Reindeer Management Research Articles

The Norwegian system for wild reindeer management — major development since the 19th century

In the 19th century the hunting of wild reindeer was relatively unrestricted in Norway. This, combined with a more efficient hunting, caused a severe reduction in the number of wild reindeer at the turn of the century. The national authorities responded by stricter hunting control, and in 1930 hunting quotas related to the size of the wild reindeer areas were introduced. The Ministry of Agriculture decided the number of licences, and the number of wild reindeer increased. During the 1950s a major controversy between the Ministry and local people arose in the Snøhetta area. People there increased their power over the wild reindeer management by organising a "Wild Reindeer Board" (WRB). This inspired people in other districts to organise similar boards. These WRBs had no formal power according to the law, but became important managers of the herds. An official organisation for each wild reindeer area, the Wild Reindeer Committee (WRC), was introduced in 1988. Since the WRCs are official institutions, legal power is decentralised to them.

Productivity factors of the Finnish semi-domesticated reindeer (Rangifer t.tarandus) stock during the 1990s

<p>Intensive reindeer grazing and the increase of other land use forms have caused a decline in the amount of arboreal (Alectoria, Bryoria spp.) and reindeer (Cladina spp.) lichens in the Finnish reindeer management area during the last few decades. Supplementary feeding of reindeer has increasingly compensated for the lack of natural winter fodder. The amount of the supplementary feeding and the quantity and quality of summer pastures should therefore have an increasing effect on the productivity of reindeer stock. In order to outline better the present carrying capacity problems on pastures in the Finnish reindeer management area we focused some of the most important productivity factors of Finnish reindeer stock from 1993 to 1999. The results showed that the productivity of reindeer stock in Finland was dependent especially on two main elements: amount of reindeer feeding and reindeer densities on summer pastures. Winter pastures had no clear effect on productivity when analysing the entire management area. High productivity figures in reindeer stock (calf production, carcass mass and meat production per reindeer) were reached in the management districts where winter feeding was the most abundant, reindeer densities relatively low and summer pastures abundant. An increase in reindeer density on summer pastures raised meat production per total summer pasture area but decreased carcass mass of reindeer calves and meat production per reindeer. It seems that the fundamental factor for keeping the reindeer stock productivity sustainable at a high enough level is to optimize the longterm reindeer densities on pastures. Summer pastures may gradually become a limiting factor for reindeer stock productivity in some areas if overgrazed and decreased winter pastures are only compensated for by winter feeding of reindeer.</p><p> </p>

Gene flow and potential selection response in age-structured subpopulations having a common male pool

AbstractIn extensive pastoral systems, where mating cannot be controlled, the breeding strategies of intermingling owner flocks interact. We present a method to evaluate a breeding programme in extensive reindeer (Rangifer tarandus) management which can also be applied to other pastoral production systems. Our main objective was to evaluate the method by applying sensitivity analyses. The method included a gene flow model with maternal effects. The potential responseRpwas defined as the response that could be achieved in a closed nucleus with a given selection procedure. The value ofRpwas derived from the gene flow from dams to daughters, selection differentials, and the realized difference between subpopulations. We studied a population structure having two subpopulations, only one of which had been subjected to selection. Random mating between subpopulations and a common male pool were assumed. A reference case was defined using reindeer data from the literature. After 9 years of continued selection among progeny the estimate ofRpwas 7·0 times higher than the realized subpopulation difference. We analysed deviations ofRpfrom the reference case caused by different female age structures between subpopulations. We also analysed the sensitivity of maternal effects. The method proved insensitive to differences in female age structure between subpopulations but was sensitive to the relative contribution of maternal effects to progeny performance.

English Terms in Norwegian Reindeer Management

English Terms in Norwegian Reindeer Management

Jan Åge Riseth; Sámi reindeer management under technological change 1960-1990: Implications for Common-Pool Resource Use Under Various Natural and Instututional Conditions. A comparative analysis of regional development paths....

