THE SCIENTIFIC RESEARCH PROGRAM
Untouched Lophophora williamsii in the
regrowth study site population
Peyote post-harvest regrowth –
observations after 8 months
&
observations after 1 year
PNF – Plant not found.
TNF – Tag not found.
NP – Not present.
– – Missing
data.
Concerning data on regrowth involving multiple pups:
1) There is not necessarily a direct 1:1
correspondence between sequential figures for individual pups within a
single plant.
2) It was not uncommon for some or all pups to be
partly or entirely covered with soil so some photos may reflect the
pre-uncovery state.
Images of the tags can be viewed via the links for
the tag numbers and images of the actual plants can be viewed using the
links in the columns headed "Regrowth as number of pups" or "Number of
crowns".
Plant No. |
Number
of ribs |
Diameter
(cm) |
Height
(cm) |
Weight
(gm) |
Regrowth as
number of pups
or
TNF, PNF |
Regrowth as
diameter of pups
(cm)
|
|
|
3
Mar. 2008 |
11 Nov. 2008
7 Mar. 2009 |
1 |
2 |
3 |
4 |
5 |
6 |
|
|
|
101 |
13 |
6.2 |
3.0 |
65 |
4
4 |
1.3
2.0 |
2.5
2.7 |
2.4
2.5 |
1.2
1.3 |
|
|
|
102 |
5 |
2.4 |
1.0 |
3 |
1
1 |
1.5
1.5 |
|
|
|
|
|
|
103 |
5 |
2.0 |
0.7 |
3 |
3
2 |
0.5
|
0.8
1.2 |
0.9
1.3 |
|
|
|
|
104 |
8 |
4.6 |
1.5 |
23 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
105 |
8 |
5.0 |
1.5 |
23 |
0
TNF, PNF |
|
|
|
|
|
|
|
106 |
13 |
6.3 |
1.6 |
45 |
2
3 |
2.0
2.0 |
2.4
2.4 |
1.9 |
|
|
|
|
107 |
8 |
5.0 |
3.0 |
31 |
6
6 |
1.5
1.8 |
2.0
2.4 |
1.8
2.2 |
1.3
1.5 |
1.6
1.9 |
1.4
1.5 |
|
108 |
8 |
5.0 |
1.5 |
31 |
TNF, PNF
3 |
2.1 |
1.8 |
2.1 |
|
|
|
|
109 |
9 |
5.8 |
1.9 |
43 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
110 |
8 |
4.1 |
1.8 |
23 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
111 |
8 |
2.7 |
0.9 |
6 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
112 |
13 |
4.8 |
0.7 |
20 |
TNF, PNF
4 |
2.1 |
2.0 |
1.7 |
1.6 |
|
|
|
113 |
13 |
6.3 |
2.6 |
74 |
1
0 |
0.9
|
|
|
|
|
|
|
114 |
8 |
4.1 |
1.2 |
17 |
2
2 |
1.7
1.7 |
1.9
1.7 |
|
|
|
|
|
115 |
5 |
2.2 |
0.8 |
3 |
0
0 |
|
|
|
|
|
|
|
116 |
8 |
4.4 |
0.3 |
23 |
3
3 |
1.7
1.7 |
1.0
0.9 |
1.4
1.6 |
|
|
|
|
117 |
8 |
5.4 |
1.7 |
28 |
3
3 |
1.3
1.8 |
2.8
3.0 |
1.8
2.1 |
|
|
|
|
118 |
8 |
5.3 |
1.3 |
34 |
5
5 |
1.0
1.0 |
1.3
1.9 |
1.0
1.3 |
1.2
1.7 |
1.4
2.0 |
|
|
119 |
13 |
5.4 |
2.3 |
48 |
4
4 |
1.9
2.2 |
0.8
0.9 |
1.5
1.3 |
1.6
1.9 |
|
|
|
120 |
8 |
5.6 |
1.4 |
28 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
121 |
13 |
6.3 |
2.6 |
71 |
2
2 |
1.9
2.4 |
2.5
2.6 |
|
|
|
|
|
122 |
5 |
2.9 |
1.0 |
6 |
1
TNF, PNF |
2.2
|
|
|
|
|
|
|
123 |
8 |
5.0 |
1.8 |
31 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
124 |
8 |
4.1 |
1.1 |
17 |
2
2 |
1.9
1.8 |
2.1
2.0 |
|
|
|
|
|
125 |
8 |
4.4 |
