key: cord-0819118-x9k4h57e
authors: Chaudhary, Anjali; Venkatramanan, V.; Kumar Mishra, Ajay; Sharma, Sheetal
title: Agronomic and Environmental Determinants of Direct Seeded Rice in South Asia
date: 2022-05-06
journal: Circ Econ Sustain
DOI: 10.1007/s43615-022-00173-x
sha: c9e85581d7c1a0d2b5feab711bfa424e580f26ab
doc_id: 819118
cord_uid: x9k4h57e

Rice (Oryza sativa L.) is the staple food of more than 50% of the world’s population. Manual puddled transplanted rice (PTR) system is still the predominant method of rice establishment. However, due to declining water tables, increasing water scarcity, water, labor- and energy-intensive nature of PTR, high labor wages, adverse effects of puddling on soil health and succeeding crops, and high methane emissions, this production system is becoming less profitable. These factors trigger the need for an alternative crop establishment method. The direct-seeded rice (DSR) technique is gaining popularity because of its low input demand compared to PTR. It is done by sowing pre-germinated seeds in puddled soil (wet-DSR), standing water (water seeding), or dry seeding on a prepared seedbed (dry-DSR). DSR requires less water and labor (12–35%), reduces methane emissions (10–90%), improves soil physical properties, involves less drudgery and production cost (US$9–125 per hectare), and gives comparable yields. Upgraded short-duration and high-yielding varieties and efficient nutrient, weed, and resource management techniques encouraged the farmers to switch to DSR culture. However, several constraints are associated with this shift: more weeds, the emergence of weedy rice, herbicide resistance, nitrous oxide emissions, nutrient disorders, primarily N and micro-nutrients, and an increase in soil-borne pathogens lodging etc. These issues can be overcome if proper weed, water, and fertilizer management strategies are adopted. Techniques like stale bed technique, mulching, crop rotation, Sesbania co-culture, seed priming, pre-emergence and post-emergence spray, and a systematic weed monitoring program will help reduce weeds. Chemical to biotechnological methods like herbicide-resistant rice varieties and more competitive allelopathic varieties will be required for sustainable rice production. In addition, strategies like nitrification inhibitors and deep urea placement can be used to reduce N(2)O emissions. Developing site and soil-specific integrated packages will help in the broader adoption of DSR and reduce the environmental footprint of PTR. The present paper aims to identify the gaps and develop the best-bet agronomic practices and develop an integrated package of technologies for DSR, keeping in mind the advantages and constraints associated with DSR, and suggest some prospects. Eco-friendly, cost-effective DSR package offers sustainable rice production systems with fewer resources and low emissions. GRAPHICAL ABSTRACT: [Image: see text]

Rice (Oryza sativa L.) is a major cereal crop cultivated in at least 95 countries across the globe [55] and provides staple food for more than half of the world's population [2, 205] . On a global scale, the total area under rice is 163.5 million hectares with an annual production of 758.9 million tons and productivity of 4641.5 kg/ha. In India, it is grown on about 42.5 million ha with a total production of 105.5 million tons and productivity of 3632.9 kg/ha. To meet the second Sustainable Development Goal (SDG) of the UN, which is to end hunger in all its forms by 2030 and achieve global food security, additional paddy is needed to be produced to feed the ever-increasing population. However, the possibility of an increase in area under rice is very limited in the coming future. Therefore, the only way to get this extra rice is to increase productivity. The main dare is to achieve this productivity gain with less water, labor, and chemicals to ensure sustainability.

The following are the major constraints associated with the productivity and sustainability of rice-based systems: (1) increasing scarcity of water and labor, (2) inefficient use of inputs (fertilizer, water, labor), (3) climate change and variability, (4) emerging energy crisis and hike in fuel prices, (5) multiplying cost of cultivation, and (6) other issues like rapid urbanization, migration of labor to cities, non-agricultural work preferences, and farm-related pollution [119] . Better agronomic management practices and innovations in technology are required to overcome these problems.

Asia accounts for more than 90% of rice production and consumption. Conventionally, rice in Asia is grown by the transplanting method. Rice nurseries are raised in the transplanting method, and after 20-30 days, those rice seedlings are transplanted into puddled soil. Rice grown by this method is known as puddled transplanted rice (PTR). Puddling the soil has its benefits for rice cultivation. It creates an impervious layer that helps to reduce water percolation losses, facilitates easy seedling establishment, controls weed, and creates anaerobic conditions to enhance nutrient availability [196] . However, repeated puddling damages soil aggregates, breaks capillary pores, lessens permeability in sub-surface layers, and forms hard-pan [1, 201, 203] , which proves detrimental to the establishment and growth of the following crop [83] . Besides, puddling and transplanting demand large amount of water (3000-5000 L water to produce 1 kg rice] [27] and human labor, which are becoming scarce and expensive day by day, thereby increasing the cost of cultivation and making the paddy production less profitable.

Moreover, the physical drudgery in transplanting -which women primarily dois a matter of concern. So, all the above factors trigger the search for an alternative rice crop establishment method. Direct seeded rice (DSR) seems a viable option to make this shift. DSR refers to the process of sowing rice seeds directly into the field in place of transplanting the rice seedlings from the nursery. Upgraded short-duration and highyielding varieties and nutrient, weed, and resource management techniques encouraged the farmers to switch to DSR culture. It is widely practiced in many Asian countries: Malaysia, Sri Lanka, Vietnam, Thailand, Cambodia, and the Philippines. This review aims to develop best-bet agronomic practices so that ecological and agronomic input efficiency can be enhanced and the environmental footprint of PTR can be reduced. Types of direct seeding, reasons for adoption of DSR, advantages and constraints of DSR, and integrated package of technologies for DSR are discussed further in this paper.

Direct seeding is the oldest known method of rice establishment. It was prevalent before the 1950s, but gradually, puddled transplanting replaced this method [75, 168, 185, 186] . Direct seeding can be done in three principal ways, which are modified with time based on technological innovations and demand for better resource-efficient practices. These direct seeding methods can be classified based on land preparation, seedbed condition, ways of sowing, and seed environment (aerobic or anaerobic) [119] .

1. Wet-DSR: in this, pre-germinated seeds (radicle 1-3 mm) are broadcast or sown in lines on wet/puddled soil. When pre-germinated seeds are sown on the surface of puddled soil, the seed environment becomes aerobic, and it is called aerobic wet-DSR (surface). It can be done using a drum seeder [187] . On the other hand, when the pre-germinated seeds are drilled into puddled soil, the seed environment becomes anaerobic and is called anaerobic wet-DSR (subsurface). In this, seeds are sown inline using an anaerobic seeder with a furrow opener and closer [16] . Wet-DSR is primarily done to manage the labor shortage and is currently practiced in Malaysia, Thailand, Vietnam, the Philippines, and Sri Lanka [21, 24, 167 ]. 2. Dry-DSR is broadcast or drilled in dry/unpuddled soil. In dry-DSR, rice is established using several different methods, including (a) broadcasting of dry seeds on unpuddled soil after either zero tillage (ZT) or conventional tillage (CT), (b) dibbled method in a well-prepared field (CT-dry-dibbledR), and (c) drilling of seeds in rows after conventional tillage (CT-dry-DSR), reduced tillage using a power-tiller-operated seeder (PTOS) (RT (PTOS)-dry-DSR), *-/zero tillage (ZT-dry-DSR), or raised beds (Bed-dry-DSR) [119] . The seedbed condition is dry (unpuddled), and the seed environment is mostly aerobic; thus, this method is known as dry-DSR. This method is traditionally practiced in rainfed upland, lowland, and flood-prone Asia areas [185, 186] . However, this method has recently been gaining importance in irrigated areas where water is becoming scarce. In dry-DSR, land preparation is done before the onset of monsoon, and seeds are sown before the wet season to take advantage of pre-monsoon rainfall for CE and early crop growth. Both wet-DSR and dry-DSR can reduce water and labor usage compared to CT-PTR. 3. Water seeding is broadcast in standing water. Water seeding has gained popularity in red rice or weedy rice, which is becoming a severe problem [13] . Aerial water seeding is the most common method used in California (USA), Australia, and European countries to suppress difficult-to-control weeds, including weedy rice. This method is also becoming popular in Malaysia. The rice varieties used possess good tolerance of a low dissolved oxygen level, low light, and other stress environments [16] . In addition to irrigated areas, water seeding is practiced in areas where early flooding occurs and water cannot be drained from the fields.

Method of DSR adopted varies considerably from location to location depending upon different factors like labor, land preparation (tillage), establishment methods, seed rate, water, and weed and nutrient management [116] .

