Proportion of the rural population who live within 2 km of an all-season road, total rural population, total rural area, etc., 2023, in support of the Sustainable Development Goals - Indicator 9.1.1.
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The Rural Access Index (RAI) measures the proportion of the rural population who live within 2 km of an all-season road. It is included in the Sustainable Development Goals as indicator 9.1.1., providing a way of measuring progress towards Goal 9 and Target 9.1. Originally developed by the World Bank in 2006, the RAI is among the most important global development indicators in the transport sector, providing a strong, clearly understandable and conceptually consistent indicator across countries. Although the underlying methodology has been recently updated to leverage additional sources of data, the RAI remains the most widely accepted metric for tracking access to transport in rural areas.
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The Rural Access Index (RAI) is a measure of access, developed by the World Bank in 2006. It was adopted as Sustainable Development Goal (SDG) indicator 9.1.1 in 2015, to measure the accessibility of rural populations. It is currently the only indicator for the SDGs that directly measures rural access.The RAI measures the proportion of the rural population that lives within 2 km of an all-season road. An all-season road is one that is motorable all year, but may be temporarily unavailable during inclement weather (Roberts, Shyam, & Rastogi, 2006). This dataset implements and expands on the most recent official methodology put forward by the World Bank, ReCAP's 2019 RAI Supplemental Guidelines. This is, to date, the only publicly available application of this method at a global scale.MethodologyReCAP's methodology provided new insight on what makes a road all-season and how this data should be handled: instead of removing unpaved roads from the network, the ones that are classified as unpaved are to be intersected with topographic and climatic conditions and, whenever there’s an overlap with excess precipitation and slope, a multiplying factor ranging from 0% to 100% is applied to the population that would access to that road. This present dataset developed by SDSN's SDG Transformation Centre proposes that authorities ability to maintain and remediate road conditions also be taken into account.Data sourcesThe indicator relies on four major items of geospatial data: land cover (rural or urban), population distribution, road network extent and the “all-season” status of those roads.Land cover data (urban/rural distinction)Since the indicator measures the acess rural populations, it's necessary to define what is and what isn't rural. This dataset uses the DegUrba Methodology, proposed by the United Nations Expert Group on Statistical Methodology for Delineating Cities and Rural Areas (United Nations Expert Group, 2019). This approach has been developed by the European Commission Global Human Settlement Layer (GHSL-SMOD) project, and is designed to instil some consistency into the definitions based on population density on a 1-km grid, but adjusted for local situations.Population distributionThe source for population distribution data is WorldPop. This uses national census data, projections and other ancillary data from countries to produce aggregated, 100 m2 population data. Road extentTwo widely recognized road datasets are used: the real-time updated crowd-sourced OpenStreetMap (OSM) or the GLOBIO’s 2018 GRIP database, which draws data from official national sources. The reasons for picking the latter are mostly related to its ability to provide information on the surface (pavement) of these roads, to the detriment of the timeliness of the data, which is restrained to the year 2018. Additionally, data from Microsoft Bing's recent Road Detection project is used to ensure completeness. This dataset is completely derived from machine learning methods applied over satellite imagery, and detected 1,165 km of roads missing from OSM.Roads’ all-season statusThe World Bank's original 2006 methodology defines the term all-season as “… a road that is motorable all year round by the prevailing means of rural transport, allowing for occasional interruptions of short duration”. ReCAP's 2019 methodology makes a case for passability equating to the all-season status of a road, along with the assumption that typically the wet season is when roads become impassable, especially so in steep roads that are more exposed to landslides.This dataset follows the ReCAP methodology by creating an passability index. The proposed use of passability factors relies on the following three aspects:• Surface type. Many rural roads in LICs (and even in large high-income countries including the USA and Australia) are unpaved. As mentioned before, unpaved roads deteriorate rapidly and in a different way to paved roads. They are very susceptible to water ingress to the surface, which softens the materials and makes them very vulnerable to the action of traffic. So, when