Peyote: the archaic, some beans and a rock

Archaic points of potential interest

See page 194 in Schultes & Hofmann 1980 concerning the claims of Adavasio & Fry 1976 related to archeological finds of peyote in rock shelters and caves in the Cuatro Cienegas Basin in Coahuila, Mexico.
This is a fascinating article that is often mentioned in conjunction with their proposal that, over the millennia, sacramental plants were progressively replaced by safer ones. While it is a tantalizing notion to entertain, it needs to be understood that Adavasio & Fry did not include adequate evidence to support either of their assertions a) that the use of Ungnadia preceeded that of Sophora and b) both were eventually replaced with Lophophora. Three points need to be made:
First, any evidence presented for the sacramental use of the Mexican Buckeye (Ungnadia speciosa Endl.) is circumstantial at best, being primarily based on its form of packaging being similar to that of the Texas mountain-laurel (Sophora secundiflora (Ort.) Lag. ex SD), their occasional comingling, and was bolstered with only one second-hand reference to it being a euphoric plant. There does not appear to be any accounts of or archaeological evidence for it actually being used for human ingestion ceremonially. This is not a small point to overlook.

Ungnadia speciosa leaves

Ungnadia speciosa leaves

archaic: Ungnadia speciosa seeds

Ungnadia speciosa seeds

Second, Sophora itself is not known to have ever actually been used as a sacramental hallucinogen per se. It was employed in a highly dangerous form of a vision quest to gain animal spirits as guardians, protectors or familiars. Granted, it was incorporated into the peyote drink as prepared by several tribes and it is reasonable to assume that to be an ancient practice. It has been closely associated physically with peyote rites, strung as beads, as well as reported to have been used medicinally, ritually and as a “narcotic” (a word that has been so misapplied, misconstrued and misused anthropologically as to have little, if any, reliably discernible meaning).

Sophora secundiflora flowers

Sophora secundiflora

Sophora secundiflora leaves

Sophora secundiflora

I do not dismiss Sophora‘s sacred stature, nor would I want to dispute its long association with the peyote ritual but it is important to keep in mind that its use (or effectiveness) as a hallucinogen has never been adequately demonstrated. It certainly is not supported by any of the published human bioassays involving either the plant or its pure alkaloids.
Descriptions of its effects were given years ago, in an upper division University of Texas at Austin anthropology class taught by Dr. William W. Newcomb (ANT 322M: “Indians of Texas”). Newcomb presented the stage of interaction with animal spirits to occur while the subject was in a deep coma-like stupor. Their successful entry into this state was said to demonstrated to onlookers by their unresponsiveness to a toothy gar-fish jaw being raked across their flesh. After intense headache, profuse vomiting and violent convulsions, a “coma” ensued that was said to last for several days. [That commentary is not included in his book Indians of Texas but rather was taken directly from my class notes.]

Sophora secundiflora seeds

Sophora secundiflora

Dr. Newcomb clearly presented it as being used ritually but not as a ritual sacrament or hallucinogen in the sense of peyote.
[See Schultes & Hofmann 1980 & 1992 for a broader discussion and also Hatfield et al. 1977 for chemical study and a discussion of the reports of ethnological use. LaBarre 1975 also includes a fascinating discussion.]
Ott 1993 mentions that despite claims by a number of people that the use of the ‘Red bean’ was the predecessor to and replaced by that of peyote, this was thoroughly challenged in a monograph by Merrill 1977.
I have had some very curious interactions with this plant; none of which involved its ingestion. It is definitely able to interact with people, and to a surprising degree to direct and influence their behavior to gather its seeds. I also believe it to be a sentient being based on my experiences with it as a living plant. It is not surprising that it was highly venerated by any people who knew it. It is also not surprising that they would gather its seeds in large numbers and store them in a special context. I’ve noticed that this still occurs although I am guessing modern containers of beans are maintained entirely for their decorative value.
Finally, my main objection to the conclusions of Adavasio & Fry concerning peyote is that they only selectively mention one solitary occurrence of the plant found by an earlier worker [Note 30].
It is very peculiar to attempt the support of such important conclusions with a single data point. Perhaps they also encountered additional examples but did not mention the details in this article. It is a puzzling omission considering their core assertion was one of safer plants being sequentially adopted.
Campbell 1958 had flatly asserted that it was not possible to demonstrate the priority of mescal beans over peyote based on the available evidence so something more is required.

It might also be added that there is a lack of evidence suggesting a continuity of culture in which a sequential series of sacramental replacements *could* occur but this seems trivial by comparison to items 1, 2 or 3.

No futher evidence was presented by Adavasio & Fry.
Disturbingly, the only find of peyote mentioned by Advasio & Fry in the same context as Sophora and Ungnadia was that of ONE string of dried peyote buttons dating from several millennia after peyote is known archeologically to have been employed by humans.
[See comments in Boyd & Dering 1996 concerning Ungnadia.]

The omission by Adovasio & Fry of any reference to additional finds is puzzling but it is far from being the only instance of cherry-picking that one can encounter in this area.
Schultes & Hofmann 1992 commented that peyote has been thought to have been in use for at least 4000 years. Dry cave and rock shelter finds in Texas are also said to have yielded dried samples of peyote that were three thousand years old and one find was purportedly dated to 7000 years. Those refer to specimens in the Witte Museum that have been claimed to be of that immense age (more on this in a moment.)
Oddly, until recently the entirety of the radiocarbon dating surrounding peyote has almost been characterized by missing information.
Let’s take a look at what is known concerning ancient peyote dating.
There are five reports where peyote was mentioned as being recovered from archaeological sites but material for only two of these can be located within the known collections. (See Terry et al. 2006 for details and references.)
One of these was from Cuatro Ciénegas, Coahuila, Mexico. This is a burial site from the transition between the Late Archaic and the Late Prehistoric Periods.
The account of Bruhn et al. 1978 gave its age based not on the actual dating of the peyote but on the dating of material thought to be associated with that single set of 8 strung and remarkably well preserved peyote buttons. Three mats had been dated with a range of 810-1070 AD (uncorrected values).
Due to the burial being a secondary interment, Martin Terry dated one of the actual Cuatro Ciénegas’ peyote specimens establishing its age as 835 ± 35 14C years BP.
Shumla Cave (No. 5, 41VV113) in southwest Texas on the other hand was an inhabited residential site (with intrusion of several burials.) The peyote was believed to have been deposited in the Eagle Nest subperiod of the Middle Archaic Period.
The exact provenience of the materials removed from the caves was not recorded but it is clear that they did mention recovering “a single mummified example” from Shumla Cave No. 5. This later became mistakenly presented as “petrified”. There was clearly more than one such artifact recovered from those excavations as three remained at the Witte for the removal of samples following the consumption of several others for earlier radiocarbon analysis. Terry et al. 2006 also reported their dating of the Shumla Caves’ peyote to 5195 ± 20 14C years BP.

 

Summary of earlier dating accounts:

Peter Furst was the first to report a date of 7000 BP for the Shumla cave material but due to several reasons the actual test data is either lost or irretrievable. It is therefore not possible to know anything further about the work or the claim. That claim oddly only appeared as a passing mention within a book review written by Furst. His date was repeated by Schultes & Hofmann and now appears stated as a fact throughout the literature.
Bruhn et al. 2002 presented a letter to the editor of Lancet in which they asserted establishing peyote use for 5700 years after dating the Shumla material (Furst’s 7000 BP). They repeated the claims in DeSmet & Bruhn 2003 citing Bruhn et al. 2002 as their primary reference.
El-Seedi et al. 2005 reported dating the Shumla Caves’ material to 3780-3660 BC.
Jan Bruhn (in a personal communication with Martin Terry) reported this was a weighted mean of 4952 ± 44 14C years.
Further investigation by Terry suggests that the discrepancy was most likely due to a failure of Bruhn to remove residual humic acid prior to radiocarbon dating. (See Terry et al. 2006)

Before leaving the subject of Sophora and Ungnadia completely, one point which must be considered is that world wide people have often venerated plants known to be deadly or exceedingly dangerous, with no intentions of using them for ingestion unless perhaps for the purpose of inducing death, or sometimes when ascertaining the guilt or innocence of a person by ordeal poisoning.
Many other ritual purposes besides hallucinogen use exist for plants. As the authors point out, the quantities found far exceed what would be needed for ingestion purposes. [Issue might be taken with their regarding a “crazed” state as being one conducive to, much less equated with, any ritual or sacred act. If anything it reflects a common culture-centric dismissal of what is viewed as a “more primitive” mindset.]
The most common usage of the red bean is that of ornamentation in the form of beads. The Mexican Buckeye would also make fine beads although none were mentioned as such.
Apparently the finds of both seeds consisted primarily of small caches of them, sometimes mixed together, which were sealed in plaited or twilled baskets which had to be torn to access the contents. [Both seeds also make a very nice sound, with good high frequency components, when shook or stirred. In quantity; the sound is absolutely mesmerizing. Such containers might have been musical instruments?]
In some sites, Sophora seeds and pods were found scattered throughout the cultural deposits.

Sophora-fruit-1 3

Sophora secundiflora seedpods

Those twilled containers could also represent power objects used just as they were. We know between almost nothing and nothing about these people’s religious and spiritual beliefs. Some people who later used the beans believed they needed to be roasted until yellow, or forcefully struck and crushed, to ‘kill’ them before use. Since the seeds recovered in those finds were apparently being stored intact perhaps they were intended to assure protection after death, or at least to be available after death.
It may be noteworthy however that in the Murrah Cave many of the individual Sophora seeds were described by Holden 1937 as being “parched”; perhaps indicating preparation for potential drug use. Alkaloids can sometimes be altered using heat so parching can be reasonably suspected to indicate preparation for some type of human use. It does not prove
It is not clear how many of these finds were in funerary context as was the case for the string of peyote and how many were found in residences (suggesting their employment by living people). The context can be complex as it is clear that burials occurred that intruded into older residential remains.
Their hypothesis is intriguing though; further work should be done to evaluate it even if it turns out to be a blind path.
A systematic review of the contents of rock shelter and cave excavations in the Chihuahuan Desert might prove a valuable avenue for anthropological studies of the religious and spiritual beliefs of people in this area before the invasion and occupation. The creation of small painted rocks and large pictoglyphs featuring shamanic themes are among the unique elements left by the archaic people who once lived around the mouth of the Pecos River.

 

A fascinating analysis was performed, by Bruhn & workers, on the aforementioned specimen of Cuatro Ciénegas peyote (the string of buttons) which was found by Taylor in 1941.
Bruhn et al. 1978 found 2.25% alkaloid in the Cuatro Ciénegas’ material in spite of it being thought to be from around 810 to 1070 AD. Their analysis was reported to show it to contain mescaline, lophophorine, anhalonine, pellotine and anhalonidine present in measurable amounts.
Phenolic alkaloids formed 35% of the total. It was noted that this is substantially lower than the 8% total alkaloid and 64% phenolic fraction which they observed in recently prepared peyote buttons.
They used tlc and GC (both with known reference samples) to determine this. See Bruhn et al. 1978 for more details.
A peculiar assessment was more recently presented by Bruhn et al. 2002, also DeSmet & Bruhn 2003 and also El-Seedi et al. 2005 where it was being noted that the total alkaloid content was lower in the far older Witte material from the Shumla Caves. They then went on to assert that while only 2% alkaloid was present there was no alkaloid other than mescaline that was detectable. That was intriguing enough but was not the end.

Bruhn then made the peculiar proposal that the reason they could only detect mescaline could be due to mescaline being more stable than the other peyote alkaloids. Reasonable enough on the surface yet it is noteworthy that in this Bruhn failed to mention any of his own previous work that contradicts this claim. Clearly something is in need of closer inspection. This claim about the Shumla specimens needs consideration in the light of his 1978 Cuatro Cienegas results. There was also his earlier report concerning degradation of peyote alkaloids in the study of 87 year old peyote buttons in Bruhn & Holmstedt 1974. In particular, their determination clearly showing that mescaline content apparently decreased *ahead* of the rate of decomposition of many of the other alkaloids. The cherry-picked selective presentation of facts in their 2002/2003/2005 account appear to have been overlooked by Bruhn’s peer reviewers or at least they dropped the ball in terms of what peer review is meant to accomplish. That is all actually fairly however when trivial compared to what they AND Bruhn’s crew missed.
The most interesting aspect of this so-called ‘mummified’ material in my mind is that, unlike Bruhn, Furst or Taylor, Terry & coworkers recognized that the specimens were not dried peyote buttons at all but rather were manufactured effigies of peyote created from some type of doughy material. (See images of both the Shumla and Cuatro Cienegas materials in Terry et al. 2006.)

Shumla_Terry_et_al_p1019_fig_3

Shumla peyote effigy

There are only the partial and hollowed out remains of three of these effigies are left due to the destructions of the rest of the materials during chemical analysis and radiocarbon dating. They were formed as a mixture of cactus materials combined with some sort of unidentified fibrous noncactaceous plant material and the resulting dough shaped by hand to vaguely resemble a living peyote cactus top. There was apparently at least two different makers of these artifacts over a period of some years as both their compositions and their dates varied. The most recently manufactured effigy had used entirely cactaceous materials.
More remarkable would be the assertion by Bruhn & coworkers that was just mentioned that this material contained 2% mescaline by weight *and* that only mescaline was detectable. Intriguing if true but in light of Bruhn & Holmsted previously establishing the deterioration of mescaline over time occurred at a faster rate than the deterioration of most of the other alkaloids I am left with far more questions than answers. It is obvious that we need to remain skeptical of Bruhn’s claim, no matter how intriguing it may be, as we proceed.
One thing that is clear, these ‘buttons’ were clearly manufactured artifacts. To be able to retain 2% mescaline after 5 millennia would require it to have once have had a far higher alkaloid content. The presence of ONLY mescaline would not be a result of some magical selective degradation process omitting mescaline but would absolutely require the involvement of some type of purification process. Or perhaps there are missing elements of this tantalizing puzzle that are presently defeating our understanding of exactly what has been established in these studies.
Did these prehistoric people really know of a route for purifying or at least greatly concentrating mescaline? It would certainly be interesting if true but establishing that Bruhn’s analytical results were actually valid has to be the starting point for answering this peculiar question and the burden of proof for establishing their validity is on the authors of that work.
Were these potent effigies a prepared drug form that were created for sacramental use rather than for simple use as effigies? No matter how they were prepared and no matter what their alkaloid content, they are clearly both deliberate and sophisticated in their preparation.
Or are Bruhn/El-Seedi/DeSmet’s reported analytical results simply needing to be questioned?

 

“Petrified” peyote buttons

The first reference to ‘petrified peyote’ was a misnomer in reference to the Shumla Caves’ adulterated & reconstituted 5 millennia old peyote effigies that were mentioned above. (See Terry et al. 2006 for details.)

More recently ‘petrified peyote buttons’ have been offered for sale (and finding at least one buyer) at a large southwestern Gem & Mineral Show and probably elsewhere.

petrified-peyote-front

Sold as petrified peyote button (front)

petrified-peyote-back

Sold as a petrified peyote button (back)

These do appear on first glance to vaguely resemble dried peyote buttons but are without a doubt either an agate or another form of chalcedony with a fine drusy quartz coating on one side. They lack the critical features (such as ribs, the distinctive apex and areoles) that are typically found in peyote buttons (see below).

Schultes 1937 peyote buttons

peyote buttons

They are amazing natural treasures but clearly are not of botanical origin.

Names associated with the Lophophoras

The Lophophoras

 

Lophophora-5-Kreuzinger

A.V. Frič’s view of Lophophora in 1936

I Lewinii (Hennings) blaßgelb Blüten” Keep this image in mind. We are going to refer to it again later. In Frič’s earlier use of this image, in 1924, he labelled this sp. lutea Frič. Frič should have kept it.

II texana

III Williamsii (Lem.) blaßrosa Blüten” In its first appearance, in Frič 1924, this was Anhalonium sp. fl. rosea Frič. This became Lophophora williamsii var. decipiens in Backeberg 1961. Fric’s account enabled Denis Cowper to locate it; it is now named Lophophora fricii.

IV caespitosa (San Luis)”

V Jourdaniana (syn. violaciflora) violetrosa Blüten.” In 1924, Frič had this image labelled as “Lewinii“.

 

Many Lophophora species names have appeared in print. Most of those are horticultural or sometimes they are erroneous. In earlier editions of this book, the problem names that were discussed were lumped together into one confusing section. In the present arrangement they are being treated separately in alphabetical order.

