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Fire Situation in Mongolia (IFFN No. 26)

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Fire Situation in Mongolia

(IFFN No. 26 – January 2002, p. 75-83)


Introduction

Mongolia is located in Central Asia with an area of 1 565 000 km2 and a population of 2.3 million, which makes Mongolia one of the least populated countries in the world. The country borders Russia in the North and China in the South. Mongolia is a highland country located deep within the interior of Eurasia and has a marked continental climate with poor soil fertility, scanty surface water resources and harsh natural conditions.

Forests and grasslands play an important role in the economic development of the country. Forest cover is 12.5 million ha or 8.1 percent of the Mongolian territory. Forests consist mostly of larch (Larix sibirica), pine (Pinus sylvestris), birch (Betula platyphylla), cedar (Pinus sibirica), spruce (Picea spp.) and saxaul (Haloxylon ammodendron). Grassland covers 70 percent of all territory. It is assumed that most of today’s steppe vegetation is on former forest sites that have been degraded by fire. The Mongolian climate and geography, coupled with its economic and social structure, account for its considerable vulnerability to natural disasters. Winters are often very cold and springs are difficult with blizzards, tornadoes and regular wildfires. Heavy rains and floods occur in summer and heavy snowfalls occur in autumn; frosts and blizzards are common. Thus, throughout the year the country is under pressure from these natural disasters.

Wildfires constitute a major factor that determines spatial and temporal dynamics of forest ecosystems. Out of the total of ca. 17 million ha of forest land, 4 million ha are disturbed to varying degrees, either by fire (95 percent) or by logging (5 percent). Logged areas have increased drastically over the past 25 years. More than 600 000 ha of timber harvest have not recovered.

Fire environment, fire regimes and the ecological role of fire

The highest fire hazard is found in the submontane larch (Larix sibirica) and pine (Pinus sylvestris) stands growing on seasonally freezing soils. These stands are distributed on Khentey, East Khentey and Khubsugul foothills that are characterised by an extremely continental climate. During the year, air temperature fluctuations can amount to 90°C, with the summer maximum being +40°C. Annual precipitation ranges from 250 to 350 mm. In exceptionally dry years, precipitation is less than 200 mm.

Forest fire statistics for the period 1963 to 1997 (see also Fig.1) reveal that the majority of fires burned within the central and eastern parts of the forested area. This can be attributed to the predominance of highly fire susceptible (highly flammable) pine and larch stands. Moreover, economic activity is much higher here as compared to other parts of the region. Extreme fire seasons are caused by long droughts. Fires burn from April to July under such conditions. The average fire season usually has two peaks. One peak is during spring (from March to mid June) and accounts for 80 per cent of all fires. The other fire peak falls within a short period in autumn (September to October) and accounts for 5 to 8 percent of all fires. In summer, fires occur very rarely (only 2 to 5 percent of the total) because of heavy rains.

The intra-annual distribution of fires has been documented by seven forest protection air bases for the Khanngai and Trans-Baikal forest zones for the period 1985 to 1994 (Table 1). In these zones, fire activity is the highest in April and May with 33.3 percent and 48.1 percent of their total number in a fire season, respectively. Fires start in late March and early April, immediately after snowmelt when forest fuels are drying rapidly on southern- and western-facing slopes.

Steppe fires under certain weather conditions often invade the adjacent forest-steppe and sub-taiga zones. In the mountain forest belt, especially in the high elevations, lightning fires are most common. Lightning storm activity increases considerably at the end of May and in early June. High fire danger is largely due to the prevalence of light-needled conifers in stands adjacent to steppe areas. These are mainly pine stands with mixed herbaceous ground cover, which is characterized by high fire danger in spring and autumn. Steppe vegetation and surrounding pine stands attain high flammability practically simultaneously. Fire occurrence depends on forest type, precipitation distribution and availability of ignition sources. Fires are frequent in pine and larch stands of the forest-steppe and sub-taiga zones, while they are rarer in larch and Siberian pine stands of the mountain taiga. 

Table 1. Intra-annual distribution of forest fire distribution in Mongolia, 1985-1992.

Local Airbase Month
  March April May June July Aug. Sep. Oct. Nov. Total
Ar. khalgai 2 18 8 2 4 34
Khovsgol 19 23 11 2 2 57
Bulgan 11 58 117 5 3 3 197
Selenge 27 52 8 3 9 1 100
Khentij 10 19 23 3 55
Dornod 1 9 6 1 17
Ulan-Baatar 25 24 7 2 7 65
Total 24 175 253 34 2 10 26 1 525
Percentage 4.6 33.3 48.1 6.5 0.4 1.9 5.0 0.2 100

In one of the most sparsely populated countries in the world, it is difficult to get accurate information on fire causes. It is known, however, that during the main fire seasons (spring and late fall), no natural fire causes exist. The recent increase in the number of fires is related to the opening of markets once highly controlled or restricted. The vast majority of fires are not deliberately set to clear land. Rather, it is a function of carelessness. One example is the collection of elk antlers for sale to European and Chinese markets. During the previous regime, a single, state run enterprise managed this market under strict controls and guidelines. Today, it is open to virtually anyone.

Fires start for three reasons:

  1. Antler collection starts in the bitter cold of February when fire is simply a survival tool.
  2. Sparks from vehicle exhaust pipes in remote forests.
  3. Tracer bullets left by the Russian military have entered the game hunting market and are used to hunt elk for the blood antlers which have a higher value in the market place.

The most obvious consequence of frequent and intense fires is the loss of forested land. The current fire pattern is affecting 14 percent of this resource annually. The brief growing season and low growth capacity of the trees means that these forests may take 200 years or more to regenerate. In addition to their commercial value, these forests are a precious ecological resource. They contain the sources of virtually all rivers in the country including the inflow to Lake Baikal (Russia), the largest freshwater lake in the world. They protect soil, rangelands, provide habitat for wildlife and serve as windbreaks.

Narrative summary of major wildfire impacts on people, property, and natural resources during the 1990’s

In an average year, 50-60 forest fires and 80-100 steppe fires occur annually. About 95 percent of steppe and forest fires in Mongolia are caused by human activities. Winters and springs from 1996 to 1998 were extremely dry and were lacking snow in most areas. From late February to early June of these years, Mongolia suffered from large-scale forest and steppe fires that devastated large parts of the country. During these fire episodes, 29 people died, 82 people were injured and 11 700 livestock were killed. Also, 218 family houses, 1 066 communication facilities, 750 fences and 26.3 million ha of pasture and forest burned. The total costs of property losses amounted to 820.2 million MN¥ (Mongolian Tughrik). Ecological and economic damage was estimated as 1 850.5 million MN¥ (December 1999 value: ca. $US 1.8 million).

Fire management organization

Until recently, a branch of the military known as the Civil Defence centrally managed fire events in Mongolia. The military maintained all training regimes, equipment and personnel with virtually no support to local communities. With the transition and associated economic difficulties, this centrally managed firefighting system has collapsed. Perhaps the single most important contributor to the increase in fire spread is the grounding of the Aerial Patrol Service. In 1969 the Mongolian Fire Protection and Aerial Patrol Service was established to provide early detection and rapid initial attack on fires. This Service was a Soviet-style aerial detection and airborne firefighting programme. The Service was staffed by 200 to 300 smokejumpers and helicopter rappellers; including a fleet of helicopters for helitack and tactical aerial support. The aerial forces operated out of seven bases distributed throughout the fire-prone regions of northern Mongolia. Smokejumpers on routine aerial patrols detected a high percentage of the fires and handled approximately 90 percent of the suppression workload. In the early 1990’s, when the communist government and Soviet financial support abruptly disappeared, the Mongolian aerial program sharply declined. At present, Mongolians cannot afford to maintain and fly their aerial patrol aircraft. Instead, they must rely on NOAA satellite imagery as their primary early warning system with a spatial resolution of 1.1 km2. The decline of the aerial program through the mid-1990’s resulted in the creation of a “fire suppression void” and no doubt greatly contributed to the horrendous fire losses experienced in the 1996 and 1997 fire season

Immediately following the 1996 fires, Mongolia received assistance from international organizations to help local people recover from the losses. The German government contributed to these efforts in the form of an Emergency Fire Aid project carried out in the northern and eastern parts of the country (October-December 1996). Since then, the government has been working to find long-term solutions to improve fire management. In a first step, the parliament passed a law designed to organize and improve firefighting efforts at all levels.

In February of 1998, the German and Mongolian governments signed an agreement to start an Integrated Fire Management Project to be implemented over the next three years (1997-2000). The GTZ, responsible for the German contribution, provided long and short-term experts, support staff, training and equipment.

The project region selected by the Integrated Fire Management Project is the Khan Khentii Strictly Protected Area and its buffer zones – one of the harder hit areas during the 1996 fires. A primary task was the establishment of a fire management plan compatible with the protected area goals and the responsibilities of the local communities. Fire Management Units in the local communities received professional training and basic hand tools suitable for the regional conditions. Information and Training Centres provided the necessary infrastructure for fire prevention activities, management information, training exercises, dispatch and field organization.

Community involvement in fire management activities

The IFM project supported Mongolia by strengthening local capacities to effectively address the issues of fire prevention, pre-suppression and suppression. This is accomplished by helping to organize cooperative efforts between protected area staff and local and national administrations responsible for fire management. Additional goals include establishing the necessary infrastructure, providing training in-country and abroad and by including all stakeholders in the planning and implementation of fire management activities.

Integrated Fire Management, like other community-based programs, focuses on flexible, pragmatic approaches designed to support local people’s role in resource management. Specifically, it entails the application of the art and science of modern wildland fire technologies and practices to the local fire problem – i.e. the community level.

In the development of the program, the IFM Project started with the philosophy that an ounce of prevention is worth a pound of cure. Hence, the most effective fire suppression strategy is an effective fire prevention program. In the summer of 1998, the IFM project began pilot activities in the buffer zone communities surrounding the Khan Khentii Special Protected Area. Specifically targeted were the potential multipliers including Information Training Centre (ITC) “extension” officers, educators, protected area rangers and key community persons. This cooperative effort led to a number of educational materials that were developed and introduced:

  • A fire prevention curriculum for school children.
  • A fire prevention video.
  • A ranger’s handbook to be used as an outreach tool in remote areas.
  • A coloring book for small children.
  • A fire mascot to carry the prevention message.

The central focus of pre-suppression work has been the drafting of a fire management plan for the protected area administration and local communities.

Suppression goals include (1) the establishment of fire management crews, (2) provision of equipment and (3) the development of a locally run “Fire Training Programme” adapted to Mongolian conditions of fuels, fire behavior and available suppression resources and logistics. In the spring of 1998, six Soum (district) governors in the protected area buffer zone formed fifteen-person (15) fire management units (FMU’s – or suppression crews) for their respective Soums. Each crew consists of a crew boss, assistant crew boss and thirteen unemployed volunteers. The crew is jointly managed through a Memorandum of Understanding between the local community and the protected area administration. After establishment of the crews, the project identified equipment to match the fuel conditions. Fuel conditions throughout northeastern Mongolia closely resemble the fuel types of the western United States, British Columbia and interior Alaska: tough steppe grass with deep dense roots, brush, larch, pine, spruce, birch, moss and muskeg like valley bottoms. GTZ equipped the crews with fire swatters, fire shovels, pulaskis, adze hoes, Council-type fire rakes, backpack pumps, crosscut saws, chainsaw and hardhats. Each crew has been equipped with personal portable radios, a vehicle mobile radio and mobile repeaters for communications with the dispatch centre. Stationary repeaters are being installed to link the Soum dispatch centers with the national coordination centre in Ulaan Baatar.

Starting in March 1999, the project assisted Mongolian fire specialists in developing a series of training materials, including a 32-hour Basic Firefighter Course with accompanying Instructor’s Manual, Student Workbook, training videos and Crewboss Manual. The training programs were adapted from existing Mongolian training and the basic courses used to train American wildland firefighters: Introduction to Wildland Fire Behavior (S-190), Firefighter Training (S-130) and basic Incident Command System concepts. Approximately one half of the course was conducted in the field, including “practice fires” for mop-up and a live fire exercise on the final day. Crews were instructed in the bump-up progressive crew method of fireline construction. A fire instructor’s training course for Mongolian instructors was established. In a subsequent phase, we observed and coached Mongolian instructors as they trained “rookie FMU crew members” and community (Soum) fire support crews. Due to unusually high precipitation during the winter, however, the project has been unable to evaluate crew performance on fires.

Wildfire database

Since the establishment of a NOAA satellite receiving station at the National Remote Sensing Centre of Mongolia in 1987, the staff of the Centre has developed and tested technologies for natural disaster monitoring, such as forest and steppe fire, drought, floods, meteorological phenomena etc.

The recent fire danger situation in forest and steppe zones challenged staff of the National Remote Sensing Centre to test and improve their operational technology to quickly process and transfer fire locations and other data to disaster-related and administrative organizations. In the last three years, 788 fires were detected primarily by satellite data and thus millions of money was saved. The accuracy of detected hot spots as a fire is estimated to be 76.9 percent of the total number of cases between 1995 and 1999.

 

Figure 1. Number of fires and area burned in Mongolia 1963-1997

It is clear that Mongolia is experiencing a dangerous increase in wildfires. From 1981 to 1995, forest and steppe fires burned an average of 1.74 million ha annually. In 1996 and 1997, the area affected by fire was 10.7 and 12.4 million ha respectively – an increase of more than six-fold. The areas hardest hit by these increases have been the forested regions. The typical forest fire season (1981-95) swept through some 140 000 ha (on average 8 percent of the total area burned), already a large area. However in 1996 and 1997, this figure radically increased to nearly 18 times the previous average – some 2.5 million ha annually, corresponding to ca. 22 percent of the total land area affected by fire. In these two years alone more forested areas burned than were harvested over the last 65 years. Figures 2 and 3 provide maps showing the forest and steppe areas burned in 1996 and 1997. Figure 4 shows the area burned in Mongolia during spring 2000. The fire statistical data for the 1980s and 1990s are given in Tables 2 and 3.

