i-

Pedobiologia 43, 851-858 (1999) Pedo l Urban & Fischer Verlag biologia http:l/www.urbanfischer.deljournalsIppeilo

Reproductive strategies of three native species from the savannas of Carimagua (Colombia) Juan J. Jiménez’”,Ana G. Moreno1 and

I Departamento de Biología I (Zoología). Facultad de Biología. Universidad Complutense, 28040. Madrid. Soain 2 Laboratoire d’Elologie des Sols Tropicaux, centre IRD. 32 Av. Henri Varagnat, 93143. Bondy, France

Accepted: 3. June 1999

Summary. Some data on the reproductive biology of three native glossoscolecid species from the Colombian “Llanos” are presented. The seasonal dynamics of reproduction varied among the species considered which displayed either one or two reproductive periods per year. Cocoons were laicl at different depths to a maximum of 50 cm. The relation between co- coon weight and adult weight was the sanie for two endogeic species, ca. 6%, whereas for one anecic species the value has been the highest obtained to date for any tropical and temperate earthworm, i.e., 16 %.

Key words: , reproductive strategies, cocoons, life cycles, vertical distribution A

Introduction Stiidies on distinct subjects of reproductive strategies in earthworms are those of Stephenson ( 1930), Walsh ( I936), Evans & Guild (1948), Gerard (1967), Satchel1 (1967), Bouché (1972), Reynolds (1973), Nowak (1975), Phillipson & Bolton (1977), Lavelle (197 1; 1978; 1979), Senapati (1 980) and Garnsey (1 994) among others. Bouché (1977) and Lavelle (1977) have defined a close relationship between reproductive strategies and ecological categories of earthworms. Epigeic worms, living and feeding on lit- ter, usually survive through cocoons. Endogeic earthworms, living and feeding in the soil, show quiescence during unfavourable conditions and enter rapidly into a reproductive period when conditions become suitable. Finally, anecic earthworms, living in the soil but feeding on the surface, employ two mechanisms to avoid mortality within the population: diapause, which may be different for adults and juveniles and cocoons at the end of the rainy season (Jiménez et al. 1998a). There is very scarce information regarding basic knowledge on the biology and ecology of - earthworm species from the Neotropical region as only a few studies have been undertaken. Németh (1 98 1) studied the earthworm fauna from the tropical forests of Venezukla, Fragoso (1993) in natural and disturbed environments in the South of Mexico, Feijoo (unpubl.) in the hillsides from Valle del Cauca in Colombia and Muñoz-Pedreros (1997) in Chile. In an earlier paper (Jiménez et al. 1998a) some data about the reproductive strategy of Mnrtiodriliis cnriinngiieizsis (Jiménez & Moreno, in press) were shown. In this paper more precise details of the life cycle and dynamics of reproduction are given for three native spe- cies from the eastern plains of Colombia, e.g. Andiodrilus sp., Glossodrilus sp. and M. cnri- innguensis.

Corresponding ncirlzol: emnil: [email protected] y------1”/.. 003 1-4056/99/43/06-85 1 $12.00/0 I 7 851 I l i, I Materials and Methods

Study site The study area is located in the well-drained isohyperthermic savannas of the Eastern Plains of Colom- bia at the Carimagua research station (CIAT-CORPOICA agreement). Average annual rainfall and tem- perature are about 2280 mm and 26°C respectively, with a dry season from December to March. Soils at the study site are oxisols characterized by their high acidity (pH (H,O) 4.3, AI saturation (>90 %) and low values of exchangeable Ca, Mg and K. Two different and contrasting ecosystems were eva- luated: a native herbaceous savanna and a 17-yr old introduced grass-legume pasture (Brachiaria de- ciiiizbeizs cv. Basilisk and Piierrrria phaseoloides CIAT 9900). Cattle stocking rates for the latter system are 1animal ha-' in the dry season and 2 ha-( in the wet season, whereas no management is per- formed in the former.