Many other ‘species’ and varieties have been proposed due to peyote’s highly variable nature. There seems little point in discussing them all. They are simply forms and many of them can be found within any large single population of peyote. Anderson and Grym have summarized them, and why they should be rejected, very nicely. For instance please compare the L. williamsii pictured elsewhere herein with Lophophora texensis below. Bohata and coworkers 2005 have treated the genus Lophophora quite excellently and readers interested in detailed information about the Lophophora species (including many great habitat photographs) are directed to their special issue of Kaktusy.

It seems obvious that most of the world’s experts now agree that five actual species presently exist, L. williamsii, L. koehresii, L. fricii, L. diffusa and the most recent species L. alberto-vojtechii. More may possibly be defined in Mexico in the future. The actual face of the genus is still being worked out and it seems likely that a number of varietal descriptions will find acceptance.
There also may be another variety or form of L. williamsii, most often confusedly known as L. williamsii var. echinata sensu Weniger. It will be touched on in its own section but will be included with more detail and images in the discussion of L. williamsii. It is somewhat distinct from a typical L. williamsii in its form, environmental tolerances and chemical make-up. Whether this qualifies it as an actual species seems doubtful but my thought is that it certainly merits some sort of recognition.

There is of course that pesky issue that, for plants at least, the concept of species is curiously defined with some nebulosity. Lacking a clear definition of what it takes to be regarded as an individual cactus species, let’s have a look at some of the names of interest.

Parenthetical names (Kanji) may be found helpful in performing online searches for additional imagery.

 

Lophophora alberto-vojtechii (小型烏羽玉)

This miniature plant is the newest Lophophora species. Considering how recently it has been noticed its range in Mexico has been found to be surprisingly large. I’m going to simply mention this species; Šnicer &/or Bohata can provide more details. It presently appears to lack any analysis.

At some point this entry will be updated. My thanks to Ade for sharing the flowering images below!

3, 4 & 5 yr. old Lophophora alberto-vojtechii

3, 4 & 5 yr. old Lophophora alberto-vojtechii
Photo by Ade

Lophophora alberto-vojtechii

Lophophora alberto-vojtechii
Photo by Ade

Lophophora alberto-vojtechii

Lophophora alberto-vojtechii
Photo by Ade

Learn more about “The Littlest Lophophora” in: Bohata 2008 Cactus & Co, 2 (12): 105-117 and in Šnicer et al. 2009. [Download a 2.3 Mb PDF copy from the Cactus Conservation Institute.]

 

Lophophora williamsii var. caespitosa (子吹乌羽玉)

This is not a variety but simply a growth form. It is not actually clear that all of these came from L. williamsii. Phytochemical analysis suggests they do not but comparative DNA work is still lacking.

Lophophora-caespitosa

Lophophora “caespitosa”

 

Lophophora decipiens

This is not a species but is simply a growth form that occurs in at least three of the Lophophora species. In modern horticulture, it is often specifically applied as a varietal name to a Lophophora fricii as var. decipiens.

Lophophora-decipiens-type-drawing-Croizat_after_BrandR

Croizat’s Type specimen of Lophophora decipiens

 

Lophophora diffusa (翠冠玉)

 

Lophophora-diffusa-Oz

Lophophora diffusa in Oz

 

Lophophora echinata

This is a confused name.

Lophophora-echinata-TerrellCounty

Lophophora williamsii looking rather ‘echinata‘ in Terrell County

 

Lophophora echinata var. diffusa

 

Lophophora echinata var. lutea

 

Lophophora fricii (银冠玉)

 

Lophophora-fricii-EricPhillips-c

Lophophora fricii from Quality Cactus

 

Lophophora jourdaniana (乔丹乌鱼玉 / 有刺烏羽玉)

Name is not presently accepted as it lacks any direct link to a wild population.

Lophophora jourdaniana

Lophophora jourdaniana grown from European seeds

 

Lophophora koehresii (考氏乌羽玉 / 顯疣烏羽玉)

 

Lophophora-koehresii-flower-CCI-a

Lophophora koehresii flower in habitat; from Cactus Conservation Institute website

 

Lophophora lutea

This is a confused name.

Rouhier_1927-fig31b

Echinocactus williamsii var. lutea from Rouhier 1926 fig. 31b

 

 

Lophophora sp. Parras de la Fuente

This is a pink flowered Lophophora fricii.

Lophophora-fricii-ParrasdelaFuente-Coahuila-flowering-e

Lophophora fricii Parras de la Fuente

 

 

Lophophora williamsii var. pentagona Croizat
[Note 28]

This is not a species but simply a growth form that occurs in all of the Lophophora species.

It is not clear to what degree this form shows up in any given population with youngsters. Plants and seeds sold domestically (inside of the US) under this name have often proven to be Lophophora diffusa (this is probably due to the illegality of L. williamsii in the US) but sometimes they are L. williamsii.

 

Lophophora-pentagona

Lophophora ‘pentagona’ seedling

 

Lophophora williamsii “var. pentagona” above was grown from German “var. pentagona” seed; most of them do not stay like this for very long.

 

Published analysis for “var. pentagona”

Mescaline 0.714% (± 0.049) dry wt
Pellotine 0.296% (± 0.065) dry wt
Habermann 1978a (from Štarha 1997)

Compare that to “L. williamsii var. typica
[Note 29]

Mescaline 0.709% (± 0.032) dry wt.
Pellotine 0.296% (± 0.065)
Habermann 1978a (from Štarha 1997)

The pentagona name game

Have some fun! See how many of the species for these “pentagona“s that you can identify without looking at the answers.

 

Echinocactus rapa Fischer & Meyer ex Regal

This is another outdated name for L. williamsii that was published in 1869.

Its publication marked the third time that an illustration of peyote appeared in print. (in Sertum Petropolitanum seu Icones et Descriptiones Plantarum quae In Horto Botanico Imperiali Petropolitano Floruerent.)

 

Regel-1869-E-rapa

Echinocactus rapa
from Regel 1869

 

 

This is Lophophora fricii.

Lophophora-fricii-AKA-roseiflora

Lophophora fricii AKA L. roseiflora

 

This is a synonym of Lophophora koehresii.

This is a synonym of Lophophora fricii.

Lophophora texensis (大型乌羽玉)

This is also not a real species despite seeds being commercially available. It is typically Lophophora williamsii that came from from south Texas.

 

Lophophora-texensis-a

Lophophora texensis” seedling that was grown from European seeds.

 

Lophophora-texensis-b

Lophophora texensis seedling that was grown from European seeds.


Lophophora Tiegleri Werd.

W. Taylor Marshall & Thor Methven Bock (1941) Cactacae, p. 138, comment that this “seems to be identical with” Lophophora Lewinii; giving its body color as yellowish-green with less pronounced tufts of wool and fewer & larger tubercles than on a L. Williamsii, and producing white to cream flowers.

L. Chavier (1953) Cactus France 38: 255, under:
Lophophora williamsii et Tiegleri” gives as synonyms: Lewinii, Tiegleri, Ziegleri and says they have a very pale yellow flower.
The photograph shown by Chavier is clearly Lophophora diffusa despite my photocopy being too poor in quality to permit reproduction here.

 

Lophophora sp. Viesca/ Vieska

 

Lophophora viridescens (Halda) Halda

Claimed to be a new “species”, its name appearring in the 1997 Acta Mus. Richnov. Sect. Nat. 4(2): 71. [Information from the 1998 Repertorium Plantarum Succulentarum XLIX]
This is apparently a new name for what was previously presented by Halda as L. diffusa ssp. viridescens and seems unlikely to ever gain any actual recognition as a species. More recently it was recognized as a synonym of Lophophora koehresii according to the International Plant Names Index (IPNI) online.

 

Lophophora williamsii (烏羽玉 / 乌羽玉)

 

Lophophora-williamsii-JimHoggCounty

Lophophora williamsii in Jim Hogg County


 

Lophophora Ziegleri

This is yet another name in horticulture that is typically a synonym for L. diffusa. It seems to have come from Werdermann.
We will recall Pizetti 1985 earlier, under Lophophora lutea, equating L. lutea and L. ziegleri and commenting it to differ from L. williamsii by having “scarcely tuberculate ribs divided by winding grooves, yellowish down, and larger, pale yellow flowers”.
Lophophora ziegleri also seems to fall into the “lutea” (i.e L. diffusa) category but this one clearly is not yellow in its body color.

 

Lophophora Ziegleri

Lophophora Ziegleri

 

Franz Buxbaum 1937 (in his article “Der Formenkreis de Strombocactus“) includes a photograph (fig. 26) from Backeberg taken of Lophophora Ziegleriana that is clearly a Lophophora diffusa and in line with Pizzetti’s comments. This name apparently came from Soulaire.

 

Lophophora-Ziegleriana-Buxbaum-1937-Abb7

Lophophora Ziegleriana
Buxbaum 1937: Figure 7

 

I’m sure you noticed how dramatically those two images differed despite being viewed as synonyms? This illustrates a common problem soon encountered by anyone trying to sort out the different forms in horticulture: Horticultural designations of such peyote “species” and varieties are at the very least unreliably defined and often may be unagreed upon between their many suppliers and growers. Eastern Europe and Japan in particular appear to be intensive centers of not just propagation but selection for unusual characteristics.

 

Crossing experiments within the genus Lophophora

Gerhard Koehres has reported successfully making the following crosses within the Lophophoras (success being judged by the production of seeds that have then been grown into actual seedlings)

Koehres noted these to be self-sterile:
L. alberto-vojtechii
L. diffusa
L. fricii
L. koehresii
L. williamsii El Huizache SLP
L. williamsii Norias del Conde SLP
Koehres listed 25 additional L. williamsii populations that he had determined were self- fertile.
L. williamsii Parras, Coahuila is said to be self fertile despite most people now placing this with L. fricii.

Koehres did not get pollination for L. koehresii using pollen from L. williamsii Huizache but found L. williamsii Huizache could be successfully pollinated using pollen from L. koehresii.

Koehres also successfully pollinated L. koehresii with pollen from L. fricii and L. diffusa. (Kada used a self-fertile L. williamsii and could get no pollination using pollen from L. diffusa, L. fricii and L. koehresii.)

L. fricii was reported by Koehres to be successfully pollinated using pollen from L. koehresii and L. diffusa. (Kada reported failures after 7 attempts involving L. diffusa pollen, 13 with L. williamsii and 18 L. koehresii pollen but reported success for 1 attempt involving a L. williamsii.)

L. diffusa was successfully pollinated by Koehres using pollen from L. koehresii. (Kada has recorded a consistent failure after 11 attempts with pollen from L. fricii, 4 with L. koehresii pollen and 3 using L. williamsii pollen.)

L. koehresii was successfully pollinated by Koehres using pollen from L. diffusa and L. fricii but not with pollen from L. williamsii Huizache (Kada reported successful pollination for 19 attempts using L. fricii pollen but none in 4 tries with L. diffusa pollen and 29 with L. williamsii pollen)

Koehres found that fruit can form from the early flowers within around 8 weeks but for the later blossoms the fruit often do not emerge until the following year. Koehres also commented that the self fertile populations are very uniform in comparison to the self sterile populations which are more highly variable in the shape of the body and the flower.

 

Lophophoras suspected of being hybrids

There are a number of Lophophoras in horticulture that are known to be or suspected to be hybrids. Most intriguing to me are Kada’s Lophophora diffusa X Obregonia denegrii. I look forward to hearing how those seedlings grow up.
At some point an entry on this subject will be created and added but the work is still ongoing.

 

Lophophora-hybrid-form-Anynymous-a

Lophophora-hybrid-form-Anynymous-b

Photos by Anonymous

 

Folk medicinal uses of peyote are many and varied.

 

All species have apparently been employed for medicinal use on a local basis.

A representative few of the most common ones:

Decoction is given for fevers, the root and/or plant chewed and used as a poultice for fractures, infections, large open wounds, snake-bite and scorpion stings.
According to Landes 1963, the Potawatomis in Kansas believed it helpful for rheumatism and paralysis.
More traditional medicinal applications will be found listed within the entry for Lophophora williamsii.

Gymnocalyciums

 This section details only those gymnocalyciums that have been reported to contain mescaline. A more comprehensive treatment of the analytical accounts of the entire genus can be located within Cactus Chemistry By Species_2014_Light which also includes the analytical results listed below.
Some synonyms are included but in most cases the names have been left however they were analyzed as the lumping resulting from the mergers help to obscure some interesting chemistry. These are not being kept separated as an suggestion that they merit recognition, this practice is being employed simply to better preserve and illustrate the published chemical variances. Synonyms are also included so this should be found more helpful than not. Similarly in those analysis involving invalid names, the abandoned names are preserved a,s while those names may be invalid, the analytical results are meaningful as they actually analyzed horticultural plants that physically exist whether they have a good name or not.

 

Gymnocalycium species

 

Gymnocalyciums: Gymnocalycium fleisheranum

Gymnocalycium fleisheranum

 

Commonly called “Chin Cactus” due to the “chin” below each areole.
See examples above and below.

 

Gymnocalyciums: Gymnocalycium triacanthum

Gymnocalycium triacanthum

 

Fruit are typically oblong and red (see image at top of page).
Hortus Third. page 530.

Name is from the Greek:
gymnos “bare” and kalyx “bud”; for its bare flower buds.

 

Gymnocalyciums: Gymnocalycium triacanthum

Gymnocalycium triacanthum

 

See also Backeberg 1959 [3: 1695-1786] (includes many pictures.) and Britton & Rose 1922 [3: 152-166] (includes a number of pictures).

 

Only a representative sampling of the species listed have entries below.

 

Gymnocalyciums: Gymnocalycium asterium

Gymnocalycium asterium

 

A simple list of the mescaline containing Gymnos:

 Gymnocalycium achirasense Till. & Schatzl

 Gymnocalycium asterium Ito (now merged into G. stellatum)

 [Available varieties include:

     v. albispinum

     v. nigrispinum

     v. paucispinum

     v. roseiflorum]

 Gymnocalycium baldianum (Speg.) Spegazzini

 Gymnocalycium calochlorum (Bödeker) Y. Ito

 Gymnocalycium carminanthum Borth & Koop

     [var. minimum is also available.]

 Gymnocalycium comarapense Backeberg

 Gymnocalycium denudatum (L.&O.) Pfeiff.

 Gymnocalycium fleischerianum Backeberg (No reference was included)

 Gymnocalycium gibbosum (Haworth) Pfeiffer

 Gymnocalycium horridispinum Frank

 Gymnocalycium leeanum (Hook.) Britton & Rose

 Gymnocalycium mesopotamicum Kiessling

 Gymnocalycium monvillei (Lemaire) Br. & R.

 Gymnocalycium moserianum Schutz

          [var. laejera is also available.]

 Gymnocalycium netrelianum (Monville) Br. & R.

 Gymnocalycium nigriareolatum Backeberg

 Gymnocalycium oenanthemum Backeberg

 Gymnocalycium paraguayense Schutz

 Gymnocalycium quehlianum (Haage) Berger

   Available varieties include:

     v. albispinum

     v. flavispinus

     v. kleinianum

     v. nigrispinum

 Gymnocalycium ragonesii Castellano

 Gymnocalycium riojense Fric ex. H.Till. & W.Till 

 Gymnocalycium riograndense Cardeñas (now Gymnocalycium pflanzii subsp. zegarrae)

 Gymnocalycium stellatum Spegazzini

 Gymnocalycium striglianum Jeggle

 Gymnocalycium triacanthum Backeberg

 Gymnocalycium uebelmannianum Rausch

 Gymnocalycium valnicekianum Jajó (now Gymnocalycium mostii subsp. valnicekianum)

 Gymnocalycium vatteri Buining (now Gymnocalycium ochoterenae subsp. vatteri)

 

 A summary of the published chemistry can be found at the end of the Gymnocalycium examples below.

 

A handful of Gymnocalycium species:

 

Gymnocalycium baldianum  (Spegazzini) Spegazzini

Carlo Luigi Spegazzini (1905) Anales del Museo Nacional de Buenos Aires. Buenos Aires, ser. 2,  3, 4: 505. as Echinocactus baldianus.
Carlo Luigi Spegazzini (1925) Anales de la Sociedad Cientifica Argentina, 99: 135. as Gymnocalycium baldianum.

 

Gymnocalyciums Gymnocalycium baldianum

Gymnocalycium baldianum

 

Small amounts of mescaline reported.

