中国对虾(Fenneropenaeus chinensis)“黄海3号”新品种的培育

2006年收集中国对虾“黄海1号”保种群以及海州湾、莱州湾2个野生群体为基础群体构建核心育种群,采用群体选育技术以仔虾Ⅰ期耐氨氮胁迫成活率和收获时对虾体重为选育指标,经过连续5代选育,培育出中国对虾“黄海3号”新品种。新品种耐氨氮胁迫能力强,仔虾Ⅰ期成活率较商品苗种提高21.2%,养殖成活率提高15.2%;生长速度快,收获对虾平均体重较商品苗种提高11.8%。AFLP 技术分析获得5代选育群体的平均多态位点比例分别为42.28%、40.64%、40.32%、39.95%和38.05%。研究结果显示,随着选育世代的增加,选育群体的遗传多样性呈现下降趋势,但随着选育时间的延长,世代之间的分化逐渐降低,群体的遗传结构开始趋于稳定。     

大豆品种的抗病性与叶片内苯丙氨酸解氨酶活性关系的研究

在抗病品种东农9674，东农1572和感病品种黑农39，东农95-165上接种大豆灰斑病菌的1号，2号，4号，6号，7号等5个生理小种，测定从接种到显症前与抗性有关的苯丙氨酸解氨酶活性的变化。研究结果表明，抗病的大豆品种接种不同生理小种的灰斑病菌后，PAL的活性分别从第6-7天起吴上升趋势且明显高于对照；相反感病品种从8-9天起PAL活性明显低于对照，因此说明PAL的活性与大豆抗灰斑病性呈正相关关系。     

有机肥部分替代化肥氮对叶菜产量和环境效应的影响

针对叶菜类蔬菜有机肥氮替代化肥氮的最佳替代比例及对经济效益和环境效应综合评价较缺乏等问题,本研究采用田间试验,对包心菜和小青菜进行等氮水平下不同比例有机肥替代化肥处理,包括:纯化肥氮(0M),25%、50%、75%和100%有机肥替代化肥(25%M、50%M、75%M和100%M),研究不同处理下蔬菜产量、经济效益、土壤氨挥发和氧化亚氮排放。结果表明, 25%M处理下包心菜和小青菜产量均达最高,且与0M处理相比包心菜和小青菜的产量分别增加15.0%(P0.05)和16.3%(P0.05)。25%M比0M处理经济效益分别增加11.7%和5.4%,但在50%M、75%M和100%M处理下经济效益为负增长。25%M处理下,氨挥发累积排放量在包心菜和小青菜季分别为42.1kg·hm~(-2)和12.9kg·hm~(-2),比0M处理分别降低23.4%(P0.05)和41.6%(P0.05); 0M和25%M处理间氧化亚氮累积排放量无显著差异, 25%M处理在包心菜和小青菜季的氧化亚氮累积排放量分别为0.74 kg·hm~(-2)和3.06 kg·hm~(-2);与25%M处理相比, 50%M、75%M和100%M处理下氧化亚氮排放分别增加33.7%～60.8%(P0.05)、50.0%～134.3%(P0.05)和56.8%～185.6%(P0.05)。基于此,提出叶菜类蔬菜有机肥氮替代化肥氮的适宜替代比例在25%左右时可实现最佳的增效减排效果。     

