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Article

The Effect of Payments for Ecosystem Services Programs on the Relationship of Livelihood Capital and Livelihood Strategy among Rural Communities in Northwestern China

1
School of Geography Science and Tourism, Xinjiang Normal University, Urumqi 830054, China
2
Xinjiang Institute of Ecology and Geography, Chinese Academy of Sciences, Urumqi 830011, China
3
Guangzhou Institute of Geography, Guangzhou 510070, China
*
Authors to whom correspondence should be addressed.
Sustainability 2015, 7(7), 9628-9648; https://doi.org/10.3390/su7079628
Submission received: 8 December 2014 / Revised: 10 July 2015 / Accepted: 13 July 2015 / Published: 17 July 2015

Abstract

:
The security and quality of livelihoods for peasant households is the core issue for rural areas in China. A stable livelihood contributes to the harmonious development of related polices, poverty eradication and sustainable use of resources. In Qinghe County, located in the extremely arid zone of Northwest China, 238 validated surveys were conducted. The analysis focuses on the importance of livelihood capitals for the selection of on- or off-farm livelihood strategies among beneficiaries of different kinds of ecological compensation packages. The goal is to see if different groups of beneficiaries are better able to pursue off-farm livelihoods activity, which reduces pressure on the resource base, and whether specific capitals are especially effective in helping households pursue off-farm livelihoods, which benefits their well-being. The findings show that proportionally more herdsmen (who participated in a pastureland rehabilitation program) were able to pursue off-farm livelihoods than farmers (who participated in the cultivated land reforestation program), and especially agro-pastoralists (who participated in both programs). Further, models of livelihood strategy show that human and financial capitals facilitate off-farm livelihoods, while productive capital tends to lead to on-farm livelihoods. These findings indicate that there is no single determinant of livelihood strategy, and future policies must consciously differentiate among beneficiaries to reach the desired result.

1. Introduction

The term “livelihood” is most commonly defined as people’s capacity to maintain a living [1] and several frameworks have been developed to analyze the sustainability of livelihoods [2,3]. The conceptual framework of the United Kingdom’s Department for International Development (DFID), which outlines a list of issues relevant to livelihood research, has attracted significant attention [4]. As the resource base possessed by households, “livelihood capitals” are grouped into human, natural, financial, physical, and social capitals [5]. The available capital constitutes a stock of assets that can be stored, accumulated, exchanged, and put to work to generate a flow of income or other benefits [6]. The condition of livelihood capital, focused on poverty alleviation and elimination, can reflect a household’s real livelihood situation. Depending on available capitals, folks employ different livelihood strategies to achieve livelihood goals. Hence, “livelihood strategies” are the range and combination of activities and choices that people make to realize their livelihood objectives, which can be classified into three categories: only farm, farm and off-farm, and only off-farm [7]. These livelihood activities are subject to the endowment with livelihood capital because they determine the possibilities for rural households to achieve goals related to revenue, safety, and welfare [2]. Generally, those with more livelihood assets tend to have more choices, a greater ability to handle stress and be better able to switch among various livelihood strategies.
From the perspective of conservation and sustainable use of ecosystem services (ES), economic instruments are primarily adopted to regulate the interests of stakeholders. Ecological compensation is a policy tool to address environmental problems that have an impact on household livelihood that is closely related to project sustainability and social fairness. As a financial incentive mechanism that transfers external or non-marketable environmental values to the local actors who provide ES, ecological compensation has attracted widespread attention in society and is being implemented in many countries with increasingly pressing ecological problems [8,9,10,11]. There are three modes of ecological compensation: compensation for the cost of ecosystem protection or damage mitigation, compensation for the funding of ecosystem protection and the loss of development opportunities, and investment in protected areas or objects with significant ecological value.
As the primary unit of economic activity and decision-making in rural areas, the household is the principal participant in ecological compensation projects, whose livelihood behavior would affect rural social and economic development, the manner of natural resource utilization, the supply of ES, and ultimately, the efficiency of the ecological compensation program [12,13,14]. In recent years, more attention has been given to evaluating the efficiency of ecological compensation, the major aspects of which are the willingness to participate in ecological compensation [15,16,17,18], as well as the impact of ecological compensation on household income [19,20,21], off-farm employment [22,23,24] and life style [25,26,27]. Additionally, a stable livelihood would result in the coordination of relevant policy development, poverty eradication and sustainable resource utilization [28,29,30].
In 1998, the revised Forest Law of China proposed that the State should establish the Forestry Ecological Efficiency Compensation Fund to protect forest resources. The State Council then promulgated regulations on Restoring Farmland to Forest in 2002, clearly defining the funds, food subsidies and other elements needed to ensure smooth progress. Subsequently, regulations on Returning Grazing Land to Grassland were promulgated in 2003, instituting grazing prohibitions, livestock-feed balances, and fine forage and production material subsidies to strengthen the protection of grasslands, especially in Inner Mongolia, Gansu, Ningxia, Qinghai, Yunnan, Sichuan, Xinjiang and so on in West China. The Chinese government has updated compensation details in succession, with a standard award of 13.5 dollars per hectare for grazing prohibition, and 3.45 dollars per hectare for livestock-feed balances each year in a pastureland rehabilitation program; however, a household is currently rewarded 204 dollars per hectare for the reforestation of cultivated land [31]. Furthermore, to prevent misappropriate funds and ensure issue schedule, all of these subsidies are issued by the form of One-Card directly to the household.
However, there are still some unresolved problems in China’s ecological compensation mechanism, such as no clear compensation range, unscientific compensation standards, relatively simple compensation models, lack of funding, undeveloped policy and regulation system, and so on.
The implementation of ecological compensation mechanisms can lead to significant changes in household assets and livelihood strategies among participating households. However, the impacts of ecological compensation programs are likely to depend on the kind of program in which a household participates. In the Chinese case, the government implemented ecological compensation payments programs designed for specific groups of beneficiaries. For present purposes, there are three categories of programs and thus beneficiaries in our research area. These include herdsmen, who participated in the pastureland rehabilitation program, farmers who participated in the cultivated land reforestation program, and agro-pastoralists who participated in both of these programs. Participation in distinct ecological compensation programs is intended to improve both household assets and thus livelihoods as well as environmental sustainability in terms of key natural resources on which households rely. The realization of a win-win situation thus depends on the accumulation of household livelihood capital and adjustments in household livelihood strategies. However, there remains limited research on the relative impacts of different ecological compensation programs as they influence households with distinct livelihood strategies.
We consider that a “one size fits all group” policy is likely to be weak and inefficient, especially in rural mountain communities with limited livelihood choices and low adaptive capacity [32,33]. We realize that it is necessary that ecological compensation mechanisms be designed to compensate a specific group of beneficiaries rather than a specific region [34]. Thus, to evaluate and clarify the household capital status within a local community, we established a comprehensive evaluation index system for livelihood capital. Index values, index structure and their situations of change were used for comparing the differences of livelihood capital among beneficiaries of different ecological compensation programs in the analysis. Then, a quantitative analysis was conducted to explore how livelihood capital affects livelihood activities (on-farm or off-farm strategies), as well as how beneficiaries of different ecological payments programs are affected. The goal is to see if different groups of beneficiaries are better able to pursue off-farm livelihoods, which reduces pressure on the resource base, and whether specific capitals are especially effective in helping households pursue off-farm livelihoods, which benefits their well-being. This could provide a reference for developing sustainable livelihoods practices and identifying the most important mode of compensation for different beneficiaries to ensure limited funds be optimally allocated.

