial management decisions, developing criteria and indicators for the assessment of sustainability, economic computations and making policy decisions. Considering the importance of forestry statistics and database the Forest Policy 1988, emphasized the need for improving periodical collection, collation and publication of reliable data on relevant aspects of forest management with recourse to modern technology and equipment.
A number of agencies such as state forest departments, Forest Survey of India, Ministry of Environment and Forests, etc. have been publishing data on various aspects of forest from time to time. However, there have not been efforts to integrate these data and produce as computerized database for easy data retrieval and reference. Recently, Sivaram (2004) developed an integrated computerized database and retrieval software on selected aspects of forest resources of Kerala utilizing the data collected from several secondary sources and the data on certain aspects were analyzed. One of the objectives of this study was to update the existing statistical database and add data on new themes and carry out statistical analysis to bring out useful information for forest management.
Data Mining in Forestry
Today, organizations are accumulating vast and growing amounts of data in different formats and different databases. This includes: i) operational or transactional data, such as sales, cost, inventory, payroll and accounting, ii) non-operational data, such as industry sales, forecast data and macro economic data and iii) meta data - data about the data itself, such as logical database design or data dictionary definitions. Data mining is finding the hidden patterns that transform data into insight (i.e. knowledge discovery) and applying discovered knowledge for business advantage (i.e. knowledge deployment) (National Informatics Centre, Government of India, http://modelling.nic.in/data_mining.htm).
Data mining involves the use of sophisticated data analysis tools which include statistical models, mathematical algorithms, and machine learning methods (algorithms that improve their performance automatically through experience, such as neural networks or decision trees). Data mining is used for a variety of purposes in both the private and public sectors. Industries such as banking, insurance, medicine, and retailing commonly use data mining to reduce costs, enhance research, and increase sales. For example, the insurance and banking industries use data mining applications to detect fraud and assist in risk assessment (e.g. credit scoring).
In addition to the technological improvement in computers and data management tools, the increased availability of information and the decreasing costs of storing it have also played a role. While data mining products can be very powerful tools, they are not self sufficient applications. To be successful, data mining requires skilled technical and analytical specialists who can structure the analysis and interpret the output that is created. Consequently, the limitations of data mining are primarily data or personnel related, rather than technology related (Seifert, 2004).
The data mining tools such as neural networks have been used in forestry science. In India, the data mining applications in forestry are scarce (Sivaram, 2007).In this paper, data mining was attempted on the forestry statistical database of Kerala state containing non-transactional data collected from several sources.
Computerized Database and Data Retrieval System
Sources of Data
The database was developed by collecting data from several secondary sources and by communicating with various agencies. The sources include the publications of the Kerala Forest Department, Ministry of Environment and Forests, Food and Agriculture Organization (FAO), Department of Statistics and Economics, Directorate of Census and the Kerala Forest Research Institute and the articles published in journals.
Thematic Elements of the Database
The database was developed on the following themes. The data on many of the aspects are of time-series type covering the period from 1980 to 2005.
i) Land and Population
ii) Forest Policies
iii) Forest Administration
iv) Forest Economy
v) Forest Area
vi) Forest Plantations
vii) Growing Stock
viii) Production of Forest Products
ix) Prices of Forest Products
x) Supply and Demand
xi) Biodiversity
xii) Mangroves and Sacred groves
xiii) Forest Degradation
xiv) Wildlife Census
xv) Ecotourism
xvi) Forest Weather
xvii) Forest Maps
Development of Database and Retrieval System
A simple interface was developed using Microsoft Visual Basic so that data addition, updation and retrieval become easy. In this system, there are different data folders named after the major themes and prefixed by a three digit code (like 001, 002, etc.) stored in the root directory C:\database_forest. In each folder, files named after the title of the data table and prefixed by a three digit code are stored. The order of appearance of the themes and files under the each theme is based on decreasing order of the three digit code. The data files may be in Excel (xls), Word (doc) or in Acrobat (pdf) format (Fig. 1).
Fig. 1. Diagram showing the database system for storage and retrieval of data files
The program interface helps to retrieve the information available in these files in a few clicks. The first click on the theme of our interest (presented in the left panel of the main menu) will provide the details of the data files available under the theme (in the upper portion of the right panel). When a click on the data file of interest is done, its content is displayed in the bottom portion of the right panel in its native format. This file can be zoomed to full screen and content can be read. If needed, copying and printing can also be performed. For example, a click on the theme Forest Plantations (highlighted) in the left panel provides the list of data files available under it in the upper portion of the right panel. Further click on ‘Trends in species-wise area under forest plantations’ displays the data available in it in the bottom portion of the screen (Fig. 2). By clicking the ‘Maximize’ button the file is zoomed to full screen and data displayed. By clicking the ‘Restore’ button the main menu is retrieved (Fig. 3). The graphs are also made available for the data wherever possible. The system also contains a glossary.
Fig. 2. Main menu of the database and retrieval system
Fig. 3. Maximized view of the left-bottom of the menu in Fig. 2 showing the details of the trends in species-wise area under forest plantations
Data Mining Applications
The spatial-temporal data presented in the database helps to appraise various aspects of the forestry sector. In this paper, using the data available in the database data mining was undertaken with the following objectives:
i) to project the future trends in the availability of teak wood from forest plantations based on its age structure under different scenarios
ii) to analyze the trends in the real prices of teak wood using spline models and
iii) to make short-term forecasts of current prices of teak wood using Artificial Neural Network (ANN) and Autoregressive Integrated Moving Average (ARIMA) models
The first objective is met in projection of availability of teakwood from forest plantations and the last two objectives are met in analysis of timber prices.
Projection of Availability of Teakwood from Forest Plantations
Importance of the study
Teak (Tectona grandis) is indigenous to India. Teak wood has high value and demand because of its durability, colour, texture, grain and aesthetic value. The long-term revenue and expenditure in plantation sectors of the forest department in Kerala have been centred on teak plantations. At present, the total forest plantation area in Kerala is 1,91,000 ha. This is 17 per cent of the total forest area of 11,20,000 ha. Apart from teak plantations, home gardens are also major source for the teak wood supply in Kerala. Most of the teak wood produced is consumed within the state mainly for new house/building construction and furniture making. Of the total timber consumption, about 5.5 per cent is teak (Krishnankutty, 2005). Future projection of supply and demand and prices is an important activity in any business enterprise to plan the required activities ahead for addressing the future demand-surplus situation and for optimal investment. Internationally, teak wood is a premium timber product. Therefore, it is important to understand the future availability of teak wood from forest plantations and how far it would meet the future demand of the society especially when there is no expansion of teak plantations and productivity is of major concern (Jayaramanand and Chacko, 1997; Sivaram, 2008a). Such exercise will aid in developing forest policies for the sustainable forest plantation management, especially of teak.
Primary data source
The data on forest plantations were obtained through extensive communications with the divisional forest officers of the Kerala Forest Department and divisional managers of the Kerala Forest Development Corporation. The officers were requested to provide the details of the individual plantations in their respective jurisdiction such as location, extent and year of and supply of teak wood obtained from various research reports and all India yield table were also used for the analysis.
Key factors involved in projections
Age structure of teak plantations The age structure of presently available plantations determines the future outturn of timber. The list of teak plantations as on year 2005 from all the territorial forest divisions was classified according to different age groups and presented in Fig. 4. Nearly 60 per cent of the plantations were found in the age group of 25-44 years.
Fig. 4. Age structure of teak plantations under territorial forest divisions- 2005
Stocking and site quality
The productivity of teak depends on the stocking and site quality of the plantations apart from the quality of planting materials, the extent of pest and disease problems. An assessment made by Jayaraman and Chacko (1997) showed that only 5 per cent of the area under teak belonged to site quality class I. Eighty six per cent of the area belonged to moderate site quality classes either II or III. In terms of stocking, the understocked and overstocked plantations were 74 per cent based on basal area per ha and 81 per cent based on number of trees per ha.
Thinning and Rotation age Thinning is an important operation to reduce competition between trees for producing commercially sizeable timber. The prescribed thinning years are 4, 8, 12, 18, 28 and 40 years. However, in practice, there is a variation in thinning years followed. The average thinning schedule worked out by Jayaraman and Chacko (1997) based on the data obtained from the records of the forest department are at 7, 10, 16, 24, 31 and 35 years.
Rotation age is the time between setting up of plantations and clearfelling of the final crop. It is mostly determined by the maximum volume production and economic return. In the field, it varies across geographic boundaries due to factors such as latitude, aspect, altitude, climatic conditions, site-specific factors, etc. The rotation age of plantation teak in its natural range has varied between 50 and 90 years, while outside the natural range the rotation age is between 40 and 60 years (Pandey and Brown, 2000). In general, teak plantations in Kerala are managed on a rotation age of 50 to 60 years.
Volume estimates There is a paucity of data on actual yield at harvest of teak from different site quality classes. The general conclusion arrived at from the available data is that the actual productivity has often been much lower than that indicated in the yield table. Expected yield in India is 4 to 6 m3 per ha per year over the likely rotation length (Leech, 1998). Mean annual increment (MAI) obtained from government owned plantations ranged from 2 to 5 m3 per ha and is often below the potential yield of the site (Enters, 2000). The actual yield obtained from thinnings and final fellings in Konni forest was reported to be 2.5 m3 per ha per year at 70 years (Pandey and Brown, 2000). Estimates of MAI of teak at 60 years including yield from thinning for different forest divisions were worked out by Jayaraman and Chacko (1997) based on the data collected from standing crop. The MAI varied from 4.0 m3 per ha in Kozhikode Forest Division to 2.2 m3 per ha in Kothamangalam Division at 60 years. The state level MAI was 3.1 m3 per ha. Chundamannil (1998) reported actual yield realized from teak plantations in Nilambur Forest Division during the period 1967 to 1994 based on the data available in the files of the forest department. The MAI ranged from 0.97 to 5.64 m3 per ha with the overall mean of 2.85 m3 per ha at 53 years.
Modeling the future availability of teak wood from forest plantations The mathematical formulation of the idea of projection is as follows.
Let ai be the area of the ith individual plantation in ha (i=1,2, …N). Let ci be the year of planting of the ith plantation. The projected availability of teak wood or projected total yield (Ptr) in a given projection year t is a sum of the quantum of yield that is obtained from thinning (Ttr) and felling (Ftr) for the given rotation age r and thinning year j =1,2, ... k.
Where
Formula used for projecting the future demand
Dt=D0(1+r)n
where
Dt = teak wood demand in the projection year t
D0 = teak wood demand in the beginning year (base year)
n = number of years between base year and intended projection year t
r = compound growth rate for teak wood
Options and assumptions involved in projections
Options In Kerala, the rotation age for teak generally ranges from 50 to 60 years due to varying growth attainment. Therefore, it was decided to make different projections according to three rotation periods 50, 55 and 60 years.
With regard to felling yield used for projection, the yield as per the all India yield table (FRI, 1970) against site quality III was used because majority of the teak plantations in Kerala were of site quality II or site quality III (Jayaraman and Chacko, 1997). We could think of two possible variations with respect to yield due to thinning. The thinning years considered were 4, 8, 12, 18, 28 and 40 years and the thinning years of 7, 10, 16, 24, 31 and 35 years as worked out by Jayaraman and Chacko (1997) based on the records of the Kerala Forest Department. The sum of the thinning yield and felling yield as per the all India yield table was termed as potential yield. The sum of the thinning yield as per Jayaraman and Chacko (1997) and felling yield as per the all India yield table was termed as estimated yield.
With respect to projection of future demand for teak wood we relied on the studies conducted by Krishnankutty (1990, 2005). According to these studies the total demand for teak wood was 64,000 m3 in 1987-88 and 96,000 m3in 2000-2001 showing the annual compound growth rate of nearly 3.2 per cent over the period of 13 years. On this basis, the future trend in the demand for teak wood was projected by considering differential annual growth rate with the demand estimated in 2000-01 as base. The different annual growth rates considered were 2, 3 and 4 per cent, respectively.
Assumptions One of the important assumptions made in the projection of future availability of teak wood is that plantations that are felled during the year will be replanted in the subsequent year. It was also assumed that the addition of new teak plantations during the projection period would be negligible. This assumption seemed plausible because there was no land available for extending teak plantations as indicated earlier.
Results and discussions
For the projection purpose, only teak plantations that come under the territorial divisions were considered. The teak plantations belonging to wildlife divisions were not considered for projection because no routine management practices such as thinning or felling were adopted in those plantations.
When the projected demand is compared with the projected figures of availability of teak wood, it appears that the extent of teak plantations in Kerala at the existing level are potential enough to meet the future demand at least up to the period 2030-2040 even at the maximum assumed annual growth rate of 4 per cent demand (Fig. 5–7). However, the past trends in the annual production of teak wood from forest plantations have been far less when compared with the projected demand scenario. For example, the production of teak wood from forests during the last five years was only about half of the demand. Therefore, activities in promoting the productivity of teak plantations and teak planting outside the forests such as home gardens and farmlands should be continued. This would help fill-up the gap between future demand and supply from forest plantations.
Fig. 5. Future trends in the gap between demand and availability of teak wood from forest plantations (rotation: 50 years)
Fig. 6. Future trends in the gap between demand and availability of teak wood from forest plantations (rotation: 55years)
Fig. 7. Future trends in the gap between demand and availability of teak wood from forest plantations (rotation: 60years)
Analysis of Timber Prices
Price analysis of teak wood
Variation in prices of forest products is one of the main sources of uncertainty in forest planning. The prices of timber depend on its length, girth and quality. Earlier, Krishnankutty (1989,1998, 2001a, 2001b and 2002) made a significant contribution in the analysis of the past and future teak wood prices using spline and auto regressive integrated moving average (ARIMA) models. The details of the trend analysis of past prices and
forecasting of future prices of teak with the updated data and using latest forecasting techniques are presented in the following sections.
Primary data source
The Kerala forest department undertakes marketing of various forest produces through different disposal methods. Timber felled from forests by the Kerala forest department are deposited in sales depots and auctioned. The data on timber prices were obtained by extensive communications/visits to timber sales divisions/timber depots of the Kerala forest department. The data collected so were compiled at division level and at state
The data relating to the period 1943-1994 was from Krishnankutty (1998) and data relating to 1994-1998 was from Krishnankutty et al. (2003). Data for the period from 1998 to 2006 was collected and compiled during this project.
Trends in current and real prices of teak wood
Teak wood is classified into as many as 50 classes based on mid-girth, length and quality. In this study, for the purpose of analysis, 5 girth classes viz., export class (185 cm and above), girth class I (150-184 cm), girth class II (100-149 cm), girth class III (75-99 cm) and girth class IV (60-74 cm) were considered. The weighted average prices per m3 were worked out using the following formula after duly accounting for the quantity of timber sold.
The changes in current prices may be due to inflation (general price increase) in the economy of the country. Therefore, the average annual current prices were converted into average real prices by deflating of Wholesale Price Index (WPI) with the base year 1993-94. The formula used for deflating (Croxton et al., 1973) is
Real Price= Current Price / Wholesale Price Index
The WPI values for the period 1956- 2006 are available with different base years (Office of the Economic Advisor, Ministry of Commerce and Industry, http://eaindustry.nic.in). The latest WPI series is available for the period 1993-2006 with the base year 1993-94. Therefore, the WPI values for the period 1956-1992 were recast using the back shifting formula (Croxton et al., 1973) with the base year 1993-94.
Modeling the prices of teak wood using spline model
Splines are piecewise polynomials of order k. The boundary points of each segment are referred to as break points, interior knots or simply knots. Knots give the curve freedom to bend and more closely follow the data. Splines with few knots are generally smoother than splines with many knots, however, increasing the number of knots usually increase the fit of the spline function to the data (Montgomery and Peck, 1982).
A spline with h knots, t1< t2<…< th, with continuous first k-1 derivatives, can be written as
This basic spline model can be easily modified to fit polynomials of different order in each segment, and to impose different continuity restrictions at the knots. If all h+1 polynomial pieces are of order k, then spline model with no continuity restriction is
where (x-ti)+0=1 if x>ti and 0 if x<=ti.Thus if the term Bij(x-ti)+j is in the model, this forces
a discontinuity at ti in the jth derivative of E(y). If this
term is absent, the jth derivative of E(y) is continuous at ti. The fewer continuity restrictions required, the better the fit because more parameters are in the model, while the more continuity restrictions require, worse the fit but smoother the final curve will be. The solution for the equations 1 and 2 can be found using the least square method.
