Isolation and identification of phosphatase producing bacteria
PPB isolated in this study was identified as
Pseudomonas sp. (8 nos.),
Bacillus sp.(6 nos.),
Brevundimonas sp.(3 nos.),
Achromobacter sp.(2 nos.) and
Arthrobacter sp. (1 no.). The ALP activity observed in the PPB isolates obtained in this study is shown in Fig 1. The ALP activities of PPB isolates were in the range of 13.6±0.021 -20.4±0.015 µmolml
-1h
-1. The bacterial isolate E/S1/20/04 (
B. altitudinis) exhibited the maximum activity of 20.4±0.015 µmolml
-1h
-1. The isolates that showed ALP activity more than 16 µmolml
-1h
-1 were E/S2/19/03 (
B. aryabattai); E/S2/19/01 (
B. anthracis); E/S3/19/03 (
B. pumilus); E/S2/19/05 (
B. paramycoides); E/S4/20/04 (
Arthrobacter sp
.) and E/S4/19/02 (
B. subtilis).
Ravikumar et al., (2007) reported that
Pseudomonas,
Vibrio and
Bacillus are the three major groups of bacteria present in the mangrove sediments are involved in the production of extra-cellular phosphatase enzymes.
Barik et al., (2001) reported that the ALP activity assay of
Bacillus sp and
Pseudomonas sp isolated from freshwater aquaculture pond were 12.013 mg of p-NPmL
-11h
-1 and 11.388 mg of p-NPmL
-11h
-1 respectively.
Abhijith et al., (2017) reported that
B. cereus strain APT23 and
B. thuringiensis strain isolated from mangrove region exhibited 10.04±4.04 μg p-NP released g
-1 h
-1 per 1×10
8 cfu in 72h.
ALP activity at varying salinity
Fig 2 shows the presence of target PhoD gene in PCR amplification. ALP activity observed in the isolates at varying salinity (0, 15, 25 and 35 ppt) is shown in Fig 3. All the isolates had the ability to grow and exhibited ALP activity in salinity ranges from 0 to 35 ppt. At 0ppt salinity, the isolates exhibited poor growth rate and low ALP activity. All the five isolates showed significantly higher ALP activity at 35 ppt. The present study clearly revealed that salinity has a great impact on the growth as well as ALP activity of the isolates. Though these isolates showed maximum activity at 35 ppt, they showed activity at zero saline condition too. Thus, these isolates could also be used in brackish water aquaculture and inland saline aquaculture.
Microcosm study to analyse potential of isolates to mobilize phosphorus from aquaculture sediment to water
Phosphate level in water and ALP activity and available-P in the sediment during the microcosm experiment is shown in Fig 4. The control tank showed stable available P, ALP activity in sediment and orthophosphate in water from 0 to 14. All the tanks inoculated with five isolates collected in the study and commercial PPB product. A gradual increase in ALP activity and available-P in sediment and orthophosphate in water were observed up to 10 days and the variation in the activity could be observed from day 10 -14. During the study period, there is a significant increase in phosphorus in water as well as ALP activity and available-P concentration in sediments was observed between control and treatment tanks. In control tank, the phosphorus content in water was maintained in the range of 3.05-3.97mg/l whereas, in commercial P bacterial product inoculated tanks, P concentration was steadily increased and observed as 1.88 mg/l at 14th day. Among the treatment groups,
B. subtilis treatment tanks showed maximum P in water ie. 1.60 mg.L
-1 followed by
B. altitudinis -1.49 mg.L
-1 and
B. pumilus-1.4 7 mg.L
-1. The soil ALP activity (µmol g
-1h
-1) was in the order of commercial P products (10.59) >
B. pumilus (10.05) e”
B. subtilis (10.04) >
B. paramycoides (9.99)
> B. altitudinis (9.59)
> B. aryabhattai (9.01). In terms of available-P content in sediments on 14th day, maximum was recorded in tanks with commercial P products (140.06 ppm) followed by
B. pumilus (134.0 ppm). With regard to available-P, there is no significant (p<0.05) difference observed between
B. pumilus and commercial product.
B. pumilus had significantly (p<0.05) increased available-P content from 35.44 ppm on 0th day to 134.05 ppm on 14
th day. With respect to Soil ALP activity and Water - P, except control, all treatments showed on par with commercial product.
The survival of inoculated bacterial isolates in treatment tanks was assessed by counting PPB in water and sediment samples at the beginning and end of the study. The initial and final PP count during the study period were in the range of 11-21 cfu/ml and 410-483 cfu/ml in water samples and 7-13 cfu.g
-1 and 2-4×10
4 cfu.g
-1 in soil samples.
Soil organic matter (SOM) content and clay content positively influenced the ALP activity. The exchange of P between sediment and water is complex phenomenon influenced by bacterial activity due to the abundance of PPB, out of total microbial mass of soils (
Alongi, 1988). The bacterial ALP activity of sediments varied based on the physicochemical properties of soil, organic matter content, C/N ratio and total P content (
Djordjevic et al., 2003). The increase in ALP activity in sediment samples of all treatment tanks with the PPB inoculum indicated that the inoculated bacterial isolates hydrolyze the organic phosphorus by producing extracellular phosphatases in the sediment which has remitted in the increase in the available P content in sediment and phosphorus in water. Similar experiment with the isolates from various sources has been carried out to demonstrate the mineralising capacity in agriculture soil
(Mader et al., 2011; Piromyou et al., 2011; Nassal et al., 2018). Thus, the application of PPB as biofertilizer in aquaculture pond will aid in hydrolysis of organic P as well as drastically reduce the usage of P based chemical fertilizers.
Soluble phosphate of above 0.20mg/l may be indicative of medium to high and highly productive fish ponds
(Adhikari et al., 2017). Based on available-P, soil could be classified as low (<30ppm), medium (30-60ppm) and high (>60ppm). The phosphate level in water of microcosm study was observed to be above the recommended optimal value. But the increase in available P content of sediment was in the range of high productivity category. In the present study, water-P, ALP activity and available-P of sediment increased up to 2.46-3.75 times, 0.63-0.92 times and 1.41-2.11 times respectively.