2. Methodology

2.1. Description of Study Area

Located in the northeastern Xinjiang Uygur Autonomous Region of China (Figure 1), the upper reaches of the Ulungur River belong to the hinterland of the Eurasian continent and are characterized by mountains along the northeastern edge of the Junggar Basin, and alpine valleys to the southeast of the Altai Mountains, with an elevational range from 900 to 3659 m; the east and north sides border on Mongolia.
Figure 1. Location of study area.
Figure 1. Location of study area.
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The basic terrain type within the area is composed primarily of mountain, hill, plain and the Gobi desert. The plain area is an important base due to its fertile land, which is suitable for planting spring wheat, oilseed rape, oil sunflower and other crops. Other areas form the base for animal husbandry, and the botanical resources are composed of plain forest, steppe, meadow and desert. Available natural capital for households includes grassland, cultivated land and forestland.
Having been grassland nomads for a long time, the local lifestyle is characterized by moving households to follow pasture and water. However, many factors such as climate change, population growth, livestock overload and indiscriminate reclamation have all contributed to grassland degradation. Seventy-five percent of the natural grassland appears to have varying degrees of degradation, more than 37% of which is seriously degraded [35], where the conflicts between forage and livestock have been exacerbated.
There are 52 villages in Qinghe County, 26 of which are grazing villages and the remainder of which are farming villages. The county is composed of seven townships, and the total population and households were 64,273 and 18,764 respectively in 2011; there is a similar percentage of males and females, with a population density of 4.08 people per square kilometer. In addition to the Han nationality, there are several ethnic minorities, such as Kazak (76.46%), Hui and others, inhabiting this area, and the poverty rates are high.
Qinghe is a large agricultural county that has a rural population more than 60% of the total population in 2011. Of a total population of 39,253 rural people and 8798 village households, 22,378 rural people and 4975 households rely primarily on grazing. Thus, whether the statistical unit is the household or the individual, the grazing population is higher than the farming population. Animal husbandry is the primary traditional industry, with rural per capita income approaching 648 dollars in 2011. Currently, livelihood strategies of planting (food crops, such as wheat and potato; economic crops, such as sunflower; grass crops, such as silage corn and high-quality forage) and some breeding (sheep, cattle, chickens, ducks, etc.) are adopted in the farming zone, whereas grazing and breeding (sheep, goats, beef cattle, dairy cattle, horses, camels, etc.) were the primary livelihood activities in the grazing zone.
Qinghe County’s public infrastructure is weak because of the remoteness of the area and the scattered population. On average, each teacher is responsible for 5.5 and 10.0 students in secondary and primary school, respectively, and there are 3.3 physicians and 2.8 hospital beds per 1000 people. Development of transportation, power and water supplies, education, healthcare, cultural opportunities and other social undertakings are relatively slow, overall.
In recent years, Qinghe County has been attentive to the development of new irrigation areas, agricultural industrialization, mining exploration and exploitation, port economy, pastoralist settlements, and so on, working towards a transition from traditional agriculture to modern industry as part of the region’s socio-economic development.
The government compensates households by providing subsidies through the ecological compensation project, but if households use these subsidies to buy forage, repair or build livestock housing, improve livestock breeds or develop non-agricultural industries, does this create a more sustainable livelihood? We therefore consider the importance of participation of distinct groups of beneficiaries in different ecological compensation programs for livelihood outcomes, notably livelihood capitals and livelihood strategies. Specifically, we focus on the effects on whether households pursue on-farm or off-farm livelihood strategies. This focus is important since on-farm livelihood strategies rely on natural resources. However, if the resource base is threatened, so are livelihood strategies. That makes an analysis of the effects of livelihood assets for on- and off-farm livelihood strategies an important question. Even more important is an analysis that considers those effects for groups participating in different ecological compensation programs. This is because receiving compensation to recuperate the resource base may itself be important to provide families the opportunity to engage in off-farm livelihoods, improving their well-being while also sustaining the resource base.