Identification of best spline model
The price trends were analyzed by fitting different spline models. The knots for the model were identified by visual examination of trend graphs. The knots identified for export class are k1=1977 and k2=1989. The knots for girth class I, II and III are k1=1967, k2=1977 and k3=1995. The knots for girth class IV are k1=1977 and k2=1998. Different spline models viz., linear spline, linear spline with discontinuities at knots, quadratic spline, quadratic spline with discontinuities at knots on first and second derivatives and quadratic spline with discontinuities at knots were fitted. The least square method was used for estimating the parameters of the model. The PROC TRANSREG procedure in SAS was used to fit the models. The best model was selected
based on Root Mean Square Error (RMSE), Adjusted R2, Akaike’s Information Criterion (AIC) and Bayesian Information Criterion (BIC; Hair et al., 2003)
Since the interpretation of quadratic spline is more complicated, linear spline with discontinuities is used to find the rate of changes of real prices of teak wood in different periods. The estimated linear spline model with discontinuity at the 2 knots k1 and k2 is given by
Thus the rate of change of real prices of teak wood with respect to the year x for the period x d” k1, k1 < x d” k2 and x > k2 are â01, â01+ â11 and â01+ â11+ â21, respectively.
Forecasting of teak wood prices using ANN and ARIMA
A time series is a sequence of observations taken sequentially in time. The succession of values in a time series is usually influenced by some external factors. If the information on the influencing factors is not known, only the past values of the time series itself can be used to build a mathematical model for forecasting future values. In this study, two different forecasting modeling approaches were used.
1. ANN model, which is a non-traditional modeling technique (Haykin, 1999).
2. ARIMA model which is a traditional statistical technique (Box and Jenkins, 1994).
The elaborate details of the above two modeling approaches are given in Sivaram (2007).
ANN model
ANN is a powerful data modeling tool that is able to capture and represent complex input/output relationships whether it be linear or non-linear. The motivation for the development of neural network
technology stemmed from the desire to develop an artificial system that could perform “intelligent” tasks similar to those performed by the human brain. ANN acquires knowledge through learning and the knowledge is stored within inter-neuron connection strengths known as synaptic weights. The most common ANN model is the Multilayer Perceptron (MLP) (Fig. 8). This type of ANN is known as a supervised network because it requires a desired output in order to learn. In MLP with one hidden layer the inputs are fed into the input layer and get multiplied by interconnection weights (synaptic weights) as they are passed from the input layer to the hidden layer. Within the hidden layer, they get summed, then processed by a nonlinear function (usually the sigmoid/hyperbolic tangent). The processed data leaves the hidden layer and finally again processed one last time within the output layer to produce the neural network output. The MLP and many
other ANNs learn using an algorithm called backpropagation. With backpropagation, the input data is repeatedly presented to the neural network. With each presentation the output of the neural network is compared to the desired output and an error is computed. This error is then fed back to the neural network and used to adjust the weights such that the error decreases with each iteration and the neural model gets closer and closer to producing the desired output. This process is known as “training”. The trained neural network is tested and validated for applications (Sivaram, 2007).
Fig. 8. Typical architecture of multi layer perceptron
In this study, the architecture of ANN used is MLP with one hidden layer for all the problems. The activation function used in the hidden neuron is sigmoid. The error minimization algorithm used is Levenberg-Marquardit algorithm (Sivaram, 2007).
ARIMA model ARIMA model is a powerful model for describing stationary and nonstationary time series. The application of the ARIMA methodology for the study of time series analysis is due to Box and Jenkins (1994). The basic concepts involved in ARIMA are described in Appendix. ARIMA model is usually denoted as ARIMA, which can be expressed as
The parameters involved in the above model can be estimated by Maximum Likelihood Method. The details are given in Box and Jenkins (1994).
In order to find the suitable ARIMA model, first the sample autocorrelation of prices were examined for different girth classes. The estimated autocorrelation function does not die out rapidly suggesting that the underlying process should be treated as nonstationary. Therefore, the first differencing was done to remove the trend. The autocorrelation and partial autocorrelation were again worked out for the differenced series. The autocorrelations for the differenced data are found to fall within 2 times of standard error. This indicated that the autocorrelations were not statistically significant. Because the sample autocorrelation or partial autocorrelation function neither tailed off nor cut off, it appeared that the mixed model is required. Therefore, the parameter values of and were varied and different combinations of ARIMA models examined. Based on the model selection criteria such as Mean Absolute Percentage Error (MAPE) the best ARIMA model was arrived at (Sivaram, 2007).
Results and discussions
Trends in current and real prices of teak wood Among the five different spline models fitted for the real prices, linear spline with discontinuities at the two knots is the best model for export class and girth class IV. The quadratic spline with discontinuities at the three knots is the best model for girth classes I, II and III. The functional form of the chosen spline models describing the real prices of teak wood and the graphical representation of the observed and predicted real prices are available in Sivaram (2008b). The rate of changes of real prices of teak worked out using linear spline model in different girth classes are given in Table 1.
Table 1. Rate of change of real prices of teak wood in different girth classes
Export class(1970-2006)
The trends in real prices of teak wood in export class based on linear spline model showed an increasing trend for the entire period. The rate of changes in different periods, x d” 1977, 1977 < x d” 1989 and x > 1989 are given by 196, 562 and 243, respectively.
Girth class I,II and III(1956-2006) With regard to girth class I, II and III, there was a decline in real prices during 1956-1967, then an increasing trend from 1968 to 1995 and then a decreasing trend in real prices during 1996-2006. All these three classes showed a rapid increase in prices for the period 1977-1995 and the rate of change is ranged from 467 to 943.
Girth class IV(1970-2006) As in the case of export class, the real prices of girth class IV also showed an increasing trend for the period 1970 to 2006 and the rate of increase ranged from 56 in 1999-2006 to 328 in 1977-1998.
The spline models indicated that there had always been positive growth rate in real prices of teak wood of Export Class and Girth Class IV. This might be due to the constant demand and also that the availability in those classes was small. Most of the teak wood produced and sold in a year was in Girth Class II and Girth Class III and generated most of the revenue from teak wood. The trends in these classes indicated the impact of government polices and acts. The National Forest Conservation Act, 1980 banned clear felling from natural forests and, therefore, the reduced supply during that period led to the price rise during the 1980s. The accelerated positive growth during the later part of 1980s and the first part of 1990s could be due to the Kerala Preservation of Trees Act, 1986 and the National Forest Policy, 1988 and stoppage of selection felling in 1988. The decline in real prices since the year 1995 could be due to globalization, increased wood import and availability of wood substitutes due to technology innovations. However, of late, the prices of teak wood is picking up in the market.
Forecasting of teak wood prices Among the ARIMA and ANN models, ARIMA model was chosen for forecasting because forecasting by ANN model was not sensible from the practical point of view despite ANN with log transformed prices showing lesser MAPE value than the ARIMA model (Fig. 9). The exact forecasting of current prices for the year 2007 for five broad girth classes is given in Sivaram (2007). The forecasts indicated that the higher girth classes viz., export class (185 cm and above), girth class I (150-184 cm) would fetch high prices than the lower girth classes might be due to higher demand for quality teak wood (Table 2). This means that that the high quality teak wood would fetch high returns in the market. Therefore, efforts should be made to produce quality teak wood.
Table 2. Forecasted percentage increase in teak wood prices using ARIMA model
|
Girth class |
Current price (INR/m3) -2006 |
Forecasted current price (INR/m3) -2007 |
Percentage increase |
|
Export |
57,270 |
69,830 |
21.9 |
|
I |
48,937 |
56,834 |
16.1 |
|
II |
44,295 |
46,231 |
4.4 |
|
III |
33,174 |
34,783 |
4.9 |
|
IV |
24,638 |
25,949 |
5.3 |
Fig. 9. Comparison of performance of ARIMA and ANN models using MAPE
General Observations
A State level forestry statistical database on various aspects forest sector collected from different sources is very important to know the trends in forestry sector in the State. This will, in turn, contribute to the development of national level database. Though the necessary action at the national level is happening, unless state forest departments are strengthened in creating and developing its own forest management information system and the forestry database, the data will not flow for national level compilation.
There are certain problematic areas in the collection of forestry statistics which need to be addressed through policy decisions and managerial interventions. There are quite a lot of estimates which are underestimated with respect to fire occurrences and area affected and extent of grazing and unauthorized collection of non-wood forest products. These are often not fully covered and reported by the field personnel or are mostly incomplete.
There are also details which are not recorded at the ground level though they can be made available. For example, exact details of site quality, timber extracted through thinning and felling are not properly recorded in Plantation Journals.
The non-reporting and underreporting severely affects the interpretation of recorded figures and its further use. For example, in GDP estimation, the value of the unrecorded production of NWFPs is considered as 10 times the value recorded by the State Forest Departments (Kolli and Rajeswari, 2008).
The required data need to be made available to evaluate the programme implementation such as afforestation/reforestation/social forestry, etc. There is no data available in the public domain on survival status of the plants/ success rate of the new plantations raised.
There are also areas (e.g. wood industries, export and import of forest products), which do not directly come under the jurisdiction of the state forest department but data are required for planning purpose. This calls for the linkage between the departments to improve the existing official statistics.
Collection of data from different sources by any single individual/group of individuals from various departments is a herculean task. The research institutes should essentially be involved in the methodology development and productive analysis of data and draw conclusions for policy development. These institutes should also be encouraged to takeup subsidiary studies which would complement the official forestry statistics.
The other general issues often cited and also highlighted in an earlier report (Sivaram, 2004) include the following:
Lack of coordination between the agencies
Non-availability of sufficient, usable and timely information
Inadequate usage of forestry statistics
Capacity building and
Lack of feedback system
However, the immediate need is that the Ministry of Environment and Forests and state forest departments need to resolve the procedural difficulties and take necessary actions to promote genuine reporting of forestry data so as to improve its quality. Simultaneously, government should encourage development/strengthening of state level forest management information system, forestry database and data mining activities so that data become useful information for forest managers and policy makers.
References
Box, G.E.P. and Genkins, G.M. 1994. Time series analysis forecasting and control. New Delhi, Pearson Education Inc.
Chundamannil, M. 1998. Teak plantations in Nilambur – an economic review. Peechi, Kerala Forest Research Institute. 71p.
Croxton, F.E., Cowden, D.J. and Klein, S. 1973. Applied general statistics. New Delhi, Prentice-Hall of India Private Limited. 754p.
Enters, P. 2000. Site technology and productivity of teak plantations in Southeast Asia. Unasylva, 51: 55-61.
Forest Research Institute. 1970. Growth and yield statistics of common Indian timber species Vol.II. Dehradu, Forest Research Institute.
Hair, J.F.; Anderson, R.E.; Talham, R.L. and Black, W.C. 2003. Multivariate data analysis. Singapore, Pearson Education Inc.
Haykin, S. 1999. Neural networks – a comprehensive foundation. New Delhi, Pearson Education Inc. 842p.
India. Ministry of Commerce and Industry. Office of the Economic Adviser to the Government of India. [Available at: http://eaindustry.nic.in]
India. National Informatics Centre. [Available at: http://modelling.nic.in/data_mining.htm]
Jayaraman, K. and Chacko, K.C. 1997. Productivity of teak and eucalypt plantations in Kerala. Peechi, Kerala Forest Research Insitute.
Kolli, R and Rajeswari, T. 2008. Forestry sector in GDP estimates. In: Training Workshop on Collection, Compilation, Validation and Dissemination of Forestry Statistics, Peechi, 21-25 April 2008. Lecture notes. Peechi, Kerala Forest Research Institute.
Krishnankutty, C.N. 1989. Long term price trend of timber in Kerala. Indian Journal of Forestry, 12(1): 7-22.
Krishnankutty, C.N. 1990. Demand and supply of wood in Kerala and their future trends. Peechi, Kerala Forest Research Institute.66p.
Krishnankutty, C.N. 1998. Timber price trends in Kerala. Peechi, Kerala Forest Research Institute. 51p.
Krishnankutty, C.N. 2001a. Teak price trends in Kerala state, India. Indian Journal of Forestry, 24(1): 1-7.
Krishnankutty, C.N. 2001b. Forecasting of teak prices in Kerala state, India, using autoregressive integrated moving average models. Indian Journal of Forestry, 24(2):119-122.
Krishnankutty, C.N. 2002. Factors influencing teak prices in Kerala. Indian Journal of Forestry, 25(1): 25-29.
Krishnankutty, C.N.; Chundamannil, M. and Sivaram, M. 2003. Teak wood price projections for Kerala state. In: International Conference on Quality Timber Products of Teak from Sustainable Forest Mangement, Peechi, 2-5 December 2003. Proceedings, Peechi, Kerala Forest Research Institute.
Krishnankutty, C.N.; Thampi, B. and Chundamannil, M. 2005. Wood balance study in Kerala and market survey. Peechi, Kerala Forest Research Institute. 54p.
Leech, J.W. 1998. Indicative estimates of hardwood volumes for the project: Hardwood plantations in the tropics and subtropics. Rome, FAO.
Montgomery, C.C. and Peck, E.A. 1982. Introduction to linear regression analysis. New York, John Wiley and Sons.
Pandey, D. and Brown, C. 2000. Teak: A global overview. Unasylva, 51(201): 3-13.
Seifert, J.W. 2004. Data mining: An overview. CRS Report for Congress. Washington D.C., The Library of Congress.
Sivaram, M. 2004. A database on forest resources of Kerala. Peechi, Kerala Forest Research Institute. 66p.
Sivaram, M. 2007. Comparison of prediction models developed by statistical and neural network techniques in applied forestry research. Peechi, Kerala Forest Research Institute. 57p.
Sivaram, M. 2008a. Projection of future availability of teak wood from forest plantations and its prices in Kerala State, India. In: Bhat, K.M. et al. Ed. Processing and marketing of teak wood products of planted forests. Peechi, Kerala Forest Research Institute. pp. 304-311.
Sivaram, M. 2008b. Computerized database on Kerala forest resources and data retrieval system. Peechi, Kerala Forest Research Institute. 46p.
VIEWPOINT: NATIONAL FORESTRY DATABASE MANAGEMENT;FUNCTIONAL REQUIREMENT STUDY
Sanjay S. Gahlout
National Informatics Centre, New Delhi- 110 003
Background
M
aintenance of proper statistics and records are essential for
the management of every sector. The forest is one of such
areas, which contributes majorly to the economy of the country. Collection of the forest related statistics is one of major issues for the management of forest resources, on a sustainable basis. Besides fulfilling the international commitments, the collection, compilation, validation and dissemination of forestry statistics is also urgently required for satisfying the national commitments for policy and planning. The present structure of statistical reporting needs to be revamped in order to improve the statistics of the forestry sector in our country.
Objective
Ministry of Environment and Forests (MoEF) is planning to improve the established mechanism for the collection of the forestry related data from the lowest level of hierarchy i.e. the range level. The data will be collected at the divisional forest office (DFO) and then given to the conservator of forest (CF) office for the validation and then transferred to the principal chief conservator forest (PCCF) office before final collection at the national level in the MoEF. The data collection mechanism includes the procurement and installation of the hardware and customized software at every level of hierarchy. The compilation of the data is another objective of the project, which will be done by the software developed. The electronic and paper dissemination of the data is one of the major objectives of the project. The data on the selective basis will be disseminated on the world wide web after proper validation and authentication from the authorized stakeholders of the data. In cut short the following are the core objectives of the NFDMS:
Create an electronic system, which consolidates data from all divisional offices for analysis.
To facilitate the generation of analysis/MIS reports for decision-making in the desired format or duly validated. This would also include
i. Publishing complete forestry statistics in India including export/import figures and mangrove statistics.
ii. Business intelligence and decision support infrastructure with online analytical processing (OLAP) capabilities. This would also provide the users a multi-dimensional and subject oriented view of the data warehouse.
iii. To create user or group specific data mart also called as departmental warehouses which will be based on the central repository.
iv. Online and web based access to the warehouse to various units.
l To enhance customer service and provide public access to the limited data and reduce the un-planned downtimes of e-applications and by
providing faster and greater access to remote customers.
Scope of Work
Logical Data Flow and Validation Process
The logical data flow and validation process depicts the flow of data as it would appear to the end user. The actual flow of data in the solution can be different. The key points are :
600 divisional offices are the field offices where the data originate. The data would be entered into the system from the divisional offices.
There are around 200 regional offices/PCCF offices which act as the data validation layer. The data from the divisional offices will be allowed to be available to the applications only when the regional offices validate and approve the data.
The regional offices consolidate into 33 state offices.
The state offices consolidate into a central data center which would be housed at some central location (may be NIC).
A disaster recovery site would be replicating the data from the central data center.
A copy of the data would also be replicated to MoEF office for analysis and reporting purposes.
The central data center would act as the datawarehouse and public portal where the role based reports and access would be provided.
Actual Data Flow to Achieve the Logical Data Flow and Validation Process The logical data flow represents the data as visible to a user of the application. In reality the data might not travel first to divisional officeàregional officeà state office àcentral data center. The application can be made in such a way that the data is entered into the central data center in asynchronous/synchronous mode and in parallel the regional, states and divisional offices are also updated.
