Biomineralisation by earthworms – an investigation into the stability and distribution of amorphous calcium carbonate
© Hodson et al.; licensee Springer. 2015
Received: 19 December 2014
Accepted: 15 April 2015
Published: 28 April 2015
Many biominerals form from amorphous calcium carbonate (ACC), but this phase is highly unstable when synthesised in its pure form inorganically. Several species of earthworm secrete calcium carbonate granules which contain highly stable ACC. We analysed the milky fluid from which granules form and solid granules for amino acid (by liquid chromatography) and functional group (by Fourier transform infrared (FTIR) spectroscopy) compositions. Granule elemental composition was determined using inductively coupled plasma-optical emission spectroscopy (ICP-OES) and electron microprobe analysis (EMPA). Mass of ACC present in solid granules was quantified using FTIR and compared to granule elemental and amino acid compositions. Bulk analysis of granules was of powdered bulk material. Spatially resolved analysis was of thin sections of granules using synchrotron-based μ-FTIR and EMPA electron microprobe analysis.
The milky fluid from which granules form is amino acid-rich (≤ 136 ± 3 nmol mg−1 (n = 3; ± std dev) per individual amino acid); the CaCO3 phase present is ACC. Even four years after production, granules contain ACC. No correlation exists between mass of ACC present and granule elemental composition. Granule amino acid concentrations correlate well with ACC content (r ≥ 0.7, p ≤ 0.05) consistent with a role for amino acids (or the proteins they make up) in ACC stabilisation. Intra-granule variation in ACC (RSD = 16%) and amino acid concentration (RSD = 22–35%) was high for granules produced by the same earthworm. Maps of ACC distribution produced using synchrotron-based μ-FTIR mapping of granule thin sections and the relative intensity of the ν2: ν4 peak ratio, cluster analysis and component regression using ACC and calcite standards showed similar spatial distributions of likely ACC-rich and calcite-rich areas. We could not identify organic peaks in the μ-FTIR spectra and thus could not determine whether ACC-rich domains also had relatively high amino acid concentrations. No correlation exists between ACC distribution and elemental concentrations determined by EMPA.
ACC present in earthworm CaCO3 granules is highly stable. Our results suggest a role for amino acids (or proteins) in this stability. We see no evidence for stabilisation of ACC by incorporation of inorganic components.
KeywordsCalcite ACC CaCO3 FTIR Synchrotron Amino acids Earthworms Stability
Approximately 20% of all biominerals are amorphous  and many of the crystalline ones form through amorphous precursors [2-4]. The most common amorphous phases are silica and amorphous calcium phosphate, but amorphous calcium carbonate (ACC) is increasingly being detected on the basis of its infrared or Raman characteristics, the lack of electron diffraction patterns in transmission electron microscopy (TEM) and / or through identification of its characteristic Ca bonding environments using X-ray absorption spectroscopy (XAS) measurements (e.g. [5-8]). Pure abiogenic ACC is highly unstable, transforming within minutes to the crystalline calcium carbonate polymorphs calcite, aragonite or vaterite [9-14]. Vaterite and aragonite are metastable under most surface conditions and transform to calcite (e.g. [11,12,15]). Despite its short life span in inorganic systems ACC has been reported from organisms as diverse as higher order plants, (where it is present as cystoliths in the leaves), , crustaceans , and ascidians or sea squirts . Results from the characterisation of various forms of biological ACC, and from inorganic experiments, suggest that the ACC present in biominerals may be stabilised by a variety of constituents and mechanisms. The magnesium ion has a higher hydration energy than the calcium ion; incorporation of Mg into ACC during its formation inhibits the dehydration stage during its crystallisation [19-21]. Phosphate is also known to become incorporated into ACC, either as a coating around ACC domains or within the ACC framework  and also inhibits its transformation to calcite [23-26]. Finally, it is also well known that a wide range of organic macromolecules including polysaccharides and proteins rich in the amino acids glutamic acid, aspartic acid, serine and glycine bind to the surface of ACC, isolating it from fluids and inhibiting its dissolution and crystallisation; such molecules can also bind strongly to free Ca2+ inhibiting or retarding its interaction with HCO3 − and CO3 2− during ACC formation and transformation [19,27-34].
Many species of earthworm secrete granules of calcium carbonate [35,36]. In granule-producing species the granules are formed within the earthworm’s calciferous glands. These glands contain a milky fluid that is a suspension of micron-scale ACC spherulites. As these spherulites pass through the glands they coalesce and crystallise forming millimetre-scale granules [37,38], dominantly composed of calcite but also containing remnant amorphous calcium carbonate and also vaterite and aragonite [38-42]. The granules, although much larger in size, have nevertheless the same spherical morphology as aggregates of calcite crystals produced in laboratory experiments that form when ACC precipitates from highly oversaturated solutions and crystallises to calcite via a spherulitic growth mechanism (e.g. [15,43]). Once formed from the ACC-rich milky fluid, the earthworm calcite granules are transferred from the glands into the earthworm oesophagus and from there they move down the intestine and are ultimately expelled into the soil.
Typically the ACC present in biominerals appears to fulfil one of two functions – either a rapidly accessible store of Ca for skeletal growth, or the production of mechanically robust, sometimes complex, skeletal architectures . However, neither of these functions seem likely for earthworm calcium carbonate granules; rather the calcium carbonate production appears to be related to pH regulation [44-48] with calcium carbonate precipitating when HCO3 − ions are in excess of those required to buffer tissue fluid pH. Thus the granules could be viewed as an excretory product.
Analyses of granules recovered from soil up to 28 days post-expulsion and stored in dry conditions for several months to years indicate that they can still contain significant quantities of ACC, suggesting that this ACC is unusually stable compared to synthetic ACC . The mechanism by which the ACC in earthworm granules is stabilised is not currently known. The purpose of the present investigation was therefore to determine whether the inorganic trace element chemistry of granules or the concentration of organic molecules present within earthworm-derived carbonate granules could account for the stability of the ACC. Our approach was to characterise the ACC content of granules and their chemical characteristics and to look for correlations between the two. We combined bulk analysis with spatially explicit analyses to address both compositional variation between granules formed by earthworms cultivated in different soils and inter- and intra-granular variation present in granules produced by individual earthworms. Additionally we carried out liquid chromatography and Fourier transform infrared (FTIR) spectroscopy to investigate the composition of the milky fluid from which the granules form. While FTIR can indicate the presence of organic material such as sugars and proteins, we chose to undertake more detailed analysis on the amino acids using liquid chromatography given the high levels of amino acids reported in studies carried out on other ACC-rich biominerals e.g. [18,50,51].
