diff --git a/knit_it.sh b/knit_it_html.sh similarity index 100% rename from knit_it.sh rename to knit_it_html.sh diff --git a/knit_it_pdf.sh b/knit_it_pdf.sh new file mode 100644 index 0000000..e13b793 --- /dev/null +++ b/knit_it_pdf.sh @@ -0,0 +1 @@ +Rscript -e 'library(rmarkdown); rmarkdown::render("./mapping_draft.Rmd", "pdf_document")' \ No newline at end of file diff --git a/mapping_draft.Rmd b/mapping_draft.Rmd index 96c6aa9..36363a2 100644 --- a/mapping_draft.Rmd +++ b/mapping_draft.Rmd @@ -546,46 +546,46 @@ ggplot() + ```{r create_cartograms, fig.width=4, fig.show="hold", fig.cap="Figure 4"} -# todo: plot as animated chorogram: -# https://www.r-graph-gallery.com/331-basic-cartogram/ -# see here for example using sf: https://github.com/dreamRs/topogRam +# # todo: plot as animated chorogram: +# # https://www.r-graph-gallery.com/331-basic-cartogram/ +# # see here for example using sf: https://github.com/dreamRs/topogRam -library(cartogram) +# library(cartogram) -# construct a cartogram using the population in 2005 -afr_cartogram <- cartogram(afr, "POP2005", itermax=5) +# # construct a cartogram using the population in 2005 +# afr_cartogram <- cartogram(afr, "POP2005", itermax=5) -# It is a new geospatial object: we can use all the usual techniques on it! Let's start with a basic ggplot2 chloropleth map: -library(tidyverse) -library(broom) -spdf_fortified <- tidy(afr_cartogram) -spdf_fortified = spdf_fortified %>% left_join(. , afr_cartogram@data, by=c("id"="ISO3")) -ggplot() + - geom_polygon(data = spdf_fortified, aes(fill = POP2005, x = long, y = lat, group = group) , size=0, alpha=0.9) + - coord_map() + - theme_void() +# # It is a new geospatial object: we can use all the usual techniques on it! Let's start with a basic ggplot2 chloropleth map: +# library(tidyverse) +# library(broom) +# spdf_fortified <- tidy(afr_cartogram) +# spdf_fortified = spdf_fortified %>% left_join(. , afr_cartogram@data, by=c("id"="ISO3")) +# ggplot() + +# geom_polygon(data = spdf_fortified, aes(fill = POP2005, x = long, y = lat, group = group) , size=0, alpha=0.9) + +# coord_map() + +# theme_void() - # As seen before, we can do better with a bit of customization -library(viridis) -ggplot() + - geom_polygon(data = spdf_fortified, aes(fill = POP2005/1000000, x = long, y = lat, group = group) , size=0, alpha=0.9) + - theme_void() + - scale_fill_viridis(name="Population (M)", breaks=c(1,50,100, 140), guide = guide_legend( keyheight = unit(3, units = "mm"), keywidth=unit(12, units = "mm"), label.position = "bottom", title.position = 'top', nrow=1)) + - labs( title = "Africa 2005 Population" ) + - ylim(-35,35) + - theme( - text = element_text(color = "#22211d"), - plot.background = element_rect(fill = "#f5f5f4", color = NA), - panel.background = element_rect(fill = "#f5f5f4", color = NA), - legend.background = element_rect(fill = "#f5f5f4", color = NA), - plot.title = element_text(size= 22, hjust=0.5, color = "#4e4d47", margin = margin(b = -0.1, t = 0.4, l = 2, unit = "cm")), - legend.position = c(0.2, 0.26) - ) + - coord_map() +# # As seen before, we can do better with a bit of customization +# library(viridis) +# ggplot() + +# geom_polygon(data = spdf_fortified, aes(fill = POP2005/1000000, x = long, y = lat, group = group) , size=0, alpha=0.9) + +# theme_void() + +# scale_fill_viridis(name="Population (M)", breaks=c(1,50,100, 140), guide = guide_legend( keyheight = unit(3, units = "mm"), keywidth=unit(12, units = "mm"), label.position = "bottom", title.position = 'top', nrow=1)) + +# labs( title = "Africa 2005 Population" ) + +# ylim(-35,35) + +# theme( +# text = element_text(color = "#22211d"), +# plot.background = element_rect(fill = "#f5f5f4", color = NA), +# panel.background = element_rect(fill = "#f5f5f4", color = NA), +# legend.background = element_rect(fill = "#f5f5f4", color = NA), +# plot.title = element_text(size= 22, hjust=0.5, color = "#4e4d47", margin = margin(b = -0.1, t = 0.4, l = 2, unit = "cm")), +# legend.position = c(0.2, 0.26) +# ) + +# coord_map() -# Add animated version: +# # Add animated version: -https://github.com/thomasp85/gganimate +# https://github.com/thomasp85/gganimate ``` diff --git a/mapping_draft.tex b/mapping_draft.tex new file mode 100644 index 0000000..051762c --- /dev/null +++ b/mapping_draft.tex @@ -0,0 +1,816 @@ +\documentclass[11pt,]{article} +\usepackage{lmodern} +\usepackage{amssymb,amsmath} +\usepackage{ifxetex,ifluatex} +\usepackage{fixltx2e} % provides \textsubscript +\ifnum 0\ifxetex 1\fi\ifluatex 1\fi=0 % if pdftex + \usepackage[T1]{fontenc} + \usepackage[utf8]{inputenc} +\else % if luatex or xelatex + \ifxetex + \usepackage{mathspec} + \else + \usepackage{fontspec} + \fi + \defaultfontfeatures{Ligatures=TeX,Scale=MatchLowercase} +\fi +% use upquote if available, for straight quotes in verbatim environments +\IfFileExists{upquote.sty}{\usepackage{upquote}}{} +% use microtype if available +\IfFileExists{microtype.sty}{% +\usepackage{microtype} +\UseMicrotypeSet[protrusion]{basicmath} % disable protrusion for tt fonts +}{} +\usepackage[margin=1in]{geometry} +\usepackage{hyperref} +\PassOptionsToPackage{usenames,dvipsnames}{color} % color is loaded by hyperref +\hypersetup{unicode=true, + pdftitle={Mapping Environmental Action in Scotland}, + pdfauthor={Jeremy H. Kidwell}, + colorlinks=true, + linkcolor=black, + citecolor=Blue, + urlcolor=Blue, + breaklinks=true} +\urlstyle{same} % don't use monospace font for urls +\usepackage{natbib} +\bibliographystyle{plainnat} +\usepackage{longtable,booktabs} +\usepackage{graphicx,grffile} +\makeatletter +\def\maxwidth{\ifdim\Gin@nat@width>\linewidth\linewidth\else\Gin@nat@width\fi} +\def\maxheight{\ifdim\Gin@nat@height>\textheight\textheight\else\Gin@nat@height\fi} +\makeatother +% Scale images if necessary, so that they will not overflow the page +% margins by default, and it is still possible to overwrite the defaults +% using explicit options in \includegraphics[width, height, ...]