
Abstract:
Under close examination, some of the events known popularly as "crop circles" have displayed
unique and surprising alterations of soil and crop structures suggestive of a genuinely unknown mechanism of
formation. The project reported herewith consists of an examination of soil from the location of a 2003 season
crop circle in the US. Sampling and analysis were performed in April of 2004. Results of both magnetic component
extraction and commercial agricultural soil analysis are discussed, along with considerations for future
analytical protocol.
Introduction:
One of the most intriguing North American crop circles of the 2003 agricultural season appeared
overnight between 23 and 24 August, near Locust Grove, Ohio. This formation was quickly dubbed "the Serpent Mound
Crop Circle" due to the noteworthy fact that it appeared in a soybean field less than a kilometer from the
so-named ancient sacred site of the Adena people.
Investigation of the formation was prompt and received considerable media coverage, both locally
and on-line. We were aware of the event within a few days of the occurrence, however with other projects
prevailing, the opportunity to investigate the event ourselves at the time did not materialize. Summaries of the
crop formation and assorted investigative findings by others may be found as referenced online at http://www.cropcirclenews.com/modules/news/article.php?storyid=164.
Analysis of crop and soil conditions has to date not been reported on by the original
investigative parties, although plant, seed and soil sampling was performed. Claims exist as well that EM and
nuclear radiation anomalies were observed, however details have also not yet been presented. The primary
investigative effort for this formation was carried out by members of the recently organized ICCRA (USA).
The formation continues to generate interest and speculation in the international crop circle
community, primarily among those focused on the interpretation of geometric meaning involved with the
formation.
On 3 and 4 April, 2004, NR attended a weekend crop circle research conference held in Adams
County, Ohio. This event was sponsored by ICCRA, and saw a variety of disciplines and facets of the phenomenon
and its research represented. Following the closing presentations of this conference on 4 April, NR and several
other attendees made a trek to the nearby field where the Serpent Mound Crop Circle had appeared over seven months
previous.
Observations were made of the site by NR, and will be recounted here. A small set of soil samples
was procured, and later, a variety of test protocols were used to examine the chemical and physical properties of
the soil. Our objective may be best established in the form of a question: what can we learn from the site of a
claimed anomalous crop circle event, over seven months after its appearance, at the start of the next agricultural
season?
The Crop Circle Location and Its Appearance:
From NR's notes:
"On the afternoon of Sunday, 4 April, I arrived at the location of the former crop circle at
about 14:30 local. Prevailing weather was cool (40°s F) and partly cloudy, and the field conditions were amenable
to easy movement. Last rainfall had been at least 48 hours previous, so the soil was moist but not muddy. Several
other participants of the weekend conference were at the site, including Dr. Charles Lietzau, Ted Robertson, Dan
Deters, and two other attendees. Ted Robertson was very helpful in pointing out the location of the formation,
still faintly visible on the ground in reverse, due to a higher density of downed stalks. The field had not been
tilled or planted, and the soil surface was fairly compact and flat from the winter’s snow burden.
The field of concern is an irregular plot bordered by Ohio SR 73, Brush Creek, and a minor branch
of Brush Creek called Weasel Run (USGS listing). The formation had appeared toward the northeastern end of the
field. The axis of symmetry of the formation appeared to be normal to the angle or path of Route 73, and at about
a 60 degree angle east of north.
As I walked the former formation, I observed as had others
that day that in a large portion of the area that had been flattened in approximately 1 to 1.5 meter wide rings,
an early growth of the low common broadleaf weed called "Deadnettle" or "Henbit" had appeared. The paths of the
former rings were now sprinkled with the cheerful purple blossoms of the Deadnettle in contrast to the outside
regions of the field, where blooming of the plant was sparse. (click pic to enlarge). A likely reason for
the dainty show may have been advantageous growth conditions due to the additional ground cover provided over
winter by the downed bean stalks.
Apart from the purple strewn ring pathways, the form of the central "vesica" or cat’s eye shaped
region of the formation could be easily seen, as well as the larger outlying swirl circle to the north of this
feature.
No EM or nuclear surveying was performed, as the appropriate equipment was either not present or
had not been properly calibrated with a standard. Our interest lay mainly in a careful examination of the soil of
this formation, and procurement of samples. This was what I busied myself with."