Materials and methods
Whole granule analysis
Earthworm-secreted calcium carbonate granules obtained in 2008 [52,53] were used in this study. In brief, 11 soils of differing properties were collected from around Berkshire, UK (see Additional file 1: Table S1). The soils were air-dried, sieved to < 250 μm and remoistened to a water content equal to 65% of their water holding capacity. Individual clitellate Lumbricus terrestris earthworms were kept in 300 g (dry weight equivalent) of soil for 27 days then the soils were wet sieved at 500 μm to remove freshly produced granules. There were six replicate treatments per soil and the granules produced in each of the six replicates were pooled for analysis. No granules were produced by earthworms kept in the most acidic soil (St Albans Wood, pH 4.3), leaving 10 sets of granules for characterisation. These granules are referred to in this study as “bulked granules”. Unless otherwise stated all the analyses reported in this paper relating to these granules are part of the current study and have not been reported elsewhere. For the current study the bulked granules (0.0410–0.1401 g of material) were digested in 10 mL of 5% analytical grade HNO3 and analysed by inductively coupled plasma-optical emission spectroscopy (ICP-OES) for a whole suite of elements.
In 2012 a further 7 granules from the bulked granule samples (collected four years previously in 2008) from the Hamble, St Albans Field and Soil Science soils were each individually analysed by FTIR for their ACC content following the same method as above. We also dissected out the calciferous glands from earthworms cultivated in the Hamble soil for 28 days and collected the milky fluid for bulk FTIR analysis.
Following the FTIR bulk analysis of the powders for % ACC in 2010 and 2012, these same powders were used for amino acid analysis in 2013. In addition, a further 5 individual granules each from the 2008 bulk granule Hamble, St Albans Field and Soil Science soil samples that had not been previously analysed by FTIR, together with 3 milky fluid samples extracted from the calciferous glands of earthworms cultivated in the Hamble soil, were also analysed for their amino acid content.
The intra-crystalline fraction of protein in the granules was isolated by bleaching for 48 h with 12% NaOCl following the methods of Penkman et al. ; no bleaching was undertaken on the milky fluid samples due to the lack of biomineral. Amino acids were extracted by demineralisation of the powders and/or individual granules followed by hydrolysis of the peptide bonds in strong acid (7 M HCl, 110°C, for 24 h). During the hydrolysis step, both asparagine (Asn) and glutamine (Gln) undergo irreversible deamidation to aspartic acid (Asp) and glutamic acid (Glu), respectively . The acid was evaporated to dryness and the amino acid pellet resuspended in the standard rehydration fluid used in the NEaar laboratory, which contains an internal standard (the non-protein amino acid L-homo-arginine, 0.01 mM) for quantification. Rehydrated samples were analysed by reverse-phase high-pressure liquid chromatography (RP-HPLC) following a method modified after Kaufman and Manley . This method allows the quantification of the L- and D- enantiomers of aspartic acid/asparagine (Asx), glutamic acid/glutamine (Glx), serine (Ser), alanine (Ala), tyrosine (Tyr), valine (Val), methionine (Met), phenylalanine (Phe), leucine (Leu), and isoleucine (Ile). Glycine (Gly), L-histidine (L-His) and L-threonine (L-Thr) are also detected. Procedural blanks and standards of known D/L values and concentrations were randomly interspersed with samples to allow calculation of the limit of detection (LOD) and monitoring of instrument performance. The two sets of bleached samples (bulked powders and individual granules) were prepared and analysed in separate batches by RP-HPLC and the LOD was calculated for each batch, using the average concentration of amino acids found in procedural blanks: LOD = [average blanks] × 3.
Previous X-ray diffraction indicated that the granules were predominantly calcite . For the current study we repeated this bulk XRD analysis in 2014 six years after collecting the granules, on powders produced by crushing several of the bulk granules. XRD scans were collected in reflection geometry with samples placed on a flat plate (zero-background holders) using a Bruker D8 Discover with CuKα radiation over a 2θ range of 3–90°(0.01°/step and 1 s/step). Patterns were compared to the standard mineral files compiled in the PDF2 database (ICDD PDF-2 Powder Diffraction File database) using the software EVA from Bruker. Phase quantification (weight %) was carried out with pattern-matching refinement of the crystalline phases using the Rietveld refinement software TOPAS .
Spatially resolved analysis
For the spatially resolved analyses a new set of granules were produced in 2013. Mature, clitellate Lumbricus terrestris were obtained from Worms Direct (Drylands, Ulting, Nr Maldon, Essex, CM9 6QS, UK). Individual earthworms were cultured in 300 g (dry weight equivalent) < 250 μm Hamble soil to which 100 mL of deionised water had been added (see  and Additional file 1: Table S1 for a full characterisation of this soil). The earthworms were kept in the soil for 39 days. Subsequently the soil was wet sieved to < 500 μm to recover granules and the granules were air-dried. The earthworms were transferred to individual petri dishes lined with moist tissue paper and left for 24 hours to depurate. The soil egested by the earthworms in this period was wet sieved at 500 μm and any granules were collected and air-dried. In total we used nine earthworms to produce granules. Two “old” granules (i.e. the granules had resided in the soil for up to 39 days) were collected from the bulk soil by sieving and two “fresh” granules (i.e. the granules had been secreted within the last 24 hours) were collected from the depurate secreted by the same randomly selected earthworm. These granules were prepared for the spatially resolved analyses. Hereafter, the “old” granules are referred to as Old-1 and Old-2, and the “fresh” granules are referred to as Fresh-1 and Fresh-2.
