DATA
& METHODOLOGY
The Data Used
The project uses various sources of data to examine both the current distribution of land-use intensity in Vancouver as well as looking at relative potential to densify based on a set of criteria that match what was outlined as goals of EcoDensity and Smart Growth Theory.
The Data was derived from the following sources:
- Census Data: DMTI Census Data 2001
o Population
o Total dwellings
o
Average number of bedrooms per dwelling
- GVRD Spatial Data 2001:
o City boundaries
o Roads (major, minor, allroads)
o Roads buffer polygons (major, minor)
o Land-use layer 2001
o Land-use layer 2006
o Schools points (Secondary and Elementary)
o Vancouver neighbourhood boundaries
- Translink:
o Transit stop locations
o Transit lines
o
Average speeds of different transit types
- Georeferenced:
o Community centre locations (City of Vancouver website)
o
Canada Line and stations
Current Densities
The first step of the mapping was to examine the current density and land-use intensity patterns in Vancouver to create clear visual representation of the situation today.
There are in existence various maps showing basic density in Vancouver, and, whereas these are useful for a snapshot view of the city’s population distribution, absolute density measures fail to adjust for various variability within areas. In other words, whereas a pure density map would show high density in the West End and a low-density in Stanley Park, it would not take into account what those two land areas mean for possible population accommodation; that Stanley Park cannot accommodate any people, for example. The first step that this project intended to do was to look at the lands available for ‘population accommodation’ based on retaining our current land-use divisions (i.e. we are not going to build housing in a park). Land-use under any residential classification was therefore included along with ‘open and undeveloped’ since this land was assumed to be at least potentially convertible to future residential development. Only ‘Commercial-Residential/Mix’ category was somewhat difficult to include as it included large mixed areas surrounding the Central Business District (CBD) and especially along Broadway. These were partially excluded by using an older data set of Land-use from 2001which showed commercial specifically only along retail locations and not the entire block set as the 2006 did. The 2001 commercial polygons were erased from the ‘Commercial-Residential/Mix’ category of 2006 and the remaining areas were assumed to be generally residential areas. The 2001 land-use layer was not exclusively used at it had to many irregularities in other classifications especially in the Downtown area.
The following table shows the included and excluded
land-uses:
Excluded
Land-uses |
Included
Land-uses |
Agricultural |
Residential - Rural |
Institutional |
Residential - Single Family and Duplexes |
Industrial |
Residential - Townhouse and Low-rise Apartments |
Industrial - Extractive |
Residential - High-rise Apartments |
Transportation, Communication and Utilities |
Open and Undeveloped |
Recreation and Protected Natural Areas |
Commercial - Residential/Mixed* |
Commercial |
|
Harvesting and Research |
|
Lakes and Water Bodies |
|
|
|
The next step was to remove the road areas with the assumption that these lands are not potential residential land. Existing road buffer polygon layers were used which had three different buffer polygon sizes depending on the road hierarchies (i.e. major roads had larger polygons). These road polygons were therefore removed from the residential land-uses using the ‘erase’ tool.
The remaining lands were considered the Residential Land Area, since this was all land that was potentially available for residential use in the city. A new field was created and the residential land polygon areas were calculated. The Residential Land Area layer was then joined with the Census DA layer for Vancouver using the ‘union’ tool. A table was created using the ‘Sum’ function which summarized the total polygon areas within each DA, and this was later ‘joined’ to the Census DA layer to finally give the total residential land area within each DA.
The first
map that was generated was the Population per
Residential Hectare (RHA) by DA which converted the area of residential
land by DA into hectares and divided the DA population by that number.
(See
Map: Population per
Residential Hectare)
The Second map was created using the same Residential Hectare data but looking at the number of dwellings registered on the census by DA per RHA. (See Map: Dwelling per Residential Hectare)
The third map used available Census data to calculate the number of bedrooms by DA by multiplying the Census data for ‘average number of bedrooms per dwelling’ by ‘total dwellings’ to determine the total bedrooms per DA. This was then divided by the population per DA to give us a map showing the average number of bedrooms per person by DA. Certain DA’s, however, were excluded since there seemed to be errors in the Census Data and these DA’s didn’t have any listed average bedroom value. (See Map: Bedrooms per Capita)
Current Amenities
The second point to examine was what infrastructure was in place to serve people in each area, with the assumption that increased density would benefit from certain existing infrastructure and amenities. Surplus population would therefore be better placed in areas which have more ‘amenities’ available. The amenities considered to be important were the following:
- Parks
- Schools (Elementary and Secondary)
- Community Centres
- Local Commercial Nodes
- Public Transit
Schools were obtained from existing data in point shapefiles in the
GVRD
spatial data set. Community Centres were not available and therefore
were
manually georeferenced using the City of Vancouver website addresses
and
‘Google Maps’ for location check. Parks were extracted from the
Land-use layer
and added as a separate layer.