The logical data flow, however, always remains same like the divisional level always enters the data and the regional level always validates the data. The applications will be configured appropriately to achieve these results.
The underlying architecture of the solution is web services based which utilizes the data warehouse features of the RDBMS servers.
Divisional level offices have low and unreliable connectivity to the central data center so an asynchronous mode of data transfer is proposed for them. Also the application should be self-sustaining so that each DFO is capable of working on its own and reach the data center for consolidation when and as the connectivity is available. Each divisional level office would be having a workgroup (low-end) database server which will be also loaded with NFDMS application and message queuing services. The divisional office users would use the local application and database for data entry. The captured data would be consolidated to the central datacenter in an asynchronous mode using the message queuing and web-services technology.
Regional offices would be using the central data center for normal operations. However, the relevant data (the data which needs to be validated by regional offices) would be replicated from the datacenter to the regional level offices in an asynchronous mode. Each regional office would be having a standard database server and message queuing services. Once the data is available at the local regional office, they would be able to use their local application and database servers to validate the data if the ISP link is down. Once the data is validated it would be available for use. These validated data information is then copied to the central data center in an asynchronous mode when the regional office works in an offline mode.
The solution has to be designed to maximize the security, consolidation, flexibility and modularity of all the components. The solution is to be modular in concept where each component of the solution is separated but integrated with each other. This will allow scalability, security and flexibility to the entire solution. Following different types of servers may be deployed for the solution.
Database server
Application integration server
Application server and portal server
Message queuing
System management server
Firewall server
Pictorial Representation of the Solution
Design and Database
The database of the information pertaining to all the three (or more) level of hierarchy has to be elucidated in consultation with all the stakeholders, primarily with the pilot units.
Software Design and Development
It will comprise at least of the following:
a) Design of a relational database management system (RDBMS) covering the information for computerized data access so that designed database can handle various queries by end users at every level of hierarchy.
b) Development of software covering the data and information for access by different agencies at the ministry, state, regional and district levels and public.
Major Milestones of the Solution
a) Procurement and installation of the hardware at every level of hierarchy with the specifications given.
b) Procurement and installation of the system software at every level of hierarchy.
c) Development and installation of the customized software for the forest data collection at every level of hierarchy.
d) Development and installation of the software for the dissemination of the information.
Output
The output of the complete solution will comprise at least
of the following:
a) Installation of the hardware at every level of hierarchy.
b) Development and installation of the customized software for the forest data collection at every level of hierarchy.
c) Development and installation of the software for the dissemination of the information.
Time Frame for Milestones
1. Scope of milestone – a: One year from the date of start.
2. Scope of milestone – b: In sync with the item (a)
3. Scope of milestone – c: Six months from the date of start.
4. Scope of milestone – d: Two months after the finalization item (c)
Item no. a to c should be done concurrently. After the development of item no. c its review and editing should be completed within two months. Item no. d should start after the item no. c is finished to the satisfactory level.
(Courtesy: India. Ministry of Environment and Forests. Survey and Utilisation Division. 2007. National forestry database management system: A vision. New Delhi, The author. pp. 60-66).
DATA REQUIREMENTS FOR THE VALUATION OF GREEN BELT DERIVED ECOSYSTEM GOODS AND SERVICES
Rajiv Pandey
Indian Council of Forestry Research and Education, Dehradun - 248 006
Introduction
F
orests play an important role in day to day life of every citizen
specially those who are living in and around forests and also in
environmental sustainability and supports for development of food production. It generates employment to the forest dependent and rural poor and can play a pivotal role in the rural poverty alleviation programmes. India is having 2.5 per cent of world’s geographical area and 1.8 per cent of world’s forests and supports 17 per cent of planet’s human population and 18 per cent of livestock population. However, the contribution of the forest has not been reflected properly in the system of national accounts due to non-availability of data for various produced goods and services. Moreover, the contribution of trees outside forests and green belt are either not accounted for or accounted under different sectors rather than forest sector. This ultimately has impact on the proper management and conservation of the forest in totality. Besides, the rapid changes in large scale human and biophysical processes – population explosion and migration, over-harvesting, changes in traditional land use and livestock rearing practices lead to decrease of the overall productivity of socio-ecological systems in terms of quality and quantity. This is critically disturbing the balance between the productivity of forest ecosystem and households dependency on forest. Therefore, at present proper policy formulation is needed, which should adhere to the demand from the forest, tree outside forests and green belt by the households and integrate sustainable forest productivity. This is not possible without allocating sufficient amount of funds against its worth under forestry sector. However, the lack of the economic value of these, which is either not available or grossly underestimated, if available, compelled the policy planners for its non-accounting in this sector. In this paper, emphasis is laid on the unaccounted contribution of green belt for the urban poor for its ecosystem goods and services. It also contains the different value of the green belt functions as well as estimation methods for its value. Further, this information fulfills the demand of the national forest programmes, polices and strategy processes, which strive to address cross-cutting issues such as poverty and food security related to the multiple functions of forests in social, economic and environmental contexts. Moreover, the United Nations Forum on Forests (UNFF) also underscore the need for improved data collection on a full range of goods and services of all types of forests and trees outside forest boundaries, based on rapid, cost effective and policy-oriented methods towards better forest policy formulation and national forest programme development.
Green Belt
According to Wikipedia, a green belt is a policy or land use designation used in land use planning to retain areas of largely undeveloped, wild, or agricultural land surrounding or neighbouring urban areas.
The very purpose of green belt policy are to:
protect natural or semi natural environments;
improve air quality within urban areas;
ensure that urban dwellers have access to countryside, with consequent educational and recreational opportunities; and
protect the unique character of rural communities which might otherwise be absorbed by expanding suburbs.
The green belt has many benefits for people:
Walking, camping, and biking areas close to the cities and towns.
Habitat for wild plants and animals.
Cleaner air and water.
Better land use of areas within the bordering cities.
A different/contrarian interpretation of the green belt’s effects/motivation (for example, suggested by economist Tim Harford) is that a green belt is created by residents to preserve the bourgeois status quo of those already living within the zone, and especially the advantage of landlords who profit from a scarcity of housing. In this interpretation, the stated motivation and benefits of the green belt are well-intentioned (public health, environment), but these benefits accrue as intentioned or claimed (for example, critics claim that only a small fraction of the population ever sets foot on the green belt for leisure purposes and a green belt is not strongly linked to clean air and water). Rather, the ultimate result of the decision to green belt a city is to maintain the middle class status quo, thus exacerbating high housing prices by concentrating demand within the zone and stifling competitive forces in general. Another area of criticism comes from the fact that, since a greenbelt does not extend indefinitely outside a city, it might spur the growth of areas much further away from the city core than if it had not existed, thereby, actually increasing urban sprawl. There are many examples whereby the actual effect of green belts is to act as a land reserve for future freeways and other highways.
Green Belt Ecosystem Derived Goods and Services
Ecosystem services are the conditions and processes through which natural ecosystems and the species which make them up sustain and fulfill human life. They maintain biodiversity and the production of ecosystem goods, such as seafood, forage, timber, biomass fuels, natural fibre, and many pharmaceuticals, industrial products, and their precursors. In addition to the production of goods, ecosystem services are the actual life-support functions, such as cleansing, recycling, renewal, and they confer many intangible aesthetic and cultural benefits as well (Daily, 1997). Ecosystems goods are generally tangible, material products that result from ecosystem processes; whereas ecosystem services are in most cases improvements in the condition or location of things of value.
Tangible Benefits
Beyond their aesthetic and ecological value, trees can contribute to the satisfaction of energy requirements as well as the daily food requirements of urban dwellers, particularly in the case of the poorest elements of society.
Food production through tree growing is common in many cities in Asia, Latin America and Africa (Yeung, 1987; Sanyal, 1985; Streiffeler, 1987; Ninez, 1985; Skinner, 1981). Fruit-trees are often an important component of urban home gardens besides the edible staple food items.
Wood fuel provides between 25 and 90 per cent of urban household energy supplies (Kuchelmeister, 1998). Poor urban households spend a significant proportion of their cash income in obtaining wood energy.
Principle sources of timber in urban areas are plantations, street trees, shelterbelts or windbreaks and greenbelts, parks and gardens.
Services
Green belt plays important role for improving the environment of urban areas.
Cleaning the air
Plants help remove pollutants from the air in three ways: absorption by the leaves or the soil surface; deposition of particulates and aerosols on leaf surfaces; and fallout of particulates on the leeward (downwind) side of the vegetation because of the slowing of air movement. Moreover, plants are effective sinks for pollution. Keller (1979) has quantified an 85 per cent reduction in lead behind a shelter-belt of trees. Soil effectively absorbs gaseous pollutants, including carbon monoxide, sulphur dioxide, nitrogen oxides, ozone and hydrocarbons. Trees
intercept dust: a belt of trees measuring 30 metres in width has been found to intercept almost all dust in the air. Trees also often mask fumes and disagreeable odours. Trees also help to increase the relative humidity of urban air through evapo-transpiration.
Modifying temperature extremes
Trees, shrubs and other vegetation help to control temperature extremes in urban environments by modifying solar radiation. The shade of one large tree may reduce the temperature of a given building to the same extent as would 15 air conditioners at 4,000 British thermal units (BTU), i.e. 4,220 kJ, in a similar but unshaded building. Energy saving through tree-planting around houses ranges from 10 to 50 per cent for cooling and from 4 to 22 per cent for heating (NAA/ISA, 1991).
Noise reduction
Excessive noise levels in cities contribute to ill health for both physical and psychological damage. Trees by refracting or dissipating noise therefore, reduce the risk of these damages.
Water use, reuse and conservation
Green belt can help in the protection of urban water supply, wastewater treatment systems and storm water management. Green belt has greatest potential of wastewater reuse in arid zones in developing countries (Braatz, 1994; Kuchelmeister, 1991 and 1998).
Soil conservation
Trees and forests are a means of soil conservation through organic matter deposition.
Biodiversity
Biodiversity of green belt may exist at genetic, species, and ecosystem level.
Genetic diversity: Insurance against change; opportunities for the future - diverse genetic traits may enable species to adapt to changing conditions or environment.
Species diversity: Pollinators for food crops - many creatures help to transfer pollen for reproduction purposes.
Ecosystem diversity: It is a resource of national and global importance.
Social Benefits
The green belt provides following social benefits to the society:
Improving the aesthetic quality of urban areas
The aesthetic and recreational value of green belt is appreciated by most urban dwellers. It fulfills certain psychological, social and cultural needs of the urban dweller (Dwyer et al., 1991).
Health
Parks and green areas provide opportunities for healthy physical activity. In addition, the passive benefit to physical and mental health of an urban landscape with trees has been documented in industrialized countries (Ulrich, 1984 and 1990); enjoyment of green areas may help people to relax or may give them fresh energy. Improving air quality through the planting of vegetation certainly has an impact on health particularly through decreased incidence of respiratory illnesses.
Employment
Tree planting can be labour intensive and provide work opportunities which may be especially important in poorer cities.
Education
Urban forests are increasingly appreciated in environmental education. Easily accessible trees and woodlands provide a vital facility for both formal and informal learning.
Recreation
Green areas greatly enhance outdoor recreation.
Community building and property value improvement
Public involvement with trees in towns can help strengthen neighbourhood communities by providing people with an opportunity to work together for the benefit of the local environment (NUFU, 1998). It also helps to increase the property value situated adjacent to these green areas (Webb, 1998; Morales et al., 1983; Kuchelmeister, 1998).
The Value of Green Belt
The list of goods and services that it can provide is immense. However, anthropogenic point of view, the ecosystem functions are important for the goods and services. The ecosystem functions are ‘the capacity of natural processes and components to provide goods and services that satisfy human needs, directly or indirectly’ (De Groot, 1992). For convenience, the ecosystem functions of green belt are also being defined into four primary categories (De Groot et al., 2000):
1. Regulation Functions
This group of functions relates to the capacity of natural and semi-natural ecosystems to regulate essential ecological processes and life support systems through bio-geochemical cycles and other biospheric processes. In addition to maintaining ecosystem (and biosphere) health, these regulation functions provide many services that have direct and indirect benefits to humans (such as clean air, water and soil, and biological control services).
2. Habitat Functions
Natural ecosystems provide refuge and reproduction habitat to wild plants and animals and thereby contribute to the (in situ) conservation of biological and genetic diversity and evolutionary processes.
3. Production Functions
Photosynthesis and nutrient uptake by autotrophs converts energy, carbon dioxide, water and nutrients into a wide variety of carbohydrate structures which
are then used by secondary producers to create an even larger variety of living biomass. This broad diversity in carbohydrate structures provides many ecosystem goods for human consumption, ranging from food and raw materials to energy resources and genetic material.
4. Information Functions
Because most of human evolution took place within the context of undomesticated habitat, natural ecosystems provide an essential ‘reference function’ and contribute to the maintenance of human health by providing opportunities for reflection, spiritual enrichment, cognitive development, recreation and aesthetic experience.
Valuing Ecosystem Functions, Goods and Services
The importance (or ‘value’) of ecosystems is roughly divided into three types: ecological, sociocultural and economic value.
Ecological Value
The ‘ecological value’ or importance of a given ecosystem is, therefore, determined both by the integrity of the regulation and habitat functions of the ecosystem and by ecosystem parameters such as complexity, diversity and rarity (De Groot et al., 2000). Since most functions and related ecosystem processes are inter-linked, sustainable use levels should be determined under complex system conditions (Limburg et al., 2002), taking due account of the dynamic interactions between functions, values and processes (Boumans et al., 2002).
Socio-Cultural Value
In addition to ecological criteria, social values (such as equity) and perceptions play an important role in determining the importance of natural ecosystems and their functions, to human society. Natural systems are a crucial source of non-material well-being and indispensable for a sustainable society. The socio-cultural value mainly relates to the information functions.
Economic Value
Economic valuation methods fall into four basic types, each with its own repertoire of associated measurement issues: (1) direct market valuation, (2) indirect market valuation, (3) contingent valuation and (4) group valuation.
1. Direct market valuation
This is the exchange value that ecosystem services have in trade, mainly applicable to the ‘goods’ (i.e. production functions) but also some information functions (e.g.
recreation) and regulation functions.
2. Indirect market valuation
If no explicit markets exist for services, one must resort to more indirect means of assessing values. A variety of valuation techniques can be used to establish the (revealed) willingness to pay (WTP) or willingness to accept compensation (WTA) for the availability or loss of these services.
Avoided cost (AC) Services allow society to avoid costs that would have been incurred in the absence of those services. Examples are waste treatment (which avoids health costs) by green areas.
Replacement cost (RC) Services could be replaced with human-made systems; an example is natural waste treatment by marshes which can be (partly) replaced with costly artificial treatment systems.
Factor income (FI) Many ecosystem services enhance incomes; an example is natural water quality improvements, which increase commercial fisheries catch and thereby, incomes of fishermen.
Travel cost (TC) Use of ecosystem services may require travel. The travel costs can be seen as a reflection of the implied value of the service. An example is recreation areas that attract distant visitors whose value placed on that area must be at least what they were willing to pay to travel to it.
Hedonic pricing (HP) Service demand may be reflected in the prices people will pay for associated goods; an example is that housing prices at beaches usually exceed prices of identical inland homes near less attractive scenery.
3. Contingent valuation (CV)
Services demand may be elicited by posing hypothetical scenarios that involve the description of alternatives in a social survey questionnaire.
4. Group valuation
Derived from social and political theory, this valuation approach is based on principles of deliberative democracy and the assumption that public decision making should result, not from the aggregation of separately measured individual preferences, but from open public debate.
Table 1 provides an overview of the classification of main functions, goods, services, its value type, method of estimation and data requirements that can be attributed to green belt derived ecosystems and their associated ecological structures and processes.
Database for Valuation in Totality
A wealth of information on forestry and other natural resources is available in unmanaged way. However, the availability and utilization of these resources for the policy planners are not readily available due to various reasons. Moreover, if it is available, it is not objective oriented. Therefore, proper database with proper and indentified objectives as per the expert consultation is needed for the various aspects of forestry, tree outside forests and green belt. It should also dealt with the spatio temporal distribution with a fixed periodicity to fulfill the defined purposes. Moreover, the sample study may also be appropriate to serve the purpose as it will utilize less resources. Moreover some data are needed to define the basic nature of the green belt. These are:
Size and shape of the area
Species identification
Density and growth
Supply of fuelwood, fodder, timber and staple foods
Biomass and organic carbon generated
Pollution deposition and absorption
Noise reduction
Temperature and humidity regulation
Use in water supply and wastewater treatment systems
Use as recreational, cultural and educational purposes
Employment generated for planting and maintenance
Summary
It can be concluded that the holistic view of the various functions, goods and services, which is directly or indirectly contributing for the human welfare is critical for valuation point of view. Moreover, the value in totality may be worked out either combining these all or deriving a single measurable indicator, which contains or reflects all the desired information either on sample basis or census basis depending on the availability of resources and precision required. These may be used either directly or for estimating the rates and ratio for the incorporation into the system of national accounts. This information may be used for various forestry and environment related issues at international level too.