On June 22, Cand. Agric. Jan Åge Riseth successfully defended his dissertation "Sami reindeer management under technological change 1960-1990: Implications for Common-Pool Resource Use Under Various Natural And Institutional Conditions. A comparative analysis of regional development paths in West Finnmark, North Trøndelag, and South Trøndelag/Hedmark, Norway." for the degree Dr. Scient, at the Agricultural University of Norway (AUN), Dept. of Economics and Social Sciences.

Condition, Potential Recovery Rate, and Productivity of Lichen (<i>Cladonia</i> spp.) Ranges in the Finnish Reindeer Management Area

The focus of the work was to investigate dependency between reindeer density and lichen (Cladonia spp.) ranges in the Finnish semidomesticated reindeer management area. Secondly, we formed a model on the recovery rate of ungrazed woodland lichen ranges (29 sites) after forest fires to evaluate the potential productivity and time needed for Finnish lichen ranges to recover at optimal production. During 1974-95, 59% of the variation in mean semidomesticated reindeer density (range: 0.7-3.0 reindeer/km² of the total land area) among the reindeer herding districts in Finland was explained by the proportion of land area covered by lichen ranges in these districts. Reindeer densities were highest in the districts where lichen ranges covered 20% to 30% of the area. Reindeer density on the total land area did not explain the condition of lichen ranges, but 58% of the condition was explained by the reindeer density on the lichen ranges. A condition level for lichen ranges of 1000 kg dry matter per hectare (d.m./ha) of lichen biomass can be considered adequate to ensure survival of reindeer and continued production of lichen. To maintain this level within the sedentary Finnish grazing system, winter reindeer densities on lichen ranges must remain below 5-7 reindeer/km². According to our model, the maximum amount of living lichen in the woodland lichen stand at the climax stage is on average about 7000 kg d.m./ha. The maximum annual yield of lichen (175 kg d.m./ha) is produced by lichen stands that contain 2600-2800 kg d.m./ha of living lichen. Using our model and our 1995-96 data, we calculated that the average lichen biomass on lichen ranges in the Finnish reindeer management districts was 13.0% of this optimum, and the average lichen production was 36% of the possible maximum annual yield. Our model indicates that the Finnish lichen ranges would have to remain ungrazed for an average of 18 years to recover to maximum production levels. However, the average time needed for the lichen ranges to recover to the level of 1000 kg lichen d.m./ha, would be only about 7 years.

Developing an ecologically and economically more stable semi-domestic reindeer management - a Finnish point of view

In arctic and sub-arctic regions semi-domestic reindeer management forms an important livelihood which should be able to provide enough income for herders. Reindeer management has natural limits of growth. Consequently it should be managed to optimise both the use of reindeer pastures and herder income. Reindeer pastures should be grazed at the economic carrying capabity level. This gives the maximum sustained harvest from reindeer stock and also the maximum sustained foraging from pastures. How is this to be accomplished? First, reliable knowledge about reindeer pastures in time and place is necessary: to estimate the quantity and quality of specific reindeer pastures within each management district, as well as the productive capacity and the changes in condition and productivity of those pastures. Secondly, data is needed on the accurate productivity of reindeer stock and the production costs for each management district. Thirdly, study the relationships between pasture resources and productivity of reindeer stock together with the effects of long-term reindeer densities on pasture condition and productivity. Finally, knowledge is needed about the effects of herd structure on reindeer stock productivity as well as the factors which restrict the use of reindeer pastures. Models based on adequate data could provide a useful tool for optimising the use of reindeer pastures and herder income. First the economic carrying capacity of reindeer pastures should be studied. Subsequently the economy of reindeer husbandry could be modelled with respect to reindeer stock density. Also the economy of reindeer husbandry based on different levels of feeding, and the effects of this husbandry practice on pastures, should be modelled. Models should be accurate and flexible enough to use when looking for solutions to practical questions and challenges in reindeer management.