In order to avoid the use of resin and any potential subsequent organic contamination we attempted to prepare sections of granules for spatial analysis using either a microtome or a cryomicrotome. However, during trials we found the granules were too friable to be cut in this fashion, even when the granules were covered in adhesive or held in epoxy resin. Therefore polished sections were prepared by embedding the granules in EpoFIX (Struers) resin blocks, which were ground on a coarse diamond wheel to expose the centre of the granule. The exposed surfaces were mechanically polished for 3–5 minutes using a 0.3 μm particle size corundum slurry. The bases of the resin blocks were subsequently ground until the total thickness of the block was ~3.15 mm.
The spatial distribution of ACC in the Old-1, Old-2, Fresh-1 and Fresh-2 granules was evaluated through synchrotron-based μ-FTIR maps acquired at Beamline B22 (Multimode InfraRed Imaging And Microspectroscopy, MIRIAM) of the Diamond Light Source on a Bruker Vertex 80 V FTIR instrument connected to a Hyperion 3000 microscope. Spectra were collected in reflectance mode with a liquid N2 cooled mercury-cadmium-telluride broadband detector at a resolution of 4 cm−1 by co-adding between 128 and 1024 scans per point. Large-scale maps (c. 650 μm × 760 μm, aperture 25 × 25 μm) were produced for the Old-1 and Old-2 granules using an internal globar source and a gold mirror as a reference. For the Fresh-1 and Fresh-2 granules, large maps (740 μm × 750 μm, aperture 20 × 20 μm) were acquired using the synchrotron source and a zinc selenide slide as a reference. After evaluating areas with potentially high ACC contents on both old and fresh granules, detailed maps (c. 100 μm × 150 μm) were produced using the synchrotron source but with a 6 × 6 μm aperture and a gold mirror reference. In all cases, step size was equal to the aperture dimensions and no oversampling was carried out.
The bulk mineralogy of the granules was assessed by non-destructive X-ray microdiffraction (μXRD) on the polished granules after the μ-FTIR. μXRD data were collected in reflection geometry using a Nonius PDS 120 powder diffraction system [41,61]. A 100 μm diameter beam of Cu Kα radiation was selected by a pinhole from a 300 μm diameter primary beam producing a footprint on the granule surface of ~750 × 100 μm. The probing depth is estimated to be no greater than 35 μm for these calcium carbonate granules . NIST silicon powder SRM640 and silver behenate were used as external standards; calibration and data collection were performed using Diffgrab™. During data collection of at least 8000 s, the polished samples were spun continuously in the plane of the sample surface.
After the X-ray microdiffraction, elemental distribution within the granules was mapped using a Cameca SX100 electron microprobe operating at 20 kV and 100 nA with the beam set to a spot size of 1 μm. Wavelength dispersive spectrometers (WDS) were used to detect elements Mg, Mn, Fe, Na, S, P and Sr while the elements Ca, Al and Si were detected using an energy dispersive spectrometer (EDS). Maps were 512 × 512 pixels with a step size of 2 μm and dwell times of 50 μs.
Results and discussion
Amino acid composition of milky fluid extracted from the calciferous gland of Lumbricus terrestris earthworms
Amino acid content/picomol mg−1
53914 ± 33
82116 ± 489
126484 ± 3622
59950 ± 218
89784 ± 1218
135972 ± 2598
33449 ± 151
57377 ± 1005
77156 ± 1266
26546 ± 35
42055 ± 428
58750 ± 1860
16640 ± 668
26532 ± 1338
44539 ± 106
55022 ± 1808
106161 ± 4433
128852 ± 1961
25831 ± 159
58534 ± 528
59731 ± 1632
43439 ± 25
70961 ± 422
101471 ± 3208
12024 ± 209
20348 ± 354
21983 ± 604
31258 ± 168
49848 ± 510
73772 ± 2197
20818 ± 68
32369 ± 296
50379 ± 1857
50905 ± 386
74546 ± 466
119497 ± 3190
26320 ± 179
39651 ± 119
63205 ± 1371
358 ± 80
610 ± 98
1242 ± 614
X-ray diffraction of the powdered bulked granule samples for this study confirmed our previous results  that the granules are predominantly calcite; trace quartz and vaterite were also detected (Additional file 3: Table S2, Additional file 4: Figure S1). The quartz is most likely due to inclusions in the granules . We were unable to detect the diffuse peaks indicative of ACC on the XRD traces  as the crystallinity of the calcite and quartz dominated the intensities in the traces. The presence of vaterite over 6 years since granule production confirms that “unstable” polymorphs of CaCO3 are stable in the granules. As vaterite was only present at trace levels and the bulk FTIR spectra of calcite and vaterite are almost identical (Figure 2), we did not try and distinguish between these two phases when quantifying granule composition from the FTIR spectra obtained from the analysis of the bulk granules and the spatial analysis (see below). Thus, in a sense our FTIR “calcite” below is actually representative of both crystalline CaCO3 polymorphs, vaterite and calcite.
Granule elemental composition
St Albans field
Elemental composition/mg kg−1
Granule ACC content (same samples as used for amino acid analysis, Table 4 )
St Albans field
ν3: ν4 areas
% ACC (ν3: ν4)
ν2: ν4 areas
% ACC (ν2: ν4)
ν3: ν4 areas
24.26 ± 0.39
25.82 ± 0.95
23.78 ± 1.14
25.09 ± 2.23
21.07 ± 0.49
27.68 ± 1.73
26.00 ± 1.15
20.33 ± 0.54
23.62 ± 1.40
23.41 ± 2.55
% ACC (ν3: ν4)
1.73 ± 0.24
2.70 ± 0.59
1.43 ± 0.71
2.25 ± 1.39
−0.25 ± 0.30
3.85 ± 1.07
2.81 ± 0.72
−0.71 ± 0.33
1.33 ± 0.87
1.20 ± 1.58
ν2: ν4 areas
2.68 ± 0.02
2.88 ± 0.06
2.63 ± 0.16
2.32 ± 0.06
2.32 ± 0.06
2.94 ± 0.13
2.85 ± 0.11
2.28 ± 0.02
2.59 ± 0.09
2.59 ± 0.20
% ACC (ν2: ν4)
−24.01 ± 0.30
−21.07 ± 0.88
−23.50 ± 2.40
−23.50 ± 2.40
−29.42 ± 0.95
−20.09 ± 1.90
−21.54 ± 1.67
−30.14 ± 0.32
−25.43 ± 1.39
−25.44 ± 3.08
Granule amino acid composition measured in 2012 by RP-HPLC
St Albans field
Amino acid content/pico mol mg −1
Ignoring samples with concentrations lower than the limit of detection, the data show that whilst concentrations of most analysed elements typically varied by a factor of 5 or less P concentrations varied by a factor of 11. Phosphate has been shown to stabilise ACC [23-26]. The high level of variation of P in the granules could potentially cause significant variation in granule ACC content as well.