1.1 |
14 |
2
2 |
1.6
2.0 |
1.5
1.6 |
|
|
|
|
|
126 |
13 |
5.0 |
2.0 |
54 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
127 |
8 |
4.3 |
1.2 |
28 |
1
1 |
1.8
2.0 |
|
|
|
|
|
|
128 |
13 |
4.9 |
1.6 |
34 |
3
3 |
1.6
1.7 |
2.4
2.8 |
2.0
2.0 |
|
|
|
|
129 |
10 |
5.3 |
2.0 |
34 |
4
4 |
2.0
2.2 |
2.0
2.2 |
1.0
1.7 |
2.2
2.3 |
|
|
|
130 |
8 |
5.3 |
1.6 |
23 |
2
2 |
1.1
1.1 |
3.1
3.7 |
|
|
|
|
|
131 |
8 |
4.8 |
2.6 |
26 |
3
3 |
1.4
1.9 |
1.2
1.5 |
1.1
1.4 |
|
|
|
|
132 |
8 |
4.4 |
1.5 |
17 |
2
2 |
1.5
1.9 |
2.0
2.0 |
|
|
|
|
|
133 |
8 |
4.2 |
1.7 |
20 |
0
1 |
0.8 |
|
|
|
|
|
|
134 |
8 |
3.4 |
1.1 |
9 |
0
2 |
1.4 |
1.6 |
|
|
|
|
|
135 |
13 |
5.4 |
1.0 |
28 |
2
2 |
2.8
3.2 |
1.7
1.9 |
|
|
|
|
|
136 |
13 |
5.7 |
2.3 |
48 |
2
3 |
1.9
2.4 |
1.9
2.3 |
1.4 |
|
|
|
|
137 |
8 |
4.6 |
1.5 |
17 |
3
3 |
1.8
1.6 |
1.8
1.6 |
1.7
1.3 |
|
|
|
|
138 |
13 |
5.7 |
2.6 |
43 |
TNF, 4
4 |
1.1
1.2 |
1.4
1.7 |
1.8
2.4 |
1.1
1.4 |
|
|
|
|
139 |
5 |
2.9 |
1.0 |
6 |
1
1 |
1.8
1.9 |
|
|
|
|
|
|
140 |
10 |
5.4 |
1.2 |
28 |
0
0 |
|
|
|
|
|
|
|
141 |
13 |
5.0 |
1.0 |
23 |
4
4 |
1.6
– |
1.6
– |
1.8
– |
1.5
– |
|
|
|
142 |
13 |
6.4 |
2.1 |
62 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
143 |
13 |
6.3 |
1.9 |
51 |
TNF, PNF
TNF, PNF |
|
|
|
|
|
|
|
144 |
5 |
3.9 |
1.7 |
23 |
2
2 |
1.0
1.4 |
1.0
1.3 |
|
|
|
|
|
145 |
5 |
3.5 |
0.9 |
11 |
1
1 |
1.4
1.5 |
|
|
|
|
|
|
146 |
13 |
5.9 |
1.5 |
37 |
2
2 |
1.8
2.0 |
1.6
1.9 |
|
|
|
|
|
147 |
13 |
5.7 |
1.6 |
34 |
4
4 |
1.0
1.5 |
1.4
1.5 |
1.4
2.0 |
1.8
2.0 |
|
|
|
148 |
13 |
6.8 |
3.0 |
54 |
1
1 |
2.5
3.4 |
|
|
|
|
|
|
149 |
13 |
6.7 |
1.5 |
51 |
6
6 |
1.8
2.1 |
1.1
2.0 |
1.0
1.9 |
0.9
1.4 |
1.1
2.0 |
1.8
2.0 |
|
150 |
5 |
2.9 |
1.0 |
9 |
2
2 |
1.3
1.4 |
1.3
1.4 |
|
|
|
|
|
The plants being surveyed are part of a
larger population occurring on private land in South Texas. The area of
the survey site itself is defined with a transect of 17-gauge electric
fence wire secured with steel stakes the locations of which are
recorded with a high resolution GPS. The transect zigzags through the
study site with all plants in the study being located within
approximately one-half meter of the wire. The area of the study site
has not yet been accurately measured but we estimate it to be around
half a hectare.
Above are the data from the first eight months and
the first twelve months of our study on the effect of harvesting on
regrowth and mortality of peyote plants in habitat, with starting data
on 50 plants (harvested 13 MAR 2008) and follow-up data collected eight
months later (22-23 NOV 2008) and twelve months later (7 MAR 09). Diameters of original plants are given
as the mean average of the widest and narrowest diameters whenever they
were not symmetrical.