a road surface becomes saturated and is subject to traffic, the deterioration is accelerated. • Climate. Precipitation has a significant effect on the condition of a road, especially on unpaved roads, which predominate in LICs and provide much of the extended connectivity to rural and poor areas. As mentioned above, the rainfall on a road is a significant factor in its deterioration, but the extent depends on the type of rainfall in terms of duration and intensity, and how well the roadside drainage copes with this. While ReCAP suggested the use of general climate zones, we argue that better spatial and temporal resolutions can be acquired through the Copernicus Programme precipitation data, which is made available freely at ~30km pixel size for each month of the year.• Terrain. The gradient and altitude of roads also has an effect on their accessibility. Steep roads become impassable more easily due to the potential for scour during heavy rainfall, and also due to slipperiness as a result of the road surface materials used. Here this is drawn from slope calculated from SRTM Digital Terrain data.• Road maintenance. The ability of local authorities to remediate damaged caused by precipitation and landslides is proposed as a correcting factor to the previous ones. Ideally this would be measured by the % of GDP invested in road construction and maintenance, but this isn't available for all countries. For this reason, GDP per capita is adopted as a proxy instead. The data range is normalized in such a way that a road maxed out in terms of precipitation and slope (accessibility score of 0.25) in a country at the top of the GDP per capita range is brought back at to the higher end of the accessibility score (0.95), while the accessibility score of a road meeting the same passability conditions in a country which GDP per capita is towards the lower end is kept unchanged.Data processingThe roads from the three aforementioned datasets (Bing, GRIP and OSM) are merged together to them is applied a 2km buffer. The populations falling exclusively on unpaved road buffers are multiplied by the resulting passability index, which is defined as the normalized sum of the aforementioned components, ranging from 0.25 to. 0.9, with 0.95 meaning 95% probability that the road is all-season. The index applied to the population data, so, when calculated, the RAI includes the probability that the roads which people are using in each area will be all-season or not. For example, an unpaved road in a flat area with low rainfall would have an accessibility factor of 0.95, as this road is designed to be accessible all year round and the environmental effects on its impassability are minimal.The code for generating this dataset is available on Github at: https://github.com/sdsna/rai
The data here is for the underlying indicators that feed into the Welsh Index of Multiple Deprivation (WIMD). WIMD is the Welsh Government’s official measure of relative deprivation for small areas in Wales. It is designed to identify small areas where there are the highest concentrations of several different types of deprivation. The full index is only updated every 4 to 5 years but many of the indicators are updated in the interim period and some are updated annually. All indicators are available down to Lower Super Output Area level. This is a geography that is built from census data – it aims to outline small areas with a population between 1,000 and 3,000 people.
Reporting of Aggregate Case and Death Count data was discontinued on May 11, 2023, with the expiration of the COVID-19 public health emergency declaration. Although these data will continue to be publicly available, this dataset will no longer be updated.
The surveillance case definition for COVID-19, a nationally notifiable disease, was first described in a position statement from the Council for State and Territorial Epidemiologists, which was later revised. However, there is some variation in how jurisdictions implemented these case definitions. More information on how CDC collects COVID-19 case surveillance data can be found at FAQ: COVID-19 Data and Surveillance.
Aggregate Data Collection Process Since the beginning of the COVID-19 pandemic, data were reported from state and local health departments through a robust process with the following steps:
This process was collaborative, with CDC and jurisdictions working together to ensure the accuracy of COVID-19 case and death numbers. County counts provided the most up-to-date numbers on cases and deaths by report date. Throughout data collection, CDC retrospectively updated counts to correct known data quality issues.
Description This archived public use dataset focuses on the cumulative and weekly case and death rates per 100,000 persons within various sociodemographic factors across all states and their counties. All resulting data are expressed as rates calculated as the number of cases or deaths per 100,000 persons in counties meeting various classification criteria using the US Census Bureau Population Estimates Program (2019 Vintage).
