landrace |
A breed that has largely developed through adaptation to the natural environment and traditional production system in which it has been raised (FAO, 2013).
|
Global assessment (1st work programme) |
landscape composition |
The abundances of patch types represented within a landscape. Composition is not spatially explicit because it refers only to the variety and abundance of patch types, but not their placement or location (dispersion) in the landscape.
|
Pollination assessment |
landscape configuration |
The distribution, size and abundances of patch types represented within a landscape. Configuration is spatially explicit because it refers not only to the variety and abundance of patch types, but also to their placement or location (dispersion) in the landscape.
|
Europe and Central Asia assessment |
landscape functioning |
The capacity or potential of landscapes to provide services (Bolliger & Kienast, 2010).
|
Global assessment (1st work programme) |
landscape heterogeneity |
Landscape heterogeneity is a complex phenomenon involving the size, shape and composition of different landscape units and the spatial (and temporal) relations between them (G. Cale & J. Hobbs, 1994).
|
Global assessment (1st work programme) |
landscape heterogeneity |
Landscape heterogeneity is a complex phenomenon involving the size, shape and composition of different landscape units and the spatial (and temporal) relations between them.
|
Sustainable use assessment |
landscape planning |
An activity concerned with reconciling competing land uses while protecting natural processes and significant cultural and natural resources.
|
Pollination assessment |
landscape socio-ecological approach |
The landscape scale approach incorporates the socio-ecological system, including natural and human-modified ecosystems, influenced by ecological, historical, economic, and socio-cultural processes. The landscape includes an array of stakeholders small enough to be manageable, but large enough to deliver multiple functions for stakeholders with differing interests.
|
Land degradation and restoration assessment |
landscape |
A human-defined area ranging in size from c. 3 km2 to c. 3002 km. Landscape is spatially heterogeneous in at least one factor of interest and often consists of a mosaic of interacting ecosystems.
|
Land degradation and restoration assessment |
landscape |
An area delineated by an actor for a specific set of objectives, constitutes an area in which entities, including humans, interact according to rules (physical, biological, and social) that determine their relationships; Place-based systems that result from interactions between people, land, institutions (laws, rules and regulations) and values. Interactive aspects that define a landscape are functional interactions, negotiated spaces and multiple scales.
|
Global assessment (1st work programme), Asia-Pacific assessment |
landscape |
An area of land that contains a mosaic of ecosystems, including human-dominated ecosystems.
|
Americas assessment, Sustainable use assessment, Europe and Central Asia assessment |
large scale land acquisition |
The control (whether through ownership, lease, concession, contracts, quotas, or general power) of larger than locally-typical amounts of land by any persons or entities (public or private, foreign or domestic) via any means (‘legal’ or ‘illegal’) for purposes of speculation, extraction, resource control or commodification at the expense of agroecology, land stewardship, food sovereignty and human rights. It is sometimes also called land grabbing.
|
Global assessment (1st work programme) |
large scale land acquisition |
See ‘Grabbing (of wild species and space)’.
|
Sustainable use assessment |
law of the sea |
The United Nations Convention on the Law of the Sea (UNCLOS), in force since 1994, defines the rights and obligations of nations (167 at present) with regard to the use of the world's oceans and their resources, and the protection of the marine and coastal environment. The UNCLOS also defines national marine jurisdiction on maritime territories and provides guidelines related to the use and management of marine environment and resources.
|
Sustainable use assessment, Global assessment (1st work programme) |
leaching |
The dissolution and movement of dissolved substances by water.
|
Europe and Central Asia assessment |
leaf area index |
The total area of green leaves per unit area of ground covered (FAO, 2018a).
|
Global assessment (1st work programme) |
leakage |
An environmentally damaging activity that is relocated elsewhere after being stopped locally.
|
Americas assessment |
leakage effect |
Phenomena whereby the reduction in emissions (relative to a baseline) in a jurisdiction/sector associated with the implementation of mitigation policy is offset to some degree by an increase outside the jurisdiction/sector through induced changes in consumption, production, prices, land use and/or trade across the jurisdictions/sectors. Leakage can occur at a number of levels, be it a project, state, province, nation or world region.
|
Global assessment (1st work programme) |
learning (traditional and formal) |
Learning refers to the process of knowledge and skills acquisition. Studies on learning have payed attention to the different ways people acquire knowledge, practices, and beliefs (i.e. imitation, copying, trial-and-error), but also to the dynamics of kn.
