2003 Piru Fire Historical Imagery
Data files
Dec 13, 2022 version files 4.22 GB
-
1930_imagery_1.tfw
90 B
-
1930_imagery_1.tif
164.62 MB
-
1930_imagery_1.tif.aux.xml
6.15 KB
-
1930_imagery_1.tif.ovr
55.91 MB
-
1930_imagery_10.tfw
90 B
-
1930_imagery_10.tif
188.07 MB
-
1930_imagery_10.tif.aux.xml
6.38 KB
-
1930_imagery_10.tif.ovr
65.45 MB
-
1930_imagery_11.tfw
90 B
-
1930_imagery_11.tif
43.81 MB
-
1930_imagery_11.tif.aux.xml
5.76 KB
-
1930_imagery_11.tif.ovr
16.08 MB
-
1930_imagery_12.tfw
90 B
-
1930_imagery_12.tif
59.79 MB
-
1930_imagery_12.tif.aux.xml
5.96 KB
-
1930_imagery_12.tif.ovr
20.16 MB
-
1930_imagery_13.tfw
90 B
-
1930_imagery_13.tif
46.81 MB
-
1930_imagery_13.tif.aux.xml
5.82 KB
-
1930_imagery_13.tif.ovr
16.08 MB
-
1930_imagery_14.tfw
90 B
-
1930_imagery_14.tif
48.48 MB
-
1930_imagery_14.tif.aux.xml
5.89 KB
-
1930_imagery_14.tif.ovr
17.36 MB
-
1930_imagery_15.tfw
90 B
-
1930_imagery_15.tif
49.91 MB
-
1930_imagery_15.tif.aux.xml
5.84 KB
-
1930_imagery_15.tif.ovr
18.10 MB
-
1930_imagery_16.tfw
90 B
-
1930_imagery_16.tif
40.91 MB
-
1930_imagery_16.tif.aux.xml
6.13 KB
-
1930_imagery_16.tif.ovr
13.97 MB
-
1930_imagery_17.tfw
90 B
-
1930_imagery_17.tif
53.11 MB
-
1930_imagery_17.tif.aux.xml
6.14 KB
-
1930_imagery_17.tif.ovr
18.10 MB
-
1930_imagery_2.tfw
90 B
-
1930_imagery_2.tif
162.46 MB
-
1930_imagery_2.tif.aux.xml
6.25 KB
-
1930_imagery_2.tif.ovr
55.37 MB
-
1930_imagery_3.tfw
90 B
-
1930_imagery_3.tif
176.57 MB
-
1930_imagery_3.tif.aux.xml
6.40 KB
-
1930_imagery_3.tif.ovr
61.57 MB
-
1930_imagery_4.tfw
90 B
-
1930_imagery_4.tif
113.29 MB
-
1930_imagery_4.tif.aux.xml
6.43 KB
-
1930_imagery_4.tif.ovr
37.82 MB
-
1930_imagery_5.tfw
90 B
-
1930_imagery_5.tif
204.54 MB
-
1930_imagery_5.tif.aux.xml
6.51 KB
-
1930_imagery_5.tif.ovr
70.13 MB
-
1930_imagery_6.tfw
90 B
-
1930_imagery_6.tif
123.32 MB
-
1930_imagery_6.tif.aux.xml
6.36 KB
-
1930_imagery_6.tif.ovr
42.64 MB
-
1930_imagery_7.tfw
90 B
-
1930_imagery_7.tif
92.05 MB
-
1930_imagery_7.tif.aux.xml
6.18 KB
-
1930_imagery_7.tif.ovr
31.62 MB
-
1930_imagery_8.tfw
90 B
-
1930_imagery_8.tif
171.06 MB
-
1930_imagery_8.tif.aux.xml
6.49 KB
-
1930_imagery_8.tif.ovr
60.14 MB
-
1930_imagery_9.tfw
90 B
-
1930_imagery_9.tif
122.14 MB
-
1930_imagery_9.tif.aux.xml
6.37 KB
-
1930_imagery_9.tif.ovr
41.65 MB
-
ortho_1-2_1n_s_ca111_2009_1.sid
1.72 GB
-
ortho_1-2_1n_s_ca111_2009_1.sid.aux.xml
20.86 KB
-
README.txt
19.93 KB
Abstract
The increased occurrences of drought and fire may be contributing to the loss of biodiverse ecosystems in Mediterranean regions. Specifically, the conversion of diverse native shrublands, such as chaparral, to non-native annual grassland by fire is of great conservation concern in California. To avoid or slow the loss of chaparral, it is important to understand the underlying causes of landscape conversion. Studies investigating the interaction of multiple potential drivers are particularly crucial to identification of vulnerable areas of the landscape. Here we used aerial imagery to evaluate vegetation transitions between chaparral, sage scrub, grassland, and tree domination and their potential drivers within Ventura County, California, a strongly Mediterranean climate region. We used random forest algorithms and conditional inference trees to determine the climatic, topographic, and fire-related variables contributing most to vegetation change. Our results support that chaparral conversion to grass (27% of chaparral plots) is a result of landscape position, fire, and drought acting in tandem. In particular, lower elevation, southwest facing slopes that experience a post fire drought are at very high likelihood of conversion to non-native annual grass. Additionally, our results show that these grasslands, once formed, rarely convert to other community types. Therefore, protecting shrub dominated areas that are most likely to convert (low elevation, more southwest facing slopes, less annual precipitation) is crucial to preserving native vegetation diversity.
1930 aerial imagery was obtained from the Map and Image Laboratory at the University of California, Santa Barbara. Imagery is from the 1930 flight C-870 and was mapped on a scale of 1:18,000. The 2009 imagery was obtained from the United States Geological Survey Digital Orthophoto Quarter Quads and is a true color aerial photograph at one-meter spatial resolution. The 1930 imagery was georectified to the 2009 imagery using 300-400 ground control points. Ground control points were selected from temporally stable objects such as trees, rock outcrops, roads, and permanent structures. Each image was then warped using triangulation and pixels were resampled to the nearest neighbor, creating a georectified image with one-meter spatial resolution. Mosaicked images were then validated for spatial accuracy by identifying 40-100 ground control points and ensuring a root mean square error of 10 pixels or less.
GIS software is required to view this imagery. Refer to the README.txt file for more information.