Eartlitvorrn satnpling The experimental design was carried on the basis of a stratified random sampling procedure. In both systems, a defined area of90~90in was isolated and divided into regular quadrats of IOX IO m. Two physical methods were performed during 17 months (from April 1994 to September 1995, except June 1994): hand sorting and washing-sieving of, respectively, five monthly I x I ~0.5ni and ten 20~20x20 cm soil samples (after Lavelle 1978). Monoliths were split into IO cm layers to assess the vertical pat- tern, and cocoons collected from each layer washed in water and carried to the laboratory. See Lavelle (1978), Jiménez et al. (1998a) and Jiménez et al. (1998b) for sampling details.

Incubntion of cocoons Cocoons obtained in field samples were weighcd and deposited in Petri dishes with moistened filter papers. Each day culturcs wcrc reinoistencd and hatched inclividuals weighcd. The temperature in the laboratory was maintained between 26 and 28 "C.

Results

Mating could never be observed in thc field (this probably happens by night but it was not possible to go outside the station for security reasons) so it has been assessed from indirect methods.

Cocoons: Morphology, size aiid incubation time The cocoons produced by Glossodriliis sp. are whitish, slightly spherical (Table I), with the end sharp-pointed and extended. Their average size was 3.0x2.2 mm and 6.2 mg of fresh weight in vivo. None of the 79 cocoons collected in the field emerged under laboratory con- ditions, so incubation time, number and weight of newly hatched worms could not be deter- mined for this species. Cocoons of Aizdiodrilirs are also spherical, whitish translucent with a mean diameter of sp. mg. 5 mm and a fresh weight of 78.9 A unique zygote can be observed through the cocoon with an incubation period of 13 days and a fresh weight of 55.7 mg at hatching. Almost 50 % of the cocoons did not hatch in the laboratory and 7 1 % of the total weight of the cocoon cor- responded to earthworm weight. The cocoon of M. carinzagiierzsis'was yellawish, ovoid in shape, rather large (23.6X 14 mm) and weighing on average 1,808 mg. In each cocoon the number of embryos emerged was two (one individual emerged from only one cocoon) weighing 760 mg (Fig. 1). The aver- age incubation time for this species, considering all the cocoons, was 23.5 days and 80 % Of the cocoon weight was attributed to the worms. Considering all the cocoons cultured under controlled conditions the hatching ratio was 73.9 %.

852 Pedobiologia 43 (1999) 6 Table 1. Main biological features of cocoons for three species from Carimagual

~~ ~- Glossodrilits sp. Atzdiodriliis sp. M. cnriiiingrierzsis Cocoons studied 79 88 46 Morphology Spherical Spherical Ovoid Size (mm) 3.0x2.2 6 23.6~14 Fresh weight in vivo (mg) 6.2rt: 1.4 78.9 & 22.2 1,&08+414.5 (4.6-8.1) (30-1 30) (890-3020) Incubation time (days) - 12.8 f 6.3 23.3 & 12.9 ( 1-28) (1-48) Individuals per cocoon - 1.02&0.15 1.91 & 0.29 Weight of newly hatched 52 55.7 & 22.9 760+2219.4 individuals (mg) (20- 1 20) (270-1760) Individual weight / Cocoon weight (%) 80.6 71 79.7 Hatching rate in the lab (%) O 48.3 73.9 I Mean + standard deviation (minimum and niaxilnitzn within brackets) 2 Data from individuals in the field - Not determined

1400 Fig. 1. Box-plot of weight of juveniles of A4. c¿/ririirtgire/z.ris showing the e mean 1200 (dotted line), 5 % and 95 % percentiles