{} +\setkeys{Gin}{width=\maxwidth,height=\maxheight,keepaspectratio} +\IfFileExists{parskip.sty}{% +\usepackage{parskip} +}{% else +\setlength{\parindent}{0pt} +\setlength{\parskip}{6pt plus 2pt minus 1pt} +} +\setlength{\emergencystretch}{3em} % prevent overfull lines +\providecommand{\tightlist}{% + \setlength{\itemsep}{0pt}\setlength{\parskip}{0pt}} +\setcounter{secnumdepth}{5} +% Redefines (sub)paragraphs to behave more like sections +\ifx\paragraph\undefined\else +\let\oldparagraph\paragraph +\renewcommand{\paragraph}[1]{\oldparagraph{#1}\mbox{}} +\fi +\ifx\subparagraph\undefined\else +\let\oldsubparagraph\subparagraph +\renewcommand{\subparagraph}[1]{\oldsubparagraph{#1}\mbox{}} +\fi + +%%% Use protect on footnotes to avoid problems with footnotes in titles +\let\rmarkdownfootnote\footnote% +\def\footnote{\protect\rmarkdownfootnote} + +%%% Change title format to be more compact +\usepackage{titling} + +% Create subtitle command for use in maketitle +\newcommand{\subtitle}[1]{ + \posttitle{ + \begin{center}\large#1\end{center} + } +} + +\setlength{\droptitle}{-2em} + + \title{Mapping Environmental Action in Scotland} + \pretitle{\vspace{\droptitle}\centering\huge} + \posttitle{\par} + \author{\href{http://jeremykidwell.info}{Jeremy H. Kidwell}} + \preauthor{\centering\large\emph} + \postauthor{\par} + \predate{\centering\large\emph} + \postdate{\par} + \date{2019-02-01} + + +\begin{document} +\maketitle + +\hypertarget{introduction15541312}{% +\section[Introduction]{\texorpdfstring{Introduction\footnote{This + research was jointly funded by the AHRC/ESRC under project numnbers + AH/K005456/1 and AH/P005063/1.}}{Introduction}}\label{introduction15541312}} + +Until recently, environmentalism has been treated by governments and +environmental charities as a largely secular concern. In spite of the +well-developed tradition of ``eco-theology'' which began in earnest in +the UK in the mid-twentieth century (and which has many precursors in +previous centuries), third-sector groups and governments, particularly +in Britain and Europe, have largely ignored religious groups as they +have gone about their business crafting agendas for behaviour change, +developing funding programmes, and developing platforms to mitigate +ecological harm, motivate consumers and create regulation regimes. That +this has changed is evidenced by the fact that several prominent +non-religious environmental groups have commissioned studies and crafted +outreach programmes to persons with a particular faith tradition or to +``spiritual communities'' including RSPB (2013) and the Sierra Club USA +(2008).\footnote{This is not to say that there have been no + collaborations before 2000, noteworthy in this respect is the WWF who + helped to found the Alliance of Religion and Conservation (ARC) in + 1985.} Further, since 2008, the Scottish Government has provided a +significant portion of funding for the ecumenical charity, +Eco-Congregation Scotland, which works to promote literacy on +environmental issues in religious communities in Scotland and helps to +certify congregations under their award programme. What is not well +known, however, even by these religious environmental groups themselves, +is whether or how their membership might be different from other +environmental groups. This study represents an attempt to illuminate +this new interest with some more concrete data about religious groups in +Scotland and how they may differ from non-religious counterparts. + +\hypertarget{eco-congregation-scotland-the-basics}{% +\section{Eco-Congregation Scotland: The +Basics}\label{eco-congregation-scotland-the-basics}} + +There are 344 eco-congregations in Scotland. By some measurements, +particularly in terms of individual sites and possibly also with regards +to volunteers, this makes Eco-Congregation Scotland one of the largest +environmental third-sector groups in Scotland.\footnote{This suggestion + should be qualified - RSPB would greatly exceed ECS both in terms of + the number of individual subscribers and budget. The RSPB trustee's + report for 2013-2014 suggests that their member base was 1,114,938 + people across Britain with a net income of £127m - the latter of which + exceeds the Church of Scotland. If we adjust this based on the + Scottish share of the population of the United Kingdom as of the 2011 + census (8.3\%) this leaves us with an income of £9.93m. The British + charity commission requires charities to self-report the number of + volunteers and staff, and from their most recent statistics we learn + that RSPB engaged with 17,600 volunteers and employed 2,110 members of + staff. Again, adjusted for population, this leaves 1,460 volunteers in + Scotland and 176 staff. However, if we measure environmental groups + based on the number of sites they maintain, RSPB has only 40 reserves + with varying levels of local community engagement. For comparison, as + of Sep 14 2015, Friends of the Earth Scotland had only 10 local groups + (concentrated mostly in large urban areas). Depending on how one + measures ``volunteerism,'' it may be possible that ECS has more + engaged volunteers in Scotland as well - if each ECS group had only 4 + ``volunteers'' then this would exceed RSPB.