Origin: Argentina (Andalgalá (mountains east of), Catamarca, Cuesta de Portezuelo, Cuesta de Totoral,Hualfin, Sierra Ancasti,Sierra Graciana, Sierra de Guayamba, Sierra de Narvaes, Sierra de Manchao) Collections have been reported from (500m-)900m-1700m(-2000m)

 Habitat: Among grasses. (IUCN citing Charles 2009)

86. Echinocactus Baldianus Speg. (n. sp.)

Diag. Hybocactus, parvus globoso -depressus, obscure snbcinerascente-viridis; costis 9-11 latis et obtusissimis, sulco acuto profundiusculo limitatis, fere in tuberculis solutis; areolis parvis: aculéis gracilibus saepius 5, ómnibus marginalibus radiantibus adpressis sordide pallideque ciñereis; floribus apicalibus erectis mediocribus extus obscure glauco-viridibus glaberrimis laxe squamosis, squamis sensim in phylla intense purpurea transeuntibis, laciniis stigmaticis brevibus 6 albo-ochroleucis. Speggazini 1905

Depressed-spherical body, to 7 cm in diameter and 10 cm tall. [Eventually to 3.5 inches in diameter; Anderson 1998]
Epidermis is dark greyish to bluish-green.
9-11 ribs, fewer at first, becoming more distinctly tuberculate.
5-7 pinkish-grey to horn-grey or ash-grey, radial spines. More or less appressed or directed laterally, somewhat darker below at first. Spines are weak and flexible; sometimes twisting.
No centrals.
[1.5 inch wide] flowers are variable; lighter or darker red to a more or less blood-red. [White, pink, orange, red or shades in between; borne in spring.
Flowering can occur for several months. Anderson 1998] Pilbeam notes flowers to be variable as pink through red but proposes that hybridization may be responsible for some of the color forms.
Flowers around Christmas in habitat.
Bears dark green elongated fruit.
Backeberg 1977: page 183.
Pilbeam 1995: pages 43-44,  fig 14.

Photos with flower: Anderson 1998: page 80 & Pilbeam 1995: plate 15.

Anderson 1998 claims flowering size (1.5 inches in diameter) can be reached in 12 months from seed and it will handle 10°F briefly.

Listed by IUCN as “Least Concern” as, despite a restricted range and pressure from collection activity, it has a continuous range. Local collection and fire are said to be the primary threats.
Perea, M. & Trevisson, M. 2013. Gymnocalycium baldianum. The IUCN Red List of Threatened Species. Version 2014.2. <www.iucnredlist.org>

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

Gymnocalycium calochlorum  (Bödeker) Y.Itô

Friedrich Bödeker (1932) Monatsschrift der Deutschen Kakteen-Gesellschaft, 4: 260. as Echinocactus calochlorus.
Yoshi Itô in John Borg  (1952) Cacti, 90. as Gymnocalycium calochlorum.

 

Gymnocalyciums: Gymnocalycium calochlorum

Gymnocalycium calochlorum

 

Small amounts of mescaline reported.

Origin: Argentina (The original collection did not include a locality. Reported to occur at Cordoba, Nono, Villa Bura Borchero, La Mudana, Las Rabonas. Collections have been recorded from 900 and 1000m according to Pilbeam; 800-1500m according to IUCN.)

Habitat:  “often buried in crumbling granite, where it can be difficult to find if not in flower or fruit (Charles 2009). It grows in high-altitude grasslands and chaco forest.” IUCN

Cushion forming plant with depressed-spherical cushion-like single heads.
Bodies are grey-green to blue-green to around 6 cm diameter and to 4 cm high.
Around 11 tuberculate ribs with creamy-white felted round areoles.
Up to 9 closely set whitish to pale pinkish-brown radial spines that are thin, wispy, rough, appressed, more or less curving; to 9(-12.5) mm long. No centrals.
Pale pink flowers to 6 cm long, opening only moderately. Produced only from the youngest areoles. Petals are not revolute.
Floral tube is long and of a lighter green according to Backeberg or bluish according to Pilbeam.
Fruit is bluish-green and long-ovoid.
Backeberg 1977 page 184,
and Pilbeam 1995: pages 52-53, Photos as fig. 21 and plates 25 (flowering) & 26 (in habitat),
and Pizzetti 1985 entry #117 (includes picture)

Listed by the IUCN as a species of “Least Concern” due to a perception of it being locally abundant and resistant to disturbances.  The IUCN says both “It is very widespread…” and  “…the range is not particularly wide,…”
Demaio, P. & Trevisson, M. 2013. Gymnocalycium calochlorum. The IUCN Red List of Threatened Species. Version 2014.2.

 

Gymnocalyciums: Gymnocalycium calochlorum

Gymnocalycium calochlorum

 

Recognized varieties mentioned by Pizzetti (only the first is respected by Pilbeam):
 var. proliferum; with larger darker or glacous stems, flowers that open widely and flower segments that curve outward (may be
brownish-white, pink or white; often pink at base.)

 var. roseiacanthum; a smaller variety (half the size of the
species). Glaucous green with yellowish rounded areoles and contorted
pinkish spines. Flowers are large and white with red bases. These
plants occur in the Sierra de Córdoba.

Pizzetti recommends protection from intense cold and shady positions when the sun is hottest. Prefers cool weather.

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

 

Gymnocalycium gibbosum (Haworth) Pfeiffer

Adrian Hardy Haworth (1816) Botanical Register; 2: 137. as Cactus gibbosus.
Louis Pfeiffer ex Ludwig Mittler (1844) Taschenbuch für Cactusliebhaber. Leipzig, 2: 124. as Gymnocalycium gibbosum.

 

Gymnocalyciums: Gymnocalycium gibbosum

Gymnocalycium gibbosum

 

Presence of mescaline reported but unconfirmed.

Origin: Southern Argentina. [Río Chubut, Río Negro and Chubul Provinces:
Lat. 40-45o S.; La Plata, Mendoza, San Luis] 

Pilbeam 1995 mentions the species as being widespread in Argentina “covering a great deal of Patagonia, the provinces La Pampa and Buenos Aires and as far west as Mendoza and reported from southern Argenia, at Chubut, Rio Negro and Santa Cruz; recently by Pilz from Argentina, Abra de la Ventura.” Collections have been reported from 400-500m.
The IUCN cites Hunt et al. 2006 as giving occurrences “at elevations of 0 to 1,000 m“.

Habitat:monte shrubland and patagonian steppe (estepa patagónica)” “likes the sandy or gravelly alluvial soil along the Río Negro and Río Colorado, where it grows under bushes and other plants (Charles 2009).” IUCN

gymnocalyciums: Haworth 1816 BotanicalRegister, 137, diagnosis of Cactus gibbosus

Haworth 1816 Botanical Register, 2: 137, Latin diagnosis of Cactus gibbosus

Solitary glaucous, dull or dark (bluish)green well-armed stems, (Pilbeam: dark green to blue-black or greyish-green”) later sooty or brownish-green, to 10 [-24] inches (12-15 cm) high and 6 inches (10-12 cm) thick. Starts
globular then becomes more cylindrical.

Areoles set 1.5-2 cm apart.
12-14 [-19] strongly tubercled, straight, notched and rounded ribs with lightly sunken round areoles with greyish (Pilbeam describes as brownish-cream) wool. Prominent chins below areoles. 
7-12 radial spines, stiff, spreading, needle-shaped to awl-shaped, typically straight but  may be slightly curved, and mostly brown. (or light brown with a reddish base.) Up to 3.5 cm long. Nearly spineless at apex.
Can have 1-3 central spines (0-6 according to Pilbeam) but usually they are absent. When present they are often not readily distinguishable from the radial spines.
White (to faintly pink or reddish) flowers to 2-1/2 [to 2-3/4] inches long (6 cm long opening to 6 cm wide). Inner petals are lanceolate. Petals shaded from white to pink. Stamens and stigma are white; stigma has 12 yellowish lobes.
Diurnal flowers in summer.
Produced a club-shaped short, dark-green fruit.
Seldom branches unless injured or grafted, but some varieties do branch freely.
page 530 in Hortus Third
and Backeberg 1977: page 186
and Borg 1937: page 239
and Innes & Glass 1991: page 127 [Includes
picture of flowers]

and Lamb & Lamb 1971: page 654
and Pilbeam 1995: pages 73-76, fig. 37 & 38, plate 47
and Pizzetti 1985 Entry #119. (has color photo)


Listed by IUCN as a species of “Least Concern” due to having no major threats and having a wide range in which it occurs abundantly.   ListedIts range includes protected areas.
Demaio, P. & Trevisson, M. 2013. Gymnocalycium gibbosum. The IUCN Red List of Threatened Species. Version 2014.2.

 

Gymnocalyciums: Gymnocalycium gibbosum

Gymnocalycium gibbosum

Hortus recognizes:
 cv. Ferox has more numerous spines

 cv. Nigrum has very dark spines

 cv. Schlumbergii has more numerous spines that are stiff pinkish red to amber yellow.

     page 530 in Hortus Third

 

Gymnocalyciums: Gymnocalycium gibbosum var. schlumbergii

Gymnocalycium gibbosum cv. Schlumbergii

 

Many varieties exist in both the wild and in cultivation. First described in 1812. Has been known by many names over the years due to its varieties.
 Entry #119 in Pizzetti 1985

Pilbeam 1995 mentioned that “Nearly 30 varietal names have been allocated to this species.”

 cv. Nobile is said to have a larger sperical stem and longer overlapping spines; white with red base.

 Borg 1977 mentions var. caespitosum Hort., var. ferox Lab., var. leucacanthum K.Schum., var. Schlumbergeri K.Schum., var. nobilis K.Schum., and var. leonensis Hildm.

 Backeberg 1977 mentions var. leucodictylon (K.Schum.) Y.Ito, var. nigrum Backbg, and var. nobile (Haw.) Y.Ito.

 var. rostratum is also commercially available. It is described as having a dark grey stem.

IPNI lists:

v. borthii

v. brachypetalum

f. cerebriforme

var cerebriformis

var. chubutense

ssp ferdinandii

ssp. ferox

ssp. gastonii

var. nigrum

ssp. radekii

ssp. radovanii

This has always been a popular plant and is widely grown.

Innes & Glass recommend indirect light and a 50°F minimum temperature.
Pizzetti describes it as cold tolerant but taking no frost, tolerant of heat and requiring some sun.
I’ve found it to be able to survive frost but typically scarring badly afterwards. In Texas,  it was repeatedly attacked by thrips.

[See also Backeberg 1959 [3: 1752-1755] (includes pictures of several varieties, also fig. 1687, page 1756 and fig. 1688, page 1757.) and Backeberg 1977 page 186 and Britton & Rose 1922 [3: 158-159] (picture in fig. 166 page 157.]

 

Reported analysis:

92.1% water by weight (pH of juice: 4.6-5) Herrero-Ducloux 1930b

 Mescaline, Anhalamine & Lophophorine

 (all identified by chemical tests)
Mata & McLaughlin 1982 cited Herrero-Ducloux 1930b and Reti 1950 (who also cited Herrero-Ducloux)

 [Ott 1993, page 114, cites Der Marderosian 1966; mentioning this is a simple listing of mescaline species, rather than a primary source.]

 Štarha et al. 1997 did not observe mescaline to be present. See the alkaloid list further below.

Reti 1950 and Chemical Abstracts 1930 says that Enrique Herrero-Ducloux 1930b isolated small amounts of alkaloids from this cactus which he noted gave chemical reactions similar to those of mescaline [Colorless birefringent crystals, n 1.544, mp 160-162°], and what he thought was probably a mixture of anhalonine and lophophorine [Colorless birefringent crystals, n 1.552, mp 188-190°].

No definitive proof was done and apparently only Dr. Štarha has cared enough to follow through during the 70 years which have passed.

 

Gymnocalyciums: Gymnocalycium gibbosum

Gymnocalycium gibbosum

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

 

 

 

 Gymnocalycium leeanum (Hooker) Britton & Rose

William Jackson Hooker (1845) Botanical Magazine; or, Flower-Garden Displayed…, 71: t. 4184, as Echinocactus leeanus
Nathaniel Lord Britton & Joseph Nelson Rose (1922) Cactaceae, 3: 154, fig. 164, as Gymnocalycium leeanum
Wolfgang Papsch (2000) Gymnocalycium, 13 (3): 371. as Gymnocalycium reductum var. leeanum

 

Gymnocalyciums: Gymnocalycium-leeanum-HBG

Gymnocalycium leeanum

Presence of mescaline reported but unconfirmed.

Origin: Argentina and Uruguay

Habitat: Grasslands in rocky places and on hills. Also in organic materials among rocks. Sometimes under shrubs.  IUCN citing Charles 1009.

Echinocactus Leeanus: depresso-globosus obscure subglauco-v i r i d i s tuberculis subhemisphaericis majusculis obtuse hexahedris mammiformibus confluentibus, in series irregulares subverticales dispositis, areolis ovalibus tomentosis, aculeis subgracilibus quorum subdecem patentibus rectiusculis cum unieo centrali porrecta v i x majore, floribus majusculis pallide flavescentibus. (Hooker 1845)

Bluish-green stems ~3 inches thick. Depressed to spherical. [“rather flattened” Innes & Glass]
~16 ribs, irregular, strongly tubercled (more or less six-sided)
Radial spines about 7-10(-11) needle-shaped, thin, appressed, 1/2 inch long.
Central spine 1 straight and directed outward. Not always present.
Flowers pale yellow [“yellowish-white, 2-2½ in long and high” Innes & Glass] to 2 inches (unisexual).
Blooms in early summer.
Backeberg 1959 [3, pages 1735-1737, (includes pictures of two varieties.)
and Backeberg 1977: page 188
and Britton & Rose 1922: page 154 (picture in fig. 164, page 156)
and Hortus Third: page 530.
and Innes & Glass 1991: page 128 (includes picture of species and var. netrelianum, both with flower)

[Schuster 1990 has photo on p. 128.] 

 var. brevispinum Backeberg is described from Maldonado, Uruguay. It is said to have much shorter and straighter spines.

var. netrelianum (Monv.) Backeb, (= G. netrelianum (Monv.) Britt. and Rose Hortus Third Page 530. [see entry of G. netrelium]) Backeberg lists separately; G. leeanum var. netrelianum (Uruguay): tubercle said to be broader than high, spines longer [5-8, centrals absent; Backeberg 1977].

 Innes & Glass describe var. netrelianum as being slightly more globular with fewer, shorter spines (5-7), usually no centrals and having citron yellow flowers 1.5 to 1.75 inches in diameter.

Listed by IUCN as a species of “Least Concern” due to having a fairly wide range that includes protected areas. Its major threats appear to be from human activity and grazing.
Kiesling, R. 2013. Gymnocalycium reductum. The IUCN Red List of Threatened Species. Version 2014.2. www.iucnredlist.org.

Innes & Glass recommend slight shade and a minimum of 50°F.

 

Reported chemistry of Gymnocalycium leeanum:

 Tyramine (gc),

 N-Methyl-tyramine (gc),

 Hordenine (ms, gc),

 Mescaline (chemical tests; unconfirmed),

 Anhalonine (chemical tests)

 and Lophophorine (chemical tests)

     Mata & McLaughlin 1982 citing DeVries et al. 1971 and Herrero-Ducloux 1930b (Apparently DeVries and coworkerrs did not find mescaline, finding the first three phenethylamines instead.
The UT library is missing the first several issues of both journals. It is unknown to me what variety either DeVries or Herrero-Ducloux used or whether this was either noted or even taken into account.)

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

 

 

 

 Gymnocalycium multiflorum (Hooker) Britton & Rose

William Jackson Hooker (1845) Curtis‘ Botanical Magazine, 71: t. 4181, as Echinocactus multiflorus.
Nathaniel Lord Britton & Joseph Nelson Rose (1918) Addisonia, 3: 5, pl. 83, as Gymnocalycium leeanum.
[Now considered lumped as a synonym with Gymnocalycium monvillei
i.e. Nathaniel Lord Britton & Joseph Nelson Rose (1922) Cactaceae, 3: 161, as Gymnocalycium monvillei Pfeiff. ex Britton & Rose.]