I h 1000 l .!I e 3.- 800 T $ ...... 600 i 3a~ 1 5 400 h e 200 l I O Lower individual Higher individual t weight weight I I Seasonal dynciniìcs t At Carimagua, the dynamics of cocoon production showed that earthworms mainly laid their I cocoons at both the beginning and end of each wet season, when fluctuation of soil moisture was higher in the soil profile. Glossodriliis sp. and M. caririiagiterzsis showed a unique re- productive period whilst Ancliodribs sp. seemed to display bimodal dynamics (Fig. ?). Glossodrilus sp. laid its cocoons at the end of the rainy period. The first cocoons in the sa- vanna appeared in October 1994 till reaching a maximum in January when all the population, totally inmatures, were inactive. In the pasture, on the contrary, the first cocoons were found in September 1994 with a maximum number obtained in February. Mainly the total number of cocoons hatch at the onset of the following rainy season. This is the reason for the peaks in cocoon deposition observed during summer months. Cocoons of Andiodriliis sp. were found at two different periods during the rainy season. In the savanna, cocoons were collected at the beginning, with a maximum number, and in the middle of the rainy season. In the second year of the study two peaks appeared in the same months, though the number of cocoons was lower than that obtained in the first year. In the pasture, a large number of cocoons was obtained compared with the savanna. Ape& was also

Pedobiologia 43 (1999) 6 853 a) 2200 O o savanna 2000 Pasture 1800 l-7E 1600 2 1400 p1 1200 lo00 O2 s 800 5600 400 200 O'

W4AMJLASOND JFMAMJJLAS95 Months

50 b) O savanna o Pashrre 40

10

O

Months

20

7 15 u-lE ri 3 10 oO 65

Months

Fig. 2. Monthly average number of cocoons (N m-2) collected in both systems ,,r (a) Glossodrilcis spa (washing-sieving technique), (b) AndiodriZcis sp. (hand sorting method) and (c) M. carimaguensis (hand sorting method in the pasture)

854 Pedobiologia 43 (1999) 6 o10

10-20

E 20-30 -N-302 a 30-40 X=8.7an x- 12.4 cm E 40-50

v) 50-60 60-70

70-80

100 80 GO 40 20 O 20 40 60 80 100 Population (%)

n b) 0-10

10-20

20-30 T N-20 N=51 E 30-40 x=6.5 cm X=5.Gcm x 40-50 50-60

60-70 70-80

100 80 60 40 20 O 20 40 60 80 100 Population (%) c) o- 10

10-20

E 20-30 o 30-40 x[ 40-50 50-GO

GO-70

70-80

100 80 GO 40 20 O 20 40 GO 80 100 Population (%)

Fig. 3. Yearly average vertical distribution of cocoons in the savanna (grey) and in the pasture (black) for (a) Glossodriliu sp. (washing-sieving technique), (b) Andiodriho sp. (hand-sorting method) and (c) M.caritnagitensis (hand-sorting method in the pasture)

Pedobiologia 43 (1999) 6 855 observed in May 1994 followed by another cocoon deposition in October. By the second year the highest values appeared in May-June and August. M. carirnaguensis deposited its cocoons in the pasture at the end of the rainy season and the maximum number obtained for this species was in September-October. In the following year some cocoons were obtained in March what confirms that some cocoons do not hatch until the onset of the next rainy season.

Vertical patterns The depah at which cocoons were laid has been assessed from the total number of cocoons collected in each stratum (Fig. 3). Aizdioclrilirs sp. and Glossodrilirs sp. are topsoil species so most of the cocoons were found in the first 20 cm of soil profile. The mean depth for Glosso- clrilus sp. was 8.8 cm in the savanna and 12.4 cm in the pasture. These data were based on the number of cocoons obtained by the washing-sieving technique; since some cocoons were ob- tained below 20 cni depth in the hand-sorting method a correction in the percentage of coco- ons found was needed. The vertical distribution of cocoons for M. crrriinngirensis could only be determined in the pasture as only one cocoon was obtaincd in the 20-30 cm layer in the savanna in July 1994. The cocoons were found at an average depth of 26 cm reaching a maximum of 50 cm.

Cocoori six ~'ersiiscrdirlt sire The higher the size of the adult the larger the cocoon it forms (Fig. 4), although the relation- ship between the variables considered was the sanic for two specks differing in size: Aidi- or1t'ilu.s sp. and G/o.ssodrilirs sp. However, this value rose to 16 % of adult weight for ILI. cari- riingiierisis (Table 2).

