Determination of residues of malachite green in aquatic animals

Residues of malachite green (MG) were extracted from homogenized animal tissues with a mixture of McIlvaine buffer (pH 3.0)-acetonitrile, and purified over an aromatic sulfonic acid solid-phase extraction column followed by HPLC or LC-ESI-MS-MS analysis. Ascorbic acid and N,N,N',N'-tetramethyl-1,4-phenylenediamine dihydrochloride were added to reduce de-methylation of the dye. Responses were recorded at 620 nm (HPLC) or by multiple-reaction-monitoring (LC-MS-MS) after post-column oxidation using PbO(2). MG and its primary metabolite leuco-malachite green (LMG) were successfully determined at 2.5-2000 microg/kg in catfish, eel, rainbow trout, salmon, tropical prawns and turbot, with a limit of detection at 1 microg/kg (HPLC) and 0.2 microg/kg (LC-MS-MS) for both MG and LMG. Recoveries for LMG were between 86+/-15% (prawn) and 105+/-14% (eel). Freeze-thawing cycles, and storage at 4 degrees C and -20 degrees C affected the recovery of both MG and LMG. Analyses of eel, trout and (processed) salmon field samples collected at local retailers, fish-market and -shops demonstrated trace levels of MG-residues.     

A confirmatory analysis of malachite green residues in rainbow trout with liquid chromatography-electrospray tandem mass spectrometry

A quantitative liquid chromatography-tandem mass spectrometric (LC-MS/MS) method has been developed for the determination of malachite green (MG) and its metabolite leucomalachite green (LMG) in fish. Residues were extracted with an acetonitrile-acetate buffer and purified using the automated solid-phase extraction (ASPEC). Residues were analyzed with a reversed-phase LC-MS/MS using a positive-ion electrospray ionisation (ESI). Isotope-labelled leucomalachite green (LMG-D5) was used as an internal standard for the quantification of LMG residues. The related dye, brilliant green (BG) was used as an instrumental standard. Identification and quantification of analytes were based on the ion transitions monitored by multiple reaction monitoring (MRM). The decision limit (CCalpha) for MG and LMG was 0.13 and 0.16 microgkg(-1). The respective detection capabilities (CCbeta) were 0.22 and 0.27 microgkg(-1). The absolute recovery (repeatability SD(r)) was in the range of 58-65% (7.8-11.2%) for MG and 59-68% (9.7-16.9%) for LMG. LMG was quantified also based on the internal standard, giving a recovery (repeatability SD(r)) of 103-110% (4.8-9.3%). The method was further evaluated by analyzing a total of 34 fish residue monitoring samples, of which eight samples were found to be non-compliant containing low residues of LMG.     

Determination of malachite green and leucomalachite green in edible goldfish muscle by liquid chromatography-ion trap mass spectrometry

A liquid chromatography-ion trap mass spectrometry method with three "time segments" has been developed to determine malachite green (MG) and its major metabolite, leucomalachite green (LMG) in edible goldfish muscle. By using the optimized "time segments", MG and LMG as well as the internal standard atrazine-d(5) were analyzed with good sensitivity with positive ESI-MS in a single run. The homogenized fish muscle tissues were extracted with a solution of perchloric acid and acetonitrile, followed by partitioning with dichloromethane. Strata-x polymeric solid-phase extraction column was used for the clean-up process. The determination of MG and LMG was achieved by using a reversed-phase HPLC gradient program coupled with MS/MS in multiple-reaction-monitoring mode. Matrix calibration curves were linear over the ranges of 5-500 ng/ml for MG and 1-100 ng/ml for LMG. Recoveries of the fish tissue extraction at three spiked levels (2, 10 and 30 ng/g for MG as well as 0.4, 2 and 6 ng/g for LMG) were better than 71% and 89%, respectively. Relative standard derivations from six determinations were less than 8%. The method detection limits were 0.13 ng/g for MG and 0.06 ng/g for LMG.     

Simultaneous determination of malachite green and its metabolite leucomalachite green in eel plasma using post-column oxidation

A rapid HPLC method with solid-phase extraction (SPE) clean-up for malachite green (MG) and leucomalachite green (LMG) in eel plasma was developed. MG and LMG were extracted with a buffered methanolic solution. The extract was subjected to aromatic sulphonic acid SPE. MG and LMG were eluted from the SPE column with methanol after a treatment with ammonia gas. The reconstituted eluate was analyzed on a Chromspher B column with acetonitrile-ion-pair buffer (ph 4.0) (6:4, v/v) as the mobile phase and detection at 610 nm after post column oxidation with PbO₂. The average recoveries for MG and LMG over the linear range of applicability (20–2500 ng/ml) were 82±1% and 83±1%, respectively. The limits of quantification were 5.0 μg/1 for MG and 0.9 μ/1 for LMG.     

