유기질비료와 화학비료 시용에 따른 작물체의 질소동위원소비 (${\delta}^{15}N$) 차이 유무를 조사하기 위해 포트 조건에서 돈분 퇴비 (+13.9‰) 와 요소(-2.3‰) 를 시용하여 70일간 재배한 옥수수의 뿌리, 줄기, 잎, 알곡에 대한 ${\delta}^{15}N$ 값을 분석하였고, 동위원소 질량수지 방정식을 이용하여 옥수수 전부위에 대한 ${\delta}^{15}N$ 값을 계산하였다. 옥수수의 ${\delta}^{15}N$값은 토양 질소의 영향과 질소의 형태변환과정에 수반되는 동위원소분할효과에 의해 시용한 퇴비와 요소의 ${\delta}^{15}N$ 값과 차이를 보였다. 옥수수 전부위, 뿌리 및 줄기의 ${\delta}^{15}N$ 값은 요소와 퇴비 시용에 따른 유의성 있는 차이 (p<0.05)를 나타내지 않았지만, 잎과 알곡의 ${\delta}^{15}N$ 값은 각각 퇴비 처리구(+14.3‰, +16.2‰) > 무처리구(+13.2‰, +13.9‰) > 요소-퇴비 혼합처리구(+10.1‰, +12.6‰) 요소 처리구 (+10.1‰, +12.4‰)의 순서로 유의성 있는 차이가 나타났다. 따라서, 본 연구는 시용 질소원의 종류(퇴비 또는 화학비료)를 확인하는데 있어서 작물의 잎 또는 알곡의 ${\delta}^{15}N$ 값 활용 가능성을 제시해주는 것으로 판단되었다. 하지만, 보다 일반적인 결론을 얻기 위해서는 다양한 종류의 토양과 작물에 대한 연구가 요구된다.
유기질비료와 화학비료 시용에 따른 작물체의 질소동위원소비 (${\delta}^{15}N$) 차이 유무를 조사하기 위해 포트 조건에서 돈분 퇴비 (+13.9‰) 와 요소(-2.3‰) 를 시용하여 70일간 재배한 옥수수의 뿌리, 줄기, 잎, 알곡에 대한 ${\delta}^{15}N$ 값을 분석하였고, 동위원소 질량수지 방정식을 이용하여 옥수수 전부위에 대한 ${\delta}^{15}N$ 값을 계산하였다. 옥수수의 ${\delta}^{15}N$값은 토양 질소의 영향과 질소의 형태변환과정에 수반되는 동위원소분할효과에 의해 시용한 퇴비와 요소의 ${\delta}^{15}N$ 값과 차이를 보였다. 옥수수 전부위, 뿌리 및 줄기의 ${\delta}^{15}N$ 값은 요소와 퇴비 시용에 따른 유의성 있는 차이 (p<0.05)를 나타내지 않았지만, 잎과 알곡의 ${\delta}^{15}N$ 값은 각각 퇴비 처리구(+14.3‰, +16.2‰) > 무처리구(+13.2‰, +13.9‰) > 요소-퇴비 혼합처리구(+10.1‰, +12.6‰) 요소 처리구 (+10.1‰, +12.4‰)의 순서로 유의성 있는 차이가 나타났다. 따라서, 본 연구는 시용 질소원의 종류(퇴비 또는 화학비료)를 확인하는데 있어서 작물의 잎 또는 알곡의 ${\delta}^{15}N$ 값 활용 가능성을 제시해주는 것으로 판단되었다. 하지만, 보다 일반적인 결론을 얻기 위해서는 다양한 종류의 토양과 작물에 대한 연구가 요구된다.
To study whether N isotope composition (${\delta}^{15}N$) of crop reflects the kind of fertilizer (chemical or organic) applied to field, a pot experiment was conducted. Corn (Zea mays L.) was cultivated under greenhouse conditions for 70 days. Composted pig manure and urea were applied a...
