Elsevier

Aquatic Botany

Volume 63, Issue 2, 1 March 1999, Pages 83-93
Aquatic Botany

Rooting and vegetative propagation in Laguncularia racemosa

https://doi.org/10.1016/S0304-3770(98)00122-3Get rights and content

Abstract

Reproduction and dispersal in mangrove species occurs mainly through propagules. Vegetative propagation is considered to be insignificant by many researchers, however, for restoration projects, it could be an important advantage. Therefore, we carried out experiments with shoot cuttings of Laguncularia racemosa and Rhizophora mangle under controlled conditions as well as in the field to prove the feasibility of vegetative propagation in these mangrove species.

None of 110 planted R. mangle cuttings survived the experiments, but the results with L. racemosa were promising. We observed that the single most important factor for survival of L. racemosa cuttings was rooting of the shoots prior to cutting from the parent trees. This is a common feature in the study area, the Ciénaga Grande de Santa Marta, Colombia. Seasonal floodings of lower branches induce secondary root growth and can even lead to natural vegetative propagation. Other factors that have favorable effects on the survival of the cuttings are a large shoot diameter, manual defoliation to reduce transpiration, and direct sun irradiation. Additionally, burying a small part of the roots in a way that allows some roots to freely float in the surface water, improves the survival rate to 95%. However, the watering with rooting agents shows slightly negative effects. The surviving shoots grow rapidly and fruit set can be observed within six months after planting in the field.

In restoration attempts with L. racemosa it is, therefore, possible to bypass the very sensitive seedling phase by planting shoot cuttings. The value of this method is linked to quicker establishment and reproduction of the cuttings as well as the possibility to plant them in flooded areas, where establishment of propagules and survival of seedlings of L. racemosa is very difficult to achieve.

Introduction

Vegetative propagation in mangroves is considered insignificant for spreading and colonisation (Rabinowitz, 1978; Tomlinson, 1986). In general, mangrove species are supposed to have little or no capacity for vegetative regeneration, and no natural capacity for vegetative dispersal (Tomlinson, 1986). However, reports on vegetative propagation can be found: some mangrove genera (e.g., Avicennia, Rhizophora, and Sonneratia) have a limited ability to spread vegetatively, because their lower branches may recline under their own weight and root distally (Tomlinson, 1986). A vegetative seaward expansion through clone formation can be observed in Sonneratia alba J. Smith and in an analogous manner in Rhizophora sp. (Holbrook and Putz, 1982; Crewz and Lewis, 1991). Propagation through shoot cuttings and air-layering is known for Sonneratia apetala B. Ham. and Xylocarpus granatum Koen. (Kathiresan and Ravikumar, 1995). Many authors wrote about air-layering of Rhizophora mangle L., Avicennia germinans (L.) Stearn, and Laguncularia racemosa (L.) Gaertn. f. (Pulver, 1976; Carlton and Moffler, 1978; Crewz and Moffler, 1984; González and Rivas, 1993). Although most of these experiments showed promising results during the layering phase and all species can take roots, only layers of L. racemosa, S. apetala and X. granatum were reported to survive transplantation into the field.

Reproduction and dispersal of mangroves occurs mainly through propagules. As a result, most mangrove restoration efforts have relied upon planting of propagules and seedlings, although seedling mortality is often extremely high. In some cases older, already established plants have been transplanted (Davis, 1940; Pulver, 1976; Elster, 1997; Elster, 1998). Limited work has been carried out on vegetative propagation, but it could be a very fast and efficient way of regeneration. Therefore, we investigated the feasibility of propagating mangroves by the planting of shoot cuttings. Two species were promising due to their characteristic properties:

  • 1.

    R. mangle, because the tips of the aerial roots develop a normal root system in contact with water and these roots can then establish themselves in the soil firmly;

  • 2.