Globally, water is becoming a scarce resource. The groundwater table is declining at an alarming rate. On the other hand, conventional rice cultivation requires substantial water. The lack of ability to recreate water calls for the need to conserve and ensure adequate water drops. It has been estimated that up to 5000 L of water is used to produce just 1 kg of rough rice [27] , which is way too high. Rice consumes two to three times more freshwater than any other cereals [18, 31, 239] . Barker et al. [18] also reported that rice consumes about 50% of total irrigation water used in Asia. In India, per capita water availability decreased by 72.3% between 1951 and 2005 (5831 m 3 and 1611 m 3 in 1951 and 2015, respectively) and is likely to decline further by 77.8% till 2050 (1292 m 3 in 2050) (modified from Gardner-Outlaw and Engelman [68] ). Water availability decreases because of the increasing population, declining water table, deteriorating water quality, inefficient irrigation systems, and competition from non-agricultural sectors. So, water scarcity acts as a driving force for adopting direct seeding. Since the last decade, there have been numerous efforts to find alternatives to conventional PTR [119] . Excellent water management will ensure the availability of sufficient water for crop production.

Many studies have reported the potential of DSR as a replacement for PTR. For example, an average of 67-104 mm (11-18%) irrigation water savings in wet-DSR than CT-PTR was observed under on-farm trials in the Philippines [236] while keeping the criteria of irrigation application same for both the rice establishment methods. However, in another study done in the Muda region of Malaysia by Cabangon [30] , it was found that the application of irrigation water in dry-DSR was less by ~ 200 mm (40%) than CT-PTR. Likewise, in India, 10-15% water savings have been reported with dry-DSR compared to CT-PTR when the criteria of irrigation application were either the appearance of hairline cracks or tensiometer-based (− 20 kPa at 20-cm depth) [22, 96, 228, 229] .

As DSR requires less water and is more tolerant of water stress than PTR, it has a more adaptive capacity to climate change. Climate change is likely to increase rainfall variability and the risk of drought and water stress in the coming future. With the growing shortage of water, dry-DSR with minimum/reduced or zero tillage further enhances the potential of this technology by saving labor [35, 104] .

CT-PTR is very labor-intensive. On the other hand, Indian farming is witnessing labor scarcity [209] . Major reasons contributing to the scarcity are low wages and temporary employment in agriculture, migration of labor to cities in search of urbanized lifestyle, physical drudgery involved in farming, preference for nonagricultural work, and involvement in social welfare schemes like The Mahatma Gandhi National Rural Employment Guarantee Act (MGNREGA), 2005. Covid-19 pandemic-related curbs have further worsened the situation. Moreover, labor scarcity is season-and location-specific because of the mismatch in demand and supply at the right time and place. Dawe [47] reported that labor required for agricultural work is declining at the rate of 0.1-0.4%, with an average of 0.2% per year. Because of severe labor scarcity, labor wages have gone up drastically in the last few years. This has made the CT-PTR system uneconomical. All these factors urge the need for alternative practices like DSR.

DSR demands less labor as it avoids raising nurseries, uprooting seedlings, puddling, and transplanting. Instead of transplanting, which requires 25-50 persondays/ha, DSR requires about 5 person-days/ha [16, 47] . Thus, the requirement of labor in DSR is spread out over a longer period. This, in turn, avoids the problem of labor scarcity at peak season and having less dependence on hired labor. It has been reported that the labor requirements for crop establishment (CE) in direct seeding compared with transplanting decrease by more than 75% [47, 92, 167] . Depending on the season, location, and type of DSR method used, labor requirements reduced from 11 to 66% in DSR compared with CT-PTR [114, 187] . The variation in labor savings largely depends on the labor used for controlling weeds in DSR. If weeds can be managed effectively using herbicides, it can save additional labor. The newly emerging techniques of ZT-Dry-DSR report substantial labor savings, as no puddling and tillage are required in this operation. It has been reported that PTR can be substituted with wet-DSR at places where only labor/wage rate is a major limiting factor (e.g., Malaysia, Sri Lanka). But, in areas where water and labor are scarce, PTR should be replaced with dry-DSR (e.g., South Asia). Global drivers for shift from PTR to DSR are shown in Figs. 1, 2, 3, and 4. 

Puddling has varying effects on the well-being of soil health (soil quality, especially on soil physical properties), which claims to be another reason for the shift from CT-PTR to dry-DSR on plowed soil (no puddling) or in ZT conditions, where an upland crop is grown after rice [73, 76, 119] . This is particularly relevant to the rice-wheat system, in which soil goes through the wetting and drying phenomenon [118] . Puddling breaks soil aggregates, destroys capillary pores, disperses fine clay particles, and forms hard-pan at shallow depth. Although puddling helps transplant and establish seedlings, control weeds, better water, and nutrient availability, it adversely affects the growth and yield of succeeding upland crops [69] .

Numerous studies have been published that evaluated the effects of puddling in rice on succeeding wheat crops. Kumar [116] compiled and analyzed 35 such studies, out of which 28 showed adverse effects of puddling on subsequent wheat crop productivity. Five cases mentioned no impact, and only one study showed positive puddling results. The parameters considered were location, soil type, rice establishment method, number of crop cycles, rice yield, wheat yield, and percentage of change in wheat yield. In two medium-term studies carried out at Pantnagar (5-years) and Modipuram (7-years), the performance of wheat was evaluated after either puddled or dry-DSR. It was observed that the Pantnagar site had 12% higher wheat yield in dry-DSR plots than in CT-TPR in all 5 years [208, 210, 223b] . However, at Modipuram, the wheat yield was the same in the first 3 years, followed by 0.5-1.0 t/ha (9-25%) higher yield in dry-DSR plots in the later years [69] . The main reason for the lower grain yield of wheat after CT-PTR was poor root development due to the puddling done in the preceding rice crop [1, 25, 40, 89, 161] .

Similarly, Gangwar [65, 66] compared the DSR-based cropping system productivity with the PTR-based cropping system productivity. He observed that the DSR-wheat, DSR-chickpea, and DSR-mustard system productivities (14.96 t/ha, 14.48 t/ha, and 13.48 t/ha, respectively) were higher than the PTR systems (13.53 t/ha, 12.12 t/ha, and 11.81 t/ ha respectively). It can be understood that puddling benefits the rice crop, but it has detrimental effects on the growth and yield of the succeeding crop as it badly affects soil health [133, 224] . Therefore, it becomes imperative to find alternative methods to puddling. More attention should be paid to the regions where water availability is less and crops are grown after rice cultivation.

Conservation agriculture (CA) involves minimum soil disturbance (reduced tillage or zero tillage), permanent soil covers through crop residues or cover crops (incorporation/retention), and crop diversification (sequences and rotations) for achieving higher productivity [135] . Conservation tillage (CT) involves zero or minimal tillage followed by row seeding using a drill. As stated by Ladha [119] when CT utilizes crop residue as mulch with improved crop and resource management practices, it is termed CA. Conventional agriculture (resource intensive) has led to declining/stagnating crop and factor productivity and a deteriorating resource base in cereal systems [111, 137] . Zero tillage is primarily promoted in wheat in the rice-wheat system and covers about 3 million hectares of land in Indo-Gangetic Plains (IGP) of South Asia [77, 80] . Factors responsible for rising interest and wide adoption of ZT in wheat are increased productivity (3-12%, due to timely planting), profitability by the reduction in production cost (by avoiding tillage), better resource-use efficiency, and farmer's livelihood, particularly in areas where rice harvest is delayed [51, 77, 84, 119] . Now, efforts are being made to develop ZT rice followed by ZT wheat -commonly referred to as "double-zero tillage" to explore the full potential of zero tillage.

The economic motive for farmers is to get higher profitability which can be defined as the difference between the gross economic returns and the total cost. With CT, farmers get a higher net economic return under wet or dry DSR than TPR, with 13% higher for wet DSR [33] . Under dry-DSR with ZT, the economic returns are even higher by 25.9% than TPR due to increased savings in water input and cost of cultivation. Such an increase in farmers' profitability can be explained by two reasons, a reduction of production costs and an expansion of the total revenue.

The production costs include two parts, the cost of inputs (seeds, agro-chemicals, fertilizers and pesticides, water), and the cost induced by the use of production factors (human labor and machines) in field operations (such as land preparation, sowing, irrigation, weeding, agro-chemicals applications, harvesting, threshing). Overall analysis of 77 published studies in Asian countries done by [116] shows that various methods of DSR reduced the cost of production by US$9-125/ha compared with conventional practice (TPR). According to Chakraborty [33] , wet-DSR induces a reduction in cost by 2.4-8.8%. These cost reductions under DSR are mainly due to lower labor costs, tillage costs, or both.

According to the rice establishment method, the necessity of tillage can be relatively relaxed. Under TPR, rice seedlings are transplanted into puddled soil after land preparation with wet intensive tillage, a very energy-intensive method. Tillage operations account for 15% of the total production cost in irrigated rice, and farmers in the Indo-Gangetic Plains are assumed to spend US$50-60/ha on land preparation [129] . On the contrary, under dry-DSR, seeds are sown on unpuddled soil, either after dry tillage or minimal tillage. Of course, reduced tillage significantly lowers the production cost (US$37-92/ha) [116] . According to Chakraborty [33] , wet-DSR and dry-DSR have a higher grain yield than TPR under conventional tillage, and wet-DSR has the most considerable yield advantage (1.3-4.7%). The main benefits of minimum and zero tillage practices are conservation of organic matter and soil moisture, reduction in water and wind erosion, reduction in fuels and animal and human energy, and time and water required for land preparation, and possible provision of a favorable environment for biological activity [56] .