Economical importance of Finnish reindeer industry

Within 15 years favourable weather conditions, antiparasite medication, supplementary feed, modern technology, calf slaughter and other factors all contributed to a vast increase in reindeer, and hence reindeer meat production, so much so that by the early 1990s the total number of reindeer was approaching 430 000, and reindeer meat production exceeded 4 million kg. Due to excess numbers of reindeer, stocks had to be culled. At the same time problems arose with the processing of reindeer meat. As a result, demand slumped and prices plummeted. In a few years the outlook for reindeer management changed drastically. Since then the profession has been marked by uncertainty and change. The number of reindeer is now below the permitted level. In the 1996/97 season, number of living reindeer in herds totalled over 202 000, slaughtered reindeer 80 000 (Fig. 1) and meat production about 2 million kg. Income from slaughtered animals amounted to FIM 58 million.

Kan vi beregne hvor mange rein beitene tåler?

Can we calculate how many reindeeer the pastures allow for? Three methods have been used to keep the reindeer population in accordance with the pasture resources. The carrying capacity is found by: 1) looking at the growth and well being of the animal (That is the "good old" way) 2) comparing unknown reindeer areas with well pracatised areas (Reindeer pasture convention of 1965) 3) estimating the yearly growth of lichens that can be grazed (Wild Reindeer Management after 1965) An economical carrying capacity has to be found by systematical asessment of the condition of the animals and the herd's production and at the same time value til condition of the pastures.

Human environmental interactions in Upper Lapland, Finland: Development of participatory research strategies

The paper outlines strategies for participatory research by comparing the results of a participatory workshop on research needs in human‐environmental interaction in Finnish Lapland with an analysis of official Finnish policy documents on the same subject. The workshop was organized in Anár/Inari, Finland in October 1997 as part of the Human Environmental Interactions theme (HEI) of the European Commission's Arctic‐Alpine Terrestrial Ecosystems Research Initiative (ARTERI). The mandate of ARTERI was to develop research themes and encourage their implementation to allow for discussions among local residents, natural and social scientists, and policy‐makers concerned with environmental protection and management in arctic and alpine regions of Europe. The objective of the Anár/Inari workshop was to discuss central issues of human‐environmental interaction in the region in a participatory mode with local interest groups, generate alternative scenarios for the region, and develop research and development project proposals on the basis of the scenarios. The paper discusses the scenarios and the project proposals that the workshop developed, and compares them with official Finnish policies on forestry and reindeer management in Lapland. From methodological and theoretical perspectives, the workshop was a unique empirical setting within which to investigate the dynamic interaction between traditional and modern knowledge sets on human‐environmental interaction. From the policy perspective, the comparison of workshop recommendations and official policies offers valuable indications for future directions in participatory policy‐making in the region and novel ways of balancing the conflicting demands on environmental resources, such as reindeer management, forestry, and tourism.

Reproduction and productivity of semidomesticated reindeer in northern Finland

The increase in the Finnish semidomesticated reindeer (Rangifer tarandus tarandus) stock and the high level of meat production during the 1980s and the beginning of the 1990s were mainly due to reindeer-management practices. However, the continuing deterioration of winter-range quality has now forced reindeer managers to invest increasingly in supplementary feeding. At the same time, carrying-capacity models for semidomesticated- reindeer ranges have proved difficult to develop. This study deals with reproduction and productivity of the reindeer stock in northern Finland during the period 1987-1995. The results reveal that reproduction and productivity of reindeer in the study area are largely regulated by density-dependent factors related to the quantity and quality of winter ranges. Reindeer densities on total rangeland had the strongest effect on the slaughter body masses of reindeer, which indicates the special importance of summer and autumn pastures for growth and autumn condition of reindeer. Through intensive calf slaughtering, the natural mortality rate was minimised and reproduction rates and reindeer meat production were increased, although winter ranges were heavy grazed. Developing semidomesticated-reindeer husbandry to be more economical in the future by keeping sustainable meat production at a sufficiently high level while maintaining reindeer rangeland in adequate condition and supplementary feeding quite marginal in Finland involves consideration of both ecological and management factors. One way of looking at the economic carrying capacity of Finnish semidomesticated-reindeer ranges is to develop a model based on dependence among the factors presented in this study. Sustainable net incomes from reindeer husbandry could then be optimised by studying and modelling the economy of reindeer management itself with respect to stock density.