The FTIR spectra obtained for the powdered bulked granules resemble that of calcite (Figure 2), in support of our previous X-ray diffraction data  and the XRD data obtained on bulked powdered granules in this study. Despite amino acids being detected in the milky fluid and the granules by RP-HPLC (Table 4) and peaks corresponding to organic molecules being present in the milky fluid FTIR spectra, no peaks suggestive of organic molecules were seen in the spectra of obtained for the granules. This presumably reflects the sensitivity of the two techniques for detecting organic molecules. As the mechanism by which organic molecules are thought to stabilise ACC involves sorption and inhibition of dissolution and crystallisation [19,27-34] it could be that any stabilising organic molecules are present at very low concentrations, potentially as molecular monolayers. Such a signal would be heavily diluted within the bulk granules analysed by FTIR and thus hard to detect.
The ratio of the ν3: ν4 and ν2: ν4 peak areas in the granule spectra varied between samples (Table 3), potentially because of varying amounts of ACC and calcite between samples. When peak areas were entered into the calibration curve equations determined on artificial ACC:calcite mixtures (Figure 1) to quantify the % ACC present in the granules, the ν3: ν4 peak area equation consistently yielded larger values than the ν2: ν4 peak area equation and the values derived from the ν2: ν4 peak area equation were often negative (Table 3). The negative values may arise due to differences in grain size and orientation between the synthetic standards used to construct the calibration curves and the powdered granules (see for example ). We took great care to grind all our samples to the same degree and for a significant period of time to ensure homogeneity of the powder and significant grain size reduction. Unfortunately small sample size made the use of the grinding curve approach of  impractical as a check for grain size effects though our use of peak area rather than peak height may have off-set any significant effects. Typically reductions in peak height are accompanied by increasing peak width, the two changes largely cancelling each other out when peak area is assessed (as in this study). Additionally or alternatively the negative values may be due to differences in crystal properties such as crystallinity between the synthetic standards and the granule carbonates, as is often the case when comparing biogenically produced carbonates with abiogenic carbonates (e.g. ). However, the two sets of values are well correlated (r = 0.8, p ≤ 0.01 for the 2010 data, r = 1.0, p ≤ 0.05 for the 2012 data, Pearson correlation) suggesting that they are at least a good indicator of relative amounts of ACC. Thus the bulk FTIR analysis indicates that the granules from the different samples have varying amounts of ACC and that this ACC is long lived. The first ACC measurements were made in 2010, 2 years after extraction of the granules from the soil. The second set of measurements, carried out two years later (in 2012), yielded lower ACC concentrations thus suggesting further crystallization of the ACC. Nevertheless, the 2010 ν2: ν4 peak areas (and calculated ACC %) showed strong correlations with the 2012 ν2: ν4 peak areas (p = 0.7, p ≤ 0.05, Pearson correlation) and 2012 ν3: ν4 peak areas (p = 0.8, p ≤ 0.05, Pearson correlation). Thus, despite the reduction in ACC between 2010 and 2012, earthworm ACC appears to be stable for several years. The stability of biogenic ACC is rarely assessed on these timescales but in many cases reported in the literature, biogenic ACC appears to be associated with transient features, e.g. the formation of sea urchin spicules  or the storage of Ca to be used during cuticle growth following moulting in crustaceans (e.g. [67,68]. Therefore, the level of ACC stability in the earthworm granules is unprecedented and warrants further investigation.
Mean granule amino acid (n = 5) and ACC composition (n = 7)
Amino acid content / pico mol mg −1
St Albans field
217 ± 103
293 ± 74
269 ± 31
145 ± 80
150 ± 29
173 ± 27
179a ± 20
128b ± 33 (2)
129b ± 17
108a ± 16
84ab ± 23
78b ± 11
16 ± 1
15 ± 9 (1)
22 ± 6
262 ± 40 (1)
223 ± 70 (3)
228 ± 74 (3)
50a ± 8
29b ± 14 (3)
39ab ± 6 (1)
227a ± 43
173a ± 54
131ab ± 17
7a ± 3 (2)
146 ± 44
148 ± 46
133 ± 24
31 ± 5 (1)
40 ± 12 (1)
33 ± 8 (1)
97 ± 33 (4)
133 ± 48 (2)
128 ± 45 (2)
58 ± 16
78 ± 24
61 ± 8
9 ± 5 (3)
10 ± 6 (4)
ν3: ν4 areas
23.15a ± 0.97
27.41b ± 3.24
27.91b ± 1.33
% ACC (ν3: ν4)
1.04a ± 0.60
3.69b ± 2.01
3.99b ± 0.83
ν2: ν4 areas
2.56a ± 0.07
2.90b ± 0.30
2.90b ± 0.11
% ACC (ν2: ν4)
−25.82a ± 1.10
−20.69b ± 4.52
−20.77b ± 1.60
In 2008, when the first set of granules were collected, we determined their elemental composition by acid digestion and analysis by inductively coupled plasma-optical emission spectroscopy (ICP-OES). No significant correlations are seen between the peak area ratios or % ACC (Table 3) and granule elemental composition (Table 2) (e.g., Figure 4b). Given the wide range of P concentrations in the granules, and the role of P in stabilising ACC in some systems [22-26] we had anticipated a possible correlation between P concentration and % ACC. The lack of such a correlation might be due to the heterogeneous distribution of both phosphate and ACC within granules or be because the ACC in the granules is not stabilised by phosphate. Additionally, since the bulk FTIR and amino acid analysis were performed on the same samples, different to those used for the elemental analysis, it is perhaps not surprising that there were many significant correlations between the FTIR peak ratios and granule amino acid content and none between the ACC and the granule elemental compositions.