Each county within jurisdictions is classified into multiple categories for each factor. All rates in this dataset are based on classification of counties by the characteristics of their population, not individual-level factors. This applies to each of the available factors observed in this dataset. Specific factors and their corresponding categories are detailed below.
Population-level factors Each unique population factor is detailed below. Please note that the “Classification” column describes each of the 12 factors in the dataset, including a data dictionary describing what each numeric digit means within each classification. The “Category” column uses numeric digits (2-6, depending on the factor) defined in the “Classification” column.
Metro vs. Non-Metro – “Metro_Rural” Metro vs. Non-Metro classification type is an aggregation of the 6 National Center for Health Statistics (NCHS) Urban-Rural classifications, where “Metro” counties include Large Central Metro, Large Fringe Metro, Medium Metro, and Small Metro areas and “Non-Metro” counties include Micropolitan and Non-Core (Rural) areas. 1 – Metro, including “Large Central Metro, Large Fringe Metro, Medium Metro, and Small Metro” areas 2 – Non-Metro, including “Micropolitan, and Non-Core” areas
Urban/rural - “NCHS_Class” Urban/rural classification type is based on the 2013 National Center for Health Statistics Urban-Rural Classification Scheme for Counties. Levels consist of:
1 Large Central Metro
2 Large Fringe Metro
3 Medium Metro
4 Small Metro
5 Micropolitan
6 Non-Core (Rural)
American Community Survey (ACS) data were used to classify counties based on their age, race/ethnicity, household size, poverty level, and health insurance status distributions. Cut points were generated by using tertiles and categorized as High, Moderate, and Low percentages. The classification “Percent non-Hispanic, Native Hawaiian/Pacific Islander” is only available for “Hawaii” due to low numbers in this category for other available locations. This limitation also applies to other race/ethnicity categories within certain jurisdictions, where 0 counties fall into the certain category. The cut points for each ACS category are further detailed below:
Age 65 - “Age65”
1 Low (0-24.4%) 2 Moderate (>24.4%-28.6%) 3 High (>28.6%)
Non-Hispanic, Asian - “NHAA”
1 Low (<=5.7%) 2 Moderate (>5.7%-17.4%) 3 High (>17.4%)
Non-Hispanic, American Indian/Alaskan Native - “NHIA”
1 Low (<=0.7%) 2 Moderate (>0.7%-30.1%) 3 High (>30.1%)
Non-Hispanic, Black - “NHBA”
1 Low (<=2.5%) 2 Moderate (>2.5%-37%) 3 High (>37%)
Hispanic - “HISP”
1 Low (<=18.3%) 2 Moderate (>18.3%-45.5%) 3 High (>45.5%)
Population in Poverty - “Pov”
1 Low (0-12.3%) 2 Moderate (>12.3%-17.3%) 3 High (>17.3%)
Population Uninsured- “Unins”
1 Low (0-7.1%) 2 Moderate (>7.1%-11.4%) 3 High (>11.4%)
Average Household Size - “HH”
1 Low (1-2.4) 2 Moderate (>2.4-2.6) 3 High (>2.6)
Community Vulnerability Index Value - “CCVI” COVID-19 Community Vulnerability Index (CCVI) scores are from Surgo Ventures, which range from 0 to 1, were generated based on tertiles and categorized as:
1 Low Vulnerability (0.0-0.4) 2 Moderate Vulnerability (0.4-0.6) 3 High Vulnerability (0.6-1.0)
Social Vulnerability Index Value – “SVI" Social Vulnerability Index (SVI) scores (vintage 2020), which also range from 0 to 1, are from CDC/ASTDR’s Geospatial Research, Analysis & Service Program. Cut points for CCVI and SVI scores were generated based on tertiles and categorized as:
1 Low Vulnerability (0-0.333) 2 Moderate Vulnerability (0.334-0.666) 3 High Vulnerability (0.667-1)
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The average for 2023 based on 196 countries was 38.64 percent. The highest value was in Papua New Guinea: 86.28 percent and the lowest value was in Bermuda: 0 percent. The indicator is available from 1960 to 2023. Below is a chart for all countries where data are available.