To study whether N isotope composition (${\delta}^{15}N$) of crop reflects the kind of fertilizer (chemical or organic) applied to field, a pot experiment was conducted. Corn (Zea mays L.) was cultivated under greenhouse conditions for 70 days. Composted pig manure and urea were applied at 0 and 0 (C0U0), at 0 and 300 (COU2), at 300 and 0 (C2U0) and at 150 and $150kg\;N\;ha^{-1}$ (C1U1), respectively. The ${\delta}^{15}N$ values of composted pig manure and urea were + 13.9‰ and -2.3‰, respectively. The ${\delta}^{15}N$ values of whole parts (roots + stems + leaves + grains) were + 12.7, + 12.9, + 14.0 and + 13.0‰ for C0U0, C0U2, C2U0 and C1U1 treatments, and were not significantly affected by the application of isotopically different N sources (P<0.05). However, leaves or grains showed significantly (P<0.05) different ${\delta}^{15}N$ values between treatments. The ${\delta}^{15}N$ values of leaves and grains were + 14.3 and + 16.2‰ for C2U0, +13.2 and +13.9‰ for C0U0, +10.1 and + 12.6‰ for C1U1 and +10.1 and +12.4‰ for C0U2 treatments. The different ${\delta}^{15}N$ values of corn from the values of N sources (compost and urea) applied to soil showed that the ${\delta}^{15}N$ values of corn were affected not only by the isotope composition of N source, but also by N pool mixing and isotope fractionation accompanying N transformation. This study suggests that although the ${\delta}^{15}N$ values of crop are not identical to the ${\delta}^{15}N$ values of N sources applied to fields, the application of isotopically different N sources such as compost and chemical fertilizer may result in qualitative difference in ${\delta}^{15}N$ values of crop.
To study whether N isotope composition (${\delta}^{15}N$) of crop reflects the kind of fertilizer (chemical or organic) applied to field, a pot experiment was conducted. Corn (Zea mays L.) was cultivated under greenhouse conditions for 70 days. Composted pig manure and urea were applied at 0 and 0 (C0U0), at 0 and 300 (COU2), at 300 and 0 (C2U0) and at 150 and $150kg\;N\;ha^{-1}$ (C1U1), respectively. The ${\delta}^{15}N$ values of composted pig manure and urea were + 13.9‰ and -2.3‰, respectively. The ${\delta}^{15}N$ values of whole parts (roots + stems + leaves + grains) were + 12.7, + 12.9, + 14.0 and + 13.0‰ for C0U0, C0U2, C2U0 and C1U1 treatments, and were not significantly affected by the application of isotopically different N sources (P<0.05). However, leaves or grains showed significantly (P<0.05) different ${\delta}^{15}N$ values between treatments. The ${\delta}^{15}N$ values of leaves and grains were + 14.3 and + 16.2‰ for C2U0, +13.2 and +13.9‰ for C0U0, +10.1 and + 12.6‰ for C1U1 and +10.1 and +12.4‰ for C0U2 treatments. The different ${\delta}^{15}N$ values of corn from the values of N sources (compost and urea) applied to soil showed that the ${\delta}^{15}N$ values of corn were affected not only by the isotope composition of N source, but also by N pool mixing and isotope fractionation accompanying N transformation. This study suggests that although the ${\delta}^{15}N$ values of crop are not identical to the ${\delta}^{15}N$ values of N sources applied to fields, the application of isotopically different N sources such as compost and chemical fertilizer may result in qualitative difference in ${\delta}^{15}N$ values of crop.
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대상 데이터
3%. The compost, which was made from solid pig manure with sawdust and dried at 45-6012 for 7 days, was collected from the livestock farming station at Seoul National University, Korea. They were crushed to pass a 2-mm sieve.
데이터처리
Using Generalized Linear Models procedures (SAS Institute, 1989), data were analyzed with least square difierence test after one-way ANOVA for the completely randomized design with three replications to compare the significance among the treatments.
성능/효과
This effect resulted in the relatively lower δ15N value of urea-derived N in com of C1U1 than in C0U2 since the isotope fractionation factor (the degree of δ15N enrichment in substrate) of dentrification is usually higher than that of immobilization (Hgberg, 1997). In conclusions, although the δ15N value of whole components of com was not significantly afiected by the application of urea or compost, leaves or grains showed significantly different δ15N values with application δ15Ndepleted urea or -enriched compost. The different δ15N values of com from the values of N sources (soil, compost and urea) suggests that not only the δ15N signatures of N sources but also N pool mixing and isotope fractionation accompanying N transformation in soil determine the δ15N values of com.
6 g organic-N kg1. The δ15N values of total N, NH4+-N, NCh'-N and organic N of the soil were 6.3%가 8.3%, 9.4% and 6.2%, respectively (Table 1).
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