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41.
针对2-萘酚生产废水p H值低、色泽深,亚硫酸盐和萘磺酸盐高、COD浓度高的特点,采用酸化脱硫-两级络合萃取-氧化絮凝工艺处理,介绍了专利工艺的流程设计,给出了主要工艺设计参数及投资运行成本。工程运行结果表明,该工艺设计合理、技术成熟、处理效果稳定,2-萘酚生产废水经处理后达到GB 8978—1996《污水综合排放标准》一级排放标准要求;回收的萘磺酸钠固体可返回2-萘酚生产系统套用;反萃取黑液经蒸发浓缩,合成的减水剂产品各项指标达到或超过GB 8076—2008《混凝土外加剂》高效减水剂指标要求。 相似文献
42.
在对拜泉县水资源及利用现状调研的基础上,通过建立指标模型,找出存在的问题及原因,提出了提高水资源利用效率,实现可持续发展的对策建议。 相似文献
43.
Modulation of steroidogenesis by coastal waters and sewage effluents of Hong Kong, China, using the H295R assay 总被引:2,自引:1,他引:1
Gracia T Jones PD Higley EB Hilscherova K Newsted JL Murphy MB Chan AK Zhang X Hecker M Lam PK Wu RS Giesy JP 《Environmental science and pollution research international》2008,15(4):332-343
BACKGROUND, AIM, AND SCOPE: The presence of a variety of pollutants in the aquatic environment that can potentially interfere with the production of sex steroid hormones in wildlife and humans has been of increasing concern. The aim of the present study was to investigate the effects of extracts from Hong Kong marine waters, and influents and effluents from wastewater treatment plants on steroidogenesis using the H295R cell bioassay. After exposing H295R cells to extracts of water, the expression of four steroidogenic genes and the production of three steroid hormones were measured. MATERIALS AND METHODS: Water samples were collected during the summer of 2005 from 24 coastal marine areas and from the influents and effluents of two major waste water treatment plants (WWTPs) in Hong Kong, China. Samples were extracted by solid phase extraction (SPE). H295R cells were exposed for 48 h to dilutions of these extracts. Modulations of the expression of the steroidogenic genes CYP19, CYP17, 3betaHSD2, and CYP11beta2 were determined by measuring mRNA concentrations by real-time polymerase chain reaction (Q-RT-PCR). Production of the hormones progesterone (P), estradiol (E2), and testosterone (T) was quantified using enzyme linked immunosorbent assays (ELISA). RESULTS: Extracts from samples collected in two fish culture areas inhibited growth and proliferation of H295R cells at concentrations greater or equal to 10(5) L equivalents. The cells were exposed to the equivalent concentration of active substances in 10,000 L of water. Thus, to observe the same level of effect as observed in vitro on aquatic organisms would require a bioaccumulation factor of this same magnitude. None of the other 22 marine samples affected growth of the cells at any dilution tested. Twelve of the marine water samples completely inhibited the expression of CYP19 without affecting E2 production; inhibition of CYP17 expression was observed only in one of the samples while expression of CYP11beta2 was induced as much as five- and ninefold after exposure of cells to extracts from two locations. The expression of the progesterone gene 3betaHSD2 was not affected by any of the samples; only one sample induced approximately fourfold the production of E2. Although more than twofold inductions were observed for P and T production, none of these values were statistically significant to conclude effects on the production of these two hormones. While influents from WWTPs did not affect gene expression, an approximately 30% inhibition in the production of E2 and a 40% increase in P occurred for the exposure with influents from the Sha Tin and Stonecutters WWTPs, respectively. Effluents from WWTPs did not affect the production of any of the studied hormones, but a decrement in the expression of the aldosterone gene CYP11beta2 was observed for the Sha Tin WWTP exposure. No direct correlation could be established between gene expression and hormone production. DISCUSSION: Observed cytotoxicity in the two samples from fish culture areas suggest the presence of toxic compounds; chemical analysis is required for their full identification. Although effluents from WWTPs did not affect hormone production, other types of endocrine activity such as receptor-mediated effects cannot be ruled out. Interactions due to the complexity of the samples and alternative steroidogenic pathways might explain the lack of correlation between gene expression and hormone production results. CONCLUSIONS: Changes observed in gene expression and hormone production suggest the presence in Hong Kong coastal waters of pollutants with endocrine disruption potential and others of significant toxic effects. The aromatase and aldosterone genes seem to be the most affected by the exposures, while E2 and P are the hormones with more significant changes observed. Results also suggest effectiveness in the removing of compounds with endocrine activity by the WWTPs studied, as effluent samples did not significantly affect hormone production. The H295R cell showed to be a valuable toll in the battery required for the analysis of endocrine disrupting activities of complex environmental samples. RECOMMENDATIONS AND PERSPECTIVES: Due to the intrinsic complexity of environmental samples, a combination of analytical tools is required to realistically assess environmental conditions, especially in aquatic systems. In the evaluation of endocrine disrupting activities, the H295R cell bioassay should be used in combination with other genomic, biological, chemical, and hydrological tests to establish viable modes for endocrine disruption and identify compounds responsible for the observed effects. 相似文献
44.
