Method for repairing heavy metal polluted tailing sand by using ciliate desert-grass
A technology of tailings sand and heavy metals, which is applied in the field of phytoremediation, can solve the problems of lack of methods for repairing tailings, etc., and achieve the effects of increasing arsenic enrichment, increasing pH value, and strong arsenic absorption
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Embodiment 1
[0047] Example 1 Modifier configuration and centipede cultivation
[0048] 1. Collection of heavy metal pollution tailings sand samples:
[0049] The tailings sand was collected from the surface layer (0-30cm) of the Dabaoshan tailings pond in Shaoguan City, Guangdong Province, mixed evenly and air-dried under natural conditions, and passed through a 2mm sieve. The pH of the tailings sand was 3.63 and the average arsenic content was 248.35mg / kg, which exceeded the "Soil Environment" Quality Agricultural Land Pollution Risk Control Standard (GB15618-2018) The highest risk screening value of arsenic pollution in agricultural land soil (40mg / kg). At the same time, the average cadmium content was 1.8 mg / kg, the average lead content was 197.51 mg / kg, and the average zinc content was 541.10 mg / kg.
[0050] 2. Improved ratio:
[0051] A modifier is added to the heavy metal polluted tailing sand and mixed evenly to obtain the improved heavy metal polluted tailing sand. In terms of ...
Embodiment 2
[0058] Select the centipede grass seedlings with good growth and similar height of about 4 cm cultivated in step 3, wash the roots and move them to a plastic pot filled with improved arsenic high-pollution tailings sand, place them in an artificial climate room and carry out the experiments. Cultivation, artificial climate chamber setting conditions are the same as step 3, 1 seedling is planted in each pot, water is applied once every 2 days, and potted for 60 days. Example 2 The growth status of centipede grass and the enrichment of arsenic
[0059] 1. Experimental method
[0060] 1. Sample collection:
[0061] The centipede grass after potted planting 60d in Example 1 step 4 was sampled, and the plant height of the centipede grass in the 8 improved groups was measured (under the natural growth state of the centipede grass, the vertical distance between the highest part of the plant and the rhizome), Photographs were taken to record the centipede grass in each treatment gro...
Embodiment 3
[0072] Example 3 Passivation of lead and zinc by improved repair method
[0073] 1. Experimental method
[0074] The soil samples after planting centipede grass in Example 1 were collected, and the effectiveness of lead and zinc in the improved tailings sand before and after planting centipede grass was determined by DTPA extraction method.
[0075] 2. Experimental results
[0076] The measurement results are shown in Table 4.
[0077] Table 4 Effects of adding amendments and centipede grass restoration methods on the availability of lead and zinc in tailings (average value)
[0078]
[0079] It can be seen from Table 4 that after improving the arsenic high-pollution tailings sand and planting centipede grass for 60 days under the conditions of improvement group 3 and improvement group 4, the content of available lead in the soil was significantly reduced, and the content of available zinc was also reduced. Considering the absorption and accumulation of arsenic by centip...
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