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通过模拟试验,深入研究了污泥氨在自然状态和不同温度下的释放特征及其影响因素,并结合污泥低温干化工艺的特点,建立了污泥氨释放的收集与处理系统.结果表明,污泥在储存的四天时间内,氨在空气条件下自然释放的日平均释放量为0.11μg/(g·d),在污泥干化过程中,氨的主要释放量集中在0~30min的早期阶段,氨的释放与水的蒸发同步发生,干化温度决定了污泥氨的释放强度,控制污泥在低温下完成干化过程,是抑制污泥氨释放强度的有效措施.通过多级湿式除尘除气不但可以去除污泥干化时释放的绝大部分氨和其他有害气体(如硫化氢),而且几乎可以去除全部烟尘. 相似文献
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本文完善了电热板消解方法,增加了微波消解法.并将两者进行比对试验,实验结果表明对浸出液中总铬进行前处理消解时,电热板与微波消解法都适用,两种方法之间不存在明显的系统误差,准确度、精密度都符合质控要求. 相似文献
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Aishi Zhu 《International Journal of Green Energy》2018,15(3):201-207
The storage of fresh agricultural products is not easy because of its high moisture. Dehydration is an efficient preservation method. The investigation of drying modeling and transfer characteristics are important for selecting operating conditions and equipment design. The drying behavior of Lactuca sativa slices, with the thickness of 2 mm, was investigated at 60.0–80.0°C and 0.60–1.04 m sec?1 velocity in a convective hot air drier. The mass transfer during the drying process was described using six thin drying models. The convective heat transfer coefficient α and mass transfer coefficient kH were finally calculated. The results showed that the drying process could be separated into three stages including accelerating rate, constant rate, and falling rate period, which was influenced by hot air temperature and velocity, and the Modi?ed Page model agreed well with the experimental data. When the operating temperature was increased from 60.0°C to 80.0°C, α was found increased from 88.07 to 107.93 W·m?2·K?1, and kH increased from 46.32 × 10–3 to 68.04 × 10–3 kg·m?2·sec?1·ΔH?1. With the increase of air velocity from 0.60 to 1.04 m·sec?1, α was increased from 78.85 to 101.35 W·m?2·K?1, and kH was enhanced from 51.78 × 10–3 to 65.85 × 10–3 kg·m?2·sec?1·ΔH?1. 相似文献
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基于利用烟气余热的污泥低温干化技术,通过模拟试验和结合工程实践,首次分析研究了污泥对烟气中颗粒物的去除作用及其影响因素.结果表明,被试的四种污泥对烟气中PM2.5、PM10和TSP的去除率分别为18%~42%、32%~55%和39%~62%,污泥对烟气中PM2.5去除率的大小与污泥的细微结构和有机质含量相关联,烟气中颗粒物的去除率随污泥堆积密度和污泥含水率的增加而增加,随污泥粒度的增加而减少,污泥粒径变小时,污泥中水分更容易蒸发成微小水滴,有利于烟气中的细小颗粒物被吸附和凝结. 相似文献
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Changes in nitrification rates of an acid grassland soil with and without air drying have been monitored over 9 days, after first flushing native nitrate from the soils with deionised water. The results confirmed that full re-establishment of nitrification after air drying takes several days, supporting the hypothesis that any immediate first flush of nitrate from air-dried soils originates from cell lysis or flushing of ‘stored’ nitrate. Ammonium spiking confirmed that nitrification was not ammonium substrate limited. It was also found that ammonium accumulates in the soil during the drying process, providing a substrate pool once the population of nitrifiers has re-established. Over the first week of incubation, nitrate immobilisation was less conspicuous in the soil that had been rewetted after air drying compared with the incubated field moist soil. 相似文献