改性尿素硝酸铵溶液调控氮素挥发和淋溶的研究

为了提高肥料的利用率,以尿素硝酸铵溶液为原料、聚氨酸为保护剂,复合抑制剂NBPT(N-丁基硫代磷酰三胺)和DMPP(3,4-二甲基吡唑磷酸盐)为材料,开发出改性尿素硝酸铵溶液(YUL1和YUL2),研究其对华北平原夏玉米追肥过程中的氨挥发和淋溶损失的调控效果。田间试验设置6个处理:不施氮肥(CK)、农民习惯追施尿素(CN)、优化追施尿素(CNU)、优化追施尿素硝酸铵溶液(UAN)、优化追施改性尿素硝酸铵溶液(YUL1)和优化追施改性尿素硝酸铵溶液(YUL2)。采用扫描电镜和能谱仪分析相关指标变化,在夏玉米喇叭口期追施氮肥后15d内进行田间原位连续动态观测氨挥发和土壤铵态氮和硝态氮变化,并在玉米成熟期测定产量,计算经济效益。结果表明,改性尿素硝酸铵溶液清澈无杂质,流延后成膜表面光滑、致密,抑制剂在膜表面分布均匀;能谱测试膜层表面磷硫含量增高,证明复合抑制剂与尿素硝酸铵溶液达到有效融合。在同等优化施氮量下:与CNU相比, YUL1氨挥发总量显著降低19.3%, YUL2增加9.6%;与UAN相比, YUL1、YUL2分别显著降低57.3%和42.0%。与其他施氮处理相比, YUL1和YUL2夏玉米季生长中后期0～20 cm土层依然保持相对较高的氮素含量水平,夏玉米收获后土壤硝态氮含量分别比CNU高46.0%和43.4%,比UAN高45.6%和44.7%;180～200cm土层硝态氮含量显著低于其他处理。在保证产量和净收益的同时,改性尿素硝酸铵肥料显著降低了氮素的氨挥发和淋溶损失浓度,尿酶抑制剂含量相对较高的YUL1抑制氨挥发的效果更好,硝化抑制剂含量相对高的YUL2硝态氮向下淋失的风险更小。     

氨氮和亚硝酸氮对南美白对虾的毒性研究

用通常的生物毒性试验方法进行了氨氮和亚硝氨氮对体长5cm南美白对虾的急性毒性试验。在海水pH8.15、水温T＝27℃、盐度S＝20．0‰条件下，求得了两种物质对南美白对虾24h、48h、72h、96h的半死浓度，提出总氨氮和非离子氨氮对南美白对虾的安全浓度分别为2．667mg/L和0．201mg/L，亚硝酸氮的安全浓度为5．551mg/L。氨氮对南美白对虾的毒性强于亚硝酸氮，并提出降低氨氮和亚硝酸氮含量的措施。     

Effect of ammonia on the growth rate and oxygen consumption of juvenile greenlip abalone, Haliotis laevigata Donovan

Juvenile greenlip abalone, Haliotis laevigata, (mean whole weight 4.48±1.9 g, mean±s.d., n=953) were highly sensitive to ammonia as indicated by depressed growth rate and food consumption measured over 2–3 months in bioassay tanks. For growth rate expressed on a whole weight basis, the EC₅ and EC₅₀ values (5 and 50% growth reductions) were 0.041 mg FAN l⁻¹ (Free Ammonia–Nitrogen) and 0.158 mg FAN l⁻¹, respectively. Shell growth rates declined over the entire experimental range (0.006–0.188 mg FAN l⁻¹). At the end of the bioassay, groups of abalone were transferred to respiratory chambers. Oxygen consumption rate increased to a maximum of 188% of control values at 0.235 mg FAN l⁻¹ and decreased slightly at the highest concentration of 0.418 mg FAN l⁻¹.     

Use of treated mine water for rainbow trout (Oncorhynchus mykiss) culture: a production scale assessment

In previous proof-of-concept work, it was shown that the use of treated coal mine water for rainbow trout (Oncorhynchus mykiss) culture in a cage was technically feasible, though only a 50-fish bioassay was grown and no work on production-related issues was conducted. To further advance the use of treated mine water, an under-utilized water resource throughout Mid Appalachia, work was conducted to assess the effects of using treated coal mine water for the intensive production of rainbow trout in a flow-through system. During this study, comprehensive water quality data were collected to supplement fish weight and length data taken during routine monthly sampling events. The 8000 fish grew well in the raceway system over the 9 months of production, where a feed conversion ratio of 1.4 and a condition factor of 5.1 × 10⁻⁴ were measured with stocking and harvest densities of 26.4 and 50.2 kg/m³, respectively. Further, total net production was 3275 kg (7220 lb) with 98.6% survival. Throughout the study, dissolved ion concentrations (Fe, Al, Mg, Ca, and SO₄) often exceeded recommended tolerance limits. Further, elevated ammonia nitrogen concentrations generated from a component of the mine water-treatment process were identified as a potential limiting factor for aquaculture development. However, when the non-ideal effects of high ionic strength and the speciation of dissolved metal–ligand complexes were taken into account, the concentrations of free metal ions were within recommended tolerance limits.     