Tablc 2. Investment of adult wcight in the I'ormotion or cocoons

Species Adult weight Cocoon wcight Cocoon w./Adtilt w. (w) (mg) (%I

Glossodrilris sp. 110.6 (Il = 32) 6.2 (11= 60) 6.2 A II dioddii1.s sp . 1,340 (n = 26) 78.9 (II = 88) 5.9 M. enrimogiterisis 11,240 (n = 29) I ,SOS (n = 46) 16.1

Mca O

PA

r = 0.884

Fig. 4. Relationship between fresh weight Q (Lo. natural scale) of cocoons and adults :' 0 for % species from tropical (A) and tempe- Il, 3Il, 6 4 5 8 9 10 11 rate sites (O) plus three species from Cari- magua (U) (p <0.01). Data were taken from Adult weight (mg) Lavelle (198 I) and Barois et al. (1996)

856 Pedobiologia 43 (1999) 6 Fecirndity Estimates of fecundity are based on field data from July 1994 to June 1995. It was necessary to use a correction factor to recalculate density of adults for Glossodrilus sp. as it has been observed that almost 50% of the population was lost when the hand-sorting method was employed (Jiménez, unpubl.). The higher values of fecundity, i.e. number of cocoons pro- duced per adult per year, appeared for Glossoddus sp. This species produced 9.9 cocoons- adult-' . year) in the savanna and 13 cocoons . adult-! .year1 in the pasture. Aiirlìoclr.iliis sp. and M. cariniagiietzsis presented lower values, 0.61 and 0.50 for the former in respectively savanna and pasture systems, and 0.25 for the latter (actually, this value was 0.49, the product of 0.25 by 1.9 I individuals per cocoon).

Discussion Factors affecting reproductive activity of earthworms are both temperature and moisture in the soil (Evans & Guild 1948). Michalis & Panidis (1993) concluded that both factors affect the reproductive pattern for the lumbricid Octorlr-ihis cotnplanat~is(Dugés) and Reinecke & Kriel (1980) made similar observations for the compost worm Eisenirifericlri (Savigny). At Cariniagiia the strong seasonal climatic variations restrict cocoon deposition to only 8 months, as the rest of the year the earthworm community is inactive. In general, two dif- ferent strategies appear, continuous deposition of cocoons for Anrliodrilm sp. and cocoon de- M. position at the end of the rainy season and diapause or death of adults for, respectively, cn- ririingiietisis and Glossorlriliis sp. Cocoon size is not always correlated with adult size (Edwards & Bohlen 1996). However, Lavelle (1981) found a clear positive relationship between the size of the adults and the co- coons produced for temperate and tropical earthworms. The high reproduction investment made by M.carimagoensis may be the result of a niore complex strategy before entering dia- pause. The value obtained for this species has been the highest to date, and that is why it is an outlier in Figure 4. Most of unhatched cocoons showed fungal infection over their surface. This could deter- mine the low values of hatching in the laboratory, although we cannot assure that these filngi were the cause or the result of cocoon non-viability, as it has been mentioned by Senapati (1980) for Indian worms. There seems to be a clear relationship between the number of cocoons produced and their location in the soil profile (Satchel1 1967). He concludes that species in a high mortality risk environment present a greater rate of cocoon production. In this sense Glossorlrilus sp. pro- duced the largest amount of cocoons located preferentially in the first 10 cm of soil. Many of ' these cocoons will not hatch and die, a typical r-strategy species (Pianka 1970). On the con- trary, M. cnriningiietisis produced much fewer cocoons, having the ability to descend deeper into the soil to aestivate, a K-strategy species.

Acknowledgements This study was included within the STD-3 European Macrofauna Project and the Tropical Lowlands Pro- gram at the International Centre for Tropical Agriculture, CIAT (Cali, Colombia). The first author ex- presses his deepest gratitude to T. Decaëns for his help in field work and comments arisen in this study.

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