 

Gymnocalyciums: Gymnocalycium-multiflorum-flower

Gymnocalycium multiflorum

Gymnocalycium: Gymnocalycium multiflorum Hooker 1845

gymnocalyciums; Gymnocalycium multiflorum Latin diagnosis

 

Herrero-Ducloux 1932a reported recovering small quantities of a ‘mescaline-like’ alkaloid from this species. Reti notes as occuring in Cordoba and Catamarca in Argentina, also in Brazil, Uruguay and Paraguay.
This species is fairly frequent in cactus collections and is readily available commercially. It is one of the more easily
recognizable Gymnocalycium species.

  This report is unconfirmed as it apparently lacks any further work. This species is regarded to be a synonym of Gymnocalycium monvillei which HAS been reported to contain mescaline. See more details under that name.

 

Gymnocalyciums: Gymnocalycium multiflorum

Gymnocalycium multiflorum

 

  G. monvillei is listed as being a species of “Least Concern” by the IUCN.
Demaio, P., Lowry, M., Trevisson, M. & Méndez, E. 2013. Gymnocalycium monvillei. The IUCN Red List of Threatened Species. Version 2014.2. <www.iucnredlist.org>. 

 

External resources:

Gymnocalycium.free.fr

 

 

 Gymnocalycium riograndense Cardeñas

Martin Cárdenas (1958) Kakteen und Andere Sukkulenten, 9: 24, as Gymnocalycium riograndense.
Graham Charles (2005) Cactaceae Systematics Initiatives: Bulletin of the International Cactaceae Systematics Group, 20: 18, as Gymnocalycium pflanzii subsp. zegarrae .

 

Gymnocalyciums: Gymnocalycium-riograndense

Gymnocalycium riograndense

 

Mescaline reported in small amounts.

Origin: Bolivia. Along Rio Grande “between the Cordillera de Cochabamba and the plano of the Rio Guarayos”. Pizzetti 1985.

Habitat: (As G. pflanzi) growing in deep rich soils in sunny rocky areas on slopes or under spiny shrubs. Cactus-Art.

Plants broadly spherical, to 6 cm high, to 20 cm diameter [2-1/2 inches tall and up to 8 inches in diameter]. Initially remaining simple but offshooting from base as adults.
Body is glossy, dark green. [The plant in Pizzeti’s photo is not dark]
Around 13 ribs, to 3 cm wide; Tubercles are obtusely conical, separated by transverse dividing lines; a slender conical beak is below the tubercles.
Round areoles covered with white felt when young but later becoming bare.
8(-9) thin-subulate radial spines, to 2.5 cm long; slightly curving.
They are stiff, grey, black-tipped, brownish below. Later becoming brown all over.
No centrals.
Beaker-shaped flowers are white, with a bluish-red throat.
Backeberg 1977 page 193
and Pizzetti 1985 Entry #126 (Has picture.)

Pizzetti recommends mild winter heat.

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

 

 

 

 Gymnocalycium valnicekianum Jajó

Bedrich Jajó (1934) Kaktusář; odborný měsičnik. Astrophytum spolek pestitelu kaktusu a jinych sukkulentu. Brno, 5: 73. as Gymnocalycium valnicekianum.
Massimo Meregalli & Graham J. Charles (2008) Cactaceae Systematics Initiatives: Bulletin of the International Cactaceae Systematics Group, 24: 25.  as Gymnocalycium mostii subsp. valnicekianum

 

Gymnocalyciums: Gymnocalycium valnicekianum

Gymnocalycium valnicekianum

 

Mescaline reported in small amounts.

Origin: Argentina (Córdoba & El Zapata). (500-)900-1300(-1500)m.

Habitat: Grows among tall grasses in mossy cracks and cavities in rocky cliffs. Cactus-Art.

Broadly spherical at first, later growing spherical to elongated; up to 30 cm high and 18 cm in diameter, sometimes offsetting. Pilbeam notes it to grow larger in cultivation.
Epidermis is smooth and dark grass-green.
Around 10(-13) ribs with swollen, rounded, chin-like tubercles and elliptical areoles with light grey wool.
Spine are variable in number, 7-15 or more. They are whitish-grey to
dirty white, and thickened below. 1-6 central spines. Spines have darker tips at first.”The plants in habitat are each one different from its neighbours! Some had strong spines others weak, curly, straight, long or short ones and in all different combinations” Cactus-Art

Flowers are white with a reddish throat and reddish striped outer petals; 5 cm dia.
Seeds are matt black.
Backeberg 1977 page 195
Pilbeam 1995: 151-152 (Fig. 97)

 Koehres offers var. polycentrale

Schütz also distinguishes var. centrispinum.

 

IUCN lists Gymnocalycium mostii as a species of “Least Concern” due to there being abundance of plants, no significant threats and occurrence in a protected range.
Demaio, P. & Trevisson, M. 2013. Gymnocalycium mostii. The IUCN Red List of Threatened Species. Version 2014.2. <www.iucnredlist.org>. 

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

 

 

 

Gymnocalycium vatteri  Buining

Albert Frederik Hendrik Buining (1950) Succulenta, 66 (1950), as Gymnocalycium vatteri.
Wolfgang Papsch (1993) Gymnocalycium, 6 (1): 79, as Gymnocalycium ochoterenae subsp. vatteri, spelling as ‘ochoterenai‘.
Pilbeam 1995 dismissed the merger by Papsch and a new proposed variety of vatteri, also by Papsch, on the basis of the species known high degree of variability.

 

Gymnocalyciums: Gymnocalycium vatteri

Gymnocalycium vatteri

Mescaline has been reported in small amounts.

Origin: Argentina (Córdoba, Sierra Grande, near Nono). 800-1000m.

Habitat: Amidst rocks and grasses.

Buining 1950 Succulenta, 66, Latin diagnosis of G. vatteri

Buining 1950 Succulenta, 66, Latin diagnosis of G. vatteri

 

Solitary typically but offesetting around the base with age.
Starting flattened hemisperical at first, growing to 4 cm high and 9 cm in diameter.

Epidermis is matt, olive green.
(8-)11(-16), ribs; up to 2.5 cm across and uo to 12 mm high.
Tubercles are swollen and humped, possessing an acute transverse notch beneath.
Areoles are somewhat depressed, ~5 mm wide with grey wool.
3(-5) [1 or 2, sometimes 3 in Pilbeam) Radial spines are appressed or projecting; Pilbeam notes them standing out in youth but curving towards the body with age. They are up to 2 cm and thicker at their base; horn-colored or a dirty darker color.
Spines on the lower part of the plant are variable in both length and curvature but are fairly stout and also sometimes projecting; other spines may be bent and closely appressed.
White flower with a reddish throat in Backeberg and a brownish-grey throat in Pilbeam. 5 cm. long and 4 cm in diameter.
Glossy, light brown seeds; 1 mm in length.
There is a form with more conspicuously claw-like spines but they can also be irregularly interlacing.
Backeberg 1977: page 195 (Fig. 146)
Pilbeam 1995: 152-153 (Fig. 98)

 

Hardy to -5°C. Light shading is recommended. Cactus-Art. Pilbeam describes as slow growing.

 

Gymnocalyciums: Gymnocalycium vatteri

Gymnocalycium vatteri

 

Koehres offers var. cereiformis

 

Gymnocalyciums: Gymnocalycium vatteri

Gymnocalycium vatteri

 

 

External resources:

Cactus-Art

Gymnocalycium.free.fr

 

 

 All of Dr. Štarha’s values for the next section were determined by GC and/or GC-MS. All of the plants that he analyzed were grown from seed in Czechoslovakian greenhouses.

 

Reports of mescaline within the Gymnocalycium species

Synonyms are often mentioned but expect them to keep changing as long as humans keep trying to categorize plants.

Gymnocalyciums: Gymnocalycium achirasense flower

Gymnocalycium achirasense

Gymnocalycium achirasense Till & Schatzl

 Tyramine (0.00159% [± 0.00008])

 N-Methyltyramine (0.00045% [± 0.00006])

 Hordenine (0.00129% [± 0.00006])

 Mescaline (0.00007% [± 0.00001])

 N-Methylmescaline (0.00013% [± 0.00001])

 N,N-Dimethylmescaline (0.00025% [± 0.00002])

 Anhalamine (0.00097% [± 0.00001])

     Štarha et al. 1998 (% by fresh weight)

 [All of Starha’s values in this genus are expressed as % by fresh weight.]

 
Gymnocalyciums: Gymnocalycium-monvillei-Paraguay-6848-EWerdermann-sn-HBG-2006

Gymnocalycium monvillei

 

Gymnocalyciums: Gymnocalycium-asterium-v-paucispinum

Gymnocalycium asterium var. paucispinum

Gymnocalycium asterium Ito

(now merged with Gymnocalycium stellatum)

 Tyramine (0.00089% [± 0.00013])

 N-Methyltyramine (0.00012% [± 0.00004])

 Hordenine (0.00105% [± 0.0001])

 Mescaline (0.00013% [± 0.00002])

 N-Methylmescaline (0.00031% [± 0.00004])

 N,N-Dimethylmescaline (0.0005% [± 0.00004])

 O-Methylanhalidine (0.00011% [± 0.00002])

 Anhalidine (Trace)

 Anhalamine (0.00054% [± 0.00002])

 Anhalonidine (Trace)

 Pellotine (Trace)

 Anhalonine (Trace)

 Lophophorine (Trace)

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium-asterium

Gymnocalycium asterium

Compare the analysis of G. asterium to that of G. stellatum.

Gymnocalyciums: Gymnocalycium-baldianum-flowera

Gymnocalycium baldianum

Gymnocalycium baldianum (Spegazzini) Spegazzini

  Tyramine (less than 0.0001%)

  Hordenine (approximately 0.001%)

  Mescaline (less than 0.0001%)

  Anhalinine (less than 0.0001%)

  Anhalidine (less than 0.0001%)

  Anhalamine (less than 0.0001%)

  Anhalonidine (less than 0.0001%)

  Pellotine (less than 0.0001%)

  Anhalonine (less than 0.0001%)

  Lophophorine (less than 0.0001%)

      Štarha 1996

 Reported to contain Betalains as pigments. Wohlpart & Mabry 1968
cited Dreiding 1961

 

Gymnocalyciums: Gymnocalycium calochlorum

Gymnocalycium calochlorum

Gymnocalycium calochlorum (Boedecker) Y.Itô

  Mescaline (between 0.0001-0.001%)

 Tyramine (between 0.0001-0.001%)

  N-Methyltyramine (less than 0.0001%)

  Hordenine (approximately 0.001%)

  N-Methylmescaline (less than 0.0001%)

  Anhalinine (less than 0.0001%)

  Anhalidine (less than 0.0001%)

  Anhalamine (less than 0.0001%)

  Anhalonidine (between 0.0001-0.001%)

  Pellotine (less than 0.0001%)

      Štarha 1996 (% by fresh weight)

Gymnocalyciums: Gymnocalycium calochlorum

Gymnocalycium calochlorum

Gymnocalycium carminanthum Borth & Koop

 Tyramine (0.00007% [± 0.00003])

 N-Methyltyramine (Trace)

 Hordenine (0.00016% [± 0.00005])

 Mescaline (0.00006% [± 0.00005])

 N-Methylmescaline (Trace)

 N,N-Dimethylmescaline (0.00008% [± 0.00002])

 O-Methylanhalidine (0.00007% [± 0.00002])

 Anhalamine (0.00088% [± 0.00003])

 Anhalonidine (Trace)

     Štarha et al. 1998 (% by fresh weight)

 

Gymnocalycium comarapense Backeberg

 Tyramine (Between 0.001-0.001%)

 N-Methyltyramine (Less than 0.001%)

 Hordenine (Less than 0.001%)

 Mescaline (Less than 0.001%)

 N-Methylmescaline (Less than 0.001%)

 Anhalamine (Less than 0.001%)

 Pellotine (Less than 0.001%)

     Štarha 1995 (% by fresh weight)

Gymnocalyciums: Gymnocalycium-denudatum-HBG

Gymnocalycium denudatum

Gymnocalycium denudatum (Link & Otto) Pfeiffer

 Tyramine (0.00066% [± 0.00006])

 N-Methyltyramine (0.00061% [± 0.00002])

 Hordenine (0.00052% [± 0.00005])

 Mescaline (Trace)

 N-Methylmescaline (0.00008% [± 0.00001])

 N,N-Dimethylmescaline (0.00073% [± 0.00005])

 O-Methylanhalidine (0.00025% [± 0.00003])

 Anhalinine (0.00006% [± 0.00002])

 O-Methylanhalonidine (0.0001% [± 0.00002])

 Anhalidine (Trace)

 Anhalamine (0.00048% [± 0.00002])

 Anhalonidine (Trace)

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium fleisheranum

Gymnocalycium fleisheranum

Gymnocalycium fleischerianum Backeberg

(Now considered

  Tyramine (0.0001-0.001% dry wt.)

  N-Methyltyramine (0.001% dry wt.)

  Hordenine (0.0001-0.001% dry wt.)

  Mescaline (0.0001-0.001% dry wt.)

  N-Methylmescaline (0.0001-0.001% dry wt.)

  N,N-Dimethylmescaline (0.0001-0.001% dry wt.)

  Anhalamine (0.0001-0.001% dry wt.)

  Anhalonidine (0.00001-0.0001% dry wt.)

    Štarha 2001c did not include a citation for this information. (G. fleischerianum is included only in his table on page 91 and not in the by species breakdown)

Gymnocalyciums: Gymnocalycium fleisheranum

Gymnocalycium fleisheranum

 

Gymnocalyciums: Gymnocalycium gibbosum

Gymnocalycium gibbosum

Gymnocalycium gibbosum (Haworth) Pfeiffer

 92.1% water by weight (pH of juice: 4.6-5.0) Herrero-Ducloux 1930b

  Tyramine (Less than 0.0001%) Štarha et al. 1997

  N-Methyltyramine (approximately 0.001%) Štarha et al. 1997

  Hordenine (approximately 0.001%) Štarha et al. 1997

  Mescaline (unquantified and tentatively identified. Colorless birefringent crystals, n 1.544, mp 160-162o were claimed to show the “reactions of mescaline”) Herrero-Ducloux 1930b. Mescaline was NOT observed by Štarha
et al. 1997.

 N-Methylmescaline (Between 0.0001-0.001%) Štarha et al. 1997

  N,N-Dimethylmescaline (Less than 0.0001%) Štarha et al. 1997

  O-Methylanhalidine (approximately 0.001%) Štarha et al. 1997

  Anhalinine (approximately 0.001%) Štarha et al. 1997

  O-Methylanhalonidine (approximately 0.001%) Štarha et al. 1997

  Anhalidine (Between 0.0001-0.001%) Štarha et al. 1997

  Anhalamine No quantification (or accurate identification) attempted; Herrero-Ducloux 1930b [Our source was Reti; CA gives this as Anhalonine. I presently lack the primary paper.] (approximately 0.001%) Štarha et al. 1997

  Anhalonidine (Less than 0.0001%) Štarha et al. 1997

  Pellotine (Between 0.0001-0.001%) Štarha et al. 1997

  Anhalonine (Between 0.0001-0.001%) Štarha et al. 1997

  Lophophorine No quantification (or accurate identification) attempted; Herrero-Ducloux 1930b. Between 0.0001-0.001%: Štarha et al. 1997

 Gymnocalycium horridispinum Frank

  Mescaline (between 0.0001-0.001%)

  Tyramine (approximately 0.001%)

  N-Methyltyramine (less than 0.0001%)

  Hordenine (approximately 0.001%)

  N-Methylmescaline (less than 0.0001%)

  Anhalinine (less than 0.0001%)

  Pellotine (less than 0.0001%)

      Štarha 1996 (% by fresh weight)

Gymnocalyciums: Gymnocalycium leeanum

Gymnocalycium leeanum

Gymnocalycium leeanum (Hooker) Br. & R.

