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Development of zinc tolerance by the ammonia oxidising community is restricted to ammonia oxidising Bacteria, rather than Archaea

机译:氨氧化社区对锌耐受性的发展仅限于氨氧化细菌,而不是古细菌

摘要

Both ammonia oxidizing Bacteria (AOB) and ammonia oxidizing Archaea (AOA) are abundant in soil, but, their relative contributions to soil nitrification are still debated and different studies have reported contrasting results. It is therefore still unclear under which soil conditions AOB or AOA dominate nitrification. Zinc contamination of soils has a pronounced effect on nitrification in soil, however previous studies have shown that this effect is transient due to the development of a tolerant nitrifying community. This study investigates the influence of long-term zinc (Zn) stress on the nitrifying community and determines the role of the Archaea and Bacteria in nitrification of soils exposed to Zn. To assess this, a grassland soil was artificially spiked with 1300 and 2400 mg Zn kg-1, as ZnCl2, and incubated outside, receiving each 4 months 150 mg NH4+-N kg-1. Nitrification was inhibited by Zn after incubation for 1 week and 2 months. However, after 12 months Zn exposure, nitrification in both Zn-contaminated treatments was restored to the initial nitrification rate of the uncontaminated soil. The soil ammonia oxidiser community in both Zn treatments developed larger Zn tolerance than the uncontaminated soil. Soil was sampled after 12 months incubation and the samples were subsequently subjected to Stable Isotope Probing (SIP) of DNA by incubating 20 g of pre-incubated soil under 13CO2 atmosphere at 30 °C for 24 days in gas-tight sealed bottles. Ammonia was supplied at days 0, 8 and 16 (100 mg N kg-1 soil) following injection of 6 ml of 13CO2 or 12CO2, in triplicate. Bottles were opened twice weekly to ensure aerobic conditions, resealed and CO2 concentrations were reestablished. Soil was sampled at day 24, total DNA was extracted from soil and DNA extracts were subjected to isopycnic centrifugation in a CsCl gradient (Beckman Coulter ultracentrifuge, rotor VTI 65.2, 24h, 186000 g) separating 13C-labelled DNA from 12C labelled DNA into different fractions. Only active populations, i.e. populations that autotrophically consumed CO2, incorporate 13C into their DNA. The abundance of ammonia oxidizing Bacteria and Archaea was measured in each fraction by qPCR of amoA genes, using primers amoA-1F and amoA-2R to target AOB and primers Crenamo23F and Crenamo616R to target AOA. 13C was assimilated by AOB in the uncontaminated soil, as indicated by a higher relative abundance of AOB in heavier fractions than in 12C-incubated samples. This clear shift was not observed for the AOA. After Zn exposure for 12 months a similar pattern was observed in both Zn treatments. These results show that, although ammonia oxidising Archaea dominate the number of nitrifying microorganisms in the uncontaminated soil, ammonia oxidizing Bacteria are responsible for soil nitrification. Stress conditions, arising from chronic zinc exposure, increased the relative abundance of AOB to AOA and did not change the predominance of AOB in soil nitrification activity. These results indicate that the recovery of nitrification after long-term Zn exposure and development of Zn tolerance in this soil is due to the activity of AOB, rather than AOA.
机译:氨氧化细菌(AOB)和氨氧化古细菌(AOA)在土壤中均很丰富,但是它们对土壤硝化的相对贡献仍在争论中,并且不同的研究报告了相反的结果。因此,仍不清楚在哪种土壤条件下AOB或AOA主导硝化作用。土壤中的锌污染对土壤中的硝化作用具有显着影响,但是先前的研究表明,由于耐受性硝化群落的发展,这种影响是短暂的。本研究调查了长期锌胁迫对硝化群落的影响,并确定古细菌和细菌在暴露于锌的土壤硝化中的作用。为了对此进行评估,将1300和2400 mg Zn kg-1作为ZnCl2人工掺入草原土壤,并在室外保温,每4个月接受150 mg NH4 + -N kg-1。孵育1周和2个月后,Zn抑制了硝化作用。但是,在锌暴露12个月后,两种受锌污染的处理中的硝化作用都恢复到未污染土壤的初始硝化率。两种锌处理的土壤氨氧化剂社区都比未污染的土壤具有更大的锌耐受性。孵育12个月后对土壤取样,然后通过将20 g预孵育的土壤在13CO2气氛下,30°C的密封容器中孵育24天,对样品进行DNA的稳定同位素探测(SIP)。一式三份注入6 ml 13CO2或12CO2后,在第0、8和16天(100 mg N kg-1土壤)供应氨。每周打开瓶​​子两次,以确保有氧条件,重新密封并重新建立CO2浓度。在第24天对土壤取样,从土壤中提取总DNA,然后将DNA提取物在CsCl梯度(贝克曼库尔特超速离心机,转子VTI 65.2,24h,186000 g)中进行等温离心,将13C标记的DNA与12C标记的DNA分离为不同的分数。只有活动种群,即自养消耗二氧化碳的种群,才将13C整合到其DNA中。通过使用amoA-1F和amoA-2R引物靶向AOB以及使用Crenamo23F和Crenamo616R引物靶向AOA的amoA基因的qPCR测定每个级分中氨氧化细菌和古细菌的丰度。在未污染的土壤中,AOB吸收了13C,这表明重馏分中AOB的相对丰度比12C孵育样品高。对于AOA,没有观察到这种明显的变化。锌暴露12个月后,两种锌处理均观察到相似的模式。这些结果表明,尽管氨氧化古细菌在未污染的土壤中主导着硝化微生物的数量,但氨氧化细菌却是土壤硝化的原因。慢性锌暴露引起的胁迫条件增加了AOB对AOA的相对丰度,并且没有改变AOB在土壤硝化活性中的优势。这些结果表明,长期暴露于锌中后硝化的恢复以及该土壤中锌耐受性的发展归因于AOB的活性,而不是AOA的活性。

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