|
Global assessment (1st work programme) |
learning (traditional and formal) |
Learning refers to the process of knowledge and skills acquisition. Studies on learning have payed attention to the different ways people acquire knowledge, practices, and beliefs (i.e. imitation, copying, trial-and-error), but also to the dynamics of knowledge transmission, or the different sources from which knowledge, practices, and beliefs are passed from one individual to another (i.e. from parents, peers, teachers, prestigious peoples, media, etc.). Social learning is defined as the acquisition of new information by copying others, and it is a key human strategy that allows for the accumulation of culturally transmitted knowledge.
|
Sustainable use assessment |
legal and regulatory instrument |
see “Policy instruments”.
|
Sustainable use assessment |
legal personality |
any entity that has the ability to conclude and negotiate international agreements in accordance with its external commitments; become a member of international organizations; join international conventions, such as the European Convention on Human Rights, stipulated in Article 6(2) of the Treaty on European Union
|
Invasive alien species assessment |
legal pluralism |
Legal pluralism is a sensitizing concept for situations in which people draw upon several legal systems, irrespective of their status within the state legal system.
|
Sustainable use assessment |
level of resolution |
Degree of detail captured in an analysis. A high level of resolution implies a highly detailed analysis, usually associated with finer spatial and temporal scales. A low level of resolution implies a less detailed analysis, usually associated with coarser spatial and temporal scales.
|
Asia-Pacific assessment |
life frames of nature’s values |
Frames that illustrate the in which people conceptualise how nature matters. Life frames mediate between ways of being/living and the prioritization of different sets of broad and specific values. The four archetypes of living from, living in, living with and living as nature are not mutually exclusive. They offer a range of sources-of-concern for nature that can overlap or be emphasized in diverse contexts (section 2.2.6).
|
Values assessment |
limestone karsts |
Referred to simply as karsts are sedimentary rock outcrops that consist primarily of calcium carbonate.
|
Asia-Pacific assessment |
linguistic uncertainty |
Imprecise meaning of words, including vagueness and ambiguity.
|
Scenarios and models assessment |
livelihood diversification |
Livelihood diversification is defined as the process by which rural families construct a diverse portfolio of activities and social support capabilities in their struggle for survival and in order to improve their standards of living”.
|
Sustainable use assessment |
livelihood resilience |
The capacity of all people across generations to sustain and improve their livelihood opportunities and well-being despite environmental, economic, social and political disturbances.
|
Land degradation and restoration assessment |
livelihood security |
Adequate and sustainable access to income and resources to meet basic needs (including adequate access to food, potable water, health facilities, educational opportunities, housing, time for community participation and social integration).
|
Land degradation and restoration assessment |
living in harmony with nature |
Within the context of the IPBES Conceptual Framework - a perspective on good quality of life based on the interdependence that exists among human beings, other living species and elements of nature. It implies that we should live peacefully alongside all other organisms even though we may need to exploit other organisms to some degree.
|
Asia-Pacific assessment, Europe and Central Asia assessment, Africa assessment, Americas assessment, Sustainable use assessment, Scenarios and models assessment |
local |
adj. Referring to places, people, things or events within a short distance of an identified locality.
|
Pollination assessment |
local communities |
Local communities” refers to non-indigenous communities with historical linkages to places and livelihoods characterized by long- term relationships with the natural environment, often over generations.
|
Sustainable use assessment |
local community |
A group of individuals that interact within their immediate surroundings and/or direct mutual influences in their daily life. In this sense, a rural village, a clan in transhumance or the inhabitants of an urban neighbourhood can be considered a local community, but not all the inhabitants of a district, a city quarter or even a rural town. A local community could be permanently settled or mobile.
|
Pollination assessment |
local ecological knowledge |
Knowledge about nature, including organisms (animals and plants), ecosystems and ecological interactions, held by local people who interact with and use natural resources. This is a manifestation of indigenous local knowledge (ILK), but includes also knowledge held by those local people who may not be officially recognized as indigenous (in legal terms). Like traditional ecological knowledge, LEK can be seen as a knowledge-practice-belief complex. In other words, it is a cumulative body of knowledge, practice, and belief, evolving by adaptive processes and handed down through generations by cultural transmission (Berkes, 2012). This encompasses ways of knowing and doing, which are dynamic concepts relying on building on experience and adapting to changes, thereby imbibe a strong learning-by-doing component.
