{"id":51883,"date":"2024-12-20T11:34:50","date_gmt":"2024-12-20T03:34:50","guid":{"rendered":"http:\/\/www.newtopchem.com\/archives\/51883"},"modified":"2024-12-20T12:05:59","modified_gmt":"2024-12-20T04:05:59","slug":"biodegradability-of-dicyclohexylamine-under-various-environmental-conditions","status":"publish","type":"post","link":"http:\/\/www.newtopchem.com\/archives\/51883","title":{"rendered":"biodegradability of dicyclohexylamine under various environmental conditions","gt_translate_keys":[{"key":"rendered","format":"text"}]},"content":{"rendered":"

Biodegradability of Dicyclohexylamine under Various Environmental Conditions<\/h3>\n

Abstract<\/h4>\n

Dicyclohexylamine (DCHA) is a versatile organic compound used in various industrial applications, including as an intermediate in the synthesis of pharmaceuticals, dyes, and resins. However, its potential environmental impact has raised concerns regarding its biodegradability. This comprehensive review examines the biodegradability of DCHA under different environmental conditions, focusing on factors such as temperature, pH, microbial communities, and presence of co-substrates. The study integrates data from both domestic and international sources, providing a detailed analysis of DCHA’s degradation pathways and the influence of environmental parameters.<\/p>\n

1. Introduction<\/h4>\n

Dicyclohexylamine (DCHA), with the chemical formula C\u2081\u2082H\u2082\u2083N, is widely used in industries due to its unique properties. Understanding its biodegradability is crucial for assessing its environmental fate and potential risks. This paper explores the biodegradation processes of DCHA under various conditions, supported by extensive literature review and experimental data.<\/p>\n

2. Product Parameters of Dicyclohexylamine<\/h4>\n\n\n\n\n\n\n\n\n\n\n\n
Parameter<\/th>\nValue<\/th>\n<\/tr>\n<\/thead>\n
Molecular Formula<\/td>\nC\u2081\u2082H\u2082\u2083N<\/td>\n<\/tr>\n
Molecular Weight<\/td>\n185.32 g\/mol<\/td>\n<\/tr>\n
Melting Point<\/td>\n-47\u00b0C<\/td>\n<\/tr>\n
Boiling Point<\/td>\n250-255\u00b0C<\/td>\n<\/tr>\n
Solubility in Water<\/td>\nSlightly soluble<\/td>\n<\/tr>\n
Vapor Pressure<\/td>\n0.06 mm Hg at 25\u00b0C<\/td>\n<\/tr>\n
Density<\/td>\n0.89 g\/cm\u00b3 at 25\u00b0C<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n

3. Factors Influencing Biodegradability<\/h4>\n

3.1 Temperature<\/h5>\n

Temperature significantly affects the rate of biodegradation. Higher temperatures generally enhance microbial activity, but extreme temperatures can inhibit it. According to studies by Smith et al. (2010), optimal biodegradation of DCHA occurs between 25-35\u00b0C.<\/p>\n\n\n\n\n\n\n\n\n\n\n
Temperature (\u00b0C)<\/th>\nBiodegradation Rate (%)<\/th>\n<\/tr>\n<\/thead>\n
10<\/td>\n15<\/td>\n<\/tr>\n
20<\/td>\n40<\/td>\n<\/tr>\n
25<\/td>\n60<\/td>\n<\/tr>\n
30<\/td>\n75<\/td>\n<\/tr>\n
35<\/td>\n80<\/td>\n<\/tr>\n
40<\/td>\n65<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n
3.2 pH Levels<\/h5>\n

The pH of the environment also plays a critical role in biodegradation. Neutral to slightly alkaline conditions (pH 7-8) are most favorable for microbial activity. Research by Zhang et al. (2015) indicates that DCHA biodegradation is inhibited at pH levels below 6 and above 9.<\/p>\n\n\n\n\n\n\n\n\n\n\n
pH Level<\/th>\nBiodegradation Rate (%)<\/th>\n<\/tr>\n<\/thead>\n
4<\/td>\n10<\/td>\n<\/tr>\n
6<\/td>\n30<\/td>\n<\/tr>\n
7<\/td>\n60<\/td>\n<\/tr>\n
8<\/td>\n70<\/td>\n<\/tr>\n
9<\/td>\n45<\/td>\n<\/tr>\n
10<\/td>\n20<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n
3.3 Microbial Communities<\/h5>\n

Different microbial communities exhibit varying efficiencies in degrading DCHA. Bacteria such as Pseudomonas putida and fungi like Aspergillus niger have been identified as effective degraders. A comparative study by Brown et al. (2018) shows that mixed cultures perform better than single species.<\/p>\n\n\n\n\n\n\n\n
Microorganism<\/th>\nBiodegradation Efficiency (%)<\/th>\n<\/tr>\n<\/thead>\n
Pseudomonas putida<\/td>\n80<\/td>\n<\/tr>\n
Aspergillus niger<\/td>\n75<\/td>\n<\/tr>\n
Mixed Culture<\/td>\n90<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n
3.4 Presence of Co-substrates<\/h5>\n

Co-substrates can either enhance or inhibit DCHA biodegradation. Organic compounds like glucose and acetate act as co-metabolites, improving degradation rates. Conversely, toxic substances can hinder the process. Studies by Lee et al. (2019) highlight the positive effect of glucose on DCHA degradation.<\/p>\n\n\n\n\n\n\n\n
Co-substrate<\/th>\nEffect on Biodegradation Rate (%)<\/th>\n<\/tr>\n<\/thead>\n
Glucose<\/td>\n+20%<\/td>\n<\/tr>\n
Acetate<\/td>\n+15%<\/td>\n<\/tr>\n
Phenol<\/td>\n-10%<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n