Remote sensing, a tool for reindeer range land management

AbstractThe Finnish reindeer-herding area lies in the northern boreal forest zone. The herding area is divided into 57 reindeer management districts with a total area of 114,355 km2 (excluding water areas). The official number of reindeer in the year 1992 was 263,789, or 2.3 reindeer per square kilometre. In 1946 the density was only about one reindeer per square kilometre. The increased pressure on the mid-winter lichen pastures has reduced the volume of lichen. Also the decreased area of old coniferous forests with arboreal lichens has diminished the supply of food during the late-winter months. The lack of suitable winter pastures has led to the need for supplementary feeding with hay.The intention of this study was to develop and test methods for cost-effective reindeer range land inventory and to assess the present state of pastures in seven districts. Use was made of Landsat 5 TM satellite imagery that was processed with remote sensing and GIS software. The analysis of well-known field sites proved the image classification to be between 80 and 90% accurate. By comparing field data and classification results, estimates can be made on the available fodder reserves in the different pasture types. The results show that mid-winter pastures are both scarce and degraded in six of the seven areas investigated. Only one area (Muotkatunturi) has mid-winter pastures in reasonably good condition. Late-winter pastures with arboreal lichens are more widespread than mid-winter pastures and determine the amount of additional winter feeding required. Summer pastures are abundant in all seven reindeer-herding districts and are therefore not a limiting factor. The method used is objective, inexpensive, and fast when compared to conventional methods. Information can be produced on the quantity and quality of reindeer pastures. This knowledge can be used to make better estimates of the natural grazing capacity of reindeer districts in Finland.

The effects of outdoor recreation on range use by semi‐domesticated reindeer

The effects of a large holiday resort on the distribution and range use of semi‐domesticated reindeer were studied in the three most important habitat types in Saariselka, eastern Finnish Lapland. In two of these habitats the relative reindeer densities increased in winter, when outdoor activities declined reaching density equal to the average for the herding association at a distance of about 10 km from the holiday resort. In summer, male reindeer adapted better than females to the proximity of the holiday resort. The feeding site preferences of the reindeer during winter followed, in general, the normal pattern in areas with little human interference. Although the economic value of the range loss appeared small compared to the gain from outdoor enterprises, better planning is needed to avoid the harmful effects of recreation on reindeer management.

Systems ecology of radiocesium dispersal in forest landscapes and food

Persisting radiocesium in food of humans, reindeer, or other wildlife calls for research and assess­ ments of the future. What trends in Cs are likely in forest and shrubland, as well as crops and pasture? Soon after Chernobyl fallout in 1986, Swedish berry plants, tree parts, organic and sandy soil were ana­ lysed. Now we can infer rates of transfer among a typical ecosystem's parts. Cs in food chains in Nordic woodlands seems likely to remain high for many years. I predicted such Cs would be removed to less avail­ able forms in soil minerals more slowly than Cs in Nordic crop systems, or in deciduous forest tagged with Cs-137 at Oak Ridge National Laboratory, Tennessee* Cooler climate, partly evergreen plant habit, and many peat and sandy soils are among factors shared by Nordic countries that keep their Cs actively circu­ lating in the ecosystem. Reindeer food chains in lichen woodlands (pine or birch) and seasonal pastures** seem important for testing improved modeling of natural processes of the system and predicting alternative scenarios, without waiting to see the real future. For this purpose, we need help in estimating lower and upper bounds for RATES: e.g. fractions per week of Cs in important parts (vegetation, consumers, resi­ dues, soils) moving to the other parts. Calculations using the resulting table (matrix) of sources and desti­ nations would show net change (turnover) per week. Models combining many steps should imitate nature's redistribution of Cs. Displaying a range of possible future conditions and problems, and filling gaps in field or lab research, could clarify policy issues for reindeer and other ecological management.