2.2. Methodological Approach

2.2.1. Data Collection

Because the nomadic tradition functions seasonally, with herding families returning to high mountain rangelands in the summer and to desert pastures in the winter, our survey was restricted to a specific time range to ensure the full participation of the respondent groups. An appropriate survey time was before households moved to summer or winter pastures; this was also a season of relative leisure, when we did not worry about disturbing them. Two preliminary investigations were conducted in April 2013, with the goals of collecting natural and socio-economic statistical data from the seven townships and county departments, building a suitable index system for the research area to evaluate livelihood capital as well as designing questions and options for the questionnaire. Above all, the questionnaire was designed to focus on the livelihood capitals and livelihood strategies of farmers, herdsmen and agro-pastoralists.
We excluded the town of Qinghe from the investigation on the grounds that there was no existing ecological compensation project. The final version of the questionnaire was launched employing PRA (Participatory Rural Appraisal) [36] in a total of 22 representative villages during a two-week period in November 2013, with each questionnaire requiring approximately 1 to 1.5 h to complete. We administered 241 questionnaires by household interviews using proportional selective sampling (with a sampling fraction of 1.6%) based on both population size and the dimensional distribution of the six townships. After excluding three invalid questionnaires (with incomplete data), we collected a total of 238 validated questionnaires, of which 78, 106 and 54 were from farmers, herdsmen, and agro-pastoralists, respectively. Detailed information is listed below in Table 1.
Table 1. Sampling distribution and proportion based on different beneficiaries and towns.
Table 1. Sampling distribution and proportion based on different beneficiaries and towns.
TownsAreleArele TuobieAgashi AobaoChagan GuoleSaer TuohaiTake ShikenTotal
Number of households (household)48252959139820251695111314015
Potential number of survey households (household)774722332718224
Actural number of survey households (household)total814924362919238
farmers271681110678
herdsmen37231117139106
agro-pastoralists1710586454
Number of villages (unit)1413666449
Number of survey villages (unit)total75242222
grazing villages33121111
farming villages42121111