} + +In seeking to conduct GIS and statistical analysis of ECS, it is +important to note that there some ways in which these sites are +statistically opaque. Our research conducted through interviews at a +sampling of sites and analysis of a variety of documents suggests that +there is a high level of diversity both in terms of the number of those +participating in environmental action and the types of action underway +at specific sites. Work at a particular site can also ebb and flow over +the course of time. Of course, as research into other forms of activism +and secular environmental NGOs has shown, this is no different from any +other third sector volunteer group. Variability is a regular feature of +groups involved in activism and/or environmental concern. + +For the sake of this analysis, we took each Eco-Congregation Scotland +site to represent a point of analysis as if each specific site +represented a community group which had ``opted-in'' on environmental +concern. On this basis, in this section, in the tradition of human +geography, we ``map'' environmental action among religious communities +in Scotland a variety of ways. This is the first major geographical +analysis of this kind conducted to date in Europe. We measure the +frequency and location of ECS sites against a variety of standard +geo-referenced statistical data sets, seeking to provide a statistical +and geographically based assessment of the participation of religious +groups in relation to the following: + +\begin{itemize} +\tightlist +\item + Location within Scotland +\item + Religious affiliation +\item + Relation to the Scottish Index of Multiple Deprivation (SIMD) +\item + Relation to the 8-Fold Scottish Government Urban-Rural Scale +\item + Proximity to ``wilderness'' (based on several different designations) +\end{itemize} + +For the sake of comparison, we also measured the geographical footprint +of two other forms of community group in Scotland, (1) Transition Towns +(taking into account their recent merge with Scotland Communities +Climate Action Network) and (2) member groups of the Development Trust +Association Scotland (``DTAS''). These two groups provide a helpful +basis for comparison as they are not centralised and thus have a +significant geographical dispersion across Scotland. They also provide a +useful comparison as transition is a (mostly) non-religious +environmental movement, and community development trusts are not +explicitly linked to environmental conservation (though this is often +part of their remit), so we have a non-religious point of comparison in +Transition and a non-environmental point of comparison with DTAS + +\hypertarget{technical-background}{% +\section{Technical Background}\label{technical-background}} + +Analysis was conducted using QGIS 2.8 and R 3.5.2, and data-sets were +generated in CSV format.\footnote{Kidwell, Jeremy. (2016). + Eco-Congregation Scotland, 2014-2016. University of Edinburgh. + \url{http://dx.doi.org/10.7488/ds/1357}.} To begin with, I assembled a +data set consisting of x and y coordinates for each congregation in +Scotland and collated this against a variety of other specific data. +Coordinates were checked by matching UK postcodes of individual +congregations against geo-referencing data in the Office for National +Statistics postcode database. In certain instances a single +``congregation'' is actually a series of sites which have joined +together under one administrative unit. In these cases, each site was +treated as a separate data point if worship was held at that site at +least once a month, but all joined sites shared a single unique +identifier. As noted above, two other datasets were generated for the +sake of comparative analysis.\footnote{For further detail on Dataset + generation, see Kidwell, Forthcoming, 2018.} These included one +similar Environmental Non-Governmental Organisation (ENGO) in Scotland +(1) Transition Scotland (which includes Scotland Communities Climate +Action Network);\footnote{My dataset on transition towns will be made + available later in 2016. Initial data was aquired from the Transition + Scotland website + \url{http://www.transitionscotland.org/transition-in-scotland} on + December 10, 2014. We are currently in the process of collaboratively + generating a more up-to-date dataset which will reflect their + collaboration with SCCAN.} and another community-based NGO, Scottish +Community Development Trusts.\footnote{Data was acquired from the + Development Trusts Association website, + \url{http://www.dtascot.org.uk}, accessed on 20 July 2015. As above, + we are currently in the process of active collaboration with + volunteers from the DTAS to co-generate a new dataset.} As this report +will detail, these three overlap in certain instances both literally and +in terms of their aims, but each also has a separate identity and +footprint in Scotland. Finally, in order to normalise data, we utilised +the PointX POI dataset which maintains a complete database of Places of +Worship in Scotland.\footnote{PointX data for ``Landscape Data'' items + is sourced from Ordnance Survey Land-Line and MasterMap(R) and the + data points are augmented with additional information provided through + research by PointX staff, and data aquired from unidentified ``local + data companie(s)'' and the ``118 Information'' database (see: + \url{http://www.118information.co.uk}). This data is under license and + cannot be made available for use. It is important to note that I + became aware of inaccuracies in this dataset over the course of use + and subsequently generated my own dataset in collaboration with + churches in Scotland. This will be made available later in 2016. I am + in active conversation with OS about improving the quality of the data + in PointX regarding places of worship.} + +\hypertarget{background-and-history-of-eco-congregation-scotland}{% +\section{Background and History of Eco-Congregation +Scotland}\label{background-and-history-of-eco-congregation-scotland}} + +Eco-Congregation Scotland began a year before the official launch of +Eco-Congregation England and Wales, in 1999, as part of an effort by +Kippen Environment Centre (later renamed to Forth Environment Link, or +``FEL'') a charity devoted to environmental education in central +Scotland\footnote{From \url{http://www.forthenvironmentlink.org}, + accessed 12 July 2015.