 

Figure 2. Forest and steppe fire map of Mongolia for the spring fire season 1996. Source: Computer Information Center, Mongolia.

 

Figure 3. Forest and steppe fire map of Mongolia for the spring fire season 1997. Source: Computer Information Center, Mongolia.

 Table 2. Wildfire statistics of Mongolia, 1981-1989.

 Year

Total No. of Fires on Forest, Other Wooded Land, & Other Land Total Area Burned on Forest, Other Wooded Land, & Other Land
Area of Forest Burned 

 

Area of Other Wooded Land and Other Land Burned
Human Causes 

  

 

Natural Causes

 

Unknown Causes 


No. ha ha ha No. No. No.
1981 94 169 200 4 600 164 600
1982 109 1 100 000 156 300 943 700
1983 95 245 400 87 400 158 000
1984 116 513 900 156 200 357 700
1985 99 1 896 700 3 400 1 893 300
1986 204 3 187 000 30 600 3 156 400
1987 233 1 228 000 143 300 1 084 700
1988 142 243 000 2 300 240 700
1989 192 1 281 000 51 000 1 230 000
Average 160 1 096 022 82 400 1 060 000      

 

 Table 3. Wildfire statistics of Mongolia, 1990-1999.

 Year

Total No. of Fires on Forest, Other Wooded Land, & Other Land Total Area Burned on Forest, Other Wooded Land, & Other Land
Area of Forest Burned 

 

Area of Other Wooded Land and Other Land Burned
Human Causes 

  

 

Natural Causes

 

Unknown Causes 


No. ha ha ha No. No. No.
1990 129 2 577 000 55 000 2 522 000      
1991 101 6 099 000 639 000 6 035 100      
1992 171 1 541 000 390 700 1 123 300      
1993 63 2 763 000 202 000 2 561 000      
1994 126 3 600 000 165 000 3 435 000      
1995 120 168 570 34 200 134 370      
1996 417 10 194 400 2 363 600 7 830 800      
1997 239 12 440 000 2 710 00 9 730 000      
1998 132 5 200 000 700 000 4 500 000      
1999 76 3 130 000 30 000 3 100 000      
Average 157 4 771 297 731 950 40 971 570      

 

 

Figure 4. Forest and steppe area burned in Mongolia in spring 2000 (date of satellite image: 24 April 2000). The total area burned was 2.87 million ha. Source: A. Sukhinin, Sukachev Institute for Forest, Fire Laboratory, Krasnoyarsk, Russian Federation.

 

Figure 5. Forest and steppe area burned in Mongolia in spring 2001. The total area burned was 0.84 million ha. Source: Computer Information Center, Mongolia.

 

Figure 6. Open, park-like pine stand (Pinus sylvestris) in the steppe-forest transition zone in Mongolia. The pine forests are regularly affected by surface fires. Photo: GFMC.

Public policies

The underlying causes for a dramatic increase of forest and steppe fires in Mongolia are deeply rooted in the changing socio-economic conditions of the country. The government has recently taken significant steps in this direction through the establishment of a Fire Management Agency. Pursuant to newly enacted legislation, the Mongolian Civil Defence and State Police will transfer their responsibilities to the new agency including associated resources (personnel, budget and equipment).

National endeavors to strengthen fire management capabilities of government institutions as well as local communities have been supported by the Integrated Fire Management (IFM) Project. The GTZ project was terminated at the end of 2000. The FAO in 2000 granted a Technical Cooperation Project (TCP) to improve fire management in Mongolia that will be implemented in 2001. It is planned that FAO and GTZ will collaborate in assisting the country to upgrade its fire management capabilities. For future development the areas of particular concern are:

  • National Oversight – Appropriate oversight will be required: (1) to ensure quality control and preparedness; (2) to help with the standardization of training, procedures, and safety; (3) to provide technical assistance and specialised training; (4) to facilitate cooperation/coordination among agencies; (5) to evaluate training and determine need for additional training; and 6) to determine fire management program needs.
  • National Level Training Centre – Mongolia has a major and complex fire problem. Only a handful of firefighters has received basic fire training. To effectively fight complex and large fires require training beyond the basic level. Wildland firefighters in developed and some undeveloped countries take several higher courses that are more specialized. Large and complex fires require a higher level of understanding of fire behavior, strategy and tactics, and organization. ICS requires multi-agency training of ICS principles.
  • Coordination and Cooperation – A remaining challenge is the coordination of management planning with other institutions and agencies responsible for fire management at the regional and national levels. The project has not had sufficient time to adequately address this need. Nevertheless, experiences tell us that this kind of coordination is an integral part of the decentralization process in Mongolia and will require profound changes at all levels of affected government.
  • Communications System – All interagency team members need a common radio system – one they can program to an incident fire frequency. All agencies should be linked to local and regional dispatch centers.
  • Early Warning Systems – Faster detection means smaller fires, a need for fewer firefighters and greatly reduced expenses associated with firefighting. A system of staffed observers, ground and air, would significantly increase detection capability and significantly speed up fire crew attack and containment time.

IFFN/GFMC contribution submitted by:

Johann G. Goldammer
The Global Fire Monitoring Center

c/o Freiburg University
P.O.Box
D – 79085 Freiburg
GERMANY

Tel:                            ++49-761-808011
Fax:                           ++49-761-808012
e-mail:                       jggold@uni-freiburg.de

 References

The Mongolia country report has been compiled by J. Goldammer, Global Fire Monitoring Center (GFMC) on the base of the following sources published in International Forest Fire News:

Dieterich, J.H. 1991. Fire losses and fire control programs. International Forest Fire News No. 5, 4-5.

Erdenesaikhan, N., and M. Erdenetuya, Researcher. 1999. Forest and steppe fire monitoring in Mongolia using satellite remote sensing. International Forest Fire News No. 21, 71-74.

Ing, S.K. 1999. The social conditions of wildfire in Mongolia. International Forest Fire News No. 21, 75-80.

Shulman, D. 1996. Wildfires in Mongolia 1996. International Forest Fire News No. 15, 30-35.

Shulman, D. 1997. Strengthening disaster response capability in Mongolia. Project accomplishment summary. International Forest Fire News No. 16, 20-22.

Valendik, E.N., G.A. Ivanova, Z.O. Chuluunbator, and J.G. Goldammer. 1998. Fire in forest ecosystems of Mongolia. International Forest Fire News No. 19, 58-63.

Wingard, J.R., and N. Erdenesaikhan. 1998. The German – Mongolian Technical Cooperation GTZ Integrated Fire Management Project Khan Khentii Protected Area, Mongolia. International Forest Fire News No. 19, 64-66

Wingard, J.R., and W. Moody. 2000. Integrated Fire Management: The Mongolia experience. International Forest Fire News No. 23, 16-21.


Country Notes
IFFN No. 26

24. November 2017/by GFMCadmin

Mongolia: Forest and Steppe Fire Monitoring in Mongolia Using Satellite Remote Sensing (IFFN No. 21 – September 1999)

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Forest and Steppe Fire Monitoring in Mongolia Using Satellite Remote Sensing

(IFFN No. 21 – September 1999, p 71-74)


Introduction

Mongolia is a country located in a Central Asian highland with an area of 1,565,000 km2 and a population of 2.3 million, which makes Mongolia one of the least populated countries in the world. The country borders Russia in the North and China in the South. Mongolia is located deep within the interior of the Eurasian mainland far from seas and oceans, is a highland country, and has a markedly continental climate with poor soil fertility, scanty surface water resources, and harsh natural conditions.

Forests and grasslands play an important role in the economic development of the country. Forest covers 10% and grassland 70% of all territory. Mongolian nature and geography, its economic and social features account for its considerable vulnerability to natural disasters. Winters are often very cold, springs are difficult with blizzards, tornadoes and regular wildfires. Heavy rains and floods occur in summers and in autumn heavy snowfalls, frosts and blizzards are common. This means that throughout the year the country is under the pressure from some of these natural disasters.

Some of the disaster experts have estimated the disaster proneness based on the number of human losses. Most of them do not include such natural hazards, like heavy snowfall, drought, or wildfires to disasters unless there are not so many human deaths. But in the case of Mongolia, such hazards cause directly and indirectly much more losses to the livestock and, also damage to the environment. Animal husbandry is one of the most important sectors in the Mongolian economy and still is the basis of our living conditions. This is why meteorological hazardous phenomena and wildfires, which are affecting on pasture conditions, have such a negative influence on Mongolian development as a whole.

Satellite Remote Sensing in Wildfire Disaster Monitoring

There are several satellites for monitoring of natural resources, which have been used also in studies on wildfires over the world. In the beginning of the 1970s, American researchers have studied forest fire mapping and inventory by using Multi-Spectral Scanner (MSS) imagery on board of Landsat satellite series.

The Geostationary Operational Environmental Satellite (GOES) is part of a network of geosynchronous orbiters designed to provide meteorological observations for the entire world. Besides its usefulness in monitoring and measuring cloudiness, GOES have been used to detect large-scale fires indirectly by the identification of smoke plumes

Also, European Resource Satellite ERS-1, American Defence Meteorological Satellite Program (DMSP), Japanese JERS-1, and National Ocean and Atmospheric Administration (NOAA) series satellites are used for vegetation fire studies.

Of the above-mentioned earth resources satellites, the NOAA series satellite is the most suitable for monitoring after the rapid development of natural disasters, such as wildfires, floods, meteorological phenomena, and so on.

The current sequence of NOAA satellites has been in continuous operation since 1978. There are four major advantages of using NOAA series satellites for fire detection and fuel mapping (early warning).

  1. Spectral Resolution. The AVHRR (Advanced Very High-Resolution Radiometer) sensor onboard of NOAA satellite acquires data in 5 spectral channels. The Spectral location of Channel 3 (3.55-3.93 (m), coincides with the radiation of maximum intensity from a black body with a temperature 780 to 800K, and is therefore well suited to the detection of elevated heat sources, which indicate the presence of active fires. Channels 4 and 5 (near infrared channels) are located in the thermal infrared part of the electromagnetic spectrum where all radiation is emitted by the earth surface according to its temperature and radiation and used for estimation of cloudiness, cold surface of the earth. Channels 1 and 2 are invisible and near-infrared parts of the electromagnetic spectrum where all radiation is reflected sunlight and widely used for estimation of vegetation cover.

  2. Spatial Resolution. The resolution of AVHRR data is 1.1 square kilometers. Although the resolution is rather low, due to the very high sensitivity of the channel-3 to the hot sources, even 50m long fire fronts can be detected in the steppe. Full (1.1 km) and lower resolution (4 km) data can be recorded and transmitted directly from the satellite in the High-Resolution Picture Transmission (HRPT) for selected areas of the world within a radius of 2500 km from a receiving station.

  3. Frequent temporal coverage. Currently, there are 2 NOAA satellites in complementary near-polar orbits, NOAA-12 and NOAA-14, one crossing over Mongolia at local solar times of approximately 07:30 and 19:30, and the other at 02:30 and 14:30. The orbital characteristics are such that with two satellites in operation, the possibility exists for twice daily and twice nightly coverage at any point in Mongolia.

  4. Overpass time. The current afternoon, approximately 14:30 overpass time of NOAA-14 is the best available in terms of fire detection and monitoring in Mongolia

Fire damage of the last three years in Mongolia

Forests and grasslands play an important role in the economic development of the country. Forest cover is 12.5 million ha or 8.1% of the Mongolian territory. Forests consist mostly of larch, pine, birch, cedar, spruce, and saxauls (Haloxylon ammodendron). Grassland covers 70% of all territory. During the last few years, Mongolia has experienced various natural or non-natural hazards and of them, one of the most dangerous is Forest and steppe fires.

In an average year, 50-60 forest fires and 80-100 steppe fires occur, annually. About 95 percent of steppe and forest fires in Mongolia are caused by human activities. Although humans cause most fires, nature has the burning materials.

Winters and springs from 1996 to 1998 were extremely dry and were lacking of snow in most areas. From late February to early June, Mongolia suffered from large-scale forest and steppe fires that devastated large parts of the country. Fire damage data are given in Table 1.

Tab.1. Fire damages in Mongolia 1996-98

Casualties

29 people died, 82 people had different kinds of injuries, and 11,700 livestock died, 218 family houses, 1066 communication facilities, 750 fences, 26.3 million ha pasture, and forest burned. The total cost of the property 820.2 million MN¥ (Mongolian Tugrig). Ecological and economical damage estimated as 1,850.5 million MN¥.

According to the statistics since 1963, we can see that the frequency of forest and steppe fires has increased (Fig.1).

Fig.1.gif (11288 Byte)

Fig.1. Number of fires and area burned in Mongolia 1963-1997

The methodology of fire detection and main results of fire disaster monitoring

Since the establishment of the NOAA satellite receiving station at the National Remote Sensing Center of Mongolia, in 1987, the staff of the Center has developed and tested technologies for natural disaster monitoring, such as forest and steppe fire, drought, floods, meteorological phenomena, etc.

Recent fire danger situations in forest and steppe zones challenged staff of the National Remote Sensing Center to test and improve their operational technology to quickly process and transfer data containing burning sites to disaster-related and administrative organizations. In the last three years, 788 fires were detected primarily by satellite data and thus millions of money were saved. The accuracy of detected hot spots as a fire is estimated as 76.9 % of the total number of cases in the last five years.