Besides saving water and labor, DSR provides economic benefits by integrating an additional crop (crop intensification). This becomes the reason for the spread and rapid adoption of DSR in many regions. Furthermore, early maturity (7-11 days) of DSR than PTR allows it to incorporate another crop and fits well in different cropping systems.

In Long An Province in the Mekong River Delta region of Vietnam, DSR facilitated double cropping in place of a single crop of PTR [167] . Early harvesting of dry-DSR in August was possible due to the early establishment and short-duration varieties (95-105 days), leaving sufficient time and rainfall for another rainfed rice crop to grow. My [151] reported that some farmers could grow a third rice crop from December to February with additional irrigation. Thus, DSR is increasing gradually and steadily over different regions. Availability of new high-yielding and short-duration varieties and new herbicides for weed control made this shift technically viable [149, 167] . Rising rice production has helped increase food security, but there is a widely recognized need to assess the sustainability of such production systems [49] .

Agriculture contributes to the emission of greenhouse gases (GHGs) (mainly CO 2 , CH 4 and N 2 O), which cause global warming. Based on data from the meta-analysis by Joseph Poore and Thomas Nemecek [180] , published in Science, crop production accounts for 27% of food emissions. About 21% of these food's emissions come from crop production for direct human consumption, and 6% comes from animal feed production. They are the direct emissions that result from agricultural production -this includes elements such as the release of nitrous oxide from fertilizers and manure, carbon dioxide from agricultural machinery, and methane emissions from rice production. Rice-based cropping systems play a significant role. GHG emissions, mainly CO 2 and CH 4 from rice fields, are substantial and sensitive to management practices. Therefore, rice is an essential target for mitigating GHG emissions [246] .

Rice is among the three major crops of the world, occupying ~ 155 million ha of land. An increasing population of India will demand 25% more rice by 2025 [129] . In the Indo-Gangetic Plain of Northern India, Punjab, India, produces 50% of the nation's rice and is known as the "food bowl of India." The most common method of rice cultivation in the IGP is puddled transplanting. This flooded rice culture is the primary culprit of methane emissions because prolonged flooding results in anaerobic soil conditions. This accounts for 10-20% of total global methane emissions [86, 189] . CH 4 is produced in flooded soils due to reducing C compounds to CH 4 in limited oxygen supply. The standing water in conventional rice fields restricts oxygen from the atmosphere into the soil. A small but particular bacterial group named methanogens makes the water-saturated soil devoid of oxygen, and anaerobic conditions are formed. Therefore, methane emissions are high in conventional PTR, where standing water conditions are maintained throughout the crop growth. On the other hand, DSR fields are not continuously submerged underwater, so anaerobic conditions are not created. As a result, methane emissions are low [174] .

Pathak [174] conducted a 2-year field experiment in the Jalandhar district of Punjab, India, to quantify GHG mitigation, water, and labor-saving potential of DSR with TPR. He found that the average GWP of CO 2 , CH 4 , and N 2 O in TPR was 2.91 t/ha, and in DSR, it was 1.94 t/ha. It was also concluded that if the entire state under TPR is converted to DSR, GWP will reduce by 33%. Along with this, 3-4 irrigations were saved under DSR without yield loss. Tractor use decreased to 58% and human labor use reduced to 45% in DSR compared to TPR. This shows that by reducing GHG emissions, water, and labor (both human and machine) without reducing yield, DSR can be a feasible alternative to PTR for mitigating and adapting to climate change and increasing farmers' income [174] . A similar study was conducted at the Indonesian Agricultural Environment Research Institute (IAERI), Central Java, Indonesia. Susilawati [231] reported that CH 4 emissions were 47% less in DSR than PTR. GWP reduced by 46.4% under DSR without any significant loss of yield.

Many studies which compared CH 4 emissions from various tillage and crop establishment methods along with similar water management techniques revealed that CH 4 emissions were lower in wet (8-22%) or dry-DSR (24-79%) as compared to CT-PTR [116] . Ishibashi [91] compared ZT-dry-DSR and CT-TPR and found that the former is 20% more efficient in reducing GWP. Pathak [173] simulated for Indian conditions and found that dry-DSR on raised beds or ZT can reduce CO 2 equivalent per hectare by 40-44% compared to CT-TPR. Harada [79] reported that GWP declined by 42% in Japan by changing puddling to zero tillage.

Even in CT-PTR, CH 4 emissions vary from study to study. The reason may be individual or combined effects of climatic conditions, edaphic factors, and water management [10] . Therefore, it can be concluded that DSR is more efficient in reducing GHG emissions, mainly CH 4 , if proper crop management practices are adopted and precise nutrient use employed [32] . In addition, under DSR, the dissimilatory nitrate reduction to ammonium (DNRA) pathway can reduce N 2 O emissions and protect NO 3 − from leaching losses [164] .

Weeds are a major biotic constraint to the success of DSR in general and dry-DSR in particular [98, 185, 186, 215] . Competition by the weeds is not only for nutrients; the case has also been with space, light, and moisture in the entire growing season [3] . Earlier research has shown that yield loss is greater in DSR than in transplanted rice without effective weed control options [17, 185, 186] . Weeds create more problems in DSR than in puddled transplanting because (1) emerging DSR seedlings are less competitive with concurrently emerging weeds, and (2) in wet-and dry-DSR, the initial flush of weeds is not controlled due to the absence of flooding [113, 185, 186] . Failure to manage weeds in DSR leads to very low or no yield, so controlling weeds effectively in DSR is a real challenge [147, 216] . Direct seeded rice is heavily infested with weeds, so the success of DSR depends on effective weed management [36,185,186,215a, 219] . Yields were reduced by 96% in dry-DSR, 61% in wet-DSR, and 40% in the machinery-transplanted crop due to uncontrolled weeds [107, 126] . Aerobic systems are subjected to much higher weed pressure than CPTR [185, 186] , in which weeds are suppressed due to prevailing anaerobic environments in flooded conditions [146] . Heavy yield losses due to lack of proper weed management can reach up to 70-100% in dry-DSR [122, 123] , and this has been reported by many researchers [65, 66, 208, 210, 211, 217, 223] .

Several parameters decide the economic consequences of weeds in rice, such as infestation rate, the types of weeds, the cultivated varieties, and the measures taken to control them. Farmer's income is affected due to the following factors:

• A quantity effect due to substantial reductions in yield • Due to the presence of weeds seeds (including red rice) in the grain, a price effect • A cost effective, due to increased costs of production incurred by control measures such as labor, equipment, chemicals, and energy [233] [234] [235] This reduction in farmers' income can eventually lead to the abandonment of rice production.

Weedy rice (O. sativa f. spontanea), also known as red rice, has become a severe concern in areas where rice production has shifted from transplanting to direct seeding, especially dry-DSR. The weedy rice paradox is well known but underestimated. Weedy rice is conspecific and congeneric of cultivated rice; it has both acquired and wild rice traits. Then, it is challenging to control it either traditional or biotechnologically because it promotes crop-weed hybridization and the introgression of characteristics such as herbicide resistance [233] [234] [235] . It is challenging to manage weedy rice because of its similarity with rice in genetics, morphology, and phenology. Weedy rice is highly competitive and can cause severe yield losses ranging from 15-100% [116] . Weedy rice can also reduce milling quality if mixed with rice seeds during harvesting [160] . It can also increase the cost of production. Farmers may end up using most of the labor saved by DSR to control weeds.

Vegetatively, weedy rice possesses several traits of the agricultural weed syndrome [243] , such as crop mimicry, seed dispersal, seed dormancy, rapid growth, high nutrient use efficiency, and herbicide resistance. Beyond these common traits, weedy rice exhibits high genetic and phenotypic diversity [156, 188, 238] . This diversity is dependent on the ecotype and habitat.

Selective control of weedy rice has never been achieved at a satisfactory level with herbicides [155] . Therefore, FAO [54] recommends an integrated approach that encompasses preventive, cultural, mechanical, and chemical methods targeting different phases of the weedy rice cycle. Moreover, clean and certified seeds should be used [185, 186] . It was observed by Azmi and Abdullah [12] that pre-plant application of soil-incorporated moline was effective in reducing the seed bank of weedy rice. Selective control of weedy rice can be achieved from herbicide-resistant rice technologies, but the risk of gene flow poses a constraint for the long-term utility of this technology [112] .