Local Commercial Nodes were determined as commercial zone agglomerations throughout the City outside of the Downtown CBD area. Although for the initial Residential Land area selection, both land-use maps for 2001 and 2006 were combined to correct certain classification errors in the data, for the local commercial nodes only the older 2001 data was used because it provided separate residential and commercial classification in many areas where the newer map simply had ‘residential/commercial – mix’ zoned. Thus the commercial polygons for the land-use 2001 layer were selected and made into a new layer. Because the commercial zoning divided commercial zones into many tiny polygon areas and what was wanted was the commercial node areas outside the CBD, the polygons were thus aggregated using the ‘Aggregate Polygons’ tool under ‘Coverage Tools’. The aggregation parameter was tested over several distance settings to determine what would be appropriate in presenting an accurate picture of commercial node areas. The resulting aggregated polygons were checked with various known commercial areas to check for the most accurate distance parameter, which was thus set at 100 m. Also, the ‘orthogonal feature’ parameter was activated to maintain angular polygons and, finally, all polygons under 10,000 square metres were eliminated so as to only select the more major commercial nodes in the city with the assumption that these would perhaps be most appropriate for focusing densification around.
The final, and perhaps most important amenity examined for densification was Public Transit infrastructure. The data was obtained from Translink it and included a layer of all transit lines and stop locations. Each line was associated with a route number and these were classified into four transit types using the Translink website: ‘Skytrain’, ‘rapid-bus’, ‘diesel bus’ and ‘trolley bus’. Finally the future Canada Line Skytrain and stations were digitized using the locations based on the Canada Line website as this line will be completed soon and will greatly affect transit accessibility in that area.
Proximity Rasters
Once the amenities were selected and layers were created based on what was important in the criteria for potential densification, raster layers needed to be generated to look at relative proximity to these amenities with the intention of later running Multi-Criteria Evaluations.
The following Proximity Rasters were created:
- Proximity to Parks
- Proximity to Elementary Schools
- Proximity to Secondary Schools
- Proximity to Community Centres
- Proximity to Local Commercial Nodes
Also, a complex cost distance path raster was created to look at:
- Relative Time Proximity to CBD by walking and transit
The initial step was to create a raster layer outline of Vancouver which was done by using a created Vancouver outline shape file, although this had to be modified to include areas where bridges crossed False Creek so as not to create a complete barrier here in our later transit analysis. All the subsequent rasters were limited to the extent of the ‘Vancouver_outline’ raster and were set at resolutions of 25 metres.
The first five proximity rasters (parks, elementary schools,
secondary schools, community centres and local commercial nodes) were
calculated using the ‘Straight Path Distance’ tool under ‘Spatial
Analyst’. It
wasn’t considered important enough to look at road geometry here since
with
walking and cutting through blocks and parks a more simple
straight-line
proximity was deemed sufficiently accurate.
Transit
Accessibility to the CBD
To calculate the transit accessibility to the Downtown, data on stop distances to Downtown was unavailable from Translink and therefore a somewhat complex model was needed to estimate times to the CBD for people walking and using transit - the forms of transportation which would want to be the focus of future densification rather than relying on auto-dependent development. The analysis performed was to use a Cost-Distance Path measurement to the Downtown using relative transit and walking speeds as the friction component (or cost).
Travel Form |
Average Speed[1] |
Relative Cost Friction Assigned |
Walking |
5 km/h |
500 |
Trolley – Bus |
13.5 km/h |
164 |
Diesel Bus |
15.2 km/h |
116 |
Rapid Bus |
21.6 km/h |
100 |
Skytrain |
40.3 km/h |
62 |
The relative cost friction was calculated based on the walking speed and this was added in a new ‘Cost’ field in the transit lines layer based on each lines’ transit type. This transit line layer was then converted to raster with the Cost field as the new raster value. For the buses it was assumed that the transit stops were close enough to each other to assume that the overall line was the same friction value but for the Skytrains more steps were needed to ensure that the analysis wouldn’t assume that one could simply get on a Skytrain anywhere along its length and therefore an effective ‘block’ was needed along the line except at station locations.