} to broaden the scope of its environmental +outreach to churches in central Scotland.\footnote{Interview with + Margaret Warnock, 29 Aug 2014.} Initial funding was provided, through +Kippen Environment Centre by way of a ``sustainable action grant'' (with +funds drawn from a government landfill tax) through a government +programme called Keep Scotland Beautiful (the Scottish cousin of Keep +Britain Tidy). After this initial pilot project concluded, the Church of +Scotland provided additional funding for the project in the form of +staff time and office space. Additional funding a few years later from +the Scottish Government helped subsidise the position of a business +manager, and in 2011 the United Reformed Church contributed additional +funding which subsidised the position of a full-time environmental +chaplain for a 5-year term, bringing the total staff to five. + +The programme launched officially in 2001 at Dunblane Cathedral in +Stirling and by 2005 the project had 89 congregations registered to be a +part of the programme and 25 which had completed the curriculum +successfully and received an Eco-Congregation award. By 2011, the number +of registrations had tripled to 269 and the number of awarded +congregations had quadrupled to +\texttt{sum(ecs\$award1\ \textless{}\ "01/01/2012",\ na.rm=TRUE)}. This +process of taking registrations and using a tiered award or recognition +scheme is common to many voluntary organisations. The ECS curriculum was +developed in part by consulting the Eco-Congregation England and Wales +materials which had been released just a year earlier in 1999, though it +has been subsequently revised, particularly with a major redesign in +2010. In the USA, a number of similar groups take a similar approach +including Earth Ministry (earthministry.org) and Green Faith +(greenfaith.org). + +In the case of Eco-Congregation Scotland, congregations are invited to +begin by ``registering'' their interest in the programme by completing a +basic one-sided form. The next step requires the completion of an award +application, which includes a facilitated curriculum called a ``church +check-up'' and after an application is submitted, the site is visited +and assessed by third-party volunteer assessors. Sites are invited to +complete additional applications for further awards which are +incremental (as is the application process). Transition communities, at +least in the period reflected on their map, go through a similar process +(though this does not involve the use of a supplied curriculum) by which +they are marked first as ``interested,'' become ``active'' and then gain +``official'' status.\footnote{From the Transition map key, ``Green pins + are `official' groups Blue pins are active communities who are + connected to the Scottish Transition network Yellow pins show interest + in this area''} + +\hypertarget{representation-by-regional-authorities-council-areas}{% +\section{Representation by Regional Authorities (Council +Areas)}\label{representation-by-regional-authorities-council-areas}} + +Perhaps the first important question to ask of these groups is, where +are they? I calculated the spread of eco-congregations and transition +groups across each of the 32 council areas in Scotland. Every council +area in Scotland has at least one eco-congregation or transition group). +The most are located in , with 48, whereas the mean among all the 32 +council areas is 10.75, with a median of 8, standard deviation of +9.4698162, and interquartile range of 11.5. The following choropleth +maps show the relative concentration of eco-congregations (indicated by +yellow to red). + +(\emph{TODO: need to implement}) Though there are too few +eco-congregations and transition groups for a numerically significant +representation in any of the intermediate geographies, mapping the +concentration of sites by agricultural parishes allows for a more +granular visual and I include this for comparison sake. Note, for the +sake of a more accurate visual communication, we have also marked out +areas of Scotland that are uninhabited with hash marks on the map of +agricultural parishes. (\emph{TODO: this will be done in the final +draft, once I get my image masking fixed!}).\footnote{This was + calculated by calculating a 10m wide footprint for every postcode in + Scotland, areas which are not within 10m of a postcode (as of May + 2014) are counted as uninhabited.} + +\begin{figure} +\centering +\includegraphics{figures/plot_admin_ecs_choropleth-1.pdf} +\caption{Figure 1} +\end{figure} + +\includegraphics{figures/plot_admin_ecs_normed_choropleth-1.pdf} +\includegraphics{figures/plot_admin_ecs_normed_choropleth-2.pdf} + +Given the way population and places of worship are unevenly distributed +across Scotland it is important to represent data in terms of relative +distribution. For this study, we attempted to ``normalise'' our data in +two different ways, (1) as shown by Figure 2 above, by taking population +figures from the 2011 census (see data sheet in Appendix A) and (2) by +adjusting relative to the number of places of worship in each council +region.\footnote{See note above regarding the data used from the PointX + POI database. Note, for our research,we filtered out religious groups + not represented within the Eco-Congregation footprint. We discuss + representation by tradition and religion further below.adition and + religion further below.} The latter of these two can yield +particularly unexpected results. Thus, of the 4048 ``places of worship'' +in Scotland, the highest concentration is actually the region, with 435, +second is 329 (). Rank of Council Areas by population and number of +places of worship is also included in Appendix A. + +We can use this data to normalise our figures regarding Eco-Congregation +Scotland communities and this draws the presence in Edinburgh of ECS +communities into even sharper relief, as Edinburgh, though ranked second +in terms of population and fifth in terms of places of worship, ranks +first for the presence of all ECS congregations and awarded ECS +congregations. However, taking population as the basis for normalisation +first, we find that Edinburgh is far from the most prominent outlier. In +trying to communicate this difference for a lay-audience, we have chosen +to list this difference as a multiplier (i.e.