|
Sustainable use assessment |
local economies |
Local economies and subsistence economies are defined as those that are small in scale and in which the use of resources (including wild species) are limited and exclusively used to meet local needs rather than accumulated or sold for profit.
|
Sustainable use assessment |
logging |
Logging is defined as the removal of whole trees or woody parts of trees from their habitat. Logging generally results in the death of the tree, but also includes cases in which it may not, such as coppicing. Logging occurs in forests that may be classified as primary, naturally regenerating, planted, and plantation. This assessment does not address logging from plantation forests except as it has bearing on the practice in the other forest types. Harvest of non-woody parts of trees ( leaves, propagules and bark) are here defined as gathering.
|
Sustainable use assessment |
uncertainty |
Any situation in which the current state of knowledge is such that: the order or nature of things is unknown, the consequences, extent, or magnitude of circumstances, conditions, or events is unpredictable, and credible probabilities to possible outcomes cannot be assigned. Uncertainty can result from lack of information or from disagreement about what is known or even knowable. Uncertainty can be represented by quantitative measures (e.g., a range of values calculated by various models) or by qualitative statements (e.g., reflecting the judgment of a team of experts).
|
Sustainable use assessment |
uncertainty |
Any situation in which the current state of knowledge is such that (1) the order or nature of things is unknown, (2) the consequences, extent, or magnitude of circumstances, conditions, or events is unpredictable, and (3) credible probabilities to possible outcomes cannot be assigned.
|
Pollination assessment |
uncertainty |
Any situation in which the current state of knowledge is such that: 1. the order or nature of things is unknown, the consequences, extent, or magnitude of circumstances, conditions, or events is unpredictable, and 2. credible probabilities to possible outcomes cannot be assigned. 3. Uncertainty can result from lack of information or from disagreement about what is known or even knowable. Uncertainty can be represented by quantitative measures (e.g. a range of values calculated by various models) or by qualitative statements (e.g. reflecting the judgment of a team of experts).
|
Asia-Pacific assessment, Americas assessment |
uncertainty |
Any situation in which the current state of knowledge is such that: the order or nature of things is unknown, the consequences, extent, or magnitude of circumstances, conditions, or events is unpredictable, and credible probabilities to possible outcomes cannot be assigned. Uncertainty can result from lack of information or from disagreement about what is known or even knowable. Uncertainty can be represented by quantitative measures (e.g. a range of values calculated by various models) or by qualitative statements (e.g. reflecting the judgment of a team of experts).
|
Africa assessment |
uncertainty |
see linguistic uncertainty, decision uncertainty, stochastic uncertainty, and scientific uncertainty.
|
Scenarios and models assessment |
uncertainty |
Any situation in which the current state of knowledge is such that: (i). the order or nature of things is unknown; (ii). the consequences, extent, or magnitude of circumstances, conditions, or events is unpredictable; and (iii). credible probabilities to possible outcomes cannot be assigned. Uncertainty can result from lack of information or from disagreement about what is known or even knowable. Uncertainty can be represented by quantitative measures (e.g. a range of values calculated by various models) or by qualitative statements (e.g. reflecting the judgment of a team of experts).
|
Land degradation and restoration assessment |
units of analysis |
The IPBES Units of Analysis result from subdividing the Earth’s surface into units solely for the purposes of analysis. The following have been identified as IPBES units of analysis globally: Terrestrial: Tropical and subtropical dry and humid forests Temperate and boreal forests and woodlands Mediterranean forests, woodlands and scrub Tundra and High Mountain habitats Tropical and subtropical savannas and grasslands Temperate Grasslands Deserts and xeric shrublands Wetlands - peatlands, mires, bogs Urban/Semi-urban Cultivated areas (incl. cropping, intensive livestock farming etc.) Aquatic, including both marine and freshwater: Cryosphere Aquaculture areas Inland surface waters and water bodies/freshwater Shelf ecosystems (neritic and intertidal/littoral zone) Open ocean pelagic systems (euphotic zone) Deep-Sea Coastal areas intensively used for multiple purposes by humans These IPBES terrestrial and aquatic units of analysis serve as a framework for comparison within and across assessments and represent a pragmatic solution. The IPBES terrestrial and aquatic units of analysis are not intended to be prescriptive for other purposes than those of IPBES assessments. They are likely to evolve as the work of IPBES develops.