In 2012 to further investigate the relationship between amino acid concentrations and ACC contents, and because of concerns regarding granule heterogeneity following our previous observations of elemental [39-41] and phase [42,49] heterogeneity in the granules, we analysed individual granules taken from the “bulked granules” sample set. Amino acid and ACC analyses were carried out on separate sets of granules due to limited sample size available for analysis. We were not able to determine the elemental variability between individual granules as the granules have too low a mass to yield solutions of appropriate volume and concentration for analysis on our ICP-OES. Granules from the Hamble, Soil Science and St Albans Field soils were selected; 7 were analysed for ACC, 5 for amino acids (Table 5).
The data are very similar to those obtained on the bulk granules (Tables 3 and 4). Individual granules have highly variable amino acid concentrations, though the relative proportions of amino acids are similar. The mean RSDs for the amino acid concentrations for the Hamble, Soil Science and St Albans granules were 26, 35 and 22% respectively. In contrast the mean RSDs for the FTIR peak area ratios (ν2:ν4 and ν3:ν4) were 6%, though the mean RSD for the calculated % ACC was higher at 16%. The FTIR peak area ratios suggest that the granules from the Soil Science and St Albans soils have higher ACC contents than those from Hamble but, where there is a significant difference, they have lower amino acid concentrations. This pattern is different from the correlations resulting from our analysis of the bulk granules (Tables 3 and 4, Figure 4a).
The lack of consistent relationships between the FTIR/ACC and amino acid data in Tables 3, 4, and 5 could be due to granule heterogeneity. An additional significant hindrance to the interpretation of the data in Table 5 is that the amino acid and ACC determinations were carried out on separate granules and that elemental analysis was not performed. For this reason we attempted spatially resolved μ-FTIR at the Diamond Light Source and combined that with elemental analysis of the same granules by electron microprobe analysis (EMPA). We hoped to be able to map out both ACC and amino acid distribution using μ-FTIR on individual granules. Bulk FTIR did not reveal the presence of organic molecules in the granules but we hoped that spatially-resolved analyses of the inherently heterogeneous granules would reveal areas of higher, detectable, concentrations of ACC and associated organic functional groups. This would then allow comparison of ACC, organic functional group and elemental distribution taking into account spatial distributions, on individual granules.
Spatially resolved analyses
We carried out spatial analysis on 4 granules. Two granules (Old-1 and Old-2) were recovered from soil up to 39 days post secretion. The other two (Fresh-1 and Fresh-2) were recovered within 24 hours of secretion. Non-destructive μXRD on thin sections of the granules indicated that the crystalline phases present were dominantly calcite. Only calcite was detected in Fresh-1 and Fresh-2 granules. Old-1 granule contained trace amounts of aragonite and Old-2 trace amounts of quartz. Aragonite has been detected in granules previously (e.g. [38,39,42]) and the trace amounts of quartz are most likely due to inclusions present in the granules (e.g. ).
We had hoped to use the μ-FTIR data to map out the distribution of bands related to organic compounds. After demineralising samples of milky fluid obtained from the calciferous gland, Gago-Duport et al.  observed peaks at c. 1654 cm−1 (amide I), 1540 cm−1 (amide II) and c. 1100 cm−1 (polysaccharides). Because we detected amino acids in the milky fluid (Table 1) and granules (Tables 4 and 5) and also observed peaks in the milky fluid bulk FTIR spectra that correspond to organic molecules (Figure 1), but not in the bulk granule spectra we had hoped that we might observe such peaks in spatially resolved spectra obtained from the ACC-rich regions of the granules by μ-FTIR mapping. However, these spectra also showed no conclusive evidence for the presence of amide I and polysaccharide species in our mapped samples. There was a wide, variably shaped peak in the range 1570–1350 cm−1 in all our spectra taken on the granules. This wavenumber range includes the ν3 calcite band at 1420–1470 cm−1 and also the amide II (1540 cm−1) and lipid/amide III band (1450 cm−1) . Point analyses on the resin used to produce the thin sections indicate that contamination from the resin is unlikely to be contributing to this peak. However, to date we have been unable to deconvolute this mixed component peak. It seems that the amino acids detected in our bulk analysis are present in concentrations that are too low to allow their distribution to be mapped out by the μ-FTIR mapping used here.
The elemental mapping of the fresh granules revealed concentric zoning of the style observed in our previous studies [40,41] (e.g. Figures 5h, 6h, 6i). There appeared to be no spatial correlation between the elemental distributions, imaged by the EPMA, and the distribution of ACC within the granules, as determined by the μ-FTIR mapping.
This study has demonstrated, as have previous studies, that earthworm-secreted calcium carbonate contains ACC. Additionally, in this work we have shown that this ACC is highly heterogeneously distributed but also remarkably stable and can persist for several years. We have also shown that granules contain significant concentrations of amino acids and that granule elemental and amino acid concentration can vary significantly between granules. Considering bulk composition we were unable to identify a dominant controlling factor to account for the ACC in the granules, though significant correlations suggest a link between mass of ACC and amino acid concentration. Using μ-FTIR mapping we have demonstrated the spatial heterogeneity of ACC within granules and, by coupling this to compositional mapping of the same granules, shown that there is no clear correlation between ACC and elemental distribution. We were unable to determine the distribution of organic molecules in the granules using μ-FTIR mapping, possibly due to their low concentration against a background of calcium carbonate. To take our understanding of this system further requires either the isolation of volumes of granules with differing ACC contents for analysis of their organic molecular composition or spatially explicit mapping of the organic molecules present in the granules, perhaps by Time-of-Flight Secondary Ion Mass spectrometry (TOF-SIMS) together with further investigation into the composition of the milky fluid.