2.2.2. Measurement of Livelihood Capital

Identification of the Primary Indicators Related to Livelihood Capitals

After considering the definition of livelihood capital, the relevant literature [21,37], actual characteristics of regional situations as well as what data were available, we selected 15 indicators to represent the attributes of livelihood capital (human capital, natural capital, financial capital, physical capital and social capital) in the study area. Each livelihood capital has three indicators to capture its salient features. Table 2 lists the relevant details of the indicators.
Table 2. Indicators of livelihood capital.
Table 2. Indicators of livelihood capital.
Livelihood CapitalIndicatorsImplicationFormula
Human capital (C1)Labor capacity C11Labor ability of each family member is assigned as full labor (1), half labor (0.5), or off-labor (0). The labor ability values of all family members are summed and standardized.C1 = 0.260C11 + 0.393C12 + 0.347C13
Education level C12The education level of each family member is assigned as college and above (1), high school (0.75), middle school (0.5), primary school (0.25), or illiterate (0). The education level values of all family members are summed and standardized.
Male labor C13Index of C13 is set to a binary variable: if a family has at least one adult male laborer, then C13 is assigned as 1; otherwise, C13 is 0.
Natural capital (C2)Cultivated land resource C21Index of C21 is the standardized cultivated land area per capita.C2 = 0.413C21 + 0.270C22 + 0.317C23
Grassland resource C22Index of C22 is the standardized grassland area per capita.
Forestland resource C23Index of C23 is the standardized forestland area per capita.
Physical capital (C3)Livestock C31Livestock is the most significant physical capital in the study area. The primary livestock types include camel, horse, cattle and sheep, weighted as 1, 0.8, 0.6, and 0.2, respectively. The livestock capital of one family is the sum of each livestock number multiplied its weight. The index of C31 is the standardized livestock capital of the sample family.C3 = 0.386C31 + 0.398C32 + 0.216C33
Physical equipment C32Physical equipment includes warm barns, hay mowers, motors, vehicles, stockyards, etc. A value of 1 is added for each type of physical equipment that the family owns. The index of C32 is the standardized the sum of physical equipment value.
Housing conditions C33① Housing size: 5 rooms and above (1), 4 rooms (0.75), 3 rooms (0.5), 2 rooms (0.25), and 1 room (0); ② Housing type: concrete house (1), brick house (0.75), civil house (0.5), tent (0.25), and thatched cottage (0); ③ Grades of size and type were weighted equally (0.5:0.5). The index of C33 is the standardized sum of each housing situation multiplied by its weight.
Financial capital (C4)Cash income per capita C41A households’ financial capital is primarily from cash income. The index of C41 is the standardized cash income per capita.C4 = 0.192C41 + 0.381C42 + 0.427 C43
Access to low-interest loans C42Formal financial institutions (banks, credit cooperatives) and individuals (relatives and friends) are two major sources of low-interest loans. The index of C42 is set to a binary variable: if a household can get a loan, then C42 is assigned as 1, otherwise C42 is 0.
Access to cash support C43The index of C43 is set as a binary variable: if a household can get free cash assistance, then C43 is assigned as 1, otherwise C43 is 0.
Social capital (C5)Leadership potential C51① There is significant social capital for family members employed in government agencies, with access to a stable income and other assistances. Officials in a family: if a family member engages in a government agency, then its value is 1, if not, it is 0; ② The frequency of opposition during a community meeting: often (1), usual (0.75), sometimes (0.5), few (0.25), or never (0); ③ Officials and frequency were weighted 0.7:0.3, respectively. The index of C51 is the standardized sum of a leadership situation multiplied by its weight.C5 = 0.447C51 + 0.205C52 + 0.348C53
Confidence C52Grades of confidence in people around: all (1), most (0.75), half (0.5), little (0.25), or none (0). The values are standardized.
Relatives C53The index of C53 is the standardized number of relatives in the township.
Total livelihood capital (C)C = C1 + C2 + C3 + C4 + C5
The main investigation information are given below: (1) Human capital, including family size and each member’s gender, age, education level, occupation and health condition; (2) Natural capital, including area of cultivated land per capita, area of grassland per capita, area of forestland per capita, yield of cultivated land per mu, yield of forestland per mu, production reduction caused by natural disasters, availability of good crop varieties, pasture quality, grazing time, etc.; (3) Physical capital, including number of livestock, number of livestock for sale, cost of feed, physical equipment of family for production and life, availability of housing for size and type; (4) Financial capital, including cash income by their livelihood strategy, low-interest or interest-free loans and other subsistence allowances provided by governments; (5) Social capital, including members of family employed in governments, opposition frequency when a community meeting, confidence proportion in people around, and relatives number in the township.

Determining the Weighted Scores

The weight of an indicator plays a significant role in livelihood capital quantification because it can influence the final results. The majority of existing studies assign weight in a subjective manner; however, this may not be sufficiently precise for judging local livelihood capital. To improve the reliability of the quantification, this paper attempts to calculate objective weights using the entropy method.
The features of entropy weight method are as follows [38,39]: (1) Supposing the values of evaluated objects in the index j are absolutely equal, the entropy value gets a maximum that is equal to 1, yet the entropy weight is equal to 0. This means deciders cannot acquire any helpful information from this group of index j; (2) If there exists a considerable difference among the values of evaluated objects in the index j, the entropy value is small and the value of the entropy weight is large. This denotes that decision makers can gain helpful information from the group of index j. Meanwhile, evaluated objects that have great differences in the index j should be highlighted. The entropy can be used as an important basis for choosing indexes; (3) From the perspective of information, the entropy represents the quantity of helpful information provided by the index, which means the value of the entropy weight represents the significance of indexes. The entropy weight, reflecting the real importance of indexes, signifies the degree of competition between indexes rather than the coefficient.
The general process to calculate entropy weight is as follows [40,41,42,43,44]:
If there are “p” livelihood capital samples (i = 1,2,3,…,p) and each sample has “q” evaluated variables (j = 1,2,3,…,q), then matrix X can be constructed as follows in Equation (1):
X = { X 11 X 12 X 1 q X 21 X 22 X 2 q X p 1 X p 2 X p q }
When measuring the weights, the raw data must be standardized to eliminate error caused by the types of dimensions and units based on the formula given below:
Y i j = ( X i j min { X j } ) / ( max { X j } min { X j } )
where, Yij corresponds to the normalized value for an evaluated variable (j) in a particular livelihood sample (i), Xij represents the original datum matrix of livelihood capital in Table 2, and min { X j } and max { X j } are the minimum and maximum value of each evaluated variable group, respectively.
The ratio of index value of index j and sample i is shown in Equation (3):
P i j = Y ij / i = 1 p Y ij
The information entropy (Ej) is given by the following equation,
E j = ( 1 / ln   p ) × i = 1 p ( P i j × ln   P i j )
A low value of Ej represents a high effect of index j. Therefore, entropy weight (wj) of variable j can be calculated with the following equation:
W j = ( 1 E j ) / j = 1 q ( 1 E j )