Küster A Pohl K Altenburger R 《Environmental science and pollution research international》2007,14(6):377-383
Background, Goals and Scope During the last years the miniaturization of toxicity test systems for rapid and parallel measurements of large quantities
of samples has often been discussed. For unicellular algae as well as for aquatic macrophytes, fluorescence-based miniaturized
test systems have been introduced to analyze photosystem II (PSII) inhibitors. Nevertheless, high-throughput screening should
also guarantee the effect detection of a broad range of toxicants in order to ensure routinely applicable, high-throughput
measuring device experiments which can cover a broad range of toxicants and modes of action others than PSII inhibition. Thus,
the aim of this study was to establish a fast and reproducible measuring system for non-PSII inhibitors for aquatic macrophyte
species to overcome major limitations for use.
Methods A newly developed imaging pulse-amplitude-modulated chlorophyll fluorometer (I-PAM) was applied as an effect detector in short-term
bioassays with the aquatic macrophyte species Lemna minor. This multiwell-plate based measuring device enabled the incubation and measurement of up to 24 samples in parallel. The
chemicals paraquat-dichloride, alizarine and triclosan were chosen as representatives for the toxicant groups of non-PSII
herbicides, polycyclic aromatic hydrocarbons (PAHs) and pharmaceuticals and personal care products (PPCPs), which are often
detected in the aquatic environment. The I-PAM was used (i) to establish and validate the sensitivity of the test system to
the three non-PSII inhibitors, (ii) to compare the test systems with standardized and established biotests for aquatic macrophytes,
and (iii) to define necessary time scales in aquatic macrophyte testing. For validation of the fluorescence-based assay, the
standard growth test with L. minor (ISO/DIS 20079) was performed in parallel for each chemical.
Results The results revealed that fluorescence-based measurements with the I-PAM allow rapid and parallel analysis of large amounts
of aquatic macrophyte samples. The I-PAM enabled the recording of concentration-effect-curves with L. minor samples on a 24-well plate with single measurements. Fluorescence-based concentration-effect-curves could be detected for
all three chemicals after only 1 h of incubation. After 4–5 h incubation time, the maximum inhibition of fluorescence showed
an 80–100% effect for the chemicals tested. The EC50 after 24 h incubation were estimated to be 0.06 mg/L, 0.84 mg/L and 1.69
mg/L for paraquatdichloride, alizarine and triclosan, respectively.
Discussion The results obtained with the I-PAM after 24 h for the herbicide paraquat-dichloride and the polycyclic aromatic hydrocarbon
alizarine were in good accordance with median effective concentrations (EC50s) obtained by the standardized growth test for
L. minor after 7 d incubation (0.09 mg/L and 0.79 mg/L for paraquat-dichloride and alizarine, respectively). Those results were in
accordance with literature findings for the two chemicals. In contrast, fluorescence-based EC50 of the antimicrobial agent
triclosan proved to be two orders of magnitude greater when compared to the standard growth test with 7 d incubation time
(0.026 mg/L) as well as with literature findings.
Conclusion Typically, aquatic macrophyte testing is very time consuming and relies on laborious experimental set-ups. The I-PAM measuring
device enabled fast effect screening for the three chemicals tested. While established test systems for aquatic macrophytes
need incubation times of ≥ 7 d, the I-PAM can detect inhibitory effects much earlier (24 h), even if inhibition of chemicals
is not specifically associated with PSII. Thus, the fluorescence-based bioassay with the I-PAM offers a promising approach
for the miniaturization and high-throughput testing of chemicals with aquatic macrophytes. For the chemical triclosan, however,
the short-term effect prediction with the I-PAM has been shown to be less sensitive than with long-term bioassays, which might
be due to physicochemical substance properties such as lipophilicity.