In 2024, the average annual per capita disposable income of rural households in China was approximately 23,119 yuan, roughly 43 percent of the income of urban households. Although living standards in China’s rural areas have improved significantly over the past 20 years, the income gap between rural and urban households is still large. Income increase of China’s households From 2000 to 2020, disposable income per capita in China increased by around 700 percent. The fast-growing economy has inevitably led to the rapid income increase. Furthermore, inflation has been maintained at a lower rate in recent years compared to other countries. While the number of millionaires in China has increased, many of its population are still living in humble conditions. Consequently, the significant wealth gap between China’s rich and poor has become a social problem across the country. However, in recent years rural areas have been catching up and disposable income has been growing faster than in the cities. This development is also reflected in the Gini coefficient for China, which has decreased since 2008. Urbanization in China The urban population in China surpassed its rural population for the first time in 2011. In fact, the share of the population residing in urban areas is continuing to increase. This is not surprising considering remote, rural areas are among the poorest areas in China. Currently, poverty alleviation has been prioritized by the Chinese government. The measures that the government has taken are related to relocation and job placement. With the transformation and expansion of cities to accommodate the influx of city dwellers, neighboring rural areas are required for the development of infrastructure. Accordingly, land acquisition by the government has resulted in monetary gain by some rural households.
The “rurality index” represents the level of dependence, thus fragility, of a certain region to agriculture and rural means of livelihood in 2010. A population strongly dependent from agriculture is subject to suffer larger consequences from agriculture productivity drop due to climatic alteration than a population less dependent by rural livelihood means. The index results from the first cluster of the Principal Component Analysis preformed among 14 potential variables. The analysis identify four dominant variables, namely “rural population density”, “dietary supply”, “dependency ratio” and “agriculture share GDP”, assigning a weight of 0.22 to the “rural population density” and 0.26 to the other three variables. Before to perform the analysis the variable “rural population density” was log transformed to shorten the extreme variation and then with the other variables were score-standardized (converted to distribution with average of 0 and standard deviation of 1; “dietary supply” with inverse method) in order to be comparable. The 5 arc-minutes grid “rural population density” of 2000 was collected from FAO GeoNetwork, sampled at 0.5 arc-minutes and then the values were adjusted in order to have national rural population totals equal to the 2010 values reported by the World Urbanization Prospects, the 2011 Revision. The 0.5 arc-minutes grid “dependency ratio” was calculated from the 2010 age distribution population for Africa produced by Worldpop Project computing the number of people with less than 15 years old or older than 65 years old per 100 people. The values were adjusted to the country total reported by the UN Population and Demographic Office estimation (World Population Prospect - the 2012 Revision). The country based value for “agriculture share GDP” and “dietary supply” were collected from World Bank and FAO statistics. The values reported are the average of the period 2008-2012. Tabular data were linked by country to the national boundaries shapefile (FAO/GAUL) and then converted into raster format (resolution 0.5 arc-minute). Rural population, or population with large number of dependent people are more fragile (i.e. sensible) to climatic stress, due to impact on food production. Similarly, high reliance on agriculture’s contribution to national GDP, makes country more susceptible to climate risk. Finally, populations with scarce dietary supply are more sensitive to climate impact on food production, because already affected by food supply concerns. This dataset has been produced in the framework of the “Climate change predictions in Sub-Saharan Africa: impacts and adaptations (ClimAfrica)” project, Work Package 4 (WP4). More information on ClimAfrica project is provided in the Supplemental Information section of this metadata.
As of June 2018, the consumer price index (CPI) in rural Chandigarh was 142.9, meaning CPI was about 43 percent more than in 2012, while urban CPI in the union territory of Chandigarh was lower at 138.6, meaning an increase of about 38 percent compared to the year 2012.