Calculating Livelihood Capital Index

We can estimate the index value of livelihood capital Ci as:
C i = i p w j Y i j
The value of the index is a view to evaluate livelihood capital and is called the livelihood capital index. The livelihood capital index values of typical beneficiaries are the averages of sample households. Another new view is the livelihood capital structure, consisting of human, natural, financial, physical, and social capitals.

2.2.3. Models of Livelihood Capitals and Livelihood Strategies among Beneficiaries of Different Ecological Payment Programs

This study focuses on the choice of on-farm or off-farm livelihoods, which is well-established as a key indicator of livelihood strategies. This choice implies a binary variable that indicates whether the livelihood strategy is on-farm or off-farm. Hence, binary logistic regression is an appropriate ideal model to analyze individual decision-making behavior, which can be used to describe the causal relationship between livelihood strategy (e.g., dependent variable Y) and livelihood capital (e.g., independent variable Ci) [45,46]. When using the logistic distribution, we need to make Y a random dependent variable, ranging from 0 to 1 (1 stands for choosing this type of livelihood activity), and Ci (i = 1,2,…,p) be the independent variables associated with Y in observation p of the livelihood samples. The form of the logistic probability function is:
P = E x p ( Z ) 1 + E x p ( Z )
Z = b 0 + b 1 C 1 + b 2 C 2 + + b p C p + ε i = b 0 + i = 1 p b i C i
where, P is the probability, Z is the linear combination of Ci(i = 1,2,…,p), Exp is the exponent function, b0 is the constant, and bi (i = 1,2,…,p) is the regression coefficient.
In the statistical analysis process, we set the probability of “choose off-farm” as P (Y = 1), whereas probability of “not choose off-farm” is set as 1-P (Y = 1). Usually, the logistic probability function is transformed by Logit to obtain the linear expressions between dependent variable and independent variables as follows:
L o g i t ( P ) = L n ( P 1 P ) = b 0 + i = 1 n b i X i
The maximum likelihood method is commonly used to estimate parameters, and the model can be run by SPSS17.0. A positive regression coefficient indicates a positive relationship between livelihood capital and off-farm livelihood strategies, whereas a negative regression coefficient indicates an adverse relationship between livelihood capital and non-farm livelihood strategies. The odds ratio, an important indicator quantifying the degree of influence that an independent variable has on a dependent variable, can be measured as a specific value between the incident frequency of occurrence and not occurrence, with the result that the probability of livelihood strategies increases or decreases by exp(bi) times as the livelihood capital (Ci) increases or decreases by one unit [2,47].

3. Results and Discussions

3.1. Analysis of Household Livelihood Strategies

Figure 2 indicates the proportion of households engaged in each livelihood activity. Depending upon grassland, cultivated land, forestland resource and human input, agricultural activities (crop planting, animal husbandry) and off-farm activities (outside employment, wage job, business, etc.) are the primary livelihood activities for households in the study region, with low levels of non-farm strategies overall. Farmers engage in planting, husbandry and off-farm industries to support their families and show the highest proportion of engagement in business, wage jobs and part-time jobs among the three types of beneficiaries. Among herdsmen, 96.15% and 24.36% are occupied in husbandry and outside employment, respectively, and few are engaged in planting. The dominant livelihood practice of agro-pastoralists is husbandry, but a significant proportion of agro-pastoralists engage in transportation. Generally, herdsmen and agro-pastoralists depend more on natural resources than farmers.
Figure 2. Main livelihood activity of different beneficiaries from ecological compensation.
Figure 2. Main livelihood activity of different beneficiaries from ecological compensation.
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3.2. Comparison of Household Livelihood Capital