Figure 2 shows an example of grassland fire dynamics from 27 March to 7 April 1998, on the territory of Dashbalbar village, Dornod Province, the northeastern part of Mongolia near the border with Russia. A total of 984,000 hectares of grassland was burnt in this incident.

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27 March 1998

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29 March 1998

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30 March 1998

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1 April 1998

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7 April 1998

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Total burned area: 983893.85ha

Fig.2. Steppe fire dynamics in spring 1998, Dashbalbar county of Dornod Province, Mongolia, as depicted by NOAA-AVHRR.

Figure 3 shows the burnt areas of Mongolia in fire seasons of 1996, 1997, and 1998.

https://i0.wp.com/gfmc.online/wp-content/uploads/mn_7_9-1.gif?resize=522%2C369&ssl=1 (29433 Byte) https://i0.wp.com/gfmc.online/wp-content/uploads/mn_7_10-1.gif?resize=522%2C369&ssl=1 (27210 Byte) https://i0.wp.com/gfmc.online/wp-content/uploads/mn_7_11-1.gif?resize=522%2C369&ssl=1 (41261 Byte)

Fig.3. Burnt area maps of Mongolia for the years 1996, 1997 and 1998

Figure 4 shows a total fire frequency map in the last 3 years (burnt areas in one year shown in pink, 2 times burnt in 2 years in purple, and areas burnt each year in 3 years in red).

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Fig.4. Fire frequency map of Mongolia for the period 1996-1998

In the last three years, a total of 21,207,464 ha of land was burnt and 75.4% of the total area burned only in one year, 20.5% of the area burnt in each of the two years, and 4.1% burnt in all 3 years.

The burned land area, based on the land cover map obtained from NOAA/AVHRR seasonal data of 1997. The total area of grassland is 78,266,382 ha. The vegetation type most affected by annual fires is grassland.

Conclusions

  1. Development of space technology and its application, integrated use of Geographic Information System (GIS) has provided a new method for natural resource management, natural disaster monitoring, which has received great attention because of their wide view, high observation frequency, and low cost. It is especially sound in the Mongolian context, as a developing country, if we consider the country’s specific conditions: sparse population, vast area, and bad development of infrastructures such as communication and road systems.

  2. Development of the above-mentioned technologies requires a lot of mental and physical investment, and Remote Sensing and GIS technology should be wider introduced for all decision-making systems to ensure human safety, health, environmental protection, and sustainable development of the countries in the world.

N. Erdenesaikhan
Ministry of Nature and the Environment
Government Building No. 3
Baga Toiruu-44
Ulaanbaatar-11
MONGOLIA

Fax: ++976-1-321401
Tel: ++976-1-312269
e-mail: Baigyam@magicnet.mn

and

Ms. M. Erdenetuya
Researcher
National Remote Sensing Center
Khudaldaany street-5
Ulaanbaatar-11
MONGOLIA

Fax: ++976-1-321401
Tel: ++976-1-329984
e-mail: mtt@magicnet.mn


Top
Country Notes
IFFN No. 21

24. November 2017/by GFMCadmin

Mongolia: The Social Conditions of Wildfire in Mongolia (IFFN No. 21 – September 1999)

mn

The Social Conditions of Wildfire in Mongolia

(IFFN No. 21 – September 1999,p. 75-80)


Introduction

The increased awareness in the 90s of “natural disasters” and their effects on the human population has been widely publicized. The destruction which wildfires pose in various parts of the world has not escaped the media’s attention. Yet, seldom reported are the effects which anthropogenic activity has on the natural environment surrounding human populations. There exists a two-way street rarely spoken of. As pointed out by Machlis (1995) the conservation movement has come to recognize that biophysical and social systems are “inextricably intertwined”. Not only are humans effected by natural catastrophes but, to some extent and without intention, even affect them. Hence, the global wildfire trend in many parts of the world is only an example of the effects of human activity in anthropogenically engineered landscapes. It is undeniable that human and social conditions potentially play a critical role in the shaping of the natural environment.

Mongolia, like other countries having abandoned a centralized command economy in the early 90s to embrace an open market one, is currently undergoing the effects of this transition. In addition, the challenges to adapt to political changes from a socialist system to a democratic one in 1996 requires the element of time. Both political and economic level transitions are effected by, and bear consequences at the social level. Similarly, changes at the social level often have a direct impact on the surrounding natural environment. It is with this awareness that plans for the implementation of changes must be considered if they are to be successful in alleviating anthropogenically induced environmental disasters.

Based on the recognition of an inherent symbiotic relationship between the social and natural environments pertaining to the wildfire problem in Mongolia, a four month intensive research study was conducted under the auspices of the GTZ (Deutsche Gesellschaft für Technische Zusammenarbeit) to identify the underlying reasons for increased wildfire occurrence, particularly acute in Mongolia since 1996. The research findings were extensive, touching upon all aspects (political, economic, and social) of Mongolian culture as they pertain to wildfire. This article, for purposes of brevity, will therefore only summarize some of the more particular social conditions relating to the current wildfire problem in Mongolia.

Mongolia’s Current Wildfire Situation

Though Mongolia’s forest types are naturally adapted to fire, the increase in fire frequency and intensity within the past few years has disturbed this naturally occurring cycle. Forests cover approximately nine per cent of its territory (Valendik et al. 1998). This would amount to approximately 17.5 million ha of land. Since 1990, more than one half of the forested area, has been effected by fires, while 10.7 million ha of this amount was burnt in 1996 alone (Tsedendash 1991). In 1996, 368 fires occurred effecting 14 aimags (provinces), more than doubling the figures for normal years of fire occurrence (Mongol Messenger 1998). The continuing trend of fire in Mongolia has been highlighted post 1996 by the fact that 239 fires occurred in 1997, and the latest figures indicate that more than 3.1 million ha were burned during the spring fire season of 1999. All of these fires are thought to be anthropogenically caused. The general belief among those interviewed is that there is a definite correlation between the increase in fires within the past three years and the current economic situation. It is felt that the rise in anthropogenically caused wildfires is a direct result of changes to the country’s socio-economic conditions.

Mongolia’s Current Social Condition

The basic fact is that since the transition to democracy and open market economy Mongolia has, and continues to, develop rapidly. Domestic economic instability in 1991 provided the challenges of inflation and unemployment, plus a large deficit inherited from the absence of Soviet budgetary support. In addition, the country’s economic growth has since this time been largely stagnated perpetuated by its small population, poor transport and communication networks, the existence of few industrial establishments, poor infrastructure, lack of domestic markets, increased poverty, and high unemployment (the most notable change).

Since the beginning of the transition period, open unemployment emerged for the first time in Mongolia (Schmidt 1995). In rural areas some estimates of unemployment run as high as 80-90 per cent. The lack of income among the increasing number of poor in Mongolia and the limited options available to better the situation has meant a turning toward the only alternative possible under such conditions – dependency on natural resource utilization. The collection of natural resources for both personal consumption as well as sale is often seen as the only option for survival.

Hence, dependency on natural resources for means of subsistence has led to dramatically increased pressures on natural surroundings and protected areas. It was reported that there is generally no choice for people but to use natural resources for subsistence survival. Some people have exhausted their numbers of livestock by selling them off for food and clothing and have in the process become very poor with little alternative but to gather and sell natural resource products. Particularly the young are forced to sell these products to support their families. Some of the main activities conducted for purposes of income generation include logging, fuelwood collection, hay making, hunting and fishing, and, most importantly, the collection of non-timber forest products (deer antlers, pine nuts, berries, herbs and grasses). As alternatives for income diminish, so does the concern for nature in general: “People are interested in nature in order to find a profit, instead of protecting it. Because Mongolians export deer horns and deer tail at high prices” (personal interview). It was said that the past three years has been particularly “bad” in terms of the numbers of people going into the forest due to everyone’s current need for a means of acquiring an income.

Physical Mobility: A Move for the Better?

To accentuate the problem of increased human activity in natural areas is the general trend in increased migration patterns. Increased human activity in more natural areas is contributed to by the general increase in physical mobility, as people more actively move about in the hopes of improving current social conditions. Not only is the rural population dependent on natural resources, but so also the urban population. Hence, the impact of physical mobility on wildfires is said to be significant as urban dwellers travel to natural areas and are believed to, out of inexperience and carelessness in dealing with nature, cause the occurrence of wildfires.

Significantly contributing to the rise in physical mobility is, in particular, the return to the traditional occupation of livestock herding. The basic reason for this shift to a pastoral way of life is largely, if not solely, due to the current economic downturn since the onset of market economy. Many feel that raising livestock is the only sensibly viable solution against increasing unemployment, poverty, and inflation. However, this trend has significant impacts on the shaping of, not only the communities or social environments which it effects but also, the natural environment, upon which the communities depend. Against the backdrop of uncertain economic times, a large portion of the population are no doubt merely trying to survive. However, this means of survival cannot be deemed sustainable if the current trend is to continue. As is the case in many developing countries, a compromise is currently being made, whereby human subsistence is weighed against humanly dependent natural areas.

A direct result of these additional pressures, connected to the trend in occupational herding, is the increasing potential for anthropogenic wildfire occurrence through increased factors of risk. Risk factors include intensive natural resource utilization and rangeland preparation – possibly with the use of fire. Hence, it is to be expected that an increase in occupational herding, unless better controlled, will inevitably have a significant impact on the future of the environment and fire management strategies.

Impediments to the Reduction of Anthropogenic Wildfire

Measures to alleviate the wildfire problem has been said to have been hindered by the challenges dealing with environmental law implementation and enforcement. It was said that law enforcement improvements should be the onus of the people to not only be more careful with fire, but also be more responsible in the appropriate implementation of environmental laws. Since the jobs of law enforcement officers is seen to be difficult, it was expressed that local citizens must assist them by informing them of activities in the forest. However, difficulties in social conditions is said to be largely responsible for the inability of local citizens to act responsibly in enforcing the laws.

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Fig.1. The rural communities in Mongolia face difficult living conditions after the political and socio-economic changes in the country.

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Fig.2. Mongolian herdsmen at the highly flammable steppe-forest interface of Mongolia. Photos: Soo Kuen Ing

The problems of weakening social controls has been associated with the transition to democracy and market economy. The attitude expressed by many is that, for most people, “watching over our livestock is our only concern” (personal interview). People tend to show a lack of interest in getting involved with the dealings of others during difficult times, as was expressed by a local in this way: “if one of them were my acquaintant, I would not automatically betray him to the police. Since it is a small soum (county), there are only a few people, so we do not automatically betray each other” (personal interview). Law enforcement is hindered as empathy for the other is high in the face of current economic hardships.

In addition, the general lack of knowledge on laws was blamed on poor information dispersal since democracy. Though it was said that radio and television stations do, on occasion, broadcast laws, many citizens have no access to either source. It was often mentioned that newspapers and other methods of obtaining information are also difficult for rural citizens to acquire, coupled with a general lack of interest on legal issues. Those who had some knowledge of environmental laws claimed the inappropriate implementation of some of them. An example mentioned was the 1997 issued Order by the Minister of Nature and Environment which prohibits people to enter the protected area from 10 March – 1 June (since this time period coincides with the spring fire season). However, as this time of year also coincides with the period for antler collection it was voiced to not be in conformity with the needs of the people, resulting ironically in increased wildfire risk: “If we allowed people to go they would not cause a fire. If we forbid people to go then they would go secretly. If they happen to see us going to do our usual check up in the forest they run away after causing the fire” (personal interview with forest ranger). Hence, there is a clear problem noted in regards to the appropriateness of the Order. Whereas people used to go with permission (enabling monitoring and control), the new Order no longer allows the issuing of permission during this period, resulting in people stealthily entering the forest. The implementation of the Order is, therefore, inappropriate and counterproductive to meeting objectives to reduce wildfire risk.

The breakdown in law enforcement effectiveness is thought to rest upon the general weakening of responsibility at the federal and provincial levels. It was expressed that if these levels of government were to tighten up on law enforcement controls then local law enforcement would also improve. In cases pertaining to violations of environmental law it is usually the rangers and the environmental state inspector who enforce the law. However, as law enforcement officers in natural areas are limited in their means and authority to better control the situation legal structures are additionally weakened. Law enforcement is largely ineffective as for some no “real” punishment can be issued for illegal use or entry into the forest, since often the only risk is confiscation in the amount of fee payment. Permits for forest use and prohibition laws are often of no use and not enforceable under the difficult living conditions. Persons who cause fires cannot be penalized when the individual, as is true in many cases, has no means of paying fines. To make matters worse, enforcement officials are in a position where they are unable to properly enforce laws, as social conditions are drastic and the number of those breaking the law greatly outnumber officials. Due to governmental constraints in funding, patrolling must be currently done with privately owned modes of transportation (e.g. using one’s own horses). Even articles for purposes of self defence are the private property of officers. Hence, environmental law enforcement is weakened to the extent that it is not fully supported by higher government levels resulting in haphazard, largely inefficient, and non-standardized practices.

Toward a Holistic Socio-Ecological Understanding of Wildfire

With closer examination, it becomes obvious that the current wildfire problem in Mongolia is complex. The basic underlying reasons for the increase in wildfire occurrence, particularly noticeable since 1996, are directly related to the effects of the fundamental issues of poverty and inappropriate development. These issues are at the heart of most of the potentially negative trends.

Increased herding practices supplemented by lowered education, resulting in an increase in natural area and resource utilization, and the elevation of anthropogenic wildfire risk must be broken in order to effectively and sustainably tackle the problem of recently increased anthropogenic wildfire occurrence. Alternatives addressing the above social issues is necessary to counter the trend in lifestyle change. Sustainable herding practices would mean a reduction in the numbers of herders and the creation of a better infrastructure to provide avenues for business and trade, while education, particularly targeting male youths, must become more accessible in preparation for other occupations.