~there are 2.x times as +many congregations as their share of population and an average figure of +congregations might allow for) as this conveys the difference in a +straight-forward way. Outliers where the disparity between their +relative share of the total ECS footprint and their relative share of +population is different by a positive ratio of more than double include +the Orkney Islands (3.7 times more eco-congregations than their expected +average share based on population), Argyll and Bute +(\texttt{admin\_lev1{[}CODE=S12000023{]}\$ecs\_pop\_factor} 4.2x), +Stirling (2.76x), and Perthshire and Kinross (2.18x). Interestingly, +there are no outliers whose relative share of the total footprint of ECS +is double or more in the negative direction (see Appendix A chart for +full numbers). + +Turning to the total of 4048 ``places of worship'' in Scotland, we find +a slightly different picture of the relative concentration of +Eco-Congregations in Scotland. In this case, the outliers are + +Whereas our initial measurements indicated a prominent lead for +Edinburgh, by normalising our data in this way we can highlight the +stronger-than-expected presence of several others that might otherwise +escape notice because they lie in a region with significantly lower +population or numerically less places of worship. Taking the PointX data +on ``places of worship'' in Scotland, we find a less dramatic picture, +but also a slightly different one. The positive outliers include East +Renfrewshire (3.4x) Edinburgh (2.9x), Stirling (2.2), West Lothian +(1.9x) and Aberdeen (1.5x). Again, negative outliers are far less +dramatic, with only Midlothian possessing a ratio of more than 100\% +negative difference from the number of ``places of worship'' at 1.5x +\emph{fewer}. + +\includegraphics{figures/create_admin_barplot-1.pdf} + +\includegraphics{figures/create_choropleth_others-1.pdf} +\includegraphics{figures/create_choropleth_others-2.pdf} +\includegraphics{figures/create_choropleth_others-3.pdf} + +We can compare the representation in these various regions against our +comparison groups to see how other community-based organisations cluster +in Scottish administrative districts. Here there are some significant +contrasts. Scottish Community Development trusts are most intensely +concentrated in the Highlands and Argyll \& Bute. But, this is +consistent with all the other categories, Eco-Congregations, Places of +Worship, and dtas are all over-represented in this area, varying only by +the degree. Edinburgh is different, here we find that Eco-Congregations +and Transition projects are over-represented, while dtass are +under-represented. Finally, the highlands are another strong contrast, +here we find a very strong over-representation by transition towns and +dtass while the representation of Eco-Congregations is relatively close +to the population share for that area. The two areas of greatest +contrast for Eco-Congregations from the other groups are unsurprising, +Edinburgh is the location of the ECS offices, while Stirling is the area +in which ECS first began (see Appendix B for full data). + +\hypertarget{christian-denominations}{% +\section{Christian Denominations}\label{christian-denominations}} + +Eco-Congregation Scotland describes itself as an ``ecumenical movement +helping local groups of Christians link environmental issues to their +faith, reduce their environmental impact and engage with their local +community.'' There are several ties to the Church of Scotland, as the +denomination provides office space to Eco-Congregation Scotland in the +Church of Scotland complex at 121 George Street in Edinburgh and +provides funding for one full-time member of staff. In spite of this, +ECS has, from the start, attempted to emphasise its ecumenical +aspirations and this is reflected in a wide variety of ways. The name +``eco-congregation'' is meant to be tradition neutral (in interviews, +staff noted how they have sought to avoid names such as ``eco-kirk'' +which would be the more obvious Presbyterian title, or ``eco-community'' +or ``eco-church'' which might indicate allegiance towards another). +Further, the group has a environmental chaplain on their staff whose +position is funded by the United Reformed Church, and other members of +staff are funded by the Scottish government, and as such, carry no +formal affiliation with a religious institution. This diversity and +ecumenicism is reflected in a membership which is, though dominated by +the Church of Scotland, nevertheless, made up of a range of Christian +traditions. + +Though these are not numerically significant, it is important to note +that some member congregations describe themselves as ecumenical +communities, and others are hybrids reflecting the merging of two +traditions. As this ecumenical/hybrid designation involves a small +number of the overall total, for the sake of this research, these have +been combined into a category called ``ecumenical.'' Further, as +research conducted by Church of Scotland statistician Fiona Tweedie has +shown, in many Scottish communities with only one church, members of +this church will specify their denominational affiliation in a variety +of ways (Roman Catholic, Quaker, Methodist, etc.) even though the church +and its minister are formally affiliated with the Church of +Scotland.\footnote{Fiona Tweedia, \emph{Ecumenical Audit: Questionnaire + Findings} (2014).