At this point we are inferring mortality of a
harvested plant if it produced no regrowth of buttons (zero in the "Regrowth
as number of pups" column) up to the present.
The percentage of multiple regrowth buttons per
harvested plant (up to 6 new buttons per plant) is gratifying, and
shows the benefit of the good harvesting practice of cutting high (at
or above the junction of green aerial stem and the beige subterranean
stem) and relatively level. The rather large size (up to about 2.5 cm
in diameter) attained by some of these new buttons in only eight months
was also gratifying, but the contribution of soil moisture from the
hurricane in the summer of 2008 probably made this a
better-than-average year for the growth of new buttons from old
rootstocks.
An unexpected problem that arose in the first study
monitoring at the 8-month time point was the fact that we were unable
to locate 11 out of the original 50 numbered tags and the plants to
which they referred. The tags had been tied with 17-gauge wire to very
large nails driven into the ground next to each plant in the study.
Some lost tags were probably covered over with soil that washed down
the slopes with the rains associated with the hurricane during the
summer of 2008. Other tags and plants may have been dug up and
buried by feral hogs, which are numerous on the property. Large holes
(made by animals, not humans) were evident under many of the nurse
shrubs where most of the peyote plants grow. We encountered a similar
picture in Spring of 2009.
This inability to locate these tags and the
corresponding plants effectively reduced the number of plants
in the study from 50 to 39 (a 22% loss). It also poses a question of
interpretation, as the loss of such plants could be considered
"natural" mortality if it is due to the digging of feral hogs.
At present, we are simply eliminating from the study
those plants whose tags were not found — where the plants themselves
were likewise not found.
We harvested, measured and tagged 20 more plants on
23 NOV 2008, to bring the total number of plants in the "harvested"
group up to 59. {The results from our March 2009 visit concerning those
twenty individuals can be found farther below.}
The preliminary figure for mortality that may be
attributable to harvesting, then, is 5/39, or about 13%.
2010 data
We also tagged and measured
a control group of 50 plants on 23 NOV 2008, which in future monitoring
will give us an idea of the magnitude of natural mortality not
associated with harvesting.
7 March 2009 update:
Interestingly we found the same number of harvested
study plants (with their tags) but as can be seen in the table above
these were not entirely the same plants & tags as had been located
on 23 November 2008.
On this visit we used a Trimble
high-resolution GPS instrument to record the location of all tags
and/or plants located.
Complete or partial burial of plants and their tags
was sometimes encountered. To aid in future visits we added a rebar
stake near each tagged plant.
We did photograph additional plants that appeared to
be previously harvested plants showing regrowth. One of which was
lacking a photograph of the tag and, based on its location in the
sequence of images, appeared likely to match #134 – which was recorded
as being both found and measured. There were two additional images that
also had no accompanying tag photos.
These are referred to here as TNF 1 (possibly #134), TNF 2 & TNF
3.
All of the 50 members of our control group were
located but photographic data is not available for one of them.
Images and data concerning the control group can be
found below.
Control #154
Control group
Plant No.
|