Table 1. Physiographic zone wise growing stock (stems and volume)
|
Function |
Ecosystem processes and components |
Goods and services |
Value type |
Valuation methods |
Data requirements |
|
Regulation |
function - Mai |
ntenance of essenti |
al ecological processes |
and life su |
pport system |
|
Gas regulation |
Role of ecosystems in bio-geochemical cycles (e.g. O2/O2 balance, ozone layer, etc.) |
UVb-protection by O3 (preventing disease) Maintenance of (good) air quality Influence on climate |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost Avoided cost |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Climate regulation |
Influence of land cover and biol. mediated (e.g. DMS-production) on climate |
Maintenance of a favorable climate (temp., precipitation, etc.) |
Direct ecological value Indirect socio-culture value Indirect economic value |
Group valuation |
Spatio-temporal data of relevant indicators and value by heterogeneous group |
|
Disturbance prevention |
Influence of ecosystem structure on dampening env. disturbance |
Storm protection |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Water regulation |
Role of land cover in regulating runoff and discharge |
Drainage and natural irrigation |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost Factor income |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Water supply |
Filtering, retention and storage of fresh water (e.g. in aquifers) |
Provision of water for consumptive use(e.g. drinking, and industrial use) |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost Factor income |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Soil retention |
Role of vegetation root matrix and soil biota in soil retention. |
Maintenance of arable land. Prevention of damage from erosion/siltation |
Direct ecological value Indirect socio-culture value Indirect economic value |
Avoided cost |
Spatio-temporal data of relevant indicators and associated maintance or control cost (In field or lab condition) |
|
Soil formation |
Weathering of rock, accumulation of organic matter |
Maintenance of productivity on arable matter land |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost Factor income |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Nutrient regulation |
Role of biota in storage and re-cycling of nutrients |
Maintenance of healthy soil and productive ecosystems |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Waste treatment |
Role of vegetation and biota in removal or breakdown of xenic nutrients and compounds |
Pollution control/detoxification Filtering of dust particles Abatement of noise pollution |
Direct ecological value Indirect socio-culture value Indirect economic value |
Replacement cost |
Spatio-temporal data of relevant indicators and associated replacement unit cost (In field or lab condition) |
|
Pollination |
Role of biota in movement of floral gametes |
Pollination of wild plant species Pollination of crops |
Direct ecological value Indirect socio-culture value Indirect economic value |
Contingent valuation |
Willingness to pay for change in the services |
|
Biological control |
Population control through trophic-dynamic relations |
Control of pests and diseases Reduction of herbivory (crop damage) |
Direct ecological value Indirect socio-culture value Indirect economic value |
Contingent valuation |
Willingness to pay for change in the services |
|
Habitat fu |
nction – Provid |
ing habitat (suitable |
living space) for wild plan |
t and anima |
l species |
|
Refugium function |
Direct ecological value Indirect socio-culture value Indirect economic value |
Maintenance of biological and genetic diversity |
Direct ecological value Direct socio-culture value Indirect economic value |
Contingent valuation |
Willingness to pay for change in the services |
|
Nursery function |
Direct ecological value Indirect socio-culture value
Indirect economic value |
Maintenance of commercially harvested species |
Direct ecological value Direct socio-culture value Indirect economic value |
Contingent valuation |
Willingness to pay for change in the services |
|
Production |
functions – Pr |
ovision of natural re |
sources |
|
|
|
Food |
Conversion of solar energy into edible plants and animals |
Gathering of fruits, etc. Small-scale subsistence farming |
Indirect ecological value Indirect socio-culture value Direct economic value |
Direct valuation |
Market price |
|
Raw materials |
Conversion of solar energy into biomass for human uses |
Fuel and energy (e.g. fuel wood) Fodder and fertilizer (e.g. leaves, litter) |
Indirect ecological value Indirect socio-culture value Direct economic value |
Direct valuation |
Market price |
|
Genetic resources |
Genetic material and evolution in wild plants and animals |
Improve crop resistance to pathogens and pests Other applications (e.g. health care) |
Indirect ecological value Indirect socio-culture value Direct economic value |
Contingent valuation |
Willingness to pay for change in the services |
|
Medicinal resources |
Variety in (bio)chemical substances in, and other medicinal uses of, natural biota |
Drugs and pharmaceuticals |
Indirect ecological value Indirect socio-culture value Direct economic value |
Direct valuation |
Market price |
|
Ornamental resources |
Variety of biota in natural ecosystems with (potential) ornamental use |
Resources for handicraft, pets, worship |
Indirect ecological value Indirect socio-culture value Direct economic value |
Direct valuation |
Market price |
|
Information |
function – Pro |
viding opportunities |
for cognitive developmen |
t |
|
|
Aesthetic information |
Attractive landscape features |
Enjoyment of scenery (scenic roads, housing, etc.) |
Indirect ecological value Direct socio-culture value Indirect economic value |
Hedonic price Travel cost |
Willingness to pay for per unit use of the services |
|
Recreation |
Variety in landscapes with (potential) recreational uses |
Travel to natural ecosystems for eco-tourism, outdoor sports, etc. |
Indirect ecological value Direct socio-culture value Indirect economic value |
Travel cost |
Willingness to pay for per unit use of the services |
|
Cultural and artistic information |
Variety in natural features with cultural and artistic value |
Use of nature as motive in books, film, painting, folklore, architect., etc. |
Indirect ecological value Direct socio-culture value Indirect economic value |
Contingent valuation Replacement cost |
Willingness to pay for change in the services |
|
Spiritual and historic information |
Variety in natural features with spiritual and historic value |
Use of nature for religious purposes (i.e. heritage value of natural ecosystems and features) |
Indirect ecological value Direct socio-culture value Indirect economic value |
Contingent valuation Hedonic cost |
Willingness to pay for change in the services |
|
Science and education |
Variety in nature with scientific and educational value |
Use for school excursions, etc.Use of nature for scientific research |
Indirect ecological value Direct socio-culture value Indirect economic value |
Contingent valuation |
Willingness to pay for change in the services |
References
Boumans, R.; Costanza, R.; Farley, J.; Villa, F. and Wilson, M. 2002. Modeling the dynamics of the integrated earth system and the value of global ecosystem services using the GUMBO model. Ecological Economics, 41: 529–560.
Braatz, S. 1994. Urban forestry in developing countries: status and issues. In: Sixth National Urban Forest Conference, Minneapolis, Minnesota, 14-18 September 1993. Growing greener communities: Proceedings edited by C. Kollin; J. Mahon and L. Frame. Washington D.C., American Forests. pp. 85-88.
Daily, G.C. 1997. Introduction: What are ecosystem services? In: Daily, G.C. Ed. Natures services: societal dependence on natural ecosystems, Washington D.C., Island Press. pp. 1-10.
De Groot, R.S. 1992. Functions of nature: Evaluation of nature in environmental planning, management and decision making. Groningen, Wolters-Noordhoff.
De Groot, R.S.; van der Perk, J.; Chiesura, A. and Marguliew, S. 2000. Ecological functions and socio-economic values of critical natural capital as a measure for ecological integrity and environmental health. In: Crabbe, P.; Holland, A.; Ryszkowski, L.; Westra, L. Eds. Implementing ecological integrity: Restoring regional and global environmental and human health. Dordrecht, Kluwer Academic Publishers. pp. 191–214.
De Groot, R.S.; Wilson, M.A.; and Boumans, R.M.J. 2002. A typology for the classification, description and valuation of ecosystem functions, goods and services. Ecological Economics, 41: 393–408.
Dwyer, J.F.; Schroeder, H.W. and Gobster, P.H. 1991. The significance of urban trees and forests: Toward a deeper understanding of values. Journal of Arboriculture, 17(10): 276-284.
Keller, T. 1979. The possibilities of using plants to alleviate the effects of motor vehicles. TRRL Symposium Report, 513 DOE/DT.
Kuchelmeister, G. 1991. Urban and peri-urban multipurpose forestry in development cooperation - experience, deficits and recommendations. Unpublished report to Commission of the European Communities.
Kuchelmeister, G. 1998. Urban forestry in the Asia-Pacific Region - status and prospects. Rome, FAO.
Limburg, K.E.; O’Neil, R.V.; Costanza, R. and Farber, S. 2002. Complex systems and valuation. Ecological Economics, 41: 409–420.
Morales, D.J.; Micha, F.R. and Weber, R.C. 1983. Two methods of evaluating trees on residential sites. Journal of Arboriculture, 9(1): 21-24.
National Arborist Association. 1991. The importance of large tree maintenance in mitigating global climate change. Amherst, National Arborist Association.
National Urban Forest Unit. 1998. Trees matter: The benefits of trees and woods in towns. London, National Urban Forest Unit.
Ninez, V. 1985. Working a half potential: constructure analysis of home garden programmes in the Lima slums with suggestions for an alternative approach. Food and Nutrition Bulletin, 7(3): 8-14.
Sanyal, B. 1985. Urban agriculture: who cultivates and why? A case study of Lusaka, Zambia. Food and Nutrition Bulletin, 7(3): 15-24.
Skinner, G.W. 1981. Vegetable supply and marketing in Chinese cities. In: Plucknett, D.L. and Beemer Jr, H.L. Eds. Vegetable farming systems in China. Boulder, Westview Press.
Streiffeler, F. 1987. Improving urban agriculture in Africa: A social perspective. Food and Nutrition Bulletin, 9(2): 8-13.
Ulrich, R.S. 1984. View through a window may influence recovery from surgery. Science, 224: 420-421.
Ulrich, R.S. 1990. The role of trees in wellbeing and health. In: Fourth Urban Forestry Conference, St Louis, Missouri, 15-19 October 1990. Proceedings edited by P.D. Rodbell. The author.
Webb, R. 1998. Urban and peri-urban forestry in South-East Asia: A comparative study of Hong Kong, Singapore and Kuala Lumpur. Rome, FAO. (draft)
Yeung, Y. 1987. Examples of urban agriculture in Asia. Food and Nutrition Bulletin, 9(2): 14-23.
FORESTRY STATISTICS REPORTING SYSTEM- A CRITICAL PROCESS ANALYSIS TOWARDS ITS REALIZATION
Raman Nautiyal
Indian Council of Forestry Research and Education, Dehradun – 248 006
Introduction
F
orests and forestry provide a host of goods and services to the
mankind, most of which are unrecorded and underestimated. The
influence of forest based products, organized or unorganized, on general rural economy is too high to be ignored. However, there has been a general lethargy in estimation of the contribution of the forestry sector to the Indian economy, with similarities with other developing countries. Concerns about the quality of estimates constructed from the available forestry data have been expressed not only in the highest national forums, but also in various international forums. This is contrary to the fact that India has been a leader in statistical reporting since centuries, with Arthshastra and the famous Ain-e-Akbari taking the lead. Introspection and analysis is now important to build the future of statistical reporting in respect of the forestry sector of India.
Data constitute the building blocks of policy and research. With a shift in definitions of forestry-based indicators of development, introduction of a plethora of technicalities and increasing focus on forests as a resource to be conserved than exploited, the data needs have changed drastically. It has introduced the need of application of technology in reporting. Time constraint and urgent need of information requires data of high quality and integrity to be delivered with a minimum time lag, limiting to zero. How is it possible to ensure the data availability and a high quality of reporting simultaneously within a short span of time is the subject mater of discussion with the people who actually provide data. It is well known fact that we may have grand plans with grander intentions of implementing them; ultimately it is the lowest official who can make them or break them with the quality and reliability of figures he enters in the basic data form.
Global Importance of Data
Isolation is passé. With nature transcending political boundaries, environment has become a global concern. Any policy decision by a government on environment is bound to affect the whole world order. Needless to see thousands attending Bali, raising concerns of global degradation in environment and discussing ways and means to ensure the availability of resource for our future generations. Sustainability is the buzzword today.
Regular global assessment of forests is now being conducted by international organizations such as FAO of UN and International Tropical Timber Organization (ITTO). Sharing of information by various organizations has become the order of the day as it helps a lot in validation. Why validation? At stake is the exchange of money in order to strike a balance between the consumers and producers with a common aim to check over-exploitation of scarce resources.
The most important of all is the issue of climate change followed by certification, with an interlinking between the two. Forest certification as followed by the international community is to ensure that forest products in any form come from sustainably managed forests. By linking it to the economy (i.e. import) the issue is becoming one of the major concerns of the consumers. This will definitely have a long-term impact on the export of forest products from uncertified forests. The entire process of forest certification in turn depends upon data transformed into precise and meaningful estimates. Moreover, the member countries of ITTO, which includes India, agreed to strive for an international trade in tropical timber from sustainably managed forests way back in 1990 and known as Year Objective 2000. However, an assessment was made in 2000 according to which the tropical countries had made considerable progress in formulating and adopting policies compatible with the objective but no significant progress was found in implementing these policies. A re-commitment was made towards achieving exports of tropical timber and timber products from sustainably managed sources, renaming this commitment as ‘ITTO Objective 2000’. It remains a central goal of the organization, supported by renewed efforts to raise the capacity of government, industry and communities to manage their forests and add value to their forest products, and to maintain and increase the transparency of the trade and access to international markets.
Coming to climate change and claiming carbon credits, again estimation has a very important role to play. A scientifically (statistically) sound methodology to estimate the growing stock, coupled with the will to measure and provide data and build regular estimates, is essential to take logical decisions in time for framing policies for the forestry and environmental sector vis-à-vis the international concerns about the same. Further, it is essential to identify the indicators that can convey the health of the sector in a concise and precise form. Say, fifteen parameters that can comprehensively describe the status of India’s forests.
In addition to the national interest, the commitments of the government of India to various international organizations have also to be fulfilled. One such commitments is to provide forest related data to the International Tropical Timber Organization, which then shares it with FAO and other interested parties. Being a signatory to the International Tropical Timber Agreement (ITTA) of the ITTO, India is required to file annual data on demand and supply, production and consumption and import and export of forest products. In absence of data it also becomes difficult to give suggestions or comment on the queries of International Standard Industrial Classification (ISIC), Revision 4, regarding forestry, logging, gathering of all non-wood forest products and support services to forestry and logging. Besides, data for FAO outlook studies is also required to be provided.
History of Forestry Statistical Reporting
Historically, the statistical reporting in respect of forestry sector in India (SRI) is conducted at the following two levels: States; and Centre including all 35 States and Union Territories (UTs). The state forest departments (SFDs) are the primary source of forestry statistics. At state level, again two data sources could be distinguished viz. (i) Working Plans; and (ii) Annual Administrative Reports. The Central (All-India) reporting makes use of data supplied by States and data collected from other central agencies.
The working plans date back to 1856, when the scientific forestry started in the country. Dr. Brandis prepared the first forest working plan for Pegu Yomo Forests of Myanmar. The next milestone was laid by D’ Arcy in 1891, who wrote a treatise on preparing Working Plans highlighting importance of stock-mapping with strip sampling. Still further, Ribbentrop prepared a Working Plan Code in 1929 for Uttar Pradesh using strip surveys and stock-maps. After Independence, Seth (1952) made further contributions to the working plan system. The second source of data from SFDs are the Annual Administrative Reports (AAR), which are as old as the working plans and include data on plan implementation, administrative aspects and financial outcome. Reports of Forest Divisions aggregated at the circle and state levels form the basis of AAR.
Until 1984, the Central Forestry Commission (CFC), working directly under the Central Board of Forestry, was responsible for the task of data collection and post-processing dissemination. As regards land use and allied data, the Directorate of Economics and Statistics in the Ministry of Agriculture brings out the Indian Agriculture Statistics on an annual basis, which contains land use statistics including forestry and wooded areas. In 1976, the National Commission on Agriculture (NCA) made a very thorough study of the forest statistical reporting system of the country, looked into emerging information needs, and made comprehensive recommendations for improvement of the forest statistics at the Central level (NCA – 1976). An important outcome was the Forest Survey of India, established in 1981 for the following two categories of primary data collection and reporting; (i) The State of the Forest Report which is a biennial publication based on nationwide high resolution satellite data; and (ii) National forest inventory based upon field sampling using sample plots covering 10 per cent of the districts of the country every 2 years.