} So, we should be careful not to assume that the +various denominational affiliations of eco-congregations are indicative +in an absolute way. + +A wide variety of historians and sociologists of religion have noted the +regional significance of different Christian denominations in Scotland +so we sought to assess the relative distribution and concentration of +eco-congregations by denomination. Finding comparative statistics is a +complex task, made more complicated by several factors. First, most +demographic data on religious belonging in Scotland comes in the form of +the 2011 census and as such is far more atomised than this data-set +which identifies groups at the level of ``congregations'' rather than +individuals. Equating these two is also complex, as participation by +members of congregations can be measured in a variety of ways, there are +often a small number of active participants in each eco-congregation +group, but may also be a large scale, but passive, support by the wider +community. + +So why provide this kind of data (i.e.~at the level of individual +churches) when more granular data (i.e.~at the level of individuals +persons) is available in the form of the census and related parallel +publications such as the 2008 Scottish Environmental Attitudes survey? +We believe that mapping places of worship provides a useful intermediate +level of analysis and may complement our more atomised understanding of +EA which has been assessed at the level of individual persons to date. +Because representation within some administrative areas of Scotland, can +lead to a small number of data points, we have kept analysis to a +National level and have not provided more specific administrative-area +level calculations. + +\begin{longtable}[]{@{}lr@{}} +\caption{ECS by denomination}\tabularnewline +\toprule +& x\tabularnewline +\midrule +\endfirsthead +\toprule +& x\tabularnewline +\midrule +\endhead +Baptist & 4\tabularnewline +C of S & 254\tabularnewline +C of S / URC & 3\tabularnewline +Cong & 1\tabularnewline +Ecu & 5\tabularnewline +FCS & 1\tabularnewline +Independent & 2\tabularnewline +Meth & 4\tabularnewline +Non. & 1\tabularnewline +Quaker & 1\tabularnewline +RC & 15\tabularnewline +SEC & 41\tabularnewline +Unitarian & 1\tabularnewline +URC & 11\tabularnewline +\bottomrule +\end{longtable} + +As one might expect, there is a strong representation of the Church of +Scotland, almost 74\% of eco-congregations, with this number remaining +the same when we only count awarded sites. We can confirm, on the basis +of this analysis that ECS has a disproportional representation by Church +of Scotland churches. At the 2002 church census count, it only +represented 40.20\% of Scottish churches (1666 of 4144 total churches). +Similarly, on the 2011 Scottish census, only 32.44\% of persons claimed +to be members of the Church of Scotland. We can adjust this +representation to 60\%, if one excludes the 2,445,204 persons (46\% of +the total on the census) who reported either ``no religion'' or +adherence to a religious tradition not currently represented among the +eco-congregation sites. There is a slight over-representation by the +United Reformed church, though this seems considerably more dramatic +when one takes into account the fact that this is a trebling or more of +their overall share of Scottish churches. The URC makes up only sightly +more than 1\% of church buildings in Scotland and a tiny 0.04\% of +respondents to the 2011 census. The Scottish Episcopal church hovers +right around a proportional representation within ECS. More concerning +are the significant underrepresentation by Roman Catholic churches, +Baptists, the Free Church of Scotland, and other independent churches. + +While Roman Catholic churches make up just over 10\% of the church +buildings in Scotland, less than 5\% of churches registered as +eco-congregations are RC. Even more dramatic is the quartering of +baptist churches, and the non-existent representation among the +significant group of independent churches and small denominations. These +make up nearly 25\% of all Scottish churches (over a thousand) and yet +only 4 have registered as eco-congregations. We provide several +tentative advisories in response to these under-representations in the +final section of this paper. + +\hypertarget{eco-congregations-urban-rural-and-remote}{% +\section{Eco-Congregations, Urban, Rural and +Remote}\label{eco-congregations-urban-rural-and-remote}} + +\begin{verbatim} +## OGR data source with driver: ESRI Shapefile +## Source: "/Users/jeremy/gits/mapping_environmental_action/data", layer: "SG_UrbanRural_2016" +## with 8 features +## It has 6 fields +\end{verbatim} + +Rather than bifurcate congregations into an urban/rural dichotomy, for +this study we used the Scottish Government's six-point remoteness scale +to categorise eco-congregations along a spectrum of highly populated to +remote areas. This 8-fold scale (calculated biennially) offers a more +nuanced measurement that combines measurements of remoteness and +population along the following lines: + +\begin{enumerate} +\def\labelenumi{\arabic{enumi}.