|
Sustainable use assessment |
units of analysis |
The IPBES Units of Analysis result from subdividing the Earth's surface into units solely for the purposes of analysis. The following have been identified as IPBES units of analysis globally: Terrestrial: Tropical and subtropical dry and humid forests, Temperate and boreal forests and woodlands, Mediterranean forests, woodlands and scrub, Tundra and High Mountain habitats, Tropical and subtropical savannas and grasslands, Temperate Grasslands, Deserts and xeric shrublands, Wetlands - peatlands, mires, bogs, Urban/Semi-urban, Cultivated areas (incl. cropping, intensive livestock farming etc.).; Aquatic, including both marine and freshwater: Cryosphere, Aquaculture areas, Inland surface waters and water bodies/ freshwater, Shelf ecosystems (neritic and intertidal/ littoral zone), Open ocean pelagic systems (euphotic zone), Deep-Sea, Coastal areas intensively used for multiple purposes by humans.These IPBES terrestrial and aquatic units of analysis serve as a framework for comparison within and across assessments and represent a pragmatic solution. The IPBES terrestrial and aquatic units of analysis are not intended to be prescriptive for other purposes than those of IPBES assessments. They are likely to evolve as the work of IPBES develops.
|
Global assessment (1st work programme), Americas assessment |
units of analysis |
The IPBES Units of Analysis result from subdividing the Earth's surface into units solely for the purposes of analysis. The following have been identified: IPBES units of analysis (terrestrial): Tropical and subtropical dry and humid forests; Temperate and boreal forests and woodlands; Mediterranean forests, woodlands and scrub; Tundra and High Mountain habitats; Tropical and subtropical savannas and grasslands; Temperate Grasslands; Deserts and xeric shrublands; Wetlands - peatlands, mires, bogs; Urban/Semi-urban; Cultivated areas (incl. cropping, intensive livestock farming etc.).; IPBES units of analysis (aquatic, including both marine and freshwater units):; Cryosphere; Aquaculture areas; Inland surface waters and water bodies/ freshwater; Shelf ecosystems (neritic and intertidal/ littoral zone); Open ocean pelagic systems (euphotic zone); Deep-Sea; Coastal areas intensively used for multiple purposes by humans.; These IPBES terrestrial and aquatic units of analysis serve as a framework for comparison within and across assessments and represent a pragmatic solution, which may evolve as the work of IPBES develops. The IPBES terrestrial and aquatic units of analysis serve the purposes of IPBES, and are not intended to be prescriptive for other purposes.
|
Global assessment (1st work programme), Asia-Pacific assessment |
units of analysis |
Units of analysis result from subdividing the Earth's surface into units solely for the purposes of analysis. The terrestrial and aquatic units of analysis serve as a framework for comparison within and across IPBES assessments and represent a pragmatic solution. The terrestrial and aquatic units of analysis used by IPBES are not intended to be prescriptive for purposes other than those of IPBES assessments. They are likely to evolve as the work of IPBES develops.
|
Europe and Central Asia assessment |
units of analysis |
The IPBES Units of Analysis result from subdividing the Earth's surface into units solely for the purposes of analysis. The following have been identified: IPBES units of analysis (terrestrial): Tropical and subtropical dry and humid forests, Temperate and boreal forests and woodlands, Mediterranean forests, woodlands and scrub, Tundra and High Mountain habitats, Tropical and subtropical savannas and grasslands, Temperate Grasslands, Deserts and xeric shrublands, Wetlands - peatlands, mires, bogs, Urban/Semi-urban, Cultivated areas (incl. cropping, intensive livestock farming etc.).; IPBES units of analysis (aquatic, including both marine and freshwater units): Cryosphere, Aquaculture areas, Inland surface waters and water bodies/ freshwater, Shelf ecosystems (neritic and intertidal/ littoral zone), Open ocean pelagic systems (euphotic zone), Deep-Sea, Coastal areas intensively used for multiple purposes by humans. These IPBES terrestrial and aquatic units of analysis serve as a framework for comparison within and across assessments and represent a pragmatic solution, which may evolve as the work of IPBES develops. The IPBES terrestrial and aquatic units of analysis serve the purposes of IPBES, and are not intended to be prescriptive for other purposes.
|
Africa assessment |
units of analysis |
The IPBES Units of Analysis result from subdividing the Earth?s surface into units solely for the purposes of analysis. The following have been identified as IPBES units of analysis globally:Terrestrial:Tropical and subtropical dry and humid forestsTem.
|
Global assessment (1st work programme) |
unpredictability |
Something difficult or impossible to foretell or foresee.
|
Scenarios and models assessment |