Recommendations and Perspectives The results of this study show that the I-PAM represents a promising tool for decreasing the incubation times of aquatic macrophyte
toxicity testing to about 24 h as a supplement to existing test batteries. The applicability of this I-PAM bioassay on emergent
and submerged aquatic macrophyte species should be investigated in further studies. Regarding considerations that physicochemical
properties of the tested substances might play an important role in microplate bioassays, the I-PAM bioassay should either
be accompanied by evaluating physicochemical properties modeled from structural information prior to an experimental investigation,
or by intensified chemical analyses to identify and determine nominal concentrations of the toxicants tested. The chemicals
paraquat-dichloride, alizarine and triclosan were chosen as representatives for the toxicant groups of non-PSII herbicides,
PAHs and PPCPs which are often detected in the aquatic environment. Nevertheless, in order to ensure a routinely applicable
measuring device, experiments with a broader range of toxicants and samples of surface and/or waste waters are necessary.
ESS-Submission Editor: Dr. Markus Hecker (MHecker@Entrix.com) 相似文献
45.
Zhang B Hong M Zhang B Zhang XL Zhao YS 《Environmental monitoring and assessment》2007,133(1-3):379-386
Endemic fluorosis was investigated and studied in the west region of the Songnen plain, Northeast China in 2001–2002. The
results showed that the fluorine distribution in aquatic environment was that the fluorine concentrations in the lake water
and unconfined ground water were higher than that in the river water and confined ground water. The lake water (Alkali lake)
is connected with unconfined ground water. In unconfined ground water, from the east and southeast areas to the west and the
northwest areas of the plain, fluorine concentration fluctuated with high and low alternatively. The fluorine in the water
comes from the weathering of rocks and minerals in the mountains and hills around the Songnen Plain. The main influence factors
of the fluorine distribution in aquatic environment are discussed. Unconfined ground water containing high fluorine is used
as drinking water. In this region, the fluorine concentration in drinking water is evidently correlated to the morbidity of
dental and skeletal fluorosis. High fluorine concentration in drinking water has endangered human health. 相似文献
46.
Lemly AD 《Environmental monitoring and assessment》2007,125(1-3):361-375
This paper gives step-by-step instructions for assessing aquatic selenium hazards associated with mining. The procedure was
developed to provide the U.S. Forest Service with a proactive capability for determining the risk of selenium pollution when
it reviews mine permit applications in accordance with the National Environmental Policy Act (NEPA). The procedural framework
is constructed in a decision-tree format in order to guide users through the various steps, provide a logical sequence for
completing individual tasks, and identify key decision points. There are five major components designed to gather information
on operational parameters of the proposed mine as well as key aspects of the physical, chemical, and biological environment
surrounding it — geological assessment, mine operation assessment, hydrological assessment, biological assessment, and hazard
assessment. Validation tests conducted at three mines where selenium pollution has occurred confirmed that the procedure will
accurately predict ecological risks. In each case, it correctly identified and quantified selenium hazard, and indicated the
steps needed to reduce this hazard to an acceptable level. By utilizing the procedure, NEPA workers can be confident in their
ability to understand the risk of aquatic selenium pollution and take appropriate action. Although the procedure was developed
for the Forest Service it should also be useful to other federal land management agencies that conduct NEPA assessments, as
well as regulatory agencies responsible for issuing coal mining permits under the authority of the Surface Mining Control
and Reclamation Act (SMCRA) and associated Section 401 water quality certification under the Clean Water Act. Mining companies
will also benefit from the application of this procedure because priority selenium sources can be identified in relation to
specific mine operating parameters. The procedure will reveal the point(s) at which there is a need to modify operating conditions
to meet environmental quality goals. By recognizing concerns early in the NEPA process, it may be possible for a mining company
to match operational parameters with environmental requirements, thereby increasing the likelihood that the permit application
will be approved. 相似文献
47.
Houghton DC 《Environmental monitoring and assessment》2007,135(1-3):253-264
Over 300,000 caddisfly specimens representing 249 species were collected from nearly 250 sites throughout Minnesota during
2000 and 2001 to determine the effects of human disturbance on the composition of caddisfly trophic functional groups at the
landscape level. Canonical correspondence analysis determined that stream width was the most important variable influencing
functional group composition in regions of the state with relatively low disturbance, and that differences in the caddisfly
fauna between sizes of streams generally followed trends predicted by the river continuum concept. In regions of the state
with moderate disturbance, both stream width and the percentage of disturbed habitat upstream of a site were important variables
influencing functional group composition. In highly disturbed regions, no variables corresponded to changes in the composition
of caddisfly functional groups. Instead, ecosystems were homogeneous: fine-particle filtering collectors dominated in all
sizes of streams. The observed aquatic ecosystem homogenization is attributed mostly to input of fine-particle organic and
inorganic sediment from extensive agriculture. 相似文献
48.