The livelihood capital index of sample households is 1.714 (Figure 3). There is a clear difference in the livelihood capital index among heterogeneous households in the study area. Agro-pastoralists have the highest livelihood capital index, with an index of 1.794, followed by herdsmen and farmers with indices 3.60% and 8.68% lower than agro-pastoralists, respectively. These differences may be influenced by factors such as natural conditions, resource availability, production mode and cultural customs.
Figure 3. Livelihood capital index of the different households.
Figure 3. Livelihood capital index of the different households.
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The livelihood capital polygon best illustrates the composition and structure of household livelihood capital. The center of the livelihood capital pentagon represents a zero value, whereas the external boundary (vertex) represents a maximum value of some capital. The ideal livelihood capital polygon is a regular polygon, namely balanced and coordinated development of various types of livelihood capitals. Figure 4a shows the accumulation and development were happened in Qinghe County’s household livelihood capitals. Human capital has a comparative advantage and could ensure a sufficient labor capacity to develop new revenue streams. Natural capital is at a relative disadvantage and is constrained by the natural environment of the research area and a reduction in available land.
A change in the index of livelihood sustainable capacity before and after ecological compensation can reflect whether the livelihood capital structure is moving in a positive direction; the dividing line between a positive and negative change is the value 1. Although the livelihood capital index of herdsmen and agro-pastoralists are somewhat higher than those of farmers (Figure 3), their change in index of livelihood sustainable capacity is experiencing a backward, particularly for the agro-pastoralists (Figure 4b).
Figure 4. (a) Livelihood capital pentagon of the different households; (b) The change in livelihood sustainable capacity before and after ecological compensation.
Figure 4. (a) Livelihood capital pentagon of the different households; (b) The change in livelihood sustainable capacity before and after ecological compensation.
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3.3. Relationship between Livelihood Strategy and Livelihood Capital

Pearson correlation coefficients were calculated for indices of the five types of livelihood capital to verify the applicability of the model. Table 3 shows that the absolute value of correlation coefficients between explanatory variables is between 0 and 0.4, indicating that the capital variables are statistically independent of one another. Consequently, it is suitable to apply the logistic regression model to sample households.
Table 3. The correlation coefficients between different livelihood capitals.
Table 3. The correlation coefficients between different livelihood capitals.
Human CapitalNatural CapitalPhysical CapitalFinancial CapitalSocial Capital
Human capital1
Natural capital−0.0801
Physical capital0.2300.1071
Financial capital−0.084−0.0490.0071
Social capital0.0890.1360.149−0.0121
To understand the determinants of livelihood strategy and to compare the differences among beneficiaries of different ecological compensation programs, livelihood strategies were divided into two types (i.e., farm or non-farm activities) primarily based on the share of total earnings derived from these two types of activities. Table 4 clearly shows that there is a close relationship between households’ livelihood capitals and their adopted livelihood strategies.
Table 4. Logistic regression model analysis of livelihood strategies.
Table 4. Logistic regression model analysis of livelihood strategies.
Types of Capital Total SampleFarmersHerdsmenAgro-Pastoralists
Human capital (C1)B0.67744.0075 ***2.1540 ***4.2730 *
S.E.1.00801.78291.19022.3753
Natural capital (C2)B−2.53100.0643−0.02093.3623 *
S.E.3.20024.01504.95632.0119
Physical capital (C3)B−2.5683 **−2.5075−1.9518 **−2.8853
S.E.1.29722.57771.58364.9299
Financial capital (C4)B0.8815 *2.0550 **0.9208−1.0732
S.E.0.58101.45980.77332.3931
Social capital (C5)B−1.5229−0.1175−0.12972.0315
S.E.1.30152.65971.68455.0890
ConstantB0.7594−3.9690−1.1719−5.1611
S.E.0.79782.17751.06333.8666
S.E. corresponds to standards error; * Significance level: 10%; ** Significance level: 5%; *** Significance level: 1%.

3.3.1. Herdsmen

Out of 106 questionnaires, 60.90% of herdsman households engaged in farm livelihood activities, whereas 39.10% of the interviewed families engaged in non-farm activities. As shown in Table 4, there is a high correlation between livelihood strategy and human and physical capital. The results show that physical capital plays a positive role in farm livelihood strategy, indicating that households with higher levels of physical capital have a greater potential for engaging in farm livelihood activities. Non-farm livelihood activities, however, show a positive relationship with human capital. This suggests that it is human capital that drives the rural household choice of an off-farm livelihood strategy. With regard to details, the probability of a farm livelihood strategy increases by 7.042 times when the physical capital is increased by one unit; the chances of an off-farm livelihood strategy increase by 8.619 times for additional unit of human and capital (see Table 5 and Figure 5a).
Figure 5. (a) Relationship between livelihood strategy and livelihood capital for herdsmen; (b) For farmers; (c) For agro-pastoralists.
Figure 5. (a) Relationship between livelihood strategy and livelihood capital for herdsmen; (b) For farmers; (c) For agro-pastoralists.
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Table 5. Estimation value of the relationship between livelihood strategy and livelihood capital.
Table 5. Estimation value of the relationship between livelihood strategy and livelihood capital.
Types of CapitalTotal SampleFarmersHerdsmenAgro-Pastoralists
Human capital(C1)1.968855.00928.619371.7365
Natural capital(C2)0.07961.06640.979328.8555
Physical capital(C3)0.07670.08150.14200.0588
Financial capital(C4)2.41457.80682.51130.3419
Social capital(C5)0.21810.88910.87847.6255
Constant2.13700.01890.30980.0057