[Now considered

  Anhalonine (Unconfirmed) Herrero-Ducloux 1930b

 Not observed by DeVries et al. 1971

  Hordenine (%?) DeVries et al. 1971

  Lophophorine (Unconfirmed) Herrero-Ducloux 1930b

 Not observed by DeVries et al. 1971

  Mescaline (Unconfirmed) Herrero-Ducloux 1930b

 Not observed by DeVries et al. 1971

  N-Methyltyramine  (?%) DeVries et al. 1971

  Tyramine (0.00583%) DeVries et al. 1971

Gymnocalyciums: Gymnocalycium leeanum

Gymnocalycium leeanum

 

 

Gymnocalyciums: Gymnocalycium-mesopotamicum-HBG

Gymnocalycium mesopotamicum

 Gymnocalycium mesopotamicum Kiessling

 Tyramine (Trace)

 N-Methyltyramine (Trace)

 Hordenine (Trace)

 Mescaline (Trace)

 N-Methylmescaline (Trace)

 N,N-Dimethylmescaline (0.00279% [± 0.0005])

 Anhalamine (0.0019% [± 0.00028])

 Anhalonidine (0.00005% [± 0.00003])

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium-monvillei-Paraguay-6848-EWerdermann-sn-HBG-2006

Gymnocalycium monvillei

 Gymnocalycium monvillei (Lemaire) Britton & Rose

 Tyramine (Between 0.0001-0.001%)

 N-Methyltyramine (Between 0.0001-0.001%)

 Hordenine (Approximately 0.001%)

 Mescaline (Less than 0.0001%)

 N-Methylmescaline (Less than 0.0001%)

 N,N-Dimethylmescaline (Less than 0.0001%)

 O-Methylanhalidine (Less than 0.0001%)

 Anhalinine (Less than 0.0001%)

 O-Methylanhalonidine (Less than 0.0001%)

 Anhalidine (Less than 0.0001%)

 Anhalamine (Less than 0.0001%)

 Anhalonidine (Between 0.0001-0.001%)

 Pellotine (Between 0.0001-0.001%)

 Anhalonine (Between 0.0001-0.001%)

 Lophophorine (Less than 0.0001%)

     Štarha et al. 1997 (% by fresh weight)

 

Gymnocalycium moserianum Schutz

 Tyramine (0.00077% [± 0.0001])

 N-Methyltyramine (0.0001% [± 0.00003])

 Hordenine (0.00011% [± 0.00003])

 Mescaline (0.00007% [± 0.00001])

 N-Methylmescaline (0.00151% [± 0.00015])

 N,N-Dimethylmescaline (0.00071% [± 0.00006])

 O-Methylanhalidine (0.00007% [± 0.00001])

 Anhalinine (0.00007% [± 0.00001])

 O-Methylanhalonidine (0.00007% [± 0.00001])

 Anhalidine (0.00007% [± 0.00001])

 Anhalamine (0.00215% [± 0.00014])

 Anhalonidine (0.00014% [± 0.00003])

 Pellotine (0.00012% [± 0.00003])

 Anhalonine (Trace)

 Lophophorine (Trace)

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium multiflorum

Gymnocalycium multiflorum

Gymnocalycium multiflorum

(Now considered to be at least partially a synonym with Gymnocalycium monvillei.)

Herrero-Ducloux 1932a reported recovering small quantities of a ‘mescaline-like’ alkaloid from this species.

This report for this cactus species presently lacks confirmation.

 

 Gymnocalycium netrelianum Britton & Rose

 Tyramine (Less than 0.001%)

 Hordenine (Between 0.0001-0.001%)

 Mescaline (Between 0.0001-0.001%)

 N-Methylmescaline (Less than 0.001%)

 Pellotine (Less than 0.001%)

     Štarha 1995a (% by fresh weight)

Gymnocalycium nigriareolatum Backeberg

 Tyramine (0.00047% [± 0.00005])

 N-Methyltyramine (0.00008% [± 0.00002])

 Hordenine (0.0014% [± 0.00006])

 Mescaline (0.00006% [± 0.00002])

 N-Methylmescaline (0.00006% [± 0.00001])

 N,N-Dimethylmescaline (0.00009% [± 0.00002])

 O-Methylanhalidine (0.00012% [± 0.00006])

 Anhalamine (0.00019% [± 0.00004])

 Anhalonidine (0.00008% [± 0.00002])

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium-oenanthemum

Gymnocalycium oenanthemum

Gymnocalycium oenanthemum Backeberg

 Tyramine (Between 0.0001-0.001%)

 N-Methyltyramine (Less than 0.0001%)

 Hordenine (approximately 0.001%)

 Mescaline (Less than 0.0001%)

 N-Methylmescaline (Less than 0.0001%)

 N,N-Dimethylmescaline (Less than 0.0001%)

 O-Methylanhalidine (Less than 0.0001%)

 O-Methylanhalonidine (Less than 0.0001%)

 Anhalidine (Less than 0.0001%)

 Anhalamine (Less than 0.0001%)

 Anhalonidine (Between 0.0001-0.001%)

 Pellotine (Between 0.0001-0.001%)

 Anhalonine (Less than 0.0001%)

 Lophophorine (Less than 0.0001%)

      Štarha et al. 1997 (% by fresh weight)

Gymnocalycium paraguayense Schutz

 Tyramine (0.00047% [± 0.00004])

 N-Methyltyramine (0.00104% [± 0.00014])

 Hordenine (0.00043% [± 0.00008])

 Mescaline (0.00011% [± 0.00006])

 N-Methylmescaline (0.00041% [± 0.0001])

 N,N-Dimethylmescaline (0.00427% [± 0.00032])

 Anhalamine (0.00505% [± 0.0005])

 Anhalonidine (0.00017% [± 0.00006])

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium-quehlianum

Gymnocalycium quehlianum

Gymnocalycium quehlianum (Haage) Berg.

  Tyramine (Between 0.0001-0.001%)

  N-Methyltyramine (Between 0.0001-0.001%)

  Hordenine (approximately 0.001%)

  Mescaline (Less than 0.0001%)

  N-Methylmescaline (Less than 0.0001%)

  N,N-Dimethylmescaline (Less than 0.0001%)

  Anhalinine (Less than 0.0001%)

  O-Methylanhalonidine (Between 0.0001-0.001%)

  Anhalonidine (Less than 0.0001%)

  Pellotine (Less than 0.0001%)

  Anhalonine (Less than 0.0001%)

  Lophophorine (Less than 0.0001%)

      Štarha et al. 1997 (% by fresh weight)

 Gymnocalycium ragonesii Cast.

 Tyramine (0.00009% [± 0.00002])

 N-Methyltyramine (0.00005% [± 0.00001])

 Hordenine (0.0035% [± 0.00014])

 Mescaline (Trace)

 N-Methylmescaline (Trace)

 N,N-Dimethylmescaline (Trace)

 O-Methylanhalidine (0.00048% [± 0.00003])

 Anhalinine (0.00109% [± 0.00018])

 O-Methylanhalonidine (0.00007% [± 0.00001])

 Anhalidine (0.00006% [± 0.00001])

 Anhalonidine (Trace)

 Pellotine (Trace)

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium riograndense

Gymnocalycium riograndense Cardeñas

(Now Gymnocalycium pflanzii subsp. zegarrae)

Tyramine (Between 0.0001-0.001%)

 N-Methyltyramine (Less than 0.001%)

 Hordenine (Less than 0.001%)

 Mescaline (Between 0.0001-0.001%)

 N-Methylmescaline (Less than 0.001%)

 Anhalinine (Less than 0.001%)

 Anhalidine (Less than 0.001%)

 Anhalonidine (Less than 0.001%)

 Pellotine (Less than 0.001%)

 Anhalonine (Less than 0.001%)

 Lophophorine (Less than 0.001%)

     Štarha 1995a (% by fresh weight)

Gymnocalycium riojense Fric ex H.Till & W.Till

  Tyramine (0.001% dry wt.)

  N-Methyltyramine (0.00001-0.0001% dry wt.)

  Hordenine (0.001% dry wt.)

  Mescaline (0.00001-0.0001% dry wt.)

  N-Methylmescaline (0.00001-0.0001% dry wt.)

  Anhalinine (0.00001-0.0001% dry wt.)

  O-Methylanhalonidine (0.00001-0.0001% dry wt.)

  Pellotine (0.00001-0.0001% dry wt.)

  Anhalonidine (0.00001-0.0001% dry wt.)

     Štarha 2001c cited Štarha 2001a

Gymnocalyciums: Gymnocalycium-stellatum-HBG

Gymnocalycium stellatum

Gymnocalycium stellatum Spegazzini

  Tyramine (Between 0.0001-0.001%)

  N-Methyltyramine (Less than 0.0001%)

  Hordenine (approximately 0.001%)

  Mescaline (Less than 0.0001%)

  N-Methylmescaline (Between 0.0001-0.001%)

  N,N-Dimethylmescaline (Less than 0.0001%)

  Anhalinine (Between 0.0001-0.001%)

  O-Methylanhalonidine (Less than 0.0001%)

  Anhalamine (Less than 0.0001%)

  Anhalonidine (Between 0.0001-0.001%)

  Pellotine (Between 0.0001-0.001%)

  Anhalonine (Between 0.0001-0.001%)

  Lophophorine (Less than 0.0001%)

      Štarha et al. 1997 (% by fresh weight)

Gymnocalycium striglianum Jeggle

  Tyramine (Less than 0.001%)

 Hordenine (Less than 0.001%)

 Mescaline ( “readily apparent” at around 0.001%)

 N-Methylmescaline ( “readily apparent” at around 0.001%)

 Anhalinine (Less than 0.001%)

 Anhalidine (Less than 0.001%)

 Anhalamine ( “readily apparent” at around 0.001%)

 Anhalonidine (Less than 0.001%)

 Pellotine ( “readily apparent” at around 0.001%)

 Anhalonine (Less than 0.001%)

 Lophophorine (Less than 0.001%)

     Štarha 1995a (% by fresh weight)

Gymnocalyciums: Gymnocalycium triacanthum

Gymnocalycium triacanthum

Gymnocalycium triacanthum Backeberg

 Tyramine (Trace)

 N-Methyltyramine (0.00005% [± 0.00001])

 Hordenine (0.00054% [± 0.00004])

 Mescaline (Trace)

 N-Methylmescaline (Trace)

 N,N-Dimethylmescaline (Trace)

 O-Methylanhalidine (0.00015% [± 0.00001])

 Anhalinine (0.00014% [± 0.00001])

 Anhalidine (Trace)

 Anhalonidine (0.0006% [± 0.00001])

     Štarha et al. 1998 (% by fresh weight)

Gymnocalyciums: Gymnocalycium triacanthum

Gymnocalycium triacanthum

Gymnocalycium uebelmannianum Rausch

  Tyramine (Between 0.0001-0.001%)

  N-Methyltyramine (Between 0.0001-0.001%)

  Hordenine (Between 0.0001-0.001%)

  Mescaline (Between 0.0001-0.001%)

  N-Methylmescaline (Less than 0.0001%)

  N,N-Dimethylmescaline (Less than 0.0001%)

  O-Methylanhalidine (Less than 0.0001%)

  Anhalinine (Between 0.0001-0.001%)

  O-Methylanhalonidine (Between 0.0001-0.001%)

  Anhalidine (Less than 0.0001%)

  Anhalamine (Between 0.0001-0.001%)

  Anhalonidine (Between 0.0001-0.001%)

  Pellotine (Between 0.0001-0.001%)

  Anhalonine (Less than 0.0001%)

  Lophophorine (Less than 0.0001%)

      Štarha et al. 1997 (% by fresh weight)

Gymnocalyciums: Gymnocalycium valnicekianum

Gymnocalycium valnicekianum seedling

Gymnocalycium valnicekianum Jajó

(now Gymnocalycium mostii subsp. valnicekianum)

 Tyramine (Between 0.0001-0.001%)

 N-Methyltyramine (Less than 0.001%)

 Hordenine ( “readily apparent” at around 0.001%)

 Mescaline (Less than 0.001%)

 Anhalinine (Less than 0.001%)

 Anhalonidine (Between 0.0001-0.001%)

 Pellotine (Less than 0.001%)

 Anhalonine (Less than 0.001%)

 Lophophorine (Less than 0.001%)

     Štarha 1995a (% by fresh weight)

Gymnocalyciums: Gymnocalycium vatteri

Gymnocalycium vatteri

 Gymnocalycium vatteri Buining

(now Gymnocalycium ochoterenae subsp. vatteri, or not; depending upon with whom you want to agree.)

  Mescaline (between 0.0001-0.001%)

  Tyramine (approximately 0.001%)

  N-Methyltyramine (between 0.0001-0.001%)

  Hordenine (approximately 0.001%)

  N-Methylmescaline (between 0.0001-0.001%)

  Anhalinine (approximately 0.001%)

  Anhalidine (less than 0.0001%)

  Anhalonidine (between 0.0001-0.001%)

  Pellotine (between 0.0001-0.001%)

  Anhalonine (less than 0.0001%)

  Lophophorine (less than 0.0001%)

      Štarha 1996 (% by fresh weight)

Gymnocalyciums: Gymnocalycium vatteri

Gymnocalycium vatteri

 

 

 Parting comment on the genus Gymnocalycium and South American globulars:

 It is puzzling that this large genus and area has been neglected for so many years, in light of the intense academic interest which has intermittently surrounding such plants.The work of Dr. Štarha underscores the need for more in depth work. While the reported concentrations overall are low, this is in line with the majority of cacti tested; the high mescaline producers are only sporadically represented and apparently difficult to predict.  Štarha’s results are encouraging despite low values.

 Considering how many different Gymnocalycium species are readily available, how easy they are to grow, how often this is mentioned in the literature and how many of the larger flat species actually resemble Peyote in color and appearance, it is mind boggling that more people have not pursued further chemical work in this fascinating and attractive group.

 G. platense and G. riograndensis have long been suggested as probable mescaline containing species but, as far as it can be determined, this was implied solely by morphology as no actual chemical work had been done. More recently, Dr. Štarha did indeed find small amounts of mescaline in the latter.

 An interesting mention is made of globular cacti in Margaret Ashley Towle 1961. Her reference, Eugenio Yácovleff & Fortunato L. Herrera 1934, mention Lobivia (L. corbula), Mammillaria (M. herrerae) (equating these first two) and Melocacti in passing, during their discussion of the many varied forms of cacti found depicted in ceramic designs. (pages 319-320, ceramic design examples also on page 321). [Their reference to Melocacti was in regards to the Peruvian species which form distinct Cereus-like columns somewhat resembling Neoraimondia and Armatocereus species but it should be mentioned that most Melocacti exist as fairly globular plants.]

 Some types of globular cacti are clearly depicted. While mescaline has not yet been reported from these plants, many Lobivia, Mammillaria, Melocacti, and Echinopsis species, as well as additional non-mescaline containing Gymnocalyciums, have all been reported to contain alkaloids.

 I would suggest more representative species be examined for all.

Azketium ritteri

Aztekium ritteri (Bödeker) Bödeker

Friedrich Boedeker  (1929) Monatsschrift für Kakteenkunde, 1: 52. Aztekium ritteri
Friedrich Boedeker  (1928) Zeitschrift für Sukkulentenkunde. Berlin 3 (14): 305–306. Echinocactus ritterii


Aztekium ritteri

 

Small amounts of mescaline have been reported. 

Etymology: The wonderful texture of its surface has been likened to some Aztec motifs, hence the genus name Aztekium. Friedrich Ritter (who had been living in Mexico) was the specific namesake.

Habitat: From Nuevo Leon, Mexico growing in xeric scrub on limestone and gypsum cliffs.

Often remains solitary but may be freely offsetting from base with age (or if grafted or after exposure to pesticides & fungicides). 
Greyish-green to grey body is broad and rounded to around 2 inches in
diameter; with a depressed wooly top.

Short napiform taproot.
9-11 ribs, [Ed.: Sometimes swirling] folded, with subsidiary and narrower ribs in between.] 
Cultivated plants tend to be more green. Especially so on grafted plants. This is considered a detractant to the beauty of this plant by most authorities and serious collectors.
Areoles are closely set and bear white hairs.
Few spines; weak, bent or contorted. Usually 1-3; 3-4 mm in length.
White flowers 8 mm in diameter, appearing to have a stalk.
[Pizetti describes flowers as being about 1 cm wide; with white segments and outer perianth parts with pink edges. Anderson 1998 describes the flowers as white to light pink and appearing sporadically throughout the summer.]
Pink fruit is berrylike and appears only when ripe.
Black seeds are 0.5 mm long.
    Backeberg 1977: 79-80 and
    Pizetti 1985 entry #15.

Backeberg noted that there is also a form with flower that is longer (has longer stalk)

See also Backeberg 1961 [5: 2890-2892], (includes pictures on page 2891, fig. 2722, and the larger flowered form in flower, fig. 2723.) and Lamb & Lamb 1971 [2: 378] (with picture). Pizetti has color picture.