The production of granules for the bulk analysis was carried out during NERC grant NE/F009623/1 awarded to MEH, Trevor Piearce (University of Lancaster) and Matt Canti (English Heritage); Denise Lambkin carried out the experiments. We thank Anne Dudley (University of Reading) for assistance with the ICP-OES analysis of these granules. Milky fluid samples were obtained by EAAV as part of NERC grant NE/H021914/1A awarded to MEH and Stuart Black (University of Reading). We thank John Morgan (University of Cardiff) and Trevor Piearce (University of Lancaster), for teaching us how to dissect out calciferous glands from earthworms. A White Rose Consortium grant awarded to MEH, KP, LGB and Andy Brown (School of Process, Environmental and Materials Engineering, University of Leeds), John Harding and Colin Freeman (both Department of Materials Science and Engineering, University of Sheffield) helped support the work on individual granule analyses. We thank the Diamond Light Source for the provision of beamtime under grants SM9197 and SM8989. We thank the beamline scientists Drs Mark Frogley, Katia Wehbe and Gianfelice Cinque for assistance with sample preparation, data acquisition and analysis at Diamond and Stefani Lutz and Beatriz Vallina (Leeds) for help during the beamtime. We thank John Spratt (NHM) for his assistance with the electron microprobe analysis. We thank the Leverhulme Trust for financial support to the NEaar laboratory and Sheila Taylor (University of York) for provision of technical support for amino acid analyses. We thank the three anonymous reviewers and the editors for their helpful suggestions and comments. This study has run on and off since 2008 and MEH thanks everyone for their enthusiasm and patience.
- Lowenstam HA, Weiner S. On biomineralization. Oxford: OUP; 1989.Google Scholar
- Aizenberg J, Hanson J, Koetzle TF, Weiner S, Addadi L. Control of Macromolecule Distribution within Synthetic and Biogenic Calcite Crystals. J Amer Chem Soc. 1997;119:881–6.View ArticleGoogle Scholar
- Addadi L, Raz S, Weiner S. Taking advantage of disorder: Amorphous calcium carbonate and its roles in biomineralization. Adv Mat. 2003;15:959–70.View ArticleGoogle Scholar
- Gower LB. Biomimetic Model Systems for Investigating the Amorphous Precursor Pathway and Its Role in Biomineralization. Chem Rev. 2008;108:4551–627.View ArticleGoogle Scholar
- Gong YUT, Killian CE, Olson IA, Appathurai NP, Amasino AL, Martin MC, et al. Phase transitions in biogenic amorphous calcium carbonate. PNAS. 2012;109:6088–93.View ArticleGoogle Scholar
- Raz S, Hamilton PC, Wilt FH, Weiner S, Addadi L. The transient phase of amorphous calcium carbonate in sea urchin larval spicules: The involvement of proteins and magnesium ions in its formation and stabilisation. Adv Funct Mater. 2003;13:480–6.View ArticleGoogle Scholar
- Politi Y, Levi-Kalisman Y, Raz S, Wilt F, Addadi L, Weiner S, et al. Structural characterisation of the transient amorphous calcium carbonate precursor phase in sea urchin embryos. Adv Funct Mater. 2006;16:1289–98.View ArticleGoogle Scholar
- Li C, Hong G, Yu H. Facile fabrication of honeycomb-patterned thin films of amorphous calcium carbonate and mosaic calcite. Chem Mater. 2010;22:3206–11.View ArticleGoogle Scholar
- Faatz M, Gröhn F, Wegner G. Amorphous calcium carbonate: synthesis and potential intermediate in biomineralization. Adv Mater. 2004;16:996–1000. Pedobiol 2011, 54S:S119 - S129.View ArticleGoogle Scholar
- Faatz M, Gröhn F, Wegner G. Mineralization of calcium carbonate by controlled release of carbonate in aqueous solution. Mater Sci Engineer. 2005;25:153–9.View ArticleGoogle Scholar
- Ogino T, Suzuki T, Sawada K. The formation and transformation mechanism of calcium carbonate in water. Geochim Cosmochim Acta. 1987;51:2757–67.View ArticleGoogle Scholar
- Rodriguez-Blanco JD, Shaw S, Benning LG. The kinetics and mechanisms of Amorphous Calcium Carbonate (ACC) crystallization to calcite, via vaterite. Nanoscale. 2011;3:265–71.View ArticleGoogle Scholar
- Bots P, Rodriguez-Blanco JD, Roncal-Herrero T, Shaw S, Benning LG. Mechanistic insights into the crystallization of amorphous calcium carbonate to vaterite. Crystal Growth and Design. 2012;12:3806–14.View ArticleGoogle Scholar
- Bolze J, Peng B, Dingenouts N, Panine P, Narayanan T, Ballauff M. Formation and growth of amorphous colloidal CaCO3 precursor particles as detected by time-resolved SAXS. Langmuir. 2002;18:8364–9.View ArticleGoogle Scholar
- Rodriguez-Blanco JD, Bots P, Roncal-Herrero T, Shaw S, Benning LG. The role of pH and Mg on the stability and crystallization of amorphous calcium carbonate. J Alloys Compounds. 2012;536(S1):S477–9.View ArticleGoogle Scholar
- Setoguchi H, Okazaki M, Suga S. Calcification in higher plants with special reference to cystoliths. In: Crick RE, editor. Origin, evolution and modern aspects of biomineralization in plants and animals. New York: Plenum Press; 1989.Google Scholar
- Tao J, Zhou D, Zhang Z, Xu X, Tang R. Magnesium-aspartate-based crystallisation switch inspired from shell molt of crustacean. PNAS. 2009;106:22096–101.View ArticleGoogle Scholar
- Aizenberg J, Lambert G, Weiner S, Addadi L. Factors involved in the formatin of amorphous and crystalline calcium carboante: a study of an Ascidian skeleton. J Am Chem Soc. 2002;124:32–9.View ArticleGoogle Scholar
- Rodriguez-Blanco JD, Shaw S, Bots P, Roncal-Herrero T, Benning LG. The role of Mg in the crystallisation of monohydrocalcite. Geochim Cosmochim Acta. 2014;127:204–20.View ArticleGoogle Scholar
