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This paper describes the influence of four criteria: (i) buffer zone width, (ii) amount of surface runoff water entering the BZ, (iii) seasonal variation and (iv) vegetation type.
These studies can also be classified into two fold: (i) buffer capacity determination problem, and (ii) FA entrance sequence determination problem.
In the beginning, two buffer solutions have been prepared: (i) buffer I with a pH value of 6.0, and (ii) buffer II with a pH value of 7.0.
Following extraction, three main metal-ion fractions were obtained: i) buffer soluble (extracts 1 6); ii) acid soluble (extracts 7 9); iii) ash (non-soluble Zn and/or Cd).
mda-7/IL-24 IBs were washed using '3 + 1' washing buffers (about 1 g IBs were solubilized in 30 mL washing buffer): buffer I, buffer II, buffer III, and deionized water (Table 2).
Positive controls were treated with DNase I buffer containing 10 unit/ml of DNase I (Promega #M6101).
Bacteria were harvested by centrifugation and resuspended in 1X DNase I buffer (New England Biolabs, MA, USA).
Each sample was incubated at room temperature for 10 min with 2.5 µl DNase I and 0.8 µl DNase I buffer to remove genomic DNA.
4.5 µl of the restriction enzyme Sal I (10 U/µl) and 6.5 µl of 10× Sal I buffer were added.
For DNA digestion, embryos were incubated with RNase-free DNase I (50 U/ml in DNase I buffer; Ambion) for 1h at 37°C.
10× the volume in µL of the weight of the sample was added to the sample for CER I buffer (from kit with the addition of one protease and one phosphatase tablet dissolved in it).
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