Urban to rural mobility has a great impact on the increased numbers dependent on natural resources. As support measures to rural areas become limited or absent due to governmental constraints employment or development opportunities continue to decrease thereby increasing poverty, and further promoting dependency on natural resources for locals’ subsistence and income. When life becomes unaffordable in urban centres people are forced to move into the country where subsistence often does not depend on money but rather on resources for trade and barter. In addition, if local statements indicating an increase in the use of rural environmental areas by urban dwellers for purposes of income generation are accurate then fire management plans need to address this issue with increased and more widespread active prevention programs within more urban areas as well. Due to the obvious correlation between poverty in rural areas with the amount of dependency on natural areas and their resources, physical mobility trends must be more fully understood so as not to become immense barriers to the successful implementation of fire management plans in the reduction of anthropogenic wildfire occurrence.

As poverty is one of the main reasons for the heavy reliance on natural areas and their resources, the development of rural areas is crucial for the alleviation of current pressures. Unemployment and the current trend in the uneven distribution of wealth and opportunity since the transition to market economy only further emphasizes the need to address these problems. Under the present situation, rural development would require conscious efforts to be made in the creation of incentives focusing on decreasing human dependency on natural areas. Living conditions to address the level and extent of poverty must be improved. Only through these changes can both physical and social mobility patterns hope to be altered as social demands on natural areas be reduced to minimalize anthropogenic wildfire risk and potential occurrence.

Some of the research’s findings, as given here, illustrate under which social conditions the occurrence of wildfire are dependent for its reduction or increase. Though it is often assumed that the problem of increased wildfires is the result of decreased awareness through reduced propaganda or education warning against fire, the study has revealed that a general awareness of the dangers of fire does exist, but that out of general need, people are currently not in a position to effectively eliminate the occurrence of anthropogenic wildfire. Social needs must first be addressed. Hence, awareness, though it does play an important role, is not the key issue to be addressed for the long-term reduction of wildfires. Education is not enough as measures must be taken to ensure a more stable social environment. The true problems must be recognized before they can be suitably addressed. Resonance of the state of the social environment goes on to effect the surrounding humanly-influenced “natural” environment. The uncovered trends revealed in the research serve to assist in the recognition of the wider social conditions currently having an impact on the recent increase in anthropogenic wildfire for the areas of Batschireet and Mongonmort.

Support for the conservation of nature must be accompanied by a valuing of it at all levels – individual, local, national, and global. In Mongolia, this issue is a sensitive one. Current social conditions have caused an overvaluing of the natural environment for its resources resulting in an elevation in wildfire risk and occurrence.

It is hoped that the results of this study will assist in addressing pertinent social issues before they become unsurmountable and cause irreparable damage to the natural environment upon which the social environment in Mongolia so greatly depends. If not addressed, the social problems revealed in this research study will continue to exist regardless of whether wildfire occurrence continues to be the symptom. It must be remembered that wildfire occurrence is only one expression, one symptom of larger underlying problems prevalent within the social environment. Human activity and its effect on natural surroundings can no longer be denied. To ignore the social issues as noted would only result in the generation of new, recurring, and / or continued existence of current undesirable symptoms within the environment around Batschireet and Mongonmort – natural or otherwise. Action must be taken or irreparable damage to the natural environment through wildfire occurrence could very well be nature’s final means of addressing the problem for us. A socio-ecological balance must, therefore, be sought after. Improvements need to be made to the area of law implementation and enforcement. The trend toward a breakdown in social controls is but yet another symptom of the serious concerns which need to be confronted within society. Poverty, inflation, and unemployment are some of the major societal ills which need to be addressed.

Environmental lawlessness is born out of the survival needs of the people who are currently living in difficult economic times. Should the above mentioned problems be reduced or eliminated, the consequence could very likely be a turn to the adherence of laws.

Conclusions

The study revealed that the current problem of wildfire in Mongolia is largely a result of the causal relationship which exists between the social conditions now existent in Mongolia and the activities which are born out of the needs of the people. According to those interviewed, it is a fact that the increase in the number of wildfires since the mid-1990s corresponds to changes in social conditions.

Recognition of the symbiotic relationship between social conditions, human activity in natural areas, and the occurrence of anthropogenic wildfire stresses the importance of each of these components for the effective minimalization of the current anthropogenic wildfire problem in Mongolia. Since both natural and social environments are so closely interconnected and interdependent of one another for a healthy existence, a fragile balance must be strived for to ensure the well-being of both. There is a very strong anthropogenic component to the seemingly “natural” wildfire problem in Mongolia. In recognizing the importance of this relationship, it is necessary to address the problem of wildfire in Mongolia holistically and in accordance with social scientific values. Local needs and sustenance requirements must be considered since natural resource utilization is bound up with these needs. If the basic social and economic requirements of the local population were to be adequately met then future pressures on these environmental areas would be reduced as a direct consequence. An awareness of the symbiotic relationship which humans share with their environment is of fundamental importance in understanding the causes and effects of this interaction in order to alter the current negative wildfire trend.

References

Machilis, G.E. 1995. Social science and protected area management: The principles of partnership in expanding partnerships in conservation. Island Press, Washington, D.C., 45-57.
Mongol Messenger. 1998. Ulaanbaatar, Mongolia. March 11.
Narangerel. 1997. Some factors of forest fires in temperate forest conditions. Ulaanbaatar, Mongolia. Unpublished.
Schmidt, S. 1995. Mongolia in transition. The impact of privatization on rural life. Verlag für Entwicklungspolitik. Saarbrücken, Germany.
Tsedendash, G. 1991. Forest Features of Mongolia. Ulaanbaatar, Mongolia. Unpublished report.
Valendik,E.N., G.A.Ivanova, Z.O.Chuluunbator, and J.G.Goldammer. 1998. Fire in Forest Ecosystems of Mongolia. Int. Forest Fire News No. 19, 58-63.

 

Soo Kuen Ing
Global Fire Monitoring Center (GFMC) & Fire Ecology Research Group
Max Planck Institute for Chemistry, c/o University of Freiburg
P.O.Box
79085 Freiburg
GERMANY

Fax:  ++49-761-808012
e-mail: sooing@hotmail.com


Country Notes
IFFN No. 21

24. November 2017/by GFMCadmin

Mongolia: Integrated Fire Management (IFFN No. 23)

mn

Integrated Fire Management: The Mongolia Experience

(IFFN No. 23 – December 2000, p. 16-21)


Introduction

After a grueling 14 hour drive across seemingly endless expanses of rolling steppe, we arrive at our destination – the outskirts of a small town in northern Mongolia. The temperature is -20°C with stinging winds blowing out of the Northwest at 30 knots. Our small team of eight people is greeted by an even smaller contingency of firefighters – four men on horseback equipped with wet rags and blankets as their only tools. It is early spring 1998, the beginning of the fire season and we have just arrived at the scene of the first fire in the region. It is also the starting point for the German-funded Integrated Fire Management Project. The goal is to develop a fire management concept for one of Mongolia’s largest protected areas and its surrounding communities.

The scene we witnessed that spring morning is common, but the fire is earlier than normal. Following a general trend in Asia, fire seasons in Mongolia are starting earlier, lasting longer, and are more intense. Recent seasons have highlighted a drastic increase in wildfires. Available statistics indicate that historically an average fire season affected 1.74 million hectares of forest and steppe annually. From 1996 to 1999, more than 30 million ha have gone up in smoke – in four short years, an area larger than Holland or about half the size of France. Some of the hardest-hit areas have been the taiga forest regions in the north. In the last four years, more forested areas burned than were harvested in Mongolia over the last 65 years. The brief growing season and low growth capacity of the trees mean that these forests may take 200 years or more to regenerate.

Background

Mongolia has two fire seasons – a spring fire season (February to early June) where all fires are human-caused, and a short, less intense fall season (September to late October) again entirely human-caused. At least 90% of all fires occur during the spring. Lightning strikes during the summer season (when most precipitation falls) can cause fire, but are rare and result in minimal loss. Major fires occur in the steppe zones, the mountain forest-steppe transition zones, and the primary forested area-the taiga. In the mountain forest and steppes, grass dominates the south slopes while Siberian larch (Larix sibirica), Siberian and Scotch pine (Pinus sibirica and Pinus sylvestris), and White birch (Betula rotundifolia) dominate the north and eastern slopes. Fanned by strong spring winds, fires spread quickly in the steppe. Devastating stand replacement fires are common in both the mountain forest-steppe and taiga forests.

Until recently, a branch of the military known as the Civil Defense centrally managed fire events in Mongolia. The military maintained all training regimes, equipment, and personnel with virtually no support to local communities. With the transition and associated economic difficulties, this centrally managed fire fighting system has collapsed.

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Fig. 1. Number of Fire Occurences and Size of AffectedSteppe and Forested Area by Year (1963 – !997).

Perhaps the single most important contributor to the increase in fire spread is the grounding of the Aerial Patrol Service. In 1969 the Mongolian Fire Protection and Aerial Patrol Service were established to provide early detection and rapid initial attack on fires. The program was a Soviet style aerial detection / airborne firefighting program staffed with 200 to 300 smokejumper / helicopter rappellers and a fleet of helicopters for helitack and tactical aerial support. The aerial forces operated out of seven bases distributed throughout the fire-prone regions of northern Mongolia. Smokejumpers on routine aerial patrols detected a high percentage of the fires and handled approximately 90% of the suppression workload. In the early 1990’s, when the communist government and Soviet financial support abruptly disappeared, the Mongolian aerial program took a nosedive. At present, Mongolians cannot afford to maintain and fly their aerial patrol aircraft. Instead, they must rely on NOAA satellite imagery as their primary early warning system with a spatial resolution of 1.1 km2. The decline of the aerial program through the mid-1990’s resulted in the creation of a “fire suppression void” and no doubt greatly contributed to the horrendous fire losses experienced in the 1996 and 1997 fire season

The increase in the number of fires is related to the opening of markets once highly controlled or restricted. The vast majority of fires are not deliberately set to clear land. Rather, it is a function of carelessness. One example is the collection of elk antlers for sale to European and Chinese markets. During the previous regime, a single, state-run enterprise managed this market under strict controls and guidelines. Today, it is open to virtually anyone. Fires start for three reasons: (1) collection starts in the bitter cold of February where the fire is simply a survival tool; (2) sparks fly from vehicle exhaust pipes driven into remote forests, and (3) tracer bullets left by the Russian military have entered the game hunting market and are used to hunt elk for the blood antlers which have a higher value on the market place.

Innovative Solutions – an Integrated Approach

Assessment of the devastating 1996 and 1997 fire seasons highlighted the need for decentralizing fire management including the development of locally organized handcrews and implementation of an aggressive grassroots fire prevention / fire fighting program. In February of 1998, the German and Mongolian governments signed an agreement to start an Integrated Fire Management Project to be implemented over the next three years. The priority target areas selected were the buffer zone Soums (districts) surrounding the south-end of the Gorkhi-Terelj National Park and Khan Khentii Strictly Protected Area, an area hard hit by the 1996-1997 firestorms.

Defining Integrated Fire Management

Integrated Fire Management, like other community-based programs, focuses on flexible, pragmatic approaches designed to support local people’s role in resource management. Specifically, it entails the application of the art and science of modern wildland fire technologies and practices to the local fire problem – i.e. the community level.

Fire management is most effectively broken down into three discrete components: (1) prevention, (2) pre-suppression, and (3) suppression.

  1. Prevention includes all measures that help prevent the outbreak of fires or help the reduction of the fire severity and spread. A comprehensive fire prevention program uses all three elements of education – engineering and enforcement to reduce risk, hazards, and exposures. Education and enforcement programs target risk while engineering targets hazards and exposures.
  2. Pre-suppression is typically defined as the actions and activities needed to ensure suppression organizations are fully prepared for any required wildfire suppression measures. The central focus of pre-suppression work is management planning and GIS-based mapping.
  3. Suppression refers to the activities and actions involved in controlling and extinguishing unwanted wildland fires, including the establishment, training, and equipping of fire management units.

 The sustainability of this kind of fire management program depends on four factors:

  • Development of methods that focus on the practical capacity of local communities and seek to integrate component activities for fire prevention, pre-suppression, and suppression.
  • Development of mechanisms for inter-institutional cooperation between and among all involved and/or affected organizations and individuals
  • Laying the groundwork for effective coordination prior to and during fire events
  • Establishing a framework for appropriate oversight at the national level to integrate the above-mentioned components (common goals and activities) as well as to standardize administrative procedures, training programs, strategies, tactics, material, and equipment

Local Community Capacity Building

To date, the focus of the IFM Project has been capacity building at the local community level. Using participatory methodologies such as PRA (participatory rural appraisal), participants identified specific activities for prevention, pre-suppression, and suppression components.

Fire Prevention

In the development of the program, the IFM Project started with the philosophy that an ounce of prevention is worth a pound of cure. Hence, the most effective fire suppression strategy is an effective fire prevention program. In the summer of 1998, the IFM project began pilot activities in the buffer zone communities surrounding the Khan Khentii Special Protected Area. Specifically targeted were the potential multipliers including, Information Training Center (ITC) “extension” officers, educators, protected area rangers, key community persons. Together with them a number of educational materials have been developed and introduced including: (1) a fire prevention curriculum for school children; (2) a fire prevention video; (3) a ranger’s handbook to be used as an outreach tool in remote areas; (4) a coloring book for small children; and (5) a fire mascot to carry the prevention message.