Per capita disposable income in urban regions of China is significantly higher than in rural areas of the country. However, the ratio between them has decreased gradually since its peak in 2007, when urban per capita disposable income was 3.14 times as high as rural per capita disposable income. In 2024, the ratio dropped to 2.34.
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China Consumer Price Index (CPI): Rural data was reported at 102.100 Prev Year=100 in 2018. This records an increase from the previous number of 101.254 Prev Year=100 for 2017. China Consumer Price Index (CPI): Rural data is updated yearly, averaging 102.647 Prev Year=100 from Dec 1985 (Median) to 2018, with 34 observations. The data reached an all-time high of 123.400 Prev Year=100 in 1994 and a record low of 98.500 Prev Year=100 in 1999. China Consumer Price Index (CPI): Rural data remains active status in CEIC and is reported by National Bureau of Statistics. The data is categorized under Global Database’s China – Table CN.IA: Consumer Price Index: Rural.
Economic activity indicators showing the employment status and working patterns of people living in urban and rural areas.
These documents are part of the larger compendium publication the Statistical Digest of Rural England, a collection of rural statistics on a wide range of social and economic government policy areas. The statistics allow comparisons between the different rural and urban area classifications.
Indicators:
Data source: Office for National Statistics (ONS) Annual Business Inquiry (ABI)
Coverage: England
Rural classification used: Office for National Statistics Rural Urban Classification
Next release date: tbc
Defra statistics: rural
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Per California Water Code Section 10609.80 (a), DWR has released an update to the indicators analyzed for the rural communities water shortage vulnerability analysis and a new interactive tool to explore the data. This page remains to archive the original dataset, but for more current information, please see the following pages: - https://water.ca.gov/Programs/Water-Use-And-Efficiency/SB-552/SB-552-Tool - https://data.cnra.ca.gov/dataset/water-shortage-vulnerability-technical-methods - https://data.cnra.ca.gov/dataset/i07-water-shortage-vulnerability-sections - https://data.cnra.ca.gov/dataset/i07-water-shortage-social-vulnerability-blockgroup This dataset is made publicly available pursuant to California Water Code Section 10609.42 which directs the California Department of Water Resources to identify small water suppliers and rural communities that may be at risk of drought and water shortage vulnerability and propose to the Governor and Legislature recommendations and information in support of improving the drought preparedness of small water suppliers and rural communities. As of March 2021, two datasets are offered here for download. The background information, results synthesis, methods and all reports submitted to the legislature are available here: https://water.ca.gov/Programs/Water-Use-And-Efficiency/2018-Water-Conservation-Legislation/County-Drought-Planning Two online interactive dashboards are available here to explore the datasets and findings. https://dwr.maps.arcgis.com/apps/MapSeries/index.html?appid=3353b370f7844f468ca16b8316fa3c7b The following datasets are offered here for download and for those who want to explore the data in tabular format. (1) Small Water Suppliers: In total, 2,419 small water suppliers were examined for their relative risk of drought and water shortage. Of these, 2,244 are community water systems. The remaining 175 systems analyzed are small non-community non-transient water systems that serve schools for which there is available spatial information. This dataset contains the final risk score and individual risk factors for each supplier examined. Spatial boundaries of water suppliers' service areas were used to calculate the extent and severity of each suppliers' exposure to projected climate changes (temperature, wildfire, and sea level rise) and to current environmental conditions and events. The boundaries used to represent service areas are available for download from the California Drinking Water System Area Boundaries, located on the California State Geoportal, which is available online for download at https://gispublic.waterboards.ca.gov/portal/home/item.html?id=fbba842bf134497c9d611ad506ec48cc (2) Rural Communities: In total 4,987 communities, represented by US Census Block Groups, were analyzed for their relative risk of drought and water shortage. Communities with a record of one or more domestic well installed within the past 50 years are included in the analysis. Each community examined received a numeric risk score, which is derived from a set of indicators developed from a stakeholder process. Indicators used to estimate risk represented three key components: (1) the exposure of suppliers and communities to hazardous conditions and events, (2) the physical and social vulnerability of communities to the exposure, and (3) recent history of shortage and drought impacts. The unit of analysis for the rural communities, also referred to as "self-supplied communities" is U.S. Census Block Groups (ACS 2012-2016 Tiger Shapefile). The Census Block Groups do not necessarily represent socially-defined communities, but they do cover areas where population resides. Using this spatial unit for this analysis allows us to access demographic information that is otherwise not available in small geographic units.