Number of crowns
|
Number of ribs
|
Diameter of crowns
(in cm)
|
|
22 Nov. 2008
7 Mar. 2009
|
22 Nov. 2008
|
22 Nov. 2008
7 Mar. 2009
|
|
151
|
2
2
|
8, 8
|
3.8
3.5
|
4.3
4.7
|
|
|
152
|
1
|
8
|
3.7
3.8
|
|
|
|
153
|
1
1
|
8
|
3.5
3.8
|
|
|
|
154
|
4 (+4 pups)
4 (+4 pups)
|
13, 13, 13, 8
|
3.4
3.2
|
5.0
5.8
|
6.1
6.3
|
5.0
5.6
|
155
|
1
1
|
8
|
4.3
4.8
|
|
|
|
156
|
2
2
|
8, 8
|
4.3
4.8
|
4.9
4.7
|
|
|
157
|
1
1
|
8
|
4.8
5.5
|
|
|
|
158
|
1
1
|
8
|
5.7
5.8
|
|
|
|
159
|
1
1
|
8
|
4.7
5.0
|
|
|
|
160
|
1
1
|
13
|
4.7
5.2
|
|
|
|
161
|
1
1
|
8
|
5.1
5.2
|
|
|
|
162
|
1
1
|
8
|
4.0
5.2
|
|
|
|
163
|
1
1
|
13
|
6.1
6.5
|
|
|
|
164
|
1
1
|
13
|
7.4
7.4
|
|
|
|
165
|
3
3
|
8, 8, 8
|
5.8
5.6
|
3.5
3.9
|
3.2
3.8
|
|
166
|
1
1
|
13
|
6.0
5.6
|
|
|
|
167
|
2
2
|
13, 10
|
4.2
5.3
|
5.3
5.9
|
|
|
168
|
2
|
10, 11
|
5.2
5.3
|
5.1
4.7
|
|
|
169
|
1
1
|
8
|
3.2
4.7
|
|
|
|
170
|
1
1
|
10
|
5.2
5.6
|
|
|
|
171
|
1
1
|
13
|
7.5
7.0
|
|
|
|
172
|
1
|
13
|
5.0
5.5
|
|
|
|
173
|
1
1
|
8
|
4.8
4.9
|
|
|
|
174
|
1
1
|
10
|
5.2
5.9
|
|
|
|
175
|
1
1
|
8
|
3.6
4.1
|
|
|
|
176
|
1
1
|
8+ (transition)
|
5.0
5.0
|
|
|
|
177
|
1
1
|
8
|
6.0
5.2
|
|
|
|
178
|
1
1
|
13
|
5.8
5.9
|
|
|
|
179
|
1
1
|
8
|
4.5
4.2
|
|
|
|
180
|
1
1
|
13
|
7.2
7.3
|
|
|
|
181
|
1
1
|
5
|
2.5
2.9
|
|
|
|
182
|
1
1
|
8 (barely)
|
2.8
4.0
|
|
|
|
183
|
1
|
8
|
3.8
4.2
|
|
|
|
184
|
1
1
|
8
|
4.0
4.7
|
|
|
|
185
|
1
1
|
5
|
2.7
3.0
|
|
|
|
186
|
3
2
|
8, 8, 8
|
3.6
3.8
|
2.4
2.1
|
3.0
NP
|
|
187
|
2
2
|
8, 8
|
4.3
4.5
|
5.0
5.0
|
|
|
188
|
1
1
|
8
|
4.4
4.7
|
|
|
|
189
|
1
1
|
8
|
3.6
4.0
|
|
|
|
190
|
2
2
|
13, 13
|
6.4
5.8
|
6.0
5.5
|
|
|
191
|
1
1
|
8
|
3.8
3.3
|
|
|
|
192
|
1
1
|
5
|
2.6
2.8
|
|
|
|
193
|
3
3
|
10, 10, 10
|
4.5
4.0
|
4.5
4.4
|
5.0
4.7
|
|
194
|
2
2
|
8, 8
|
4.1
3.9
|
3.2
3.3
|
|
|
195
|
3
4
|
8, 8, 13
|
4.4
4.1
|
NP
1.8
|
4.0
3.7
|
3.0
2.9
|
196
|
1
1
|
8
|
3.0
3.0
|
|
|
|
197
|
1
2
|
10
|
4.9
4.5
|
NP
1.2
|
|
|
198
|
1
1
|
8
|
4.2
4.1
|
|
|
|
199
|
1
1
|
10
|
4.8
4.6
|
|
|
|
200
|
1
1
|
11 (transition)
|
5.4
5.5
|
|
|
|
Control group data
for 2010
Late-harvested plants
The following 20 plants (#201-220) were harvested
during the November 2008 monitoring to make up for lost plants from the
original group of 50 harvested plants. The March 2009 data presented
here follow a severe drought that lasted throughout the winter and into
the spring, up through the date of the March monitoring. Several of the
harvested plants looked and felt dead at ground level. The Fall 2009
monitoring should reveal whether they survived harvesting or not. Do
peyote harvesters routinely anticipate drought and its effects on the
survival of the harvested plants? Do they stop harvesting during a
drought?
Do droughts occur in a conscientiously harvested
greenhouse?
* This sole post-harvest regrowth pup in
this drought-harvested subgroup was regrowth from an apical meristem,
not from a subterranean areole. This apical meristem regrowth was
possible only because the crown was removed with a high cut, slightly
above ground level, so that the apical meristem remained in the stem of
the living plant rather than being removed with the harvested crown.
2010 data for
late-harvested plants
Regrowth study site showing typical Tamaulipan
thornscrub vegetation
If you would like to help
support additional studies of this type, designed to answer basic
questions that are critical to the optimal stewardship/management of
vulnerable cactus species, please send a contribution,
of $25 USD or whatever amount you can afford, to the Cactus
Conservation Institute, 909 E. Sul Ross Ave., Alpine, TX 79830.
We also now accept donations via PayPal.
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