However, weedy rice control methods that can be applied under DSR are neither practical nor sustainable as they are usually thought. Indeed, weedy rice is difficult to control because of its genetic, morphological, and phenological similarities with rice. Then, the integrated weed management (IWM) strategies typically do not lead to the total eradication of the weed infestation. Incomplete control of the weed for a given year could lead to eliminating the results of several years of sound control. Weedy rice escapes of 5% or less can produce enough seeds to restore original soil seed bank population levels [62] .

In addition, the IWM is not sustainable because the IWM methods are expensive, timeconsuming, and are not environment-friendly since they require more fuel energy, water, and herbicide [233] [234] [235] .

The composition of weed flora can change drastically with a shift from CT-TPR to alternative tillage and rice establishment methods [218] . Changes in weed composition and diversity in DSR were led by the changes in rice establishment method along with water, tillage, and weed management practices [116] . DSR is infested by complex weed flora, including grasses, broadleaf weeds, and sedges. In a study conducted at Modipuram, India, Singh [218] reported that the number of species of grasses, broadleaves, and sedges in CT-PTR was 6, 4, and 4, respectively, whereas in dry-DSR, it increased to 15 grass species and 19 broadleaf species, and the number of sedge species remained unaffected. This clearly shows that some new grass and broadleaf species that were not adapted to CT-PTR appeared in dry-DSR. More species-rich vegetation and diverse weed flora were observed in dry-DSR than in CT-TPR by Tomita [237] . About 46 species were present in transplanted rice in 1989, and, after 3 years (six seasons of rice) of wet-DSR, 21 new weed species were added to the weed flora [14, 148] . Higher numbers and more diverse flora in dry-DSR could lower the efficacy of weed management strategies, including herbicides. Therefore, it is imperative to incorporate a systematic weed monitoring program and the introduction of DSR. Then, only it would be possible to develop effective integrated weed management strategies, which include identifying new herbicides that are effective against a broad spectrum of weeds.

Increased practice of DSR also increased herbicide use for controlling weeds in rice, which resulted in the appearance of resistance in weeds against certain herbicides. The first case of herbicide resistance was seen in F. miliacea against 2,4-D in Malaysia in 1989. Later on, this number of resistant weed biotypes against different herbicides increased to 10. Post DSR introduction, several herbicide-resistance cases in weeds were also observed in Thailand (5), Korea (10), and The Philippines (3) [116] .

DSR can help reduce methane emissions, but aerobic soil conditions in DSR, especially in dry-DSR, contribute to increased nitrous oxide emissions. The biologic processes of nitrification and denitrification are the effective mechanisms of nitrous oxide emission from agricultural soils. Nitrification occurs in aerobic soil conditions, while denitrification occurs under anaerobic conditions [171] . Due to the prevailing anaerobic conditions in TPR, denitrification is the principal mechanism for N 2 O emissions, whereas DSR nitrification is the primary mechanism [172] . Pathak [174] quantified the N 2 O emissions from DSR and TPR fields of Punjab, India. They reported that emissions from DSR fields were slightly higher than TPR. Cumulative emission of N 2 O during the entire crop duration in 2010 was 2.0-2.2 kg/ha in DSR and 1.6-1.8 kg/ha in TPR. In a study conducted in India comparing N 2 O emissions from CT-TPR and different dry-DSR methods (CT-dry-DSR, bed-dry-DSR, ZT-dry-DSR), it was found that N 2 O emissions were 0.31-0.39 kg N/ha in CT-TPR, which increased to 0.90-1.1 kg N/ha in CT-dry-DSR and bed-dry-DSR and 1.3-2.2 kg N/ha in ZT-dry-DSR. Similarly, a study conducted in western Japan also observed higher emissions of N 2 O under ZT-dry-DSR than in CT-TPR [90] . These results suggest the need to deploy strategies to reduce N 2 O emissions from dry-DSR to minimize adverse environmental impacts. Methane emission starts at redox potential of soil below − 150 mV and is stimulated at less than − 200 mV [100, 128, 245] . Nitrous oxide production increases at redox potentials above 250 mV [85] . Hou [85] suggested developing water management practices so that soil redox potential can be kept at an intermediate range (− 100 to + 200 mV) to minimize emissions of both CH 4 and N 2 O. This range is high enough to prevent CH 4 production and low to encourage N 2 O reduction to N 2 as the critical soil redox potential identified for N 2 O production is + 250 mV [85] . The overall effect of direct-seeding methods on GWP depends on the total emissions of all three major GHGs. It has been observed that measures to reduce one source of GHG emissions lead to increases in other GHG emissions, and this trade-off between CH 4 and N 2 O is a significant hurdle in devising an effective GHG mitigation strategy for rice [246] . Very few studies have compared different rice production systems in total GWP, taking all three GHGs.

Nutrient dynamics in DSR and TPR systems vary due to the difference in land preparation and water management techniques [104] . Nutrients needed for direct-seeded rice have faced tight competition from weeds. In DSR, soil conditions are mostly aerobic because of dry land preparation, while in PTR, the soil is mainly kept flooded and is puddled. Puddling positively impacts weed control [194] and nutrient availability [244] . Less oxygen in the rhizosphere in submerged conditions prevents oxidation of NH 4+ and reduces leaching [108] . It also increases the availability of P [208, 210, 223, 250] and Fe [165, 230] .

Deficiencies of micronutrients are of major concern in DSR. The shift from PTR to DSR reduces Zn availability to rice because of its reduced release from highly insoluble fractions in aerobic rice fields [67, 108] . Reasons for Zn deficiency are high pH, high carbonate content [127] , and more bicarbonates in calcareous soils [64] , which immobilize Zn due to inhibition effect [72] . Zn uptake in DSR is also affected by source and time of application [72] . When pH is below neutral in the rhizosphere, the availability of P and Zn increases because of their increased solubility [108, 195] . The availability of Fe is high in anaerobic soils because of low redox potential. However, Fe becomes a limiting factor in aerobic soils when soil pH is high. Due to unsaturated soil conditions in DSR, plants can show chlorosis because of iron deficiency. Prolonged iron deficiency may also lead to severe yield losses in DSR; hence, care should be taken to manage iron deficiency. Singh [208, 210, 223] reported that in dry-DSR, the iron content was about half of the submerged PTR and WSR treatments. The values were below the critical limit of 4.5 ppm. Therefore, appropriate nutrient management strategies need to be developed based on nutrient dynamic studies in DSR.

Soil-borne pathogens such as root-knot nematodes (RKNs) pose a severe threat when PTR is shifted to DSR. Meloidogyne graminicola, a root-knot nematode, was first reported in 1963 from the Louisiana State University, Baton Rouge, USA. In a study at Tarlac, Philippines, RKNs were the most damaging pathogen for aerobic rice Apo [182] . It was reported that rice yield in untreated plots was 0. 

DSR is susceptible to various diseases, and rice blast is the most common [24] . Damage due to rice blast increases under water stress conditions [23] ; processes such as liberation and germination of spores and infection in rice that were causing blast are affected by the water level [106] . The crop microclimate, especially dew deposition, is affected by water management, making the environment congenial for host susceptibility [192, 197] . As influenced by water management, the changes in crop physiology also trigger host susceptibility [23] . In aerobic rice, blast resistance is the foremost important trait for breeding programs in Brazil [29] .

A few other diseases and insect problems reported in DSR are sheath blight and dirty panicle [178] , brown spot disease and planthoppers [197] , and soil-borne pathogenic fungus Gaeumannomyces graminis var. graminis in Brazil without additional irrigation [181] .

Compared to PTR, DSR is more prone to lodging [200] . Lodging makes crop harvesting difficult. It also reduces yield and impairs the quality of rice both in terms of appearance and taste [130, 200] . Rice cultivars with lodging-resistant characteristics like intermediate plant heights, large stem diameters, thick stem walls, and high lignin content should be preferred and promoted [124] . Moreover, it has been observed that a wider band of sclerenchyma at the periphery of the stem [184] and more vascular bundles [34] make the cultivars more resistant to lodging. In addition, lower positioning of panicles in the plant's canopy is associated with increased lodging tolerance [88, 200] . Hill seeding, lodgingresistant cultivars, optimum N dose, seeding rates, seeding depth, and method can help overcome lodging [104] . Hill seeding is efficient because lodging resistance depends on the number of panicles in a hill and many panicles in hill-seeded rice.

The decline in yield has been reported in direct-seeded rice [110, 242] . It may be due to various reasons viz., soil sickness [241] , plant autotoxicity [43, 52, 97, 157] , presence of G. graminis var. graminis in dry-DSR [181] , and continuously growing DSR for more than 2 years [53] .

DSR has excellent potential in South Asia, but its performance has not reached its full potential due to the lack of a proper production technology package. The essential prerequisites for a successful DSR and some recommendations for a successful crop are discussed in detail in the coming sections.

