Open Access Open Access  Restricted Access Subscription Access

Exposure of Eichhornia crassipes (Mart.) Solms to Salt Water and its Implications


Affiliations
1 CSIR-National Institute of Oceanography, Dona Paula, Goa 403 004, India
 

In this article, we discuss the effect of salinity on the viability and decomposition of Eichhornia crassipes plant under normal photoperiod, dark condition and physiological response. Highest concentration of total organic carbon (27.43 mg C l-1) was recorded in 15 psu salinity after 45 days. The TOC output was more in case of leaf (3.6 mg C l-1) than petiole (2.39 mg C l-1) under dark condition, after 21 days in freshwater. Salt stress was found to enhance the superoxide dismutase activity at 20 psu in both leaf and petiole. Enzyme activity declined when salt-stressed plants were transferred to nutrient enriched freshwater. This indicated that 20 psu could be a plant's salt tolerance limit. The potential transfer test conducted in this study showed that Eichorrnia introduction through shipping activities is less likely.

Keywords

Eichhornia crassipes, Salinity Stress, Superoxide Dismutase, Total Organic Carbon.
User
Notifications
Font Size

  • Gopal, B., Water Hyacinth, Elsevier, Amsterdam, 1987, p. 471.
  • Mehra, A., Farago, M. E. and Banerjee, D. K., The water hyacinth: an environmental friend or pest? A review. Resour. Environ. Biotechnol., 1999, 2, 255–281.
  • Tag El Seed, M., Water hyacinth – The successful weed. In Aquatic Weeds in the Sudan (ed. Obeid, M.), University of Khartoum, Sudan, 1975, pp. 50–68.
  • Reddy, K. R. and DeBusk, W. F., Decomposition of water hyacinth detritus in eutrophic lake water. Hydrobiologia, 1991, 211, 101–109.
  • deBusk, T. A. and Dierberg, F. E., The effect of nitrogen and fibre content on the decomposition of the water hyacinth [Eichhornia crassipes (Mart.) Solms]. Hydrobiologia, 1984, 118, 199–204.
  • Ogwada, R. A., Reddy, K. R. and Graets, D. A., Effects of aeration and temperature on nutrient regeneration from selected aquatic macrophytes. J. Environ. Qual., 1984, 13, 239–243.
  • Sangiorgio, F. et al., Ecosystem processes: litter breakdown patterns in mediterranean and Black Sea transitional waters. Transit. Water Bull., 2007, 3, 51–55.
  • Sangiorgio, F. et al., Environmental factors affecting Phragmites australis litter decomposition in Mediterranean and Black Sea transitional waters. Aquat. Conserv.: Mar. Freshwater Ecosyst., 2008, 18, S16–S26.
  • Hunt, H. W., Ingham, E. R., Coleman, D. C., Elliott, E. T. and Reid, C. P. P., Nitrogen limitation of production and decomposition in prairies, mountain meadow, and pine forest. Ecology, 1988, 69, 1009–1016.
  • McClaugherty, C. A., Aber, J. D. and Melillo, J. M., Forest litter decomposition in relation to soil nitrogen dynamics and litter quality. Ecology, 1984, 66, 266–275.
  • Barik, S. K., Mishra, S. and Ayyappan, S., Decomposition patterns of unprocessed and processed lignocellulosic in a freshwater fish pond. Aquat. Ecol., 2000, 34, 185–204.
  • Gaur, S., Singhal, P. K. and Hasija, S. K., Process of decomposition in Eichhornia crassipes(Mart.) Solms: 1. Early decomposition in different plant parts and effect of site variation. J. Environ. Biol., 1989, 10, 23–33.
  • Singhal, P. K., Varghese, L. and Galegaonkar, L., Abiotic and microbial decomposition of pre- and post-bloom leaves of water hyacinth (Eichhornia crassipes (Mart.) Solms). Hydrobiologia, 1993, 259, 115–119.
  • Bayo, M. M., Casa, J. J. and Cruz-Pizarro, Decomposition of submerged Phragmites australis leaf litter in two highly eutrophic Mediterranean coastal lagoons: relative contribution of microbial respiration and macroinvertebrate feeding. Arch. Hydrobiol., 2005, 163, 349–367.
  • Mendelssohn, I. A., Sorrell, B. K., Brix, H., Schierup, H., Lorenzen, B. and Maltby, E., Controls on soil cellulose decomposition along a salinity gradient in a Phragmites australis wetland in Denmark. Aquat. Bot., 1999, 64, 381–398.
  • Fonnesu, A., Pinna, M. and Basset, A., Spatial and temporal variations of detritus breakdown rates in the River Flumendosa basin (Sardinia, Italy). Int. Rev. Hydrobiol., 2004, 89, 443–452.
  • Polunin, N. V. C., The decomposition of emergent macrophyte in freshwater. Adv. Environ. Res., 1984, 14, 115–166.
  • Cunha-Santino, M. B., Bianchini Jr, I. and Okawa, M. H., The fate of Eichhornia azurea (Sw.) Kunth. detritus within a tropical reservoir. Acta Limnol. Bras., 2010, 22, 109–121; doi:10.4322/actalb.02202001.
  • Godshalk, G. L. and Wetzel, R. G., Decomposition of aquatic angiosperms. II. Particulate components. Aquat. Bot., 1978, 5, 301–327.
  • Reice, S. R. and Herbst, G., The role of salinity in decomposition of leaves of Phragmites australis in desert streams. J. Arid. Environ., 1982, 5, 361–368.
  • Eisa, S., Hussin, S., Geissler, N., and Koyro, H. W., Effect of NaCl salinity on water relations, photosynthesis and chemical composition of quinoa (Chenopodium quinoa Willd.) as a potential cash crop halophyte. Aust. J. Crop Sci., 2012, 6, 357–368.
  • Zagorchev, L., Kamenova, P. and Odjakova, M., The role of plant cell wall proteins in response to salt stress. Sci. World J., 2014; article ID 764089, 9 pages; http://dx.doi.org/10.1155/2014/764089.
  • Wang, J. et al., Physiological and proteomic analyses of salt stress response in the halophyte Halogeton glomeratus. Plant Cell Environ., 2015, 38, 655–669.
  • Fridovich, I., Superoxide dismutases. Adv. Enzymol. Relat. Areas Mol. Biol., 1986, 58, 61–79.
  • Raychaudhuri, S. S. and Deng, X. W., The role of superoxide dismutase in combating oxidative stress in higher plants. Bot. Rev., 2000, 66, 89–98.
  • DeCasabianca, M. and Laugier, T., Eichhornia crassipes Production on petroliferous wastewaters: effects of salinity. Bioresour. Technol., 1995, 54, 39–43.
  • Bax, N., Williamsona, A., Aguero, M., Gonzalez, E. and Geeves, W., Marine invasive alien species: a threat to global biodiversity. Mar. Pollut., 2003, 23, 313–323.
  • Vinita, J., Shivaprasad, A., Revichandran, C., Manoj, N. T., Muraleedharan, K. R. and Binzy, J., Salinity response to seasonal runoff in a complex estuarine system (Cochin Estuary, west coast of India). J. Coastal Res., 2015; doi:10.2112/JCOASTRES-D-13-00038.
  • Kaladharan, P., Krishnakumar, P. K., Prema, D., Nandakumar, A., Khambadkar, L. R. and Valsala, K. K., Assimilative capacity of Cochin inshore waters with reference to contaminants received from the backwaters and the upstream areas. Indian J. Fish., 2011, 58(2), 75–83.
  • Jayachandran, P. R., Nandan, S. B. and Sreedevi, O. K., Water quality variation and nutrient characteristics of Kodungallur–Azhikode estuary, Kerala, India. Indian J. Geo-Mar. Sci., 2012, 41(2), 180–187.