Analysis of mutations and bone marrow micronuclei in Big Blue rats fed leucomalachite green

Leucomalachite green (LMG) is the major metabolite of malachite green (MG), a triphenylmethane dye that has been used widely as an antifungal agent in the fish industry. Concern over MG and LMG is due to the potential for consumer exposure, suggestive evidence of tumor promotion in rodent liver, and suspicion of carcinogenicity based on structure-activity relationships. In order to evaluate the risks associated with exposure to LMG, female Big Blue rats were fed up to 543 ppm LMG; groups of these rats were killed after 4, 16, or 32 weeks of exposure and evaluated for genotoxicity. We previously reported that this treatment resulted in a dose-dependent induction of liver DNA adducts, and that the liver lacI mutant frequency (MF) was increased, but only in rats fed 543 ppm LMG for 16 weeks. In the present study, we report the results from lymphocyte Hprt mutant assays and bone marrow micronucleus assays performed on these same rats. In addition, we have determined the types of lacI mutations induced in the rats fed 543 ppm LMG for 16 weeks and the rats fed control diet. No significant increases in the frequency of micronuclei or Hprt mutants were observed for any of the doses or time points assayed. Molecular analysis of 80 liver lacI mutants from rats fed 543 ppm LMG for 16 weeks revealed that 21% (17/80) were clonal in origin and that most (55/63) of the independent mutations were base pair substitutions. The predominant type of mutation was G:C --> A:T transition (31/63) and the majority (68%) of these involved CpG sites. When corrected for clonality, the 16-week lacI mutation frequency (36 +/- 10) x 10(-6) in treated rats was not significantly different from the clonally corrected control frequency (17 +/- 9 x 10(-6); P = 0.06). Furthermore, the lacI mutational spectrum in treated rats was not significantly different from that found for control rats (P = 0.09). Taken together, these data indicate that the DNA adducts produced by LMG in female rats do not result in detectable levels of genotoxicity, and that the increase in lacI MF observed previously in the liver of treated rats may be due to the disproportionate expansion of spontaneous lacI mutations.     