Good field preparation is the starting point of DSR. Proper land preparation facilitates good and uniform crop establishment, aids in uniform water control and good drainage, reduces the amount of irrigation water needed, increases the area of cultivation due to fewer bunds, better input use efficiency (water, nutrients and agrochemicals), increases crop productivity, and helps in controlling weeds [95, 96, 121, 190, 207] . Lantican [121] observed the correlation between DSR yield and precision of land leveling in the Philippines. They estimated an average yield loss of 0.9 t/ha due to deficiency in land leveling, which results primarily from water stress in areas not leveled.

Studies conducted by the Rice-Wheat Consortium of the Indo-Gangetic Plains (RWC) showcased a widespread problem of poor leveling in South Asia [95] . Considerable variability of 8-15 cm in field level is observed due to traditional leveling in Indo-Gangetic Plains. This results in poor crop establishment of rice because of unequal water distribution in soil profile and inundation of newly germinating seedlings [73] . Laser-assisted precision land leveling was introduced in 2001 as a pioneer for alternative tillage and crop establishment methods in the region. It ensures better crop establishment by allowing planters/drills to place seed at a uniform distance and depth [96] , resulting in consistent crop stand, precise water control, and enhanced herbicide use efficiency [39] .

Optimum plant density with uniform crop emergence is crucial for attaining good yields in DSR. Good crop establishment depends on many factors, viz., soil type, seedbed preparation, sowing date, seed rate and seed preparation, planting machinery used, and depth of seeding. The soil type recommended for the direct-seeded crop is medium to heavy textured soils because it suffers from iron deficiency in light soils, which can cause significant yield losses [104] . The seedbed should be free of weeds and precisely leveled at sowing. To treat a herbicide such as a paraquat or glyphosate, it is necessary to knock down any existing annual or perennial weeds. Sowing time varies from location to location. In northern India, rice is grown during the Kharif season before the onset of the monsoon. The optimum time for sowing DSR is about 10-15 days before the onset of monsoon [73, 102, 116] . In general, seeding time for DSR should be as close as possible to the time of nursery sowing for the PTR.

Seed priming has been reported to show positive effects on the emergence, yield, and quality of dry direct seed rice [57, 58, 81] . It also improves stand establishment under variable field conditions. Seed priming techniques were tried for improving germination and crop performance of dry-DSR [125] . Various treatments included hydro-priming, water hardening, and Osmo-hardening with KCI. It was observed that mean germination time reduced and improved germination index, seedling vigor index, and germination energy. Hydro-priming was the best treatment, followed by water hardening, in improving seedling growth, leaf area index, panicles m −2 , and grain yield of dry-DSR. Early literature shows a high-speed rate of up to 200 kg/ha to grow DSR crops [78] . The reason may be to suppress weeds or poor germination conditions, low germination percent, damage due to rats, insects, and birds. However, based on trials in IGP, the optimum seed rate is 20-25 kg/ ha for medium-fine-grain rice cultivars with 20 cm spacing between the rows and 5 cm spacing within rows [73, 76] . For basmati rice in Punjab, India, seed rates of 30, 40, and 50 kg/ha were evaluated by Sudhir-yadav [227] , and they found that the seed rate of 30 kg/ ha yielded the highest. For accurate and precise seeding, the crop can be drilled using a multi-crop planter with a seed-metering system (e.g., inclined plate, cupping system, or vertical plates) [73, 76] . Various seed drills used for direct seeding (viz., conventional seed cum fertilizer drill, zero till drill, inverted T-tyne zero-till seed-cum-fertilizer drill, vertical plate metering mechanism, and inclined plate metering mechanism) and machines with inclined plate metering mechanism are most suitable for DSR. These machines help maintain row to row and seed to seed spacing with negligible breakage. Seeding depth is critical for all varieties of rice. After pre-sowing irrigation, the sowing depth for dry DSR should be 2-3 cm and 3-5 cm for DSR to maximize uniform CE. As sowing is done during peak summers, it is essential to have enough moisture during the germination period to avoid moisture stress [73, 236] .

Water management at all crop growth stages is crucial, viz., seedling emergence, active tillering, panicle initiation, and flowering. Proper water management, especially during the crop establishment phase (first 7-15 days after sowing), is crucial in dry drill-seeded rice [16, 114] . To avoid seed rotting, the soil must be kept moist but not saturated from sowing to emergence. After sowing in dry soil, it is essential to provide flush irrigation to wet the soil if it is unlikely to rain, then saturating the field at the three-leaf stage [28] . This practice will ensure good rooting and seedling establishment and enhance the germination of weeds. Therefore, early weed control with an effective pre-emergence herbicide will be possible to check weed emergence and growth.

Precise land leveling is essential for the uniform spread of water and easy drainage, which is needed during the CE phase of dry-DSR. When water control and drainage are poor, the crop is likely to fail due to submergence in the early stage. Bund management also plays an important role in maintaining uniform water depth and limiting water losses via seepage and leakage [121, 240] . The bunds must be prepared as soon as possible after sowing, including compacting and plastering any holes or cracks. After CE, the following four broad water management options are available: (1) continuous flooding; (2) frequent irrigation, that is, DSR with safe alternate wetting and drying (AWD), which involves flooding the field with shallow depth (5 cm) and reirrigating a few days after water disappearance; (3) infrequent irrigation where scarcity of water limits rice yields; and (4) no irrigation under rainfed conditions [87] .

Given the aim of achieving high yields of dry-DSR with less water, option 2 is preferred, but this is subject to the availability of irrigation water. Like CT-TPR, dry-DSR can also be irrigated using safe AWD to economize in water use. However, knowledge regarding optimal soil water status to implement safe AWD in dry-DSR is still limiting. Nevertheless, farmers and researchers provide many anecdotal reports indicating that a safe AWD irrigation interval in dry-DSR is longer than that in CT-TPR because of less soil cracking in the former than in the latter [87] .

In a 6-year study on sandy-loam soil conducted in Modipuram, India, it was observed that dry-DSR could be irrigated safely at the appearance of soil hairline cracks [22, 69] . This study recorded an average savings of 9% irrigation water when irrigation took place on the appearance of soil hairline cracks. Another study conducted by Sudhir-Yadav [228, 229] in Punjab, India, on clay loam soil observed 33-53% irrigation water saving in dry-DSR with AWD compared with CT-TPR without compromising grain yield. Moreover, dry-DSR with residue mulch would require appropriate irrigation scheduling and water management as residue mulch would influence evaporation, infiltration, and transpiration very differently from conventional practice. A climate-smart approach for water management under different crop establishment methods is crucial to reduce water footprint in agriculture [134] .

The success of DSR depends mainly on effective weed management, especially the integrated approach -that targets different phases of the weed cycle, as a single method may not provide adequate control and long-term sustainability. Integrated weed management (IWM) is pivotal for effective and sustainable weed control in dry-DSR [185, 186] . IWM can be categorized broadly into (a) cultural, (b) mechanical, (c) chemical, and (d) biological methods for weed control.

Hand weeding to control weedy rice can be very effective for minimizing the infestation of weedy rice, especially if it is performed after the seedling stage because weedy rice can be more easily identified than rice cultivar. It is usually taller, has more tillers, and its leaves have different colors. However, this method has its disadvantages: it is a slow, tedious, and time-consuming process, which may also induce damage to rice seedlings and mistaken removal of rice seedlings. It has been estimated that 150 to 200 labor days/ha are required to keep rice crops free of weeds, and then its economic profitability directly depends on the labor cost [101] .

Proper land preparation and tillage helps in reducing weed infestation. Precise land leveling helps in better crop establishment [96] and controlling weeds through precise water control and improved herbicide efficiency [39] . It can reduce weed population up to 40%, labor requirement for weeding purposes by 75%, and weeding cost by 40% [190] . Tillage determines the vertical distribution of weed seeds in the soil profile, which affects seedling establishment that depends on seed predation, seed dormancy, seed longevity, and the potential of seedlings to emerge from a given depth [38] . Therefore, when weed load is high and control is suboptimal, conventional tillage may be a more suitable option as it can bury weed seeds below the germination zone and reduce weed problems. Zero tillage can be helpful at places where annual weeds (which reproduce primarily by seeds) are prevalent, assuming that reduced tillage does not increase weed seed production. In the case of perennial weeds, which reproduce vegetatively or through underground tubers, e.g., sedges weeds can be controlled by a non-selective herbicide such as glyphosate before crop planting. Often, land leveling is overlooked as an option for managing weeds, but it can be crucial. Therefore, more work in this area is required to clarify the exact role of land leveling in weed dynamics and composition.