The first step for the Skytrain was to digitize the Canada Line. As this line would soon be completed in 2009, it was important to look at its influence on transit accessibility to the Downtown and how the neighbourhood surrounding it might be potentially important for densification.
In creating the ‘block’, all three Skytrain Lines (Millennium, Expo and Canada Line) were buffered by 50 m to be large enough to be represented in the 25 m resolution rasters created. Another buffer of 20 m was then done to represent the actual line itself. This second buffer was then removed from the wider raster using the ‘erase tool’ and thus a polygon strip on either side of the Skytrain lines was obtained. The next step was to ‘cut’ the polygons in edit mode to cut out strips where the stations were located along the line and erase these; effectively leaving a polygon strip that follows the Skytrain along the line except where stations are situated. Converting these to raster and using the ‘Raster Calculator’ this Skytrain block area was then cut out of the Transit Cost raster layer.
The
picture on the right shows the final Transit Cost layer with
the blocks (the white gaps) along the Skytrain lines (shown in red) and
each
transit line
is represented by an appropriate friction with the overall remaining
land area
at the friction of walking speed.
Multi-Criteria
Evaluation (MCE)
Having created raster layers for all the current density maps and the selected amenities in Vancouver, the next step was to run the Multi-Criteria Evaluation and thus produce maps combining the information and showing the areas that best matched the criteria for potential densification.
The first
step was to combine all of the beneficial
amenities raster into a single MCE output which then could be used to
compare to the current density levels. The first step in the MCE was to
normalize all of the raster layers so as to convert the varying data to
a
simple 0-100 scale. This also involved reversing the values so that,
for
example, a low distance to a community centre would score a high number
since
it would be matching our MCE criteria the most closely. The simple
formula used
in the raster calculator to normalize all of the amenity rasters was
the
following:
(1 - [layer]/MAX) * 100 |
Where MAX represents the maximum value
found in the layer |
The second step needed was to assign various weights to each of the factors based on the relative importance of each factor in our goal of proper densification. This was more difficult as it involved a certain amount of subjective variability and potential for uncertainties, however, since the normalized rasters were already available it was possible to attempt several variations on the weightings. For the purposes of this project only one of the weighted MCEs was used but bearing in mind that it is easily possible to use the underlying normalized raster layers as tools in performing many other MCEs in future research.
The weights were based on the assumption that the most important amenity factor was transit accessibility to the CBD as this was seen as the most difficult to change. It is feasible for example to add an extra school into a neighbourhood, however, much harder to make a distant area more transit accessible to the CBD, such as through building another Skytrain line. Along this same logic commercial nodes were seen to be the second most important as they are already developed secondary commercial centres outside the CBD and provide the perfect nodes to concentrate development. Parks are also considered very difficult to increase and existing parks provide a good green space amenity surrounding which density can be concentrated. Finally community centres, elementary and secondary schools were considered less central but still important amenities for increased population as it was generally assumed that, even their current capacity wasn’t able to meet increases in population in the area, it would be easier to expand capacity within existing school sites than building more schools on scarce land.
Amenity |
Raster
layer name |
MCE
weighted multiple |
|
Transit accessibility |
ntranscostd |
10 |
|
Proximity to commercial nodes |
distcomrnodes |
5 |
|
Proximity to parks |
distparks |
2 |
|
Proximity to community centres |
distcommcentr |
1.5 |
|
Proximity to secondary schools |
distschoolss |
1.5 |
|
Proximity to elementary schools |
distschoolse |
1 |
|
|
Total MCE Weights |
21 |
The following
equation shows the full process of calculating the final MCE for
amenities, including the normalization, the reversing of values and the
relative
weighting:
(1 - [ntranscostd] / 1715938.875) * (10 / 21) + (1 - [distcomrnodes] / 2926.175048828125) * (3 / 21) + (1 - [distparks] / 1131.923095703125) * (2 / 21) + (1 - [distcommcentr] / 4465.49267578125) * (1.5 / 21) + (1 - [distschoolss] / 3418.7900390625) * (1.5 / 21) + (1 - [distschoolse] / 2970.690185546875) * (1 / 21) |