Habitat photos: Chastek 1994 Kaktusy 2: 40-41

Backeberg & Pizetti (& many others) describe the species as cold sensitive but I have seen them tolerate hard freezes (6°F) in a covered but unheated outdoor cactus bed Austin Texas when totally dry. I would recommend protection from freezing despite that lucky experience.

Once considered an endangered species due to being found only in a restricted area experiencing heavy collection activity. More populations across a broad range have since been discovered. The habitat includes inaccessible populations due to restricted access for both humans and browsers so it has been downgraded to become listed as a species of “Least Concern“.
      B. Fitz Maurice & W.A. Fitz Maurice 2013. Aztekium ritteri. The IUCN Red List of Threatened Species. Version 2014.2. www.iucnredlist.org.

Reported analysis:
(Plants greenhouse grown in Czechoslovakia)
N-Methyltyramine (0.0031% by fresh wt.)
3-Methoxytyramine (Less than 0.0001% by fresh wt.)
Hordenine (Less than 0.0001% by fresh wt.)
N,N-Dimethyl-3,4-dimethoxyphenethylamine (0.0036% fresh wt.)
Mescaline (0.0009% by fresh wt.) (Which is not quite a mg per kg.)
Anhalidine (0.0008% by fresh wt.)
Pellotine (0.0026% by fresh wt.)
    Štarha 1994

[Aztekium ritteri has had an unconfirmed claim of caffeine. No reference was cited and none has been located. Claims for caffeine have never been sustantiated in any cactus species.]

Glucaric acid (tlc by Kringstad & Nordal 1975)
Quinic acid (tlc, glc & gc-ms by Kringstad & Nordal 1975)

 

 

Alwin Berger 1929 Kakteen, pp. 259-260.

Aztekium ritteri description

 

External links:

Dave’s Garden’s

IPNI

ThePlantList

Tropicos

NMCR 2010 poco – thelegonus

Gallery

Some more Trichocereus that were still at NMCR in 2010:
from poco albiflorus through thelegonus.

 

This is the final photo set of our 1 August, 2010 visit to New Mexico Cactus Research.
The featured image above illustrates how the cacti had overgrown some of their tags. Many of the plant tags were in rough shape, some were missing completely, some were missing a part of the tag and some had become illegible.
More images illustrating the new growth on all of the cuttings which Horst kindly provided will be coming in the future.

 

Trichocereus poco albiflorus

From Cuchu Ingenio, Bolivia. Tag also had the note “possibly Argentina”
Seeds had been collected by “DM” and were obtained by NMCR 4/1977, Horst planted them in April 1980.
Now lumped with Trichocereus tarijensis.

 

Trichocereus-poco-albiflorus-NMCR

 

Trichocereus riomizquiensis

FR856 type from Chuyllas, Bolivia (Rio Mizque).
Seeds had been obtained from Riviere de Carault in November of 1972 and were planted on the first of July in 1980 by Horst.

 

Trichocereus-riomizquensis-NMCR-2010

Trichocereus-riomizquensis-NMCR-2010

 

 

 

Trichocereus rubinghanus (I am presently unable to locate this name.)

Grown from seeds obtained from Riviere de Carault but missing a tag.

 

Trichocereus-rubinghanus-NMCR-2010

 

Trichocereus scopulicolus

 FR991 grown from seeds that Horst obtained from Riviere de Carault. They were planted in 1980. Date of seed acquisition is unknown due to partial tag destruction.

 

Trichocereus-scopulicolus-NMCR_2010

 

Trichocereus spachianus forma brevispinulus

Grown from seed provided by RIV. Horst described this as being an old form which is present in European nurseries.

 

Trichocereus-spachianus-brevispinulosus-NMCR-2010

 

Trichocereus strigosus

Seeds were obtained from “Lopez” in June 1976; they were planted in July of 1980.

 

Trichocereus-strigosus-NMCR-2010

 

Trichocereus terscheckii

“Cardon Grande” from Argentina. Seeds came from “Lopez” in February 1976; Horst planted them July 1980.

 

 

Trichocereus thelegonus

These production mothers were grown from seeds that NMCR acquired from Field in February of 1976. (This is also the featured image on this page.)

 

Trichocereus-thelegonus-NMCR-2010-f

 

This is what they can become when not repeatedly cut for sale.

 

Trichocereus-thelegonus-NMCR-2010-m


Trichocereus-thelegonus-NMCR-2010-l



 

Unclear Trichocereus
This was lacking a locateable label.

 

unclear-Trichocereus-NMCR-2010

 

My visit is divided as :

Visiting NMCR in 2010
A-H Ariocarpus – Hoodia
M-R Mammillaria – Ritterocereus
Trichocereus bridgesii – deserticola 
Trichocereus macrogonus — pachanoi
Trichocereus poco — Trichocereus thelegonus
 (You are here)

I hope that you have enjoyed seeing NMCR!

NMCR 2010 macrogonus-pachanoi

Gallery

 

A few more of the Trichocereus still at NMCR in 2010:
macrogonus through pachanoi

 

More images of some of the cacti encountered during a visit to NMCR in 2010.
Most of the plants on this page were grown from seed planted in 1980 by Horst. The peculiar and misnamed “v. puquiensis” is the one exception.

Trichocereus macrogonus var. giganteus at NMCR in 2010.
Grown from seed planted in 1980 that came from Robert Field but in 2011 Robert Field told me he had no knowledge of this name. Field DOES have a Trichocereus macrogonus that his father acquired from Blossfeld’s Andean collecting expedition.
This looks very much like that Trichocereus macrogonus at Field’s. Notice that it almost lacks v-marks and only expresses them weakly? Compare to images of the Trichocereus macrogonus at Field’s in “The Macrogonus Onus” (forthcoming here) and at the Trichoserious website.

Trichocereus-macrogonus-giganteus-Field-NMCR

Trichocereus-macrogonus-giganteus-Field-NMCR

 

 

Horst also offered this:

Trichocereus macrogonus KK923

Mother plant in 2010 from Knize seeds that were planted in 1980.

 

Trichocereus-macrogonus-KK923-NMCR_2010

Trichocereus-macrogonus-KK923-NMCR_2010

 

Trichocereus pachanoi var. crassiarboreus

Labeled Trichocereus pachanoi var. crassiarboreus at NMCR. Grown from seeds obtained from Riviere de Carault.
Compare this to Tegelberg’s plant bearing the same name at the Huntington.
Trichocereus-pachanoi-crassiaboreus-NMCR

Trichocereus pachanoi var. puquiensis is clearly a mislabel but isn’t it beautiful!
It was obtained as a live plant from John Rahart in Quartzite at the Mineral Show.

 Trichocereus-pachanoi-var-puquiensis-NMCR-2010

Trichocereus-pachanoi-var-puquiensis-NMCR-2010

 

 

 

Trichocereus pachanoi Tarapoto

      Grown from seed from Tarapota, Peru. Unfortunately Horst did not remember the source for the seeds and all of the planting records were destroyed by the water and mold that were mentioned earlier. (Their planting date not clear but it was well after 1980.)

Trichocereus-pachanoi-Tarapoto-NMCR-2010

 

 

 

And of course our old friend the pachanot was there.

The Trichocereus pachanot mothers at NMCR.

 

Trichocereus-pachanot_NMCR

Trichocereus-pachanot_NMCR

 

 

 

My visit is divided as :

Visiting NMCR in 2010
A-H Ariocarpus – Hoodia
M-R Mammillaria – Ritterocereus
Trichocereus bridgesii – deserticola 
Trichocereus macrogonus — pachanoi (You are here)
Trichocereus poco — Trichocereus thelegonus

I hope that you enjoy seeing NMCR!
 

 

NMCR 2010 M-R

Gallery

A few more of the plants at NMCR in 2010:
from Mammillaria through Ritterocereus 

 

More images of some of the cacti encountered during a visit to NMCR in 2010.
Most of the plants on this page were grown from seed by Horst. The first two are vegetatively propagated.

This first image did not turn out well but was one of my favorites.
Before his illness disrupted his plans, Horst had begun propagating a cristate form of the popular monstrose Mammillaria bocasana cv. “Fred”.

Horst was preparing to release this clone under the name “Ethel” to be an appropriate counterpart for “Fred”.
NMCR-Mammillaria-bocasana-cv-Ethel

 

 

monstrose Mammillaria bocasana cv. “Fred”

 

 

Mammillaria elongata cv. “Golden Stars”
 Mammillaria-elongata-NMCR

 

 

Mammillaria microcarpa
(in the first image it is next to a Matucana madisoniorum)

Mammillaria-microcarpa-NMCR

 

Mammillaria occidentalis 

 

Mammillaria species (no label) 

 

Parodia splendens f. major
Parodia-splendens-f-major-NMCR

 

 

Parodia variabilis  

Parodia-variabilis-NMCR

 

 

Pyrrhocactus bulbocalyx

 

 

Ritterocereus edulis
As Horst commented, the name suggests a use for food of some sort. He had been unable to learn more about it or the origin of the name choice.

 

 

My visit is divided as :

Visiting NMCR in 2010
A-H Ariocarpus – Hoodia
M-R Mammillaria – Ritterocereus (You are here)
Trichocereus bridgesii – deserticola 
Trichocereus macrogonus — pachanoi
Trichocereus poco — Trichocereus thelegonus

I hope that you enjoy seeing NMCR!
 

 

Hybrids 2

F1 hybrids

(The first ten are larger images of the same plants as were shown on the previous page. Those share the same parents. There may be two peruvianus forms involved with the plants in the other images and some of those are additional views of other plants shown. Pachanot was a parent in all cases.)

 

F1 hybrids produced by George Fuller (using both directions of crossing) for Trichocereus pachanot X Trichocereus peruvianus:

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

pachanot X peruvianus (F1)

pachanot X peruvianus (F1)

 

the Peyote Crisis and some Suggestions – Revisited

This article and the rest of the book Sacred Cacti are now best viewed at http://sacredcacti.com  My apologies for any 404 pages resulting from any link on this website that is being overlooked by me.
It appears to be a ripe time for reevaluating the article entitled “the Peyote crisis & some suggestions“.
This was variously positioned as Chapter 2 or Chapter 3 in the revisions of the book Sacred Cacti.
That chapter, as written, is greatly in need of revision & updating; and some additional questions being asked about *its* suggestions. Our use of the word “I” in this article simply means we want to say this with one voice. Use of the word “we” refers to the reader and ourselves.
This commentary, as written, is meant to serve the great need for better accurate public education and has been constructed primarily for clarity of presentation of the contained material. It has not been created with the same density of in-line references such as would be the case for a work that was intended for print publication in a peer reviewed journal. It is hoped that adequate documentation and references are included for the benefit of people wanting to learn more but if YOU want to learn more or need any additional clarification or supportive documentation please drop an email to keepertrout at gmail and ask.
Accompanying this information is the feeling that there is some urgency in it being released. It is therefore being made available for public inspection and comment without further delay.
The plants of tomorrow begin with the seeds that are planted today.

Commentary & thoughts
by Keeper Trout, Blake Edwards & Martin Terry

I also went to survey the gardens in February [1998]. The situation is sad, intolerable, several parcels hunted completely clean. On inquiring with the dealers, I was able to hand sort well over 10,000 dime sizers, most w/roots. They are picked that way because the payment is per unit. […] those 10,000 plus babies are now growing. My idea is to purchase all the babies we can for their eventual re-planting in Texas.”
Leo Mercado 6 July 1998 (personal communication).

Those same plants were later seized (as part of a dump-truck load containing more than 11,230 living peyote plants) and destroyed by a “multijurisdictional task-force” of law enforcement officials despite Leo at that time having been found in court to be in compliance with Arizona state law permitting the sincere religious use of peyote. In the aftermath of what can only legitimately be described as a terroristic home invasion, Leo posted a notice online that he had replanted the 200 or so peyote plants that had been missed or dropped during the raid.
No charges were filed, which fact was likely to prevent a return of his peyote as had occurred after the first time that they seized Leo’s peyote. Instead Leo’s landlord found himself being threatened with the seizure and forfeiture of his property if he did not evict Leo and his family. The basis of that threat was his supposedly renting to a “known illegal drug dealer”, namely Leo!
Apparently Leo’s living example as a human of only modest means successfully propagating and cultivating large numbers of peyote plants outside of Texas was too powerful of an example to be allowed to exist. At the very least, his Kearny, Arizona shade-house and gardens had to be seen as an awkward truth running counter to the lies actively being propagated about it being impossible to grow peyote outside of its native habitat.
From Ch. 3 in Sacred Cacti 3rd edition (with some edits).

 

Lophophora-williamsii-threatened-by-knife

Cutting crowns flush at the level of the ground has been established to be the best known harvesting technique for peyote. This approach to enable sustainable harvesting has been known of and employed by peyote consumers in Mexico for millenia. The archaeological peyote specimens discovered strung on a cord at Cuatro Cienegas are more than a thousand years old; the Shumla peyote effigies are over six thousand years old.

 

First, concerning the “crisis”….

One suggestion, really, is all that is required; assuming that it can be heard, without prejudice, where it matters.

Cultivate the Medicine.

It is really simple yet that simple truth of the matter has been almost completely buried, if not forgotten or deliberately obscured, in rhetoric that has at times variously been self-serving, manipulative, deceptive, disingenuous, confused, based on misunderstandings, culturally bigoted, or sometimes even entirely delusional. There really was not any delicate way to put that so I apologize for trodding on anyone’s conceptual toes.

Some people might ask:
If peyote is a pressured species, why isn’t it cultivated?

The question, “why isn’t it cultivated?” is a really good one. You and I will be exploring its answers in some detail.

We should start by clarifying some things and being certain that we all have a good grasp of an unnecessarily convoluted story.

 

The conservation status of peyote

Peyote is most certainly not extinct as some people strangely seem to believe and are even willing to say openly as if it were a fact. It is not yet really even an endangered species as more than a million living peyote crowns were no doubt harvested in South Texas again this past year by the licensed peyote distributors (I have to say probably as the numbers are not yet available).

A perception that the pressure from peyote harvesting is endangering the species is nothing new. While it does not appear on any federal listing of endangered species, peyote WAS declared an endangered species by the Texas Organization of Endangered Species (TOES) according to Morgan 1983: 83-84. Despite having a long history of cost sharing with land owners for brush removal and clearing of land, since the late 1970’s the U.S. Soil Conservation Service has refused to do so in any area containing peyote, as the SCS recognizes it to be a potentially endangered member of Texas flora (Morgan 1984: 292). Their lack of financial contribution has not slowed the clearing of land in the development of South Texas.

Only recently was peyote actually finally recognized as having adequately dwindling numbers to merit being assigned a status of “vulnerable” and being placed on the IUCN Red List of Threatened Species. Version 2013.2. [http://www.iucnredlist.org/details/151962/0].

Debates as to whether it should or should not be placed on the Red List had been going back and forth for some years, Oddly, what seems to have tipped the balance of opinion was the appearance of cosmetic/pharmaceutical industry products known as Pomada de Peyote. [Link 1] [Link 2] [Link 3] [Link 4] [Link 5].
I’m not including these links to suggest that any should be patronized but simply to note what came up in a Google search for “pomada de peyote” on 1 November, 2014.
Here are images of five of the products that were found to be offered on the first search results page.

 

Pomada-de-Peyote

 

It is certain that as both a liniment and an ointment, similar formulations have existed for a very long time at the folk level, and more recently as products of a local cottage industry. These products have likely achieved visibility only when the distribution venue was moved from local yerbarias to online marketing.

The use of peyote is traditional among some Hispanics in South Texas, too.
“When I was younger, you could buy it at the market in Nuevo Laredo, or at any of the local yerberias (herb shops),” [Salvador] Johnson said.
His wife, Vicenta, said that elderly Hispanics still use the drug as a cure for a variety of ailments, including as a rubbing lotion to treat arthritis when it is mixed with alcohol.
Grant 2000 Ft. Worth Star-Telegram, Sunday, 23 January.

One of the companies now producing pomada de peyote is an established business that is substantial in size and has previously developed other successful product lines. The future development of this product will be interesting to watch. It may be noteworthy that the number of different producers showing up as hits on the first Google search result page went from two to five within the past year.

Peyote is not endangered as a species for a variety of reasons. The most notable being that there are large expanses of the Mexican peyote populations left. The secondary reason is that not all peyote is accessible for harvest. In some cases, harvests are deterred by a lack of road access but in at least one instance a local population (in Mexico) is protected by the resident humans who interestingly do not use their local peyote for any purposes other than as an external analgesic applied to burns, bruises and aching muscles & joints.