The stale seedbed technique can decrease weed seed bank from the soil where a particular cropping system is followed year after year. This could be very useful in IGP, where rice-wheat is the major cropping system. It depletes 5-10% of weed seeds present in soil [207] . In this technique, single irrigation is applied 15 days before rice sowing to facilitate weed germination and emergence. After that, soil moisture is maintained at an optimum level. A nonselective herbicide (glyphosate or paraquat) or mechanical method kills emerged weeds. This helps reduce weed emergence and the number of weed seeds in the soil seed bank [185, 186] . Singh [218] reported that the stale seedbed technique in DSR reduced weed density by 53% over control. Chauhan and Johnson [37] observed better weed control when the stale seedbed technique was used with paraquat and zero-till because weed seeds placed deeper than 1 cm do not emerge. In large-scale farmer participatory trials in India, combined use of stale seedbed and pendimethalin gave effective control of weeds in DSR [222] . However, the economic impacts of the stale seedbed technique are ambiguous because delayed planting shortens the season and reduces the yield [74] . Moreover, it has adverse effects on the environment since it requires fuel energy, water, and herbicide.

Applying mulch on soil is another way of controlling weeds in DSR. Mulching has multiple benefits, viz., conserves moisture, suppresses weeds, prevents soil erosion, adds organic matter to soils, improves soil health, and decreases fluctuations in diurnal temperature [183] . Water savings of about 20-90% were achieved from mulching done in China and India [245] . Mulches suppress weeds by providing a physical obstruction to germinating weeds [141, 142, 144] , blocking sunlight, and releasing allele-chemicals in the soil [42, 248] .

Kumar [115] reported that problematic weeds of DSR such as Echinochloa crusgalli, E. colona, Dactyloctenium aegyptium, and Eclipta alba were sensitive to wheat straw when used as mulch. Singh [219] also found that wheat residue mulch of 4 t/ha reduced the emergence of grass weeds by 44-47% and of broadleaf weeds by 56-72% in dry drill-seeded rice. This reduction in weed emergence resulted in 17-22% higher grain yield hence economic returns in mulched plots compared to control. Crop residue retention has also been advocated in the intensive rice-wheat system in the region because of increasing concern about decreasing soil organic matter and environmental pollution caused by the burning of crop residues [76] . Straw mulch from previous crops and post-emergence herbicides could be a promising strategy to control weeds in direct-seeded rice. Combining straw and plastic mulches with the direct-seeded rice system will help achieve the desired targets. Instead of straw burning that leads to soil health degradation and environmental pollution, residue recycling offers organic matter build-up and temporal improvement in soil health [132, 137] . This brings in the concept of circularity also in rice production systems.

In DSR, brown manuring with Sesbania can be another good option to control weeds, improve soil health, and yield higher. Sesbania is a legume used as green manure in rice cultivation either as pre-rice or inter or mixed crop with rice [218] . Seeds of Sesbania are sown at 25 kg/ha together with rice. When it is about 30-40 cm tall, after 25-30 days of growth, it is killed with 2,4-D ethyl ester at 0.50 kg/ha to produce brown manure.

Nawaz [152] evaluated five different rice-wheat cropping systems and found brown manuring with Sesbania in DSR decreased weed density by 41-56% and weed biomass by 62-75% sole DSR. Sesbania co-culture reduced broadleaf and grass weed density by 76-83% and 20-33%, respectively, and total weed biomass by 37-80% compared with a sole rice crop [219] .

Sesbania followed by 2,4-D was more effective in suppressing broadleaves and sedges and less effective on grasses. Therefore, to further enhance the effectiveness of this technique, it is recommended to use pendimethalin as a pre-emergence herbicide to overcome the problem of grasses, which is otherwise difficult to control.

Other benefits of Sesbania co-culture include atmospheric nitrogen fixation and crop emergence in areas where soil crust formation is a problem [73, 218] . Despite all these benefits, Sesbania co-culture may pose risks of competition with rice if 2,4-D applications are delayed due to continuous rain or ineffective, hence increasing the cost of production. Moreover, some herbicides may also kill Sesbania. Sesbania co-culture may limit herbicide use and positively impact soil nitrogen build-up.

Weed-competitive cultivars can be a low cost but effective strategy to get higher yields and economic returns [4] . Varieties having good mechanical strength of coleoptile for rapid germination and higher seedling vigor to compete with weeds are best suited for direct seeding [94, 256] .

Better developed roots, high leaf area index, and tillering capacity were associated with weed suppressive rice cultivars [63] . Gealy and Moldenhauer [70] reported that weed-suppressive rice cultivars have twice root biomass than those of non-suppressive types. Due to higher root biomass and root proliferation, weed-suppressive cultivars competed better for resources with weeds and reduced weed loss by 44% and weed prevalence by 30% compared to non-suppressive cultivars [70] . PR 115 variety of coarse rice and Pusa Basmati 1121, Punjab Mehak 1, CSR 30, Pusa basmati 1, and Taraori basmati varieties are most suitable for direct seeding basmati rice in Haryana and Punjab.

Crop rotation can be one of the most promising strategies in weed management if the crop rotation system design is based on sound agronomic knowledge, as weed population density and biomass production can be reduced significantly using a temporal diversification scheme [162] . By changing the cropping system, weed flora shifts, due to which some weeds disappear and new weeds emerge. Crop rotation helps to diversify weed management programs, decreasing the selection pressure that supports the dominance of a few weedy species in a given field [154] . Change in composition of weeds, weed density, and weed dry weight when rice-wheat cropping sequence is changed was studied by Singh [216] . They recorded minimum weed density in rice-wheat-green gram sequence followed by rice-wheat, rice-chickpea, and rice-pea sequence.

Changing rice-wheat rotation also helps in the identification of weedy rice. Singh [214] reported that by rotating rice with soybean, mungbean, Kharif maize, or cotton, weedy rice could be controlled because other herbicides and cultural practices can be used which otherwise are not used in rice. Chokkar [41] reported that introducing potato and pea in between rice and wheat could also improve weed control without herbicide applications. The results from a 2-year experimental study done by He [82] showed that increasing agricultural diversity through rotations, particularly potato-rice rotation, significantly increased rice production's social, economic, and ecological benefits.

Cover crops can be planted when the main crop is not cultivated and become part of a rotation system. They reduce weed proliferation during fallow; indeed, thick cover crop stands to compete well with weeds during the cover crop growth period and reducing light transmittance to weed seeds prevents most germinated weed seeds from completing their life cycle and reproducing. Another possible advantage is that some cover crops may also improve soil fertility through nitrogen fixation, reducing synthetic fertilizers [207] .

When rotation sequences include crops that differ in planting and maturation dates, competitive and allelopathic characteristics, and associated management practices (e.g., tillage, cultivation, mowing, and grazing), weeds can be confronted with an unstable and frequent inhospitable environment that prevents their proliferation. Crop rotation is based on growing a series of different types of crops in the same area in sequential seasons. The planned rotation may increase to a few years or even more extended periods. Farmers usually do not follow one specific crop rotation plan. They choose alternate crops based on their requirements, possibilities, environmental conditions, and budget. By rotating the rice crop with other crops, such as soybean or cotton, it breaks the cycle of the weedy rice seeds. Such a method is widely used by rice farmers in Asia and Brazil, where HR rice varieties are widely grown [11] .

Although crop rotation is efficient, sustainable, and consistent with the bioeconomy, its adoption remains lower than expected [82, 176] . Two main reasons explain this situation. On the one hand, monoculture requires fewer farm implements, knowledge, and practical experience and is more straightforward than crop rotation. Moreover, some countries, e.g., Malaysia, are not self-sufficient in rice production; then, arable lands are reserved and monocropped with rice to ensure food security [191] . On the other hand, the impacts of crop rotation on economic returns are not clearly established. They depend on the time horizon (short-vs. long-term), how the rotation is organized (crop, pasture, fallow), the market price of the crops that rotated, and the various costs incurred to produce these crops. Crop rotation involves risk as in crop rotation, investing in a season consists of the input of much money to buy different seedlings of the various crops to be planted. In addition, pests and diseases from other crops can spread and infect more crops. There is also the risk of a specific crop yield not being successful. Improper implementation can cause much more harm than good. It is obligatory crop diversification because crop diversification also requires investment in different planting techniques for each unique crop that costs time and money. After all, each crop needs a different type of attention. Another limitation is that specific locations and climates are more favorable for monocultures. Other crops cannot grow well within that particular type of temperature and soil conditions other than that particular crop.

Some studies conclude that compared to monoculture, economic returns are lower in the short term (e.g., 176], while others demonstrate that crop rotation significantly increases rice's social, economic, and ecological benefit production [82] . These various conclusions show that even though crop rotation is a well-known and long-used method for maintaining or increasing crop yields, more research is needed to understand factors affecting its economic impacts and weed demography in different rotation systems.

Controlling weeds through any physical activity that hinders the growth of weeds comes under mechanical control.

Mowing is removing or cutting shoots of weeds by using a sickle or mower.

It successfully controls annual weeds while less practiced in perennial weeds because they have stored food in below-ground parts (rhizomes, stolons) and come in several flushes. Mowing must be done before flowering or seed setting to prevent the dispersal of seeds. Weed thus obtained should be buried deep or burnt to remove the viability of weed seeds [129] .