Pre-Suppression

The central focus of pre-suppression work has been the drafting of a fire management plan for the protected area administration and local communities. Planning, however, is hampered by history. The planning process was a form of strict control. All plans were in essence a promise to perform. Failure to fulfill the objectives could be dealt with harshly. Managers are naturally tentative when it comes to spelling out activities and tend to convert planning documents to long-winded descriptions of the problem or resource. To overcome these difficulties, the project has worked to redefine the Fire Management Plan as a “Management Guideline” allowing managers to treat the document with the necessary flexibility.

To support pre-suppression activities, the IFM Project has engaged in a comprehensive fire management mapping effort. In an initial stage, NOAA-14 satellite imagery has been compiled to show annual fire coverages with overlays on forest types. In a second phase, the project helped to design fire risk, hazard and danger maps at a scale of 1:100,000 for the entire region. Further development of these maps is in progress.

Suppression

Suppression goals include (1) the establishment of fire management crews, (2) provision of equipment and (3) the development of a locally run “Fire Training Program” customized for Mongolian conditions-its fuels, fire behavior, available suppression resources, and logistics. In the spring of 1998, six Soum (district) governors in the protected area buffer zone formed fifteen-person (15) fire management units (FMUs – or suppression crews) for their respective Soums. The crew consists of a crew boss, assistant crew boss, and thirteen unemployed volunteers. The crew is jointly managed through a Memorandum of Understanding between the local community and the protected area administration.

After the establishment of the crews, the project identified equipment to match the fuel conditions. Fuel conditions throughout Northeastern Mongolia closely resemble the fuel types of the western United States, British Columbia, and interior Alaska-tough steppe grass with deep dense roots, brush, larch, pine, spruce, birch, moss, and muskeg like valley bottoms. GTZ equipped the crews with fire swatters, fire shovels, Pulaskis, Adze Hoes, fire rake (Council type), backpack pump, crosscut saw, a chainsaw and hardhats. Each crew has been equipped with personal portable radios, a vehicle mobile radio, and mobile repeaters for communications with the dispatch center. Stationary repeaters are being installed to link the Soum dispatch centers with the national coordination center in Ulaanbaatar.

Starting in March 1999, the project assisted Mongolian fire specialists in developing a series of training materials including a 32 – hour Basic Firefighter Course with accompanying Instructor’s Manual, Student Workbook, training videos and Crewboss Manual. The training programs were adapted from existing Mongolian training and the basic courses used to train American wildland firefighters-Introduction to Wildland Fire Behavior (S-190) and Firefighter Training (S-130) and basic Incident Command System concepts. Approximately one-half of the course was conducted in the field, including “live burns” for mop-up and a final day live-fire exercise. Crews were instructed in the bump-up progressive crew method of fireline construction. A fire instructor’s training course for Mongolian instructors followed this. In a subsequent phase, we observed and coached Mongolian instructors as they trained “rookie FMU crew members” and community (Soum) fire support crews. Due to unusually high precipitation during the winter, however, the project has been unable to evaluate crew performance on fires.

Inter-Institutional Cooperation

Effective resource management requires inter-institutional cooperation in part due to overlapping responsibilities, but also because of the need to share institution or agency resources. This is even truer with fire because, (1) fires can occur anywhere the right conditions exist and (2) unlike some resources (such as forests), fire moves – and its devastating path affects everyone as it inflicts damage to soil, water, wildlife, vegetation, air quality, and human beings.

Mongolia has recognized the need for a pluralistic approach to fire management in legislation, however mechanisms for inter-institutional cooperation have not yet been clearly defined. Most actors, particularly in the rural locations where the project is active, remain cut off from regional and national level resources. The IFM Project is assisting with the first moves in the arena by helping to establish cooperative agreements between the protected area administration and local governments for the joint management of the established fire management units. These agreements however are relatively simple in form and function and do not encompass regional or national level agencies.

Effective Coordination

Fire events are life-threatening and without proper coordination in the field can be unnecessarily dangerous. It is, therefore, imperative that coordination be spelled out as part of normal planning activities. Several countries achieve this through the Incident Command System. It is essentially a military concept of the organization, adapted for disaster management – fire, floods, earthquakes, etc. The organization expands or contracts depending on incident size, needs, or complexity. If all the components are in place and everyone is playing the game, the incident is handled efficiently. It is designed to be an inter-agency or single agency / small fire or major widespread firestorm. All participating agencies are trained to work together, often on the same team, sharing the resources needed to get the job done. Essential ICS components include:

  • common terminology (equipment, strategy/tactics, standards etc )
  • modular organization with five functions – Command, Plans, Logistics, Finance/ Administration and Operations (the firefighters)
  • Integrated communications
  • Unified command if multi-jurisdictional
  • Consolidated Action Plan for each work shift
  • A designated “span of control” (3 -7 per supervisor)
  • Designated incident facilities
  • Properly trained and equipped disaster specialists (firefighters)
  • Resource management (continual accountability for all resources)

 National Oversight

In a decentralized fire management environment, the need to maintain oversight remains. This does not mean direct involvement in implementation, but rather the development of policies, norms, guidelines, and procedures that are conducive to or supportive of the initiatives taking place at the regional and sub-regional levels. At a minimum, it means (1) creating an open forum for discussion (open-door policy-making) inclusive of all stakeholders, (2) compiling, analyzing, and distributing information that supports informed decision-making, (3) standardizing procedures and practices, and (4) continuous monitoring, evaluation, and improvement of existing policies. Without this oversight, fire management initiatives at the community level risk becoming an island solution with little chance of replication in other areas.

Mongolia has recently taken significant steps in this direction through the establishment of a Fire Management Agency. Pursuant to newly enacted legislation, the Mongolian Civil Defense and State Police will transfer their responsibilities to the new agency including associated resources (personnel, budget, and equipment).

Conclusions

After a short two years of project life, it is still too early to claim the successful development of a comprehensive model for integrated fire management.

Areas of particular concern are:

  • National Oversight – Appropriate oversight will be required (1) to ensure quality control and preparedness; (2) to help with the standardization of training, procedures, and safety; (3) provide technical assistance and specialized training; (4) to facilitate cooperation/coordination between agencies; (5) to evaluate training and determine the need for additional training; and 6) to determine fire management program needs.

  • National Level Training Center – Mongolia has a major and complex fire problem. Only a handful of fighters has received basic fire training. To effectively fight complex and large fires requires training beyond the basic level. Wildland firefighters in developed and some undeveloped countries take several higher courses that are more specialized. Large and complex fires require a higher level of understanding of fire behavior, strategy and tactics and organization. ICS requires multi-agency training of ICS principles.

  • Coordination and Cooperation – A challenge remains the coordination of management planning with other institutions and agencies responsible for fire management at the regional and national levels. The project has not had sufficient time to adequately address this need. Nevertheless, experiences tell us that this kind of coordination is an integral part of the decentralization process in Mongolia and will require profound changes at all levels of the affected government.

  • Communications System – All interagency team members need a common radio system – one they can program to an incident fire frequency. All agencies should be linked to local and regional dispatch centers.

  • Early Warning Systems – Faster detection means smaller fires, a need for fewer firefighters, and greatly reduces expenses associated with firefighting. A system of staffed observers, ground, and air, would significantly increase detection capability and significantly speed up fire crew attack and containment time.

Contact address

James R. Wingard
Principal Advisor, GTZ Integrated Fire Management Project
Ulaanbaatar
MONGOLIA

Tel/Fax: ++976-1-320886
E-mail: jrwingard@magicnet.mn

William Moody
North Cascades Fire Service
Twisp, Washington
U.S.A.

Tel/Fax: ++1 509-997-5971
E-mail: bmoody@methow.com


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| IFFN No. 23 | Specials | Country Notes |

24. November 2017/by GFMCadmin

Mongolia: Fire Losses and Fire Control Programs (IFFN No. 5 – June 1991)

mn

Fire Losses and Fire Control Programs

(IFFN No. 5 – June 1991, p. 4-5)


The Mongolian People’s Republic continues to be faced with wildfire problems that over the years have destroyed lives, homes, livestock, improvements, and valuable natural resources. During the spring of 1990 a forest fire, burning in the Bulgan and Selenge Districts of Northcentral Mongolia, burned an estimated 600,000 hectares. This same spring another individual fire burning in the steppe (grassland) of Northeastern Mongolia (Dornod District) destroyed homes, animal shelters, 300 tons of hay, and over 3,000 head of livestock before being controlled at more than 600,000 hectares.

Records indicate that the average annual forest area burned for the 22 year period (1963-1985) was 145,000 hectares. More recent statistics for the four year period 1986-1989 (see table below) show an average of 43,000 hectares of forest land burned – well below the 23-year average. Steppe fire losses for the same 4-year period totaled more than 5.6 million hectares for an annual average of more than 1.4 million hectares.

The nucleus of the Mongolian fire control organizations is a cadre of 150 smokejumpers located at six field sites in the Northcentral and Northeastern part of the country, and at the headquarters in Ulaan Baatar, the capital city of Mongolia. The smokejumper unit was established in 1969 and received much of its early training from the Soviets who have a long history of utilizing aerial operations in wildland fire fighting. The Mongolian fire control organization is currently doing most of their own training and recently received a smokejumper simulator through FAO that will be used in refresher training for experienced personal and for introductory training for new recruits.

Operating on the premise that a rapid initial attack is the best means of keeping fires small the smokejumpers utilize the AN2 single-engine bi-plane and the MI8 helicopter to transport the jumpers to the fires and for flying fire detection patrol….many of which have a squad of jumpers on board so fires can be attacked as quickly as possible.

Strong winds that may continue for several days are common during the spring fire season. When fires start and burn under these conditions, the planes are frequently grounded, smoke jumping is too hazardous, and fires are difficult to control. Conventional fire fighting methods are mostly unsuccessful in these situations and considerable effort is expended toward protecting life and property ahead of the fire. Future considerations are being directed toward preparing fuel breaks, especially in the grassland areas, so that backfiring during major fire incidence will have some opportunity for success.

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From: John H. Dieterich
Address:
630 E. Wesleyan Dr.
USA – TEMPE, Arizona 85282


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Country Notes

24. November 2017/by GFMCadmin

Mongolia: Community-based Wildfire Management in Mongolia (IFFN No. 23)

mn

Community-based Wildfire Management in Mongolia

(IFFN No. 23 – December 2000, p. 57-60)


Preface

It is a fact that the number of wildfires has increased since the early 90s corresponding to changes in social conditions. Though, there are currently three distinct fire seasons which effect the forests of Mongolia, the evolution of the spring and fall fire seasons, accounting for approximately 85-88 per cent (Valendik et al. 1998), is a reflection of increased anthropogenic pressures responsible for wildfire ignition. Hence, the dramatic increase, particularly within the past three to four years, has been “socially” induced by humans. Drastically increased human activities within natural areas have caused a strain on natural environments, effecting an unnatural increase in wildfire occurrence in Mongolia. Recent increased human activity within natural areas has been recognized to be the cause of the current increase in anthropogenic wildfire. The study has revealed that the current problem of wildfire in Mongolia is only a symptom of the dysfunctioning relationship between humans (caused by their activities) and their natural environment. The reasons explaining the causes of human activity responsible for the increase in wildfire occurrence are more indirect and less apparent.

The Social Conditions of Wildfire in Mongolia

Political

For the first time, a nominally democratic system is now in force in Mongolia. A wide range of tasks has thus been decentralized and delegated to local authorities. Many local governments have been overwhelmed by the enormous commitments referred to them by the central government and ministries (Bruun 1996). Responsibilities are neglected and policy implementation has suffered as a consequence. Apparently, the blurred division of authority has made decision-making less transparent and also less legitimate in some localities, as compared to the state of affairs before the introduction of democratic reforms in local governance.

Economic

In January 1991 Soviet aid disappeared and Soviet advisers left the country. As a result, Mongolia has suffered from external shocks to the economy. The loss of trade and aid left large gaps in external trade and fiscal balances which were too wide for Mongolia to cover with stabilization measures alone (Rana 1996). One of the main problems to the implementation of effective economic reforms is the natural geographical barriers of distance. Coupled with very poor infrastructure the country has had to suffer great polarities in economic development distribution. Whereas the command economy in practice suspended the significance of geographical distance by means of cheap and abundant energy supplies, the transition to world market prices on fuel has certainly sharpened the Mongolians’ awareness of distance, both within their own country and in terms of their location in the world. Especially those living in rural areas are unable to buy or sell products. The distance and lack of available, or affordable transportation make trading nearly impossible. When trading does occur then only under the conditions as set by travelling merchants, thus rural people are at a highly disadvantaged position for fair trading. In rural areas, only an average of thirty per cent of the total income is said to be in cash while the rest is in kind. In urban areas the average is seventy per cent in cash (Bruun 1996). However, it has been said that semi-nomadic livestock herders tended to suffer less than their urban countrymen during the national crisis of the early 1990s (Bruun 1996) which is perhaps the reason for the fact that herding is becoming increasingly popular during difficult economic times.

Social

The poor economic situation in Mongolia has led to a breakdown of social services which were once heavily subsidized by the state under the socialist system. The lack of income among the increasing number of poor in Mongolia and the limited options available to better the situation has meant a turning toward the only alternative possible under such conditions – dependency on natural resource utilization. The collection of natural resources for both personal consumption as well as sale is often seen as the only option for survival. The result of this dependency on natural resources has led to dramatically increased pressures on natural surroundings and protected areas. The majority of the population now relies on natural resources for its subsistence. It is estimated that particularly the young are forced to sell natural resources to support their families. Some of the main activities conducted for purposes of income generation include logging, fuelwood collection, hay making, hunting and fishing, and, most importantly, non-timber forest product collection. Since the overriding majority of the population heavily depends on these resources for their subsistence and overall survival, issues of natural ecosystem maintenance and sustainability have become a clear concern.