- Cobourne G, Mountjoy G, Rodriguez-Blanco JD, Benning LG, Hannon AC, Plaisier JR. Neutron and X-ray diffraction and empirical potential structure refinement modelling of magnesium stabilised amorphous calcium carbonate. J Non-Cryst Solids. 2014;401:154–8.View ArticleGoogle Scholar
- Blue CR, Done PM. Chemical controls on the magnesium content of amorphous calcium carbonate. Geochim Cosmochim Acta. 2015;148:23–33.View ArticleGoogle Scholar
- Akhtar S, Barralet JE, Farrar D, Wright AJ. Influence of phosphate ions on the stability of amorphous calcium carbonate. Key Eng Mater. 2006;309–311:179–82.View ArticleGoogle Scholar
- Gal A, Kahil K, Vidavsky N, DeVol RT, Gilbert PUPA, Fratzl P, et al. Particle accretion mechanism underlies biological crystal growth from an amorphous precursor phase. Adv Func Mater. 2014;24:5420–6.View ArticleGoogle Scholar
- Al-Sawalmih A, Li C, Siegel S, Fratzl P, Paris O. On the stability of amorphous minerals in lobster cuticle. Adv Mater. 2009;21:4011–5.View ArticleGoogle Scholar
- Clarkson JR, Price TJ, Adams CJ. Role of metastable phases in the spontaneous precipitation of calcium carbonate. J Chem Soc Faraday Trans. 1992;88:243–9.View ArticleGoogle Scholar
- Weiner S, Levi-Kalisman Y, Raz S, Addadi L. Biologically formed amorphous calcium carbonate. Conn Tiss Res. 2003;44:214–8.View ArticleGoogle Scholar
- Lam RSK, Charnock JM, Lennie A, Meldrum FC. Synthesis-dependant structural variations in amorphous calcium carbonate. CrystEngComm. 2007;9:1226–36.View ArticleGoogle Scholar
- Wang SS, Xu A-W. Amorphous Calcium Carbonate Stabilized by a Flexible Biomimetic Polymer Inspired by Marine Mussels. Cryst Growth Des. 2013;13:1937–42.View ArticleGoogle Scholar
- Bentov S, Weil S, Glazer L, Sagi A, Berman A. Stabilization of amorphous calcium carbonate by phosphate rich organic matrix proteins and by single phosphoamino acids. J Struct Biol. 2010;171:207–15.View ArticleGoogle Scholar
- Su J, Liang X, Zhou Q, Zhang G, Wang H, Xie L, et al. Structural characterization of amorphous calcium carbonate-binding protein: an insight into the mechanism of amorphous calcium carbonate formation. Biochem J. 2013;453:179–86.View ArticleGoogle Scholar
- Guillement B, Faatz M, Gröhn F, Wegner G, Gnanou Y. Nanosized Amorphous Calcium Carbonate Stabilized by Poly(ethylene oxide)-b-poly(acrylic acid) Block Copolymers. Langmuir. 2006;22:1875–9.View ArticleGoogle Scholar
- Luquet G, Fernández MS, Badou A, Guichard N, Le Roy N, Corneillat M, et al. Comparative ultrastructure and carbohydrate composition of gastroliths from astacidae, cambaridae and parastacidae freshwater crayfish (crustacea, decapoda). Biomolecules. 2013;3:18–38.View ArticleGoogle Scholar
- Tobler DJ, Rodriguez-Blanco JD, Dideriksen K, Sand KK, Bovet N, Benning LG, et al. The effect of aspartic acid and glycine on amorphous calcium carbonate (ACC) structure, stability and crystallization. Procedia Earth and Planetary Science. 2014;10:143–8.View ArticleGoogle Scholar
- Freeman CL, Harding JH, Quigley D, Rodger PM. Structural Control of Crystal Nuclei by an Eggshell Protein. Angew Chem Int Ed. 2010;49:5135–7.View ArticleGoogle Scholar
- Canti MG, Piearce TG. Morphology and dynamics of calcium carbonate granules produced by different earthworm species. Pedobiol. 2003;47:511–21.Google Scholar
- Darwin C. The formation of vegetable mould, through the action of worms, with observations on their habits. London: John Murray; 1881.Google Scholar
- Briones MJI, López E, Méndez J, Rodríguez JB, Gago-Duport L. Biological control over the formation and storage of amorphous calcium carbonate by earthworms. Mineral Mag. 2008;72:227–31.View ArticleGoogle Scholar
- Gago-Duport L, Briones MJI, Rodríguez JB, Covelo B. Amorphous calcium carbonate biomineralization in the earthworm's calciferous gland: Pathways to the formation of crystalline phases. J Struct Biol. 2008;162:422–35.View ArticleGoogle Scholar
- Fraser A, Lambkin DC, Lee MR, Schofield PF, Mosselmans JFW, Hodson ME. Incorporation of lead into calcium carbonate granules secreted by earthworms living in lead contaminated soils. Geochim Cosmochim Acta. 2011;75:2544–56.View ArticleGoogle Scholar
- Brinza L, Quinn PD, Schofield PF, Mosselmans JFW, Hodson ME. Incorporation of strontium in earthworm-secreted calcium carbonate granules produced in strontium-amended and strontium-bearing soil. Geochim Cosmochim Acta. 2013;113:21–37.View ArticleGoogle Scholar
- Brinza L, Schofield PF, Mosselmans JFW, Donner E, Lombi E, Paterson D, et al. Could earthworm-secreted calcium carbonate incorporate Zn in contaminated soils? Soil Biol Biochem. 2014;74:1–10.View ArticleGoogle Scholar
- Brinza L, Schofield PF, Hodson ME, Weller S, Ignatyev K, Geraki K, et al. Combining μXANES and μXRD mapping to analyse the heterogeneity in calcium carbonate granules excreted by the earthworm Lumbricus terrestris. J Synchrotron Rad. 2014;21:235–41.View ArticleGoogle Scholar
- Beck R, Andreassen J-P. Spherulitic Growth of Calcium Carbonate. Cryst Growth Des. 2010;10:2934–47.View ArticleGoogle Scholar
- Aoki K. Kalzium im Blut des Regenwurms. Proceedings of the Imperial Academy of Japan. 1934;10:121–4.Google Scholar
- Kaestner A. Invertebrate zoology. New York: Interscience; 1967.Google Scholar
- Kühle JC. Vergleichende Untersuchungen zur Funktion der Kalkdrüse verschiedener Regenwurmarten bei unterschiedlicher CO2-Atmosphäre. Verhandlungen der Gesellschaft für Ökologie. 1980;8:411–5.Google Scholar