In most situations, relying only on the manual wedding is not economical or practical. The mechanical methods control weeds and yield at par with chemical control, provided they are correctly done. Mechanical weeding is not practiced in IGP due to labor and economic constraints. In DSR, rotary weeders and cono weeders for mechanical weeding have been effective in controlling weeds. Rao [185, 186] and Singh [218] have reviewed manual and mechanical methods of weed control. Singh [213] reported from Pantnagar, India, that pendimethalin at 1.0 kg/ha along with farm waste as mulch (7.5 t/ha) supplemented with one hand weeding (HW) at 45 DAS decreased weed count, weed biomass with highest weed control efficiency (91.3%) which was comparable with HW thrice at 30, 60, and 90 DAS (farmers' practice).

Labor scarcity, high labor wages, and the demand to raise yield and maintain profit on a limited land base have been the major drivers for farmers to seek alternatives to manual weeding. Herbicides are one such alternative. Effective weed management practices are essential in DSR culture, with herbicide application seemingly indispensable [15] . The trend for increased herbicide use has been reinforced by the spread of DSR [153] . Chemical control measures are generally more focused on the early stage of weed emergence and growth when weed control is more accessible. Once weeds become big, they are difficult to control [19] . In dry direct drill-seeded rice, the "critical period" of weed competition has been reported to be 15-45 days after seeding [185, 212, 253] . If weeds are suppressed effectively during this period, minimal yield losses occur. It is crucial to select the right herbicide depending upon the weed flora present in a given field. In addition, the right rate, timing, and application techniques should be used.

Preplant/Burndown Herbicides. Preplant/burndown herbicides control existing annual and perennial weeds before rice sowing, especially under the ZT system. Glyphosate 0.5-1.0% by volume and paraquat 0.5% by volume are recommended for burndown application [76] . Glyphosate is a systemic nonselective herbicide, and it controls most annual and perennial weeds. To be effective, it should be applied when weeds are growing actively so that the herbicide is absorbed and translocated into the entire plant system. For the same reason, grazing of fields should be avoided. Light irrigation before spraying glyphosate is recommended in a situation where the weeds are under stress. Paraquat is a nonselective contact herbicide, and it should be used in fields infested with annual weeds. This herbicide should be avoided when areas are infested with perennial weeds.

Different pre-emergence herbicides are used to control weeds in India's direct-seeded rice. Pendimethalin, oxadiargyl, and pyrazosulfuron have been reported as effective pre-emergence herbicides to control weeds in dry direct-seeded rice [73, 76, 185, 218] . Good soil moisture is essential for the activation of pre-emergence herbicides. Some common preemergence herbicides used in DSR are pendimethalin, butachlor, oxadiargyl, pyrazosulfron, penoxsulam, pretilachlor, thiobencarb, flufenacet, anilofos. These herbicides, along with recommended dose, are listed in the table. Singh [220] evaluated three pre-emergence herbicides pendimethalin 1.0 kg/ha, butachlor 1.0 kg/ha, and oxadiargyl 0.09 kg/ha and found weed density after application of these herbicides were 10-13, 15, and 16-23 plants/ m 2 , respectively, compared to 51 plants/m 2 in weedy check at Taraori location. Kaur [105] evaluated seven pre-emergences (pendimethalin 0.75 g/ha, butachlor 1.50 kg/ha, thiobencarb 1.50 kg/ha, anilofos 0.375 kg/ha, pretilachlor 0.75 kg/ha, oxadiargyl 0.09 kg/ha, and pyrazosulfuron-ethyl 0.015 kg/ha) herbicides for their efficacy against weeds in DSR.

In DSR, more than one flush of weeds occurs during crop duration. Pre-emergence herbicides gave effective control during the early stage of crop growth and post-emergence herbicides during the second flush of weeds. If weeds are not controlled properly, they can cause a significant qualitative and quantitative loss in grain yield. A single herbicide cannot give effective weed control throughout the crop growth period, so sequential herbicide application is made. Some common post-emergence herbicides used in DSR are bispyribac-sodium, fenoxaprop-p-ethyl, ethoxysulfuron, chlorimuron-ethyl, metsulfuron-metyl, and acifluorfer, 2,4-D. These herbicides, along with recommended dose, are listed in the table. Continuous use of a single herbicide on a long-term basis should be avoided; rather, it should be rotated with another herbicide with a different mode of action to prevent/delay resistance development. Tank mixtures of herbicides can be used when two or more herbicides are compatible with broadening the weed control spectrum so that each herbicide controls the weeds missed by the other one Table 1 .

In countries where DSR is widely adopted, herbicide use increased steadily, resulting in resistance in weeds against certain herbicides. Selective control of weedy rice was never achieved satisfactorily with herbicides, such as the application of non-selective herbicides before and after the emergence of weedy rice, but before planting rice. Indeed, the application of pre-emergence (antigerminative) herbicides provides weedy rice control, but it is phytotoxic if applied less than 15 days before crop sowing. Moreover, the physiological similarity of weedy rice to cultivated rice makes it challenging to use post-emergence herbicides in rice fields. Rather than an IWM, herbicide-resistant (HR after that) rice technologies offer opportunities for selective control of weedy rice [36, 50, 71, 214] . Two nongenetically modified herbicide-resistant rice cultivars are commercialized; the Clearfield rice and the Provisia rice systems, both developed by BASF, were launched in the early 2000s and 2018.

Clearfield rice is a group of cultivars that encompasses imidazolinone-resistant rice (IMI-rice). Imidazolinone is a broad-spectrum group of herbicides that can be applied pre-or post-emergence. It inhibits some enzymes (ALS) involved in producing amino acids when applied. Without the latter, the plant cannot synthesize proteins and slowly dies. Since Clearfield adoption from the early 2000s (e.g., in the USA, Europe, Brazil, and Malaysia), weedy rice infestation has decreased, and increases in rice production have been reported, for instance, up to 50% in Brazil [131] . In Malaysia, this system introduced in 2010 has increased yield production by 5 to 8 times [138] . HR weeds are an ongoing challenge worldwide, and Provisia™ Rice System provides a tool to weedy rice becoming resistant to the Clearfield technology. The system allows farmers to safely apply the broadspectrum Provisia herbicide for post-emergence control of a wide range of weeds, including weedy rice. It complements the Clearfield production system for rice because farmers can rotate different herbicide modes of action for sustainable management of resistant rice types and annual grasses. However, weedy rice -as most weeds -evolves to become herbicide-resistant, according to the usual "treadmill of herbicide resistance." Since weedy rice is now resistant to Clearfield, it will inevitably become resistant to Provisia in the future [50] .

Studies have shown that rice plants and weeds also compete through allelopathy. Kato-Noguchi [103] identified 3-hydroxy-β-ionone and 9-hydroxy-4-megastigmen-3-one as main allelochemicals in Kartik-shail and BR 17, two high-yielding rice cultivars of Bangladesh. The allelopathic potential of 111 rice cultivars on weeds in the Philippines was studied by Olofsdotter [157] who reported that the dry weight of weeds reduced up to 34% after 8 weeks of seeding. The reduction in weed's dry weight is due to allelochemicals released by these rice cultivars [158] . The allelopathic potential of many rice cultivars like BR17 against Echinochloa crusgalli and E. colo-num had already been reported in various studies [59, 60, 93] . Several rice cultivars through the release of allelochemical had been found to suppress predominant weeds of rice, such as E. crus-galli [97, 198] , Cyperus difformis [198] , and Sagittaria montevidensis [198, 199] .

Seal and Pratley [198] evaluated the allelopathic multi-weed suppression of 27 different rice cultivars against five major aquatic weeds of Australia and found that cultivar Amaroo inhibited Alisma-taceae weeds by an average of 97%, whereas Echinochloa crus-galli was inhibited by 72%.

Not much work is done in India to exploit the rice's allelopathic property for weed control in DSR. Cultivars with improved allelopathic potential can be developed, competing better with weeds and lowering herbicides' dependence. So, there is a broad scope to identify, develop, and exploit cultivars with higher allelopathic potential in proper cropping systems.

It can be summarized that the components of integrated strategies for weed control in DSR are crucial for the adoption and scaling of this technology in South Asia.

The Sustainable Rice Platform (SRP 2015) is a multi-stakeholder partnership (established in 2011 and co-convened by UN Environment and the International Rice Research Institute) to promote resource-use efficiency and sustainability both onfarm and throughout the rice value chain. It is developing a range of tools to promote sustainable rice cultivation, including standards [225] related to priorities defined in a set of 12 performance indicators [226] .

Standards are based on 41 requirements under eight significant themes: integrated pest management (IPM). The latter includes one provision (no. 18.1) about weed management, which impacts 4 of the 12 performance indicators: profitability, productivity, biodiversity, and food safety. Requirement no. 18.1 "weed management" lists standard preventive weed control methods and the conditions for appropriate use of herbicides that all belong to what is usually called IWM. The SRP Standard seeks to encourage IWM that combines preventive weed control actions and punctual curative weed control actions when preventive methods are not effective on their own [225] . Preventive control methods help manage conditions to avoid weed build-up and include resistant varieties, crop rotation, or intercropping. Curative weed control methods help treat weed build-up and can consist of mechanical control, biological control, and chemical control (e.g., synthetic herbicides). Herbicides are used only if and when action thresholds are exceeded, and the severity of the weed is expected to cause significant damage or loss.