A species of bacteria that is capable of utilizing imazaquin as the sole carbon source was isolated from soil with repeated imazaquin applications, and was identified as Arthrobacter crystallopoietes (designated as strain “WWX-1”). This isolate degrades imazaquin as high as 200 μg ml−1, and the estimated dissipation half-lives increased from 1.51 d for the treatment at 50 μg ml−1 to 4.75 d for 200 μg ml−1. Optimal growth of WWX-1 in mineral salt medium with 50 μg ml−1 imazaquin was obtained at 35 °C and a pH of 5.0. Growth of WWX-1 was also observed in mineral salt medium with the addition of other imidazolinone herbicides such as imazethapyr and imazapyr, but not with different classes of herbicides such as metsulfuron-methyl. Two imazaquin metabolites were detected, and spectral analysis with HPLC–MS, 1H NMR, and IR revealed one metabolite with a molecular weight (MW) of 199 as quinoline-2,3-dicarboxylic anhydride. We propose that A. crystallopoietes (WWX-1) could serve as an efficient biodegradation system for remediation of water and soils that are heavily contaminated with imazaquin or other structurally similar chemicals. 相似文献
49.
Berghahn R Mohr S Feibicke M Meinecke S Sperfeld E 《Environmental science and pollution research international》2007,14(3):190-193
Goal, Scope and Background One of the advantages of long-term mesocosm experiments as compared to short-term standard toxicity tests in the laboratory
is the potential for detecting secondary effects due to the interaction of species and recovery with biomass of macrophytes
being an important endpoint. However, generating biomass data by harvesting is often laborious, time-consuming, costly and
restricted to the end of the experiment. Moreover, valuable information may get lost, in particular in single application
studies, since maximal primary effects and secondary effects or recovery occur per se at different times. Potamogeton natans was used as an example in order to test whether number and area of floating leaves can be reliably measured and be used as
intermediate and final endpoints in mesocosm effect studies.
Methods Digital photos, which were taken of the water surface in the course of an indoor pond mesocosm study on herbicide effects,
were subjected to image analysis. The results were compared to wet weight and ash-free dry weight of Potamogeton at the end of the herbicide study.
Results and Discussion Both number and area of floating leaves indicated the same herbicide effects as wet weight and ash-free dry weight of Potamogeton. Error introduced by the different work steps is small and can be further minimised by a number of method improvements.
Recommendations and Perspectives In indoor mesocosm studies, errors due to the perspective adjustment may be circumvented by taking the photos perpendicular
to the water surface. Correction for lens aberration, identical light conditions and the use of fluorescence images are considered
promising. Field applications are proposed. 相似文献
50.
Sustainable development planning must be based on environmental and biophysical baseline indices that effectively define comparative development potential and environmental constraints. As such, indices must define the comparative advantage of the natural resource base and measure the fundamental capacity to sustain production rates of natural resource goods and services used to create societal well being. Complex biophysical and socioeconomic characteristics affect the identification and selection of sustainable development strategies. When derived from effective baseline indicators, indices may be used to define the spatial and temporal distribution of economically viable production opportunities and may be expressed in derived indices that realistically describe basic production opportunities and guide the selection of feasible, long-term development strategies. Specifically, representative indices are critical in the identification of development goals and realistic objectives and can be used to evaluate, select and implement sustainable development strategies and plans. It is stressed that the relevancy and effectiveness of public policies depend on the identification of representative evaluation models and baseline indices to define development strategies that are both environmentally sustainable and economically viable. In this context, the role of baseline indicators that define natural resource production capacities is discussed. This includes potential resource uses, derived benefits and their economic and environmental impacts. Key thematic indicators are suggested that may be especially useful in identifying development alternatives and impacts. This suggested that clearly defined environmental pollution limits or impact standards be used to define public risk tolerance limits and carrying capacity constraints. It is argued that these measures may be more effective in directing policy choices than economic valuation of non market goods and services that represent environmental externalities associated with resource exploitation options and economic development strategies. To this end, examples of thematic indicators and derived indices are introduced that may prove effective in resource assessment, economic evaluation and strategic development planning. 相似文献