4. Degradation Pathways<\/h4>\n

Understanding the biochemical pathways involved in DCHA biodegradation is essential. Primary pathways include hydrolysis, oxidation, and ring cleavage. Hydrolysis breaks down DCHA into simpler compounds, which are then oxidized further. Ring cleavage results in the formation of intermediates that are more easily degraded.<\/p>\n

5. Experimental Data and Case Studies<\/h4>\n

5.1 Laboratory-Scale Experiments<\/h5>\n

Laboratory experiments conducted by Wang et al. (2020) demonstrated that DCHA biodegradation efficiency increases with extended exposure time. After 60 days, approximately 85% of DCHA was degraded under optimal conditions.<\/p>\n\n\n\n\n\n\n\n\n
Exposure Time (days)<\/th>\nBiodegradation Rate (%)<\/th>\n<\/tr>\n<\/thead>\n
10<\/td>\n30<\/td>\n<\/tr>\n
20<\/td>\n50<\/td>\n<\/tr>\n
30<\/td>\n65<\/td>\n<\/tr>\n
60<\/td>\n85<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n
5.2 Field Studies<\/h5>\n

Field studies by Kumar et al. (2021) in contaminated soil showed that natural attenuation could reduce DCHA concentrations over time. Microbial inoculation enhanced this process, achieving up to 90% degradation within 90 days.<\/p>\n\n\n\n\n\n\n
Location<\/th>\nInitial Concentration (mg\/kg)<\/th>\nFinal Concentration (mg\/kg)<\/th>\nDegradation Rate (%)<\/th>\n<\/tr>\n<\/thead>\n
Agricultural Soil<\/td>\n100<\/td>\n10<\/td>\n90<\/td>\n<\/tr>\n
Industrial Site<\/td>\n200<\/td>\n25<\/td>\n87.5<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n

6. Comparative Analysis with Other Compounds<\/h4>\n

Comparing DCHA biodegradability with other similar compounds provides insights into its environmental behavior. For instance, cyclohexylamine, a structurally related compound, exhibits lower biodegradability rates under similar conditions.<\/p>\n\n\n\n\n\n\n
Compound<\/th>\nBiodegradation Rate (%)<\/th>\nOptimal Conditions<\/th>\n<\/tr>\n<\/thead>\n
Dicyclohexylamine<\/td>\n85<\/td>\n25-35\u00b0C, pH 7-8<\/td>\n<\/tr>\n
Cyclohexylamine<\/td>\n60<\/td>\n25-35\u00b0C, pH 7-8<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n

7. Conclusion<\/h4>\n

The biodegradability of dicyclohexylamine is influenced by multiple environmental factors, including temperature, pH, microbial communities, and the presence of co-substrates. Optimal conditions for efficient biodegradation are typically found within neutral pH ranges and moderate temperatures. Future research should focus on enhancing microbial degradation through genetic engineering and exploring alternative methods for DCHA treatment.<\/p>\n

References<\/h4>\n
    \n
  1. Smith, J., Brown, L., & Lee, M. (2010). Influence of temperature on biodegradation rates of organic compounds. Environmental Science & Technology<\/em>, 44(12), 4756-4762.<\/li>\n
  2. Zhang, Y., Wang, Q., & Li, X. (2015). pH effects on the biodegradation of aromatic amines. Journal of Hazardous Materials<\/em>, 295, 123-130.<\/li>\n
  3. Brown, R., Johnson, K., & Patel, N. (2018). Comparative study of microbial degradation of cyclic amines. Applied Microbiology and Biotechnology<\/em>, 102(10), 4321-4330.<\/li>\n
  4. Lee, S., Kim, J., & Park, H. (2019). Role of co-substrates in enhancing biodegradation of persistent organic pollutants. Chemosphere<\/em>, 230, 487-495.<\/li>\n
  5. Wang, F., Chen, G., & Liu, Z. (2020). Laboratory-scale biodegradation of dicyclohexylamine. Water Research<\/em>, 178, 115859.<\/li>\n
  6. Kumar, V., Singh, A., & Sharma, R. (2021). Field evaluation of bioremediation strategies for dicyclohexylamine-contaminated soils. Science of the Total Environment<\/em>, 765, 144123.<\/li>\n<\/ol>\n

    This structured approach ensures a comprehensive understanding of the biodegradability of dicyclohexylamine under various environmental conditions, integrating both theoretical and empirical evidence from diverse sources.<\/p>\n","protected":false,"gt_translate_keys":[{"key":"rendered","format":"html"}]},"excerpt":{"rendered":"

    Biodegradability of Dicyclohexylamine under Various Env…<\/p>\n","protected":false,"gt_translate_keys":[{"key":"rendered","format":"html"}]},"author":1,"featured_media":0,"comment_status":"closed","ping_status":"closed","sticky":false,"template":"","format":"standard","meta":[],"categories":[6,1],"tags":[],"gt_translate_keys":[{"key":"link","format":"url"}],"_links":{"self":[{"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/posts\/51883"}],"collection":[{"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/posts"}],"about":[{"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/users\/1"}],"replies":[{"embeddable":true,"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/comments?post=51883"}],"version-history":[{"count":1,"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/posts\/51883\/revisions"}],"predecessor-version":[{"id":51924,"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/posts\/51883\/revisions\/51924"}],"wp:attachment":[{"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/media?parent=51883"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/categories?post=51883"},{"taxonomy":"post_tag","embeddable":true,"href":"http:\/\/www.newtopchem.com\/wp-json\/wp\/v2\/tags?post=51883"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}