Not much work on fertilizer management has been done for DSR than CT-PTR. Due to aerobic conditions and alternate wet and dry cycles, there is less availability of several micronutrients such as Zn and Fe and other nutrients including N [179] . Also, nitrogen losses are higher in dry-DSR than in CT-PTR due to nitrification/denitrification, volatilization, and leaching [46, 150, 175, 211] .

General recommendations for NPK fertilizers are similar to those in PTR, except that a slightly higher N (22.5-30 kg/ha) dose is suggested in DSR [69] . This is to balance the higher losses and lower availability of N from soil mineralization at the early stage and the longer duration of the crop in the main field in dry-DSR. Earlier studies conducted in Korea indicated that 40-50% more N fertilizer should be applied in dry-DSR than in CT-TPR [170, 255] , although higher N application also leads to disease susceptibility and crop lodging. Split applications of N are recommended to maximize grain yield, increase N uptake, and reduce N losses. It ensures the supply of N to match crop demand at critical growth stages. Since more N is applied in dry-DSR than in CT-PTR and losses are higher, more efficient N management for dry-DSR is needed.

Slow-release (SRF) or controlled-release N fertilizers (CRFs) offer options to reduce N losses because of their delayed-release pattern, which may match crop demand in a better way [206] . The one-shot application also reduces the labor cost. CRF improves N use efficiency and yield compared to untreated urea [61] , but their use is limited because of their high cost. They are four to eight times costlier than conventional fertilizers [204] .

Split application of K has also been suggested for direct seeding in medium-textured soil [177] . Deficiency of Zn and Fe is more common in aerobic/non-flooded rice systems than in flooded rice systems [202, 208, 210, 223a, 44, 163, 254, 216] . Therefore, micronutrient management is critical in dry-DSR. A total of 25-50 kg/ha zinc sulfate is recommended [5] [6] [7] [8] [9] . For iron, it has been observed that foliar application is superior to soil application [6] [7] [8] [9] 45 ].

Due to the early maturity of DSR, it gives the chance to include an additional crop in the system, which can help economically and help in crop rotation and improve soil fertility and help reduce weeds. As far as the circular economy is considered, DSR harvest can reach markets about 15 days early. This market can give incentives to reuse post-harvest products like straw, husk, and bran, adding value to the circularity. Instead of burning the straw, it can be used, which farmers usually burn to clear land for the next crop. This will help reduce carbon dioxide emissions and preserve soil microbiology. So, it is a win-win situation both for farmers and the environment. These crop residues can be used to produce, for instance, new bio-fertilizer through composting new materials for healthy buildings and energy (e.g., biofuels). The rice, duck, and fish-integrated farming is another wellknown system for which circular principles are present. All agricultural practices, such as tillage, pesticide application, harvesting, threshing, can potentially be concerned by the circular economy. Weed management in rice that should easily fit the sustainability criteria and the circularity principles but require additional research and development. Bioherbicides seem to be a sustainable option to fulfill the circularity principle. Eco-friendly, costeffective DSR package offers sustainable rice production systems with fewer resources and low emissions.

This study identified that DSR is feasible both technically and economically compared to PTR. Moreover, with proper conservation and management strategies, DSR adoption will likely increase in the coming future, provided weed control in DSR, especially the control of weedy rice, should be at the center of any strategy aiming to improve the sustainability of rice production in the long run. Eco-friendly, cost-effective DSR package offers sustainable rice production systems with fewer resources and low emissions.

A few important conclusions that have emerged from this review are as follows.

• First, DSR is a more resource-efficient, climate-resilient, and sustainable alternative agricultural system, but many agronomic DSR practices have become inefficient because of the lack of mechanization, precision application, and proper education. So, adopting adequate management practices is very important. • The primary bottleneck experienced with direct seeding is the infestation of weeds.

Pre-emergence and post-emergence herbicides can be vital in controlling weeds, but environment friendlier weed control methods must be sought and substantially reduce the cost of weed management for farmers. Techniques like stale bed technique, mulching, crop rotation, Sesbania co-culture, seed priming, and systematic weed monitoring program will help to reduce weeds. However, a single weed control method is not viable, so an integrated approach based on climatic conditions, edaphic factors, and weed flora are critical. Furthermore, given the drawbacks associated either with IWM or the use of herbicide-resistant rice varieties, development of competitive and allelopathic rice varieties for increased rice competitiveness must be targeted. • The selection of a proper cultivar is very crucial. As DSR is aerated rice, dry and wet conditions responsive rice varieties should be promoted. • Poor stand establishment is another hindrance in the wide-scale adoption of DSR. More practical seed priming techniques can help to solve the issue. • Effective management strategies, well-developed biotechnological and genetic approaches, and a better understanding of pest and disease dynamics will help resolve blast and root-knot nematode infestation in DSR [136] . • New resource conservation technologies (RCTs) like laser land leveling, short-duration cultivars, irrigation scheduling based on soil matric potential (SMP), crop diversification and raised bed planting should be recommended based on sites and soils.

• On the research front, new and improved rice varieties suitable for DSR are required.

• Despite many integrated approaches, additional research on weed management, especially weedy rice control, is required for comprehensive spectrum weed control. • More efforts are needed to study the nutrient dynamics in soils under DSR as the availability of micronutrients, mainly Fe and Zn, reduces DSR. Also, research is required on soil ecology in rice soils. • According to the climatic edaphic factors and resources available locally, there is a need to develop a site-specific package of production technologies for different rice production systems. Anticipatory research and development strategies need to be framed for a place where DSR will be practiced. • To combat higher N 2 O emissions in DSR, there is a need to monitor GHG emissions.

However, not many studies quantify the emissions and study the combined effect of all three GHGs (CO 2 , CH 4 , and N 2 O) in rice systems. Therefore, baseline data to develop better management strategies is lacking. Furthermore, more approaches like nitrification inhibitors and deep urea placement can be worked out to reduce the emissions hence, global warming.

• Intense convincing has to be done to the various stakeholders in rice production. They include the policymakers and farmers. Their understanding of the benefits will enhance its wide spread. Another green revolution in direct-seeded rice with better management techniques is the need of the hour.

Author Contribution All the authors contributed to the review paper. The first draft of the manuscript was written by Anjali, and all the authors commented on previous versions of the manuscript. All the authors read and approved the final manuscript.

Funding Author Anjali gets funding from Union Grants Commission (UGC) as a research fellow. The authors have no relevant financial or non-financial interests to disclose.

Data Availability Not applicable.

Code Availability Not applicable.

Ethics Approval Not applicable.

Consent for Publication Not applicable.

The author declares no competing interests.

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Weedy rice and the sustainability of alternative establishment methods

On the sustainability of direct-seeded rice

Agronomic practices and biotechnological methods dealing with the occurrence, dispersion, proliferation and adaptation of weedy rice (Oryza sativa f. spontanea)

Sustainability, efficiency and circularity of weedy rice management strategies

On-farm strategies for reducing water input in irrigated rice: case studies in the Philippines

Differences in weed vegetation in response to cultivating methods and water conditions in rainfed paddy fields in northeast Thailand

Genetic diversity of seed dormancy and molecular evolution of weedy red rice, theses and dissertations

More rice, less water Integrated approaches for increasing water productivity in irrigated rice-based systems in Asia

Mechanisms and control of percolation losses in irrigated puddled rice fields

1978) I. Growth inhibition due to continuous cropping of dryland rice and other crops

Evaluation of the aerobic rice technology: three years of experiments in the Philippines. Internship Thesis, Plant Production Systems (WUR)

The red queen in the corn: agricultural weeds as models of rapid adaptive evolution

Opportunities to manipulate nutrient-by-water interactions in rainfed lowland rice systems

Soil redox and pH effects on methane production in a flooded rice soil

Mitigating greenhouse gas emissions from ricewheat cropping system in Asia

Directseeded rice culture in Sri Lanka: lessons from farmers

Utilization of allelopathy for weed management in agroecosystems

Phosphorous dynamics in acid soils that undergo alternate flooding and drying

Performance of direct-seeded basmati rice in loamy sand in semiarid subtropical India

Effect of water management on dry seeded and puddled transplanted rice. Part 2. Water balance and water productivity

Maharashtra Chamber of Commerce and Industry and Rice Exporters Association of Pakistan

Yield and nitrogen use efficiency of permanent bed rice-wheat systems in northwest India: effect of N fertilization, mulching and crop establishment method

Establishment of dry seeding cultivation method. Annual Research Report 1993 (Rice). National Crop Experiment Station

Developing selection protocols for weed competitiveness in aerobic rice