National Requirements – GDP
The indicator of growth of a sector on a national (macro) scale is its contribution to the Gross Domestic Product (GDP) of the country and is expressed as an estimated percentage of the total GDP. This particular indicator has not been very encouraging. As shown below, the share of the forestry sector to the GDP of India has been on a steady decline since the 1950s, rising marginally during the early 1980s Table 1 and Fig. 2. Main reason for this trend has been the encouraging support given to conservation and not exploitation. A simple maxim followed by the Central Statistical Organization in determining GDP is ‘Cut and count’. With emphasis being now laid on conservation, the forestry sector is providing more services than goods. Thus, the GDP share is not the proper indicator to judge the growth of the forestry sector in the national scenario.
Table 1. The decadal contribution of the forestry sector to the GDP of India
|
Year |
Share |
|
1950-51 |
2.6 |
|
1960-61 |
1.9 |
|
1970-71 |
1.8 |
|
1980-81 |
2.2 |
|
1990-91 |
1.6 |
|
2000-01 |
1 |
|
2005-06 |
0.7 |
Fig. 1. The decadal trend of contribution of forestry sector to GDP of India
International Requirements
The reporting system followed by international organizations and stakeholders in the forestry sector can be divided into two main categories with sub-categories: removals and production on one side and trade on the other. While former contains information about removals from forests and production of goods by forest based raw material and also the comparison of same goods produced by materials other than those coming from forests, the latter mainly pertains to the trade in primary and secondary products coming from forest and wood based industries.
The data of forest products is provided to the ITTO in specially designed formats known as Joint Forest Sector Questionnaires (JFSQ) (Table 2) which are well-known as JQ. The JQ system is a continually under review and is dynamic in the sense that it evolves with the time and policies. JQ1 is designed for removals and production while JQ2 for import and export. The removals have a main head – round wood further classified into two broad heads, namely wood fuel, including wood for charcoal and industrial round wood (wood in rough). The later is further classified into three subheads, saw logs and veneer logs; pulpwood (round and split) and other industrial round wood. All these heads have two main sections, coniferous and non-coniferous.
The production has many parameters with broad heads being wood charcoal, chips and particles, residues, sawn wood, wood based panels, wood pulp, recovered paper, paper and paper board, etc. Due emphasis is also given on the nature of raw material – coniferous, non-coniferous and tropical. Thus, ITTO is not just about tropical wood but also of other forest products.
The major international statistical reports that are brought out are:
1. Annual review and assessment of the world timber situation (ITTO)
2. Forest Products (FAO)
3. Forest Products Annual Market Review {United Nations (FAO)}
4. State of World’s Forests (FAO)
The international community and their reporting systems are mainly concerned about the following:
1. Logs, sawn wood and veener, plywood
2. Secondary processed products
3. Lesser used species
4. Particle board
5. Fibre board
6. Wood pulp
7. Paper and paper board
8. Industrial round wood
9. Illegal logging issues
Table 1. Physiographic zone wise growing stock (stems and volume)
|
Format code |
Format name |
Type of information dealt with |
|
JQ1 |
Production |
Removals of wood – round wood, including wood fuel Production of charcoal, chips, particles, pulp, paper, paper board, particle board, etc. |
|
JQ2 |
Trade |
Export and import of forest products |
|
DOT1 |
Import |
Country-wise import – information processed by ITTO |
|
DOT2 |
Export |
Country-wise export – information processed by ITTO |
|
SP1 |
Trade |
Trade in secondary wood and paper products like processed sawn wood, packing equipment, paper, paperboard, writing paper, printed articles, etc. |
|
ITTO1 |
Estimates |
Production and trade estimates |
|
ITTO2 |
Species |
Trade in tropical species |
|
ITTO3 |
Miscellaneous |
Subjective – comments on trade, deviations, tariffs, forest law, plantations, etc. |
|
ECE1 |
Species |
Trade in round wood and sawn wood: temperate species |
|
EU1 |
Trade |
Trade with countries outside EU (European Union) |
|
EU2 |
Removals |
Removals by type of ownership |
|
EU3 |
Species |
Trade in saw logs/pulpwood and other |
|
JQ2 |
Cross-reference |
Cross-references and validation |
|
SP1 |
Cross-reference |
Cross-references and validation |
Some of the major broad definitions of the terms used in the international reporting systems are as follows:
|
Term |
Definition |
Reported in |
|
Removals |
Volume of all trees, living or dead, that are felled and removed from the forest, other wooded land or other felling sites, includes recovered natural losses, period removal of non-stem wood, excludes bark and other non-woody biomass, any wood that is not removed. |
Cubic meters (CUM) under bark |
|
Production |
Solid weight or volume of all production of forest products, includes products immediately consumed for production of other products (e.g. pulp), excludes veneer sheets used for plywood production within the same country. |
CUM/metric tonnes (depending upon the product) |
|
Industrial roundwood-wood in the rough |
Roundwood that will be used in the production of other goods and services (except source of fuel). |
CUM under bark |
|
Sawlogs and veneer logs |
Roundwood that will be sawn (or chipped) lengthways for manufacture of sawnwood or railway sleepers (ties) or used for production of veneer (mainly by peeling or slicing) |
CUM under bark |
|
Pulpwood round and split |
Roundwood that will be used for the production of pulp, particle board or fibreboard |
CUM under bark |
|
Other industrial round wood |
Roundwood that will be used outside the forest processing sector for the production of other goods and services (except as fuel) |
CUM under bark |
|
Wood chips and particles |
Wood that has been deliberately reduced to small pieces during the manufacture of other wood products and is suitable for pulping, for particle board and fibre board production, for use as fuel or other purposes, excludes chips made directly from roundwood. |
CUM solid volume excluding bark |
|
Wood residues |
Volume of roundwood left over after the production of forest products in the forest processing industry and not been reduced to chips and particles |
CUM solid volume excluding bark |
The production side of the forestry sector also needs to be examined closely. Somewhere down the line we have taken the state forest departments as synonyms of the national forestry sector. Sector is a super set with state forest departments as one of the subsets of this superset. With the advancement in social and agro forestry, joint forest management, and the rising interest of business houses like ITC in forestry, the sectoral outlook needs to be well-defined. Confusing or limiting the sector with the state forest departments is also, to some extent, responsible for the pseudo-estimates as far as national economy is concerned.
Economic Weights of the Parameters Reported Upon
Based on the past experience of ICFRE in management of data related to the forestry sector, both collection and dissemination, the parameters covering the forestry sector of India can be divided into three main categories according to their importance in understanding the economics of the Indian forestry sector and their thematic contribution to the national economy, policy and support. Those that are important to be measured for economic considerations constitute level 1; ones who are important for policy framework, planning and management constitute level 2; and the third, level 3, are those that are required for refinement of information, support decision-making and provide, in tandem with the other two, a bird’s eye perspective of the general health of the forestry sector of our country (Level 3). While level 1 parameters are essential to answer some of the most important questions related to the economy of the forestry sector, level 2 are required for formulating the policy framework. Level 3 parameters are useful for relating various policy issues, if included in the database. Table 3 below gives the parameters included in the three categories:
Table 3. Classification of the parameters on which statistical reporting is based upon
|
Level 1 parameters |
Level 2 parameters |
Level 3 parameters |
|
Production of charcoal, chips, wood residues
Wood based panels, veneer sheets, plywood and paper
Fibre board, Medium Density Fibre (MDF) board
Coniferous and non-coniferous pulp
Industrial wood removals and production
Recovered paper, fuelwood
Non-wood Forest Products
Trade in secondary wood products
Employment generation
|
Area under ownership
Establishment
Research, wildlife and socio-economic parameters like forest villages
Forest offences
Plan outlay
Silviculture- Seed Production Areas, Clonal and Seedling Seed Orchards
Forest nurseries
|
Pulp segregated into mechanical, chemical, sulphate bleached, unbleached, sulphite bleached, unbleached, Dissolving
Paper and paper board segregated into graphic, newsprint, uncoated mechanical, uncoated wood-free, coated, sanitary, household, packing
Wildlife related, eco-tourism
Meteorology
Air and water quality parameters
|
Present Status of Forestry Databank – Parameters Recorded and Disseminated and the Status of Non-Response
The present status of the national forestry databank is not at all rosy. There are glaring and huge gaps in the databank that make the entire exercise of estimation and analyzing demand and supply worthless of being taken up. The Indian Council of Forestry Research and Education (ICFRE), which under a mandate from the Ministry of Environment and Forests, Government of India, collects, processes, validates and disseminates statistics pertaining to the forestry sector of India, publishes two bulletins related to the subject. One, the quarterly Timber/Bamboo Trade Bulletin (TBTB) contains the prices of eight important timber species and bamboo from 19 different markets of the country, while the other, Forestry Statistics India (FSI) is a biennial publication that covers 17 parameters across 77 tables in (Table 4). The table below gives the parameters on which data are collected and disseminated:
Table 4. Details of parameters on which data are collected for the Forestry Statistics India
|
Chapter no. |
Title of the chapter |
Tables included |
|
Chapter 1 |
Demographic data |
Distribution of population and sex ratio |
|
Chapter 2 |
Area |
Distribution of geographical area and actual forest cover
Actual recorded forest cover – comparative situation
Area by ownership
Forest area by composition
Area under encroachment
|
|
Chapter 3 |
Diversion of forest area |
Statement of compensatory afforestation under FCA, 1980 |
|
Chapter 4 |
Land use and soil conservation |
Statewise wastelands of India
Category – wise wastelands of India
State – wise and category – wise wastelands of India
|
|
Chapter 5 |
Afforestation |
Afforestation on forest land |
|
Chapter 6 |
Forest management |
Progress of joint forest management
Seed production areas
List of vegetative multiplication gardens
Seed orchards
Seedlings raised
|
|
Chapter 7 |
Wildlife |
Wildlife sanctuaries in India
National parks in India
State – wise number of national parks, sanctuaries with their area
Eco-development project-IX Plan
Funds released to states under project elephant – IX Plan
Project Tiger fund release
Statement showing year – wise position of funds released and expenditure during IX Plan
Population of tigers in the country as reported by the states
Name of the tiger reserves in tiger range states with year of creation and area
Biosphere reserves
|
|
Chapter 8 |
Livestock and fodder |
State – wise livestock in India
Area under fodder crop, permanent pasture and other grazing lands
State – wise estimated dry and green fodder production
|
|
Chapter 9 |
Forest offences |
Offences under the Indian Forest Act
Offences under the Wildlife Protection Act
Forest fires
Seizure of wildlife articles
|
|
Chapter 10 |
Plan-wise progress |
Centrally sponsored schemes and assistance for afforestation in degraded forests
Annual plan – outlay (forestry and wildlife)
Agreed outlay for IX Plan for ecology and environment
Plan outlay for ecology and environment
|
|
Chapter 11 |
Wood based industries |
Indian paper industry
Wood and non-wood based paper and paper products
Information on wood based factories
|
|
Chapter 12 |
Forest product and energy consumption |
Production of timber and fuelwood
Production of sal seeds and tendu/kendu/bidi leaves
Production of gums and resins
Production of canes/rattans and bamboos
Production of other NTFP
|
|
Chapter 13 |
Revenue and expenditure |
State – wise forest revenue and expenditure
State – wise expenditure on forestry research
|
|
Chapter 14 |
Education and training |
Details of forestry training institutions |
|
Chapter 15 |
Organization |
State – wise number of territorial and functional circles, division and ranges in the forest department
Forest personnel/staff in position
Forestry research institutions (under the state government)
|
|
Chapter 16 |
Import and export |
Export statistics of forest products
Import statistics of forest products
|
|
Chapter 17 |
Economic indicators |
Gross domestic product for forestry sector |
Trends in Statistical Reporting
Past Trends Outturn of timber Forests in India have been fulfilling the demand for timber for long. The contribution of the forestry sector to the national income of India and to its economy has been immense. The first attempts to estimate the total outturn of of timber (roundwood in rough, industrial roundwood removals, etc.) were made by the Department of Economics and Statistics, Ministry of Agriculture,Govt. of India in the annually published India Forestry Statistics. Estimates of the outturn do have gaps, but they present a fairly good picture of removals of timber from the forest. The outturn of timber increased from 25,78,000 cubic meters in 1947-48 to 6714000 cubic meters in 1971-72. The following Fig. 2-5 gives the general trend from 1947 onwards upto 1972:
Fig. 2. Past trends in removal of timber- outturn (Source: India Forest Statistics)
Fig. 3. Past trends of outturn of roundwood (Source: India Forest Statistics)
Fig. 4. Roundwood as a percentage of timber (Source: India Forest Statistics)
Fig. 5. Recent trends in timber production in India
Current scenario The total removal of roundwood in 2005 has been estimated to the order of 2800000 cubic meters. Of this coniferous comprised of 533000 cubic meters, while non-coniferous comprised of the remaining 2351000 cubic meters. Estimates of timber removals in India from 2004 and 2005 are:
|
|
|
2004 |
2005 |
|
Roundwood |
1,000 m3 |
2,868.90 |
2,884.40 |
|
Industrial roundwood (wood in the rough) |
1,000 m3 |
9,971.73 |
9,534.88 |
|
Sawlogs and veneer logs |
1,000 m3 |
2,161.77 |
2,067.07 |
|
Other industrial roundwood |
1,000 m3 |
1,716.16 |
1,640.98 |
The estimates for import of timber during 2004 and 2005 are as under:
|
|
|
20 |
04 |
20 |
05 |
|
|
|
Quantity |
Value |
Quantity |
Value |
|
Roundwood |
1,000 m3 |
3,764.11875 |
30,694,606,935 |
4,173.29875 |
37,404,217,805 |
|
Industrial roundwood (wood in the rough) |
1,000 m3 |
3,740.37875 |
30,681,482,924 |
4,170.20500 |
37,392,020,193 |
|
Sawnwood |
1,000 m3 |
102.69600 |
566,008,109 |
69.50400 |
608,169,865 |
The estimates of export of timber during 2004 and 2005 are as under:
|
|
20 |
04 |
20 |
05 |
|
|
Quantity |
Value |
Quantity |
Value |
|
Roundwood |
0.35875 |
1,550,354 |
5.24375 |
50,625,465 |
|
Industrial roundwood (wood in the rough) |
|
|
4.34500 |
47,037,132 |
|
Sawnwood |
13.01300 |
180,332,809 |
1.18000 |
9,423,591 |
Non-response The non-response to the data requirements and demands of information is the main reason for underestimation of the contribution of the forestry sector of India to the national economy. The non-response of furnishing data varies from as low as 3.57 per cent to as high as 82.1 per cent. These figures are based on the number of tables reported and total number of tables in respect of state forest departments as required for Forestry Statistics India 2005, the flagship publication of ICFRE related to Forestry Statistics. The states have been identified as highly responsive, moderately responsive, highly non-responsive and minimal responsive based on these percentages. The table below gives the number of states in each category:
Table 1. Physiographic zone wise growing stock (stems and volume)
|
Measure of non-response |
Percentage of non-response |
Number of states |
|
Highly responsive |
0.1 – 10 |
3 |
|
Moderately responsive |
10.1 – 20 |
2 |
|
Highly non-responsive |
20.1 – 40 |
2 |
|
Minimal responsive (stubborn) |
40.1 – 90 |
6 |
Rest of the states have submitted complete data. The estimates to be submitted to the various organizations depend upon the availability of data for the Forestry Statistics India.
An in-depth analysis of reasons for the gaps in data is essential to plan a mechanism that can yield results. When compared to agriculture, the statistical reporting in the forestry sector seems to suffer from an absence of a well-oiled network that can provide data on a sustained basis to a well-designed central database. The road from the top of the network right down to the bottom reveals some disturbing yet interesting facts about the statistical reporting system, which was very much in place and successful in providing data not very long ago. In fact, the very foundation of data within the state forest departments lies in the concept of Working Plans, which provide complete data, and also in the annual reports submitted on a regular basis to the state governments. One school of thought is that working plans provide a basis for sustainable management of forests, thereby looking into the issue of forest certification.
Most of the states report NA for as simple a parameter as revenue and expenditure. It is also not clear as to what NA stands for – Not Available or Not Applicable. The following are the possible reasons for NAs, even though data may be available somewhere:
1. Differences in terminologies One of the major problems in getting the data from the field is heterogeneity in terms. The diversity in terminologies of parameters makes it very difficult for the field staff to really understand the meaning of the fields to be filled in. This generally results in fields being returned unfilled or marked as NIL or NA.
2. Weak or absent statistical cells The reporting units in state forest departments are weak. In many cases, they just function in the name of a unit. Inadequate staffs, absence of facilities and computing prowess coupled with poor capacity building programmes have become the bane of statistical reporting. In some of the departments there are no exclusive statistical units. The reporting work has been delegated to certain offices that have taken the responsibility in addition to their main mandate, resulting in low priority given to this important work.
