Оценка направленности и механизмов влияния внесения биоугля на субстрат-индуцированное дыхание почв в длительном лабораторном эксперименте
- Авторы: Смирнова Е.В.1, Гиниятуллин К.Г.1, Окунев Р.В.1, Валеева А.А.1, Рязанов С.С.2
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Учреждения:
- Казанский федеральный университет
- Институт проблем экологии и недропользования Академии наук Республики Татарстан
- Выпуск: № 9 (2023)
- Страницы: 1190-1202
- Раздел: ОРГАНИЧЕСКОЕ ВЕЩЕСТВО И МИКРОБНАЯ АКТИВНОСТЬ ПОЧВ
- URL: https://journals.rcsi.science/0032-180X/article/view/138200
- DOI: https://doi.org/10.31857/S0032180X23600312
- EDN: https://elibrary.ru/DVUMZO
- ID: 138200
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Аннотация
В лабораторном эксперименте изучали влияние биоугля (БУ) на субстрат-индуцированное дыхание (СИД) почв. В опыте использовали 10 образцов БУ, полученных из древесных и травянистых материалов в двух режимах пиролиза. Интенсивность СИД определяли через 3 сут, 3 и 6 мес. инкубации. При кратковременной инкубации не наблюдалось влияния БУ на СИД. Исключением был вариант с внесением БУ на основе кукурузы, в котором наблюдалось увеличение СИД на 34.6%. При инкубации в течение 3 мес. обнаруживалось значимое увеличение СИД (от 30.4 до 54.8%) при внесении пяти БУ. При инкубации в течение 6 мес. значимое увеличение СИД (от 30.4 до 65.9%) наблюдалось при внесении восьми БУ. Для оценки свойств БУ, оказывающих влияние на СИД, использовали Лассо регрессию и 23 показателя свойств БУ в качестве потенциальных предикторов. Обнаружено, что при трехдневной инкубации положительное влияние на СИД оказывают следующие свойства БУ: содержание окисляемого органического вещества, обменного кальция и рН водной суспензии, а слабое отрицательное – содержание обменного натрия. При инкубации в течение 3 мес. наблюдается положительное влияние окисляемого органического вещества, а через 6 мес. – содержания золы. Поскольку в опытах наблюдалось только положительное статистически значимое влияние БУ на СИД, cделаy вывод, что для объективной оценки эффективности их использования для секвестрации СО2 в почвах необходимы балансовые расчеты, в которых наряду с количеством внесенного в почвы с БУ устойчивого углерода, должно учитываться потенциальное увеличение эмиссии СО2 из почв за счет активации почвенной сапрофитной микробиоты.
Об авторах
Е. В. Смирнова
Казанский федеральный университет
Автор, ответственный за переписку.
Email: tutinkaz@yandex.ru
Россия, 420008, Казань, ул. Кремлевская, 18
К. Г. Гиниятуллин
Казанский федеральный университет
Email: tutinkaz@yandex.ru
Россия, 420008, Казань, ул. Кремлевская, 18
Р. В. Окунев
Казанский федеральный университет
Email: tutinkaz@yandex.ru
Россия, 420008, Казань, ул. Кремлевская, 18
А. А. Валеева
Казанский федеральный университет
Email: tutinkaz@yandex.ru
Россия, 420008, Казань, ул. Кремлевская, 18
С. С. Рязанов
Институт проблем экологии и недропользования Академии наук Республики Татарстан
Email: tutinkaz@yandex.ru
Россия, 420087, Казань, ул. Даурская, 28
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