} +\tightlist +\item + Large Urban Areas - Settlements of over 125,000 people. +\item + Other Urban Areas - Settlements of 10,000 to 125,000 people. +\item + Accessible Small Towns - Settlements of between 3,000 and 10,000 + people, and within a 30 minute drive time of a Settlement of 10,000 or + more. +\item + Remote Small Towns - Settlements of between 3,000 and 10,000 people, + and with a drive time between 30 and 60 minutes to a Settlement of + 10,000 or more. +\item + Very Remote Small Towns - Settlements of between 3,000 and 10,000 + people, and with a drive time of over 60 minutes to a Settlement of + 10,000 or more. +\item + Accessible Rural Areas - Areas with a population of less than 3,000 + people, and within a drive time of 30 minutes to a Settlement of + 10,000 or more. +\item + Remote Rural Areas - Areas with a population of less than 3,000 + people, and with a drive time of between 30 and 60 minutes to a + Settlement of 10,000 or more. +\item + Very Remote Rural Areas - Areas with a population of less than 3,000 + people, and with a drive time of over 60 minutes to a Settlement of + 10,000 or more. +\end{enumerate} + +The key question which this analysis seeks to answer is whether ECS, or +the other groups surveyed, are more concentrated in Urban or Rural +areas, so as is the case below with our analysis of deprivation, we are +concerned with the outer conditions, i.e.~the urban areas (items 1-2) +and remote areas (items 7-8). + +Of all the groups surveyed in this study, Eco-Congregation Scotland is +the most heavily concentrated in large urban areas (33.53\%), exceeding +by almost 50\% the rate for all places of worship (22.96\% in large +urban areas). Transition is a much more modest 20\% and development +trusts a bit lower at 15\%. It is interesting to note that the rate of +ECS concentration in these large urban areas matches the level of +overall population distribution (34.5\%). On the other end of the scale, +Eco-Congregation Scotland is the least concentrated in remote rural +areas (with 3.93\% on level 7 and 5.44\% on level 8 on the urban-rural +scale), though again, they correlate roughly to the general population +distribution (3.2\% and 2.9\% respectively). Places of worship outpace +both the population of Scotland and the footprint of Eco-Congregation +Scotland, with 14.98\% in very remote rural areas, but this is exceeded +by transition at 16.47\% and both by Scottish community development +trusts at 32.14\%. So while Eco-Congregation Scotland correlates roughly +with Scottish population distribution across the urban-rural scale, it +has a considerably more urban profile than either of the other two +groups surveyed. + +\includegraphics{figures/create_ur_barplot-1.pdf} + +\begin{figure} +\centering +\includegraphics{figures/create_urbanrural_ecs_chart_choropleth-1.pdf} +\caption{Figure 9} +\end{figure} + +\hypertarget{wealth-employment-and-literacy}{% +\section{Wealth, Employment, and +Literacy}\label{wealth-employment-and-literacy}} + +\begin{verbatim} +## OGR data source with driver: ESRI Shapefile +## Source: "/Users/jeremy/gits/mapping_environmental_action/data", layer: "sc_dz_11" +## with 6976 features +## It has 9 fields +\end{verbatim} + +\includegraphics{figures/create_simd_barplot-1.pdf} + +Another crucial point of assessment relates to the relation of +Eco-Congregation communities to the Scottish Index of Multiple +Deprivation. This instrument aggregates a large variety of factors which +can lead to deprivation including crime rates, employment levels, access +to services (implicating remoteness), and literacy. By assessing ECS, +Transition, and dtas against the deprivation scale, we can assess +whether eco-congregations fall within particular demographics and also +whether the fully aggregated SIMD measurement provides a useful point of +comparison for our purposes. The SIMD essentially divides Scotland into +6407 geographic zones and then ranks them based on their relative +deprivation. This data set can be split into any number of groups, but +for our purposes we have settled on Quintiles, splitting the SIMD data +set at every 1302 entries. We then measured where each transition group, +ECS, and dtas fell within these zones and calculated how they fell into +these five quintiles, from more to least deprived. + +The first, and most compelling finding is that, in general +Eco-Congregation Scotland and Transition Scotland are both roughly the +same and match the level of population distribution in the lowest +quintile of the general SIMD measurement. 8\% of transition groups and +eco-congregation groups which have received awards and 9\% of the +population are located within this quintile. However, taken in relation +to the distribution of places of worship in the lowest quintile, we find +that eco-congregations are located at half the rate that places of +worship are (15\%) and dtass match this much more closely at 14\%. +Turning towards the top quintile, this pattern also holds, here both +transition groups (21\%) and eco-congregations (21\% and 29\% of awarded +congregations) depart from the population distribution in this upper +quintile (which is 10\%). Again, general places of worship (at 11\%) and +DTASs (at 5\%) take the opposite direction. We can say decisively that +in communities which have been identified as good candidates for +intervention to reduce deprivation, ECS and Transition are less likely, +and they are over-represented at the areas which fall into the least +deprived quintile. + +We can find divergence between transition communities and +eco-congregation when we split out SIMD domains. In the lowest quartile, +measuring exclusively for the income domain, ECS is more represented +(11\%) - roughly the same as DTAS (12\%), and transition is less (6\%) +represented. In general (as shown on the chart in Appendix D), these +trends hold when representation of our groups are measured within other +non-remoteness domains of the SIMD. Our basic conclusion is that +transition towns are least likely to operate within the lowest quartile +of SIMD and DTASs are most likely, with ECS somewhere in the middle. +Given the general disparity against the presence of places of worship, +it seems fair to suggest that this might be an area for improvement, +perhaps even worth developing a special programme which might target +areas in SIMD quartile 1 for eco-congregation outreach. This might be +considered particularly in light of the starkest underrepresentation of +ECS and transition within the SIMD domain of education, skills, and +training. + +\begin{verbatim} +## Reading layer `SSSI_SCOTLAND' from data source `/Users/jeremy/gits/mapping_environmental_action/data/SSSI_SCOTLAND.shp' using driver `ESRI Shapefile' +## Simple feature collection with 15872 features and 7 fields +## geometry type: POLYGON +## dimension: XY +## bbox: xmin: -296506.9 ymin: 530237.9 xmax: 467721.5 ymax: 1220310 +## epsg (SRID): NA +## proj4string: +proj=tmerc +lat_0=49 +lon_0=-2 +k=0.9996012717 +x_0=400000 +y_0=-100000 +datum=OSGB36 +units=m +no_defs +\end{verbatim} + +\begin{verbatim} +## Reading layer `WILDLAND_SCOTLAND' from data source `/Users/jeremy/gits/mapping_environmental_action/data/WILDLAND_SCOTLAND.shp' using driver `ESRI Shapefile' +## Simple feature collection with 42 features and 3 fields +## geometry type: MULTIPOLYGON +## dimension: XY +## bbox: xmin: 76877.24 ymin: 578454.1 xmax: 435367.1 ymax: 1190510 +## epsg (SRID): NA +## proj4string: +proj=tmerc +lat_0=49 +lon_0=-2 +k=0.9996012717 +x_0=400000 +y_0=-100000 +datum=OSGB36 +units=m +no_defs +\end{verbatim} + +\begin{verbatim} +## Reading layer `National_Forest_Inventory_Woodland_Scotland_2017' from data source `/Users/jeremy/gits/mapping_environmental_action/data/National_Forest_Inventory_Woodland_Scotland_2017.shp' using driver `ESRI Shapefile' +## Simple feature collection with 199698 features and 7 fields +## geometry type: POLYGON +## dimension: XY +## bbox: xmin: 65210.1 ymin: 532547.9 xmax: 461253.7 ymax: 1209179 +## epsg (SRID): NA +## proj4string: +proj=tmerc +lat_0=49 +lon_0=-2 +k=0.9996012717 +x_0=400000 +y_0=-100000 +datum=OSGB36 +units=m +no_defs +\end{verbatim} + +\hypertarget{proximity-to-wilderness}{% +\section{Proximity to ``Wilderness''}\label{proximity-to-wilderness}} + +Chasing down a curiosity, I decided to try and calculate whether +proximity to ``wilderness'' or ``scenic nature'' or just trees might +have some impact on generating more mobilised communities. I realised +that there would be several problems with this kind of calculation up +front, first being that ``nature'' is a deeply problematic construct, +reviled by geographers and philosophers alike. With this in mind, I +identified several different ways of reckoning wilderness, starting with +the highly anachronistic ``Scenic Land'' designation from the 1970s. +Then I pursued the more carefully calculated ``core wild areas'' +generated by SNH just a few years ago. However, even the core wile areas +concept has been criticised heavily, so I also expanded out my search to +include all sites of special scientific interest and then went even +wider to include the Scottish Forestry Service's ``Native Woodland'' and +finally, the most generic possible measurement, any land identified as +forested at the last Forest Inventory. + +Proximity to these areas was the next concern, because many of these +designations deliberately exclude human habitat, so it was necessary to +measure the number of sites within proximity. There is a question which +lies here regarding aesthetics, namely, what sort of proximity might +generate an affective connection? From my own experience, I decided upon +the distance represented by a short walk, i.e.~a half-kilometre. +However, with the more generic measurements, such as SSSI and +forestation, this wouldn't do, as there are so many of these sites that +a buffer of 500 meters encapsulates almost all of inhabited Scotland. So +for these sites I also calculated a count within 50 metres. + +So what did I discover? The results were inconclusive. First, it is +important to note that on the whole, Eco-Congregations tend to be more +urban than place of worship taken generally at a rate of nearly 3:1 +(5.4\% of Eco-Congregations lie in areas currently designated as ``Very +Remote Rural Areas'' whereas nearly 15\% of places of worship lie in +these areas), so what I was testing for was whether this gap was smaller +when specifying these various forms of ``wild'' remoteness. For our +narrowest measurements, there were so few sites captured as to render +measurement unreliable. There are, for obvious reasons, 0 sites located +within any of SNG's core wild areas. Similarly, there are very few of +our activist communities located within SSSI's (only +\texttt{st\_within(pow\_pointX\_sf,\ sssi)} places of worship out of +over 4k, 2 transition towns, (or 2\%) and 7 community development trusts +(3\%)). However, expanding this out makes things a bit more interesting, +within 50 metres of SSSI's in Scotland lie +\texttt{st\_within(ecs\_sf,\ st\_buffer(sssi,\ dist\ =\ 50))} +Eco-Congregations (or just under 1\%), which compares favourably with +the +\texttt{st\_within(pow\_pointX\_sf,\ st\_buffer(sssi,\ dist\ =\ 50))} +places of worship (or just 1.5\%) far exceeding our ratio (1:1.5 +vs.~1:3). This is the same with our more anachronistic measure of +``scenic areas,'' there are 7 eco-congregations within these areas, and +175 places of worship, making for a ratio of nearly 1:2 (2.1\% +vs.~4.3\%). Taking our final measure, of forested areas, this is hard to +calculate, as only one Eco-Congregation lies within either native or +generally forested land. + +\begin{verbatim} +## [1] 0 3 59 +\end{verbatim} + +\begin{verbatim} +## [1] 7 62 610 +\end{verbatim} + +\includegraphics{figures/wilderness_plots-1.pdf} +\includegraphics{figures/wilderness_plots-2.pdf} + +\hypertarget{appendix-a}{% +\section{Appendix A}\label{appendix-a}} + +\hypertarget{appendix-b}{% +\section{Appendix B}\label{appendix-b}} + +(JK note to self: same as above, but augmented with multipliers by which +categories are different from one another) + +\hypertarget{appendix-c---data-by-urban-rural-classification}{% +\section{Appendix C - Data by Urban / Rural +Classification}\label{appendix-c---data-by-urban-rural-classification}} + +\renewcommand\refname{Citations} +\bibliography{biblio.bib} + + +\end{document}