In Texas it is a different story. The vast majority of its peyote populations have long since been removed during the course of the modern-day occupation/development of South Texas real estate and the collateral development of its assorted resources. Some peyote finds protection on large ranches with tall fences designed to retain game animals that are hunted for a hefty fee. When the owners of such large tracts of brush also do not permit peyote harvesters to access their land those properties form unintentional peyote reserves. The land that is left as accessible is heavily impacted by the existing peyote trade. In addition, the commercial peyote harvest has been insufficient for meeting NAC needs for some time.

There are two distinct but inseparable subtopics within this main topic of the threats to peyote, whether those threats are due to habitat loss or over-harvesting or any of the other known challenges that peyote faces.

One is the future of peyote as a species and the other is the future of the NAC as a Medicine-based spiritual organization that has both adequate and uninterrupted access to its Medicine.
We will examine both of those subtopics separately as this overview unfolds.

 

What has happened to create dwindling peyote populations?

Reading the popular press or listening to people talk, one would think that overharvesting by Native Americans or “hippies” is the cause. One or the other or both typically gets the most common and most vocal blame. This is true, despite it being absolutely clear that the vast majority of peyote’s obliteration, both in terms of absolute numbers and in total acreage, has actually been the incidental destruction of populations during the process of land conversion. All other factors combined pale by comparison.

There have been many reasons for this; the development of land for various projects, such as construction projects, shipping centers, parking lots and tract communities, or as a result of the brush suppression methods that enable ranchers to use their land for agriculture or ranching. Once a piece of land has been converted, peyote does not return.

 

peyote gardens today

Aerial view of a portion of the Peyote Gardens in Starr County showing extent of the land use and clearing. Photo clipping came from a topographic map from the US Geological Survey (USGS).

Most of peyote’s habitat in South Texas is covered with a tangle of dense thorny brush. To make their land available for agriculture or cattle, it was once a common practice for landowners to root-plow the soil due to the tendency of the thorny brush to come back with an aggressive vigor after being cleared.
Root-plowing severs the roots below the soil surface thereby weakening whatever of the roots can’t be uprooted and suppressing their ability for good regrowth. Or at least suppressing it for longer than might be the case without it. Repeating the process a few times does help but it is noteworthy that what actually becomes most suppressed is the diversity of life while the actual species that were attempted to be eradicated often go on to become the predominate vegetation.

 

rootplowed land

rootplowed land

Land in Maverick County that was root plowed several decades ago. The ranch foreman claimed that peyote was here before that occurred.
Their most likely intended target for eradication was the Acacia rigidula which comprises about a third of the plants seen in the lower image above.

 

Root-plowing has been determined to have lasting adverse impacts when used in dry regions. In arid environments with abundant limestone, in this case it is present as a calcareous gravel, rainwater dissolves the carbonates and other soluble ions but there is insufficient volume of water to carry what is dissolved more than a fairly short distance into the earth, accumulating and eventually creating a bed of ‘caliche’ at the depth of maximum moisture penetration. Due to rainfall being variable in the total amounts delivered per storm, this eventually forms an irregular gradient of alkali concentrations existing between the caliche and the surface ; with the surface obviously being the most life friendly. The layer of decomposing organic materials at or near the surface adds to the ability of the soil to support life.
This natural zoning develops over long periods of time with whatever level of moisture they DO have accessible. As it becomes increasingly basic with increasing depth this also means that that the surface is most amenable to supporting life. Accompanying that is the observation that, as rains moved part of the soluble alkali into the earth, that action helps make the surface more life friendly.
This fragile balance becomes completely undone with the mixing of the top half meter of soil during root plowing.
In this process, the more basic material that has been migrating away from the surface is partially returned to the surface during the mixing process. Recovery is typically slow since the reduction of the alkalinity at the surface level relies on repeated water percolation over time. The resulting increase of surface alkalinity leads to a die-off of small cover plants following seed germination and adds prolonged difficulty in reestablishing the normal flora. In adjacent areas that are used for agriculture due to being more sandy loamy than gravelly, and additionally due to the topography of the land being flatter & less sloping, this creates problems with blowing dust.

As a result root-plowing is now discouraged for those soil types and when it becomes needed specialized implements are used to selectively remove single plants.
The important thing to understand about root-plowing is that unlike the thorny brush that the root-plowing is intended to eradicate, a single thorough root-plowing will generally permanently exterminate all of the existing peyote on that a given piece of land.
If you want to gain a really solid grasp of this technology and a better understanding about why it would impact peyote so adversely, visit http://YouTube.com and search for “root plow” or “rootplowing“. Nothing describes the process better than watching a root-plow in action.

Other brush-clearing methods are not less destructive to peyote but they do impact the soil and ability of the land to recover less than root-plowing. YouTube can provide looks at modern techniques of “brush clearing in South Texas” as well.

 

root plow

 

Root plow Those fins are designed to force the severed roots to the soil surface and into the sun to dry and die.

 

The root plow is a tool for removing vegetation by cutting it below the soil surface […] killing brush and light vegetation by undercutting it […] at depth from 20 to 50 centimeters (8-20 inches). […] The advantage of the root plow is that it cuts the vegetation below the bud ring, killing brush that would normally resprout if cut at ground level.
US Army 1974 Tactical Land Clearing, p. 3-6

 

root plowing

Trunnion-mounted root-plow in action.
Both scanned photos came from a 1974 US Army
training manual entitled “Tactical Land Clearing”.

A new threat to peyote in South Texas are windfarms which choose the highest points in the Bordas Escarpment for their placement. These of course need an access road permitting both construction and maintenance. Those roads potentially carve through some of what few undisturbed peyote populations still remain in South Texas.

 

What do we actually know about the harvesting of peyote?

Surprisingly little study has been done on the impact of harvesting itself. As far as I am aware, only one organization, a nonprofit group named the Cactus Conservation Institute, has taken the time to learn more despite the immense need for this information as regards both the NAC and peyote conservation. It is clear that the peyote plant is a resilient species or it never could have permitted mass harvests to continue for so many years in the face of diminishing habitat. There are many articles that are available concerning the harvesting of the peyote plant and about its habits and habitat.

It IS known that the best way to cut peyote is at ground level. Cutting too deeply increases mortality and weakens those plants which do manage to recover.
The one existing study on the subject was published in Terry & Mauseth 2006. Using a histological evaluation, it was established that only the stem tissue was capable of producing new growth. Root tissue could only grow roots. A visible clear and sharp line of division was noted to exist between the two tissues.

Peyote harvesters often use a shovel with sharpened edge or a machete. Both of those tools can work great for cutting at ground level or they can be mis-employed and produce a deeply angled cut.

 

a cut peyote

Peyote plant after the crown has been removed

 

What do we know about the impact of peyote harvesting on wild populations?

A simple overview:

More complete details concerning the items in this list can be gleaned at the Cactus Conservation Institute website or in Kalam et al. 2013, Klein et al. 2015, Terry et al 2011, 2012, 2013 & 2014.

1) Peyote harvest causes a small increase in mortality.

2) If harvesting is repeated too frequently, this rate of mortality increases.

3) Harvesting also reduces the amount of harvestable biomass of sacrament per plant.

4) The aforementioned observation (3) is initially obscured by the increase in numbers due to the common occurrence of multiple regrowth. However, the sum total biomass of head (crown) tissue per plant, even after 4 years of uninterrupted regrowth, was still significantly smaller than the biomass of the original single head that had been harvested four years before. The study to determine the minimum sustainable recovery period after harvesting is still not complete, but it now clear that the time required for recovery from a single harvesting event is greater than six years.

5) Analysis has also shown that even after four years the regrowth had regained only half the potency of the original crown. It is not yet known how long it takes for the original potency to be re-established in the regrowth buttons.

6) Current and future seed production contributions to the local population are lost along with the harvested plants. The typical fate for peyote seeds following a harvest is into the trash or compost.
During the late 1990s, Leo Mercado was able to successfully recover (and plant) many thousands of seeds from the piles of hairs and tufts that accumulated from the peyote cleaned in preparation for a large ceremony. That event, at an annual NAC meeting at Mirando City, consumed more than a thousand crowns. (Information from a personal communication with Leo in 1998.)

7) The oldest and largest plants have been selected for by their environment as those are the plants which are best suited to survive the peak adverse periods of weather. These are commonly preferentially harvested – precluding any future contribution they might have made to the genetics of the population.
This last point may be subtle but played out over a long time can become significant. Following the removal of these genetically superior products of natural selection, future adverse periods of weather will likely begin to produce an increased adverse impact on the remaining population.

 

multiple regrowth

Peyote plant with multiple regrowth

 

Recovery

Let’s go over through that overview again but this time from a slightly different angle of thought and consider those factors in terms of recovery.
Recovery after harvesting is a core concept for this subject as it interweaves an impact assessment with a determination of sustainability. If the harvesting of a natural renewable resource is not sustainable, both harvesting and availability are temporary and transient phenomena with an inevitable end point involving either the loss or increased scarcity of that resource. /span>
There is nothing mysterious or unclear about what is being witnessed. A dramatic multiplication of undersized individuals is in fact the classical model resulting from harvesting activities involving an overexploited natural resource, be it fish or ginseng roots. (See Terry & Trout 2013. This link is a PDF file.)

Recovery is best understood not by looking at recovery of the individuals which are involved but of the health of local populations which are composed of many individuals.
Recovery of a population will accordingly have several factors based on what we looked at in our overview:

1) Replacement of the plants which die as a result of harvesting. (Replacement in this case is being considered only in terms of the natural recruitment of new seedlings although cultivation and wildcrafting would also enter the picture in this area. Wildcrafting is the conscious planting of seeds or return of plants in such locations where the plant formerly occurred naturally or could have occurred naturally.) This decrease in survival is thankfully a fairly low rate but it is not insignificant if a field is revisited as each subsequent visit may result in the reharvesting of plants which are still drawing their sustenance from the original reserves of the remaining taproot fragment from their mother and have not yet had time to manage to grow a replacement taproot.
The rate of mortality has increased with each time that reharvesting occurred in what limited study of the topic has occurred so mindfulness is needed not just of how deeply a plant is cut but also when it was last cut. Until after the point that a plant can regrow a taproot it is vulnerable to outright death from loss of its photosynthetic tissues as occurs in harvesting. This subtle but simple fact is somehow often either missed or trivialized: when the crown tissue has been removed the peyote plant loses its ability to use the sunlight. This remains true until after a new crown can be made and it reaches the surface of the ground where it can absorb sunlight to once again photosynthesize and feed itself. Repeated cutting too frequently forces the plant to exhaust its limited reserves and interferes with good regrowth and survival.
Plants that have been harvested need adequate time to replace their missing storage tissues (by photosynthesis in the crowns of the regrowth pups) before being reharvested or their death rate increases; eventually requiring their actual replacement.

2) Regrowing new crown tissue to replace the harvested crown with its equivalent prior to reharvesting.
Even though multiple crowns commonly result following harvesting, it takes some point greater than six years for their combined total weight to match that of the original crown. (The study to determine how long it takes for the sum of the regrowth buttons to equal the weight of the original harvested crown is still ongoing.)
Harvesting prior to following that point of recovery will provide smaller and steadily decreasing volumes of harvests. This is a practice which feeds into the spiral towards smaller, weaker plants with higher loss rates.

3) Recovering the original level of alkaloids.
After four years the average alkaloid level of new growth was only half that of the original crown. It is presently unknown how long it takes for the preharvest alkaloid level to be restored. Harvesting prior to following that point of potency recovery will provide an inferior quality of harvests, requiring consumers to ingest more plants, which also feeds into the extinction vortex towards smaller, weaker plants with higher loss rates.

4) The population also has to recover from the impact of however many years it would take seeds from those harvested plants to be replaced by new seed-producing crowns, and this must be taken into account if wanting to accurately assess the impact of harvesting. Every plant which is taken means that many less seeds are available for the local population for at least a handful of years. This is not insignificant as wild peyote in nature primarily reproduces via seeds. Removing a plant means removing all future seed contribution by that plant.
If older plants are preferentially harvested and as numbers dwindle the age of first harvest also decreases, it rapidly produces a situation where the only plants to harvest may have flowered only once or twice or not at all, creating a huge seed production deficit for the local population.
In the event of adverse weather (whether prolonged drought or beyond average freezing) causing an above average loss rate, this adds to the risk that the local population may not recover.

I’ll let you, the reader, do the math for yourself.

 

reharvested L. williamsii

This plant was previously harvested multiple times and the severed crowns sold through the licensed distributors. While the harvesting was conservative enough to not lose the original taproot, this individual strains the concept of “sustainability“. Also notice the steep angle showing careless cutting during two previous harvests.

 

What about the sustainability of harvesting?

Peyote harvesting appears to be a sustainable practice, at least in potential or in theory. In its present-day application however, the slow attrition process leading to the endangered species path has already clearly begun. It is clear that the consumers of peyote still have plenty of peyote to last for some years to come. Maybe even for the rest of our lifetimes, especially if you are middle aged like me.
Sustainability is not something defined by the here-and-now though. A commonly cited definition of sustainability is found in the 1987 Brundtland Report for The United Nations World Commission on Environment and Development, meeting the needs of the present without compromising the ability of future generations to meet their own needs”
As Kimberly Cover pointed out in 2005, that report’s definition is curiously similar to the Iroquois concept of thinking with responsibility for the next seven generations.

Much more study is needed to better define what was seen in the limited harvesting studies that exist but this is how it looks at the moment: The increased rate of mortality that results from a one time harvest is low enough so as not to adversely impact the long term survival of a population. That only appears to be true when adequate time is permitted between harvests. Some period greater than six years is all we can say about that number pending future data emerging. If enough plants of adequate size and potency exist to fill the anticipated needs of the active NAC membership and those plants are being reharvested no more often than they can regrow and return to being what they were prior to the point when they were first cut, harvesting appears to be sustainable.
Anything which creates an average result that achieves less than that, such as is presently the case, is not a sustainable practice.

 

So, let’s come back to our question, “Why ISN’T peyote cultivated?”

Probably the single most important element as to why cultivation is not already a part of the picture is the simple fact that none of the non-NAC people who are legally involved in the supply side have actual legal protection permitting them to cultivate peyote. They are in general law-abiding respected citizens who want to stay out of any trouble. Additionally, the peyote distributors can lose their licenses for violating the law.
As the licensed distributor Mauro Morales told Franks in 2007 . You have to make sure you don’t have a problem with the law, you know?

The portion of South Texas where peyote occurs naturally is commonly referred to as the Peyote Gardens, despite there being a complete lack of historical peyote cultivation. There are presently at least two pertinent stumbling blocks preventing this land from actually being used for creating a real peyote garden (or otherwise addressing the fatal long-term flaws that are inherent within the existing distribution system). Those are located within the Texas DPS (Department of Public Safety) regulations concerning peyote harvesting:

One for the Distributors:
Ҥ13.42. Peyote Distributor Registration. (d) Activity not authorized. A distributor registration does not authorize the distributor to: (1) manufacture or cultivate peyote; (2) ingest or use peyote; (3) deliver to an individual who is an Indian as the term is defined in AIRFA, unless the individual is also an Indian as the term is defined in this subchapter; or (4) import or export peyote except as permitted by federal law.

&
Another for the Ranchers has two pertinent features of interest:

“§13.55 adopted to be effective July 18, 2001, 26 Tex Reg 5266 (only a part is being included below) Nothing in this subchapter affects the ability of a landowner to: […] (2) burn or clear land for purposes unrelated to harvesting, cutting, collecting, or possessing peyote.” and within that same subsection, (b) Prohibited. Unless registered as a distributor or reported to the director as a current employee of a distributor, a landowner may not sell, harvest, cut, collect, transport, or possess peyote. A landowner does not possess peyote in violation of the Act or this subchapter if the peyote is unharvested and growing in its natural state.”

Landowners are permited to charge access fees for peyote harvesting but interestingly there is another clause in this same regulation that adds:
“(d) Harvest fee limitation. Unless the landowner is registered as a distributor, the director will deem the landowner to be selling or distributing peyote if the landowner bases the fee charged or collected under subsection (c)(1) of this section on the amount of peyote harvested, cut, or collected by the Indian using or entering the land”

Notice that this is a dysfunctional “one-price-regardless-of-harvest-size” scenario that actually encourages the maximum possible harvesting to occur per visit. Since the law further sets the retail price as being per piece (i.e. per button) and not by weight there is just as much financial motivation to harvest tiny plants as older ones. Increasing difficulty in gaining access adds additional motivation to maximize the harvests recovered on every visit.

