GROWTH AND MACRONUTRIENT REMOVAL OF WATER HYACINTH IN A SMALL SECONDARY SEWAGE-TREATMENT PLANT

Studies have been made of the growth characteristics of water hyacinth, Eichhornia crassipes (Mart.) Solms, and its ability to remove N, P and K, in a secondary settling pond of a small secondary sewage treatment plant serving both the academic and residential blocks of the Swire Marine Laboratory, University of Hong Kong. The treatment plant consists of, in series, a primary settling tank, a trickling filter compartment and a secondary settling pond from which part of the treated wastewater is recycled to the primary settling tank while the remaining effluent (1 to 2 m3 daily) mixes with and hence is diluted by the outflowing seawater from the aquarium system of the Swire Marine Laboratory before discharge to the sea. Samples of wastewater have been taken regularly from the primary sedimentation pond, the outflow of the trickling filter, the secondary settling pond and the effluent of the treatment plant (before mixing with aquarium outflow) since January, 1992. Physical, chemical and biological characteristics of the samples have been determined and are typical of secondary effluents, with a mean pH of about 7.5, total solids 1200 mg L-1, suspended solids 45 mg L-1, conductivity 2000 muS cm-1, salinity 1 ppt, dissolved oxygen 2 mg L-1, BOD5 45 mg L-1, Kjeldahl-N 30 mg L-1, NH4-N 25 mg L-1, NO3-N 4 mg L-1, total P 10 mg L-1, K 35 mg L-1 and total coliforms of less than 10(5) colonies 100 ml - 1. Water hyacinth plants have been stocked in the secondary settling pond as an integral part of the treatment plant so as to improve the quality of, as well as to retrieving and recycling nutrient elements from, the wastewater. The plants are periodically harvested to maintain an active growing crop. The growth rate, standing crop biomass, tissue nutrient composition, nutrient storage and accumulation rate of two growth cycles, one from February 25 to March 18 (mean temperature 17.6-degrees-C) and the other from 22 April to 12 May (24.8-degrees-C) are reported. The water hyacinth assumed a relatively high standing crop biomass of 10 kg m-2 (5 to 6 t DM ha-1), and growth rates of 48 and 225 g m-2 day-1, respectively, for the first and second growth period. Nutrient storage capacities were relatively high, at about 20, 7.5 and 16.5 g m-2 for N, P and K, respectively. The nutrient composition was very high, reaching 5.42% for N, 1.97 for P, and 4.57 for K. Both the stem and lamina accumulated high levels of N, while the petiole had the highest level of P and K. Apart from nutrient removal, the water hyacinth also helped to decrease the suspended solids, BOD5 value and total coliforms of the wastewater. It is concluded that water hyacinth improves the quality of wastewater in such small-scale sewage treatment plants and it is recommended that frequent harvests of water hyacinth would increase the treatment efficiency, especially during the active growing season with high temperatures coupled with intense solar radiation.