Abstract Views: 315

PDF Views: 109




  • Exposure of Eichhornia crassipes (Mart.) Solms to Salt Water and its Implications

Abstract Views: 315  |  PDF Views: 109

Authors

Temjensangba Imchen
CSIR-National Institute of Oceanography, Dona Paula, Goa 403 004, India
S. S. Sawant
CSIR-National Institute of Oceanography, Dona Paula, Goa 403 004, India
Wasim Ezaz
CSIR-National Institute of Oceanography, Dona Paula, Goa 403 004, India

Abstract


In this article, we discuss the effect of salinity on the viability and decomposition of Eichhornia crassipes plant under normal photoperiod, dark condition and physiological response. Highest concentration of total organic carbon (27.43 mg C l-1) was recorded in 15 psu salinity after 45 days. The TOC output was more in case of leaf (3.6 mg C l-1) than petiole (2.39 mg C l-1) under dark condition, after 21 days in freshwater. Salt stress was found to enhance the superoxide dismutase activity at 20 psu in both leaf and petiole. Enzyme activity declined when salt-stressed plants were transferred to nutrient enriched freshwater. This indicated that 20 psu could be a plant's salt tolerance limit. The potential transfer test conducted in this study showed that Eichorrnia introduction through shipping activities is less likely.

Keywords


Eichhornia crassipes, Salinity Stress, Superoxide Dismutase, Total Organic Carbon.

References





DOI: https://doi.org/10.18520/cs%2Fv113%2Fi03%2F439-443