    L. racemosa, because adventitious roots arise on the lower part of the stems (Jenı́k, 1970), shoots start rooting above ground when flooded and partly inundated branches can develop an extensive root system (Fig. 1(a) and (b)). The occurrence of lower branches with secondary roots is a common phenomenon in L. racemosa in the study area due to prolonged inundations. Many lower branches are continuously flooded for several months during the rainy season (Elster, 1997). Most of the flooded branches develop roots during this time. In addition to these observations local fishermen report that L. racemosa branches used as piles for their stilthouses start to grow.

Section snippets

Study sites

The present study was undertaken at two highly disturbed sites in the north of the Ciénaga Grande de Santa Marta, a brackish lagoon system on the Caribbean coast of Colombia (Fig. 2). Human induced changes in the hydrological system of the area, which have obstructed freshwater entering the connecting channels, has led to a severe increase in salinity during the past 35 years. As a result, ca. 30 000 ha of the original 51 150 ha of mangrove forest died (González, 1991). The surviving mangrove

L. racemosa

During the main rainy season 1995 (August to November), young shoots of L. racemosa were cut and planted under different conditions to observe their rooting and growth response. The cuttings varied in diameter (0.3–2.4 cm) and length (20–105 cm) and had at least four to five buds in accordance with Flinta (1960), who recommended at least three to four buds and a diameter of up to 2.5 cm for cuttings of Populus. The shoots used were from healthy, mature trees growing throughout the study area and

Results

None of the R. mangle cuttings survived the experiments. However, the results in L. racemosa were promising; shoot cuttings in one of the experimental conditions had a 95% survival rate after the first six months (see Table 1, Table 2, and Fig. 4). In addition, a capacity for natural vegetative propagation and localized spread was encountered. Lower branches that recline, both root extensively in contact with water (Fig. 1(a) and (b)), and in the moist ground. Several `young plants' were

Discussion

Secondary root growth is very abundant in L. racemosa when sufficient water is available. The rooting of lower branches in moist soils permits a natural vegetative propagation and local spread of L. racemosa, similarly as reported by Tomlinson (1986)for the genera Avicennia, Rhizophora, and Sonneratia, and by Holbrook and Putz (1982)and Crewz and Lewis (1991)for Rhizophora sp. and Sonneratia alba. It is often difficult to distinguish between L. racemosa plants that established themselves in

Acknowledgements

We thank the INVEMAR and CORPAMAG/PRO-CIÉNAGA (both Santa Marta, Colombia) for collaboration and access to laboratory and boat facilities as well as C. Carbonó and J. Döring for technical assistance. We further thank E. Ashton for improvements on the manuscript. The research was supported by the GTZ (TÖB, “Flanking Program for Tropical Ecology”, PN: 90.2136.1), Eschborn/Germany.

References (21)

  • K Kathiresan et al.

    Vegetative propagation through air-layering in two species of mangroves

    Aquat. Bot.

    (1995)
  • A.H Baldwin et al.

    Hurricane damage and regeneration in fringe mangrove forests of southeast Florida, USA

    J. coast. Res.

    (1995)
  • J.M Carlton et al.

    Propagation of mangroves by air-layering

    Env. Conserv.

    (1978)
  • Crewz, D.W., Lewis, R.R., 1991. An evaluation of historical attempts to establish emergent vegetation in marine...
  • Crewz, D.W., Moffler, M.D., 1984. An evaluation of air-layering with three species of mangroves. In: Webb, F.J., Jr....
  • J.H Davis

    The ecology and geologic role of mangroves in Florida

    Pap. Tortugas Lab.

    (1940)
  • Elster, C., 1997. Beziehung zwischen ökologischen Faktoren und der Regeneration dreier Mangrovenarten im Gebiet der...
  • Elster, C., 1998. Regenerationsmöglichkeiten der Mangrove im Gebiet der Ciénaga Grande de Santa Marta (Kolumbien)....
  • Elster, C., Perdomo, L., Schnetter, M.-L., in press. Impact of ecological factors on the regeneration of mangroves in...
  • Ensminger, I., 1996. Hydrologische Veränderungen am Canal Cları́n und ihre Bedeutung für die Regeneration...
There are more references available in the full text version of this article.

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