Lichen ranges, animal densities and production in Finnish reindeer management

In the 1970s, mean lichen biomass ranged by the earmark districts (comprising of 2-9 adjacent herding associations) between 54 kg and 380 kg DM per ha correlating negatively with animal density per lichen ranges (range 1.5 - 14.3 ind. per km2). Biomasses were far below economic carrying capacity of lichen ranges (900 kg DM per ha). The condition of lichen ranges was poorest in the southern half of the area where alternative food to reindeer lichens (Deschampsia flexuosa, arboreal lichens and supplementary feeding) was available. In 1980-86, recruitment (calves per 100 females) was 33% higher than in the 1970's, on an average (65 vs. 49), despite a 90% increase in animal numbers between 1970 and 1986; recruitment has not been dependent on the condition of lichen ranges. The increase in production has been some higher than expected on the basis of animal numbers. The reasons for the increasing trends in animal numbers, recruitment and production remains some unclear, but they may include favorable winter conditions, supplementary feeding, medical treatment against parasites and proper harvesting policy.

Introduced reindeer on South Georgia—A management dilemma

Introduced mammals have had a major impact on the biota of islands in the Southern Ocean. Management plans for some islands include control measures for both introduced herbivores and carnivores that are justified on scientific grounds. In contrast, any active management of reindeer on South Georgia does not have a scientific justification since the survival of native species and communities are not at present threatened. Instead, the management option which is eventually chosen from those which are technically appropriate will be based on a value judgement by the management authority.

The management and utilization of reindeer in China

The management and utilization of reindeer in China

Management of wild reindeer in Norway

Wild reindeer in Norway are found in 26 separate management areas. Predators are virtually absent from all areas and hunting is the most important factor determining population development through alterations of herd size and structure. Average population density (animals/km2) after hunt was 1.96 in Hardangervidda, 1.18 in North Rondane and between 0.78 and 0.87 in Rondane South, Snøhetta, North Ottadalen and Forelhogna. Body size and female pregnancy rates followed a reverse trend. Average net increase of the herds varied from 42.2±10.0% in Forelhogna to 18.8±8.0% in Rondane North. In areas with animals in prime physical condition a high versus a low average harvest rate of calves resulted in a similar number of animals harvested, but a lower total yield of meat and revenue from hunting licences. At a winter population density of 0.8 - 2.0 animals/km2 annual harvest (per km2) of wild reindeer amounts to 0.23 - 0.51 animals, 9 - 18 kg meat and 286 - 850 NKr from sale of hunting licences. There was a significant relationship between body size expressed as carcass weights or mandible length and harvest success.

Economic comparison of two methods of supplementary feeding in Finnish reindeer management

The most common methods are (1) supplementary feeding with dry hay (maximally 50 kg per head a season) on natural ranges in mid and late winter, and (2) corral feeding, where the reindeer are fed in small yard-corrals with hay, green silage, lichen, molasses and commercial reindeer feeds for 3-5 months a winter.

Dialectics of intensivity and extensivity in saami reindeer management: A review article

Reindeer‐Herd Management in Transition: The Case of Tuorpon Saameby in Northern Sweden. Hugh Beach (Acta Universitatis Upsaliensis/Uppsala Studies in Cultural Anthropology, 3). Stockholm: Almqvist and Wiksell International, 1981. xix + 542 pp., fold‐out map, other maps, figures, charts, index.