3. Heterogeneity in units The units of measurement of like observations also differ from state to state. Bamboo, for example, is reported in notional tonnes, running metres, cubic metres, numbers and metric tonnes. Similar is the case with some other parameters. To add to the problem, there are no scientific conversion factors from one unit to the other. The net result is the figures are not amenable to mathematical treatment. In some cases the units are too subjective, as head loads. It is not clear as to what is the measurement of a headload. It is not unreal to assume that the weight or volume of a headload differs from state to state, may be similar for a group of states. Same is the case with bundles.
4. Lack in keeping pace with technology The pace of technological advancement is much more than what the forestry sector has coped up with, and with inbuilt diversity. There are some SFDs that are networked at the range level, quite in contrast with absence of even obsolete electronic data processing devices at the division level. Where present, the analytical capabilities are low, resulting in a technological cloud where there is concentration of gadgets but a low knowledge base for their operation.
5. Identification of data sources Data sources for each of the parameter being assessed should be identified and mapped to the national database. Inbuilt validation and conversion factors will help in automated estimation of parameters of interest.
6. Untrained and aged staff The average age of the forest department staff deployed in the field is nearing fifty years. A good number of the staff is nearing retirement. At this age it has no inclination to take up computing and learn the nuances of technology. Moreover, their workload doesn’t inspire them to take up additional work.
Issues Presented for Resolution
Estimation of Illegal/Unrecorded Removal
Assessment of information needs
Major exercise of assessment of information needs is essential to be carried out for each state, synchronized for each region and finally synthesizing into those of the country. The final output that is required, once finalized, will then determine the course of reporting and estimation. The straight jacket solution of what is available and what can be the output may not work for the forestry sector as there are too many parameters and diverse outputs are required, which may be dynamic with time.
Setting Up/Strengthening Statistical Cells
Each state forest department needs to be equipped with statistical cells/units for supervising the reporting mandate. Mere setting up of cells may not be sufficient. They have to be well-organized units with trained and skilled manpower, and possibly of a separate cadre.
Assessment of functional requirement
Once established, the minimum functional requirement of these units needs to be assessed for each SFD as regards to the computing capabilities, databases and skill development. Ways and means
have to be identified for fulfilling these requirements on a priority basis.
Homogenizing Manual
The diversity in the forest administration needs to be studied thoroughly and manual for data collection imbibing the unique features of measurement and analysis should be prepared. Detailed guidelines on data sources, what to measure and how and methodology of reporting should be a part of this manual. Adoption of internationally recognized ITC (HS) code for classifying forest products in the SFDs will ensure the correct mapping of production to JQ1 and JQ2.
Data mining and warehousing
A data mining and data warehousing project needs to be implemented in the forest department to fill in the gaps in data that have occurred due to slackness in reporting work. The filling of gaps is important to have a complete time series on data for forecasting and analyzing demand and supply, thereby enabling policy decisions on the sector. Relational databases, knowledge based expert systems, Geographical Information System (GIS), Distributed Query Capabilities over Internet, Virtual Private Networks (VPN) and other technological implementation will augment the speed of data mining programmes.
Capacity building
Once the detailed technical programme on forest statistical system is prepared, a constructive capacity building programme needs to be implemented in each of the thirty-five SFDs. The capacity building programme should be unique for a group of SFDs having similar lags in technology and knowledge base.
References
Behari, B. and Nautiyal, R. 2007. National forestry database management system (NFDMS): Theme, concepts and vision. In: India. Ministry of Environment and Forests. Survey and Utilization Divison. National forestry database management system – a vision. The author. pp. 1-11.
Kishwan, J.; Sohal, H.S.; Nautiyal, R.; Kolli, R. and Yadav, J. 2008. Statistical reporting in Indian forestry sector: Status, gaps and approach. International Forestry Review, 10(2): 331- 340.
Mishra, R.P. 2007. National forestry database management system (NFDMS): Theme, concepts and vision. In: India. Ministry of Environment and Forests. Survey and Utilization Divison. National forestry database management system – a vision. The author. pp. 29-34
GIS INTEGRATED SAMPLING DESIGN FOR FOREST INVENTORY IN INACCESSIBLE AREAS
Rajesh Kumar and Prakash Lakhchaura
Forest Survey of India, Dehradun- 248 195
Introduction
F
orests have acquired increasing importance in the recent past for
their role not only in meeting the material requirements but also for
their ecological and environmental functions. Therefore, accurate and up-to-date information on forest resources is of paramount importance for formulating policies. Some of the important parameters used for measuring forest resources are forest cover, growing stock, annual increment, species composition, biodiversity, non-timber forest products, etc. Forest managers, planners and policy makers need information about availability of wood from important tree species growing in and outside forest areas. Detailed information on distribution of timber species, volume, biomass, number of stems, regeneration status, etc. within different zones and regions of the country is highly useful for effective planning.
History of Forest Inventory
With the start of scientific management of forests in India in 1863 field inventory on a systematic basis started for the preparation of the ‘Working Plans’ at the division level. This was extended to almost entire forest area of the country and is continuing even today. Such inventories were for divisional level and for different time frame. However, such inventories were not organised to generate estimates at state/national level for a given time frame. Field inventory of unexplored forest areas started after the launch of a FAO/UNDP/GOI project named as Pre-Investment Survey of Forest Resources (PISFR) in 1965 which led to the foundation of NFI.
From 1965 to 1981, Forest inventory was confined to certain project areas for setting up wood based industries and the sampling design was adopted as per prevailing condition of areas. In 1981, National Forest Inventory (NFI) scheme was launched with the creation of Forest Survey of India (FSI).
The country was divided into grids of 2½’ x 2½’ and systematic sampling was followed by taking two plots of 0.1 ha in each grid. Each year only selected districts were covered due to limitation of manpower and districts/state level reports were produced. About three-fourth of forested area of the country could be inventoried in 20 years.
Present Methodology of National Forest Inventory
The basic goal is to generate national level growing stock information on two year basis and improve the estimate in subsequent cycles. However, all the districts of the entire country will be covered in 20 years. To overcome this fact, and to generate national level growing stock estimates on a two year cycle, the country was stratified into 14 physiographic zones according to tree species composition and other physiographic and ecological parameters. Ten percent of districts are inventoried in every cycle of 2 years.
The 1:50,000 scale Survey of India toposheet is divided into 36 grids of 2 ½´ x 2 ½¢, further each grid is divided into 4 sub-grids of 1 ¼´ x 1 ¼¢ forming the basic sampling units. Two of these sub-grids are randomly selected and corresponding sub-grids in all the 2 ½´ x 2 ½¢ grids are selected to form the sample. The intersection of diagonals of such sub-grids are marked as center of plot on the map. At the centre of selected subgrid a plot of 0.1 ha area is laid out in each such grid and data are collected from the plots falling in forest area only. For collecting data on soil, forest floor (humus & litter carbon), sub-plots of 1m x 1m are laid at each corner within the 0.1 ha plot. The data regarding herbs and shrubs (including regeneration) are collected from four square plots of 1m x 1m and 3m x 3m, respectively. These plots are laid out at 30 meters from the centre of 0.1 ha plot in all four directions along diagonals in non-hilly area and along trails in hilly areas.
The data collected in the field is checked and entered by the zonal offices and sent to headquarter for processing. At the headquarters, the data received from the zones is again checked for inconsistencies and data is rectified before processing. Processing is carried out by using a specially designed software for different parameters such as area estimation, volume estimation, stand and stock tables, standard error estimation, etc.
However, the use of the existing methodology for forest inventory is not feasible in areas which are thickly forested and with a hilly terrain without proper road network. Such areas exist in many parts of our country, especially in Eastern Himalayan region for which a separate sampling design needed to be developed. The existing national sampling design for forest inventory is based on stratified random sampling taking each physiographic zone as a strata. Since, stratified sampling permits usage of different sampling design in different strata, a separate sampling design for Eastern Himalayan physiographic zone (EHZ) was developed.
The new sampling design known as stratified cluster design for EHZ is based on remote sensing and GIS techniques and was developed keeping the following objectives in mind:
a. Reduction in time to carry out forest inventory
b. Achievement of desired level of precision
c. Easy accessibility of sample points.
The paper highlights methodology of the new sampling design using GIS in Papumpare, West Kameng and Dibang Valley of Arunachal Pradesh as examples.
a. Reduction in Time to Carry Out Forest Inventory
Past inventories of forest resources for different districts of Arunachal Pradesh were studied and it was found that the standard error percentage was on an average 7 per cent at district level which is much below the permissible error of 15 per cent at the district level. Keeping in mind, if the permissible error is kept at ±10 per cent level at the district level the sampling intensity can be lowered to achieve the desired level of precision. As the road network is not well spread it is presumed that the disturbance in forest cover and area will also not be very high. If variation in forest cover for both dense and open forests at different altitudes can be captured, then cluster of sample points may provide micro level variations. Consequently, after a series of permutations and combinations it was decided that 25 clusters of five sample points in each cluster will capture the total variation of the forest resources of the district.
b. Achievement of Desired Level of Precision
To achieve the desired level of precision, stratification of forest according to altitudinal zones was carried out. It is well known that different altitude zones support different tree species, which may cause variation in growing stock and these needs to be estimated. After going through the old inventories, important species were identified and information about their altitudinal preferences were collected from literature. On the basis of this information, it was found that if three altitude classes viz. 0-900m, 900-2,400m and above 2,400m, are taken into consideration then all the tree species can be appropriately estimated. Here it is worth mentioning that, there are some species like Abies densa which is found distributed at very high altitude zone in Eastern Himalayas (between 2,700m-3,900m). To capture its occurrence, if any, an altitudinal strata of above 3,000m can also be prepared. However, in the present study only 3 altitudinal strata, viz. 0-900m, 900-2,400m and greater than 2,400m were created.
In any altitude zone, variation in vegetation cover is due to slope, aspects, soil, etc. resulting in dense or open formation of canopy cover and, therefore, within each altitudinal strata further stratification was done according to forest cover i.e. very dense forest (VDF), moderately dense forest (MDF) and open forest (OF). Accordingly, a total to 9 strata in different altitudinal zones and with different forest cover density were created which is depicted in Table 1 form for West Kameng District.
Table 1. Area under different strata in West Kameng District
|
Altitude zone |
VDF |
MDF |
OF |
Total |
|
0-900 |
9,845 |
27,592 |
3,459 |
40,896 |
|
900-2400 |
50,725 |
1,44,574 |
37,716 |
2,33,015 |
|
2400 and above |
30,933 |
74,972 |
33,551 |
1,39,456 |
c. Easy Accessibility of Sample Points
Since the road network and track network is not well spread, large number of sample points become inaccessible in Eastern Himalayas. To do away this problem, road network and established track network were digitized from the Survey of India (SOI) toposheet and road map of concerned district of Arunachal Pradesh.
A buffer of seven hundred metres from the centre of the road (Fig. 1) was created deliberately with an intention to avoid this buffer from random selection as being close to road, the area is prone to destruction. This is verified from the fact that the dense forest in such areas (centre of road to 700m on either side) have a canopy density of 56 per cent as compared to 70 per cent for the entire district. Subsequently, another buffer of 2,000 metres from the centre of the road (Fig. 1) was created and this buffer minus the previous buffer was considered for random selection of desired cluster points (i.e. 2,000m – 700m = 1,300m).
Fig. 1. Road network map of West Kameng with two buffer zones of 700m and 2,000m
For randomly selecting the sample clusters, use of GIS technique was applied. Firstly, the digital elevation model was created on the basis of contours at a distance of 300m from which 3 different altitudinal zonations were created as shown below in Fig. 2.
Fig. 2. Contour map of West Kameng
On the basis of altitude and forest cover (VDF/MDF/OF), nine strata were created. These are VDF/MDF and open with 0-900m, 900-2,400m, and >2,400m. Then, according to the size of strata the 25 clusters were proportionately allocated to all the strata (Table 2).
Table 2. Proportionate distribution of cluster sampling points
|
Altitude Zone |
VDF |
MDF |
OF |
Total |
|
0-900 |
2 |
2 |
1 |
5 |
|
900-2,400 |
4 |
6 |
2 |
12 |
|
2,400 and above |
2 |
4 |
2 |
8 |
Latitude and longitude of the cluster centers of the desired number of clusters were randomly generated through GIS for each stratum for field inventory. At this point, a sample plot of 0.1 ha was laid out and four other plots laid out at a distance of 200 metre from this point in all the four directions i.e. north, south, east and west. Accordingly, each cluster will have five sample plots of 0.1 ha each with associated herbs and shrubs plots.
There is a possibility that road network may not extend to a particular altitudinal strata, in which case nearness to road/track network was considered and extra points were allocated, which were utilized if clusters were inaccessible. In each 0.1 ha plot, data pertaining to species wise and diameter classwise trees were recorded along with other parameters for estimation of growing stock. In addition, data on shrubs and herbs were also recorded from the desired sampled plots for further analysis. Thus, the new sampling design fulfills all the above stated three objectives (Fig. 3).
Fig. 3. Generation of cluster sample points
Conclusion
Remote sensing and GIS tools have been used successfully for studying the forest resources of many countries like Nepal and USA. These tools are playing an important role in stratification of area for laying of sample plots, particularly in hilly and mountainous region, where conventional method is not yielding the desired results. In India, this methodology using remote sensing and GIS has been successfully used for carrying out sampling in Eastern Himalayan Physiographic Zone, which is very hilly and thick forested. The results obtained for the districts in Arunachal Pradesh where this new technique was applied shows a standard error of 4 per cent only substantiating the efficacy of the new sampling design.
References
Forest Survey of India. 1976. Report on the forest resources of Kameng and Subansiri districts, Arunachal Pradesh, 1975. Dehradun, Forest Survey of India.
Forest Survey of India. 1988. Report on the forest resources of East and West Kameng districts of Arunachal Pradesh, 1982-85. Dehradun, Forest Survey of India.
Forest Survey of India. 1991. Report on the forest resources of Lower Subansiri district of Arunachal Pradesh, 1985-86. Dehradun, Forest Survey of India.
Forest Survey of India . 1997. Forest resources survey of Dibang district. Dehradun, Forest Survey of India.86p.
Forest Survey of India. 2005. State of forest report, 2003. Dehradun, Forest Survey of India.
ON PLANNING AND IMPLEMENTING A FORESTRY DATA BANK IN INDIA
K.D. Singh
Academy of Forest and Environmental Sciences, FRI Campus, Dehradun - 248 006
Introduction
I
nformation and knowledge are very precious commodities, which
not only enhance individual and corporate capacity, but also offer
potential advantage to plan and implement effective action, thereby ensure higher probability of success and minimum cost. A unique advantage of the modern technology is that one can store and retrieve large mass of data and undertake complex analysis and reporting, almost impossible earlier. Equally important is possibility of almost instant communication, which earlier would have taken days, weeks or even months. The present paper is intended to provide some basic ideas about establishing a computerized information system in the forest sector of the country and provide easy access even to distant users such as communities living in the remote forest areas. Three aspects of the problem will be covered in the paper viz. a) Information content; b) information communication network; and c) capacity building needs. The choice of hardware and software technology is purposely left out as innovations in the field are advancing fast and any presentation on the subject is likely to be obsolete by the time the paper is published.
The paper takes up the problem of data collection and reporting at the local level, which so far has evaded solution. For this purpose, the sources of data and their users are classified as: one originating from traditional reporting system; and the other data, important but presently non-reported. A new institutional arrangements and empowerment is suggested, which will cover the non-reported items such as subsistence NTFP, grazing and fuelwood collection and other forest sector contributions.
The Existing Systems of Data Collection and Reporting
The main types of data, techniques used for their
collection and reports published with special reference to the existing data could be listed as follows:
A. Spatial Data
These data exist, but might not be fully converted into digital products. The concerned reports could be grouped into following categories:
i. Existing administrative and technical reports of state forest departments.
These contain data like administration boundaries, forest type boundaries, general map of the tract dealt with, lines of communication, etc. Common guidelines for digitization of these data need to be developed. Each state, under the supervision of a designated officer, should be made responsible for the input preparation and quality control, for which training needs to be provided. The digitization could be carried out by recognized (or listed) contractors. Quality control will be exercised in respect of all final products. These data will be periodically updated.
ii. In the immediate term, the geo-coded IRS images (23 m resolution) could be the main source of forest cover state and change mapping. The legend could be in more detail than done by FSI. Existing stock maps will be very useful for this purpose. The interpretation could be done digitally/visually. This step needs to be coordinated with FSI’s State of Forest Report mapping both for source data as well as interpreted data produced by them. In due course, LISS IV data could be used with a resolution of 5.8 m.
iii. Conservation/protected areas:
The Wildlife Institute of India is digitizing this layer, which needs to be incorporated in the information system.
iv. Geo-referenced sample plot and other research data:
For the purposes of growth/yield determination, by forest type, all existing ICFRE/state sample plot data will need to be geo-referenced and computerized.
