水中有机磷杀虫剂的生物降解性和对微生物的影响

通过对三种有机磷杀虫剂(杀螟松、甲基1605、乐果)废水生物处理模拟试验和微生物呼吸耗氧特性试验,表明三者均可被微生物降解;三者对未驯化活性污泥微生物的生长有一定抑制作用,但对驯化培养后的微生物菌群的生长、代谢有促进作用。有机磷杀虫剂的浓度,pH值,菌种培养条件等因素对微生物菌群的生态演替和有机物的去除效果都能产生影响。     

石灰石湿式烟气脱硫工艺中添加剂的研究

石灰石湿式烟气脱硫工艺中使用添加剂 ,可提高脱硫率和石灰石利用率等。本研究应用旋流板塔处理模拟烟气 ,系统研究了几种无机及有机添加剂对湿式石灰石脱硫过程的影响 ,选出了适宜的添加剂及其添加浓度 ;得到了脱硫率与主要操作参数之间的关系 ,为工业设计和操作提供了参考数据。并对添加剂强化过程机理进行了讨论     

甲醛污染水的生物学效应

本实验研究甲醛污染的淡水和海水对细菌、植物和动物的生物学效应。甲醛的毒害作用是显著的。含0.036—0.36%甲醛的纯水能引起鼠伤寒沙门氏菌组氨酸缺陷型菌株TA100的回复突变,含0.036%、0.0036%、0.00036%甲醛的水溶液行短期(6h)处理紫露草花枝基部,24h休复后发现四分体细胞中微核率显著增高。含0.0018%、0.0036%、0.018%甲醛的水处理蚕豆根,引起根尖细胞中微核率明显增高。0.00018%甲醛的海水使马粪海胆幼虫在45min内死亡。0.0072%甲醛的海水使该幼虫在2min内死亡。0.0072%甲醛的海水能使贻贝担轮幼虫在5min内死亡。0.00018%甲醛的海水使贻贝幼虫在48h内死亡。0.000108%甲醛的海水使马粪海胆幼虫在72h内死亡。实验证明蚕豆根尖细胞和海胆幼虫是良好的监测淡水与海水污染的材料,甲醛能引起DNA中碱基对置换突变。甲醛在海水中产生增效效应。     

我国四个港湾疏浚物石油污染

文中叙述了１９８８￣１９９０年间，我国４个港湾－大连湾、天津港、深圳湾及珠江河段各疏浚区疏浚物中油类污染调查及分布状况。文中介绍了站位布设原则，样品采集、样品处理、分析测试方法。进行了沾污疏浚物油类出溶出实验，认为油类溶出实验是估价疏浚物油类污染的程度的重要手段。讨论了４港湾疏浚物油类污染水平。大连湾海域疏浚物石油污染明显，珠江河段，深圳湾及天津港疏浚物稍受影响，基本上是清洁的。     

转化纤维素资源生成酒精的研究

研究了高温厌气的热纤梭菌(Clostridium thermocellum)转化纤维素物质直接生成酒精的过程,发酵产物除酒精外,还有乙酸、少量乳酸、H_2、CO_2和还原糖,还原糖的主要成份为木糖,纤维二糖和葡萄糖、诱变菌转化纤维素的能力与野生菌相比有明显提高,能发酵细小纤维、稻草和凤眼莲,酒精最大浓度可分别达4.0,3.2和9.3g/L。     

Optimum nitrogen use and reduced nitrogen loss for production of rice and wheat in the Yangtse Delta region

A long-term field and lysimeter experiment under different amount of fertilizer-N application was conducted to explore the optimal N application rates for a high productive rice-wheat system and less N leaching loss in the Yangtse Delta region. In this region excessive applications of N fertilizer for the rice-wheat production has resulted in reduced N recovery rates and environment pollution. Initial results of the field experiments showed that the optimal N application rate increased with the yield. On the two major paddy soils (Hydromorphic paddy soil and Gleyed paddy soil) of the region, the optimal N application rate was 225-270 kg N hm(-2) for rice and 180-225 kg N hm(-2) for wheat, separately. This has resulted in the highest number of effective ears and Spikelets per unit area, and hence high yield. Nitrogen leaching in the form of NO(3-)-N occurs mainly in the wheat-growing season and in the ponding and seedling periods of the paddy field. Its concentration in the leachate increased with the N application rate in the lysimeter experiment. When the application rate reached 225 kg N hm(-2), the concentration rose to 5.4-21.3 mgN l(-1) in the leachate during the wheat-growing season. About 60% of the leachate samples determined contained NO(3-)-N beyond the criterion (NO(3-)-N 10 mg l(-1)) for N pollution. In the field experiment, when the N application rate was in the range of 270-315 kg hm(-2), the NO(3-)-N concentration in the leachate during the wheat-growing season ranged from 1.9 to 11.0 mg l(-1). About 20% of the leachate samples reached close to, and 10% exceeded, the criterion for N pollution. Long-term accumulation of NO(3-)-N from leaching will no doubt constitute a potential risk of N contamination of the groundwater in the Yangtse Delta Region.     