3.3.2. Farmers

Out of 78 questionnaires, 75.01% were from farm households and 24.99% were from off-farm households. Table 4 demonstrates that the relation between physical capital and farm strategy is positive-going. In this regard, the growth in physical capital will lead to a higher likelihood of farmers choosing farm strategies. In contrast, human and financial capitals express a negative effect on farm livelihood activities. That is, an increase in human and financial capitals brings about improved access to non-farm opportunities. Human capital, however, has a larger effect on non-farm livelihood activities than financial capital. According to the logistic regression analysis, the probability of off-farm livelihood activities increases by 55.009 and 7.807 times, respectively, with a one-unit increase in human and financial capitals (see Table 5 and Figure 5b). One possible interpretation of this result is that financial resources are more limited (low deposits, low rewards, and high debts) in farming households to develop off-farm strategy than herdsmen and agro-pastorlists. This would explain the significance of financial capital for farmers.

3.3.3. Agro-Pastoralists

In the agro-pastoralist group, the proportion of farm households is 88.89% and the proportion of off-farm households is 11.11%. The proportion of off-farm households is 27.99% lower than in herders and 13.88% lower than in farmers. The results in Table 4 suggest that there is a significant correlation between livelihood strategies and human, natural, physical, financial and social capital. Human, natural and social capital appear to have a clear positive influence on non-farm livelihood activities, but physical and financial capital have a negative impact on these activities. Compared with other beneficiaries, agro-pastoralists do have the highest overall level of capitals. So perhaps, participating in the PES programs may be less important than in the other groups. In Table 5 and Figure 5c, the probability of off-farm livelihood activities increases by 71.737 and 28.856 times, respectively, in response to a one-unit increase in human and natural capital.

3.3.4. Comparison among Different Households

The slope of the curve in Figure 5 indicates the association degree between livelihood capital and livelihood strategy, that is, a steeper slope corresponds to a higher level of correlation. A shared phenomenon among the three types of beneficiaries is that human capital is a catalyst in increasing the opportunity of non-farm activities, but differs in the level of correlation extent. The probability of off-farm livelihood practices to human capital of agro-pastoralists is approximately 1.3 and 8.3 times greater than that of farmers and herdsmen, respectively. The financial capital (farm or off-farm earnings, ecological compensation rewards, deposits, etc.) of farmers and the natural capital of agro-pastoralists influences their correlation to off-farm livelihood activities, whereas physical capital influences correlation to farm activities in herdsmen. It is clear that the livelihood strategies of different beneficiaries from ecological compensation are influenced by their capital base. Consequently, when considering follow-up policies for acceleration of non-farm or farm industries, governments should consciously differentiate among the beneficiaries to achieve the desired effect and to ensure that limited resources are allocated optimally. For example, identifying the priorities of each target group for compensation capital should be encouraged.

3.4. Livelihood Strategy Implications

Given the pattern of livelihood strategies in this region, with weak livelihoods and earning inequalities, strong external interventions are needed to influence the household choice of a particular livelihood pathway.
Animal husbandry and agriculture, as the sources of food and cash, are relatively more important to a local resident’s livelihood in this region than other strategies. Highlighting physical capital illustrates an important mechanism for development of farm livelihood activities. Farm strategies are indispensable in today’s society to maintain food security of the household and also to improve production conditions.
Simultaneously, it is increasingly recognized that the expansion of non-farm employment is a more effective method for the augmentation of income and alleviation of household poverty. Partial surplus labor enhances a family’s total income through entering off-farm activities. Emphasis on human capital (such as training, culture and education, and improvements in healthcare) and other capital relevant to the different beneficiaries mentioned above (such as greater access to low-interest loans and establishment of cooperative organizations) makes households less dependent on natural resources or farm activities and is a vital technique for boosting non-farm livelihood strategies. This requires the support of an educated and energetic labor force, as well as the construction of market, traffic, communication, and other infrastructures to vitalize local economies and create more development opportunities.
Overall, a mixed livelihood strategy is a channel for diversifying to ensure revenue growth and higher living standards, which could also alleviate the pressure on ecological environment and reduce the vulnerability of single livelihood activity. It is worth mentioning that we must pay close attention to the important role of national cultural and let household be actively involved in by forming a spatial and temporal buffer zone to prevent life maladjustments and cultural discontinuities when entering into a new livelihood.

4. Concluding Remarks and Policy Recommendations

4.1. Concluding Remarks

Qinghe County’s livelihood strategy is dominated by animal husbandry and agriculture practices. A households’ livelihood activity type is usually singular and not sufficiently diversified to ensure livelihood security. Pursuing the simultaneous development of animal husbandry, agriculture and non-farm employment may be the most desirable path to local rural sustainable development.
Differences exist both in the livelihood capital index and livelihood capital structure among the different types of households. Natural capital is at a relative disadvantage in Qinghe County, although a majority of households rely on it to make a living, particularly herdsmen (who participated in pastureland rehabilitation program) and agro-pastoralists (who participated in both pastureland rehabilitation and cultivated land reforestation programs).
Although choices vary among beneficiaries of different ecological compensation programs, the manner in which a household chooses livelihood options directly depends on the availability and accessibility of livelihood capital. The findings permit the conclusions below: human, natural and financial capital facilitate off-farm livelihoods practices, while productive capital tends to lead to on-farm livelihoods behaviour. Considering the fact that different groups of beneficiaries are better able to pursue off-farm livelihoods, as well as specific capitals are especially effective, future policies need to consider the demands of different beneficiaries to allocate resources appropriately and effectively.