- Versteegh EAA, Black S, Hodson ME. Environmental controls on the production of calcium carbonate by earthworms. Soil Biol Biochem. 2014;70:159–61.View ArticleGoogle Scholar
- Voigt O. Die Funktion der Regenwurm-Kalkdrüsen. Zoologische Jahrbücher: Abteilung für allgemeine Zoologie und Physiologie der Tiere. 1933;52:677–708.Google Scholar
- Lee MR, Hodson ME, Langworthy GN. Earthworms produce granules of intricately zoned calcite. Geology. 2008;36:943–6.View ArticleGoogle Scholar
- Aizenberg J, Lambert G, Addadi L, Weiner S. Stabilisation of amorphous calcium carbonate by specialised macromolecules in biological and synthetic precipitates. Adv Mater. 1996;8:222–6.View ArticleGoogle Scholar
- Gotliv B, Addadi L, Weiner S. Mollusk shell acidic proteins: In search of individual functions. ChemBioChem. 2003;4:522–9.View ArticleGoogle Scholar
- Lambkin DC, Gwilliam KH, Layton C, Canti MG, Piearce TG, Hodson ME. Soil pH governs production rate of calcium carbonate secreted by the earthworm Lumbricus terrestris. Appl Geochem. 2011;26:S64–6.View ArticleGoogle Scholar
- Lambkin DC, Gwilliam KH, Layton C, Canti MG, Piearce TG, Hodson ME. Production and dissolution rates of earthworm-secreted calcium carbonate. Pedobiol. 2011;54S:S119–29.View ArticleGoogle Scholar
- Chester R, Elderfield H. The application of infrared absorption spectroscopy to carbonate mineralogy. Sedimentology. 1967;9:5–21.View ArticleGoogle Scholar
- Rodriguez-Blanco JD, Shaw S, Benning LG. How to make stable ACC: protocol and structural characterization. Miner Mag. 2008;72:283–6.View ArticleGoogle Scholar
- Penkman KEH, Kaufman DS, Maddy D, Collins MJ. Closed-system behaviour of the intra-crystalline fraction of amino acids in mollusc shells. Quat Geochronol. 2008;3:2–25.View ArticleGoogle Scholar
- Hill RL. Hydrolysis of proteins. Adv Protein Chem. 1965;20:37–107.Google Scholar
- Kaufman DS, Manley WF. A new procedure for determining DL amino acid ratios in fossils using Reverse Phase Liquid Chromatography. Quat Sci Rev. 1998;17:987–1000.View ArticleGoogle Scholar
- Coelho AA. Indexing of powder diffraction patterns by iterative use of singular value decomposition. J Appl Crystallography. 2003;36:86–95.View ArticleGoogle Scholar
- NIST: Web book http://webbook.nist.gov/chemistry/name-ser.html
- Lambiv-Dzemua G, Gleeson SA, Schofield PF. The importance of lithiophorite over asbolane in the ore zone mineralogy of the Nkamouna Co-Mn laterite deposit, southeast Cameroon. Mineral Deposita. 2012;48:155–71.View ArticleGoogle Scholar
- Benning LG, Phoenix VR, Yee N, Tobin MJ. Molecular characterization of cyanobacterial silicification using synchrotron infrared micro-spectroscopy. Geochim Cosmochim Acta. 2004;68:729–41.View ArticleGoogle Scholar
- Arnold RE, Hodson ME, Black S, Davies NA. The influence of mineral solubility and soil solution concentration on the toxicity of copper to Eisenia fetida Savigny. Pedobiol. 2003;47:622–32.Google Scholar
- Davies NA, Hodson ME, Black S. Is the OECD acute worm toxicity test environmentally relevant? The effect of mineral form on calculated lead toxicity. Environ Pollut. 2003;121:49–54.View ArticleGoogle Scholar
- Poduska KM, Regev L, Boaretto E, Addadi L, Weiner S, Kronik L, et al. Decoupling local disorder and optical effects in infrared spectra: differentiating between calcites with different origins. Adv Mater. 2011;23:550–4.View ArticleGoogle Scholar
- Stalport F, Coll P, Cabane M, Person A, González RN, Raulin F, et al. Search for past life on Mars: Physical and chemical characterisation of minerals of biotic and abiotic origin: part 1 – calcite. Geophys Res Lett. 2005;32, L23205.View ArticleGoogle Scholar
- Becker A, Bismayer U, Epple M, Fabritius H, Hasse B, Shi J, et al. Structural characterisation of X-ray amorphous calcium carbonate (ACC) in sternal deposits of the crustacean Porcellio saber. Dalton Trans. 2003; 551–5.
- Becker A, Ziegler A, Epple M. The mineral phase in the cuticles of two species of Crustacea consists of magnesium calcite, amorphous calcium carbonate, and amorphous calcium phosphate. Dalton Trans. 2005; 1814–20.
- Penkman KEH, Preece RC, Keen DH, Maddy D, Schreve DC, Collins MJ. Testing the aminostratigraphy of fluvial archives: the evidence from intra-crystalline proteins within freshwater shells. Quat Sci Rev. 2007;26:2958–69.View ArticleGoogle Scholar
- Hendy EJ, Tomiak PJ, Collins MJ, Hellstrom J, Tudhope AW, Lough JM, et al. Assessing amino acid racemization variability in coral intra-crystalline protein for geochronological applications. Geochim Cosmochim Acta. 2012;86:338–53.View ArticleGoogle Scholar
- Penkman KEH, Preece RC, Bridgland DR, Keen DH, Meijer T, Parfitt SA, et al. An aminostratigraphy for the British Quaternary based on Bithynia opercula. Quat Sci Rev. 2013;61:111–34.View ArticleGoogle Scholar
- Demarchi B, Rogers K, Fa DA, Finlayson CJ, Milne N, Penkman KEH. Intra-crystalline protein diagenesis (IcPD) in Patella vulgata. Part 1: Isolation and testing of the closed system. Quat Geochronol. 2013;16:144–57.View ArticleGoogle Scholar
- Crisp M, Demarchi B, Collins MJ, Penkman KEH. Isolation of the intra-crystalline proteins and kinetic studies in Struthio camelus (ostrich) eggshell for amino acid geochronology. Quat Geochronol. 2013;16:110–28.View ArticleGoogle Scholar
- Gower LB, Odom DJ. Deposition of calcium carbonate films by a polymer-induced liquid-precursor (PILP) process. J Cryst Growth. 2000;210:719–34.View ArticleGoogle Scholar
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