Soil Sampling:
Seven locations were selected on a meridian line that
bisected the long dimension of the central vesica shape, and formed the axis of symmetry. Please reference Figure
A (click pic to enlarge) for placement. Two outlying control locations, each approximately thirty meters
beyond the furthest downed region of the original formation were selected, along with the five formation- related
points shown. Credit is given to Mr. Ted Robertson of Ellettsville, Indiana, for providing the background map
shown with our sampling site annotations.
At each location, we used a wooden spoon to procure approximately 500 ml of soil from both
surface (from 0 to 2 cm depth) and an equal amount from a depth greater than 3 inches, or 7.5 cm approximately.
Each soil volume was sealed into a ziplock plastic baggie and labeled on the outside with black permanent marker.
Thus, a total of fourteen soil samples were taken from the formation site.
The selection of sample sites, while extemporaneous, also provided inclusion of three primary
zones that we believe are critical to understanding crop circle dynamics. The necessity of controls is obvious.
We also need to understand differences, if any, between the affected soil in the downed regions within the
formation and non-downed regions also within the formation.
The sampling procedure followed should be considered a valuable training exercise and proving
ground in addition to its primary objective. Even as the samples were taken, at least two points for future
improvement in protocol were seen and noted! C. Lietzau pointed that without washing the sampling spoon between
each sample, cross contamination could occur that could potentially skew quantitative analysis or chemical
assaying. This was acknowledged. To enter this as a viable error source into our results appeared to be the most
viable option for now. We thus observed and approximated the typical amount of clinging dirt from sample to
sample, given a physical wipe, and entered this as a maximum contamination figure of one half gram (500 mg) dried
soil per sample, to be compared with the final dried weights of the samples proper. A better sampling device may
also be in order - wood was used to prevent ionic migration from metal spoons or spades - however a device like
a core sampler fabricated from ceramic or Teflon might provide the ultimate in sample integrity, also delivering
samples at different core depths.
Field History:
On 18th April, we spoke with Mr. George McCoy who farms the field in which the crop circle had
appeared. George was helpful and knowledgeable, and provided us with some quality information for our
understanding.
The field in question has been farmed no-till for at least six years. The crop seed used for 2003
was Roundup Ready soybean, purchased locally. (Monsanto designation listed as "glyphosate-tolerant soybean line
40-3-2") Going back in rotation we find corn, hay, and soybeans in that order. Herbicides used included Roundup
and Atrex. In 2003, Roundup was applied twice.
George acknowledged that the region of the field closer to Weasel Run had zones that were quite
iron rich and reddish, as we noted in our "furthest" control soil samples. To his knowledge, no houses or
outbuildings had ever existed on the field property, however to the northwest was a location said to have once
supported an historical Indian (Shawnee) village. We would presume that the region of the field would also have
- in centuries past - been frequented by the Moundbuilder peoples.
Soil Analysis Part I - Magnetic Particle Extraction:
A. Procedure:
All soil samples were transported to Gibsonburg in their respective baggies. Dessication of the
samples was performed in NR's garage attic, a warm dry undisturbed location. Each soil sample was emptied out onto
a pencil labelled paper plate, and the original transport baggie was placed next to it open. Paper towel squares
were gently placed over each plate to afford dust shielding. Each sample was carefully screened by hand for worms,
which when found, were transplanted into NR's garden. (A zero casualty experiment is a good experiment!)
Soil samples were allowed to air dry for eight days, until no discernible moisture could be seen
and felt upon breaking open clods. All samples were re-packed into their respective baggies and transported to our
Toledo lab location.
Each soil sample was in its turn decanted in portions into
a glazed ceramic vessel serving as a mortar. A 2 cm diameter silicon carbide tube was used as a pestle, and each
sample was ground as finely as possible. The samples were each then sifted through a 316 stainless steel 12 mesh
screen, resulting in a more or less uniform particle distribution for the final sieved product. Between 300 and
450 ml of end product for each of the fourteen samples resulted. Gravel and larger sieve removals were transferred
to labelled residue baggies. Polycarbonate beakers, screen, and grinding tools were dry wiped clean between each
sample. (click pic to enlarge)
For each sample, we then decanted slightly more than 150 ml of the sieved product into a separate
beaker, and tapped down to a precise packed volume of 150 ml.