An experimental study on nitrification biofilm performances using a series reactor system

Total ammonia nitrogen (TAN) concentration is often a key limiting water quality parameter in intensive aquaculture systems. Removing ammonia through biological filtration is thus the first objective in recirculating aquaculture system design. In this study, the performance characteristics of a steady-state nitrification biofilm were explored using a series of reactors. Four nitrification kinetics parameters were estimated using the data collected from the experimental system, including minimum TAN concentration, half saturation constant, maximum TAN removal rate and maximum specific bacterial growth rate. Experimental data showed that a minimum TAN concentration was needed to support a steady-state nitrification biofilm. For the temperature of 27.2°C, the mean minimum TAN concentration was 0.07 mg/l. For a single substrate-limiting factor, the relationship between TAN removal rate (R) and TAN concentration (S) was represented by an empirical equation [R=1859(S−0.07)/(S+1.93)]. The characteristics of nitrite oxidation were also demonstrated by the experiment system. The results of this study will help to better understand the characteristics of nitrification biofilters applied in recirculating aquaculture systems.     

Response of ammonia oxidizing microbes to the stresses of arsenic and copper in two acidic alfisols

Soil pollution by elevated heavy metals exhibits adverse effects on soil microorganisms. Ammonia oxidizing bacteria and ammonia oxidizing archaea perform ammonia oxidative processes in acidic soils. However, influence of heavy metal stress on soil ammonia oxidizers distribution and diversity is inadequately addressed. This study investigated the responses of ammonia oxidizing bacteria and archaea to heavy metals, Cu and As during short-term laboratory experiment. Two different acidic alfisols named as Rayka and Hangzhou spiked with different concentrations of As, Cu and As + Cu were incubated for 10 weeks. Significant reduction in copy numbers of archaeal-16S rRNA, bacterial-16S rRNA and functional amoA genes was observed along elevated heavy metal concentrations. Ammonia oxidizing archaea was found to be more abundant than ammonia oxidizing bacteria in all the heavy metal treatments. The potential nitrification rate significantly decreased with increasing As and Cu concentrations in the two soils examined. Denaturing gradient gel electrophoresis analysis revealed no apparent community shift for ammonia oxidizing archaea even at higher concentrations of As and Cu. Phylogenetic analysis of archaeal amoA gene from 4 clone libraries indicated that all the archaeal amoA sequences were placed within 3 distinct clusters from soil and sediment group 1.1b of Thaumarchaeota. Our results could be useful for the better understanding of the ecological effects of heavy metals on the abundance and diversity of soil ammonia oxidizers.     

Comparison of ammonia and greenhouse gas emissions during the fattening of pigs, kept either on fully slatted floor or on deep litter

Five successive batches of fattening pigs were raised, each during a four month period, on a totally concrete slatted floor in one experimental room and on straw based deep litter in another. The rooms were automatically ventilated to maintain a constant ambient temperature. Available floor space was of 0.75 m² per pig kept on the slatted floor and 1.20 m² per pig kept on the deep litter. With this last system, about 46 kg of straw were supplied per pig throughout a fattening period. The slurry pit was emptied and the litter removed after each batch. Once a month, the emissions of ammonia (NH₃), nitrous oxide (N₂O), methane (CH₄), carbon dioxide (CO₂), and water vapour (H₂O) were measured continuously for 6 consecutive days by infra-red photoacoustic detection.The performance of the animals was not significantly different according to the floor type.Gaseous emissions from pigs raised on the slatted floor and on the deep litter were, respectively, 6.2 and 13.1 g per pig per day for NH₃, 0.54 and 1.11 g per pig per day for N₂O, 16.3 and 16.0 g per pig per day for CH₄, 1.74 and 1.97 kg per pig per day for CO₂ and 2.48 and 3.70 kg per pig per day for H₂O. Except for the CH₄ emissions, all the differences were significant (P < 0.001). Thus, pig fattening on deep litter releases nearly 20% more greenhouse gases than on slatted floor, with 2.64 and 2.24 kg of CO₂-equivalents, respectively (P < 0.001). Whatever the floor type, emissions increased from the beginning to the end of the fattening periods by about 5 times for NH₃, 4 times for N₂O, 3 times for CH₄ and 2 times for CO₂ and H₂O. Correlation coefficients between CO₂-emissions and H₂O, NH₃ and CH₄ emissions were, on average for both floor types, 0.82, 0.77 and 0.74, respectively.Although rearing pigs on straw generally has a good brand image for the consumer, this rearing system produces more pollutant gases than keeping pigs on slatted floors.