This data set depicts the distribution of marginal areas by administrative zones in Santiago, Cape Verde, according to a Marginality Index methodology. The Marginality Index measures the incidence of food insecurity and poverty (FIP) among the households living in each area. The index is created as a function of the most relevant variables of the year 2000 Demographic Census, using the principal components methodology. Areas with an index score above a selected threshold level have been classified as vulnerable. The boundaries of administrative zones were digitized from scanned and rectified topographic maps (Carta Militar de Portugal, Ilha de Santiago 1969).
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Rural Tourism Accommodation Price Index: Rural Tourism Accommodation Price Index interannual variation rates and indices by Autonomous Communities. Monthly. Autonomous Communities and Cities.
In September 2021, the consumer sentiment index in rural India stood at 62. Since the low of around 45 in April and July 2020, the index has just slightly increased by around 15 index points up to September 2021. Therefore, the propensity for consumption in rural India has hardly recovered from the time before the COVID-19 pandemic. Compared to the urban consumer sentiment index the rural optimism to consumption witnessed an even lower decrease, but started recovering earlier.
More information about the Welsh Index of Multiple Deprivation, its indicators and domains, and its background can be found via the link below.
The 2011 Rural Urban Classification defines areas as rural if they fall outside of areas forming settlements with populations of at least 10,000.
When data are not available at a small enough geographical scale, it may be possible to apply the Local Authority Rural Urban Classification. This classification categorises local authority districts and unitary authorities on a six point scale from rural to urban. Local Authority Districts are categorised as rural or urban based on the share of their resident population that live in rural areas.
The number of Local Authorities that are now classed as rural has reduced compared with the 2001 classification. When applying the classification for statistical purposes it is important to note that a Local Authority that is classed as urban will contain rural areas and vice versa.
Interim results identifying rural hub towns to be used in the 2011 Local Authority Classification was published separately in May 2014.
Defra statistics: rural
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China Consumer Price Index (CPI): Rural: MP: HC: Health Care Appliance & Article data was reported at 104.239 Prev Year=100 in 2015. This records an increase from the previous number of 103.123 Prev Year=100 for 2014. China Consumer Price Index (CPI): Rural: MP: HC: Health Care Appliance & Article data is updated yearly, averaging 101.300 Prev Year=100 from Dec 2001 (Median) to 2015, with 15 observations. The data reached an all-time high of 104.239 Prev Year=100 in 2015 and a record low of 96.900 Prev Year=100 in 2004. China Consumer Price Index (CPI): Rural: MP: HC: Health Care Appliance & Article data remains active status in CEIC and is reported by National Bureau of Statistics. The data is categorized under China Premium Database’s Inflation – Table CN.IA: Consumer Price Index: Rural.
Geographic proximity to service centres and population centres is an important determinant of socio-economic and health outcomes. Consequently, it is a relevant dimension in the analysis and delivery of policies and programs. To measure this dimension, Statistics Canada developed an Index of Remoteness of communities. For each populated community (census subdivision), the index is determined by its distance to all the population centres defined by Statistics Canada in a given travel radius, as well as their population size.
Proportion of the rural population who live within 2 km of an all-season road, total rural population, total rural area, etc., 2023, in support of the Sustainable Development Goals - Indicator 9.1.1.