Our rectangular test magnet (ferrite, 1" by 2" by 3")
measuring 1230 gauss at the center of the used face was wrapped in a clean baggie to provide a tight plastic
"skin" around the magnet surface. The magnet was held at a 45o angle over a large plastic tub, and the contents of
the beaker holding the 150 ml sample were slowly sifted across the surface of the magnet, allowing such magnetic
particles as would to be retained. Upon completion of the operation, a slight puff of air was used to dislodge
non-magnetic clinging dust. (click pic to enlarge)
The wrapped magnet was transferred to an open plastic baggie that had been pre-weighed to
milligram precision (Stanton Unimatic lab balance). The magnet was then removed upward, allowing the attracted
contents to fall into the outer baggie. The magnet wrapping baggie was then also removed and discarded. The
baggie containing the magnetic soil residua was then re-weighed and the net weight of the residue was recorded.
Residue bags have been retained for our records and further work.
Each sample of soil was treated identically, between 15 April and 18 April. The remainder of each
sieved soil sample was set aside in labelled baggies for agricultural soil testing (next section).
B. Results:
Every sample tested produced a small quantity of magnetic residue. The sample size and balance
resolution was found to be quite adequate for the protocol used and residue quantity recovered. We gave careful
consideration to the question of proper units for expressing our results. Because of unknown and/or variable soil
composition, we decided to express the content of magnetic particulates in the form of milligrams per unit volume
(a derivative of planar soil area) rather than milligrams per gram, as has been the previous traditional unit used
by W. Levengood. However, in order to provide a useful comparison, we measured the weight of several of our 150ml
samples and designated a rough average of 180 grams per sample. Using this figure, we can then easily render the
results in milligrams per unit weight (mg/g).
The following tables and plot display our results:
Table 1: Raw weight data
| Sample # |
Tot Post Wt (g) |
Sample Bag Pre-Wt (g) |
Net Magnetic Residue (g) |
Soil 150 ml Wt |
 |
| AS |
3.869 |
3.412 |
0.457 |
|
| A3 |
3.625 |
3.388 |
0.237 |
|
| BS |
3.657 |
3.434 |
0.223 |
|
| B3 |
3.699 |
3.455 |
0.244 |
|
| CS |
3.563 |
3.414 |
0.149 |
|
| C3 |
3.472 |
3.385 |
0.087 |
|
| DS |
3.73 |
3.457 |
0.273 |
|
| D3 |
3.637 |
3.385 |
0.252 |
|
| ES |
3.65 |
3.389 |
0.261 |
|
| E3 |
3.794 |
3.4 |
0.394 |
188.65 |
| FS |
3.836 |
3.388 |
0.448 |
|
| F3 |
3.93 |
3.425 |
0.505 |
179.59 |
| GS |
5.432 |
3.47 |
1.962 |
|
| G3 |
4.561 |
3.38 |
1.181 |
|
Table 2: Calculations for magnetic content
| Sample # |
Content of Magnetic Species mg/ml |
Content of Magnetic Species mg/g (185g per sample avg.) |
 |
| AS |
3.05 |
2.47 |
| A3 |
1.58 |
1.28 |
| BS |
1.49 |
1.21 |
| B3 |
1.63 |
1.32 |
| CS |
0.99 |
0.81 |
| C3 |
0.58 |
0.47 |
| DS |
1.82 |
1.48 |
| D3 |
1.68 |
1.36 |
| ES |
1.74 |
1.41 |
| E3 |
2.63 |
2.13 |
| FS |
2.99 |
2.42 |
| F3 |
3.37 |
2.73 |
| GS |
13.08 |
10.61 |
| G3 |
7.87 |
6.38 |
Table 3: Table 3: Sorting by sample type
(Blue = controls, Red = formation downed, Green = formation not downed)
| Surface Samples |
Net Magnetic Residue (mg) |
Content of Magnetic Species mg/ml |
Content of Magnetic Species mg/g (185g per sample avg.) |
 |
| AS |
457 |
3.05 |
2.47 |
| BS |
223 |
1.49 |
1.21 |
| CS |
149 |
0.99 |
0.81 |
| DS |
273 |
1.82 |
1.48 |
| ES |
261 |
1.74 |
1.41 |
| FS |
448 |
2.99 |
2.42 |
| GS |
1962 |
13.08 |
10.61 |
 |
| A3 |
237 |
1.58 |
1.28 |
| B3 |
244 |
1.63 |
1.32 |
| C3 |
87 |
0.58 |
0.47 |
| D3 |
252 |
1.68 |
1.36 |
| E3 |
394 |
2.63 |
2.13 |
| F3 |
505 |
3.37 |
2.73 |
| G3 |
1181 |
7.87 |
6.38 |

As may be easily noted, a range of magnetic particle distribution exists, although a correlation
to specific zones of the formation or control areas does not seem strong. Both surface and subsurface samples from
site "G" contained dramatically more ferrous content than other regions. We noted by eye the reddish hue of the
soil from this location, and acknowledge George McCoy's confirmation of the iron rich (oxidized) nature of that
spot.