Trends in Findings Pertinent to Anthropogenic Wildfire Occurrence

Increase in Occupational Herding

A direct result of economic and social pressures is the trend toward an increase in occupational herding which heightens the potential risk for anthropogenic wildfire occurrence. Risk factors include intensive natural resource utilization and rangeland preparation – possibly with the use of fire. The growing influence of this group should be recognized when considering the implementation of fire management plans. Hence, it is to be expected that an increase in occupational herding, unless better controlled, will inevitably bear a significant impact on the environment and fire management. Especially due to the recognition of the growing influence of herders, alternatives to this occupation should be sought to alleviate the pressures on natural areas and their resources before problems of natural degradation or wildfire become uncontrollable. Sustainable herding practices would mean a reduction in the numbers of herders and the creation of better infrastructure to better promote avenues for business and trade, while education, particularly targeting male youths must become more accessible to increase levels of qualification for other occupations.

Increased Physical Mobility

A noted increase in migration has been observed in Mongolia particularly within the past five years as the effects of market economy have made their toll. Since the beginning of the transition process, open unemployment emerged for the first time in Mongolia (Schmidt 1995). In rural areas some estimates of unemployment run as high as 80-90 per cent of the population. The trend toward increased physical mobility is economically related. The lack of infrastructure, income, employment opportunities, and means to financial assistance are the primary motivators of physical mobility as individuals seek to improve personal situations. The increase, particularly in urban to rural mobility is a great concern for discussions on wildfire management since this trend is also largely connected to the trend in a return to occupational herding practices, as mentioned above. Urban to rural mobility also has a great impact on the increased numbers dependent on natural resources. When life becomes unaffordable in urban centres people are forced to move into the country where subsistence often does not depend on money but rather on resources for trade and barter.

Increased Social Deviance in the Adherence of Laws

In addition to the problem of poverty is the establishment of new laws that are deemed inappropriate and inapplicable given the current social conditions in these areas. An example is the law prohibiting entry into protected areas for the collection of natural resources from 10 March to 1 June which only serves to eliminate previously established forms of control. Whereby compulsory registration for forest entry and natural resource extraction were commonly practiced, the inappropriate new law now prevents this form of control. Such laws are not only counter productive to ensuring that natural areas be protected, but also undermine the authority of enforcement officers leaving them powerless to control the situation and, in the case of fire occurrence, to detect the person responsible. Hence, the enactment of inappropriate new laws and the inability of locals to change their current behaviour are felt to be a couple of the main problems in the area of law implementation.

As law enforcement officers in natural areas are limited in their means and authority to better control the situation, legal structures are additionally weakened. Law enforcement is largely ineffective as, for some, no “real” punishment can be issued for illegal use or entry into the forest, since often the only risk is confiscation in the amount of fee payment. Permits for forest use and prohibition laws are often of no use and not enforcable under such difficult living conditions. Persons who cause fires cannot be penalized when the individual, as is true in many cases, has no means of paying fines. To make matters worse, enforcement officials are in a position where they are unable to properly enforce laws, as situations are so drastic and the number of those breaking the law greatly outnumber officials. Due to governmental constraints in funding, patrolling must be currently done with privately owned modes of transportation (e.g. using one’s own horses). Even articles for purposes of self defence are the private property of officers. Hence, environmental law enforcement is weakened resulting in haphazard, largely inefficient, and non-standardized practices. During seasons of high fire risk, few rangers are available to patrol vast areas of forest, making it virtually impossible to effectively control trespassers. Given the current state of affairs, assistance to rangers has become practically non-existent as locals are in a position to empathize with each other resulting in conscious inactivity in matters of public control. Enforcement in the prevention or early detection of fires is thereby hindered as enforcement controls are weak at a time when society is simply unable to conform to prescribed regulations, and enforcement officers are limited in their options for penalizing offenders. Environmental lawlessness is born out of the survival needs of the people who are currently living in difficult economic times. Should the above mentioned problems be reduced or eliminated, the natural consequence could very likely be a turn to the adherence of laws.

Discussion

Though considerable progress in wildfire suppression has been recently achieved due to the GTZ Integrated Fire Management (IFM) Project in Mongolia, long distances, restricted access and steep slopes continue to make fire prevention the key to sustainable development. As illustrated, the complexity of the trends is due to the effects of more basic and widespread issues of poverty and inappropriate development. With this recognition, most trends are inherently interrelated. Hence, a reduction in the lifestyle trend toward increased subsistence herding would automatically have an effect on improvements to the implementation and enforcement of environmental laws as current pressures on natural areas would consequently be reduced. In the same way, if the trend toward increased division of urban and rural wealth disparities were to be adequately addressed then changes to the trend in lifestyle would also be noticed. These trends are reflections of ongoing and dynamic social conditions, i.e. the same conditions which effect the current trend in increased anthropogenic wildfire occurrence. Thus, the natural and social environments of Mongolia affect and are simultaneously effected by these current trends.

An understanding of these trends is thereby crucial when considering the implementation of an effective wildfire management plan. The establishment of the office of Ministry for the Protection of Nature and the Environment in Mongolia to address the growing expressions of concern for the natural environment is but only a first step. Proper recognition of the underlying reasons affecting the apparent problems is fundamental for successful and sustainable policy implementation. Similarly, an effective fire management plan greatly depends on how these problems are addressed. In order to do so, the recognition of social trends is necessary to better understand the potential influences and impacts which these trends may have on fire management plans.

Conclusion

The above given trends in human activity show under which social conditions the occurrence of wildfire are dependent for its reduction or increase. Though it is often assumed that the problem of increased wildfires is the result of decreased awareness through reduced propaganda or education warning against fire, the study has revealed that a general awareness of the dangers of fire does exist, but that out of general need, people are currently not in a position to effectively eliminate the occurrence of anthropogenic wildfire. Social need must first be addressed. Hence, awareness, though it does play an important role, is not the key issue to be addressed for the long-term reduction of wildfires. Education is not enough as measures must be taken to ensure a more stable social environment. The true problems must be recognized before they can be suitably addressed. Resonance of the state of the social environment goes on to effect the surrounding humanly-influenced “natural” environment. The uncovered trends serve to assist in the recognition of the social conditions currently having an effect on the increase in anthropogenic wildfire for the areas of Batschireet and Mongonmort in Mongolia.

It must be remembered that wildfire occurrence is only one expression, one symptom of larger underlying problems prevalent within the social environment. Human activity and its effect on natural surroundings can no longer be denied. To ignore the social issues as noted would only result in the generation of new, recurring, and / or continued existence of current undesirable symptoms within the environment in Mongolia – natural or otherwise. Action must be taken or irreparable damage to the natural environment through wildfire occurrence could very well be nature’s final means of addressing the problem for us. A socio-ecological balance must, therefore, be sought.

Literature

Bruun, O., and O. Odgard (eds.) 1996. Mongolia in transition: Old patterns, new challenges. Curzon Press Ltd., Richmond, Surrey. 272p.
Rana, P.B., and N. Hamid (eds.). 1996. From centrally planned to market economies: The Asian approach. Vol. 2. People’s Republic of China and Mongolia. Oxford University Press, New York, U.S.A.
Schmidt, S. 1995. Mongolia in transition. The impact of privatization on rural life. Verlag für Entwicklungspolitik. Saarbrücken, Germany.
Valendik, E.N., G.A. Ivanova, and Z.O. Chuluunbator. 1998. Fire in forest ecosystems of Mongolia. Int. Forest Fire News No. 19, 58-63.

 

Contact address

Soo Ing
Fire Ecology Research Group
Max Planck Institute for Chemistry
c/o Freiburg University
P.O.Box
79085 Freiburg
GERMANY

Fax: ++49-761-808012
Tel: ++49-761-808011
E-mail: fire@uni-freiburg.de


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| IFFN No. 23 | Specials | Country Notes |

24. November 2017/by GFMCadmin

Mongolia: Integrated Fire Management – The Mongolia Experience (IFFN No. 23 – December 2000)

mn

Forest Fires in Northern Mongolian Mountains

(IFFN No. 27 – July 2002, p. 92-97)


Introduction

This paper focuses on the forest zone located in Northern Mongolia from 46°30′-52°00 N and 98°00-113°00′ E. Mongolian forests are characterized by discontinuous fire seasons with a long spring fire period starting with the onset of long drought accounting for 80% of all fires and a short autumn fire period when 15-18% of fires occur. In summer, fires are very rare because of frequent abundant rainfalls. Steppe fires are considered to be primarily responsible for starting fires in forest-steppe ecotone and in the subtaiga, since they spread into forest stands under favourable conditions. In the belt of the mountain taiga, particularly in its upper zone, most fires are started by lightning (Valendik et al.1997, 1998). Therefore, the forest danger in the northern region of the country is a natural phenomenon with a repeating character that is linked to the droughts of spring and autumn.

Forest fire hazard and fire regimes

Fire occurrence in the forest regions of Northern Mongolia are resulting from inappropriate human activities and have increased from year to year. Currently they contribute to 95 percent of all fires occurring annually in the country. Besides of that, warming of climate, the trend of desertification and droughts are natural conditions that favour the spread of fires and blowups.

During the last few years, the fire regimes of forests in high-altitude zones have changed dramatically. The evaluation of the a pyrological classification is shown in the Table 1. The classification distinguishes forest fire occurrence (n) on 100,000 ha:

n<0.5                      = low

0.6<n<2                 = moderate

2.1<n<4.0              = high

4.1<n<6                 = very high

6.1<n                      = extreme

The distribution of fires between forest fire districts was generally even and moderate between 1975-1989, and high and very high during 1990-1994, and developed to the extreme rating in 1995-1999 (other than mountain taiga and mountain sub-taiga districts of Khuvsgul and Khentii).

Extremely large fires occurred in some years. In 1996-1997 13.4% of the total forest fund area had been affected by fire and greatly altered the characteristics of fire hazard. However, not every forest fire influences the forest ecosystem negatively. Surface fires that consume raw humus and surface fuels in low-productivity forests of the tundra and taiga zones influence the frost regime of the soils and lead to better growth conditions and formation of high-quality forests.

Table.1.Change of fire occurrence and regimes in forests of Northern Mongolia between1975 and 1999.

* n – fire occurrence; c – degree of area affected by fire

Forest fire danger

Long-term and short-term seasonal frost and permafrost sites are characteristic features of mountain forest sites in Northern Mongolia. This zone is characterized by continental cold and dry climate. Moisture supply for the vegetation is secured by rainfall and additionally by the moisture that is set free by melting seasonal frost that will supply the needed moisture for the root system of plants and woods. Occurrence and impacts fires entering forest sites with seasonal frost depend on the season. During the period June to August the melting frost supplies sufficient moisture to the upper soil, the organic and litter layers and the understory vegetation, thus reducing the spread and intensity of fires. Under the cold spring and autumn conditions, the surface fuels are dry and support the spread of fires and the development of fires with intensities that are higher than the summer fires and thus more damaging.

 The degree of fire danger in Northern Mongolia depends on the following natural factors (Chuluunbaatar 1998):

  1. Long-periods of daylight during the spring, causing an increase in solar radiation
  2. A strong, cyclone-caused continental wind
  3. High wind and solar radiation penetration of the forest canopy of the subalpine, pseudotaiga and forest-steppe high altitudinal belt forests
  4. Rapid fire development rich in dead plants.

The forest vegetation is divided into following classes characterized by fire:

Except for the data on the percent of moisture in terrestrial cover it is necessary to know the percent of moisture in conifer needles, strobes, bark and all other litter-fall fractions. Research conducted in Mongolia revealed that during the fire season the moisture content (percentage of moisture compared to dry weight) in terrestrial combustible matter was variable depending on the period following the onset of vegetative growth. Thus the warm season of each year in the mountainous region of northern part of Mongolia was conventionally divided into four pyrologically active phenologyc periods (Chuluunbaatar 2001), namely:

1st period – until leaf initiation. This is the most fire-hazardous period when terrestrial cover fraction consists of dead (cured) grass and litter. The moisture content in forest combustion fuell at this period is as follows: In forb-pine forests: conifer needles 4.0-14.6, bark 3.6-14.8, sprigs 2.5-16.6, strobes 2.8-19.1, mosses 3.9-34.2, litter 17.1-100.9, grass 6.1-167.3. In forb-larch forests the percent of moisture of combustion fuel was as follows: conifer needles 3.4-7.9, sprigs 4.6-15.6, strobes 4.4-10.6, mosses 19.9-155.9, litter 9.6-151.1, grass 6.6-136.5, cowberry (Vaccinium vitis-idea L.) 77.2-143.1. In forb-birch forests: leaf 5.3-14.6, sprigs 6.1-24.8, litter 50.0-97.8, grass 7.8-157.8.

2nd period – from leaf initiation stage until the standing of grass and litter decay. From this stage spreading of fire becomes almost impossible. At this periods the moisture content in the fire hazardous fuel is the following: In forb-pine forests: conifer needles 20.4-40.1, bark 13.2-32.3, sprigs 20.5-34.0, strobes 30-47.6, mosses 49.0-191.8, litter 64.1-198.4, grass 173.3-500.8, cowberry (Vaccinium vitis-ideaL.) 88.7-139.7; in forb-birch forests: leaf 10.2-283.0, sprigs 16.6-85.4, mosses 68.5-322.2, cowberry (Vaccinium vitis-idea L.) 112.8-157.2, litter 63.4-149.7, grass 288.6-492.6.