B. Statistical Data
C. Existing Working Plans or State Statistical
Reports
Important statistical data appearing in Part-I of the working plan could be organized in form of a database linked with geo-referenced map described under (I) above. A minimum core data should be identified for computerization. All India guidelines will be needed to ensure uniformity.
D. Existing FSI/State Inventory Data
FSI/states have inventoried a major part of the country under resources survey scheme and working plans. These data are valuable sources of information.
E. Annual Administrative Reports
DFOs will be the main source of information for data included in this category such as plantation areas, burnt areas, changes in forest boundary etc. An experiment should be done in few divisions to begin with.
F. JFM and Other Projects
Most of states already have with them a data collection and reporting system for JFM, which could be standardized and incorporated in the database.
Collection and Reporting of Non-Traditional Data Items
This section is concerned with creation of new community based institutions for gathering of annual statistics on inventory, harvesting, regeneration and prices of non-timber forest produce, grazing and fuelwood removals, which is not captured in the traditional system.
A. Community Level Reporting System
The local use forestry, to be sustainable, must have a scientific basis (empirical or observation based) embedded in the local governance. Community must ensure protection, empowered to take responsibility of management, in particular of NTFP, and maintain database on: what is growing, how much has been actually removed in the past, what can be removed in future in different time interval and what needs to be regenerated. Without such plans/controls, sustainable management is not possible. An initiative has been taken by the author on the feasibility of a cost-effective institution for above purposes, as indicated in Fig. 2 and 3 with special reference to NTFP management. The institutional needs for agroforestry are comparable to NTFP.
Fig. 1. Local institutional infrastructure for NTFP management
In Fig. 1, two categories of institutions are being experimented. The one on right hand side consists of local community based institutions. The other on left hand side is formed by more specialized forest department (FD) staff with 6-8 months formal training in NMTFP management.
Fig. 2. All-India coordinated NTFP research network and communication system
Fig. 3. Vision of national/state forest database management system
At the next higher level, market information centers (MIC) are suggested, which would be a very important input to sustainable NTFP management, ensuring fair prices to community and taking further steps regarding pre-processing and processing, value addition in general. At the professional level, the forestry extension officer will overview effective provisioning of knowledge and information services to CSG and MIC. Suitable training curricula for the extension staff will be developed. The FD extension staff, working closely with community centres, will organize NTFP planning on a 5-year cycle, over view correct annual recording of production, consumption and sales data.
B. Knowledge Support System for Community
Forest Managmnent
These are two related issues. The first is development of an All-India Coordinated NTFP Research Network (see Fig. 2). ICFRE, in close cooperation with other central and state research organizations, is expected to take a lead role in developing a strong NTFP knowledge basis to guide the process. The second is establishing a communication system for the knowledge and information to percolate to the community level. States are expected to assume a lead role in establishing an effective communication system, as a part of national network, to provide enabling environment for the effective sharing and use of the knowledge.
In Fig. 1 and 2, a forestry professional has been visualized and named as forestry extension officer to serve in all districts (or forest divisions) in network with state and central forest research institutes. The main function of the person will be to provide knowledge and technology support to market information centres and community support groups and guiding the planning process.
Proposed Information Flow and Networking
An indicative idea of the computerized network is given in Fig. 3. This will channel the spatial, statistical and text information such as government orders and reports. A proper feasibility study and functional requirement study would be necessary before ordering the system. The most critical step will be preparing the staff to adopt the computerized system.
Strengthening of GOI/State Institutions Capacity
Kishwan et al. (2008) provide a comprehensive account of problems in the statistical reporting in the Indian forestry
sector, gaps and approach (International Forestry Review, 2008), summed up as follows:
“The collection, processing and dissemination of statistics pertaining to the forestry sector in India have become a major cause of concern for policy planners and researchers. The status of estimates related to various parameters of the forestry and logging sector in the country is not up to the mark. Inordinate delay in data availability, difficulty in validation and general non-response complicate the problem. The forestry sector in general and the state forest departments in particular need to be revitalized for giving priority to statistical reporting work by taking policy decisions. The sector has also lagged behind in adapting the tools of modern technology, particularly those relating to the information technology. The paper examines the issue in detail, critically analyzing various reasons for gaps, and discusses the methods to plug these with a view to create a reliable databank for the forestry sector in India.”
A major problem with the existing arrangement for data reporting owes to the fact that the system of data reporting by states to ICFRE lacks authority like in the past (till 1984), when the Central Board of Forestry (CBF) was monitoring state compliance in sending statistics. CBF was supported by a technical body Central Forestry Commission (CFC), headed by an officer of DIG rank, to overview compilation, interact with states not only on statistical but on all state problems, and to compile and publish state data in a common national format. This was a continuing process. The discussions at CFC were also leading not only to improved statistics, but also in taking timely and effective measures in solving state forestry problems. A similar close connection needs to be revived, if present problem of incomplete and delayed reporting is to be overcome.
The new community level institutions, described above, needs to be planned and implemented as a concurrent project fully funded from central funds with adequate training to staff involved in the task. States receiving external assistance from World Bank and Japan may start the task on a priority basis. Needed equipment/ tools may be funded from existing budget. In the second phase, other states may be involved and benefit from the first phase experiment.
A national committee with states as a member may be constituted on an immediate basis to overview and report on the steps described in Section 2-4 above The state units should be constituted, which will work in close cooperation of FSI Zonal Units. A system of annual meetings and feedback mechanism may be developed to improve and streamline the procedure.
References
Chuahan, K.V.S.; Sharma, A.K. and Kumar, R. 2008. Non-timber forest products subtenance and commercial uses, trends and future demands. International Forestry Review, 10(2): 201-216.
Kishwan, Jagdish; Sohal, H.S.; Nautiyal, Raman; Kolli, Ramesh and Yadav, Janardan. 2008: Statistical reporting in the Indian forest sector - status, gaps and approach. International Forestry Review, 10(2): 331-340.
Singh, K.D. and Nilsson, N.E. 2008. Institutionalizing strategic forest planning in India. International Forestry Review, 10(2): 387-400.
FOREST STATISTICS IN INDIA
S.P. Sharma
Advisor (Statistics), Ministry of Environment and Forests, Govt. of India, New Delhi- 110 003
Introduction
E
stimates of production, consumption, future demand, imports,
exports and cost of production of any import resource play very
important role in taking policy decisions and planning for the concerned sector. Forests provide very important resources for building capital assets, construction, raw material for a number of industries, goods and services for the rural people particularly the tribals. Besides, the direct use of forest products in our daily life, the forests provide recreation in the form of eco-tourism through trekking, visiting zoological parks, sanctuaries. Many other intangible benefits e.g. controlling land-slides, floods, soil erosion and temperature increasing rains and carbon sequestration and improving soil fertility by growing humus formation. In the times of increasing possibility of global warming, the value of forests need not be emphasized. However, there have been data gaps in forestry statistics possibly due to late realization of importance of forests and their contribution to the growth of national income and generation of wealth. In fact, due to delay in availability of data and lack of data on some parameters, the national picture of forestry remains unclear specially the contribution of forestry sector in the gross domestic product (GDP) particularly that of the non-timber forest products (NTFPs). Further, the commitments of Government of India to the international organizations e.g. International Tropical Timber Organisation, the Food and Agriculture Organisation of the United Nations (FAO) remained largely unfulfilled.
Main Requirements of Data
The forestry statistics are required mainly for the following uses at the
international, national, state-level and local administrative levels:
(i) For policy formulation, decision making
(ii) For framing legal and other regulatory measures and their implementation
(iii) For estimations of contribution to GDP, capital stock, capital formation
(iv) For preparation of environmental outlook/state of environment reports as national and international commitments
(v) As international commitments for providing data to understand the state of forests, wildlife, mangroves and coral reefs as resources to production and ways of human welfare
(vi) To assess the health of the forestry sector vis-a-vis the pressures, impacts and responses of the societies
The Major International Sources
The following types of forestry statistics are compiled, analysed, and published by the international agencies:
(a) World timber situation
(b) Annual market review of forest products
(c) Imports of forest products
(d) Exports of forest products
(e) Production of logs, sawn wood, veneer, plywood
(f) Consumption wood products, pulp, paper
(g) Prices of wood, boards, plywood and paper
(h) Production and consumption of secondary processed products
The FAO and ITTO play very important role in disseminating forestry statistics at the international level. The important international publications are:
(a) Annual Review and Assessment of the World Timber Situation
(b) Forest Products
(c) State of the World’s Forests
(d) Forest Products: Annual Market Review
Present Status of Forestry Statistics in India
The major forest statistics are mainly being collected by the state forest departments as by-products of their regulatory requirements. The same are being compiled and published at the national level by the following organizations:
(i) Forestry Statistics India by ICFRE
(ii) Timber/Bamboo Trade Bulletin by ICFRE
(iii) Forests and Wildlife Statistics by MoEF
(iv) State of Forest Report by Forest Survey of India
While the other data are collected from the state forest departments, the FSI collects the data through the remote sensing satellite on a planned sample survey basis. It also verifies the satellite data by ground level surveys.
The various types of forest statistics are being presented in Forestry Statistics India report published usually biennially by Indian Council for Forestry Research and Education (ICFRE), Dehradun.
Limitations of Data
While, there is long delay in receiving the data from the state forest departments by the ICFRE, there is also lack of uniformity in units and coverage in some states. On some parameters, data are not being collected. Some of the major limitations are as below:
(a) Units of measurement of bamboo are not same for all the states leading to non-comparability and non-additivity
(b) Area under forest fires is estimated without estimating the value of loss to assets and crops, current income in terms of loss of trees, fodder, NTFPs, etc.
(c) Lack of estimate of fuel wood collected by people through head loads
(d) Lack of estimates of grazing area and animals feeding on forest grass and plants
(e) Lack of man-hours used in such forestry activities
(f) Estimates of intangible value of services of forests consumed by people
(g) Unrecorded production of industrial wood and production of minor forest produce are grossly under-estimated
(h) Wood and NTFP production data from social forestry, farm forestry and agroforestry are not available
(i) Data from forest under private lands, Common property resources (CPRs) are not available;
(j) Species-wise timber production and their prices are not available
(k) Data on seed certification are not available; and
(l) Requirement of data for natural resource accounting are not being met
Recommendations and Suggestions
An international seminar was held recently on forestry statistics in New Delhi by the MoEF in collaboration with the ITTO. Some recommendations were made in that seminar. Based on the interaction with the senior officers of ITTO, CSO and other officers of state forest departments, the following suggestions are being made for strengthening the system of forestry statistics in India:
(a) Microscopic assessment of contribution of forestry sector in state domestic product (SDP) and GDP needs to be carried out
(b) At the state level, data may be collected in their own format and then it should be converted into one standard format and the same should be uploaded on website so that one can directly enter the data in one format
(c) Separate statistical cells may be set up in all states
(d) Uniformity of units of measuring NTFPs may be established in a time bound manner
(e) Estimates of consumption of timber may be prepared based on a national study
(f) Mechanism of seed certification for entire country may be developed
(g) Forestry statistics may be linked with the users’ demand and historic data may be analysed with trend analysis for future by type and region
(h) Plan for collection of data through nation-wide survey on NTFPs, grazing, collection of fodder, fuel-wood may be made
(i) Capacity building of state forest departments in statistical techniques, and strengthening of SFDs with modern computer-internet facilities may be done in five-year period
BIBLIOGRAPHY ON FOREST STATISTICS
1. Abdelgalil, E.A. 2004. Deforestation in the drylands of Africa: Quantitative modelling approach. Environment, Development and Sustainability, 6(4): 415-427.
2. Adekunle, V.A.J. 2007. Non-linear regression models for timber volume estimation in natural forest ecosystem, southwest Nigeria. Research Journal of Forestry, 1(2): 40-54.
3. Adesoye, P.O.; Ogunola, A.A.; Awotoye, O.O. and Ogunfidodo, A. 2008. Incorporating crown dimensions into stem height and basal area growth models for African white wood (Triplochiton scleroxylon). Ghana Journal of Forestry, 19-20: 45-53.
4. Affleck, D.L.R. 2006. Poisson mixture models for regression analysis of stand-level mortality. Canadian Journal of Forest Research, 36(11): 2994-3006.
5. Aiaots, J. 2003. Comparison of the Finnish forest growth model MOTTI with the Estonian state-owned forest difference model based on Estonian permanent sample plot data. Transactions of the Faculty of Forestry, Estonian Agricultural University, (36): 125-141.
6. Ajayi, S.; Osho, J.S.A. and Ijomah, J.U. 2006. The use of DBH and stem height to determine tree volume equation for Gmelina arborea (Roxb) plantations in Ukpon River Forest Reserve, Cross River State, Nigeria. Global Journal of Agricultural Sciences, 5(2): 141-146.
7. Akay, A.E. and Sessions, J. 2005. Applying the decision support system, TRACER, to forest road design. Western Journal of Applied Forestry, 20(3): 184-191.
8. Akay, M.; Gunduz, O. and Esengun, K. 2006. A regression analysis of the economic factors effecting the import of forest industry products in Turkey. Journal of Applied Sciences, 6(2): 357-361.
9. Alcamo, J.; Vuuren, D. van; Ringler, C.; Cramer, W.; Masui, T.; Alder, J. and Schulze, K. 2005. Changes in nature’s balance sheet: Model-based estimates of future worldwide ecosystem services. Ecology and Society, 10(2).
10. Alig, R.J.; Lewis, D.J. and Swenson, J.J. 2005. Is forest fragmentation driven by the spatial configuration of land quality? The case of western Oregon. Forest Ecology and Management, 217(2-3): 266-274.
11. Alix Garcia, J. 2007. A spatial analysis of common property deforestation. Journal of Environmental Economics and Management, 53(2): 141-157.
12. Alvarez, I.A.; Velasco, G. del N.; Barbin, H.S.; Lima, A.M.L.P. and Couto, H.T.Z. 2005. Comparison of two sampling methods for estimating urban tree density. Journal of Arboriculture, 31(5): 209-214.
13. Andersen, L.E. and Granger, C.W.J. 2006. Modeling Amazon deforestation for policy purposes: Reconciling conservation priorities and human development. Environmental Economics and Policy Studies, 8(3): 201-210.
14. Angelsen, A. 2008. REDD models and baselines. International Forestry Review, 10(3): 465-475.
15. Aoyagi, S. and Managi, S. 2004. The impact of subsidies on efficiency and production: Empirical test of forestry in Japan. International Journal of Agricultural Resources, Governance and Ecology, 3(3-4): 216-230.
16. Arevalo, C.B.M.; Volk, T.A.; Bevilacqua, E. and Abrahamson, L. 2007. Development and validation of aboveground biomass estimations for four Salix clones in central New York. Biomass and Bioenergy, 31(1): 1-12.
17. Arii, K.; Caspersen, J.P.; Jones, T.A. and Thomas, S.C. 2008. A selection harvesting algorithm for use in spatially explicit individual-based forest simulation models. Ecological Modelling, 211(3-4): 251-266.
18. Backeus, S.; Wikstrom, P. and Lamas, T. 2005. A model for regional analysis of carbon sequestration and timber production. Forest Ecology and Management, 216(1-3): 28-40.
19. Bala, B.K. 2006. Computer modelling of energy and environment for Bangladesh. International Agricultural Engineering Journal, 15(4): 151-160.
20. Barik, S.K. and Mishra, S.K. 2008. Assessment of the contribution of forests to the economy of the northeastern states of India. International Forestry Review, 10(2): 349-361.
21. Bartle, J.; Olsen, G.; Cooper, D. and Hobbs, T. 2007. Scale of biomass production from new woody crops for salinity control in dryland agriculture in Australia. International Journal of Global Energy Issues, 27(2): 115-137.
22. Belleau, A.; Bergeron, Y.; Leduc, A.; Gauthier, S. and Fall, A. 2007. Using spatially explicit simulations to explore size distribution and spacing of regenerating areas produced by wildfires: Recommendations for designing harvest agglomerations for the Canadian boreal forest. Forestry Chronicle, 83(1): 72-83.
23. Bertomeu, M.; Bertomeu, M. and Gimenez, J.C. 2006. Improving adoptability of farm forestry in the Philippine uplands: A linear programming model. Agroforestry Systems, 68(1): 81-91.
24. Blackstock, T.H.; Burrows, C.R.; Howe, E.A.; Stevens, D.P. and Stevens, J.P. 2007. Habitat inventory at a regional scale: a comparison of estimates of terrestrial broad habitat cover from stratified sample field survey and full census field survey for Wales, UK. Journal of Environmental Management, 85(1): 224-231.
25. Blagoev, G. 2005. A method for individual modeling of the process of log sawing to lumber. Annals of Warsaw Agricultural University, Forestry and Wood Technology, (56): 50-55.