While statistics may be applied to the raw data, our small number of meaningful samples would
likely obfuscate any data treatment. We allow the data to stand as is, in a qualitative mode, or as a first order
evaluation.
C. Discussion:
In previous research  by Levengood
et al, the distribution of anomalously high amounts of ferrous particles in crop circle formations is discussed.
Certainly, the notion that such a component to the phenomenon exists has become part of the prevailing crop circle
paradigm. Numerous other formation investigators have performed in-situ magnet dragging tests and have claimed
that their magnets are loaded with ferrous residue when they are done. We would suggest, however, that these tests
have often not been performed with a precise and documented protocol and sufficient controls. In discussion with
Nancy Talbott of BLT Research, we find that soil sampling and analysis has generally lagged behind plant stalk
sampling in procedure and treatment.
In a more general evaluation of previous work on soil analysis, we find that two very fundamental
components are noticeably absent. First is a thorough (or at least stated) understanding by the crop circle
research community as a whole as to what constitutes typical agricultural soil content. Secondly, there seems to
be a previous lack of use of accredited agricultural laboratories that routinely do in-depth analysis of crops and
soil.
If we focus specifically on the concept of magnetic extraction, we must ask ourselves, "what do
we expect to find here?" The answer would seem to be "anomalous quantities and forms of magnetic media." The key
to this is the term "anomalous." What constitutes anomalous? In his discussion of the claimed H- Glaze found at
Cherhill, UK, 1993, R. Ashby disclosed the discovery of Fe3O4 magnetite in the form of an amorphous glaze and
micro-spherical species . In a number of unpublished research
reports, Levengood and Burke have repeatedly cited the observation of microspherical Fe or magnetic iron oxide in
crop circles, presumed to have been of meteoric origin. However, in order to ascertain the anomalous, we have to
first thoroughly understand what is not anomalous!
Under an optical microscope, we find that a portion of our extracted magnetic material from the
Serpent Mound formation seems to be non-magnetic coating or dust on magnetic particulates, dragged along for the
ride, so to speak. By performing a swirl in distilled water over a magnet, the magnetic residue from sample B-3
was washed and "refined". We find that about 30% by weight of the residue rinsed off, leaving a much purer
collection of magnetic species to examine. We also note that aqueous separation may indeed prove a more viable and
complete extraction method that we should consider in the future.
Much of the material remaining consists of irregular grains ranging from 100 microns up to a
millimeter in diameter of what appears to be natural magnetite Fe3O4. Some smaller darker grains of
irregular shape may well be meteoric or from abrasion of plow points, discs, and harrows in the field, in years
previous to the no-till farming. We also observed in our washed residue some number of spherical particles, from
about 10 microns to perhaps 50 microns diameter. The fabled microspheres of crop circle lore? What are these
structures?