Optimum Nitrogen Use and Reduced Nitrogen Loss for Production of Rice and Wheat in the Yangtse Delta Region

A long-term field and lysimeter experiment under different amount of fertilizer-N application was conducted to explore the optimal N application rates for a high productive rice–wheat system and less N leaching loss in the Yangtse Delta region. In this region excessive applications of N fertilizer for the rice–wheat production has resulted in reduced N recovery rates and environment pollution. Initial results of the field experiments showed that the optimal N application rate increased with the yield. On the two major paddy soils (Hydromorphic paddy soil and Gleyed paddy soil) of the region, the optimal N application rate was 225–270 kg N hm^–2 for rice and 180–225 kg N hm^–2 for wheat, separately. This has resulted in the highest number of effective ears and Spikelets per unit area, and hence high yield. Nitrogen leaching in the form of NO ₃ ^– -N occurs mainly in the wheat-growing season and in the ponding and seedling periods of the paddy field. Its concentration in the leachate increased with the N application rate in the lysimeter experiment. When the application rate reached 225 kg N hm^–2, the concentration rose to 5.4–21.3 mgN l^–1 in the leachate during the wheat-growing season. About 60% of the leachate samples determined contained NO ₃ ^– -N beyond the criterion (NO ₃ ^– -N 10 mg l^–1) for N pollution. In the field experiment, when the N application rate was in the range of 270–315 kg hm^–2, the NO ₃ ^– -N concentration in the leachate during the wheat-growing season ranged from 1.9 to 11.0 mg l^–1. About 20% of the leachate samples reached close to, and 10% exceeded, the criterion for N pollution. Long-term accumulation of NO ₃ ^– -N from leaching will no doubt constitute a potential risk of N contamination of the groundwater in the Yangtse Delta Region.     

城市生活垃圾堆肥及垃圾专用肥对柑桔增产效应

城市生活垃圾堆肥及垃圾堆肥配制的专用肥对柑桔的肥效实验结果表明，垃圾堆肥作为基肥使用比常规施肥能使柑桔增产１２．４％－１４．５％，比空白对照增产７４．７％，施用垃圾专用肥的柑桔产量比常规施肥增产４．２％－５０．３％，比空白对照增产５８．４％－１２９．０％。施垃圾肥柑桔的营养成份（如维Ｃ，还原糖等）和常规施肥没有明显差异，也未发现重金属对桔子的污染。     

Bioaccumulation and elimination of avermectin B1a in the earthworms (Eisenia fetida)

The acute toxicity, bioaccumulation, and elimination of avermectin B1a (AVM B1a) in earthworm (Eisenia fetida) were investigated in different exposure systems. The LC50 of AVM B1a on earthworms were 24.1 mg/kg and 17.1 mg/kg, respectively, for 7 and 14 days in artificial soil. The LC50 tested by the filter paper for 2 days was 4.63 microg/cm2. The earthworms were cultivated in artificial soil containing 0.6 mg/kg and 3.0 mg/kg AVM B1a, respectively for bioaccumulation experiments. The AVM B1a residues in earthworms were determined with HPLC-fluorescence method. The results showed that AVM B1a was taken up from the concentrated artificial soil by the earthworms and the steady-state levels were reached after 9-18 days of exposure. On the 18th day, the final concentrations of AVM B1a in the earthworms treated with two different dosages were 107 ng/g and 165 ng/g, respectively; there were not significantly accumulation. About 80.0% and 94.8% of the accumulated AVM B1a were eliminated respectively in two groups within 1 day after they were exposed to AVM B1a-free soil, but a trace amount of AVM B1a was found for a relative long time in earthworms.     

Phytoremediation of petroleum hydrocarbons in tropical coastal soils II. microbial response to plant roots and contaminant

GOAL, SCOPE AND BACKGROUND: The goal of this study was to understand the interaction between plants and microorganisms during petroleum-hydrocarbon bioremediation in Pacific Islands coastal soils. Total bacteria and hydrocarbon-degrading microorganisms population dyanamics were examined in the rhizospheres of tropical trees and shrubs, which were evaluated for their phytoremediation potential in a greenhouse experiment. The respective and combined effects of plant roots and diesel contaminant on the microbial populations were determined in relation to diesel fuel depletion. An increase in the grading populations size of the hydrocarbon-degrading populations of microbes, elicited by rhizodeposition, is generally regarded as conducive to an enhanced degradation of petroleum hydrocarbon pollutants in vegetated soil. METHODS: The soil was a coastal sandy loam (pH 7.8) which was artificially contaminated with 10 g of No. 2 diesel fuel/kg soil or left uncontaminated. The pots were irrigated with fertilizer and 1% NaCl. The enumerations were carried out in the contaminated and uncontaminated rhizospheres of three trees, kiawe (Prosopis pallida), milo (Thespesia populnea), and kou (Cordia subcordata) and three shrubs, beach naupaka (Scaevola sericea), false sandalwood (Myoporum sandwicense), and oleander (Nerium oleander). Unplanted control soils were included in the experiment. Total bacteria and phenanthrene-degrading bacteria were enumerated on plates. Diesel- and pristane-degrading microorganisms were enumerated by the most-probable-number technique in tissue-culture plates. RESULTS AND DISCUSSION: All four types of microorganisms responded to the rhizosphere of the 6 plants in uncontaminated soil and to the diesel contaminant in unplanted soil. In contaminated rhizospheres, no effect of the plant on the hydrocarbon-degrader numbers was visible. Total bacteria responded more to the plant roots than to the contaminant. The phenanthrene-degrading bacteria and pristane-degrading microorganisms were more influenced by the contaminant than by the plants. The diesel-degrading microorganisms were equally stimulated by the plants and the contaminant. The numbers of hydrocarbon degraders were similar in the contaminated rhizospheres of the three effective plants (kiawe, kou, and milo) and in those of the three ineffective shrubs. CONCLUSION: The results suggest the quality of the rhizodeposition is plant-dependent and governs the type of diesel-degrader populations that will be enhanced by a given plant. RECOMMENDATIONS AND OUTLOOK: In the proposed phytoremediation-benefit model plant roots maintain high levels of hydrocaron degraders in uncontaminated soil. When the root enters a contaminated zone of soil, those hydrocarbon degraders that prefer the contaminant would switch to the contaminant as a carbon source, effectively removing the hydrocarbons. If the root exudates and the contaminant are equally attractive to the hydrocarbon degraders, the contaminant degradaton would be less effective.