浸泡条件下孔雀石绿及其代谢物隐色孔雀石绿在斑点叉尾 组织中分布及消除规律研究

以7 mg/L的孔雀石绿浸泡斑点叉尾 苗种5min后将其饲养于池塘的网箱中, 研究了在养殖模式下孔雀石绿及其代谢物隐色孔雀石绿在斑点叉尾 苗种各组织中的分布及消除规律。采用高效液相色谱串联质谱法(HPLC-MS/MS)分析孔雀石绿及其代谢物隐色孔雀石绿在斑点叉尾 血液、肌肉、皮肤、肝脏、肾脏组织中的浓度水平。采用药代动力学分析软件3p97对血药浓度时间数据进行分析。结果表明, 孔雀石绿和隐色孔雀石绿血药浓度时间曲线符合有吸收二室模型, 动力学方程分别为: C孔雀石绿 =683.063 e-0.248 t+ 11.176 e-0.006 t- 694.239e-0.333 t, C隐色孔雀石绿 =757.240 e-0.222 t + 14.474 e-0.007 t 771.714 e-0.382 t。血液中孔雀石绿和隐色孔雀石绿达峰时间Tpeak分别为3.480和3.623h, 峰浓度值Cmax分别为81.560和159.619 ng/mL, 表观分布容积Vd/F分别为37.689和21.125 L/kg, 分布相的一级速率常数分别为0.248和0.222/h, 消除相的一级速率常数分别为 0.006和0.007/h, 吸收半衰期T(1/2) 分别为2.794和3.124h, 消除半衰期T(1/2)分别为113.068和105.841h, 中央室向周边室转运的一级速率常数K12分别为0.020和0.015/h, 周边室向中央室转运的一级速率常数K21分别为0.159和0.121/h, 药-时曲线下面积AUC分别为2493.944和3601.863 ngh/mL。肌肉、皮肤、肝脏和肾脏组织中孔雀石绿和隐色孔雀石绿浓度水平的结果表明, 孔雀石绿在斑点叉尾 4种组织中浓度由高到低的顺序是皮肤肌肉肾脏肝脏, 其中斑点叉尾 皮肤组织易蓄积孔雀石绿, 其残留时间最长, 肝脏组织由于对孔雀石绿有极强的代谢转化功能而浓度较低。孔雀石绿在肌肉、皮肤、肝脏和肾脏组织中的消除方程分别为C=5.570 e-0.009t、C=6.302 e-0.007t、C=4.791 e-0.006t和C=4.591 e-0.002t, 相关系数r20.773, 消除半衰期T1/2肌肉、皮肤、肝脏和肾脏分别为3.2、4.1、4.8和14.4d。肌肉、皮肤、肝脏和肾脏组织中孔雀石绿分别在45、60、30和60d才未被检测到; 隐色孔雀石绿在斑点叉尾 4种组织中浓度由高到低的顺序是肝脏皮肤肌肉肾脏, 残留时间最长的组织也是皮肤组织。隐色孔雀石绿在肌肉、皮肤、肝脏和肾脏组织中的消除方程分别为C=6.491 e-0.004t、C=6.958 e-0.003t、C=6.722 e-0.007t和C=6.162 e-0.002t, 相关系数r20.673, 消除半衰期T1/2肌肉、皮肤、肝脏和肾脏分别为7.2、9.6、4.1和14.4d。肌肉、皮肤、肝脏和肾脏组织中隐色孔雀石绿分别在90、90、60和90d才未被检出。试验期间(2011年5月17日至7月15日)平均水温为26.4℃, 孔雀石绿和隐色孔雀石绿90d后在各组织中才未检测到, 因此, 使用7 mg/L孔雀石绿浸泡2龄斑点叉尾 苗种孔雀石绿及其代谢物隐色孔雀石绿至少应经过2376℃d后才能消除。       

Simultaneous determination of malachite green, gentian violet and their leuco metabolites in catfish or trout tissue by high-performance liquid chromatography with visible detection

A sensitive analytical procedure for the determination of residues of leucomalachite green (LMG)-malachite green (MG) and leucogentian violet (LGV)-gentian violet (GV) in catfish or trout tissue is presented. Frozen (−20°C) fish fillets were cut into small pieces and blended in a Waring blender. A 20-g amount of homogenized fish tissue was extracted with acetonitrile-buffer, partitioned against methylene chloride, and cleaned up on tandem neutral alumina and propylsulfonic acid cation-exchange solid-phase extraction cartridges. Samples of 100 μl (0.8 g equiv.) were chromatographed isocratically in 10 min using an acetonitrile-buffer mobile phase on a short-chain deactivated (SCD) reversed-phase column (250×4.6 mm I.D.) in-line with a post-column PbO₂ oxidation reactor. The PbO₂ post-column reactor efficiently oxidized LMG to the chromatic MG, and LGV to the chromatic GV permitting visible detection at 588 nm for all four compounds. Linearity was demonstrated with standards over the range of 0.5–50 ng per injection. Recoveries of LMG, MG, LGV and GV from catfish tissues fortified at 10 ng/g were 75.4±3.0, 61.3±4.1, 72.6±3.7 and 87.9±2.5, respectively, while trout tissues fortified at 10 ng/g yielded recoveries of 82.6±2.3, 48.6±1.8, 72.1±2.1 and 83.8±4.6 (mean±S.D., N=4), respectively.     

Malachite green pre-enrichment medium for improved salmonella isolation from heavily contaminated samples

V an S chothorst , M. & R enaud , A. M. 1985. Malachite green pre-enrichment for improved salmonella isolation from heavily contaminated samples. Journal of Applied Bacteriology 59 , 223–230.
Large numbers of competitive bacteria may hinder the isolation of salmonellas from food and environmental samples when a pre-enrichment method is used. The addition of 0.1 g/1 of malachite green (MG) to buffered peptone water (BPW) inhibited the multiplication of Gram-positive bacteria. Brilliant green had a similar effect but only when the normal recommended concentration of 0.02 g/1 was raised to 0.05 g/1. Pure strains of salmonellas were inhibited by MG in BPW, but addition of non fat dried milk (NFDM) (5 g/1 or more) counteracted this effect. MG did not affect the recovery of salmonellas injured by heat, freezing, low water activity or acidity in BPW with NFDM. It was concluded that addition of MG to BPW may improve the possibility of isolating salmonellas from heavily contaminated materials by limiting the competitive growth of Gram-positive bacteria and the subsequent lowering of the pH of the broth.     