One valuable "forensic" clue concerning the possible origin of the crop circle microspheres came
to our attention recently . Microspherical fly ash from coal
fired power plant exhausts, although now scrubbed by electrostatic and magnetic precipitation to a level claimed
to be over 90%, can contain up to 40% magnetic Fe3O4 - in the same shape and size as the better known glassy
sphere (aluminosilicate) fractions! In short - a large portion of fly ash emptied into our ecosphere over the
decades consists of magnetic iron and magnetite microspheres identical to those cited in crop circle studies.
Soils worldwide may well be highly loaded with these species, quite apart from (though not necessarily refuting)
meteoric origins. The US Clean Air Act of 1970 purportedly imposed limitations and controls on fly ash, as well
as SO2 and heavy metal fractions, however specific data relating to fly ash emissions by annual weight are
disturbingly difficult to find. We do find references that the annual US production of fly ash combustion
by-product is on the order of 50 million metric tons in recent years .
We have in our lab a sample of class F fly ash, and have
performed a magnetic extraction on a small portion. Indeed, a great number of magnetic dark microspheres can be
seen under the view of our microscope. (click pic to enlarge)
If the form of magnetic components in the soil is disregarded, do we find any evidence
that in any of our sampled locations there is an anomalously high concentration of these particles in an
absolute sense? Again, we must ask, "what constitutes anomalous?" In numerous lab reports by Levengood and Burke
since 1995, a figure of "0.4 mg/g" is cited as being a maximum typical figure for magnetic species content in
agricultural soil. The origins of this figure remain unclear and anecdotally referenced. We investigated this
topic recently.
What we have discovered is that soil science acknowledges a very broad range of possible magnetic
content in soils - entirely dependent on location and local geology! An excellent short resource paper by
Thorleifson describes the magnetic content in soil across
Canada as varying over an order of magnitude between .2 g/kg (identical to milligram per gram) and 5 g/kg. Thus
it would seem that the .4mg/g figure for maximum content in typical soil may actually be on the low end of a broad
range of soil variability. It would also seem that with the exception of control soil "G" in the near bottomland
zone closest to Weasel Run, the magnetic content of our Serpent Mound formation soil samples lies entirely within
a non-anomalous range of concentration.
Thus we come back to our questions about what constitutes the anomalous; do we find any anomalous
magnetic material in our soil samples from the Serpent Mound formation? To the extent sampled, it would appear
not. There does not seem to be compelling evidence that the magnetic materials extracted show a strong pattern
of either quantity or form that relates directly to the crop circle formation. We temper this however with the
statement that for true evaluation a far greater sample density with many multiple control positions would be
needed.
Soil Analysis Part II - Commercial Agricultural Testing
A. Procedure:
In March of 2004, we established contact with Mr. Mark Flock of Brookside Laboratories in New
Knoxville, Ohio. Mark indicated that a thorough regimen of chemical / compositional tests were available for soil
samples, and have formed a basis for agricultural science for many years. For a modest fee, approximately 50ml of
sieved dried soil could be analyzed for chemical content, organic content, and cation exchange capacity. Mr. Flock
was unfazed by the admittedly unusual circumstances of the samples, and has been most helpful in further technical
discussion since.
Approximately 75 ml of eight of the fourteen original soil samples taken from the Adams County
location were packed and prepared for analysis by Brookside's technical staff. We hand delivered these to the New
Knoxville facility on 23 April, 2004. The standardized test ordered for each sample was designated as the
Brookside S001B protocol.
B. Results:
On 28th April we received results from Brookside, and made an initial examination of the numbers
included. All data was conveniently recorded on two run sheets, copies of which are appended herewith as Example
A and B.
 |
 |
| Example A |
Example B |
A number of subtle relationships seemed apparent, and on 29th April, we conferred with Mark Flock
of Brookside in order to walk through the results, and consult his knowledge and experience base.
There exist several cases where soil from within the formation differs from the control regions A
and G, or a trend that would seem to relate was observed. This was more apparent on the surface soil
samples than the subsurface. All of these cases were found among clay fraction cation species, and "extractable
minors". This latter category concerns elements that are present in the soil in parts per million, and may include
both compounds and ionic forms.
The cation species wherein we see a trend related to the formation include:
Calcium - a slight increase in saturation percent over controls (saturation percent indicating
the amount of a particular cation in the soil divided by the total cation capacity for that soil sample)
Magnesium - a slight decrease in saturation percent over controls.