Many ranchers don’t like peyote or peyote harvesting or peyote people and express a familiar bias directed against them. A not untypical attitude is Sahagun’s 1994 quote of ranch owner Robert East. I don’t want them here. That’s all there is to it. I think it’s a dope business, that peyote.” Racism and bigotry often still exist close to the surface in South Texas, in all directions. When talking with ranchers, several times I’ve heard it said that the cause for the disappearance of peyote wasover-grazing by the Indians.”

While that degrading analogy blames the “Indians” there is actually a highly valuable insight if we look at what IS actually real within that notion — namely, as is also true for a rancher’s grazing animals, the NAC is in fact being constrained and provided with its Medicine in a regulated and controlled manner rather than having the freedom to do as they choose. Blaming Native Americans for the, ahem, “over-grazing” problem is about as sound as a rancher blaming their grazing animals for “eating too much” rather than, in this case, correctly recognizing that any “overgrazing” was the direct result of negligent planning, counter-productive activities and incompetent management on the part of the ranch manager.

Similarly the fees charged by ranchers for access are high enough to stimulate maximizing the harvesting per visit as well. Johnson has mentioned ranchers’ greed raising access costs from what once was a pittance to something more significant.

Grant gave a 2000 estimation of it then typically costing $1,500 or $2,000 a month for a peyote lease; which provided a small work crew with access to locate and harvest crowns that were then being sold at the retail level for around $0.15 each.

There is no question that the public perception of the peyote trade being profitable contributed to that increase in peyote lease fees. Not everyone shares completely identical motivations. Sahagun 1994 described rancher Rick Walker as being fed up with trespassers. But he suggested another reason for guarding the peyote gardens on his land. Peyote, he said, may one day become a hot commodity – for ranchers.”

There is at least one rancher in South Texas, the identity of whom is being withheld, who has discovered a unique way to legally make money from his peyote and still protect them from any harm. Instead of leasing his land for the harvest of peyote buttons, he instead “showcases” his peyote plants. He permits organized “eco-tours” to bring visitors onto his property in a bus as part of a fee-based tour. They are allowed to visit his property under tightly controlled circumstances in order to witness and photograph his healthy population of peyote plants. The tour bus also takes the visitors away at the end of the visit so there is no risk of theft.
That population is, just as importantly, also located far enough away from the nearest road to ensure that none of their visitors will be able to return on foot.

While this may sound cynical, one other highly significant factor in the perpetuation of the status quo is that the peyote distributors actually derive a very good living from their trade.

Despite the low cost per button, it is actually a moderately lucrative profession in what is historically an economically depressed region of Texas since the three remaining peyote distributors combined now typically report a total sales of a little under a half million dollars per year ($530,230 in 2013, $434,609 in 2012, $466,590 in 2011, $459,699 in 2010 and $493,834 in 2009 according to DPS records). This reflects their combined totals so in reality it is split into uneven thirds based on how much they actually sell. Each distributor’s total sales pays for their lease fees, their expenses and is also what they pay to the small group of their ’employees’ who help them harvest peyote. In most cases their employees are their relatives.
Unlike the ranches, the distributors are authorized to pay and charge a fee on a per-button basis. Resale prices to their consumers had risen from around $0.09 in 1990 to $0.15 in 2000 and to $0.33 per button in 2011. (A hidden cost factor within that is that the rise in cost had been accompanied by a decrease in size and potency which meant people were required to eat more buttons. See Terry et al. 2012. Link goes to the PDF at CCI’s website.)
A perceived threat to their income and livelihood is no doubt going to be an important motivating factor and can add some illumination to the larger picture and help us to better understand why there is such resistance to change at the distributor level.

Sahagun 1994 quoted Johnson as saying,

I love what I do, enjoy the hell out of it. But hey, you don’t get rich picking peyote.

It is not a huge amount of money but in a region where relatively few other alternative options for similarly lucrative employment opportunities exist it is certainly something that the people involved are going to care about. Relatively few of the distributors and harvesters could successfully turn into peyote growers without investing resources and time in buying land and/or learning skill sets they do not presently possess. Even if they decided to take that path, it would put them on equal footing at the starting gate along with their new competition only if they had the same level of interest, education and skills as a professional gardener or nursery operator.

While the state law that was mentioned previously as granting the distributors their licensing specifically prohibits the distributors from cultivating peyote, the federal law also recognizes that the NAC, or anyone else who is producing peyote for the NAC, has a need to “manufacture” their Medicine (21 CFR 1307.31). [The regulation says “Any person who manufactures peyote for or distributes peyote to the Native American Church, however, is required to obtain registration annually and to comply with all other requirements of law.” That potentially open door for cultivation would apply to any person, NAC or otherwise. There is no special restriction to NAC members in this regulation.] Manufacturing a plant obviously requires growing it or else modern technology has become much farther advanced than I am aware.

Congress has further added an affirmative clause that suggests NAC cultivation was at least being envisioned as enough of a possibility that its regulation needed inclusion.

(b) Use, possession, or transportation of peyote
(1) Notwithstanding any other provision of law, the use, possession, or transportation of peyote by an Indian for bona fide traditional ceremonial purposes in connection with the practice of a traditional Indian religion is lawful, and shall not be prohibited by the United States or any State. No Indian shall be penalized or discriminated against on the basis of such use, possession or transportation, including, but not limited to, denial of otherwise applicable benefits under public assistance programs.
(2) This section does not prohibit such reasonable regulation and registration by the Drug Enforcement Administration of those persons who cultivate, harvest, or distribute peyote as may be consistent with the purposes of this section and section 1996 of this title. (In 42 USC § 1996a.) [Again, this applies to all persons, but it certainly includes the NAC.]

Which, at the very least, suggests that the road to the future cultivation of peyote by the NAC appears to be open as an available option that is protected by federal law. As AIRFAA treats cultivation in exactly the same manner as it does distribution, and because regulated distribution requires a long-standing registration process that functions daily before our very eyes, it would seem to be obvious that Congress intended cultivation to be not merely a hypothetical possibility, but a real option that should be realizable by the act of registration (to be defined and regulated, of course, by DEA).

 

peyote-buttons-Safford-1916

Dried peyote buttons from Safford 1916

 

 

Robledo 2006 included a thought-provoking comment that was left unexplained but touches on an often overlooked contribution to peyote harvesting by the NAC:

Out of the approximate 5 million buttons sold legally each year in the U.S. and Canada, deep South Texas provides about 2 million, with Salvador and his team of peyoteros providing at least 1 million themselves.
What is not mentioned by Robledo is what source provides the other 3 million of those buttons. It is noteworthy that the amount being estimated as procured independently of the activities of the licensed distributors exceeds their total output by 50%. It is reasonable to assume that he refers to the peyote that is being provided by the independent NAC members who are harvesting their own peyote. This brings us to another element in the story that we will return to again later – in the second part of this chapter.
Before moving onward this also is a great example of how much of the current “wisdom” about the peyote trade is based on untraceable rumor rather than documented fact. In the case of Robledo’s intriguing assertion of an actual numeric value for the unregulated peyote trade there are two glaring and inescapable facts that might be easily overlooked: 1) The claim lacks mention of its actual source or providing any indication about where or how this information came into Robledo’s awareness, and 2) it is an absolute impossibility for anyone to keep track of, much less tally with accuracy, the actual extent of the peyote trade occurring independently of the licensed distributors.

 

In 1988, after interviewing the active licensed distributors, John Morthland commented:

Dealers worry constantly about running out of stock, so they keep sources secret from outsiders and even from each other. They are also afraid that if Indians ever discovered the choice growing areas, they might try to bypass the dealers.”

An actual attempt by some peyote distributors to control the peyote trade and deliberately try to prevent cultivation by their customers actually goes back a very long time. Some comments from BIA Special Agent “Pussyfoot” Johnson were featured in an intriguing account by his supervisor that appears in a 1909 issue of the Indian School Journal, entitled “History, Use and Effects of Peyote.”

About twenty-three years ago a white man appeared at Laredo from the Territory in quest of peyotes.
He learned from the Indians up north that in a range of hills about forty miles east of Laredo, these peyotes could be found, He employed Mexicans to gather a supply, which he took north with him. He came in contact with a shipper by the name of Villegas, founder of the house known as L. Villegas and Company. Villegas then began buying these peyotes of ignorant Mexicans and shipping them north to the Indians. This house has been doing this for more than twenty years, but the business has been kept as secret as possible. Villegas has always refused to give the Indians any information as to the source of supply and has also refused all these years to supply Indians with the whole plant, fearing that they would transplant them and thus establish their own source of supply. Half a dozen years ago a member of the firm named Wormser withdrew and established the house of Wormser Brothers, of course taking the secret of the peyotes with him.
These two houses very craftily called these peyotes by the name of Japanese buttons, and created the impression locally that they were for some mysterious use by the Japanese.
These two houses, in this way, have built up a commercial monopoly in peyotes for the whole United States, practically.
About forty miles east of Laredo and four miles from the Texas-Mexican Railway, is an ancient Mexican town of about fifteen families, called Los Ojuelos. It has a graveyard larger than the town itself. It is located close to the edge of some rough, rocky graveled hills, on which these peyotes grow wild; none are cultivated anywhere. They grow wild under the shelter of a bush on these rocky ledges.
[…]
The Mexicans who gather the plant do not pull it up by the roots, but merely cut off the tops, leaving the potato itself in the ground. The top part of this potato then rots. The lower roots then grow and three or four peyotes often thereby appear where there originally was but one. It requires from one to two months’ time properly to dry these peyote tops for the market.
In this village, Los Ojuelos, are two small stores run by V. Laurel and Bro., and the other by Gayetasio Ochoa, the latter being postmaster. The villagers gather these peyotes and turn them into these two stores for supplies, getting about $2.50 a thousand for them. An industrious worker can not gather more than two hundred per day.

 

Modern workers appear to be able to harvest faster.

It used to be you’d go out for a couple of hours and you’d find 500 to 1,000 plants,” he said. “Now, you go out for six hours and you don’t come back with much.
Mauro Morales in Roebuck 2004.

In three hours his two brothers gathered about five potato sacks, some 4000 buttons in all.”
De Cordoba 2004 speaking of his time with Salvador Johnson.

 

Some statistics from the Texas Department of Public Safety (DPS)

Year

# of Buttons

Reported Sold

Total Sales

($US)

Price per Thousand

($US)

Notes

1986 1,913,212 $149,307.52 $ 78
1987 1,766,409 $137,046.30 $ 78
1988 1,575,766 $129,051.01 $ 82
1989 1,572,102 $129,619.62 $ 82
1990 1,772,126 $156.607.29 $ 88
1991 1,859,189 $182,544.02 $ 97
1992 1,886,434 $192,695.25 $102
1993 No data. No data. na [data from DPS in 2005]
1993 1,978,646 $210,247.60 $106 [data from DPS in 2011]
1994 No data. No data. na [data from DPS in 2005]
1994 2,184,739 $246,632.94 $113 [data from DPS in 2011]
1995 No data. No data. na [data from DPS in 2005]
1995 2,252,174 $234,750.20 $104 [data from DPS in 2011]
1996 2,258,993 $278,579.50 $123
1997 2,317,380 $274,500.62 $118
1998 2,076,167 $277,119.71 $133
1999 2,093,335 $335,823.02 $160
2000 2,057,020 $310,722.10 $151
2001 1,934,600 $360,676.00 $186
2002 1,820,847 $422,289.50 $232 [data from DPS in 2005]
2002 1,703,914 $404,859.50 $237 [data from DPS in 2011]
2003 1,779,170 $416,727.00 $234 [data from DPS in 2005]
2003 1,781,170 $416,727.00 $234 [data from DPS in 2011]
2004 1,658,195 $393,572.50 $237 [data from DPS in 2005]
2004 1,304,691 $304,002.50 $237 [data from DPS in 2006]
2004 1,669,806 $393,572.50 $236 [data from DPS in 2011]
2005 1,565,534 $407,789.50 $260
2006 1,619,115 $463,714.75 $286
2007 1,605,345 $474,321.80 $296
2008 1,475,469 $463,148.00 $314
2009 1,604,623 $493,834.00 $308
2010 1,483,697 $459,699.00 $310
2011 1,413,846 $466,590.50 $330
2012 1,106,209 $434,609.00 $393
2013 1,363,978 $530,230.00 $389
2014 1,128,787 $426,300.00 $378

The above reflects the reported activities of the licensed distributors (and their employees) based on figures provided by the Texas Department of Public Safety (DPS).

There are presently three peyote distributors and this has been true since 2006. Four licensed peyote dealers were still in operation in 2003-2005. Prior to that there were five and before that there were more. I have heard that a fourth has submitted his paperwork to DPS. It appears to be a relative of one of the existing distributors who is growing older and facing retirement in the future.

It is an interesting point of clarity that the licensed distributors who sell peyote prefer to be called “peyote dealers” rather than peyoteros.

Math in the fourth column is mine so any mistakes there are mine.

The late 1990s is when the average size plummeted for the buttons showing up in NAC meetings in central Texas. In the late 1990s sacks of Mexican peyote became more common.

 

It is very easy to see that a lot more peyote populations exist in Mexico than are inside of the USA.

The distribution of Lophophora williamsii

map-Anderson-Koehres

The suggested distribution of peyote
Composite map created from Anderson1980 & Koehres

Concerning this map:
It is important to be aware that peyote grows only in soils that are acceptable to it. This is true within any region it occurs, and therefore this map suggests there is a far more substantial distribution and many more populations than really exist (or have ever existed) within the shaded zones.

Anderson created this map by placing the reported herbarium collections, some of which are now known to be erroneous, as dots on a map and then drawing a line encircling them all.
For those reasons reason it is extremely doubtful that any peyote actually lives within large sections of the indicated areas. To put it another way, the presence of a solidly shaded area does not imply a continuous peyote population anywhere within it. It certainly does not indicate a lawn of Lophophora.

Koehres created his map similarly but incorporates his own field information which is superior to that of Anderson.

 

How difficult is peyote to grow?

It is easy to find it said that peyote is difficult or even impossible to grow.

After interviewing peyoteros in 1988 John Morthland wrote,

Indeed, peyote is almost impossible to cultivate. Once a seed germinates, the plant takes five years to grow big enough for picking, and the root of a harvested peyote takes nearly that long to bloom again.

 

Morthland’s “almost impossible” estimates are actually optimistic despite being shorter than reality. A professional cactus cultivator would consider them to be more typical than impossible and would simply take those numbers in stride in his or her production planning.
The reality is that peyote is among the easiest and the most forgiving of the cactus species to grow from seed.

Peyote, like any other cactus species, is fairly slow growing which is why what is developing contains the elements of a crisis-in-the-making. After cultivation begins in a meaningful way, more than a decade can be expected to elapse prior to the first acceptable harvest.

The widely circulated meme that cultivation is somehow either a difficult challenge or an absolute impossibility is probably just simple propaganda that conveniently serves licensed distributors, law enforcement and the powers-that-be alike.
Cactus cultivators have not reported similar results as the image of what is largely Lophophora diffusa in the next photograph should illustrate. These seedlings shown below are growing in Prague.

 

diffusa-in-prague

It is also surprisingly common to find it said that peyote cannot be cultivated anywhere outside of its natural ranges. People like Leo Mercado who, in theory, have proved this to be in error have actually proven just how right Voltaire was when saying:

It is dangerous to be right in matters on which the established authorities are wrong.”

At least, we now understand WHY peyote cultivation is considered to be impossible: not because of any technical issues but rather because the federal, state and/or local police will come and destroy the peyote plants if they learn of their existence.

The Peyote Foundation 1998

The Peyote Foundation 1998

Leo’s “impossible” shade house in 1998.
Taken with Leo’s permission from their newsletter

 

That is only the beginning of this story as it is clear that the cultivation of peyote is easy. Cultivation of someone else’s spiritual sacrament, however, rapidly becomes a quite different subject altogether.
The one very significant hurdle for the cultivation of peyote is a lack of acceptance by more than a relatively few members of the NAC.

This will be explored in more detail when this commentary continues.

 

More is still to come with part 2.

 

Related Reading Off-Site – Cactus Conservation Institute’s website

 

Additional Related Reading Off-Site – Edward Anderson’s thoughts on the Peyote Crisis.