26. Blanco, J.A.; Seely, B.; Welham, C.; Kimmins, J.P. and Seebacher, T.M. 2007. Testing the performance of a forest ecosystem model (FORECAST) against 29 years of field data in a Pseudotsuga menziesii plantation. Canadian Journal of Forest Research, 37(10): 1808-1820.
27. Boer, R.; Wasrin, U.R.; Hendri, P.; Dasanto, B.D.; Makundi, W.; Hero, J.; Ridwan, M. and Masripatin, N. 2007. Assessment of carbon leakage in multiple carbon-sink projects: A case study in Jambi Province, Indonesia. Mitigation and Adaptation Strategies for Global Change, 12(6): 1169-1188.
28. Borner, J. and Wunder, S. 2008. Paying for avoided deforestation in the Brazilian Amazon: From cost assessment to scheme design. International Forestry Review, 10(3): 496-511.
29. Bourque, C.P.A. and Hassan, Q.K. 2008. Projected impacts of climate change on species distribution in the Acadian forest region of eastern Nova Scotia. Forestry Chronicle, 84(4): 553-557.
30. Bourque, C.P.A.; Neilson, E.T.; Gruenwald, C.; Perrin, S.F.; Hiltz, J.C.; Blin, Y.A.; Horsman, G.V.; Parker, M.S.; Thorburn, C.B.; Corey, M.M.; Meng Fan Rui and Swift, D.E. 2007. Optimizing carbon sequestration in commercial forests by integrating carbon management objectives in wood supply modeling. Mitigation and Adaptation Strategies for Global Change, 12(7): 1253-1275.
31. Boyland, M.; Nelson, J. and Bunnell, F.L. 2005. A test for robustness in harvest scheduling models. Forest Ecology and Management, 207(1-2): 121-132.
32. Brack, C.L. 2006. Updating urban forest inventories: An example of the DISMUT model. Urban Forestry and Urban Greening, 5(4): 189-194.
33. Broada, L.R. and Lynch, T. 2006. Growth models for Sitka spruce in Ireland. Irish Forestry, 63(1-2): 53-79.
34. Brooks, J.R. 2007. Taper, volume, and weight of small black cherry and red maple trees in West Virginia. Northern Journal of Applied Forestry, 24(2): 104-109.
35. Brooks, J.R. and Wiant, H.V. Jr. 2004. Estimation of volume growth using Zeide’s growth types: An updated evaluation. Northern Journal of Applied Forestry, 21(3): 164-165.
36. Brown, G.S.; Rettie, W.J.; Brooks, R.J. and Mallory, F.F. 2007. Predicting the impacts of forest management on woodland caribou habitat suitability in black spruce boreal forest. Forest Ecology and Management, 245(1-3): 137-147.
37. Cacho, O. and Lipper, L. 2006. Abatement and transaction costs of carbon-sink projects involving smallholders. ESA Working Paper, 25 pp.
38. Campbell, K.A. and Dewhurst, S.M. 2007. A hierarchical simulation-through-optimization approach to forest disturbance modelling. Ecological Modelling, 202(3-4): 281-296.
39. Campion, J.M.; Dye, P.J. and Scholes, M.C. 2004. Modelling maximum canopy conductance and transpiration in Eucalyptus grandis stands not subjected to soil water deficits. Southern African Forestry Journal, 202: 3-11.
40. Canavan, S.J. and Hann, D.W. 2005. The two-stage method for measurement error characterization. Forest Science, 50(6): 743-756.
41. Carlson, C.A.; Burkhart, H.E.; Allen, H.L. and Fox, T.R. 2008. Absolute and relative changes in tree growth rates and changes to the stand diameter distribution of Pinus taeda as a result of mid-rotation fertilizer applications. Canadian Journal of Forest Research, 38(7): 2063-2071.
42. Catchpoole, K.; Nester, M.R. and Harding, K. 2007. Predicting wood value in Queensland Caribbean pine plantations using a decision support system. Australian Forestry, 70(2): 120-124.
43. Chamshama, S.A.O.; Mugasha, A.G. and Zahabu, E. 2004. Stand biomass and volume estimation for Miombo woodlands at Kitulangalo, Morogoro, Tanzania. Southern African Forestry Journal, 200: 59-70.
44. Chen Wen Bo and Zhao Xiao Fan. 2007. Estimation of forest parameters based on TM imagery and statistical analysis. Journal of Forestry Research, 18(3): 241-244.
45. Chen Yuan Zheng; Ma Xiang Qing. 2007. Research on the reproductive ecology of endangered plant populations. Chinese Journal of Eco Agriculture, 15(1): 186-189.
46. Chopra, K. and Dasgupta, P. 2008. Assessing the economic and ecosystem services contribution of forests: Issues in modelling, and an illustration. International Forestry Review, 10(2): 376-386.
47. Christie, M.; Hanley, N. and Hynes, S. 2007. Valuing enhancements to forest recreation using choice experiment and contingent behaviour methods. Journal of Forest Economics, 13(2-3): 75-102.
48. Cienciala, E.; Apltauer, J.; Exnerova, Z. and Tatarinov, F. 2008. Biomass functions applicable to oak trees grown in Central-European forestry. Journal of Forest Science, 54(3): 109-120.
49. Croitoru, L. 2007. Valuing the non-timber forest products in the Mediterranean region. Ecological Economics, 63(4): 768-775.
50. Crowe, K. 2008. Modeling the effects of introducing timber sales into volume-based tenure agreements. Forest Policy and Economics, 10(3): 174-182.
51. Dong Ren Cai; Chen Chun Di; Deng Hong Bing and Zhao Jing Zhu. 2008. Forestland prediction of China based on forest ecosystem services for the first half of 21st century. Journal of Forestry Research, 19(3): 181-186.
52. Dzierzon, H. and Mason, E.G. 2006. Towards a nationwide growth and yield model for radiata pine plantations in New Zealand. Canadian Journal of Forest Research, 36(10): 2533-2543.
53. Etienne, A.; Valderrama, J.M. and Diaz Ambrona, C.H. 2008. Productive model of evergreen oak and annual pastures in Extremadura (Spain). Options Mediterraneennes Serie A, Seminaires Mediterraneens, 79: 65-68.
54. Fajardo, A. and McIntire, E.J.B. 2007. Distinguishing microsite and competition processes in tree growth dynamics: An a priori spatial modeling approach. American Naturalist, 169(5): 647-661.
55. Favada, I.M.; Kuuluvainen, J. and Uusivuori, J. 2007. Consistent estimation of long-run non-industrial private forest owner timber supply using micro data. Canadian Journal of Forest Research, 37(8): 1485-1494.
56. Finley, A.O.; Banerjee, S. and McRoberts, R.E. 2008. A Bayesian approach to multi-source forest area estimation. Environmental and Ecological Statistics, 15(2): 241-258.
57. Finley, A.O.; Banerjee, S.; Ek, A.R. and McRoberts, R.E. 2008. Bayesian multivariate process modeling for prediction of forest attributes. Journal of Agricultural, Biological, and Environmental Statistics, 13(1): 60-83.
58. Furstenau, C.; Badeck, F.W.; Lasch, P.; Lexer, M.J.; Lindner, M.; Mohr, P. and Suckow, F. 2007. Multiple-use forest management in consideration of climate change and the interests of stakeholder groups. European Journal of Forest Research, 126(2): 225-239.
59. Garcia Quijano, J.F.; Deckmyn, G.; Ceulemans, R.; Orshoven, J. van and Muys, B. 2008. Scaling from stand to landscape scale of climate change mitigation by afforestation and forest management: A modeling approach. Climatic Change, 86(3-4): 397-424.
60. Giri, Navin. 2004. Assessment of tree resources outside forests: A lesson from Tanzania. Banko Janakari, 14(2): 46-52.
61. Gockede, M.; Rebmann, C. and Foken, T. 2004. A combination of quality assessment tools for eddy covariance measurements with footprint modelling for the characterisation of complex sites. Agricultural and Forest Meteorology, 127(3-4): 175-188.
62. Green, C.; Tobin, B.; O’Shea, M.; Farrell, E.P. and Byrne, K.A. 2007. Above and belowground biomass measurements in an unthinned stand of Sitka spruce (Picea sitchensis (Bong) Carr.). European Journal of Forest Research, 126(2): 179-188.
63. Guan, B.T.; Lin Shu Tzong; Lin Ya Hui and Wu Yi Sui. 2008. No initial size advantage for Japanese cedars in crowded stands. Forest Ecology and Management, 255(3-4): 1078-1084.
64. Guo, Q.F.; Brandle, J.; Schoeneberger, M. and Buettner, D. 2004. Simulating the dynamics of linear forests in Great Plains agroecosystems under changing climates. Canadian Journal of Forest Research, 34(12): 2564-2572.
65. Hall, R.J.; Skakun, R.S.; Arsenault, E.J. and Case, B.S. 2006. Modeling forest stand structure attributes using Landsat ETM+data: Application to mapping of aboveground biomass and stand volume. Forest Ecology and Management, 225(1-3): 378-390.
66. Hanninen, R. 2004. Econometric models in forest sector forecasting. Journal of Forest Economics, 10(2): 57-59.
67. Hao QingYu; Meng FanRui; Zhou YuPing and Wang, J.X. 2005. A transition matrix growth model for uneven-aged mixed-species forests in the Changbai Mountains, northeastern China. New Forests, 29(3): 221-231.
68. Hao Qing Yu; Meng Fan Rui; Zhou Yu Ping and Wang, J.X. 2005. Determining the optimal selective harvest strategy for mixed-species stands with a transition matrix growth model. New Forests, 29(3): 207-219.
69. Harper, G.J.; Polsson, K. and Goudie, J. 2008. Modelling vegetation management treatments with the tree and stand Simulator. Forestry Chronicle, 84(1): 53-59.
70. Hartter, J. and Boston, K. 2007. An integrated approach to modeling resource utilization for rural communities in developing countries. Journal of Environmental Management, 85(1): 78-92.
71. Herbst, M.; Roberts, J.M.; Rosier, P.T.W. and Gowing, D.J. 2006. Measuring and modelling the rainfall interception loss by hedgerows in southern England. Agricultural and Forest Meteorology, 141(2-4): 244-256.
72. Hetemaki, L.; Hanninen, R. and Toppinen, A. 2004. Short-term forecasting models for the Finnish forest sector: Lumber exports and sawlog demand. Forest Science, 50(4): 461-472.
73. Horne, P.; Boxall, P.C. and Adamowicz, W.L. 2005. Multiple-use management of forest recreation sites: A spatially explicit choice experiment. Forest Ecology and Management, 207(1-2): 189-199.
74. Hu, H.F. and Wang, G.G. 2008. Changes in forest biomass carbon storage in the South Carolina Piedmont between 1936 and 2005. Forest Ecology and Management, 255(5-6): 1400-1408.
75. Huth, A.; Drechsler, M. and Kohler, P. 2005. Using multicriteria decision analysis and a forest growth model to assess impacts of tree harvesting in Dipterocarp lowland rain forests. Forest Ecology and Management, 207(1-2): 215-232.
76. Hynynen, J.; Ahtikoski, A.; Siitonen, J.; Sievanen, R. and Liski, J. 2005. Applying the MOTTI simulator to analyse the effects of alternative management schedules on timber and non-timber production. Forest Ecology and Management, 207(1-2): 5-18.
77. Hyytiainen, K. and Penttinen, M. 2008. Applying portfolio optimisation to the harvesting decisions of non-industrial private forest owners. Forest Policy and Economics, 10(3): 151-160.
78. Hyytiainen, K.; Hari, P.; Kokkila, T.; Makela, A.; Tahvonen, O. and Taipale, J. 2004. Connecting a process-based forest growth model to stand-level economic optimization. Canadian Journal of Forest Research, 34(10): 2060-2073.
79. Ishizuka, S.; Iswandi, A.; Nakajima, Y.; Yonemura, S.; Sudo, S.; Tsuruta, H. and Muriyarso, D. 2005. Spatial patterns of greenhouse gas emission in a tropical rainforest in Indonesia. Nutrient Cycling in Agroecosystems, 71(1): 55-62.
80. Jayaraman, K. and Sunanda, C. 2007. Yield prediction models for Acacia mangium and Acacia auriculiformis plantations in Kerala. Indian Journal of Forestry, 30(1): 1-4.
81. Jiang LiChun and Brooks, J.R. 2008. Taper, volume, and weight equations for red pine in West Virginia. Northern Journal of Applied Forestry, 25(3): 151-153.
82. Joibary, S.S.; Darvishsefat, A.A. and Kellenberger, T.W. 2007. Forest type mapping using incorporation of spatial models and ETM+ data. Pakistan Journal of Biological Sciences, 10(14): 2292-2299.
83. Kancs, D. and Wohlgemuth, N. 2008. Evaluation of renewable energy policies in an integrated economic-energy-environment model. Forest Policy and Economics, 10(3): 128-139.
84. Kangas, A.; Leskinen, P. and Kangas, J. 2007. Comparison of fuzzy and statistical approaches in multi-criteria decision making. Forest Science, 53(1): 37-44.
85. Kangas, J. and Kangas, A. 2005. Multiple criteria decision support in forest management - the approach, methods applied, and experiences gained. Forest Ecology and Management, 207(1-2): 133-143.
86. Kangas, J. and Leskinen, P. 2005. Modelling ecological expertise for forest planning calculations-rationale, examples, and pitfalls. Journal of Environmental Management, 76(2): 125-133.
87. Kaonga, M.L. and Coleman, K. 2008. Modelling soil organic carbon turnover in improved fallows in eastern Zambia using the RothC-26.3 model. Forest Ecology and Management, 256(5): 1160-1166.
88. Karlsson, J.; Ronnqvist, M. and Bergstrom, J. 2004. An optimization model for annual harvest planning. Canadian Journal of Forest Research, 34(8): 1747-1754.
89. Kauppinen, T.; Vincent, R.; Liukkonen, T.; Grzebyk, M.; Kauppinen, A.; Welling, I.; Arezes, P.; Black, N.; Bochmann, F.; Campelo, F.; Costa, M.; Elsigan, G.; Goerens, R.; Kikemenis, A.; Kromhout, H.; Miguel, S.; Mirabelli, D.; McEneany, R.; Pesch, B.; Plato, N.; Schlunssen, V.; Schulze, J.; Sonntag, R.; Verougstraete, V.; Vicente, M.A. de and Wolf, J. 2006. Occupational exposure to inhalable wood dust in the member states of the European Union. Annals of Occupational Hygiene, 50(6): 549-561.
90. Keles, S. and Baskent, E.Z. 2007. Modeling and analyzing timber production and carbon sequestration values of forest ecosystems: A case study. Polish Journal of Environmental Studies, 16(3): 473-479.
91. Keles, S.; Yolasigmaz, H.A. and Baskent, E.Z. 2007. Long-term modelling and analyzing of some important forest ecosystem values with linear programming. Fresenius Environmental Bulletin, 16(8): 963-972.
92. Kijazi, M.H. 2005. Possibility schema for interdisciplinary forest management evaluation and decision-making. Forestry Chronicle, 81(3): 375-380.
93. Kishwan, J.; Sohal, H.S.; Nautiyal, R.; Kolli, R. and Yadav, J. 2008. Statistical reporting in the Indian forestry sector: Status, gaps and approach. International Forestry Review, 10(2): 331-340.
94. Kleinn, C. and Vilcko, F. 2006. A new empirical approach for estimation in k-tree sampling. Forest Ecology and Management, 237(1-3): 522-533.
95. Knoke, T. 2008. Mixed forests and finance - methodological approaches. Ecological Economics, 65(3): 590-601.
96. Kobler, A.; Pfeifer, N.; Ogrinc, P.; Todorovski, L.; Ostir, K. and Dzeroski, S. 2007. Repetitive interpolation: A robust algorithm for DTM generation from aerial laser scanner data in forested terrain. Remote Sensing of Environment, 108(1): 9-23.
97. Kong Fan Hua; Yin Hai Wei and Nakagoshi, N. 2007. Using GIS and landscape metrics in the hedonic price modeling of the amenity value of urban green space: A case study in Jinan City, China. Landscape and Urban Planning, 79(3-4): 240-252.
98. Kosir, B. 2006. Work study - a forgotten scientific branch in forestry? Nova Mehanizacija Sumarstva, 26(2): 17-22.
99. Kosir, B.; Kosir, Z. and Krc, J. 2006. Natural composition of tree species as a basis for model development of stumpage price. Croatian Journal of Forest Engineering, 27(2): 71-80.
100. Koskela, L.; Sinha, B.K.; Nummi, T. 2007. Some aspects of the sampling distribution of the Apportionment Index and related inference. Silva Fennica, 41(4): 699-715.
101. Koukal, T.; Suppan, F. and Schneider, W. 2007. The impact of relative radiometric calibra |