Malachite green pre-enrichment medium for improved salmonella isolation from heavily contaminated samples

Large numbers of competitive bacteria may hinder the isolation of salmonellas from food and environmental samples when a pre-enrichment method is used. The addition of 0.1 g/l of malachite green (MG) to buffered peptone water (BPW) inhibited the multiplication of Gram-positive bacteria. Brilliant green had a similar effect but only when the normal recommended concentration of 0.02 g/l was raised to 0.05 g/l. Pure strains of salmonellas were inhibited by MG in BPW, but addition of non fat dried milk (NFDM) (5 g/l or more) counteracted this effect. MG did not affect the recovery of salmonellas injured by heat, freezing, low water activity or acidity in BPW with NFDM. It was concluded that addition of MG to BPW may improve the possibility of isolating salmonellas from heavily contaminated materials by limiting the competitive growth of Gram-positive bacteria and the subsequent lowering of the pH of the broth.     

Biodegradation of malachite green by Ochrobactrum sp.

This study presents the biodegradation of malachite green (MG), a triphenylmethane dye, using a novel microorganism isolated from textile effluent contaminated environment. The organism responsible for degradation was identified as Ochrobactrum sp JN214485 by 16S rRNA analysis. The effect of operating parameters such as temperature, pH, immobilized bead loading, and initial dye concentration on % degradation was studied, and their optimal values were found to be 30 °C, 6, 20 g/L and 100 mg/L, respectively. The analysis showed that the extracellular enzymes were responsible for the degradation. The biodegradation of MG was confirmed by UV–visible spectroscopic and FTIR analysis. The phytotoxicity test concluded that the degradation products were less toxic compared to MG. The kinetics of biodegradation was studied and the activation energy was found to be 10.65 kcal/mol.     

Confirmation of malachite green, gentian violet and their leuco analogs in catfish and trout tissue by high-performance liquid chromatography utilizing electrochemistry with ultraviolet-visible diode array detection and fluorescence detection

A sensitive analytical procedure for the confirmation of residues of malachite green (MG), gentian violet (GV) and their leuco analogs (LMG and LGV) in catfish and trout tissue at 10 ng/g is described. Frozen (−20°C) fish fillets were cut into small pieces and homogenized in Waring blendors. The compounds of interest were extracted from 20-g amounts of homogenized fish tissue with acetonitrile-buffer, partitioned against methylene chloride, and isolated with tandem neutral alumina and propylsulfonic acid cation-exchange solid-phase extraction cartridges. Samples of 100 μl (0.8 g equiv.) were chromatographed isocratically in 10 min using an acetonitrile-buffer mobile phase on a short-chain deactivated (SCD) reversed-phase column (150×4.6 mm I.D.) in-line with a post-column oxidation coulometric electrochemical cell (EC), a UV-Vis diode array detector and a fluorescence detector.     

Biodegradation of malachite green by Micrococcus sp. strain BD15: Biodegradation pathway and enzyme analysis

Malachite green (MG) is extensively used, although it is carcinogenic and mutagenic. In our previous study, the novel Micrococcus sp. strain BD15 was observed to efficiently decolorize MG. The aims of this study were to identify the metabolites after degradation by this strain and to identify the enzymes involved in degradation. UV–Visible, FTIR, GC–MS and LC–MS analyses were performed to determine the degradation products, and our results indicate that the intermediates of MG degradation include 4-(Dimethylamino)benzophenone, Michler's ketone, 4-(methylamino)benzophenone, 4-aminobenzophenone, 4-methylaminobenzoic acid, 4-hydroxyl-N,N-dimethylaniline, N,N-dimethylaniline, hydroxyl-4-(dimethylamino)benzophenone and 4-hydroxyl-aniline. In addition, enzyme analysis revealed that laccase and NADH-DCIP reductase are involved in the degradation of MG. To our knowledge, this is the first study of the detailed biodegradation pathway of MG by Micrococcus sp. strains.     