Potassium - a slight decrease in saturation percent over controls.
In extractable minors, we find:
Boron - a slight increase in ppm over controls.
Iron - a slight increase in ppm over controls. Fe in this extractable form is not to be confused with magnetic
Fe3O4 or Fe as discussed in the previous section of this paper.
Mr. Flock indicated that in the table of exchangeable cations, a maximum value of 7% to 10%
deviation may be expected in raw value (not the calculated saturation percent) among samples from a single
relatively homogeneous field, from identical depths. Mark’s opinion was that disregarding the circumstances, the
differences in the aforementioned five elements, while not dramatic trends, seemed significant and would at least
be worthy of further investigation. The Ca deviation was of particular interest, as was the B (boron).
Comparing the subsurface control samples with the single subsurface sample for area E (in the
vesica shape) we find the relationships to be somewhat less clear. We also find deviations between surface and
subsurface samples in the same locations. This was not surprising, in Mark’s view.
We inquired with Mark as to whether the spread of values for soil components would be of use in
predicting whether crops growing in those same areas the next season would be more lush and vigorous, or
attenuated. He indicated that this was highly dependent on the crop planted. If the same crop were planted a
second time, he felt that it might be possible that the increased Ca and B would promote better growth, but this
was very speculative. We furthermore inquired as to whether Ca, Fe, and B could potentially leach into the surface
soil from downed beanstalks over winter. Mark felt that in his experience, this was unlikely with no precedence to
support it.
Overall, Mark felt that George McCoy’s field was exemplary and fertile, and he was impressed with
the high amount of Mn (manganese) present. One suggestion levied for Mr. McCoy was that the content of zinc (Zn)
might need to be raised for optimum corn growth.
C. Discussion:
While commercial agricultural analysis has apparently been under-utilized by crop circle research,
we find at least one anecdotal account of a shift in the level of an apparently ionic species (Na) in grass
stems . In previous analytical work done for BLT Research,
calcium carbonate and calcium oxalate have been encountered in soil samples from both crop circle and UFO landing
trace cases. The shifting in the relative saturation percents of calcium, as well as Mg and K from the Serpent
Mound crop circle soil samples should provide incentive for further similar testing, although we admit that little
can be concluded from this small initial effort. Access to and processing of soil samples from high strangeness
crop circle cases in 2004 and beyond will be essential.
The shifting of cation species, if found to be a repeating property of crop circle soils must be
considered carefully. If we apply deductive reasoning, we find that ultimately only three mechanisms can exist
for this phenomenon:
- Ca, B, and Fe were added and K and Mg were extracted to and from the surface zone soil by unknown physical
means.
- The forms of Ca, B, Fe, K, and Mg were altered from cationic form to a compound form, or vica versa. In
either case, the resulting form may not measurable by the same instrumentation as the starting form.
- Some mechanism of (apparently low energy) nuclear transmutation is invoked.
Occam's Razor would suggest explanation number two as being the most reasonable. However, only
repeated observation of trends and consideration of the properties of the included elements will clarify what
biological and or chemical process would influence those particular components. We must also consider the remote
possibility that the action of human visitors in the form of soil compaction from footsteps might be involved.
This does not, however, easily explain the changes seen in the sample from location "C" - within the formation,
but not downed.
Conclusions and General Discussion:
The success of this project must be considered at several levels. It is our opinion that our
forensic approach to the phenomenon and the event is worthy of application toward future events of its kind.
We examined selected soil from a claimed high strangeness crop circle over seven months after the
event, and would conclude the following:
- A rigorous procedure for magnetic particle extraction showed little meaningful relationship between
magnetic (Fe and Fe3O4) particulates and soil sample position inside and outside the formation.
- Commercial agricultural analysis of soil samples may show a subtle but viable shifting in the
percent saturation of cation species in clay soil fractions within the crop circle area, versus controls.
Affected species include Ca, K, Mg, B, and Fe.
In addition to the analytical conclusions, we have found much of value in the learning and
refinement of methodology. We also have noted a variety of caveats and shortcomings of protocol that must be
addressed in any future experimental procedures of this type. What have we learned along these various lines?