4.2. Policy Recommendations

For a district such as Qinghe County in a less-developed region of western China, the questions of how to transform traditional nomadic production into modern animal husbandry and how to give consideration to both ecological and economic interests in land reforestation, are both difficult and important for local governments.
According to the different correlation types between livelihood capital and livelihood strategy, we recommend identifying the most significant and preferred compensation mode for different beneficiaries.
(1) Herdsmen should be compensated for their human capital in priority. The manner in which the government trains grassroots cadres, livestock breeders and crop growers is of great importance to a household’s ability to self-develop. Training should focus on grass cultivation, shelter feeding, multiple-birth breeding, hybrid-fattening, practical job skills and so on. In addition, particular attention should be given to the academic education and training of the younger generation, giving them the capacity to move out of the farming and grazing community.
(2) In addition to continuing to improve the farmers’ human capital, it is vital to give priority to enhance farmers’ financial capital stock. Construction of agricultural information services, ability of accessing small loans and development of private financial capital are all the effective channels to broaden the diversification way of credit services. Improving the employment structure and helping rural surplus labor pursue off-farm livelihood activities is another method to accumulate their financial capital. Besides, further promote the reform of rural health care and education systems can reduce the cost of the financial capital.
(3) Agro-pastoralists should focus on supporting human capital and natural capital. On the basis of enhancing the stock of human capital, natural capital should be more actively protected. Consequently, we need to heavily emphasize the protection of natural capital from exploitation, henceforth, and enhance conversion abilities among human, physical, financial and social capitals. We need to be aware of the difficulty of restoring the ecological environment in this fragile arid zone once it has been destroyed.
Meanwhile, concentrated planning should guide households in appropriately using grant rewards, implementing grazing in warm seasons and feeding in cold seasons, as well as constructing commercial forests. Inevitably, a thorough system of stock breeding, disease control, forage production and product distribution network should be established.
Moreover, contractual responsibility and delimitation of prime grassland are greatly needed to strengthen supervision and regulation during the implementation of ecological compensation policies. To keep a monitoring mechanism running smoothly and effectively, it is also necessary to build a community team of county officials, township professionals and village operators and to include mutual supervision by households. Awards can be used to support a household that impeaches the overstocking behavior of others.
Above all, ecological compensation, as an ecological project, should be combined with various measures, such as poverty alleviation, agricultural science and technology, comprehensive agricultural development, water and soil conservation, adjustment of industrial structure, ecological migration, and settling of pastoralists, to ensure household earnings that will continue to increase beyond the compensation period, improve the integrity of regional economic development, and promote the formation of mechanisms for household self-development.

Acknowledgments

This work was supported by the project WATERCOPE funded by International Fund for Agricultural Development (I-R-1284-WATERCOPE). The authors would like to appreciate the help of principal Nurbek from Qinghe County Party School, Yuxia Shan, Yesiboli Helati, Ayiken Dalailihan, Nurhabu Bayimuhemaiti and Yerlan Baterhan from Xinjiang University of Finance and Economics for their pious language translations in questionnaire survey. The authors also express much thank to Bureau of Statistics of Qinghe County in data collection and anonymous referees for their helpful comments and very specific suggestions.

Author Contributions

Fei Wang, Degang Yang and Changjian Wang designed research; Fei Wang, Changjian Wang and Xinhuan Zhang performed research, Fei Wang and Changjian Wang contributed new analytic tools. All authors wrote the paper. All authors have read and approved the final manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

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MDPI and ACS Style

Wang, F.; Yang, D.; Wang, C.; Zhang, X. The Effect of Payments for Ecosystem Services Programs on the Relationship of Livelihood Capital and Livelihood Strategy among Rural Communities in Northwestern China. Sustainability 2015, 7, 9628-9648. https://doi.org/10.3390/su7079628

AMA Style

Wang F, Yang D, Wang C, Zhang X. The Effect of Payments for Ecosystem Services Programs on the Relationship of Livelihood Capital and Livelihood Strategy among Rural Communities in Northwestern China. Sustainability. 2015; 7(7):9628-9648. https://doi.org/10.3390/su7079628

Chicago/Turabian Style

Wang, Fei, Degang Yang, Changjian Wang, and Xinhuan Zhang. 2015. "The Effect of Payments for Ecosystem Services Programs on the Relationship of Livelihood Capital and Livelihood Strategy among Rural Communities in Northwestern China" Sustainability 7, no. 7: 9628-9648. https://doi.org/10.3390/su7079628

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