Functionalization of sawdust with monosodium glutamate for enhancing its malachite green removal capacity

In this paper, waste sawdust was functionalized by monosodium glutamate for improving its cationic sorption capacity. The functionalized sawdust (FS) and crude sawdust (CS) were compared for their malachite green (MG) sorption behaviors with a batch system. The effects of various experimental parameters (e.g. initial pH, sorbent dose, dye concentration, contact time, and temperature etc.) were investigated and the sorption kinetic and thermodynamic characteristics were understood. The MG removal ratios on FS and on CS increased with increasing initial pH and came up to the maximum value beyond pH 6 for FS and pH 8 for CS, respectively. The ratio of sorbed MG kept above 95% for 250 mg/l of MG solution when 2.0 g/l or more of FS was used. The MG removal percentage decreased more on CS than on FS with increasing initial MG concentration. The isothermal data of MG sorbed on FS and on CS followed the Langmuir model. By functionalizing, the sorption capacity (Q(m)) of sawdust for MG was increased from 85.47 to 196.08 mg/g and the sorption equilibrium time of MG was shortened from 23 to 4.5 h. The MG sorption processes on FS and on CS followed the pseudo-second-order rate kinetics. The sorptions of MG on FS and on CS were spontaneous and exothermic processes and lower temperatures were favorable for the sorption processes.     

Malachite green induces cardiovascular defects in developing zebrafish (Danio rerio) embryos by blocking VEGFR-2 signaling

Malachite green (MG) is a triphenyl methane dye used in various fields that demonstrates high toxicity to bacteria and mammalian cells. When bud stage zebrafish embryos were treated with MG at 125, 150, and 175 ppb for 14 h, the development of trunk including intersomitic vessels was inhibited in MG-treated flk-1-GFP transgenic embyos. MG clearly induced whole growth retardation. MG induced severe cell death in trunk intersomite region of zebrafish embryos and in human vascular endothelial cells in a dose-dependent manner. MG inhibited heart rates and cardiac looping. MG attenuated whole blood formation and inhibited vascular endothelial growth factor (VEGF)-induced receptor (R)-2 phosphorylation in vascular endothelial cells. In conclusion, MG significantly alters the cardiovascular development causing growth retardation in zebrafish through the blocking VEGFR-2 activation in early cardiovascular development. It suggests that MG may be an environmental toxic agent with the potential to induce embryonic cardiovascular defects in vertebrates.     

Thermodynamics of ligand binding to a heterogeneous RNA population in the malachite green aptamer

The malachite green aptamer binds two closely related ligands, malachite green (MG) and tetramethylrosamine (TMR), with nearly equal affinity. The MG ligand consists of three phenyl rings emanating from a central carbon, while TMR has two of the three rings connected by an ether linkage. The binding pockets for MG and TMR in the aptamer, known from high-resolution structures, differ only in the conformation of a few nucleotides. Herein, we applied isothermal titration calorimetry (ITC) to compare the thermodynamics of binding of MG and TMR to the aptamer. Binding heat capacities were obtained from ITC titrations over the temperature range of 15-60 °C. Two temperature regimes were found for MG binding: one from 15 to 45 °C where MG bound with a large negative heat capacity and an apparent stoichiometry (n) of ~0.4 and another from 50 to 60 °C where MG bound with a positive heat capacity and an n of ~1.1. The binding of TMR, on the other hand, revealed only one temperature regime for binding, with a more modest negative heat capacity and an n of ~1.2. The large difference in heat capacity between the two ligands suggests that significantly more conformational rearrangement occurs upon the binding of MG than that of TMR, which is consistent with differences in solvent accessible surface area calculated for available ligand-bound structures. Lastly, we note that the binding stoichiometry of MG was improved not only by an increase in the temperature but also by a decrease in the concentration of Mg(2+) or an increase in the time between ITC injections. These studies suggest that binding of a dynamical ligand to a functional RNA requires the RNA itself to have significant dynamics.     