- The heterogeneity of crop circles and their parent fields is such that no substitute exists for maximum
sampling! At least for soil analysis, the higher density of sampling the better. We are far from a point where
statistical treatments can be used that would permit us to reduce soil sampling numbers. Raw data and sampling
must be maximized for the foreseeable future.
- A consistent protocol for sample acquisition and treatment must be documented and adhered to. The same
minutae of procedure should exist in the field as would exist in a commercial or academic lab. Sophistication
of tools is of far less concern that appropriate protocol.
- Ferrous microspheres, long held in crop circle research to be of meteoric origin, and observed in our
own samples, may be of terrestrial origin in the form of coal combustion fly ash fractions. This does not rule
out the possibility of meteoric particulates, however it casts a greater onus for proof upon such claims.
- The value of agricultural science and testing is indespensible. The lack of use of this resource
constitutes one of crop circle research's great shortcomings. We do acknowledge that the expenses involved are
considerable, and that only additional financial support from institutions combined with possible cooperative
efforts with soil scientists and testing firms can address this.
- Another often under-utilyzed valuable resource is the one person who knows the crop circle situation the
most intimately - the farmer. Farmers' knowledge of their fields' history and treatment may hold supremely
important clues in high-strangeness crop circle cases.
In the end, no firm answers are available from such a truncated study as this, nor were any
anticipated. However, we are extremely intrigued by the hints of cation activity in the soil, and find in this
modest evidence plenty of reason to sample future crop formations in similar - but far more exhaustive - fashion.
Intuition is an important tool to the detective or scientific criminologist, and it was intuition combined with a
respect and appreciation for the majesty of chemistry that led us to these results. And as suspected, we learned a
lot along the way.
It would be tempting to devote a closing ramble to the speculation of how the results of this
study support this or that model of crop circles. We must refrain however - it would not be appropriate. Too many
years and valuable scientific man-hours have been spent in presumption. For simple concepts or anomalies, this is
not a major faux pas. Scientific Method is based on the acquisition of evidence to support or refute a hypothesis.
However for phenomena as rich and complex as crop circles, the researcher / anomalist must be very open and
accomodating of a continually re-adjusting body of evidence. Many good minds have felt frequently that something
is looking back up our microscope at us here, with the faintest hint of a smirk. We would not dare to argue. So
what then is our duty in this whole sordid affair? What should our mindset and methodology be? We are the
detectives, sworn to use our intuition, our resourcefulness, our minds, as well as the good tools of science, to
solve a mystery and solve it with all the tenacity of Sherlock Holmes tracking the elusive Professor Moriarty. We
will prevail.
We would like to thank the following individuals for their contributions and inspiration: Nancy
Talbott, W.C. Levengood, John Burke, Jeff Wilson, Dr. Charles Lietzau, Ted Robertson, Roger Sugden, Delsey
Knoechelman, Kelley Theofilos, George McCoy, Mark Flock, and Dr. Samuel Faile.
References:
- Levengood, W.C. and Burke, J.A. (1995) "Semi-Molten Meteoric Iron Associated with a Crop Formation."
Journal of Scientific Exploration, Vol. 9, No. 2, pp. 191-199
- Lab Report #122 Edmonton, Alberta, Canada - 1999 BLT Research Inc. http://www.bltresearch.com/edmonton.html
- Ashby, R. (2001) "The H-Glaze" http://www.xstreamscience.org/H_Glaze/h_glaze_0.htm
- "Coal Fly Ash - Material Description" (2003) Turner Fairbank Highway Research Center, US Department of
Transportation Federal Highway Administration http://www.tfhrc.gov/hnr20/recycle/waste/cfa51.htm
- Kalyancu, R.S. and Olson, D.W. (2001) "Coal Combustion Products" US Geological Survey Fact Sheet 076-01 http://pubs.usgs.gov/fs/fs076-01/fs076-01.html
- Thorleifson, L.H. (2000) "Ferromagnetic Minerals in Canadian Soils: Examples of Variability in Abundance
and Distribution" Geological Survey of Canada, The Demining Technology Information Forum Journal
- Wilson, J. (2004) private correspondence re: 1991 formation in grass, Troy, Illinois.
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