3 rd period – lasts until wilting of the grass-herb layer. Under dry weather conditions, the spread of fires is easily possible. The moisture content in combustion fuel during this period is as follwos: In forb-pine forests -conifer needles 9.3-29.3, bark 8.3-32.3, sprigs 19.2-33.5, strobes 33.0-45.6, mosses 33.6-116.5, litter 62.5-213.8, grass 185.2-226.3; in forb-larch forests: conifer needles 19.8-66.7, strobes 20.3-64.4, sprigs 20.0-30.0, mosses 106.4-227.4, cowberry (Vaccinium vitis-idea L.) 120.2-134.9, litter 84.9-264.8, grass 21.4-323.7; in forb- birch forests: leaf 27.3-50.8, sprigs 33.9-57.9, mosses 119.4-205.2, cowberry (Vaccinium vitis-idea L.) 123.0-142.7, litter 83.1-191.8, grass 27.2-304.4.

4th period – starts at leaf-fall and lasts until the onset of snow cover formation. At this period the grass stand continues dying off and wilting. The hazard of natural fires is lowered though under conditions of dry long and warm autumn widespread forest fires can break out. The moisture content in combustion fuel forms in forb-pine forests: conifer needles 11.1-20.5, bark 14.3-21.3, sprigs 13.8-18.8, strobes 12,5-34.3, mosses 37.1-96.1, litter 42.6-152.7, grass 167.3-185.5; in forb-larch forests: conifer needles 11.5-47.7, strobes 13.3-30.1, sprigs 14.1-21.5, mosses 51.1-96.6, cowberry (Vaccinium vitis-ideaL.) 112.9-117.1, litter 39.2-168.9, grass 38.6-156.4; in forb-birch forests: leaf 23.3-26.6, sprigs 19.3-34.1, mosses 74.7-104.7, cowberry (Vaccinium vitis-idea L.) 123.0-125.0, litter 103.0-154.5, grass 109.7-169.2.

Classification scale of forest fire danger (fire weather)

We have evaluated the forest fire danger of each of districts within the pyrological subdivision zones of Northern Mongolia. Up to 15 to 20% of the total number of forest fires which occur annually in Northern Mongolia break out at weather / temperature conditions in the above-mentioned provinces are below zero degree Celsius. As for the above weather condition, the following formula (Telitzyn et al. 1981) can be used to evaluate a forest fire danger (Sofronov 1985, Chuluunbaatar 1998):

å(t-t),°C

where

å= is sum

t = air temperature at 15:00 h

t = dew point temperature at 15:00 h

It is an expression suitable for our country because it includes the amount of precipitation of 3 mm and above, 1-3 mm, and <1 mm. It also includes below-zero values of air temperature.

There are strong differences between spring-summer and summer-autumn. Concluding from this, the summer estimation scale is not necessarily useful for above regions, but the period of the continuation of the autumn fire danger and the number is a few, the sum (å(t-t),°C) of the deficit of the dew point and the temperature does not exceed the variation of the temperature of fire danger in spring, and these showed that it is possible to evaluate the fire danger in spring and autumn by one estimation scale (Tab.2). 

Table.2.Classification scale of forest fire danger of weather

Influence of forest fires on the forest phytocoenoses

The forest-vegetation are divided into following sections resulting from the characters of fires occurred there:

1.   Plants that grow immediately on freshly burned sites (Chamaenerion angustifolium L., Corydalis sibirica L., Polygonatum sibiricum Dealer., Cerastium pauciflorum Steve., Chenopodium album L., Artemisia marcocephala J., Carex amgunensis ER., and others)

2.   Plants that grow on burned sites that are part of the phytcenose affected by fire and are promoted by fire effects (Bromus pumpellianus Sc., Poa sibirica Roc., Trisetum sibiricum Rub., Artemisia integrifolia L., Geranium vlassovianum F., Fragaria orientalis Los., and others).

3.   Plants that are adapted to forest fire. The fire does not change the vegetation cover and composition but rhizome grasses and sedges are promoted (Chuluunbaatar et al. 1999).

Resulting from the increasing occurrence of extremely large fires, the consequences of fire become increasingly negative, e.g., destruction of forest trees and other plants, affecting rivers, soil erosion in mountain forests, and an overall deterioration forests that results in increasing susceptibility to subsequent fires and a decrease of the natural recovery potential.

Betula platyphylla Sukach. grows by coppices (shoots) and Populus tremula L grows by suckers from roots that have been affected by surface and ground fires. The forest fire character and its influence of this region differs by altitude belt: Forest in the subtaiga belt of mountainous zone that grows in elevations between 600 and 1200 m above sea level (a.s.l.) is effectively affected by medium- and high-intensity ground and surface fires. Here all combustible materials on the forest floor and the lichen layer is totally consumed by fire. As a result severe soil erosion occurs in some places.

In the forest of the mountain subtaiga which grow on altitudes between 1300 and 1700 m a.s.l. intense surface, ground, and spotting fires dominate and often become crown fires.

Medium- to high-intensity fires woodland fires, crown fires and sometimes ground fires occur in the forest of the mountain taiga that grows in altitudes between 1800 and 2100 m a.s.l..

Figure 1. Large-scale clearcuts in the montane-boreal forests of Northern Mongolia, associated with the effects of wildfires, have resulted in extended areas of birch forests that were established by post-fire coppicing with a small share of coniferous species. Source: GFMC.

 Conclusions

Birch (Betula platyphylla Sukach.) and pine (Pinus sylvestris L.) grove with grass cover are common for subtaiga mountain zone of Northern Mongolia. As long as the absolute height above sea level reaches its maximum, taiga dark-conifer and larch (Larix sibirica Ldb.) grove become prevailing. The pyrologic characters of these taiga forests don’t noticeably vary during the fire-hazardous season.

In Northern Mongolia, forests fires are one of the major factors determining the trends of altitudinal belt-specific forest formation processes.

 

IFFN/GFMC contribution submitted by:

Tseveen Chuluunbaatar
Institute of Botany, Mongolian Academy of Sciences

Jukov avenue-77
Ulaanbaatar-51

Mongolia-210351

Tel: 976-11-457006
Fax: 976-11-451837
e-mail:       tschuka@hotmail.com

References

Chuluunbaatar, Ts. 1998. Forest fire danger of Northern Mongolia. Ulaanbaatar, 25 pp.

Chuluunbaatar, Ts. and Zoyoo, D. 1999. The forest fire influence on the forest phytocenoses of the Eastern Khuysugul. In: Diversity of the plant cover within the Baikal Region. Ulan-Ude, 85 pp.

Chuluunbaatar, Ts. 2001.Forest fire danger and its reduction methods. Ulaanbaatar, 125 pp.

Sofronov, M.A. 1985. Drought indicators of forest fire. In: Forest fires and their consequences. Krasnoyarsk, 55-56.

Telitzyn G.P., Kostyrina T.B., Dunda E.E. 1981. Recommendations improve the methods forest fire control in MPR. Khabarovsk, 36 p.

Valendik, E.H., G.A. Ivanova, and Ts. Chuluunbaatar. 1997. The problem of forests in Mongolia. In: Asian ecosystems and their protection. Ulaanbaatar,137 p.

Valendik, E.N., G.A. Ivanova, Z.O. Chuluunbaatar, and J.G. Goldammer. 1998. Fire in forest ecosystems of Mongolia. International Forest Fire News No. 19, 58-63.


Country Notes
IFFN No. 27

24. November 2017/by GFMCadmin

Mongolia: Wildfires in Mongolia 1996 (IFFN No. 15 – September 1996)

mn

Wildfires in Mongolia 1996

(IFFN No. 15 – September 1996, p. 30-35)


Introduction

During the months of March and April, 1996, Mongolia began to experience wildland fire events significantly exceeding normal activity levels for this period of time. The fire activity intensified in late April and continued unabated through the month of May, burning extensive areas of forest and grazing land. In mid May, a request for assistance was received at the U.S. Office of Foreign Disaster Assistance (OFDA). Ray Dionne, Disaster Operations Officer from OFDA, and Deanne Shulman, Fire Management Specialist from the United States Forest Service, were dispatched to Mongolia to assess the fire situation, and identify critical needs and problems impacting the effectiveness of the Mongolian response to this emergency situation. During the period 21 May to 5 June, 1996, they consulted with Mongolian government officials responsible for the management of the fire disaster, conducted aerial reconnaissance of heavily impacted fire areas, participated in fire logistic support missions, interviewed firefighters, and met with the American Ambassador, U.S. Agency for International Development personnel, and the International Donor Community.

The Mongolia Wildland Fire Environment

Mongolia has a land area of 1,566,371.52 square kilometers, a land area slightly larger than Alaska. The average altitude of the country is about 1,600 m a.s.l., making it one of the highest countries of the world.

The majority of forested land is located in the northern half of the country and covers approximately 10% of the total land base. Fires occur primarily within three vegetative zones: the taiga forest zone, the mountain forest steppe zone, and the steppe zone. The Mongolian taiga zone, occurring only in the northernmost areas of the country, is the southern edge of the vast Siberian taiga forest, the largest contiguous forest system on earth. These boreal coniferous forests are composed primarily of Siberian Larch (Larix sibirica, 70%), and Siberian Pine (Pinus sibirica, higher elevations). Mosses and lichens provide abundant ground fuels. The mountain forest steppe zone covers 25% of Mongolia and is comprised of both steppe (grassland) vegetation found on the drier slope aspects and mixed coniferous hardwood forest of pine, larch, and birch (Betula platyphylla) with a grass understorey on the cooler, moist northern slopes. The topography is characterized by hilly, mountainous terrain separated by wide river valleys. The mountain steppe zone occurs in a belt across the northern portion of the country. The extensive grasslands of the steppe zone covers nearly the entire far eastern part of Mongolia and extends westward in a belt through the central portion of the country. The topography of the steppe zone ranges from gently rolling to flat terrain. In a typical year, the majority of fires occur in the grasslands or grass understory of the steppe and mountain steppe zones.

Weather patterns create two distinct fire seasons in Mongolia. Spring weather is dominated by strong, dry winds. These spring winds can become very fierce and it is not uncommon for airplane traffic bound for Ulaanbaatar to be diverted to other cities due to wind during the spring. These winds are characteristic from March through June and can create intense fire potential in the dry, dead grass from the previous fall. July and August are generally rainy and produce new grass growth. During September and October, the new grass dries and again becomes available fuel for wildfire. Winters tend to be bitterly cold and dry.

Table 1 shows the number of forested acres burned each year from 1978 to 1994 (1995 Natsagdoogiin and Lamjabiin, Information On Group Training Course in Reforestation Promotion Leader “Forestry, Forest Industries, Unpublished Report).

 Tab.1. Forested area burned annually in Mongolia

The Situation in Spring 1996

Fire Conditions: An unusually dry winter (1995/96) resulted in significantly lower than average fuel moistures in the grasslands and forests of Mongolia. The strong, spring, northwest winds quickly spread any fire ignition through the tinder-dry and readily available fuels. The primary ignition source of these forests are the local inhabitants, through careless use of fire or discarded cigarettes. Much of the adult population in Mongolia smoke cigarettes. During spring, many people derive extra income by collecting deer antlers in the forest and selling them. Careless smoking while involved in this activity can result in ignitions in forested areas.

Fire Damage: Information gathered from briefings in Ulaanbaatar with Deputy Prime Minister Purevdorj, Chairman of the State Emergency Commission and General Damdinsuren, Deputy Chairman of the State Emergency Commission and Chief of Civil Defense Committee of Mongolia indicated the following as of 30 May 1996:

  • There were a total of 352 fires in the country, of which 22 had been extinguished, 94 were contained, and 36 remained uncontrolled.
  • A total of 3.5 million hectares of forested land and 5.9 million hectares of grassland was burned. Most of the fire activity was in the northern thirteen provinces. One fire in the taiga zone of the northern Huvsgol region had a 128.7 kilometer front in the Mongolia portion and extended across the border into Russia.
  • There had been 23 fatalities, including six persons killed while involved in fire suppression activities. Sixty people had been treated for serious burn injuries.
  • 168 gers (Mongolian traditional dwellings) were destroyed leaving 750 people homeless.
  • 7,800 animals died in the fires, and many fences, range improvements, and water developments destroyed.
  • Over 2000 telephone poles were burned, severing some communication links to provincial areas.

Personal observations from aerial reconnaissance and interviews with field personnel conducted on 25, 26 and 29 May in the Tov and Selenge province indicated immense areas burned in both forest and grasslands with intense, stand-replacing crown fires in approximately 10% of the burned forested areas. Many of the fires were in remote, high elevation locations with limited accessibility. Smoke covering the region limited full utilization of the few aircraft available. The extent of pasture land burned will have immediate adverse impacts on the available grazing land of nomadic herdsmen. Discussions with various officials indicate that a fire season of this magnitude and devastation has never occurred within their career span, although Chief of Civil Defense General Damdinsuren stated that 30 or 40 years ago there was a fire season of a similar catastrophic proportion. Old fire scars and mosaic regeneration patterns observed from the air indicate a history of stand-replacement fires in these forested ecosystems.

51964 Byte

Fig.1. Daily updates of fire activities were provided by the National Remote Sensing Center. The photograph shows the fire status map of 27 May 1996 (Photo: D.Shulman)

The Government of Mongolia Response

Emergency Response Organisation: The State Emergency Commission is chaired by the Deputy Prime Minister and has overall responsibility for dealing with the fire emergency situation. This commission consists of representatives from all the ministries. The Chief of the Civil Defense Committee is the Deputy Chair of the State Emergency Commission. The mission of the Civil Defense Committee is to protect human lives and properties from natural disasters. In a wildfire emergency situation, the Civil Defense Committee is responsible for all operational aspects of fire suppression efforts. The provincial branches of the Civil Defense Committee do not have full-time employee staff. Civil Defense representatives are in a reservist status and are activated in a civil defense capacity only in the event of an emergency incident. The Civil Defense organization includes approximately 200 smokejumpers based in seven northern provinces. It also includes approximately 100 specialized rescue personnel who are trained firefighters.