Utilization of unconventional lignocellulosic waste biomass for the biosorption of toxic triphenylmethane dye malachite green from aqueous solution

Biosorption potential of novel lignocellulosic biosorbents Musa sp. peel (MSP) and Aegle marmelos shell (AMS) was investigated for the removal of toxic triphenylmethane dye malachite green (MG), from aqueous solution. Batch experiments were performed to study the biosorption characteristics of malachite green onto lignocellulosic biosorbents as a function of initial solution pH, initial malachite green concentration, biosorbents dosage, and temperature. Biosorption equilibrium data were fitted to two and three parameters isotherm models. Three-parameter isotherm models better described the equilibrium data. The maximum monolayer biosorption capacities obtained using the Langmuir model for MG removal using MSP and AMS was 47.61 and 18.86 mg/g, respectively. The biosorption kinetic data were analyzed using pseudo-first-order, pseudo-second-order, Elovich and intraparticle diffusion models. The pseudo-second-order kinetic model best fitted the experimental data, indicated the MG biosorption using MSP and AMS as chemisorption process. The removal of MG using AMS was found as highly dependent on the process temperature. The removal efficiency of MG showed declined effect at the higher concentrations of NaCl and CaCl₂. The regeneration test of the biosorbents toward MG removal was successful up to three cycles.     

Biodegradation of leuco derivatives of triphenylmethane dyes by <Emphasis Type="Italic">Sphingomonas</Emphasis> sp. CM9

A leuco derivatives of triphenylmethane dyes degrading bacterium, strain CM9, was isolated from an aquafarm field. Based on morphology, physiologic tests, 16S rDNA sequence, and phylogenetic characteristics, it was identified as Sphingomonas sp. This strain was capable of degrading leucomalachite green (LMG), leucocrystal violet and leucobasic fuchsin completely. The relationship between bacterium growth and LMG degradation suggested that strain CM9 could use LMG as the sole source of carbon. The most LMG degradation activity of CM9 crude extract was observed at pH 7.0 and at 30°C. Many metal ions had little inhibition effect on the degradation activity of the crude extract. CM9 also showed strong decolorization of triphenylmethane dyes to their leuco derivatives. GC/MS analysis detected two novel metabolic products, methylbenzene and 4-aminophenol, during the LMG degradation by CM9.     

DNA staining in agarose and polyacrylamide gels by methyl green

ABSTRACT

Methyl green (MG) is an inexpensive, nonproprietary, traditional histological stain for cell nuclei. When bound to DNA and upon excitation with orange-red light, it fluoresces brightly in the far red region. We compared MG with ethidium bromide (EtBr), the conventional stain for DNA in gels, and Serva DNA stain G? (SDsG), a proprietary stain marketed as a safer alternative to EtBr for staining of electrophoresed DNA bands in agarose and polyacrylamide gels. DNA-MG fluorescence was recorded and 2.4 μg/ml MG produced crisp images of electrophoresed DNA after incubation for 10 min. Stain solutions were stable and detection limits for faint bands as well as relative densitometric quantitation were equivalent to EtBr. MG, EtBr and SDsG cost 0.0192, 0.024 and 157.5 US cents/test, respectively. MG is an effective stain for visualizing DNA in agarose and polyacrylamide gels. Its major advantages including low cost, comparable quality of staining, storage at room temperature, photo-resistance and low mutagenic profile outweigh its disadvantages such as staining of tracking dye and requirement for a gel documentation system with a red filter.     

四个可持续发展实验区绿地系统可达性比较研究

我国可持续发展实验区所在城市均十分重视绿地系统对其可持续发展的重要支撑作用。布局合理的城市绿地系统不但能提高城市生态空间容量,也能充分满足不同位置城市居民的需求,这使得城市绿地与其被服务对象——城市居民之间的可达性成为评价城市绿地系统服务价值的重要指标。以高德公司生产的电子导航地图中居民区点和绿地系统数据为基础,采用GIS缓冲区分析法,分别探讨了我国4个有代表性的国家可持续发展实验区西城区、石景山区、绍兴市和日照市这4个城市的城市绿地系统斑块特征,以及5,5—15,15—30min时间距离内所覆盖城市居民点数量,对其绿地可达性及其服务能力进行比较分析和研究。研究结果表明:4个可持续发展实验区内的绿地系统分布均比较合理,覆盖面广,尤其是30min时间距离内可达的绿地满足了95%的住区;80%以上的住区居民可以在15min内到达周边任意绿地,为城市绿地管理部门打造"一刻钟生活圈"提供了良好的基础。但同时也发现,提供服务的绿地斑块面积比较细碎,大型绿地的配置率相对较低;而且多数绿地斑块从属于多个时间距离半径内,承受较大人口压力。最后,建议城市规划过程中,注重绿地系统与住区从时间尺度上的协调分析。此外,尝试性地采用日常生活中普遍使用的电子导航地图开展城市绿地系统可达性分析,研究结果与城市居民的生产生活密切相关,对城市绿地系统规划具有实际指导意义。