一种新型造纸厂生物固体颗粒对作物和土壤的影响

M. Mozaffari, Hannah Hays
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引用次数: 2

摘要

美国是全球造纸工业的主要生产国之一,约占世界纸张供应量的24%。尽管原料和生产方法多种多样,但富C造纸厂生物固体(PB)是造纸过程中的主要副产品。垃圾填埋是PB管理的主要方法。不断增加的堆填成本及其潜在的环境后果促使研究和发展努力寻找PB的有益用途。这一明智的选择降低了纸张的整体生产成本,并提高了环境的可持续性。PB的颗粒化通过降低运输成本来增加其适销性。本研究是为了更好地了解一种新开发的造纸厂生物固体颗粒(PPB)对甜椒(Capsicum annuum L.)和土壤的特性和影响。尿素和PPB的施氮量分别为45、90、135和180 kg N hm -1,外加0 N的对照处理。该PPB的总C和N浓度分别为379和14 g·kg-1, C:N比值为27.2。氮素处理显著影响辣椒株高、干生物量、氮浓度和氮素吸收量(P≤0.0839)。株高31.2 ~ 44.4 cm;135 kg·ha-1尿素氮和PPB-N分别产生最高和最短植株。未施氮、尿素氮和PPB-N处理的辣椒干生物量分别为5.3、5.7 ~ 7.5和5.9 ~ 6.5 g·株-1。对照处理(0 N)的氮素浓度为36.4 g·kg-1,任意N处理辣椒的氮素浓度为32.0 ~ 40.7 g·kg-1。PPB速率与植株氮浓度呈负相关,但并不总是具有统计学意义。一般来说,尿素处理的辣椒比对照或PPB处理的辣椒去除土壤中更多的氮。未施氮处理和施尿素或PPB处理的植株氮素吸收量分别为194、229 ~ 270和155 ~ 164 mg·株-1。辣椒对氮的吸收和浓度数据表明,较高的PPB速率导致原生土壤和PPB-N的固定,因为它的C:N比较宽(27.2)。施氮处理对土壤pH、SOM、全碳和N (P < 0.1)有显著影响。收获后土壤有机质和全碳含量分别为17.4 ~ 19.4 g·kg-1和21.9 ~ 35.0 g·kg-1。观察到的土壤总碳和SOM的增加突出了PPB作为改善土壤健康和固碳的潜在有益用途。通过共施或将矿物氮掺入颗粒中,缩小PPB的C:N比将使其成为一种有吸引力的有机氮肥。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Effect of a Newly Developed Pelleted Papermill Biosolids on Crop and Soil
The US is one of the leading global producers of paper industry with approximately 24 percent of the share of world paper supply. Despite diversity of the feedstock and production methods, C rich papermill biosolids (PB) is a major byproduct of paper production process. Landfilling is the predominant method of PB management. Increasing landfill cost and its potential environmental consequences have incentivized research and development efforts to find beneficial uses for PB. This sensible option reduces the overall paper production costs and increases environmental sustainability. Pelletization of PB increases its marketability by reducing transportation costs. This greenhouse study was conducted to gain a better understanding of the properties and effects of a recently developed pelletized papermill biosolids (PPB) on bell pepper (Capsicum annuum L.) and soil. Urea and PPB were each applied at four total N rates equivalent to 45, 90, 135, and 180 kg N ha﹣1 and an additional control treatments of 0 N was included. The total C and N concentration in this PPB were 379 and 14 g·kg﹣1 respectively and its C:N ratio was 27.2. Nitrogen treatment significantly (P ≤ 0.0839) influenced pepper height, dry biomass, N concentration, and N uptake. Plant height ranged from 31.2 to 44.4 cm; 135 kg·ha﹣1 urea-N and PPB-N produced the tallest and shortest plants respectively. Dry biomass of the pepper that did not receive any N, those treated with urea-N or PPB-N were 5.3, 5.7 - 7.5, and 5.9 - 6.5 g·plant﹣1 respectively. Nitrogen concentration in control treatment (0 N) was 36.4 g·kg﹣1 and that of pepper treated with any N ranged from 32.0 - 40.7 g·kg﹣1. There was an inverse numerical, albeit not always statistically significant, relationship between PPB rate and plant N concentration. Generally, pepper treated with urea removed significantly more N from soil than control or PPB treated pepper. Nitrogen uptake by plants that did not receive any N and those amended with urea or PPB were 194, 229 - 270, and 155 - 164 mg·plant﹣1 respectively. Pepper N uptake and concentration data indicate that higher rates of PPB resulted in immobilization of native soil and PPB-N due to its wide C:N ratio (27.2). Nitrogen treatment significantly influenced soil pH, SOM, total C and N (P > 0.1). Soil organic matter and total C in post-harvest soil samples were 17.4 - 19.4 and 21.9 - 35.0 g·kg﹣1 respectively. The observed increase in soil total C and SOM highlights the potential beneficial use of PPB as a means to improve soil health and sequester C in soil. Narrowing the C:N ratio of PPB, by coapplication or incorporation of the mineral N into the pellets will make it an attractive organic N fertilizer.
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