In response to the fire situation, the State Emergency Commission declared a “state of emergency”. Special coordination groups were established in local areas impacted by the fire situation to direct suppression efforts and provide humanitarian relief as needed. The military and police forces were mobilized to fight the fires as were thousands of local people. Border troops near Russia were also mobilized. All available resources were mobilized in the fire suppression effort, which on a daily basis ranged from 3,000 to 10,000 firefighting personnel and from 1,000 to 3,000 vehicles. Local individuals were conscripted to fight fire and were organized in crews under the leadership of military personnel or other officials.

Prioritization Criteria for Resource Commitments: Priority fires for the limited suppression resources were determined based on the fire’s proximity to population centers and threat to National Parks and Strictly Protected Areas. Due to the limited resources available and the number and magnitude of active fires, it was determined that some remote fires would have no suppression activity.

Intelligence Gathering: The Ministry of Nature and Environment maintains a very modern Information and Computer Centre that compiles environmental data. This includes meteorological, water quality and pollution data. NOAA computerized satellite imagery is used for meteorological purposes and environmental monitoring. During the wildfire emergency, fires were mapped daily using computerized satellite imagery. The fires were then numbered and listed by province and county with the latitude and longitude indicated for each. The map and list were sent daily to the Civil Defense Commission and the Ministry of Nature and Environment. Another service that the computer centre provided was meteorological data for the Mongolian Hydrometeorological Service, Weather Modification Centre “Khuryn Shim”. Other fire situation intelligence data were gathered through information from the field. Generally, this information was two days old by the time it was received in Ulaanbaatar. There was no radio communication from the fires to the local command centres. Information from the fires was carried by people on horseback or vehicles to local command centres and then telephoned to Ulaanbaatar.

Aircraft and Equipment: Aircraft committed to the firefighting effort included four military MI-8 helicopters utilized for logistic support and firefighter transport only. These helicopters were not equipped for tactical uses such as bucket drops or rappelling. An AN-26 airplane was used to “cloud seed” in an effort to produce rainfall. AN-2 aircraft were used by smokejumpers and military paratroopers to parachute to remote fires. There are no airtankers in the country.

A country-wide inventory list provided by the Civil Defense Committee dated 28 May 1996 indicates the following firefighting tools and equipment:

Tab.2. Inventory list of firefighting tools and equipment available in Mongolia during the 1996 wildfire episode

Fire fighting equipment observed include homemade “swatters” (pieces of tire rubber, linoleum, perforated metal, or felt attached to the end of a wood handle), five gallon backpack pumps (Russian made), two and a half gallon pressurized agricultural type water sprayers (Russian made), small steel rake-like brooms, air blowers (donated by the People’s Republic of China), and kerosene burn equipment. Wet clothes and tree boughs were the primary tools used to beat out the edges of the fire.

No safety equipment or fire resistant clothing was observed (with the exception of one smokejumper wearing a yellow Nomex shirt that was given to the smokejumper unit in 1990 when a UN-sponsored United States team installed a parachute maneuvering simulator for the smokejumpers in Ulaanbaatar, USDA Report 9151-2803-MTDC).

Strategy and Tactics: The non-professional firefighters (military, police, and locals) used direct flanking attacks by beating out the edges of the fire perimeter. This method can be effective in light wind conditions and grassy, light fuels. It is considerably less effective in the heavier ground fuel conditions of the taiga forests in the north, or windy conditions. The smokejumpers and trained firefighters were utilizing indirect backfire and burn out techniques where appropriate to control the fire.

Cloud seeding to enhance precipitation was used to suppress fires where weather conditions met required parameters. The Weather Modification Centre had cloud seeded twenty times during the spring to assist in fire suppression. Meteorologists at the Ministry for Nature and Environment Information and Computer Centre analyzed satellite imagery to determine which clouds may be favorable for cloud seeding. This information is sent to the Weather Modification Centre of the Hydrometeorology Service. Silver iodide “bullets” are fired from either an AN-26 airplane or the ground into the selected clouds to form a nucleus for raindrop formation.

46262 Byte

Fig.2. Smiling young fire-fighting supporters demonstrate home-made fire swatters. Photo: D.Shulman.

Logistics: A communication schematic provided by the Civil Defense Commission shows short-wave radios located at seven smokejump bases in the northern provinces. Civil Defense communications between Ulaanbaatar headquarters and the province capitals is done by telephone. Communications directly to or from fire locations are carried out by people on horseback or vehicles. The smokejumper units have “line of sight” radios (Russian made) with a maximum 6 mile range depending on terrain, with which they can communicate with each other and aircraft directly overhead.

There were three MI-8 helicopters utilized for logistic missions. Equipment and supplies were transported by vehicle or animal to the fire locations. Crates of canned meat and tools were observed being transported on helicopter logistic missions, but local firefighters complained of inadequate food supplies, sleeping bags, and tents.

Identified Problems

Economic Constraints: The fragile market economy and limited emergency government funds available to support the fire fighting effort significantly impacted the fire suppression operation. Smokejumper fire detection patrol flights, normally scheduled based on a fire danger rating, were delayed this year due to funding shortages for aircraft fuel. Fires that could have been detected early and suppressed while small were not detected until they became large. Smokejumper units were understaffed due to low pay and hazardous duties. The normal contingent is 300 smokejumpers. This year, however, Civil Defense could only attract 200 smokejumpers. In the transition economy, all purchases must be made in cash. Cash to pay for aircraft fuel was a continuing problem. Food and local transportation to fires was coordinated and organised at local command centres, but lack of funds to buy fuel and purchase food locally caused considerable supply and distribution problems. Local firefighters continued to receive salaries from their regular employers. Those firefighters recruited from the ranks of subsistence herders were provided food while fighting fires.

Communications: The Civil Defense Committee lacks basic communication equipment to effectively manage an emergency incident of any kind. This lack impedes the flow of adequate, accurate, and timely information between field personnel and individuals responsible for resource allocation, strategic planning, and logistic support decisions. In a rapidly changing, geographically dispersed emergency incident such as a widespread wildfire, up-to-date information is crucial for decision makers.

Disaster Management: An emergency situation of this magnitude requires an incident management structure that incorporates specialists and workers from all spheres of the government and local populations. There was no clear emergency management structure to develop an overall strategic plan, implement the plan, and provide logistic support and financial expertise to support the operation. Lack of a strategic plan and logistics problems were resulting in inefficient use of firefighting resources. Information relating to specific daily costs of supporting the fire suppression effort was difficult to obtain, frustrating members of the international donor community requiring a cost analysis to justify recommendations for cash donations.

Additional Information

A chronological narrative of specific daily activities during this assessment is documented in the Trip Report on file at the U.S. Office of Foreign Disaster Assistance. The full text of the Mongolia Wildfire Assessment Technical Report is also on file at OFDA.

From: Ms. Deanne Shulman
Fire Management Specialist
Address:
Sequoia National Forest
Cannell Meadow Ranger District
United States Forest Service
P.O. Box 3
USA – Kernville, CA 93238

Fax: ++1-619-376-3795
Tel:  ++1-619-376-3781


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Country Notes

24. November 2017/by GFMCadmin

Mongolia: Mongolia Fire Update (IFFN No. 15 – September 1996)

mn

 

Mongolia Fire Update

(IFFN No. 15 – September 1996, p. 35-36)


In August 1996 the editor of IFFN received an update of information on the fires of 1996 provided by the Mr. Erdenesaikhan Naidansuren National Remote Sensing Centre which belongs to the Ministry for Nature and Environment of Mongolia:

From 27 February to 3 June 1996 a total of 386 forest and steppe fires broke out in 115 places over Mongolia and total of 2.3 million ha of forest, 7.8 million ha of pasture land have been affected by these fires. More than 7000 livestock, 210 houses, 560 communication facilities and 576 facilities for livestock were devastated by the blaze, leaving many peoples homeless. Also 25 people died and 65 were seriously injured by this fires. The Government of Mongolia quoted environmental damage of US$ 2 billion as preliminary estimation.

The development of space technology has provided a new method for forest fire monitoring, especially using meteorological satellites, which have received great attention because of their wide view, high observation frequency and low cost. All staff of the National Remote Sensing Center from the beginning to end of fire conflagration have worked with high efficiency to serve all organizations involved in disaster management. At this time our center received and processed NOAA AVHRR imageries which allowed precise fire location. People in the entire country are now recognizing the importance of satellite remote sensing data for wildfire prevention and fighting. At present we are working on the evaluation of the economic and environmental damages caused by the wildfires. There are several problems like restoration of forests, establishment of powerful fire prevention systems, improvement of satellite fire monitoring equipment and lack of the natural disaster monitoring experts by satellite.

 

 

From: Erdenesaikhan Naidansuren
Researcher, National Remote Sensing Center
Address:
Ministry for Nature and Environment
Hudaldaany gudamj-5
Ulaanbaatar-11
MONGOLIA

Fax: ++976-1-321401
Tel:  ++976-1-329984


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Country Notes

 

24. November 2017/by GFMCadmin

Mongolia: Strengthening Disaster Response Capability in Mongolia Project Accomplishment Summary (IFFN No. 16 – January 1997)

mn

 

Strengthening Disaster ResponseCapability
in Mongolia
Project Accomplishment Summary

(IFFN No. 16 – January 1997, p. 20-22)


Background

During spring, 1996, Mongolia experienced an extreme wildfire season, far exceeding normal fire activity levels. Millions of hectares of valuable grazing land and forest were burned, lives lost, families left homeless, and thousands of livestock perished. During this period, the government of Mongolia requested international assistance and the United States Office of Foreign Disaster Assistance sent a two person assessment team to Mongolia. Based on that assessment, two recommendations were developed with an objective of strengthening overall disaster response capability in Mongolia: 1) provide emergency incident management training using the Incident Command System to the Civil Defense Committee of Mongolia, and 2) provide communication equipment and training in the use and deployment of this equipment during disaster situations to Civil Defense. The United States Agency for International Development approved funding for implementation of the recommendations and expressed support for a more regional application of the Incident Command System by including a representative from the Asian Disaster Preparedness Center on the project team. During the period 18 September – 26 October 1996 a seven-person team worked in partnership with the Civil Defense Committee of Mongolia to accomplish the project objectives. (See also Wild Fires in Mongolia 1996 and Mongolia Fire Update in the previous issue of IFFN)

Project Accomplishments

  1. A four person instructor cadre from the United States Forest Service conducted two 32-hour training course sessions on the Incident Command system, an emergency incident management system used in the United States for disaster response. The training was held in the Civil Defense building in Ulaanbaatar, Mongolia, and included translated materials and interpreters. The Civil Defense Committee of Mongolia sponsored the course and their staff was actively involved in course preparations, translations of course materials, and selection of trainees. A total of 61 persons attended, representing a cross section of agencies involved in disaster response.

  2. A two person instructor cadre from the United States Forest Service and the United States Bureau of Land Management conducted two 24-hour training sessions on emergency response communication systems and communication equipment use. This training was also sponsored by Civil Defense and utilized translated materials and interpreters. The course included actual “hands-on” use of the communications equipment. A total of 21 persons completed this training.

  3. A communication equipment package was donated to the Mongolia Civil Defense. This equipment will meet basic emergency response needs for one or two provinces, depending on the complexity of the incident.

  4. A country-wide disaster communications plan was prepared and presented to the Mongolia Civil Defense Committee. This plan includes a description of the current emergency response communication system; recommendations for development of a more effective system that would meet the needs for logistic, operational, and national coordination communication links; training and development needs; establishment and use of radio cache systems; maintenance requirements for the communication system; identification of specific communications equipment required to meet the information flow needs during a disaster; and costs for purchasing recommended equipment. A copy of this plan was given to other potential foreign donor groups to encourage additional funding to augment the initial equipment donation of the United States.

  5. Demonstrations of communications equipment were conducted for interested foreign donor groups to encourage consideration of additional funding to purchase the required equipment recommended in the country-wide disaster communications plan.

  6. A field demonstration of communication equipment was conducted in the Hovsgol province. Use of equipment was demonstrated in remote, mountainous terrain, and local Civil Defense employees were trained in equipment use.

  7. The manager of the Learning and Professional Development Unit of the Asian Disaster Preparedness Center participated in the design stage of the Incident Command System training course and in the implementation phases of both the Incident Command System and communications training courses. The Asian Disaster Preparedness Center is considering including the Incident Command System as part of its disaster management training curriculum.

Results and Analysis

Both training courses were well received by the participants. The Incident Command system training generated many questions concerning the framework within which the system operates, such as the existence of policy or legislation mandating the use of the Incident Command System in the United States, cooperative operating agreements between agencies, pre-designated emergency response teams, etc. The communication equipment donation addressed a critical need of the Civil Defense for emergency response. Communication links are mandatory for effective emergency incident response and the country’s dire lack of communication equipment during the 1996 spring wildfire disaster was well publicized by the international media.

After 75 years of communist government and centralized economy, Mongolia is in a transition period to a market economy. Since the election last June, when Mongolia voted in its first Democratic government, many agencies are experiencing dramatic change both in structure and personnel. Senior level personnel in many agencies have been replaced with new appointees and newly created departments are just now defining their role and mission. This transition period is optimal for creating new governmental frameworks and legislation for more effective emergency response management.

 

 

From:  Ms. Deanne Shulman
Fire Management Specialist
Address:
Sequoia National Forest
Cannell Meadow Ranger District
United States Forest Service
P.O. Box 3
USA – Kernville, CA 93238


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